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Presentation for Smallholder Mitigation: Mitigation Options and Incentive Mechanisms - Expert Workshop 7 - 8 July 2011
Citation preview
Comparison of cost-benefit analyses
for mitigation in different
agroecosystems
Alex De Pinto
IFPRI
Rome
July, 2011
Challenges and Opportunities
Opportunities (besides CC mitigation)
• Help small poor farmers dealing with the effects of
climate change
• Provide farmers with an additional source of income
• Food security and resilience
Challenges
• Uncertainty
• Identify “correct” set of incentives
Co-benefits of mitigation
Mitigation practices overlap considerably with
sustainable use of resources
Positive correlation between soil C and crop
yield. Some agricultural practices improve soil
fertility and induce C sequestration
More efficient water use (reduces CO2 from
fuel/electricity): good for adaptation
Agricultural R&D, advisory services, and
information systems
Total technical mitigation potentials (all practices, all GHGs: MtCO2-eq/yr) for each region by 2030.
Note: based on the B2 scenario though the pattern is similar for all SRES scenarios.
Source: Smith et al. (2007a).)
Global mitigation potential in agriculture
We Can Do Better Now
The Example of GhanaProvince Most Common Cropping
system/rotation
Most Common Cropping
system/rotation
Mitigation Options
Ashanti Maize, cassava, 2 years
fallow
No- burning/Manure/recommended amount of
fertilizer
Brong Ahafo Maize, cassava, 2 years
fallow
Yam, 2 years fallow No- burning/Manure/recommended amount of
fertilizer
Central Maize, cassava, 2 years
fallow
No- burning/Manure/recommended amount of
fertilizer
Eastern Maize, cassava, 2 years
fallow
Evolving into oil palm
No- burning/Manure/recommended amount of
fertilizer
Greater Accra Tomato, watermelon, maize Tomato, watermelon,
maize
Manure/recommended amount of fertilizer/no-till
Northern Yam, maize, groundnuts, 1
year fallow
Manure/recommended amount of fertilizer
Upper East Sorghum, groundnuts, maize,
fallow
Millet, groundnuts,
sorghum, fallow
Manure/recommended amount of fertilizer
Upper West Sorghum, groundnuts, maize,
fallow
Maize, groundnuts,
sorghum, fallow
Manure/recommended amount of fertilizer
Volta Maize, cassava, 2 years
fallow
Yam, 2 years fallow,
maize, cassava, 2 year
fallow
No- burning/Manure/recommended amount of
fertilizer
Western Maize, cassava,
Evolving into cocoa
The Example of Ghana
Source: own simulations with DSSAT
SOC (kg[SOC]/ha/yr)High : 150
Low : 1
Fertilizer, Manure Fertilizer, Manure, No-Till
SOC (kg[SOC]/ha/yr)High : 150
Low : 1
Fertilizer, Manure, Residue management Fertilizer, Manure, Residue management No-Till
Page 10
GHANA
Price of CO2eq
$20 GCM Type, grwoth scenario, CO2 sequestered Opt. Fertilizer Opt. Fertilizer, ManureOpt. Fertilizer, Manure , Residue management
CNRM-CM3, A2, Kg/yr 290862046.9 393020643.9 905733453.5
CSIRO-Mk3.0, A2, Kg/yr 288863610.3 378381542.6 876924355.8
ECHam5, A2, Kg/yr 308123656.7 401986671.4 938978094.2
MIROC3.2, A2, Kg/yr 462430229.8 544717157 1042135805
Low Scenario
Total mitigation potential: ton CO2eq/yr 1,060,129 1,388,660 3,218,312
Total mitigation potential US$/yr $21,202,589 $27,773,205 $64,366,248
As % of Agricultural GDP 0.33% 0.43% 0.99%
High Scenario
Total mitigation potential: ton CO2eq/yr 1,697,119 1,999,112 3,824,638
Total mitigation potential US$/yr $33,942,379 $39,982,239 $76,492,768
As % of Agricultural GDP 0.52% 0.62% 1.18%
Average
Total mitigation potential: ton CO2eq/yr 1,238,881 1,576,362 3,453,261
Total mitigation potential US$/yr $24,777,630 $31,527,245 $69,065,211
As % of Agricultural GDP 0.38% 0.49% 1.07%
MOZAMBIQUE
Price of CO2eq
$20 GCM Type, grwoth scenario, CO2 sequestered Opt. Fertilizer Opt. Fertilizer, ManureOpt. Fertilizer, Manure , Residue management
CNRM-CM3, A2, Kg/yr 130278112.9 284978331.9 639189652.3
CSIRO-Mk3.0, A2, Kg/yr 111638795.1 265190642.5 647180509.5
ECHam5, A2, Kg/yr 121155914.5 302669238.5 670911010.3
MIROC3.2, A2, Kg/yr 111587996.8 276227946.3 665151061.7
Low Scenario
Total mitigation potential: ton CO2eq/yr 409,528 973,250 2,345,826
Total mitigation potential US$/yr $8,190,559 $19,464,993 $46,916,520
As % of Agricultural GDP 0.26% 0.62% 1.49%
High Scenario
Total mitigation potential: ton CO2eq/yr 478,121 1,110,796 2,462,243
Total mitigation potential US$/yr $9,562,413 $22,215,922 $49,244,868
As % of Agricultural GDP 0.30% 0.71% 1.56%
Average
Total mitigation potential: ton CO2eq/yr 435,501 1,035,918 2,406,082
Total mitigation potential US$/yr $8,710,026 $20,718,364 $48,121,631
As % of Agricultural GDP 0.28% 0.66% 1.53%
We can get a sense for
Agricultural contribution
To mitigation and magnitude
Of payments
We can construct spatially-
explicit mitigations costs per
ton of CO2eq
$ Ton CO2eq
$Cton.tif
<VALUE>
9.859458923 - 20
20.00000001 - 35
35.00000001 - 50
50.00000001 - 65
65.00000001 - 80
80.00000001 - 95
95.00000001 - 110
110.0000001 - 125
125.0000001 - 175
175.0000001 - 280
Mozambique
Fertilizer, Manure, Residue management No-Till
This map can be used with
other maps (e.g. poverty,
biodiversity) to identify
areas of intervention
# People < $1.25
125povMoz.tif
VALUE
0 - 108
108.0000001 - 252
252.0000001 - 454
454.0000001 - 764
764.0000001 - 1,369
1,369.000001 - 2,933
2,933.000001 - 6,820
6,820.000001 - 12,264
12,264.00001 - 23,025
23,025.00001 - 39,546
# People < $1.25
125povMoz.tif
VALUE
0 - 108
108.0000001 - 252
252.0000001 - 454
454.0000001 - 764
764.0000001 - 1,369
1,369.000001 - 2,933
2,933.000001 - 6,820
6,820.000001 - 12,264
12,264.00001 - 23,025
23,025.00001 - 39,546
Mozambique
Number of People who live with less than $1.25/day
$ Ton CO2eq
$Cton.tif
<VALUE>
9.859458923 - 20
20.00000001 - 35
35.00000001 - 50
50.00000001 - 65
65.00000001 - 80
80.00000001 - 95
95.00000001 - 110
110.0000001 - 125
125.0000001 - 175
175.0000001 - 280
Mozambique
Fertilizer, Manure, Residue management No-Till
CO2eq Sequestration Potential
cnra2_fmr
<VALUE>
11 - 20
20.00000001 - 30
30.00000001 - 40
40.00000001 - 50
50.00000001 - 60
60.00000001 - 70
70.00000001 - 135
# People < $1.25
125povMoz.tif
VALUE
0 - 108
108.0000001 - 252
252.0000001 - 454
454.0000001 - 764
764.0000001 - 1,369
1,369.000001 - 2,933
2,933.000001 - 6,820
6,820.000001 - 12,264
12,264.00001 - 23,025
23,025.00001 - 39,546
# People < $1.25
125povMoz.tif
VALUE
0 - 108
108.0000001 - 252
252.0000001 - 454
454.0000001 - 764
764.0000001 - 1,369
1,369.000001 - 2,933
2,933.000001 - 6,820
6,820.000001 - 12,264
12,264.00001 - 23,025
23,025.00001 - 39,546
Mozambique
Number of People who live with less than $1.25/day
Mozambique
CO2 Mitigation Potential
Fertilizer, Manure, Residue management No-Till
CBA for 5 Countries, 6 AEZ,
6 crop/cropping systems
Country AEZ Soil Texture Crop
Morocco Arid Loam Soft Wheat
Morocco Arid Loam Potato
Morocco Arid Loam Onion
Kenya Arid Clay Maize
Kenya Arid Sand Maize
Kenya Semi-arid Loam Maize
Kenya Semi-arid Sand Maize
Kenya Semi-arid Clay Maize
Kenya Temperate Loam Maize
Kenya Humid Loam Maize
Ghana Humid Sandy/Clay/Loam Maize/Cassava/Fallow
Mozambique Semi-arid Sandy/Loam Maize/Cassava/Fallow
Mozambique Semi-arid Clay Maize/Cassava/Fallow
Vietnam Humid Clay Rice
The Case of Kenya
Annual net profit per tCO2e from maize production in 4 AEZs of Kenya
Package 1 Package 2 Package 3 Package 4
RES
RES, FERT &
MNR
RES, FERT, MNR,
SWC & ROT
FRT, MNR, RES,
SWC, ROT, & IRG
Annual net
profit/tCO2e
Annual net
profit/tCO2e
Annual net
profit/tCO2e
Annual net
profit/tCO2e
Arid Clay 12.29 30.78 0
(-0.33)
0
(-53.02)
Arid Sand 0
(-17.12)
14.19 0
(-9.64)
0
(-22.78)
Semi-arid Loam 0
(-43.89)
0
(-23.36)
0
(-28.79)
0
(-53.40)
Semi-arid Sand 0
(-41.26)
0
(-13.41)
0
(-13.18)
0
(-6.83)
Semi-arid Clay 0
(-81.78)
0
(-55.26)
0
(-68.67)
0
(-73.02)
Temperate Loam 0
(-3.27)
0
(-19.85)
0
(-23.20)
0
(-19.54)
Humid Loam N/A* 0
(-99.01)
0
(-96.93)
0
(-71.72)
*Applying only residues to loamy soils in the humid AEZ resulted in a loss in SOC over the 40-year
period
Notes: RES=50% residues applied to soil, FERT=40kg N/ha, MNR=3t/ha/yr, SWC=soil water
availability before planting is 30% of field capacity and small amount (2 mm/ha/10-day) of soil
moisture is additionally available in the root zone throughout the growing season; ROT=rotation with
dry beans every 4th
year; IRG=meet full crop water demand. Results are for an open pollinated variety maize.
Source: Bryan, E. et al. 2011
The Case of Morocco – 30 year analysis
NPV of Alternative Practices
Discount
Rate
4% 6% 8% 10% Reduction in
CO2 Emissions
Soft
Wheat
Traditional 10, 880, 537 8, 068, 904 5, 910, 625 4, 234, 504
0.9 Tons
CO2eq/year Zero Tillage 22, 363, 552 17, 588, 878 13, 906, 118 11, 030, 175
Potato
Traditional irrigation 14, 388, 214 10, 766, 683 8, 067, 484 6, 033, 598
0.3 Tons
CO2eq/year
Drip irrigation 88, 932, 314 70, 207, 148 55, 888, 428 44, 801, 899
Onion
Traditional irrigation 9, 455, 430 6, 920 634 5, 027, 825 3, 599, 420
0.4 Tons
CO2eq/year
Drip irrigation 84, 047, 807 65, 746, 343 51, 773, 878 40, 976, 765
Source: Khalil Allali calculations
The Case of Ghana
Maize-Cassava-Fallow
Manure Applications of Various Levels
The Case of Ghana
Maize-Cassava-Fallow
Manure Applications of Various Levels
Maize-Cassava-Fallow
Manure Applications of Various Levels
Yield Variability Increases
Mean-Standard Deviation Utility Function
We follow Saha (1997) and we assume that farmers’
preferences can be represented by a mean-SD utility
function
Changing change risk attitude
Under the assumption of risk aversion, decreasing
(constant) [increasing] absolute risk aversion preferences
require
Decreasing (constant) [increasing] relative risk aversion is
denoted by
Maize-Cassava-Fallow
Manure Applications of Various Levels
Yield Variability Increases
Maize-Cassava-Fallow
Manure Applications of Various Levels
Different Use of Inputs Manure + N
Maize-Cassava-Fallow
Manure Applications of Various Levels
Different Soil Different Results
ψ
c
1/α
Effect of Payments on Investments
on Soil Fertility
ψ
c
1/α
with carbon paymentswith carbon payments
Effect of Payments on Investments
on Soil Fertility
Maize-Cassava-Fallow
Payments Are Not Required for an Indefinite
Amount of Time - 0 N
Maize-Cassava-Fallow
Payments Are Not Required for an Indefinite
Amount of Time – 60 Kg N
All These Results Are Predicated On
Knowledge / quantification of how different agronomic
practices and different crops affect GHG emissions
(DSSAT/Century, CropSys, EPIC, APSIM)
Capability of “reasonably” predict future land-use choices,
crop choices, agronomic practices (surveys, models of
land-use change)
Major obstacle: creating a baseline
Considerations
Risk-neutrality hides some of the complexities of
implementing payment for environmental service
schemes
Could save money proposing the “right practices” to
the “right” farmers
Solution: create tiers of farmers?
Good targets are farmers whose actions are “highly”
predictable
How do we account for the co-benefits?