中国粮食生产非CO2温室气体排放演变特征研究

陈耀, 刘志磊, 周云, 韩张亮

中国环境科学 ›› 2025, Vol. 45 ›› Issue (11) : 6453-6463.

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中国环境科学 ›› 2025, Vol. 45 ›› Issue (11) : 6453-6463.
碳排放控制

中国粮食生产非CO2温室气体排放演变特征研究

  • 陈耀1, 刘志磊2, 周云1, 韩张亮2,3
作者信息 +

Evolutionary characteristics of non-CO2 greenhouse gas emissions in China's grain production

  • CHEN Yao1, LIU Zhi-lei2, ZHOU Yun1, HAN Zhang-Liang2,3
Author information +
文章历史 +

摘要

基于1961~2021年的联合国粮食及农业组织(FAO)、《中国统计年鉴》等官方数据,系统解析了全球五大粮食主产国水稻甲烷(CH4)、小麦氧化亚氮(N2O)和玉米N2O排放现状及演变规律,并深入探讨了中国三大粮食作物CH4和N2O排放的长期变化趋势及其驱动因素.研究表明:近年来,中国水稻CH4和小麦N2O的排放量在五国中均始终位居首位,但其单位粮食质量的碳排放量均处于五国中下游水平;玉米N2O的排放量和单位粮食质量的碳排放量在五国中均位列第二.在1961~2021年,中国水稻CH4、小麦N2O和玉米N2O的排放量分别增加了13.9%、474.0%和831.5%,而其单位粮食质量的非CO2碳排放量则分别显著下降了69.9%、40.5%和38.3%.化学氮肥大量施用是导致小麦和玉米N2O排放量快速增加的驱动因素.本文揭示了中国在三大粮食作物碳减排方面已取得显著进展,但小麦和玉米的N2O排放量迅速上升,已成为制约中国粮食生产碳减排进程的主要瓶颈.

Abstract

Using the data from Food and Agriculture Organization of the United Nations (FAO) and the China Statistical Yearbook spanning 1961 to 2021, this paper systematically analyzes the current status and evolution patterns of methane (CH4) emissions from rice, nitrous oxide (N2O) emissions from wheat, and N2O emissions from maize in the world's five major grain-producing countries. It further explores the long-term trends and driving factors of CH4 and N2O emissions from China’s three staple grain crops. The results show that in recent years, China’s rice CH4 emissions and wheat N2O emissions consistently ranked highest among the five countries while maize N2O emissions and the corresponding emissions per unit grain mass both ranked second. However, the carbon emissions per unit grain mass for both crops was in the middle-to-lower range among the five nations. Between 1961 and 2021, China’s rice CH4 emissions, wheat N2O emissions, and maize N2O emissions increased by 13.9%, 474.0%, and 831.5%, respectively. Conversely, their non-CO2 carbon emissions per unit grain mass significantly decreased by 69.9%, 40.5%, and 38.3%, respectively. The heavy application of chemical nitrogen fertilizer was identified as the key driver that triggers the rapid increase in wheat and maize N2O emissions. This study reveals that China has made significant progress in reducing carbon emissions from its three major grain crops. Nevertheless, the rapid rise in N2O emissions from wheat and maize has become a major constraint hindering further progress in decarbonizing China’s grain production.

关键词

粮食作物 / 甲烷 / 氧化亚氮 / 温室气体

Key words

grain crops / methane / nitrous oxide / greenhouse gases

引用本文

导出引用
陈耀, 刘志磊, 周云, 韩张亮. 中国粮食生产非CO2温室气体排放演变特征研究[J]. 中国环境科学. 2025, 45(11): 6453-6463
CHEN Yao, LIU Zhi-lei, ZHOU Yun, HAN Zhang-Liang. Evolutionary characteristics of non-CO2 greenhouse gas emissions in China's grain production[J]. China Environmental Science. 2025, 45(11): 6453-6463
中图分类号: X511   

参考文献

[1] 宁 静,李亚洁,王 震,等.中国粮食主产省区农业碳排放特征及影响因素 [J]. 水土保持研究, 2024,31(1):450-459. Ning J, Li Y J, Wang Z, et al. Characteristics and influencing factors of agricultura carbon emissions in major grain producing provincesin China [J]. Research of Soil and Water Conservation, 2024,31(1):450-459.
[2] 王 旭.推动农业减排固碳促进绿色低碳发展 [J]. 中国畜牧业, 2022,14:14-20. Wang X. Accelerate emission reduction and carbonsequestration in agriculture and promoting green andlow-carbon development [J]. China Animal Industry, 2022,14:14-20.
[3] 于 博,刘雪晴,赵晓杰,等.“双碳”目标下农业“土-能-粮-废”关联作用与影响机制 [J]. 中国人口·资源与环境, 2023,33(11):67-77. Yu B, Liu X Q, Zhao X J, et al. Exploring the mechanisms of the land-energy-food-waste nexus in agriculture in the context of achieving the 'dual carbon' goals [J]. China Population, Resources and Environment, 2023,33(11):67-77.
[4] 秦晓波,王金明,王 斌,等.稻田甲烷排放现状、减排技术和低碳生产战略路径 [J]. 气候变化研究进展, 2023,19(5):541-558. Qin X B, Wang J M, Wang B, et al. Status of methane emissions from paddy fields, mitigation technologies and strategic pathways for low- carbon production [J]. Climate Change Research, 2023,19(5):541-558.
[5] 李迎春,林而达,熊 伟,等.中国农业氧化亚氮排放情景研究 [J]. 地理科学进展, 2009,28(4):636-642. Li Y C, Lin E D, Xiong W, et al. Modelling N2O emissions from agriculture in China [J]. Progress in Geography, 2009,28(4):636-642.
[6] 张 扬,李 涵,赵正豪.中国粮食作物种植变化对省际农业碳排放量的影响研究 [J]. 中国农业资源与区划, 2023,44(7):29-38. Zhang Y, Li H, Zhao Z H. Rresearch on effects of grain crop planting changes on agricultural carbon emissions between provinces in china [J]. Chinese Journal of Agricultural Resources and Regional Planning, 2023,44(7):29-38.
[7] 江敬安,陈 丽,沈 兵,等.世界肥料产业发展趋势及展望 [J]. 现代化工, 2023,43(1):13-20. Jiang J A, Chen L Sheng B, et al. Development trend and prospect of world fertilizer industry [J]. Modern Chemical Industry, 2023,43(1): 13-20.
[8] Xia L L, Ti C P, Li B L, et al. Greenhouse gas emissions and reactive nitrogen releases during the life-cycles of staple food production in China and their mitigation potential [J]. Science of the Total Environment, 2016,55(6):116-125.
[9] Li Y P, Wu W A, Yang J X, et al. Exploring the environmental impact of crop production in China using a comprehensive footprint approach [J]. Science of the Total Environment, 2022,82(4):83-98.
[10] 张青青,曲衍波,展凌云,等.中国粮食生产碳排放动态演进及驱动效应 [J]. 地理学报, 2023,78(9):2186-2208. Zhang Q Q, Qu Y B, Zhan L Y, et al. Dynamic evolution and driving effects of carbon emissions from grain production in China [J]. Acta Geographica Sinica, 2023,78(9):2186-2208.
[11] 张明洁,张京红,李文韬,等.中国农作物碳足迹核算研究概述 [J]. 中国农业资源与区划, 2023,44(5):148-154. Zhang M J, Zhang J H, Li W T, et al. Review on research of crop carbon footprint accounting in china [J]. Chinese Journal of Agricultural Resources and Regional Planning, 2023,44(5):148-154.
[12] 范行行,介晓磊,李 玲,等.河南省农业减污降碳协同效应及其驱动因素 [J]. 环境科学, 2025,46(8):4864-4875. Fan H H, Jie X L, Li L, et al. Synergistic effects of agricultural pollution reduction and carbon reduction and its driving factors in henan province [J]. Environmental Science, 2025,46(8):4864-4875.
[13] 沈亚强,陈龙骏,金玉婷,等.嘉兴市农业温室气体排放特征及减排路径 [J]. 浙江农业学报, 2018,30(10):1755-1764. Shen Y Q, Chen L J, Jin Y T, et al. Characteristics and mitigation pathways of agricultural greenhouse gas emissions in Jiaxing City [J]. Acta Agriculturae Zhejiangensis, 2018,30(10):1755-1764.
[14] Chen Z C, Balasus N, Lin H P, et al. African rice cultivation linked to rising methane [J]. Nature Climate Change, 2024,14(2):126-133.
[15] 周镕基,徐沈玥.2000~2021年中国水稻生产净碳汇的时空演变及其与水稻产值的耦合研究 [J]. 中国环境科学, 2025,45(7):4091-4106. Zhou R J, Xu S Y. Spatiotemporal evolution of net carbon sequestration in rice production and its coupling with rice output value in China, 2000~2021 [J]. China Environmental Science, 2025,45(7):4091-4106.
[16] Xu L, Yuan S, Wang X Y, et al. High yields of hybrid rice do not require more nitrogen fertilizer than inbred rice: A meta-analysis [J]. Food and Energy Security, 2021,10(2):341-350.
[17] 傅志强,黄 璜,谢 伟,等.高产水稻品种及种植方式对稻田甲烷排放的影响 [J]. 应用生态学报, 2009,20(12):3003-3008. Fu Z Q, Huang H, Xie W, et al. Effects of high-yielding rice cultivar and cultivation pattern on methane emissions from a paddy field [J]. Chinese Journal of Applied Ecology, 2009,20(12):3003-3008.
[18] 肖志祥,傅志强,徐华勤,等.双季稻品种根际特征与甲烷排放差异及其关系 [J]. 环境科学, 2019,40(2):904-914. Xiao Z X, Fu Z Q, Xu H Q, et al. Differences and relationship between rhizosphere characteristics and methane emissions of double-cropping rice variety [J]. Environmental Science, 2019,40(2):904-914.
[19] 陈友德,赵 杨,高杜娟,等.稻油不同轮作模式对农田甲烷和氧化亚氮排放的影响 [J]. 环境科学, 2020,41(10):4701-4710. Chen Y D, Zhao Y, Gao D J, et al. Effects of different rotation patterns of Oil-Rice on methane and nitrous oxide emissions in rice fields [J]. Environmental Science, 2020,41(10):4701-4710.
[20] Zhang H, Xue Y G, Wang Z Q, et al. Morphological and physiological traits of roots and their relationships with shoot growth in“super”rice [J]. Field Crops Research, 2009,113(1):31-40.
[21] Jiang Y, Wang L L, Yan X J, et al. Super rice cropping will enhance rice yield and reduce CH4 emission: A case study in Nanjing, China [J]. Rice Science, 2013,20(6):427-433.
[22] 杨 晨,胡珮琪,刁贝娣,等.粮食主产区政策的环境绩效:基于农业碳排放视角 [J]. 中国人口·资源与环境, 2021,31(12):35-44. Yang C, Hu P Q, Diao B D, et al. Environmental performance evaluation of policies in main grain producing areas:from the perspective of agricultural carbon emissions [J]. China Population, Resources and Environment, 2021,31(12):35-44.
[23] 李思琪,华而实,陈敏鹏.中国水稻甲烷排放空间格局演变与技术减缓潜力分析 [J]. 中国环境科学, 2025,45(3):1218-1230. LI S Q, Hua E S, Chen M P. Spatial evolution of rice methane emission and technology mitigation potential in China [J]. China Environmental Science, 2025,45(3):1218-1230.
[24] 田沛佩,卢宏玮,李丹,等.2008~2017年中国地级市化肥施用碳足迹的时空演变格局 [J]. 中国环境科学, 2021,41(2):967-973. Tian P P, Lu H W, Li D, et al. Spatial-temporal patterns of carbon footprint of fertilizer application in China during 2008 to 2017 [J]. China Environmental Science, 2021,41(2):967-973.
[25] 朱永官,王晓辉,杨小茹,等.农田土壤N2O产生的关键微生物过程及减排措施 [J]. 环境科学, 2014,35(2):792-800. Zhu Y G, Wang X H, Yang X R, et al. Key Microbial processes in nitrous oxide emissions of agricultural soil and mitigation strategies [J]. Environmental Science, 2014,35(2):792-800.
[26] Zou J W, Huang Y, Qin Y M, et al. Changes in fertilizer-induced direct N2O emissions from paddy fields during rice-growing season in China between 1950s and 1990s [J]. Global Change Biology, 2009,15:229-242.
[27] Fao. Faostat database-agriculture production [R]. Rome: Food and Agriculture Organization of the United Nations, 2019.
[28] 巨晓棠,谷保静.我国农田氮肥施用现状、问题及趋势 [J]. 植物营养与肥料学报, 2014,20(4):783-795. Ju X T, Gu B J. Status-quo, problem and trend of nitrogen fertilization in China [J]. Journal of Plant Nutrition and Fertilizers, 2014,20(4): 783-795.
[29] 江达仁,熊若愚,吴家青,等.精准条播育秧机插下侧深施肥对优质早籼稻产量、品质形成及氮素吸收的影响 [J]. 作物学报, 2024, 50(12):3096-3106. JiangD R, Xiong R Y, Wu J Q, et al. Effects of side-deep fertilization on yield formation and nitrogen absorption of high-quality early indica rice under precision sowing in line and machine planting [J]. Acta Agronomica Sinica, 2024,50(12):3096-3106.
[30] 王俊岭.减肥减药促农业品质提升 [J]. 农产品市场周刊, 2018,(8): 26-27. Wang J L, Reducing fertilizer and pesticide use to improve agricultural quality [J]. Agricultural Products Market Weekly, 2018,(8):26-27.
[31] 王响玲,宋柏权.氮肥利用率的研究进展 [J]. 中国农学通报, 2020, 36(5):93-97. Wang X L, Song B Q. Nitrogen fertilizer use efficiency: Research progress [J]. Chinese Agricultural Science Bulletin, 2020,36(5):93-97.
[32] 刘洪涛,郭小夏,成升魁,等.我国粮食生产的耕地资源环境效应特征与代价分析 [J]. 中国环境管理, 2019,11(4):67-78. Liu H T, Guo X X, Cheng S K, et al. Resource properties and corresponding cost of arable land resulted from grain production in China [J]. Chinese Journal of Environmental Management, 2019,11(4):67-78.
[33] Xia L L, Cao L, Yang Y, et al. Integrated biochar solutions can achieve carbon-neutral staple crop production [J]. Nature Food, 2023,4(3): 236-246.
[34] Kotus T, Simansky V, Drgonova K, et al. Combination of biochar with n-fertilizer affects properties of soil and N2O emissions in maize crop [J]. Agronomy-Basel, 2022,12(6):13-14.
[35] Wu G, Yang S, Luan C S, et al. Partial organic substitution for synthetic fertilizer improves soil fertility and crop yields while mitigating N2O emissions in wheat-maize rotation system [J]. European Journal of Agronomy, 2024,15(4):70-77.
[36] Chen X P, Cui Z L, Fan M S, et al. Producing more grain with lowerenvironmental costs [J]. Nature, 2014,514(7523):486-489.

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中国工程院战略研究与咨询项目(2023-XY-23)

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