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Comparison of cost-benefit analyses for mitigation in different agroecosystems Alex De Pinto IFPRI Rome July, 2011

De pinto a cost benefit analyses for mitigation

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Page 1: De pinto a cost benefit analyses for mitigation

Comparison of cost-benefit analyses

for mitigation in different

agroecosystems

Alex De Pinto

IFPRI

Rome

July, 2011

Page 2: De pinto a cost benefit analyses for mitigation

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

Page 3: De pinto a cost benefit analyses for mitigation

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

Page 4: De pinto a cost benefit analyses for mitigation

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

Page 5: De pinto a cost benefit analyses for mitigation

We Can Do Better Now

Page 6: De pinto a cost benefit analyses for mitigation

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

Page 7: De pinto a cost benefit analyses for mitigation

The Example of Ghana

Source: own simulations with DSSAT

Page 8: De pinto a cost benefit analyses for mitigation

SOC (kg[SOC]/ha/yr)High : 150

Low : 1

Fertilizer, Manure Fertilizer, Manure, No-Till

Page 9: De pinto a cost benefit analyses for mitigation

SOC (kg[SOC]/ha/yr)High : 150

Low : 1

Fertilizer, Manure, Residue management Fertilizer, Manure, Residue management No-Till

Page 10: De pinto a cost benefit analyses for mitigation

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

Page 11: De pinto a cost benefit analyses for mitigation

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

Page 12: De pinto a cost benefit analyses for mitigation

# 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

Page 13: De pinto a cost benefit analyses for mitigation

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

Page 14: De pinto a cost benefit analyses for mitigation

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

Page 15: De pinto a cost benefit analyses for mitigation

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

Page 16: De pinto a cost benefit analyses for mitigation

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

Page 17: De pinto a cost benefit analyses for mitigation

The Case of Ghana

Maize-Cassava-Fallow

Manure Applications of Various Levels

Page 18: De pinto a cost benefit analyses for mitigation

The Case of Ghana

Maize-Cassava-Fallow

Manure Applications of Various Levels

Page 19: De pinto a cost benefit analyses for mitigation

Maize-Cassava-Fallow

Manure Applications of Various Levels

Yield Variability Increases

Page 20: De pinto a cost benefit analyses for mitigation

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

Page 21: De pinto a cost benefit analyses for mitigation

Maize-Cassava-Fallow

Manure Applications of Various Levels

Yield Variability Increases

Page 22: De pinto a cost benefit analyses for mitigation

Maize-Cassava-Fallow

Manure Applications of Various Levels

Different Use of Inputs Manure + N

Page 23: De pinto a cost benefit analyses for mitigation

Maize-Cassava-Fallow

Manure Applications of Various Levels

Different Soil Different Results

Page 24: De pinto a cost benefit analyses for mitigation

ψ

c

1/α

Effect of Payments on Investments

on Soil Fertility

Page 25: De pinto a cost benefit analyses for mitigation

ψ

c

1/α

with carbon paymentswith carbon payments

Effect of Payments on Investments

on Soil Fertility

Page 26: De pinto a cost benefit analyses for mitigation

Maize-Cassava-Fallow

Payments Are Not Required for an Indefinite

Amount of Time - 0 N

Page 27: De pinto a cost benefit analyses for mitigation

Maize-Cassava-Fallow

Payments Are Not Required for an Indefinite

Amount of Time – 60 Kg N

Page 28: De pinto a cost benefit analyses for mitigation

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

Page 29: De pinto a cost benefit analyses for mitigation

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?