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Findings and recommendations to the
Africa Regional Department
Ciniro Costa Jr
c.costajr@cgiar.org
Climate change impacts of the UK Department for International
Development’s (DfID) commercial agriculture portfolio
GHG emissions and removals assessment
of DfID’s commercial agriculture portfolio
AgDevCo - Ghana
(agroforestry, soil and
forestry management)
LFSP – Zimbabwe
(livestock and
soil management)
MADE - Ghana
(soil and fertiliser
management)
AgDevCo - Mozambique
(livestock)
CSAZ – Zambia
(soil management
and post-harvest losses)
NuTEC - Uganda
(livestock and
soil management)
PropCom Maikarfi - Nigeria
(soil management and
avoided deforesttation)
LIFT_NUTSEM – Myanmar
(irrigated rice and
fertiliser management)
• Seven programmes across eight countries
GHG emissions and removals assessment
of DfID’s commercial agriculture portfolio
Beef Cattle
2%
Goats
1%
Poultry
97%
Livestock herd size (25.6 Mi heads)
Maize
54%
Rice
12%
Paddy Rice
3%
Sorghum
15%
Cotton
9%
Groundnuts
5%
Soybean
1%
Sugar bean
1% Cocoa
0.5%
Crop area (1.0 Mha)
• 24 value chains associated with an area of ~ 4 million ha
Estimating net GHG emissions: Rapid
assessment
Step 1
Collect data
(farm activities)
Step 2
GHG and carbon
stock change
estimates
Rapid assessment
• Used interviews and literature reviews to
identify extent of activities
• Indicates the magnitude of net GHG effects
among field activities, cropping systems or
value chains
Caveats
• Carbon stock change (occur over 20 years)
• Land use change
Step 3
Programme
feedback
0.95
1.38
0.20 0.25
1.90
0.95
0.75
0.52 0.42
-0.58 -0.64 -0.67 -0.69 -0.82
-1.03
-1.33
-1.62
-5.46
Sorghum
M
aize
Sugarbean
Groundnuts
Upland
rice
Soybean
Cotton
Paddyrice
Cocoa
Programmes’ interventions have reduced
emissions and increased crop productivity
Changes in net
GHG emissions
(tCO2e/ha/y)
Changes
in productivity
(t/ha/y)
*negative values represent reduction
**values for livestock meat were not assessed due to the lack of data collected on livestock production and productivity
• Changes in farmers’ practices enhance crop production
while reducing net GHG emissions
-10.66
-0.67 -0.45 -0.23 -0.14 -0.02 -0.001
-5.80
-1.50 -1.30 -0.88
0.45 0.29 0.17 0.14 0.05 0.05 0.003
Reduced
deforest. im
proved
cookstoves
Reduced
N-Fertilizer use
(im
proved
seeds)
Reduced
post-harvestloss (im
proved
storage) - m
aize
Im
proved
water m
anag. in
paddy rice
Reducing burning of crop
residues
Reduced
diesel use (im
proved
tillage practices)
Im
proved
goat breeding/feeding
Agroforestry im
provem
ents
M
inim
um
tillage
M
anure application
Good
agronom
ic practices
N-Fertiliser (urea)use
Goat (increased
herd)
Lim
ing
Burningcrop
residues
N-M
anure
application
Diesel(m
echanisaton)
Poultry (increased
herd)
Net GHG emissions
(tCO2e/ha/y or tCO2e/animal/year)
Agricultural interventions
• Across programmes soil organic carbon (SOC) sequestration outweighed
increases in GHG emissions by five times
Avoided emissions Carbon
sequestration
GHG emissions
Case studies: Maize production in
African countries
Total net change in GHG
emissions (tCO2e/ha/y)
Net changes in GHG sources and sinks (tCO2e/ha/y)
*Negative values represent emission reduction
Zambia
• Agriculture intensification may promote soil C sequestration that partly offsets
input-related emissions
• Avoided food loss can significantly avoid increased GHG emissions while
enhancing food security
-1.50
-0.13 -0.02
0.07
-0.45
Improved
practices, crop
rotation,
minimum tillage
Burning
reduction Diesel use Liming
Avoided food
loss
-1.58
-0.45 Avoided
losses
Ag
Practices
-2.03
Avoided
food
loss
-1.58
-0.45 Avoided
losses
Ag
Practices
-2.03
-0.08
(without C seq)
Case studies: Maize production in
African countries
-0.24
12.0
-1.34
10.9
Without With
Current
Expected
deforestation
-0.88
0.14 0.05
0.45
12.2
-1.50
-0.14
Improved
practices
(minimum tillage
expected)
Burning residues
(expected
reduction) Diesel use
N-fertilizer use
(urea) Deforestation
Ghana
*Negative values represent emission reduction
0.64 | 0.36
(without C seq)
Net changes in GHG sources and sinks (tCO2e/ha/y)
• Emissions from deforestation outweigh mitigation generated from agricultural
interventions
• Multiple factors drive LUC and so impacts cannot be directly attributed to
programme interventions alone
Total net change in GHG
emissions (tCO2e/ha/y)
Sustainable intensification
• Sustainable intensification increases crop or livestock production and may
reduce land use change and related ecological impacts
• Intensification practices, however, are not necessarily aligned with LED
• Intensification of crop or livestock productivity can reduce GHG emissions
per unit of product, but increases overall emissions (e.g., use of fertilizers)
• Intensification can increase emissions where it drives agricultural expansion
in high carbon stock areas
Totalarea (seven
programmes)
Increase in
productivity
Potential land sparing
across programmes
Mha t/ha Mha
Totalpotential land
sparing (Mha)
4.20 up to 200% 4.09
Expected scenario (at programme end)
Recommendations for enhancing emission
reduction and productivity resilience
Guidance for low-emission
development:
(1) Avoid land use change
(2) Improve production efficiency
(3) Offset emissions with carbon storage
(4) Refine monitoring and reporting to
capture emission-relevant
information (e.g., amount of N-fert. applied,
livestock number, crop/pasture area size and
productivity).
Nutrient management
N-fixing crops / legumes
No-tillage
Improved feed and manure
management
Avoid
land conversion
Water management
Improved seeds
GHG reductions
Cover crops
Agroforestry
Grazing optimization
Silvopastoral
Enhancing C sequestration
Land restoration
Residue
management
LIVESTOCK
PADDY RICE
CROPS
LAND USE CHANGE
Thank you!
For more information contact:
Ciniro Costa Jr C.Costajr@cgiar.org
Lini Wollenberg Lini.Wollenberg@uvm.edu
Resources:
• MRV Platform for agriculture: https://www.agmrv.org
• SAMPLES: https://samples.ccafs.cgiar.org
• CCAFS website: https://ccafs.cgiar.org

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Climate change impacts of the UK Department for International Development’s (DfID) commercial agriculture portfolio: Findings and recommendations to the Africa Regional Department

  • 1. Findings and recommendations to the Africa Regional Department Ciniro Costa Jr c.costajr@cgiar.org Climate change impacts of the UK Department for International Development’s (DfID) commercial agriculture portfolio
  • 2. GHG emissions and removals assessment of DfID’s commercial agriculture portfolio AgDevCo - Ghana (agroforestry, soil and forestry management) LFSP – Zimbabwe (livestock and soil management) MADE - Ghana (soil and fertiliser management) AgDevCo - Mozambique (livestock) CSAZ – Zambia (soil management and post-harvest losses) NuTEC - Uganda (livestock and soil management) PropCom Maikarfi - Nigeria (soil management and avoided deforesttation) LIFT_NUTSEM – Myanmar (irrigated rice and fertiliser management) • Seven programmes across eight countries
  • 3. GHG emissions and removals assessment of DfID’s commercial agriculture portfolio Beef Cattle 2% Goats 1% Poultry 97% Livestock herd size (25.6 Mi heads) Maize 54% Rice 12% Paddy Rice 3% Sorghum 15% Cotton 9% Groundnuts 5% Soybean 1% Sugar bean 1% Cocoa 0.5% Crop area (1.0 Mha) • 24 value chains associated with an area of ~ 4 million ha
  • 4. Estimating net GHG emissions: Rapid assessment Step 1 Collect data (farm activities) Step 2 GHG and carbon stock change estimates Rapid assessment • Used interviews and literature reviews to identify extent of activities • Indicates the magnitude of net GHG effects among field activities, cropping systems or value chains Caveats • Carbon stock change (occur over 20 years) • Land use change Step 3 Programme feedback
  • 5. 0.95 1.38 0.20 0.25 1.90 0.95 0.75 0.52 0.42 -0.58 -0.64 -0.67 -0.69 -0.82 -1.03 -1.33 -1.62 -5.46 Sorghum M aize Sugarbean Groundnuts Upland rice Soybean Cotton Paddyrice Cocoa Programmes’ interventions have reduced emissions and increased crop productivity Changes in net GHG emissions (tCO2e/ha/y) Changes in productivity (t/ha/y) *negative values represent reduction **values for livestock meat were not assessed due to the lack of data collected on livestock production and productivity • Changes in farmers’ practices enhance crop production while reducing net GHG emissions
  • 6. -10.66 -0.67 -0.45 -0.23 -0.14 -0.02 -0.001 -5.80 -1.50 -1.30 -0.88 0.45 0.29 0.17 0.14 0.05 0.05 0.003 Reduced deforest. im proved cookstoves Reduced N-Fertilizer use (im proved seeds) Reduced post-harvestloss (im proved storage) - m aize Im proved water m anag. in paddy rice Reducing burning of crop residues Reduced diesel use (im proved tillage practices) Im proved goat breeding/feeding Agroforestry im provem ents M inim um tillage M anure application Good agronom ic practices N-Fertiliser (urea)use Goat (increased herd) Lim ing Burningcrop residues N-M anure application Diesel(m echanisaton) Poultry (increased herd) Net GHG emissions (tCO2e/ha/y or tCO2e/animal/year) Agricultural interventions • Across programmes soil organic carbon (SOC) sequestration outweighed increases in GHG emissions by five times Avoided emissions Carbon sequestration GHG emissions
  • 7. Case studies: Maize production in African countries Total net change in GHG emissions (tCO2e/ha/y) Net changes in GHG sources and sinks (tCO2e/ha/y) *Negative values represent emission reduction Zambia • Agriculture intensification may promote soil C sequestration that partly offsets input-related emissions • Avoided food loss can significantly avoid increased GHG emissions while enhancing food security -1.50 -0.13 -0.02 0.07 -0.45 Improved practices, crop rotation, minimum tillage Burning reduction Diesel use Liming Avoided food loss -1.58 -0.45 Avoided losses Ag Practices -2.03 Avoided food loss -1.58 -0.45 Avoided losses Ag Practices -2.03 -0.08 (without C seq)
  • 8. Case studies: Maize production in African countries -0.24 12.0 -1.34 10.9 Without With Current Expected deforestation -0.88 0.14 0.05 0.45 12.2 -1.50 -0.14 Improved practices (minimum tillage expected) Burning residues (expected reduction) Diesel use N-fertilizer use (urea) Deforestation Ghana *Negative values represent emission reduction 0.64 | 0.36 (without C seq) Net changes in GHG sources and sinks (tCO2e/ha/y) • Emissions from deforestation outweigh mitigation generated from agricultural interventions • Multiple factors drive LUC and so impacts cannot be directly attributed to programme interventions alone Total net change in GHG emissions (tCO2e/ha/y)
  • 9. Sustainable intensification • Sustainable intensification increases crop or livestock production and may reduce land use change and related ecological impacts • Intensification practices, however, are not necessarily aligned with LED • Intensification of crop or livestock productivity can reduce GHG emissions per unit of product, but increases overall emissions (e.g., use of fertilizers) • Intensification can increase emissions where it drives agricultural expansion in high carbon stock areas Totalarea (seven programmes) Increase in productivity Potential land sparing across programmes Mha t/ha Mha Totalpotential land sparing (Mha) 4.20 up to 200% 4.09 Expected scenario (at programme end)
  • 10. Recommendations for enhancing emission reduction and productivity resilience Guidance for low-emission development: (1) Avoid land use change (2) Improve production efficiency (3) Offset emissions with carbon storage (4) Refine monitoring and reporting to capture emission-relevant information (e.g., amount of N-fert. applied, livestock number, crop/pasture area size and productivity). Nutrient management N-fixing crops / legumes No-tillage Improved feed and manure management Avoid land conversion Water management Improved seeds GHG reductions Cover crops Agroforestry Grazing optimization Silvopastoral Enhancing C sequestration Land restoration Residue management LIVESTOCK PADDY RICE CROPS LAND USE CHANGE
  • 11. Thank you! For more information contact: Ciniro Costa Jr C.Costajr@cgiar.org Lini Wollenberg Lini.Wollenberg@uvm.edu Resources: • MRV Platform for agriculture: https://www.agmrv.org • SAMPLES: https://samples.ccafs.cgiar.org • CCAFS website: https://ccafs.cgiar.org