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1 Midwest Manure Summit – Green Bay – February 2011
Cemagref
Environmental science and technology
research institute
2 Midwest Manure Summit – Green Bay – February 2011
Cemagref
9 centres + 2 branches (Strasbourg
and Martinique)
Workforce of
1400 including 500 scientists,
200 doctorate and 40 post-doctorate
students
110 M€ budget including 79 M€ Core
Budget and 31 M€ contracts (2010)
Public research institute (EPST)
3 Midwest Manure Summit – Green Bay – February 2011
Competences
Scientific and technical support for public policyin the form of research, science advice, models and operational tools
An engineeringapproach that includes multi-disciplinary components
Land, water and environmental technologies Fields directly related to the needs of Society
4 Midwest Manure Summit – Green Bay – February 2011
Organisation
Water
Resources, environments, uses and risks
Environmental technologies
Networks, water treatment, waste
LandTerritorial development, biodiversity, risks and
vulnerabilities
12 research themes
3 departments
5 Midwest Manure Summit – Green Bay – February 2011
International partnerships (out of Europe)
Canada : Laval
University, INRS,
University of British
Columbia,
Mc Gill Univ.,
Ministry of Natural
Resources,IRDA
US : USGS, MIT,
UC Berkeley,
UC Davis
USDA-ARS
Brazil : Sao Paulo
University, Brasilia
University, EMBRAPA,
National Water Agency
(ANA)
Mediterranean area :IAV Hassan II Marocco,
INRGREF Tunisia
South Africa :Cape Town University, IWMI
Australia :ANU, CSIRO, USYD,
UTS, UNSW, Univ. of
Western Australia,
Monash Univ.,
Newcastle Univ.
New Zealand :
NIWA, Landcare Research
6 Midwest Manure Summit – Green Bay – February 2011
Cemagref organisation
Technologies for sustainable
agricultural systems
Technologies for clean,
energy-efficient processes
Water and waste technologies
and processes
Integration, modelling and
environmental evaluation
Environmental technologiesNetworks, water treatment, waste
7 Midwest Manure Summit – Green Bay – February 2011
A set of technological platforms
1.5 T Agro&Process MRI in Rennes Test facility for irrigation systems in Aix
Computer cluster in Clermont-Ferrand
Low-speed aeraulic platform in Rennes
Tractor test track and truck
equipped with dynamometric
apparatus in Antony
Remote sensing
in Montpellier
L’Esturial in Bordeaux
Test facility
for manure
spreading
in Clermont
Reduction
of pesticide
pollutions
in Montpellier
8 Midwest Manure Summit – Green Bay – February 2011
Cemagref in Rennes
60 permanent staffs
20 PhD students
2 research units
Food product quality
Environmental management and biological
treatment of wastes (GERE)
9 Midwest Manure Summit – Green Bay – February 2011
Cemagref and livestock effluents
Labo mobile
In line or single
analysis N2O, NH3,
CO2, CH4
+ ventilation
Floating chamber
plastic tent + sucking
Wind tunnel
Static chamber
10 Midwest Manure Summit – Green Bay – February 2011
In situ measurement of green house gas emission
11 Midwest Manure Summit – Green Bay – February 2011
In situ measurement of treatment plants performances
12 Midwest Manure Summit – Green Bay – February 2011
Pilot experiments
Biological pilot treatment plant
used for studying nitrogen
removal.
Equipment to measure
ammonia emissions in
controlled conditions
13 Midwest Manure Summit – Green Bay – February 2011
Pilot experiments
Combined anaerobic digestion
+aerobic nitrogen removal
14 Midwest Manure Summit – Green Bay – February 2011
Laboratory test to assess methanogenic potential from animal
wastes
1- Pressure is measured to calculate
the biogas amount
2- Headspace is analysed for
CO2/CH4 ratio
15 Midwest Manure Summit – Green Bay – February 2011
Some others lab equipments….
CODGas chromatograph
HPLC (VFA,
Sugars, Lipids…)
TKN
Microscopy
European perspectives on technical
and economical approaches to
phosphorus recycling
Marie-Line Daumer
17 Midwest Manure Summit – Green Bay – February 2011
Plan
Context
– Why recycling P is important ?
– What is the problem in Europe ?
Phosphorus in animal manure
– Sources of animal P
– P from Cattle manure
– P from Poultry manure
– P from Pig manure
Phosphorus Recycling from liquid effluents
– Current techniques
– Developing techniques
Conclusions
18 Midwest Manure Summit – Green Bay – February 2011
Context : Why recycling P is important ?
Phosphorus is a limited Resources
– Available for the next 100 – 400 years depending on the
technical and economical criteria for the extraction.
Phosphorus is contributing to surface water eutrophication
Photo :
http://eauxpluviales.wordpress.com/2008/02/10/introduction/
Environmental impact
Wildlife (fauna and flora) disturbances
Economical consequences :
• Drinkable water (less authorized
resources and more expensive to purify)
• Leisure use compromised
• Fish farming impossible
19 Midwest Manure Summit – Green Bay – February 2011
Context : What is the problem in Europe?
Source JRC-IES
Livestock concentration
Source JRC-IES
Solution = Transfer ?
500 km
20 Midwest Manure Summit – Green Bay – February 2011
Phosphorus in animal manure : sources
Source JRC-IES
Most of the phosphorus is from bovine and other grazing animals
21 Midwest Manure Summit – Green Bay – February 2011
Phosphorus in animal manure : Cattle
Vaches laitièresVaches allaitantes
100 0 100 Kilometers
N
Source : AGRESTE-Statistique
agricole annuelle 1995
Mise en page : Cemagref GERE
Labo SIG
édité le 21/05/01
GEOFLA®©IGN2000
Dairy cows
Others
Bovine and grazing animals are spread
over all the territory :
Manure is already used locally
Example for France (comparable to UK)
Grazing is still significant, bovine farms
have usually enough land :
No or low surplus at the farm level
Excepted in Netherlands
In the current context P from cattle manure is
not an issue excepted in some cases
But it can become if bands are increasing
without increasing the surfaces.
22 Midwest Manure Summit – Green Bay – February 2011
Long term effect (NTK/P)
0
2
4
6
8
10
deep
litte
r
yard
scr
apin
g
com
poste
d man
ure
undilu
ted li
quid m
anure
dilute
d liq
uid m
anur
e
calv
es s
lurr
y
dirty
wat
er
N/P
in
bo
vin
e m
an
ure
N/P in manure N/P mini for crops N/P max for crops
0
2
4
6
8
10
deep
litte
r
yard
scr
apin
g
com
poste
d man
ure
undilu
ted li
quid m
anure
dilute
d liq
uid m
anur
e
calv
es s
lurr
y
dirty
wat
er
N/P
in
bo
vin
e m
an
ure
N ammo/P N/P mini for crops N/P max for crops
Phosphorus in animal manure : Cattle
Short term effect (Namm./P)
Bovine manures are quite well balanced
Considering long term effect
(mineralization of organic nitrogen)
P surplus in solid manures
No surplus at farm level:
•Complementary mineral N
P surplus at farm level
•Exportation of the manureP surplus in liquid manures
•Recycling by extraction
23 Midwest Manure Summit – Green Bay – February 2011
Phosphorus in animal manure : cattle
P recycling by extraction will depend on the country
France
1
1
2
2
UK
4
4
Spain
Italy
3
3Germany
5
5
The proportion of manure from housed cattle produced
as liquid on a country by country basis (Burton and
Turner, 2003).
Liquid manure
Extraction
Solid manure
Exportation
24 Midwest Manure Summit – Green Bay – February 2011
Phosphorus in animal manure : poultry
GEOFLA®©IGN2000
Source : AGRESTE-Statistique
agricole annuelle 1995
Mise en page : Cemagref GERE
Labo SIG
édité le 21/05/01
N
100 0 100 Kilometers
Poules pondeusesPoulets de chair et coqsDindes, dindonsCanards
Laying Hens
Broilers
Turkeys
Ducks
Example for France
(comparable to other countries)
Poultry are in defined areas
Poultry farms have usually not enough
land :
High surplus at the farm level
25 Midwest Manure Summit – Green Bay – February 2011
0
2
4
6
8
10
Duc
k sl
urry
Layin
g Hen
s Slu
rry
Layin
g Hen
s M
anure
Drie
d Lay
ing H
ens
Man
ure
Bro
ilers
Man
ure
Turkey
Man
ure
N/P
in
po
ult
ry m
an
ure
N/P in manure N/P mini for crops N/P max for crops
0
2
4
6
8
10
Duc
k sl
urry
Layin
g Hen
s Slu
rry
Layin
g Hen
s M
anure
Drie
d Lay
ing H
ens
Man
ure
Bro
ilers
Man
ure
Turkey
Man
ure
N/P
in
po
ult
ry m
an
ure
N ammo/P N/P mini for crops N/P max for crops
Long term effect (NTK/P) Short term effect (Namm./P)
Phosphorus in animal manure : poultry
Poultry manures are not balanced P surplus in solid manures
•High dry matter content
•Low bedding material
•Heat available
Easy to dry and to export
P surplus in liquid manures
•Recycling by extraction (see
below)
26 Midwest Manure Summit – Green Bay – February 2011
• Other solution developed for solids
– Combustion (in UK mainly): 3 units
– The biggest one :
• 400.000 ton dry solid poultry manure
• 800-850°C
• Electricity produced 38.5 MW
• Supported with subsidies from a governmental program on non-fossil fuel electricity generation.
• Ashes used as K and P fertilizer
Phosphorus in animal manure : poultry
27 Midwest Manure Summit – Green Bay – February 2011
Phosphorus in animal manure : pigs
Example for France
(comparable to other countries)
Pigs are in defined areas
Pigs farms have usually not enough land :
High surplus at the farm level
GEOFLA®©IGN2000
Source : AGRESTE-Statistique
agricole annuelle 1995Mise en page : Cemagref GERE Labo SIG
édité le 21/05/01
N
100 0 100 Kilometers
Truies
28 Midwest Manure Summit – Green Bay – February 2011
Long term effect (NTK/P) Short term effect (Namm./P)
Phosphorus in animal manure : pigs
Pigs slurries are not balanced
P surplus in liquid (slurries)
•Recycling (see below)
0
2
4
6
8
10
Sow
Wea
ner
Fatte
nerM
ixt
N/P
in
pig
slu
rry
N ammo/P N/P mini for crops N/P max for crops
0
2
4
6
8
10
Sow
Wea
ner
Fatte
nerM
ixt
N/P
in
pig
slu
rry
N/P in manure N/P mini for crops N/P max for crops
29 Midwest Manure Summit – Green Bay – February 2011
Phosphorus in animal manure : pigs
Main pig farmers are producing slurries (liquid manure)
1
1
France
2
2
Denmark3
3
Germany
4
4
Spain
Italy
5
5
The proportion of manure from housed pigs produced as
liquid on a country by country basis (Burton and Turner,
2003).
6
6Netherlands
Liquid manure
Extraction
30 Midwest Manure Summit – Green Bay – February 2011
• Most of P from animal is coming from cattle in Europe but– Cattle are spread over all the territory
– In cattle farms, P surplus are low. Solids are in concern.
– Local application complemented by mineral N fertilization when required.
– Exportation of solid manure on short distances because of volume (bedding material) and dry matter
• Less than 10% of P is coming from poultry in Europe but– Poultry are produced in specific areas
– In poultry farms, P surplus are high, solids are in concern
– Exportation after drying is developed –medium distances- high dry matter, low bedding materials
– Exportation of ashes after combustion (ashes used as mineral fertilizer, UK mainly)
• Less than 10% of P is coming from pigs in Europe but– Pigs are produced in specific areas
– In pigs farms, P surplus are high, liquids are in concern
– Exportation after mechanical separation is developed –short distances-(low dry matter)
Phosphorus in animal manure : conclusion
31 Midwest Manure Summit – Green Bay – February 2011
P recycling from liquid manure: current techniques
History
N : 3-4 kg.m-3
P : 1 kg.m-3
Raw slurry
Spreading basis : 170 kg organic
N/ha/year
43-57 kg P/ha
Low surplus
N : 0,5-1 kg.m-3
P : 0,8-1 kg.m-3
Biological treatment
Nitrate directive
1991
140-340 kg P/ha
High surplus
!
N and P have to be removed in
the same ratio!
32 Midwest Manure Summit – Green Bay – February 2011
Recycling P from liquid manure: current techniques
• P in liquid manure is as small and dense particles (calcium P
or magnesium P) Mechanical separation
– Developed at a large scale only for pig slurry and mainly in
France, Belgium and Spain
Centrifuge decanter
33 Midwest Manure Summit – Green Bay – February 2011
Recycling P from liquid manure: current techniques
Press-auger Decantation
+ press
auger
Vibrating
screen
Filter-
press
Vacuum or
band filter
Centrifuge
decantor
Mass % 4-8 4-8 15-20 15-20 11-16 10-13
P% 6-26 25-35 3-32 92-97 80-92 70-80
N% 2-14 2-14 5-24 5-15 32-38 14-25
DM% 30-36 30-36 11-8 26-27 24-26 30-35
P(kg/t) 12 12 5 11 15 23
N (kg/t) 7.5 7.5 5.2 9 10 11
Energy
(KW/m3)
1 1 <1 5 1.5 3-6
Invest (k€) 40-50 40 10-15 350 60-90 125
Further
treatment
Drying or
composting
Drying or
composting
Composting
with bulking
Compostin
g
Composting
with bulking
Composting
Performances of separation devices
34 Midwest Manure Summit – Green Bay – February 2011
• Limits of mechanical separation
– Post-treatment of solid required
– Product outlet (short distances- 20km)
– Competition with other organic fertilizers (composts from
household wastes)
• Other techniques
– Developed only at pilot scale
– Too sophisticated to be manage at farm level in European
context
– Too expensive
Recycling P from liquid manure: current techniques
35 Midwest Manure Summit – Green Bay – February 2011
Recycling P from liquid manure: Perspectives
Biologically
treated
pig slurry
separation Sludge (OM)
precipitation
filtration
Mineral fertilizer
Struvite
(MgNH4PO4)
+
CaPO4
acidification
Liquid
(K)
Liquid (P)
Which acid ?
•HCl
•H2SO4
•HNO3
•Acetic
•Formic
Technical approach 1
36 Midwest Manure Summit – Green Bay – February 2011
Recycling P from liquid manure: Perspectives
Biologically
treated
pig slurry
acidification separation Sludge (OM)
precipitation
filtration Liquid
(K)
Mineral fertilizer
Struvite
(MgNH4PO4)
+
CaPO4
Liquid (P)
Which technique?
Decantation
•72h
•Sludge = 50%
•Liquid (P)= 50%
Draining + polymère
•<1h
•Sludge = 20%
•Liquid (P)= 80%
Technical approach 2
37 Midwest Manure Summit – Green Bay – February 2011
Recycling P from liquid manure: Perspectives
Biologically
treated
pig slurry
acidification separation Sludge (OM)
precipitation
filtration Liquid
(K)
Mineral fertilizer
Struvite
(MgNH4PO4)
+
CaPO4
Liquid (P)
Which reactant?
•MgCl2 + NaOH
•MgO
Technical approach 3
38 Midwest Manure Summit – Green Bay – February 2011
• Mineral fertiliser quality
Recycling P from liquid manure: Perspectives
g/kg
TS 838±1
P 96±2 26%(P2O5)
NTK 4±1 <1%
Ca 142±26 24%(CaO)
Mg 70±10 14%(MgO)
K 50±4 7%(K2O)
Na 17±1
Normalized NPK (N-P2O5-K2O): 0-26-7 +24% of CaO +14% of MgO,.
In compliance French standard NF U42-001/A8 class II (> 18% of P2O5+K2O).
Close to the limits for class III products (fertilizers supplying calcium and magnesium).
The neutralizing value of the products was not analysed in the present study.
39 Midwest Manure Summit – Green Bay – February 2011
Recycling P from liquid manure: Perspectives
Amount (kg/m 3) P.U.(€/k
g)
Price (€/m 3)
Formic Acetic Formic Acetic
Acid 8 20 1 8 20
MgO 1 2 1.5 1.5 3
Invest 1.4 1.4
En.&
Maint.
1.4 1.4
Total 12.3 26.1
Economical approach
40 Midwest Manure Summit – Green Bay – February 2011
Recycling P from liquid manure: Perspectives
Economical approach
acide
66%
MgO
12%
investissement
11%
énergie et
maintenance
11%
acide
66%
MgO
12%
investissement
11%
énergie et
maintenance
11%
acide
66%
MgO
12%
investissement
11%
énergie et
maintenance
11%
acide
66%
MgO
12%
investissement
11%
énergie et
maintenance
11%
acide
66%
MgO
12%
investissement
11%
énergie et
maintenance
11%
acide
66%
MgO
12%
investissement
11%
énergie et
maintenance
11%
Total 12.3€/m3 of pig slurry treated
Acid
66%
MgO
12%
Invests
11%
Energy &
maintenance
11%
41 Midwest Manure Summit – Green Bay – February 2011
•Treatment point of view :
• cost >Centrifugation (2€/m 3 ) but …
•No further composting required
•Product that can be sold
Conclusions
•Fertilizing point of view (first approxim.):
0
10
20
30
40
50
60
70
0 100 200 300 400 500 600 700 800 900 1000km
Eu
ros
.kg
P-1
Mineral product Solid from centrifuge decanter
Solid product after optimisation Triple super P. Public price including transport
42 Midwest Manure Summit – Green Bay – February 2011
• Fertilizer point of view :
– Recycled P : 15€/kgP
– Mineral P: 10 €/kgP (public price including transport)
– In ten years?
– Higher agronomic efficiency than current mineral P?
• Ingoing works :– Optimization
– Full scale pilot for pig slurry and agro-food indutries effluents (dissolution not required)
– Assessment of fertilizer value
– Environmental assessment of the process
Conclusions
43 Midwest Manure Summit – Green Bay – February 2011
Thank you for your attention
More [email protected]
www.cemagref.fr