"Challenges, opportunities and priorities for transitioning to low emissions agriculture" was presented by Lini Wollenberg at a NUI Galway seminar on January 30, 2020.
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Challenges, opportunities and priorities for transitioning to low emissions agriculture
1. Lini Wollenberg, CCAFS
NUI Galway seminar, Jan 30, 2020
Challenges, opportunities and
priorities for transitioning to low
emissions agriculture
2. Why mitigation in agriculture
and food systems?
1. Significant
• 10-12% of global emissions
• Agriculture contributes on average
30% of countries’ total emissions
2. Necessary
Reductions in other sectors will not
be enough to achieve 2 °C and 1.5
°C targets
3. Possible
Many practices are compatible with
SDGs, hence the possibility of “low
emissions development”
Agricultureemissions,bycountry
Percentofnationalemissionsfromagriculture
Richards et al. 2015
3. • Paddy rice - alternate wetting and drying (AWD)
• Livestock systems - improving feeding, animal and herd management;
pasture management
• Cereal crops- building soil organic matter, e.g. through integrated soil
fertility management; nutrient efficiency through technologies such as urea
deep placement; BNI in crops
• Perennial crops- transitioning from annual crops or degraded land to
agroforestry, forestry or grassland
Low emission development options
• Avoided conversion of high carbon landscapes
(forests, peatlands, mangroves, grasslands)
• Reduced food loss and waste- storage, packaging,
waste recycling
• Supply chain energy use – fertilizer production, cooling,
transportation
• Dietary shifts- shift to low emissions food products, e.g.
beef to chicken
7. Strategic scaling of LED
1. Identify emission hot spots (subsectors, regions) and
mitigation priorities
2. Analyze scaling opportunities
3. Select interventions providing the best levers for large-
scale change
8. 1. Identify emission hot spots (subsectors
regions) and mitigation priorities
Source: Carbon Disclosure Project. 2015. The Forgotten 10%. London: Carbon Disclosure Project.
Available from: www.cdp.net
Global
emissions
sources
Livestock is
a hot spot!
9. Country emissions
Agriculture emissions, bycountry
Percentof nationalemissions from
agriculture
Richards et al. 2015
Livestock-producing
countries
predominate
Mostly developing
countries
10. Mitigation priorities: Paddy Rice in Vietnam
Alternate wetting and drying (AWD)
Delaying re-irrigation until water level
has gone down to ~15cm below soil
surface. Reduces CH4 field emissions
by ~50%.
Fertilizer deep placement
Applying fertilizer below the soil
surface (often slow release fertilizer).
Reduces N2O emissions.
Short duration varieties
Switching to varieties with a shorter
maturity duration. Reduces CH4 field
emissions ~proportional to reduced
growing time.
Sustainable straw management
Reduced rates of incorporation and
burning of straw. Reduces CH4 field
emissions and black carbon
emissions.
The International Rice Research InstituteLED options Scaling area Mitigation
potential
Barriers Enabling
Conditions
- Incentives
Co-Benefits
AWD large high medium medium medium
Fertilizer deep placement medium low high high medium
Short duration varieties small low low low high
Sustainable straw mngmt large medium medium medium high
Slide courtesy of Ole Sander, IRRI
11. Regions suitable to Alternate Wetting and Drying
in Vietnam
• Based on cropping calendar, rice extent and water balance
(biophysical factors only, methodology: Nelson et al., 2015)
Slide courtesy of Ole Sander, IRRI
12. • Policy: Paris Agreement
• Leadership: Greta
Thunberg
• Learning & innovation:
farmer field schools,
producer coops, digital tools
• Finance: markets,
investors, development
assistance, philanthropy
• Alliances, social
movements: G77, youth
• Information: Media, science
• Security/health/disaster:
fires, flooding, climate
migrants
2. Analyze scaling opportunities
Behavior
change
Drivers Institutions
• Government
• Market
• Civil society
• Individuals
• Organizations
13. Learning from existing large-scale implementation
of LED
• Review of 24 LED-relevant projects. Seven projects had ten or
more years of implementation experience, and eight other projects
had five or more years
o In China, 2.5 million households received payments for
restoring 2 million ha of land.
o In Nigeria, 2.5 million farmers used urea deep placement to
reduce fertilizer inputs by 25% and increase yields by 18-25%.
o Laser leveling in India reduced irrigation times on 500,000 ha,
raising yields by 7% and increasing profitability by USD 113-
175/ha/yr.
Wollenberg et al. 2019, TCAF/World Bank
14. Good practice features for transformational LED
project design
Principles Features of successful large-scale mitigation projects
Technology
transfer and
infrastructure
1. Strong value propositions for farmers beyond carbon payments
2. Farmer- and local government-driven decisions about practices
3. Effective technical change agents with capacity for large-scale outreach
4. Farmer access to integrated support services (on-line knowledge platforms for climate information services
and technical option feasibility and suitability analysis, ICT-based services, carbon accounting linked to project
activities, centers for input and service delivery)
Finance 1. Subsidy or credit used to catalyze new practices
2. Where offered, result-based carbon payments can create incentives for sustaining projects or incremental
improvements
3. Aggregated carbon payments to communities during times of low carbon prices to reduce transaction
costs and increase reward size
4. Public-private partnership, with public support to de-risk farmer transitions and private investment, and
private funds to drive scale
5. Low entry requirements for participation in enterprises or carbon schemes
6. Low transaction costs for finance delivery
MRV 1. Low-cost MRV methodologies specific to practices, e.g. use of existing statistics, such as fertilizer sales or
milk yields, remote sensing for agroforestry or AWD
2. Activity-based monitoring
3. Continuously improved modeling and science to verify activity data
4. Automated payments
Policy 1. National policy mandate for change in practices (not necessarily climate policy)
2. Inter-ministerial and administrative unit coordination, including between central and local government
Wollenberg et al. 2019, TCAF/World Bank
15. 3. Select best levers for change
Develop priority interventions for achieving large-scale impacts
1. Set targets, commitments and champions, for example 2020 Zero
Deforestation commitments; IKEA’s “Food is Precious” initiative, with
target to reduce food waste by 50% by the August and monitor progress
2. Build on existing initiatives and build partnerships: SDGs, LDN,
4p1000, 12.3 Champions Initiative
3. Aim for systemic change not just scaling up local practices, e.g.
Improve transparency and accountability of finance, mainstream incentives
and technologies into government & company policies
4. Use complementary drivers, institutions and scales to build synergy,
momentum and reach tipping points e.g. public-private partnerships,
incentives for all actors along a supply chain, bottom-up and top down
processes
5. Enable learning, innovation, adaptation toward targets
16. Key drivers for scaling up LED agriculture
Target NDCs
and national
action Enable
private-public
finance
Mitigation as co-benefit of
ag development
Largest reductions:
avoided deforestation,
livestock, soil C protection,
beef consumption, food
loss
Biggest emitters:
e.g. US, Brazil,
China, India
Reduce
consumer
demand
for beef
Reliable
MRV
18. • Updating and increasing
ambition of NDCs
• Carbon trading - Article 6
rules
• MRV
Challenges
19. 14
12
9
8 7
3 3 3 2 2 1 1 1
12
21
0
5
10
15
20GigatonnesCO2e
The countries with the largest agricultural emissions
50% from 4
countries + EU
76% from 12
countries + EU
Cumulativeagricultural
emissions1990-2010
Challenges
20. Are not always the countries planning action
104 countries included mitigation in agriculture in their Nationally
Determined Contribution
Richards 2018
https://cgspace.cgiar.org/handl
e/10568/73255
<50% of the top 10
developing countries with
the largest opportunities to
scale up mitigation
included mitigation in their
NDC.
Challenges
21. Buchner et al. 2017
And finance has been poor relative to other
sectors
Challenges
22. Development finance is more substantial than
climate change mitigation finance for agriculture
3
8.6
0
2
4
6
8
10
AFOLU mitigation
finance
Agricultural ODA
$billionUSD
(FAO AIDmonitor)
23. Challenges
Carbon payments have not been viable in agriculture
Constraints:
(1) Need for upfront investment, payments come too late
(2) High program costs necessary to deliver significant impacts,
(3) Need to reduce risk and uncertainty for all program participants to enable
enrollment and long-term participation, and
(4) Equity concerns: poorer farmers likely to not benefit
Sources: Shames et al. 2012, Engle 2016, Newton et al. 2016, Börner et al. 2018,
Keating 2019).
High costs occur due to upfront investment needs, transaction costs of dealing with
numerous smallholders, carbon credit program complexity and needs for robust MRV.
High risk due to uncertain C markets, the long-term nature of carbon sequestration and
its impermanence, leakage, poor data for emission factors and activity data and climate
change.
24. Need for locally relevant interventions
Potential GHG reductions as % of baseline (FAO 2018)
Regional mitigation options for LED livestock
.
Challenges
26. 9/8/2020 26
Landscape
transitions
Crop
transitions
Rice
crops
Crops
(non rice) Fertilizer Livestock
- 4.7M
TotalAnnualtCO2e
Landscape
and crop
transitions
Management practice
improvements
Increased
emissions
Reduced
emissions/
increased C
sequestration
(1,865,626)
(905,776)
(433,447)
(616,320)
(32,068)
(819,848
)
435,313
1,723,672
2.1 M
Mitigation benefits of USAID’s agricultural development portfolio
https://ccafs.cgiar.org/blog/greenhouse-gas-emission-analyses-nine-agricultural-development-projects-reveal-
mitigation#.WqrhAGbMzEY
25developmentprojects,15countries,3continents.
Opportunity: Low emissions development
27. Mitigation strategy, principles,
measurement, and capacity
• Green Climate Fund
• World Bank
• ADB
• EU Sustainable Finance
• Climate Bonds Initiative
Opportunity: Increasing interest by public and private
finance
28. A strategy for financing the transformation of food
systems under a changing climate
https://ccafs.cgiar.org/publications/financing-transformation-food-systems-under-changing-
climate#.XjIp7S3MzEY
29. • Thai rice production accounts for
almost 60% of emissions from
agricultural activities (4th largest
emitter of GHGs from rice globally)
• 5-year NAMA project: low-emission
production; policy formulation and
supporting measures
• 100,000 farmers in 6 provinces
• GHG reduction of ~1 million tons of
CO2eq
• Thai Rice Dep. and MoNRE with
the consortium comprising GIZ,
IRRI-CCAFS and private sector
partners
Thai Rice NAMA support project
approved for ~ EUR 15 M funding
Example: Climate finance
30. Private drone companies help scale out
technologies for better N management in
Mexico
• 3 drone companies delivering N
recommendations to farmers
using NDVI from their drones
and an algorithm developed by
CIMMYT and collaborators.
• Farmers are willing to pay for
this service (approx. 3 UDS /
ha per flight.
• N saving of ca. 60 – 70 kgN/ha
Slide courtesy of Ivan Ortiz-
Monasterio, CIMMYT
Example: public-private partnership
31. Manure management in peri-urban areas to reduce
pollution: Indonesia, China
SIDPI project,
Lembang
Indonesia
https://ccafs.cgiar.org/s
ustainable-
intensification-dairy-
production-
indonesia#.WqrnGWb
MzEY
Example: Urgent actions that have mitigation co-benefits
32. Plant-based meat, is ~1 percent of
the meat market and expected to
increase.
Plant Based
Foods
Association, a
trade
organization, in
2016 had 22
Beyond Meat
stock increased
163% in public
offering in May
2019
Industry-led
movement
Beyond Meat has
markets in 50
countries around
the world, including
Taiwan and Korea
and 14 European
countries
Pat Brown,
Impossible Foods,
plans “to …completely
replace the need for
animals in the food
system, full stop.
This is not a fad, but
a necessity.”
Sept 2019
Example: Consumption change
33. Conclusions for transformational change
• Agriculture can help achieve the 2 °C target, but action has been slow
• Evidence suggests opportunities for mitigation at scale: Business models,
development programs with significant mitigation impacts, multiple projects at
scale.
• Focus now on delivering large-scale impacts in priority countries and
production systems
Assess feasibility with suitability mapping, investment cases, policy
Catalyze large-scale change in these locations
− Work with drivers of agricultural change
− Build on design principles from large-scale
success cases
− Use public finance to leverage ambitious
scales of private sector action
34. Importance of imagination and challenging
existing orders
Walper 2016
UNFCCC adopted in 1992, yet emissions have increased
Solutions often reflect the society that generated the problem in
the first place
• Proponents need to “fit in” to have a voice at the table
• Solutions need credibility in public discourse
• Result is built-in conservatism of approaches
There is no discrete solution set and system-level change will be
needed for large scale change
Imagination and going beyond technical mind sets will be
necessary
35. Some practical resources for low
emissions agriculture
FAO-STAT emissions data: http://www.fao.org/faostat/en/#data
MRV platform for agriculture: https://www.agmrv.org
IPCC Emission Factor Database: https://www.ipcc-
nggip.iges.or.jp/EFDB/main.php
NDC database https://cgspace.cgiar.org/handle/10568/73255
Financing the Transformation of Food Systems under a Changing
Climate
https://ccafs.cgiar.org/publications/financing-transformation-food-
systems-under-changing-climate#.XjIp7S3MzEY
Examples of CSA business cases
https://ccafs.cgiar.org/fr/invest#.XjJPDC3MzEY
CCAC Kiosks: Manure management: http://www.manurekiosk.org,
Paddy rice https://ghgmitigation.irri.org
36. Questions for discussion
1. What kinds of incentives are needed for farmers, input suppliers,
policy makers etc. to shift to LED by 2050?
What kinds of systemic change could provide these incentives?
What are the constraints to such change?
2. What are the potential trade-offs of of focusing on the largest
emitters now? Or seeking large scale impacts by 2030 or 2050?
3. Should countries with high domestic agricultural emissions (e.g.
>50% of national emissions) be a priority for mitigation? Or only
countries with high emissions?
4. What are the pros and cons of public v private finance as a driver
for LED?
5. Choose a supply chain in a particular country and identify strategic
interventions for LED to achieve zero emissions by 2050.
37. Global sources of carbon sinks
Afforestation/
reforestation
29%
Agroforestry
1%
Wetland restoration
12%Forest mgmt
22%
Soil carbon
18%
Biochar
18%
Chart Title
A/R Agroforestry Wetland restoration Forest mgmt Soil C Biochar
9.9 – 26 GTCO2e
39. Use of minimum N input requirements in maize
(N gaps) by Yara and IFA
www.yieldgap.org
50% Yw
80% Yw
• Minimum amount of N needed to replace all N taken up in the aboveground
maize biomass for target yield (% of water-limited yield potential - %Yw)
• (Avoided) GHG emissions estimated for intensification and area expansion
scenarios for cereal self-sufficiency in SSA towards 2050
Opportunity
40.
41.
42. Action #1: Zero agricultural land expansion
on high carbon landscapes
THE CHALLENGE: Zero agricultural land expansion in supply
chains through 2050 to maintain existing high biomass
landscapes
• In 2050, land use change due to agriculture will generate 6 GtCO2/yr
• Only a few commodities responsible for most deforestation: palm oil,
beef, soy, pulp, rubber, cocoa and coffee
• 80% of global forest loss is expected to take place in 11 deforestation
fronts (2030 projection). S America is a hot spot.
The 11 deforestation fronts,
with projected losses, 2010–
2030. Source: WWF Living
Forests Report (2015).
WHERE is action
needed ?
43. Action #2: Protecting high carbon soils
• Peatlands hold 32% - 46% of all soil carbon (~500– 700 Gt)
THE CHALLENGE: Avoid soil C loss on 250 million hectares of
croplands by 2030, by protecting high soil C landscapes
WHERE is action
needed?
Figure 6. Global soil organic carbon map (SOC t/ha in top 30 cm). Source: FAO 2019.
44. Action #7: Reducing beef and dairy
consumption for healthy and sustainable
climate-friendly diets
• Consumption of beef & dairy is the largest single driver of agricultural
GHGs globally.
• Beef production contributes 2.9 GtCO2e/yr and dairy 1.4 GtCO2e/yr.
THE CHALLENGE: Incentivize dramatic reductions in beef and dairy
consumption in 15 high- and middle-income countries and all C40 cities
by 2030
WHERE is
action
needed?
Figure 8. Meat
supply per
person, 2013.
Source: Our World
in Data 2019.
C40 cities
80% of global food
consumption in
2050 will occur in
cities
45. Action #8: Reducing food loss and waste
The food supply chain contributes ~13.7 Gt CO2e/yr, and 15–45% of food is
lost or wasted (2.1 to 6.2 GtCO2e/yr)
THE CHALLENGE: Reduce food loss and waste by 50% in five major
supply chains where both GHGs and loss or waste are high, such as beef,
dairy, intensive fruit and vegetable production.
Figure 10. Share of global food loss and waste by region, 2009 (100% = 1.5 quadrillion kcal). Source: Lipinski et al. 2013.
WHERE is
action
needed?
46. • IRRI and Northwest Focal Area
Network (FAN), a agri-food network
of various organizations
• FAN received Climate and Clean
Award 2018 for behavior change
• Targets irrigation groups of 10-25
farmers which undergo training and
attend learning events on AWD
• Reached thousands of farmers
since 2017; targets to reach 50,000
despite meager resources
• Nationwide TV coverage by Mr.
Rezaul Karim Siddique, famous TV
agri journalist
Mobilizing concerted action
for AWD+ outscaling in Bangladesh
Example: Grassroots action
What are the most important opportunities? What might be the most efficient?
What are realizable approaches/ management options?
What are relevant financing options and mechanisms?
What are practically applicable MRV options?
What should be policy priorities?
How is the climate change mitigation objective for terrestrial carbon sinks aligned with country policies and Nationally Determined Contributions (NDCs)?
What are the challenges to align the climate change mitigation objectives with other development priorities such as biodiversity conservation, improving agricultural productivity, increasing food security, eliminating poverty, etc.?
49Gt CO2e
Less than 30 years before carbon budget is exhausted
(Carbon budget will be exhausted by 2027, assuming 1.5 °C pathway
Atmosphere can only absorb 420 Gt CO2 to stay below 1.5°C
42 Gt CO2 is emitted globally every year (Mercator 2018)
If 2 °C goal, budget will be exhausted by 2045
The Group of 77 at the United Nations is a coalition of 135 developing nations
In the China project, soil and biomass carbon increased to 11.54 and 23.76 MtC (42 and 87 MtCO2e) respectively, in Niger, where 200 million trees were planted on 5 million hectares, and in Ethiopia, where 8 million people (12% of population) mitigated ~3.4 MtCO2e per year through land restoration.
Significant experience exists regarding the large-scale implementation of technical practices relevant to CSA involving often millions of farmers and hundreds of thousands of hectares.
Agricultural projects have achieved large mitigation impacts, especially through carbon sequestration, as a co-benefit of agriculture activities that generate improved yields or incomes.
Main challenges to achieving scale for carbon projects in agriculture have been to:
(1) reduce program costs while also delivering significant impacts, and
(2) reduce risk and uncertainty for all program participants to enable enrollment and long-term participation
(3) secure upfront investment
Large-scale projects have been generally effective in facilitating CSA technology transfer and supporting infrastructure, making finance available, establishing GHG and adaptation, accounting and standards systems, and providing national or international policy support
National capacities and context can play a strong role in influencing readiness for large-scale project implementation. The private sector can also drive adoption of practices with low entry requirements and solid business cases.
Most projects will require upfront investment to catalyze behavior change. Results-based payments will only be possible if such investments are already occurring. This raises the question of how much RBCF facilities such as TCAF should seek mechanisms for funding project development and not just payments for results. While, TCAF is a results-based instrument and should target projects with the strong readiness and capacity for high impacts, it may also need to allow for initial investments or partnerships to establish projects or help a prospective “winner” projects build their capacity.
A checklist provides a blueprint of features for transformational CSA projects. The design features are similar to what would be required for effective large-scale agricultural projects, with the addition of MRV.
Plus Cross-cutting
1. System change at national levels to achieve maximal impact at lowest costs, rather expensive replication of pilot projects
2. Building momentum for participation with low entry requirements, especially for carbon payment projects
3. Setting priorities for large-scale impacts and target countries, production systems, value chains, partners and participants where success is likely
4. Synergies across technology transfer, finance, carbon accounting and standards, and policy
5. Reduced risk and uncertainty by using improved technical information, low-cost loans, grants
6. Building on existing successful large-scale projects
7. Use of meaningful environmental and social safeguards
Build in flexibility to be adaptive, facilitate learning, readjust to achieve targets, persist
e.g. UNFCCC treaties (Kyoto to Paris Agreement), development aid
At COP24 in Katowice, Poland, countries were unable to include guidance on Article 6 into the Paris Rulebook--except for paragraph 77(d) which stipulates how “a Party participating in cooperative approaches that involve the use of internationally transferred mitigation outcomes (ITMOs) towards its NDC under Article 4, or authorizes the use of mitigation outcomes for international purposes other than achievement of its NDC” report on such use in the structured summary of the Paris Agreement’s transparency framework. Countries will work to finalize guidance on Article 6 with a view to delivering decision text by the end of COP25. As Article 6 is one of the last pieces of the Paris Rulebook to be completed, increased high-level engagement from Ministers is possible and they require better understanding of the political issues related to Article 6 and the technical ones that still need work in advance of Katowice. This briefing provides a topline summary of CAN-I’s positions on Article 6 and explains key
For instance, countries have not yet agreed on an accounting system to avoid double counting and other elements needed to prevent potential environmental integrity risks.
http://www.climatenetwork.org/publication/briefing-implementation-guidelines-article-6-paris-agreement-june-2019
http://www.climatenetwork.org/publication/briefing-implementation-guidelines-article-6-paris-agreement-june-2019outstanding technical issues.
Looking at cumulative agricultural emissions
China, India, Brazil – 32% of emissions
There are four countries, plus the EU, that have contributed about half of emissions from agriculture since 1990.
And 12 countries + the EU have contributed about 76% of emissions from agriculture since 1990. (8 are developing countries)
Most countries seek mitigation in livestock and grassland systems or paddy rice interventions.
More than 80% of the countries in Sub-Saharan Africa (SSA) refer to the reduction of agricultural emissions, including livestock, in their nationally determined contribution (NDC) to mitigate climate change.
Less than 50% of the top 10 developing countries with the largest opportunities to scale CSA practices included CSA interventions in their NDC.
But, finance for mitigation in the agriculture sector is low. So not only is mitigation a problem, but so is the lack of resources to do it!
But, finance for mitigation in the agriculture sector is low
For example, farmer participation in the Australian Emissions Reduction Fund was low for methodologies where MRV expenses were high, potential for increased income was low, uncertainty of the practices’ benefits was high, and there was a need to commit to maintaining practices for the long-term.
These challenges have been overcome where projects created sufficient incentives for farmers to adopt new practices and found ways to overcome the high transaction costs of project development and MRV. Linking carbon financing to benefits that farmers valued, such as climate change adaptation, rural development, and ecosystem services, and building on existing developing projects have been key to enabling successful project implementation (Shames et al. 2016).
Most programs have been pragmatic in recognizing the need for low entry requirements, low cost MRV and sufficient incentives to encourage program participation. Many have sought to rely on simple, activity-based MRV. The Kenya Agricultural Carbon Project designed interventions based on farmers’ existing practices. Brazil’s ABC program increased the list of eligible practices and reduced loan interest rates in response to initial low enrollment. The Australian Emissions Reduction Fund found that enrollment was highest for vegetative carbon sinks, driven primarily by the ease of MRV (Keating 2019). A common entry point among agricultural carbon projects for introducing new practices has been a local decline in agricultural viability (
payments for ecosystem services (ES) suggest that programs are more successful to the extent they offer a hybrid of outcome and activity-based payments, in-kind rather than cash payments, payments for social value of ES rather than ES provision cost, differentiated payments, short duration payments where profitability is expected in the near term, indexing of payments according to price index correlated with opportunity cost to support permanence, discount for leakage, target low cost, high benefit sites, group payments, spatial coordination through agglomeration bonuses, reduce participation hurdles for poor and support alternative incomes (Engel 2016a, 2016b).
Natural resource efficiency can, in many cases, be enhanced by conventional productiv- ity improvements. For example, in the past four decades the introduction of advanced genetics, feeding systems, animal health controls and oth- er technologies has enabled industrialized coun- tries to reduce their overall land requirements for livestock by 20 percent while at the same time doubling total meat production. P
Mottet et al. (2017) showed that the area needed to produce human-edible livestock feed (cereals, pulses, soybeans and cassava) would shrink by 8 percent between 2010 and 2025 if feed conver- sion ratios improved by 5–15 percent, and this despite a projected 21 percent increase in the de- mand for meat.
Wider adoption of existing best practices and technologies in feeding, health and husbandry, and manure management – as well as greater use of currently underutilized technologies such as biogas generators and energy-saving devices – could help the global livestock sector cut its GHG emissions by as much as 30 percent (Ger- ber et al., 2013; Mottet et al., 2016). F
CCAFS, working with FAO, examined the mitigation co-benefits of IFAD and USAID’s agricultural investment portfolios.
This figure shows the USAID analysis, for 25 diverse agricultural development projects and several dozens of practices across 15 countries in 3 continents.
You can see that across the entire portfolio,blue is negative emissions, yellow is positive, that ag investments resulted in substantial net mitigation co-benefits, 2.6 MtCO2e/yr. Looking at interventions across categories you can see that the major source of emissions was livestock and secondarily fertilizer use, but that this was offset by land use change and rice and crop management.
So current trajectories of agricultural development can yield substantial mitigation co-benefits, especially when considered at the larger portfolio level.
That is the good news…
******
Landscape and crop transitions
1) Landscape transitions- Within the agricultural development projects, project interventions focused on both avoided land conversion (avoided change from forest) and active land conversion (agricultural or degraded lands changed to forest).
2) Crop transitions- This area include transitions to perennial crops or agroforestry. Also transitions from flooded rice systems to other crops such as wheat. Transitions land into irrigated rice. (Check why 5802 in positive)
Management practice improvements
1) Rice crops- AWD, UDP, Short Duration Rice
2) Crops- Soil, manure, and water management improvements- also includes crop residue burning reduction and perennial management.
3) Fertilizer- increases and decreases
4) Livestock- herd size management, feed quality and breeding improvements. Grassland increases. With better feeding practices and increases in cow weight comes increased emissions.
Citigroup Inc., Mitsubishi UFJ Financial Group and Industrial and Commercial Bank of China joined the pledge, which begins by asking the firms to self-assess their sustainability practices. Signers, including top European banks BNP Paribas SA, Barclays Plc and UBS Group AG,
According to Cristina Figueres: Transitioning to low-carbon and climate-resilient economies that are aligned with the Paris Agreement requires additional investment of at least $60 trillion from now until 2050
- Thailand is the 4th largest emitted of rice-related GHG. Rice production accounts for almost 60% of emissions from agricultural activities.
- The 5-year Thai Rice NAMA project will focus on low-emission production (i.e. AWD, laser land levelling, straw and stubble management, site-specific nutrient management, etc.) and policy formulation and supporting measures.
- It targets to reach 100,000 farmers in 6 provinces in Thailand, which can contribute to GHG reduction of about 1 million tons of CO2eq.
- The consortium of GIZ, SRP, IRRI-CCAFS and public- and private sectors worked closely with the Thai Rice Department under the Ministry of Agriculture and Cooperatives and the Ministry of Natural Resources and Environment.
Adresses rate, not timing source or placement
De Vries M, Wouters AP, Vellinga TV. 2017. Environmental impacts of dairy farming in Lembang, West Java; Estimation of greenhouse gas emissions and effects of mitigation strategies. CCAFS Working Paper no. 221. Wageningen, the Netherlands: CGIAR Research Program on Climate Change, Agriculture and Food Security (CCAFS). Available online at: www.ccafs.cgiar.org
Using data from a survey of 300 dairy farmers in Lembang in 2016. Total GHG emissions were 33 ton CO2e. per farm/year, and emission intensity was 1.9 kg CO2e per kg of fat and protein corrected milk (FPCM) and 8.8 kg CO2e per kg live weight.
Feeding and manure management interventions evaluated in a scenario analysis in this study changed total GHG emissions by -12 to +24%,
Largest reductions in GHG emission intensity were found in the scenarios with maize silage feeding, improved manure management, and an increased amount of roughage in the diet.
Fertilizer companies (specifically Yara) use the N-gaps published (www.yieldgap.org) in their work on intensification of low-input cropping systems: size of the challenge and potential for improvement
International Fertilizer Association (IFA) regards the N-gaps data as vitally important to help the fertilizer value chain developing science-based estimations of climate-smart nutrient requirements for future agriculture in SSA
Coordinated joint activities (science-industry-policy workshops, policy briefs, demonstrations) are underway to raise (inter)national political awareness for the size of the intensification challenge and to create enabling environment for intensification of crop production in Ethiopia, Kenya and Tanzania
] Expansion of croplands, pastures and forest plantations generated ~2.6 GtCO2/yr from 2010 to 2014 due to the conversion of tropical forests,
Pendrill et al. 2019
[ii] Searchinger et al. 2019
[iii] EVIDENCE
[iv] Searchinger et al. 201
[v] https://www.tfa2020.org/en/
[vi] https://www.cdp.net
[vii] https://www.unilever.com/Images/eliminating-deforestation-position-statement_tcm244-423148_en.pdf
[viii] https://climatepolicyinitiative.org/indonesia/
Countries with high levels of carbon that have also committed to Land Degradation Neutrality targets should be prioritized (Figures 6 and 7).
Yet one-third to up to 40% of the world’s soils are
Degraded (see Rumpel et al. 2018).
Since the industrial revolution, land use change and agricultural cultivation have generated a loss of 214 ± 67 Pg C from soils globally, or about 22 times the carbon emissions from fossil fuels in 2014. Improved agricultural practices can help avoid further loss of and in some places restore SOC, which supports adaptation to climate change as well as mitigation. Improving SOC enhances yield stability, water storage and infiltration, nutrient cycling and biodiversity, and can reduce erosion.
The potential for maintaining or improving the organic carbon stocks of the world's agricultural soils differs widely among different climate zones, soil types and associated land use as well as land governance systems. A recent publication estimated that cropland soils worldwide could have the potential to store an additional 0.9 to 1.95 Pg C per year.12 The contribution to lowering global temperatures through soil carbon sequestration has been estimated to be 0.1°C between 2015 and 2100 when achieving a storage rate of 0.68 Pg carbon per year, which could potentially be achieved with current management approaches and would not entail decreasing the area for food production.
Avoiding further loss of soil carbon from peatlands and croplands, the latter of which comprise about 1.5 billion hectares globally, is a priority both for ensuring food security and for the climate. This will require not only protecting specific high carbon landscapes (especially peatlands) but also slowing the rate of soil carbon loss in cultivated croplands by supporting additional carbon sequestration where possible. Soils that have already lost huge amounts of carbon historically can also be considered as hotspots for restoration, however, these efforts are likely to be more costly and will require long-term interventions. Interventions to increase SOC should not increase net GHG emissions, due to for example increased nitrogen fertilizer or fossil fuel use.
Zomer et al. 2017
https://www.co2.earth/global-co2-emissions
Mayer et al. 2018 (Available online at: https://doi.org/10.1126/sciadv.aaq0932)
TO BE CHECKED IF RELELEVENT. Outcome document “Unlocking the potential of Soil Organic Carbon” available online at: http://www.fao.org/3/b-i7268e.pdf; for example the global Conservation Agriculture Community of Practice (CA-CoP), led by FAO; see Zomer et al. 2017 (available online at: https://www.nature.com/articles/s41598-017-15794-8); see correction for Sandermann et al. 2017 (available online at: https://www.pnas.org/content/115/7/E1700)
250 mil ha
About double the agricultural land of Russa, of if you combine any two countries of the top four, you have it covered: US, India, Russia, China, Brazil
Agricultural land areas
1United States174.45 million hectares20052India159.65 million hectares20053Russia121.78 million hectares20054China103.4 million hectares20035Brazil59 million hectares20036Australia49.4 million hectares2005South Asia average47.26 million hectares20057Canada45.66 million hectares2003Group of 7 countries (G7) average37.12 million hectares20058Ukraine32.45 million hectares20059Nigeria30.5 million hectares200310Argentina27.9 million hectares2003
Country land areas
Or a bit smaller than Argentina and larger than Algeria or Kazakhstan or Denmark or DRC
Gerber PJ, Steinfeld H, Henderson B, Mottet A, Opio C, Dijkman J, Falcucci A, Tempio G. 2013. Tackling climate change through livestock – A global assessment of emissions and mitigation opportunities. Food and Agriculture Organization of the United Nations (FAO): Rome.
Projections
Springman et al. 2016
Kiff et al. 2016; Stehfest et al. 2013
The Rangpur Division in Northwest Bangladesh is one of the country’s most vulnerable areas due to scarce irrigation water and drought which makes it difficult to produce specifically the Boro rice (dry season irrigated rice). Boro rice accounts for over half of the country’s rice production. Additionally, the rising cost of fuel for pump irrigation aggravates the plight of the resource-poor rice farmers.
Under the “'No-regret mitigation strategies in rice production project” being supported by CCAFS and CCAC, IRRI’s partnership with the Northwest Focal Area Network (NFAN) has been reaching thousand of farmers in the 8 districts and 17 locations in Rangpur Division in terms of social mobilization, information dissemination, capacity building, and field testing activities towards AWD adoption despite the meager resources. IRRI’s long-standing collaboration with FAN—a rice-based multi-sectoral network in northwest Bangladesh comprising farmers’ organizations, academe, development NGOs and government agencies—has opened doors for AWD outscaling to thousands of farmers in the region.
Farmers and private owners of shallow-tube wells are organized in irrigation groups of 10-25 farmers, which cover roughly 15-20 acres of paddy field. Each group is trained on AWD techniques, data collection, and record-keeping, and field testing activities are being implemented.
The NFAN AWD+ outscaling is an effective model of how different stakeholders can and should work collectively towards a common goal of helping improve the rice sector and the lives of the rice farmers even with limited resources.
To illustrate: the Bangladesh Rice Research Institute, Bangladesh Agricultural Research Institute, and IRRI provide the technical know-how and information materials to extension officers; the Department of Agriculture Extension trains the farmers; the North Bengal Institute of Development Studies and Hajee Mohammad Danesh Science and Technology University conducted baseline surveys and data management; the Barind Multipurpose Development Authority (BMDA) helps in technology dissemination; and the Rangpur Dinajpur Rural Service (RDRS) serves as the network secretariat and coordinator for farmer mobilization.
Achievements of the NFAN work so far have also been covered extensively by Mr. Rezaul Karim Siddique, a famous TV agricultural journalist.