双碳视角下乡村地域系统碳效应研究进展

张千禧; 曹智; 王介勇

doi:10.12357/cjea.20220798

双碳视角下乡村地域系统碳效应研究进展

doi: 10.12357/cjea.20220798

张千禧^{1, 2,},
曹智^1, ,,
王介勇¹

1.
中国科学院地理科学与资源研究所/中国科学院区域可持续发展分析与模拟重点实验室　北京　100101
2.
中国科学院大学资源与环境学院　北京　100049

基金项目: 国家自然科学基金项目(41931293, 42271279, 41801175)资助

详细信息

作者简介:
张千禧, 研究方向为乡村转型机理与模式。E-mail: zhangqianxi22@mails.ucas.ac.cn

通讯作者:
曹智, 研究方向为土地利用与乡村发展。E-mail: caoz@igsnrr.ac.cn

中图分类号: F323.22
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出版历程
- 收稿日期: 2022-10-19
- 录用日期: 2023-03-03
- 网络出版日期: 2023-03-06

Research progress of rural regional system carbon effect from the perspective of Dual Carbon

ZHANG Qianxi^{1, 2
,},
CAO Zhi^{1
, ,},
WANG Jieyong¹

1.
Institute of Geographic Sciences and Natural Resources Research, Chinese Academy of Sciences / Key Laboratory of Regional Sustainable Development Modeling, Chinese Academy of Sciences, Beijing 100101, China
2.
College of Resources and Environment, University of Chinese Academy of Sciences, Beijing 100049, China

Funds: The study was supported by the National Natural Science Foundation of China (41931293, 42271279, 41801175).

More Information

Corresponding author: E-mail: caoz@igsnrr.ac.cn

摘要

摘要: 乡村是国土空间的重要组成部分, 乡村减排增汇是实现双碳目标的关键举措。乡村碳效应包括碳排放效应和碳汇效应,因核算范畴、方法、指标等不同, 各研究结果间差异较大, 尚未达成一致结论。本文基于人地关系地域系统理论构建乡村碳循环体系, 使用Meta分析方法综述乡村碳效应定量研究成果, 以期为形成乡村空间碳效应的系统认知提供参考。结果表明: 1)农业生产碳排放占乡村碳排放总量的20%, 作物种植和禽畜养殖碳排放分别占农业碳排放的30%和70%。少施1 t氮肥可减排9.526 t CO₂, 相当于节约9555 kWh电, 可用于生产27 t大米; 减少1%的牛羊数量可减少4.48%的养殖业碳排放。2)乡村居民生活碳排放占乡村碳排放总量的80%, 其碳减排潜力高于农业生产; 燃煤占直接碳排放的80%, 若将1%煤炭消费替换为生物质能, 乡村生活将减排3624.8万t CO₂, 节电3636 kWh。3)1990—2022年间, 我国乡村净碳汇呈增长态势, 乡村年均净碳汇50 025.8万t, 相当于节约7.36亿 t 标准煤, 123亿元固碳成本。建议增加新型长效肥料研发投资, 推广种养一体化生态农业模式, 加大低碳生活理念宣传力度, 推进乡村数字化能源系统建设, 以充分发挥乡村减排增汇潜力。
- 双碳目标 /
- 乡村地域系统 /
- 碳效应 /
- 碳排放 /
- 碳汇 /
- 碳减排 /
- 碳增汇
Abstract: As an important constituent of national land space, rural carbon emission reduction and sink increase are crucial ways to achieve the dual carbon goal. Rural carbon effect involves carbon emission and carbon sink, and the estimation results vary widely between studies, with no consistent conclusion due to different accounting scopes, methods, indicators, and other factors. Firstly, this study constructs a rural carbon cycle system based on the human-earth system theory. Secondly, the Meta-Analysis method is used to integrate previous quantitative studies of rural carbon effects and estimate the overall effect size. Finally, it summarizes the influencing factors of rural carbon effect and puts forward suggestions for rural governance. This study aims to provide a reference for a quantitative cognition on the carbon effect of the rural regional system. The results show that: 1) Carbon emission from agricultural production accounts for 20% of the total rural carbon emission and 10.37% of the total average annual carbon emission in China, with 30% coming from crop cultivation and 70% from livestock farming. Fertilizer application plays a 58.23% role in crop cultivation carbon emission, while 67.40% of livestock farming carbon emission originates from animal enteric fermentation. Applying 1 t less nitrogen fertilizer can reduce carbon emission by 9.526 t CO₂, which is equivalent to an electricity saving of 9 555 kWh and can be used to produce 27 t of rice, improving nitrogen use efficiency by 1% can conserve 375 000 t of raw coal, and reducing the number of cattle and sheep by 1% can reduce carbon emission from livestock farming by 4.48%. 2) About 80% of rural carbon emission come from the residential living, which has a higher carbon reduction potential than agricultural production. Nearly 65% of residential living carbon emission is indirectly generated, with housing construction accounting for about 45.32%. Coal burning contributes to 80% of direct carbon emission, and replacing coal consumption by 1% with biomass energy could reduce residential living carbon emission by 36,248,000 t CO₂, corresponding to an electricity saving of 3635.7 kWh. Additionally, in the process of urbanization, the cost of eliminating the 91.54 million ton of increased carbon emission from the 1% rural-to-urban population would be at least 6.1 billion Yuan. 3) Between 1990 and 2022, the net carbon sink of rural in China assumes a growth trend, the average annual rural net carbon sink is 500 258 200 t·a^-1, equivalent to saving 736 million tons standard coal and 12.3 billion Yuan in carbon sequestration costs. The net rural carbon emission in China has increased from 1990 to 2022, but the carbon sequestration potential of farmland protection cultivation has not been fully exploited at present. Increasing the rural environmental governance level by 2% using emerging technologies could reduce rural agricultural production carbon emission by 2%. Therefore, it is proposed to increase investment in research and development of new long-acting fertilizers, promote the ecological agriculture model that integrates planting and breeding, enhance efforts to publicize the low-carbon living concept, and advance the construction of rural digital energy system, thus the potential of rural emission reduction and sink increase can be given full utilized.
- Dual Carbon goals /
- Rural regional system /
- Carbon effect /
- Carbon emission /
- Carbon sink /
- Carbon emission reduction /
- Carbon sink increase

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图 1 乡村碳循环体系

Figure 1. Rural carbon cycle system

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图 2 中国乡村农业生产和居民生活碳排放核算结果汇总

Figure 2. Summary of the carbon emission accounting results of rural agricultural production and residential living in China

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图 3 中国养殖业(1995—2013年)与种植业(2003—2019年)碳排放变化情况

Figure 3. Carbon emission changes in breeding industry (1995−2013) and planting industry (2003−2019) in China

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图 4 中国乡村碳汇核算结果汇总

Figure 4. Summary of the accounting results of rural carbon sink in China

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图 5 中国乡村净碳汇核算及其变化研究结果对比

Figure 5. Comparison of various studies on rural net carbon sink accounting and its changes in China

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表 1 中国乡村碳排放与碳汇相关文献的筛选结果

Table 1. Screening results of literatures concerning rural carbon emission and carbon sink in China

核算内容 Accounting content		文献的作者, 出版时间 Author and publishing date of literature	碳核算时期 Carbon accounting period	节点年份数 Number of node years
乡村农业生产碳排放 Carbon emission of rural agricultural production	广义农业 (种植业和养殖业) Generalized agriculture (planting and breeding industry)	田成诗等, 2021 TIAN C S, et al., 2021	2006—2016	3
		江艳军等, 2019 JIANG Y J, et al., 2019	2008—2016	9
		田云等, 2012 TIAN Y, et al., 2012	1995—2010	16
		徐嘉琦, 2022 XU J Q, et al., 2022	2004—2020	17
		韦沁, 2018 WEI Q,2018	1997—2015	19
		张俊飚等, 2014 ZHANG J B, et al., 2014	2002—2011	4
	狭义农业 (种植业) Narrow agriculture (planting industry)	张颂心, 2021 ZHANG S X, et al., 2021	2000—2018	19
		杨雪, 2022 YANG X,2022	2003—2020	18
		黄晓慧等, 2022 HUANG X H, et al., 2022	2007—2019	13
		贺青等, 2021 HE Q, et al., 2021	2003—2018	16
		田云等, 2011 TIAN Y, et al., 2011	1993—2008	16
		戴小文等, 2020 DAI X Y, et al., 2020	2007—2016	10
	养殖业 Breeding industry	田云等, 2012 TIAN Y, et al., 2012	1995—2010	16
		陈瑶, 2016 CHEN Y,2016	2001—2013	13
		姚成胜等, 2017 YAO C S, et al., 2017	2000—2014	15
		胡向东等, 2010 HU X D, et al., 2010	2000—2007	8
		张金鑫等, 2020 ZHANG J X, et al., 2020	1997—2017	21
		苏旭峰等, 2022 SU X F, et al., 2022	2000—2018	19
乡村居民生活碳排放 Carbon emission of rural residential living		朱琳, 2018 ZHU L,2018	2005—2014	10
		黄芳等, 2013 HUANG F, et al., 2013	2000—2010	11
		张咪咪, 2011 ZHANG M M,2011	1997—2007	11
		凤振华等 ,2010 FENG Z H, et al., 2010	2005—2007	3
		万文玉等, 2017 WANG W Y, et al., 2017	2001—2013	13
乡村农业碳汇 Carbon sink of rural agriculture		曹执令等, 2022 CAO Z L, et al., 2022	2007—2022	14
		陈罗烨等, 2016 CHEN L H, et al., 2016	1991—2011	21
		田云等, 2015 TIAN Y, et al., 2015	2000—2012	4
		张俊飚等, 2013 ZHANG J B, et al., 2013	1995—2010	16
		李强等, 2022 LI Q, et al., 2022	2005—2020	16
		李翠菊, 2012 LI C J,2012	1990—2010	21

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表 2 化肥碳排放系数

Table 2. Fertilizers carbon emission factors

t(CE)∙t⁻¹
化肥类型 Fertilizer type	生产、运输、包装过程 Production, transportation and pack process	使用过程 Utilization process	总量 Gross	来源 Source
氮肥 Nitrogen fertilizer	7.759	1.767	9.526	[44-45]
磷肥 Phosphate fertilizer	2.332	0.733	3.065	[44-46]
钾肥 Potash fertilizer	0.660	0.550	1.210	[44-46]
对参考文献中的数据进行了单位换算, 统一为t(CE)∙t⁻¹。数量关系为: CE=(12/44)×CO₂, CE为碳当量。 The unit of data in the reference is converted to CE. The quantitative relationship is CE=(12/44)×CO₂ and CE is carbon equivalent.

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表 3 乡村居民生活碳排放的影响因素及其作用效果

Table 3. Influencing factors and their effects of rural residential living carbon emission

影响因素 Influencing factor	可量化指标 Quantifiable index	每提升1%所带来的碳排放变化 Change in carbon emission resulting from 1% uplift (%)	来源 Source
经济增长 Economic growth	乡村居民人均收入 Income per rural inhabitant	0.43	[52]
技术进步 Technological progress	能源利用效率 Energy efficiency	−2.12	[53]
能源结构 Energy structure	煤炭消费占比 Coal consumption percentage	0.26	[54]
能源结构 Energy structure	生物质能消费占比 Biomass energy consumption percentage	−1.50	[55]
产业结构 Industrial structure	第一产业产值占比 Primary industry output percentage	−1.99	[56]
人口规模 Population Size	乡村人口总数 Rural population	−3.98	[52]

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表 4 中国主要粮食作物年均碳汇量及碳投入价值

Table 4. Average annual carbon sink and carbon input value of major grain crops in China

作物 Crop	固碳量 Carbon sequestration [t(C)∙hm⁻²∙a⁻¹]	大气CO₂吸收量 Absorption of atmospheric CO₂ [t(C)∙hm⁻²∙a⁻¹]	碳投入价值 Carbon input value [¥∙hm⁻²∙a⁻¹]	来源 Source
小麦 Wheat	3.62	13.28	245	[57–58]
玉米 Maize	3.98	14.58	162	[57–58]
水稻 Rice	4.32	15.83	254	[57–58]
1)大气CO₂吸收量=单位面积作物固碳量×作物种植面积; 2)面积数据来源于《2021年中国统计年鉴》; 3)碳投入价值指作物种植耗能和化肥、农药等生产资料使用造成的碳排放量与碳价格的乘积。1) Atmospheric CO₂ absorption = carbon sequestration per unit area multiplied by crop area; 2) Crops area data from China Statistical Yearbook (2021). 3) Carbon input value refers to the multiplication of the total carbon emission caused by the consumption of energy (diesel, electricity, etc.) and production materials (fertilizers, pesticides, etc.) in the cultivation of crops and the price of carbon.

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表 5 不同估算条件下的乡村农田土壤碳汇潜力(中国、美国与全球)

Table 5. Soil carbon sink potential of rural farmland under different assessment conditions (China, US and world)

研究区 Study area	固碳潜力 Carbon sequestration potential [10⁸ t(C)∙a⁻¹)]	估算条件 Assessment condition	来源 Source
中国 China	0.25~0.37	综合养分管理, 作物轮作及有效的保护系统 Comprehensive nutrient management, rotation of crops and effective protection system	[61]
	0.110~0.365	作物产量提高且作物残茬清除量减少 Crop yield increased and crop residue removal reduced	[62]
	0.325	50%的免耕以及50%秸秆还田 50% no-tillage and 50% straw returning	[63]
	0.16~0.20	保护性耕作和水土流失综合治理 Conserving cultivation and soil erosion comprehensive harness	[64]
	0.20~0.25	改善土壤管理和农田经营机制 Improving soil management and farmland management mechanism	[65]
	0.33	20世纪80年代农业生产条件 On the basis of agricultural production condition in the 1980s	[66]
	0.121~0.344	施氮与100%秸秆还田 Nitrogen fertilizer and 100% straw returning	[67]
美国 USA	0.75~2.08	RMP(资源管理计划)和优化土地利用 Resource Management Plans and land use optimization	[68]
	0.9~1.8	退耕还草 Restoring farmland to grassland	[69]
	0.6~0.7	IPCC(联合国政府间气候变化专门委员会)推荐方法 Intergovernmental Panel on Climate Change recommended methods	[70]
全球 World	4.0~8.0	RMP(资源管理计划)与保护性耕作 Resource Management Plans and conserving cultivation	[71]
	5.0~20.0	应用土壤管理新技术 Applying new soil management technologies	[69]
	3.0~15.0	土地利用/土地覆被变化研究和氮沉降 Land use/land cover change studies and nitrogen deposition	[72]

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表 6 不同农田管理措施下农田土壤固碳率的区域差异

Table 6. Regional differences in soil carbon sequestration rate under various farmland management measures in China

农田管理方式 Farmland management method	具体措施 Concrete measure	研究区 Study area	土壤类别 Soil type	作物熟制 Crop cropping system	固碳率 Carbon sequestration [kg(C)∙hm⁻²∙a⁻¹]	来源 Source
秸秆还田模式 Straw returning pattern	堆沤还田 Composting return	华东地区 East China	壤土 Loam soil	小麦-玉米两熟制 Wheat-maize cropping system	447.05	[73]
	堆沤还田 Composting return	华中地区 Central China	麦田土 Wheat soil	小麦一熟制 Wheat single cropping system	676.8	[74]
	覆盖还田 Straw mulching return	华东地区 East China	壤土 Loam soil	小麦-玉米两熟制 Wheat-maize cropping system	118.63	[73]
		华中地区 Central China	麦田土 Wheat soil	小麦一熟制 Wheat single cropping system	410.4	[74]
		华南地区 South China	水稻土 Paddy soil	水稻两熟制 Double rice cropping system	906.8	[75]
		东北地区 Northeast China	中层黑土 Middle layer black soil	玉米一熟制 Maize single cropping system	770	[76]
		西北地区 Northwest China	黄壤 Yellow soil	两年三熟制 Two-year triple cropping system	160	[77]
	过腹还田 Straw return after livestock digestion	华东地区 East China	壤土 Loam soil	小麦-玉米两熟制 Wheat-maize cropping system	604.44	[73]
	过腹还田 Straw return after livestock digestion	华中地区 Central China	麦田土 Wheat soil	小麦一熟制 Wheat single cropping system	758.4	[74]
	炭化还田 Carbonization returning	华南地区 South China	水稻土 Paddy soil	水稻两熟制 Double rice cropping system	1118.2	[75]
	粉碎翻压还田 Breaking and ploughing return	东北地区 Northeast China	中层黑土 Middle layer black soil	玉米一熟制 Maize single cropping system	1740	[76]
耕作模式 Cultivation pattern	翻耕 Plough tillage	华北地区 North China	潮褐土 Meadow cinnamon soil	小麦-玉米两熟制 Wheat-maize cropping system	615.5	[78]
		南方地区 Southern China	水稻土 Paddy soil	水稻-小麦两熟制 Rice-wheat cropping system	449.89	[79]
		西北地区 Northwest China	黑垆土 Black loessial soil	小麦一熟制 Wheat single cropping system	76.85	[80]
		南方地区 Southern China	水稻土 Paddy soil	水稻两熟制 Double rice cropping system	1008	[75]
	免耕 No-tillage	华北地区 North China	砂壤土 Sandy loam soil	玉米一熟制 Maize single cropping system	144	[81]
		西北地区 Northwest China	人为土 Anthropic soils	小麦-玉米两熟制 Wheat-maize cropping system	1090.7	[82]
		华北地区 North China	砂壤土 Sandy loam soil	小麦一熟制 Wheat single cropping system	410	[81]
		华北地区 North China	壤土 Loam soil	小麦-玉米两熟制 Wheat-maize cropping system	1137	[83]
		华北地区 North China	潮褐土 Meadow cinnamon soil	小麦-玉米两熟制 Wheat-maize cropping system	329.1	[78]
		南方地区 Southern China	水稻土 Paddy soil	水稻-小麦两熟制 Rice-wheat cropping system	2333.71	[79]
		西北地区 Northwest China	黑垆土 Black loessial soil	小麦一熟制 Wheat single cropping system	148.58	[80]
		南方地区 Southern China	水稻土 Paddy soil	水稻两熟制 Double rice cropping system	888	[75]
	旋耕 Rotary tillage	西北地区 Northwest China	人为土 Anthropic soils	小麦-玉米两熟制 Wheat-maize cropping system	877.2	[82]
		华北地区 North China	潮褐土 Meadow cinnamon soil	小麦-玉米两熟制 Wheat-maize cropping system	1011.1	[78]
		南方地区 Southern China	水稻土 Paddy soil	水稻两熟制 Double rice cropping system	1065.02	[75]
	深松 Deep scarification	西北地区 Northwest China	人为土 Anthropic soils	小麦-玉米两熟制 Wheat-maize cropping system	1048.9	[82]
	深松 Deep scarification	华北地区 North China	壤土 Loam soil	小麦-玉米两熟制 Wheat-maize cropping system	959	[83]
施肥模式 Fertilization pattern	单施化肥 Single application of chemical fertilizer	南方地区 Southern China	水稻土 Paddy soil	水稻两熟制 Double rice cropping system	140	[84]
		东北地区 Northeast China	淋溶土 Alfisols	—	23.5	[85]
		华北地区 North China	砂壤土 Sandy loam soil	小麦-玉米两熟制 Wheat-maize cropping system	104.67	[86]
		华北地区 North China	砂壤土 Sandy loam soil	小麦-玉米两熟制 Wheat-maize cropping system	76	[87]
		南方地区 Southern China	黄泥土 Yellow clayey	水稻一熟制 Rice single cropping system	950	[88]
		南方地区 Southern China	黄泥土 Yellow clayey	水稻两熟制 Double rice cropping system	620	[88]
		南方地区 Southern China	黄壤 Yellow soil	玉米一熟制 Maize single cropping system	839.05	[89]
		华中地区 Central China	水稻土 Paddy soil	水稻两熟制 Double rice cropping system	1525	[90]
		西北地区 Northwest China	壤土 Loam soil	—	240.51	[91]
	单施有机肥 Single application of organic fertilizer	南方地区 Southern China	水稻土 Paddy soil	水稻两熟制 Double rice cropping system	100	[84]
		东北地区 Northeast China	淋溶土 Alfisols	—	195.3	[85]
		华北地区 North China	砂壤土 Sandy loam soil	小麦-玉米两熟制 Wheat-maize cropping system	1653	[87]
		南方地区 Southern China	黄壤 Yellow soil	玉米一熟制 Maize single cropping system	1300.48	[89]
		西北地区 Northwest China	壤土 Loam soil	—	215.91	[91]
	混施有机肥化肥 Mixed application of organic and chemical fertilizers	南方地区 Southern China	水稻土 Paddy soil	水稻两熟制 Double rice cropping system	170	[84]
		东北地区 Northeast China	淋溶土 Alfisols	—	489	[85]
		华北地区 North China	砂壤土 Sandy loam soil	小麦-玉米两熟制 Wheat-maize cropping system	564	[86]
		华北地区 North China	砂壤土 Sandy loam soil	小麦-玉米两熟制 Wheat-maize cropping system	798	[87]
		南方地区 Southern China	黄泥土 Yellow clayey	水稻一熟制 Rice single cropping system	1090	[88]
		南方地区 Southern China	黄泥土 Yellow clayey	水稻两熟制 Double rice cropping system	990	[88]
		南方地区 Southern China	黄壤 Yellow soil	玉米一熟制 Maize single cropping system	1153.33	[89]
		华中地区 Central China	水稻土 Paddy soil	水稻两熟制 Double rice cropping system	3120	[90]

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表 7 中国乡村减排增汇措施及其效果

Table 7. Measures and their effects of rural emission reduction and sink increase in China

乡村地域系统 Rural regional system	活动 Activity	属性 Attribute	减排增汇重点 Emission reduction and sink increase focus	途径 Approach	具体措施 Concrete measure	减排效果 Emission reduction effect	增汇效果 Sink increase effect	来源 Source
农业系统 Agricultural system	种植业 Planting industry	碳源/碳汇 Carbon source/ carbon sink	肥料施用 Fertilizer application	使用生物炭 Using biochar	15 t∙hm⁻²生物碳 15 t∙hm⁻² Biochar	1322.34 kg(CO₂)∙hm⁻²∙a⁻¹	16.88 g(C)∙kg⁻¹	[93]
				添加抑制剂 Adding inhibitors	施用硝化抑制剂 Application of nitrification inhibitors	2.42 kg(N₂O)∙hm⁻²	228.5 kg(C)∙hm⁻²	[94]
				改用长效肥料 Switching to slow-acting fertilizer	施用长效碳酸氢铵 Application of long-effect ammonium bicarbonate	0.03 kg(CO₂)∙kg⁻¹	4.53 g(C)∙kg⁻¹	[95]
				测土配方培肥 Soil testing formula fertilization	施用控释肥 Application of controlled-release fertilizer	13.26 μg(C)∙m⁻²∙h⁻¹	617 k g(C)∙hm⁻²	[96]
			农田管理 Farmland management	水分管理 Water management	间歇灌溉 Intermittent irrigation	2854.5 kg(CO₂)∙hm⁻²	2526.6 kg(C)∙hm⁻²	[97]
				水分管理 Water management	烤田处理 Drying treatment	469.9 kg(CH₄)∙hm⁻²∙a⁻¹	0.24 t(C)∙hm⁻²∙a⁻¹	[97]
				肥料控制 Fertilizer control	氮肥减量施用 Reducing nitrogen application	1034 kg(CO₂)∙hm⁻²	570 kg(C)∙hm⁻²	[87]
				品种选育控制 Variety breeding control	种植杂交水稻 Planting hybrid rice	13.93 mg∙m⁻²∙h⁻¹	7.66 g∙m⁻²∙d⁻¹	[98-99]
			燃烧秸秆转化 Converting burning straw		秸秆炭化 Straw carbonization	602.82 kg(CO₂)∙kg⁻¹∙a⁻¹	164.45 kg(CO₂)∙kg⁻¹∙a⁻¹	[100]
			燃烧秸秆转化 Converting burning straw		秸秆沼气化 Straw biogasification	27530 kg(CO₂)∙kg⁻¹∙a⁻¹	—	[101]
	养殖业 Breeding industry	碳源 Carbon sink	肠道发酵 Enteric fermentation	沼气工程 Biogas project	秸秆全量利用技术 Whole straw utilization	12 ×16510⁴ t(CO₂)∙a⁻¹	—	[102]
				沼气工程 Biogas project	8 m³水压式沼气池 Hydraulic biogas digester	1612 g(CO₂)∙a⁻¹	—	[103]
				提高饲料消化率 Increasing digestibility of feed	使用舔砖或营养添加剂 Utilization of lick block or nutritional additives	CH₄减排25% 25% reduction of CH₄ emission	—	[104]
				改善饲料质量 Improve feed quality	秸秆氨化处理 Straw ammoniation treatment	11.04 kg(CH₄)∙head⁻¹∙a⁻¹	—	[105]
				改善饲料质量 Improve feed quality	饲喂青贮玉米秸秆 Silage corn straw as feed	32.68 L(CH₄)∙d⁻¹	—	[105]
			粪便管理 Manure management	固体粪便利用 Solid manure utilization	反应器式堆肥 Reactor composting	33.27 g(CO₂)∙kg⁻¹	—	[106]
				添加覆盖物 Mulching	表面罩多孔渗水膜 Porous permeable membrane coverage	0.42 g(C)∙m⁻³∙h⁻¹	—	[107]
				添加覆盖物 Mulching	稻草覆盖粪便表面 Porous permeable membrane coverage	0.28 g(C)∙m⁻³∙h⁻¹	—	[108]
村庄系统 Village system	居民生活 Residential living	碳源 Carbon source	劳动力 Labor	人力资源投入 Human resource input	(地区总人口/地区GDP)提高1% Ratio of regional population to GDP increased by 1%	903.8 ×10⁴ t(CO₂)∙a⁻¹	—	[109]
乡域系统 Rural system			劳动力 Labor	城镇化 Urbanization	(地区总人口/农村总人口)降低1% Ratio of regional population to rural population decreased by 1%	1897.23×10⁴ t(CO₂)∙a⁻¹	—	[56]
城镇系统 Township system			产业 Industry	农业产业结构 Agricultural industrial structure	(种植业产值/农林牧渔产值)降低1% Ratio of planting industry output to agriculture, forestry, animal husbandry and fishery output decreased by 1%.	246.12×10⁴ t(CO₂)∙a⁻¹	—	[56]
			产业 Industry	农业对外开放度 Agricultural openness degree	(农产品进口量/粮食总产量)提高1% Ratio of agricultural product imports to grain output increased by 1%	307.4×10⁴ t(CO₂)∙a⁻¹	—	[110]
			技术 Technology	农业科技进步 Agricultural scientific and technological progress	农业科技支出提高1% Agricultural science and technology expenditure increased by 1 %	491.66×10⁴ t(CO₂)∙a⁻¹	—	[111]
			技术 Technology	农业机械化程度 Agricultural mechanization degree	农业机械总动力降低1% Total power of agricultural machinery reduced by 1%	150.13×10⁴ t(CO₂)∙a⁻¹	—	[56]
				乡村环境治理水平 Rural environmental governance level	(环境治理完成项目额/地区GDP)提高1% Ratio of completed environmental governance projects to regional GDP increased by 1%	487.98×10⁴ t(CO₂)∙a⁻¹	—	[112]
			经济 Economy	经济发展水平 Economic development level	(地区GDP/地区总人口)降低1% Ratio of regional GDP to regional population decreased by 1%	3718.88×10⁴ t(CO₂)∙a⁻¹	—	[56]
			经济 Economy	经济规模 Economic scale	地区GDP降低1% Regional GDP decreased by 1%	959.81×10⁴ t(CO₂)∙a⁻¹	—	[110]

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参考文献(112)

[1]	丁仲礼, 段晓男, 葛全胜, 等. 国际温室气体减排方案评估及中国长期排放权讨论[J]. 中国科学(D辑:地球科学), 2009, 39(12): 1659−1671 DING Z L, DUAN X N, GE Q S, et al. Evaluation of international greenhouse gas emission reduction schemes and discussion on China’s long-term emission rights[J]. Science in China (Series D:Earth Sciences), 2009, 39(12): 1659−1671
[2]	本报评论员. 改善农村环境建设美丽乡村[N]. 光明日报, 2018-02-06(2) Improving rural environment, constructing beautiful countryside[N]. 2018-02-06(2)
[3]	LIU Y S, LI Y H. Revitalize the world’s countryside[J]. Nature, 2017, 548(7667): 275−277 doi: 10.1038/548275a
[4]	CRIPPA M, SOLAZZO E, GUIZZARDI D, et al. Food systems are responsible for a third of global anthropogenic GHG emissions[J]. Nature Food, 2021, 2(3): 1−12
[5]	韦玉琼, 龙飞, 岳欣冉. 乡村振兴背景下农村碳排放变动及减排策略[J]. 农业经济问题, 2022, 43(9): 62−73 WEI Y Q, LONG F, YUE X R. Carbon emission changing and reduction strategy of agriculture and rural areas under the background of rural vitalization[J]. Issues in Agricultural Economy, 2022, 43(9): 62−73
[6]	Intergovernmental Panel on Climate Change. Climate Change 2013: Mitigation of Climate Change Contribution of Working Group Ⅲ to the Fourth Assessment Report of the Intergovernmental Panel on Climate Change[R]. Cambridge, UK: Cambridge University Press, 2013
[7]	谭秋成. 中国农业温室气体排放: 现状及挑战[J]. 中国人口•资源与环境, 2011, 21(10): 69−75 TAN Q C. Greenhouse gas emission in China’s agriculture: situation and challenge[J]. China Population, Resources and Environment, 2011, 21(10): 69−75
[8]	SHUKLA P R, SKEG J, CALVO BUENDIA E, et al. Climate Change and Land: an IPCC special report on climate change, desertification, land degradation, sustainable land management, food security, and greenhouse gas fluxes in terrestrial ecosystems[M]. Cambride, UK: Cambridge University Press, 2019
[9]	TANS P P, FUNG I Y, TAKAHASHI T. Observational constraints on the global atmospheric CO₂ budget[J]. Science, 1990, 247(4949): 1431−1438 doi: 10.1126/science.247.4949.1431
[10]	李波, 张俊飚, 李海鹏. 中国农业碳排放与经济发展的实证研究[J]. 干旱区资源与环境, 2011, 25(12): 8−13 LI B, ZHANG J B, LI H P. Empirical study on China’s agriculture carbon emissions and economic development[J]. Journal of Arid Land Resources and Environment, 2011, 25(12): 8−13
[11]	李波, 张俊飚, 李海鹏. 中国农业碳排放时空特征及影响因素分解[J]. 中国人口•资源与环境, 2011, 21(8): 80−86 LI B, ZHANG J B, LI H P. Research on spatial-temporal characteristics and affecting factors decomposition of agricultural carbon emission in China[J]. China Population, Resources and Environment, 2011, 21(8): 80−86
[12]	田成诗, 陈雨. 中国省际农业碳排放测算及低碳化水平评价−基于衍生指标与TOPSIS法的运用[J]. 自然资源学报, 2021, 36(2): 395−410 doi: 10.31497/zrzyxb.20210210 TIAN C S, CHEN Y. China’s provincial agricultural carbon emissions measurement and low carbonization level evaluation: based on the application of derivative indicators and TOPSIS[J]. Journal of Natural Resources, 2021, 36(2): 395−410 doi: 10.31497/zrzyxb.20210210
[13]	吴昊玥, 何艳秋, 陈柔. 中国农业碳排放绩效评价及随机性收敛研究−基于SBM-Undesirable模型与面板单位根检验[J]. 中国生态农业学报, 2017, 25(9): 1381−1391 WU H Y, HE Y Q, CHEN R. Assessment of agricultural carbon emission performance and stochastic convergence in China using SBM-Undesirable model and panel unit root test[J]. Chinese Journal of Eco-Agriculture, 2017, 25(9): 1381−1391
[14]	韦惠兰, 杨彬如. 中国农村碳排放核算及分析: 1999—2010[J]. 西北农林科技大学学报(社会科学版), 2014, 14(3): 10−15 WEI H L, YANG B R. Accounting and analysis of carbon emission in rural areas of China[J]. Journal of Northwest A& F University (Social Science Edition), 2014, 14(3): 10−15
[15]	李治国, 王杰. 中国城乡家庭碳排放核算及驱动因素分析[J]. 统计与决策, 2021, 37(20): 48−52 LI Z G, WANG J. Accounting and driving factors analysis of household carbon emissions in urban and rural China[J]. Statistics & Decision, 2021, 37(20): 48−52
[16]	刘晶茹, Glen P. Peters, 王如松, 等. 综合生命周期分析在可持续消费研究中的应用[J]. 生态学报, 2007, 27(12): 5331−5336 LIU J R, PETERS G P, WANG R S, et al. Hybrid life-cycle analysis and its applications in sustainable consumption researches[J]. Acta Ecologica Sinica, 2007, 27(12): 5331−5336
[17]	朱勤, 彭希哲, 陆志明, 等. 1980—2007年中国居民生活用能碳排放测算与分析[J]. 安全与环境学报, 2010, 10(2): 72−76 ZHU Q, PENG X Z, LU Z M, et al. Calculation and analysis on carbon emissions from household energy consumption in China during 1980–2007[J]. Journal of Safety and Environment, 2010, 10(2): 72−76
[18]	李科. 我国城乡居民生活能源消费碳排放的影响因素分析[J]. 消费经济, 2013, 29(2): 73−76,80 LI K. Analysis on the influencing factors of carbon emissions from domestic energy consumption of urban and rural residents in China[J]. Consumer Economics, 2013, 29(2): 73−76,80
[19]	刘莉娜, 曲建升, 邱巨龙, 等. 1995—2010年居民家庭生活消费碳排放轨迹[J]. 开发研究, 2012(4): 117−121 LIU L N, QU J S, QIU J L, et al. Carbon emission trajectory of household consumption from 1995 to 2010[J]. Research on Development, 2012(4): 117−121
[20]	张馨, 牛叔文, 赵春升, 等. 中国城市化进程中的居民家庭能源消费及碳排放研究[J]. 中国软科学, 2011(9): 65−75 ZHANG X, NIU S W, ZHAO C S, et al. The study on household energy consumption and carbon emissions in China’s urbanization[J]. China Soft Science, 2011(9): 65−75
[21]	万文玉, 赵雪雁, 王伟军, 等. 我国农村居民生活能源碳排放的时空特征分析[J]. 生态学报, 2017, 37(19): 6390−6401 WAN W Y, ZHAO X Y, WANG W J, et al. Analysis of spatio-temporal patterns of carbon emission from energy consumption by rural residents in China[J]. Acta Ecologica Sinica, 2017, 37(19): 6390−6401
[22]	TANS P P, FUNG I Y, TAKAHASHI T. Observational contrains on the global atmospheric CO₂ budget[J]. Science, 1990, 247(4949): 1431−1438 doi: 10.1126/science.247.4949.1431
[23]	田云, 张俊飚. 农业碳排放国内外研究进展[J]. 中国农业大学学报, 2013, 18(3): 203−208 TIAN Y, ZHANG J B. International and domestic research progress on agricultural carbon emission[J]. Journal of China Agricultural University, 2013, 18(3): 203−208
[24]	王喜, 鲁丰先, 秦耀辰, 等. 河南省碳源碳汇的时空变化研究[J]. 地理科学进展, 2016, 35(8): 941−951 doi: 10.18306/dlkxjz.2016.08.003 WANG X, LU F X, QIN Y C, et al. Spatial and temporal changes of carbon sources and sinks in Henan Province[J]. Progress in Geography, 2016, 35(8): 941−951 doi: 10.18306/dlkxjz.2016.08.003
[25]	邢燕燕, 张艳芳. 农用地碳汇效应估算及时空变化特征分析−以陕西省为例[J]. 干旱地区农业研究, 2011, 29(3): 203−208,259 XING Y Y, ZHANG Y F. Study on effects of carbon fixed by different agricultural vegetation patterns in Shaanxi[J]. Agricultural Research in the Arid Areas, 2011, 29(3): 203−208,259
[26]	吕斯涵, 张小平. 山东省农业净碳汇时空演化特征分析[J]. 水土保持学报, 2019, 33(2): 227−234 LYU S H, ZHANG X P. Spatial-temporal characteristics of agricultural net carbon sink in Shandong Province[J]. Journal of Soil and Water Conservation, 2019, 33(2): 227−234
[27]	田云, 张俊飚. 中国农业生产净碳效应分异研究[J]. 自然资源学报, 2013, 28(8): 1298−1309 doi: 10.11849/zrzyxb.2013.08.003 TIAN Y, ZHANG J B. Regional differentiation research on net carbon effect of agricultural production in China[J]. Journal of Natural Resources, 2013, 28(8): 1298−1309 doi: 10.11849/zrzyxb.2013.08.003
[28]	曹执令, 黄飞, 伍赛君. 中国农业生产碳汇效应与生产绩效的时空特征[J]. 经济地理, 2022, 42(9): 166−175 CAO Z L, HUANG F, WU S J. Carbon sink measurement and spatio-temporal evolution of agriculture production in China[J]. Economic Geography, 2022, 42(9): 166−175
[29]	陈罗烨, 薛领, 雪燕. 中国农业净碳汇时空演化特征分析[J]. 自然资源学报, 2016, 31(4): 596−607 CHEN L Y, XUE L, XUE Y. Spatial-temporal characteristics of China’s agricultural net carbon sink[J]. Journal of Natural Resources, 2016, 31(4): 596−607
[30]	杨果, 陈瑶. 中国农业源碳汇估算及其与农业经济发展的耦合分析[J]. 中国人口·资源与环境, 2016, 26(12): 171−176 YANG G, CHEN Y. China’s agriculture carbon sink estimation and its coupling analysis with agricultural economy development[J]. China Population, Resources and Environment, 2016, 26(12): 171−176
[31]	刘彦随, 周扬, 李玉恒. 中国乡村地域系统与乡村振兴战略[J]. 地理学报, 2019, 74(12): 2511−2528 LIU Y S, ZHOU Y, LI Y H. Rural regional system and rural revitalization strategy in China[J]. Acta Geographica Sinica, 2019, 74(12): 2511−2528
[32]	刘彦随. 现代人地关系与人地系统科学[J]. 地理科学, 2020, 40(8): 1221−1234 LIU Y S. Modern human-earth relationship and human-earth system science[J]. Scientia Geographica Sinica, 2020, 40(8): 1221−1234
[33]	刘昱, 陈敏鹏, 陈吉宁. 农田生态系统碳循环模型研究进展和展望[J]. 农业工程学报, 2015, 31(3): 1−9 LIU Y, CHEN M P, CHEN J N. Progress and perspectives in studies on agro-ecosystem carbon cycle model[J]. Transactions of the Chinese Society of Agricultural Engineering, 2015, 31(3): 1−9
[34]	CONRAD R. The global methane cycle: recent advances in understanding the microbial processes involved[J]. Environmental Microbiology Reports, 2009, 1(5): 285−292 doi: 10.1111/j.1758-2229.2009.00038.x
[35]	祝贞科, 肖谋良, 魏亮, 等. 稻田土壤固碳关键过程的生物地球化学机制及其碳中和对策[J]. 中国生态农业学报(中英文), 2022, 30(4): 592−602 ZHU Z K, XIAO M L, WEI L, et al. Key biogeochemical processes of carbon sequestration in paddy soil and its countermeasures for carbon neutrality[J]. Chinese Journal of Eco-Agriculture, 2022, 30(4): 592−602
[36]	BARANČÍKOVÁ G, MAKOVNÍKOVÁ J, HALAS J. Effect of land use change on soil organic carbon[J]. Agriculture (Polnohospodárstvo), 2016, 62(1): 10−18
[37]	GLASS G V. Primary, secondary, and meta-analysis of research[J]. Educational Researcher, 1976, 5(10): 3−8 doi: 10.3102/0013189X005010003
[38]	MOHER D, LIBERATI A, TETZLAFF J, et al. Preferred reporting items for systematic reviews and Meta-analyses: the PRISMA statement[J]. Annals of Internal Medicine, 2009, 151(4): 264−269,W64 doi: 10.7326/0003-4819-151-4-200908180-00135
[39]	吴贤荣, 张俊飚, 程文能. 中国种植业低碳生产效率及碳减排成本研究[J]. 环境经济研究, 2017, 2(1): 57−69 WU X R, ZHANG J B, CHENG W N. The efficiency and reduction cost of carbon emission in China’s planting industry[J]. Journal of Environmental Economics, 2017, 2(1): 57−69
[40]	苏旭峰, 杨小东, 冉启英. 基于碳排放视角的中国畜牧业绿色增长分析[J]. 生态经济, 2022, 38(4): 101−107 SU X F, YANG X D, RAN Q Y. Analysis on the green growth of animal Husbandry in China from the Perspective of Carbon Emissions[J]. Ecological Economy, 2022, 38(4): 101−107
[41]	孟祥海, 程国强, 张俊飚, 等. 中国畜牧业全生命周期温室气体排放时空特征分析[J]. 中国环境科学, 2014, 34(8): 2167−2176 MENG X H, CHENG G Q, ZHANG J B, et al. Analyze on the spatial temporal characteristics of GHG estimation of livestock by life cycle assessment in China[J]. China Environmental Science, 2014, 34(8): 2167−2176
[42]	郭娇, 齐德生, 张妮娅, 等. 中国畜牧业温室气体排放现状及峰值预测[J]. 农业环境科学学报, 2017, 36(10): 2106−2113 GUO J, QI D S, ZHANG N Y, et al. Chinese greenhouse gas emissions from livestock: trend and predicted peak value[J]. Journal of Agro-Environment Science, 2017, 36(10): 2106−2113
[43]	金书秦, 李颖, 胡浚哲. 农业碳减排的技术与政策[J]. 开放导报, 2021(6): 97−104 JIN S Q, LI Y, HU J Z. Technical options and policy arrangements for reduction of agricultural carbon emission[J]. China Opening Journal, 2021(6): 97−104
[44]	陈舜, 逯非, 王效科. 中国氮磷钾肥制造温室气体排放系数的估算[J]. 生态学报, 2015, 35(19): 6371−6383 CHEN S, LU F, WANG X K. Estimation of greenhouse gases emission factors for China's nitrogen, posphate, and potash fertilizers[J]. Acta Ecologica Sinica, 2015, 35(19): 6371−6383
[45]	国家发展与改革委员会. 省级温室气体清单编制指南(试行)[R]. 北京: 国家发展与改革委员会, 2011 National Development and Reform Commission. Provincial greenhouse gas inventory guidelines (Trial)[R]. Beijing: National Development and Reform Commission, 2011
[46]	WEST T O, MARLAND G. A synthesis of carbon sequestration, carbon emissions, and net carbon flux in agriculture: comparing tillage practices in the United States[J]. Agriculture, Ecosystems and Environment, 2002, 91(1): 217−232
[47]	DAVID W K, GEOFFREY H, DAVID S A, et al. A process for capturing CO₂ from the atmosphere[J]. Joule, 2018, 2(10): 2179 doi: 10.1016/j.joule.2018.09.017
[48]	WEI Y M, LIU L C, FAN Y, et al. The impact of lifestyle on energy use and CO₂ emission: an empirical analysis of China’s residents[J]. Energy Policy, 2007, 35(1): 247−257 doi: 10.1016/j.enpol.2005.11.020
[49]	张保留, 吕连宏, 吴静, 等. 农村居民生活碳达峰路径及对策[J]. 环境科学研究, 2021, 34(9): 2065−2075 ZHANG B L, LYU L H, WU J, et al. Rural household carbon-peak path and countermeasures[J]. Research of Environmental Sciences, 2021, 34(9): 2065−2075
[50]	杜威, 樊胜岳. 城镇化进程中居民生活碳排放动态特征分析[J]. 生态经济, 2016, 32(5): 48−52,101 DU W, FAN S Y. Dynamic analysis of carbon emissions for urban and rural residents in the process of urbanization[J]. Ecological Economy, 2016, 32(5): 48−52,101
[51]	曲建升, 刘莉娜, 曾静静, 等. 中国居民生活碳排放增长路径研究[J]. 资源科学, 2017, 39(12): 2389−2398 QU J S, LIU L N, ZENG J J, et al. A study on growth path for China’s household CO₂ emissions[J]. Resources Science, 2017, 39(12): 2389−2398
[52]	汝醒君, 汪臻. 中国农村居民生活用能碳排放影响因素研究[J]. 生态经济, 2017, 33(1): 73−76 RU X J, WANG Z. Study on influence factors of rural residents’ CO₂ emission in China[J]. Ecological Economy, 2017, 33(1): 73−76
[53]	颜光耀, 陈卫洪, 钱海慧. 农业技术效率对农业碳排放的影响−基于空间溢出效应与门槛效应分析[J]. 中国生态农业学报(中英文), 2023, 31(2): 226−240 YAN G Y, CHEN W H, QIAN H H. Effects of agricultural technical efficiency on agricultural carbon emission — Based on spatial spillover effect and threshold effect analysis[J]. Chinese Journal of Eco-Agriculture, 2023, 31(2): 226−240
[54]	徐子瀛. 我国农村居民生活消费碳排放影响因素的门限效应研究[J]. 统计与管理, 2019(3): 22−25 XU Z Y. Study on the threshold effect of the factors influencing the carbon emissions of rural residents’ domestic consumption in China[J]. Statistics and Management, 2019(3): 22−25
[55]	陈冲影, 姚春生, 黎明. 中国农村生活用能及其碳排放分析(2001-2010)[J]. 可再生能源, 2012, 30(4): 121−127 CHEN C Y, YAO C S, LI M. Analysis of rural residential energy consumption and its carbon emission in China, 2001-2010[J]. Renewable Energy Resources, 2012, 30(4): 121−127
[56]	胡婉玲, 张金鑫, 王红玲. 中国农业碳排放特征及影响因素研究[J]. 统计与决策, 2020, 36(5): 56−62 HU W L, ZHANG J X, WANG H L. Characteristics and Influencing Factors of Agricultural Carbon Emission in China[J]. Statistics & Decision, 2020, 36(5): 56−62
[57]	佘玮, 黄璜, 官春云, 等. 我国典型农作区作物生产碳汇功能研究[J]. 中国工程科学, 2016, 18(1): 106−113 SHE W, HUANG H, GUAN C Y, et al. Study on the carbon sink function of crop production in typical agricultural areas of China[J]. Strategic Study of CAE, 2016, 18(1): 106−113
[58]	白保勋, 陈东海, 徐婷婷, 等. 主要粮经作物与轮作模式净碳汇价值分析[J]. 生态经济, 2021, 37(9): 97−101 BAI B X, CHEN D H, XU T T, et al. Analysis on net carbon sink value of main grain crops and crop rotation[J]. Ecological Economy, 2021, 37(9): 97−101
[59]	ZHANG H LI S. Carbon emissions’ spatial-temporal heterogeneity and identification from rural energy consumption in China[J]. Journal of Environmental Management, 2022, 304: 114286 doi: 10.1016/j.jenvman.2021.114286
[60]	张国, 逯非, 王效科. 保护性耕作对温室气体排放和经济成本的影响−以山东滕州和兖州为例[J]. 山东农业科学, 2014, 46(5): 34−37 ZHANG G, LU F, WANG X K. Influences of conservation tillage on greenhouse gas emission and economic cost — a case study of Tengzhou and Yanzhou in Shandong Province[J]. Shandong Agricultural Sciences, 2014, 46(5): 34−37
[61]	LAL R. Soil carbon sequestration in China through agricultural intensification, and restoration of degraded and desertified ecosystems[J]. Land Degradation & Development, 2010, 13(6): 469−478
[62]	YU Y Q, HUANG Y, ZHANG W. Modeling soil organic carbon change in croplands of China, 1980–2009[J]. Global and Planetary Change, 2012, 82/83: 115−128 doi: 10.1016/j.gloplacha.2011.12.005
[63]	YAN H M, CAO M K, LIU J Y, et al. Potential and sustainability for carbon sequestration with improved soil management in agricultural soils of China[J]. Agriculture, Ecosystems & Environment, 2007, 121(4): 325−335
[64]	黄耀, 孙文娟. 近20年来中国大陆农田表土有机碳含量的变化趋势[J]. 科学通报, 2006, 51(7): 750−763 doi: 10.1360/csb2006-51-7-750 HUANG Y, SUN W J. Variation trend of organic carbon content in farmland topsoil in Chinese mainland in recent 20 years[J]. Chinese Science Bulletin, 2006, 51(7): 750−763 doi: 10.1360/csb2006-51-7-750
[65]	郑聚锋, 程琨, 潘根兴, 等. 关于中国土壤碳库及固碳潜力研究的若干问题[J]. 科学通报, 2011, 56(26): 2162−2173 doi: 10.1360/csb2011-56-26-2162 ZHENG J F, CHENG K, PAN G X, et al. Some problems on the study of soil carbon pool and carbon sequestration potential in China[J]. Chinese Science Bulletin, 2011, 56(26): 2162−2173 doi: 10.1360/csb2011-56-26-2162
[66]	梁二, 蔡典雄, 代快, 等. 中国农田土壤有机碳变化: Ⅱ 土壤固碳潜力估算[J]. 中国土壤与肥料, 2010(6): 87−92 LIANG E, CAI D X, DAI K, et al. Changes in soil organic carbon in croplands of China: Ⅱ Estimation of soil carbon sequestration potentials[J]. Soil and Fertilizer Sciences in China, 2010(6): 87−92
[67]	LU F, WANG X K, HAN B, et al. Soil carbon sequestrations by nitrogen fertilizer application, straw return and no-tillage in China’s cropland[J]. Global Change Biology, 2009, 15(2): 281−305 doi: 10.1111/j.1365-2486.2008.01743.x
[68]	LAL R, KIMBLE J M, FOLLETT R F, et al. The Potential of US Crop Lands to Sequester Carbon and Mitigate the Greenhouse Effect[M]. Chelsea, Michigan, USA: Ann Arbor Press, 1998
[69]	METTING F B, SMITH J L, AMTHOR J S, et al. Science needs and new technology for increasing soil carbon sequestration[J]. Climatic Change, 2001, 51(1): 11−34 doi: 10.1023/A:1017509224801
[70]	SPEROW M, EVE M, PAUSTIAN K. Potential soil C sequestration on U. S. agricultural soils[J]. Climatic Change, 2003, 57(3): 319−339 doi: 10.1023/A:1022888832630
[71]	LAL R. Soil carbon sequestration impacts on global climate change and food security[J]. Science, 2004, 304(5677): 1623−1627 doi: 10.1126/science.1097396
[72]	MCGUIR A D, SITCH S, CLEIN J S, et al. Carbon balance of the terrestrial biosphere in the twentieth century: analyses of CO₂, climate and land use effects with four process-based ecosystem models[J]. Global Biogeochemical Cycles, 2001, 15(1): 183−206 doi: 10.1029/2000GB001298
[73]	李新华, 朱振林, 董红云, 等. 秸秆不同还田模式对玉米田温室气体排放和碳固定的影响[J]. 农业环境科学学报, 2015, 34(11): 2228−2235 LI X H, ZHU Z L, DONG H Y, et al. Effects of different return modes of wheat straws on greenhouse gas emissions and carbon sequestration of maize fields[J]. Journal of Agro-Environment Science, 2015, 34(11): 2228−2235
[74]	马守臣, 邵云, 李春喜, 等. 秸秆还田方式对麦田生态系统土壤呼吸季节动态及碳收支的影响[C]//中国农学会耕作制度分会2016年学术年会论文摘要集. 乌鲁木齐: 中国农学会耕作制度分会, 2016 MA S C, SHAO Y, LI C X, et al. Effects of straw return methods on the seasonal dynamics of soil respiration and carbon balance in wheat field ecosystems[C]//The Paper Abstract of 2016 Annual Academic Conference of Cropping System Branch of Chinese Agricultural Society. Urumchi: Cropping System Branch of Chinese Agricultural Society, 2016
[75]	张卫红. 秸秆还田方式与水稻品种对双季稻田CH₄和N₂O排放的影响[D]. 北京: 中国农业科学院, 2016 ZHANG W H. The impact of different straw returning forms and rice varieties on CH₄ and N₂O emission in a double rice field[D]. Beijing: Chinese Academy of Agricultural Sciences, 2016
[76]	梁尧, 蔡红光, 杨丽, 等. 玉米秸秆覆盖与深翻两种还田方式对黑土有机碳固持的影响[J]. 农业工程学报, 2021, 37(1): 133−140 LIANG Y, CAI H G, YANG L, et al. Effects of maize stovers returning by mulching or deep tillage on soil organic carbon sequestration in Mollisol[J]. Transactions of the Chinese Society of Agricultural Engineering, 2021, 37(1): 133−140
[77]	王明明. 8年保护性耕作对黄土高原玉米—小麦—大豆轮作系统土壤碳固定的影响[D]. 兰州: 兰州大学, 2011 WANG M M. Conservation tillage influence on soil carbon sequestration in a maize-wheat-soybean rotation system on the Loess Plateau[D]. Lanzhou: Lanzhou University, 2011
[78]	韩宾, 孔凡磊, 张海林, 等. 耕作方式转变对小麦/玉米两熟农田土壤固碳能力的影响[J]. 应用生态学报, 2010, 21(1): 91−98 HAN B, KONG F L, ZHANG H L, et al. Effects of tillage conversion on carbon sequestration capability of farmland soil doubled cropped with wheat and corn[J]. Chinese Journal of Applied Ecology, 2010, 21(1): 91−98
[79]	宋知远. 长三角稻麦轮作农田秸秆还田方式的净减排潜力及推广策略[D]. 南京: 南京农业大学, 2019 SONG Z Y. Potential of straw return modes on the net emission mitigation and its extension policy suggestions in a rice-wheat rotation system of Yangtze Delta Plain[D]. Nanjing: Nanjing Agricultural University, 2019
[80]	张霞. 耕作与施肥对渭北旱塬黑垆土碳库构成的影响[D]. 杨凌: 西北农林科技大学, 2018 ZHANG X. Effects of tillage and fertilization on composition of organic carbon pool in Dark Loessial soil of Weibei Hiagland[D]. Yangling: Northwest A&F University, 2018
[81]	王小彬, 王燕, 代快, 等. 旱地农田不同耕作系统的能量/碳平衡[J]. 生态学报, 2011, 31(16): 4638−4652 WANG X B, WANG Y, DAI K, et al. Coupled energy and carbon balance analysis under dryland tillage systems[J]. Acta Ecologica Sinica, 2011, 31(16): 4638−4652
[82]	禄兴丽. 保护性耕作措施下西北旱作麦玉两熟体系碳平衡及经济效益分析[D]. 杨凌: 西北农林科技大学, 2017 LU X L. Carbon Balance and Economic Benefit of Winter W heat-Summer maize in the Dryland of Northwestern China Under Conservation Tillage[D]. Yangling: Northwest A&F University, 2017
[83]	张恒恒, 严昌荣, 张燕卿, 等. 北方旱区免耕对农田生态系统固碳与碳平衡的影响[J]. 农业工程学报, 2015, 31(4): 240−247 doi: 10.3969/j.issn.1002-6819.2015.04.034 ZHANG H H, YAN C R, ZHANG Y Q, et al. Effect of no tillage on carbon sequestration and carbon balance in farming ecosystem in dryland area of Northern China[J]. Transactions of the Chinese Society of Agricultural Engineering, 2015, 31(4): 240−247 doi: 10.3969/j.issn.1002-6819.2015.04.034
[84]	樊红柱, 秦鱼生, 陈庆瑞, 等. 长期施肥紫色水稻土团聚体稳定性及其固碳特征[J]. 植物营养与肥料学报, 2015, 21(6): 1473−1480 FAN H Z, QIN Y S, CHEN Q R, et al. Distribution and stability of soil aggregates and carbon sequestration in purple paddy soil under long-term fertilization[J]. Journal of Plant Nutrition and Fertilizer, 2015, 21(6): 1473−1480
[85]	兰宇, Muhammad Imran Asshraf, 韩晓日, 等. 长期施肥对棕壤有机碳储量及固碳速率的影响[J]. 环境科学学报, 2016, 36(1): 264−270 LAN Y, ASSHRAF M, HAN X R, et al. Effect of long-term fertilization on total organic carbon storage and carbon sequestration rate in a brown soil[J]. Acta Scientiae Circumstantiae, 2016, 36(1): 264−270
[86]	尹云锋, 蔡祖聪. 不同施肥措施对潮土有机碳平衡及固碳潜力的影响[J]. 土壤, 2006(06): 745−749 YIN Y F, CAI Z C. Effect of fertilization on equilibrium levels of organic carbon and capacities of soil stabilizing organic carbon for Fluvo-aquic soil[J]. Soils, 2006(06): 745−749
[87]	常乃杰. 气候变化背景下施肥管理措施对环渤海区域主要粮食作物产量和固碳减排的影响[D]. 北京: 中国农业科学院, 2020 CHANG N J. Study on the response of main crops yield and soil carbon sequestration and greenhouse gas eEmission under different fertilization practices to future climate change in Bohai Rim[D]. Beijing: Chinese Academy of Agricultural Sciences, 2020
[88]	王飞, 李清华, 林诚, 等. 不同施肥模式对南方黄泥田耕层有机碳固存及生产力的影响[J]. 植物营养与肥料学报, 2015, 21(6): 1447−1454 WANG F, LI Q H, LIN C, et al. Effect of different fertilization modes on topsoil organic carbon sequestration and productivity in yellow paddy field of Southern China[J]. Journal of Plant Nutrition and Fertilizer, 2015, 21(6): 1447−1454
[89]	张雅蓉, 李渝, 刘彦伶, 等. 长期施肥下黄壤有机碳库演变及固存特征[J]. 西南农业学报, 2018, 31(4): 770−778 ZHANG Y R, LI Y, LIU Y L, et al. Evolution and sequestration characteristics of organic carbon pool in yellow soil under long-term fertilization[J]. Southwest China Journal of Agricultural Sciences, 2018, 31(4): 770−778
[90]	彭华, 纪雄辉, 刘昭兵, 等. 洞庭湖地区长期施肥条件下双季稻田生态系统净碳汇效应及收益评估[J]. 农业环境科学学报, 2009, 28(12): 2526−2532 PENG H, JI X H, LIU Z B, et al. Evaluation of net carbon sink effect and economic benefit in double rice field ecosystem under long-term fertilization[J]. Journal of Agro-Environment Science, 2009, 28(12): 2526−2532
[91]	颉鹏. 河西绿洲农田生态系统土壤碳汇时空演变研究[D]. 兰州: 甘肃农业大学, 2009 JIE P. Research on spatial and temporal evolution of soil carbon sequestration of oasis farmland ecosystem in Hexi[D]. Lanzhou: Gansu Agricultural University, 2009
[92]	中华人民共和国农业农村部. 中央农村工作会议系列解读⑤强化种业企业创新能力切实推进种业振兴行动[EB/OL]. (2023-01-04). http://www.moa.gov.cn/ztzl/zyncgzh2022/mtbd_29318/202301/t20230105_6418357.htm Ministry of Agriculture and Rural Affairs of the People’s Republic of China. Interpretation of the central rural work conference series ⑤Strengthen the innovation ability of seed enterprises and effectively promote the revitalization of planting industry[EB/OL]. (2023-01-04). http://www.moa.gov.cn/ztzl/zyncgzh2022/mtbd_29318/202301/t20230105_6418357.htm
[93]	高利华. 滴灌条件下水炭耦合对土壤节水保肥和固碳减排综合效应研究[D]. 呼和浩特: 内蒙古农业大学, 2017 GAO L H. Research of coupling effects of water and biochar on preserving water and nutrients and fixing carbon and reducing emission’s combined effects on base of drip irrigation[D]. Hohhot: Inner Mongolia Agricultural University, 2017
[94]	赵自超, 韩笑, 石岳峰, 等. 硝化和脲酶抑制剂对华北冬小麦-夏玉米轮作固碳减排效果评价[J]. 农业工程学报, 2016, 32(6): 254−262 ZHAO Z C, HAN X, SHI Y F, et al. Effect of nitrification and urease inhibitor on carbon sequestration and greenhouse gas emissions in winter wheat and summer maize rotation system in North China[J]. Transactions of the Chinese Society of Agricultural Engineering, 2016, 32(6): 254−262
[95]	舒常禄, 马秀枝, 蒙美莲, 等. 炭基肥施用对农田土壤性质及温室气体排放的影响[J]. 内蒙古农业大学学报(自然科学版), 2017, 38(2): 49−61 SHU C L, MA X Z, MENG M L, et al. Effects of biochar based fertilizer amendment on soil properties and greenhouse gas emission[J]. Journal of Inner Mongolia Agricultural University (Natural Science Edition), 2017, 38(2): 49−61
[96]	李方敏, 樊小林, 刘芳, 等. 控释肥料对稻田氧化亚氮排放的影响[J]. 应用生态学报, 2004(11): 2170−2174 LI F M, FAN X L, LIU F, et al. Effects of controlled release fertilizers on N₂O emission from paddy field[J]. Chinese Journal of Applied Ecology, 2004(11): 2170−2174
[97]	汤宏, 曾掌权, 沈健林, 等. 秸秆与水分管理稻田的温室气体排放和碳固定[J]. 环境科学与技术, 2021, 44(1): 41−48 TANG J, ZENG Z Q, SHEN J L, et al. Greenhouse gases emissions and carbon sequestration by soils in rice paddy fields as affected by rice straw incorporation and water management[J]. Environmental Science & Technology, 2021, 44(1): 41−48
[98]	李晶, 王明星, 陈德章. 水稻田甲烷的减排方法研究及评价[J]. 大气科学, 1998, 21(3): 99−107 doi: 10.3878/j.issn.1006-9895.1998.03.11 LI J, WANG M X, CHEN D Z. Studies on mitigation methods of methane emission from rice paddies[J]. Chinese Journal of Atmospheric Sciences, 1998, 21(3): 99−107 doi: 10.3878/j.issn.1006-9895.1998.03.11
[99]	林瑞余, 蔡碧琼, 柯庆明, 等. 不同水稻品种产量形成过程的固碳特性研究[J]. 中国农业科学, 2006, 38(12): 2441−2448 LIN R Y, CAI B Q, KE Q M, et al. Characteristics of carbon fixation in different rice cultivars during yield formation process[J]. Scientia Agricultura Sinica, 2006, 38(12): 2441−2448
[100]	李飞跃, 汪建飞. 中国粮食作物秸秆焚烧排碳量及转化生物炭固碳量的估算[J]. 农业工程学报, 2013, 29(14): 1−7 doi: 10.3969/j.issn.1002-6819.2013.14.001 LI F Y, WANG J F. Estimation of carbon emission from straw burning and carbon sequestration from biochar producing using crop straw in China[J]. Transactions of the Chinese Society of Agricultural Engineering, 2013, 29(14): 1−7 doi: 10.3969/j.issn.1002-6819.2013.14.001
[101]	王艺鹏, 杨晓琳, 谢光辉, 等. 1995—2014年中国农作物秸秆沼气化碳足迹分析[J]. 中国农业大学学报, 2017, 22(5): 1−14 WANG Y P, YANG X L, XIE G H, et al. Temporal variation in carbon footprint of crop residue for biogas utilization in China from 1995 to 2014[J]. Journal of China Agricultural University, 2017, 22(5): 1−14
[102]	石祖梁, 贾涛, 王亚静, 等. 我国农作物秸秆综合利用现状及焚烧碳排放估算[J]. 中国农业资源与区划, 2017, 38(9): 32−37 SHI Z L, JIA T, WANG Y J, et al. Comprehensive utilization status of crop straw and estimation of carbon from burning in China[J]. Chinese Journal of Agricultural Resources and Regional Planning, 2017, 38(9): 32−37
[103]	郝先荣, 沈丰菊. 户用沼气池综合效益评价方法[J]. 可再生能源, 2006, 23(2): 4−6 HAO X R, SHEN F J. Evaluation on the composite benefit of household biogas digesters[J]. Renewable Energy Resources, 2006, 23(2): 4−6
[104]	LENG R A. Improving ruminant production and reducing methane emissions from ruminants by strategic supplementation[R]. Washington DC: EPA, 1991: 105
[105]	DONG H M, TAO X Y, XIN H W, et al. Comparison of enteric methane emissions in China for different IPCC estimation methods and production schemes[J]. Transactions of the ASABE, 2004, 47(6): 2051−2057 doi: 10.13031/2013.17802
[106]	巴士迪. 奶牛粪便堆肥过程温室气体和氨气排放规律及养分损失研究[D]. 北京: 中国农业科学院, 2020 BA S D. Greenhouse gas and ammonia emissions and nutrient losses from dairy manure composting[D]. Beijing: Chinese Academy of Agricultural Sciences, 2020
[107]	SOMMER S G, PETERSEN S O, SØGAARD H T. Greenhouse gas emission from stored livestock slurry[J]. Journal of Environmental Quality, 2000, 29(3): 744−751
[108]	HANSEN M N, SOMMER S G, HENRIKSEN K. Methane emissions from livestock manure — effects of storage conditions and climate[J]. Dias Report, 2002, 81: 45−53
[109]	张颂心. 中国农业碳排放量测算及影响因素分析-基于省级面板数据的研究[J]. 湖北农业科学, 2021, 60(1): 60−64,95 ZHANG S X. Calculation of agricultural carbon emission and analysis of influencing factors in China: Research based on the data of provincial panel[J]. Hubei Agricultural Sciences, 2021, 60(1): 60−64,95
[110]	李慧, 李玮, 姚西龙. 基于GWR模型的农业碳排放影响因素时空分异研究[J]. 科技管理研究, 2019, 39(18): 238−245 LI H, LI W, YAO X L. Study on spatial and temporal variation of impacting factors of agricultural carbon emissions based on the GWR model[J]. Science and Technology Management Research, 2019, 39(18): 238−245
[111]	黄琳庆, 赵聪, 蔡悦灵. 低碳视角下农业碳排放、农业科技进步与农业经济发展的实证研究——基于中国省域面板数据[J]. 江苏农业科学, 2016, 44(5): 541–544 HUANG L Q, ZHAO C, CAI Y L, An empirical study on agricultural carbon emissions, agricultural science and technology progress and agricultural economic development from a low carbon perspective —Based on provincial panel data in China[J]. Jiangsu Agricultural Sciences, 2016, 44(5): 541–544
[112]	胡中应, 胡浩. 产业集聚对我国农业碳排放的影响[J]. 山东社会科学, 2016(6): 135−139 HU Z Y, HU H. The impact of industrial agglomeration on agricultural carbon emissions in China[J]. Shandong Social Sciences, 2016(6): 135−139