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Sustainable land management and carbon
 finance: a case study on landless mobile
  pastoralists in the Hindu Kush Himalaya
     mountains of northern Pakistan
    Henri Rueff, Inam ur Rahim, Sayed Aziz
      Rehman, Daniel Maselli, Khurshid
       Muhammad, Nafees Muhammad
             henri.rueff@geog.ox.ac.uk
Carbon in a pro-poor and pastoralism context
> Rangelands are being only recently scrutinized for carbon
  schemes
> 30% of the world’s land cover is rangeland
> Pastoralists are often composing the poorest segment society
> Perception towards pastoralists: contributors or degraders?
  Valuing ES!
> Carbon market dysfunctions: CDM failed to deliver SD
> Alternative: social carbon credits towards SD and poverty
  reduction, community based carbon projects (CCSB/Plan Vivo)
> Advantages of a carbon scheme for herders: trading a
  commodity without a hub
> Land richer in carbon enhances adaptation
Research question
> Poor current market conditions with low carbon prices:
   > what schemes could work?
> Conventional mitigation schemes in rangelands are based on pasture
  improvement and stock reduction:
   > How does avoided emissions renouncing cropping compares to these
      conventional rangeland mitigation schemes?
   > How can carbon finance enhance SLM?

                           Looking at an overstocking case
              Livelihood




                                       Baseline scenario (overstocking)

                           Minimum carbon payment
                            Mitigation scenario (carrying capacity)




                                                              Time
Context in the Naran valley (Pakistan
Himalayas)

> Under the guidance of developement agencies in the 80s, herders
  have been planting off-season potatoes and peas at high altitude,
  which rewards 10 times the usual herding activity, nevertheless....
> Steep slopes without terracing leading to soil loss
> Rapid decline in yields
> Land becomes unsuitable for cropping nor grazing after a short
  period
> Herders are pushed to pastures at higher elevations fostering
  degradation because of a shorter growing season
> Changes in the division of labour. The fittest crop, the weaker
  (elders) herd in hostile environments
Methodology
Hypotheses
(i) cropping on alpine pastures reduces former carbon storage
(ii) the avoided emission from renouncing cropping is a superior mitigation
     choice than improved pastures

To solve (i)
72 soil core samples discriminating in triplicates for
> 2 land uses (cropping, pasture)
> 3 aspects (North, South)
> 3 elevations (low 3000, middle 3100, and high 3200 m a.s.l.)
> 2 soil depths (shallow 0-10, deep 10-30 cm)
Soil samples were air-dried, sifted
36 above and below-ground (coarse roots) biomass samples oven-dried
Potassium dichromate oxidation treatment

To solve (ii) we compare data with existing literature and integrate an ex-ante
    model (FAO) (in progress)
Case study: pastoral system in the Himalaya of
Pakistan
Results soil



                                                                                       18
                 400                      18                   21
Soil organic carbon




                                                                                       15
                 350                      15                   18
                 300                                           15                      12
                                          12
       [g kg-1]




                 250                                           12                       9
                                           9
                 200                                            9                       6
                 150                       6                    6
                                           3                                            3
                 100                                            3
                  50                       0                    0                       0
                       Pasture Cropland        South   North        Low   Mid   High        0-10 cm 10-30 cm
Results biomass

                                                  400




                                 Biomass carbon
                                                  350
                                                  300




                                     [g m-2]
                                                  250
                                                  200
                                                  150
                                                  100
                                                   50
                                                        Pasture Cropland

> Avoided emissions are likely to yield higher payments than
  conventional grassland improvement (under investigation)
  Preventing the conversion of pastures into cropping fields avoids
  an average loss of 12.2 t C ha-1 or 44.8 t CO2e ha-1.
> Enteric methane release from livestock in the pasture scenario is
  largely nullified by increasing greenhouse gas releases due to
  fertilizer inputs needed in the cropping scenario. (likely, under
  investigation)
Discussion – issues to consider


> Solve non-market leakage issues
Mitigate here but transfer emissions elsewhere!
Solution: contractual, monitoring

> Solve market leakage issues
Consequences of the lack of supply of off-
season crops to the market
Solution: integrate in the mitigation scenario,
use buffer credits, monitoring, terracing
Discussion – issues to consider

> Predict baseline
Selling a commodity reflecting the avoidance of
what you think will occur
Solution: use proxies, understand project
boundaries

> Transaction costs
Main cause of dysfunctions
Solution: create larger project units, sell high
quality carbon credits at a higher price (poverty
alleviation, SLM)
Conclusion

> Carbon payment is attractive but does it work?
> Complex accounting, unawareness among
practitioners and pastoralists
> More important than carbon – valuing overall
ecosystem services provided by pastoralists and
build societal awareness (food security, biodiversity
Landscaping, cultural heritage etc…)
Thank you

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Henri RUEF "Sustainable land management and carbon finance: a case study on landless mobile pastoralists in the Hindu Kush Himalaya mountains of northern Pakistan"

  • 1. Sustainable land management and carbon finance: a case study on landless mobile pastoralists in the Hindu Kush Himalaya mountains of northern Pakistan Henri Rueff, Inam ur Rahim, Sayed Aziz Rehman, Daniel Maselli, Khurshid Muhammad, Nafees Muhammad henri.rueff@geog.ox.ac.uk
  • 2. Carbon in a pro-poor and pastoralism context > Rangelands are being only recently scrutinized for carbon schemes > 30% of the world’s land cover is rangeland > Pastoralists are often composing the poorest segment society > Perception towards pastoralists: contributors or degraders? Valuing ES! > Carbon market dysfunctions: CDM failed to deliver SD > Alternative: social carbon credits towards SD and poverty reduction, community based carbon projects (CCSB/Plan Vivo) > Advantages of a carbon scheme for herders: trading a commodity without a hub > Land richer in carbon enhances adaptation
  • 3. Research question > Poor current market conditions with low carbon prices: > what schemes could work? > Conventional mitigation schemes in rangelands are based on pasture improvement and stock reduction: > How does avoided emissions renouncing cropping compares to these conventional rangeland mitigation schemes? > How can carbon finance enhance SLM? Looking at an overstocking case Livelihood Baseline scenario (overstocking) Minimum carbon payment Mitigation scenario (carrying capacity) Time
  • 4. Context in the Naran valley (Pakistan Himalayas) > Under the guidance of developement agencies in the 80s, herders have been planting off-season potatoes and peas at high altitude, which rewards 10 times the usual herding activity, nevertheless.... > Steep slopes without terracing leading to soil loss > Rapid decline in yields > Land becomes unsuitable for cropping nor grazing after a short period > Herders are pushed to pastures at higher elevations fostering degradation because of a shorter growing season > Changes in the division of labour. The fittest crop, the weaker (elders) herd in hostile environments
  • 5. Methodology Hypotheses (i) cropping on alpine pastures reduces former carbon storage (ii) the avoided emission from renouncing cropping is a superior mitigation choice than improved pastures To solve (i) 72 soil core samples discriminating in triplicates for > 2 land uses (cropping, pasture) > 3 aspects (North, South) > 3 elevations (low 3000, middle 3100, and high 3200 m a.s.l.) > 2 soil depths (shallow 0-10, deep 10-30 cm) Soil samples were air-dried, sifted 36 above and below-ground (coarse roots) biomass samples oven-dried Potassium dichromate oxidation treatment To solve (ii) we compare data with existing literature and integrate an ex-ante model (FAO) (in progress)
  • 6. Case study: pastoral system in the Himalaya of Pakistan
  • 7.
  • 8. Results soil 18 400 18 21 Soil organic carbon 15 350 15 18 300 15 12 12 [g kg-1] 250 12 9 9 200 9 6 150 6 6 3 3 100 3 50 0 0 0 Pasture Cropland South North Low Mid High 0-10 cm 10-30 cm
  • 9. Results biomass 400 Biomass carbon 350 300 [g m-2] 250 200 150 100 50 Pasture Cropland > Avoided emissions are likely to yield higher payments than conventional grassland improvement (under investigation) Preventing the conversion of pastures into cropping fields avoids an average loss of 12.2 t C ha-1 or 44.8 t CO2e ha-1. > Enteric methane release from livestock in the pasture scenario is largely nullified by increasing greenhouse gas releases due to fertilizer inputs needed in the cropping scenario. (likely, under investigation)
  • 10. Discussion – issues to consider > Solve non-market leakage issues Mitigate here but transfer emissions elsewhere! Solution: contractual, monitoring > Solve market leakage issues Consequences of the lack of supply of off- season crops to the market Solution: integrate in the mitigation scenario, use buffer credits, monitoring, terracing
  • 11. Discussion – issues to consider > Predict baseline Selling a commodity reflecting the avoidance of what you think will occur Solution: use proxies, understand project boundaries > Transaction costs Main cause of dysfunctions Solution: create larger project units, sell high quality carbon credits at a higher price (poverty alleviation, SLM)
  • 12. Conclusion > Carbon payment is attractive but does it work? > Complex accounting, unawareness among practitioners and pastoralists > More important than carbon – valuing overall ecosystem services provided by pastoralists and build societal awareness (food security, biodiversity Landscaping, cultural heritage etc…)