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Wageningen, 26 March 2015
Frédéric Baudron,
CIMMYT-Ethiopia
Revisiting the Borlaug hypothesis
& alternative approaches to manage the
agriculture-nature interface
Norman Borlaug
1970: Recipient of the Nobel
Peace Price
1964: Director of CIMMYT’s
Wheat Program
‘Father of the Green Revolution’
(Mexico, India, Pakistan)
CIMMYT’s icon ever since
0
1
2
3
4
1960 1970 1980 1990 2000 2010
Maizeyield(tha-1)
0
1
2
3
4
5
6
1960 1970 1980 1990 2000 2010
Wheatyield(tha-1)
India
Mexico
The Green Revolution
● High-yielding, ‘modern’ varieties of
wheat, rice and later maize
 Morphology (short, many tillers, erect leave)
 Traits (high yield potential, wide adaptation, etc)
● Accompanied by a suite of other
changes:
 Technological changes (fertilizer, irrigation)
 Changes in land use
 Changes in the labor economy
● Positive outcomes:
 Improved rural incomes (farmers and laborers)
 Lower food prices
 Transformed a number of developing countries
(e.g. India) from large food importers and recipients
of food aid into food secure countries
The Borlaug Hypothesis: Land Sparing
0
5
10
15
20
25
30
1961 1971 1981 1991 2001 2011
Millionhectares
Mexico, maize
0
0.5
1
1.5
2
2.5
3
3.5
1961 1971 1981 1991 2001 2011
Millionhectares
Mexico, wheat
15.3 Mha
1.4 Mha
0
5
10
15
20
25
1961 1971 1981 1991 2001 2011
Millionhectares
Spared
Actual
India, maize
0
20
40
60
80
100
120
1961 1971 1981 1991 2001 2011
Millionhectares
India, wheat
13.6 Mha
81.6 Mha
Investing in Agriculture to Conserve
nature
● Protected areas are not sufficient
(only 12% of all terrestrial land)
● Growing underfunding of protected
areas
● Species range shift due to climate
change
● Human population tends to be
concentrated in areas rich in
biodiversity
(from
Balmford et
al., 2001)
Agriculture is Expanding
● Additional 3 billion people by 2050
● Increase in global wealth and per
capita consumption
● Rising number of undernourished
people
● National food security… and political
stability
● Global demand for agricultural
products expected to double from
2005 to 2050 (Tilman et al., 2011)
Annual per capita dependence of caloric
demand and GDP (Tilman et al., 2011)
Food price and violent protests (Lagi et al.,
2011)
Cropland expansion in the
tropics and subtropics
Fate of remaining
biodiversity-rich areas?
(FAO, 2010)
Change in
Biodiversity
Altered
Ecosystem
Processes
Increased Flow of
Ecosystem Goods
& Services
Increased
Human Benefits
Change in
Species Traits
Negative Consequences of
Agriculture on Biodiversity
Change in
Biodiversity
Biotic Removals
& Additions
Altered
Ecosystem
Processes
Increased Flow of
Ecosystem Goods
& Services
Increased
Human Benefits
Change in
Species Traits
Negative Consequences of
Agriculture on Biodiversity
Altered
Biogeochemical
& Hydrological
Cycles
Change in
Biodiversity
Biotic Removals
& Additions
Altered
Ecosystem
Processes
Increased Flow of
Ecosystem Goods
& Services
Increased
Human Benefits
Change in
Species Traits
Negative Consequences of
Agriculture on Biodiversity
Altered
Biogeochemical
& Hydrological
Cycles
Change in
Biodiversity
Biotic Removals
& Additions
Altered
Disturbance
Regimes
Altered
Ecosystem
Processes
Increased Flow of
Ecosystem Goods
& Services
Increased
Human Benefits
Change in
Species Traits
Negative Consequences of
Agriculture on Biodiversity
Altered
Biogeochemical
& Hydrological
Cycles
Change in
Biodiversity
Biotic Removals
& Additions
Altered
Disturbance
Regimes
Altered
Ecosystem
Processes
Increased Flow of
Ecosystem Goods
& Services
Increased
Human Benefits
Change in
Species Traits
Altered Habitats
Negative Consequences of
Agriculture on Biodiversity
Altered
Biogeochemical
& Hydrological
Cycles
Change in
Biodiversity
Biotic Removals
& Additions
Altered
Disturbance
Regimes
Altered
Ecosystem
Processes
Increased Flow of
Ecosystem Goods
& Services
Increased
Human Benefits
Change in
Species Traits
Altered Habitats
Negative Consequences of
Agriculture on Biodiversity
Benefits of Land Sparing
● Country-level evidences of
spared land (in theory)
● Biodiversity: Ghana, India,
Uganda (e.g. Phalan et al., 2011;
Hulme et al., 2013)
● Intensification and climate
change mitigation
● Yield gaps
● Poverty traps (low level equilibrium)
(Mueller et al., 2012)
(Phalan et al., 2011)
● Land sparing is ‘imperfect’ (slower
growth, but not reduction in cultivted area)
 Elastic demand for food crops
 Subsidies
 Shift to other crops
● Far-reaching impacts of agro-
chemicals
● Intensification may attract migrants
● Poor access to knowledge and
capital
● Poor transport and infrastructures
Limits to land Sparing
Rudel et al., 2009
Land Sharing as an alternative
(Wright et al., 2012)● Low external input use and retention
of patches of natural habitat
● Integration of land uses
● Dependency of many (open-habitat)
species on farmland
● Farmlands structurally similar to
native vegetation support high
biodiversity
Limits to Land Sharing
● Efficiency of large-scale national
program is very variable
● Organic inputs are scarce
● Extensive practices
 Low yield
 Extra land for the production of biomass and
manure
● Possibility of displacement
 More the 1/3 of the food consumed by
Sweden in 1994 was imported 0
1
2
3
4
5
6
7
8
9
10
Minimum Maximum
Annualadditionallandrequired
fortheperiod2000-2030(Mha)
Land degradation
Protected areas
Urban expansion
(Lambin and Meyfroidt, 2011)
Land Sparing or Sharing?
Based on What Criteria?
● Response of the species of interest
to farming intensity
Land Sparing or Sharing?
Based on What Criteria?
(Baudron and Giller., 2014)
● Response of the species of interest
to farming intensity
● Scale and landscape-specific
circumstances
 Topography, productivity, ‘spatial grain’
Land Sparing or Sharing?
Based on What Criteria?
● Response of the species of interest
to farming intensity
● Scale and landscape-specific
circumstances
 Topography, productivity, ‘spatial grain’
● Threats to the species of interest
 Intensification vs. expansion, contrast
farmland-natural vegetation
Land Sparing or Sharing?
Based on What Criteria?
● Response of the species of interest
to farming intensity
● Scale and landscape-specific
circumstances
 Topography, productivity, ‘spatial grain’
● Threats to the species of interest
 Intensification vs. expansion, contrast
farmland-natural vegetation
● Socio-economic factors
 Land pressure, endowment, technological
options, markets, policies
Land Sparing or Sharing?
Based on What Criteria?
Beyond Sparing vs Sharing?
● Producing differently
● Beyond the plot
● Beyond production
● Supportive markets and policies
● Towards multifunctional landscape mosaics
Beyond Sparing vs Sharing?
Producing differently
Beyond Sparing vs Sharing?
Producing differently
● Managing spillover effects
 Conservation agriculture
 ‘Precision Agriculture’
Beyond Sparing vs Sharing?
Producing differently
(Steffen et al., 2011)
● Managing spillover effects
 Conservation agriculture
 ‘Precision Agriculture’
● Maintaining resilience
 Stress tolerant varieties
 Mixture of species/cultivars
Beyond Sparing vs Sharing?
Producing differently
● Managing spillover effects
 Conservation agriculture
 ‘Precision Agriculture’
● Maintaining resilience
 Stress tolerant varieties
 Mixture of species/cultivars
● Maintaining ecological interactions
 Intra-guild interactions (resource partitioning, competition,
facilitation)
 Trophic interactions (decomposers, predators, parasites)
 Spatial dynamics (ecological subsidies) and temporal
dynamics (disturbance regime)
 Stability by self organization
Beyond Sparing vs Sharing?
Beyond the plot
Beyond Sparing vs Sharing?
Beyond the plot
● Redesigning farming systems
at farm-level
 Management of populations of
natural enemies
 Facilitative interaction
 Nutrient transfer
10
15
20
25
30
35
40
0 2 4 6 8 10 12 14 16 18 20 22 24
Airtemperature(°C)
Time of the day (h)
Outside canopy
Under canopy
0
20
40
60
80
1 10 30
Numberofrovebeetles
captured
Distance to ensete field (m)
Beyond Sparing vs Sharing?
Beyond the plot
● Redesigning farming systems
at farm-level
 Management of populations of
natural enemies
 Facilitative interaction
 Nutrient transfer
● Redesigning farming systems
at landscape-level
 Collective action at territory level
 Institutional innovation
(Baudron et al., submitted)
Beyond Sparing vs Sharing?
Beyond production
Beyond Sparing vs Sharing?
Beyond production
● Reduction of food losses and
wastes
 Storage and cooling facilities
 Transport from the farm to the market
Beyond Sparing vs Sharing?
Beyond production
● Reduction of food losses and
wastes
 Storage and cooling facilities
 Transport from the farm to the market
● Access to food
 ‘Food sovereignty’: equitable distribution and
local accessibility
 Securing land tenure to smallholders
Beyond Sparing vs Sharing?
Beyond production
● Reduction of food losses and
wastes
 Storage and cooling facilities
 Transport from the farm to the market
● Access to food
 ‘Food sovereignty’: equitable distribution and
local accessibility
 Securing land tenure to smallholders
● Changes in consumption patterns
 Discourage grain fed livestock
 Discourage biofuel production that competes
with food crop production
Beyond Sparing vs Sharing?
Supportive markets and policies
Beyond Sparing vs Sharing?
Supportive markets and policies
● Valuing biodiversity, and returning this
value to farmers
 Pricing (embodying the true costs and benefits of agricultural
practices) and labelling of commodities
 Compensation (foregone use of land, disservices) and
rewards (PES)
Beyond Sparing vs Sharing?
Supportive markets and policies
● Valuing biodiversity, and returning this
value to farmers
 Pricing (embodying the true costs and benefits of agricultural
practices) and labelling of commodities
 Compensation (foregone use of land, disservices) and
rewards (PES)
● Policy framework
 Agri-environment payments to farmers
 Policies that prevent deforestation & encourage
abandonment
 Control of immigration in developing countries
 Removal of perverse policies (e.g. subsidies)
 Incentives that promote production and
consumption patterns that are less demanding in
NR
Beyond Sparing vs Sharing?
Towards multifunctional landscape mosaics
Relativeabundance
Crop productivty Livestock productivity
Fuelwood availability
Wild food
?
Relativeabundance
Food system, nutrition
?
Relativeabundance
Beyond Sparing vs Sharing?
Towards multifunctional landscape mosaics
Natural ennemies Pollinators Hydrology Erosion control
Interactions between patches
Nutrient transfer
Conclusion
● Green Revolution: adapted to the context
of the 60s and 70s, but no longer the right
model
● Major move of CIMMYT towards
‘sustainable intensification’
● Agriculture as an opportunity for
conservation (not only a threat)
● Biodiversity as input to farming
● Expanding the partnership between
conservation organizations and
agricultural agencies
THANK YOU

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Revisiting the Borlaug hypothesis

  • 1. Wageningen, 26 March 2015 Frédéric Baudron, CIMMYT-Ethiopia Revisiting the Borlaug hypothesis & alternative approaches to manage the agriculture-nature interface
  • 2.
  • 3. Norman Borlaug 1970: Recipient of the Nobel Peace Price 1964: Director of CIMMYT’s Wheat Program ‘Father of the Green Revolution’ (Mexico, India, Pakistan) CIMMYT’s icon ever since
  • 4. 0 1 2 3 4 1960 1970 1980 1990 2000 2010 Maizeyield(tha-1) 0 1 2 3 4 5 6 1960 1970 1980 1990 2000 2010 Wheatyield(tha-1) India Mexico The Green Revolution ● High-yielding, ‘modern’ varieties of wheat, rice and later maize  Morphology (short, many tillers, erect leave)  Traits (high yield potential, wide adaptation, etc) ● Accompanied by a suite of other changes:  Technological changes (fertilizer, irrigation)  Changes in land use  Changes in the labor economy ● Positive outcomes:  Improved rural incomes (farmers and laborers)  Lower food prices  Transformed a number of developing countries (e.g. India) from large food importers and recipients of food aid into food secure countries
  • 5. The Borlaug Hypothesis: Land Sparing 0 5 10 15 20 25 30 1961 1971 1981 1991 2001 2011 Millionhectares Mexico, maize 0 0.5 1 1.5 2 2.5 3 3.5 1961 1971 1981 1991 2001 2011 Millionhectares Mexico, wheat 15.3 Mha 1.4 Mha 0 5 10 15 20 25 1961 1971 1981 1991 2001 2011 Millionhectares Spared Actual India, maize 0 20 40 60 80 100 120 1961 1971 1981 1991 2001 2011 Millionhectares India, wheat 13.6 Mha 81.6 Mha
  • 6. Investing in Agriculture to Conserve nature ● Protected areas are not sufficient (only 12% of all terrestrial land) ● Growing underfunding of protected areas ● Species range shift due to climate change ● Human population tends to be concentrated in areas rich in biodiversity (from Balmford et al., 2001)
  • 7. Agriculture is Expanding ● Additional 3 billion people by 2050 ● Increase in global wealth and per capita consumption ● Rising number of undernourished people ● National food security… and political stability ● Global demand for agricultural products expected to double from 2005 to 2050 (Tilman et al., 2011) Annual per capita dependence of caloric demand and GDP (Tilman et al., 2011) Food price and violent protests (Lagi et al., 2011)
  • 8. Cropland expansion in the tropics and subtropics Fate of remaining biodiversity-rich areas? (FAO, 2010)
  • 9. Change in Biodiversity Altered Ecosystem Processes Increased Flow of Ecosystem Goods & Services Increased Human Benefits Change in Species Traits Negative Consequences of Agriculture on Biodiversity
  • 10. Change in Biodiversity Biotic Removals & Additions Altered Ecosystem Processes Increased Flow of Ecosystem Goods & Services Increased Human Benefits Change in Species Traits Negative Consequences of Agriculture on Biodiversity
  • 11. Altered Biogeochemical & Hydrological Cycles Change in Biodiversity Biotic Removals & Additions Altered Ecosystem Processes Increased Flow of Ecosystem Goods & Services Increased Human Benefits Change in Species Traits Negative Consequences of Agriculture on Biodiversity
  • 12. Altered Biogeochemical & Hydrological Cycles Change in Biodiversity Biotic Removals & Additions Altered Disturbance Regimes Altered Ecosystem Processes Increased Flow of Ecosystem Goods & Services Increased Human Benefits Change in Species Traits Negative Consequences of Agriculture on Biodiversity
  • 13. Altered Biogeochemical & Hydrological Cycles Change in Biodiversity Biotic Removals & Additions Altered Disturbance Regimes Altered Ecosystem Processes Increased Flow of Ecosystem Goods & Services Increased Human Benefits Change in Species Traits Altered Habitats Negative Consequences of Agriculture on Biodiversity
  • 14. Altered Biogeochemical & Hydrological Cycles Change in Biodiversity Biotic Removals & Additions Altered Disturbance Regimes Altered Ecosystem Processes Increased Flow of Ecosystem Goods & Services Increased Human Benefits Change in Species Traits Altered Habitats Negative Consequences of Agriculture on Biodiversity
  • 15. Benefits of Land Sparing ● Country-level evidences of spared land (in theory) ● Biodiversity: Ghana, India, Uganda (e.g. Phalan et al., 2011; Hulme et al., 2013) ● Intensification and climate change mitigation ● Yield gaps ● Poverty traps (low level equilibrium) (Mueller et al., 2012) (Phalan et al., 2011)
  • 16. ● Land sparing is ‘imperfect’ (slower growth, but not reduction in cultivted area)  Elastic demand for food crops  Subsidies  Shift to other crops ● Far-reaching impacts of agro- chemicals ● Intensification may attract migrants ● Poor access to knowledge and capital ● Poor transport and infrastructures Limits to land Sparing Rudel et al., 2009
  • 17. Land Sharing as an alternative (Wright et al., 2012)● Low external input use and retention of patches of natural habitat ● Integration of land uses ● Dependency of many (open-habitat) species on farmland ● Farmlands structurally similar to native vegetation support high biodiversity
  • 18. Limits to Land Sharing ● Efficiency of large-scale national program is very variable ● Organic inputs are scarce ● Extensive practices  Low yield  Extra land for the production of biomass and manure ● Possibility of displacement  More the 1/3 of the food consumed by Sweden in 1994 was imported 0 1 2 3 4 5 6 7 8 9 10 Minimum Maximum Annualadditionallandrequired fortheperiod2000-2030(Mha) Land degradation Protected areas Urban expansion (Lambin and Meyfroidt, 2011)
  • 19. Land Sparing or Sharing? Based on What Criteria?
  • 20. ● Response of the species of interest to farming intensity Land Sparing or Sharing? Based on What Criteria? (Baudron and Giller., 2014)
  • 21. ● Response of the species of interest to farming intensity ● Scale and landscape-specific circumstances  Topography, productivity, ‘spatial grain’ Land Sparing or Sharing? Based on What Criteria?
  • 22. ● Response of the species of interest to farming intensity ● Scale and landscape-specific circumstances  Topography, productivity, ‘spatial grain’ ● Threats to the species of interest  Intensification vs. expansion, contrast farmland-natural vegetation Land Sparing or Sharing? Based on What Criteria?
  • 23. ● Response of the species of interest to farming intensity ● Scale and landscape-specific circumstances  Topography, productivity, ‘spatial grain’ ● Threats to the species of interest  Intensification vs. expansion, contrast farmland-natural vegetation ● Socio-economic factors  Land pressure, endowment, technological options, markets, policies Land Sparing or Sharing? Based on What Criteria?
  • 24. Beyond Sparing vs Sharing? ● Producing differently ● Beyond the plot ● Beyond production ● Supportive markets and policies ● Towards multifunctional landscape mosaics
  • 25. Beyond Sparing vs Sharing? Producing differently
  • 26. Beyond Sparing vs Sharing? Producing differently ● Managing spillover effects  Conservation agriculture  ‘Precision Agriculture’
  • 27. Beyond Sparing vs Sharing? Producing differently (Steffen et al., 2011) ● Managing spillover effects  Conservation agriculture  ‘Precision Agriculture’ ● Maintaining resilience  Stress tolerant varieties  Mixture of species/cultivars
  • 28. Beyond Sparing vs Sharing? Producing differently ● Managing spillover effects  Conservation agriculture  ‘Precision Agriculture’ ● Maintaining resilience  Stress tolerant varieties  Mixture of species/cultivars ● Maintaining ecological interactions  Intra-guild interactions (resource partitioning, competition, facilitation)  Trophic interactions (decomposers, predators, parasites)  Spatial dynamics (ecological subsidies) and temporal dynamics (disturbance regime)  Stability by self organization
  • 29. Beyond Sparing vs Sharing? Beyond the plot
  • 30. Beyond Sparing vs Sharing? Beyond the plot ● Redesigning farming systems at farm-level  Management of populations of natural enemies  Facilitative interaction  Nutrient transfer 10 15 20 25 30 35 40 0 2 4 6 8 10 12 14 16 18 20 22 24 Airtemperature(°C) Time of the day (h) Outside canopy Under canopy 0 20 40 60 80 1 10 30 Numberofrovebeetles captured Distance to ensete field (m)
  • 31. Beyond Sparing vs Sharing? Beyond the plot ● Redesigning farming systems at farm-level  Management of populations of natural enemies  Facilitative interaction  Nutrient transfer ● Redesigning farming systems at landscape-level  Collective action at territory level  Institutional innovation (Baudron et al., submitted)
  • 32. Beyond Sparing vs Sharing? Beyond production
  • 33. Beyond Sparing vs Sharing? Beyond production ● Reduction of food losses and wastes  Storage and cooling facilities  Transport from the farm to the market
  • 34. Beyond Sparing vs Sharing? Beyond production ● Reduction of food losses and wastes  Storage and cooling facilities  Transport from the farm to the market ● Access to food  ‘Food sovereignty’: equitable distribution and local accessibility  Securing land tenure to smallholders
  • 35. Beyond Sparing vs Sharing? Beyond production ● Reduction of food losses and wastes  Storage and cooling facilities  Transport from the farm to the market ● Access to food  ‘Food sovereignty’: equitable distribution and local accessibility  Securing land tenure to smallholders ● Changes in consumption patterns  Discourage grain fed livestock  Discourage biofuel production that competes with food crop production
  • 36. Beyond Sparing vs Sharing? Supportive markets and policies
  • 37. Beyond Sparing vs Sharing? Supportive markets and policies ● Valuing biodiversity, and returning this value to farmers  Pricing (embodying the true costs and benefits of agricultural practices) and labelling of commodities  Compensation (foregone use of land, disservices) and rewards (PES)
  • 38. Beyond Sparing vs Sharing? Supportive markets and policies ● Valuing biodiversity, and returning this value to farmers  Pricing (embodying the true costs and benefits of agricultural practices) and labelling of commodities  Compensation (foregone use of land, disservices) and rewards (PES) ● Policy framework  Agri-environment payments to farmers  Policies that prevent deforestation & encourage abandonment  Control of immigration in developing countries  Removal of perverse policies (e.g. subsidies)  Incentives that promote production and consumption patterns that are less demanding in NR
  • 39. Beyond Sparing vs Sharing? Towards multifunctional landscape mosaics Relativeabundance Crop productivty Livestock productivity Fuelwood availability Wild food ? Relativeabundance Food system, nutrition ? Relativeabundance
  • 40. Beyond Sparing vs Sharing? Towards multifunctional landscape mosaics Natural ennemies Pollinators Hydrology Erosion control Interactions between patches Nutrient transfer
  • 41. Conclusion ● Green Revolution: adapted to the context of the 60s and 70s, but no longer the right model ● Major move of CIMMYT towards ‘sustainable intensification’ ● Agriculture as an opportunity for conservation (not only a threat) ● Biodiversity as input to farming ● Expanding the partnership between conservation organizations and agricultural agencies

Notes de l'éditeur

  1. Although increased use of fertilizer increases greenhouse gas emission due to the energy costs of manufacture, these costs are offset by reduced greenhouse gas emissions through deforestation, as less land is needed to produce the same quantity of food or other products.
  2. Increase in yield generally leads to a slower growth of cultivated area compared with population growth, but not to an increase in forested areas Unmet demand in the developing world, and emerging markets such as biofuels or grain-fed livestock
  3. Farm abandonment leads to regeneration of forest that supports a narrower range of species than a heterogeneous mosaic of land-uses, and intensification leads to a loss of spatial and temporal heterogeneity
  4. ‘Food sovereignty’ promotes the right of people to define their own food production and consumption at the local, national and global level (Rosset, 2008) Poultry and fish are three times more efficient as cattle in converting grain into meat
  5. ‘Food sovereignty’ promotes the right of people to define their own food production and consumption at the local, national and global level (Rosset, 2008) Poultry and fish are three times more efficient as cattle in converting grain into meat
  6. ‘Food sovereignty’ promotes the right of people to define their own food production and consumption at the local, national and global level (Rosset, 2008) Beef fed on pasture or crop residues; poultry and fish Poultry and fish are three times more efficient as cattle in converting grain into meat