Scientia Agricultura Sinica ›› 2024, Vol. 57 ›› Issue (21): 4290-4307.doi: 10.3864/j.issn.0578-1752.2024.21.010

• SOIL & FERTILIZER·WATER-SAVING IRRIGATION·AGROECOLOGY & ENVIRONMENT • Previous Articles     Next Articles

Structural Characteristics, Development Trends, and International Comparison of Greenhouse Gas Emissions in China’s Agri-Food System Under the Dual-Carbon Objectives

NIU KunYu1(), GE RuoHao1, CHEN MeiAn2, JIN ShuQin3, LIU Jing1   

  1. 1 Institute of Agricultural Economics and Development, Chinese Academy of Agricultural Sciences, Beijing 100081
    2 Institute for Global Decarbonization Progress (iGDP), Beijing 100600
    3 Research Center for Rural Economy, Ministry of Agriculture and Rural Affairs, Beijing 100000
  • Received:2023-12-04 Accepted:2024-01-04 Online:2024-11-01 Published:2024-11-10

Abstract:

【Objective】This study adopted a comprehensive industry chain perspective to analyze the characteristics, structure, and trends of greenhouse gas emissions in the agricultural food system, contributing to the effective advancement of China’s low-carbon strategy. 【Method】Based on the latest statistics from the United Nations Food and Agriculture Organization, the statistical analysis, comparative analysis, and scenario analysis methods were used to analyze the trend and structural characteristics of greenhouse gas emissions in the agricultural food systems of China, the United States, Western Europe, India, Brazil, and globally from 1990 to 2020. Scenarios (baseline, 2 ℃ temperature control, and 1.5 ℃ temperature control) and specific stages were employed to predict China’s agricultural food system greenhouse gas emissions in 2050. This analysis formed the basis for identifying key areas for emission reduction and outlining achievable pathways. 【Result】Among the major economies mentioned, China was the only country with a significantly increasing per capita greenhouse gas emission in the agricultural food system, although it remained lower than that of developed economies. It was expected that, with the completion of industrialization, the advancement of low-carbonization in the energy industry, and increased difficulty in emission reduction in agricultural production, China’s share of greenhouse gas emissions from the agricultural food system in the total societal emissions would initially decrease and then rise. In this context, the food consumption stage was the fastest-growing segment in China’s agricultural food system greenhouse gas emissions, while the emission proportion from agricultural production was decreasing but still represented the largest share in the system. Unlike other major economies where enteric fermentation emissions were significantly higher, China’s agricultural production greenhouse gas emissions showed a diverse pattern, including enteric fermentation, rice cultivation, fertilizer application, and energy utilization. 【Conclusion】Future emission reduction efforts should focus on formulating comprehensive carbon-neutral strategies for the agricultural food system, low-carbonization of energy structures, promoting shifts in food consumption patterns, and advancing market-oriented emission reduction initiatives.

Key words: agri-food system, greenhouse gas emissions, structural characteristics, trends, international comparison

Table 1

Research scope of GHG emissions for agri-food systems"

农业活动类型
Type of agricultural activities
CH4 N2O CO2 氟化气体
F-gases
农业生产环节温室气体排放
Greenhouse gas emissions from agricultural production
农作物秸秆残留物焚烧 Burning - crop residues
农作物秸秆残留 Crop residues
肠道发酵 Enteric fermentation
施入农田的粪便 Manure applied to field
排放到牧场的粪便 Manure left on pasture
粪便管理 Manure management
水稻种植 Rice cultivation
草原火灾 Savanna fires
合成化肥的施用 Application of synthetic fertilizers
有机土壤排水 Drained organic soils
农场内能源使用 On-farm energy use
土地利用变化有关的排放
Land-use change-related emissions
林地转化为其他用途的土地 Net forest conversion
潮湿的热带森林火灾 Fires in humid tropical forests
有机土壤火灾 Fires in organic soils
供应链前端排放
Emissions at the front end of the supply chain
化肥生产 Fertilizers manufacturing
农药生产 Pesticide production
食品生产后的排放
Post-production emissions
家庭食品消费 Household food consumption
食品包装 Food packaging
食品生产和加工 Food production and processing
食品运输 Food transport
食品零售 Food retail
食品废弃物处理 Food waste disposal

Table 2

Sub-scenario setting and key assumptions for the agri-food system by segments"

农业活动类型
Type of agricultural activities
预测方法以及依据 Scenario setting and assumptions for emissions projections
基准情形
Baseline
温控目标为2 ℃情形
2 ℃ climate target scenario
温控目标为1.5 ℃情形
1.5 ℃ climate target scenario
农业温室气体排放
Agricultural greenhouse gas emissions
水稻种植
Rice cultivation
1.5×108 t
调整灌溉方式,推广滴灌技术、干湿交替灌溉[19],平均减排量130 kg/667m2[20],减排潜力为 0.3×108 t
Promoting drip irrigation technology and implementing alternate wetting and drying irrigation[19] can result in emission reduction of 130 kg/667m2[20]. The emission reduction potential is estimated to be 0.3×108 t
进一步考虑灌溉调整、水稻直播旱种的推广[21],平均减排量约为400 kg/667m2,减排潜力约为 0.8×108 t
Considering additional irrigation adjustments and promoting dry direct-seeding of rice[21] can reduce emissions by around 400 kg/667m2, with an estimated potential reduction of 0.8×108 t
氮肥施用
Nitrogen fertilizer application
1.7×108 t [16]
加大力度推广测土配方施肥和保护性耕作[22],平均减排量为1.5 kg/667m2 [20],减排潜力为 0.5×108 t
Intensifying efforts to promote soil testing and formula fertilization as well as conservation tillage[22] can result in a emission reduction of 1.5 kg/667m2[20]. The estimated emission reduction potential is about 0.5×108 t
在继续推广测土配方施肥和保护性耕作基础上,推广缓释肥和氮肥增效剂[23-24],到2050年将使用比例提高到50%,减排潜力为 0.9×108 t,预计比基准情形下降54.2%
Further promoting slow-release fertilizers and nitrogen fertilizer enhancers[23-24], with the goal of increasing the adoption rate to 50% by 2050, is estimated to have an emission reduction potential of 0.9×108 t. Projected decrease by 54.2% from the base scenario
肠道发酵
Enteric fermentation
3.1×108 t [16]
推广动物育种,在饲料中添加茶皂素、益生菌等添加剂[22],减排潜力为 0.4×108 t
Promoting animal breeding and incorporating additives such as tea saponins and probiotics into feed[22] has the potential to reduce emissions by 0.4×108 t
考虑膳食结构调整[25],考虑采用食物添加剂中例如茶皂素、益生菌以及脂类物质的补充[26-27] ,减排潜力为 1.3×108 t
Considering dietary changes[25] and adding food supplements like tea saponins, probiotics[26-27], and lipids could reduce emissions by an estimated 1.3×108 t
畜禽粪污
管理
Livestock manure management
1.6×108 t [16]
加大力度推广畜禽粪污产沼[20]和畜禽规模化养殖,减排潜力为0.2×108 t Promoting the anaerobic digestion of livestock and poultry manure[20] and the large-scale breeding of livestock and poultry has the potential to reduce emissions by 0.2×108 t 在畜禽粪污产沼和规模化养殖基础上,考虑膳食结构调整以及优化畜禽粪污管理,减排潜力1.2×108 t
Further considering dietary structure adjustments, and optimizing the management of livestock and poultry manure, there is a potential emission reduction of 1.2×108 t
农场能源
On-farm energy use
1.5×108 t
大力发展光伏农业,发展绿色能源,推广农机电气化设备,农业部门电气化率达到30%[18],农场能源温室气体排放将比基准情形下降25.5%
It is anticipated that the electrification rate in the agricultural sector will reach 30%[18], leading to a projected decrease of 25.5% in GHG emissions compared to the baseline scenario
农业电气化率达到40%[18],预计农场能源温室气体排放将比基准情形下降37.2%
With 40 per cent electrification of agriculture[18], greenhouse gas emissions from on-farm energy are projected to decrease by 37.2% compared to the baseline scenario
化肥农药生产环节 Fertilizer and pesticide production 2.4×108 t
预计到2050年工业行业电气化率将达到58.5%,二氧化碳将比基准情形下降48.9%
Electrification of the industrial sector is projected to reach 58.5% by 2050, with a CO2 reduction of 48.9% compared to the baseline scenario
预计到2050年,工业行业电气化率将达到69.2%,二氧化碳将比基准情形下降72.8%
Electrification of the industrial sector is projected to reach 69.2% by 2050, with a 72.8% reduction in carbon dioxide compared to the baseline scenario
食品生产加工环节
Food production and processing
7.3×108 t
食品消费环节
Food consumption
4.5×108 t
减少固体燃料的使用,促进炊事电气化[28]。煤炭在能源消费中占比将下降到3.4%,非化石能源占比达 73.2%,相应的二氧化温室气体排放将比基准情形下降67.8%
Cut solid fuel use, promote cooking electrification[28]. In the 2 ℃ scenario, coal’s share drops to 3.4%, non-fossil energy rises to 73.2%, leading to a 67.8% CO2 emission drop compared to the baseline
煤炭在能源结构中的比重将进一步下降,相应的二氧化碳温室气体排放量将比基准情形下降84.0%
The share of coal in the energy mix would be further reduced and the corresponding GHG emissions of CO2 would be reduced by 84.0% compared to the baseline scenario

Fig. 1

Stages of growth of GHG emissions from China’s agri-food system (1990-2020)"

Fig. 2

Trends in per capita GHG emissions from agri-food systems in major economies and globally (1990-2020)"

Fig. 3

Trends in GHG emissions from major economies and global agri-food systems (1990-2020)"

Fig. 4

Trends in the share of GHG emissions from various segments of China’s agri-food system (1990-2020)"

Fig. 5

Trends in GHG emissions from various segments of China’s agri-food system (1990-2020)"

Fig. 6

Trends in emissions of different types of gases from agri-food China’s systems (1990-2020)"

Fig. 7

Composition of agricultural GHG emissions in major economies in 2020"

Fig. 8

Share of GHG emissions from different livestock species in major economies in 2020"

Fig. 9

Scenario projections of GHG emissions from agri-food systems in China"

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