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Making upland resource managers more receptive to “downstream friendly” practices through
compensation
Chapika SANGKAPITUX1, Andreas NEEF 2, Ke NANTHASEN1 and Nongkran PRAMOON1
1Department of Agricultural Economics, Chiang Mai University2 The Uplands Program (SFB 564), University of Hohenheim
Jointly funded by National Research Council of Thailand (NRCT)
and German Research Foundation (DFG)
International Symposium “Interdependencies between upland and lowlandagriculture and resource management”, Stuttgart-Hohenheim, 1-4 April 2008
1. Problem statement
2. Methodology/Study area
3. Downstream: Willingness to pay for upstream
water resource improvement
4. Upstream: Willingness to accept compensation
for downstream-friendly practices
5. Conclusion and policy implications
Outline
Problem statement
• External effects on downstream area
Water quality contamination due to erosionand agrochemical leaching
Water shortage in dry season
• Development of upstream agriculturetowards cash crop economy
Excessive use of agro-chemicals
Dry-season irrigation
Erosion-prone practices
Problem statement
• Proposed solution by policy-makers/scientistsConversion to agricultural conservation practices• to plant vetiver grass for erosion control• to adopt water saving technologies • to apply bio-insecticides and organic fertilizers
instead of agro-chemicals
What is their willingness to pay?
Effect on downstream people: obtain better water resources
Effect on upstream people: increases costs and risk of production What compensation would they accept?
Downstream communities as
Beneficiaries
Upstream Communities as
Service Providers
Choice Experiments Method:Willingness to accept
compensation for agricultural conservation adoption
Choice Experiments Method:Willingness to pay for water
resource improvement
Flow of services and
Flow of fund
Flow of FundFlow of services
Methodology
Methodology
• Choice Experiments (CE) to estimate downstreamfarmers’ WTP and upstream farmers’ WTA usingConditional Logit Model
• Tobit model to investigate factors determiningfarmers’ willingness to adopt “downstreamfriendly” practices through compensation
• Household samples: 166 for upstream area and151 for downstream area
Study Area
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Mae Sa Watershed, Chiang Mai Province
Upstream
Downstream
Northern Thailand
Socio-Economic Characteristics Average
Age (years) 57.43
Education (years) 5.05
Farm size (rai/household) 6.2
Agricultural income from rice and soybean (baht/hh/year) 38,754
Non-agricultural income (baht/hh/year) 133,452
Background Data: Downstream Farmers
1 rai = 0.16 ha1 EUR = 48 Baht
Water source Household consumption
Drinking and cooking
Agriculture
Community water piping system 118 (78%) 38 (14%) -
Pond 24 (16%) 21 (25%) -
Ground water 9 (6%) 5 (3%) -
Bottled water - 87 (58%) -
Mae Sa - - 71 (37%)
Mae Sa and Mae Tang irrigation - - 12 (63%)
Water Sources
Attributes and Levels for Choice Experiments
Attribute Level
Water for agriculture Level 1: No water shortageLevel 2: 1 month shortageLevel 3: 2 months shortage (status quo)
Water for household consumption
Level 1: No water shortageLevel 2: 1 month shortageLevel 3: 2 months shortage (status quo)
Water quality Level 1: Drinking and cookingLevel 2: Household useLevel 3: Cultivation (status quo)
Water fee (baht/HH/year) 375, 290, 150
Downstream farmers’ willingness to payfor water resource improvements
Model output
Attribute Coefficient t-statistics
Marginal willingness to pay (baht/household/year)
Sufficient water quantity for cultivation (no water shortage) 0.7462 9.46*** 324
Sufficient water quantity for household consumption (no water shortage)
0.4940 5.29*** 215
Good water quality for consumption 0.7763 6.10*** 338
Good water quality for household use 0.1710 3.36*** 74
Water fee -0.0023 -2.31**
Factors determining downstream farmers’willingness to pay for water resource improvement
Positive effect: past drought experience, farm size, participation in environmental activities, buying bottled water for consumption
Negative effect: non-agricultural income, access to other water sources for agriculture
Attitude toward Conservation Practices
Conservation practicesPractice ranked as
most effectiveNo. of hh (%)
Water quality:
• application of bio-insecticides• reforestation and forest conservation at community level• planting Vetiver grass for erosion control
58 (38.4)54 (35.8)39 (25.8)
Water quantity:
• reforestation and forest conservation at community level• installation of drip irrigation system• installation of micro sprinkler
67 (44.4)49 (32.5)35 (23.2)
Village No. of sample hh
Major crops Average per capita income(baht/year)
No. of family members
Farm size(rai)
Ethnicity
Pha Nok Kok 37 Fruit 5%Flower 8%Vegetable 84%
24,944 5 7.24 Hmong
Buak Chan 29 Vegetable 72% 11,141 10 12.43 Hmong
Mae Sa Mai 50 Fruit 16% Vegetable 74%
13,166 7 9.46 Hmong
Muang Kum 50 Flower 22%Vegetable 74%
42,194 4 2.44 Northern Thai
Upstream: Basic data
Attribute Level
Application of bio-insecticides (% increase of area)30, 50, 70, 100
Planting vetiver grass (% increase of area)10, 20, 30, 40
Installation of water saving irrigation system
50% Micro sprinkler, 100% Micro sprinkler, 50% Drip irrigation ,100% Drip irrigation
Compensation (baht/rai/year)300, 546, 1010, 1717
Attributes and Levels for Choice Experiments
Upstream farmers’ willingness to acceptcompensation for “downstream friendly” practices
Model output
AttributeCoefficient t-statistics
Marginal willingnessto accept
(baht/household/year)
Application of bio-insecticides -0.0024 -1.713* 10
Planting Vetiver grass -0.0064 -1.764* 27
Installation of water saving irrigation system (50% of area under microsprinkler)
0.2530 3.631** -
Compensation 0.00024 2.653**
Upstream Farmers: Willingness-to-Accept Compensation
Upstream farmers would be willing to accept compensation
• at the rate of around 10 baht/rai/year per 1% areaincrease under application of bio-insecticides
• at the rate of around 27 baht/rai/year per 1% areaincrease under erosion control with vetiver grass
No compensation is needed to adopt micro-sprinklers on 50% of the area
Factors determining farmers’ willingness to adopt “downstream friendly” practices
• Resource tenure security: higher probability to adopt “downstream friendly” practices is found among farmers with low tenure security
• Soil erosion and water scarcity: higher probability to adopt “downstream friendly” practices is found among farmers who have faced problems of soil erosion and water scarcity in the past
• Ratio of agr.-income/total income: higher probability to adopt “downstream friendly” practices is found among farmers with high ratio of agr.-income/total income
Conclusion and Policy Implications• There is a clear potential for establishing compensation
schemes for provision of environmental services in northernThai watersheds
policy-makers need to move from ineffective command-and-control towards incentive-based approaches
• The important policy implication is to get both upstreamand downstream resource managers involved
policy-makers need to revise their exclusive focuson ‘fixing uplanders’ resource management practices’downstream beneficiaries should/are willing to contributeto sustaining the services provided by upstream peoplea regulatory and institutional framework needs to be put inplace to bring service providers and beneficiaries together
Thank you for your attention
The research team would like to thank;• Assoc. Prof. Dr. Mitsuyasu Yabe (Kyushu University, Japan)and Assoc. Prof. Dr. Varaporn Panyawadee (Mae Jo University,Thailand) for their support and valuable comments
• NRCT and DFG for continuous financial support