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Mixed crop-livestock farming : an economical and environmental-friendly way to intensify production?
A case study in a european context
J. Ryschawy*, Choisis N.*, Choisis J-P.*, Gibon A. *
*INRA Toulouse, UMR 1201 DynaforBP52627, 31326Castanet-Tolosan Cedex, France
Corresponding author : [email protected]
EAAP Congress 2010 – Session 28 – 25 August 2010 Heraklion, Crete Island, Greece
A L I M E N T A T I O N
A G R I C U L T U R E
E N V I R O N N E M E N T
Study rationales A worldwide reconsideration of mixed crop-livestock systems (MCLS)
in relation to sustainable development of agriculture.
MCLS appear as 'eco-efficient' over the world (Wilkins, 2008), i.e. as a possible way to intensify production while :
- Generating higher economic efficiency & economies of scope 1st
(Herrero et al., 2010; Vermersch, 2007; Lapierre, 2004 ; de Wit et al., 2001)
- Improving land management & maintaining biodiversity 2nd
(Hendrickson, 2008 ; Wilkins, 2008)
- Having environmental-friendly practices & improving nutrient cycling 3rd
(Hendrickson et al., 2008 ; Russelle et al. 2007 ; Powell et al., 2004;)
A comparative assessment of specialized farms vs MCLS according to the three dimensions in a case-study.
Definition of MCLS :
'Integration of livestock and crop production for sale at the farm level' (Hendrickson et al., 2008 ; Wilkins, 2008 ; Russelle et al., 2007 ; Powell, 2004 ; Lhoste,2004)
EAAP Congress 2010 –Session 28 – Heraklion – 25 August 2010 ©J. Ryschawy, INRA
Objectives: To assess & compare farm economics and farmers' management practices
© INRA, UMR Dynafor
Study objectives and case study
© INRA, UMR Dynafor
Coteaux de Gascogne
FRANCE
Toulouse
A case-study : the 'Coteaux de Gascogne'- Upland area with frequent summer draughts
- Part of the European LTER Network
- Participative working with actors
- Limited specialization of agriculture
4%
10%14%
21%29% 24%
4% 14%
74%
57%
47%
0%
10%
20%
30%
40%
50%
60%
70%
80%
1950 1980 2010
Dairy farms
Beef farms
Crops farms
Mixed farms
Evolution of farms
structures since 1950
(on 58 farms of the case-study)
European region where MCLS maintained up to now.(47% of local farms in 2006)
An account of every farm working land in a continuous reference area (4000 ha) 93% of the UAA (Choisis et al., 2010)
A 'spatially-explicit' survey method 2006(Mottet et al., 2006; Choisis et al., 2010)
- Information on farm structure and technical-economical dimension
- Data on farmer's land-management practices from the parcel up to the farm level
Study methodology
Dairyfarms
Beeffarms
Cropfarms
Mixed farms
UAA (ha) 93 ± 52 89 ± 58 66 ± 58 118 ± 23
Nb of cows (ha) 48 ± 20 54 ± 36 n.a. 48 ± 37
EAAP Congress 2010 –Session 28 – Heraklion – 25 August 2010 ©J. Ryschawy, INRA
55 54 50 49
0
10
20
30
40
50
60
Crops farms Mixed farms Dairy farms Beef farms
CROP PRODUCTION (qx/ha)
1,681,12
0,820
0,5
1
1,5
2
2,5
Dairy farms Mixed farms Beef farms
STOCKING RATE (LU/ha)Intensity of production according to production systems
P= 0,034a
c
b
1. Animal production
Indicator used: Stocking rate (LU/ha MFA)
Relative intensity of cattle production in MCLS vs local LFS
2. Crop production
Indicator used: Wheat yield (ql/ha)
Relative intensity of crop production in MCLS
Hypothesis : MCLS are an economical and environmental-friendly way to intensify production.
EAAP Congress 2010 –Session 28 – Heraklion – 25 August 2010 ©J. Ryschawy, INRA
a
ba
b
P= 0,04
Local systems efficientMCLS have the highest efficiency (NS) (use fewer inputs and diversify sold productions)
1st dimension : Economic performance of farms according to production systems (1/2)
Indicator 1: Economic Efficiency at the farm level= (Turnover - Operational Costs)/Turnover *100
60%
68%
69%
72%
50% 55% 60% 65% 70% 75%
Dairy farms
Crops farms
Beef farms
Mixed farms
EAAP Congress 2010 –Session 28 – Heraklion – 25 August 2010 ©J. Ryschawy, INRA
P= 0,34
Costs higher in dairy farms (P<0,05)/ MCLS close to beef farms
1st dimension : Economic performance of farms according to production systems (2/2)
0
200
400
600
800
1000
Total cost per cow
Feed Cost per Cow
Global costs
Fertilizer cost
0
200
400
600
800
1000
Total cost per cow
(€/cow/year)
Feed Cost per Cow (€/cow/year)
Global costs (€/ha/year)
Fertilizer cost (€/ha/year)
Dairy farms
Beef farms
Mixed farms
EAAP Congress 2010 –Session 28 – Heraklion – 25 August 2010 ©J. Ryschawy, INRA
Data from the survey 2006 on the area
Total cost per cow
Fertilizer cost
per ha UAA
Total cost per ha UAA
Feeding costs per
cow
P<0,05
P<0,001
P<0,05
P<0,001
MCLS intermediate in comparison with other production systems In total UAA, less grasslands and more crops vs beef farms Comparable to Dairy farms Conservation SN grasslands in MCLS : Biodiversity
2nd dimension : Land use at farm level according to production systems
87%
52% 47%
14%
7%
30%32%
55%
7%17% 21%
31%
0%
25%
50%
75%
100%
Crop farms Dairy farms Mixed farms Beef farms
Semi-natural grasslands
Temporary grasslands
Crops
Proportions
of each type
of land use in
UAA
EAAP Congress 2010 –Session 28 – Heraklion – 25 August 2010 ©J. Ryschawy, INRA
a bb c
1. Selection of qualitative indicators of crop management practices
Type of ploughing Type of organic fertilization Presence of mineral fertilization Level of mineral fertilization (on wheat) Herbicides treatments Fungicides treatments
2. Definition of types of crop management practices An MCA A K-means classification on the MCA (on 51 out of the 58 farms)
Projection of the 4 farms structures on the MCA factorial map to cross the information with the classification on practices
3rd dimension-1 : Characterization of farmers’ crop management practices
EAAP Congress 2010 –Session 28 – Heraklion – 25 August 2010 ©J. Ryschawy, INRA
Projection of variables on the MCA factorial map
Variability explained by each axis F1-F2 = 42,3% of variability exp.
Explanation of axis
Projection of individuals on the MCA factorial map
Projection of variables on MCA factorial map d = 0.5
1
2
3
4
5
6
7
8
9
10
12
13
14
15 16
17
18
19
20
21
22
23
24
25
26
28
29
30
32
34
35
36
37
38
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41
42
43
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46
47
48
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51
52
54
55
56
WSOL.A
WSOL.B
WSOL.C
DESHCP.A
DESHCP.B
DESHCP.C
FONGCP.A
FONGCP.B
FONGCP.C FERO.A
FERO.B
FERO.C
AM.A
AM.B
FER.A
FER.B
FER.C
Low inputs High inputs
Conventional tillage
No tillage
F1 (24,6%)
F2 (
17,7
%)
24,6%
17,7%
13,7%11,1%
9,6% 9,0%6,3% 5,3%
2,2%0,6%
0%
10%
20%
30%
Axis1 Axis2 Axis3 Axis4 Axis5 Axis6 Axis7 Axis8 Axis9 Axis10
Eigen values
EAAP Congress 2010 –Session 28 – Heraklion – 25 August 2010 ©J. Ryschawy, INRA
1. New conservation systems- simplified tillage practices- low use of inputs(7 farms)
2. Conventional systems - conventional tillage- high use of inputs(17 farms)
3. Traditional systems : - conventional tillage - intermediate use of inputs(22 farms)
4. New conservation systems : - simplified tillage practices- intermediate use of inputs(5 farms)
d = 0.5
1
2
3
4
5
6
7
8
9
10
12
13
14
15 16
17
18
19
20
21
22
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36
37
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41
42
43
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46
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48
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56
d = 0.5
1
2
3
4
Low inputs High inputs
Conventional tillage
No tillage
4 Types of crop management practices
EAAP Congress 2010 –Session 28 – Heraklion – 25 August 2010 ©J. Ryschawy, INRA
Beef farms : Type 3 (and 1) Rather traditional practices
d = 0.5
1
2
3
4
5
6
7
8
9
10
12
13
14
15 16
17
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34
35
36
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41
42
43
44
45
46
47
48
49
50
51
52
54
55
56
Low inputs
Conventional tillage
No tillage
High inputs
Crossing the 4 types with farm structures
Crop farms : Type 3 and 4
Traditional or NCS
Mixed farms : Large diversity of practices: 4 Types
to study furtherEAAP Congress 2010 –Session 28 – Heraklion – 25 August 2010 ©J. Ryschawy, INRA
Dairy farms :Type 2 (and 3)
Rather conv. practices
3rd dimension-2 : ANNUAL APPARENT N FARM GATE BALANCE
NS = (N inputs – N outputs)/ UAA in kgN/ha of UAA on a year
AGRICULTURAL SYSTEM
Animal activity
Plant & soil activity
Hyp 3 : a part of produced crops is used to feed the animals
Animal dejections
Hyp 1 : all dejections are used in the system
Straw, hay
Hyp 2 : all straw and hay are reused for animals
Animal products (meat, milk,…)
Crops
Methodology :
Simon J.-C. et Le Corre L., 1992
Concentrates
Straw, hay
N Fertilizersfor each type of crop
N Fixation by Legumes
EAAP Congress 2010 –Session 28 – Heraklion – 25 August 2010 ©J. Ryschawy, INRA
(Legendre, 2007) (Sabatté, 2000)
60,5
37,9
-11,9
24,7
101
16
-20
0
20
40
60
80
100
120
Dairy farms Beef farms Crops farms Mixed farms Cattle farms in Midi-Pyrénées
Crop farms in France
Apparent farm-gate N balances of local farms in 2006
MCLS has the best N balance : N better recycled in MCLS than in specialized systems Dairy farms have surplus Crop farms have lacks of Nitrogen
Comparison with
other dataN sold (kgN/ha UAA) according to
production systems
EAAP Congress 2010 –Session 28 – Heraklion – 25 August 2010 ©J. Ryschawy, INRA
a
c
b
b
P<0,001
Discussion / Conclusion
In the study area, MCLS appear to have a better economical efficiency and
less Nitrogen inputs than those with specialized LFS.
A result in line with literature (Herrero, 2010 ; Wilkins, 2008; Russelle et al., 2007;
Vermerch, 2007; Lenné et al. 2006 ; Lapierre, 2004).
Point of vue of economy of scope (Vermersch, 2007) versus economy of scale
Study should be strengthened on much years and other indicators like organic
matter in the soils (Russelle et al., 2007)
Farmers with MCLS appear however to have heterogeneous management
practices but locally more environmental-friendly than others (Russelle et al., 2007; Schiere et al., 2002)
Differences between conventional and traditional farming systems / NCS
Discussions between old (traditional knowledge) and new generations.
Still working with local actors about those scientific issues using those
reliable and originals methods of surveys and participative working
EAAP Congress 2010 –Session 28 – Heraklion – 25 August 2010 ©J. Ryschawy, INRA
THANK YOU FOR YOUR ATTENTION !Some questions ?
A L I M E N T A T I O N
A G R I C U L T U R E
E N V I R O N N E M E N T
Bibliographic references (1/2)
Choisis J.P., Sourdril A., Deconchat, M., Balent, G., and Gibon A. Comprendre la dynamique régionale des exploitations de polyculture élevage pour accompagner le développement rural dans les Coteaux de Gascogne. Cahiers Agriculture 19(2):97-103 . 2010.
de Wit J., Prins U., and Baars T. Partner Farms : experiences with livestock farming systems research support intersectoral cooperation in the Netherlands. Livestock farming systems : Product quality based on local resources leading to improved sustainability EAAP Publications N° 118, 317-322. 2006.
Hendrickson J.R., Hanson J.D., Tanaka D.L., and Sassenrath G.F. 2008. Principles of integrated agricultural systems : Introduction to processes and definition. Renewable Agriculture and Food Systems 23(4):265-271.
Herrero M., P.K.Thornton P.K., Notenbaert A.M., Wood S., Msangi S., Freeman H.A., Bossio D., Dixon J., Peters M., vandeSteeg J., Lynam J., ParthasarathyRao P., Macmillan S., Gerard B., McDermott J., Seré C., and Rosegrant M. 2010. Smart Investments in Sustainable Food production : Revisiting Mixed Crop-livestock systems. Science 327:822-825.
Lapierre,O. 2004. Culture et élevage : quelles relations, quelles synergies ? Oléagineux, Corps Gras, Lipides 11:261-267.
Lenné,J.M., andThomas D. 2006. Integrating crop-livestock research and development in Sub-Saharan Africa: Option, imperative or impossible? Outlook on Agriculture 35 (3):167-175.
Bibliographic references (2/2)
Lhoste P. 2004. Les relations agriculture-élevage. Oléagineux, Corps Gras, Lipides 11:253-255.
Mottet A. 2005. Transformations des systèmes d'élevage depuis 1950 et conséquences pour la dynamique des paysage dans les pyrénées. Thesis. INP Toulouse.
Powell J.M., Pearson R.A., and Hiernaux P.H. 2004. Crop-Livestock Interactions in the West African Drylands. Agronomy Journal 96:469-483.
Russelle M.P., Entz M.H, and Franzluebbers A.J. 2007. Reconsidering integrated crop-livestock systems in North America. Agronomy Journal 99:325-334.
Schiere J.B., Ibrahim M.N.M., and van Keulen H. 2002. The role of livestock for sustainability in mixed farming :criteria and scenario studies under varying resource allocation. Agriculture, Ecosystems and Environment 90:139-153.
Simon J.-C., andLe Corre L. 1992. Le bilan apparent de l'azote à l'échelle de l'exploitation agricole : Méthodologie, exemple de résultats. Fourrages 129:94-102.
Vermersch P. L'éthique en friche. 2007. Quae, Paris 113 pp.
Wilkins,R.J. 2008. Eco-efficient approaches to land management: a case for increased integration of crop and animal production systems. Philosophical Transactions of the Royal Society B-Biological Sciences 363:517-525.
Apparent N farm-gate balances Our Aim : Identify management deficiency as regards N fertilization
Assessment of the method selected : Farm-gate apparent N balance
A method coined for the assessment of potential pollution risk due to surplus of Nitrogen inputs at the farm level Simon J.-C. and Le Corre L., 1992. Le bilan apparent de l'azote à l'échelle de l'exploitation agricole : méthodologie, exemple de résultats. Fourrages, 129, 79-94. Cited by Vayssières J., 2009 for evaluation of aspects of N dynamics.
Assets : Reliable method with a fast calculation based on a basic principle
(Chambaut H. and Le Gall A., 1998).
Limits : Balance only “apparent” on a year Processes like leaching are ignored.
Principle of the method : Annual apparent N farm Gate balances calculated at the whole-farm scale. Farm is considered as closed black box N surplus (in kgN/ha/year) calculated as follows:
NS = Nin- Nout/UAA
Description of each type of farm structure with means of characteristics
Dairy farms Beef farms Crops farms Mixed farms
Nb farms 6 12 7 23
UAA (ha) 93 ± 52 89 ± 58 66 ± 58 118 ± 82
MFA (ha) 48 ± 32 77 ± 53 13 ± 12 64 ± 56
WU 2.3 ± 1.1 1.3 ± 0.6 0.5 ± 0.4 1.8 ± 1.0
Nb of cows 48 ± 20 54 ±36 N.A. 48 ±37
Indicators Level of indicatorsType of ploughing Conventional None Both
Organic fertilization None Manure Slurry
Mineral fertilization Yes No
Level of Mineral fertilization (on wheat)
Low<90 UN/ha
Intermediate90-130 UN/ha
High > 130 UN/ha
Herbicides treatments NoneBroadleaf
killerBroadleaf and
grass killer
Fungicides treatments None 1 2
Description of indicators choosenfor the MCA
Characterisation of mineral fertilization for each types of crop management practice
Indicators Levels 1 2 3 4
Number of individuals 7 17 22 5
UAA Has 47 134 74 135
Crop area Has 39 61 36 53
Corn mineral fertilization UN/ha 0 104 60 68
Wheat mineral fertilization UN/ha 10 122 90 148
Artificial grasslands mineral fertilization UN/ha 30 57 47 14
SN grasslands mineral fertilization UN/ha 16 20 14 0
Characterisation of each types of crop management practice
Indicators Levels 1 2 3 4
Number of individuals 7 17 22 5
UAA 47 134 74 135
Crop area 39 61 36 53
No tillage (%) 71 18 9 100
Both (%) 70 36
Conventional (%) 29 12 55Manure (%) 57 82 82 40Slurry (%) 12
0 (%) 43 6 18 60No (%) 86 41 90 40Yes (%) 14 47 5 60n.a. (%) 12 5
Low 8 6 16 0Intermediate 6 6 20 2
High 0 22 8 8
Broadleaf killer (%) 18 27
Broadleaf and grass killer (%) 82 69 80
None (%) 100 4 20
1 treatment (%) 41 60
2 treatments (%) 59 100
None (%) 100 40
Level of Mineral fertilization
(on wheat)
Mineral fertilisation
Type of tillage
Organic fertilisation
Herbicides treatment
Fungicides