ADDRESSING METHANE EMISSIONS FROM LIVESTOCK

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Transcription:

ADDRESSING METHANE EMISSIONS FROM LIVESTOCK CAROLYN OPIO LIVESTOCK POLICY OFFICER, FAO

OUTLINE Methane emissions from livestock Why livestock is important for the methane discourse Addressing enteric methane from livestock From science to action Key messages

METHANE EMISSIONS FROM AGRICULTURE Agriculture accounts for 50% of global methane emissions Within agriculture, 78% of methane emissions are from livestock FAOSTAT, 2014

GHG EMISSIONS FROM GLOBAL LIVESTOCK SUPPLY CHAINS GLEAM, 2013

REGIONAL SHARE OF GLOBAL METHANE EMISSIONS FROM LIVESTOCK GLEAM, 2013

ENTERIC METHANE EMISSION INTENSITY

9.6 MILLION TONNES OF CH4 FROM MANURE MANAGEMENT (~240 MILLION TONNES CO2-e)

WHY FOCUS ON ENTERIC METHANE FROM LIVESTOCK?

THE RUMEN AND THE ESSENTIAL ROLE OF MICROBES Enteric CH4 a by-product of rumination Enteric fermentation Energy Rumen Methanogens H2 Influenced by diet and diet quality, other factors (animal type and weight, overall productivity, management) takes place in the rumen fermentation vat containing billions of microbes efficient in digestion of cellulose rich diets converting human inedible products to high value protein process provides animal with nutrients: VFA and protein principal source of energy for animal: ~70% of energy symbiotic relationship between animal and microbes

ROLE OF RUMINANTS IN FOOD SECURITY AND LIVELIHOODS many of people who depend on livestock are among the most vulnerable populations 730 million poor live in rural and marginal areas 430 million are poor livestock keepers direct food - high value protein traction and nutrients for arable crop safety net/banking: animals sold during times of need household income - sale of products national economy

SIGNIFICANT CONTRIBUTION TO GLOBAL WARMING Gt CO2 eq. GWP100 Global anthropogenic GHG emissions 49 Global methane emissions 6,9 Global enteric CH4 emissions 2,7 ENTERIC CH4 AS A SHARE OF % Global human-induced emissions 6 Global CH4 emissions 30 CH4 from Agriculture 70 GHG emission from livestock 40

POTENTIAL FOR IMMEDIATE GAINS FOR GLOBAL CLIMATE GLOBAL EMISSIONS FROM RUMINANTS WEIGHTED FOR TWO DIFFERENT GWPS (expressed in CO2-e) 9,00 8,00 7,00 6,00 CO2 CH4 5,00 +18% N2O 4,00 3,00 2,00 1,00 +6% 0,00 Gigatonnes CO2 eq. GWP 100 GWP20 100-year horizon: traps 28 times more heat than CO2 20-year horizon: 84 times more heat than CO2 short life span: 12 years in atmosphere

Addressing the emission intensity gap LARGE TECHNICAL MITIGATION POTENTIAL Production units aligned to average emission intensity of 10th percentile Production units aligned to average emission intensity of 25th percentile enteric CH4 emissions can be reduced by approximately between 22% and 33% (530 820 million tco2 eq.) with no system change

MITIGATION POTENTIAL

ENTERIC METHANE EMISSIONS ARE ENERGY LOSSES: 2-12% OF FEED ENERGY IS LOST There is a strong link between GHG emission intensity and resource use efficiency

PARTITIONING OF FEED ENERGY Ruminant animals with low levels of production efficiency have relatively high methane emissions per unit of product because these animals use a large fraction of their feed intake solely for maintenance.

REDUCTION IMPROVES PRODUCTIVITY RELATIONSHIP BETWEEN MILK YIELD AND ENTERIC CH4 PER KG MILK

ADDRESSING ENTERIC METHANE FROM LIVESTOCK

A WIDE RANGE OF TECHNICAL INTERVENTIONS TO IMPROVE NATURAL RESOURCE USE EFFICIENCY & PRODUCTIVITY AND REDUCE EMISSIONS Enteric CH4 : at animal AND herd level Improved feeding practices and feed processing (improving forage quality, feed processing, concentrate use) Supplementary feeding - interventions that act on rumen microbiology Improved herd management and animal husbandry (improved genetics, health, reproduction)

Feeding practices Supplements & additives Herd mgt. A wide range of mitigation options for reducing methane from enteric fermentation Many have some mitigation uncertainty, are not cost effective, have poorly understood interactive effects with other emission sources, or other associated risk. Interventions that have relatively small risk and are uniformly associated with increased productivity and high reduction potential In regions of the world that have not yet adopted these practices, significant GHG reductions are possible while also providing a steady or growing supply of animal protein. Dickie et al. 2014

BENEFITS FROM ENTERIC CH4 REDUCTION Mixed dairy production in South Asia Specialized beef production in South America Notes Global impacts Enteric Methane Baseline 213 (62%) 201 (50%) - Million tonnes CO2 eq. - Percentage of enteric methane in total GHG mitigation Enteric Methane mitigation -54 (77%) -95 (51%) - Million tonnes CO2 eq. - Percentage of enteric methane reduction in total GHG mitigation Total GHG mitigation -70-187 - -Million tonnes CO2 eq. Human health impacts - (formation of tropospheric ozone) Annually avoided crop yield losses due to Ozone Local impacts 18 32 10.3 18.4 - Thousands lives saved annually; - Mortalities avoided from reductions in ozone - Millions metric tons - Considers major stable crops including wheat, rice, maize, and soy Productivity increase 13 (+24%) 5 (+47%) - Million tonnes of protein; - Percentage increase in milk and meat protein supplied Livelihoods impacted 318 5 - Millions of poor livestock keepers impacted by intervention;

SUMMARY: WHY FOCUS ON ENTERIC CH4? Opportunity for high impact. 78% of agricultural and 30% of global methane emissions; expected to grow Low cost and wide range of co-benefits (climate, productivity, profitability, food security, nutritional benefits, human health benefits, adaptation (green energy), etc.) Technologies are available: Existing, cost-effective reduction opportunities (esp. for low productive systems) using relatively common practices >> number of barriers need to be overcome

FROM SCIENCE TO ACTION: ISSUES TO CONSIDER Importance of the sector: food security, livelihoods, income, economic development, exposure to CC Complexity added by the diversity and heterogeneity of livestock systems Barriers:limited awareness of emissions levels, reduction opportunities and benefits, lack of information on technologies and practices, lack of institutional capacity, etc. Finance and investment important for up-scaling and impact

WHAT IS REQUIRED FOR ACTION? Building of an evidence-base and tools for decision-making regarding the actions to address enteric methane and technologies and practices Engaging with appropriate stakeholders and other relevant organizations to share knowledge, experiences, outcomes, and key recommendations

GLOBAL ACTION TO ADDRESS ENTERIC CH4 EMISSIONS

OBJECTIVES building knowledge and innovation through generation and dissemination of information and tools to support the identification and prioritization of high potential areas for intervention. enhancing policy capabilities and as well as building political will and action to address enteric methane emissions for improved food security and livelihoods and support to policy actions for mainstreaming enteric methane in regional and national frameworks. leveraging of partnerships and finance to overcome constraints to uptake and generate results at scale

GLOBAL ACTION TO ADDRESS ENTERIC CH4:PHASE 1 Engagement and Analysis Defining the ruminant production systems Identifying the existing and available technologies and interventions Understanding the constraints and barriers to intervention Identifying the key stakeholders Identification of the intervention packages Assessing emissions, emission reduction potential Assessing the costs and benefits associated with interventions Assessing the barriers to uptake, opportunities for up-scaling Identifying relevant policy and institutional options to support adoption and up-scaling Investment and financial models for upscaling of interventions Identification of possible test sites and implementation partners Pilot test sites in regions to assess impact of selected interventions Identify regional partners for Phase 2 Dissemination and global outreach activities

TOOLS: LINKING PRODUCTIVITY GAINS TO EMISSIONS REDUCTION Bridging the milk yield gap Methane emissions = 64% xi= Yield gaps due to animal husbandry practices yi= Gap in productivity due to genotype A protocol and accounting tool, validated by third party, to certify emission reduction to support farmers in accessing climate finance (NAMA, carbon credit) Focus on dairy sector, in order to improve dairy productivity and reduce the intensity of GHG emissions pe kilogram of milk. Allows development of the sector while reducing the environmental impact of growth.

KEY MESSAGES Agricultural emissions are highly variable and reflect the diversity of production environments. Implementation needs to adapt to local conditions and technological solutions differ from place to place; blanket solutions are bound to fail. In developing countries, any mitigation strategy in agriculture needs to prioritize food security and livelihoods, with mitigation a co-benefit. In the case of ruminant livestock, the number of people involved and incidence of poverty are particularly high. In absence of direct incentives for mitigation, mitigation can only be pursued through productivity increases, allowing for necessary sector growth. The strong correlation between productivity increases and methane mitigation implies large opportunities for low-cost mitigation, and wide-spread social and economic benefits. Addressing enteric methane emissions will require specific scoping of the mitigation options, possible tradeoffs as well as barriers to adoption. Farm viability is key to successful adoption of mitigation technologies.

Thank you Carolyn.Opio@fao.org