201
ECOMMUNAUTÉ FRANÇAISE DE BELGIQUE ACADÉMIE UNIVERSITAIRE WALLONIE-EUROPE UNIVERSITÉ DE LIÈGE - GEMBLOUX AGRO-BIO TECH BEEF CATTLE SYSTEMS IN THE CONTEXT OF SUSTAINABLE AGRICULTURE IN BAC KAN PROVINCE, THE NORTHERN MOUNTAINOUS REGION OF VIETNAM Thi Huong Trà HOÀNG Dissertation originale Présentée en vue de l’obtention du grade de Docteur en Sciences agronomiques et Ingénierie biologique Membres du Jury Monsieur le Professeur BAUDOIN J. P., Président Messieurs les Professeurs LEBAILLY Ph., Promoteur VU CHI Cuong, Co-Promoteur (National Institute of Animal Sciences, Vietnam) BURNY Ph., Membre DOGOT, T., Membre THEWIS A., Membre VU DINH Ton, Membre (Hanoi University of Agriculture, Vietnam) - 2011 -

BEEF CATTLE SYSTEMS IN THE CONTEXT OF SUSTAINABLE ...bictel-fusagx.ulg.ac.be/ETD-db/collection/... · (2011). Beef cattle systems in the context of sustainable agriculture in Bac

  • Upload
    others

  • View
    3

  • Download
    0

Embed Size (px)

Citation preview

Page 1: BEEF CATTLE SYSTEMS IN THE CONTEXT OF SUSTAINABLE ...bictel-fusagx.ulg.ac.be/ETD-db/collection/... · (2011). Beef cattle systems in the context of sustainable agriculture in Bac

ECOMMUNAUTÉ FRANÇAISE DE BELGIQUE

ACADÉMIE UNIVERSITAIRE WALLONIE-EUROPE

UNIVERSITÉ DE LIÈGE - GEMBLOUX AGRO-BIO TECH

BEEF CATTLE SYSTEMS IN THE CONTEXT OF SUSTAINABLE

AGRICULTURE IN BAC KAN PROVINCE,

THE NORTHERN MOUNTAINOUS REGION OF VIETNAM

Thi Huong Trà HOÀNG

Dissertation originale

Présentée en vue de l’obtention du grade de

Docteur en Sciences agronomiques et Ingénierie biologique

Membres du Jury

Monsieur le Professeur BAUDOIN J. P., Président

Messieurs les Professeurs LEBAILLY Ph., Promoteur

VU CHI Cuong, Co-Promoteur (National Institute of Animal Sciences, Vietnam)

BURNY Ph., Membre

DOGOT, T., Membre

THEWIS A., Membre

VU DINH Ton, Membre (Hanoi University of Agriculture, Vietnam)

- 2011 -

Page 2: BEEF CATTLE SYSTEMS IN THE CONTEXT OF SUSTAINABLE ...bictel-fusagx.ulg.ac.be/ETD-db/collection/... · (2011). Beef cattle systems in the context of sustainable agriculture in Bac

Copyright. Aux termes de la loi belge du 30 juin 1994 sur le droit d'auteur et les droits

voisins, seul l'auteur a le droit de reproduire partiellement ou complètement cet ouvrage de

quelque façon et de quelque forme que ce soit ou d'en autoriser la reproduction partielle ou

complète de quelque manière et sous quelque forme que ce soit. Toute photocopie ou

reproduction sous autre forme est donc faite en violation de ladite loi et de ses modifications

ultérieures.

Page 3: BEEF CATTLE SYSTEMS IN THE CONTEXT OF SUSTAINABLE ...bictel-fusagx.ulg.ac.be/ETD-db/collection/... · (2011). Beef cattle systems in the context of sustainable agriculture in Bac

Thi Huong Tra HOANG. (2011). Beef cattle systems in the context of sustainable

agriculture in Bac Kan province, the northern mountainous region of Vietnam. (PhD Thesis).

University of Liege – Gembloux Agro-Bio Tech, Gembloux, Belgium. 183 P., 47 Tabl., 42

Fig.

Summary:

Among livestock types, beef cattle production is ranked as a very important sub-sector in the

extremely harsh natural conditions characterising the northern uplands of Vietnam, where

ethnic minorities are often concentrated on land resources which are not hospitable to crops.

To help local people to escape from poverty, many organisations have initiated development

projects featuring beef cattle production, but it still remains under-developed, hence the

generally high level of poverty faced by farmers.

Thus, the study aims to assess the characteristics and appropriateness of beef cattle feeding

systems, which are compared from the point of view of sustainability.

Stratified sampling was used to select 97 households within free-range, part-time grazing, and

cut-and-carry feeding systems, which were surveyed in Bac Kan province between 2007 and

2009. The collection of field data was implemented using various survey instruments such as

structured questionnaires and interview guides. Data processing consisted in descriptive

statistics, correlations between the variables, and the calculation of socio-economic indicators.

Based on the sample surveyed, the differences between the three systems of cattle

management were highlighted.

Access to grazing land and its topography, the ethnicity of the communities, the relative

importance of agricultural and forest production, and opportunities for off-farm employment

were all factors influencing the cattle systems. Those using the “cut-and-carry” fodder system

are practicing the most efficient husbandry style among the systems from both the social and

economic points of view, except for lack of proper management and use of cattle manure.

Manure use for cultivation in this system was limited because of the predominantly steep

slope lands and the habits of the indigenous peoples. Animal manure utility was evaluated as

less important in the cut-and-carry system compared to other systems practiced in the

lowlands.

However, good prospects are seen to improve conditions in the rural uplands in the future.

Thus, different strategies should be implemented to fill the gap and improve the position of

farmers. The study derives helpful recommendations for farmers keeping beef cattle to

strongly develop their production, alleviate poverty, and improve their livelihoods.

Page 4: BEEF CATTLE SYSTEMS IN THE CONTEXT OF SUSTAINABLE ...bictel-fusagx.ulg.ac.be/ETD-db/collection/... · (2011). Beef cattle systems in the context of sustainable agriculture in Bac
Page 5: BEEF CATTLE SYSTEMS IN THE CONTEXT OF SUSTAINABLE ...bictel-fusagx.ulg.ac.be/ETD-db/collection/... · (2011). Beef cattle systems in the context of sustainable agriculture in Bac

Thi Huong Tra HOANG. (2011). Le système de l’élevage bovin non laitier dans

l’agriculture durable dans la province de Bac Kan dans la région montagneuse nord du

Vietnam (thèse de doctorat in anglais). Université de Liège – Gembloux Agro-Bio Tech,

Gembloux, Belgique, 183 P., 47 Table., 42 Fig.

Résumé :

Parmi les productions animales, l’élevage bovin représente une filière-produit très importante

pour les zones montagneuses nord du Vietnam où les minorités ethniques sont souvent très

présentes et où les ressources foncières ne sont pas compatibles avec l’agriculture. Pour aider

les populations locales dans la lutte contre la pauvreté, de nombreuses organisations ont initié

des projets de développement axés sur les productions bovines. Toutefois, ces zones restent

sous-développées et les éleveurs sont souvent dépourvus.

Dans ce contexte, notre recherche s’est fixée pour objectif de caractériser, de comparer et

d’évaluer les systèmes d’alimentation des bovins du point de vue de la durabilité.

Un échantillon stratifié composé de 97 exploitations a été constitué avec des éleveurs en libre

parcours, en pâturage partiel et en affouragement. Ces exploitations localisées dans la

province de Bac Kan ont été enquêtées de 2007 à 2009. Les données ont été récoltées sur le

terrain au départ de différentes enquêtes réalisées avec des questionnaires semi-structurés et

des guides d’entretien. L’analyse des données a eu recours à la statistique descriptive, à

l’analyse des corrélations entre variables et au calcul d’indicateurs socio-économiques. Sur la

base des enquêtes, des différences entre les trois systèmes d’élevage bovin ont pu être mises

en évidence.

L’accès aux pâturages et la topographie, l’ethnicité, l’importance relative des productions

agricoles et forestières et les possibilités d’emplois extra-agricoles sont tous des facteurs qui

influencent les systèmes. Le système d’affouragement représente le mode d’élevage le plus

performant lorsque l’on envisage les retombées sociales et économiques, mais il est

relativement limité pour la gestion et l’utilisation des effluents d’élevage en raison de sols à

forte pente et des habitudes des populations. Le recyclage des matières organiques est moins

performant dans ce système lorsqu’on le compare aux systèmes adoptés dans les terres basses.

En conclusion, il semble se dégager des perspectives intéressantes pour l’élevage bovin dans

les zones rurales montagneuses. Toutefois, différentes stratégies doivent être adoptées afin de

réduire les écarts de pauvreté et d’améliorer la compétitivité des éleveurs. L’étude propose

des recommandations pour les exploitants qui pratiquent l’élevage bovin afin qu’ils renforcent

les performances de cette filière, luttent contre la pauvreté et améliorent leurs conditions de

vie.

Page 6: BEEF CATTLE SYSTEMS IN THE CONTEXT OF SUSTAINABLE ...bictel-fusagx.ulg.ac.be/ETD-db/collection/... · (2011). Beef cattle systems in the context of sustainable agriculture in Bac
Page 7: BEEF CATTLE SYSTEMS IN THE CONTEXT OF SUSTAINABLE ...bictel-fusagx.ulg.ac.be/ETD-db/collection/... · (2011). Beef cattle systems in the context of sustainable agriculture in Bac

ACKNOWLEDGEMENTS

I am deeply indebted to many persons who have helped, supported and accompanied me

during the process of working on this dissertation. My greatest debt and special gratitude go

to my promoter, Prof. Dr. Philippe Lebailly, for his invaluable intellectual guidance, support

and continuous encouragement at all stages of my study. He constantly provided scientific

advice and support, and nevertheless gave me the maximal freedom and flexibility to follow

my own ideas and working timetable. I am especially grateful to him for his commitment to

my work, which has enabled me to learn a great deal.

I would like to extend my deep thanks to Assoc. Prof. Dr. Vu Chi Cuong, who immediately

agreed to be the second supervisor and who gave me his support and advice throughout the

study process.

My sincere thanks go to other members of my thesis committee, Prof. Dr. André Théwis,

Prof. Dr. Philippe Burny, Prof. Thomas Dogot, Prof. Vu Dinh Ton for their valuable

comments and advice on the content of the thesis in the different processes to improve its

quality both in language and quality for the final version approved for the public defence.

I am indebted to Dr. Nguyen Tuan Son, Hanoi University of Agriculture for his support in

applying for a PhD scholarship from BTC/CTB and the first phase of the pre-doc study as

local promoter; however, we were unable to continue our partnership due to his very busy

schedule.

I am grateful to Prof. Dr. Frank Heidhues, University of Hohenheim, Germany, who

immediately agreed to advise me on the direction my thesis should take and its content, thus

opening up my view for the study. A special thank-you goes to my friends, Dr. Dominic

Smith, Technical Advisor in International Market Development and Investment JSC (MDI)

Company cum Senior Technical Advisor in Helvetas Vietnam, and Dr. Do Anh Tai, Thai

Nguyen University, Vietnam. Their moral support always encouraged me, as did our fruitful

discussions and the comments they made during the writing process of this dissertation. I

would also like to express sincere thanks to Dr. Le Quang Bao, ETH University, Switzerland,

for his reference documents and valuable advice on the methodology of sustainable

assessment by using the multi-criteria analysis approach. I would like to show a deep

gratitude to help from Mr. David Rorke, Rorke Translation and Interpreting Co. LTD,

Vietnam for his edition to improve my thesis not only in languages but also in the quality.

My thesis would not have been complete without the warm help and support of the farmers

and local authorities in Nghien Loan commune, Cong Bang commune, Pac Nam district and

Bac Kan province, who were so kind and generous in giving their time and patient in helping

me during my field visits. I cannot help thinking of my interpreters, Ms. Thuan in the Nghien

Loan commune and Ms. Nhung in Cong Bang commune who helped me during the fieldwork

and for giving me insight into Tay and H’Mong cultures.

I also wish to give many thanks to all of the members of the Department of Economics and

Rural Development – Gembloux Agro-Bio Tech – University of Liege for their friendship and

help, especially Mrs. Nadine Stoffelen, chief secretary, and Ms. Anne Pompier, assistant

secretary, with administrative support, and Ms. Christine Fadeur, assistant secretary who

assisted me in searching reference materials. There are numerous other people who

accompanied me during the process of writing my dissertation. In particular, I would like to

convey my special thanks to Dr. Brigitte Duquesne for her great help at the first phase of

studying, which contributed to enhancing the quality of the final work. I want to express my

Page 8: BEEF CATTLE SYSTEMS IN THE CONTEXT OF SUSTAINABLE ...bictel-fusagx.ulg.ac.be/ETD-db/collection/... · (2011). Beef cattle systems in the context of sustainable agriculture in Bac

gratitude for the mental support to edit its first draft from Mr. Olivier Machiels and for the

thorough statistics check done by Ms. Eléonore Horge.

I would like to convey my sincere thanks to Belgian Technical Cooperation (BTC/CTB) for

its financial support for my study in Belgium as well as field visits in Vietnam.

I would like to express my thanks to the board of directors of the National Institute of Animal

Sciences (NIAS), Hanoi, Vietnam, for their support that helped me to continue studying. I

would also like to thanks to Prof. Dr. Le Viet Ly, formal Vice Director of the NIAS for his

valuable encouragement and advice in the progress of the study. I am in debt of his help.

I cannot help thinking of my close friends for their encouragement and help during my study.

Without their sincere friendship, my study in Gembloux would have been very difficult.

I am greatly indebted to my parents, my brothers and sister for their warm love, support, and

encouragement during my study. This thesis is the loving dream of my father, to whom I

would like to dedicate it as a present as he enters his eighties. I am so indebted to my mother-

in-law who cared for my children during my study, without whose help I would never have

finished my study. I cannot adequately express the depth of my appreciation and love for my

dear husband, Pham Huu Hung, my closest friend and confident, and my darling daughters, Y

Nhi and Da Quynh, who have stuck with me, encouraging me throughout the long time I was

away studying in Belgium. You are all my love!

Page 9: BEEF CATTLE SYSTEMS IN THE CONTEXT OF SUSTAINABLE ...bictel-fusagx.ulg.ac.be/ETD-db/collection/... · (2011). Beef cattle systems in the context of sustainable agriculture in Bac

ABBREVIATIONS

ANOVA Analysis of Variance

asl. above sea level

DST Bac Kan’s Department of Sciences and Technology

CPRGS Comprehensive poverty reduction and growth strategies

EBA Employment Based Analysis

FMD Foot-and-mouth disease

GDP Gross Domestic Product

GDVC General Department of Vietnam Customs

GM Gross Margin

GSO Vietnam General Statistic Office

Ha Hectare(s)

HH Household(s)

ILRI International Livestock Research Centre

km Kilometre

LUC Land Use Certificate

M Mean (Average value of a variable)

MARD Ministry of Agriculture and Rural Development

mil. Million

N Number of samples (sample size)

NIAS National Institute of Animal Sciences

NMR Northern Mountainous Region

Num. Number

PCR Bac Kan Party Committee Report

PSO Bac Kan Provincial Statistic Office

RPR Residue-to-Product Ratios

Sig. Significance (P value)

SPSS Statistical Package for the Social Sciences

TFP Total Factor Productivity

TLU Tropical Livestock Unit

U.S. United States of America

VND Vietnamese Dong

Page 10: BEEF CATTLE SYSTEMS IN THE CONTEXT OF SUSTAINABLE ...bictel-fusagx.ulg.ac.be/ETD-db/collection/... · (2011). Beef cattle systems in the context of sustainable agriculture in Bac
Page 11: BEEF CATTLE SYSTEMS IN THE CONTEXT OF SUSTAINABLE ...bictel-fusagx.ulg.ac.be/ETD-db/collection/... · (2011). Beef cattle systems in the context of sustainable agriculture in Bac

TABLE OF CONTENTS

1 INTRODUCTION .................................................................................................... 1

1.1 BACKGROUND ............................................................................................. 1

1.2 STATEMENT OF PROBLEMS ...................................................................... 3

1.2.1 Competition with the dairy cattle sector ......................................................... 3

1.2.2 Imported cattle products .................................................................................. 3

1.2.3 Development trend of beef cattle markets’ products in Vietnam ................... 4

1.2.4 Cattle production on smallholder farms and sustainable agriculture .......... 6

1.2.5 Cattle production in Bac Kan province, in Vietnam’s NMR ......................... 7

1.2.6 The problems in a nutshell .............................................................................. 8

1.3 RESEARCH QUESTIONS AND OBJECTIVES OF THE STUDY ................. 8

1.4 HYPOTHESES AND METHODOLOGY ........................................................ 9

1.5 STRUCTURE OF THE THESIS ..................................................................... 9

2 BIBLIOGRAPHY .................................................................................................. 11

2.1 CONCEPTUAL FRAMEWORK OF SUSTAINABLE AGRICULTURE AND CATTLE PRODUCTION SYSTEMS ............................................................ 11

2.1.1 Sustainability of agricultural systems ........................................................... 11 2.1.1.1 Definition of sustainable development ...................................................................... 11 2.1.1.2 Sustainability of an agricultural system ..................................................................... 12 2.1.1.3 What is a sustainable farming system? ...................................................................... 12

2.1.2 Livestock production system ......................................................................... 14 2.1.2.1 Definition of a livestock production system ............................................................... 14 2.1.2.2 What is a sustainable livestock production system?.................................................. 16

2.1.3 Beef cattle production in the context of sustainable agriculture ................. 18 2.1.3.1 Development of beef cattle production and economic efficiency ............................. 18 2.1.3.2 Development of beef cattle production and social solidarity .................................... 20 2.1.3.3 Development of beef cattle production and environmental sustainability ............... 20

2.1.4 Beef cattle production and poverty alleviation ............................................. 22

2.1.5 Beef cattle production systems in the Northern Mountainous Region of

Vietnam .......................................................................................................... 23

2.1.6 Concept of the study ...................................................................................... 24

2.2 GENERAL DESCRIPTION OF THE RESEARCH SITES AND THEIR CHARACTERISTICS ................................................................................... 27

2.2.1 An overview of the Northern Mountainous Region of Vietnam ................. 27

2.2.2 General introduction to Bac Kan province .................................................. 30

Page 12: BEEF CATTLE SYSTEMS IN THE CONTEXT OF SUSTAINABLE ...bictel-fusagx.ulg.ac.be/ETD-db/collection/... · (2011). Beef cattle systems in the context of sustainable agriculture in Bac

ii

2.2.2.1 Geography, population and climate conditions in Bac Kan ....................................... 30 2.2.2.2 An introduction to the agricultural sector in Bac Kan province ................................. 33

2.2.3 Description of Pac Nam district and its characteristics ............................... 43 2.2.3.1 General information ................................................................................................... 43 2.2.3.2 Cattle markets and cattle resources in Pac Nam district ........................................... 46

3 RESEARCH METHODOLOGY ............................................................................ 51

3.1 SELECTION OF STUDY SITES .................................................................. 51

3.1.1 Geographical situation of the selected communes ....................................... 51

3.1.2 Population and land resources ..................................................................... 53

3.1.3 Agricultural sector in the selected communes.............................................. 55

3.1.4 Forest development in the selected communes and its orientation ............. 55

3.1.5 Off-farm activities, infrastructure, and water source ................................. 56

3.2 TARGET GROUP SELECTION................................................................... 57

3.2.1 Selection of cattle farming households......................................................... 57

3.2.2 Selection of stakeholders in cattle markets and cattle marketing chains .... 57

3.2.3 Selection of other target groups .................................................................... 57

3.3 STUDY FRAMEWORK ................................................................................ 58

3.4 CONCEPTUAL MODEL OF COLLECTING AND ANALYSING DATA ...... 58

3.4.1 Data collection and data sets ......................................................................... 59 3.4.1.1 Selection of PRA tools ................................................................................................ 59 3.4.1.2 Structured questionnaire ........................................................................................... 59 3.4.1.3 Difficulties and challenges in accessibility to selected households and collection of data ................................................................................................ 62

3.4.2 Identification of criteria in cattle production ............................................... 64 3.4.2.1 Livestock in general and cattle production ................................................................ 64 3.4.2.2 Feeding resources ...................................................................................................... 64 3.4.2.3 Disease and losses ...................................................................................................... 65

3.4.3 Identification of costs and returns from cattle production .......................... 65 3.4.3.1 Production costs ......................................................................................................... 65 3.4.3.2 Product identification ................................................................................................ 67

3.4.4 Selection of indicators in the influence assessment

of cattle feeding system .................................................................................. 68 3.4.4.1 Economic viability and efficiency ............................................................................... 68 3.4.4.2 Social solidarity .......................................................................................................... 70 3.4.4.3 Environmental stability .............................................................................................. 71

3.4.5 A sustainable reference system ..................................................................... 72

3.4.6 Proposed data analyses ................................................................................. 73 3.4.6.1 Descriptive statistics and frequency analysis ............................................................. 74 3.4.6.2 Comparison among systems ...................................................................................... 74 3.4.6.3 Correlation analysis .................................................................................................... 74 3.4.6.4 Farm size and herd size classification......................................................................... 74

Page 13: BEEF CATTLE SYSTEMS IN THE CONTEXT OF SUSTAINABLE ...bictel-fusagx.ulg.ac.be/ETD-db/collection/... · (2011). Beef cattle systems in the context of sustainable agriculture in Bac

iii

3.4.6.5 Influence assessment approach of sustainable agriculture ....................................... 75 3.4.6.6 Assessment of the cattle trading and marketing chain .............................................. 75

4 RESULTS AND DISCUSSIONS .......................................................................... 77

4.1 CHARACTERISATION OF SELECTED HOUSEHOLDS IN DIFFERENT BEEF CATTLE FEEDING SYSTEMS ......................................................... 77

4.1.1 An introduction to the cattle feeding systems in the study area .................. 77 4.1.1.1 Cut-and-carry system ................................................................................................. 78 4.1.1.2 Free-range system ...................................................................................................... 79 4.1.1.3 Part-time grazing system ........................................................................................... 79 4.1.1.4 Historical development of the selected beef cattle systems ..................................... 80

4.1.2 General socio-economic characteristics of selected households in the

systems ........................................................................................................... 83 4.1.2.1 Family size, labour source and education .................................................................. 83 4.1.2.2 Off-farm activities ...................................................................................................... 86 4.1.2.3 Land resources and farm size ..................................................................................... 87 4.1.2.4 Cropping and forest activities .................................................................................... 89 4.1.2.5 Livestock production systems .................................................................................... 95 4.1.2.6 Analysis of the economic efficiency of livestock production ..................................... 99 4.1.2.7 Analysis of the economic efficiency of farm and non-farm activities ...................... 102

4.1.3 Resource flow in smallholder households and cattle production .............. 104

4.1.4 Section summary ......................................................................................... 105

4.2 CHARACTERISATION OF SELECTED CATTLE FEEDING SYSTEMS .. 107

4.2.1 Characteristics of cattle production in selected systems ............................ 107 4.2.1.1 Reasons for keeping cattle ....................................................................................... 107 4.2.1.2 Cattle breed and herd size classification .................................................................. 108

4.2.2 Management of cattle production in cattle feeding systems ...................... 110 4.2.2.1 Feed resources and grass production ...................................................................... 110 4.2.2.2 Reproductive performance and breeding management of cattle ........................... 117 4.2.2.3 Veterinary services and cattle losses ....................................................................... 121 4.2.2.4 Cattle shelters and hygiene conditions .................................................................... 123

4.2.3 Other issues for the developing smallholder farm cattle production ........ 124 4.2.3.1 Credit issues in livestock production and cattle development ................................ 124 4.2.3.2 Role of extension services and other organisations in cattle production ................ 125

4.2.4 Brief description of trading cattle in the study sites ................................... 125

4.2.5 Section summary ......................................................................................... 128

4.3 COMPARISON AMONG BEEF CATTLE PRODUCTION SYSTEMS ON THE DIMENSION OF AGRICULTURAL SUSTAINABILITY .................... 130

4.3.1 Analysis of the economic efficiency of cattle production in cattle feeding

systems ......................................................................................................... 130 4.3.1.1 Analysis of production costs .................................................................................... 130 4.3.1.2 Analysis of cattle gross return .................................................................................. 134 4.3.1.3 Net cattle income among the three systems ........................................................... 135 4.3.1.4 Fattening cattle in the cut-and-carry system ........................................................... 136 4.3.1.5 Analysis of selected economic indicators in cattle feeding systems ........................ 137

Page 14: BEEF CATTLE SYSTEMS IN THE CONTEXT OF SUSTAINABLE ...bictel-fusagx.ulg.ac.be/ETD-db/collection/... · (2011). Beef cattle systems in the context of sustainable agriculture in Bac

iv

4.3.2 Analysis of the social solidarity of cattle production in cattle feeding

systems ......................................................................................................... 139 4.3.2.1 Analysis of labour used in cattle production activities among the systems ............ 139 4.3.2.2 Analysis of employment opportunities in beef cattle production systems ............. 140 4.3.2.3 Analysis of gender issues in cattle feeding systems ................................................. 143

4.3.3 Analysis of the environmental stability of cattle production

in cattle feeding systems .............................................................................. 144

4.3.4 Measuring cattle production in the systems in all dimensions

of sustainable agriculture ........................................................................... 148

4.3.5 Section summary ......................................................................................... 149

5 CONCLUSIONS AND RECOMMENDATIONS .................................................. 151

5.1 CONCLUSIONS ........................................................................................ 151

5.1.1 Empirical findings ....................................................................................... 151

5.1.2 Limitations of the study ............................................................................... 153

5.2 RECOMMENDATIONS ............................................................................. 154

6 REFFERENCES ................................................................................................. 157

7 ANNEXES .......................................................................................................... 173

Page 15: BEEF CATTLE SYSTEMS IN THE CONTEXT OF SUSTAINABLE ...bictel-fusagx.ulg.ac.be/ETD-db/collection/... · (2011). Beef cattle systems in the context of sustainable agriculture in Bac

LIST OF TABLES

Table 1: Population of cattle by breed in Bac Kan province ..............................................40

Table 2: Example of differences in lean meat capacity of cattle .......................................49

Table 3: Brief description of all communes in Pac Nam district ........................................52

Table 4: Some key statistical data for the selected communes ........................................53

Table 5: Population, family size, and number of households in the study area in 2007 ....54

Table 6: Major crop production in the selected communes ...............................................55

Table 7: Number of selected households per cattle systems ............................................57

Table 8: Tools and brief information collected in the study ...............................................60

Table 9: Selected indicators and their description ............................................................72

Table 10: General characteristics of beef cattle feeding systems .......................................77

Table 11: Family size and labour force in cattle production systems in 2007 .....................84

Table 12: Off-farm activities and income for the selected cattle feeding systems in 2007 .....................................................................................87

Table 13: Land resources of beef cattle feeding systems in the study area in 2007 ...........88

Table 14: Classification of farm sizes among the cattle husbandry systems in 2007 ..........88

Table 15: Net income analysis of crop production in cattle feeding systems in 2007 ..........93

Table 16: Forest allocation and production in the selected systems ...................................95

Table 17: Number of main livestock types kept per farm household in the different systems ......................................................................................96

Table 18: Description of pig production in the cattle feeding systems (% households) .......98

Table 19: Reproductive performance of sows in the cattle feeding systems .......................99

Table 20: Losses in livestock production (exception for cattle) in selected systems in 2007 ............................................................................. 102

Table 21: Reasons for keeping cattle in selected cattle systems ...................................... 107

Table 22: Cattle herd size and structure in the cattle feeding systems ............................. 109

Table 23: Classification of cattle herd sizes among selected cattle feeding systems ........ 110

Table 24: Feed resources used in selected systems ........................................................ 112

Table 25: Feed shortage seasons and strategies to get through the feed shortage season ................................................................................. 113

Table 26: Grass production in beef cattle feeding systems .............................................. 114

Table 27: Labour spent on different cattle production activities in selected households with or without grass production .................................................... 115

Table 28: Net income analysis of cattle production with and without grass production ..... 116

Table 29: Reproductive performance of cows in the different beef cattle feeding systems ............................................................................................... 120

Table 30: Classifications of cow body condition in selected household ............................ 120

Table 31: Vaccination and disease treatment in selected systems ................................... 122

Page 16: BEEF CATTLE SYSTEMS IN THE CONTEXT OF SUSTAINABLE ...bictel-fusagx.ulg.ac.be/ETD-db/collection/... · (2011). Beef cattle systems in the context of sustainable agriculture in Bac

vi

Table 32: Losses of cattle (economic efficiency) in beef cattle systems in 2007 ............... 123

Table 33: Cattle shelters in selected systems .................................................................. 123

Table 34: Loan issues in different beef cattle systems ..................................................... 125

Table 35: Feeding costs of cattle production in cattle feeding systems (mil. VND/household) ....................................................................................... 131

Table 36: Analysis of total costs of cattle feeding systems (mil. VND/household) ............ 133

Table 37: Correlations between total cattle production costs and selected variables (N = 97) ........................................................................ 134

Table 38: Gross return analysis of cattle feeding systems................................................ 135

Table 39: Correlations between net cattle income and related variables (N=97) .............. 136

Table 40: Analysis of economic efficiency in different cattle feeding systems................... 139

Table 41: Family labour spent on different activities in beef cattle feeding systems ......... 140

Table 42: Analysis of social solidarity in cattle feeding systems ....................................... 142

Table 43: Analysis of return from cattle production per labour day among the systems................................................................... 143

Table 44: Proportion of female working time in comparison to men in selected systems .............................................................................. 143

Table 45: Proportion of women working in different cattle production activities ................ 144

Table 46: Influence of beef cattle feeding systems on environmental stability .................. 147

Table 47: Cattle production losses in the beef cattle systems during the cold outbreak in the early 2008................................................................... 147

Page 17: BEEF CATTLE SYSTEMS IN THE CONTEXT OF SUSTAINABLE ...bictel-fusagx.ulg.ac.be/ETD-db/collection/... · (2011). Beef cattle systems in the context of sustainable agriculture in Bac

LIST OF FIGURES

Figure 1: Conceptual framework for sustainable analysis ..................................................13

Figure 2: A general conceptual model for a livestock production system ...........................14

Figure 3: A general conceptual model for livestock production ..........................................15

Figure 4: Classification of world livestock production systems ...........................................16

Figure 5: Determinants of sustainability .............................................................................17

Figure 6: Schematic representation of the overlapping scope of indicators of ecological, economic, and social aspects of livestock system sustainability .........................18

Figure 7: Relative contribution of biological resources to the global production of CH4 in the atmosphere ...................................................................................22

Figure 8: The development of beef cattle production systems on sustainable agriculture ..................................................................................26

Figure 9: Poverty rate by different ethnic groups in Vietnam .............................................29

Figure 10: Cattle population and cattle meat production in the NMR from 2000 to 2009 ....30

Figure 11: Bac Kan province, Pac Nam district and geographical location of selected communes .........................................................................................................31

Figure 12: Bac Kan population distribution by ethnic groups in 2002 ...................................32

Figure 13: Gross output at constant price 1994 for the agriculture sector ............................34

Figure 14: Land use in Bac Kan province in 2007 ...............................................................35

Figure 15: Areas planted in the main cultivated crops .........................................................36

Figure 16: Gross output of main cultivated crops ................................................................37

Figure 17: Development of livestock population in Bac Kan ................................................38

Figure 18: Total gross output from animal production in Bac Kan ........................................39

Figure 19: Development trend (2005–2008), plan (2006–2015) of the provincial cattle population ..........................................................................................................42

Figure 20: Cattle population by districts during 2003–2008 .................................................43

Figure 21: Land area and its distribution (hectares) for different sectors in 2007 .................44

Figure 22: Cultivation crop and livestock gross outputs in Pac Nam district ........................45

Figure 23: Development of livestock production by species in Pac Nam district ..................46

Figure 24: Structure of land resource in the selected communes in 2007 ............................54

Figure 25: Livestock population in the selected communes in the study area in 2007 .........55

Figure 26: Forest development in the selected communes in the study area in 2007 ..........56

Figure 27: Study framework ................................................................................................58

Figure 28: Procedure for data collection and analysis .........................................................59

Figure 29: Activity worksheet in SWOT analysis of sustainable beef cattle production ........61

Figure 30: Barometer of sustainability - a static representation of the reference system. ....73

Figure 31: Transect description of selected systems and their cropping calendar ...............80

Figure 32: Historical evolution of the cattle feeding systems. ..............................................83

Page 18: BEEF CATTLE SYSTEMS IN THE CONTEXT OF SUSTAINABLE ...bictel-fusagx.ulg.ac.be/ETD-db/collection/... · (2011). Beef cattle systems in the context of sustainable agriculture in Bac

viii

Figure 33: Education level of household heads in the production systems (% of households) .............................................................................................85

Figure 34: Farm land size classifications in selected households in the three systems in 2007 ..................................................................................................................88

Figure 35: Average agricultural land area in the selected systems in 2007 .........................90

Figure 36: Allocation of land areas for major crops in the selected systems in 2007 ...........92

Figure 37: Net income obtained in the major livestock types in selected systems in 2007 ............................................................................. 101

Figure 38: Net household income in the cattle feeding systems in 2007 ............................ 103

Figure 39: Resource flow in selected households for cattle production ............................. 105

Figure 40: Classification of cattle herd size (small, medium, large) in selected households ..................................................................................... 110

Figure 41: Average cattle net income in selected beef cattle feeding systems in 2007 ...... 136

Figure 42: Measuring the sustainability of the different cattle feeding systems .................. 149

Page 19: BEEF CATTLE SYSTEMS IN THE CONTEXT OF SUSTAINABLE ...bictel-fusagx.ulg.ac.be/ETD-db/collection/... · (2011). Beef cattle systems in the context of sustainable agriculture in Bac

1 INTRODUCTION

1.1 BACKGROUND

Vietnam’s ethnic minorities are often concentrated in remote, isolated, and mountainous

zones, and have a low living standard in comparison with the Kinh and Chinese ethnic groups

(van de Walle and Gunewardena, 2001). The poverty rate is extremely high among these

groups (Neefjes and Thanh, 2003). The Northern Mountainous Region (NMR) of Vietnam is

ranked second in poverty just behind the Central Highlands Region. It is estimated that the

poverty rate will remain as high as 37% in the mountainous regions in 2010 (CPRGS, 2003).

The NMR accounted for around 29% of the country’s total rural areas and about 13% of the

national population in 2007 (GSO, 2008). Most ethnic minority people in the NMR are

essentially engaged in the agricultural sector, often facing adverse natural conditions, poor

infrastructure, and a lack of basic resources (Castellas et al., 2002a; Minot et al., 2003).

According to Steinfeld and Mack (1997), livestock production contributes a great deal to rural

development. Livestock husbandry has positive effects on the diet, health, income, financial

security, sustainable crop yields, employment opportunities, and social status of households

(ILRI, 2003). Subsequently, raising livestock is a way to enhance the economic viability and

sustainability of a farming system (Steinfeld and Mack, 1997). The development of livestock

contributes not only to rural growth but also to poverty reduction and livelihood improvement

among the resource-deprived farmers because livestock development often benefits the poor

(de Haan, 1995; Devendra and Thomas, 2002). If livestock husbandry is properly managed, it

will play an important role in alleviating poverty and counteracting environmental

degradation. In addition, well-managed animal production can make agricultural systems in

developing countries more productive and sustainable (ILRI, 2003). The development of the

livestock sub-sector is also considered by the Vietnamese government as one of the main

strategies to achieve poverty reduction (CPRGS, 2003), because it contributed to around 20%

of the total agricultural GDP in 2007 (GSO, 2008), with the aim to contribute to around 32%

in 2010 and 40% in 2020 (Vietnam Ministry of Agriculture and Rural Development - MARD,

2008). Compared to other regions, livestock income accounts for the biggest proportion of

total household income in the NMR (Maltsoglou and Rapsomanikis, 2005). Huyen (2004)

also found that animal husbandry shows a great potential to generate income for households

in the northern mountainous areas in Vietnam. Therefore, the development of animal

husbandry is considered as a promising solution to improve livelihoods for farmers.

Despite the low growth rate of Vietnam’s population compared to other developing countries,

overall population growth in the country means that cultivated land per capita is highly

limited. Thus, the high dependence of farmers on agricultural land is obvious, especially in

the highlands where available land is largely unsuitable for crop growing (Huyen, 2004). This

is seen as a critical factor in environmental deterioration (Ellis, 2000), because the pressure on

land will be very intense in rural areas. The lack of land resources as a vital asset for farmers

also implies that the rural poor tend to be highly dependent on natural resources extracted

from the environment (Ellis, 2000).

Among livestock types, beef cattle production is ranked as a very important sub-sector in

areas subject to extremely harsh natural conditions in mountainous areas where livestock

husbandry is indicated more than crop growing (Beganger and Vissac, 1993). However, in

Vietnam, most cattle are owned by small-scale farmers with limited land (Ly, 1995). It is

recorded that nearly two thirds of households in the rural northern mountains raise cattle

(Maltsoglou and Rapsomanikis, 2005). An indigenous cattle breed—Yellow cattle are

Page 20: BEEF CATTLE SYSTEMS IN THE CONTEXT OF SUSTAINABLE ...bictel-fusagx.ulg.ac.be/ETD-db/collection/... · (2011). Beef cattle systems in the context of sustainable agriculture in Bac

2 Introduction

predominant in Vietnam—are often kept in extensive cattle systems in the MNR. It is

reported that local breeds of livestock are often more adaptable to specific environmental

contexts and weather changes, foodstuff availability and quality, and have desirable

characteristics (Gender in Agriculture, 2009). Although local cattle are well adapted to harsh

environments, their body size is small and their growth rate is low, which are constraints to

their development potential. Cattle production in these zones is distinguished according to

feeding systems, namely free-range, part-time grazing, and cut-and-carry (Nho et al., 2003;

Mui, 2003; Tra, 2007).

In Vietnam, beef production per capita increased considerably, 6.0% annually, from 1.2 kg in

1995 to 2.2 kg in 2009, and subsequently increasing to 2.4 kg in 2007 (GSO, 2010). This was

due to an increase in domestic demand resulting from a gradual increase in capital income and

from the government’s efforts to implement poverty alleviation policies and strategies and

livestock development programmes. Minot et al. (2003) also certify that the main forces

pushing up the demand for livestock products in Vietnam are total population growth and

improved living standards. Nevertheless, this increase was lower than the substantial increase

ratio of total meat production per capita annually in the country (nearly 7.5%) that soared

from around 19.2 kg in 1995 to approximately 40.4 kg per annum in 2009 (calculated from

FAO data, 2010). The demand for meat products is expected to rise by 6-7% in the next five

years (MARD, 2008). However, beef production contributed only a small amount to meat

production (around 6.0% of total meat production in Vietnam in 2009).

During the period 1995-2000, there was a slight increase of the cattle herd countrywide of 0.5

mil. head (from 3.6 mil. head in 1995 to around 4.1 mil. head in 2000). Then a sharp

reduction of the cattle population was recorded the next year, a decrease to 3.9 mil. head in

2001. A sudden increase of cattle population countrywide was recorded between 2002 and

2007 (Annex 1). This was in response to government support policies such as a subsidy for

crossbreeding cattle and for grass production, providing loans and credit, and support for a

breeding selection programme. On the other hand, a considerable decrease of cattle

population countrywide was recorded between 2008 and 2009. This might also be a result of

policies of the Vietnam government that prompted a sharp boost of the cattle herd for several

years but which were not highly sustainable or suitable to the conditions of many regions

where many cattle died, were sold or were otherwise eliminated. Failure of the crossbreeding

programme in Bac Kan is an example illustrating the unfruitful effects of those development

programmes (Tra, 2007). In addition, the economic crisis and outbreaks of diseases such as

foot-and-mouth disease (FMD) are other reasons for this reduction. Nevertheless, the total

cattle herd in Vietnam still increased at a rate of 4.5% annually on average during the last 15

years. A rather similar trend was also recorded in the live weight of cattle countrywide, which

reached a rate of around 8.5% annually (more than doubling from 83,000 tonnes in 1995 to

189,000 tonnes in 2009). Differences between the ratio of the cattle herd increase and live

weight of cattle might be related to imports of beef and dairy cattle for breeding under

national and provincial cattle development programmes as well as growing imports of exotic

breeds, crossbred cattle, and their offspring in many areas. Thus, it can be said that cattle

production tended to develop rather strongly in the country due to government support

policies.

Page 21: BEEF CATTLE SYSTEMS IN THE CONTEXT OF SUSTAINABLE ...bictel-fusagx.ulg.ac.be/ETD-db/collection/... · (2011). Beef cattle systems in the context of sustainable agriculture in Bac

Introduction 3

1.2 STATEMENT OF PROBLEMS

1.2.1 Competition with the dairy cattle sector

Despite its late development, the strong growth of dairy herds in all agro-ecological regions in

Vietnam is considered to be due to the high milk demand, especially in big cities, and strong

support from the government through various policies, especially the priority strategy to close

the gap between production and consumption (Hemme et al., 2006; Luthi et al., 2006).

During the period 1995-2009, there was a sharp rise in dairy cattle herds, from about 22,600

head in 1995 to 115,500 head in 2009. Simultaneously, there was a dramatic increase in milk

production of over 200,000 tonnes (from 65,800 tonnes to 278,000 in the same period) (GSO,

2010). The government provided substantial financial support for the importing of dairy

cattle, for example, from 2001-2005, 10,356 dairy cows were imported into the country. In

addition, many provinces of Vietnam had their own import programme (live dairy cattle and

semen). However, there are no statistical data for the country as a whole on the budget and

number of cattle and doses of semen imported since the government issued its policies

regarding the dairy cattle sector.

It is important to note that there is strong competition between beef cattle production and the

number of dairy animals culled for slaughter as a beef resource for domestic consumers.

According to estimates from MARD (2006), the rate of culling and replacing dairy cows is

around 17% annually. Thus, approximately 20,000 head of dairy cows may be eliminated and

slaughtered for meat in 2009. In addition, only around 80% of dairy heifers are finally

selected to become dairy cows. Thus, it is estimated that over 10,0001 head of dairy heifers

are culled for meat or are raised as beef cattle. Furthermore, the ratio of male to female calves

is around 50/50 out of approximately 50,000 calves. So about 25,000 male calves are born

and are often channelled to the beef market around a week after birth at a weight of

approximately 35-40 kg per head.

1.2.2 Imported cattle products

Over the past decades, beef cattle production in Vietnam has achieved a positive development

trend. There has been a dramatic increase in cattle meat production chiefly due to numerous

support strategies under cattle development programme for the whole country, and this

includes cattle production in Vietnam’s NMR. However, increasing consumer demand,

mainly in urban areas, has required large quantity of imports of beef from outside to fill the

demand shortfall. According to GAIN (2006), Vietnam’s economic development is causing

income per capita to steadily increase, encouraging consumer spending. As a result,

Vietnam’s per capita meat consumption is increasing as well, including a higher demand for

beef. Despite increasing demand, beef consumption per capita is still low. Dac (2002)

indicates that the country is importing a significant volume of high quality meat, especially

high quality beef to meet the high demand for quality. Beef is Vietnam’s highest meat import

and it is expected that beef importing will continue to grow to meet local demand, especially

in big cities due to low domestic cattle and buffalo meat production in the country and limited

resources particularly for grazing (GAIN, 2006).

According to statistical data collected from the General Department of Vietnam Customs

(GDVC, 2010), cattle and buffalo meat imported into Vietnam accounted for around 12% of

1 According to MARD data (2006), around 75% of total dairy cows were serviced, of which around 70% were

successful. There were 70,000 milking cows in 2009 (GSO, 2010).

Page 22: BEEF CATTLE SYSTEMS IN THE CONTEXT OF SUSTAINABLE ...bictel-fusagx.ulg.ac.be/ETD-db/collection/... · (2011). Beef cattle systems in the context of sustainable agriculture in Bac

4 Introduction

total meat imports. Despite the growth of cattle production in the country, the quantity of

imported beef increased sharply by 2,000 tonnes or around USD 10.0 mil during the period

2000-2008 (from 56 tonnes [USD 0.3 mil.] in 2000 to 2,056 tonnes [USD 10.27 mil.] in 2008,

indicating a soaring demand on the part of local consumers, with low and preferential

government tax rates. However, these rapid changes had a serious effect on the cattle and

buffalo population throughout the country because imported frozen beef products were lower

in price and higher in quality than domestic beef products in Vietnam. Therefore, the

government of Vietnam decided to implement quota policies and steeply increase taxes in late

2008, from 12% to 17% (decree 83/2008/QD-BTC), with a further increase in early 2009

from 17% to 33% (decree 52/2009/TT-BTC) in order to support domestic cattle production.

The result was nearly halving the quantity of beef imported in 2009 (only 1,151 tonnes or

USD 6.65 mil.) (GDVC, 2010) (Annex 2).

Further, large numbers of live cattle and buffalo were also imported legally and illegally into

Vietnam from China, Thailand, Laos, and Myanmar. Some 5,700 head of breeding cattle and

buffalo and 47,000 head of fattening animals from Thailand and Lao were registered for

veterinary check by the Department of Animal Health – MARD at the end of 2009

(Department of Animal Health, 2010). According to a survey of Vietnam Economic News

(04/01/2010), around 1,000 head of beef cattle were legally imported from Laos to Vietnam.

Around 90% of cattle in slaughterhouses in the south were sourced from Thailand. On the

other hand, large numbers of live cattle and buffalo were imported illegally through the

borders between Vietnam, Laos, Cambodia and Thailand that might not be recorded and

controlled2. Furthermore, live cattle and buffalo also illegally imported through borders

between China and Vietnam, but there was no record about this. Cattle and buffalo are

routinely imported to Vietnam, which may be due to price differentiation, shortage of cattle

resources, and high Vietnamese consumer demand. Thus, domestic cattle products have to

compete not only with the price of imported cattle products, but also their quality and

quantity. Thus, heavy beef and live animal imports as well as unsustainable cattle

development programme policies impacted negatively on the development trend of beef

cattle, with decreased cattle herd population and meat production on a countrywide scale and

in Vietnam’s NMR. Thus, there are bright prospects for the development of cattle production

on smallholder farms especially in the NMR.

1.2.3 Development trend of beef cattle markets’ products in Vietnam

So far, however, there has been little discussion about development trends of agricultural

products in Vietnam’s modern retail trade, especially on cattle products. In the trend of

developing economies such as Vietnam, transformation of the retail trading structure has

become a central issue for smallholder farms. These rapid changes are having a serious effect

on the trade of agricultural products, including cattle products; especially it will also bring

opportunities for development of beef cattle production.

Schipmann (2010) conducted a study of these changes in modern retail structures in Thailand.

It can be said that the development of modern supply chains will soon find its way into

Vietnam as well as other developing countries. The speed, spatial distribution, and expansion

of modern retail structures are determined by the interplay of various factors including

economic growth, increasing consumer diversification, and ‘the westernization of diet’

(Schipmann, 2010). Maruyama and Trung (2007) argue that the major reasons identified by

Vietnamese respondents for shopping at supermarkets are self-service, guarantee of quality,

2 http://vneconomy.vn/20100104094912563P0C19/thit-trau-bo-ngoai-dang-lan-at-thi-truong.htm

Page 23: BEEF CATTLE SYSTEMS IN THE CONTEXT OF SUSTAINABLE ...bictel-fusagx.ulg.ac.be/ETD-db/collection/... · (2011). Beef cattle systems in the context of sustainable agriculture in Bac

Introduction 5

fixed prices, safe and clean goods, the ability to search for something unique, and a one-stop

service.

In recent years, there has been an increased consumer interest in foods in supermarkets caused

the greater number of supermarkets in Vietnam (Maruyama and Trung, 2007), especially in

Hanoi and Ho Chi Minh City. However, only small quantities of animal meats are sold to

supermarkets, including beef, but a rather large amount of frozen meat is available in

supermarkets in Hanoi (personal observation). Smith and Tra (2008) find that despite the

number of supermarkets in Hanoi, only a small amount of domestic chicken meat is sold in

them. Most chicken products are sold in wet market or fresh-product markets. Thus, domestic

beef is undoubtedly no different with chicken products. However, the role of supermarkets is

growing in Vietnam. The number of supermarkets and shopping malls has increased rapidly,

from only 12 (10 supermarkets and 2 trade centres) in 6 out of 64 cities and provinces in 1995

to 210 supermarkets and 32 shopping malls in 30 cities by late 2004 (Maruyama and Trung,

2007). Reardon et al. (2008) find that supermarkets spring up as a result of consumer demand

(highlighting demand incentives and demand capacity) and supply of supermarket service

(highlighting supply incentive and supply capacity). Similarly, according to Maruyama and

Trung (2007), the increase in supermarkets in the past decade may be due to the following

factors: (i) increases in income; (ii) urbanisation; (iii) consumers are younger and more

knowledgeable; (iv) weakness of traditional markets; (v) support from the Vietnamese

government; and (vi) relaxing of regulations on foreign direct investment and food retailing

since the 1990s. However, their analysis shows that at present, traditional markets remain the

major distribution channels for food products. In the case of fresh food, they verified the

continued dominance of traditional markets in terms of proximity, freshness, and price, which

factors are the main barrier to the development of supermarkets.

Actually, supermarkets are initially established in high-income areas of urban centres. In their

early stages of development, supermarkets emphasise staples and processed products, offering

these products at low prices to attract a broad customer base and thus compete fiercely with

traditional shops (Reardon et al., 2007). By 2002, the supermarket shared around 63% in East

Asia and 33% in Southeast Asia of processed/packaged food in the retail market (Pingali,

2006). Maruyama and Trung (2007) report that in 1999, just 5 years after the first

supermarkets were opened in Vietnam, supermarkets accounted for nearly 20% of purchases

of household products in major cities. Schipmann (2010) discusses that the trends of

supermarket expansion observed nowadays in developing countries reflect the same

development that took place in the retail sector in the U.S. and Europe a few decades ago.

Schipmann (2010) indicates that improved agricultural production systems have to be focused

in order to support smallholders in developing countries and improve their livelihoods;

nowadays, however, it is recognized that efficient production of agricultural products is not an

end in and of itself. Therefore, lucrative markets for produce are needed, and farmers must be

given access to these markets. For farmers, supermarkets are not only a new type of market

outlet, but they are also quite different from traditional markets, as reflected by the products

they offer (product variety and product quality) as well as their procurement systems. Peardon

et al. (2008) discuss that the rapid rise of supermarkets has transformed agri-food markets;

however, those transformations bring in not only potentially great opportunities but also great

challenges. Thus, according to their point of view, development models, policies, and

programmes all must adapt to these changes. Supermarkets aim to attract consumers by

offering a wide variety of products, many of which might not always be found in traditional

markets (Schipmann, 2010). Supermarkets also implement tremendous changes in

procurement systems such as establishing distribution centres, making bulk purchases from

wholesale markets, and implementing contractual arrangements with suppliers (Schipmann,

Page 24: BEEF CATTLE SYSTEMS IN THE CONTEXT OF SUSTAINABLE ...bictel-fusagx.ulg.ac.be/ETD-db/collection/... · (2011). Beef cattle systems in the context of sustainable agriculture in Bac

6 Introduction

2010). In addition, Tisdell (2010) indicates that supermarkets tend to favour a characterised

product and want easy traceability of the products.

Thus, there are different positive impacts of supermarket expansion for farmers: (i) an

additional market outlet for farmers; (ii) farmers benefit from a diversification of their product

portfolio; and (iii) the higher financial benefits can have positive effect on the income of

smallholder farmers (Schipmann, 2010). On the other hand, the additional requirements of

supermarkets are considered a barrier for smallholder farmers: (i) requiring improved

technologies to meet the supermarket’s quality requirements; (ii) smallholder farmers have

difficulties meeting the requirements of improved technologies due to a lack of both capital

and economics of scale; (iii) supermarkets prefer to deal with large-scale farmers, thus

excluding small-scale producers. Although supermarkets do not deal directly with individual

producers, in a new stage of development of supermarkets and hypermarkets, middlemen will

reflect the demand of supermarkets if they want to obtain sales to them (Tisdell, 2010).

Nevertheless, supermarkets that provide various types of products, that continue to add new,

high-quality products at reasonable prices, and that are built near the homes of consumers,

have the opportunity to build store loyalty and to increase market share (Maruyama and

Trung, 2007). On the other hand, Reardon et al. (2008) conclude that over the last five to 10

years, many farms have been driven out of business due to changes in product standards

imposed by modern supply chains and the implied investment in production.

Thus, it could be expected in the next few years or decades, cattle farmers will actively

participate in the modern retail markets, and trade their cattle directly to slaughterhouses, no

longer selling directly to retailers and middlemen acting as intermediaries. Beef products from

slaughterhouses will be largely sold by supermarkets and hypermarkets, although some will

be consumed by markets and shops. Accordingly, a question arises based on the forecast

development of modern supply chains: “How can smallholder cattle farmers successfully are

linked to such modern supply chains in the near future?” According to Haantuba and de Graff

(2008), in order to improve and expand trade linkages between smallholder farmers and

supermarkets, different elements must be emphasised: (i) improving penetration by

smallholder producers; (ii) generating marketable surplus through improvement of production

practices such applying good agricultural practices; and (iii) building credibility. Thus, the

development of beef cattle households in the coming years will have to addresses both

advantages and disadvantages of the development of modern markets in Vietnam.

1.2.4 Cattle production on smallholder farms and sustainable agriculture

Obviously, livestock production in general and cattle production in particular in small-scale

production contributes to society not only in terms of employment opportunities but also in

terms of poverty alleviation, with an overall contribution to economic growth. Thus, livestock

production provides not only diversified products and income, but also year-round

employment. According to a report from Livestock in Development (1999), the development

of livestock will create the potential for the poverty reduction by increasing employment

opportunities for the poor, and will enhance the specific contributions of livestock to

livelihoods of the poor. Similarly, Eguienta et al. (2002) point out that animals can be raised

to provide both meat and employment. The production of beef cattle also provides

employment opportunities in rural, mountainous, and remote areas, where a high rate of

unemployment is recorded, because of the intensive labour requirement for grazing. In

addition, the role of women in livestock production is highly valued, including tethering,

tending, and other tasks.

Page 25: BEEF CATTLE SYSTEMS IN THE CONTEXT OF SUSTAINABLE ...bictel-fusagx.ulg.ac.be/ETD-db/collection/... · (2011). Beef cattle systems in the context of sustainable agriculture in Bac

Introduction 7

Besides social contributions, animal production also forms a major capital reserve for farming

households (Seré and Steinfield, 1996). In poor areas especially, livestock production plays a

very important role as a source of income for smallholders (Epprecht, 2005). Beef cattle on

smallholder farms also play many roles in the economic spectrum. Keeping cattle helps

farmers to increase their income; when combined with other activities, its economic efficiency

also increases (Quan, 2001).

There tends to be a strong mutual antagonism between sustainable development and

environmental protection, in such a way that the poor are often forced to degrade the

environment that they strongly depend on (Ellis, 2000; Taylor, 2001). Their livestock may be

allowed to overgraze grasslands (Ellis, 2000). To profit from animal husbandry, human and

economic pressures can steer livestock production in ways that are detrimental to the

environment (Seré and Steinfeld, 1996). Thus, small subsistence and semi-subsistence

farmers are possibly both victims of and contributors to the un-sustainability. Cattle

production is highlighted as an environmental risk due to releasing methane and other

greenhouse gases. In addition, environmental degradation such as degradation of soil and

erosion can also result from cattle overgrazing.

It is clear that negative effects of cattle production in particular and other agricultural

activities in general hinder the availability of resources over time. Therefore, through proper

management of their resources in a sustainable way, farmers can help to prevent this.

Sustainability is an important criterion in assessing the performance of existing farm activities

and systems (McConnel and Dillon, 1997). In addition, a good understanding of existing

systems is required to recommend improved farming systems (Beets, 1990).

Thus, in order to focus on effective natural resource management in mountainous regions, the

study needs to take a holistic approach, taking into consideration not only livestock systems

and cropping systems but also the environmental and socio-economic context in selected

households (Eguienta et al., 2002). In addition, the production of cattle is affected not only by

internal factors and external factors, but also by animal factors (Skunmun et al., 2001). Thus,

the study is going to treat the issue of sustainability of cattle production systems by focusing

on comparison among cattle feeding systems on the three dimensions of sustainability:

ecological, economic, and social-cultural. It will address the question, if and to what extend

beef cattle production in the mountainous regions, highlighting different cattle feeding

systems, can contribute to these three pillars.

1.2.5 Cattle production in Bac Kan province, in Vietnam’s NMR

Bac Kan is one of the poorest provinces in the NMR. In 2004, around 51% of its population

were ranked as poor, which figure is extremely high compared to the national poverty rate of

the time (19.5%) (Bac Kan Province Annual Report - PAR, 2005; GSO, 2005). Its poverty

level was considerably reduced but still very high in 2007 compared to the national figure

(37% versus 15%) (Bac Kan PAR, 2008; GSO, 2008). Cattle production accounted for an

important proportion in the total gross output of the provincial livestock sub-sector, about

29%, while it accounted for only around 4% on average countrywide in 2005 (Bac Kan

People’s Committee Report - PC, 2006; MARD, 2006). To help local people in the NMR to

escape from poverty, many governmental and non-governmental organisations and

institutions have initiated projects to promote the development of livestock in general and

beef cattle in particular. Modalities for development of cattle production in the NMR have

been promoted as a potential solution to enhance economic growth and livelihoods for

farmers, especially the poor. However, the cattle production sector still remains under-

developed, hence the generally high poverty level of farmers. On the other hand, for the NMR

Page 26: BEEF CATTLE SYSTEMS IN THE CONTEXT OF SUSTAINABLE ...bictel-fusagx.ulg.ac.be/ETD-db/collection/... · (2011). Beef cattle systems in the context of sustainable agriculture in Bac

8 Introduction

including Bac Kan province, certain doubts prevail about the environmental dimension

because the province is among ones prone to climate change impacts. In addition, there is a

serious lack of understanding of how the beef cattle market really works in the province.

Lapar et al. (2003) find that livestock producers in Vietnam do not have an enabling

environment to improve production activities because there is a lack of an organised animal

market system. Furthermore, the need for socio-economic research into institutional

frameworks for the processing and marketing of livestock products is important (PPLPI-

Policy brief, 2004). Thus, there should also be an effort to study and analyse cattle production

in the province and domestic markets for beef cattle products. However, in this study context,

some brief insight into the local cattle markets and marketing chain of beef cattle will be

provided in order to round out sustainable development trends in beef cattle production

systems.

1.2.6 The problems in a nutshell

Both qualitative and quantitative data related to the sustainable impacts of different cattle

production feeding systems are still lacking. Nevertheless, the limited information on the

livestock sector in developing countries in general and in Vietnam in particular can partly be

explained by the complexity of the subject (Seré and Steinfeld, 1996). Although the issues are

complex, livestock production on smallholder farms in Vietnam has been widely studied.

Nevertheless, the comparison of various systems used in the context of sustainable agriculture

development has not yet been investigated so far. Hence, the purpose of the study is to focus

on the comparison influence of the various cattle feeding systems used by different ethnic

minorities in the context of sustainable agriculture and their potential improvement in the near

future. Addressing these issues will bring significant practical recommendations to farmers,

researchers, and policy-makers as they seek to improve rural development in general and beef

cattle sub-sector in particular in the NMR.

1.3 RESEARCH QUESTIONS AND OBJECTIVES OF THE STUDY

The general purpose of this study is to understand how beef cattle production systems in the

NMR can be improved in the short term and sustained in the long term. Thus, a

characterisation is made of the cattle feeding systems, the socio-economic and institutional

issues linked to them, and the point of view of the farmers themselves. A comparative

analysis of the systems and their constraints and opportunities is likewise made. In addition,

the study assesses the sustainable dimensions of cattle farming systems in order to highlight

the influence of beef cattle production sub-sector on the general sustainability of agriculture.

The overall question of the study is: what are positive influences of the cattle production

systems on agricultural sustainability?

In the study, the two main research questions are derived: (i) what are appropriateness of the

beef cattle feeding systems and their influences on agricultural sustainability? And (ii) what

would be the possible development trend of these systems in the NMR of Vietnam?

The study was conducted to achieve the following objectives:

Page 27: BEEF CATTLE SYSTEMS IN THE CONTEXT OF SUSTAINABLE ...bictel-fusagx.ulg.ac.be/ETD-db/collection/... · (2011). Beef cattle systems in the context of sustainable agriculture in Bac

Introduction 9

- To characterise the current situation of selected households among cattle feeding systems;

- To characterise the present state of production in cattle feeding systems, including free-

range, part-time grazing and cut-and-carry;

- To compare among beef cattle production systems on the economic, social and

environmental dimensions in the context of sustainable agriculture, with a strong focus on

social-economic indicators; and

- To formulate recommendations for the development of sustainable cattle production

systems in the Northern Mountainous Region of Vietnam.

1.4 HYPOTHESES AND METHODOLOGY

With the major purpose of contributing to the sustainable development of beef cattle

husbandry in the northern highlands, this study strongly emphasizes the influence of beef

cattle production systems at the small household level and the development trend of cattle

feeding systems in Vietnam’s NMR. Based on the study context as well as the actual situation

of households on the study site, four hypotheses were tested in this study, including:

- Cattle production in selected households is the most important source of income in

livestock production sector, all of cattle feeding systems combined;

- Among beef cattle feeding systems, the cut-and-carry system is the most profitable and

provides the most employment opportunities in the study area;

- All beef cattle feeding systems have positive social and economic influences but a negative

environmental influence as far as the sustainable development of agriculture is concerned

in the study area; and

- Cut-and-carry system is the best suited system, which will exploit future market

development trend of cattle products and highly compatible with natural resources.

This study mentions a range of dimensions for the sustainable development of beef cattle

production. It therefore focuses on qualitative analysis using discourse and text analysis,

descriptive analysis, correlation and comparison of beef cattle feeding systems as core

analytical instruments. As for influencing assessment, the influence of beef cattle production

on social solidarity, environmental stability, and economic efficiency are analysed to

determine which beef cattle feeding systems in the NMR would be sustainable. The study was

conducted in areas where the various cattle feeding systems are in place. In addition, there are

beef cattle markets available on the study sites. Cong Bang and Nghien Loan communes in

Pac Nam district, Bac Kan province, were selected for this study.

1.5 STRUCTURE OF THE THESIS

The dissertation is structured in five chapters. Chapter 1 gives some general introductory

information regarding Vietnam, poor communities in the NMR, along with livestock

production and cattle production. Then it states problems of beef cattle production in Vietnam

in general and Bac Kan province in particular. The chapter continues with objectives and

hypotheses, and also provides a brief introduction of the methodological approaches used in

the study in order to attract initial attention. Chapter 2 of the dissertation opens with a

definition and a conceptual framework of the study. It endeavours to define sustainable

agriculture and explain cattle production in the context of pathways to sustainability and

poverty reduction. It should be noted that the discussion of the agricultural sector, livestock

Page 28: BEEF CATTLE SYSTEMS IN THE CONTEXT OF SUSTAINABLE ...bictel-fusagx.ulg.ac.be/ETD-db/collection/... · (2011). Beef cattle systems in the context of sustainable agriculture in Bac

10 Introduction

production and cattle production sub-sector and their characteristics in Vietnam were

reviewed in the DEA thesis written by the author submitted and approved in 2007; therefore,

this information is not repeated in the study itself, but would be a useful reference during

discussion of the findings. The study site is then introduced and its characteristics are given to

provide insight as to why that area was selected. Chapter 3 of the dissertation is designed to

provide a discussion of research methodology for the study. After reviewing the reasons for

selecting the study sites and describing the communities, the paper goes on to discuss

selection of sample sizes and tools, selection of indicators as well as selection of analytical

instruments for the study. Results and discussions of the study are given in Chapter 4, which

divides into three sections. Section 1 introduces the characteristics of the selected households

and selected cattle feeding systems. Then it analyses crop, forest and livestock production

systems, their economic efficiencies, and linkage among cattle production and resources of

these sub-sectors in the selected households. Section 2 describes in detail the cattle production

systems, including their purpose, production scale, feed resources, breeding and management

and related issues. Section 3 analyses and discusses of the influences of beef cattle feeding

systems on three pathways to sustainable agriculture, including economics, society, and

environment, with strong focuses on socio-economic indicators. Chapter 5 concludes by

summarising the results and drawing conclusions, mentions limitations of the study, and

formulates recommendations for intervention activities to improve cattle production in the

systems.

Page 29: BEEF CATTLE SYSTEMS IN THE CONTEXT OF SUSTAINABLE ...bictel-fusagx.ulg.ac.be/ETD-db/collection/... · (2011). Beef cattle systems in the context of sustainable agriculture in Bac

2 BIBLIOGRAPHY

2.1 CONCEPTUAL FRAMEWORK OF SUSTAINABLE AGRICULTURE AND CATTLE PRODUCTION SYSTEMS

This section explores the conceptual framework of the sustainable development of agriculture

and cattle production systems. It starts with a theoretical approach to sustainable agricultural

systems, including definitions of sustainable development, sustainability of agricultural

systems, and sustainable farming systems. The next section defines livestock production

systems and their pathways on the road to sustainability. Then, it moves to the core issue—

cattle production and its sustainable aspects including social, economic and environmental

issues. In addition, cattle production in the context of poverty alleviation and a description of

cattle systems in Vietnam are also included in this section.

2.1.1 Sustainability of agricultural systems

2.1.1.1 Definition of sustainable development

The term sustainable development means “development that meets the needs of the present

without compromising the ability of future generations to meet their own needs” (World

Commission on Environment and Development – WCED, 1987). Correspondingly, FAO

(1989) also develops one of the most detailed definitions of sustainable development as “the

management and conservation of the natural resource base, and the orientation of

technological and institutional change in such a manner as to ensure the attainment and

continued satisfaction of human needs for present and future generations. Such sustainable

development in the agriculture, forestry and fisheries sectors conserves land, water, plant and

animal genetic resources, is environmentally non-degrading, technically appropriate,

economically viable and socially acceptable”. This definition highlights the objectives of

optimizing benefit from a limited resource, minimizing the environmental degradation

generated by its uses, and regulating the rate of use of given resources over time.

The definition of sustainable development given by the FAO Council (quoted in Garcia,

1996) refers to the need to control: (i) the resource base; (ii) technological change; and (iii)

institutional change.

In addition, such controls are needed to ensure following:

- Satisfaction of human needs for present and future generations;

- Conservation of land, water, plants and animal genetic resources;

- Non-degradation of the environment;

- Use of appropriate technology;

- Economically viable exploitation; and

- Socially acceptable situations.

Sustainable development is the kind of human activities that maintains and continues the

historical fulfilments of the whole community of life (Engel, 1990, cited by Bossel, 1999).

According to Sen (2005), the term sustainable development is indicated into two aspects:

(i) ability to deal with short-term human needs; and (ii) ability to meet long-term social,

economic and ecological sustainability.

Page 30: BEEF CATTLE SYSTEMS IN THE CONTEXT OF SUSTAINABLE ...bictel-fusagx.ulg.ac.be/ETD-db/collection/... · (2011). Beef cattle systems in the context of sustainable agriculture in Bac

12 Bibliography

According to the United Nations’ definition in 1997, development is a multidimensional

undertaking to achieve a higher quality of life for all people, in which economic development,

social development and environmental protection are interdependent and mutually reinforcing

components of sustainable development (UN, 1997). Ness et al. (2007) state that sustainable

development means having to integrate three important dimensions including social

solidarity, economic efficiency and environmental stability. Thus, the development is

sustainable if it encompasses those three pathways.

2.1.1.2 Sustainability of an agricultural system

The characteristics of an agricultural system tend to reflect the characteristics of human

society at large to which the faming system belongs such as human work, social organisation,

technology and culture (Gomiero, 2004). Agriculture is a dynamic, adaptive and evolving

system.

Lewandowski et al. (1999) define sustainable agriculture as the management and utilization of

the agricultural ecosystem in a way that maintains its biological diversity, productivity,

generation capacity, vitality, and ability to function, so that it can fulfil—today and in the

future—significant ecological, economic and social functions at the local, national and global

levels and does not harm other ecosystems. Similarly, a sustainable agricultural system is a

production system that can indefinitely meet the demands for food, fibre and fuel at socially

acceptable economic and environmental costs (Crosson, 1993 cited by Lynam, 1994). The

sustainable development of a system is considered to be possible only if each component

system as well as the total system is viable (Bossel, 1999). According to McConnel and

Dillon (1997), the sustainability of a system means the capacity of that system to maintain its

productivity and/or profitability at a satisfactory level over a long period of time regardless of

year-to-year fluctuations. The concept involves the evaluation of farm activities and systems

in terms of interrelation among their ecological, economic and socio-cultural sustainability

over infinite time. Lewandowski et al. (1999) indicate that sustainable agriculture is the

management and utilisation of the agricultural ecosystem in a manner that maintains its

biological diversity, productivity, regeneration capacity, vitality and ability to function, so

that it can fulfil not only today, but also reach the future significant ecological, economic and

social functions at the different levels, from local to regional and does not damage other

ecosystems.

Similarly, Douglass (1984) cited by Thompson and Nardore (1999) describes three ways to

conceptualise sustainable agriculture: (i) resource sufficiency: the agricultural practice is

sustainable if the resources needed are in hand or foreseen; (ii) ecological sustainability: the

requirement to identify the biological limits to agricultural practice; and (iii) social

sustainability: identifying the political and ethical limits of agricultural systems and practices.

According to Thompson and Nardore (1999), research and policy for sustainable agriculture

should be divided into two paradigms. First, sustainability defined as resource efficiency

means accounting for the rates at which resources are produced and depleted, framing

strategies for conservation, regeneration and substitution for increasingly scarce resources.

Secondly, sustainability defined in terms of production integrity emphasising dynamic system

models of complex ecological and social processes, and system vulnerability to anthropogenic

stress.

2.1.1.3 What is a sustainable farming system?

A sustainable farming system is a system that has no negative trend in total factor

productivity (Lynam and Herdt, 1989). According to Lynam (1994), assessing the

Page 31: BEEF CATTLE SYSTEMS IN THE CONTEXT OF SUSTAINABLE ...bictel-fusagx.ulg.ac.be/ETD-db/collection/... · (2011). Beef cattle systems in the context of sustainable agriculture in Bac

Bibliography 13

sustainability of a farming system is to have a measure of its internal organisation,

management and performance over time. In addition, its external factors also need to be

considered, which could be measured by yield trends, disease build-up or profitability. The

sustainable development of farming systems is also defined as development that meets the

requirement of the farm family for basic needs such as food, fuel-wood and the like without

damaging the resource base, thereby compromising the ability of the future generations to

produce their needs on the same land and using the same resources (Beets, 1990).

Conway (1985) uses the term sustainability as a measure of a system’s function in

profitability, stability, and equitability. The sustainable development of a production system

will exist whenever the relevance of three dimensions including environment, economy, and

society is considered at the same time together (Tisdell, 1996; Becker, 1997) (Figure 1). In

addition, these dimensions will be set in the framework of policy and cultural environments.

Thus, a sustainable farming system should be balanced in the three aspects of environmental

stability, social equitability and economical productivity.

Figure 1: Conceptual framework for sustainable analysis Source: Becker, 1997

Farming systems in general and livestock production systems in particular are components of

an agricultural system hierarchy. An adequate representation of a farming system is required

in a multidimensional approach or multi-criteria approach, where many aspects and levels of

analysis have to be taken into account such as economic, environmental, social, cultural, and

many other perspectives associated with stakeholders, including farmers and consumers

(Gomiero, 2004). Thus, livestock production should not be considered uniquely as a

component belonging to a farming system.

Ethnic/cultural environment

Policy environment

Environmental stability

Su

sta

inab

le

develo

pm

en

t

Susta

ina

ble

D

evelo

pm

ent

Economic

efficiency

Social solidity

Page 32: BEEF CATTLE SYSTEMS IN THE CONTEXT OF SUSTAINABLE ...bictel-fusagx.ulg.ac.be/ETD-db/collection/... · (2011). Beef cattle systems in the context of sustainable agriculture in Bac

14 Bibliography

2.1.2 Livestock production system

2.1.2.1 Definition of a livestock production system

In fact, a livestock production system is a subset of a farming system (Lynam, 1994; Steinfeld

and Mäki-Hokkonen, 1995; Seré and Steinfeld, 1996; Steinfeld and Mack, 1997; Ibrahim and

Olaloku, 2000). Thus, a livestock production system is defined as the combination of

resources, livestock species, techniques, and activities mobilized by a community for a farmer

to convert natural resources into livestock products (Lhoste et al., 1993 quoted by Eguienta et

al., 2002). Traditionally, in Vietnam or in other developing countries, livestock studies have

often been organised on the basis of disciplines such as breeding, nutrition, or experiments in

research stations (Petheram, 1996). Consequently, a livestock farming system is a set of

interacting activities that can be synergetic or competitive including: (i) managed to satisfy

the farmer’s objectives in both the short and long terms; (ii) decided by one level of

management (farmer or family level); and (iii) compatible with the natural environment

(Ibrahim and Olaloku, 2000). The livestock system analysis must, therefore, comprise the

complete farm household system because the livestock production system includes not only

produce marketed outputs and products for home consumption, draught power, and manure

for crop production, but also plays an asset function with important social-cultural roles

(Steinfeld and Mack, 1997).

Figure 2: A general conceptual model for a livestock production system Source: Eguienta et al., 2002

In the context of a farming system approach, Eguienta et al. (2002) present a tight relationship

of indicators among household characteristics, cropping and livestock production systems

(Figure 2). It is important not only to analyse the livestock production itself more precisely,

but also to investigate statistical relationships among variables pertaining to household

characteristics, cropping systems, animal husbandry systems (herd management practices,

Page 33: BEEF CATTLE SYSTEMS IN THE CONTEXT OF SUSTAINABLE ...bictel-fusagx.ulg.ac.be/ETD-db/collection/... · (2011). Beef cattle systems in the context of sustainable agriculture in Bac

Bibliography 15

surveillance techniques and use of hillsides), and performance indicators (herd growth,

mortality, traction needs, household rice self-sufficiency levels). From this analysis, the

authors developed a typology of farmers and examined their common characteristics and

potential trajectories toward new organisational structures or innovative feed production

techniques.

The relationships among factors or agents of livestock production are presented in Figure 3.

Livestock breeds and genetic resources, herd composition, and feeding are the predominant

determinants of an animal husbandry system (Lhoste, 1986 quoted in Ibrahim and Olaloku,

2000).

Figure 3: A general conceptual model for livestock production Source: Modified from Lhoste (1986) quoted in Ibrahim and Olaloku (2000)

According to Seré and Steinfeld (1996), there is the need for an objective assessment of the

key factors affecting sustainability, and to provide a better understanding of the measures to

enhance the positive influences and mitigate possible negative effects of some agricultural

and development practices. Thus, a classification and characterisation of the world's livestock

systems has enabled many studies of livestock-environment interactions by both livestock

systems and impact domains. Therefore, from a regional and global perspective, livestock

production systems should be defined, described and put in a geographic context in order to

identify interactions between livestock and the environment in a system. Hence, a

classification of the world livestock production systems based on a qualitative and

quantitative description in order to contribute to structuring global assessments of the

interactions between livestock and the environment is presented in Figure 4. According to

Steinfeld and Mäki-Hokkonen (1995), the classification criteria of livestock production

system were limited to integration with crops, relation to land and agro- ecological zone. Seré

and Steinfeld (1996) divide livestock production systems into solely livestock production

Page 34: BEEF CATTLE SYSTEMS IN THE CONTEXT OF SUSTAINABLE ...bictel-fusagx.ulg.ac.be/ETD-db/collection/... · (2011). Beef cattle systems in the context of sustainable agriculture in Bac

16 Bibliography

systems and mixed farming systems. In solely livestock production systems, there are landless

livestock production systems and grassland-based systems. In mixed farming systems, there

are rain-fed livestock production systems and irrigated systems. A further classification of

those systems basing on types of livestock and geographical conditions was made. In

addition, livestock production systems may further be classified according to their main

products such as meat, milk or to services such as breeding or draught (Steinfeld and Mack,

1997).

In brief, the objectives of the approach referring to livestock farming system research are to

gain knowledge about farming and livestock systems, and to conduct research that will

provide the information necessary to design interventions for improving the performance of

the livestock production systems and contributing to the sustainable livelihood of the local

people.

Figure 4: Classification of world livestock production systems

Source: Steinfeld and Mäki-Hokkonen (1995); Seré and Steinfeld (1996)

2.1.2.2 What is a sustainable livestock production system?

Thompson and Nardone (1999) state that resources for livestock production are not available

infinitely, while humans and their nutritional needs can be considered infinitely. Furthermore,

the consumption of livestock products will increase steadily, especially in developing

countries, this implying that animal products supplied for human consumption must be

available infinitely. If animal production efficiency is not improved, therefore, the resource

will be harmed or even destroyed. According to Timon (1993), the sustainable development

of animal production poses many challenges: (i) to the primary users of livestock; (ii) to their

extension, research, and support services; (iii) to local and regional development authorities;

(iv) to investment agencies, government policy makers and their institutional organisations;

and (vi) to the consumer or user of animal products.

Page 35: BEEF CATTLE SYSTEMS IN THE CONTEXT OF SUSTAINABLE ...bictel-fusagx.ulg.ac.be/ETD-db/collection/... · (2011). Beef cattle systems in the context of sustainable agriculture in Bac

Bibliography 17

Thus, different elements must be determined (Figure 5) in order to effectively plan a

sustainable livestock development programme or a sustainable animal production system in

broader terms: (i) a comprehensive understanding of the human need to advance development

from individual and communal to national levels; (ii) a thorough analysis of the technical,

economic, and social implications of proposed interventions; and (iii) an assessment of

potential environmental impact (long- and short-term) that may influence local and/or global

conditions (Timon, 1993).

Figure 5: Determinants of sustainability Source: Timon, 1993

Similarly, according to Francis and Callaway (1993), the sustainability of an animal

production system depends on some of the following elements:

- Resource efficiency—most efficient possible use of non-renewable resources and,

whenever possible, substituting local renewable resources from those imported from

outside the farm;

- Profitability—economically profitable in both the short and long term;

- Productivity—maintaining and enhancing the productivity of all basic resources rather than

destroying or degrading them;

- Environmental soundness—minimal negative impacts on both the farm and farm borders;

- Social viability—equitable systems favouring farm owners, contributing to a viable rural

economy, infrastructure and community, and supporting and integrating with society

overall.

According to Barbier (1987) quoted in Payraudeau and van der Werf (2005), to be

sustainable, an activity must be viable from both an environmental and an economical

viewpoint, fair at its economic and social dimensions, and tolerable in its social and

Page 36: BEEF CATTLE SYSTEMS IN THE CONTEXT OF SUSTAINABLE ...bictel-fusagx.ulg.ac.be/ETD-db/collection/... · (2011). Beef cattle systems in the context of sustainable agriculture in Bac

18 Bibliography

environmental aspects. Moreover, sustainable production systems are adjusted to local,

national, and social conditions (Olesen et al., 2000). In addition, various options for achieving

sustainability, through alternative resources generated by research should be considered in

association with socio-economic and institutional issues (Okigbo, 1991). Garcia (1996)

advises that identifying of partially integrated indicators is useful and necessary to indicate

overlapping components of sustainability among eco-biological, techno-economic, and socio-

cultural pathways (Figure 6). He also observes that there are also fully integrated indicators

among the dimensions; however, one would have fundamental challenges to develop those

indicators, although changes in them would capture the changes of sustainability itself.

Figure 6: Schematic representation of the overlapping scope of indicators of ecological,

economic, and social aspects of livestock system sustainability Source: adapted from Garcia, 1996

Thus, the present study is conducted to understand three cattle feeding systems (free-range,

part-time grazing and cut-and-carry) in the Vietnam’s NMR in terms of household objectives,

household activities and resources, flow and interaction among resources, and socio-economic

and environmental issues.

2.1.3 Beef cattle production in the context of sustainable agriculture

According to Phillips and Sorensen (1993), to be sustainable in the short term, cattle

production systems must fulfil the requirements of the farmers for cost effectiveness and

minimal environmental pollution and minimum divergence from the welfare needs of the

cattle. In the long term, sustainability will only be achieved by the effective use of renewable

resources, minimum use of non-renewable resources, and the avoidance of environmental

pollution. The way of keeping cattle might threaten human existence such as by

desertification and climate change. Hence, assessing sustainable cattle production should be

conducted in all different pathways.

2.1.3.1 Development of beef cattle production and economic efficiency

Economic viability is included as one of the important pillars in the sustainable development

framework. According to Sen (2005), economic sustainability is considered in terms of the

costs of production and the prospects for continued economic viability in the face of changing

Page 37: BEEF CATTLE SYSTEMS IN THE CONTEXT OF SUSTAINABLE ...bictel-fusagx.ulg.ac.be/ETD-db/collection/... · (2011). Beef cattle systems in the context of sustainable agriculture in Bac

Bibliography 19

environmental, social, and economic conditions. Among many causes of farm un-

sustainability, the cost of various inputs is one of the key criteria (McConnell and Dillon,

1997). The optimal combination of inputs is calculated in such a way that the lowest

investment of input per unit of output is achieved at the point of maximum economic yield

(Holt, 1988, cited by Okigbo, 1991). Okigbo (1991) explains that the total variable costs of

inputs will be reduced by investing lower level of inputs, but it does not imply that it reduces

the variable costs per unit of outputs. The productivity achieved may not reach demand when

reducing input level because it results in low output (Okigbo, 1991). However, low input

systems may be developed for poor farmers who cannot afford costly inputs.

On the other hand, the economic viability of a production system depends upon various

attributes such as the level of economic returns, the instability and uncertainty of returns, and

in monetary economies, the associated financial requirements for the farming system, the

availability of finance and its implications for the financial liquidity of the farm (Tisdell,

1996). There are many aspects of economic sustainability including sustained yield, economic

performance and viability of farming and economic return (Sen, 2005). Furthermore, in the

development of sustainable production systems, the analysis of internal farm resources should

be made (Francis et al., 1986 quoted by Okigbo, 1991). Thus, the development of

economically viable agricultural production systems should be based on assessment of one or

more production systems from several alternative systems.

Hence, economic efficiency is essential for the sustainable development of beef cattle

production systems, because animal production also forms a major capital reserve for farming

households (Seré and Steinfeld, 1996). In poor areas, livestock production plays a very

important role as a source of income for smallholders (Epprecht, 2005). Huyen (2004) also

finds that in rural areas, cattle production is a money saving opportunity for households,

particularly interesting for the minority ethnic groups. Keeping cattle helps farmers to

increase their income, and combined with many other purposes, its economic efficiency also

increases (Quan, 2001). With regard to commodity production, calf raising is economically

effective as this activity enables use of local pastureland and labour, and has relatively low

production costs (Dzuc, 2003). Keeping cattle can lead to the use of agricultural by-products

and other feed resources that do not compete with human food, especially in mountainous

regions, where food security still a big issue for many households.

Cattle are the most important ruminant species in Vietnam and most of them are kept by

smallholder farms (Ly, 1995). Maltsoglou and Rapsomanikis (2005) found up to 23.9% of

households in Vietnam kept cattle. The highest proportion of households raising cattle was

found in the Northern Mountainous Region (65.5%). They are becoming one of the most

important sources of income, capital sink, aside from their use in traction (Ly, 1995). Cattle

are also raised for long-term savings and a form of wealth that can be sold to get cash at times

of need (Perkins, 2002). Production of meat and milk from ruminants is a tradition second in

importance compared to the provision of draught power and the production of manure (Ogle

and Phuc, 1997). However, mechanization is gradually reducing the role of draught animals,

especially in the lowlands (Huyen, 2004; Tra, 2007).

In the lowlands, cattle play a secondary role after pig and poultry production, while they play

the most important role in mountainous and hilly regions, where their contribution was over

22% in household livestock income (Epprecht, 2005). As reflected in the results found by

Quan (2001), households keeping cattle in Quang Binh province have rather good earnings

from cattle production, while they obtain poor earnings from poultry production and even lose

if raising pigs. On the other hand, Tung et al. (2007) find that keeping cattle in the NMR is a

source of good annual earnings, better than those from other sources, while it is a loss for

households in the Red River Delta and North Central Coast.

Page 38: BEEF CATTLE SYSTEMS IN THE CONTEXT OF SUSTAINABLE ...bictel-fusagx.ulg.ac.be/ETD-db/collection/... · (2011). Beef cattle systems in the context of sustainable agriculture in Bac

20 Bibliography

Moreover, cattle play an important role in harsh natural conditions in mountainous regions

where the development of livestock is more suitable than crop growing (Beganger and Vissac,

1993). Minot et al. (2003) observe that especially in remote provinces, income is split

between maize and cattle production. In spite of its importance, income from cattle husbandry

still accounts for a small part of the total income of households in the NMR (Epprecht, 2005),

although still higher than that in other regions.

2.1.3.2 Development of beef cattle production and social solidarity

Social solidarity implies the continued satisfaction of basic human needs such as food and

fibre, and social and cultural necessities such as security, equity, freedom, education, and

employment (Brown et al., 1987). Livestock husbandry provides not only diversified products

and income but also year-round employment. Besides economic contributions, Eguienta et al.

(2002) point out that animals can be raised to both produce meat and enhance employment

opportunities.

Livestock production in general and beef animal production in particular turns biological

inputs (feed resources and technology) in combination with social inputs including labour,

capital, and organisational capacity into outputs such as meat, manure, draught power, and

income (Thompson and Nardone, 1999). Among livestock types, the production of beef cattle

also provides opportunities of worker in rural areas, especially where a high rate of

unemployment is recorded. In Vietnam’s mountainous regions, the cattle grazing system

predominates and is highly labour-intensive. However, farmers are often only active about 65-

70% of their working time (Quan, 2001). Tung et al. (2007) also show that raising cattle

provides high employment opportunities in Northern Vietnam. Among smallholders, labour

redundancy is the predominant situation, where the extra labour might be employed to raise

cattle—a labour intensive sub-sector compared to others. Similarly, Tung et al. (2007) find

that the beef cattle production sector creates annually high employment opportunities in

Northern Vietnam. Furthermore, the author points out that income for labour derived from

this sector is higher than the average wage paid for hired labour in mountainous provinces. In

addition, in small-scale production, women play a vital role, especially where they actively

participate in all activities related to livestock management (Zaved et al., 2004).

Understanding the various roles women play in cattle feeding systems also becomes an

indicator in assessing the sustainable development of beef cattle production as a means of

improving their role and livelihoods.

2.1.3.3 Development of beef cattle production and environmental sustainability

The environment is a vital condition of human beings, and negative effects from any activity

will hinder the availability of resources over time (Sen, 2005). Environmental sustainability is

defined as the maintenance, continued productivity, and functioning of the ecosystem or of

natural capital both as source of inputs and as a sink for waste (Goodland, 1995 quoted by

Sen, 2005). It is said that demographic and poverty pressures are fundamental driving forces

affecting the environment in developing countries (Blackburn, 1998). There is a strong mutual

antagonism between sustainable development and environmental protection in such a way that

the poor are often forced to degrade the very environment that they depend on (Ellis, 2000;

Taylor, 2001), such as by allowing their livestock to overgraze grasslands (Ellis, 2000).

Livestock husbandry can contribute to societies, but human and economic pressures can direct

livestock production in ways that are detrimental to the environment (Seré and Steinfeld,

1996). According to Seré and Steinfeld (1996), there is not a clear assessment of the scale and

nature of the interaction between livestock production and the environment because of a lack

of technical analysis for making informed policy decisions and devising technical intervention

Page 39: BEEF CATTLE SYSTEMS IN THE CONTEXT OF SUSTAINABLE ...bictel-fusagx.ulg.ac.be/ETD-db/collection/... · (2011). Beef cattle systems in the context of sustainable agriculture in Bac

Bibliography 21

programmes. Nevertheless, it is increasingly clear that livestock-environment linkages should

be seen in the context of their human, economic, and political aspects, as well as that of

natural resource utilization. Moreover, the linkages between sustainable development, poverty

alleviation, and environmental protection should be also recognized (Wells and Brandon,

1992 quoted by Taylor, 2001).

There has been a huge increase in grain consumption by livestock, especially in intensive and

specialized systems of meat production on the grounds of increasing efficiency to supply food

for poor countries, and this is strongly affecting the sustainable development of agriculture

(Thompson and Nardone, 1999). Consequently, the ability of ruminants to transform feeds not

suitable for humans into high-quality food will be of great importance in the long term for

feeding a growing population (Thompson and Nardone, 1999). Ruminants play an important

environmental role in disease control in mixed crop or grazing systems because the biological

cycle of insects, fungi, and weeds is broken by the regular rotation of crop with pastures

(Thompson and Nardone, 1999). Moreover, with good management, livestock production can

make a positive contribution to natural resource (Boyazoglu, 1998).

On the contrary, if livestock production is not well-managed, it can contribute not only to land

degradation, water pollution, and emission of greenhouse gases but also to the loss of

biodiversity (Boyazoglu, 1998). It is a fact that manure from beef cattle production negatively

impacts environmental quality (Thompson and Nardone, 1999). According to Payraudeau and

van der Werf (2005), a farming activity is sustainable if its polluting emissions and its use of

natural resources can be supported in the long-term use of natural environment.

According to Leng (1993), methane is an important component of gases accumulating in the

atmosphere that cause a warming effect and climate change, and it is the gas most associated

with animal agriculture. Methane production from ruminants appears to be a major issue

although it contributes only around 18% of the overall warming due to the fermentative

digestion of ruminants (Figure 7). In addition, he finds that methane has a thermogenic affect

around 4–6 times higher than that of carbon dioxide. Payraudeau and van der Werf (2005)

state that in the overall assessment of agricultural sustainability, the first step would be the

diagnosis of the environmental impact of agriculture. At the livestock production scale, the

activity is considered sustainable when the production is optimized, inputs minimized, and

pollution emission minimized (CORPEN, 2003 cited in Payraudeau and van der Werf, 2005).

Becker (1997) argues that the discount rate of resource depletion and pollution in terms of

physical units may be used to assess environmental sustainability.

Page 40: BEEF CATTLE SYSTEMS IN THE CONTEXT OF SUSTAINABLE ...bictel-fusagx.ulg.ac.be/ETD-db/collection/... · (2011). Beef cattle systems in the context of sustainable agriculture in Bac

22 Bibliography

Figure 7: Relative contribution of biological resources to the global production of CH4

in the atmosphere. Source: Bolle et al. (1986) quoted in Leng (1993)

2.1.4 Beef cattle production and poverty alleviation

Besides the influence of cattle production on economic, social, and environmental aspects, the

cattle production sub-sector also plays an important role in poverty alleviation. According to

the Livestock in Development report (1999), development of the livestock sub-sector will

create a potential for poverty reduction by increasing labour opportunities for the poor and

will enhance the specific contribution of livestock to poor livelihoods. Beets (1990) indicates

that developing agricultural production is one of main ways of addressing the problem of

poverty because agriculture growth will both promote economic growth and reduce poverty,

especially in rural areas. In addition, improving agricultural productivity may have a strong

effect on smallholder farms with abundant labour resources (Dixon et al., 2001).

According to Steinfeld and Mack (1997), using animal as a growth engine is one of the

development opportunities in the agricultural sector, because livestock production plays a

major role in rural development, such as a source of nutrition, manure and traction power for

crop growing, cash income, employment, reducing risks, and capital savings. Moreover,

keeping livestock may help to enhance the economic viability and sustainability of a farming

system (Steinfeld and Mack, 1997). Many farmers report that animal production is a key

activity to improve their income, especially for the poor (Quan, 2001). Livestock production

is a critical source of household income especially in poor areas (Epprecht, 2005). Developing

the livestock sector in rural Vietnam has contributed to increased rural incomes and, to a

certain extent, to poverty reduction among small-scale farmers (Vietnam Development Report

– VDR, 2003).

According to Schipmann (2010), agriculture is as an avenue out of poverty, being a key factor

in reducing poverty in rural areas. Agriculture growth can help alleviate poverty through three

pathways—economics, society, and environment. Firstly, the real price of off-tradable

products may decline because of agriculture growth, in turn improving the purchasing power

of the poor. Secondly, agriculture can use unskilled labour more intensively than other sectors

of economy. Lastly, agriculture growth can increase the income of smallholders and thereby

reduce poverty among them, as well as generate indirect effects through an increased demand

for off-agriculture outputs (Bresciani et al., 2004).

Page 41: BEEF CATTLE SYSTEMS IN THE CONTEXT OF SUSTAINABLE ...bictel-fusagx.ulg.ac.be/ETD-db/collection/... · (2011). Beef cattle systems in the context of sustainable agriculture in Bac

Bibliography 23

Steinfeld and Mack (1997) state animal production plays an important role in rural

development. De Haan (1995) finds that livestock development often benefits the poor.

Therefore, the development of livestock stimulates not only rural growth, but also poverty

alleviation. Cattle production is a top priority in diversification of household incomes,

particularly in remote areas (Minot et al., 2003). Quan (2001) finds that the gross output from

cattle production accounts for about 10% of the gross household income in the Central Coast

of Vietnam. He shows that income from cattle production in total income from livestock

accounts for the highest proportion in poor households in comparison to other household

groups, reaching nearly 30%, although lack of capital is a major limiting factor in economic

activities in this household group.

Thus, the sustained and widespread development of beef cattle production will be a necessary

strategy for successful and sustainable development of the NMR and improvement of farmer

living standards and poverty alleviation is an issue confronting policy makers, researchers,

and farmers. Beef cattle production in the NMR is an answer, but a good understanding of

existing systems is required to design improved farming systems (Beets, 1990). Principally, in

order to decrease poverty and improve economic growth through agricultural sector

development, two options for policy makers and farmers are identified: either the expansion

of production or production intensification (Zeller et al., 2000). However, those options are

not really suitable for small-scale farmers in Vietnam. This study will investigate beef cattle

production in smallholder farms and different recommendations will be given based on real

conditions.

2.1.5 Beef cattle production systems in the Northern Mountainous Region of Vietnam

Classification of cattle production systems in the world identifies such factors as feeding

systems, purpose of cattle rearing, farm intensification, cattle genotypes and terrains, and

scale of production. Rachmat et al. (1992) (cited in Huyen, 2009) break down cattle

production according to feeding systems based on the main feed source. Tung et al. (2009)

also classify cattle production according to different feeding systems based on modes of cattle

keeping. Tung and Giang (2008) divide cattle production according to purpose of cattle

husbandry, including cow-calf cattle production and fattening cattle. Nicholson et al. (1994)

also classify cattle production based on the purpose of cattle rearing. Classification of cattle

production into different genotypes and terrains is found in the studies of Huyen (2009);

Phung (2001); Phung and Koops (2003). Huyen et al. (2010) also categorise cattle production

based on terrains, lowlands or uplands. Huyen et al. (2010); Tung et al. (2009); Tung and

Giang (2008) also put cattle production in Vietnam into different classifications depending on

herd size (small, medium and large). However, there was no study in Vietnam focussing on

feeding systems and their influences on sustainable agriculture. Therefore, in the context of

the study, classification of cattle production was studied according to feeding systems

identified by husbandry strategies and approaches. In Vietnam, beef cattle production is often

practised in mixed farming systems that combine crop production and cattle production. See

the classification of Seré and Steinfeld (1996).

Nevertheless, in Vietnam, beef cattle herds are classified into three typical production

systems: state-run farms, private large- and medium-size farms, and smallholder farms.

Currently, there is no state-owned specialized beef breeding cattle farm, with the exception of

commercial offspring raised in these farms. In state-run farms, beef cattle are mainly imported

exotic breeds such as Brahman, Drought Master, Red Sindhi, and Sahiwal and their offspring.

In addition, crossbreeds of Limousine, Charolais, and Simmental are also imported into

Page 42: BEEF CATTLE SYSTEMS IN THE CONTEXT OF SUSTAINABLE ...bictel-fusagx.ulg.ac.be/ETD-db/collection/... · (2011). Beef cattle systems in the context of sustainable agriculture in Bac

24 Bibliography

Vietnam. Animals are fed high rations of concentrate and high-yielding grasses to shorten the

keeping time and optimise performance (Tra, 2007).

Private large- and medium-size farms feature mainly crossbred animals from high-

performance breeds or crossbreeds between exotic and local breeds. This type of production

system has been recently and extensively developed in many provinces, including the NMR.

These farms are conducted as intensive or semi-intensive production units. In the case of

intensive cattle production, a high percentage of concentrate and planted grasses are also used.

The semi-intensive system uses natural fallow land for forage and pasture.

In small-scale cattle production, beef cattle are often raised in intensive or semi-intensive

production systems (Hung and Binh, 2004). In general, semi-intensive cattle production is

also characterised by small herd size and is practised by a low percentage of farmers.

Extensive cattle production is still predominant, particularly in the uplands. Smallholder

farmers raise beef cattle in using the free grazing, cut-and-carry feeding methods, mixing

grazing and stable feeding (hereinafter referred to as part-time grazing) (Nho et al., 2003;

Mui, 2003, Tra, 2007). Traditionally, free-grazing cattle have always been popular among

most of ethnic minority groups. Different production systems often resulted in different

economic efficiencies (Quan, 2001).

The cut-and-carry cattle feeding system refers to households that keep cattle in a stable. Cattle

are fattened by and cutting and carrying back feed resources for them. Cattle are also housed

and practiced cutting and carrying back feed resource, especially in crop season in other areas

such as the Red River Delta. However, this is a difference from others; only mature male

cattle are fattened in this way in the study area involving H’Mong households. All bulls over

three years old are often confined for fattening throughout the year or during a short period

before selling (from one to three months or longer time depending on the owner’s capacity).

Supplementary feed such as maize or pig feed (a combination of vegetables, banana stems

with or without maize commonly fed to pigs, also used as part of the feed for cattle) was often

used, while the main feed resources were natural or planted grass and forest tree leaves.

However, other cattle in their households such as cows, calves, heifers, and steers are allowed

out to graze part-time. Farmers explain that fattening bulls is efficient in the short term and is

much better than other cattle feeding methods. This finding is also indicated by Niem et al.

(2001); Nho et al. (2003); Huyen et al. (2006); Tra (2007).

In the study area, the free-range system refers to that used by households that allow cattle to

graze freely without being controlled by the owners. This free-range system is also described

by Tra (2007) and Nho (2003). In selected households, a regular check was made daily,

weekly or monthly according to individual family strategy and labour availability.

Households practising this system have good market access and high land use pressure.

Allowing cattle to graze part-time is the predominant method of cattle husbandry currently

seen throughout the country. In cropping season, farmers keep their stock at home in the

morning, and are taken out to graze by their owners in afternoon. After harvesting, cattle are

allowed to graze all day in the fields until the next planting seasons, and are sheltered at night.

Cattle graze on unplanted land, common land or fallow land. This method of cattle production

is also described in Tra (2007); Tung and Giang (2008); and Tung et al. (2009).

2.1.6 Concept of the study

With the main objective of studying the development of beef cattle production in Vietnam’s

NMR, this study concentrates on analysing the influence of cattle production on the

agricultural sustainability. However, this influencing assessment is very broad and not always

Page 43: BEEF CATTLE SYSTEMS IN THE CONTEXT OF SUSTAINABLE ...bictel-fusagx.ulg.ac.be/ETD-db/collection/... · (2011). Beef cattle systems in the context of sustainable agriculture in Bac

Bibliography 25

easy to quantify. In this study, the influence on sustainable agriculture is examined from the

perspective of production systems and beef cattle production development in all dimensions

of sustainable agriculture: social, economic, and environmental.

A combination of several criteria should be proposed to use in the assessment of

environmental sustainability, because several criteria are better suited than single-criterion

approaches (Payraudeau and van der Werf, 2005). Thus, in the study several indicators will be

used to analyse the sustainable development of beef cattle. In the study framework, indicators

such as total factor productivity, gross margin, household net cash income, role of women,

employment opportunities, return on labour, farmer awareness, current status of threats of

environmental pollution (manure management, collection, and utilisation) and stocking rate

are looked at in assessing the influence of beef cattle production on overall sustainability.

Factoring in the influence of cattle feeding systems on sustainability and the above logical

approach, the concept of the study is illustrated in Figure 8.

Page 44: BEEF CATTLE SYSTEMS IN THE CONTEXT OF SUSTAINABLE ...bictel-fusagx.ulg.ac.be/ETD-db/collection/... · (2011). Beef cattle systems in the context of sustainable agriculture in Bac

Figure 8: The development of beef cattle production systems on sustainable agriculture

Sustainable

agriculture

Economic

sustainability

Environmental

solidarity

Sustainable

development

of beef cattle

production

Social

stability

Manure use

and storage

Stocking rate

Return on

labour

Role of women

Employment

opportunity

Gross cattle

margin

Total Factor

Productivity

Sustainable

development of

cattle feeding

systems

Household

net income

Farmer

awareness

Page 45: BEEF CATTLE SYSTEMS IN THE CONTEXT OF SUSTAINABLE ...bictel-fusagx.ulg.ac.be/ETD-db/collection/... · (2011). Beef cattle systems in the context of sustainable agriculture in Bac

Bibliography 27

2.2 GENERAL DESCRIPTION OF THE RESEARCH SITES AND THEIR CHARACTERISTICS

This section will give an overall view and description of the Northern Mountainous Region

and the study sites (Bac Kan province and Pac Nam district).

2.2.1 An overview of the Northern Mountainous Region of Vietnam

Three quarters of the country is mountainous and hilly, with a great diversity in fauna,

climate, people, and flora. According to Donovan et al. (1997), the Northern Mountainous

Region (NMR) includes 17 provinces namely: Tuyen Quang, Ha Giang, Cao Bang, Lang Son,

Lao Cai, Yen Bai, Hoa Binh, Bac Kan, Thai Nguyen, Son La, Quang Ninh, Dien Bien, Lai

Chau, Bac Giang, Phu Tho, Thanh Hoa, and Nghe An (Donovan et al. [1997] cited by Lentes,

2003). However, according to the national ecological identification, the NMR includes only

14 provinces separated into two sub-regions consisting of Northeast and Northwest, where

Quang Ninh, Thanh Hoa and Nghe An provinces are excluded (GSO, 2009). In the context of

this study, the term NMR will be used in harmony with the national ecological geography

definition embracing only 14 provinces.

The NMR accounts for about 29% of the total country area (about 95,434 km2), but has a

population of about 11.2 mil. inhabitants, roughly 13% of the country’s population, with 85%

of them living in rural areas, much higher than the national figure (73%) for 2007. The

population density of the NMR in 2007 was 116 persons per km2, which was significantly

lower than the national average population density (257 persons per km2) in the same year. In

the NMR, there are 30 ethnic minorities. Minot et al. (2003) find that a high proportion of the

population in the NMR were members of ethnic minority groups, extremely higher compared

to national data. For example, in 1998, it was around 50% versus 12%, respectively. Its

topography is hilly to mountainous, with altitudes typically ranging between 500 and 1,000

meters above sea level (asl.) (Minot et al., 2003). Ethnic minorities generally employ farming

approaches very adapted to their specific location. However, due to the varied and fractured

topography, there is a wide range of ecosystems (Vien, 2003). H’Mong people often stay in

the highest mountain zones, 800 meters or more asl., with scarce water and low temperatures

(Huyen, 2004; Lan, 2005). On the other hand, Tay, Nung and Kinh people are often located in

lower mountainous zones, with better water resources, warmer temperatures and closer to

transport facilities, markets and services, towns and other villages (Vien, 2003; Lan 2005).

Dao and Thai people are often settled at a halfway point in mountainous zones (Huyen, 2004;

Lan 2005).

These regions are confronted with many difficulties compared to lowland and delta areas.

According to Castella et al. (2002a), there are up to seven major characteristics that

distinguish mountainous regions from others. Firstly, there are many biophysical constraints

including steep slopes, uneven terrain, access difficulties, low soil quality, and harsh natural

conditions (Castella et al., 2002a; CPRGS, 2003; Minot et al., 2004). Secondly, the NMR has

to cope with the region environmental degradation; specifically deforestation, soil erosion and

degradation, and natural disasters (Castella et al., 2002a; Tai, 2004). The next characteristic

highlighted is poor infrastructure, which means underdeveloped communication and

transportation networks (Castella et al., 2002a; CPRGS, 2003; Minot et al., 2004). Then

economic constraints are major difficulties, namely subsistence agriculture, lack of capital,

and limited market access. The relatively high density of the population linked with the

scarcity of suitable land for production is also stated as one of the main difficulties in these

regions. Furthermore, cultural constraints such as low education level, multiplicity of ethnic

Page 46: BEEF CATTLE SYSTEMS IN THE CONTEXT OF SUSTAINABLE ...bictel-fusagx.ulg.ac.be/ETD-db/collection/... · (2011). Beef cattle systems in the context of sustainable agriculture in Bac

28 Bibliography

languages, and conflicts among different ethnic groups (Vien, 2003) are mentioned. Finally,

intellectual constraints are caused by lack of knowledge and understanding about the

mountain environment and there are insufficient development plans for mountainous areas

(Castells et al., 2002a). Besides, farmers in the mountainous regions have limited resources

and are strongly dependent on agricultural and forest activities (Minot et al., 2003).

As reflected above, most of the poor people in Vietnam belong to minority ethnic groups,

concentrated mainly in mountainous regions, remote, or isolated areas. Many activities and

national programmes have been implemented for minority groups. However, they still face

many difficulties in the areas of basic infrastructure and social services (CPRGS, 2003). The

population of Vietnam’s NMR increased dramatically, for instance by about 300% between

1960 and 1984, and it is assumed that the population will double in the next 20 years

(Jamieson, 1998 cited in Friederichsen and Heidhues, 2000). The trend of population growth

in mountainous areas as well as the process of land allocation will increase basic human needs

and require new and/or alternative farm and off-farm activities (Huyen, 2004; Friederichsen

and Heidhues, 2000). As a result, it is predicted that the poverty rate will increase in the

mountains due to the vicious circle of increasing population, environmental degradation, and

the marginalization of ethnic minority groups (Castella et al., 2002a), not to mention the

recent context of serious climate change and natural disasters. Among regions in Vietnam, the

NMR is ranked as the most sensitive area in terms of climate change impacts. The pressure on

land is and will continue to be strong in the highlands, where a high proportion of available

land does not favour crop cultivation.

Extremely high percentage of people from ethnic groups are among the poor, accounting for

about 69% of those under the poverty level, compared to 23% for the total national

population, 2002 census (Figure 9). Mountain areas are known to be the poorest in the

country (VDR, 2003). For both Vietnam and the NMR, the Kinh and Chinese ethnic groups

are better off than the other ethnic groups. In 1993, the poverty rate for Kinh and Chinese in

the NMR was approximately 74% and for other ethnic minorities was 88.5%, but by 2003 the

poverty rate for Kinh and Chinese in the NMR had fallen to 24%, but for ethnic minority

people the poverty rate was still high at around 67%.

The highest proportion of households whose principal income is from animal production

among regions throughout the country is that in the NMR (Maltsoglou and Rapsomanikis,

2005), which underscores its significance in the region. Data from 1998 is an example—97%

compared to 81%, respectively (Minot et al., 2003). During the period 1993–1998, livestock

activities contributed from 9 to 13% to the overall income of households in the NMR (Minot

et al., 2003). Surprisingly, in 2001, Epprecht (2005) records that the share of livestock-

derived income out of total income was above 22% in the northern uplands, putting this area

at the top of the list in the country. According to Minot et al. (2003), about 60% of selected

households in the NMR said that high performance practices and income from animal

production had improved their standard of living. The authors also found that in the poorest

households, the highest proportion of the total family income was generated from livestock

production, which highlights the potential of animal production for the poor.

The national population growth rate of about 1.2% during 2005–2007 is considered moderate

in developing countries; however, the overall population is still large. The increasing of total

population in Vietnam implies that there will be an increasingly limited cultivated land area

per capita in the future. The pressure of intensification of land use will significantly increase

in rural areas, especially in the highlands, where the land area available is not highly

favourable to crop production. The fact that poverty figures in the northern uplands are still

high despite all the efforts put forth by the government, institutions and organisations

focusing on research, development aid and cooperation, illustrates the complexity of this

Page 47: BEEF CATTLE SYSTEMS IN THE CONTEXT OF SUSTAINABLE ...bictel-fusagx.ulg.ac.be/ETD-db/collection/... · (2011). Beef cattle systems in the context of sustainable agriculture in Bac

Bibliography 29

issue. Further deforestation and degradation of the uplands are foreseen, jeopardising food

security. Therefore, animal husbandry is seen as a preference for agricultural development

(Huyen, 2004). Nevertheless, after crop production, animal production is still ranked the

second most important activity contributing cash income to families (Huyen, 2004). As a

result of its contribution to the agriculture GDP, the development of the rural economy

through livestock is one of the main focuses of the Vietnam government (CPRGS, 2003). It is

also foreseen that this sector will contribute to around 30% of gross agricultural sector outputs

in the 2010 development plan, and 35% in 2015 (MARD, 2006). However, this goal will not

likely be achieved because of the economic crisis, bird flu and other factors.

Figure 9: Poverty rate by different ethnic groups in Vietnam Source: Neefjes and Thanh, 2003.

The NMR shows a little higher growth rate in cattle herds compared to that throughout the

country (about 6% compared to 4.5% annually, on average), from around 0.6 mil. to 1.0 mil.

head from 2000 to 2009, peaking at 1.1 mil. head in 2007 (Figure 10). Thus, the growing

cattle population in the NMR might be a result of the government’s development strategies

for cattle production. Nevertheless, this development is still under expectation because the

NMR is considered as a favourable area for ruminant production. A high percentage of

available unused land is unsuitable for crops. Nonetheless, cattle numbers in the NMR

represented a considerable proportion of the total national cattle population (from around 15

to 17% in the same period).

Cattle meat production in the NMR gradually increased from 11,500 tonnes in 2000 to 15,300

tonnes in 2005, virtually stabilising in 2006 at around 15,400 tonnes). Over the next two years

(2007 and 2008) the cattle meat yield jumped to 18,000 and 19,700 tonnes, respectively.

Nevertheless, a sharp reduction of 2,800 tonnes of cattle meat production was recorded in

2009 in the NMR. Thus, cattle meat production in the NMR also fluctuated strongly, due

variously to changing government strategies, policies and environmental effects such as

diseases and the cold outbreak (in late 2007–early 2008). Nevertheless, the growth of beef

cattle production in Vietnam has increased steadily over time.

58.1

81.5

28.9

43.9

23.1 24.3

86.4 88.5

69.3 66.7

53.5

73.9

0

20

40

60

80

100

Vietnam NMR Vietnam NMR

1993 2002

%

Total Kinh & Chinese Other ethinic groups

Page 48: BEEF CATTLE SYSTEMS IN THE CONTEXT OF SUSTAINABLE ...bictel-fusagx.ulg.ac.be/ETD-db/collection/... · (2011). Beef cattle systems in the context of sustainable agriculture in Bac

30 Bibliography

Figure 10: Cattle population and cattle meat production in the NMR from 2000 to 2009 Source: GSO, 2010

In summary, the NMR is distinguished by poor accessibility, poor infrastructure, poor living

conditions, harsh and degraded natural conditions, a high proportion of ethnic minority

groups, a rather low population density and relatively low urbanization, and very limited

access to productive resources and services. Its inhabitants are experiencing a high level of

poverty and essentially depend on the agricultural sector for their subsistence and limited

income. However, productive land is scarce because so much of the area is unsuitable for

production. In addition to this, the area frequently suffers from natural disasters and climate

change events. The development of this rural area is a high national high priority. Besides,

cattle production is considered as a priority in improving the poverty in the region by support

policies from the Vietnamese government.

2.2.2 General introduction to Bac Kan province

There are several reasons for selecting Bac Kan province and Pac Nam district: (i) it is one of

the poorest provinces in the NMR, where the cattle population is among the most dense; (ii)

Pac Nam is the poorest district in the province, located in remote area with much emphasis on

cattle production; (iii) Pac Nam borders on Tuyen Quang, Ha Giang and Cao Bang provinces,

where cattle husbandry is widespread, which highlights the potential of opening large cattle

markets in the district; (iv) there are many cattle markets in the district, providing outlets for

local people who develop cattle production; and (v) this sub-sector is still not as strong as it

might be. Detailed information about those areas is given in the following parts to help

explain the selection of the study sites.

2.2.2.1 Geography, population and climate conditions in Bac Kan

Bac Kan is a mountainous province located in the northeast region of Vietnam, from 21048 to

22044 north latitudes and 105

026 to 106

015 east longitudes (GSO, 2005). Sharing its borders

are Cao Bang province to the north, Tuyen Quang province to the west, Lang Son province to

the southeast, and Thai Nguyen province to the south (Figure 11). As of 2007, Bac Kan has

eight administrative districts/towns. Bac Kan town is located about 166.0 km from Hanoi, the

capital of Vietnam.

0

5

10

15

20

25

0

200

400

600

800

1000

1200

2000 2001 2002 2003 2004 2005 2006 2007 2008 2009

Ca

ttle

mea

t p

rod

uct

ion

(1

,00

0 t

on

nes

)

Ca

ttle

po

pu

lati

on

(1

,00

0 h

ead

s)

Cattle herd size Cattle meat yield

Page 49: BEEF CATTLE SYSTEMS IN THE CONTEXT OF SUSTAINABLE ...bictel-fusagx.ulg.ac.be/ETD-db/collection/... · (2011). Beef cattle systems in the context of sustainable agriculture in Bac

Bibliography 31

Figure 11: Bac Kan province, Pac Nam district and geographical location

of selected communes Source: Bac Kan PSO, 2006; own presentation

Bac Kan province was first established in 1900 by the French. Then it was merged into Thai

Nguyen province. It has been separated again since 1997. The province has therefore just

been re-established for somewhat over a decade. The provincial authorities are greatly

interested in the development plan of the province in general and of the agricultural sector in

particular. Bac Kan is roughly 500–1,000 meters above sea level and its topography is

extremely diverse with mainly midlands, mountains, and very steep slopes with a grade of

around 15 to 20%, with a complex network of rivers and springs (GSO, 2005). Because the

land is steeply sloped, soil erosion and degradation is common. Soil quality is poor with high

PH levels. In addition, the ‘slash-and-burn’ agriculture practiced situation in the uplands is

another cause of soil erosion and degradation, creating treeless hills and mountains. There is a

complex network of five large rivers and springs that provide irrigation water and running

water. Particularly, the province is home to the headwaters of various rivers such as the Gam,

Cau, and Bac Giang. The steep slopes and high level of precipitation during the rainy season

also lead to flash flooding in the region. Bac Kan province must prepare to cope with many

impacts of climate change. According to Tra et al. (2009), Bac Kan province is prone to

drought, flash floods, landslides, and soil erosion that are immediate risks to local people.

Other related climate change events such as temperature changes, changing in the seasons,

high precipitation, waterlogging, and inconsistency of water resources, thunderstorms, and

hailstorms also occur in the province. The frequency and intensity of these events as well as

impacts tend to be increasing gradually. It is said that the weather in Bac Kan is changing,

resulting gradually in two clearly marked seasons—dry and rainy—instead of the usual four

seasons (Tra, 2009).

Cong Bang commune

Nghien Loan

commune

Page 50: BEEF CATTLE SYSTEMS IN THE CONTEXT OF SUSTAINABLE ...bictel-fusagx.ulg.ac.be/ETD-db/collection/... · (2011). Beef cattle systems in the context of sustainable agriculture in Bac

32 Bibliography

Its natural land area is 4,857 km2, occupying 1.5% of Vietnam’s land areas. The total

population of the province was 305,800 persons, accounting for around 0.4% of the national

population (according to 2007 census), of which 259,700 persons were living in rural area,

accounting for roughly 85% of the population, which is more or less equal with that in the

NMR but significantly higher than the figure for the country (72.5%) (GSO, 2008). Although

population growth showed a declining trend, it still grew at an estimated rate of 1.2%, which

was slightly higher than the average growth rate of the national population (1.0%). The

population density of the province in 2007 was quite low compared to the average population

density in the NMR and the country as a whole (62 compared to 162 and 257 persons per

km2, respectively) (calculated from data of Bac Kan PSO, 2008; GSO, 2008). However, the

density varies drastically among the provinces districts and towns.

As much as 86.7% of the population of the province was made up of ethnic minority groups

(Bac Kan PSO, 2006), a significantly higher proportion than that of ethnic minorities living in

the NMR (roughly 50%). Twenty three different ethnic groups were living in the province, the

key ones being Tay, Nung, Dao, Kinh, and H’Mong (Figure 12). The Tay people occupied the

largest part of total population, i.e. 54.3% (GSO, 2005). The second biggest group was the

Dao people, about 16.5%; ranking next are the Kinh people, accounting for 13.3% of the total

population. The Nung and H’mong peoples rank behind those ethnic groups, with 9.5% and

5.4%, respectively. Around 1.0% of the total population of the province belong to 18 other

ethnic groups.

Figure 12: Bac Kan population distribution by ethnic groups in 2002 Source: GSO, 2005

There are two clearly identified seasons in Bac Kan. The hot, rainy season lasts from April to

September (summer), and the cold, dry season (winter) ranges from October to March. The

average temperature is 22.7oC. It ranges from around 20.8 to 28.5

oC from February to

October, and then drops to about 15 to 18oC from November to January (Bac Kan Statistical

Year Book, 2007). Significantly, in late 2007 and early 2008, there was a serious cold

outbreak in many provinces including Bac Kan, causing much damage to the agricultural

sector, with Bac Can suffering some of the severest cattle losses in the whole country

(MARD, 2009). Rainfall fell very low, around 4–82 ml per month from October to April,

while it climbed up to about 150–350 ml per month from May to September, 2007.

Page 51: BEEF CATTLE SYSTEMS IN THE CONTEXT OF SUSTAINABLE ...bictel-fusagx.ulg.ac.be/ETD-db/collection/... · (2011). Beef cattle systems in the context of sustainable agriculture in Bac

Bibliography 33

Economic growth in the province showed a positive trend, reaching almost 10% annually, on

average, during the period 1997–2000. Then, economic growth in Bac Kan province jumped

to around 12% annually on average, from 2001 to 2007, quite something when compared to

the national economic growth rate for the same time (7.5%). Optimistically, the province

planned to reach an economic growth of 20.0–22.0% over the next five years (Bac Kan Party

Committee Report - PCR, 2007). However, 50.8% of provincial households were still living

under the poverty line in 2005 (Bac Kan PRC, 2006), which was considered extremely high

compared to the national data (19.5% in 2004). Nevertheless, the poverty rate of the province

has been reduced to around 38%, but it is still significantly higher than the national data

(14.8%) in 2007 (Bac Kan PRC, 2008; GSO, 2008).

Looking at the province’s GDP more closely, it is clear that Bac Kan is a strongly agriculture-

based province, where farmers are largely dependent on subsistence production for livelihood.

The agriculture sector is given great priority in the provincial rural development plan. Despite

its importance, the share of agricultural, forestry and fishery output in the province’s total

output has dropped dramatically, from 58.2% in 2000 to 42.8% in 2005 and to 34.9% in 2007

(Bac Kan – PSO, 2006; 2008). Nevertheless, the proportion of agriculture, forestry and

fishery output was still nearly twice as high of that sector’s GDP data countrywide (35%

compared to 20%) (GSO, 2008). Meanwhile, the services sector recorded considerable

growth, from around 11% in 2000 to 21.5% in 2005 and up to 35.4% in 2007. Meanwhile, the

industrial sector for the same periods reached 27.2%, 30.5% and then dropped to 29.6%,

respectively. These changes were probably due to improved strategies in the provincial

economic climate in this period.

2.2.2.2 An introduction to the agricultural sector in Bac Kan province

(a) Employment, resources and gross output

The total labour force of Bac Kan in 2007 was 164,025 persons, of which 128,265 were

working in agriculture and forestry, accounting for about 78% of the total jobs in the

province. The proportion of agricultural labour in the province was 1.2 times higher than the

country figure (65%). Thus, the agricultural sector played a very important role in Bac Kan

province in terms of both labour force and gross output contribution. Development of this

sector is a crucial part in the development strategies of Bac Kan province. However, its share

in total provincial GDP declined substantially to about 18%, from 58% in 2000 to around

40% in 2007 (Bac Kan CPR, 2008). Provincial output from the agricultural sector reached

604.4 billion VND, which is one of the lowest values in the NMR and ranking just above Lai

Chau, a new province established in 2004, and accounted for a small percentage compared to

overall country’s agricultural value. Apparently, the role of agriculture in the completely

provincial economic sector was considerable in terms of labour and subsequent product

consumption. However, there will be a rapid decline of the agricultural GDP in proportion to

the province’s total GDP in next five years as the provincial development action plan, which

proposes a drop to 23% of total provincial GDP in 2010. On the other hand, the contribution

of industry is planned to increase substantially to 35% in the given time, while services are

anticipated to rise slightly, to 45% (Bac Kan PCR, 2006).

The gross output of agricultural activities of the province during the period 1997-2007 is

shown in Figure 13. Actually, the crop cultivation sub-sector shared the dominant proportion

in the total gross output of agriculture over this time. The value of crop production ranged

around 68-75% during the period 1997–2007, which was lower than the crop cultivation

outputs in the country (roughly 80%) in the same period (Bac Kan PSO, 2002; 2006; 2008).

The corresponding figures for livestock and the service sector ranged between 25–31% and

Page 52: BEEF CATTLE SYSTEMS IN THE CONTEXT OF SUSTAINABLE ...bictel-fusagx.ulg.ac.be/ETD-db/collection/... · (2011). Beef cattle systems in the context of sustainable agriculture in Bac

34 Bibliography

under 1%, respectively in that period. Significantly, livestock production in Bac Kan province

played a more crucial role in the agricultural sector compared with the national livestock

sector during that time (17-19%).

Meanwhile, crop production increased approximately by 7.5% per annum on average, from

170,997 mil. VND to 329,685 mil. VND. Similarly, the growth rate of livestock in the

province showed a substantial increase (9.0% annually, on average); it is higher than that for

the country (8.2%), where provincial policies and strategies have been promoting a change

from crop to livestock production over the last decade. Its gross output more than doubled,

from 72,158 mil. VND in 1997 to 150,502 mil. VND in 2007. However, it occupied an

extremely small part of the country’s gross livestock outputs. Meanwhile, the service sector

experienced better growth, 8.6% annually, increasing from 1,881 to 3,864 mil. VND in the

period.

Figure 13: Gross output at constant price 1994 for the agriculture sector Source: Bac Kan PSO, 2002; 2006; 2008

Total land area in Bac Kan province was 486,841 ha in 2007. The pie chart below compares

the land area used for different activities, with the highest proportion of land in this province

being forest (68.0%), including natural forest and planted forest, whereas agricultural land

accounted for a small part (8%) (Figure 14). This agricultural land was used for crop

cultivation, aquaculture, and other agricultural activities. Only about 4.0% of the land area

was devoted to non-farming activities. Another noteworthy feature is that roughly 20.0% of

the land area is unusable3 (Bac Kan PSO, 2008). Of this, only a small part is flat land (3.5%)

suitable for cultivation, and large areas of land are hilly (91.7%) and rocky mountains (4.8%),

which are basically unusable for cultivation because poor soil quality, while the development

3 Agricultural land includes agricultural production land (rice land, planted grass land, annual cropping land,

and permanent cropping land), forest land (production forest, protected forest and specific-use forest) and

aquaculture land and other agricultural lands. There is much disagreement among Vietnam’s professional

land use and management experts regarding the term unusable or non-useable land due to its lack of

precision. Up to now, this term has replaced by using the term “land use without certificate” because the land

areas in question have not yet been allocated to local people or organisations yet. Therefore, these land areas

designate land remaining after deduction of all lands owning land use certificate of agricultural land, non-

farming land, aquacultural land and other agricultural lands, which might include all types of land such as

agricultural land, forestland, natural pastureland, fallow land, or even cropping land used by the local people

but not yet been certified by the authorities.

0

50

100

150

200

250

300

350

1997 1998 1999 2000 2001 2002 2003 2004 2005 2006 2007

Gro

ss o

utp

uts

of

ag

ricu

ltu

ral

sect

or

(1,0

00

mil

. V

ND

)

Livestock Crop Services

Page 53: BEEF CATTLE SYSTEMS IN THE CONTEXT OF SUSTAINABLE ...bictel-fusagx.ulg.ac.be/ETD-db/collection/... · (2011). Beef cattle systems in the context of sustainable agriculture in Bac

Bibliography 35

of livestock is relatively less dependent on this (Huyen, 2004). Therefore, such lands have

often been used for grazing cattle and buffalo.

Figure 14: Land use in Bac Kan province in 2007 Source: Bac Kan PSO, 2008

(b) Crop production in the province

It is clear that paddy areas occupied the largest part, considered as the main food crop in the

province. Paddy areas grew gradually, by 2.0% annually, on average, climbing from about

16,000 ha in 1997 to over 21,300 ha in 2007, as shown in Figure 15. Ranking next in

importance was the maize area. It increased considerably, around 13.5% per annum, from

about 6,500 ha in 1997 to around 16,100 ha in 2007. Maize production is important in terms

of animal feed resources. Cassava production fluctuated from 2,000 to 3,000 ha from the

1997–2005 period, while its role in animal feed was gradually reduced. In addition, no data

was available for cassava during the year 2006 and 2007.

Page 54: BEEF CATTLE SYSTEMS IN THE CONTEXT OF SUSTAINABLE ...bictel-fusagx.ulg.ac.be/ETD-db/collection/... · (2011). Beef cattle systems in the context of sustainable agriculture in Bac

36 Bibliography

Figure 15: Areas planted in the main cultivated crops Source: Bac Kan PSO, 2002; 2006; 2008

In terms of gross output, maize production showed the most dramatic growth, reaching more

than 25.0% per year, a rise from nearly 15,000 tonnes in 1997 to nearly 60,000 tonnes in

2007. This shows the substantial increase in demand for feed resources used for the

development of livestock production in the province recently as well as its increasing use as a

cash crop. Nevertheless, paddy production yielded the largest gross output, growing nearly

1.5 times in 2007 as compared to 1997 (Figure 16). The people living in the province,

including ethnic minority groups, are rice-consumers. Moreover, all households share the

common objective of achieving food security through paddy rice production (Castella and

Erout, 2002). On the other hand, cassava production showed strong fluctuation, reaching its

highest level in 2002, up to around 34,000 tonnes from roughly 18,000 tonnes in 1997, before

dropping to 21,000 tonnes in 2005. Data on cassava production were also not available for

2006 and 2007, which might not consider as an important indicator in statistical database of

the province since 2006.

0

5

10

15

20

25

1997 1998 1999 2000 2001 2002 2003 2004 2005 2006 2007

Pla

nt

are

a o

f m

ain

cro

ps

(10

00

ha

)

Paddy rice Maize Cassava

Page 55: BEEF CATTLE SYSTEMS IN THE CONTEXT OF SUSTAINABLE ...bictel-fusagx.ulg.ac.be/ETD-db/collection/... · (2011). Beef cattle systems in the context of sustainable agriculture in Bac

Bibliography 37

Figure 16: Gross output of main cultivated crops Source: Bac Kan PSO, 2002; 2006; 2008

(c) Livestock production and development trends

Livestock production in Bac Kan is an important sub-sector of agriculture. The major types

are buffalo, cattle, swine and poultry. Livestock has shown a strong growth in the agricultural

sector over the past decade in the province since its establishment (Figure 17). The cattle

population recorded its greatest increase of 4.6% annually from 1997 to 2007, higher than the

national rate, climbing from 27,900 head in 1997 to 44,945 head in 2007, due to strong

government support policies.

The swine population increased only slightly at 1.5% annually, on average, in the given time

(between 122,311 and 155,034 head). The slow advance of this sub-sector might be due to

great market fluctuation, with a very large population being recorded between 2000 and 2001

with approximately 160,000 head, then dropping to 147,000 head in 2002. The swine

population remained constant during the three-year period 2003–2005 with around 155,000

head, then decreasing to 145,000 head in 2006 before returning to virtually the same

population in 2007 as in 2005.

Interestingly, buffalo showed a 0.8% annual decrease in population, on average, falling from

89,893 head in 1997 to 87,921 head in 2007. In spite of the buffalo’s role in upland areas and

a growing consumer interest in buffalo meat as a new specialty food in Vietnam, the drop in

the number of buffalo might be due to their decreased use for draught power and

transportation in rural upland areas.

On the other hand, the poultry population also recorded a slight climb of 0.7% per year, on

average, and increased from 945,000 birds in 1997 to 1,113,077 birds in 2007. Poultry

production in Bac Kan seems to have been unaffected by avian influenza since the end of

2002, when the population increased sharply in 2003 and kept stable during next 3 years.

However, this sub-sector showed an declining trend in 2006 and 2007. This might be

explained by disease outbreaks and the lack of a vaccination programme.

0

15

30

45

60

75

90

105

1997 1998 1999 2000 2001 2002 2003 2004 2005 2006 2007

Gro

ss o

utp

ut

in c

rop

s (1

00

0 t

on

s)

Paddy rice Maize Cassava

Page 56: BEEF CATTLE SYSTEMS IN THE CONTEXT OF SUSTAINABLE ...bictel-fusagx.ulg.ac.be/ETD-db/collection/... · (2011). Beef cattle systems in the context of sustainable agriculture in Bac

38 Bibliography

Figure 17: Development of livestock population in Bac Kan Source: Bac Kan Provincial Statistical Office, 2002; 2006; 2008

The gross output from livestock production showed some fluctuations during the period from

1997 to 2005 (Figure 18) (no data for the years 2006 and 2007 recorded in the provincial

statistical year book). In the first two years, the total gross output of the province reached

about 4,700 tonnes.

In the next three years, the gross output increased by more than 2,300 tonnes compared to the

first two years, ranging at around 7,000 tonnes per year. For next the three-year period, there

was a considerable upward trend, peaking at about 11,000 tonnes in 2004 and then dropping

slightly to around 10,000 tonnes in 2005. It is noteworthy that pork production was dominant,

accounting for about 64% of the total meat produced in the province in 2005. The

corresponding figures for cattle and poultry were 26% and 10%, respectively (Bac Kan PSO,

2006). Cattle meat production in 2007 represented 29% of total meat production.

Interestingly, the share of cattle in total meat produced in Bac Kan was over five times higher

than the share of that for the whole country (4.5%) in the same year. No data was recorded for

meat production in the province during 2006 and 2007. It is explained that this data has not

been considered as an important indicator in statistical database of the province since 2006.

0

200

400

600

800

1000

1200

1400

0

30

60

90

120

150

180

1997 1998 1999 2000 2001 2002 2003 2004 2005 2006 2007

Po

ult

ry p

op

ula

tio

n (

1,0

00

bir

ds)

Liv

esto

ck p

op

ula

tio

n (

1,0

00

hea

ds)

Pig Cattle Buffalo Poultry

Page 57: BEEF CATTLE SYSTEMS IN THE CONTEXT OF SUSTAINABLE ...bictel-fusagx.ulg.ac.be/ETD-db/collection/... · (2011). Beef cattle systems in the context of sustainable agriculture in Bac

Bibliography 39

Figure 18: Total gross output from animal production in Bac Kan Source: Bac Kan PSO, 2002; 2006; 2008

(d) Cattle production in Bac Kan

Cattle production was one of the most strongly developed livestock sub-sectors in the

province, underscoring its further potential in the NMR. Cattle density in the province was

roughly 13 head per 100 people, higher than the NMR overall average (nearly 9 head),

coming after Cao Bang province which has the highest cattle density (24 head) (calculated

from GSO, 2008). Cattle production in the province was characterised by low investment,

high risk due to diseases and mortality, low efficiency, and high environmental pollution. The

most dominant breed is a local race, namely Yellow cattle. In order to support beef cattle

production and increase herd size, cattle development programmes are being implemented

throughout the country, including Bac Kan province. Expansion of the cattle herds was

promoted by importing crossbred animals, high quality cows and bulls from other provinces,

as well as selecting high quality local cattle breeds (Bac Kan PC, 2006). However, the

development of cattle production in the study site was not as vigorous as expected.

The crossbreeding programme was introduced into the province during the period 1990–2007

by the Department of Extension Services and other organisations. It was undoubtedly noted

that the exotic and crossbred cattle ratio occupied only a small proportion compared to

Yellow cattle (0.7%) in 2005 (Table 1) and compared to that of the whole country (30%). The

cattle crossbreeding programme has been developed substantially in other provinces. Son La

province is an example, where crossbred cattle accounted for around 11.0% in 1999 (Huyen et

al., 2006), and around 15% by 2005 (Tang, 2007 - personal communication).

Plans call for crossbreeding to increase by roughly 50% the provincial cattle population in the

next five years (about 100,000 head) from around 300 head in 2005 (Project document for

cattle development - Bac Kan Provincial People’s Committee, 2006) (Table 1). It has been a

challenging plan for the province. In early 2006, the province imported only 18 bulls for

crossbreeding, but only one bull survived and developed well while other bulls died or were

eliminated due FMD and other reasons. At the end of 2006, other crossbreeding herds were

imported into the province in order to reach the aims of the program. However, their impact

was limited, which could be explained by lack of farmer awareness, outbreaks of FMD and

the adopting of new technologies such as artificial insemination (Tra, 2007).

0.0

3.0

6.0

9.0

12.0

1998 1999 2000 2001 2002 2003 2004 2005Gross output of livestock and

poultry (1000 tones)

Page 58: BEEF CATTLE SYSTEMS IN THE CONTEXT OF SUSTAINABLE ...bictel-fusagx.ulg.ac.be/ETD-db/collection/... · (2011). Beef cattle systems in the context of sustainable agriculture in Bac

40 Bibliography

Table 1: Population of cattle by breed in Bac Kan province

Breeds 2001 2002 2003 2004 2005

Yellow cattle (head) 32,335 33,456 35,082 36,948 38,276

Red Sindhi crosses (head) - - 264 293 273

Source: Bac Kan DARD, 2006

Numerous programmes for crossbreeding (Laisind) cattle4 have been introduced into all

districts. However, the imported breeds have not adapted well to the hilly and mountainous

regions for various reasons. However, the development of crossbreeding cattle in Cho Don

District, Bac Kan province, was an exceptional example, implemented during 2003–2005

(Bac Kan DIST, 2005). There were 38 crossbred calves born over the two years of the project.

According to provincial authorities, the strong development of that programme was the result

of high investments, its small scale, and widespread cooperation and support from different

organisations. First, the high investment costs were subsidized, e.g., each crossbreeding bull

was subsidized at around 15 mil. VND for the two years period, including 100% of breeding

costs, grass variety costs, supplemental concentrate feeds (1.0 tonne), veterinary costs,

fertiliser, silage tank, and stable. Moreover, each selected local cow-calf was given a subsidy

of around 9.5 mil. VND in the given time, including 70% breeding costs and other supports.

Secondly, this programme was conducted in a limited area (one district) and on a limited scale

(4 households keeping bulls for crossbreeding and 22 households keeping local cow-calf

pairs). Moreover, this a scientific research rather than a development program. Lastly, other

supports were provided, including 50% subsidy of the interest rate, training in artificial

insemination, training in silage processing and management skills, and field trips. Technicians

and livestock specialists received high salaries in order to help farmers carry out the

programme.

Cattle production in Bac Kan was a small-scale production, divided into free grazing, part-

time grazing, and cut and carry. Free grazing is the traditional practice in most ethnic minority

groups. In the study area, the free-range system is identified as households who allow cattle to

graze freely without being tended by the owners. The free-range system has also been

described by Tra (2007) and Nho (2003). In selected households, a regular check was

conducted daily, weekly or monthly according to individual family strategies and labour

availability. Households practising this system have good market access but experience high

land pressure. Part-time grazing has gradually replaced free grazing due to increasing limited

land area. Grazing cattle part time is currently the predominant method used in cattle

husbandry throughout the country. In cropping season, farmers keep their stock at home in the

morning, and the owners take them out to graze in the afternoon. After harvesting, cattle are

allowed to graze all day in the fields until the next crop is ready for planting and they are

housed in a stable at night. Cattle graze on unplanted land, common land or fallow land. This

method is also described in Tra (2007). The cut-and-carry method is practiced mainly by the

H’Mong minority. This feeding system is characterised by households keeping cattle in a

corral and cutting and carrying feed resources to fatten the cattle. This system is also practiced

in other areas such as the Red River Delta. However, different from others, only mature male

animals are fattened this way in the study area in H’Mong households. All bulls over three

4 Crossing Red Sindhi with local cattle has been developed since the 1920s. The distinctive reddish coat of this

animal can be seen throughout the country nowadays, resulting mainly from the national crossbreeding

programme namely “Sindhi-sation” (Ly, 1995; MARD, 2006). The offspring of crossbred Red Sindhi and

Yellow cattle in Vietnam are called Laisind.

Page 59: BEEF CATTLE SYSTEMS IN THE CONTEXT OF SUSTAINABLE ...bictel-fusagx.ulg.ac.be/ETD-db/collection/... · (2011). Beef cattle systems in the context of sustainable agriculture in Bac

Bibliography 41

years old are often confined for fattening throughout the year or for a certain time before

selling (from one to three months or longer time depending on the owner’s capacity).

Supplementary feeds such as maize or pig feed (a combination of vegetables, banana stems

with or without maize commonly cooked for pigs is fed in part to cattle) are often used, while

the main feed resources are natural or planted grass and forest tree leaves. However, other

cattle belonging to the household such as cows, calves, heifers, and steers, are allowed to

graze part time. Farmers explain that bulls can be fattened efficiently this way in a short time,

more so than for other cattle types (Niem et al., 2001; Nho et al., 2003; Huyen et al., 2006;

Tra, 2007).

Slopes and communal pastures are often used for cattle grazing in Bac Kan province.

However, there is no report or data related to these production systems of cattle. Generally,

management of cattle production management was poor. Vaccination programmes have been

implemented for only about 40% to 50% of the total animals in the province (Bac Kan

Veterinary Department, 2008). The poor performance of vaccination programmes was

explained by their being poorly perceived by farmers and the topography isolation of the areas

in which they live. Recently, high-yield grass varieties have been planted in many districts

under the provincial cattle development programme since 2006. However, the grasses were

planted limited regions and in small areas.

The province implemented the cattle herd development plan during the period 2006–2010

(Figure 19). Over the five years (2006–2010), the cattle population was expected to increase

by around 60% annually, on average, up to 184,016 head from 38,549 head in 2005. This

great expansion was to be achieved by importing high quality male and female cattle from

other provinces for crossbreeding, as well as selecting high quality local cattle breeds. The

local breeds would be improved using Zebu breeds or their crossbreeds, with over 1,100 bulls

and 28,500 cows being imported. Correspondingly, local cows will be selected with support

from the government. In addition, local bulls, especially H’Mong animals, will be evaluated

and chosen for improvement. Poor sires will be culled or castrated. In fact, getting the cattle

population up to over 180,000 head by 2010 or to 300,000 head by 2015 is a challenging

mission for the provincial authorities and farmers due to both the time and animal population

factors. Looking in more details at the actual cattle population and development plan, the

actual cattle herd was far lower than that on the development plan as proposed by the

provincial policy makers.

Page 60: BEEF CATTLE SYSTEMS IN THE CONTEXT OF SUSTAINABLE ...bictel-fusagx.ulg.ac.be/ETD-db/collection/... · (2011). Beef cattle systems in the context of sustainable agriculture in Bac

42 Bibliography

Figure 19: Development trend (2005–2008), plan (2006–2015)

of the provincial cattle population Source: Bac Kan PSO, 2006; 2008; Bac Kan People Committee Report, 2005

The cattle herd by districts from 2003-2008 is presented in Figure 20. Apparently, the biggest

cattle herd in this province is located in Pac Nam district, where the cattle population was

9,778 head, accounting for over one quarter of the total cattle in Bac Kan province. Cattle

herds in the districts from 2003 to 2007 increased in six out of seven districts, with especially

sharp growth recorded between 2006–2007, except for Ba Be district, where there was a

decreased to 7,800 head after a maximum of over 9,200 head in 2005. The strong increasing

during 2006–2007 was the result of government cattle projects, including support policies

such as breeding subsidies, feeding resources, planting grass, and giving credit as mentioned

above. Despite the great support from the government, a heavy decrease of the cattle herd was

seen in 2008, possibly because of reduced cattle imports from other provinces while cattle

development projects were being implemented in Bac Kan.

Overall, Bac Kan is a poor province, strongly dependent on the agricultural sector for many

purposes such as food, employment, livestock feed resources, and income. The development

of the agricultural sector remains a high priority in the overall provincial economic

development plan, which focuses on poverty alleviation and enhances economic growth.

More than two third of the labour force work in this sector. Agriculture is the leading

contributor to the total GDP of the province. Bac Kan gross outputs from agriculture were

small compared to other provinces in the NMR. Crop production nevertheless still plays a

predominant role, contributing the most important part in terms of gross outputs of agriculture

as well as being a cash resource for the province. Moreover, crop production also accounted

for the central component of livestock production in the form of grain and by-product feed

resources. In the wintertime, by-products are an important feed resource for ruminants in the

province. However, Bac Kan has a great potential for cattle development due to the abundant

source of land area, especially non-used land considered unsuitable for crop production.

Cattle production has been a top priority in this mountainous province, due to the existing

potential. However, cattle production seemed to be lagging, remaining mainly in the hands of

small-scale farmers.

0

50

100

150

200

250

300

2005 2006 2007 2008 2009 2010 2015

Ca

ttle

her

d (

1,0

00

hea

ds)

Real cattle herd Cattle herd in the development plan

Page 61: BEEF CATTLE SYSTEMS IN THE CONTEXT OF SUSTAINABLE ...bictel-fusagx.ulg.ac.be/ETD-db/collection/... · (2011). Beef cattle systems in the context of sustainable agriculture in Bac

Bibliography 43

Figure 20: Cattle population by districts during 2003–2008 Source: Bac Kan PSO, 2009

2.2.3 Description of Pac Nam district and its characteristics

2.2.3.1 General information

Pac Nam was the poorest district in the province with 72.8% of its inhabitants living under the

poverty line in 2005 (Pac Nam People’s Committee Report, 2006), an extremely high figure

compared to the provincial poverty rate (50.8%). However, in 2007, there was a sharp

decrease of over 20%, leaving 50% of the people in the poverty bracket, but still higher figure

than elsewhere in Bac Kan province. This district was set up in 2003, separated from Ba Be

district. The district authorities are also very interested in policies that might help to improve

agriculture sector development. The cattle sub-sector is seen to be the most developed among

districts and town in the province, based on the cattle population and cattle density. The

potential for cattle development in the district is based on available natural resources (land

areas) and cattle markets. Pac Nam district shares borders with Cao Bang and Tuyen Quang

provinces and Ba Be district. It is located approximately 85.0 km from Bac Kan town and

250.0 km from Hanoi. Pac Nam’s natural land area is 473.6 km2, occupying about 9.8% of

Bac Kan’s total land area. The entire population of this district is 27,950 persons, accounting

for 9.3% of provincial population, of which 100% live in rural areas. The population density

was slightly lower than the provincial population density in 2005 (59.0 persons per km2

compared to 63.0) (Pac Nam District Statistical Office - DSO, 2008).

Almost all of the people in this district work in rural areas, but agriculture land accounted for

a very small part of the total land of the district (9% or 4,408.4 ha) in 2007. Forest land held a

dominant share at 42% and unused land represented for about 49% of the total land in the

district (Figure 21). The high proportion of unusable land5 includes hills and bare, rocky

mountains for the most part. The hills and mountains are not very suitable for crop

production, but could be developed for forestry. A large part of that area has been used for

cattle and buffalo grazing land. However, the development of forest areas based on

5 The term “unused land or non-usable land” was explained in the part 2.2.2.2

0

2

4

6

8

10

12

14

2003 2004 2005 2006 2007 2008

Catt

le p

op

ula

tio

n b

y d

istr

ict

(1000 h

ead

s)

Ba Be

Pac Nam

Ngan Son

Cho Don

Na Ri

Bach Thong

Cho Moi

Page 62: BEEF CATTLE SYSTEMS IN THE CONTEXT OF SUSTAINABLE ...bictel-fusagx.ulg.ac.be/ETD-db/collection/... · (2011). Beef cattle systems in the context of sustainable agriculture in Bac

44 Bibliography

Programme 3276, National 661 Programme

7 has absorbed a large share of that resource. Thus,

it can be said that Pac Nam district has a great potential in terms of land use, especially the

large area of unusable land, for improvement of the agricultural sector.

Figure 21: Land area and its distribution (hectares) for different sectors in 2007 Source: Pac Nam DSO, 2008

Livestock production accounted for a small part of the district’s total gross output during the

period 2004–2008. However, there was rapid growth in livestock gross output in 2005

compared to 2004 and several years later, to a peak of 9,343 mil. VND, due to the heavy

development of swine, cattle and poultry production after the district was set up. Poultry

disease and FMD affecting swine and ruminant production caused a decline of the gross

output in livestock production. On the other hand, the gross output of crop production

increased gradually year by year, from 22,601 mil. VND in 2004 to 31,924 mil. VND in 2008,

an annual rate of 28% (Figure 22).

6 Programme 327 was established pursuant to Decision No. 327 of the Prime Minister on the policies and

objectives in re-greening barren land and hills, including protection of existing forest areas, natural

regeneration, and forest plantations from 1993 to 2000. 7 The Vietnam government has implemented the National 661 Programme approved by Parliament in 1997 and

by the Prime Minister with Decision No. 661/QD–TT dated July 29, 1998 with the purpose of achieving 5

mil. hectares of reforestation and of increasing nation-wide forest coverage up to 43% of the total land cover

throughout the provinces from 1998–2010.

Agriculture

4408.4 ha

9%

Forestry

19,590.3 ha

42%

Non-usable

land

22,570.8 ha

49%

Page 63: BEEF CATTLE SYSTEMS IN THE CONTEXT OF SUSTAINABLE ...bictel-fusagx.ulg.ac.be/ETD-db/collection/... · (2011). Beef cattle systems in the context of sustainable agriculture in Bac

Bibliography 45

Figure 22: Cultivation crop and livestock gross outputs in Pac Nam district Source: Pac Nam DSO, 2009

Poultry production decreased from 94,000 birds in 2004 to 92,000 in 2005 and then dropped

to 89,000 birds in 2006. The poultry population increased again during 2007 and grew sharply

in 2008. The swine population showed an explosion in 2005 (about 19,000 head), more than

20% compared to the year 2004 (16,000 head), which can be explained by the heavy

development of this sub-sector in order to compensate the losses in poultry production due to

the birth flu outbreak and other outbreaks (Figure 23). Particularly, the buffalo herd increased

slightly, contrary to the provincial and country production trend. The prevalent use of buffalo

for draught power in lowland field areas, which are difficult to plough and the development of

new market demands may explain this, especially since buffalo meat is sold at the same price

as beef. The cattle population climbed from roughly 6,200 head in 2004 to over 7,600 head in

2008. Notwithstanding, a decline of 10% was recorded in 2005 compared to 2004 due to an

FMD outbreak; and then a increase in 2007, peaking at around 12,200 head due to

government support policies. Finally, a decrease of around 20% compared to 2007 was seen

in 2008. Cattle production is one of the most important livestock sub-sectors in the district.

The availability of land and cattle markets is the driving forces contributing to the

development of cattle production in Pac Nam district (it has a designation of 45% of non-

useable land and well patronised cattle markets are available in the district). Detailed

information on cattle markets in Pac Nam district is given in the following section of this

chapter.

In early 2006, there were only two bulls for crossbreeding imported into the district but one

bull was lost due to FMD. Then 40 crossbreeding bulls were imported at the end of 2006.

Simultaneously, the selection programme of local Yellow bulls and cows was carried out with

a plan of 217 selected bulls and 1,000 selected cows (Pac Nam Annual Report, 2007). High

quality local cows from neighbouring provinces such as Tuyen Quang and Cao Bang were

also imported. Roughly 160 ha were sown with grass. However, diseases such as FMD,

Pasteurellosis affected many cattle. Other animals were kept in unfavourable conditions,

causing weight loss, roughening of their features, and draught inefficiency. Some households

that accepted the experimental cattle asked to give them back to the project (Tra, 2007). Tra

(2007) finds that the cattle development project remains an enormous challenge for the district

as well as the selected communes.

0

5

10

15

20

25

30

35

2004 2005 2006 2007 2008

Gro

ss o

up

ut

in a

gri

cult

ure

(10

00

mil

. V

ND

)

Crop Livestock

Page 64: BEEF CATTLE SYSTEMS IN THE CONTEXT OF SUSTAINABLE ...bictel-fusagx.ulg.ac.be/ETD-db/collection/... · (2011). Beef cattle systems in the context of sustainable agriculture in Bac

46 Bibliography

Figure 23: Development of livestock production by species in Pac Nam district Source: Pac Nam DSO, 2005; 2009

2.2.3.2 Cattle markets and cattle resources in Pac Nam district

Tra (2007) finds that one of the key advantages for cattle production in Bac Kan province in

general and Pac Nam district in particular is the prevalence of cattle markets, which is

relatively different from most provinces in the NMR of Vietnam. Available cattle markets

with a high demand from consumers resulted in a constantly high flow of live cattle through

these markets, which were considered convenient for trading cattle by local households.

However, as mentioned earlier, cattle production in the province is still under-developed. In

fact, the markets are vitally important because they offer farmers essential opportunities to

participate in economic activities (IFAD, 2003). Phuong (2008) mentions that farmers can

trade their available resources and thereby benefit from the buying and selling of agricultural

products in markets. However, in Vietnam, especially in the north, beef cattle markets are

seen to be under-developed compared to the market for other livestock products, although

cattle selling is considered to be one of the essential factors conducive to the development of

beef cattle.

There are three main cattle markets in Pac Nam district, namely Cong Bang, Boc Bo, and

Nghien Loan (Annexes 14, 15). Among those, the Nghien Loan market is referred to as a

wholesale cattle market and all of the live cattle were sourced from other local markets and/or

neighbouring markets in other provinces. The Cong Bang and Boc Bo markets are retail cattle

markets that open one or two days earlier than the Nghien Loan market, respectively, which

means that after trading in those ones, cattle were finally brought to the Nghien Loan market.

Normally, if cattle were not purchased in Cong Bang and Boc Bo, “leftover” cattle belonging

to live cattle retailers will be transported to the wholesale market. Owners (retailers) will have

to sell at a favourable price or even a somewhat discounted price to avoid further weight loss

before the next market day (five days until the next market day).

Cattle sold in the local markets of Pac Nam district often came from local farmers, retailers

and middlemen/collectors. Then, cattle in the local markets were sold into three channels—

slaughterhouses, farmers, and middlemen. Only about 5% of cattle are sold directly to

slaughterhouses located in Thai Nguyen, Bac Giang, Hung Yen and Hanoi. In fact, few cattle

are sold directly to slaughterhouses Van et al. (2005). The highest proportion of cattle was

purchased by middlemen (around 93% of cattle), who often deliver the animals to

86

88

90

92

94

96

98

0

5

10

15

20

25

2004 2005 2006 2007 2008

Po

ult

ry p

op

ula

tio

n (

1,0

00

bir

ds)

An

ima

k p

op

ula

tio

n (

1,0

00

hea

d)

Buffalo Cattle Pig Poultry

Page 65: BEEF CATTLE SYSTEMS IN THE CONTEXT OF SUSTAINABLE ...bictel-fusagx.ulg.ac.be/ETD-db/collection/... · (2011). Beef cattle systems in the context of sustainable agriculture in Bac

Bibliography 47

slaughterhouses as mentioned above or to those in southern Vietnam. Actually, a small

number of cattle were sold to southern Vietnam from the district markets. It depends on

demand and price differences between the two regions. Farmers who need cattle for breeding

purchased around 2% of the animals directly from markets. Another 3% of cattle for breeding

were bought by farmers through middlemen. In fact, selling and buying cattle in markets is an

easy transaction (Tra, 2007).

In the study sites, the main season for cattle trading is from August to around the end of

January or early February. From August onwards, field work was finished. Cattle and buffalo

were brought to the market for sale if households needed cash or wanted to change to other

better breeds. In these months, consumer demand increases as well, peaking at the Lunar New

Year (in January and/or February). Tra (2007) finds that the number of cattle sold in Nghien

Loan market often fluctuated between 300 and 500 head per market day during this season,

with a peak time of over 700-800 head (buffalo were often sold in smaller number). In other

markets, around 100-200 cattle were sold per market day during this season. Conversely, from

January-February through July, the number of cattle sold was considerably reduced,

especially after the Lunar New Year (around 100-200 head and 30-50 head in Nghien Loan

and other local markets, respectively). This might be explained by the low consumer demand

for beef and high demand for using cattle and buffalo as draught power for crop production.

In Nghe An province, Liem et al. (1997) find that the peak cattle trading season is between

March and April, when the new growing period starts and feed is relatively abundant. July to

September is the least attractive season due to farmers concentrating on cropping activities.

The difference between the two provinces may be explained by differences in geography and

cropping seasons and other characteristics. Specifically, during 2005-2007, movements of

cattle and buffalo in Pac Nam district and Bac Kan province as well as other neighbouring

provinces were greatly reduced. Trading in cattle markets dropped dramatically and the

highest number of cattle in each market day in the peak season varied between 100 and 150

head in the Nghien Loan market, whereas the other markets traded around 30-60 cattle. This

significant change is explained by the impact of a major outbreak of foot-and mouth disease

(FMD) in the province.

Cattle sold in the Pac Nam cattle markets were often sourced from local farmers,

neighbouring provinces, and from China. The number of cattle from the different sources

changed according to fluctuation of prices dictated by market and consumer demand.

Currently, local cattle accounted for about 30%, while approximately 60% come from

neighbouring provinces and 10% from China (brought in through its borders with Ha Giang

and Cao Bang provinces). In comparison, in 2005, Van et al. (2005) found that around 43% of

cattle in Bac Kan province markets were produced locally and 57% were from neighbouring

provinces such as Cao Bang, Tuyen Quang and Ha Giang. No information related to Chinese

cattle was included in their report. On the other hand, during 2007 and earlier, it was

estimated that around 15% of cattle purchased in Pac Nam markets came from local farmers,

while about 60-70% were Chinese cattle, and the rest were brought in from neighbouring

provinces, including Ha Giang, Cao Bang, and Tuyen Quang. Price disparity among the

different regions of Vietnam might be the major reason for this movement of cattle from other

provinces and China to the markets in Pac Nam district. Importantly, Vietnamese imports of

Chinese live cattle were small scale and not undertaken on a regular basis due to official

regulation. It is illegal for retailers and middlemen to import from the Chinese border in Ha

Giang and bring the animals through Cao Bang province. Live cattle were imported

exclusively for the purpose of slaughtering. This cross-border trade of cattle was carried out

with no veterinary and customs checks. Most cattle were moved along trails through natural

forests by local hired labour. There is no official information about the number of Chinese

Page 66: BEEF CATTLE SYSTEMS IN THE CONTEXT OF SUSTAINABLE ...bictel-fusagx.ulg.ac.be/ETD-db/collection/... · (2011). Beef cattle systems in the context of sustainable agriculture in Bac

48 Bibliography

cattle imported, their quality and epidemic disease control in these border provinces as well as

in Bac Kan province. Thus, no tax was collected and no disease control was performed on

these beef cattle from China. On the other hand, the illegal importing of live cattle through the

borders at lower prices and without veterinary controls may increase challenges for cattle

farmers having to compete with cheaper imported cattle and the threat of trans-boundary

communicable diseases.

During that time, a high proportion of cattle from Pac Nam markets was transported to

slaughterhouses in Hanoi. However, Chinese cattle were felt to be of lower quality, with dark

red-coloured meat compared to that of local cattle. According to owners of selected

slaughterhouses, they could be feedlot cattle that were fed a high percentage of concentration

and given rapid weight-gain supplements. From 2007 to the present, slaughterhouses in Hanoi

primarily purchase cattle from Thailand and Laos through the borders of the Central Region,

at lower prices than cattle from Pac Nam market. Interviews of several slaughterhouses

owners in Hanoi indicated that most of their fattened cattle purchased for slaughter were from

Laos and Thailand during 2009-2010, at a price of around 3,000-5,000 VND lower per kilo of

lean meat. Thus, Chinese cattle trading through Cao Bang and Ha Giang provinces have

decreased considerably in the markets of Pac Nam district.

Actually, no difference in price per kilo of lean meat was seen among cattle breeds sold in

markets. Cattle were bought according to the buyer’s evaluation of lean meat on the animal,

its sex, and age. This type of cattle evaluation is also described by Tra (2007); Ngoan and

Giang (2008). A study from QNRDP (2002) also describes similar buyer preference based on

lean meat yield. In all markets in the study area, two thirds of the cattle sold were male cattle

for slaughtering. Another third was cows and their calves, which were often sold together.

Normally, selling high quality, young cows as breeding animals to farmers might fetch a

slightly higher price, as they will be kept for reproduction. Nevertheless, cattle were rarely

sold as breeding animals, with the exception of those destined for government cattle projects

at given times. On the other hand, female animals for slaughter were often sold at a somewhat

lower price per kilo of lean meat than male cattle due to their poorer lean meat potential and

higher fat, which translations at around 5,000 VND less per kilo of lean meat. Similarly, there

were differences of 3,000 to 5,000 VND recorded for older, mature cattle.

Besides, the lean meat capacity of cattle also depends on the breed’s shape—bone, rump, leg,

and shoulder structure—and the way the animals are raised. Cattle with big rumps, large

shoulders, small legs, and small bone frame are considered to have a high lean meat yield.

According to interviewees, the lean meat yield is about 30-35% of live cattle weight,

depending on cattle types and keeping styles, sex, age, and constitution. However, a lower

ratio (28%) can be seen in cattle of poor constitution and a higher one (up to 40%) for the best

quality cattle. QNRDP (2002) also found that lean meat yield ranges from 30% of live weight

for a cow in poor condition to up to 40% for the heavily muscled bulls of Yellow and Laisind

crossbreeds, respectively. Table 2 indicates an example of the differences between the two

cattle types with the same weight but differences in terms of lean meat performance. The

higher the proportion of lean meat, the higher the weight of lean meat achieved and the higher

the value obtained. A difference of over 1.35 mil. VND might result from a different

constitution of the animal’s body. This also demonstrates that a wrong estimation of lean meat

capacity will result in a significant economic loss.

Page 67: BEEF CATTLE SYSTEMS IN THE CONTEXT OF SUSTAINABLE ...bictel-fusagx.ulg.ac.be/ETD-db/collection/... · (2011). Beef cattle systems in the context of sustainable agriculture in Bac

Bibliography 49

Table 2: Example of differences in lean meat capacity of cattle

Cattle type Estimated lean meat

capacity (%) Live weight (kg)

Lean meat yield

(kg) Value (VND)

Animal 1 30.0 300 90 8,100,000

Animal 2 35.0 300 105 9,450,000

Difference between the

two beef animals 5.0 0 15 1,350,000

Source: Key person interview, 2009

According to interviews among farmers, retailers, middlemen, and slaughterhouse owners, the

lean meat price for live cattle in Pac Nam cattle markets was rather stable during the period

2001–2006, between 40,000 and 50,000 VND per kilo. However, during this period, the price

of beef in markets tended to fluctuate greatly upward. For example, in Hanoi markets, beef

wavered from around 40,000 to 80,000 VND per kilo (see Annex 3). Although the fluctuation

of the lean meat price in local markets was not so obvious in the last years, it climbed sharply

to around 70,000 VND in 2007 and stayed a constant level in 2008. Then, the price of beef

soared to around 90,000 VND per kilo by the end of 2008 and through 2009. Partially, the

soaring price of lean meat might reflect the impact of the economic crisis and severe inflation.

On the other hand, the price of beef in Hanoi markets fluctuated between 90,000 to around

110,000 VND per kilo. Thus, there was a large gap between the price paid for the estimated

lean meat yield of live cattle and the price of beef in markets. It is important to note that the

estimate of lean meat yield of cattle is very different from the amount of beef meat sold on the

market. Middlemen and slaughterhouse owners estimate only the lean meat yield per animal,

but after slaughtering, they also sell the animal’s bones, head, internal parts, hooves, and hide,

which explains in part the different price between estimated lean meat yield of live cattle in

the market and the final amount of beef sold to consumers. Despite the increasing price of

cattle, the growth of cattle herd size belonging to households in Pac Nam district and Bac Kan

province gradually fell or stabilized.

Interestingly, buffalo meat is valued almost the same as cattle meat in the markets. Most

consumers make no distinction between buffalo and cattle meat. However, buffalo meat is

considered a specialty food in many restaurants in urban areas. This might explain the

increasing number of households now keeping buffalo instead of cattle among the selected

households. It is found that in Bac Kan, the price of cattle and buffalo meat doubled between

1995 and 2000, indicating the potential emergence of profitable livestock systems in the

future (Helvetas, 2000).

In summary, Pac Nam district is the poorest among the districts and towns of the province.

However, cattle production in the district is the most developed in terms of quantity.

Availability of cattle markets and land resources in the district are major factors to promote

strong development of cattle production compared to others. Market accessibility is

considered as an important issue for the development of agricultural products. Nevertheless,

cattle production in the district is still under-developed, and the development of cattle

husbandry could be a key poverty alleviation strategy in the district. This begs the questions:

why has cattle production not developed as strongly as it should have in the context of

availability of cattle markets?

Page 68: BEEF CATTLE SYSTEMS IN THE CONTEXT OF SUSTAINABLE ...bictel-fusagx.ulg.ac.be/ETD-db/collection/... · (2011). Beef cattle systems in the context of sustainable agriculture in Bac
Page 69: BEEF CATTLE SYSTEMS IN THE CONTEXT OF SUSTAINABLE ...bictel-fusagx.ulg.ac.be/ETD-db/collection/... · (2011). Beef cattle systems in the context of sustainable agriculture in Bac

3 RESEARCH METHODOLOGY

Chapter 3 first describes the selection of research study areas at the commune level. In this

section, the main characteristics of selected sites as well as households are developed. The

selected areas are characterised in terms of topography, socio-economics, and infrastructure,

giving the rationale for the choice of the research sites and providing the basis for empirical

investigation. It then introduces the research design, selection of sample sizes and households,

and data selection framework. The next part presents the methods of collecting data and

challenges in data collection. Finally, there are approaches to inputs and outputs calculation,

selection indicators and description of selected indicators, and data analyses.

3.1 SELECTION OF STUDY SITES

The selection of the two communes was firstly conducted by skimming statistical data from

Pac Nam district statistical data office. Then the local authorities were contacted to get advice

and recommendations. Several communes matched the requirement (availability of cattle

markets, existing cattle feeding systems, and easy accessibility) were visited by direct

observation, and talks were held with communal officers and local persons. Additionally, a

collection of secondary data from those communes was also implemented to get direct insight

on their current situation. Finally, two suitable communes were selected, Nghien Loan and

Cong Bang.

3.1.1 Geographical situation of the selected communes

Brief information on all communes in Pac Nam district is presented in Table 3. According to

collected information in those communes, Cong Bang and Nghien Loan were chosen due to:

(i) Cong Bang commune is made up mostly of households of Tay minority practising the free-

range system and access to the commune is easy; (ii) the part-time grazing system is common

in most of the remaining communes in the district, but it is easy to access households in

Nghien Loan commune; (iii) the cut-and-carry system is practised in the uplands in both

communes where H’Mong people live; and (iv) cattle markets are located in both communes.

Cong Bang commune is located about 12 km from Pac Nam district centre, while Nghien

Loan commune is about 20 km from there. Another feature to note is that Nghien Loan

commune is located 10 km from Ba Be town, the formal district centre; whereas Cong Bang

commune is located around 40 km far from that (see Figure 11).

Some key statistical data of both communes are presented in Table 4. The natural area of the

selected communes is 56.1 and 56.6 km2, respectively (Pac Nam District Statistical Office,

2008). A high percentage of poor was recorded in both Cong Bang and Nghien Loan

commune in 2007 (52.9 and 53.2%, respectively), dramatically higher than the poverty rate of

the north-eastern region (21.4%). This figure is also lightly higher compared to the poverty

rate of Pac Nam district (50.9%) and much higher than that of Bac Kan province (38%).

There are major Tay, Nung, H’Mong and Dao settlements in Nghien Loan commune, whereas

no Nung people live in the Cong Bang commune. Tay people accounted for the largest part of

these communes (around 40%), much lower than the average data of the Bac Kan province

(54.3%). The second biggest group, the Dao people, accounted for 43.1% and 25.0% in the

Cong Bang and Nghien Loan communes, respectively, these figures are dramatically higher

than the provincial figure (16.5%). The H’Mong population is around 16.1 and 19.1%,

respectively, which were significantly higher figure compared to the provincial figure (5.4%).

Page 70: BEEF CATTLE SYSTEMS IN THE CONTEXT OF SUSTAINABLE ...bictel-fusagx.ulg.ac.be/ETD-db/collection/... · (2011). Beef cattle systems in the context of sustainable agriculture in Bac

52 Research methodology

Table 3: Brief description of all communes in Pac Nam district

Communes Location and topography Free-range Part-time grazing Cut-and-carry

Cong Bang 12 km from district centre

Good communication route

Easy to access to commune

Has a cattle market

***

-

***

Giao Hieu 8 km from district centre

Good communication route

Easy access to commune

No cattle market

*

households

scattered

**

*

Nhan Mon 10 km from district centre

Poor communication route

Easy access to commune

No cattle market

*

households

scattered

**

***

Boc Bo In the central of the district

Good communication route

Easy to access to commune

Has a cattle market

*

***

*

household

scattered

Bang Thanh 22 km from district centre

Poor communication route

Difficult to access to commune

Small cattle market

***

-

**

Xuan La 7 km from district centre

Good communication route

Easy to access to commune

No cattle market

*

households

scattered

**

*

household

scattered

Nghien Loan 20 km from district centre

Good communication route

Easy access to commune

Has the largest cattle market

*

households

scattered

***

***

An Thang 35 km from district centre

Harsh geography

Very poor communication route

Difficult to access to commune

No cattle market

*

households

scattered

* * *

*

household

scattered

Cao Tan 20 km from district centre

Harsh geography

Very poor communication route

Difficult to access to commune

No cattle market

*

households

scattered

**

* * *

but difficult

access households

Co Linh 13 km from district centre

Poor communication route

Difficult to access to commune

No cattle market

*

households

scattered

**

* * *

but difficult

access households

Note: ***large household number; **medium household number; *small household number; - no or few

households

Page 71: BEEF CATTLE SYSTEMS IN THE CONTEXT OF SUSTAINABLE ...bictel-fusagx.ulg.ac.be/ETD-db/collection/... · (2011). Beef cattle systems in the context of sustainable agriculture in Bac

Research methodology 53

Table 4: Some key statistical data for the selected communes

Description Cong Bang commune Nghien Loan commune

Total natural land (km2) 56.1 56.6

Total agricultural land (ha) 317.1 619.3

No. of villages 12 15

Poverty rate (%) 52.9 53.2

Food amount per person (kg) 420 430

Minorities (% households)

- Tay 40.1 40.0

- Nung 0.0 14.4

- H’Mong 16.1 19.1

- Dao 43.1 25.0

- Others 0.7 0.5

Source: Pac Nam District Statistical Office, 2008; commune statistical data 2008

3.1.2 Population and land resources

Cong Bang commune has a total population of 2,510 persons, half compared to that in Nghien

Loan commune (5,170 persons). Therefore, with almost the same natural land area, the Cong

Bang commune had a dramatically difference in population density (42.7 person/km2)

compared to that in Nghien Loan commune (91.3 persons/km2). The location of the

communes might partially explain the different population densities. In former times, Nghien

Loan was located rather near the district centre (formally Ba Be town), while Cong Bang was

far from it (around four times as far). In addition, the agricultural land area in Nghien Loan is

twice as large as the agriculture land in Cong Bang. Thus, population density in these

communes was considerably different from the average population density in the province

and district. Family size in both communes was equal (around 5.5 persons), noticeably

different compared to the average provincial figure (4.3 persons) (Table 5). Around 99.6% of

the households in Cong Bang commune are involved in the agricultural sector, and 97.3% in

Nghien Loan commune. Thus, the proportion of agricultural households in these communes is

also dramatically higher compared to the provincial figure (84%).

Page 72: BEEF CATTLE SYSTEMS IN THE CONTEXT OF SUSTAINABLE ...bictel-fusagx.ulg.ac.be/ETD-db/collection/... · (2011). Beef cattle systems in the context of sustainable agriculture in Bac

54 Research methodology

Table 5: Population, family size, and number of households in the study area in 2007

Criteria Cong Bang commune Nghien Loan commune

Total population (persons) 2,510 5,170

Population density

(persons/km2)

42.7 91.3

Average family size (persons) 5.5 5.3

Number of households 454 971

Agricultural households 452 945

Source: Pac Nam District Statistical Office, 2008; Commune statistical data, 2008

Land use by different activities is presented in Figure 24.

Figure 24: Structure of land resource in the selected communes in 2007 Source: Pac Nam District Statistical Office, 2008; Commune statistical data, 2008

Surprisingly, over 97% of households in the selected communes engaged in the agriculture

sector, but agricultural land accounted for just 317.1 and 619.3 hectares in Cong Bang and

Nghien Loan communes, which represented for only 8.6 and 11.0% of the total land area in

the selected communes, respectively. Forest area accounted for nearly half of the land

resource in Cong Bang (approximately 48.3% or 2,576.3 ha), whereas Nghien Loan commune

had around one quarter of forest land (26.8% or 1,514.8 ha). An extremely high proportion of

the land resource in Nghien Loan commune was unused land, which accounted for 60.0%

(equal to 3,388.2 ha), whereas a smaller area of unused land area was recorded in Cong Bang

commune that amounted to 41.5% (2,213.3 ha). Non-agriculture land accounted for a small

percentage in both communes (1.6% and 2.1%). Although, unusable land and forestland is

larger in Nghien Loan compared to that in Cong Bang communes, the higher available land

resources for cattle grazing is still recorded in Cong Bang commune due to the population in

Nghien Loan commune is almost double in Cong Bang communes. Thus, free-range cattle

production in Cong Bang commune might exist that it probably take advantages of large

forest land and unusable land resource as well as low population density.

0.0

1.0

2.0

3.0

4.0

5.0

6.0

Cong Bang Nghien Loan

Lan

d a

rea

by

cate

gori

es (

1000

ha)

Non-Agriculture

Unused

Forest

Agriculture

Page 73: BEEF CATTLE SYSTEMS IN THE CONTEXT OF SUSTAINABLE ...bictel-fusagx.ulg.ac.be/ETD-db/collection/... · (2011). Beef cattle systems in the context of sustainable agriculture in Bac

Research methodology 55

3.1.3 Agricultural sector in the selected communes

Cong Bang and Nghien Loan communes were completely agriculture-based communes. All

farmers were strongly dependent on it for subsistence production and income. The major

crops in the study communes were rice, maize, soybean and cassava (Table 6). Cassava

production accounted for a small percentage compared to other crops. The maize area is as

large as that for rice production in Nghien Loan, perhaps because of the pig production

development in a semi-intensive system.

Figure 25 presents the animal population by commune of four major animal types in 2007.

That of Nghien Loan commune is two to three times higher compared to Cong Bang

commune for three out of the four types studied, except for buffalo, which were slightly lower

in number (1,100 head versus 1,179 head). It is important to note that households keeping

cattle accounted for roughly 55-60% in the selected communes.

Table 6: Major crop production in the selected communes

Crops Cong Bang commune Nghien Loan commune

Area (ha) Production yield (tons) Area (ha) Production yield (tons)

Maize* 108.4 335.0 316.0 978.0

Rice* 167.6 719.0 316.0 1357.0

Soybean - - 257.5 514.1

Cassava 25.0 250.0 12.4 136.0

Source: Pac Nam District Statistical Office, 2008; Commune statistical data, 2008

* Maize and rice are double crops grown in the fertile fields of both communes

Figure 25: Livestock population in the selected communes in the study area in 2007 Source: Pac Nam District Statistical Office, 2008; Commune statistical data, 2008

3.1.4 Forest development in the selected communes and its orientation

Figure 26 presents the planted forest area and percentage of households planting forest by

commune in 2007. Planted forest occupied a rather small area, only 6.6% and 3.5% of the

0

2

4

6

8

10

12

14

16

Cattle Buffalo Poultry Pigs

To

tal

liv

esto

ck h

erd

(1

,00

0 h

ead

s)

Cong Bang

Nghien Loan

Page 74: BEEF CATTLE SYSTEMS IN THE CONTEXT OF SUSTAINABLE ...bictel-fusagx.ulg.ac.be/ETD-db/collection/... · (2011). Beef cattle systems in the context of sustainable agriculture in Bac

56 Research methodology

total forest area in Nghien Loan and Cong Bang communes (around 99.6 ha compared to 89.9

ha), respectively. It is also noteworthy that a very low percentage of households (8.4%) in

Cong Bang commune planted forest. The number of households in Nghien Loan who

involved in planting forest is over four times higher than that of Cong Bang. On the other

hand, households in Cong Bang commune planted a larger forest area per household on the

average than in Nghien Loan, on which they planted 4.5 Bung more (10.9 Bung versus 6.4

Bung, respectively) (1 Bung = 1,000 m2). It is important to note that the development of forest

cultivation related heavily related to cattle population due to the gradual limitation of

pastureland.

Figure 26: Forest development in the selected communes in the study area in 2007 Source: Cong Bang and Nghien Loan commune statistical data, 2008

1 Bung = 1,000 m2

3.1.5 Off-farm activities, infrastructure, and water source

In the Cong Bang commune, a high percentage of households were involved in off-farm

activities due to the strong development of the commune market, to which people living in

surrounding communes come to exchange goods and culture. They were all retailers or

service providers. In contrast, fewer households were involved in off-farm activities in

Nghien Loan commune. Generally, households in Cong Bang and Nghien Loan had rather

good access to infrastructure such as roads, electricity, primary schools and medical stations.

However, only 54.6% of households in the Cong Bang commune had access to electricity,

while a higher percentage of households in Nghien Loan commune did (67.4%). Particularly,

households located in remote areas of the selected communes had difficulties in accessing not

only electricity but also schools and medical stations. In addition, neither commune had a

high school, although there is one in the district. Overall, developing cattle production

remained an enormous challenge in the district as well as communes.

0

500

1000

1500

2000

2500

3000

Nghien Loan commune Cong Bang commune

Fo

rest

Area

(h

a)

Natural forest

Planted forest

0

5

10

15

20

25

30

35

40

Nghien Loan commune Cong Bang commune

Ho

use

ho

lds

pla

nte

d f

orest

(%

)

0

2

4

6

8

10

12

Pla

nte

d f

orest

area

per h

ou

seh

old

(B

un

g)

Proportion of household planted forest (%)

Average planted forest area

Page 75: BEEF CATTLE SYSTEMS IN THE CONTEXT OF SUSTAINABLE ...bictel-fusagx.ulg.ac.be/ETD-db/collection/... · (2011). Beef cattle systems in the context of sustainable agriculture in Bac

Research methodology 57

3.2 TARGET GROUP SELECTION

3.2.1 Selection of cattle farming households

Selection of households and cattle feeding systems was made using both stratified and

random selection. Households in the two communes keeping cow and calf pairs were

stratified with the help of village heads and other local authorities. Then, the simple random

technique was applied to select each household category from the lists.

The simple random technique is easy to handle compared to other techniques (Wolff, 1996

cited by Huyen, 2004). Using simple random sampling requires planning, high survey costs

and is comparatively restrictive; a rather accurate estimate of the total population can be

obtained because sample selection is based on equal probabilities (Doppler et al., 2002).

Nevertheless, samples taken from defined groups of households should be sufficiently large to

allow valid statistical requirements for analyses to be drawn and to avoid random error (Udo

et al., 1998, Dopple et al., 2002; Sen, 2005). The selection of sample size in the study also

depended on the number of households in each class, the available capacities (time and funds)

for the study, and the degree of homogeneousness of the population in the study area. In

addition, easy accessibility to investigated households is also an important criterion to select

them. Only 15 H’Mong households using the cut-and-carry system were selected in each

commune. Just 30 households using the free-range system in Cong Bang commune were

chosen. And 37 households in Nghien Loan were selected for part-time grazing. Hence, 97

households in the three cattle feeding systems were selected for the study (Table 7). It is

important to note that the sample size of each system is not repeated in each table or figure

henceforward; with exceptions for special cases, for which their sample size will be indicated

clearly in tables/figures.

Table 7: Number of selected households per cattle systems

Cattle feeding systems Cong Bang commune Nghien Loan commune Total

Cut-and-carry 15 15 30

Free-range 30 - 30

Part-time grazing - 37 37

Total 45 52 97

3.2.2 Selection of stakeholders in cattle markets and cattle marketing chains

Due to time and funding restrictions as well as the limited number of stakeholders at some

stages, stakeholders in the cattle marketing chain were selected for analysis, as follows: 5

retailers in live cattle markets; 5 groups of live cattle middlemen in cattle markets; 3

slaughterhouses in Hanoi; 2 slaughterhouses cum retailers in Bac Kan; 4 beef wholesalers in

Hanoi markets; 3 beef retailers in Hanoi markets (Annex 7); and 4 local authorities.

3.2.3 Selection of other target groups

The following stakeholders were considered as key ones participating in the data collection:

(i) local authorities (chair or vice chair of the people’s committee); (ii) representatives or

heads of departments of agriculture, veterinary medicine, and extension services; (iii)

Page 76: BEEF CATTLE SYSTEMS IN THE CONTEXT OF SUSTAINABLE ...bictel-fusagx.ulg.ac.be/ETD-db/collection/... · (2011). Beef cattle systems in the context of sustainable agriculture in Bac

58 Research methodology

representatives or heads of mass and community-based organisations such as farmer unions,

women’s union, youth league, etc. These stakeholders were meant to be at all levels

(province, district and commune). Therefore, different interviews were organised separately at

different levels to ensure that the data/information and findings were diverse and inclusive of

different voices, power levels and interests.

3.3 STUDY FRAMEWORK

Figure 27 presents a framework for the study based on the objectives of the study, the context

of study areas, and the conceptual framework of cattle production and sustainable agriculture.

Figure 27: Study framework

3.4 CONCEPTUAL MODEL OF COLLECTING AND ANALYSING DATA

A data collection and analysis procedure is conducted following the steps in Figure 28. Two

questionnaires were designed according to the data analysis framework and required

indicators. The questionnaires were pre-tested, modified, and amended twice in order to

collect the maximum required data. Following this, the data bank was designed and final

sample sizes were determined. Selection of the sample was made afterwards. Formal data

collections were carried out to gather needed data. Finally, the collected data were entered

into the data bank and checked prior to analysis. The databank was built to safeguard,

Page 77: BEEF CATTLE SYSTEMS IN THE CONTEXT OF SUSTAINABLE ...bictel-fusagx.ulg.ac.be/ETD-db/collection/... · (2011). Beef cattle systems in the context of sustainable agriculture in Bac

Research methodology 59

formalise and summarise the collected information using Microsoft Excel Version 2003.

Quantitative and qualitative collected data were coded. Data checking was conducted every

day after carrying out the surveys. Extensive checks and cross-checks were implemented

during the survey time to avoid missing data or errors. Unexplained data were treated as

missing values. Following sections present detail information of those steps and approaches

used.

Figure 28: Procedure for data collection and analysis

3.4.1 Data collection and data sets

3.4.1.1 Selection of PRA tools

A range of PRA tools used to collect data in the study is presented in Table 8.

3.4.1.2 Structured questionnaire

The main tool was formal a survey using structured questionnaire. The formal survey is

conducted using two structured questionnaires designed to gather the required data. Pre-tests

of the questionnaires were carried out twice. The final versions were revised and completed.

The collection of data was conducted by a multi-visit survey, which is thought to be much

more accurate than a single visit survey since it offers the opportunity for various cross-

checks.

The first structured questionnaire was organised into three parts. Part 1 included: (i) general

information such as household characteristics: family composition, education, age, family

labour, land resource, farm size, land costs, off-farm activities; (ii) crop production: area,

yield, seasons, family consumption, selling and prices, inputs and price, by-products; and (iii)

Page 78: BEEF CATTLE SYSTEMS IN THE CONTEXT OF SUSTAINABLE ...bictel-fusagx.ulg.ac.be/ETD-db/collection/... · (2011). Beef cattle systems in the context of sustainable agriculture in Bac

60 Research methodology

livestock production (including beef cattle): breeds, numbers, performance, outputs, inputs,

feed, and prices.

Table 8: Tools and brief information collected in the study

Tools Related persons Information collected

Secondary data Government offices,

libraries, other sources

Information and data related to the study area and cattle

production

Formal survey Households

Household characteristics, crop and livestock production

Characteristics of current beef cattle feeding systems

Inputs and outputs of cattle production

Feed resources and services

Opinions and experiences of farmers

Potentials/opportunities and difficulties in beef cattle keeping

Case study Households

Detailed description of some households

Descriptive data useful to the illustration of the findings

Highlight the factors that influence the development of cattle

Calendar tool Households Investigate information about feed resources, planting seasons

Observation Households,

communes, pastures

Services, infrastructure, and attitude of interviewees

Communal pasture management to evaluate the pasture

situation

Key persons

interview

Official staff, retailers,

middlemen,

wholesalers, slaughter-

house owners

Grazing land and management

Opportunities and constraints in the cattle production system

Veterinary, extension services and their activity and

contribution to livestock production in general and beef cattle

in particular

Activities of other organisations and cattle production

Feed resources used by animals, area of pastures, etc.

All market information

Group discussion Households groups

from both communes

Considering the necessity to gather information on each

feeding system

Part 2 consists of: (i) characteristics of current beef cattle feeding systems: number of cattle,

breeds, changes of cattle during the last year, their management; (ii) production of beef cattle:

herd structure, reproductive performance, mortality, death lost, weaning age, etc.; (iii) inputs

and outputs of cattle production: purchased animals, feed resources and other expenses,

selling value, selling age, number of animals sold, animals slaughtered or given as presents,

and draught power hired out or used in the family, manure; (iv) feed resources used for cattle

and seasonality; strategies to make it over a shortage season, using communal pastures and

grasslands; (v) opinions of farmers about husbandry objectives and role of cattle in the

family’s economy, motivational factors, experience, management, diseases and risks, market

information, prices; (vi) fattening cattle: characteristics and efficiency; (vii)

potentials/opportunities and difficulties in beef cattle production over time; and (viii) time to

start keeping cattle, description of feeding systems and reasons for changing (historical

development of beef cattle production systems).

Part 3 includes: (i) credit issues and household demand; (ii) environmental issues and farmer

awareness; (iii) role of extension services and activities; role of other organisations and

activities related to cattle production; (iv) natural resources, ecological conditions, socio-

Page 79: BEEF CATTLE SYSTEMS IN THE CONTEXT OF SUSTAINABLE ...bictel-fusagx.ulg.ac.be/ETD-db/collection/... · (2011). Beef cattle systems in the context of sustainable agriculture in Bac

Research methodology 61

economic and institutional changes, culture, related to beef cattle production; (v)

infrastructure and services; and (vi) labour costs, capital costs, and capital sources.

The second questionnaire was designed to obtain information such as labour in cattle

production, manure use and storage, loss of cattle during cold outbreaks in 2008 and strategies

to cope, households who stop raising cattle and the reasons, time of feed resources shortage

and strategies, and development trend of their cattle herds over time.

SWOT analysis

SWOT analysis is a strategic planning tool employed to evaluate strengths, weaknesses,

opportunities, and threats which encountered in the developing beef cattle production in the

study area.

Figure 29: Activity worksheet in SWOT analysis of sustainable beef cattle production Source: Adapted from Arslan and Deha Er (2008)

The aim of the SWOT analysis is to identify the current situation of beef cattle, to derive

lessons learned, and to generate effective solutions for the future development of beef cattle

production in the study area in particular and the northern mountainous region of Vietnam in

general. The SWOT analysis was conducted through household discussions group in both

communes, data collected from household interviews and brainstorming. Strengths are

attributes of the farmers themselves, their resources as well as other conditions that are helpful

for achieving the sustainable development of beef cattle production in general and specific

feeding systems. The weaknesses identified are harmful to achieving the objective.

Opportunities and threats are external attributes, which are helpful or harmful to the

objectives of sustainably developing different cattle feeding systems in the future. The group

meetings were carried out using an activity worksheet listing all the questions related to

Strengths

What are existing advantages in households?

What are strengths in development of beef cattle?

What factors are supporting development?

What benefits may be derived from cattle

production?

How much are farmers aware about cattle

development in its social, economic and

environmental dimensions?

Opportunities

Where are good opportunities for the beef cattle

development?

What are interesting trends?

What changes are usual practices?

What technology is available for beef cattle

development?

What are good conditions for cattle production?

Threats

What obstacles are present?

What challenges will be encountered?

Are there required support and necessary

facilities available for farmers and their cattle

herds?

Is changing technology a threat?

What are the safety implications for farmers of

their family, society?

Weaknesses

What are existing disadvantages?

What factors are not supporting development?

What could be improved?

What is not being done properly?

What should be avoided?

What are obstacles to progress?

What elements need to be strengthened?

Where are complaints coming from?

Are there any weak links in the production

chains?

Activity worksheet

Page 80: BEEF CATTLE SYSTEMS IN THE CONTEXT OF SUSTAINABLE ...bictel-fusagx.ulg.ac.be/ETD-db/collection/... · (2011). Beef cattle systems in the context of sustainable agriculture in Bac

62 Research methodology

internal and external factors in the development of beef cattle production in the study area in

general or specific beef cattle feeding systems in particular (Figure 29).

3.4.1.3 Difficulties and challenges in accessibility to selected households and collection of data

The study was conducted among ethnic minority groups (Tay and H’Mong). Numerous

difficulties and challenges were encountered during the reconnaissance phase, household

selection and data collection using different tools because of language problems, topography,

time schedule, climate, and cropping seasons. In order to achieve a level playing field, as it

were, and to understand clearly the current situation of households in the selected areas, two

main female local interpreters were selected based on their knowledge of the Tay and

H’Mong languages, culture and geography and who work permanently in the communities. It

was first necessary to get some basic information about the Tay and H’Mong peoples and

their culture. The author lived together with the interpreters in the communes during the

reconnaissance phase and data collection to foster friendship with them and to promote a good

atmosphere. Close communication and discussion among us before and during the visits

helped the steps to go smoothly.

Additionally, the village leaders and local authorities also strongly supported the author while

carrying out the study, providing lists of households in villages and their characteristics, also

detailing the cattle production situation. Each visit and the name of households to be visited

were also announced to the local leaders in advance, who then turned back to the villagers.

They encouraged the villagers to stay at home to wait for us.

However, many communication and data collection difficulties were encountered when

working locally in the Tay and H’Mong languages. Most Tay people could speak Vietnamese

very well. Nevertheless, the length of the questionnaires and the technical agricultural

production terms made them unwieldy. Encouragement from the author and interpreters and

relating humorous stories helped loosen up the atmosphere among the interviewers and

interviewees. Based on their wrong or misleading answers, the questions were often

simplified or reworded to make them more understandable and help us to gather the greatest

insight and information from the farmers.

Besides, during the interview and group discussions with local people on the lists, especially

H’Mong people, many visits were delayed due to local festivals, minority people’s feast-days,

the rice harvesting season, land preparation for planting, etc. This was further complicated by

the local geography. Therefore, during the rainy season or on rainy days (even light rain), we

often had to cancel our planned visits to the selected households.

Accessibility to H’Mong households was most challenging during the data collection phase.

All H’Mong households live in the remotest areas with poor quality, narrow, sinuous roads

dangerous to people unfamiliar with them. Especially under rainy conditions, the roods

become slippery and unsafe. In addition, such roads are often at the edge of deep precipices.

The long distance from the commune centres made it difficult to travel to the H’Mong

households. The H’Mong households in Coc Not village, Cong Bang commune, are around

15 km away with no public transportation and cannot be accessed on motorbike or bicycle,

only on foot. Normally, it took from 3.5 to 4.0 hours to walk to that village. Therefore, the

local interpreters and communal officers hesitated to visit those households frequently,

especially during the rainy season. On rainy days, we visited nearby households or

households living on flat land areas and easy to access. Sometimes trips had to be postponed

for a week or more. Each trip often took longer than expected because many H’Mong

householders were not at home, although their village leaders had informed them about the

Page 81: BEEF CATTLE SYSTEMS IN THE CONTEXT OF SUSTAINABLE ...bictel-fusagx.ulg.ac.be/ETD-db/collection/... · (2011). Beef cattle systems in the context of sustainable agriculture in Bac

Research methodology 63

visit because many H’Mong householders acted as cattle retailers. They have to purchase

cattle in neighbouring provinces and trade in local markets, which requires them to leave their

homes very regularly. And many of the wives could not speak the Vietnamese or Tay

languages well. Normally, an interview using questionnaires requires communication and the

contribution of both husband and wife in each family, where possible.

The selection of H’Mong households keeping cattle was rather difficult due to their specific

home locations. Five H’Mong households in Na Chao village, Cong Bang commune, met the

study requirements, living in the highest rocky mountains of the commune. Some of those

households were selected for the study. However, to visit them, the author and the interpreter

had to travel along a rocky and extremely slippery steep road for around 5 km. It took an hour

and half for us to go around 0.5 km around a large rocky mountain. We eventually decided

not to visit those households because they were scattered, access was so difficult and it was

simply too dangerous for us. For similar reasons we did not select certain H’Mong households

in Na Phai and Khau Tau villages in Nghien Loan commune.

Several visits were conducted in Khuoi Un village, Nghien Loan commune, to see Mr. Nong

Van Van family - one H’Mong household, but we could not meet him, except for his elderly

wife, who could not speak Vietnamese or Tay language. He was not at home even though the

village leader informed his family several times. He explained that he was busy with his own

business (trading cattle from different markets). Finally, the interview was conducted with his

wife and children with support of his neighbours and cross-checked with them. The interview

took a long time (nearly three hours). Questions were translated into the H’Mong language for

her by the village leader and explained by her neighbour. Her answers were cross-checked

with her neighbours and children and then translated into the Vietnamese language. However,

she did not understand many questions. The questions were changed or simplified to gain

correct information. A cross-check with her husband was done later on a Sunday, when he

was attended in a church service. Thus, to interview a H’Mong household, several visits were

needed. Other families could not be visited due to the limited accessibility (harsh geography

and scattered location, few households keeping cow-calf pairs in the long term).

Particularly, many interviews were conducted in the evenings after the workday, which meant

that data were collected from husband and wife as well as other family members (mature

children and their parents). Many visits took place during the planting, harvesting or

ploughing seasons, so that farmers could not stay at home in daytime for the interview. With

Tay households, accessibility to their house at night time is easier because most of them live

in the lowlands and are served by small roads. On the other hand, it took several days and

several trips to reach the H’Mong people. Very few households were interviewed in the

daytime; most were interviewed at night. Going to those households at night is difficult and

dangerous because they live at the top of different mountains and are a long way from each

other. Each night, only one or two households could be visited with help from the village

leaders, the interpreter and/or a host with whom we lived (and with assistance of many

torches!).

Thus, several lessons were drawn from our data collection work with the Tay and H’Mong

people: (i) to work closely and directly with the local interpreter and local authorities about

the purpose of the study and content of the interview and group discussions; (ii) to have a

well-prepared plan for the visit to local people; (iii) to inform the local people in advance

about the day and time of the visit and interview in order to avoid waiting for a long time;

(vi) to talk with both husband and wife and other family members during interviews in order

to cross-check collected data; (v) to interview with short and clear questions and the visit can

be organised at night if farmers are busy during the day with farm activities.

Page 82: BEEF CATTLE SYSTEMS IN THE CONTEXT OF SUSTAINABLE ...bictel-fusagx.ulg.ac.be/ETD-db/collection/... · (2011). Beef cattle systems in the context of sustainable agriculture in Bac

64 Research methodology

3.4.2 Identification of criteria in cattle production

3.4.2.1 Livestock in general and cattle production

Animal production data in general and cattle production data in particular were investigated

through major indicators including herd structure, reproductive performance, mortality rate,

stocking rate, and outputs (ILCA, 1990). Herd structure formed by different age and sex of

animals, e.g. breeding cows (>3 years), calves (0-6 months and 6-12 months), heifers (1-2

years and 2-3 years), mature bulls (>3 years), and steers (1-2 years and 2-3 years).

Reproductive performance was recorded for each cow owned by the household and its

breeding history through indicators such as: (i) first-calving age is the age (months) at which

the cow its first gives birth; (ii) calving interval is the average period of time (days) between

the two successive deliveries; (iii) reproductive life is the number of calves expected to be

produced per cow in her whole life at which the cow will be culled or eliminated; and (iv)

num. calves is number of calves born of each cow during the time of the interview in the

selected households.

Outputs from cattle production were determined as follows: (i) draught power and

transportation is the total time (days) cattle are used for draught power and transportation for

the farm and hired to other farms; (ii) manure amount is the estimated amount of manure used

for crop production; (iii) value of meat production of livestock sector (cattle production) in

households is determined by the number of animals sold to the market for slaughter and

slaughter for home consumption (animals slaughtered in one year for family consumption or

festivals) multiplied by price paid by middlemen; (iv) breeding animals sold as replacement

for heifers or steers determined by the current market price; (v) other animal sales for cash are

computed by the number of animals sold multiplied by the market price; (vi) disposal for

other reasons (e.g. gifts, ceremonies, exchange) is estimated by the number of animals at their

current market price; and (vii) increase in herd size is calculated by the total head of animals

at the end of the year minus total animal at the start of the year, adding in the number of

animals born or bought at their current price.

Inputs include feed resources, veterinary services, breeding or replacement animals, family

labour, hired labour, interest payment for loans, and depreciation of animal shelters. Mortality

is the number of animals that died and their estimated market value in order to estimate the

economic losses.

3.4.2.2 Feeding resources

General and key person interviews were used to investigate feed types and their growing

season covers the different kinds of feed used for cattle such as natural and planted grasses,

fodder tree leaves and shrubs, crop residues and agricultural by-products as well as seasons of

their growth and use. We also asked about the quantity of food supplements used during the

whole year and price. Crop, agricultural residues and by-products were estimated using the

Residue-to-Product-Ratios (RPR) approach (Koopmans and Koppejan, 1997). A value of

1.757 was used for the RPR of rice straw because it can actually be measured (Koopmans and

Koppejan, 1997). Measurement related to maize cobs referred to a value of RPR = 0.273.

Maize stalk yield was calculated using a RPR equal to 2.0 (value obtained from actual field

trials conducted by Bhattacharya et al., (1993) quoted in Koopmans and Koppejan (1997).

Maize husk will be determined by a value of 0.2 (Koopmans and Koppejan, 1997). Residues

from the agricultural sector might be used for many purposes such as fodder, fertiliser, fuel,

animal bedding, and fibre (Koopmans and Koppejan, 1997). Therefore, questionnaires and

Page 83: BEEF CATTLE SYSTEMS IN THE CONTEXT OF SUSTAINABLE ...bictel-fusagx.ulg.ac.be/ETD-db/collection/... · (2011). Beef cattle systems in the context of sustainable agriculture in Bac

Research methodology 65

key person interviews were used to determine the amount used as feed resources for animals

was calculated according to the average proportion that farmers use for their cattle.

3.4.2.3 Disease and losses

Data on diseases and losses in animal as well as cattle production were factored in, such as (i)

mortality of animals, i.e. the total number of animals that died from a disease, and the lost

value (risk of animals dying from diseases or other causes); (ii) diseases as determined by

name and symptom of common diseases to obtain an understanding of disease risk; (iii)

investment in prevention and treatment of diseases, i.e. the cost of veterinary services paid out

in one year; (iv) seasons of epidemic diseases or times in which epidemic diseases often

occur; and (v) farmer awareness about vaccination, parasite and disease prevention.

3.4.3 Identification of costs and returns from cattle production

3.4.3.1 Production costs

Squire and van der Tak (1975) reflect that documentation of benefits is more difficult than

calculation of costs. However, there are many debates on how to calculate the costs of

production. Costs of livestock production in general and cattle production in particular in

different feeding systems are investigated by the costs of hired land, hired labour, feeding,

breeding or replacement costs, veterinary services, interest payment for loans, depreciation of

cash invested in building animal sheds, classified into variable costs and fixed costs.

(a) Fixed costs

According to McConnell and Dillon (1997), fixed costs in a farm are those of input items,

usually services rather than physic things, which remain constant regardless of production size

or level of production outputs.

The first category of fixed costs is land. In the study context, the land resource used for cattle

production is only allocated as planted grass land, and in small area. In the study, cattle

production is the focus object, therefore, the value of planted grass land used for cattle

production is denoted as feeding costs, one of variable costs’ items as non-cash feed expense,

but not used as an item in fixed costs as usual.

The second category of fixed costs is depreciation of breeding cows and bulls raised by the

households. Actually, on the study site, the salvage value of a cow after bearing calves was

almost equal to its breeding value at purchasing time, with the exception of very old cows

purchased with a slightly lower price per kilo of lean meat yield than the others. Particularly,

cows in selected household were prone to be sold at any age. Selected households in the study

area often purchased a mature cow in the market or from their relatives or neighbours at the

estimated market price of its lean meat capacity, as with any other cattle type. Further, bulls

were not kept for breeding purposes alone, but as fattening animals for slaughter. Therefore,

breeding animals were estimated unchanged value during reproductive life until elimination

or slaughtering phase. Thus, depreciation expense of breeding cows and bulls in each year

also was computed at zero in the study.

According to McConnell and Dillon (1997) and Dillon and Hardaker (1993), the interest

payment for loans used for farm activities was computed as an expense in farm activities—an

item of fixed costs. In the study, loans used for livestock production in general and cattle

production in particular did not vary according to production scale or total outputs due to the

borrowed money often used a part to purchase from one to several cattle.

Page 84: BEEF CATTLE SYSTEMS IN THE CONTEXT OF SUSTAINABLE ...bictel-fusagx.ulg.ac.be/ETD-db/collection/... · (2011). Beef cattle systems in the context of sustainable agriculture in Bac

66 Research methodology

Opportunity cost of capital owned by households in farming activities is also considered as an

item in fixed costs (McConnell and Dillon, 1997). The household’s own capital included the

capital invested in the breeding herd for cattle production and the capital that remained (or the

capital remaining) from production of the last year (Hemme et al., 2006). Nevertheless, it

should be noted that the interest on capital owned by households are not included in the

calculation of the farm expenses (Dillon and Hardaker, 1993). The study also used this

determination in calculating production costs.

The last category of fixed costs is the depreciation and annual maintenance or repair of cattle

sheds. In the questionnaire, acquisition values in cash as well as the service life of the cattle

stable were given. In the context of the study, straight-line depreciation was used, which is

indicated as the simplest and most often used technique, in which the salvage value or

residual value of the cattle shelter was estimated by the value of the asset at the time it was

damaged or had to be disposed of, and equal to zero.

(b) Variable costs

According to McConnell and Dillon (1997), variable costs are those of input items the

amounts of which (usually but not necessarily proportionally) change according to size of

production or level of output of production.

The social prices of agricultural factors were based on the opportunity costs of inputs (Hai,

2002). In households, where no market value of inputs exists, their estimated values must be

imputed (McConnell and Dillon, 1997). In order to factor in crop residues used as animal

feeds if the farm had not actually purchased them, their opportunity costs might be based on

an estimate of what their utilisation was worth, for instance, what a farmer could earn at a job

outside the farm could be used as the wage cost of collecting and drying straw (McConnell

and Dillon, 1997). Although rice straw and maize leave are rarely sold among selected

households, their actual purchasing price in few households was still used for these

calculations. On the other hand, other farm-produced feed resources such as maize, rice and

rice bran were calculated at the farm-gate price.

The value of the amount grown grass brought to cattle as a feed resource is calculated as a

variable cost item. Grass yield is calculated by the amount of planted grass cut per day

multiplied by the number of days per harvesting period and then multiplied by the number of

harvestings per year. Grass value was estimated by price of grass sold in the markets or its

exchanged value among farmers.

Draught power used for land tillage was calculated by an expense for crop production as a

variable cost. Its value was estimated by total time (days) multiplied by the actual price paid

for hiring a buffalo or cattle draught animal per day for land preparation.

The cost for manure used for crop production was also computed by its selling price in the

study area despite of its rarely being traded.

Veterinary service and diseases’ treatment payment is calculated by actually expenses that

households pay for those issues. Breeding animal purchased in a year is actually payment of

households.

The determination of family labour cost is considered as a complex issue defined in different

ways in different studies. According to Fox et al. (2005), the full opportunity cost will be used

if the daily labour wage is obtained. Theoretically, the social price of labour is equal to the

value of the marginal product of labour employed in the next best alternative occupation (Hai,

2002). According to the author, there are many types of labour used in agriculture and

opportunities for off-farm employment are not always available. Therefore, in general, one of

Page 85: BEEF CATTLE SYSTEMS IN THE CONTEXT OF SUSTAINABLE ...bictel-fusagx.ulg.ac.be/ETD-db/collection/... · (2011). Beef cattle systems in the context of sustainable agriculture in Bac

Research methodology 67

the solutions is to estimate the opportunity cost as the shadow wage gained by the average

skilled labourer in the study region area. This calculation of labour cost may not be accepted

in regions where farmers, who often live in remote or mountainous areas, do not have chance

to find work in leisure time. Moreover, Squire and van der Tak (1975) explain that, in case of

severe unemployment, the shadow wage of labour would be zero. Similarly, Fox et al. (2005)

also use the zero opportunity cost for labour in case of high unemployment levels and when

alternative activities are idle. Thus, in this study context, opportunity cost of family labour

was not calculated in the variable costs of any production. However, the wages paid to hired

labour in production activities was still used as a wage rate to compare the efficiency of

labour for each production.

3.4.3.2 Product identification

(a) Main products

Major returns derived from beef cattle production include weight gain of the cattle herd, sold

cattle, breeding cattle and their social value. The gross livestock return in the study was

calculated according to the formula applied by Dillon and Hardaker (1993); Tung et al

(2007); Tung and Giang (2008):

(+) Sale of stock

(+) Value of stock used for domestic consumption: slaughter, gift, payment in kind

(+) Value of livestock products produced

(+) Value of stock at the end of accounting period

(-) All purchases of livestock

(-) Value of stock obtained as payment in kind and gifts

(-) Value of stock at the beginning of accounting period

The value of the cattle herd owned or produced at the start or at the end of the farming

accounting periods was estimated at market price through interviews and cross-check with

experts. However, there are two main alternatives to product prices, including net selling price

at the farm gate and gross replacement cost at the kitchen door. Net selling price was chosen

as the basic evaluation for non-cash output in livestock in general and cattle production in

particular, since this study measures the performance of the farm as a system (Dillon and

Hardaker, 1993)

(b) By-products

By-products of cattle production are manure and draught and transportation power. As

mentioned above, cattle manure was valued at the selling price. Cattle and buffalo draught

power as an item of returns from livestock and cattle production was valued at the price paid

for hiring draught animals in the area or at the cost of hiring labour for doing an equivalent

job (ILCA, 1990). When valuing the total farm income, the value of manure and draught

power for crop production was reflected in the value of the produced crop (ILCA, 1990).

Page 86: BEEF CATTLE SYSTEMS IN THE CONTEXT OF SUSTAINABLE ...bictel-fusagx.ulg.ac.be/ETD-db/collection/... · (2011). Beef cattle systems in the context of sustainable agriculture in Bac

68 Research methodology

3.4.4 Selection of indicators in the influence assessment of cattle feeding system

The purpose of this section is to select a set of representative indicators to assess the potential

influence of cattle production on agricultural sustainability at the household scale. For Dantsis

et al. (2010) agricultural sustainability is regarded as a key prerequisite for the long-term

profitability of farming and rural areas, which will be analysed through the potential

influences on environment, society, and economics through indicators. According to Garcia

(1996), determining proposed sustainable indicators should look at environmental, resource,

economic, and social aspects of sustainability in an integrated dimension. Indicators were

selected according to their relevant ability to describe the pressures as well as the contribution

of cattle production on sustainability of agriculture. According to Dantsis et al. (2010),

selected indicators should be significant in terms of sustainability, assessing relevant to the

agricultural activity description, measurable, based on easily obtainable information,

reproducible and comprehensible. Although it was challenging for every indicator to meet all

these requirements, it was important that this be adhered to as much as possible.

Garcia (1996) indicates that “indicators for sustainable development should be relevant,

reflecting key forces and properties of the exploited ecosystem as well as sufficiently accurate

and precise in order to be acceptable and effective”. In addition, he also mentions that

“selected indicators should be accompanied with detailed information concerning type of

indicator, purpose of the indicator, relevance to policy, relevance to sustainable development,

linkages with other indicators, targets, data requirements, and appropriate methodologies”.

These criteria are also applied in the study.

According to Garcia (1996), each indicator may integrate more than one variable, so it would

be needed to track: (i) the resource endowment, including its abundance, diversity, and

resilience; (ii) the environment, for example by reference to its pristine condition; (iii) the

technology in terms of capacity as well as environment-friendliness; (iv) the institutions, e.g.

fishing rights, enforcement system; (v) the human benefits, e.g. food, employment, income;

(vi) the economics of exploitation, e.g. costs, revenues, prices; and (vii) the social context,

e.g. social cohesion, participation, compliance.

Thus, there is indeed a need for a simple representation of sustainability by selected indicators

in an integrated manner, although there remain the complexity of the sustainability issue, the

number of parameters, and the range of potentially useful indicators (Garcia, 1996). He also

indicates that the development of sustainability indicators requires: (i) reference to agreed sets

of principles, rules and concepts; and (ii) standard protocols for their calculation, based on

accepted, peer-reviewed scientific methodologies and “the best scientific information

available”. According to his point of view, selected indicators should be accompanied by

detailed information such as (i) purpose; (ii) relevance to policy; (iii) relevance to sustainable

development; (vi) linkages with other indicators; (v) targets; (vi) relations with international

conventions and agreements; (vii) data requirements; and (viii) appropriate (recommended)

methodology. The determination of indicators of social, environmental, and economic

pathways was indicated in order to assess the level of sustainability of the three selected beef

cattle feeding systems. Correspondingly, the selection of indicators in the different elements

of beef cattle production in the context of sustainable agriculture is presented in the following

sections with a detailed explanation and evidence from other studies.

3.4.4.1 Economic viability and efficiency

According to Sen (2005), economic indicators which could be used to evaluate the

sustainability of an agricultural system include livestock productivity, farm productivity, and

Page 87: BEEF CATTLE SYSTEMS IN THE CONTEXT OF SUSTAINABLE ...bictel-fusagx.ulg.ac.be/ETD-db/collection/... · (2011). Beef cattle systems in the context of sustainable agriculture in Bac

Research methodology 69

production efficiency. Additionally, in smallholders, productivity is a necessary condition to

achieve family sustainability (McConnell and Dillon, 1997). Productivity in unit or financial

terms in relevant time should be used to measure sustainable systems. It is primarily a

measure of the relative suitability of a system or activity in a particular agro-ecological

environment. It is also an indicator of relative efficiency of resource use and management

performance in commercial farms, whereas on non-commercial farms productivity is a

necessary condition for achieving family sustainability, but only to certain limits (McConnel

and Dillon, 1997). According to Becker (1997), there are several economic indicators, which

are often used for assessing economic efficiency of a production system. The Total Factor

Productivity (TFP) might be a favourable indicator, and is calculated by the ratio of the total

value of all outputs to the total value of all inputs for a production system in one cycle period

(Becker, 1997). According to Lynam and Herdt (1989), TFP is the appropriate measurement

of the output. Thus, during a given period, a production system is seen as sustainable when it

shows a trend equal to or greater than the total productivity. However, its simple measurement

is challenged due to the lack of considering external costs such as environmental effects. In

order to overcome this deficiency, the Total Social Factor Productivity (TSFP) was developed

to calculate the production costs of the environment. Both assessing of TFP or TSFP could

help to measure the sustainability of a system. Nevertheless, appropriate assessment of

environmental costs and the boundary of internalization are hard questions for researchers

(Becker, 1997). The system is sustainable if it can maintain its output at a level higher or

equal to its historical average, and the slope of the trend line is upward (Lynam and Herdt,

1989). TFP measures how efficiently a farm is combining all inputs to produce a unit of

outputs (Sen, 2005). Thus, in the context of this study, the first indicator—TFP is selected.

TFP is calculated by the ratio of total output to total input, i.e. the total gross returns divided

by the total costs. The total farm (cattle) returns will be calculated by the total output of farm

(cattle) over 1 year (yield multiplied by the net market price); and the total costs = variable

costs + fixed costs.

TFP beef cattle = tscattlebeefTotal

returnscattlebeefTotal

cos

Besides, FAO (1999) also considers that profitability is an economic criterion. Profitability is

one of the main indicators that ensure agriculture production is profitable or not, but not at the

expense of the environment. Low or negative profitability usually indicates that production is

exploited in an economically wasteful manner and production capacity and effort are

excessive on both economic and biological grounds (FAO, 1999). Profitability is computed by

the ratio of total value of outputs minus total value of inputs divided by total value of inputs

(Tisdell, 1996). However, the profitability of the farm investment in the study is measured by

the gross margin, expressed by the total farm income less the total farm variable costs—the

second indicator. This indicator is used as an economic indicator in assessing economic

stability in Sen (2005), Rasul and Thapa, (2004), Dantsis et al. (2010). Furthermore, gross

cattle margin per TLU is also calculated to evaluate cattle farm profitability per unit of kept

cattle.

Gross cattle margin = Gross cattle outputs – Total variable cattle expenses

Among indicators used to assess economic efficiency, a very low level of household net cash

income can be seen as an indicator measuring poverty. In addition, family earnings, which

measure the total income available to the farm family for all purposes, are also needed to

Page 88: BEEF CATTLE SYSTEMS IN THE CONTEXT OF SUSTAINABLE ...bictel-fusagx.ulg.ac.be/ETD-db/collection/... · (2011). Beef cattle systems in the context of sustainable agriculture in Bac

70 Research methodology

assess poverty (Dillon and Hardaker, 1993). Thus, in the study, the last indicator—household

net cash income was employed, which is defined by total farm receipts plus farm cash and/or

loans received and other household receipts, minus farm payments, interest and principal

payments. A summary of selected indicators of the economic dimension is presented in

Table 9.

3.4.4.2 Social solidarity

From the concept of sustainable development, sustainability does not mean only economic

efficiency of production but it also means the long-term remaining and development of social

aspects (Sen, 2005). Sen (2005) finds that social sustainability could be analysed through

indicators such as the living standard (including income, income distribution, food security,

consumption and education, gender equality, management skill, liquidity, and local culture

and event). In the study conducted by Zeller et al. (2000), poverty alleviation and employment

opportunities were used as core indicators to assess the social solidarity. Sydorovych and

Wossink (2008) state that sustainable agriculture should provide sufficient employment

opportunities in local communities. In addition, Rasul and Thapa (2004) say that the ability to

generate employment within the system was considered as an indicator of equity. FAO (1999)

also considers employment to be a social criterion. Employment opportunity is the capacity of

the cattle feeding system to exploit its labour requirement from the household. Farmers in

mountainous regions have limited resources and strongly depend on agricultural and forestry

activities (Minot et al., 2003). Thus, farmers in this region will have increased basic human

needs as well as the requirement to look for new and/or alternative farm and off-farm

activities if their labour is available (Huyen, 2004), because population growth in these areas

is high. The more labour is employed in agricultural activities; the lower will be the migration

of local people looking for work.

Employment opportunity is identified by the number of persons working on the cattle

production, the number of days people work in the sub-sector, the number of days required

per unit of land use for cattle as well as for a Tropical Livestock Unit (TLU). Furthermore, the

proportion of time used in cattle production in comparison to all livestock production is also

indicated in this study.

The basic concept of Employment-Based Analysis (EBA) is to count the number of jobs that

an economic activity provides, or how many people in the family it supports over a given

period of time and over a given resource (Taylor, 2001). EBA provides quantitative measures

of sustainable employment. On the other hand, employment opportunities generated from beef

cattle production were calculated to measure the capability of household labour engaged in

this sub-sector. Employment opportunities were calculated by employment of full-time job,

defined by 8 working hours per day. Annual employment provided by beef cattle will be

measured over a number of TLU of cattle kept by households over the land area used for beef

cattle production. The employment opportunities are defined by:

- The EBA (people-year for 1 hectare) = AxTL

N

*

Where, N is the number of days of family labour employed in beef cattle production; L

denotes the land area (in hectares) required for beef cattle production; T denotes time period

calculated by the number of years in this study (here it is one year); A is used as a land base

(here it is a hectare).

Page 89: BEEF CATTLE SYSTEMS IN THE CONTEXT OF SUSTAINABLE ...bictel-fusagx.ulg.ac.be/ETD-db/collection/... · (2011). Beef cattle systems in the context of sustainable agriculture in Bac

Research methodology 71

- The EBA (people-year for 1 TLU) = AxTL

N

*

Where, N is the amount of time (days) family labour is employed in beef cattle production; L

denotes TLU kept by the family; T denotes time periods calculated over a period of 1 year in

this study; A means a TLU, as TLU base.

Measuring poverty alleviation over time to assess social solidarity in its dimensions such as

food insecurity, malnutrition, or illiteracy is suitable, but it is a difficult task (Zeller et al.,

2000). Therefore, those indicators were not considered in the study. Specifically, a study on

poverty must also include gender analysis to determine how best to improve conditions for

rural women (Ashby, 1999). Therefore, the present study emphasizes women’s specific roles

in this sub-sector. The role of women was also assessed by the percentage of female labourers

in the total time employed for cattle production. In addition, their role in decision-making in

activities related to cattle production was also indicated in this study. In addition, return per

labour day is also used as an indicator in social aspect to assess the efficiency of labour

working in this sector. Selected indicators of the social pathway are summarised in Table 9.

3.4.4.3 Environmental stability

Environment is a vital condition for human beings, especially in the context of climate change

issues in the whole world. Vietnam is ranked as one of the most at-risk countries. Actually,

climate change poses risks to lives and livelihoods throughout the world, but is exacerbated in

some places by conditions of socio-economic vulnerability and by physical risk factors which

contribute to the frequency and severity of natural events. Climate change is an increasingly

critical and complex issue in Vietnam, especially in the age of economic development and

globalization. In fact, cattle production is highlighted by its risk to the environment due to

releasing methane and other factors. Negative effects from cattle production in particular and

other agricultural activities in general will affect the availability of resources over time.

Grazing animals are often associated with environmental risk due to overgrazing and loss of

biodiversity (Schillhorn van Veen, 1999). Prolonged heavy grazing undoubtedly contributes

to the disappearance of palatable plant species and the subsequent dominance by other, less

palatable, herbaceous plants or bushes. Excessive livestock grazing also causes deforestation,

soil compaction and erosion, decreased soil fertility and water infiltration, and a loss in

organic matter content and hence water storage capacity (De Haan et al., 1996).

Resilience—the ability of an ecosystem to recover from a given stress—is known to be the

first step in assessing environmental sustainability (Becker, 1997; Barbier et al., 1990 cited in

Rodrigues et al., 2003). Normally, land degradation, soil erosion, emission of greenhouse

gases, water pollution, air pollution, biodiversity, species richness, etc. might be used in

measuring environmental sustainability (Sen, 2005). Nevertheless, in this study context,

different indicators were identified including manure utility, and manure leaching out to the

surrounding environment. Manure storage and uses as well as farmer awareness of

environmental protection are also described (Table 9). In addition, the household stocking rate

(or grazing pressure) is the number of cattle calculated in Tropical Livestock Units (TLU) per

hectare of grassland in household (TLU is used to standardize the number of cattle on the

farm: one mature bull is equivalent to 1 TLU; 1 cow is equivalent to 0.7 TLU; 1 heifer or

steer is equivalent to 0.5 TLU and 1 male/female calf is equivalent to 0.2 TLU).

Page 90: BEEF CATTLE SYSTEMS IN THE CONTEXT OF SUSTAINABLE ...bictel-fusagx.ulg.ac.be/ETD-db/collection/... · (2011). Beef cattle systems in the context of sustainable agriculture in Bac

72 Research methodology

Table 9: Selected indicators and their description

Sustainable dimensions Indicators Description of indicators

Economics

Gross cattle margin Gross returns from cattle production minus from total

variable costs.

Total factor productivity Total cattle gross returns divided by the total cattle costs

Household net income Gross return from farm and off-farm activities minus from

total expenses.

Society

Employment

opportunity

Annual employment provided by beef cattle production as

family labour used (days) measured over the number of

TLU of cattle kept by households.

Women’s role Role of women in cattle production indicated by the

percentage of time they spend working on activities.

Return on labour per

day

Cattle net income divided by total labour days invested in

cattle production.

Environment

Stocking rate Number of cattle calculated in Tropical Livestock Units

(TLU) per hectare of grassland cultivated by households.

Manure use and storage Percentage of cattle manure not used but leaching out to

the surrounding environment.

Farmer awareness

Awareness of farmers on the use and storage of cattle

manure as well as its management in households and by

the community.

3.4.5 A sustainable reference system

Garcia (1996) indicates that sustainability could be defined as weak and strong sustainability.

He explains that weak sustainability allows full substitution among all forms of capital

(natural, economic, and social) and would allow depletion of the natural capital provided the

sum of all three forms is kept constant for future generations or increases over time.

Contrarily, strong sustainability assumes when the forms of capital are not interchangeable

and should be conserved separately. Thus, selected indicators should reflect and aim at a form

of strong sustainability (Garcia, 1996). Actually, it would be useful and necessary to identify

partially integrated indicators, reflecting overlapping components of sustainability. Therefore,

it would also be useful to build a framework combining the full range of social,

environmental, and economic dimensions of the sustainability relationship (Garcia, 1996).

In order to convert selected measuring indicators for sustainable aspects with different

calculation units into the same unit by nominalising, formulas are created, with 0≤ X =

minmax

min

XX

XXi

≤1, which means a higher X indicates a better performance of the study

object or 0≤X = minmax

max

XX

XiX

≤1 means a higher X indicates a higher threat of the study

object.

Page 91: BEEF CATTLE SYSTEMS IN THE CONTEXT OF SUSTAINABLE ...bictel-fusagx.ulg.ac.be/ETD-db/collection/... · (2011). Beef cattle systems in the context of sustainable agriculture in Bac

Research methodology 73

Bad Poor Medium Ok Good

0.0-0.19 0.2-0.39 0.4-0.59 0.6-0.79 0.8-1.00

E

CO

SY

ST

EM

CO

ND

IT

ON

S

Go

od

OK

Med

ium

Po

or

Ba

d

Bad Poor Medium OK Good

HUMAN SYSTEM CONDITIONS

Figure 30: Barometer of sustainability - a static representation of the reference system Source: Modified from Guijt et al. (2001).

Thus, a “sustainability barometer” is built based on a graphical representation of the location

of an exploited ecosystem on an orthogonal system representing both indexes of human and

ecosystem well-being, considered as the two fundamental dimensions of sustainability (Guijt

et al., 2001; Gacia, 1996) (Figure 30). According to Guijt et al. (2001), development is

sustainable when both human well-being and ecosystem well-being are good. The “Barometer

of Sustainability” is considered as a tool for combining indicators and displaying the results.

It is designed to measure human and ecosystem well-being together without submerging one

in the other (Guijt et al., 2001). Specifically, to identify in which level the indicator is

sustainable or not appears to be challenging, therefore, the various axes of the radar diagram

are divided into equal sections representing impacts level by Garcia (1996). The scales

include assessment values that correspond to the various intervals on each axis, e.g. the 0.0-

0.2 interval is considered “Bad” while the 0.8-1.0 interval is considered “Good” (Guijt et al.,

2001; Garcia, 1996).

3.4.6 Proposed data analyses

The SPSS (Statistical Package for the Social Sciences) software version 16 is used to analyse

the data. Data analysis in the study is based on guides from two books including “SPSS

Almost

unsustainable

Non sustainable

Ecologically

unsustainable

Intermediate

Almost

sustainable

Sustain-

able

Socially

unsustainable

Page 92: BEEF CATTLE SYSTEMS IN THE CONTEXT OF SUSTAINABLE ...bictel-fusagx.ulg.ac.be/ETD-db/collection/... · (2011). Beef cattle systems in the context of sustainable agriculture in Bac

74 Research methodology

Introductory Statistics” written by Morgan et al. (2004) and “SPSS Intermediate Statistics”

written by Leech et al. (2005).

3.4.6.1 Descriptive statistics and frequency analysis

Quantity and quality data will be analysed by descriptive analysis. Quantitative data are

means, percentages, frequencies, and ranges. Qualitative data will be recorded during the data

collection phase and will be useful for the discussion and explanation of the data collected.

Text and discourse analyses are used to interpret qualitative data.

3.4.6.2 Comparison among systems

If all samples are normally distributed with equal variances divided the sample into three

groups/levels, ANOVA is used to compare differences among them. Otherwise, the Kruskal

Wallis and Mann-Whitney Tests are used to compare among the systems if both conditions

are not met. Criteria include the farm resources (capital, labour, and land), feeding practised,

crop production, livestock husbandry, household productivity, farm efficiency, cattle keeping

efficiency of different cattle feeding systems, and cattle breeds with their reproductive

performance on calving interval, age at first calving, and reproductive life, etc.. The effects

and influences of cattle production on sustainable aspects are also compared among the

systems to get an understanding of the most promising system among selected ones. Besides,

an Independent Sample Test is used to compare between two groups such as with and without

grass production, reproductive performance between cattle and buffalo.

3.4.6.3 Correlation analysis

Correlation analysis is used to explore the relations among indicators and indicate the main

determinants of cattle production (including inputs and outputs), e.g. between net cattle

income and other normal/scale variables (cattle herd size, economic value of cattle losses,

cow numbers, etc.). In addition, relations between total gross cattle costs and other variables

such as gross crop return, grass land areas, agricultural land, swine numbers, cattle feed costs,

etc. were also analysed using correlation analysis.

3.4.6.4 Farm size and herd size classification

A simple classification of farm and herd were created relying on collected data as well as the

classification methods used by other authors in other studies. Farm size was ranked into three

levels consisting of small, medium and large to understand the impacts of production size on

the economic efficiency of selected households in selected farming systems. According to Ha

and Shively (2004), farms below 1.5 hectares in size are recorded as small farms and those

above 1.5 hectares in size are indicated as large farms. Note that they consider 1.5 hectares as

corresponding to the average farm size in their study sample. Correspondingly, depending on

the distribution of farm sizes in all selected households and categories from references, farm

size in selected households was categorized into three types including small size (<1.5 ha),

medium size (between 1.5 and 2.5 ha), and large size (>2.5 ha).

Similarly, cattle herd size was also classified as small, medium or large. These classifications

are made to understand the production scale of the selected households on the study site and

their future development trend. In fact, there is no formal classification of herd size in

Vietnam. According to Tung et al. (2009), small, medium, and large herd sizes in cattle

production in Vietnam are from 1 to 3 head, 4 to 10 head and over 10 head, respectively.

Meanwhile, Hung and Binh (2004) indicate that in Dak Lak province, where cattle production

is growing dramatically on large and diversified natural pastureland, around 33% of

Page 93: BEEF CATTLE SYSTEMS IN THE CONTEXT OF SUSTAINABLE ...bictel-fusagx.ulg.ac.be/ETD-db/collection/... · (2011). Beef cattle systems in the context of sustainable agriculture in Bac

Research methodology 75

households keep under 5 head, and another 27% of households raise from 5 to 10 head. On

the other hand, Huy (2008) records that the most popular cattle herd size in households in

upper Ha Giang province (part of the NMR) is between 1 and 3 head, while a few households

keep 4 or 5 head. Likewise, Nho et al. (2003) identify cattle herd size ranked as 1 head, 2

head, 3–5 head, 6–10 head and over 10 head. In a study conducted by Quan (2002), cattle

herd size is ranked by 1–2 head, 3–4 head, 5–6 head, 7–8 head, and over 8 head. Thus, in this

study, based on the current situation of cattle production scale and perception from selected

households, cattle herd size is categorized by three different sizes: small herd size (1–3 head),

medium herd size (4–6 head) and large herd size (over 7 head).

3.4.6.5 Influence assessment approach of sustainable agriculture

According to Sen (2005), there are several methodological approaches to characterise

sustainability in agriculture including adherence to prescribed approaches, multiple qualitative

and quantitative indicators, time trends, resilience and sensitivity, system simulation, and

indicators of sustainability. The latter is the most widely used method of sustainability

evaluation, indicated in many studies such as Becker (1997), Bossel (1999), Zeller et al.

(2000) and Sen (2005). Among those studies, Becker (1997) and Bossel (1999) assess

sustainable development through indicators in three pillars: social, economic, and

environmental ones. Zeller et al. (2000) employs the approach of rural development in

Madagascar through assessing three dimensions of sustainable development: poverty

alleviation, economic growth, and environmental stability. Sen (2005) determines the impact

of soil conservation measures on the sustainable development of agricultural systems through

an impact assessment of environmental, social, and economic dimensions.

There are several methods used to assess the impact of sustainability in agriculture including

the systematic comparison, the econometric regression and a more complex system of

modelling (Sen, 2005). However, in the context of this study, systematic comparison and a

multi-criteria approach were employed. The multi-criteria approach is applied by many

studies including Giampietro et al. (2001), Gomiero and Giampietro (2001), Gomiero (2004),

and Giampietro et al. (2006). The multi-criteria analysis approach focuses on different

dimensions (social, economic, and ecological). Giampietro (2001) finds that the integrated

assessment in the combination (integration) of various descriptive tools into one coherent

analytic process is essential. Siegmund-Schultze et al. (2010) indicate that “the spider’s web

diagram allows comparing the performance of different systems or activities in the same

diagram or to allow parallel visualisation of different indicators”. Garcia (1996) points out

that it is necessary to discuss the linkages among indicators. A set of numerical indicators was

selected, which covers all the relevant information and is representative of the cattle sub-

sector. This approach considers possible effects in relation to different dimensions of

development and is combined in “radar diagrams”—typical of multi-criteria analysis.

3.4.6.6 Assessment of the cattle trading and marketing chain

Due to complex issues involving the cattle marketing chain and the study limitations (time,

funding, and other challenges), a preliminary study of the cattle trading and marketing chain

in smallholder farms was conducted. Therefore, the role and position of stakeholders in cattle

markets and marketing chains were mainly analysed by a qualitative approach. Selected

households and key persons were interviewed directly by semi-structured lists of questions.

The purpose of the study was to collect main data on channels, opportunities and challenges

as well as to determine role and position of farmers positioned in marketing chains.

Page 94: BEEF CATTLE SYSTEMS IN THE CONTEXT OF SUSTAINABLE ...bictel-fusagx.ulg.ac.be/ETD-db/collection/... · (2011). Beef cattle systems in the context of sustainable agriculture in Bac
Page 95: BEEF CATTLE SYSTEMS IN THE CONTEXT OF SUSTAINABLE ...bictel-fusagx.ulg.ac.be/ETD-db/collection/... · (2011). Beef cattle systems in the context of sustainable agriculture in Bac

4 RESULTS AND DISCUSSIONS

This chapter is divided into three sections. Section 1 aims to give an overview of the target

households using three beef cattle feeding systems in Bac Kan province, in Vietnam’s

Northern Mountainous Region. It is an integral part of the study as no result of the beef cattle

production can be fully understood without information on the systems in which they occur.

This is especially relevant in the case of beef cattle farming systems in the NMR that has

numerous characteristics distinguishing it from other regions. Therefore, the main

characterisation of selected households and their production systems was carried out giving

the rationale for the selection of feeding systems, selection of households, and providing the

basis for empirical investigation on current beef cattle feeding systems, including free-range,

part-time grazing, and cut and carry. Section 2 attempts first description the characteristics of

cattle production in the selected feeding systems, including reasons for keeping cattle,

common breeds, and cattle herd size. Then, it moves to analyse cattle management (feed

resources, breeding, and the like). An analysis of other issues involved in cattle feeding

systems is made to highlight factors conducive to the development of the sub-sector in the

study sites both now and in the future. Section 3 intends evaluating the influences of beef

cattle feeding systems on different dimensions of sustainable agriculture—economics, society,

and environment—using different indicators selected due to their high suitability to the

context of cattle production in the NMR. Besides, an analysis of costs of and returns from

cattle production is also presented to provide insight on the economic efficiency of the cattle

feeding systems. A multi-criteria approach is used to measure their sustainability.

4.1 CHARACTERISATION OF SELECTED HOUSEHOLDS IN DIFFERENT BEEF CATTLE FEEDING SYSTEMS

4.1.1 An introduction to the cattle feeding systems in the study area

Table 10: General characteristics of beef cattle feeding systems

Item Free-range Part-time grazing Cut and carry

Minorities Tay, Nung Tay, Nung H’ Mong, Dao

Geography Lowlands Lowlands Uplands

Breed of cattle Local Yellow cattle Local Yellow cattle Local Yellow cattle

Types of husbandry

Grazing without being

tended, no or little feed

supplement

Grazing half day with

tending, more feed

supplement

Cutting feed for bull,

grazing all day for other

animals

Breeding Non-controlled or

inbreeding

Non-controlled or

inbreeding

Controlled and selected

bulls used

Pastureland resource Large and better

accessibility

Limited and poor

accessibility

Large and better

accessibility

Source: Households interview, 2008; Groups discussion; Key person interview; Secondary data

Table 10 gives a brief introduction to the beef cattle feeding systems in the selected study

sites. Detailed information is presented in the following parts, as illustrated in Figure 31.

Page 96: BEEF CATTLE SYSTEMS IN THE CONTEXT OF SUSTAINABLE ...bictel-fusagx.ulg.ac.be/ETD-db/collection/... · (2011). Beef cattle systems in the context of sustainable agriculture in Bac

78 Results and discussions

4.1.1.1 Cut-and-carry system

The cut-and-carry cattle feeding system as defined in Section 2.1.5 is not only practised by the

H’Mong people but also by some Dao households living in middle areas, that have started

learning how to fatten cattle using this approach from H’Mong persons. Other Dao people

practise free-range or part-time grazing methods depending on their location, resources, and

strategies. Thus, cattle production in Dao minority settlements is not as representative as that

of the H’Mong or Tay. Besides, Dao people live scattered in many villages, which made it

difficult to select a large enough sample size. Therefore, in the context of this study, the cut-

and-carry cattle feeding system in H’Mong households was investigated, but not for the Dao

minority.

It was difficult to access to selected H’Mong settlements located far from commune centres

within a radius of 6 to 12 km (from one to four hours walking) on trails through rocky

mountains. They often build their houses on the highest mountainsides (Figure 31 and Annex

11). This characteristic is also described by Huyen, 2004; Lan, 2005; Nho et al., 2003; Niem

et al., 2001 who say that the “H’Mong people often live in the highest mountain zones, over

800 m above sea level”. Moreover, in this area, it is very cold and dry in winter and quite cool

in summer. Nho et al. (2003) also record that the H’Mong people prefer to locate in zones of

low to moderate temperature (18-20oC) and humidity (85-86%). Another feature is that this

system was practised in areas with less market access but low land use pressure. No

transportation mean is used in these areas, except for horses. Therefore, none of the selected

H’Mong households had motorbikes. A few households with a better standard of living and in

accessibility to better way had bicycles. They transported all things by hand and on foot. No

electricity line served their villages due to their complex and specific location. H’Mong

people took advantage of streams to generate electricity but with a very low capacity, which

might be used for several small lights and a radio (see Annex 11). Radios and television sets

were seldom seen in the selected H’Mong households. Previously, there were often severe

water shortages during the dry season. However, with support from the government in such

the 1348 or 135

9 programmes, plastic water lines and cement water tanks were built in many

villages including H’Mong villages that provided enough water for families throughout the

year, especially during the dry season. Most households in the H’Mong villages lived in poor

hygiene conditions, with no toilet or bathroom. In addition, almost the totality of animal

manure and waste were washed by rain or floods into streams. Thus, pollution might affect

people living in lower areas such as the Tay and Nung minority groups.

Nevertheless, the H’Mong people have strong communal characteristics and interdependence

on each other. Tai (2005) indicates that the H’mong people have much local knowledge of

and experience in managing and using natural resources. Market day in the commune is

considered as a small and regular festival by the H’Mong people, where they meet and

communicate with others, people coming from different surrounding communes. The

purchasing purpose is of minor of importance, while the community spirit is highly prised in

their culture. H’Mong men commonly speak fluently H’Mong (their own language), Tay and

Vietnamese, while most women only speak H’Mong.

8 134 Programme was implemented under Decision No. 134/2004/QD–TT with the purpose of promoting

productive land, providing buildings and running water for impoverished ethnic minority households. 9 135 Programme was established pursuant to Decision No. 135/1998/QD-TT dated July 31, 1998 on the

policies and objectives for the socio-economic development of poor communes in mountainous and remote

areas.

Page 97: BEEF CATTLE SYSTEMS IN THE CONTEXT OF SUSTAINABLE ...bictel-fusagx.ulg.ac.be/ETD-db/collection/... · (2011). Beef cattle systems in the context of sustainable agriculture in Bac

Results and discussions 79

4.1.1.2 Free-range system

The free-range system is also described in Section 2.1.5. Traditionally, most of ethnic

minority groups in the NMR have ever used the free-grazing method. However, this has

gradually changed. The change can be explained by such reasons as dense population

reducing accessibility to land resources, expansion of cropping activities, and farmer

awareness. However, in this area, the free-range system was still practised, in which cattle

graze freely on fallow land, communal pastures, and in forested areas without being tended by

their owners, especially from about November to February, after the last cropping season, due

to the availability of unused and forest land areas and low population density. This description

of the free-range system is also indicated in Tra (2007) and Nho (2003). Besides, cattle were

often checked regularly during cropping season by some families, while in others cattle were

taken to pasture in the morning and brought back in the afternoon, and during the day, no

control from the owners was seen.

It was easy to access Tay people using the free-range system, as they live within a radius of a

kilometre or so from the Cong Bang commune centre. The commune is positioned around 12

km from the Pac Nam district town. All of the people have access not only to the market but

also to the school, the medical station and other services. They often build their houses in the

lowland, where water resources and very fertile fields are available (Figure 31). People living

in this area have access to transportation and communication. All of the selected households

had electricity. Most of them had television and motorbikes. Market day takes place regularly

every 5 days in the centre of the commune, where Tay people come to exchange their

products or purchase what they need for their family. Despite such characteristics, all of the

Tay villages have very poor hygiene and poorly manage livestock manure. Storage of manure

was virtually non-existent (Annex 13). Livestock manure was commonly encountered

throughout the commune, often left even on the main roads, where it could be washed into

rivers and streams. The headwaters of such streams are in mountains populated by H’Mong

villages. However, a high proportion of households still used the water resource in rivers and

streams for clothes washing, vegetable cleaning, and other activities.

4.1.1.3 Part-time grazing system

This system is also defined in Section 2.1.5. Cattle are allowed out to graze in the day time

and are kept in a stable at night. Allowing cattle to graze part time is the predominant method

of cattle husbandry throughout the country currently. However, in mountainous areas, cattle

pasture areas have not yet been characterised. In the study area, during the cropping season,

cattle are allowed to graze on in fallow land, communal pastures, and in forested areas, and

are tended by their owners in the afternoon. After the cropping season, cattle are often left

graze all day with tending from their owners. These characteristics are also described in Nho

(2003) and Tra (2007).

It is also easy to access Tay households using the part-time grazing system in the Nghien

Loan commune. All of them are located within a radius of 6 km from the commune centre,

and around 20 km from Pac Nam district town and 10 km from Ba Be district town (Ba Be

town is the former district centre). Therefore, transportation and communication are

accessible, with relatively good infrastructures. Their houses and main crop fields are mainly

in lowlands (Figure 31). Their houses are often built on stilts. However, timber scarcity due to

forest clearing and inappropriate forest exploitation is gradually changing their traditional

house style to the more common house. Although not all households are connected to the

electricity grid in Nghien Loan commune, all of the selected households are connected. There

is still a little dry season water deficit. All of the households live in rather good hygienic

Page 98: BEEF CATTLE SYSTEMS IN THE CONTEXT OF SUSTAINABLE ...bictel-fusagx.ulg.ac.be/ETD-db/collection/... · (2011). Beef cattle systems in the context of sustainable agriculture in Bac

80 Results and discussions

conditions with toilets and bathrooms. However, a high percentage of households still raise

animals near their houses (Annex 12).

Figure 31: Transect description of selected systems and their cropping calendar Source: Households interviews, 2008; Groups discussion; Key person interview; Calendar; Secondary data

4.1.1.4 Historical development of the selected beef cattle systems

A draft historical development of cattle feeding systems in the study sites is presented in

Figure 32. In this section, it is important to remember the characteristics of the free-range

Page 99: BEEF CATTLE SYSTEMS IN THE CONTEXT OF SUSTAINABLE ...bictel-fusagx.ulg.ac.be/ETD-db/collection/... · (2011). Beef cattle systems in the context of sustainable agriculture in Bac

Results and discussions 81

cattle system, which is the traditional system of most of ethnic minority groups in the

Northern Mountains. Cattle are allowed to graze freely for long periods on fallow land,

forested areas, and communal pastures with no tending by the owners. The cattle herd was

rarely checked. Due to free ranging, there is no labour requirement; the cattle herd often

grows to a large number. Many farmers did not know exactly how many cattle they owned

due to no regular control of the cattle herd and its movement. They knew nothing about the

growth and reproductive performance of cattle, such as which cows were gravid, how many

calves each cow had, how long the calving interval was, etc. Thus, a high number of cattle

were lost due to disease, accidents, carnivorous animals, and thieves. However, this

husbandry method has gradually changed to part-time free-grazing in both Nghien Loan and

Cong Bang communes or to part-time grazing in Nghien Loan since 2000–2003 due to the

allocation of arable land areas to households including forest land, limited pastureland

allowance, and explosion of the local population. In addition, the expanding forestry

programme has been implemented in the study site (it will be further discussed in Section 2 of

this chapter), which is also limiting land for natural pastures. Hence, many households in the

study site have changed from free grazing (with its long periods without tending their animals

and rarely checking on them during the non-cropping season) to short-term free grazing (often

checking on the herd) in the crop season in order to avoid crop destruction and subsequent

conflicts among the villagers. Several households have gradually developed the habit of

bringing their cattle back home after short grazing outings. They train their cattle to know the

way home by using salt.

Today, many households in Cong Bang commune still allow their cattle out freely during the

day and bring them home in the evening during the crop season to prevent the animals from

damaging crops. Nevertheless, in the non-cropping season, letting the animals out for long

periods of free ranging was done to save labour resource. Farmers in the commune were able

to practice this husbandry style due to the large areas of forestry and unused land available.

Thus, the more labour is required and the more cattle herds size have been reduced compared

to the formal free ranging cattle.

Box 1: Mr. Hoang Van Vuong, a Tay person living in Cong Bang commune

Mr. Vuong said that his family used to keep over 40 cattle in the past. His family did not keep abreast of

changes in the herd over time, when an animal died or strayed or when a calf was born. Vaccinating and

treating for disease were unknown. No information on reproductive capacity was recorded. In some

cases, inbreeding was shown in cows and their offspring. Family members would go out to check and

see where their cattle were grazing as well as to mark new born calves. Cattles herds belonging to

different families commonly mixed. However, the cattle herd was gradually reduced because limitation

of pasture land, reforestation, and high losses. Currently, his family kept only 5 head of cattle. They

might stop raising cattle due to short of labour resource for tending, shortage of feed resource for cattle

also.

During the same period (2000–2003), many other families in Nghien Loan commune

gradually switched to part-time grazing during the crop season and tend their animals more

closely during the non-cropping season to reduce risks to the minimum. A complete transfer

to part-time grazing only took place from 2003 to 2005 in Nghien Loan due to a great limiting

of natural pastureland and grazing areas and strong reforestation activities. Part-time grazing

is the predominant method of cattle husbandry in the NMR. During the cropping season,

Page 100: BEEF CATTLE SYSTEMS IN THE CONTEXT OF SUSTAINABLE ...bictel-fusagx.ulg.ac.be/ETD-db/collection/... · (2011). Beef cattle systems in the context of sustainable agriculture in Bac

82 Results and discussions

farmers often keep their stock in natural pastures for a half day. Sometimes, cut-and-carry for

whole cattle herd is used during crop sowing and early growing in order to avoid damage to

crops. After harvesting, cattle are allowed to graze in the fields during the whole day until the

next crop and are housed at night. Grazing is only allowed on unplanted land, common land,

and fallow land. Occasionally, cattle are penned and forage is brought to them. Thus, care

from owners is often required during grazing time. More feed resources are required to

supplement cattle feeding when penned during the cropping season. Generally, the cattle herd

size is small because of limited pastureland and difficulties to tend the animals when taken out

for grazing. The grass production was introduced during 2006-2007 to provide a replacement

feed resource for cattle, especially in the context of decreasing pastureland for grazing and the

development programme of cattle production from the government. Cattle were taken out to

graze quite a distance from the family houses. Although fattening cattle in H’Mong

households was well-known in the study sites, very few families in Nghien Loan commune or

Cong Bang commune had experimented with this before selling their animals, possibly

because of the difficulty in collecting feed resources, the shortage of feed resources in winter,

and simply it was something they were not familiar with.

Box 2: Mr. Le Van Som, a Tay person living in Nghien Loan commune

Mr. Som said that his family adopted the part-time grazing system very early, during 2000 after facing

with limitation of pastureland, partially due to reforestation and allocation of land resources to

households, and conflicts among farmers because of damaged crops. His family spends a lot of time

tending the cattle. Many people in the family had participated in this job. His family is not only

confronted with labour issues but also with a gradual limitation of grazing areas.

Cut-and-carry or stable feeding has been popular among the H’Mong minority since 2003-

2005. Bulls were confined and fed by feed resources collected from the crop fields and/or

from fodder shrubs and trees in the forest during the feed shortage season. In addition,

fattening cattle were often given a supplement of maize mash or pig cooked feed to increase

their market value. The cut-and-carry system is undoubtedly less compatible with forest

planting on pasture areas in comparison with other systems. Recently, grass cultivation by

households has alleviated some of the hard work to collect natural feed resources.

Nonetheless, development of grass production is still confronted with the limited land

resource as the priority is given to other crops. Fattening cattle provides better economic

efficiency due to breeding uniform animals of good appearance that yield good tasting beef.

Products from properly fattened cattle could be high-class commodities in the markets to

consumers that might meet the high demand of consumers in big cities and could fully join

the modern retail chains (detail information is given in Sections 2 and 3 of this chapter).

Overall, it derives a question: what are the prospects for developing these cattle feeding

systems in the future in the study area? Following sections are going to deal this. However, it

can be said that scarce natural grazing areas, market orientation, and population growth were

reasons that gradually changed from the free-range to part-time grazing, and then to cut-and-

carry or, for the future, a combination of all systems in selected households. Much work is

required to care for the cattle and cut grass for them, so cattle herd size must often be reduced.

Thus, increasing income of cattle production in selected households through practising

fattening techniques might become a major strategy for farmers to increase their sustainable

livelihoods.

Page 101: BEEF CATTLE SYSTEMS IN THE CONTEXT OF SUSTAINABLE ...bictel-fusagx.ulg.ac.be/ETD-db/collection/... · (2011). Beef cattle systems in the context of sustainable agriculture in Bac

Results and discussions 83

Figure 32: Historical evolution of the cattle feeding systems Source: Households interviews, 2009; Groups discussion; Key person interview; Secondary data.

4.1.2 General socio-economic characteristics of selected households in the systems

4.1.2.1 Family size, labour source and education

The labour force springs from the family, and these persons perform crucial roles in the

adopting of new technologies, especially since pasturing and fattening cattle are considered as

labour-intensive activities. According to Sen (2005), households that face labour shortages or

constraints may hesitate to or would not adopt new technologies that may require additional

labourers.

Table 11 presents the family structure of selected households in three cattle feeding systems.

The average family size was the largest in the cut-and-carry system and accounted for 6.9

persons on average, ranging from 3 to 14 persons. The average family size was much lower in

free-range and part-time grazing systems: 5.0 persons (varying between 2 and 9 persons) and

5.2 persons (ranging between 4 and 8 persons), respectively. There is a significant difference

among the three systems on family size with p<0.001. H’Mong family members differed

significantly to that in selected Tay families in free-range and part-time grazing systems with

both p<0.001. Thus, it could be said that among H’Mong communities located in remote areas

characterised by the spoiling and diminishing of land resources, poor infrastructure and low

living standards, their families seemed to have more members compared to other areas with

better conditions.

Average family size among the systems was quite unlike the Bac Kan provincial average for

household members (4.4 persons per family). Huyen et al. (2010) indicate that in cattle-

keeping households, the average family size is 5.1 persons. However, Tung et al. (2009) find

that the average number of family members of selected households in the NMR is 4.3

persons, which is dramatically lower than the findings of the study. There was also a slightly

Page 102: BEEF CATTLE SYSTEMS IN THE CONTEXT OF SUSTAINABLE ...bictel-fusagx.ulg.ac.be/ETD-db/collection/... · (2011). Beef cattle systems in the context of sustainable agriculture in Bac

84 Results and discussions

lower family size in free-range and part-time grazing systems compared to the average

communal family size in Cong Bang and Nghien Loan in 2007 (5.5 and 5.3 persons,

respectively). Hien (2007) finds that the average family size of Tay households in Cho Don

district, Bac Kan province, is 4.6 persons, slightly lower than that in the study. Huyen (2004)

also found that family size increases when one moves from the market-related system (near

towns, in lowlands) to intermediate systems and on to remote systems (in the uplands). Huyen

et al. (2010) also find that average family size in H’Mong households is 5.9 and 7.6 persons in

Rung Thong and Giao villages respectively, that it was also slightly higher than that in Thai

villages in the lowlands. Tai (2005) shows that the average farm size in H’Mong households

is 6.6 persons in Mai Chau district, Son La province. The average number of family members

in H’Mong households in Son La province was 7.1 persons in 2001 (Huyen, 2004).

The average number of children in cut-and-carry families was 3.0, ranging between 0 and 7

persons, while the average number of children was 1.0 person (between 0 and 2 persons) and

1.2 persons (ranging from 0 to 3 members) in the free-range and part-time grazing systems,

respectively. Those data reveal a significant difference among the three systems (p<0.001).

Between the cut-and-carry and two other systems also show significant differences (both

p<0.001). The average number of mature persons was almost equal among the systems. There

were a small number of elderly persons, showing that the three-generation family is gradually

disappearing. Thus, a high number of children possibly caused the difference in family size of

H’Mong households compared to Tay households. Perhaps, the high birth rate of the H’Mong

people resulted from a lack of accessibility to information and birth-control methods due to

their diversified geography and level of awareness. Moreover, their low education level,

traditional culture, and the new religion that has been introduced since 1990s may play role in

their awareness of birth control. Better access to information and a more convenient

geographical location of health care services may explain the low number of children in Tay

households.

Table 11: Family size and labour force in cattle production systems in 2007

Indicators Free-range Part-time grazing Cut-and-carry Sig.

M Range M Range M Range

Total family members 5.0a 4 – 8 5.2

a 2 – 9 6.9

b 3 – 14 0.001

Adults (16-55 years old) 3.3 2 – 5 3.5 1 – 6 3.1 2 – 7 0.263

Children (<16 years old) 1.0a 0 – 2 1.2

a 0 – 3 3.0

b 0 – 7 0.000

Old people (> 55 years

old) 0.6 0 – 2 0.4 0 – 3 0.8 0 – 2 0.185

Source: Households interviews, 2008 a, b

Within a row not sharing the same superscript letter (p<0.05).

If all samples are normally distributed with equal variances, ANOVA is used. But if both conditions are not met,

the Kruskal Wallis and Mann-Whitney Tests are used.

A very high illiteracy rate was found among family heads in H’Mong households practising

the cut-and-carry system (up to 83.3% compared to zero and 24.3% in the free-range and part-

time grazing systems, respectively) (Figure 33). Thus, the low educational standard of people

in this system was probably due to the harsh geography and traditional culture, making it

difficult for them to access education facilities and information. Huyen (2004) indicates that

the illiteracy level increased from the lowlands and near markets to the highlands and remote

areas. The poor education level reflects poorly on the labour capacity in the uplands compared

Page 103: BEEF CATTLE SYSTEMS IN THE CONTEXT OF SUSTAINABLE ...bictel-fusagx.ulg.ac.be/ETD-db/collection/... · (2011). Beef cattle systems in the context of sustainable agriculture in Bac

Results and discussions 85

to the lowlands. The illiteracy rate was around 30% in H’Mong households in Mai Son

district, Son La province (Huyen, 2004; Tai 2005), which was much lower than in this study

area, which possibly because they have better access to schools in Mai Son district.

A very high proportion of household heads having a secondary school education or higher

was recorded in the free-range system, highlighting a considerable difference among the

systems (83.3% versus 24.3% and zero in part-time grazing and cut-and-carry systems,

respectively). The convenient location as well as early building of the school in the Cong

Bang commune probably explains this result. A high rate of household heads attending

primary school was recorded in the part-time grazing system (51.4%), but a rather low rate of

household heads received a secondary school education or higher (24.3%). So the difficulties

to access schools in Tay households in Nghien Loan commune is due to the long distance and

poor infrastructure in comparison with those in Cong Bang commune seem to be behind these

differences. These education data in the systems are different from data collected in both

communes, e.g. in Cong Bang commune, people participated in secondary school and higher

level education, primary school and illiteracy are 55.6, 17.8 and 26.7%, where as they are

17.3, 40.4 and 42.3% in Nghien Loan commune, respectively (Pac Nam statistical data,

2008). However, education tendency in these communes seems to match with data collected

from the selected systems.

Figure 33: Education level of household heads in the production systems (% of

households) Source: Households interviews, 2008

The Vietnam government has implemented its hunger and poverty alleviation policy, with a

priority focus on remote and mountainous areas, which has helped the H’Mong people to

settle and allow their children going to school, which increased significantly the number of

people who can read and write in H’Mong households (Tai, 2005). Tai (2005) believes that

the educational level indicates the quality of labour and that it is an important factor that

determines the willingness to adopt new ideas and innovations on the farm. Nevertheless, it is

important to note that educational background tended to not play a role in decisions regarding

beef cattle feeding systems in the study. The H’Mong people having the lowest education

level seem to operate the most useful technology in fattening cattle, whereas Tay people in the

free-range system are the best educated but often practise free-range cattle production, which

0

24.3

83.3

51.4

16.7

83.3

24.3

0

0

20

40

60

80

100

Free-range Part-time grazing Cut-and-carry

Illiterature Primary school Higher education

16.7

%

Page 104: BEEF CATTLE SYSTEMS IN THE CONTEXT OF SUSTAINABLE ...bictel-fusagx.ulg.ac.be/ETD-db/collection/... · (2011). Beef cattle systems in the context of sustainable agriculture in Bac

86 Results and discussions

was considered a backward mode of production. Thus, the culture and indigenous knowledge

play critical role in keeping cattle approaches among the systems.

The Kruskal-Wallis Test indicates that there were significant differences among the systems

depending on whether they have low or higher education levels (Chi-Square = 58.8, df = 2,

p=0.000). In addition, application of the Mann-Whitney Test shows that there were

statistically significant differences in education levels between each pair in the three systems

(all p=0.000).

4.1.2.2 Off-farm activities

Table 12 presents the off-farm activities of selected households in the three cattle feeding

systems. Key off-farm activities in the free-range system were retailing, making alcohol, hired

labour, and working in government offices. Up to 89.7% of selected households have off-farm

work, with an average of 1.6 persons engaging in those activities. The average off-farm

income of these households was 12.2 mil. VND, with a range between zero and 104.4 mil.

VND. Almost half of the chosen households did retailing because of their good access to the

commune market, which attracts people from neighbouring communes. Alcohol making was

also a dominant activity, with the main product sold to the market and its by-product used in

pig production. Key off-farm activities in the part-time grazing system were cattle trading,

hired labour, and working in government offices. Of the selected households, 67.6 % had off-

farm work, with an average of 1.4 persons engaging in it. The average off-farm income in the

system was around 9.8 mil. VND. The highest average off-farm income among the systems

obtained in this system was 144 mil. VND per year. The most common off-farm activity of

households was hiring out one’s labour. Other off-farm activities varied among the

households. Although Nghien Loan market is recorded as the largest cattle trade market in the

district, the percentage of the selected households working as retailers was very small that is

quite different from the situation in Cong Bang commune.

Main off-farm activities in H’Mong households were cattle trading, working in local

communities, hired labour in farm activities, and wood collection. In this system 63.3% of

households engaged in off-farm activities, with an average of 1.1 persons. The average off-

farm income was around 2.7 mil. VND that fluctuated from zero to 15.5 mil. VND. Cattle

trading was the most important activity in this system. People purchase cattle from other areas

and sell directly for cash, conducted by around 40.8% of selected households. It is important

to note that hired labour was common in poor households with less land area (around 10%).

Collection of wood to sell in the market was performed by 13.8% of households in the cut-

and-carry system, who often experienced food shortage. Phung and Koops (2003) find that the

average off-farm income of cattle producing households living in the lowlands and uplands of

Quang Ngai province is about 8.4 mil. VND. Tai (2005) also finds that forest products are

important sources of off-farm income for households in the middle altitude and mountainous

areas, which indicates the importance of forestry in the living standard of farmers in these

zones. According to the author, however, there can be a conflict due to the overuse of forests

for immediate livelihoods, which leads to the degradation of this resource. Eguienta et al.

(2002) also find that households who cannot meet their subsistence needs have had to search

for other kinds of income such as hillside cultivation, forest exploitation, animal husbandry

and non-agricultural activities. Thus, H’Mong households practising the cut-and-carry system

in remote areas seemed to have less access to off-farm activities compared to Tay households

living in more favourable areas. According to Tai (2005), people living in the flat areas and

near towns are more market oriented and more frequently engage in off-farm activities

throughout the year compared with those in mountainous and remote areas. In addition, he

Page 105: BEEF CATTLE SYSTEMS IN THE CONTEXT OF SUSTAINABLE ...bictel-fusagx.ulg.ac.be/ETD-db/collection/... · (2011). Beef cattle systems in the context of sustainable agriculture in Bac

Results and discussions 87

also finds that households living in the lowlands obtain the highest income from off-farm

activities, while families located in the remote and mountainous zones have the lowest one.

Table 12: Off-farm activities and income for the selected cattle feeding systems in 2007

Indicators Free-range Part-time grazing Cut-and-carry Sig.

M Range M Range M Range

Households (%) 86.7 67.6 63.3

Off-farm labour (persons) 1.4a 0 – 4 1.0

ab 0 – 3 0.7

b 0 – 2 0.006

Off-farm income (mil. VND) 10.6a 0 – 104.4 9.8

a 0 – 144.0 2.7

b 0 – 15.5 0.004

Activities (% households)

- Alcohol making 30.8 13.6 4.5

- Retailing 53.8 18.2 0

- Cattle trading 0 4.5 40.8

-Officers & retirement 34.6 22.7 9.1

- Hired labour 26.9 50.0 27.4

- Wood collection 0 9.1 18.2

Source: Household interview, 2008 a, b

within a row not sharing the same superscript letter (p<0.05).

If all samples are normally distributed with equal variances, ANOVA is used. if both conditions are not met, the

Kruskal Wallis and Mann-Whitney Tests are used.

4.1.2.3 Land resources and farm size

In the uplands and remote areas, land resources constitute the major means of production for

families. In addition, farm size is also an indicator of the availability of land resources for

grass production for cattle husbandry in the study area. It is also one of the important assets of

farmers.

The farm size of selected households including the lowlands, uplands, and forest land is

presented in Table 13. The smallest farm size was recorded in the cut-and-carry system of

H’Mong households, which reached 1.78 hectares on average, ranging from 0.5 to 5.94

hectares. The average farm size in Tay households practising both the free-range and part-

time grazing systems was higher than that in the cut-and-carry system, in fact almost

equivalent, i.e. 2.15 and 2.17 hectares, which ranged from 0.48 to 6.45 hectares and between

0.20 and 6.85 hectares, respectively. No statistically significant difference was recorded

among the systems (p>0.05). Huyen (2004) also states that H’Mong people had around 2.0 ha

of land on average in Son La province in 2001. Meanwhile, Tai (2005) shows that the

H’Mong people have around 2.88 hectares of land area on average. Huyen (2009) also found

that cattle keeping farms had around 1.8 hectares of land. Huyen et al. (2010) find a slightly

higher land area per household in H’Mong villages (between 2.0 and 2.4 hectares on average).

Tung et al. (2009) conclude that the average farm size of selected households is

approximately 1.80 hectares, equal to data found for H’Mong households, but slightly lower

than that of Tay households in the study.

Page 106: BEEF CATTLE SYSTEMS IN THE CONTEXT OF SUSTAINABLE ...bictel-fusagx.ulg.ac.be/ETD-db/collection/... · (2011). Beef cattle systems in the context of sustainable agriculture in Bac

88 Results and discussions

Table 13: Land resources of beef cattle feeding systems in the study area in 2007

Indicator Free-range Part-time grazing Cut-and-carry Sig.

M Range M Range M Range

Total farm size (Ha) 2.15 0.48 – 6.45 2.17 0.20 – 6.85 1.78 0.50 – 5.94 0.348

Source: Households interviews, 2008

If all samples are normally distributed with equal variances, ANOVA is used. If both conditions are not met,

Kruskal Wallis and Mann-Whitney Tests are used.

A classification of farm size among the selected households in the systems is given in Figure

34 and Table 14.

Figure 34: Farm land size classifications in selected households

in the three systems in 2007 Source: Households interviews, 2008

Table 14: Classification of farm sizes among the cattle husbandry systems in 2007

Items Free-range Part-time grazing Cut-and-carry

N % N % N %

Small farm size (<1.5 Ha) 11 37.7 17 46.0 14 47.7

Medium farm size (1.5-2.5 Ha) 12 40.0 9 24.3 11 37.7

Large farm size (>2.5 Ha) 7 20.3 11 29.7 5 10.6

Source: Households interviews, 2008

The small farm size (<1.5 ha), medium size (between 1.5 and 2.5 ha) and large size (>2.5 ha)

accounted for 43.4%, 33.0% and 23.7% of total selected households, respectively.

Correspondingly, the average land area for the small size farm was 1.05 hectares, while it was

1.93 hectares for the medium farm size, and 4.02 hectares for the large farm size. Although,

the land areas are essentially fixed among the regions, households living in mountainous

regions still had large land areas. In addition, they could also enlarge their land resources if

1.05

1.93

4.02 43.3

33.0

23.7

0

10

20

30

40

50

0

1

2

3

4

5

Small size (<1.5 Ha) Medium size (1.5-2.5 Ha) Large size (>2.5 Ha)

Percen

tag

e of

hou

seh

old

(%

)

Avera

ge f

arm

siz

e (

Ha

)

Average farm size (Ha) Households (%)

Page 107: BEEF CATTLE SYSTEMS IN THE CONTEXT OF SUSTAINABLE ...bictel-fusagx.ulg.ac.be/ETD-db/collection/... · (2011). Beef cattle systems in the context of sustainable agriculture in Bac

Results and discussions 89

forest land and steep, hilly areas were used. Therefore, in comparison to households living in

the delta areas, their farm sizes are larger. Tai (2005) also records that families in the upland

regions have higher land availability in comparison to that of families in the high potential

paddy rice growing areas such as the Red River Delta.

4.1.2.4 Cropping and forest activities

(a) Cropping system

Figure 35 shows the average agriculture land area allocated in each household in the three

systems. The highest average agriculture land area was recorded in the cut-and-carry system,

which used far more agricultural land than the other systems (1.11 versus 0.91 and 0.86

hectare in the free-range and part-time systems, respectively). Despite the larger land area, the

cut-and-carry system showed no statistically significant difference from the other two systems

(p=0.081). The agricultural land areas of households in the cut-and-carry system varied from

0.35 to 2.50 hectares, whereas it ranged from 0.18 to 2.45 hectares in the free-range system

and between 0.20 and 2.05 hectares for part-time grazing. However, in H’Mong households,

their land resources were mainly uplands, where soil quality is poor and getting poorer, which

might be due to inappropriate management. Availability of land for agriculture among the

H’Mong people in Son La is small because they live at high altitude, and the land is degraded

and eroded (Huyen, 2004). She also found that the average farm size of Hmong households is

1.58 hectares. It is important to note that the H’Mong people have ever been familiar with

swidden or slash-and-burn agriculture. However, the government of Vietnam has attempted to

inhibit this practise through the programme called “Sedentisation” for upland people and

Land Use Certificate (LUC). In a consequence, a reduction of this practise was recorded,

together with a population boom. Nevertheless, land resource exploiting for agricultural

activities seemed to be on the upswing, which might generate threats to the environment.

According to Eguienta et al. (2002), in the last fifty years, changes in land-use policy have

contributed to an unsustainable expansion of upland use.

Page 108: BEEF CATTLE SYSTEMS IN THE CONTEXT OF SUSTAINABLE ...bictel-fusagx.ulg.ac.be/ETD-db/collection/... · (2011). Beef cattle systems in the context of sustainable agriculture in Bac

90 Results and discussions

Figure 35: Average agricultural land area in the selected systems in 2007 Source: Households interviews, 2008

Main crop allocation is presented in Figure 36. The main crops cultivated in the selected

households were rice, maize, grass, soybean, and cassava. The total farmland allocated to the

main annual crops ranged from 96% in the free-range system to 100% in the cut-and-carry

system. Huyen (2004) indicates that more than 80% of agricultural land was used for annual

crop in Thai and H’Mong households in Son La province. In the cut-and-carry system, the

highest proportion of land area was allocated for maize production, which accounted for

around 52%, varying from 29% to 100%. The large land area allocated to maize in this system

was undoubtedly due to the high demand for maize as the main food consumed by the

H’Mong people. Besides, H’Mong households often took advantage of intercropping beans

with maize (a week after sowing maize). Rice production was also implemented in a

considerable proportion of land areas among the selected households (28.3%). Thus, rice

cultivation has steadily occupied an essential role as a food resource besides maize in this

system. On the other hand, rice production played a crucial position in the free-range system,

with an average of 53.4% (varying from around 19% to 90%), while land put under maize

accounted for a small percentage. Maize and rice were the major crops in the part-time

grazing system, occupying an average of 30.1% and 36.3% of the agricultural land resource,

respectively. The strong growth of the maize area in this system in comparison with

households in the free-range system may be explained by the development of feed resources

for more intensive pig production.

Correspondingly, the higher the percentage of land allocated for rather high-yielding rice

production, the lower the proportion of food shortage among selected households in the free-

range and part-time grazing systems (6.7% and 5.4%, respectively). Usually, food insecurity

often struck households having less land assets, although farmers in these systems used high-

yielding varieties of maize and rice. Besides, higher investments in crop production for

varieties, fertilisers, herbicides, pesticides, and manure were recorded in the two systems. It is

noted that despite their larger arable land areas, low crop yields were recorded in selected

H’Mong households, which probably caused food insecurity in 30% of them during several

months before cropping season. Otherwise, these households used local crop varieties with a

longer growing time. Thus, the high land proportion allocation for rice cultivation and high-

yield crops may be partially reflected in the lower percentage of selected households facing

food insecurity in the free-range and part-time grazing systems than for the H’Mong

0

0.2

0.4

0.6

0.8

1

1.2

Free ranging Part-time grazing Cut-and-carry

0.91 0.86

1.11

Aver

ag

e ag

ricu

ltu

ral

lan

d p

er h

ou

seh

old

(Ha)

Page 109: BEEF CATTLE SYSTEMS IN THE CONTEXT OF SUSTAINABLE ...bictel-fusagx.ulg.ac.be/ETD-db/collection/... · (2011). Beef cattle systems in the context of sustainable agriculture in Bac

Results and discussions 91

households practising the cut-and-carry system. According to Tai (2005), farmers in the high

mountain zones experience food deficiency due to the limited resources of their families,

especially natural resources. It is hard enough to deal with this challenge, let alone increasing

their standard of living in the future as well.

It is important to note that cassava production gradually dropped off as a human food and

animal feed resource in all three systems. Meanwhile, grass progressively increased its

position in all systems. Households in the free-range system started emphasizing strongly the

importance of grass, which showed a rather remarkable allocated land area (around 13%),

which was presumably found by reducing pastureland for free grazing and government

policies supporting grass planting in cattle development projects. However, grass was still

allocated small areas in the total land resources used for the part-time grazing (8.0%) and cut-

and-carry (6.4%) systems.

Poor land fertility characterises land areas populated by H’Mong because of poor

management, deficits of water, and limited use of supplements such as manure and fertiliser,

as well as soil erosion and degradation of slope land characteristics. In addition, the higher the

altitudinal gradient, the less land is available even on slopes (Huyen, 2004; Tai, 2005). Soil

fertility was gradually reduced over time. Land fertility was also estimated by land use density

(computed by the sum of land allocated for different crops a year divided by the area put into

crop). Land use density is a function of land use in selected households and depends on how

fertile the land is. In almost all selected H’Mong households, land use density was low (1.1

times). Huyen (2004) found that H’Mong people living in mountainous areas face satisfy their

food demands by growing crops. Land quality was much better in Tay households practising

the free-range and part-time grazing systems. In addition, the main characteristic of these

systems are better access to water and in most cases a lowland location. Therefore, compared

to H’Mong households, Tay households in these systems achieved not only higher crop yields

but their land use density was higher (1.4 times on average). Hence, higher land pressure was

recorded in Tay households than in H’Mong households, which showed a significant

difference with p<0.05 among them. Husson et al., (2001) (quoted in Eguienta et al. 2002)

indicate that in their current environmental and institutional context, these marginalized

households have resorted to reducing fallow periods on the hillsides, which reduces the

fertility of cultivated soils and exacerbates erosion. Furthermore, Huyen (2004) brings out that

the scarcity of land resources, land fragmentation, and sloping land all lead to challenges in

using land, including setting the cropping pattern, mechanisation, and land conservation.

Page 110: BEEF CATTLE SYSTEMS IN THE CONTEXT OF SUSTAINABLE ...bictel-fusagx.ulg.ac.be/ETD-db/collection/... · (2011). Beef cattle systems in the context of sustainable agriculture in Bac

92 Results and discussions

Figure 36: Allocation of land areas for major crops in the selected systems in 2007 Source: Household interview, 2008

Table 15 analyses the net income of crop production of selected households in 2007. Net

income is an indicator to evaluate the benefit gained from crop production in one year and is

computed by subtracting from the total gross revenue of all crops the total costs (fixed and

variable costs) used in producing these crops. Gross return from crops is calculated as the

total production yields from different crops multiplied by their farm gate price. The variable

costs include seeds, fertilisers, manure, pesticides, herbicides, hired labour, hired tractor or

petrol used for tractors, ploughing using hired draught animals or family draught power costs,

and hired land if any. Fixed costs are maintenance costs and the straight-line depreciation of

all equipment and machines used in crop production, such as tractors, ploughs, harrows, etc.,

owned outright, and interest payment for loans, where applicable. Family labour is excluded

from variable costs.

Families in both the free-range and part-time grazing systems had around 11.0 mil. VND net

crop incomes on average, which ranged from 4.0 to 25.0 mil. VND and between 1.8 and 21.9

mil. VND, respectively. It was much lower for the cut-and-carry system, around 8.2 mil.

VND on average (varying between 3.0 and 16.0 mil. VND). There was a significant

difference among households in all systems on net crop income (p=0.034). Besides,

significant differences in this variable were also computed by using post hoc Turkey HSD

Tests between the part-time grazing and cut-and-carry systems (p=0.005) and between the

free-range and cut-and-carry systems (p=0.006). Although, households in cut-and-carry had

larger farms compared to those in other systems, their income was lower due to lower yields,

probably resulting from poor-performing local varieties and poor cultivation techniques, lack

of services, and poor land use management. In addition, poor soil fertility and degradation of

slope land areas were also among reasons causing poor yields. In contrast, households

practising the free-range and part-time grazing systems often owned flat, more fertile land,

used better cultivation methods, and managed land use well.

Similarly, a rather high net crop income per land unit was recorded both in the free-range and

part-time grazing systems, with around 13 mil. VND per hectare on average, ranging between

about 3.0 and 27 mil. VND, respectively. A low value was recorded in the cut-and-carry

system (7.9 mil. VND per hectare on average), fluctuating between 3 and 17 mil. VND. A

53.4

30.1 28.3

13.4 36.3 52.0

4.4

16.1

9.9

12.9

8.0 6.4

12.3 6.1 3.0

0

20

40

60

80

100

Free-range Part-time grazing Cut-and-carry

Per

cen

tag

e o

f to

tal

lan

d a

rea

(%

)

Rice Maize Soybean Grass Cassava

Page 111: BEEF CATTLE SYSTEMS IN THE CONTEXT OF SUSTAINABLE ...bictel-fusagx.ulg.ac.be/ETD-db/collection/... · (2011). Beef cattle systems in the context of sustainable agriculture in Bac

Results and discussions 93

statistically significant difference also found among the three systems on crop net income per

land unit (p=0.008). A post hoc test also indicates that between the part-time grazing and cut-

and-carry systems and free-range and cut-and-carry systems, there were significant

differences in crop net income per land unit (both p=0.000).

The difference dramatically varied among the systems according to their geographical

location. A quite low value of crop net income per labour-day of about 15,900-54,200 VND

(about 28,300 VND on average) was recorded in the cut-and-carry system. However, most

selected households in this system (over 90%) gained a higher value than payment for hiring

labour in their location (20,000 VND per day). Interestingly, labour cost in this area was also

lower than in other lowland areas, probably due to low demand and harsh location. On the

other hand, a dramatically high value of crop income per labour-day was achieved in the free-

range system (51,000 VND) fluctuating from around 15,700 to 109,200 VND. Thus, almost

all selected households earned higher value from crop production than from salaries from

hiring oneself out as a labourer in their living area (25,000 VND per day in 2007). An average

of 46,000 VND was recorded in the part-time grazing system, which varied from 11,600 to

82,000 VND, for the most part higher than wages for labour in the study area (30,000 VND).

A significant difference of net crop income per labour-day among the systems was also

recorded with p=0.000. There were also significant differences between the part-time grazing

and cut-and-carry systems and free-range and cut-and-carry systems (both p=0.000).

Table 15: Net income analysis of crop production in cattle feeding systems in 2007

Indicators Free-range Part-time grazing Cut-and-carry Sig.

M Range M Range M Range

Total crop revenue (mil.

VND/HH) 15.1

a 7.2-32.1 14.8

a 3.6-30.7 10.1

b 3.5-17.9 0.002

Total crop costs (mil.

VND/HH) 4.1

a 1.5-13.1 3.8

a 0.9-9.5 1.9

b 0.1-6.5 0.000

Crop net income (mil.

VND/HH) 11.0 4.0-25.0 11.0 1.8-21.9 8.2 3.0-16.0 0.034

Crop net income/land

resource (mil. VND/ha) 13.4

a 5.8-27.5 13.2

a 2.9-27.3 7.9

b 3.0-17.3 0.000

Crop net income/capital

(times) 3.2

a 1.1-9.2 3.5

a 1.0-10.6 7.0

b 1.6-27.4 0.000

Crop net income/labour-

day (1,000 VND) 51.0

a 15.7-109.2 46.0

a 11.0-82.0 28.3

b 15.9-54.2 0.000

Source: Household interview, 2008 a, b

within a row not sharing the same superscript letter (p<0.05).

If all samples are normally distributed with equal variances, ANOVA is used. If both conditions are not met, the

Kruskal Wallis and Mann-Whitney Tests are used.

A very high average crop net income per investment cost unit was observed in selected

households in the cut-and-carry system (7.0 times), varying between 1.6 to 27.4 times. The

crop net income per investment cost unit in the free-range and part-time grazing systems

varied between 1.0 and 10.6 times (3.2 and 3.5 times on average, respectively), which is

significantly lower than the average for H’Mong households (p=0.000 among and between

systems). Thus, it seems to record that the higher the investment in fertiliser and herbicides,

the lower crop net income per investment cost unit and the lower efficient their production.

Page 112: BEEF CATTLE SYSTEMS IN THE CONTEXT OF SUSTAINABLE ...bictel-fusagx.ulg.ac.be/ETD-db/collection/... · (2011). Beef cattle systems in the context of sustainable agriculture in Bac

94 Results and discussions

Nevertheless, the achievements from crop production in the free-range and part-time grazing

systems were still considerable.

(b) Forestry production

The livelihoods of ethnic minority groups in mountainous regions has a long history with

close connections to forests, given the extremely important resources of water, food,

medicine, firewood, timber and many other materials derived from the forest (Tai, 2005).

Huyen (2004) discusses that due to shortage of land for agricultural activities, agricultural

land was expanded through deforestation, which has a strong impact on the socio-economic

situation of the hill tribes in the mountainous regions. The Vietnam government has

implemented several reforestation programmes to help protect the environment. For that

reason, there was a sharp increase in forest area in Pac Nam district, from around 2,700

hectares in 2004 to over 9,000 in 2009 subsequent to implementing the Forest Land

Allocation programme. Forest land allocation started in 1992 with the following objectives:

(i) fix settlement of the mountainous populations and put an end to swidden or “slash-and-

burn” agriculture; (ii) protect forestry resources (it is estimated that forest cover has decreased

significantly, from 45% in 1943 to 28% in 1991, as recorded by Quy (1998) and quoted in

Castella et al. (2002b)); and (iii) develop plantations and sylvicultural production to improve

the living standards of mountain populations (Castella et al., 2002b). The programme given to

the farmers was supported through a credit programme, subsidisation of forest plant varieties,

provision of rice for families and technical training. In the following years, the cultivation of

forest land was stable according to statistical data. Actually, it area might even have been

reduced due to poor management of the farmers and lack of control from the government, but

no report about this was seen.

Only 76.7% of selected households in the cut-and-carry system had forest land, compared to

100% and 94.6% of those practising the free-range and part-time grazing systems. On the

other hand, the average forest land area in selected H’Mong households was about half that of

the selected households in the other two systems (0.66 versus around 1.30 hectares, on

average) (Table 16). Huyen (2004) records around 0.40 hectare of forest land allocated per

household in H’Mong villages in Son La province, compared to around 0.09 hectare per

family recorded by Tai (2005) in the same area. Thus, a significant difference of forest area

was analysed among three systems and between the cut-and-carry and the free-range and part-

time grazing systems (all p<0.05). This dramatic difference in proportion of households

owning forest area may be explained by the later immigration of H’Mong people (from 1979,

originating in Cao Bang province, after the border war between Vietnam and China) and the

fact that a large part of their forest land was allocated to be cropping land as mentioned above

in the land allocation section.

Proportions of households cultivating forest land were quite low in all systems. The highest

number of households owning planted forest was in the part-time grazing system (over 65%),

while the lowest percentage of households cultivating forest was around 35% in the cut-and-

carry system. Correspondingly, the highest land area used for forest production was in part-

time grazing with 0.45 hectare on average (the maximum area was 2.0 hectares), whereas the

average forest production was much lower, with 0.20 and 0.22 hectare for the other two

systems. Income from forest was almost equivalent among systems, and reached between 4.5

and 5.0 mil. VND on average, but it was mainly derived from collecting firewood for fuel,

with the exception of several households that started selling woods for paper processing or

scaffolding. Households could earn around 50-100 mil. VND per hectare of acacia or

manglietia conifer after five to seven years, which was considered better than crop production

because of the lower investment costs and labour requirement.

Page 113: BEEF CATTLE SYSTEMS IN THE CONTEXT OF SUSTAINABLE ...bictel-fusagx.ulg.ac.be/ETD-db/collection/... · (2011). Beef cattle systems in the context of sustainable agriculture in Bac

Results and discussions 95

Despite the spreading of forest production projects promoted by the government through

various incentives and financial aid, not many households implemented forest cultivation and

those who did only developed small areas. The situation of forest development might relate

to: (i) poor transportation corridors causing difficulties in harvesting wood and getting the

product out; (ii) the time involved from planting until the harvesting period; and

(iii) unreliable consumption with a lower value than expected. Another feature to note is that

forestry development interfered with cattle production in the study sites. Natural pasture areas

gradually decreased, making it difficult to raise ruminants, especially when the plants were

small. Free-range cattle production suffered extensively. Huyen (2004) feels that developing

forestry will gradually eliminate the use of forest land for livestock husbandry.

Table 16: Forest allocation and production in the selected systems

Indicators Free-range Part-time grazing Cut-and-carry Sig.

M Range M Range M Range

Allocated rate (% HH) 100.0 - 94.6 - 76.7 - -

Forest areas (ha/HH) 1.24a 0.20 – 4.40 1.31

a 0.0 – 6.10 0.66

b 0.0 -4.00 0.002

Cultivated rate (% HH) 50.0 - 65.8 - 34.8 - -

Cultivated forest area

(ha/HH) 0.20

a 0.0 – 1.40 0.45

b 0.0 – 2.00 0.22

a 0.0 – 1.60 0.019

Income from forest (mil.

VND/HH) 4.5 1.4 – 8.6 5.0 1.5 – 21.9 4.6 2.9 – 9.0 0.663

Source: Household interview, 2008 a, b

within a row not sharing the same superscript letter (p<0.05).

If all samples are normally distributed with equal variances, ANOVA is used. If both conditions are not met, the

Kruskal Wallis and Mann-Whitney Tests are used.

4.1.2.5 Livestock production systems

(a) General information on livestock production and production scale

In selected households practising the cut-and-carry and part-time grazing systems, livestock

species were ranked as following: cattle, swine, and poultry according to their importance,

whereas they were ranked as cattle, buffalo, and swine in the free-range system. Table 17

presents the average number of livestock types kept by each selected household. The buffalo

raised in the all selected households were local breeds (swamp type). They played a major

role as sources of cash, income, and cash saving. Their general use in social events such for

slaughter at festivals or wedding presents was limited due to their high value in the market,

with an exception that several high-living level households gave one or two buffalo to their

sons when they married. Buffalo played a minor role in the cut-and-carry and in part-time

grazing systems. In the cut-and-carry system, this may be explained by their poor ploughing

capacity in the uplands compared to cattle, as borne out by the very low percentage of

households keeping buffalo (26.7%), with an average of 0.6 head per family (varying from 0-

4 head). Buffalo production in the part-time grazing system was also not ranked as important

because: (i) only a quarter of households in the part-time grazing system raise buffalo

(29.7%), with an average of 0.4 head; (ii) extensive use of tractors in the part-time grazing

system area, reducing the need to use them in ploughing land areas; and (iii) their poor

reproductive performance compared to cattle. However, buffalo still played an important role

Page 114: BEEF CATTLE SYSTEMS IN THE CONTEXT OF SUSTAINABLE ...bictel-fusagx.ulg.ac.be/ETD-db/collection/... · (2011). Beef cattle systems in the context of sustainable agriculture in Bac

96 Results and discussions

in the free-range system due to: (i) their role in draught power. Although tractors have

become commonplace throughout the lowland communes, not all households can afford a

tractor for crop production. And unlike tractors, buffalo can work on uneven terrain and in

confined areas; (ii) they were highly valued in this system because keeping buffalo and cattle

provides a labour resource. Buffalo are easier to raise than cattle, especially in the situation of

gradually reduced natural pastures. Although their reproduction performance was lower in

comparison to cattle because of longer calving intervals and the later age of females at first

calving (Annex 4), the high value of mature buffalo due to their lean meat capacity compared

to cattle was still a reason for keeping them; and (iii) a high growth capacity of buffalo was

indicated by interviewees. One factor viewed advantageously was the slower movement of

buffalo, making them easier for owners to work with and tending, which has recently

prompted some selected households to change from cattle production to buffalo production,

especially in the context of reforestation and limitation of pastureland. This is substantiated by

the fact that 90% of selected households kept buffalo, with an average of 2.9 head (ranging

from 0 to 7 head). There was a statistically significant difference of average buffalo number

among the systems (p=0.006), and between the free-range and other two systems (both

p=0.000). Eguienta (2000) reports that buffalo play a critical role as draught animals, as a

source of fertiliser, and also as a form of capital for smallholders. He found that around 80%

of Cho Don District households in Bac Kan province have at least one buffalo.

Table 17: Number of main livestock types kept per farm household in the different

systems

Indicators Free-range Part-time grazing Cut-and-carry Sig.

M Range M Range M Range

Num. of households

keeping buffalo (%) 90.0 - 29.7 - 26.7 - -

Average num. of

buffalo (head) 2.9

a 0.0 – 7.0 0.4

b 0.0 – 2.0 0.6

b 0.0 – 4.0 0.006

Num. of households

keeping pigs (%) 100.0 - 100.0 - 96.7 - -

Average num. of pigs

(head) 4.6

a 1.0 – 9.0 2.9

b 0.0 – 9.0 3.1

b 0.0 – 9.0 0.001

Num. of households

keeping chicken (%) 93.3 - 94.6 - 96.7 - -

Average num. of

fowl (birds) 19.9 0.0 – 70.0 18.2 0.0 – 100.0 19.9 0.0 – 50.0 0.708

Source: Households interviews, 2008 a, b

within a row not sharing the same superscript letter (p<0.05).

If all samples are normally distributed with equal variances, ANOVA is used. If both conditions are not met, the

Kruskal Wallis and Mann-Whitney Tests are used.

Poultry production on the study sites involved chickens, ducks, muscovy ducks, and geese.

They were almost all local breeds. Chickens were the predominant type, raised free-range

with a little maize and rice supplement in the idle time (after crop harvesting). Although

chicken production provided little or no cash income for the households, quite a high

proportion of households in the study area kept them anyway (ranging from 93.3% in the part-

time grazing to 96.7% in the cut-and-carry system). Households in the selected systems raise

an average of 20 birds per household, probably because of convenience: (i) no labour

Page 115: BEEF CATTLE SYSTEMS IN THE CONTEXT OF SUSTAINABLE ...bictel-fusagx.ulg.ac.be/ETD-db/collection/... · (2011). Beef cattle systems in the context of sustainable agriculture in Bac

Results and discussions 97

required; (ii) no need to spend cash on feed resources; (iii) provides food for home

consumption, especially where the market place is far from the household and not held

regularly; and (vi) is a source of cash in a time of need. Sen (2005) also records the similar

reasons for keeping poultry in households in Quang Tri province.

A high proportion of selected households in the different systems also kept pigs (from 96.7%

to 100%). On average, pig numbers ranged from 2.9 head in the part-time grazing system to

4.6 head in the free-range system. A statistically significant difference among the systems was

analysed (p=0.006) and between the free-range and the other two systems (both p<0.01). The

high percentage of households keeping pigs may be explained by the fact that the households

took advantage of their own crop products, their residues, and by-products, thus obtaining

high resource efficiency.

(b) Pig production

General information about the pig production of the different farm household systems is

presented in Table 18. Pig production in selected households was significant in that it

provided them with a cash resource, food, and social status. Slaughtering pigs for the Lunar

New Year festival was recorded in 53.3% of the selected households in the cut-and-carry

system. A dramatic 90% of selected households slaughtered fattened pigs for the New Year

festival and other important events of their families in the free-range system. Allowing the

pigs to range freely was recorded in most of households in the cut-and-carry system as well as

in many other selected households practising the free-range system, while no selected

household practising part-time grazing husbandry kept free-range pigs. In selected households

that allowed pigs to range freely, the animals were not controlled and inbreeding was normal.

Generally, the local Meo pig breed was the main sow bred in the all systems, which ratios of

households raising them reached for 94.4, 70.6 and 100.0% in the free-range, part-time

grazing and cut-and-carry systems, respectively. The Meo breed is the major indigenous pig

breed in the Bac Kan province uplands as well as many other provinces in the NMR. The high

percentage of Meo sows kept in selected households may be explained by their high

adaptability. The selected households invest little in their husbandry, including feed, hygiene

care, and veterinary services. Sows of the Mong Cai breed was not often kept (5.6 and 29.4%

of households keeping sows in the free-range and part-time grazing systems, respectively).

The Mong Cai breed is an improved local pig breed in Vietnam, originating from the Red

River Delta. This breed has been predominantly used as a maternal line in northern Vietnam.

Only 5.6% of selected households in the free-range system use exotic sire breeds, while up to

58.8% of sows kept by households in the part-time grazing system are serviced by a boar of

these breeds.

Feed resources used for pig production were farm-produced products such as maize, rice bran,

cassava, vegetables, and banana stems. In the cut-and-carry system, forest vegetables were

predominantly used, inferring a dependence on natural resources. Particularly, during the time

of pig feed shortage, often from November to March, H’Mong households often fed their pigs

banana stems, cassava, and forest vegetables. A very low growth rate was observed in this

system due to breed characteristics and poor nutrition. In the free-range system, fermented

distillery grain was largely utilized (from alcohol making). A rather low proportion of

households in this system supplemented the diet with concentrate feeds (16.7%), whereas a

higher percentage of households practising the part-time grazing system used high quality

feed for pigs (29.7%). Thus, pig production is not as yet completely market oriented, although

higher investment costs in feeding and breeding were recorded households in the part-time

grazing system. No household in the cut-and-carry system used concentrate feed.

Page 116: BEEF CATTLE SYSTEMS IN THE CONTEXT OF SUSTAINABLE ...bictel-fusagx.ulg.ac.be/ETD-db/collection/... · (2011). Beef cattle systems in the context of sustainable agriculture in Bac

98 Results and discussions

Table 18: Description of pig production in the cattle feeding systems (% households)

Indicators Free-range Part-time grazing Cut-and-carry

Pig slaughtered for social events 90.0 67.6 53.3

Keeping Meo sow breed 94.4 70.6 100.0

Keeping Mong Cai sow breed 5.6 29.4 0.0

Servicing by crossbred sires 5.6 58.8 0.0

Using concentrate feed 16.7 29.7 0.0

Source: Households interviews, 2008

Reproductive performance of pigs was rather poor. The highest average number of live piglets

born per sow was about 6.5 piglets per litter in the part-time grazing system (varying from 5.0

to 8.4 head), while sows kept in the cut-and-carry system had the lowest litter size, with an

average of 5.4 live piglets born per litter (3.5-8.0 heads) (Table 19). Thus, the average number

of live piglets born in these systems was very low compared to other local pig breeds such as

the Mong Cai breed (about 10 to 11 head per litter on average) and the Meo breed (about 7 to

8 head per litter on average) found in Tra, 2003; Lemke, 2006. There was a significant

difference among the systems for live piglets born (p=0.041), and a significant difference was

also found between the part-time grazing and cut-and-carry systems (p=0.013). Sows kept in

the cut-and-carry system showed a higher mortality of piglets until weaning compared to the

other two systems. Thus, the smallest number of piglets at weaning per litter was recorded in

this system, with around 4.4 head, ranging between 0 to 7 head, whereas the largest number

was 6.3 head per litter in part-time grazing. A significant difference on this indicator

(p=0.007) was found between the part-time grazing and cut-and-carry systems.

A shorter pig fattening pig time was recorded in the free-range and part-time grazing systems

(6-12 months), while H’Mong households might fatten a pig from one to two years before

slaughtering at the weight of 70-80 kg or smaller. As mentioned before, the predominant sow

breed in study area was the Meo, characterised by low growth rate, poor reproductive

performance, and lengthy raising time, whereas crosses were characterised by a better growth

rate, high fertility, and shorter raising time. However, the poor performance of pig production

is due not only to low breeding quality, but also to poor management and poor feed resources.

Tra (2003) and Lemke (2006) also indicate that this breed is characterised by a poor growth

rate and poor reproductive performance compared to other indigenous breeds.

Page 117: BEEF CATTLE SYSTEMS IN THE CONTEXT OF SUSTAINABLE ...bictel-fusagx.ulg.ac.be/ETD-db/collection/... · (2011). Beef cattle systems in the context of sustainable agriculture in Bac

Results and discussions 99

Table 19: Reproductive performance of sows in the cattle feeding systems

Indicators Free-range

(N = 13)

Part-time grazing

(N = 13)

Cut-and-carry

(N = 15)

Sig.

M Range M Range M Range

Num. of litters 3.5 2.0 – 5.0 3.8 2.0 – 8.0 2.9 2.0 – 5.0 0.220

Piglets/litter (head) 6.4a 2.0 – 9.0 6.5

a 5.0 – 9.0 5.3

b 3.0 – 8.0 0.041

Weaning pigs/litter

(head) 5.4

ab 2.0 – 9.0 6.3

a 4.0 – 9.0 4.3

b 0.0 – 7.0 0.028

Litters/sow/year 1.4 1.0 – 2.0 1.4 1.0 – 2.0 1.3 1.0 – 1.5 0.871

Source: Households interviews, 2008

Data based on sows having two litters and above. a, b

within a row not sharing the same superscript letter (p<0.05).

If all samples are normally distributed with equal variances, ANOVA is used. If both conditions are not met, the

Kruskal Wallis and Mann-Whitney Tests are used.

4.1.2.6 Analysis of the economic efficiency of livestock production

The benefit of keeping a variety of livestock types in the studied households is also denoted

by net income in each species. Gross return from livestock is calculated by subtracting

purchases of livestock, value of stock obtained as payment in-kind and gifts, value of stock at

the beginning of the accounting period from the total income from sale of stock, value of

stock used for domestic consumption, value of stock at the end of the accounting period, and

the value of livestock products produced (Tung et al. 2007; Dillon and Hadarker, 1993). Total

costs of livestock production include fixed (depreciation of livestock stable and maintenance

cost, interest payments, etc.) and variable costs (feed resources, breeding or replacement

costs, veterinary services paid in cash and in-kind and hired labour).

Net income from all types of animal types in year 2007 in the free-range system came to

around 12.9 mil. VND on average (fluctuated from -19.1 to 32.6 mil. VND), which is rather

high compared to that in other systems, which reached 8.7 mil. VND (ranging between -2.5 to

21.9 mil. VND) and 11.0 mil. VND (ranging from 0.8 to 28.7 mil. VND) in the part-time

grazing and cut-and-carry systems, respectively. The dramatic differences among households

in these systems might be explained by high losses and/or expenses of production. The lowest

net income in part-time grazing could be explained by high expenses in feeds and breeding for

pig production in some households. The high losses from livestock production resulted from

poor efficiency for livestock production in some families. Nevertheless, no difference of net

income from livestock production is found among the systems (p=0.077). This economic

efficiency in the selected households among the systems might partially be explained by the

soaring of product prices throughout 2007, for example the price of a pig live weight nearly

doubled by late of 2007 compared to early 2007 (from around 15,000 to 30,000 VND per kg

live weight); the price of beef cattle and buffalo, estimated by lean meat capacity, increased

from around 50,000 to approximately 70,000 VND in the same period, and the price of

poultry products also increased by around 1.5 times in the same period. Thus, the healthy

gross revenue and net income received by some households in all the systems were rooted not

only in their skills in management and no loss from disease, but also from the tangible

increased price of their products.

Figure 37 indicates main livestock net income. Selected farmers in the free-range system

received their main income from cattle, buffalo, and pig production, whereas farmers in other

Page 118: BEEF CATTLE SYSTEMS IN THE CONTEXT OF SUSTAINABLE ...bictel-fusagx.ulg.ac.be/ETD-db/collection/... · (2011). Beef cattle systems in the context of sustainable agriculture in Bac

100 Results and discussions

systems obtained their income only from cattle and pig production. Cattle production brought

the highest benefits among livestock types among the feeding systems. Quan (2001) also finds

that households raising cattle in the mountainous zone in Quang Binh province earn the

highest income compared to poultry production and raising pigs.

The average net income generated from buffalo for households in the part-time grazing and

cut-and-carry systems was around one third and one forth that in the free-range system (1.1,

0.8 and 3.1 mil. VND, respectively). These values ranged from -20.7 to 9.1 mil. VND in the

free-range system, between -3.1 and 6.2 mil. VND in part-time grazing and -0.6 – 6.5 mil.

VND in the cut-and-carry system. Losses due to disease and accident in the systems resulted

in negative benefits for buffalo production, although the buffalo lean meat price increased

sharply from 50,000 to 70,000 VND during the investigated period. Another feature to note is

that buffalo net income showed a significant difference among the systems with p=0.000.

Significant differences were also recorded between free-range and part-time grazing

(p=0.001) and between free-range and cut-and-carry with p=0.000. Buffalo production in the

free-range system was more profitable than that in the other systems, which might be due to

more available pasture areas and use of draught power for land preparation.

Pig production in the free-range system provided the highest net income with 3.3 mil. VND

per household on average, while it was 2.2 and 1.6 mil. VND in the part-time grazing and cut-

and-carry systems, respectively. Correspondingly, disease losses also brought negative net

income for pig production in several households, which indicated a range of between -0.4 and

11.9 mil. VND, from -3.0 to 10.4 mil. VND and between -2.4 and 8.0 mil. VND in the free-

range, part-time grazing and cut-and-carry systems, respectively.

Poultry production was not very profitable in the selected households in all systems, each

earning from 0.53-0.65 mil. VND, on average. Poultry production recorded profit varying

from -1.2 to 3.2 mil. VND, between -1.1 and 4.5 mil. and between -0.7 and 3.5 mil. VND in

the selected systems, respectively. Pig and poultry net income showed no significant

difference among the systems. Better efficiency of pig production in the free-range system

might result from taking advantage of the by-products of alcohol making. Nevertheless,

livestock production in the selected systems was not as good as expected. Poor disease control

and prevention, poor management and skills might explain these results. A more detailed

analysis of cattle net income will be made in the following section. Detailed information on

livestock net income in the systems and for different farm sizes is indicated in Annex 5 and

Annex 6.

Page 119: BEEF CATTLE SYSTEMS IN THE CONTEXT OF SUSTAINABLE ...bictel-fusagx.ulg.ac.be/ETD-db/collection/... · (2011). Beef cattle systems in the context of sustainable agriculture in Bac

Results and discussions 101

Figure 37: Net income obtained in the major livestock types in selected systems in 2007 Source: Household interview, 2008

Households engaged in livestock husbandry sustained many losses due to such things as

disease outbreaks, accidents, and theft. Generally, most losses were related to disease

outbreaks. The percentage of household loss in livestock production and overall loss are

presented in Table 20. All households keeping buffalo in the part-time grazing system

experienced loss, compared to 37.5% and 22.2% of those in the cut-and-carry and free-range

systems, respectively. Around 90% of households producing pigs in the cut-and-carry system

sustained losses, with a nearly similar rate recorded in the other systems (56.7% and 48.7% in

free-range and part-time grazing, respectively). Poultry production also contributed to a high

proportion of households suffering loss, 100%, 85.7%, and 65.5% in part-time grazing, free-

range and cut-and-carry, respectively. The highest economic loss in buffalo production was

recorded in the free-range system (1.6 mil. VND on average) but the fluctuation was great,

with a maximum of 25.0 mil. VND. The family of Mr. Nong Hoang Cap in the free-range

system was an example, with a loss of 25.0 mil. VND from buffalo production in 2007 due to

FMD disease and accidents. The lowest value of livestock lost was 0.5 mil. on average in the

cut-and-carry system, ranging from 0.0 to 6.0 mil. VND.

Nevertheless, the highest economic value of pig production loss was in the cut-and-carry

system, where pigs are usually allowed to roam freely (1.3 mil. VND, on average). For

instance, Mr. Ly Van Lu suffered a very high loss of up to 6.3 mil. VND in 2007. In the

remaining systems average pig production losses were almost equivalent (0.8 and 0.6 mil.

VND per household, with an identical range from 0 to around 4.5 mil.). There was a

significant difference among the systems regarding loss of economic value in pig production

with p=0.015. In addition, there were significant differences between the cut-and-carry and

other two systems (both p<0.001).

In poultry production, the highest loss was around 1.0 mil. VND per household in the part-

time grazing system, while it was around 0.3 and 0.5 mil. VND in the free-range and cut-and-

carry systems, indicated by a statistically significant difference (p=0.000). the part-time

grazing system also showed significant differences compared to the other two systems with

both p<0.001. A high death rate of chickens was recorded in many surveyed households in all

systems, perhaps due to no vaccination and poor management, e.g. a considerable proportion

of households in the cut-and-carry system raise poultry (80%) with an average loss of around

5.3 4.8

7.8

3.1

1.1

0.8

3.3

2.2

1.6

0.53

0.53

0.65

0

3

6

9

12

15

Free-range Part-time grazing Cut-and-carry

Gro

ss m

arg

in o

f li

ves

tock

(m

il.

VN

D)

Cattle Buffalo Pig Poultry

Page 120: BEEF CATTLE SYSTEMS IN THE CONTEXT OF SUSTAINABLE ...bictel-fusagx.ulg.ac.be/ETD-db/collection/... · (2011). Beef cattle systems in the context of sustainable agriculture in Bac

102 Results and discussions

0.6 mil. VND. Thus, losses in livestock types were rather remarkable, especially in

comparison to potential profits from those activities in households.

Table 20: Losses in livestock production (exception for cattle) in selected systems in 2007

Indicators Free-range Part-time grazing Cut-and-carry Sig.

M Range M Range M Range

Loss in buffalo

production (% HH

keeping)

22.2 - 100.0 - 37.5 - -

Average value (mil.

VND/HH) 1.6 0.0 – 25.0 1.1 0.0 – 12.0 0.5 0.0 – 6.0 0.193

Loss in pig production

(% HH keeping) 56.7 - 48.7 - 89.7 - -

Average value (mil.

VND/HH) 0.8

a 0.0 – 4.2 0.6

a 0.0 – 4.6 1.3

b 0.0 – 6.3 0.015

Loss in poultry

production (% HH

keeping)

85.7 - 100.0 - 65.5 - -

Average value (mil.

VND/HH) 0.5

a 0.0 – 1.9 1.0

b 0.0 – 3.8 0.3

a 0.0 – 1.2 0.000

Source: Households interviews, 2008 a, b

within a row not sharing the same superscript letter (p<0.05)

If all samples are normally distributed with equal variances, ANOVA is used. If both conditions are not met, the

Kruskal Wallis and Mann-Whitney Tests are used.

4.1.2.7 Analysis of the economic efficiency of farm and non-farm activities

According to Tai (2005), improvement in household living standard and food security could

be implemented by increasing farm and family income. Farm income is considered as the

economic capacity of a farm to provide an economic surplus to be used by the farming family

in one year. The average household net income was the smallest in the cut-and-carry system

(26.5 mil. VND), ranging from 11.0 to 46.8 mil. VND (Figure 38). Among income sources in

the system, livestock net income accounted for the highest amount, around 40%, on average.

In this system, due to generally poor quality and degraded land resources, the development of

livestock might be the ideal option, which partially explains the high proportion of households

that practise it. In addition, the complex geography and topography of the region makes

market access difficult, also hinders the development of off-farm activities, as shown by the

small percentage of off-farm income in total household net income in the cut-and-carry

system. On the other hand, the highest household net income was recorded in the free-range

system, with 39.1 mil. VND, on average. Livestock net income was also the largest income

source in this system, accounting for around 33%, but was smaller than that in the cut-and-

carry system. Net income from crop production accounted for the highest income source in

the part-time grazing system, accounting for around 32%. Thus, with good access to markets,

better land resources in terms of both quality and quantity, households practising the free-

range and part-time grazing systems seemed to enjoy better net income from not only crop

and livestock production but also from off-farm activities. However, no statistically

significant difference among the systems was indicated (p=0.063). Tai (2005) found that

H’Mong families in the uplands earned around 11.2 mil. VND on average, while Thai people

at the middle level and on lowlands earned from around 8.0 to 26.0 mil. VND in 2001 in Son

Page 121: BEEF CATTLE SYSTEMS IN THE CONTEXT OF SUSTAINABLE ...bictel-fusagx.ulg.ac.be/ETD-db/collection/... · (2011). Beef cattle systems in the context of sustainable agriculture in Bac

Results and discussions 103

La province. He also found that farm incomes tend to decrease from farms in lowlands to the

farms in high mountainous zones. Phung and Koops (2003) show that average household

income of cattle raising farms in Quang Ngai province is about 14.7 million VND.

Figure 38: Net household income in the cattle feeding systems in 2007 Source: Households interviews, 2008

The average income from forestry ranged from 4.5 to 5.0 mil. VND among the systems and

accounted for a small amount in the free-range and part-time grazing systems compared to

other household activities, while it reached a somewhat better position in the cut-and-carry

system, but still poor. Tai (2005) also highlights that income from forestry contributes a very

small part to family income in not only H’Mong families but also to that of other hill tribes.

He feels that forest areas have been exhausted by overexploitation in the past. However, this

minor contribution does not reflect the real potential of the forest for ethnic minority groups

living in mountainous areas, as they have greater opportunities for gain from forestry than

from agriculture.

10.6 9.8

2.7

11.0

8.2

13.0

8.7

11.0

4.5

5.0

4.6

0

5

10

15

20

25

30

35

40

Free-range Part-time grazing Cut-and-carry

Net

in

com

e (M

il V

ND

)

Off-farm Crop Livestock Forest

11.0

Page 122: BEEF CATTLE SYSTEMS IN THE CONTEXT OF SUSTAINABLE ...bictel-fusagx.ulg.ac.be/ETD-db/collection/... · (2011). Beef cattle systems in the context of sustainable agriculture in Bac

104 Results and discussions

Box 3: Mr. Duong Van Lu in the cut-and-carry system

Mr. Duong Van Lu is an example of the above characteristics of H’Mong households in the cut-and-

carry system. His family has eight members, four adults and four children. His family has an off-farm

activity (collecting wood and selling it for cash in times of food shortage), which employed one person

and earned 0.54 mil. VND per year. He has 1.37 hectares of agricultural land area and no growth forest

land area. His family netted 14.2 mil. VND in net income from crop production. His family kept five

pigs and 50 chickens, no buffalo, but raised six cattle. From livestock production including cattle, his

family earned 9.7 mil. VND in net income.

Box 4: Mr. Duong Van Duong in the free-range system

Mr. Duong Van Duong is a representative household in the free-range system. The family has six

members including four adults. One person worked in off-farm activities and earned 3.6 mil. VND per

year. His family has only 0.80 hectare of agricultural land and 0.70 hectare of forest land. His family

earned 13.6 mil. VND in net crop income. His family raised four pigs, 10 chicken, four buffalo, and six

cattle. From livestock production (including cattle), his family had a net income of 10.8 mil. VND.

Box 5: Mr. Lac Van Sinh in the part-time grazing system

Mr. Lac Van Sinh is a representative of households in the part-time grazing system. He has a family of

five members, including two adults. He has 1.06 hectares of agricultural land area and 0.6 hectare of

forest land. His family earned 15.1 mil. VND in net crop production income. His family had six pigs,

one buffalo, and five cattle. From livestock production (including cattle), his family earned a net

income of 14.7 mil. VND.

4.1.3 Resource flow in smallholder households and cattle production

The schematic flow of farm resources related to cattle production is presented in Figure 39.

Generally, cattle production on the study site was closely interrelated with crop production.

Cattle provided draught power for tillage and manure as inputs to crop production, while they

consumed left-overs and other crop wastes as inputs to their production. In addition, cattle

owners also use maize as supplement feed resource for cattle in winter time and for fattening.

Cattle usually provided cash for the cattle-owning household through animals sold for

fattening or breeding, but such transactions were rarely recorded, and also for slaughtering

(meat production). Expenses for crop production might be derived from cattle production

income leading to capital growth in households and vice versa. However, strong development

of crop production may limit development of cattle due to reduced feed resources with the

decrease in pastureland available for grazing cattle. Moreover, giving high priority to other

crops might limit the growth of planted grass for cattle production and labour resources.

Nevertheless, crops destruction was recorded by selected households, especially in the free-

range system.

Likely, cattle husbandry and forest production are closely related. Forestry activities supply

timber for cattle stable construction, forest pasture for grazing, and forest fodder tree leaves as

a feed resource. In turn, cattle provide manure for forest growth. However, competition

between the two activities was observed. Expansion of the forest area limits natural pasture,

while cattle are considered one of the main causes of soil erosion and degradation, especially

in the uplands. Further, planted forest was also destroyed by cattle, especially in early stages

of growth. Another noteworthy feature is that cattle production has a direct relationship with

markets and off-farm activities. Cattle were often sold directly to markets to get cash.

However, cattle for breeding were sometimes bought at markets. Thus, cattle production can

provide a cash resource as capital for implementing off-farm activities. Off-farm activities

provide cash for cattle production in terms of buying breeding cattle or payment for veterinary

Page 123: BEEF CATTLE SYSTEMS IN THE CONTEXT OF SUSTAINABLE ...bictel-fusagx.ulg.ac.be/ETD-db/collection/... · (2011). Beef cattle systems in the context of sustainable agriculture in Bac

Results and discussions 105

services. Cattle production creates employment opportunities for the family as well as cash,

income, savings source, social status, and wealth. Conversely, households provide labour

resource and cash for cattle production. Cattle production is emphasized as an important

activity for the households. Further analysis of cattle production is made in the next Sections

in order to highlight its role and function in households. Besides, the relationship with other

actors is also presented in order to understand the flow of household resources and use.

Flow within households Flow between households and outside

Figure 39: Resource flow in selected households for cattle production Source: Households interviews, 2008; Groups discussion; Key person interview

4.1.4 Section summary

To summarise, selected households in each cattle feeding system have different characteristics

according to their ethnic minority. H’Mong households in the cut-and-carry system live in the

uplands, experience harsh living condition, and poor hygiene is common. They have poor

infrastructure and difficulties in access to information and services. An analysis of interviews

with households in the system, the family size is large, the education level low, agricultural

land areas are available, but soil fertility is poor; there is low land use pressure but low crop

yields due to poor management. Nevertheless, selected households in the system had

approximate labour source compared to other systems. A rather low percentage of selected

households worked in off-farm activities for little pay. Trading cattle as an important off-farm

activity contributed to the income of many households along with the ready availability of

cattle markets in local areas, and to the development of the cut-and-carry cattle system.

Although crop net income accounted for one of the largest income sources among activities

(around 30% of total household income), food security was still an important issue in the

system in spite of large land areas allocated for maize and rice production as main food

resources. Livestock production was used mostly for home consumption, with the exception

of cattle and buffalo. Thus, increasingly limited arable land and population growth in the

system are challenges to creating sustainable livelihoods. Development of cattle production to

a more commercial trend might be one of the most promising solutions for people in the

system.

Households

Cattle Crops Forest

Off-farm

activities

Markets Cash; Employment

Cash

Fertiliser

Seeds

Manure

Feed resource

Soil erosion

Cash

Wood for fuel

Employment

Cash

Food

Employment

Cash; Employment

Cash

Land

Manure

Feed resource

Pasture limitation

Cash

Employment

Foods

Cultured exchanged

Cash

Cash

Feed

resource

Cash

Feed

resource

Cash

Breeding

Page 124: BEEF CATTLE SYSTEMS IN THE CONTEXT OF SUSTAINABLE ...bictel-fusagx.ulg.ac.be/ETD-db/collection/... · (2011). Beef cattle systems in the context of sustainable agriculture in Bac

106 Results and discussions

Meanwhile, Tay households in the free-range system were located in the lowlands with better

soil fertility but poor hygiene conditions still prevailed. This system was identified by

medium family size, high education level, rather large farm size but quite high land use

pressure, high crop intensification - rather high investment in crops and high crop yield, and

better food security compared to H’Mong people in the cut-and-carry system. Nevertheless, a

higher level of education levels did not tend to affect the cattle husbandry system they

practise, which was considered the oldest and most traditional. Crop production occupied

roughly one fourth of total household income. Rather strong development of buffalo in

comparison to that in other systems was recorded. Livestock production was computed for a

large proportion in total net income of their families. Local people have good access to

communal pastureland areas, which might be a major reason holding their cattle production

system as free-grazing, next to labour saving because of no tending cattle. Their main off-

farm activities are retailing and alcohol making, taking advantage of the local market, thus

resulting in a significant income source for selected households that also consider as a

competition with cattle production. Their livelihoods combined off-farm activities, crop

production, and livestock husbandry.

On the other hand, characteristics of Tay households in the part-time grazing system were

quite similar to those in the free-range system, but enjoyed better hygiene conditions.

However, their education levels were much lower than those in the free-range system. Crop

production played a more important role than that in the free-range system. Buffalo

production was underdeveloped, while pig production was more market oriented. In selected

households, their cattle production is strongly linked to the household’s resources, off-farm

activities, and farm activities.

The income from cattle raising contributed a considerable amount to livestock net income

among the systems, especially in the cut-and-carry system, was accounted for the largest share

among livestock types. Thus, cattle production in selected households was the most important

source of income in livestock production sector, all of cattle feeding systems combined

It seems that the free-range cattle feeding system underwent a change over the years to a part-

time grazing approach due to changes in accessibility of natural pastureland, reforestation

policies, and additional support policies of the government for cattle production. Similarly,

the cut-and-carry approach is a spinoff of the free-range system through such influences as

income potential and increasingly limited natural land areas. Not to be discounted is that this

feeding system might also be a corollary of a combination of social-economic factors.

Overall, it can be concluded that education level does not seem to determine their cattle

keeping approaches, but employing different cattle feeding systems might be related to the

nature of separate minority groups, agricultural and forest production, and accessibility to off-

farm activities and public pasturelands. Large farm size but lack of quality land, agricultural

practices, poor accessibility to off-farm opportunities, their culture and indigenous knowledge

might be factors influencing the H’Mong people’s decision to practise the cut-and-carry

system in the past and that of the few Tay people in more recent times and in the future.

Meanwhile, cattle husbandry was a main farming activity, one of very important income

sources, playing an important role in all systems.

Page 125: BEEF CATTLE SYSTEMS IN THE CONTEXT OF SUSTAINABLE ...bictel-fusagx.ulg.ac.be/ETD-db/collection/... · (2011). Beef cattle systems in the context of sustainable agriculture in Bac

Results and discussions 107

4.2 CHARACTERISATION OF SELECTED CATTLE FEEDING SYSTEMS

4.2.1 Characteristics of cattle production in selected systems

4.2.1.1 Reasons for keeping cattle

Purposes of cattle production in selected households is presented in Table 21.

Table 21: Reasons for keeping cattle in selected cattle systems

Free-range Part-time grazing Cut-and-carry

Items % household Items % household Items % household

Breeding 100.0 Breeding 100.0 Breeding 100.0

Savings 100.0 Manure 89.2 Draught 93.3

Manure 90.0 Savings 86.5 Savings 76.7

Wealth 86.7 Income 51.4 Income 60.3

Income 60.3 Draught 48.6 Manure 26.7

Employment 10.3 Employment 10.8 Wealth 20.7

Draught 3.3 Wealth 8.1 Employment 20.7

Source: Households interviews, 2008

In the free-range system, the major reasons for cattle husbandry were breeding and savings.

Ranking next in importance were manure production and wealth. Thus, cattle manure has

started to play an important role in crop production although fertilisers seem to be overused in

the study areas; especially it has a low labour input compared to manure. Similarly, the key

reason for keeping cattle in the part-time grazing system was also breeding. Ranking next

were manure production and savings. In many households, cattle still had an important role

for draught power, because most of their land areas were highly sloped, and using cattle as

draught animals was necessary. In this system, farmers also ranked manure production as

important. On the other hand, manure derived from cattle production was viewed as less

important in H’Mong households practising the cut-and-carry system due to the steep hills as

mentioned in the last section. Draught power from cattle production was ranked quite highly

in the cut-and-carry system because of the special geography in which cattle must be used for

ploughing. Particularly, the social status of owning cattle was high in all selected systems due

to their increasing economic value. The custom of slaughtering cattle for festivals or giving an

animal as a wedding present was completely replaced by using pigs, chicken, or cash. Tra

(2007) also finds that farmers in Bac Kan province considered cattle production as the most

important livestock type because cattle are often kept for breeding, cash resource, savings,

and income. Huyen et al. (2008) also state that cattle production in Son La province supplies

not only power, manure, meat, and income to farmers but also fulfils a social function. On the

other hand, cattle are considered as a symbol of a sustainable life and safety as well in the

rural areas, provide an important means of transportation, and are used for the hardest

activities in land preparation on the farm (Huyen, 2004). She also finds that cattle are

considered as a money-saving opportunity in rural areas, especially for ethnic minority

groups.

Page 126: BEEF CATTLE SYSTEMS IN THE CONTEXT OF SUSTAINABLE ...bictel-fusagx.ulg.ac.be/ETD-db/collection/... · (2011). Beef cattle systems in the context of sustainable agriculture in Bac

108 Results and discussions

4.2.1.2 Cattle breed and herd size classification

In Bac Kan province, there is the Yellow cattle breed kept by the H’Mong people who live in

the remote, upland areas. It is considered to have a higher body weight as compared to the

local Yellow breed, and it is considered as a new breed namely H’Mong cattle (Bac Kan

DARD, 2006; Nho et al., 2003; Niem et al., 2001). Nevertheless, Bac Kan’s Department of

Sciences and Technology (DST) and National Institute of Animal Sciences (NIAS) conducted

a survey on this cattle breed in the Pac Nam district in 2009. The study finds that the live

weight of mature female and male cattle are rather different from information published in the

literature about this breed, 222 kg for a female animal on average based on 44 cows over 36

months of age. The study also finds that the average live weight of a bull is 258 kg from over

two to four years old, based on 133 head. These data are slightly higher than those for Yellow

male and female cattle indicated in many studies (180-200 kg for a cow and 250 kg for a

bull), but these data were different from the findings of Niem et al. (2001) on cattle kept by

H’Mong people in Ha Giang province (with 250-270 kg in female and 380-400 kg in male

cattle). These results can probably be explained by a mixing of cattle breeds due to loss of

control over service during grazing in the same pasture areas among hill tribes. According to

Huyen et al. (2008) and Huyen (2009), classification of cattle systems is also not based on

breeds raised by H’Mong people or Thai people in the uplands and lowlands of Son La

province. In this study, no measurement of body weight of those cattle kept in H’Mong and

Tay households was carried out in order have further classification and identification of

breeds themselves due to limitation of time, funding and geography condition. Therefore, in

the context of the study, no difference is made between Yellow cattle breeds.

Interestingly, with different husbandry methods among the systems, the average number of

cattle kept per household among the systems showed no statistical significant difference with

each other during the interview time (varies from 4.2 to 5.4 head on average) (Table 22).

However, there was a large range in cattle herd size in selected households, from 1 to 16 head.

Contrarily, Maltsoglou and Rapsomanikis (2005) find that the average cattle herd size in each

household in the northern rural mountains was 2.0 head. Tung et al. (2009) found that the

average cattle herd size in selected households in the NMR was 3.6 head. The authors also

state that the average herd size of cattle herds in households that combined grazing and

stabling is 3.4 head in the NMR. Their finding also indicates that the average herd size for

cow-calf keeping is 3.9 head per household. Huyen et al. (2010) found that people in Rung

Thong and Giao H’Mong villages in Son La province in the NMR kept from 1 to 7 head of

cattle, with an average cattle herd size of 1.7 and 4.2 head, respectively. On the other hand,

the study conducted by Bac Kan DTS and NIAS (2009) also found that H’Mong people in

Pac Nam district kept on average 2.6 head of cattle per household, which is smaller than the

finding in this study. Nevertheless, the sample size was selected randomly among households

keeping cattle in the survey conducted by Bac Kan DTS and NIAS, which could explain the

dissimilarity with this study (this study had selected households keeping cow-calf pairs, in

which the herd size is often larger than that of households selected randomly). Households

practising the free-range system, where one would expect a larger herd size due to the

husbandry approach, explained that forest development programmes and sharing available

land for the poor in other communes in the district causing others to migrate to their commune

is one of major causes of herd size reduction in their families. In addition, there was no

difference between highland or lowland households. However, Huyen (2009) finds that

selected households in the uplands with access to pasture had larger herds than farms in the

lowlands in Son La province. Huyen (2004) found that the number of cattle is associated with

the size of land area available and with the level of mechanisation as well.

Page 127: BEEF CATTLE SYSTEMS IN THE CONTEXT OF SUSTAINABLE ...bictel-fusagx.ulg.ac.be/ETD-db/collection/... · (2011). Beef cattle systems in the context of sustainable agriculture in Bac

Results and discussions 109

The average cow number was quite similar among the systems (ranging between 1.4 and 1.8

head). Tung et al. (2009) also found that the average cow number is 1.8 head in the NMR.

Cow, heifer, steer and calf numbers showed no statistically significant difference among and

between systems. Exceptionally, a statistically significant difference was found in bull

numbers among systems with p=0.005 and between the cut-and-carry and part-time grazing

systems (p=0.042). This difference might be explained by the manner of fattening bulls by

households practising the cut-and-carry system and no bull is kept solely for breeding purpose

in the free-range and part-time grazing systems; selected households often sell them as

slaughtering cattle when mature after preparing land resources.

Table 22: Cattle herd size and structure in the cattle feeding systems

Cattle herd structure Free-range Part-time grazing Cut-and-carry Sig.

M Range M Range M Range

Average num. cattle

(head/HH)

5.2 2.0 – 16.0 4.2 1.0 – 12.0 5.4 2.0 – 14.0 0.409

Average num. cows

(head/HH)

1.8 1.0 – 4.0 1.4 1.0 – 3.0 1.8 1.0 – 4.0 0.306

Average num. bulls

(head/HH)

0.4ab

0 – 2.0 0.3a 0.0 – 2.0 0.9

b 0.0 – 4.0 0.005

Average num. heifers

and steers (head/HH)

1.7 0.0 – 7.0 1.4 0.0 – 5.0 1.6 0.0 – 6.0 0.936

Average num. calves

(head/HH)

1.2 0.0 – 4.0 1.1 0.0 – 3.0 1.1 0.0 – 4.0 0.867

Total cattle TLU 3.0 1.0 – 9.0 2.4 0.8 – 6.5 3.4 1.0 – 9. 0.263

Source: Households interviews, 2008

a, b

within a row not sharing the same superscript letter (p<0.05).

TLU – Tropical Livestock Unit

If all samples are normally distributed with equal variances, ANOVA is used. If both conditions are not met, the

Kruskal Wallis and Mann-Whitney Tests are used.

Figure 40 presents the cattle herd ranking according to size. There were 37 households raising

between 1 and 3 head of cattle, an average of 2.6 head per household. The highest number of

households had a medium-size cattle herd from 4 to 6 head (43 households with 4.6 head on

average). Despite being considered as the highest growth area for cattle in Bac Kan province,

there were only a small number of large cattle herds (17 households), who kept from 7 to 16

head, with an average of 9.8 head per household.

A detailed classification of cattle herd size in each system is given in Table 23. Generally,

medium herd size accounted for the highest proportion among the systems, reaching about

40.3% in the free-range to 46% in the part-time grazing system. Small herd size accounted for

smaller percentages in the systems, which were lowest in cut-and-carry (30.0%) and highest

in part-time grazing (43.2%). The largest size accounted for the smallest ratios. The lowest

ratio recorded was only 10.3% in part-time grazing, while cut-and-carry obtained the highest

one of 20.3%.

Page 128: BEEF CATTLE SYSTEMS IN THE CONTEXT OF SUSTAINABLE ...bictel-fusagx.ulg.ac.be/ETD-db/collection/... · (2011). Beef cattle systems in the context of sustainable agriculture in Bac

110 Results and discussions

Figure 40: Classification of cattle herd size (small, medium, large) in selected households Source: Households interviews, 2008

Table 23: Classification of cattle herd sizes among selected cattle feeding systems

Items Free-range Part-time grazing Cut-and-carry

N % N % N %

Small herd size (1-3 head) 11 36.7 16 43.2 10 30.3

Medium herd size (4-6 head) 13 40.3 17 46.0 13 43.3

Large herd size (>6 head) 6 20.0 4 10.8 7 20.3

Source: Households interviews, 2008

4.2.2 Management of cattle production in cattle feeding systems

4.2.2.1 Feed resources and grass production

(a) Feed resources and strategies

The main feed resource in grazing consists of natural grasses and fodder tree leaves in

communal pasture, forest land, fallow land, rocky mountain and flat land and uplands after

harvesting. These are the most important feed resources of cattle in the selected systems and

cattle were grazed throughout the year. Besides, feed resource from planted grass also played

an important role in selected households. Rice straw and maize leaves are used by most

households but in small quantities, with an exception for households in the cut-and-carry

system (Table 24). The maize harvesting season often lasts about one month, from July to

August. Ibrahim and Olaloku (2000) also state that by-products from agricultural production

are a major feed resource used for cattle production. There are many kinds of crop residues

that can be used for feeding ruminants. Straw is one of the most important crop residues used

as a stored feed resource for cattle, especially in feed shortage season. Rice straw is also

available throughout the year, but it is mainly fed to cattle in winter time. Ly (1995) indicates

2.6

4.9

9.8

37

43

17

0

5

10

15

20

25

30

35

40

45

0

2

4

6

8

10

Small herd size (1-3

heads)

Medium herd size (4-6

heads)

Large herd size (>6 heads)

No

. h

ou

seh

old

s p

er c

att

le h

erd

siz

e

cla

ssif

icati

on

Avera

ge N

o. ca

ttle

per h

ou

seh

old

Average No. cattle No. Households

Page 129: BEEF CATTLE SYSTEMS IN THE CONTEXT OF SUSTAINABLE ...bictel-fusagx.ulg.ac.be/ETD-db/collection/... · (2011). Beef cattle systems in the context of sustainable agriculture in Bac

Results and discussions 111

that the development of cattle using these sources of feeds will be more sustainable, although

most crop residues have low nutrition value.

It is important to note that cattle are considered not competing directly with humans for cereal

grains in Vietnam. Especially, food security is not always achieved in mountainous regions

such as Bac Kan province, with its growing population, poor agricultural gross outputs, and

limited land farming area, while high percentage of the poor live under the poverty line.

Nevertheless, availability of feed resources is one of the biggest challenges confronting Asia,

both in quality and quantity (Thomas et al., 2002). Tra (2007) also finds that the potential use

of crop residues and by-products in Bac Kan will be an advantage for cattle production in the

future, especially for the food shortage season if they are properly processed and stored.

However, Trach (2004) finds that use of processed crop residues for cattle feeding is

constrained for many reasons, including inconvenience in reorganising routine activities,

psychological issues, and low economic concerns. Particularly, the very small scale

production of cattle is the main reason for not adopting new techniques. Thus, a suitable

strategy will also be needed to promote new techniques of storage and process by-products in

the NMR. In addition, banana stems, rice bran, and maize are also used as supplemental feed

resources at calving time, when draught strikes, or for fattening cattle. Maize is primarily used

as a supplement in well-off households in the cut-and-carry system, while other H’Mong

families use pig feed for fattening cattle. Meanwhile, maize and pig feed are rarely utilized in

the other two systems, with the exception of occasional periods of bad weather. In the part-

time grazing and cut-and-carry systems, during the cropping season and when grazing cannot

be practiced due to bad weather, supplementing feed resources was needed, which brought

more difficulties to households because either they had to plant grass or process and store

crop by-products. Thus, competition of cultivated land areas between cropping and grass

planting might be an issue for farmers with limited arable land available, especially in

households still faced with food insecurity such as H’Mong families.

Page 130: BEEF CATTLE SYSTEMS IN THE CONTEXT OF SUSTAINABLE ...bictel-fusagx.ulg.ac.be/ETD-db/collection/... · (2011). Beef cattle systems in the context of sustainable agriculture in Bac

112 Results and discussions

Table 24: Feed resources used in selected systems

Feed resources Free-range Part-time grazing Cut-and-carry

Rice straw * ** -

Maize leaves/young tree leaves * ** **

Cassava root * * *

Cut-and-carry natural grass, fodder

tree leaves - - ***

Grazing *** *** ***

Planted grass * ** **

Maize * * **

Rice bran * * *

Pig feed * * **

Bean plants * * *

Banana stems * * *

Source: Households interviews, 2008; Calendar; Groups discussion; Key person interview

Note: ***using a large amount; **using a medium amount; *using a small amount; - not used

The feed shortage season is a time when all cattle do have not enough feed and need to graze

longer or receive supplements from owners, lasting from October/November to

February/March. It also corresponds to after harvesting of crops. Thus, cropping lands after

harvesting can be used for cattle grazing without damage caused by the cattle. Feed

availability/abundance means cattle can feed enough, do not need to graze a long time or

require supplemental feeding, often lasting from March/April to September/October. This

time also corresponds to the growing season, when natural grasses and trees flourish in the

study area. Tra (2007) also mentions the same definitions. It means that cattle taken out to

graze have been tended by family members to avoid damage to crops. Detailed strategies of

households to cope with shortage of feed resources in selected cattle feeding systems are

shown in Table 25.

Page 131: BEEF CATTLE SYSTEMS IN THE CONTEXT OF SUSTAINABLE ...bictel-fusagx.ulg.ac.be/ETD-db/collection/... · (2011). Beef cattle systems in the context of sustainable agriculture in Bac

Results and discussions 113

Table 25: Feed shortage seasons and strategies to get through the feed shortage season

Systems Season of feed shortage Season of feed availability/abundance

Ch

ara

cteristics

of sea

son

s

- No planted grass

- Lack of natural grasses and tree resources on

grazing land

- After crop harvesting season

- Growing season of planted grass

- Abundance of natural grasses and fodder tree

leaves resources in all places

- Growing season for crops

Strategies to overcome

Fre

e-ra

ng

e

- November - February

- Long periods of free ranging without tending by

family member, regular check

- Feed some rice straw, forest banana stem, given

salt when at home

- March - October

- Shorter periods of free-range with a regular

check, but without constant tending by a

family member

- Feed some available cultivated grass

Pa

rt-time

gra

zing

- November - February

- Allow cattle to graze all day with tending by a

family member

- Feed rice straw and give salt at night

- Rarely use maize or pig feed

- March – October

- Grazing for a half day with tending by a

family member

- Feed some available cultivated grass

Cu

t-an

d-ca

rry

- October - March

- Allow cattle to graze all day with tending by

family members

- Cut-and-carry natural grasses and fodder tree

leaves if bulls are housed, but harder to collect

feed

- Feed housed bulls maize soup or pig feed

- April – September

- Allow cattle to graze all day but for several

short periods with tending by family

members, no supplemental feeds

- Fattening season of cattle

- Cut-and-carry is practised with natural

grasses, fodder tree leaves and cultivated

grass

- Feed bulls maize soup or pig feeds

Source: Households interviews, 2008; Calendar; Groups discussion; Key person interview

(b) Grass growing

With strong support strategies from the government (a subsidy of 6 mil. VND per hectare,

free elephant grass seed, and training), and despite its demonstrated efficiency in fattening

cattle, only 43.3% of selected households in the cut-and-carry system planted grass on an

average of 0.06 hectares of land (ranging from 0.0 to 0.5 hectare). Grass production is more

widely practised in selected households in the free-range system (80.0%) and with an average

area of 0.11 hectare (ranging from 0 to 0.5 hectare) and 73.3% in selected households in the

part-time grazing system, with an average area of 0.08 hectare (varying from 0 to 0.3 hectare)

(Table 26). Tung et al. (2009) indicate that only 33.8% of selected household in the NMR

grow grass for cattle production. The authors also find that the average grass production area

in the NMR is around 0.05 hectare. In the selected systems, the support from the

governmental cattle development project possibly explains the high proportion of households

cultivating grass. There is a significant difference in land area allocated for grass production

among the systems (p=0.002). Nevertheless, only the significant difference between free-

range and cut-and-carry on grass production land was analysed (with p=0.008).

Grass is often harvested when the weather is bad or at times when households in the free-

range and part-time grazing systems are too busy to tend grazing cattle. However, cattle in the

cut-and-carry system are regularly fed planted or cut natural grasses and forest fodder tree

Page 132: BEEF CATTLE SYSTEMS IN THE CONTEXT OF SUSTAINABLE ...bictel-fusagx.ulg.ac.be/ETD-db/collection/... · (2011). Beef cattle systems in the context of sustainable agriculture in Bac

114 Results and discussions

leaves for fattening. It is important to note, however, that planted grass develops vigorously in

the rainy season in the same way that natural grass and forest plants grow, so farmers are not

motivated to harvest grass frequently. No processing and storage of grass and crop by-

products were recorded in the study area during the season when grass is abundant. However,

Tay households harvest grass over a longer time than H’Mong households (March to October

versus April to September) due to soil fertility and access to water resources where they live.

No cultivated grass is available during the cold, dry season, when a severe shortage of natural

feed resources is seen. Thus, a feed deficit in the dry season is a serious issue with cattle

production. In mountainous regions, feed resources used for cattle are often stored for use

during the winter season (October to March) (Ly, 1995; Van et al., 2005).

Table 26: Grass production in beef cattle feeding systems

Indicators Free-range Part-time grazing Cut-and-carry Sig.

M Range M Range M Range

Grass growing (%

HH) 80.0 - 73.3 - 43.3 - -

Average grass area

(ha/HH) 0.11

a 0.0

1 – 0.50 0.08

ab 0.0

1 –0.30 0.06

b 0.0 – 0.50 0.020

Grass growing

season March-October March-October April-September -

Average grass yield

(tonnes/ha) 36.6

a 0.0

2 – 108.0 25.3

ab 0.0

2 – 90.0 15.6

b 0.0 – 96.0 0.015

Harvesting frequency Occasional Occasional Regular -

Proportion used for

cattle (%) 34.4 - 78.5 - 94.7 - -

Source: Households interviews, 2008; Calendar; Groups discussion; Key person interview a, b

within a row not sharing the same superscript letter (p<0.05).

If all samples are normally distributed with equal variances, ANOVA is used. If both conditions are not met, the

Kruskal Wallis and Mann-Whitney Tests are used.

Therefore, the average grass yield is quite low in the systems in comparison to results from

other studies in the NMR. Mui et al. (2005) find that the average elephant grass yield in Ha

Giang province ranged from around 50 to 130 tonnes per ha per harvest (farmers could

harvest from two to three crops depending on their management and soil fertility). Grass yield

shows statistically significant differences among the systems, which ranged from 15.6 tonnes

in cut-and-carry to 36.6 tonnes per hectare in free-range (p=0.017). There is a significant

difference in grass yield between the free-range and cut-and-carry systems (p=0.006) and no

difference is found between others. These differences are indicated by deficit of water

availability, shorter harvesting time and poor quality of the soil used for grass in the cut-and-

carry system, while low frequency of harvesting might explain the results for part-time

grazing due to its heavy dependency on natural pasture for grazing. Moreover, lack of strict

regulations in the district cattle project for farmers receiving the subsidy for grass production

meant that many households took advantage of the subsidy to plant large land areas but took

little or no responsibility for harvesting. Thus, a combination of different reasons may explain

the low yield of grass production on the study sites. In addition, in the free-range system, a

high proportion of grass is utilized for buffalo and a smaller amount is used for cattle (around

Page 133: BEEF CATTLE SYSTEMS IN THE CONTEXT OF SUSTAINABLE ...bictel-fusagx.ulg.ac.be/ETD-db/collection/... · (2011). Beef cattle systems in the context of sustainable agriculture in Bac

Results and discussions 115

65% versus 35%), while the proportion used for cattle is around 79% in part-time grazing and

95% in cut-and-carry systems.

(c) Socio-economic analysis of grass growing in cattle production among the

systems

Family labour spent on different cattle activities between households with and without grass

production is presented in Table 27. Family time used for grass production accounted for a

small value, around 12 days on average, ranging between zero and 75 days. Several

households put in grass but did not harvest it due to their grass land areas being destroyed by

grazing cattle and buffalo. Actually, these households put in grass because of the subsidy and

the cattle project in the district, not from a real demand for cattle and buffalo feed resources.

Generally, grass production was on a very small scale and was not well supported by

households, though producing it actually reduces labour time in cutting and carrying natural

grasses and fodder tree leaves. An Independent Sample Test indicated that time spent on

cutting and carrying and caring for the animals was significantly different between the two

groups (p=0.005). Similarly, time spent tending grazing animals seemed to create a higher

employment opportunity in the group that did not plant grass compared to the group planting

grass (50 days difference), but no significant difference was recorded between them. It could

be explained that without grass production, farmers need to spend more time to collect feed

resources and take their animals out to graze in order to have enough feed for their cattle.

Thus, differences in cut-and-carry time and grazing days between the two groups might be a

reason to factor in a higher time of total family labour in cattle production among households

planting grass. However, there was no statistically significant difference between the groups

on different indicators (all p>0.05).

Table 27: Labour spent on different cattle production activities in selected households

with or without grass production

Indicators Grass cultivation

(N = 64)

No grass cultivation

(N =33)

Sig.

M Range M Range

Grass cutting (day) 12.3 0.0 – 75.0 - - -

Cut and carry feed resources (day) 9.0 0.0 – 112.0 25.0 0.0 – 135.0 0.005

Grazing (day) 213.6 11.8 – 450.0 265.1 30.0 – 405.0 0.180

Total time (day) 233.9 11.8 – 483.8 290.1 30.0 – 517.5 0.917

Source: Households interviews, 2008

In order to identify differences between households raising cattle with and without planting

grass, an analysis of net income from cattle husbandry in these households is presented in

Table 28. Total return of cattle production shows a 0.5 mil. VND difference between planting

and not planting grass (8.2 versus 7.7 mil. VND, on average). Nevertheless, an Independent

Sample Test showed no statistically significant difference between them on total cattle return

(p=0.805). There was also no statistically significant difference on cattle net income between

the two classifications households with and without planting grass (p=0.184). Exceptionally,

total cattle costs differ significantly between the two groups (p=0.000), because the average

total costs for cattle production among households growing grass was double compared to

that in households without grass production (2.6 versus 1.3 mil. VND). Thus, whether they

Page 134: BEEF CATTLE SYSTEMS IN THE CONTEXT OF SUSTAINABLE ...bictel-fusagx.ulg.ac.be/ETD-db/collection/... · (2011). Beef cattle systems in the context of sustainable agriculture in Bac

116 Results and discussions

planted grass or not seemed to make little difference in household benefits. This might be

explained because only a small area of land was allocated for grass production, there was no

frequent harvesting and, in some cases, no harvesting of grass, hence poor management and

low yield of grass. Tung and Giang (2008) find that in the northern region of Vietnam, grass

production has a statistically significant difference that impacts on the economic efficiency of

cattle production in households compared to households without grass production, however

the significant different is with p=0.1

Table 28: Net income analysis of cattle production with and without grass production

Indicators Grass cultivation

(N = 64)

No grass cultivation

(N =33)

Sig

M Range M Range

Cattle total revenue (mil. VND/HH) 8.2 -0.6 – 32.0 7.7 2.4 – 17.7 0.805

Cattle total costs (mil. VND/HH) 2.6 0.04 – 21.7 1.3 0.01 – 10.5 0.000

Cattle net income (mil. VND/HH) 5.6 -3.0 – 18.5 6.4 2.3 – 16.3 0.184

Source: Households interviews, 2008

(d) Grazing land and management of natural pasture

On the study sites, farmers often graze their cattle on fallow land, on crop fields after

harvesting, and on natural unused land and forest land. In spring and summer, natural grass

and trees grow well, which could provide enough feed for cattle. In winter, the cold, dry

climate inhibits the growth of natural forage plants, leading to a chronic shortage of feed

resources. During this critical period, the food requirements of cattle increase, which force

households to let the animals out to graze for longer periods compared to other seasons (see

Table 25 above). A supplement of rice straw is of major importance in this season.

Particularly, households began to be taken with forest development on the study sites, where

forest was planted on unused land areas, thus limiting natural pastures and hindering cattle

production. It is important to note that natural pastureland and cultivated forest lands were

located haphazardly with other crop land and unused land, such that it was often referred to by

the local people as “mixing cooked sticky rice and beans”. The policy makers at different

levels (provincial and district) do not emphasise the matter of pastureland development. All of

interviewed authorities agreed that it is an important issue and should be brought up in the

development plan of the province and district as well. Nevertheless, it is complicated matter

and has not yet been carried out in the study area as well as in other areas. Selected

households said that: “Due to poor planning of forest land and other lands, we have had

difficulty in our cattle production because lack of pasturelands for grazing cattle. The

government should have planned out forest land and other lands carefully, organised large

pasturelands to help promote ruminant production”. Limited forage lands also caused

conflicts among households within and outside communes/villages that had to compete for

grazing cattle. In addition, interviewed households indicated that disagreements had occurred

among households due to cattle and buffalo destroying crops and areas planted with forest.

Thus, farmers continue to rely on natural pastures and forests to provide fodder for their

buffalo and cattle. This situation is also mentioned by Eguienta (2000). Eguienta et al. (2002)

indicate that rotating fallow fields and natural pasture improvement are notably absent from

the local system in Cho Don district, Bac Kan province. Minot et al. (2003) also indicate that

the lack of pastureland is one of the major reasons hindering the poor farmers in the

Page 135: BEEF CATTLE SYSTEMS IN THE CONTEXT OF SUSTAINABLE ...bictel-fusagx.ulg.ac.be/ETD-db/collection/... · (2011). Beef cattle systems in the context of sustainable agriculture in Bac

Results and discussions 117

development of animal production. According to Ly (2002), natural pastureland is limited in

Vietnam. The relatively low quality of natural grasslands is said to be due to the lack of

fertilisers, of water source in the winter season and of good management (Ly, 1995; Quan,

2001; Ly, 2002). Natural grasses often grow in arid or low rainfall areas, unsuitable for crop

growing (Quan, 2001). Tra (2007) found that there is serious competition among cattle herds

for grazing land located near the homes of farmers. Hence, in order to prevent loss of cattle

weight due to a lack of feed, cattle must be grazed in remote areas. Family members in these

areas are often unavailable for the hard work of tending the animals. No payment is required

for grazing land in the study areas. Care or management of grazing lands is not a matter of

concern for either users or local authorities. However, conflicts often occur in households who

keep free ranging cattle (untended by family members), especially when free-range grazing is

practiced during the cropping season or in a neighbouring commune. However, there is a

gradual reduction in cattle herds allowed to graze freely due to increasing less unused land

area available and to the high losses sustained.

Besides, there is a strong intensification of crop production in the selected households

practising the free-range system. Two crops per year are becoming common on the study site,

resulting in a narrowing of fallow land. Communal pastures in the uplands and hills are being

employed for crop production. Other reasons such as development of planted forest and the

growing local population are also expected to make it difficult to develop communal

pastureland in the near future. Particularly, there is a migrant programme for poor people

from the whole district to Cong Bang commune, where land resources have been reallocated

to newcomers. Thus, a lack of grazing areas was one of the consequences, not only causing a

reduction of cattle herd size but also stirring competition and conflicts among livestock raisers

that might hurt local social relationships. Competition between established villagers and

outsiders is expected to be stronger in the near future, if planning for natural pasture is not

considered seriously in government development programmes. Currently, the Bac Kan

provincial and Pac Nam district organisations had no concrete plans, either long-term or

short-term, for public natural pastureland for cattle and buffalo production.

4.2.2.2 Reproductive performance and breeding management of cattle

This study will not focus on productive performance because of some limitations in the study,

but will emphasise the reproductive performance in beef cattle feeding systems. The

reproductive performance of cows in the different systems is presented in Table 29. The study

results show that cows in the cut-and-carry system having their first calf at the age of around

40.5 months, on average (with a variation of 36 to 60 months). Huyen et al. (2010) find that

the age of cows at first calving in the highlands among the Thai and H’Mong people is 3.2

years on average (or around 38 months). However, Niem et al. (2001) found that the age at

first calving of cows raised in H’Mong households in Ha Giang province is shorter, only

around 33 months. Results found in the selected households in the part-time system showed

that the average first calving age of cows was also around 40.8 months, a little higher than

that in the free-range system (around 41.6 months). These figures were considerably higher

than those found by Tung et al. (2009) in local Yellow cattle (34.1 months) throughout the

country. Huyen et al. (2010) also record that cattle kept in the lowlands had a lower age at

first calving (2.8 years or around 33.6 months), compared to those in the study. The first

calving ages of Yellow cattle in the free-range and part-time grazing systems were much

higher than findings by Ly et al. (1999), who found the age at first calving of cow ranges

from 30-36 months.

The average calving interval among cows kept by H’Mong households in the uplands was

14.6 months, ranging from 12 to 24 months. Thus, this calving interval was shorter than that

Page 136: BEEF CATTLE SYSTEMS IN THE CONTEXT OF SUSTAINABLE ...bictel-fusagx.ulg.ac.be/ETD-db/collection/... · (2011). Beef cattle systems in the context of sustainable agriculture in Bac

118 Results and discussions

found by Niem et al. (2001), which was around 16 months for cattle production of H’Mong

households in Ha Giang province. Huyen (2009) also indicates that calving interval in cattle

raised in the uplands by H’Mong and Thai people in Son La province was 16.3 months on

average. Tung et al. (2009) report that the calving interval of local cattle in Vietnam is 15.4

months, on average. In free-range and part-time grazing, the calving interval is more or less

equal (16.6 and 16.3 months, respectively), which was considered higher than that in the cut-

and-carry system. These results were dramatically higher than data found by Huyen (2009),

with an average calving interval of 12.8 months for Yellow cows raised in the lowlands.

There was a significant calving interval difference among the systems (p=0.007). There were

also significant differences between the cut-and-carry and the other two systems on this

indicator (p=0.003 and 0.018, respectively). These reproductive results of Yellow cattle in the

free-range and part-time grazing systems were higher than findings by Ly et al. (1999) in

Yellow cattle in Vietnam in general; who found the calving interval of Yellow cattle is about

13-16 months. This difference between the study and the literature could be explained by

limitations in the characteristics and management among the selected systems. Otherwise, the

shortage of feed resources in the dry season and stress of weather extremes in the study sites

also limited reproductive performance. On the study sites, cows commonly calved in the

winter time with little or no care from keepers and almost no feed supplement. Huyen (2004)

also indicates that the low productivity of local breeds might be a result of low inputs in terms

of breeds and fodders.

In H’Mong households, most mature bulls are housed or controlled. Therefore, selection of

bulls for services was often controlled. Additionally, interviewees explained that they also

paid attention to their cows. Cattle in the cut-and-carry system were well managed and

controlled: (i) checking regularly for oestrus; (ii) mating service with selected bulls according

to the preference of owners; and (iii) tending the animals during calving and at fattening time

by most farmers. Actually, these activities are basic skills in the management of cattle

production, but these activities were not frequently practised among free-range and part-time

grazing systems, while cut-and-carry system farmers exhibited better management skills in

comparison with those in the other two systems. Nevertheless, there was also no suitable

breeding management programme introduced in the cut-and-carry system. In fact, the

government implemented a major programme with extensive funding support, but the result is

still poor and not yet adapted to the conditions specific to the areas. In addition, there are

research programmes on cattle kept by H’Mong people by NIAS funded by the government

and Agricultural Research for Development - Cirad Vietnam. Nevertheless, inbreeding was

not often observed in this system. Comparing the other two systems, cattle keepers in

H’Mong households seem to have a more positive reproductive performance than the others.

Thus, the higher performance of cattle in the cut-and-carry system was probably due to

selection of breeding bulls among the best ones in H’Mong villages and better management

by owners at calving time.

Contrarily, controlling of service and limited control of cattle herds was hardly practised in

the free-range and part-time grazing systems, especially when the peak reproductive season

occurred in the winter. Many households interviewed also confirmed that inbreeding was

frequently occurred because owners did not watch their animals closely during grazing time.

Selected farmers in these two systems also did not pay attention at calving times. In the study

area, no real attention was given to improving the breeds among systems. Although the cattle

development project is being implemented in different areas, the results were still limited. In

addition, little or no information on oestrus, mating services, abortion and calving was

recorded in the free-range system. The owners could not evaluate the quality and performance

of the animals in their herds. Overall, the owners exercise little or no management of their

Page 137: BEEF CATTLE SYSTEMS IN THE CONTEXT OF SUSTAINABLE ...bictel-fusagx.ulg.ac.be/ETD-db/collection/... · (2011). Beef cattle systems in the context of sustainable agriculture in Bac

Results and discussions 119

cattle herds, especially reproductive management. Similarly, most households in part-time

grazing have no sustainable strategy for the selection of breeding animals or any

understanding about how to carry out breeding management. In addition, the breeding

programme at the province and district levels was not introduced efficiently. Thus,

perpetuation of the local Yellow cattle population will be confronted with many difficulties.

Correspondingly, uncontrolled breeding animals will still be sold in the local markets by

unwary farmers, especially without certification from local authorities for breeding animals.

Particularly, no standard characteristics of the breed were introduced to the local people. It is

very difficult to apply breeding and management techniques in the free-range system, as the

cattle herds roam frequently from one pasture to another. If no breed improvement

programme is implemented, breeding quality and performance will continue to be poor and it

will probably be difficult to preserve the local Yellow cattle. Thus, inferior breeding animals

are still being sold to other households. Dzuc (2003) points out that there is likewise little

attention paid to renewal of these breeds in the northern uplands.

In H’Mong households, cows with the highest expected reproductive life is accounting for 8.4

calvings per cow on average, with a range between 2 to 10 calvings. The lowest one was in

the part-time grazing system with 6.2 calvings (varying between 2 and 8). Selected

households in the part-time system said that they might replace a cow sooner if it is not

healthy or has a poor reproduction record. This opinion seems to have better awareness on the

reproductive management of cows than that in other systems. There was a statistically

significant interaction of the systems regarding the reproductive life of cows (p=0.000).

Moreover, there were also significant differences between each pairs among the three systems

on this indicator (all p<0.01). In fact, reproductive performance was considered as the sole

criterion to keep a cow a long time or dispose of it after a short time. Nevertheless,

households might have to sell an animal earlier if the family needed cash.

Furthermore, all selected households indicated that calves were suckled until the cow had its

next calf without weaning techniques. Male calves were not castrated, even though of poor

quality for a breeding role. Thus, many low-value bulls were still kept among the systems.

However, the government’s support policies for cattle projects included selection of high

quality bulls and cows and subsidies for the use of high-performance bulls to renew local

cattle breeds. For example, the Bac Kan cattle development programme included a strategy to

have poor quality bulls castrated in order to enhance cattle herd quality. Thus, all low quality

mature bulls were slated for castration, but poor results were recorded. Tra (2007) indicates

that this was challenging in terms of time, financial support, labour, and farmer awareness. A

very low percentage of farmers agreed to the operation because castrated bulls were thought

to weigh less and not develop their typical hump, precluding their use as draught animals.

It is important to note that there is a limitation in the study on mentioning reproductive

capacity in terms of replacement rate of cows and mortality rate in selected households among

the systems in 2007 due to short of time, fund, and a poor data collection for a year and poor

memorizing of farmers, especially cattlemen in free-range. Thus, further study on these

indicators should be implemented in the coming phase to fulfil the research in all aspects.

Page 138: BEEF CATTLE SYSTEMS IN THE CONTEXT OF SUSTAINABLE ...bictel-fusagx.ulg.ac.be/ETD-db/collection/... · (2011). Beef cattle systems in the context of sustainable agriculture in Bac

120 Results and discussions

Table 29: Reproductive performance of cows in the different beef cattle feeding systems

Indicators Free-range

(N = 39)

Part-time grazing

(N = 59)

Cut-and-carry

(N = 49)

Sig.

M Range M Range M Range

Age (year) 8.0 4.0 – 14.0 7.3 5.0 – 16.0 8.1 5.0 – 14.0 0.079

Num. of calvings 3.7a 2.0 – 8.0 3.1

b 2.0 – 9.0 3.9

a 2.0 – 9.0 0.030

Age at first calving

(months) 41.5 36.0 – 60.0 41.2 36.0 – 66.0 40.5 36.0 – 60.0 0.673

Calving interval

(months) 16.6

a 12.0 – 24.0 16.3

a 12.0 – 26.0 14.6

b 12.0 – 24.0 0.007

Expected

reproductive life

(num. of calvings per

cow)

7.4a 4.0 – 10.0 6.2

b 2.0 – 10.0 8.4

c 2.0 – 10.0 0.000

Source: Households interviews, 2008

Calculated for cows giving at least two calves. a, b, c

within a row not sharing the same superscript letter (p<0.05).

If all samples are normally distributed with equal variances, ANOVA is used. If both conditions are not met, the

Kruskal Wallis and Mann-Whitney Tests are used.

Table 30 classifies cow body condition according to the viewpoint of selected households in

the different cattle feeding systems.

Table 30: Classifications of cow body condition in selected household

Classification of body

condition

Free-range

(N = 54)

Part-time grazing

(N = 68)

Cut-and-carry

(N = 60)

Poor and old (%) 25.9 36.8 25.0

Medium (%) 24.1 23.5 26.7

Good (%) 50.0 39.7 48.3

Source: Households interviews, 2008

Calculated for cows from their first calving.

Cows in poor condition and old accounted for rather a high percentage, ranging from 25% in

the cut-and-carry system to around 37% for part-time grazing. Those cows were thin, weak, of

poor reproductive performance (long calving interval, calves died after birth). They explained

why they did not eliminate those poor quality cows: (i) they kept cattle as a tradition in the

families and economic efficiency was not a consideration; (ii) they could not replace the

animals because they could not afford to purchase replacement stock; and (iii) they keep them

until they are very weak and then sell them for slaughter. Thus, a rather high proportion of

cows not in breeding condition were still raised as breeding animals. Cows ranked in medium

condition accounted for around one fourth in all systems (between 23.5 to 26.7%). The largest

percentage of cows was evaluated in good condition, which varied from 39.7 to 59.0%. These

cows were evaluated on the basis of being in good shape, having a strong frame, short calving

Page 139: BEEF CATTLE SYSTEMS IN THE CONTEXT OF SUSTAINABLE ...bictel-fusagx.ulg.ac.be/ETD-db/collection/... · (2011). Beef cattle systems in the context of sustainable agriculture in Bac

Results and discussions 121

intervals, calves rarely died after birth, and their expected reproductive life will be long

(Annexes 9 and 10).

4.2.2.3 Veterinary services and cattle losses

(a) Veterinary services and disease treatment in selected households

Thomas et al. (2002) state that diseases decrease production and increase morbidity and

mortality rates, thus, animal health issues are barriers to trade. Diseases often cause high risk

(death) for cattle in smallholders. In fact, cattle herds in the study areas are vaccinated

biannually against foot-and-mouth disease, bovine pasteurellosis, and anthrax following the

vaccination programme of the Veterinary Department. However, among the selected systems,

the vaccination programme was not completely conducted. The lowest vaccination rate was

found in H’Mong households, which included only 20% of selected households (Table 31).

Firstly, the complicated geography might explain that poor result. Besides, villagers in

H’Mong villages generally agreed to refuse vaccination of their animals due to earlier

experiences with death or emaciation of animals after injection of vaccines. Moreover, no or

inadequate explanation from veterinary staff and lack of information caused hesitancy to

implement the vaccination programme. However, the study results showed that there was no

loss from animal diseases in households that did not have their cattle vaccinated. That might

be a major reason inhibiting their acceptance of vaccination. However, poor cattle disease

prevention and poor awareness among selected households were also recorded in the system

due to assumed ill-effects of vaccine and lack of communication. Huyen (2004) also points

out that the lowest vaccination rate (around 32%) among the systems was in H’Mong

households in the uplands. She also indicates that the veterinarian visits were rarely recorded

in H’Mong villages due to the difficulty to access their areas

A moderate rate of vaccination was indicated in the free-range system (50%), despite the fact

that information about the vaccination programme was provided several days in advance.

Non-vaccination was found in half of the households due to difficulties of finding cattle in the

grazing areas. However, many households hesitated to vaccinate their animals because of

assumed undesired results such as weight loss, sickness, and death. Inappropriate

communication from veterinarians and lack of information could also be reasons for this.

However, the highest vaccination proportion is recorded in the part-time grazing system, with

86.5% participating households. Nevertheless, compared to the free-range and cut-and-carry

systems, farmers in part-time grazing implemented disease control, discovered outbreaks,

treated ill animals in a timely manner, and implemented the vaccination programme regularly,

which helped prevent outbreaks.

A mortality rate from zero to 25% is recorded in cattle in northern Vietnam (Dufhues et al.,

2004). This might be explained due to deficiencies in the veterinary system in Vietnam, but

might be due to deficiencies in the animal health surveillance system (Dufhues et al., 2004).

Anthrax, tuberculosis, FMD, salmonellosis, para-tuberculosis, and rinder pest are some of the

diseases seen on smallholder cattle farms (Dzung, 1996; Nho et al., 2003). In addition, tick

infestation of cattle is very high, hence the prevalence of tick-borne diseases, particularly

where cattle are kept in poor hygienic conditions (Noi et al., 1995b). The high mortality rate

occurs where husbandry conditions are poor and communicable diseases spread easily. Lack

of adequate veterinary services due to limited staff and equipment are key factors hindering

beef cattle production (Dzung, 1996).

It is important to note that although veterinary services are quite available in the communes,

most households in three systems treat their animals by themselves with medicines purchased

Page 140: BEEF CATTLE SYSTEMS IN THE CONTEXT OF SUSTAINABLE ...bictel-fusagx.ulg.ac.be/ETD-db/collection/... · (2011). Beef cattle systems in the context of sustainable agriculture in Bac

122 Results and discussions

in shops both in free-range and part-time grazing, whereas households in cut-and-carry treat

sick animals using traditional medicines. In general, cattle herds are vaccinated biannually

against three diseases. However, less than 50% of total cattle herds are vaccinated (Nho et al.,

2003; Huyen, 2004). Inadequate veterinary equipment, unprofessional and late-delivered

services are core reasons for the low percentage of vaccination. The level of health care

services for animal production drops significantly in remote locations (Huyen, 2004). Dzuc

(2003) finds that the local network of veterinary services is ill-prepared to face epidemics. In

addition, vaccination is a service provided exclusively by government veterinary

organisations (Huyen, 2004).

Table 31: Vaccination and disease treatment in selected systems

Indicators Free-range Part-time grazing Cut-and-carry

Vaccination (% HH) 50.0 86.5 20.0

Disease treatment Self-treatment with

medicines

Self-treatment with

medicines

Self-treatment with

traditional medicines

Source: Households interviews, 2008; Groups discussion; Key person interview

(b) Analysis of economic losses in the cattle feeding systems

Some 20% of selected households in both the cut-and-carry and part-time grazing systems

experienced losses in cattle production, while over twice as many households in the free-

range system had losses (43.3%) (Table 32). The mortality rate in those systems could be less

due to different management strategies of owners in the different production systems (free-

range without care versus grazing with tending by owners and housed). Free-range is a very

traditional husbandry method in mountainous areas, wherein cattle losses are high because of

lack of tending by owners. Undoubtedly, families keeping cattle herds in the free-range

system sustain losses due to accidents, theft, and diseases. Disease outbreaks were rarely

discovered in time or discovered in a very advanced stage. Therefore, no suitable treatment

could be given; further, very few cattle were vaccinated, as mentioned above. Moreover, there

was an inappropriate risk management model in the cut-and-carry system, where the people

reside permanently in the uplands with complicated terrains. However, these loss rates are

rather high compared to other studies. The free-range system sustained greater loss in cattle

production, losing around 0.7 head on average (maximum 5 head) as opposed to 0.3 head loss

in the other systems (maximum loss from 2 to 3 head). Tung et al. (2009) indicate that the

average mortality ratio in the NMR for the selected households during 2007-2008 was only

17.6%, with 1.4 head lost on average. In comparison with the other systems, households in the

free-range system experienced losses of 1.4 mil. VND on average that ranged between 0 and

7.5 mil. VND. Households in part-time grazing and cut-and-carry reported 1.0 mil. VND

(between zero and 14.0 mil. VND) and 0.6 mil. (from 0 to 6.5 mil. VND). Nevertheless, there

is no significant difference among systems in selected indicators (all p>0.05).

Page 141: BEEF CATTLE SYSTEMS IN THE CONTEXT OF SUSTAINABLE ...bictel-fusagx.ulg.ac.be/ETD-db/collection/... · (2011). Beef cattle systems in the context of sustainable agriculture in Bac

Results and discussions 123

Table 32: Losses of cattle (economic efficiency) in beef cattle systems in 2007

Indicators Free-range Part-time grazing Cut-and-carry Sig.

M Range M Range M Range

Loss (% HH) 43.3 - 21.6 - 20.0 - -

Average num. cattle

(head/HH) 0.7 0.0 – 5.0 0.3 0.0 – 2.0 0.3 0.0 – 3.0 0.072

Average cattle lost

value (mil. VND/HH) 1.4 0.0 – 7.5 1.0 0.0 – 14.0 0.6 0.0 – 6.5 0.087

Source: Households interviews, 2008

If all samples are normally distributed with equal variances, ANOVA is used. If both conditions are not met, the

Kruskal Wallis and Mann-Whitney Tests are used.

Box 6: Losses in cattle production in selected households

The household of Mr. Duong Van Phong practising the free-range system in Cong Bang commune lost 5

cattle including 3 calves, one steer and one heifer (calculated to be 5.7 mil. VND) due to accidents

caused by falls over cliffs in the mountains and by FMD.

Mr. Nong Van Nho, a poor householder in Cong Bang commune, raises 3 cattle including a bull

presented from a cattle project in the Pac Nam district. During 2007, his family earned 13.2 mil. VND,

including 7.5 mil. VND from the bull, 3.0 mil. VND from the increased value of the cattle herd. He lost

3 cattle, equivalent to 5.5 mil. VND, which he had borrowed from the Social Bank. However, he sold

cattle to get back 0.6 mil. VND. Remaining returns were derived from manure and draught power.

The household of Mr. Ly Van Diep, a better-off householder practising the part-time grazing system in

Nghien Loan commune lost 2 mature bulls to infectious diseases in 2007. One was Laisind crossbred

evaluated at around 12 mil. VND. In total, the 2 cattle that died were evaluated at around 14.0 mil. VND.

Nevertheless, his family gained back 6.5 mil. VND from selling those cattle to a slaughter house.

Nevertheless, his family obtained negative benefit of 2.8 mil. VND from cattle production.

4.2.2.4 Cattle shelters and hygiene conditions

The condition of cattle shelters in selected households in cattle feeding systems is indicated in

Table 34.

Table 33: Cattle shelters in selected systems

Indicators Free-range Part-time grazing Cut-and-carry

No cattle shelter (% HH) 53.3 5.4 3.3

Temporary shelter (% HH) 16.7 16.2 20.0

Good quality shelter (% HH) 30.0 78.4 76.7

Sanitary condition of cattle shelter Very poor Poor Very poor

Source: Households interviews, 2008

In the free-range system, a considerable percentage of households had no shelter for their

cattle (53.3%). Many households still keep their cattle under their houses on stilts (Annex 13),

which remains the predominant shelter in mountainous areas in former time. Nevertheless,

this way of keeping cattle is being discouraged in these areas recently due to the health risks it

Page 142: BEEF CATTLE SYSTEMS IN THE CONTEXT OF SUSTAINABLE ...bictel-fusagx.ulg.ac.be/ETD-db/collection/... · (2011). Beef cattle systems in the context of sustainable agriculture in Bac

124 Results and discussions

poses for households. This is part of a major government awareness-raising programme. The

proportion of households having no cattle shelter was more or less equal in the part-time

grazing and cut-and-carry systems (5.4% and 3.3%, respectively). The ratio of households

keeping cattle in temporary shelters was equal among the systems, ranging from 16.2% to

20.0%. A significant proportion of households in part-time grazing and cut-and-carry have

good quality shelters for their cattle (over 75%), while under a half of that result was indicated

in free-range (30%). Cattle stables are often made of wood or bamboo and located near the

owner’s house. Sanitary conditions were often poor among systems.

4.2.3 Other issues for the developing smallholder farm cattle production

4.2.3.1 Credit issues in livestock production and cattle development

A high proportion of households in cut-and-carry have taken out loans to develop livestock

production in general and beef cattle production in particular through government projects

(73.3%) with an average of 9.0 mil. VND per household (from 3.2 to 15.0 mil. VND) and

with interest rates ranging from 0.45 to 0.90% per month (Table 35). Almost all H’Mong

households use all or a part of the borrowed money to increase family income by trading

cattle or buying breeding cattle, buffalo and/or other animals, with the exception of one

household that used the loan for house repairs. Up to 63.3% of households in the free-range

system have a loan for their livestock production with an average of 14.3 mil. VND, varying

between 3.0 and 30.0 mil. VND. Of which, 47.4% of borrowers use the loan for other

purposes such as their children’s study, house building, buying a motorbike or paying medical

bills. In the part-time grazing system, 40.5% of households took out a loan for their livestock

production, with an average of 8.9 mil. VND (between 3.0 and 20.0 mil. VND). Of which,

26.6% of them used the loan for other purposes such as their children’s study, house building,

cattle trading, furniture buying and paying debt. Thus, a high rate of households used the loan

for purposes other than for their agricultural production. Similarly, Tai (2005) also found that

loans obtained were used for farm investments, family and household needs, and other social

requirements, especially in high mountainous areas, where farm incomes do not satisfy family

needs. Thus, it was hard to achieve the main purpose of lending for improvement of livestock

production. Therefore, broad dissemination of useful information as well as management of

the loan flow should be emphasized in the study area in order to raise awareness and

efficiency in this issue.

Most credit is medium-term (3 years) for livestock production, especially for cattle and

buffalo husbandry. For pig production, the duration is one year max. Users feel the term of

loans is too short, unsuitable and not timely for investment in cattle and buffalo production.

They would like to have long-term credit. Tai (2005) indicates that a credit source available

for use whenever needed might influence the decisions of farmers in both the short- and long-

term because credit is an important source of capital for households lacking cash to carry out

all the farm and off-farm activities and those of the household as well. The author finds that

the average credit amount taken out by H’Mong people is around 3.5 mil. VND.

Page 143: BEEF CATTLE SYSTEMS IN THE CONTEXT OF SUSTAINABLE ...bictel-fusagx.ulg.ac.be/ETD-db/collection/... · (2011). Beef cattle systems in the context of sustainable agriculture in Bac

Results and discussions 125

Table 34: Loan issues in different beef cattle systems

Indicators Free-range Part-time grazing Cut-and-carry

Took out a loan (% HH) 63.3 40.5 73.3

Loan value (mil. VND/HH) 14.3 8.9 9.0

Purpose of loan (% HH)

- Livestock production (% HH) 52.6 73.4 52.2

(Cattle production) (% HH) (31.6) (66.7) (59.1)

- Cattle trading (% HH) 0.0 13.3 43.5

- Other (% HH) 47.4 13.3 4.3

Source: Households interviews, 2008

4.2.3.2 Role of extension services and other organisations in cattle production

Most development programmes of cattle production in general and crossbreeding cattle in

particular are conducted by the provincial agriculture extension services. Incentives for cattle

production include the planting grasses, training in cattle production methods and feed

processing, and importing crossbred bulls. Nevertheless, not all crossbreeding programmes

have been successful, which is explained by (i) the immature administrative structure of the

new province; (ii) unclear function of extension services and staff, making them less

effective; (iii) incomplete measures among organisations; and (vi) lack of extension staff. It is

important to note that the unspecific role of extension services and their staff might be

explained not only by a lack of human resources, but also by the low qualification of staff,

especially at the commune level. In communes, no specific extension staffs are found because

they often hold more than one duty. Other organisations such as the Women’s Union, farmer

organisations, etc. play a minor role in these programmes. However, some activities are

organised by the Women’s Union, such as providing information and training courses for

women about livestock production. The cooperation among organizations and institutional

was not tightly created in implementing the activities of the development cattle programmes.

4.2.4 Brief description of trading cattle in the study sites

An important opportunity for cattle raising systems on the study sites are the high consumer

demand for beef in general and the well-developed local cattle markets in particular, which

means live cattle produced are easily traded. Thus, two questions are addressed: why cannot

cattle production develop strongly given the available cattle market areas?

Currently, it is estimated that 50% of cattle are sold directly to markets by selected farmers.

Data collected from direct household interviews indicates that of those cattle, 40% are often

traded to retailers, and around 58% are sold to middlemen. According to Nho et al. (2003) and

Van et al. (2005), most cattle from producers are purchased by middlemen and then sold to

other regions. The remaining 2% of cattle from selected households was sold to other farmers

in nearby areas or through the market for breeding. Most farmers purchased cows but not

bulls for breeding. A high percentage of households kept their own female calves for breeding

or purchased from their relatives or neighbours who could vouch for their quality. The

selected households in these systems also indicated that around other 30% of their cattle were

sold directly to collectors/retailers at cattle houses. The price of cattle purchased from cattle

houses or markets depends strongly on the middlemen and retailers. The remaining cattle

Page 144: BEEF CATTLE SYSTEMS IN THE CONTEXT OF SUSTAINABLE ...bictel-fusagx.ulg.ac.be/ETD-db/collection/... · (2011). Beef cattle systems in the context of sustainable agriculture in Bac

126 Results and discussions

(about 20%) are used as breeding stock for their own family, sold to neighbours and relatives

or given as presents to their children and relatives.

Box 7: Mr. Hoang Van Ngo – cattleman in Cong Bang commune

At the end of 2008 he sold two cattle (a cow and her calf) for a total of 4.6 mil. VND. He sold his cattle

on the hoof in free-grazing area in the forest. His house is located around 300m from the Cong Bang

cattle market. However, the cattle market opens every fifth day, whereas the time he needed cash was not

a market day. The price was paid by a retailer, and he thought that it was lower than the commune

market price. However, he still decided to sell, otherwise he would have had to wait another two days

and waste time bringing his cattle to the market. He thought that he might also depend on the estimation

from retailers or middlemen; therefore, he could trade his cattle with the same price as he did.

Mr. Le Van Pham – cattleman in Nghien Loan commune

His family sold five cattle including two cows, two calves, and one young bull in the Nghien Loan

market for a total of 8.84 mil. VND. His cattle were thin and weak, showing low meat quality, but his

family did not supplement feeds to fatten their cattle. They did not think about this strategy and could not

explain why. At the beginning of market day, middlemen and retailers came to ask and bargain for a

slightly lower price than that. By the middle of the market-day, he decided to sell after getting references

from other cattle owners, middlemen and retailers.

All selected Tay households practising the free-range and part-time grazing methods sold

their cattle at the commune markets or at their homes. Conversely, selected H’Mong

households practising the cut-and-carry system often brought their cattle to the various cattle

markets in order to get the best-price. Interestingly, in local markets, most retailers were

H’Mong people, although there were a small number of Tay and Dao sellers. Trading cattle

became an important off-farm activity in H’Mong villages, especially to augment their low

income from agricultural activities due to low land use intensification and poor fertility. They

often purchased one or two head of cattle to sell later in another market. For example, they

would purchase cattle at the Cong Bang and Boc Bo retailer markets to sell at the Nghien

Loan wholesale market. In addition, they also bought cattle from markets in other provinces

(Cao Bang, Ha Giang, and Tuyen Quang) and then sold them at the Nghien Loan market. This

involved long, strenuous journeys on foot through forests and mountains. Some of them might

select animals for fattening for around 2 to 4 months, if they see they have potential.

However, not all cattle can be fattened successfully because of their type, their health,

diseases, and inadequate feed. Moreover, H’Mong retailers never buy cattle fattened by

another H’Mong person, perhaps because they have learned that such cattle have gained their

maximum weight capacity.

All selected households in the study areas seemed to have good access to the market, and the

advantages they also enjoy in easiness of trading, availability of cattle markets, and high

consumer demand for cattle products. Actually, small-scale producers were in a weak

position, lacked negotiating power, and were poorly informed on patterns of supply, demand,

and price. These deficiencies are also recorded in the PPLPI-Policy Brief (2004). Generally,

Tay famers had a poor negotiating capacity not only at home but also in markets, while most

H’Mong households had better capacity to assess an animal’s worth, because many of them

had experience as cattle retailers in different markets as mentioned above. Around 40% of

Tay households said that they had to ask other farmers to ascertain the value of an animal for

Page 145: BEEF CATTLE SYSTEMS IN THE CONTEXT OF SUSTAINABLE ...bictel-fusagx.ulg.ac.be/ETD-db/collection/... · (2011). Beef cattle systems in the context of sustainable agriculture in Bac

Results and discussions 127

trading. A high percentage of farmers relied on the buyer’s estimate of their cattle. In

addition, middlemen and retailers gave a base line for cattle prices during market time. Thus,

most Tay cattle producers were low on market power. Liem et al. (1997) also indicate that

farmers in Nghe An cattle markets often seek help from middlemen and other farmers to

estimate their cattle value. Hence, Lapar et al. (2003) affirm that for the best development of

the sector, a way must be made to have small-scale farmers involved in the development

process.

Box 8: Mr. Vu A Giang, a H’Mong cattle farmer working as a retailer in Cong Bang commune

He has started his job as a cattle and buffalo retailer in 2006. He often purchased one or two cattle or

buffalo because he did not have much capital (his total capital was 7,000,000 VND). It was sourced from

a loan from the district cattle development project. He was formerly able to purchase several cattle per

market day easily and earned a good profit per head of cattle (around 300,000 VND). He purchased

cattle in the Cong Bang market and then sold them at the Nghien Loan market. Sometimes he fattened

cattle at home to increase their value, if possible. His wife works at cutting and carrying feed resources

back home and tends the cattle. Recently, a high number of persons trading cattle resulted in greater

competition. Buying cattle in local markets became harder. He had to go to purchase animals from other

markets in Bao Lac commune, Bao Lam district, Cao Bang province, a neighbouring area. In this

market, more cattle were available. However, profits gradually declined. Many times he could not

purchase any cattle. According to his opinion, visually estimating lean meat performance is difficult and

he has suffered many losses.

Cattle from local farmers accounted for a small proportion in the local markets, while a larger

percentage came from neighbouring provinces and China as indicated in Chapter 2.

Particularly, live cattle in local markets as well as in selected households had to compete with

animals traded illegally across the border, not only from neighbouring countries such China,

but also from countries as far away as Thailand, Laos, and Myanmar, because of price

competition and poor control over cross-border trading. In addition, cattle farmers in the study

sites also have competition from legally imported cattle meat with higher quality and lower

price. The number of local cattle traded in local markets depends strongly on seasons. Disease

outbreaks heavily impacted on trading of cattle. Thus, despite the advantages mentioned

above on the study sites, farmers were still faced with difficulties in fully accessing the

market. Phuong (2008) also finds that the poor farmers find it difficult to get involved in the

local beef market.

No association of farmers or others on study sites had been formed with a focus on trading

cattle help each other sell their product for the optimum price. Therefore, cattlemen had no

concerted power in cattle trading. There were supporting policies from the government for

cattle marketing; however, there was no intervention of the government in trading of cattle,

neither in products quality control nor in enforcement of cross-border regulations and

procedures among neighbouring countries. There was no connection programme established

between farmers and consumers. No national certification system in cattle products (live cattle

or beef) was carried out to create a sustainable linkage among stakeholders and consumers.

Agreements between Vietnam and neighbouring countries were not clearly performed to

control the healthy trading of goods, including cattle products over the borders, and to reduce

illegal trading (Alburo and Panyakul, 2009). On the other hand, retailers and middlemen

working in groups, who have informal but tight trade relations with other groups of

middlemen, retailers, and slaughterhouses, played the key role not only in price determination

Page 146: BEEF CATTLE SYSTEMS IN THE CONTEXT OF SUSTAINABLE ...bictel-fusagx.ulg.ac.be/ETD-db/collection/... · (2011). Beef cattle systems in the context of sustainable agriculture in Bac

128 Results and discussions

but also in the chain. Nonetheless, the greatest threats or inconveniences that middlemen felt

were disease outbreaks and the numerous veterinary and market inspections when

transporting animals from Pac Nam district to other provinces (around 7 such control

stations). Tra (2007) indicates a similar situation regarding the cattle marketing chain in Bac

Kan province. Lapar et al. (2003) assert that there are high transaction costs in marketing

systems and channels in Vietnam due to the many tiers from farms to markets.

It is important to note that the price of and demand for cattle kept and fattened by H’Mong

people did not differ in comparison to cattle produced by the Tay or other ethnic minority

groups in markets who did not specifically fatten their cattle. Yet, cattle raised by H’Mong

people are felt to have a high meat quality compared to other types: good taste, smell, and

texture, and well-marbled compared with others. This might be explained by the short-term

fattening process and slaughter at a reasonable age. Nevertheless, male cattle are often kept all

year round in many H’Mong households, while cattle fattened over a long period might have

a higher fat percentage than usual, which was considered as a loss by slaughterhouses.

Therefore, not all slaughterhouses were interested in purchasing such cattle and often offered

a lower price. Fattening young male cattle in H’Mong households over a period of around

only two to four months should be highly recommended to obtain the highest quality meat.

QNRDP (2002) indicates that a high beef quality in Vietnam is evaluated by lean meat with

no visible fat and little differentiation according to the age and size of animal. Generally, a

quite high percentage of cattle sold by farmers are not at the most favourable stage for meat

production, but rather they are old and no longer capable of providing draught power or

breeding. These types of cattle sold were also found in the study of IFAD Cao Bang (2007).

In fact, most cattle in the selected households were kept for dual purposes, not solely for beef.

Almost H’Mong people fattened cattle for commercial purposes, yet using the animals for

draught power was still prevalent in their households.

Additionally, it was recorded that only small quantities of beef in its various forms sold

directly to supermarkets, although many supermarkets have opened in cities. Thus, cattle

production has developed since the last decades, however, this development has not been

accompanied by critical changes to cattle and beef marketing and distribution systems.

Currently, cattle products were traded in traditional markets. Schipmann (2010) also mentions

that traditional retail structures in developing countries are characterised by spot-market

transactions. Currently, the low development of supermarkets in Vietnam has also partly been

favourable to the survival of smallholders in livestock production (Tisdell, 2010). In addition,

consumers in developing countries still prefer to purchase their food in traditional format

outlets despite of ease of access to supermarkets (Goldman et al., 2002; Maruyama and

Trung, 2006). Tisdell (2010) finds that Vietnamese consumers highly prefer to buy their fresh

meat in informal outlets. Smith and Tra (2008) also describe this consumer meat consumption

behaviour in northern Vietnam. Meijer et al. (2008) also find that agricultural products are

then traded via networks of informal traders from areas of farmer production to regional and

national wholesale and retail markets. On the other hand, the strong development of

supermarkets in the big cities as well as provincial cities is observed obviously, which will

bring both opportunities and challenges to farmers.

4.2.5 Section summary

The most important purpose of keeping cattle in the selected households in all three systems

was for breeding. In the free-range and part-time grazing systems, cattle production was also

highly important for savings and producing manure for crop growing. However, loss of the

manure resource from cattle production in all systems will be discussed more detail in the

Page 147: BEEF CATTLE SYSTEMS IN THE CONTEXT OF SUSTAINABLE ...bictel-fusagx.ulg.ac.be/ETD-db/collection/... · (2011). Beef cattle systems in the context of sustainable agriculture in Bac

Results and discussions 129

next section. In the cut-and-carry system, ranking next in the aforementioned important roles,

cattle were used for draught power and savings. It is important to note that using cattle as a

token of social status of cattle has been greatly reduced in all systems due to their increasing

economic value. Not only in H’Mong households but also in Tay families, people no longer

slaughter cattle for festivals or use them as wedding gifts, but have replaced them with

offerings of lower value.

The average cattle herd sizes and scale of production among the systems is essentially similar.

Cattle production was mostly small and medium scale. Actually, the average number of cattle

per household indicated in the survey results in the free-range system is much lower than

expected, which might partially explained by obviously increasing reforestation, reduction of

pasturelands, and population growth.

In the cut-and-carry system, shortage of feed was more serious. Planted grass has a short

harvesting season, and it is gruelling to collect natural grass and tree leaves during the dry

season. In this system, no storage of rice straw for winter was recorded due to the very

extended grazing time. Contrarily, in free-range and part-time grazing, both storage of rice

straw and taking advantage of crop by-products were practised more consistently. Although it

has a longer harvesting season for grass and tree leaves compared to that in the cut-and-carry

system, and includes storage of rice straw, there was still a feed resource deficit during the

winter in these systems. A start to growing grass was seen in all systems, but still in small

areas and poor performance. Nevertheless, pastureland for cattle grazing is becoming more

limited due to forest allocation, forest production, and land allocation. In addition, there is no

policy to develop pastureland for ruminant production at the commune, district, and even

provincial levels. It is important to note that increasingly scarce natural grazing areas are

gradually forcing a change from free-range production to part-time grazing, and to cut-and-

carry or combination of all systems. Thus, cattle herds are smaller due to the hard work of

tending animals and of cutting grass for them. With so much time required to collect feed

resources, farmers can only afford to keep a few head of cattle. The economic efficiency of

households growing grass was not significantly different from those without grass production,

which might be interpreted by small allocated land areas, irregular harvesting, poor

performance, and poor awareness of farmers in evaluation value of the planted grass. Overall,

the development of grass production is difficult due to limited arable land resources as well as

overall food security considerations.

Cattle kept for breeding in the cut-and-carry system had a better reproductive performance

than those in the other two systems, indicated by their shorter calving interval. However, they

might have a longer breeding life compared to cattle in free-range and part-time grazing. Poor

control over grazing cattle and poor management might be reasons for the poor reproductive

performance of cows in both the free-range and part-time grazing systems. A large proportion

of farmers in all systems did not give much attention to breeding quality, as indicated by the

high percentage of cows kept for breeding despite their poor condition.

In all systems, vaccination ratios are low, which might partially contribute to a high loss in the

economic value of cattle. However, farmers practising part-time grazing and cut-and-carry

sustained relatively little damage to their cattle production, whereas the free-range system

experienced rather high economic losses due to lack of care. Few households in the free-range

system paid attention to sheltering their cattle. Contrarily, a large ratio of households in part-

time grazing and cut-and-carry constructed reliable shelters for their cattle.

Good access to credit was recorded in a rather high proportion of selected households among

the systems. Nevertheless, much of the credit was not used for the right purpose. It is

imperative to explain to farmers the proper use and management of loans in order to increase

Page 148: BEEF CATTLE SYSTEMS IN THE CONTEXT OF SUSTAINABLE ...bictel-fusagx.ulg.ac.be/ETD-db/collection/... · (2011). Beef cattle systems in the context of sustainable agriculture in Bac

130 Results and discussions

the efficiency of the capital source. Cattle producer organisations are sadly lacking. Bringing

such into the cattle production development process would certainly play an important role.

Cattle farmers in all the cattle feeding systems seemed to face more disadvantages than

strengths and opportunities when they traded and joined in the cattle marketing chain. They

could not sell their animals directly to slaughterhouses but had to go through several

stakeholders; therefore, their position was crippled due to poor capacity in bargaining and

estimating the lean meat yield of cattle. They face strong competition not only from legally

imported live cattle and meat but also from animals illegally brought in from neighbouring

countries such as China, Thailand, and Laos, etc. In addition, cattle disease outbreaks also

hindered cattle trading, even eliminating it for several years on the study sites. Thus, in the

process of changing to modern retail trading in the near future, farmers keeping cattle in the

study areas might confront with many challenges.

In sum, H’Mong people have a lower education level, but they have a better cattle

management such as cattle feeding methods, fattening techniques and grass production

practice, breed selection and replacement. Thus, their culture and local knowledge play their

role in cattle production next to other factors. Due to limited pasture land areas and high

requirement of consumers on uniform and high quality products, the cut and carry systems

will be the main cattle feeding systems in the future. Thus, the challenge for the future will be

a high competitiveness between cattle production and natural resources. In addition, beef

cattle production still has a room in the domestic market due to the high demand of consumers

and tendency of increasing domestic income as the driven forces.

4.3 COMPARISON AMONG BEEF CATTLE PRODUCTION SYSTEMS ON THE DIMENSION OF AGRICULTURAL SUSTAINABILITY

4.3.1 Analysis of the economic efficiency of cattle production in cattle feeding systems

4.3.1.1 Analysis of production costs

In the context of this study, total costs were calculated including variable costs and fixed

costs. Variable costs included breeding costs, feed resources, veterinary services, and hired

labour if required, while fixed costs included depreciation of cattle shelters, annual

maintenance expenses, and interest on loans for cattle production.

(a) Feeding costs in the systems

Generally, feeding costs of cattle production was a relatively small cost in all systems due to

the fact that the households grazed their animals on natural pastures to a large extent (Table

36). The average total feeding expense was around 0.2 mil. VND higher in the part-time

grazing system compared to the cut-and-carry system (0.52 versus 0.33 mil. VND), but there

was no significant difference among the systems (p=0.707). Similarly, Huyen (2009) also

found that households living in lowlands of the NMR spend a small amount on feed resources

(around 0.3 mil. VND, on average). There was no significant difference among the systems in

terms of expenses for cultivated grass, by-products from crop production (rice straw and

maize leaves, young maize plants), and feeding costs per TLU (all p>0.05). Exceptionally,

selected households in the cut-and-carry system invested more in grains such as maize and

rice in fattening their cattle; however, a low value was recorded (0.18 mil. VND, on average

and ranging between 0 and 1.2 mil. VND), which present a significant difference among the

Page 149: BEEF CATTLE SYSTEMS IN THE CONTEXT OF SUSTAINABLE ...bictel-fusagx.ulg.ac.be/ETD-db/collection/... · (2011). Beef cattle systems in the context of sustainable agriculture in Bac

Results and discussions 131

systems and between the other systems (all p<0.005). Several households in cut-and-carry did

not use any grain fed to cattle, they just cut natural and planted grass or natural fodder tree

leaves to fatten their cattle. Thus, compared to other types of livestock production, cattle

production has significantly lower costs, especially for grains, which could be considered as

an advantage in this sub-sector, especially in uplands where food security is still an important

issue. On the other hand, the investment in feed resources in cut-and-carry such as maize is

really needed to fatten cattle in a short time with higher efficiency and reduction of labour.

Hence, farmers in this system were faced not only with a heavy capital investment but also

food insecurity.

Table 35: Feeding costs of cattle production in cattle feeding systems

(mil. VND/household)

Indicators Free-range Part-time grazing Cut-and-carry Sig

M Range M Range M Range

Planted grass 0.38 0.0 – 1.51 0.36 0.0 – 2.16 0.11 0.0 – 0.96 0.268

Crop by-products 0.04 0.0 – 0.19 0.08 0.0 – 0.39 0.06 0.0 – 1.19 0.099

Farm produced grains 0.03a 0.0 – 0.35 0.08

b 0.0 – 0.24 0.18

c 0.0 – 1.20 0.003

Total feeding costs 0.46 0.0 – 1.69 0.52 0.0 – 2.43 0.33 0.01 – 1.35 0.707

Total feed cost per TLU 0.18 0.0 – 0.85 0.21 0.0 – 1.35 0.13 0.01 – 0.06 0.363

Source: Households interviews, 2008 a, b, c

within a row not sharing the same superscript letter (p<0.05).

If all samples are normally distributed with equal variances, ANOVA is used. If both conditions are not met, the

Kruskal Wallis and Mann-Whitney Tests are used.

(b) Total costs of production

Table 37 compares the different costs borne by households in cattle production in the three

selected systems, namely free-range, part-time grazing, and cut-and-carry.

In total, the average variable costs invested for cattle production among the systems were

quite low, 1.9 mil. VND, 1.7 mil. VND and 2.3 mil. VND, respectively that showed no

statistically significant difference among them (p=0.975). Tung and Giang (2008) found in the

northwest region, small- and medium-scale cattle raising households invested 2.5 and 3.8 mil.

VND for variable costs, respectively, while in the northeast the figure was 2.9 and 5.3 mil.

VND. On the other hand, Huyen (2009) state that in Son La province, the total variable costs

of cattle production in lowlands is higher than that in uplands (1.2 versus 0.11 mil. VND on

average, respectively). The variations of total variable costs among the investigated

households in each system were dramatically high, which might be explained by expenses

entailed by the purchase of breeding cattle in some families. Usually, selected households

kept breeding animals from the last calving of their cattle herd or animals offered to them by

close relatives. Meanwhile, expenses for feed, hired labour, vaccinations, veterinary services,

and medicine accounted for a small amount in all systems, and no significant difference

appeared among the systems (p>0.05), with exception of veterinary services of 0.02, 0.06, and

0.01 mil. VND in free-range, part-time grazing and cut-and-carry, respectively (p<0.005). As

mentioned above, the main vaccination programme was almost totally subsidised by the

government in order to prevent outbreaks in sensitive zones, especially in mountainous areas

characterised by challenging geography. Diseases were often treated by owners based on

recommendations from shops or even the general store. Hired labour is rarely recorded,

Page 150: BEEF CATTLE SYSTEMS IN THE CONTEXT OF SUSTAINABLE ...bictel-fusagx.ulg.ac.be/ETD-db/collection/... · (2011). Beef cattle systems in the context of sustainable agriculture in Bac

132 Results and discussions

except for three cases in free-range and part-time grazing, where households had the

economic wherewithal but lacked labour; payment was made in kind in the form of calves

born alive.

Total fixed costs ranged from 0.11 mil. VND to 0.26 mil. VND on average in the part-time

grazing and cut-and-carry systems, respectively. Tung and Giang (2008) found that small-

scale producers invest around 0.3 mil. VND per year on cattle, whereas the figure reaches 0.7

mil. VND in medium-scale production in the northwest. On the other hand, the authors

indicate 0.5 and 0.8 mil. VND for those production scales in the northeast. It showed no

significant difference among three systems with p=0.305 for total fixed expenses, although

there were statistically significant differences among the systems for interest payments

(p=0.014). In addition, statistically significant differences were recorded between cut-and-

carry and free-range (p=0.025) and between cut-and-carry and part-time grazing (p=0.011) on

interest payments.

The highest total cattle costs were 2.6 mil. VND per household on average recorded in the

cut-and-carry system in the uplands, while the lowest one was in the part-time grazing

systems (1.9 mil. VND on average) in the lowlands. However, the total cattle costs among the

systems did not differ significantly (p=0.553). Contrarily, Huyen (2010) finds that the total

costs invested by each household keeping cattle in the lowlands come to 1.2 mil. VND, while

households living in the uplands invested 0.1 mil. VND on cattle production in Son La

province. Hung and Binh (2004) show that with an average of 3.4 head of cattle per

household, farmers have to invest around 10.0 mil. VND (including breeding costs for all

cattle herds).

The cut-and-carry system was the highest spender in terms of average cash costs, with around

2.3 mil. VND per household (between zero and 10.0 mil. VND). Left far behind was the free-

range system, which spent just under 1.5 mil. VND per household, on average (0.0-20.2 mil.

VND). The smallest spender was part-time grazing, with merely 1.3 mil. VND on average for

the cash costs of cattle production (zero to 9.1 mil. VND). Nevertheless, there was no

significant difference among systems on cash cost, with p>0.05.

Thus, it can be concluded that cattle production among the systems demanded generally low

inputs, which may allow poor farmers to improve their livelihoods through investing in cattle

production. Phung (2001) also indicates that low-input cattle production, with the advantage

of available natural pasture in the mountainous areas, might create favourable conditions for

an increase in the number of cattle, resulting in an increase in farm income.

Page 151: BEEF CATTLE SYSTEMS IN THE CONTEXT OF SUSTAINABLE ...bictel-fusagx.ulg.ac.be/ETD-db/collection/... · (2011). Beef cattle systems in the context of sustainable agriculture in Bac

Results and discussions 133

Table 36: Analysis of total costs of cattle feeding systems (mil. VND/household)

Indicators Free-range Part-time grazing Cut-and-carry Sig.

M Range M Range M Range

Cattle purchases 1.4 0.0 – 20.0 1.1 0.0 – 9.1 2.0 0.0 – 10.0 0.201

Feed resources 0.5 0.0 – 1.7 0.5 0.0 – 2.4 0.3 0.01 – 1.4 0.707

Hired labour 0.11 0.0 – 1.50 0.03 0.0 – 1.0 0 - 0.129

Veterinary services 0.02a 0.0 – 0.22 0.06

b 0.0 – 0.7 0.01

c 0-0.03 0.000

Total variable costs 1.9 0.1 – 21.5 1.7 0.0 – 10.5 2.3 0.1 – 10.5 0.975

Depreciation of

shelters 0.05

a 0.0 – 0.4 0.04

a 0.0 – 0.50 0.02

b 0.0 – 0.05 0.043

Interest payments 0.11a 0.0 – 1.44 0.07

a 0.0 – 0.5 0.25

b 0.0. – 1.1 0.014

Total fixed costs 0.16 0.0 – 1.4 0.11 0.0 – 0.5 0.26 0.0 – 1.1 0.305

Total cattle costs 2.1 0.05 – 21.7 1.9 0.04 – 10.5 2.6 0.14 – 10.6 0.553

Total cash costs 1.5 0.0 – 20.2 1.3 0.0 – 9.1 2.3 0.0 – 10.0 0.532

Source: Households interviews, 2008 a, b, c

within a row not sharing the same superscript letter (p<0.05).

If all samples are normally distributed with equal variances, ANOVA is used. If both conditions are not met, the

Kruskal Wallis and Mann-Whitney Tests are used.

Pearson’s correlations among normal/scale variables of the study were computed to find

associations between total cattle costs and other variables. Table 38 shows 10 pairs of

variables that were significantly correlated. The strongest positive correlation, which could be

considered a large size effect according to Cohen (1988) cited in Morgan et al. (2004), was

between gross cattle costs and total cattle return, R (97) = 0.731, p<0.01. This result would

mean that the more households invested in costs for cattle production, the better gross returns

they tended to have from cattle keeping. The R squared indicates that approximately 50% of

the variance in total cattle returns can be predicted from gross cattle costs.

Other strong correlations recorded as medium to large size effect size were found between

total cattle expenses and two variables (grass land areas and cattle feed costs), R (97) = 0.38

and 0.40, p<0.01. Indeed, households keeping cattle that had a relatively large land area

allocated for grass production were likely to have higher expenses in their cattle production

and vice versa. Thus, the R squared indicates that around 10% of the variance in grass land

area allocated for cattle production can be predicted from gross cattle expenses. Moreover, the

higher the feed costs invested, the higher were total costs of cattle production among selected

households in the study.

Page 152: BEEF CATTLE SYSTEMS IN THE CONTEXT OF SUSTAINABLE ...bictel-fusagx.ulg.ac.be/ETD-db/collection/... · (2011). Beef cattle systems in the context of sustainable agriculture in Bac

134 Results and discussions

Table 37: Correlations between total cattle production costs and selected variables

(N = 97)

Variables P Variables P

Gross crop returns 0.277**

Household age 0.244*

Grass land area 0.380**

Cattle feed costs 0.399**

Agricultural land area 0.293**

Cattle production scale (num. of cattle) 0.278**

Total land area 0.221* Total cattle returns 0.731

**

Total off-farm income 0.232* Pig numbers 0.247

*

Source: Households interviews, 2008

Note: *p<0.05; **p<0.01

4.3.1.2 Analysis of cattle gross return

As in any form of livestock production, the total gross return from beef cattle production was

calculated by subtracting purchases of cattle, value of cattle stock obtained as payment in-

kind and gifts, and value of cattle stock at the beginning of the accounting period from total

income from sale of stock, value of stock used for domestic consumption, value of stock at

the end of the accounting period, and value of cattle products produced (adapted from Tung

and Giang, 2008; Tung et al. 2007 and Dillon and Hadarker, 1993).

Table 39 presents an analysis of gross returns from cattle production in the three systems.

Main returns from cattle production are from selling cattle, animals slaughtered or presented

as gifts to relatives of the household, calves born alive and increasing value of cattle herd after

one year, while by-products include draught power, manure, and off-take from cattle that died

or were eliminated and sold for cash. All the selected households keep breeding cows, which

provide benefits through the calves they bear and the increased value of cattle. Cut-and-carry

showed the highest gross returns from cattle production, which reached 10.4 mil. VND on

average, varying between 3.6 and 25.6 mil. VND. Lagging far behind was the free-range

system, which received had an average of 7.4 mil. VND (fluctuating between 2.4 to 32.0 mil.

VND). The lowest one was recorded in part-time grazing that accounted for around 6.6 mil.

VND on average, ranging from 0.6 mil. VND to 20.2 mil. VND. A statistically significant

difference was found among the systems on cattle gross return with p=0.006. Likewise, there

were also significant mean differences on cattle gross return between cut-and-carry and the

other two systems, free-range (p=0.006) and part-time grazing (p=0.005).

Revenue from selling cattle accounted for a considerable value in all main products as well as

the total gross return from cattle production. The highest one obtained was 5.1 mil. on average

in the cut-and-carry system, with a maximum value of 13.5 mil. VND. The average value

received from selling cattle was smallest in part-time grazing, with 3.7 mil. VND. The

medium amount is 4.0 mil. VND achieved in the free-range system, the highest amount being

21.0 mil. VND. Meanwhile, the value of cattle given as presents or slaughtered for household

and calves born alive was negligible among the systems. On the other hand, the increased

value of the cattle herd after one year is dramatic in cut-and-carry with 3.8 mil. VND on

average, whereas it is only 0.8 mil. VND in part-time grazing. Significant ranges among

households in the systems on increasing value were analysed, which resulted from selling or

losing cattle. Besides, by-products from cattle production played only a minor role in total

returns; however, significant differences among the systems were recorded in indicators

(p<0.05). It is important to note that draught power was employed highly in the cut-and-carry

system, where hills and uplands are more easily ploughed using cattle as draught animals

Page 153: BEEF CATTLE SYSTEMS IN THE CONTEXT OF SUSTAINABLE ...bictel-fusagx.ulg.ac.be/ETD-db/collection/... · (2011). Beef cattle systems in the context of sustainable agriculture in Bac

Results and discussions 135

rather than buffalo. On the other hand, in the free-range system, most households took

advantage of buffalo power due to the animal’s apparent greater strength.

Table 38: Gross return analysis of cattle feeding systems

Indicators Free-range Part-time grazing Cut-and-carry Sig.

M Range M Range M Range

Main products/values

Selling 4.0 0.0 – 21.0 3.7 0.0 – 15.0 5.1 0.0 – 13.5 0.243

Slaughtered, present 0.7 0.0 – 7.5 0.5 0.0 – 7.4 0.1 0.0 – 1.0 0.485

Calves born 0.7 0.0 – 3.0 0.6 0.0 – 1.5 0.6 0.0 – 2.0 0.899

Increased value 1.3a -15.0 – 9.5 0.8

a -9.2 – 10.4 3.8

b -10.5–13.8 0.013

By-products

Draught power 0.2a 0.0 – 4.48 0.5

b 0.0 – 2.4 0.7

c 0.0 – 2.4 0.000

Manure 0.13a 0.0 – 1.0 0.20

a 0.0 – 0.6 0.14

b 0.0 – 0.5 0.002

Other* 0.3a 0.0 – 3.0 0.4

a 0.0 – 6.9 0.0

b - 0.026

Total cattle return 7.4a 2.4 – 32.0 6.6

a -0.6 – 20.2 10.4

b 3.6 – 25.6 0.006

Source: Households interviews, 2008

*Value from sale of dead/eliminated animals a, b, c

within a row not sharing the same superscript letter (p<0.05).

If all samples are normally distributed with equal variances, ANOVA is used. If both conditions are not met, the

Kruskal Wallis and Mann-Whitney Tests are used.

4.3.1.3 Net cattle income among the three systems

The average profit from cattle production activities appears in Figure 41. Among the selected

systems, the highest mean net income of households was recorded in the cut-and-carry

system, with 7.8 mil. VND. In the free-range and part-time grazing systems, gains amounted

to 5.3 and 4.8 mil. VND on average, respectively. Quan (2001) records that cattle keeping

households in the mountainous area of Quang Binh earn 0.5 mil. VND from cattle production

each year. On the other hand, Tung et al. (2007) found that keeping cattle in the NMR

resulted in annual profits of 1.3 to 2.7 mil. VND per household per year.

There was a statistically significant difference among the systems (p=0.003). Post hoc Tukey

HSD Tests indicate that statistically significant differences were found between the free-range

and cut-and-carry systems (p=0.023). Likewise, part-time grazing and cut-and-carry differed

significantly in their cattle net income (p=0.003). Thus, compared to other systems, fattening

cattle over a short period of two to four months resulted in the highest profit, giving a high

income to households practising this system.

Page 154: BEEF CATTLE SYSTEMS IN THE CONTEXT OF SUSTAINABLE ...bictel-fusagx.ulg.ac.be/ETD-db/collection/... · (2011). Beef cattle systems in the context of sustainable agriculture in Bac

136 Results and discussions

Figure 41: Average cattle net income in selected beef cattle feeding systems in 2007 Source: Households interviews, 2008

Table 40 shows that there are four significant correlations among scale/normal variables in the

study (between net cattle income and cattle herd size, cow number, cattle losses, and gross

cattle returns). The strongest positive correlation was between net cattle income and gross

cattle return, R (97) = 0.80, p<0.01. Thus, the correlation direction is positive, which means

that households who earned high gross cattle income tended to have high net cattle income

and vice versa. Using guidelines from Cohen (1988) quoted in Leech et al. (2005), the size

effect is significant. The R squared indicates that approximately 60% of the variance in net

cattle income could be estimated from gross cattle income.

he strong and positive correlation, which could be considered a medium to large size effect,

was between net cattle income and cattle number keeping in households, R (97) = 0.46,

p<0.01. This means that households who had large cattle herd size were likely to have high

profitability from cattle production. Thus, R squared shows that approximately 21% of the net

cattle income variance might be expected from cattle production scale. Similarly, the number

of cattle kept by households as well as the value of cattle lost in selected households during a

year also has a positive effect on net income from cattle but with small to medium size effect.

On the other hand, grass land areas, family labour, and reproductive capacity of cows shown

by intervals between calving presented no correlation.

Table 39: Correlations between net cattle income and related variables (N=97)

Variables P Variables P

Cattle production scale (num. of cattle) 0.456**

Gross cattle returns 0.794**

Number of cattle 0.244* Cattle losses 0.246

*

Source: Households interviews, 2008

Note: *p<0.05; **p<0.01

4.3.1.4 Fattening cattle in the cut-and-carry system

Under the description of the cut-and-carry system in the last chapters and sections, several

characteristics of fattening bulls have been reported, but more detailed information is

5.3 4.8

7.8

0

2

4

6

8

10

Free-range Part-time grazing Cut-and-carry

Net

catt

le i

nco

me

(Mil

. V

ND

)

Page 155: BEEF CATTLE SYSTEMS IN THE CONTEXT OF SUSTAINABLE ...bictel-fusagx.ulg.ac.be/ETD-db/collection/... · (2011). Beef cattle systems in the context of sustainable agriculture in Bac

Results and discussions 137

provided below. All bulls were housed in stables and provided feed, including natural grasses,

tree leaves, and/or planted grasses, with a supplement of maize mash or mixed hog feeds, for

various lengths of time depending on each household. Generally, to feed a bull, farmers in

H’Mong households have to spend at least two or three hours per day to collect natural grass

and leaves from forest trees. Thus, planted grass reduces the hard work of cutting natural feed

resources, especially in bad weather. The optimum fattening time was between three and four

months. The longer the fattening period, the more fat in muscle was attained.

According to interviews of households practising the cut-and-carry system, each household

earned around 1.6 mil. VND on average per head of cattle after fattening compared to its

value before fattening (ranging between 0.4 and 3.5 mil. VND). Feed resources invested in

fattening cattle were simple, low-cost family-produced feeds, except for the hard work to cut

and carry natural feed resources, especially in winter time. Therefore, very few households

fattened cattle in this season. Selected households in cut-and-carry often fatten one or two

cattle per time due to the hard work of collecting feed resources. Smith (2001) found that

cattle fattening is undertaken in many specialized and unspecialized households in China, but

with less than five head of cattle.

However, cattle raised in the cut-and-carry system exhibit a good appearance due to the care

they receive and the fattening process, which increases the value of the animals and makes

them easy to trade. Thus, farmers had a chance to convert low-value products (grass, crop by-

products, and residues) to high-value cattle products. Fattened cattle tended to be rather

uniform and of quite good quality, which might advantageously be meet the changing demand

of domestic consumers for high-value agricultural goods. Haantuba and de Graaf (2008) argue

that smallholder farmers must be co-operate in establishing grades and quality standards for

their products as a necessary condition for successful trade linkages between smallholder

farmers and supermarkets. Thus, increasing the income from small-scale cattle production in

selected households though proper fattening techniques might be a major strategy to help

farmers enjoy a sustainable livelihood.

Box 9: Mr. Thao Van Dinh – 62 years old - Khau Nen village, Nghien Loan commune

His family fattened a bull for three months and earned 3.0 mil. VND. Their feed resources were only

natural grasses and fodder tree leaves, which were cut and carried by his wife and daughters. They

needed to spend around 2.5 hours to cut the feed and bring it back home. In their opinion, the cut-and-

carry feeding method requires the hardest work among cattle production activities. They did not grow

grass because of lack of land resources and labour. Nevertheless, they intend to plant around 500m2 of

grass next year in order to reduce the hard work and time spent collecting feed resources. They will try

to take advantage of surrounding land areas. Sometimes, competition arose among family members in

feed collection.

4.3.1.5 Analysis of selected economic indicators in cattle feeding systems

It is important to note that since cattle husbandry is a key factor in their livelihoods, farmers

would be interested in sustainably developing it, especially in areas where cattle husbandry

accounts for a substantial proportion of their income. Phillips and Sorensen (1993) argue that

cattle production systems must fulfil the requirements of the households for cost effectiveness

to be sustainable in short-term. Minot et al. (2003) found that in remote area and uplands,

cattle production is one of the top priorities in diversification of household incomes. Quan

(2001) also found that income from cattle production in total income from livestock accounts

Page 156: BEEF CATTLE SYSTEMS IN THE CONTEXT OF SUSTAINABLE ...bictel-fusagx.ulg.ac.be/ETD-db/collection/... · (2011). Beef cattle systems in the context of sustainable agriculture in Bac

138 Results and discussions

for the highest proportion of income in poor households in comparison to other household

wealth rankings, although a major lack of capital limits economic activities in this household

group. Thus, assessing the profitability of beef cattle production is an important indicator.

Table 41 shows results of the selected indicators in assessing economic efficiency among the

beef cattle feeding systems. There were dramatic differences among systems on Total Factor

Productivity (TFP) of cattle production. From 17.2 on average in part-time grazing, it rose to

42.8 in cut-and-carry and peaked at 57.3 in free-range. Nevertheless, TFP of cattle production

in the selected systems showed no significant difference (p>0.05). Thus, the free-range

system seemed to bring the most economically efficient combination of all inputs to produce a

unit of outputs of cattle production, while cut-and-carry had a rather high efficiency rating for

that combination.

Cattle production created rather good profit as indicated by the gross margin in the cut-and-

carry system compared to the other systems, 8.1 mil. VND compared to 5.4 mil. VND in free-

range and 4.9 mil. VND in part-time grazing on average, respectively. Thus, it can be said that

fattening cattle in this system seemed positive from the standpoint of efficiency for selected

households when the average head of cattle was virtually common to all the systems. There

was a significant difference among systems on gross cattle margin (p=0.002). In addition,

there were statistically significant differences between cut-and-carry and free-range (p=0.019)

and with part-time grazing (p=0.002). On the other hand, Tung et al. (2009) found that in the

grazing system with supplemental feed resources in the NMR, each household obtains only

1.27 million gross cattle margin per household on average, while the average one is 5.47 mil.

VND for the whole country. Tung et al. (2009) found that in the NMR (Ha Giang, Lao Cai

and Lang Son provinces), in the grazing system with supplemental feed resources, the average

gross margin gained per household per year is around 1.27 mil. VND, much lower than the

study finding. Nevertheless, the average data for the whole country is 5.47 mil. VND, slightly

higher than the result found in the part-time grazing system in this study. These authors also

discuss that in grazing without supplemental feed, each household keeping cattle obtains a

gross margin of 5.71 mil. VND, approximately equal to data collected on the free-range

system in the study. In Vietnam’s central coast region, the authors found that free-range beef

cattle earn the lowest profit per household on average (only 0.3 mil. VND per year), while

part-time grazing and stable feeding yield 0.5 and 0.8 mil. VND per year, respectively.

Besides, beef cattle production displayed significant differences on cattle gross margin (GM)

per TLU (Tropical Livestock Unit) among the three systems with p=0.019. There was also a

difference of 0.4 mil. VND per TLU between free-range and part-time grazing on cattle GM

per TLU (2.1 versus 2.4 mil. VND), but of little significance (p=0.066). The cut-and-carry

system presented the highest cattle GM per TLU with 2.6 mil. VND and indicated a

significant difference from that in the free-range system (p=0.005), but not significant from

part-time grazing (p=0.325). A significant difference among three systems on cattle GM per

TLU was indicated (p=0.011).

On the other hand, the free-range system obtained 15.5 mil. VND on average, the highest

household net cash income among the systems. The lowest one was cut-and-carry, bringing

only 5.4 mil. VND. There was a significant difference among the systems on household net

cash income (p=0.026). Interestingly, the highest and lowest household net cash income

groups (free-range and cut-and-carry) did not differ significantly (p=0.058), while part-time

grazing and cut-and-carry showed a significant difference with p=0.006. Household net cash

income partially indicates the farm family’s well-being. It is important to note that a very low

level of household net cash income can be seen as an indicator of poverty (Dillon and

Hardaker, 1993). Actually, in cut-and-carry, the poverty rate is very high, which can be seen

in most households, as well as food insecurity being a serious issue among selected

Page 157: BEEF CATTLE SYSTEMS IN THE CONTEXT OF SUSTAINABLE ...bictel-fusagx.ulg.ac.be/ETD-db/collection/... · (2011). Beef cattle systems in the context of sustainable agriculture in Bac

Results and discussions 139

households. Although cut-and-carry had very good level of economic efficiency in cattle

production, net cash income from it among households was still very low due to poor

participation in off-farm activities, poor soil fertility resulting in low yields, and low

efficiency in other livestock production compared to other systems. In addition, due to the

complicated topography and difficult access to roads, forestry development was undertaken

but it was difficult to sell products to get cash.

Overall, cattle production in the cut-and-carry system tended to show better economic

efficiency in comparison to the other systems, especially in terms of profitability in

households and in TLUs. This could be explained why they strongly engage in cattle

production by: (i) lack of opportunity to participate in off-farm activities among H’Mong

households; (ii) their poor agricultural performance as compared to households in the other

systems; (ii) poor soil fertility and low management skills; (iv) their intrinsic character and

geographical location; and (v) the method they use to fatten cattle (local knowledge).

The cut-and-carry system seems to have the most positive economic influence, with the

exception of poor household net cash income, while the other systems had poorer results in

terms of economic efficiency but better net cash income. However, it could be said that all

systems have positive influence on economic dimension. Quan (2001) also found that

different production systems in Central Vietnam resulted in different levels of economic

efficiency, free-range beef cattle earning the least profit, while part-time grazing was

intermediate and stable feeding yielded the highest profit from cattle production.

Table 40: Analysis of economic efficiency in different cattle feeding systems

Indicators Free-range Part-time grazing Cut-and-carry Sig

M Range M Range M Range

TFP cattle (time) 57.3 1.0 – 910.8 17.2 -0.2 – 95.0 42.8 1.4 – 398.6 0.884

Gross cattle

margin (mil./HH) 5.4

a 0.1 – 17.4 4.9

a -2.8 – 10.4 8.1

b 1.8 – 18.5 0.002

Cattle GM per

TLU (mil. VND) 2.0

a 0.04 – 6.8 2.4

ab -0.7 – 6.7 2.5

b 1.4 – 4.1 0.019

Household net

cash income (mil.

VND/HH)

15.5ab

-8.2 – 121.9 15.2a -1.8 – 148.2 5.4

b -5.2 – 19.9 0.026

Source: Households interviews, 2008 a, b

within a row not sharing the same superscript letter (p<0.05).

If all samples are normally distributed with equal variances, ANOVA is used. If both conditions are not met, the

Kruskal Wallis and Mann-Whitney Tests are used.

4.3.2 Analysis of the social solidarity of cattle production in cattle feeding systems

4.3.2.1 Analysis of labour used in cattle production activities among the systems

Among activities of cattle production, grazing occupied the largest share of working time

spent in this subsector in all selected systems (Table 42). The time spent differed significantly

among and between the systems (all p=0.000). Free grazing does not entail tending by

owners, as mentioned earlier, so working time was least in the free-range system, around 95

days on average (varying from around 12 days to 165 days), while it was around 267 days

(from 186 to 358 days) and about 324 days (between 240 and 450 days) in the part-time and

Page 158: BEEF CATTLE SYSTEMS IN THE CONTEXT OF SUSTAINABLE ...bictel-fusagx.ulg.ac.be/ETD-db/collection/... · (2011). Beef cattle systems in the context of sustainable agriculture in Bac

140 Results and discussions

cut-and-carry systems, respectively. Thus, cut-and-carry entailed high employment due the

longer grazing and herd tending time, not only in the non-crop production season but also in

the crop season, in comparison to the others. The high labour requirement reflects the effort to

cut and carry natural grass and tree leaves back home to feed cattle, especially when many

cattle are kept and during the season of feed resource shortage. Farmers might be unable to

keep more than two head of fattening cattle at the same time because of the large volume of

feed needed and long distance covered in winter to carry it over harsh terrain. Thus,

competition for labour and land areas for crops is a serious matter for farmers to consider

while food insecurity threatened the H’Mong households (discussed in Section 4.1). Their

longer time spent herding in both seasons can be explained by: (i) lack of off-farm activities

that farmers in the system might participate in, so spending time on cattle production is a way

of gaining income; and (ii) due to the tough terrain, there is a shortage of natural feed

resources even in the plant growing season. In addition, cutting and carrying feed resources

for fattening bulls also created considerable employment opportunity, with an average of

around 46.6 days (ranging between 2 to 135 days).

Table 41: Family labour spent on different activities in beef cattle feeding systems

Items Free-range Part-time grazing Cut-and-carry Sig.

M Range M Range M Range

Planted grass cutting

(days) 8.0 0.0 – 48.0 8.8 0.0 – 75.0 5.3 0.0 – 60.0 0.453

Grazing, tethering

(days) 94.6

a 11.8 – 165.0 266.7

b 185.6– 358.1 323.9

c 240.0– 450.0 0.000

Cutting and carrying

feed (days) - - - - 46.6 2.0 – 135.0 -

Source: Households interviews, 2008 a, b, c

within a row not sharing the same superscript letter (p<0.05).

If all samples are normally distributed with equal variances, ANOVA is used. If both conditions are not met, the

Kruskal Wallis and Mann-Whitney Tests are used.

4.3.2.2 Analysis of employment opportunities in beef cattle production systems

Employment opportunity is the capacity of the cattle feeding system to make use of labour

supplied by the household. Farmers in mountainous regions have limited resources and

strongly depend on agricultural and forest activities (Minot et al, 2003). Thus, as basic human

needs increase in this region, so does the requirement for new and/or alternative farm and off-

farm activities (Huyen, 2004). The population growth trend in these areas is high. Therefore,

the more labour is employed in agricultural activities, the lower the migration of people in

search of work.

All indicators of labour resources used in cattle production shown in Table 43 illustrates

significant differences among the systems, with all p<0.05. The average number of family

members participating in cattle production was from 2.0 persons in free-range to 2.4 persons

in cut-and-carry. The maximum number of labourers per family engaged in cattle production

was 4 persons in all systems. A significant difference in the number of labourers among

systems was indicated (p=0.023). There was no significant difference in the number of people

participating in cattle production between free-range and part-time grazing (p=0.684);

however, between free-range and cut-and-carry and part-time grazing and cut-and-carry, a

significant difference appeared, p=0.01 and 0.000, respectively.

Page 159: BEEF CATTLE SYSTEMS IN THE CONTEXT OF SUSTAINABLE ...bictel-fusagx.ulg.ac.be/ETD-db/collection/... · (2011). Beef cattle systems in the context of sustainable agriculture in Bac

Results and discussions 141

Total working days spent tending cattle in the free-range system accounted for around one

third to one fourth in comparison to that in part-time grazing and cut-and-carry, which was

calculated at an average of 102.5 days, 275.5 and 375.8 days, respectively. Tung et al. (2007)

found that the beef cattle production sector creates high employment opportunities for

households in northern Vietnam with an average of 250 labour days annually. There were

significant differences among systems and between any two systems with all p=0.000. Thus,

cut-and-carry tended to provide the highest employment opportunities. This might be an

advantage because of large family sizes and little opportunity to access off-farm activities as

mentioned above. Nevertheless, grazing cattle consumes both a huge amount of working time

and a large number of labourers. Family members needed to accompany cattle herds during

the day, under different climate conditions such as sun, rain, cold and long cold snaps. In

addition, family members needed to follow cattle herd in many locations and under many

conditions, from the lowlands to the highlands and even over harsh terrain, with cattle having

the strength and agility for climbing in the mountainous environment. On the other hand, free-

range cattle production offered the lowest employment opportunities for selected households

in this system. Nevertheless, this is an important criterion showing the potential of a large

herd size and a large number of households keeping cattle. Large herd size was definitely a

factor in this system that did not increase investment costs and labour. In fact, most

households have adapted well and feel that free grazing is less labour intensive. Although the

availability of labour resources for the system is mentioned (in Section 4.1), local people still

feel this is the greatest advantage influencing their decision. In addition, without being tended

by their owners, cattle could eat their fill without being tended by their owners and without

supplemental feeding. Interestingly, despite the lower labour requirement, 12 households

among 30 selected households in the system stopped keeping cattle in 2009. Many felt

tethering and tending cattle was hard work, and a rather high percentage of selected

households in this system worked in off-farm activities. Land Use Certificates (LUC) are

issued to each household in the commune as land is designated for forest plantation, so

pastureland for cattle grazing is gradually limited, resulting in more intensive labour to care

for cattle, protect crops, and prevent damage to young trees.

The average percentage of cattle labour in total labour time for livestock activities was highest

in cut-and-carry, which accounted for about 73%, showing its importance as a labour

investment. A slightly lower proportion of working time for cattle was recorded in part-time

grazing (nearly 69%). Meanwhile, around a third of time spent on livestock activities was

used for cattle production in free-range (33%). Thus, the labour contribution of cattle

production in this system is not one of its strong points.

Employment opportunities calculated per unit of land resource (ha) used for cattle production

was highest in the cut-and-carry system that reached 285.5 (varying between 67.0 and 735),

while the smallest one was 59.6 in the free-range system (ranging from 4.0 to 184.0). A

significant difference was recorded among systems (p=0.000), and between each pair of three

systems (all p<0.005). On the other hand, employment opportunity per one TLU was almost

the same in part-time grazing and cut-and-carry (142 versus 148 days). In comparison to the

other two systems, free-range obtained 42.5 days, a significant difference (both p=0.000).

All indicators of labour resources used in cattle production shown in the table below illustrate

significant differences among the systems, with all p<0.05. The number of family members

participating in cattle production was 2.0 persons in free-range and 2.4 persons in cut-and-

carry, on average. The maximum number of labourers engaged in cattle production was 4

persons in all systems. There was a significant difference in the number of labourers working

among the systems (p=0.023). There are no significant differences in the number of people

participating in cattle production between free-range and part-time grazing (p=0.684), while a

Page 160: BEEF CATTLE SYSTEMS IN THE CONTEXT OF SUSTAINABLE ...bictel-fusagx.ulg.ac.be/ETD-db/collection/... · (2011). Beef cattle systems in the context of sustainable agriculture in Bac

142 Results and discussions

significant difference existed between the free-range and cut-and-carry systems and between

part-time and cut-and-carry, with p=0.01 and 0.000, respectively.

Overall, cattle production in the cut-and-carry system provided more labour opportunities in

terms of the number of people engaging in it, the number of working days, the proportion of

working time for cattle in comparison to other livestock types and employment opportunities

per land unit and TLU. Conversely, employment opportunities in cattle production in the free-

range system showed an opposite trend. Eguienta et al. (2002) found that in the long run, free-

range practices are a source of conflicts among and within villages in Bac Kan province.

Table 42: Analysis of social solidarity in cattle feeding systems

Indicators Free-range Part-time grazing Cut-and-carry Sig.

M Range M Range M Range

Num. of labourers

(persons) 2.0

a 1 – 4 2.1

a 1 – 4 2.4

b 1 – 4 0.023

Labour working time

(days) 102.5

a 11.8 – 195.0 275.5

b 185.6 – 358.1 375.8

c 270.0 – 517.5 0.000

Time spent on cattle

compared to other

livestock types (%)

33.1a 5.2 – 64.4 68.7

b 35.4 – 96.8 72.6

b 45.5 – 96.1 0.000

EBA (people days-

year for 1 ha) 59.6

a 4.0 – 184.0 214.3

b 33.0 – 1500.0 288.5

c 67.0 – 735.0 0.000

EBA (people days-

year for 1 TLU) 42.5

a 6.0 – 115.4 142.4

b 42.8 – 375.0 148.7

b 50.1 – 367.5 0.000

Source: Households interviews, 2008 a, b, c

within a row not sharing the same superscript letter (p<0.05).

If all samples are normally distributed with equal variances, ANOVA is used. If both conditions are not met, the

Kruskal Wallis and Mann-Whitney Tests are used.

With low investment in labour resources for cattle production, especially in grazing time,

households in the free-range system had the largest return per labour day of around 93,000

VND (a great range between 2,900 to 1,133,500 VND) (Table 44). The greatest return per

labour day in the system was recorded in the family of Mr. Nong Van Pya. Their family let

their cattle roam completely free, rarely checking on the herd (a few times per month). In total

they spent around 15 days annually, while total cattle net income was around 17.0 mil. VND.

On the other hand, Mr. Nong Hoang Cap family got an extremely low return per labour day,

with 2,900 VND due to the very low net cattle income obtained.

The average return per labour day in the part-time grazing system was the lowest value, at

17,700 VND. The return on labour varied between -10,000 VND and 38,400 VND. The

failure of cattle production in the family of Mr. Ly Van Diep incurred a loss of 10,000 VND

per day for their labour. The average return on labour indicated a higher value of around

4,000 VND per day in the cut-and-carry system compared to that in part-time grazing. Tung

and Giang (2008) found that the average return per labour day in the northeast and northwest

is around 31,000 VND. However, no statistically significant difference was found between

two systems on return on labour (p=0.434). Nevertheless, there were significant differences

between free-range and part-time grazing and between free-range and cut-and-carry (both

p=0.000). The three cattle feeding systems differ significantly with each other with p=0.000.

Page 161: BEEF CATTLE SYSTEMS IN THE CONTEXT OF SUSTAINABLE ...bictel-fusagx.ulg.ac.be/ETD-db/collection/... · (2011). Beef cattle systems in the context of sustainable agriculture in Bac

Results and discussions 143

Table 43: Analysis of return from cattle production per labour day among the systems

Indicators Free-range Part-time grazing Cut-and-carry Sig.

M Range M Range M Range

Return per labour day

(1,000 VND) 93.1

a 2.9 – 1,133.5 17.7

b -10.0 – 38.4 21.6

b 3.4 – 55.6 0.000

Source: Households interviews, 2008 a, b

within a row not sharing the same superscript letter (p<0.05).

If all samples are normally distributed with equal variances, ANOVA is used. If both conditions are not met, the

Kruskal Wallis and Mann-Whitney Tests are used.

4.3.2.3 Analysis of gender issues in cattle feeding systems

A study on poverty alleviation must include a gender analysis in order to determine how best

to improve conditions for rural women and improve the sustainable livelihood of farmers

(Ashby, 1999). Therefore, the role of women participating in decision making in cattle

production activities is presented in detail in this section of the study.

The highest time that female labourers devoted to cattle production in comparison to men was

recorded in the free-range system, which amounted to nearly 54%, whereas around one third

of that time was recorded in part-time grazing and about one fourth in cut-and-carry. There

was a significant difference among the systems (p=0.021). The free-range system differed

from part-time grazing (p=0.028) and cut-and-carry (p=0.009) on female labour time spent in

cattle production. Actually, grazing cattle and harvesting planted grass as well as cutting

natural grass and fodder tree leaves are a lot of work, especially for children and elderly

persons (Table 45). In fact, the assignment to collect natural feed resources also caused a

divergence among family members in the cut-and-carry system, where women still had a

weaker voice. Usually, females were responsible for collecting feed for cattle. Thus, the

percentage of working time spent on cattle by women in the cut-and-carry system is very

small compared to the others.

Table 44: Proportion of female working time in comparison to men in selected systems

Indicators Free-range Part-time grazing Cut-and-carry Sig.

M Range M Range M Range

Female labour time

(%) 53.8

a 0 – 100 33.4

b 0 – 100 28.8

b 0 – 100 0.021

Source: Household interview, 2008 a, b

within a row not sharing the same superscript letter (p<0.05).

If all samples are normally distributed with equal variances, ANOVA is used. If both conditions are not met, the

Kruskal Wallis and Mann-Whitney Tests are used.

Generally, a large proportion of women living in selected households in the free-range and

part-time systems participated in decision making in all activities (Table 46). In the free-range

system, around 86.7% of females participated in making decision in breeding selection, in

technical activities, and in vaccination and treatment of diseases with their partners in the

families, while up to 90-93.3% of them play important role in feed collection and in grass

cultivation and harvesting. These results may be partially attributed to the high education of

household heads in this system. Similarly, quite a high percentage of women had a say in

breeding selection, in technical activities, and in vaccination and treatment of diseases (73%

Page 162: BEEF CATTLE SYSTEMS IN THE CONTEXT OF SUSTAINABLE ...bictel-fusagx.ulg.ac.be/ETD-db/collection/... · (2011). Beef cattle systems in the context of sustainable agriculture in Bac

144 Results and discussions

to 75%) in part-time grazing. In contrast, in the cut-and-carry system, around 16.7% of female

had a say in these activities. A low ratio of women in this system participated in decision

making in management of cattle production (76.7%), dramatically lower than in the other

systems. However, a considerable proportion of females in the selected families had their say

in feed collection, grass cultivation, and harvesting.

It is important to note that mostly men occupy positions of vital importance in the H’Mong

family, where they are responsible for all main activities and decisions, while women play a

minor role in crop production, as well as in other livestock production activities and

household work. Particularly, in cattle production, males are responsible for the tending,

fattening, and feeding strategies, selection of cattle for breeding, and decision to sell, while

women play primarily a role in grass cutting. Grazing cattle duties are shared among family

members.

In cut-and-carry, grazing cattle are often tended by men. Particularly, looking after cattle and

carrying out technical activities for fattening cattle were up to male labourers in the system.

The male labourer in the cut-and-carry seems to be more active than the female. In contrast to

H’Mong families, all important activities are in female hands in Tay families practising the

free-range and part-time grazing systems. Particularly, many other labour-intensive off-farm

activities, as well as crop and livestock production, are cared for mainly by females. At

cropping time, most women conduct all activities while many of their partners do such things

as preparing pig feed, cooking, and grounds work, considered as odd jobs or easy work on

farms. In cattle production, women tend animals and cut planted grass, which are considered

as hard work. Regular checking on grazing animals is often shared among family members.

However, decision to sell and other important decisions are mostly handled by men in all

systems, especially in the cut-and-carry system, while in the free-range and part-time grazing

systems, a small number of women decide on selling cattle.

Table 45: Proportion of women working in different cattle production activities

Indicators Free-range Part-time grazing Cut-and-carry

Breeding selection (% HH) 86.7 73.0 16.7

Technical activities (%HH) 86.7 73.0 16.7

Vaccination and disease treatment (%HH) 86.7 75.7 16.7

Cattle looking after (%HH) 90.0 94.6 76.7

Feeding collection (%HH) 93.3 91.9 83.3

Grass cultivation and harvesting (%HH) 93.3 89.2 80.0

Selling decision (%HH) 20.0 13.5 3.3

Source: Household interview, 2009

4.3.3 Analysis of the environmental stability of cattle production in cattle feeding systems

A proper environment is a vital condition for human beings (Sen, 2005), and this holds true

especially in the context of booming climate change in the world in general and Vietnam in

particular. Actually, climate change poses risks to lives and livelihoods throughout the world,

but is exacerbated greatly in some areas.

Page 163: BEEF CATTLE SYSTEMS IN THE CONTEXT OF SUSTAINABLE ...bictel-fusagx.ulg.ac.be/ETD-db/collection/... · (2011). Beef cattle systems in the context of sustainable agriculture in Bac

Results and discussions 145

Among the issues, cattle production is a risk to the environment due to methane and other

greenhouse gas emissions, and manure production. According to Crane (1982) cited in

Phillips and Sorensen (1993), methane is one of the four most important greenhouse gases. In

addition, methane is one of factors that may have a direct effect to the environment (Timon,

1993). Negative effects from cattle production and other agricultural activities may eventually

hinder the availability of resources over time. Concern over the threats posed by long-term

climate change impacts has led to an interest in controlling emissions of greenhouse gases

such as methane generated as a by-product of the digestive processes of livestock. Hence, in

the study context, manure management, manure used for crop production, and manure

abandoned to the environment among the systems are described in Table 47.

The highest percentage of households storing their cattle manure in a fenced-off enclosure or

pit was recorded in part-time grazing (nearly 90%), whereas the lowest proportion was

recorded in the cut-and-carry system with just 50%. Nevertheless, their storage and

preservation methods were very rudimentary. Therefore, a high percentage of manure among

those households still leached into the environment. The remaining households left cattle

manure in the surrounding environment. Correlatively, the largest proportion of cattle manure

leaching into the environment was recorded in cut-and-carry with nearly 70%. The smallest

percentage was around 37% in part-time grazing. There was significant effect among systems

on the amount of manure running out (p=0.000). However, there was only a significant

interaction between part-time grazing and cut-and-carry (p<0.05). Actually, daily removal of

manure from shelters, storage and preservation of manure, and the good condition of animal

stable and surrounding corral area can decrease greenhouse gas emissions.

The part-time grazing system saw the highest amount of cattle manure used, around 1.9

tonnes per hectare, while the smallest amount was around 1.0 tonne in the cut-and-carry and

free-range systems. Cattle manure was the main source of natural fertiliser used in crop

production in selected households because the average livestock manure (including cattle

manure) applied to cultivated land areas among systems were also very low (around 2.0

tonnes in both free-range and part-time grazing systems, and a lower amount of 1.2 tonnes per

hectare was indicated in cut-and-carry system) (see Annex 8). Thus, use of cattle manure for

crop production was very low in all systems. Huyen (2004) found that a very small number of

farmers use manure for crop production in Son La province. Most cattle manure in the free-

range and cut-and-carry systems was simply abandoned to the environment and was not used

for crop production, resulting in pollution of the living environment. Despite the amount of

wasted manure, cattle manure resource used for crop and forestry production was quite

appreciated by many crop producers in the study area because it was not only cheap but also

environmentally friendly compared to chemical fertilisers. Particularly, chemical fertilisers

are currently widely used in the lowlands, where rather high crop intensification is taking

place. Compared to the free-range and cut-and-carry systems, farmers in the part-time grazing

system used large amounts of manure for crop production, thus returning cattle manure

naturally to the environment. Normally, an application of from 8.0 to 10.0 tonnes of compost

manure per hectare of crop land could be practised in most types of soil, according to

guidelines from the Vietnam Plant Protection Department. An application of up to 15.0 tonnes

per ha might also be applied to poor quality soil such as sandy soil. It is important to note that

each beef animal weighing around 220 to 340 kg can produce from 20 to 30 kg excreta/day

(Phillips and Sorensen, 1993; Godwin and Moore, 1997). Significant differences were found

among systems on the amount of cattle manure utilized (Krusal Walis Test, p=0.000). There

were statistically significant differences on cattle manure used between the part-time grazing

and cut-and-carry systems (p=0.000) and between part-time grazing and free-range (p=0.025)

using the Mann-Whitney Test.

Page 164: BEEF CATTLE SYSTEMS IN THE CONTEXT OF SUSTAINABLE ...bictel-fusagx.ulg.ac.be/ETD-db/collection/... · (2011). Beef cattle systems in the context of sustainable agriculture in Bac

146 Results and discussions

In the cut-and-carry system, all manure from cattle and other livestock types was discharged

under or behind their pens, with water streams running beside or nearby. Most animal manure

and waste was washed directly by rain or flood water into streams. Thus, the pollution might

affect directly people living in downstream areas, such the Tay and Nung minority groups.

Their indirect impact could even cause pollution to people living in other lowland areas.

Particularly, cattle manure contains various pathogens, e.g. FMD, which may be transported

with cattle excreta to water resources and may cause infection to farms downstream (Sommer

et al. 2008). Similarly, poor storage and management of cattle and other animal manure was

seen in almost households in the free-range system. Hence, poor hygiene is a serious issue in

selected households in the system. Some households undertook simple storage and

management of manure, but the pollution risk is high in almost all selected households in the

system. Most households practising the free-range system still live in very poor hygiene

condition and poorly manage livestock manure. Many households still keep their cattle under

their houses on stilts, which were common in former times in mountainous areas.

Nevertheless, this way of keeping cattle has been discontinued in these areas recently due to

pollution risk for households, thanks to extensive government awareness-raising campaigns.

Animal manure was even left wherever it landed throughout the commune, even on the roads,

thus easily discharged into rivers and streams. Moreover, such streams run from the highest

mountains through H’Mong villages. Yet, a high proportion of households still take advantage

of rivers and streams for washing clothes, cleaning vegetables, and other activities. In

contrast, households in the part-time grazing system live in better hygiene condition, but a

high percentage of households still keep their animals near their houses. According to Phillips

and Sorensen (1993), leaching of nitrates from cattle manure causes pollution of water

resources and can gradually contaminate human drinking water resources.

It is important to note again that degradation of soil and erosion are also theoretically caused

by cattle grazing, especially in the uplands, as pointed out in Chapter 2, but its actual impacts

are not deeply analysed in this study due to limited time and funds as well as it is highly

difficult to analyse. However, it is a fact that free-ranging cattle caused damage to crops and

forest, especially in the early growth stage of forest trees. This caused conflicts among

villagers both near and far. Free-grazing cattle tend to cause large influence on soil erosion

and degradation on hills and uplands, especially when herd sizes are large. On the other hand,

because cattle owners in part-time grazing and cut-and-carry tend their animals, crops and

growing forest plantations escaped harm, and this in turn avoided social conflicts among

villagers and people in nearby communes. In this study context, therefore, the cattle stocking

rate is used as an indicator to assess this degradation of land areas by calculating number of

cattle TLU per hectare of grass land. There was little difference among the systems on this

value, but no significant difference was recorded. There is no study on this indicator in

Vietnam so far. Eguienta et al. (2002) find that longstanding free-grazing practices are

harmful to the natural resource base in Bac Kan province. In an environment of increasing of

both human and animal populations, livestock is an important cause of the deterioration of

forests and pasturelands (Husson et al., 2001 cited in Eguienta et al. 2002).

Page 165: BEEF CATTLE SYSTEMS IN THE CONTEXT OF SUSTAINABLE ...bictel-fusagx.ulg.ac.be/ETD-db/collection/... · (2011). Beef cattle systems in the context of sustainable agriculture in Bac

Results and discussions 147

Table 46: Influence of beef cattle feeding systems on environmental stability

Indicators Free-range Part-time grazing Cut-and-carry Sig.

M Range M Range M Range

Manure preservation

(% HH) 73.3 - 89.2 - 50.0 - -

Cattle manure used

(tonnes/ha cultivated

land)

1.0a 0.0 – 3.9 1.9

b 0.0 – 8.0 1.0

a 0.0 – 3.7 0.000

Manure being washed

out (% cattle manure

produced at shelters)

47.0a 5.0 – 100.0 37.3

a 5.0 – 100.0 67.8

b 5.0 – 100.0 0.000

Cattle stocking rate

(TLU/ha cultivated grass

land)

22.5 0.0 – 80.0 27.5 0.0 – 166.7 16.5 0.0 – 120.0 0.096

Source: Household interview 2008; 2009 a, b

within a row not sharing the same superscript letter (p<0.05).

If all samples are normally distributed with equal variances, ANOVA is used. If both conditions are not met, the

Kruskal Wallis and Mann-Whitney Tests are used.

It is essential to mention the strong impact of climate change on the agricultural sector in

general and livestock production in particular. Cattle production in Bac Kan province is not

being spared. In early 2008, there was a damaging cold outbreak on the study sites, which has

never occurred in study sites expecting as influencing by climate change, resulting in many

dead animals and the elimination of entire cattle herds.

Table 47: Cattle production losses in the beef cattle systems during the cold outbreak in

the early 2008

Indicators Free-range Part-time grazing Cut-and-carry Sig.

M Range M Range M Range

Households suffering

loss (%) 66.7 - 16.2 - 30.0 - -

Average num. cattle

lost (head/HH) 1.4

a 0.0 – 8.0 0.3

b 0.0 – 4.0 0.6

b 0.0 – 4.0 0.000

Average value of

cattle lost (mil.

VND/HH)

3.1a 0.0 – 20.0 0.6

b 0.0 – 14.0 1.4

b 0.0 – 14.0 0.000

Source: Household interview, 2009 a, b

within a row not sharing the same superscript letter (p<.05).

If all samples are normally distributed with equal variances, ANOVA is used. If both conditions are not met, the

Kruskal Wallis and Mann-Whitney Tests are used.

Among the selected systems, the free-range system sustained the highest losses, 66.7% of

households being affected with the loss of 1.4 head and 3.1 mil. VND per household on

average. Ranking next in cattle production loss was the cut-and-carry system, affecting some

30% of households, with an average loss of 0.6 head or 1.4 mil. VND per farm. Meanwhile,

among households practising part-time grazing, over 16% of them, suffered loss, an average

of 0.3 head or 0.6 mil. VND (Table 33). Thus, the husbandry style presenting the highest

Page 166: BEEF CATTLE SYSTEMS IN THE CONTEXT OF SUSTAINABLE ...bictel-fusagx.ulg.ac.be/ETD-db/collection/... · (2011). Beef cattle systems in the context of sustainable agriculture in Bac

148 Results and discussions

losses such free grazing can be explained because of the lack of care and feed storage.

Otherwise, higher losses were also recorded in the cut-and-carry system due to lack of simple

stored feed resources such as rice straw, and their inhospitable location in the uplands with

very low temperatures compared to those felt by Tay households living in the lowlands. Thus,

stored feed in the cattle feeding systems tended to play an important role, especially in coping

with severe climate conditions. However, the selected households on the study sites are not

giving this matter routine attention.

4.3.4 Measuring cattle production in the systems in all dimensions of sustainable agriculture

To understand a farming system and its sustainable aspects, the concept of multi-criteria or

multi-dimensions must be used (Gomiero and Giampietro, 2001). The selected indicators of

different dimensions of sustainable cattle production systems can be handled by integrated

packages of indicators referring to different dimensions and systems of analysis in a “spider

diagram”, which is typical of multi-criteria analysis of sustainability.

The nominalising of selected indicators, which could be representative ones to sustainable

dimensions of cattle feeding systems, is introduced in Figure 42. It can be seen that no system

showed full sustainability in all dimensions of economics, society, and environment. In fact, it

is very difficult to reach sustainability in all pathways.

Specifically, gross cattle margin in all systems could be ranked from rather poor to medium

levels, e.g. the part-time grazing and cut-and-carry systems had medium-level gross cattle

margin (0.44 and 0.45, respectively), while the free-range system achieved a poor level with

0.37.

Regarding employment opportunities in the different systems, cut-and-carry offers the best

chance to work in cattle production among the systems, and this indicator was sorted in rather

good level, with 0.59, while free-range and part-time grazing ranked approximately equal

with each other at a medium level (0.40 and 0.44).

Although free-range did not have as many employment opportunities as the other two

systems, this system gave greater opportunity for women to participate in cattle production

activities, as indicated by the value of 0.54, much higher than that in the cut-and-carry and

part-time grazing systems (0.33 and 0.29, respectively). In the cut-and-carry system, women

seemed to spend less time and participate less in cattle production activities than men.

As mentioned in Section 4.2, grass land allocated for cattle production was very limited but

cattle production scale was very small. Therefore, cattle stocking rate was very small. The

smallest value was 0.09 recorded in the free-range system. The other two systems also had

small values of 0.14 and 0.17 in part-time grazing and cut-and-carry, respectively.

Values of the indicator “Proportion of cattle manure leaching out into the environment” in all

systems could be ranked at medium levels. However, the lowest value was 0.46 recorded in

the cut-and-carry system. The free-range and part-time grazing systems achieved a little

higher rating, with 0.57 and 0.55. Despite ranking in the medium level, strict attention should

be given to limiting the discharge of cattle manure and other livestock manure into the

environment surrounding other households in order to inhibit environmental pollution and

prevent transmission of animal diseases to people, where such risk occurs.

There are therefore compelling reasons to increase the role of women both in part-time

grazing and cut-and-carry, to reduce manure discharge in all systems, especially cut-and-

carry, and to improve the profitability of free-range and part-time grazing. The stocking rate

Page 167: BEEF CATTLE SYSTEMS IN THE CONTEXT OF SUSTAINABLE ...bictel-fusagx.ulg.ac.be/ETD-db/collection/... · (2011). Beef cattle systems in the context of sustainable agriculture in Bac

Results and discussions 149

for cattle production in all systems should also be increased through investment in grass

production for cattle husbandry in terms of land resources and management. These points

should be included in a strategy conducive to the development of sustainable cattle production

in the different systems.

Figure 42: Measuring the sustainability of the different cattle feeding systems Source: household interview, 2008; 2009

4.3.5 Section summary

The different influences of cattle production systems on the social, economic, and

environmental elements of sustainable agriculture were studied. For cattle production among

households invest was rather low in total costs and in feeding expenses more particularly. The

highest expense was replacement of breeding stock, but this cost was not regular recorded

among the systems. This is considered as an advantage of this sub-sector in the context of

significant food insecurity in the uplands, especially in H’Mong households. Among the

systems, the cut-and-carry cattle system seemed to generate the highest net cattle income,

while the other two systems tended to have approximate values. Households in the cut-and-

carry system enjoyed higher economic efficiency, which can be partially explained by their

fattening method as well as their heavy investment in labour resources, grain feed, and good

management skills. Thus, the high economic value of bulls after fattening was a feature of the

H’Mong people in cattle production, bringing a positive market-oriented trend, but still small

in size because of the rugged terrain, lack of investment in feed resources and breeding, food

insecurity, high labour consumption and strenuousness of the work involved.

Cattle husbandry in the cut-and-carry system seemed to create better employment

opportunities then in the other systems. The high labour demand was a positive benefit for

this system due to poor availability of arable land, low production intensity, and poor access

to off-farm activities. Meanwhile, the lowest employment opportunity was recorded in the

Page 168: BEEF CATTLE SYSTEMS IN THE CONTEXT OF SUSTAINABLE ...bictel-fusagx.ulg.ac.be/ETD-db/collection/... · (2011). Beef cattle systems in the context of sustainable agriculture in Bac

150 Results and discussions

free-range system, suggestive of poor social sustainability, but in the context of good

accessibility to off-farm activities, it was an advantage of the local farmers preferring this

approach. Thus, the cut-and-carry system seemed to have good potential in the development

programme on the study sites.

However, a large environmental risk from manure discharge due to lack of proper

management was indicated from the study. Manure use for cultivation was limited because of

predominantly steeply sloped lands and the local people practise the cut-and-carry system.

Furthermore, manure utility was evaluated as less importance in cut-and-carry compared to

other systems in the lowlands. Otherwise, a very high proportion of manure leaching into the

environment were recorded among the systems, indicating a lack of proper handling methods

in households, low level of cattle manure use for crops, thereby causing high pollution for

households living on the study sites. Farmers displayed poor awareness of environmental

protection. Nevertheless, analysis of the environmental aspect is not a main topic of this

study, but the thesis having a strong focus on the social and economic aspects of selected

households in the cattle feeding systems. Moreover, in the context of the study, analysis of the

environmental dimension was hampered by lack of data, shortage of funds and time, and the

complexity of the subtopic.

On the other hand, all systems showed their positive influences in economic and social

dimensions, but none of systems could achieve fully sustainable development because no

system showed sustainable indicators in all three dimensions—economics, society, and

environment. Actually, to achieve all elements of sustainable agriculture is an immense

challenge to cattle raising farmers. Their first concern is achieving economic efficiency,

which is enough of a dilemma. However, increasing their awareness of environmental

protection might be pursued, especially in the context of climate change in Vietnam, which

strongly impacts on the NMR.

Page 169: BEEF CATTLE SYSTEMS IN THE CONTEXT OF SUSTAINABLE ...bictel-fusagx.ulg.ac.be/ETD-db/collection/... · (2011). Beef cattle systems in the context of sustainable agriculture in Bac

5 CONCLUSIONS AND RECOMMENDATIONS

5.1 CONCLUSIONS

Emerging from the motivation of improving the sustainable livelihood of cattle farmers

through an assessment of appropriate cattle feeding systems with positive influences on the

sustainability of agriculture and in tandem with the development trend of cattle products in

Vietnam’s markets; the study is purposed to derive recommendations to improve cattle

production in a long-term, sustainable manner and to promote a sustainable livelihood for the

poor. The study sites were carried out in Nghien Loan and Cong Bang communes, Pac Nam

district, Bac Kan province, in the northern mountainous region (NMR) of Vietnam, where

cattle production is predominant and considered favourably. Formal surveys using structured

questionnaires and PRA tools involving 97 households were conducted to collect the required

data. This study attempts to provide both qualitative and quantitative insight into the nature

and influence of these cattle feeding systems on sustainable agriculture by using selected

indicators and a multi-criteria approach, and understanding of the development trend of cattle

systems.

5.1.1 Empirical findings

The selected households practising free-range and part-time grazing were Tay people, located

in the lowlands, enjoying better conditions, but experiencing high land use pressure and high

intensification of crop production, whereas the investigated households in cut-and-carry were

H’Mong persons in almost opposite conditions. They live in the uplands, lack basic

infrastructure, have poor soil, but land use pressure and crop intensification are low, and crop

yields are correspondingly low. Other characteristics should be noted about selected

households in the cut-and-carry system: large family size, poor education level, poor

opportunities to engage in off-farm work, and a great proportion of households suffering food

insecurity. Thus, engaging in farm activities that bring them a better chance in food security

and better living standard is essential. Although the H’Mong people have a low education

level, they practise the most modern cattle system compared with the others. They have good

knowledge and better mastery of the cattle fattening process, while this is very limited among

Tay people. In addition, the H’Mong people also have strong relationships not only inside

their commune but also in outside communes. The Tay people practising the free-range

system had the highest education level, but their approach to cattle husbandry was the most

“obsolete”. Thus, the education level of household heads was not related to their cattle

keeping methods. Differentiations of cattle feeding systems seemed to relate more to the

natural land area, farm and off-farm activities, traditions, culture, their indigenous knowledge

as the specific characteristics of the ethnic minorities. Among livestock species, cattle

production obtained the largest share of total net income, which indicated its position in

improving livelihoods of the local people.

In this study, cattle production systems in the selected households were mainly small-scale.

There was no difference in cattle production size among the systems. Despite the features of

the free-range system, the investigated households did not keep large size herds. Cattle

production scale tended reduction due to reforestation, gradual limitation of natural

pastureland and population booming. Feed resources for cattle production among the systems

did not show a special disparity; with an exception of using natural cut-and-carry feed

resources, maize, and pig cooked feed for fattening cattle in H’Mong households practising

the cut-and-carry system. Feed resources shortage was recorded among the systems in the dry

Page 170: BEEF CATTLE SYSTEMS IN THE CONTEXT OF SUSTAINABLE ...bictel-fusagx.ulg.ac.be/ETD-db/collection/... · (2011). Beef cattle systems in the context of sustainable agriculture in Bac

152 Conclusions and recommendations

season, especially in cut-and-carry. Poor storage of by-products from crop production was

seen among the three systems, while processing feed resources stored for winter time was not

recorded in any system. There were little supplemental feed resources for cattle during

adverse climate events and times of deficiency due to food insecurity in many selected

households and a non commercial production purpose of cattle in all households in spite of

starting fattening cattle for better economic efficiency. Grass production was practiced, but

the yield was poor, applied by only a small number of households and in small areas in all

systems. Due to the small proportion of land put to grass production and poor grass

performance as well as infrequency of harvesting, a comparison of economic efficiency

between households with and without grass production showed no differentiation. However,

the H’Mong people seemed to have started focusing attention on this feed resource in their

cattle production, despite the fact that their productive land areas are still limited and of poor

quality. Grass production has not been played its actual role in cattle production as expected

in the cattle development project launched by the government. In addition, most farmers have

had under-evaluation potential effects of grass production to their cattle husbandry, but their

production still based strongly on natural feeding resources. Natural public pastureland is

gradually becoming more limited due to reforestation, Land Use Certificate, and population

increase, but development planning in the study area did not include development planning

pastureland for the future. Use and management of communal grazing land was not yet

considered in any selected commune.

Cattle husbandry in the cut-and-carry system tended to have a more positive reproductive

performance than those in the other two systems, despite the more serious deficiency of feed

resources in the winter season, which could be explained by their experience in management.

However, the rather high percentages of breeding cows among the systems were in overall

rather poor condition, showing a lack of awareness of farmers in development of cattle

production as a high-quality product. Actually, farmers did not give proper attention to

breeding management such as breed selection and replacement, especially selected

households in the free-range and part-time grazing systems. Better breeding management of

cows and bulls was found in H’Mong households. All systems showed poor health care and

disease control, with a poor vaccination rate and inappropriate treatment methods. The

H’Mong people tended agree among each other not to use veterinary services due to adverse

consequences of vaccination programmes conducted by the authorities, but the government

organisations did not communicate well and handled matters poorly. Another reason is that

cattle loss due to diseases was rarely recorded among these households. In the free-range

system, a large proportion of households did not have shelters for cattle production, while the

part-time grazing and cut-and-carry systems made better provision. Most households had

access to credit programmes from the government for livestock development, but most of the

loan money was used for other purposes. Further, there was little involvement of

organisations such as extension services, farmers’ union or Women Union in support of beef

cattle development and production on the study sites, while the government has implemented

a strong cattle development project. It seems that cooperation among stakeholders in

improving cattle production in the study area is still weak. Availability of local cattle market

is assessed as an advantage in keeping cattle in the study sites but farmers in all the cattle

feeding systems seemed to face more disadvantages than advantages and opportunities in

cattle marketing chains, especially in the process of changing to modern retail trading. Thus,

the challenges for the future will be a high competitiveness between cattle production and

natural resources and development trend of cattle markets’ products.

Assessing influences of the different cattle feeding systems on various sustainable dimensions

of the agricultural sector was firstly conducted by selecting suitable indicators for cattle

Page 171: BEEF CATTLE SYSTEMS IN THE CONTEXT OF SUSTAINABLE ...bictel-fusagx.ulg.ac.be/ETD-db/collection/... · (2011). Beef cattle systems in the context of sustainable agriculture in Bac

Conclusions and recommendations 153

production sub-sectors. Then, an analysis of their influences on economics, society, and

environment was made. The results in the cut-and-carry system showed that selected

households had high employment opportunities, rather good economic efficiency, but also

were a larger risk for the environment because of unused manure due to steep and slope lands

and its management. H’Mong women in the system played an important role in non-vital

activities and feed collection—assuming the brunt of hard work. In comparison to selected

H’Mong households in the cut-and-carry system, those in free-range and part-time grazing

seemed to have poorer economic efficiency and lower employment opportunities, and all

important activities were in female hands. Comparing with H’Mong households, Tay

households had a rather low rate of manure being discharged into the environment. The high

proportion of manure abandoned to the environment among the systems, indicated a lack of

proper handling methods in households, a low level of cattle manure use but a high

percentage of chemical fertilisers used, and poor awareness of cattle owners, resulting in

environmental pollution on the study sites. It is indicated that increasing environmental

protection in the context of climate change in Vietnam is strongly emphasised in the coming

years. Although all systems had positive influence on many social-economic indicators, it is

extremely hard to find a sustainable system that takes all pathways into account.

To sum, high consumer demand, development trend of cattle markets’ products and

increasing domestic incomes encourage beef cattle development to fill the requirement, in

harmony with government support policies. Nevertheless, cattle farmers stood in a poor

position and faced high competition from imported cattle products. The development trend of

cattle feeding systems will be expected to embrace the cut-and-carry system because of

limited pastureland and consumer demand for uniform, high-quality products and tendency of

development of supermarkets and hypermarkets. Thus, a balance must be achieved between

cattle production and natural resource use as pastureland for cattle grazing will be

increasingly devoted to forest production and land allocation.

5.1.2 Limitations of the study

The present findings and their quality must be interpreted in the context of a number of

potential limitations. These were limitations faced by the study regarding study time, funding,

location, culture, language, and availability of data. Firstly, the data were obtained from a

rather limited sample size, which might not meet the statistical requirements for strict

analyses and eliminate random errors; however, the sample size of each system was still

considered satisfactory. Secondly, another limitation of this study was that quantitative data

collected from farmers was conducted mainly for one year, in 2007, which might not be

representative for selected households over a long period. Next, complicated study location,

diversified culture and languages were challenges for the author implementing the study and

collect requirement data. Then, there are important strengths in the study because it focuses

on a selection of indicators of dimensions of sustainability in cattle production among

different systems. Thus, assessing and understanding these influences on sustainability

provides an opportunity to improve farmer livelihoods through enhancement of each aspect of

society, economics, and environment at all dimensions wherever possible. Nevertheless, the

study strongly emphasises the socio-economic aspects at the grassroots level, to some extent

at the expense of the environmental pathway. Due to lack of secondary and primary data,

limitation of fund and the complicated study object, analyses of the environmental indicators

as well as calculation of environmental influences were restricted, which were not

representative for evaluation of environmental pollution caused by cattle production. Finally,

there were shortage in data collection for replacement rate of cow and mortality rate of calves,

which were caused by poor data sources from farmers. Furthermore, growth performance of

Page 172: BEEF CATTLE SYSTEMS IN THE CONTEXT OF SUSTAINABLE ...bictel-fusagx.ulg.ac.be/ETD-db/collection/... · (2011). Beef cattle systems in the context of sustainable agriculture in Bac

154 Conclusions and recommendations

cattle production among systems were also not emphasised in the study due to limitation

issues mentioned above.

5.2 RECOMMENDATIONS

According to findings of the study, in order to improve cattle production and make it

sustainable in the long term in the selected systems, different interventional activities are

required: (i) increased capacity building for local farmers; (ii) support farmers for the

sustainable development of cattle; (iii) help farmers improve product quality; (vi) strengthen

cattle resources on the study site; and (v) formulate support policies.

There is an increasing trend of number of supermarkets and consumers’ preferences in

purchasing goods in Vietnam. It is to be expected that development of beef cattle products

will have to adapt to the development trend of supermarkets and hypermarkets in the near

future, as is the case in surrounding countries such as Thailand. Thus, ways of improving each

cattle production system should be emphasised to meet the changing in the near future.

Additionally, the development of marketing cattle products might be another motivation for

raising cattle in the cut-and-carry system that is considered the favourable system among the

three systems and local farmers need to improve their cattle production in response to these

trends.

Thus, cut-and-carry cattle feeding system should be developed and expanded in the study area

in the near future. Support must be given to households in the cut-and-carry system to

improve the fattening process with consistency, especially providing guidance for creating

feed resources in the winter time. Feed resources should be increased by growing different

grass varieties, enlarging grass production areas, and increasing awareness of farmers in the

production of grass and harvesting techniques. In addition, processing and storage techniques

for planted grass and by-products of crop production should be introduced and training

provided. Setting up and implementing experiments/studies of processing and storage of

cultivated grass and by-products and assessing the model’s impacts on the production

efficiency of cattle production should also be carried out. Furthermore, farmer awareness on

prevention and treatment of diseases must be raised, vaccinations based on specific disease

characteristics as well as improved communication among the authorities and local

communities on these matters should also be emphasised.

On the other hand, in the free-range system, although production would be gradually changed

to part-time grazing coupled with cut-and-carry, the building of an awareness-raising

programme would be a critical option in the immediate future to change the habits of local

villagers so that cattle are not allowed to graze freely, are not kept in poor-quality shelters,

good breeding management, and veterinary care is introduced. In addition, households

employing part-time grazing system should also be introduced those techniques. Then,

introducing the techniques and procedures of the cut-and-carry system (fattening cattle) as

well as introducing technologies of grass production, the processing and storage of feed

resources, and experimental models should be implemented among households in both the

free-range and part-time grazing systems to help farmers improve their cattle production and

income, with a view to bringing them a more sustainable livelihood.

Then, a programme to increase awareness of farmers regarding manure management in all the

systems should be conducted. Providing guidelines for manure storage and use of composted

manure should also be applied to reduce environmental pollution for households among the

three systems.

Page 173: BEEF CATTLE SYSTEMS IN THE CONTEXT OF SUSTAINABLE ...bictel-fusagx.ulg.ac.be/ETD-db/collection/... · (2011). Beef cattle systems in the context of sustainable agriculture in Bac

Conclusions and recommendations 155

In addition, a favourable policy on the province and district on planning of public pastureland

in each commune and each district as well as in bordering areas among communes and

districts should be implemented to avoid the current situation of scattered grazing land, to

enable cattle and buffalo producers to graze their animals in sync with the reforestation

programme. Besides, increasing the awareness of local communities on employing and

managing public pasture and the allocation and utilisation of such areas should be conducted

among groups of cattle keepers.

Support for the development of cattle resources such as breed improvement programme

should be carefully carried out, including the provision of technical training sessions and an

awareness-raising programme for farmers on breed quality and management and animal

health care. A programme for the selection of breeding cows and bulls should be carefully

carried out. Elimination of poor breeding animals should be implemented among cattle

keeping farmers, by a communication programme. A little support fund for the poor in

conducting the activity is formulated. Several experimental models should also be introduced

to farmers as well.

Farmer interest groups in cattle production should be established, including formal

regulations, selection criteria, group meeting skills, facilitating skills, and relevant activities of

the groups, etc. Also needed are training sessions to enhance the management skills of

farmers, group working, and skills required to keep cattle production records and records of

other agricultural activities. This will assist farmers to work productively in groups. Building

cooperation among farmer interest groups should also focus on empowerment and mutual

activities.

It is clear that the integration of smallholder farms in modern retail markets is one important

way to improve their livelihood. Changing in the modern retail trade is gradually created in

Vietnam which might bring opportunities for cattle production farmers. Besides, more

challenging is also brought to them. Therefore, training on product quality requirements to

meet consumer demand should be strongly introduced to farmers to help them understand

changes in the modern retail markets and improve their adaptability with these changes.

Additionally, linkage programmes and workshops among farmers, traders and consumers

ought to be created to support farmers to understand the changing preferences of targeted

customers in the cities, along with farmer marketing groups. Moreover, the formation of

farmer interest groups in cattle marketing should also be a critical option for farmers in order

to improve their bargaining power and position in cattle marketing chains.

Communal development groups with their membership including key persons from farmer

interest groups, retailers, and middlemen, as well as local authorities, will be established.

Capacity building for such communal development teams and for key local people in

planning, monitoring, and management skills will be required. Cooperation among target

groups and middlemen, and linking programmes between cattle farmers and consumers

should be built up in order to help farmers meet the consumers demand for products of

quality.

Financial issue among households in development of cattle production is one of difficulties

inhibiting growth of cattle production of farmers. Therefore, a livelihood support fund (micro-

finance) from the government or organisations or from farmers themselves (self-credit

creation) in working groups should be implemented to promote active participation in the

groups and support development of farm activities.

Finally, the government, especially MARD, should provide national certification systems in

cattle products (live animals and beef) in order to provide a standard for quality control of

products in markets and supermarkets, and to build a sustainable linkage between farmers,

Page 174: BEEF CATTLE SYSTEMS IN THE CONTEXT OF SUSTAINABLE ...bictel-fusagx.ulg.ac.be/ETD-db/collection/... · (2011). Beef cattle systems in the context of sustainable agriculture in Bac

156 Conclusions and recommendations

traders, and consumers. Particularly, a control and check of beef products sold by retailers and

whole traders in retail and trade markets should seriously consider (beef origin, source such

where is beef products from, and documents owned by sellers collected meat from slaughter

houses) in order to secure its quality to meet the consumer requirement. In addition, live cattle

breed sold in markets for breeding should also certified to meet at least basic standard of

breeding animals. Agreements among neighbouring countries should also be reached to

control the healthy trading of cattle along borders and the illegal trading of live cattle, thus

reducing competition from imported products and decreasing risks from uncontrolled

diseases.

In order to have the further contribution of the research on the development of cattle

production sub-sector in general, farmers, researchers and policymakers in particular, an

additional study with larger sample sizes during a longer period should be conducted;

especially emphasising on environmental dimension (selection of favourable environmental

indicators and their calculation). Therefore, the next phase of the study should analyse this

pathway, if possible, focusing on the technical aspects of overgrazing, soil erosion caused by

cattle grazing and production, and the influence of manure on environmental pollution

through experiments. Growing performance of Yellow cattle among the cattle feeding

systems should also be investigated, especially those cattle kept by H’Mong people to obtain

a full understanding of the cattle performance.

Page 175: BEEF CATTLE SYSTEMS IN THE CONTEXT OF SUSTAINABLE ...bictel-fusagx.ulg.ac.be/ETD-db/collection/... · (2011). Beef cattle systems in the context of sustainable agriculture in Bac

6 REFFERENCES

Alburo, F., A., Panyakul, V. (2009). GMS Agricultural Trade and Facilitation Strategy

Study. Consultant report (Agriculture Trade Strategy and Facilitation), Asian

Development Bank. Incomplete Draft Report. Final Workshop 3-4 August 2009, at

Aranyaprathet district, Sa Keo province, Thailand.

Arslan, O. and Deha Er I. (2008). A SWOT analysis for successful bridge team organisation

and safer marine operations. Process Safety Progress, 27: 21–28.

Ashby, J. A. (1999). Poverty and gender: a proposal for action research. A paper prepared

for the CGIAR Conference on Poverty, Costa Rica, September 1999. Retrieved

March 30 2011: http://ciat-library.ciat.cgiar.org/paper_pobreza/019.pdf

Bac Kan Annual Report of the Department of Veterinary Health. (2008). Unpublished. Bac

Kan. Vietnamese.

Bac Kan Province Annual Report. (2008). Unpublished. Bac Kan, Vietnam.

Bac Kan - Department of Agriculture and Rural Development (DARD). (2006). Annual

report. Unpublished. Vietnam.

Bac Kan Province Statistical Office – PSO. (2008). Bac Kan, Vietnam.

Bac Kan Province Statistical Office – PSO. (2006). Bac Kan, Vietnam.

Bac Kan People’s Committee (PC). (2006). Development of Agriculture and Forestry

Production in Bac Kan Province in the period 2006-2010. Unpublished. Vietnamese.

Bac Kan Province Annual Report. (2006). Unpublished. Bac Kan, Vietnam.

Bac Kan Department of Agriculture and Rural Development (DARD) Annual Report.

(2006). Unpublished. Vietnamese. Bac Kan, Vietnam.

Bac Kan Department of Industry, Science, and Technology (DIST). (2005). Building a semi-

intensive beef cattle production model and testing dairy cattle production in Cho Don

district, Bac Kan province. Cooperation report between Bac Kan Department of

Industry, Science, and Technology and Faculty of Livestock Production and

Veterinary Health, Thai Nguyen Agricultural University. Unpublished. Vietnamese.

Bac Kan, Vietnam.

Bac Kan Province Statistical Office – PSO. (2002). Bac Kan, Vietnam.

Batz, Peters K.J., Janssen, W. (1999). The influence of technology characteristics on the rate

and speed of adoption. Agricultural Economics 21: 121-130

Page 176: BEEF CATTLE SYSTEMS IN THE CONTEXT OF SUSTAINABLE ...bictel-fusagx.ulg.ac.be/ETD-db/collection/... · (2011). Beef cattle systems in the context of sustainable agriculture in Bac

158 Refferences

Becker, B. (1997). Sustainability assessment: A review of values, concepts, and

methodological approaches. World Bank – CGIAR. Issues in Agriculture. 10.

Washington, DC. 68p.

Beets, W. C. (1990). Raising and sustaining productivity of smallholder farming systems in

the tropics. Agbes Publishing. Holland. 738p.

Beranger, C., Vissac, B. (1993). A holistic approach to livestock farming systems:

Theoretical and methodological aspects. In Brossier, J., De Bonneval, L., and

Landais, E. Eds. Systems studies in agriculture and rural development. A selection of

papers published by researchers in the Agrarian Systems and Development

Department of INRA (1990-1994). INRA. Paris. 5-17.

Blackburn, H. (1998). Livestock production, the environment and mixed farming systems. In

Nell, A. J. Ed. Livestock and the Environment. International Conference, FAO/World

Bank/USAID, Wageningen, The Netherlands. 114-123.

Bond, R., Curran, J., Kirkpatrick, C., Lee, N. (2001). Integrated impact assessment for

sustainable development: A case study approach. World Development. 29(6): 1011-

1024.

Bossel, H. (1999). Indicators for sustainable development: Theory, method, and applications.

International Institute for Sustainable Development (IISD). Canada. 124p.

Boyazoglu, J. (1998). Livestock farming as a factor of environmental, social and economic

stability with special reference to research. Livestock Production Science 57: 1–14

Bresciani, F, Dévé, F. C., Stringer, R. (2004). The multiple roles of agriculture in developing

countries. In Brouwer, F. (ed.) Sustaining agriculture and the rural environment:

Governance, policy and multifunctionality. Edward Elgar – Chelteham, UK and

Northampton, USA. 286-306.

Brown, B.J., Hanson, M. E, Liverman, D.M., Merideth, J.R.W. (1987). Global sustainability:

toward definition. Environmental management 11(6): 713-719.

Castella J.C. and Erout A. (2002). Montane paddy rice: The cornerstone of agricultural

production systems in Bac Kan province, Vietnam. In Castella, J. C., and Quang, D.

D. Eds. Doi Moi in the mountains: Land use changes and farmers’ livelihood

strategies in Bac Kan province, Vietnam. The Hanoi Publishing House. Hanoi,

Vietnam. 175-195.

Castella, J. C., Quang, D. D., Long, T. D., and Doanh, L. Q. (2002a). Scaling up local

diagnostic studies to understand development issues in a heterogeneous mountain

environment: An introduction to the SAM Program. In Castella, J. C., and Quang, D.

D. Eds. Doi Moi in the mountains: Land use changes and farmers’ livelihood

strategies in Bac Kan province, Vietnam. The Hanoi Publishing House. Hanoi,

Vietnam. 01-20.

Page 177: BEEF CATTLE SYSTEMS IN THE CONTEXT OF SUSTAINABLE ...bictel-fusagx.ulg.ac.be/ETD-db/collection/... · (2011). Beef cattle systems in the context of sustainable agriculture in Bac

Refferences 159

Castella, J. C., Boissau, S., Thanh, N. H., Novosad, P. (2002b). Impacts of forestland

allocation on agriculture and natural resource management in Bac Kan province,

Vietnam. In Castella, J. C., and Quang, D. D. Eds. Doi Moi in the mountains: Land

use changes and farmers’ livelihood strategies in Bac Kan province, Vietnam. The

Hanoi Publishing House. Hanoi, Vietnam. 197-220.

Conway, G. R. (1985). Agroecosystem analysis. Agricultural Administration 20: 31-55.

Dac, N. T. (2002). Policies for Development of Beef Cattle Production and Marketing in

Vietnam: issues and recommendations. In: ACIAR Project AS2/97/18. Profitable

beef cattle development in Vietnam. Sub-project 1: Beef marketing systems.

Dantsis, T., Douma, C., Giourga, C., Loumou, A., Polychronaki E. A. (2010). A

methodological approach to assess and compare the sustainability level of

agricultural plant production systems. Ecological Indicators 10: 256–263

De Haan, C., Steinfeld H., Blackburn H. (1996). Livestock & the environment: Finding a

balance. Report of Study by the Commission of the European Communities, the World

Bank and the governments of Denmark, France, Germany, The Netherlands,

United Kingdom and The United States of America.115p. Retrieved October 11,

2008: http://www.fao.org/docrep/x5303e/x5303e00.htm.

De Haan, C. (1995). Development support and livestock. In Wilson, R. T., Ehui, S. and

Mack, S. Eds. Livestock Development Strategies for Low Income Countries.

Proceedings of the Joint FAO/ILRI Roundtable on Livestock Development Strategies

for Low Income Countries, ILRI, Addis Ababa, Ethiopia, 27 February-02 March

1995. Food and Agriculture Organisation/International Livestock Research Institute,

Nairobi, Kenya. Retrieved October 10, 2006:

http://www.fao.org/wairdocs/ilri/x5462e/x5462e05.htm

Devendra, C., Thomas, D. (2002). Crop-animal systems in Asia: importance of livestock and

159characterisation of agro-ecological zones. Agricultural Systems 71: 5–15.

Dillon, J. L. and Hardaker, J. B. (1993). Farm management research for small farmer

development. Farm Systems Management Series 6. Food and Agriculture

Organisation of the United Nations, Rome. 145p.

Dixon, J., Gulliver, A. and Gibbon, D. (2001). Farming systems and poverty – Improving

farmers’ livelihoods in a changing world. Ed. Hall, M. FAO and World Bank. Rome

and Washington D.C. 412p.

Doppler, W., et. Al, (2002). Farming and Rural Systems Approaches. Published Lecturing

Material. University of Hohenheim. Germany.

Page 178: BEEF CATTLE SYSTEMS IN THE CONTEXT OF SUSTAINABLE ...bictel-fusagx.ulg.ac.be/ETD-db/collection/... · (2011). Beef cattle systems in the context of sustainable agriculture in Bac

160 Refferences

Dufhues, T., Lemke, T., Fischer, I. (2004). Constraints and potential of livestock insurance

schemes – A case study from Vietnam. Institute of Agricultural Economics and

Social Sciences in the Tropics and Subtropics (Ed.). Research in Development

Economics and Policy. Discussion Paper 5/2004. University of Hohenheim. F. u. T.

Müllerbader GmbH. Germany. 40p.

Dzung, N. T. (1996). Animal health improvement: a high priority for livestock development.

In Pryor, W. J. Ed. Exploring approaches to research in the animal sciences in

Vietnam. Aciar proceedings 68: 57-59.

Dzuc, T. (2003). The farm economy in Vietnam. The Gioi Publishers. Vietnam. 181p.

Eguienta, Y., Martin, C., Lecomte, P., Husson, O., Castella, J. C. (2002). Crop-livestock

interaction in Northern Vietnam: Issues, diversity of farmers’ responses, and

alternatives for sustainable integration of animals in upland agricultural systems. In

Castella, J. C., and Quang, D. D. Eds. Doi Moi in the mountains: Land use changes

and farmers’ livelihood strategies in Bac Kan province, Vietnam. The Hanoi

Publishing House. Hanoi. Vietnam. 221-247.

Eguienta, Y. (2000). Diagnostic des systèmes d’élevage bovo-bubalin dans une zone de

montagne au nord du Vietnam, District de Cho Don, Province de Bac Kan.

Unpublished. M.Sc. Thesis. Centre National d’Etudes Agronomiques des Régions

Chaudes (CNEARC), Montpellier, France. 107 p.

Ellis, F. (2000). Rural livelihoods and diversity in developing countries. Oxford University

Press. New York. 273p.

Epprecht, M. (2005). Geographic dimensions of livestock holdings in Vietnam: Spatial

relationships among poverty, infrastructure and the environment. Pro-poor Livestock

Initiative. PPLPI Working Paper. 24. FAO. Rome

FAO. (2010); Http://faostat.fao.org. Retrieved December 15, 2010.

FAO. (2006). Http://faostat.fao.org. Retrieved November 20, 2006.

FAO. (1999). Indicators for sustainable development of marine capture fisheries. FAO

Technical Guidelines for Responsible Fisheries. No. 8. Rome, FAO. 68p. Retrieved

October 15, 2010: hftp://ftp.fao.org/docrep/fao/004/x3307e/x3307e00.pdf

FAO (1989). Sustainable development and natural resource management. In: The state of

food and agriculture. FAO Agricultural series 22: 65-99.

Fox, P., Rockstroem, J., and Barron, J. (2005). Risk analysis and economic viability of water

harvesting for supplemental irrigation in semi-arid Burkina Faso and Kenya.

Agricultural Systems 83: 231-250.

Page 179: BEEF CATTLE SYSTEMS IN THE CONTEXT OF SUSTAINABLE ...bictel-fusagx.ulg.ac.be/ETD-db/collection/... · (2011). Beef cattle systems in the context of sustainable agriculture in Bac

Refferences 161

Francis, C. A., and Callaway, M. B. (1993). Crop improvement for future farming systems.

In: B. Callaway and C. A. Francis (Ed.) Crop Improvement for Sustainable

Agriculture. University of Nebraska Press, Lincoln. 1−18.

Friederichsen, J. R., Heidhues, F. (2000). Assessment of erosion control in farming systems

in northwest Vietnam: Results of an interdisciplinary study project. EC workshop on

sustainable rural development in the Southeast Asian mountainous region. Hanoi,

28-30 November 2000. Vietnam.

GAIN Report. (2006). Vietnam livestock and products annual report 2006. Number

VM6054. USDA Foreign Agricultural Service. Retrieved November 20, 2009:

http://www.fas.usda.gov/gainfiles/200609/146228906.pdf

Garcia, S. (1996). Indicators for Sustainable Development of Fisheries. Presented at the 2nd

World Fisheries Congress. Workshop on Fisheries Sustainability Indicators,

Brisbane, Australia, August, 1996. Retrieved November 20, 2010:

http://www.fao.org/docrep/w4745e/w4745e0f.htm#TopOfPage.

Gender in Agriculture (2009). Sourcebook. The World Bank, Food and Agriculture

Organisation, and International Fund for Agricultural Development.

General Statistic Office (GSO). (2010). Retrieved December 22, 2008 http://gso.gov.vn

General Statistic Office (GSO). (2008). Retrieved December 20, 2008 http://gso.gov.vn

General Statistic Office (GSO). (2007). Statistic of dairy population and milk production in

August 01, 2007. Retrieved April 6, 2011

http://www.dairyvietnam.org.vn/en/statistics.php?tkid=19&dmtk=9

General Statistic Office (GSO). (2006). Retrieve December, 20, 2006 http://gso.gov.vn.

General Statistic Office (GSO). (2005). Socio-economic statistical data of 64 provinces and

cities. Statistical Publishing House. Hanoi. Vietnam.

GESAMP (IMO/FAO/UNESCO-IOC/WMO/WHO/IAEA/UN/UNEP Joint Group of Experts

on the Scientific Aspects of Marine Environmental Protection). (2001). Planning and

management for sustainable coastal aquaculture development. Rep.Stud.GESAMP.

68: 90 p.

Giampietro, M, Mayumi, K, Munda, G. (2006). Integrated assessment and energy analysis:

Quality assurance in multi-criteria analysis of sustainability. Energy 31: 59–86.

Giampietro, M., Mayumi, K., Bukkens, S. G. F. (2001). Multiple-scale integrated

assessment of societal metabolism: an analytical tool to study development and

sustainability. Environment, Development And sustainability 3: 275–307.

Page 180: BEEF CATTLE SYSTEMS IN THE CONTEXT OF SUSTAINABLE ...bictel-fusagx.ulg.ac.be/ETD-db/collection/... · (2011). Beef cattle systems in the context of sustainable agriculture in Bac

162 Refferences

Godwin, D., Moore J.A. (1997). Manure management in small farm livestock operations –

protecting surface and ground water. Oregon State University. Retrieved April 4,

2011 from http://animalag.wsu.edu/water%20quality/Tab4em8649.pdf

Goldmana, A. Ramaswamib, S., Kriderc, R. E. (2002). Barriers to the advancement of

modern food retail formats: theory and measurement. Journal of Retailing 78: 281–

295

Gomiero, T. (2004). Multi-Objective Integrated Representation (MOIR): an innovative tool

for farming system analysis. PhD thesis. The programme in Environmental Sciences

– Universitat Authonoma de Barcelona, Bellaterra (Barcelona – Spain).

Gomiero, T. and Giampietro, M. (2001). Multiple-scale integrated analysis of farming

systems: The Thuong Lo commune (Vietnamese uplands) case study. Population and

Environment 22 (3): 315 -352.

Guijt, I., Moiseev, A., Prescott-Allen, R. (2001). IUCN Resource kit for sustainability

assessment. Part C: Slides for Facilitators. Based on the work of the IUCN/IDRC

Sustainability Assessment Team. IUCN Monitoring and Evaluation Initiative. IUCN,

Gland, Switzerland and Cambridge, UK. 92p. Retrieved April 9, 2010:

http://cmsdata.iucn.org/downloads/resource_kit_c_eng.pdf

Ha, D. T. and Shively, G. (2008), Coffee Boom, Coffee Bust and Smallholder Response in

Vietnam’s Central Highlands. Review of Development Economics, 12: 312–326

Haantuba, H. and de Graaf J. (2008). Linkages between smallholder farmers and

supermarkets: Lessons from Zambia. In: The transformation of agri-food systems:

globalization, supply chains and smallholder farmers, Eds. by McCullough, E.B.,

Pingali, P.L., Stamoulis, K.G. The Food and Agriculture Organisation of United

Nations and Earthscan. London. 207-226.

Hai, N. M. (2002). Changing comparative advantage of rice production under transformation

and trade liberalization: A Policy Analysis Matrix Study of Vietnam’s rice sector.

PhD. thesis. University of Hohenheim. Stuttgart. Germany.

HELVETAS (2000) Report of the Rapid Market Appraisal (RMA): Into Animal Products

Originating in Cao Bang Province. Helvetas. Hanoi, Vietnam. 49 p.

Hemme, T., Garcia, O., Nho, L. T., Tra, H. T. H. (2006). The Economics of Milk Production

in Hanoi, Vietnam, with Particular Emphasis on Small-Scale Producers. FAO-

PPLPI, Rome, Italy.

Hung, N. T., Binh, D. V. (2004). A survey on cattle production in households in M’Drak

district, Dak Lak province. Agricultural Science Journal 2(1). Hanoi. Vietnam.

Huy, N. L. (2008). The current situation and some recommendations to develop commercial

beef cattle stock in four upland districts of northern Ha Giang province. Vietnamese.

Journal of Agriculture and Rural Development 1, 49-56.

Page 181: BEEF CATTLE SYSTEMS IN THE CONTEXT OF SUSTAINABLE ...bictel-fusagx.ulg.ac.be/ETD-db/collection/... · (2011). Beef cattle systems in the context of sustainable agriculture in Bac

Refferences 163

Huyen L. T. T., Herold P. and Valle Zárate A. (2010). Farm types for beef production and

their economic success in a mountainous province of northern Vietnam. Agricultural

Systems, 103, 137–145.

Huyen, L. T. T. (2009). Suitability of different farm types for cattle development in northern

Vietnam. PhD thesis. Institute of Animal Production in the Tropics and Subtropics.

University of Hohenheim. Stuttgart. Germany.

Huyen, L. T. T, Herold, P. Valle Zárate A. (2008). Cattle performances and socio-economic

contribution in different farming systems in northern mountainous Vietnam. Institute

of Animal Production in the Tropics and Subtropics. University of Hohenheim.

Stuttgart. Germany. Poster in the Tropentag Conference in 2008.

Huyen. L. T. T., Lemke. U., Valle Zarate. A. (2006). Ruminant breeds and production

systems in northern Vietnam and their contribution on smallholder household in

mountainous areas. Verlag Ulrich E. Bauen. Stuttgart. Germany. 68p.

Huyen, N. T. T. (2004). The impact of animal production in mountainous farming systems

development in the northwest of Vietnam. PhD thesis. Hohenheim University. In

Doppler, W. and Bauer, S. Eds. Farming and rural systems economics 57. Margraf

Publishers GmbH. Germany.

Ibrahim H., Olaloku E. (2000). Improving cattle for milk, meat and traction. International

Livestock Research Institute (ILRI). ILRI Manual 4. Nairobi, Kenya. 135 p.

IFAD Cao Bang. (2007). A survey result about the cattle and buffalo value chain in Cao

Bang province. Consulting report of the Central for Agrarian System Research and

Development. Hanoi, Vietnam.

IFAD (2003). Promoting Market Access for the Rural Poor in Order to Achieve the

Millennium Development Goals. Roundtable Discussion Paper for the Twenty-Fifth

Anniversary Session of IFAD’s Governing Council. Rome, Italy.

ILCA (International Livestock Centre for Africa). (1990). Livestock systems research

manual. Working Paper 1, Vol. 1. ILCA, Addis Ababa, Ethiopia. 287p.

ILRI. (2003). Livestock, a pathway out of poverty: ILRI strategy to 2010. International

Livestock Research Institute, Nairobi. Retrieved June 6, 2007 from

http://www.ilri.org/Strategic/Strategy2010.pdf

Koopmans, A., Koppejan, J. (1997). Agricultural and forest residues – generation,

utilization and availability. Paper presented at the Regional Consultation on Modern

Applications of Biomass Energy, 6-10 January 1997, Kuala Lumpur, Malaysia.

Lan, D. N. (2005). Forest land allocation to households in northern Vietnam: Processes,

perception of the local people and the use of forestland. PhD thesis. University of

Hohenheim. Stuttgart. Germany.

Page 182: BEEF CATTLE SYSTEMS IN THE CONTEXT OF SUSTAINABLE ...bictel-fusagx.ulg.ac.be/ETD-db/collection/... · (2011). Beef cattle systems in the context of sustainable agriculture in Bac

164 Refferences

Lapar, M. L., Binh, V. T., Ehui, S. (2003). Identifying barriers to entry to livestock input and

output markets in Southeast Asia. Livestock sector report: Vietnam. 46p. Rome

(Italy) FAO. Retrieved May 12 2009:

http://www.fao.org/ag/againfo/resources/en/publications/sector_reports/lsr_VNM.pdf

Leech, N. L. Barrett, K. C., Morgan, G.A., Clay J. N. Quick, D. (2005). SPSS for

intermediate statistics: Use and interpretation. Lawrence Erlbaum Associates,

Publishers. Mahwah, New Jersey, London. 240p.

Lemke, U. (2006). Characterisation of smallholder pig production systems in mountainous

areas of north Vietnam. PhD thesis. Institute of Animal Production in the Tropics and

Subtropics. University of Hohenheim. Stuttgart. Germany.

Leng R. A. (1993). The impact of livestock development on environmental change. In:

Strategies for sustainable animal agriculture in developing countries, Mack S. (Ed.)

FAO Animal Production and Health Paper 107. Retrieved April 9, 2011:

http://www.fao.org/docrep/004/T0582E/T0582E09.htm

Lentes, P. (2003). The contribution of GIS and remote sensing to farming systems research

on micro- and regional scale in North West Vietnam. PhD thesis. In: Dopler, W. and

Bauer, S. (Eds). Farming and Rural System Economics, Vol. 52. Margraf Verlag,

Weikersheim. Germany.

Lewandowski, I., Härdtlein, M., Kaltschmitt, M., 1999. Sustainable crop production:

definition and methodological approach for assessing and implementing

sustainability. Crop Sci. 39: 184–193.

Liem, H. V., Toan, N. V., Perkins, J. (1999). Live cattle markets in Nghe An province. In:

ACIAR Project AS2/97/18. Profitable beef cattle development in Vietnam. Sub-

project 1: Beef marketing systems.

Livestock In Development (1999). Livestock in poverty-focused development. LID,

Crewkerne: Livestock In Development. UK. 95p.

Luthi, N.B., Fabozzi, L., Gutier, P., Trung, P.Q., Smith, D. (2006). Review, analysis and

dissemination of experiences in dairy production in Viet Nam. Pro-Poor Livestock

Policy Initiative – FAO. A living from livestock.

Ly. L. V. (1995). Beef cattle production and initial research achievements in Vietnam.

Agricultural Publishing House. Vietnamese. Hanoi, Vietnam.

Ly, L. V., Giao, H. K., Sanh, M. V. Su, V. V. and L. M. Sat. (1999). The local domestic

animal genetic resources and their conservation in Vietnam. Agricultural Publishing

House. Vietnamese. Hanoi, Vietnam.

Ly, L. V. (2002). The role of animal production in the farming systems of Vietnam. The

National Institute of Animal Husbandry. Hanoi, Vietnam. Retrieved 10 October 2006

from http://www.vcn.vnn.vn.

Page 183: BEEF CATTLE SYSTEMS IN THE CONTEXT OF SUSTAINABLE ...bictel-fusagx.ulg.ac.be/ETD-db/collection/... · (2011). Beef cattle systems in the context of sustainable agriculture in Bac

Refferences 165

Lynam, J. (1994). Sustainable growth in agricultural production: the links between

production, resources and research. In Goldswothy, P., de Vries, F. P. Eds.

Opportunities, use, and transfer of systems research methods in agriculture to

developing countries. Proceedings of an international workshop on systems research

methods in agriculture in developing countries, 22-24 November 1993, ISNAR. The

Hague. Systems approach for sustainable agricultural development series. 3-27.

Lynam, J.F. and Herdt, R.W. (1989). Sense and sustainability: Sustainability as an objective

in international agricultural research. Agric. Econ., 3: 38l-398.

Maltsoglou, I., Rapsomanikis, G. (2005). The contribution of livestock to household income

in Vietnam: A household typology-based analysis. Pro-poor Livestock Initiative.

PPLPI Working Paper 21. FAO. Rome

Maruyama, M. and Trung, L. V. (2007), Supermarkets in Vietnam: Opportunities and

Obstacles. Asian Economic Journal, 21: 19–46

Maruyama M. and Trung, L. V. (2006). A probit analysis of consumer shopping behaviour.

In: The Proceedings of Australian and New Zealand Marketing Academy Conference

2006. Retrieved 20 October 2010 from

http://smib.vuw.ac.nz:8081/WWW/ANZMAC2006/documents/Maruyama_Masayos

hi.pdf

McConnell. D. J., Dillon. J. L. (1997). Farm Management for Asia: a Systems Approach.

FAO Farm Systems Management Series – 13. FAO. Rome. Italy.

Meijer, M., Rodgriguez, I., Lundy, M. and Hellin, J., (2008). Supermarkets and small

farmers: the case of fresh vegetables in Honduras. In: McCullough, E.B., Pingali,

P.L. and Stamoulis, K.G., eds., The transformation of agri-food systems. FAO and

Earthscan, London. 333-353.

Ministry of Agriculture and Rural Development (MARD). (2009). Vietnamese. Hanoi,

Vietnam.

Ministry of Agriculture and Rural Development (MARD). (2008). Vietnamese. Hanoi,

Vietnam.

Ministry of Agriculture and Rural Development (MARD). (2006). Evaluation of beef cattle

production, development orientation in 2006-2010. Report of Department of

Livestock Production (DLP). Unpublished. Vietnamese. Hanoi, Vietnam.

Ministry of Agriculture and Rural Development (MARD). (2006b). Evaluation of dairy

cattle production subsector and its development orientation in 2006-2010 and 2015.

Report of Department of Livestock Production (DLP). Unpublished. Vietnamese.

Hanoi, Vietnam.

Page 184: BEEF CATTLE SYSTEMS IN THE CONTEXT OF SUSTAINABLE ...bictel-fusagx.ulg.ac.be/ETD-db/collection/... · (2011). Beef cattle systems in the context of sustainable agriculture in Bac

166 Refferences

Minot, N., Epprecht, M., Roland-Holst, D., Tram Anh, T., T., Trung, L. Q. (2003). Income

diversification and Poverty in the Northern Uplands of Vietnam: Patterns, Trends and

Implications. Research report 45. International Food Policy Research Institute

(IFPRI) and Japan Bank for International Cooperation (JBIC). 137p.

Morgan, G. A., Leech, N. L., Goeckner, G. W., Barrett, K. C., Clay J. N., Jensen, L., Quick

D. (2004). SPSS for introductory statistics – use and interpretation. Lawrence

Erlbaum Associates, Publishers. Mahwah, New Jersey, London. 211p.

Mui, N. T., Nho, L. T., Han, H. T., Huong, M. T. (2005). Assessing feed resources for

ruminants and starting to build grass production models in Dong Van district, Ha

Giang province. Vietnamese Journal of Agricultural and Rural Development. No. 5,

219-228. Vietnamese. Hanoi, Vietnam.

Mui, N. T. (2003). Country Pasture/Forage Resource Profiles: Vietnam. Department of

Pasture Research and Animal Feed Plant Resources. National Institute of Animal

Husbandry (NIAH), Hanoi, Vietnam. Retrieved September 30, 2006 from

http://www.fao.org/WAICENT/FAOINFO/AGRICULT/AGP/AGPC/doc/Counprof/v

ietnam/vietnam.htm

Neefjes, K., Thanh, H. X. (2003). Poverty reduction in the northern Mountains - a synthesis

of participatory poverty assessments in Lao Cai and Ha Giang provinces and regional

VHLSS data. Report supported by DFID and UNDP. 61p.

Ness, B., Urbel-Piirsalu, E., Anderberg, S., Olsson, L. (2007). Categorising tools for

sustainability assessment. Ecological Economics 60: 498 – 508.

Ngoan, L. D. and Giang, P. T. (2008). Actual situation of intensive beef cattle production in

small householder farms in Quang Ngai province. Journal of Livestock Production

and Technologies. No. 14. Accepted October, 2008. Vietnamese. Hanoi, Vietnam.

Nho, L. T., Mui, N. T., Nhi, D. L., Giang, D. H., Cuong, P. K. (2003). Assessing

development capacity of buffalo and cattle production in Ky Son district, Nghe An

province. In "Building development capacity of selection of replacement of opium

production in Ky Son - UNDCP Drug Control Program - AD/VIE/01/F21”.

Vietnamese. Hanoi, Vietnam.

Niem, N. V., Hoan, D. H., Khanh, L. C., and Con, D. X. (2001). Characteristics,

performance and development of Ha Giang Yellow cattle production in the northern

mountainous region. Scientific reports on animal husbandry and veterinary medicine

1999-2000. Agricultural Publishing House. Vietnamese. Hanoi, Vietnam, 92-104.

Nicholson, C. F., Blake, R. W., Urbina, C. I., Lee, D. R., Fox, D. G. and Van Soest, P. J.,

1994. Economic comparison of nutritional management strategies for Venezuelan

dual-purpose cattle systems. Journal of Animal Science. 72: 1680-1696.

Page 185: BEEF CATTLE SYSTEMS IN THE CONTEXT OF SUSTAINABLE ...bictel-fusagx.ulg.ac.be/ETD-db/collection/... · (2011). Beef cattle systems in the context of sustainable agriculture in Bac

Refferences 167

Noi, V. V., Cuong, V. C., Cuong, P. K. (1995b). Mortality rate from 0-12 months and

contamination rate of some parasitology of crossbreeding beef calves in Central

Coast and Central Highlands. In Ly L. V. Ed. Beef cattle production and the initial

research achievements in Vietnam. Agricultural Publishing House. Vietnamese.

Hanoi, Vietnam. 78-81.

Ogle B., Phuc, B. H. N. (1997). Sustainable intensive livestock-based systems in Vietnam.

IRD Current 14: 16-22

Okigbo, B. N. (1991). Development of sustainable agricultural production systems in Africa:

Role of international agricultural research centres and national agricultural research

systems. Distinguished African Scientist Lecture Series No. 1. International Institute

of Tropical Agriculture (IITA). Ibadan. Nigeria

Olesen, I., Groen, A. F., Gjerde, B. (2000). Definition of animal breeding goals for

sustainable production systems. J. Anim. Sci. 78: 570–582.

Pac Nam Annual Report. (2007). Unpublished. Bac Kan, Vietnam

Pac Nam District Statistical Office - DSO (2008). Unpublished. Bac Kan, Vietnam

Pac Nam People’s Committee Report (2006). Unpublished. Bac Kan, Vietnam

Payraudeau, S., van der Werf, H. M.G. (2005). Environmental impact assessment for a

farming region: a review of methods. Agriculture, Ecosystems and Environment. 10:

1–19

Perkins, J. (2002). Profitable beef cattle development in Vietnam. ACIAR - Project Review

and Final Workshop on 13-15 May 2002. Hanoi, Vietnam.

Petheram, R. J. (1996). Farming system research (FSR): a brief review and example. In

Pryor, W. J. Ed. Exploring Approaches to Research in the Animal Sciences in

Vietnam. ACIAR Proceedings No. 68. Hue University, Vietnam, 31 July - 3 August

1995. 36-44.

Philipes, C.J.C, Tind Sorensen, J. (1993). Sustainability in Cattle Production Systems.

Journal of Agricultural and Environmental Ethics, 6(1): 61-73

Phung, L. D., Koops, W. J. (2003). The impact of crossbred cattle (Red Sindhi x Yellow

local) on smallholder households in the mountainous and lowland zones of Quang

Ngai, Vietnam. Asian-Aust. J. Anim. Sci. 16(9): 1390 – 1396.

Phung, L. D. (2001). A system analysis of the use of Local Yellow and F1 (Red Sindhi x

Yellow Local) cattle by households in the mountainous and lowland zones in Quang

Ngai, Vietnam. MSc thesis. Wageningen University, Wageningen, Netherlands.

Phuong, H. A. (2009). Factors affecting market participation of smallholder beef cattle

producers in rural areas - Case study in Hanh Phuoc commune, Nghia Hanh district,

Quang Ngai province. Master Thesis. No. 44. Swedish University of Agricultural

Sciences.

Page 186: BEEF CATTLE SYSTEMS IN THE CONTEXT OF SUSTAINABLE ...bictel-fusagx.ulg.ac.be/ETD-db/collection/... · (2011). Beef cattle systems in the context of sustainable agriculture in Bac

168 Refferences

Pingali, P. (2006). Westernization of Asian diets and the transformation of food systems:

implications for research and policy. Food Policy 32: 281-298.

Pro-Poor Livestock Policy Initiative (PPLPI)-Policy brief. (2004). Policy issues in livestock

development and poverty alleviation. Retrieved 08/2009 from

http://www.fao.org/ag/againfo/programmes/en/pplpi/docarc/pb_wp10.pdf

Quan, H. M. (2001). Applying major economic and technical solutions in development of

cattle production in households in Quang Binh province. PhD thesis. Agricultural

University No. 1. Hanoi, Vietnam. Vietnamese.

Quang Ngai Rural Development Programme (QNRDP) Phase 1. (2002). First report of the

marketing specialist. Prepared for AusAID by URS Sustainable Development in

association with Brown and Root and World Wide project management services,

Australia. Retrieved September 27, 2009 from http://www.rudep.org/Doc/1125-

1st%20Marketing%20Specialist%20Report.pdf

Rachmat, R., Stür, W.W. and Graeme J. Blair. (1992). Cattle feeding systems and limitations

to feed supply in South Sulawesi, Indonesia. Agricultural Systems 39: 409-419.

Rasul, G. and Thapa, G. B. (2004). Sustainability of ecological and conventional agricultural

systems in Bangladesh: an assessment based on environmental, economic and social

perspectives. Agricultural Systems 79: 327–351

Reardon, T., Timmer, C.P., Berdegue, J. (2008). The rapid rise of supermarkets in

developing countries: Induced organisational, institutional and technological change

in agro-food systems. In: The transformation of agri-food systems: globalization,

supply chains and smallholder farmers, Eds. by McCullough, E.B., Pingali, P.L.,

Stamoulis, K.G. The Food and Agriculture Organisation of United Nations and

Earthscan. London. 47-66.

Reardon, T., Henson, S. and Berdegué, J., (2007). Proactive fast-tracking, diffusion of

supermarkets in developing countries: implications for market institutions and trade.

Journal of Economic Geography 7: 399–431.

Rodrigues, G. S., Campanhola, C., Kitamura, P.C. (2003). An environmental impact

assessment system for agricultural R&D. Environ. Impact Assess. Rev. 23(2): 219–

244.

Schillhorn van Veen, T.W. (1999). Agricultural policy and sustainable livestock

development. International Journal for Parasitology 29, 7- 15

Schipmann, C. (2010). The food system transformation in developing countries:

opportunities and challenges for smallholder farmers in Thailand. PhD thesis. Georg-

August-Universität Göttingen, Germany.

Page 187: BEEF CATTLE SYSTEMS IN THE CONTEXT OF SUSTAINABLE ...bictel-fusagx.ulg.ac.be/ETD-db/collection/... · (2011). Beef cattle systems in the context of sustainable agriculture in Bac

Refferences 169

Sen, L. T. H. (2005). Soil conservation and sustainable agriculture: A case study of the

coastal region of Quang Tri province, Vietnam. PhD thesis. In Doppler, W. and

Bauer, S. Eds. Farming and Rural System Economics 76. Margraff Publishers.

Germany.

Seré, C., Steinfeld, H. (1996). World livestock production systems - Current status, issues

and trends. FAO Animal Production And Health Paper. Publication of the LEAD

Livestock & Environment Toolbox No. 127. 46p.

Siegmund-Schultze, M., Rischkowsky B., da Veiga J.B., King, J.M. (2010). Valuing cattle

on mixed smallholdings in the Eastern Amazon. Ecological Economics 69: 857–867

Skunmun, P., Poondusit, T., Koga, A., Chantalakhana, C. (2001). Changes of cattle and

buffalo production in village farming systems and their long-term impacts on buffalo

raising. In Proceedings of National Workshop on Swamp Buffalo Development.

Hanoi, Vietnam, 17-18th

December 2001.

Smith, D., Tra, H. T. H. (2008). Market assessment for free ranging chicken products in

Hanoi. Unpublished. Submitted to The STOP AI Project - USAID. Hanoi, Vietnam.

Smith, D. (2001). Chinese live cattle and beef marketing and distribution systems. PhD

Thesis. School of Natural and Rural Systems Management. The University of

Queensland, St. Lucia, Australia.

Sommer, S. G., A. Dalsgaard, A. Roepstorf, L. S. Jensen, J. Luxhøi, T. S. Tran, M. T.

Tran,T. H. Tran, T. T. S. Dang, C. C. Vu, T. K. V. Vu. (2008). Livestock production,

manure management and plant nutrient recycling on animal farms in Vietnam.

Retrieved April 5, 2011 from

http://susane.info/en/home/detail.asp?iData=966&nChannel=News

Squire, L., van der Tak, H. G. (1975). Economic analysis of projects. A World Bank research

publication. The John Hopkins University Press. Baltimore and London. 153p.

Steinfield, H., Mack, S. (1997). Livestock development strategies. World Animal Review. 88:

18-24.

Steinfeld, H. and Mäki-Hokkonen, J. (1995). A classification of livestock production

systems. FAO. Retrieved April 7, 2006

http://www.fao.org/documents/show_cdr.asp?url_file=/DOCREP/V8180T/v8180T0y

.htm

Sydorovych, O. and Wossink, A. (2008). The meaning of agricultural sustainability:

Evidence from a conjoint choice survey. Agricultural Systems 98: 10–20

Tai, D. A. (2004). Family resources and their impact on living standard and food security of

farmers in the mountainous farming systems in northwest Vietnam. PhD thesis.

Agricultural University of Hohenheim. Eds. Doppler, W. and Bauer, S. Farming and

rural systems economics 54. Margraf Publishers GmbH. Germany.

Page 188: BEEF CATTLE SYSTEMS IN THE CONTEXT OF SUSTAINABLE ...bictel-fusagx.ulg.ac.be/ETD-db/collection/... · (2011). Beef cattle systems in the context of sustainable agriculture in Bac

170 Refferences

Tang, L. V. (2007). Personal communication. Director of the Department of Veterinary of

the Son La province.

Taylor, D. F. (2001). Employment-based analysis: an alternative methodology for project

evaluation in developing regions, with an application to agriculture in Yucatán.

Ecological Economics. 36: 249-262.

The Comprehensive Poverty Reduction and Growth Strategies – CPRGS. (2003). Vietnam.

Thomas, D., Zerbini, E., Rao, P. P., Vaidyanathan, A. (2002). Increasing animal productivity

on small mixed farms in South Asia: a systems perspective. Agricultural Systems 71:

41–57.

Thompson, P.B., and Nardone, A. (1999). Sustainable livestock production: methodological

and ethical challenges. Livestock Production Science 61: 111–119

Thuong, N. V., Ly, L. V., Noi, V. V., Dat, N. Q., Niem, N. V., Oanh, N. K. Cuong, P. K.,

Ho, V. P. (1995). Study of technologal approaches to improve meat performance of

cattle herds in Vietnam. In Ly L. V. Ed. Beef cattle production and the initial

research achievements in Vietnam. Agricultural Publishing House. Hanoi. 45-53.

Timon, V.M. (1993). Strategies for sustainable development of animal agriculture - an FAO

perspective. In: Strategies for sustainable animal agriculture in developing countries,

Mack S. (Ed.) FAO Animal Production and Health Paper 107. Retrieved April 09

2011: http://www.fao.org/docrep/004/T0582E/T0582E05.htm

Tisdell, C. (2010). An Economic Study of Small-scale Hog Growers in Vietnam: Some

Insights Gained and the Scope for Further Research. Working Paper No. 61. Working

Papers in the Series, Economic Theory, Applications and Issues, are published by the

School of Economics, University of Queensland, Australia.

Tisdell, C. (1996). Economic indicators to assess the sustainable conservation of farming

projects: An evaluation. Agriculture, Ecosystems and Environment 57: 117- 131.

Tra, H. T. H. (2009). Needs assessment of climate change – adaptation and mitigation. A

case study in Bac Kan province. Report submitted to Centre for Sustainable Rural

Development (SRD), Vietnam and Bread for the World (BftW), Vietnam.

Tra, H. T. H. (2007). Assessing failure and perspective development of crossbreeding cattle

in the northern mountainous region of Vietnam. A study in Bac Kan province. DEA

thesis. Department of Economics and Rural Development. Gembloux Agricultural

University. Belgium.

Tra, H. T. H. (2003) Assessing inputs in pig production with special focus on feed resources

and feeding management in resource and demand-driven pig production systems in

Son La province, Vietnam. Master thesis. Hohenheim University. Germany.

Page 189: BEEF CATTLE SYSTEMS IN THE CONTEXT OF SUSTAINABLE ...bictel-fusagx.ulg.ac.be/ETD-db/collection/... · (2011). Beef cattle systems in the context of sustainable agriculture in Bac

Refferences 171

Trach, N. X. (2002). Possible consequences of inappropriate intensification of animal

production in Vietnam and approaches to avoid. In 2010 trends of animal production

in Vietnam. Proceedings of the workshop organised by NIAH and CIRAD. Hanoi.

October 24-25. PRISE publications. Hanoi, Vietnam. 35-44.

Tung, D. X., et al. (2009). A survey on structure, performance, efficiency, and mode and

organisation of cattle, buffalo and pig production. Vietnamese. Unpublished.

Submitted to Department of Livestock Production, Ministry of Agriculture and Rural

Development (MARD). Vietnamese. Hanoi, Vietnam.

Tung, D. X., Giang, D. H. (2008). Assessing factors influencing economic-technological

efficiency and comparative advantage of beef cattle production in Vietnam.

Vietnamese. Unpublished Research Report. National Institute of Animal Sciences.

Vietnamese. Hanoi, Vietnam.

Tung, D. X., Thanh, N. D., Duc, D. V., Quoc, N. V., Q. M. T., Thuy, T. P. T., Loan, N. T.

(2007). Assessing economic efficiency in beef cattle production in four agro-ecology

regions in northern Vietnam. Vietnamese. Presented at the annual workshop

organised by the National Institute of Animal Sciences. Vietnamese. Hanoi, Vietnam.

Udo, H. M. J., Koops, W. J, Cornelissen, T., Steenstra, F. (1998). Analysis of livestock

systems. Lecture notes. Animal Production Systems Group. Wageningen Agricultural

University.

United Nations (UN) (1997). Agenda for Development.

http://www.un.org/Docs/SG/ag_index.htm

Van Cauwenbergh N., Biala K., Bielders C., Brouckaert V., Franchois L., Garcia Cidad V.,

Hermy M., Mathijs E., Muys B., Reijnders J., Sauvenier X., Valckx J., Vanclooster

M., Van der Veken B., Wauters E., Peeters A. (2007). SAFE—A hierarchical

framework for assessing the sustainability of agricultural systems. Agriculture,

Ecosystems and Environment 120: 229–242

Van de Walle, D., Gunewardena, D. (2001). Sources of ethnic inequality in Vietnam.

Journal of Development Economics 65: 177–207.

Van, P. T., Loan, N. T., Quoc, N. V. (2005). Assessing the situation and efficiency of cattle,

buffalo and pig production in smallholder farms in Mai Son, Pac Nam and Dong Van

districts. Vietnamese. In Annual Proceeding of a Science Workshop held by National

Institute of Animal Husbandry. Hanoi, Vietnam.

Vien, T. D. (2003). Culture, environment, and farming systems in Vietnam's northern

mountain region. Southeast Asia Studies. 41(2): 180-205.

Vietnam Development Report 2004 (VDR). (2003). Poverty. Joint donor report to the

Vietnam consultative group meeting. Hanoi. December 2003.

World Commission on Environment and Development (WCED) (1987). Our Common

Future. Brundtland Commission Report. Geneva.

Page 190: BEEF CATTLE SYSTEMS IN THE CONTEXT OF SUSTAINABLE ...bictel-fusagx.ulg.ac.be/ETD-db/collection/... · (2011). Beef cattle systems in the context of sustainable agriculture in Bac

172 Refferences

Zaved A., Sadaf, S., Luqman, M. (2004). Rural Women’s Participation in Crop and

Livestock Production Activities in Faisalabad, Pakistan. Journal of Agriculture &

Social Sciences. 2(3): 150–154.

Zeller, M., Lapenu, C., Minten, B., Ralison, E., Randrianaivo, D., Randrianarisoa, C. (2000).

Pathways of rural development in Madagascar: An empirical investigation of the

critical triangle of environmental sustainability, economic growth and poverty

alleviation. FCND discussion Paper 82. International Food Policy Research Institute.

Washington DC. USA.

Page 191: BEEF CATTLE SYSTEMS IN THE CONTEXT OF SUSTAINABLE ...bictel-fusagx.ulg.ac.be/ETD-db/collection/... · (2011). Beef cattle systems in the context of sustainable agriculture in Bac

7 ANNEXES

Annex 1: Development trend of beef production in Vietnam and the NMR

Source: FAO, 2010; GSO, 2010;

Annex 2: Development trend of imported beef products in Vietnam

Source: General Department of Vietnam Customs, 2010;

0

50

100

150

200

250

0

1000

2000

3000

4000

5000

6000

7000

1995 1996 1997 1998 1999 2000 2001 2002 2003 2004 2005 2006 2007 2008 2009

Ca

ttle

mea

t p

rod

uct

ion

(th

ou

san

d t

on

s)

Ca

ttle

po

pu

lati

on

(T

ho

usa

nd

hea

d)

Cattle Cattle herd size in the NMR Cattle meat

0

2

4

6

8

10

12

0

500

1000

1500

2000

2500

2000 2001 2002 2003 2004 2005 2006 2007 2008 2009

Imp

ort

ed c

att

le m

eat

va

lue

(mil

. U

SD

)

Imp

ort

ed c

att

le m

eat

am

ou

nt

(to

nn

es)

Amount (tonnes)

Value (mil. USD)

Page 192: BEEF CATTLE SYSTEMS IN THE CONTEXT OF SUSTAINABLE ...bictel-fusagx.ulg.ac.be/ETD-db/collection/... · (2011). Beef cattle systems in the context of sustainable agriculture in Bac

174 Annexes

Annex 3: Beef price in Hanoi markets during 2001-2009

Source: The Government Pricing Committee, 2010 and The Vietnam Economic News, 2010

Annex 4: Reproductive performance of cattle and buffalo species

Indicators

Cattle (N = 94) Buffalo (N = 28) Sig.

M Range M Range

Calving interval (months) 16.3 12.0 – 26.0 22.0 12.0 – 36.0 0.000

Age at first calving (year) 3.5 3.0 – 5.0 4.5 4.0 – 6.0 0.000

Source: Household interview 2007-2008

Annex 5: Livestock net income analysis depending on farm land size classification

Indicators

Small farm size Medium farm size Large farm size

Sig. M Range M Range M Range

Total livestock

revenue (mil. VND)

15.8a -4.9 – 34.5 18.6

ab 3.4 – 47.1 24.4

b 6.3 – 54.6 0.005

Total livestock costs

(mil. VND)

5.8 0.7 – 17.6 8.5b 1.5 – 30.0 11.3

b 3.0 – 33.1 0.001

Livestock net income

(NI) (mil. VND)

10.0 -19.1 – 28.7 10.1 -1.2 –

31.2

13.1 -2.5 – 32.6 0.259

Livestock

NI/investment costs

(times)

2.7a -1.4 – 14.4 1.5

b -0.3 – 4.7 1.7

b -0.3 – 6.1 0.012

NI/land unit (mil.

VND)

1.1a -1.7 – 3.7 0.5

b 0.1 – 1.7 0.4

b -0.1 – 0.8 0.000

NI/labour day (1,000

VND)

24.1 -120.4 – 99.4 25.6 -3.2 –

89.7

34.8 -6.4 – 112.7 0.276

Source: Household interview 2007-2008 a, b

within a row not sharing the same superscript letter (p< 0.05).

If all samples are normally distributed with equal variances, ANOVA is used. If both conditions are not met, the

Kruskal Wallis and Mann-Whitney Tests are used.

Page 193: BEEF CATTLE SYSTEMS IN THE CONTEXT OF SUSTAINABLE ...bictel-fusagx.ulg.ac.be/ETD-db/collection/... · (2011). Beef cattle systems in the context of sustainable agriculture in Bac

Annexes 175

Annex 6: Analysis of livestock net income in selected systems in the study area in 2007

Indicators

Free-range Part-time grazing Cut-and-carry

Sig. M Range M Range M Range

Total livestock

revenue (mil. VND)

21.3 -4.9 – 54.6 17.5 3.4 – 47.1 17.8 3.6 – 34.7 0.286

Total livestock costs

(mil. VND)

8.3 2.8 – 33.1 8.8 0.8 – 30.0 6.8 0.7 – 15.7 0.625

Livestock net income

(NI) (mil. VND)

13.0 -19.1 – 32.6 8.7 -2.5 –

21.9

11.0 0.8 – 28.7 0.077

NI/investment costs

(times)

2.2 -1.4 – 6.1 1.6 -0.3 – 9.9 2.4 0.1 – 14.4 0.069

NI/land unit (mil.

VND)

0.8 -1.7 – 2.9 0.5 -0.6 – 2.0 0.9 -0.2 – 3.7 0.144

NI/labour day (1,000

VND)

40.8a -120.3 –

112.7

20.6b -6.4 –

61.6

21.5b 0.9 – 31.9 0.002

Source: Household interview 2007-2008 a, b

within a row not sharing the same superscript letter (P < 0.05).

If all samples are normally distributed with equal variances, ANOVA is used. If both conditions are not met, the

Kruskal Wallis and Mann-Whitney Tests are used.

Annex 7: List of key persons interviewed in cattle value chain in Bac Kan province

Name Minority Working areas Address

1 Dinh Van Chan Kinh Middleman Nghien Loan, Pac Nam

2 La Van Thach Tay Middleman Nghien Loan, Pac Nam

3 Nong Van Vinh Tay Middleman Nghien Loan, Pac Nam

4 Nong Van Thanh Tay Middleman Nghien Loan, Pac Nam

5 Nguyen Van Thong Kinh Middleman Thai Nguyen

6 Nong Van Vang H’Mong Retailer Nghien Loan, Pac Nam

7 Ly Van Han Dao Retailer Nghien Loan, Pac Nam

8 Dang Van Ve Tay Retailer Nghien Loan, Pac Nam

9 Vu A Giang H’Mong Retailer Cong Bang, Pac Nam

10 Hoang Van Lenh H’Mong Retailer Nghien Loan-Pac Nam

11 Nguyen Quoc Tuan Kinh Slaughterhouse Dong Anh, Hanoi

12 Nguyen Huu Bang Kinh Slaughterhouse Dong Anh, Hanoi

13 Nguyen Nang Hien Kinh Slaughterhouse Dong Anh District

14 Nguyen Thi He Kinh Wholesaler Dong Anh District

15 Dong Thi That Kinh Wholesaler Dong Anh District

16 Nguyen Van Hung Kinh Wholesaler Dong Anh District

17 Nguyen Thi Soi Kinh Wholesaler Tu Liem District, Hanoi

18 Ma Van Lanh Tay Slaughterhouse/ Retailer Ba Be district, Bac Kan

19 Nguyen Thi Nga Kinh Slaughterhouse/ Retailer Pac Nam district, Bac Kan

20 Nguyen Thi Nga Kinh Beef retailer Tu Liem District, Hanoi

21 Tran Thi Nga Kinh Beef retailer Cau Giay district, Hanoi

22 Nguyen Van Khai Kinh Beef retailer Thanh Xuan district, Hanoi

Page 194: BEEF CATTLE SYSTEMS IN THE CONTEXT OF SUSTAINABLE ...bictel-fusagx.ulg.ac.be/ETD-db/collection/... · (2011). Beef cattle systems in the context of sustainable agriculture in Bac

176 Annexes

Annex 8: Amount of manure from livestock production used for crop production in

selected households

Indicators

Free-range Part-time grazing Cut-and-carry

Sig. M Range M Range M Range

Livestock manure used

(tonnes/ha of crop land) 1.9

a 0.0 – 11.7 2.1

a 0.0 – 6.7 1.2

b 0.0 – 6.6 0.007

Source: Household interview 2007-2008 a, b

within a row not sharing the same superscript letter (p< 0.05).

If all samples are normally distributed with equal variances, ANOVA is used. If both conditions are not met, the

Kruskal Wallis and Mann-Whitney Tests are used.

Annex 9: Pictures of cattle breeds in selected H’Mong households

Page 195: BEEF CATTLE SYSTEMS IN THE CONTEXT OF SUSTAINABLE ...bictel-fusagx.ulg.ac.be/ETD-db/collection/... · (2011). Beef cattle systems in the context of sustainable agriculture in Bac

Annexes 177

Annex 10: Pictures of cattle breeds in selected Tay households

Annex 11: Pictures of selected households practising the cut-and-carry system

H’Mong people habitats in the uplands and their homemade hydroelectricity

Page 196: BEEF CATTLE SYSTEMS IN THE CONTEXT OF SUSTAINABLE ...bictel-fusagx.ulg.ac.be/ETD-db/collection/... · (2011). Beef cattle systems in the context of sustainable agriculture in Bac

178 Annexes

Confinement of bulls for fattening by H’Mong households practising the cut-and-carry system

Cattle shed styles and hygiene conditions in the cut-and-carry system

Hygiene conditions next to living areas of H’Mong households in the cut-and-carry system

Page 197: BEEF CATTLE SYSTEMS IN THE CONTEXT OF SUSTAINABLE ...bictel-fusagx.ulg.ac.be/ETD-db/collection/... · (2011). Beef cattle systems in the context of sustainable agriculture in Bac

Annexes 179

Grass production during cropping season and winter season in the uplands, cut-and-carry

system

Grazing areas of cattle in the cut-and-carry system

Annex 12: Pictures of cattle shelters used in the part-time grazing system

Page 198: BEEF CATTLE SYSTEMS IN THE CONTEXT OF SUSTAINABLE ...bictel-fusagx.ulg.ac.be/ETD-db/collection/... · (2011). Beef cattle systems in the context of sustainable agriculture in Bac

180 Annexes

Cattle shelter styles and hygiene conditions in the part-time grazing system

Cattle grazing in natural pasture and grass production in the part-time grazing system

Annex 13: Pictures of cattle sheds in the free-range system

Page 199: BEEF CATTLE SYSTEMS IN THE CONTEXT OF SUSTAINABLE ...bictel-fusagx.ulg.ac.be/ETD-db/collection/... · (2011). Beef cattle systems in the context of sustainable agriculture in Bac

Annexes 181

Cattle shelter styles under Tay houses and the poor hygiene conditions in the free-range system

Grazing areas in a winter season and grass production in the free-range system

Poor hygiene conditions next to housing in the free-range system and burning of rice straw after

harvest

Page 200: BEEF CATTLE SYSTEMS IN THE CONTEXT OF SUSTAINABLE ...bictel-fusagx.ulg.ac.be/ETD-db/collection/... · (2011). Beef cattle systems in the context of sustainable agriculture in Bac

182 Annexes

Annex 14: Cattle markets on the study sites

Nghien Loan wholesale cattle market on an off-

season day

Partial view of the Cong Bang cattle market

Annex 15: Transportation of cattle from markets

Hired labour moving cattle from the market

to the area where middlemen gather

Transporting live cattle to the slaughterhouse

Page 201: BEEF CATTLE SYSTEMS IN THE CONTEXT OF SUSTAINABLE ...bictel-fusagx.ulg.ac.be/ETD-db/collection/... · (2011). Beef cattle systems in the context of sustainable agriculture in Bac

STATEMENT OF ORIGINALITY

I declare that the work presented in this dissertation is, to the best of my knowledge and

belief, original and my own work, except as acknowledged in the text, and that the material

has not been submitted either in whole or in part for a degree at this or any other university.

Hoang Thi Huong Tra

Date: 28 November 2011