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Symposium on Agroecology, Food and Nutritional security 
FAO, Rome, Sept. 18-19, 2014 
Integration wwiitthh lliivveessttoocckk 
Jean-François Soussana1, Bertrand Dumont2, Philippe Lecomte3 
1. INRA, Paris, France 
2. INRA, UMRH, Clermont-Ferrand, France; 3. CIRAD, UMR SELMET, Montpellier, France
Outline 
 Challenges in the livestock sector 
 Agroecology for livestock: five goals 
 Integrated animal health management 
 Reduced use of external inputs 
 Recoupled C-N-P cycles 
 Biodiversity use and preservation 
 Systems diversity and resilience 
 Industrial ecology for intensive livestock systems 
 Conclusions
Outline 
 Challenges for the livestock sector 
 Agroecology for livestock: five goals 
 Integrated animal health management 
 Reduced use of external inputs 
 Recoupled C-N-P cycles 
 Biodiversity use and preservation 
 Systems diversity and resilience 
 Industrial ecology for intensive livestock systems 
 Conclusions
World animal production 
provides 1/3 of proteins consumption 
1.3 
billion ‘jobs’ 
15% 
of world GHG 
emissions 
19 
billion animals 
1.4 
trillion $ 
35% 
of crop production 
30% 
of ice free land
Grassland cover 
Courtesy: K. Erbst, Vienna 
Grasslands (grazing lands): 
•Provide half of global gross energy intake by ruminants 
•A key resource which cannot be directly used by humans 
•Contribute through manure to crop fertilisation 
•Account for ca. 25% of global soil carbon stock 
•Grazing lands are one of the highest repository of plant diversity.
Livestock’s multiple roles in poor households 
Crop supporting function 
Capital and insurance function 
Socio-cultural function 
Meat and milk are “by-products”
Diversity of systems and natural resources use
8 
Livestock production systems distribution 
Sere and Steinfeld (1996) classification updated by Robinson et al. (2011) 
How can agroecology apply to highly contrasted livestock systems? 
How can livestock and crop production be better integrated?
Outline 
 Challenges for the livestock sector 
 Agroecology for livestock: five goals 
 Integrated animal health management 
 Reduced use of external inputs 
 Recoupled C-N-P cycles 
 Biodiversity use and preservation 
 Systems diversity and resilience 
 Industrial ecology for intensive livestock systems 
 Conclusions
Scope for livestock in agroecology 
 Increasing, but relatively small number of papers (ca. 40 per year in WOS, up to 
1,400 since the 1980’s in all data bases) 
 In the book by S. Gliessman (2006), one chapter devoted to livestock raises the 
important question of livestock integration: 
‘The problem lies not in the animals themselves or in the consumption of animal 
products, but rather in the way they are integrated into agroecosystems. 
Understanding the integration of the animal in its agro-ecosystem provides levers 
to ensure sustainable environmental and economic concerns ‘
Agroecology for livestock systems: 
Five goals 
Adapted from Dumont et al. (2013)
Socio-economics aspects 
 A necessary reorganization of work (generic principles but 
no "turnkey" solutions, i.e. adjust decisions continuously) 
 Extra-time spent monitoring, especially during transition 
periods 
 Tools (indicators, instructional media) enable capacity 
building 
 Diversification could stabilize income in a context of 
increasing price volatility and increased climatic hazards. 
 New technologies could facilitate information collection 
and handling of animals
Outline 
 Challenges for the livestock sector 
 Agroecology for livestock: five goals 
 1. Integrated animal health management 
 2. Reduced use of external inputs 
 3. Recoupled C-N-P cycles 
 4. Biodiversity use and preservation 
 5. Systems diversity and resilience 
 Industrial ecology for intensive livestock systems 
 Conclusions
1. Why integrated management of animal health? 
Antibiotics use per kg meat production 
Source: Scientific American (2012)
Integrated management of animal health 
- Using the principles of ecology to manage host-pathogen interactions 
• Adapt practices to reduce susceptibility to pathogens, e.g. disrupt 
host-pathogen cycles by altering the distribution of animals 
in space and time (Cabaret, 2007; Prache et al., 2011) 
• Use of bioactive plants, (e.g. common sainfoin, Onobrychis viciifolia) 
to reduce the infestation of small ruminants by digestive strongyles (Hoste et al., 
2006) 
- Mobilizing the adaptability of animals (prevention) 
- Select animals adapted to their breeding environment 
- To climate, e.g. heat (small size, low fat, high urine N content) 
-To feed restrictions (mobilization of reserves 
and compensatory growth) 
- To parasites (trypano tolerance, ticks, digestive strongyles)
Integrated management of animal health 
Intestinal parasites control: 
-mixed grazing, 
-plant secondary metabolites, 
-vermicomposting. 
West Indies ruminant systems 
(M. Boval et al., Inra)
Outline 
 Challenges for the livestock sector 
 Agroecology for livestock: five goals 
 1. Integrated animal health management 
 2. Reduced use of external inputs 
 3. Recoupled C-N-P cycles 
 4. Biodiversity use and preservation 
 5. Systems diversity and resilience 
 Industrial ecology for intensive livestock systems 
 Conclusions
3 Reduced use of external inputs
In Europe, grassland-based livestock 
production often depends on high N input 
… to grass monocultures What about legumes? 
100 - 400 kg N ha-1 year-1
600 
600 
500 
500 
400 
400 
300 
300 
200 
100 
0 
** ** *** *** ** ns ** *** ns ns ** ** *** ** * 
** * ** 
15 11 10 34 1 27 24 22 26 18 36 20 23 13 14 
Site No 
Grass 
Legume 
Mixtures 
Increased total N yield with 
grass- legume mixtures 
Total nitrogen yield [kg ha-1 yr-1] 
35 - Mixtures, on average, outperform grass monocultures at majority of sites 
- Average N yield of mixtures is at level of legume monocultures 
1 
11 10 
13 
14 
15 
18 
20 
22 
23 
24 
26 
27 
34 
35 
36 
Mid European 
Northern European 
Other
3 Reduce external inputs used for production 
- Increasing the efficiency of utilization of limiting resources 
•Improve P digestibility in swine rations incorporating natural microbial phytase 
(Dourmad et al., 2009) 
- Preserving support services for production 
•Boost productivity ponds with submerged substrates and controlling the C: N ratio in 
the rearing water (Bosma & Verdegem, 2011) 
- Promoting the use of non-recyclable resources 
Grazing lands 
Industrial by-products 
Crop residues
Outline 
 Challenges for the livestock sector 
 Agroecology for livestock: five goals 
 1. Integrated animal health management 
 2. Reduced use of external inputs 
 3. Recoupled C-N-P cycles 
 4. Biodiversity use and preservation 
 5. Systems diversity and resilience 
 Industrial ecology for intensive livestock systems 
 Conclusions
3. Recoupling the C, N and P cycles in animal systems 
Extensive perennial 
vegetation provides C-N-P 
coupling, but with low 
animal production efficiency 
Biodiversity contributes 
to plant productivity and C-N- 
P coupling 
Intensive animal agriculture 
uncouples C-N-P cycles, 
increasing losses to the 
environment 
Loss of biodiversity contributes to 
this uncoupling 
Global animal excretion: 94 Tg N; 21 Tg P, 67 Tg K per year 
(well above inorganic fertilizers)
When are C-N-P cycles coupled? 
 C, N and P are coupled by plants (i.e. autotrophy) 
 Soil decomposers and grazers uncouple C, N and P 
(i.e. heterotrophy) 
Autotrophy > Heterotrophy 
Forests and natural ecosystems 
Extensive grasslands… 
Heterotrophy > Autotrophy 
Bare soil 
Excess fertilizers 
Feedlots 
Overgrazing…Deforestation
Three stages of pasture intensification 
(Soussana and Lemaire, Agric. Ecosyst. Envir., 2014)
Restoring degraded soils provides a 
win-win option 
‘Terraprima’ project 
(www.terraprima.pt) 
Portuguese carbon fund 
Sown biodiverse leys fertilized with P 
on degraded soils 
50,000 ha were sown (1,000 farmers) 
Estimated carbon sequestration : 
1 million tons since 2009 
Stage 1 of intensification is 
usually a win-win option
Evaluating pasture intensification 
potential in Brazil 
Stocking Rates (actual/grazing potential, %) 
(L. G. Barioni, Embrapa)
Maximal critical stocking rates 
(SR*) in Europe 
Soil C 
sequestration 
Grassland intensification 
NCS, GHG 
GHG 
balance 
0 
SR*max= 2.1 LSU/ha 
HUE* =0.2 
SR*max=0.67 LSU/ha 
Compensate cost for farmers! 
(Soussana et al., 2014, EGF)
Greenhouse gas emissions per unit product may not 
decline universally with production intensity 
12.00 
10.00 
8.00 
6.00 
4.00 
2.00 
0.00 
Mean global 
dairy yield per cow 
0 1 000 2 000 3 000 4 000 5 000 6 000 7 000 8 000 9 000 
Output per cow, kg FPCM per year 
kg CO2-eq. per kg FPCM 
Gerber et al (2011) Livestock Science 139, 100-108 
Gac et al (2014), Idele, Inovations 
Agronomiques, in press 
Improved productivity and efficiency is critical to reduce GHG emissions per head 
in extensive systems 
However, in Europe, the most intensive (maize based) systems have more net 
GHG emissions than herbage based systems
Mixed crop-livestock systems 
- Majority of livestock keeping households 
- Largest share of meat and milk production in the tropics 
- Large use of crop residues by livestock
Systems and livelihoods in transition: crop-livestock integration 
taking place in W. Africa 
W. Africa 1966 – pastoral system 2004 – crop-livestock system 
Herrero et al 2009
Diversity of manure management practices in Mali
Outline 
 Challenges for the livestock sector 
 Agroecology for livestock: five goals 
 1. Integrated animal health management 
 2. Reduced use of external inputs 
 3. Recoupled C-N-P cycles 
 4. Biodiversity use and preservation 
 5. Systems diversity and resilience 
 Industrial ecology for intensive livestock systems 
 Conclusions
4. Biodiversity use and preservation 
Biodiversity preservation 
-Constructing landscapes to ensure ecosystem services 
• Grazing exclusion at flowering peak can double butterfly populations in cattle-grazed 
‘intensive’ pastures 
(Farruggia et al., 2012) 
• Collective landscape management based on coordination among farmers balances 
milk production and conservation of shorebirds (Sabatier et al., 2010, 2014)
Plant species diversity matters for pasture 
productivity 
0 2 4 6 8 10 12 
(Gross et al., Basic Appl. Ecol., 2010) 
Above-ground biomass 
(A) 
Number of Species 
4 
3 
2 
1 
0 
Log Green Biomass (g) -1 
AB r² = 0.58 ** 
MF r² = 0.61 ** 
MU r² = 0.48 * 
Overall r² = 0.51 *** 
The more plant species in a permanent grassland patch, 
the higher the local productivity 
Complementarity across neighbouring species
Outline 
 Challenges for the livestock sector 
 Agroecology for livestock: five goals 
 1. Integrated animal health management 
 2. Reduced use of external inputs 
 3. Recoupled C-N-P cycles 
 4. Biodiversity use and preservation 
 5. Systems diversity and resilience 
 Industrial ecology for intensive livestock systems 
 Conclusions
5. Increased resilience through systems diversity 
- Enhancing the complementarity of animals and the diversity of resources 
J F M A M J J A S O N D 
280 ewes LAMBING LACTATION MATIN 
Conserved forage + 
concentrate 
G 
Fertilized 
permanent 
grassland 
Native rangelands Regrowths on 
Ewe-lambs WEANING 
Increase the flexibility of the system through 
diversified resources 
18 ha fertilized 
grasslands: 4 t DM/ ha 
Manage rangelands with high biodiversity potential 
Use non-recoverable resources directly by man 
fertilized grassland 
Native rangeland 
(+ hay if needed) 
Native rangeland with 
experienced peers 
Regrowths on native 
rangelands 
(compensatory 
growth) 
Green grass on 
fertilized & native 
gld 
226600 hhaa 
Gross margin: 97Є/ewe (vs. 58 Є upland central France) Jouven & Benoit, 2011 
Dumont et al., 2013
Agroforestry: increased diversity and resilience 
of livestock systems 
(courtesy CATIE)
Outline 
 Challenges for the livestock sector 
 Agroecology for livestock: five goals 
 1. Integrated animal health management 
 2. Reduced use of external inputs 
 3. Recoupled C-N-P cycles 
 4. Biodiversity use and preservation 
 5. Systems diversity and resilience 
 Industrial ecology for intensive livestock systems 
 Conclusions
Can ecology also apply to intensive livestock systems? 
 Industrial ecology can be seen as a new way to reduce the environmental footprint of 
intensive livestock using specific technologies to reduce impacts, recycle and create 
symbiosis across sub-systems (Frosh & Gallopoulos, 1989; Holm Nielsen, 2010; Takata et al., 
2012) 
- Enhancing the value of co-products of agriculture through 
industrial technologies 
- Contributing significantly to food production by using less 
land, water and energy
Integrated agriculture-aquaculture systems 
Livestock Rice, fruits, sugar cane 
Aliment 
Feed (co-products) 
(sous-produits de culture) 
Aliments (végétaux 
aquatiques) et eau 
Fish (carp, tilapia) 
Fertilisation (fumier) 
produits 
sous Fertilisation (culture) 
de Irrigation des cultures et 
fertilisation (sédiment étangs) 
Feed and water 
Fertilization manure) 
Fertilization (co-products) 
Irrigation, fertilization 
High productivity: rice 
2t fruits + 10t fish/ha 
Gross margin: + 50-150 
US$ in Bangladesh 
Nhan et al., 2006 
Phong et al., 2010 
Decrease inputs for 
production 
Reduced pollution 
But fish can be contaminated with excreta-related pathogens or antibiotics! => WHO guidelines 
Karim et al., 2011
Intensive pig system associated with a digester 
Pig production indoors Crop production 
(Grains, oilseeds, etc.) 
Feed 
méthanisation Substrat (effluents) 
de 
On-farm feed 
production 
Biofuels Diversify to 
Digester 
Detoxify droppings before 
use to fertilize crops 
Lower mortality of piglets 
secure income 
High initial 
investment 
Other substrates (16%) 250 houses 
Sales 
Direct sales 
Manure biogas 
to produce 
Heated housing 
Fertilization (digesta) 
Silage of intercrops 
Dumont et al., 2013
Summary 
 Agroecology goes further than adjusting practices in current 
agroecosystems; goals (or principles) can be used as a guideline to 
implement combinations of agroecological practices adapted to local 
conditions 
 Some of these principles can also apply to intensive livestock farming 
systems 
- Agroecology sensu stricto: strong connection to the soil, food systems 
with high added value, preservation of biodiversity and environment, 
poverty alleviation, increased food security. 
- Industrial Ecology: closes nutrient cycles, integrates with other 
production systems, adapted to densely populated areas 
 AE and IE provide options for most livestock systems
Thank you for your attention!

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Integration with livestock

  • 1. Symposium on Agroecology, Food and Nutritional security FAO, Rome, Sept. 18-19, 2014 Integration wwiitthh lliivveessttoocckk Jean-François Soussana1, Bertrand Dumont2, Philippe Lecomte3 1. INRA, Paris, France 2. INRA, UMRH, Clermont-Ferrand, France; 3. CIRAD, UMR SELMET, Montpellier, France
  • 2. Outline  Challenges in the livestock sector  Agroecology for livestock: five goals  Integrated animal health management  Reduced use of external inputs  Recoupled C-N-P cycles  Biodiversity use and preservation  Systems diversity and resilience  Industrial ecology for intensive livestock systems  Conclusions
  • 3. Outline  Challenges for the livestock sector  Agroecology for livestock: five goals  Integrated animal health management  Reduced use of external inputs  Recoupled C-N-P cycles  Biodiversity use and preservation  Systems diversity and resilience  Industrial ecology for intensive livestock systems  Conclusions
  • 4. World animal production provides 1/3 of proteins consumption 1.3 billion ‘jobs’ 15% of world GHG emissions 19 billion animals 1.4 trillion $ 35% of crop production 30% of ice free land
  • 5. Grassland cover Courtesy: K. Erbst, Vienna Grasslands (grazing lands): •Provide half of global gross energy intake by ruminants •A key resource which cannot be directly used by humans •Contribute through manure to crop fertilisation •Account for ca. 25% of global soil carbon stock •Grazing lands are one of the highest repository of plant diversity.
  • 6. Livestock’s multiple roles in poor households Crop supporting function Capital and insurance function Socio-cultural function Meat and milk are “by-products”
  • 7. Diversity of systems and natural resources use
  • 8. 8 Livestock production systems distribution Sere and Steinfeld (1996) classification updated by Robinson et al. (2011) How can agroecology apply to highly contrasted livestock systems? How can livestock and crop production be better integrated?
  • 9. Outline  Challenges for the livestock sector  Agroecology for livestock: five goals  Integrated animal health management  Reduced use of external inputs  Recoupled C-N-P cycles  Biodiversity use and preservation  Systems diversity and resilience  Industrial ecology for intensive livestock systems  Conclusions
  • 10. Scope for livestock in agroecology  Increasing, but relatively small number of papers (ca. 40 per year in WOS, up to 1,400 since the 1980’s in all data bases)  In the book by S. Gliessman (2006), one chapter devoted to livestock raises the important question of livestock integration: ‘The problem lies not in the animals themselves or in the consumption of animal products, but rather in the way they are integrated into agroecosystems. Understanding the integration of the animal in its agro-ecosystem provides levers to ensure sustainable environmental and economic concerns ‘
  • 11. Agroecology for livestock systems: Five goals Adapted from Dumont et al. (2013)
  • 12. Socio-economics aspects  A necessary reorganization of work (generic principles but no "turnkey" solutions, i.e. adjust decisions continuously)  Extra-time spent monitoring, especially during transition periods  Tools (indicators, instructional media) enable capacity building  Diversification could stabilize income in a context of increasing price volatility and increased climatic hazards.  New technologies could facilitate information collection and handling of animals
  • 13. Outline  Challenges for the livestock sector  Agroecology for livestock: five goals  1. Integrated animal health management  2. Reduced use of external inputs  3. Recoupled C-N-P cycles  4. Biodiversity use and preservation  5. Systems diversity and resilience  Industrial ecology for intensive livestock systems  Conclusions
  • 14. 1. Why integrated management of animal health? Antibiotics use per kg meat production Source: Scientific American (2012)
  • 15. Integrated management of animal health - Using the principles of ecology to manage host-pathogen interactions • Adapt practices to reduce susceptibility to pathogens, e.g. disrupt host-pathogen cycles by altering the distribution of animals in space and time (Cabaret, 2007; Prache et al., 2011) • Use of bioactive plants, (e.g. common sainfoin, Onobrychis viciifolia) to reduce the infestation of small ruminants by digestive strongyles (Hoste et al., 2006) - Mobilizing the adaptability of animals (prevention) - Select animals adapted to their breeding environment - To climate, e.g. heat (small size, low fat, high urine N content) -To feed restrictions (mobilization of reserves and compensatory growth) - To parasites (trypano tolerance, ticks, digestive strongyles)
  • 16. Integrated management of animal health Intestinal parasites control: -mixed grazing, -plant secondary metabolites, -vermicomposting. West Indies ruminant systems (M. Boval et al., Inra)
  • 17. Outline  Challenges for the livestock sector  Agroecology for livestock: five goals  1. Integrated animal health management  2. Reduced use of external inputs  3. Recoupled C-N-P cycles  4. Biodiversity use and preservation  5. Systems diversity and resilience  Industrial ecology for intensive livestock systems  Conclusions
  • 18. 3 Reduced use of external inputs
  • 19. In Europe, grassland-based livestock production often depends on high N input … to grass monocultures What about legumes? 100 - 400 kg N ha-1 year-1
  • 20. 600 600 500 500 400 400 300 300 200 100 0 ** ** *** *** ** ns ** *** ns ns ** ** *** ** * ** * ** 15 11 10 34 1 27 24 22 26 18 36 20 23 13 14 Site No Grass Legume Mixtures Increased total N yield with grass- legume mixtures Total nitrogen yield [kg ha-1 yr-1] 35 - Mixtures, on average, outperform grass monocultures at majority of sites - Average N yield of mixtures is at level of legume monocultures 1 11 10 13 14 15 18 20 22 23 24 26 27 34 35 36 Mid European Northern European Other
  • 21. 3 Reduce external inputs used for production - Increasing the efficiency of utilization of limiting resources •Improve P digestibility in swine rations incorporating natural microbial phytase (Dourmad et al., 2009) - Preserving support services for production •Boost productivity ponds with submerged substrates and controlling the C: N ratio in the rearing water (Bosma & Verdegem, 2011) - Promoting the use of non-recyclable resources Grazing lands Industrial by-products Crop residues
  • 22. Outline  Challenges for the livestock sector  Agroecology for livestock: five goals  1. Integrated animal health management  2. Reduced use of external inputs  3. Recoupled C-N-P cycles  4. Biodiversity use and preservation  5. Systems diversity and resilience  Industrial ecology for intensive livestock systems  Conclusions
  • 23. 3. Recoupling the C, N and P cycles in animal systems Extensive perennial vegetation provides C-N-P coupling, but with low animal production efficiency Biodiversity contributes to plant productivity and C-N- P coupling Intensive animal agriculture uncouples C-N-P cycles, increasing losses to the environment Loss of biodiversity contributes to this uncoupling Global animal excretion: 94 Tg N; 21 Tg P, 67 Tg K per year (well above inorganic fertilizers)
  • 24. When are C-N-P cycles coupled?  C, N and P are coupled by plants (i.e. autotrophy)  Soil decomposers and grazers uncouple C, N and P (i.e. heterotrophy) Autotrophy > Heterotrophy Forests and natural ecosystems Extensive grasslands… Heterotrophy > Autotrophy Bare soil Excess fertilizers Feedlots Overgrazing…Deforestation
  • 25. Three stages of pasture intensification (Soussana and Lemaire, Agric. Ecosyst. Envir., 2014)
  • 26. Restoring degraded soils provides a win-win option ‘Terraprima’ project (www.terraprima.pt) Portuguese carbon fund Sown biodiverse leys fertilized with P on degraded soils 50,000 ha were sown (1,000 farmers) Estimated carbon sequestration : 1 million tons since 2009 Stage 1 of intensification is usually a win-win option
  • 27. Evaluating pasture intensification potential in Brazil Stocking Rates (actual/grazing potential, %) (L. G. Barioni, Embrapa)
  • 28. Maximal critical stocking rates (SR*) in Europe Soil C sequestration Grassland intensification NCS, GHG GHG balance 0 SR*max= 2.1 LSU/ha HUE* =0.2 SR*max=0.67 LSU/ha Compensate cost for farmers! (Soussana et al., 2014, EGF)
  • 29. Greenhouse gas emissions per unit product may not decline universally with production intensity 12.00 10.00 8.00 6.00 4.00 2.00 0.00 Mean global dairy yield per cow 0 1 000 2 000 3 000 4 000 5 000 6 000 7 000 8 000 9 000 Output per cow, kg FPCM per year kg CO2-eq. per kg FPCM Gerber et al (2011) Livestock Science 139, 100-108 Gac et al (2014), Idele, Inovations Agronomiques, in press Improved productivity and efficiency is critical to reduce GHG emissions per head in extensive systems However, in Europe, the most intensive (maize based) systems have more net GHG emissions than herbage based systems
  • 30. Mixed crop-livestock systems - Majority of livestock keeping households - Largest share of meat and milk production in the tropics - Large use of crop residues by livestock
  • 31. Systems and livelihoods in transition: crop-livestock integration taking place in W. Africa W. Africa 1966 – pastoral system 2004 – crop-livestock system Herrero et al 2009
  • 32. Diversity of manure management practices in Mali
  • 33. Outline  Challenges for the livestock sector  Agroecology for livestock: five goals  1. Integrated animal health management  2. Reduced use of external inputs  3. Recoupled C-N-P cycles  4. Biodiversity use and preservation  5. Systems diversity and resilience  Industrial ecology for intensive livestock systems  Conclusions
  • 34. 4. Biodiversity use and preservation Biodiversity preservation -Constructing landscapes to ensure ecosystem services • Grazing exclusion at flowering peak can double butterfly populations in cattle-grazed ‘intensive’ pastures (Farruggia et al., 2012) • Collective landscape management based on coordination among farmers balances milk production and conservation of shorebirds (Sabatier et al., 2010, 2014)
  • 35. Plant species diversity matters for pasture productivity 0 2 4 6 8 10 12 (Gross et al., Basic Appl. Ecol., 2010) Above-ground biomass (A) Number of Species 4 3 2 1 0 Log Green Biomass (g) -1 AB r² = 0.58 ** MF r² = 0.61 ** MU r² = 0.48 * Overall r² = 0.51 *** The more plant species in a permanent grassland patch, the higher the local productivity Complementarity across neighbouring species
  • 36. Outline  Challenges for the livestock sector  Agroecology for livestock: five goals  1. Integrated animal health management  2. Reduced use of external inputs  3. Recoupled C-N-P cycles  4. Biodiversity use and preservation  5. Systems diversity and resilience  Industrial ecology for intensive livestock systems  Conclusions
  • 37. 5. Increased resilience through systems diversity - Enhancing the complementarity of animals and the diversity of resources J F M A M J J A S O N D 280 ewes LAMBING LACTATION MATIN Conserved forage + concentrate G Fertilized permanent grassland Native rangelands Regrowths on Ewe-lambs WEANING Increase the flexibility of the system through diversified resources 18 ha fertilized grasslands: 4 t DM/ ha Manage rangelands with high biodiversity potential Use non-recoverable resources directly by man fertilized grassland Native rangeland (+ hay if needed) Native rangeland with experienced peers Regrowths on native rangelands (compensatory growth) Green grass on fertilized & native gld 226600 hhaa Gross margin: 97Є/ewe (vs. 58 Є upland central France) Jouven & Benoit, 2011 Dumont et al., 2013
  • 38. Agroforestry: increased diversity and resilience of livestock systems (courtesy CATIE)
  • 39. Outline  Challenges for the livestock sector  Agroecology for livestock: five goals  1. Integrated animal health management  2. Reduced use of external inputs  3. Recoupled C-N-P cycles  4. Biodiversity use and preservation  5. Systems diversity and resilience  Industrial ecology for intensive livestock systems  Conclusions
  • 40. Can ecology also apply to intensive livestock systems?  Industrial ecology can be seen as a new way to reduce the environmental footprint of intensive livestock using specific technologies to reduce impacts, recycle and create symbiosis across sub-systems (Frosh & Gallopoulos, 1989; Holm Nielsen, 2010; Takata et al., 2012) - Enhancing the value of co-products of agriculture through industrial technologies - Contributing significantly to food production by using less land, water and energy
  • 41. Integrated agriculture-aquaculture systems Livestock Rice, fruits, sugar cane Aliment Feed (co-products) (sous-produits de culture) Aliments (végétaux aquatiques) et eau Fish (carp, tilapia) Fertilisation (fumier) produits sous Fertilisation (culture) de Irrigation des cultures et fertilisation (sédiment étangs) Feed and water Fertilization manure) Fertilization (co-products) Irrigation, fertilization High productivity: rice 2t fruits + 10t fish/ha Gross margin: + 50-150 US$ in Bangladesh Nhan et al., 2006 Phong et al., 2010 Decrease inputs for production Reduced pollution But fish can be contaminated with excreta-related pathogens or antibiotics! => WHO guidelines Karim et al., 2011
  • 42. Intensive pig system associated with a digester Pig production indoors Crop production (Grains, oilseeds, etc.) Feed méthanisation Substrat (effluents) de On-farm feed production Biofuels Diversify to Digester Detoxify droppings before use to fertilize crops Lower mortality of piglets secure income High initial investment Other substrates (16%) 250 houses Sales Direct sales Manure biogas to produce Heated housing Fertilization (digesta) Silage of intercrops Dumont et al., 2013
  • 43. Summary  Agroecology goes further than adjusting practices in current agroecosystems; goals (or principles) can be used as a guideline to implement combinations of agroecological practices adapted to local conditions  Some of these principles can also apply to intensive livestock farming systems - Agroecology sensu stricto: strong connection to the soil, food systems with high added value, preservation of biodiversity and environment, poverty alleviation, increased food security. - Industrial Ecology: closes nutrient cycles, integrates with other production systems, adapted to densely populated areas  AE and IE provide options for most livestock systems
  • 44. Thank you for your attention!

Editor's Notes

  1. Large regional differences in kilocalorie consumption but highest rates of increase in consumption of livestock products in the developing World Global production of meat and milk are projected to more than double by 2050-2070 Livestock provides food for at least 830 million food insecure people (FAO) Livestock GDP: 20-40% of agricultural GDP 19 milliards d’animaux (hors poissons) contribuent à l’emploi de 1.3 milliard de personnes dans le monde Dans les pays en développement, la production de viande a triplé et celle de lait a doublé entre de 1980 et 2002 et on prévoit un doublement d’ici 2050 30 % des terres non gélives sont actuellement affectées à la production animale et 1/3 de la production de céréales mondiales est destiné aux animaux 70-85% de l’azote ingéré́ par les animaux est rejeté́ selon les productions et 60% de ces rejets sont perdus ; l’élevage contribue à 18% des émissions totales de GES
  2. Selecting options:
  3. pour info le premier graphique c'est l'abondance des papillons, le second leur richesse spécifique A l'oral il faut bien préciser à même chargement (c'est là où çà devient intéressant car on fait du win-no loose sur biodiversité et niveaux de poroduction)
  4. The priority will be to reduce sanitary risks, as analyzed in the World Health Organization (2006) guideline for fish farming
  5. To recycle and produce electricity Lower mortality of piglets in well heated buildings
  6. Box 5.1: Pastoralist Coping Strategies in Northern Kenya and Southern Ethiopia African pastoralism has evolved in adaptation to harsh environments with very high spatial and temporal variability of rainfall (Ellis, 1995). Several recent studies (Ndikumana et al., 2000, Oba, 2001, McPeak and Barrett, 2001, Hendy and Morton, 2001, Morton, forthcoming) have focussed on the coping strategies used by pastoralists during recent droughts in Northern Kenya and Southern Ethiopia, and the longer-term adaptations that underlie them: Mobility remains the most important pastoralist adaptation to spatial and temporal variations in rainfall, and in drought years many communities make use of fall-back grazing areas unused in “normal” dry-seasons because of distance, land tenure constraints, animal disease problems or conflict. But encroachment on and individuation of communal grazing lands, and the desire to settle to access human services and food aid, have severely limited pastoral mobility. Pastoralists engage in herd accumulation and most evidence now suggests that this is a rational form of insurance against drought. There is considerable debate on the extent to which pastoralists cope by systematically selling livestock during drought or drought-onset, and why they might not do this, but some evidence that they would sell more stock if markets were more efficient. A small proportion of pastoralists now hold some of their wealth in bank accounts, and others use informal savings and credit mechanisms through shopkeepers. Pastoralists also use supplementary feed for livestock, purchased or lopped from trees, as a coping strategy, they intensify animal disease management through indigenous and scientific techniques, and they increasingly pay for access to water from powered boreholes. Livelihood diversification away from pastoralism in this region predominantly takes the form of shifts into low-income or environmentally unsustainable occupations such as charcoal production, rather than an adaptive strategy to reduce ex-ante vulnerability. There are a number of intra-community mechanisms, to distribute both livestock products and the use of live animals to the destitute, but these appear to be breaking down due to high levels of covariate risk within communities.