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Local Landscape Solutions:
   L lL d           S l ti
An Agriculture and Food Security 
An Agriculture and Food Security
           Perspective
   Lini  Wollenberg, CCAFS at University of Vermont
                  Bonn, 8  June 2011
Land sparing: important technical 
         option in agriculture
Total anthropogenic GHG emissions
T t l th          i GHG      i i
• 18% from land‐use change (includes 
  deforestation)
• 10‐12% from all agricultural sources (or 6.8 Gt of 
  CO2‐eq) 
  CO2 eq)

Technical mitigation potential of agriculture is : 
T h i l iti ti         t ti l f      i lt     i
           5.5‐6 Gt CO2‐eq. yr‐1 by 2030 
Economic potential l
           1.5‐4.3 Gt
BUT Limited success of interventions
BUT Limited success of interventions
“Green revolution to shifting cultivation” Greenland 1975 
Agroforestry and Alternatives to Slash and Burn, Sanchez et 
     f          d l                l h d              h
    al. 2005; Swallow, Boffa and Scherr 1996
Protected area management: ICDPS, buffer zones (Hughes 
Protected area management: ICDPS buffer zones (Hughes
    and  Flintan 2001)
  • Incentive to intensify not linked to forest 
                         y
    conservation
  • Conversion linked to multiple local and macro 
    causes of (migration, infrastructure, fire, drought, 
             f ( i ti      i f t t         fi d      ht
    markets, wood extraction, technology) (Hirsch and 
    Fisher 2007)
    Fisher 2007)
  • Past projects limited by focus on local technical 
    interventions
  • Efficiencies encourage expansion
Limited land reserves 
         Limited land reserves
‐Only 445 Mha arable, non protected land left
  (
  (10%))

  ‐If current demands for food and energy met 
   If         d     d f f d d
  with no clearing of natural forest, leaves 
  balance of 71 to –347 Mha

                   (Lambin 2011)
Increased vulnerability from 
      intensification (Lin et al. 2008)
• High‐yielding, input‐intensive varieties increase 
    i h i ldi i        i     i       i i i
  demand for nutrients and water
• Nutrients and water often lost from the system 
  and external inputs required
• Outside infrastructure required to maintain 
  resources for crop production (petrochemicals)
• In Sweden and Tanzania found higher 
  management intensity (fewer wild varieties, less 
        g                y(                     ,
  temporal and spatial  diversity),  associated with 
                                        g
  less resilience to ENSO events/drought.
Importance of 
     context
        t t
     Palm et al 2010:

     (1) Tanzania 
     Population density –low
     Land availability –
     Land availability – high
     Intensification under each scenario 
     leads to surplus crop area for 
     reforestation.

     (2) W. Kenya
     Population density – high
         p                   y      g
     Land availability – low 
     Need mineral fertilizers to make 
     land available for reforestation.
      ‐ green manure or improved tree 
     fallows not enough increase in 
     yields to permit reforestation. 
     ‐
    Palm C A et al. PNAS 2010;107:19661-19666


©2010 by National Academy of Sciences
Time limit to benefits of intensification
Time limit to benefits of intensification
Northern Mountain Region of Vietnam (Leisz et al. 2009)
N th     M    t i R i      f Vi t    (L i t l 2009)
• Current swidden systems contribute significant GHG 
  emissions  
  emissions

• If the NMR farming systems change according to
  If the NMR farming systems change according to 
  government policies and programs, net C sequestration 
  occurs in first 20 years

• But, over the longer term, increased GHG emissions 
  from changes in the farming systems (e.g. increased 
  from changes in the farming systems (e g increased
  paddy and increased confinement pig raising due to 
  government policies) will overtake the C in vegetation 
Need for institutional arrangements
Need for institutional arrangements
• Regional NRM bodies adaptively manage
  Regional NRM bodies adaptively manage, 
  collaborative frameworks negotiated between 
  Federal and State levels (Australia‐
  Federal and State levels (Australia Oosterzee
  et al. 2011) 
• Integrated sustainable development for 
            d         bl d l             f
  smallholders and REDD+ (Brazil, Stella et al. 
  2011)
• Land tenure, zoning (Kissinger, 2011)
                ,    g(      g ,       )
• Enforcement, project efficacy (Agrawal 2011)
Local Landscape Solutions
        Local Landscape Solutions
1. Better understanding of local intensification and 
1 Better understanding of local intensification and
     trade‐offs dynamics in different contexts and scales
2. Develop multi‐scale institutions that address drivers,
     Develop multi scale institutions that address drivers, 
     food needs local economic needs of smallholders
         p                  y
3.   Improve sustainability of intensification: 
    ‐ innovation in efficiencies, coupling, integration and 
                       y
     multifunctionality, 
     ‐reduce emissions in agriculture and land use change
4.   Ask what are the limits to intensification?
       s    at a e t e      ts to te s cat o

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Wollenberg local landscapes bonn 2011

  • 1. Local Landscape Solutions: L lL d S l ti An Agriculture and Food Security  An Agriculture and Food Security Perspective Lini  Wollenberg, CCAFS at University of Vermont Bonn, 8  June 2011
  • 2. Land sparing: important technical  option in agriculture Total anthropogenic GHG emissions T t l th i GHG i i • 18% from land‐use change (includes  deforestation) • 10‐12% from all agricultural sources (or 6.8 Gt of  CO2‐eq)  CO2 eq) Technical mitigation potential of agriculture is :  T h i l iti ti t ti l f i lt i 5.5‐6 Gt CO2‐eq. yr‐1 by 2030  Economic potential l 1.5‐4.3 Gt
  • 3. BUT Limited success of interventions BUT Limited success of interventions “Green revolution to shifting cultivation” Greenland 1975  Agroforestry and Alternatives to Slash and Burn, Sanchez et  f d l l h d h al. 2005; Swallow, Boffa and Scherr 1996 Protected area management: ICDPS, buffer zones (Hughes  Protected area management: ICDPS buffer zones (Hughes and  Flintan 2001) • Incentive to intensify not linked to forest  y conservation • Conversion linked to multiple local and macro  causes of (migration, infrastructure, fire, drought,  f ( i ti i f t t fi d ht markets, wood extraction, technology) (Hirsch and  Fisher 2007) Fisher 2007) • Past projects limited by focus on local technical  interventions • Efficiencies encourage expansion
  • 4. Limited land reserves  Limited land reserves ‐Only 445 Mha arable, non protected land left ( (10%)) ‐If current demands for food and energy met  If d d f f d d with no clearing of natural forest, leaves  balance of 71 to –347 Mha (Lambin 2011)
  • 5. Increased vulnerability from  intensification (Lin et al. 2008) • High‐yielding, input‐intensive varieties increase  i h i ldi i i i i i i demand for nutrients and water • Nutrients and water often lost from the system  and external inputs required • Outside infrastructure required to maintain  resources for crop production (petrochemicals) • In Sweden and Tanzania found higher  management intensity (fewer wild varieties, less  g y( , temporal and spatial  diversity),  associated with  g less resilience to ENSO events/drought.
  • 6. Importance of  context t t Palm et al 2010: (1) Tanzania  Population density –low Land availability – Land availability – high Intensification under each scenario  leads to surplus crop area for  reforestation. (2) W. Kenya Population density – high p y g Land availability – low  Need mineral fertilizers to make  land available for reforestation. ‐ green manure or improved tree  fallows not enough increase in  yields to permit reforestation.  ‐ Palm C A et al. PNAS 2010;107:19661-19666 ©2010 by National Academy of Sciences
  • 7. Time limit to benefits of intensification Time limit to benefits of intensification Northern Mountain Region of Vietnam (Leisz et al. 2009) N th M t i R i f Vi t (L i t l 2009) • Current swidden systems contribute significant GHG  emissions   emissions • If the NMR farming systems change according to If the NMR farming systems change according to  government policies and programs, net C sequestration  occurs in first 20 years • But, over the longer term, increased GHG emissions  from changes in the farming systems (e.g. increased  from changes in the farming systems (e g increased paddy and increased confinement pig raising due to  government policies) will overtake the C in vegetation 
  • 8. Need for institutional arrangements Need for institutional arrangements • Regional NRM bodies adaptively manage Regional NRM bodies adaptively manage,  collaborative frameworks negotiated between  Federal and State levels (Australia‐ Federal and State levels (Australia Oosterzee et al. 2011)  • Integrated sustainable development for  d bl d l f smallholders and REDD+ (Brazil, Stella et al.  2011) • Land tenure, zoning (Kissinger, 2011) , g( g , ) • Enforcement, project efficacy (Agrawal 2011)
  • 9. Local Landscape Solutions Local Landscape Solutions 1. Better understanding of local intensification and  1 Better understanding of local intensification and trade‐offs dynamics in different contexts and scales 2. Develop multi‐scale institutions that address drivers, Develop multi scale institutions that address drivers,  food needs local economic needs of smallholders p y 3.   Improve sustainability of intensification:  ‐ innovation in efficiencies, coupling, integration and  y multifunctionality,  ‐reduce emissions in agriculture and land use change 4.   Ask what are the limits to intensification? s at a e t e ts to te s cat o