中国省域农业源N2O排放清单及特征分析

doi:10.3969/j.issn.1004-1524.2019.11.18

浙江农业学报 ›› 2019, Vol. 31 ›› Issue (11): 1909-1917.DOI: 10.3969/j.issn.1004-1524.2019.11.18

中国省域农业源N₂O排放清单及特征分析

韦良焕, 林宁, 莫治新^*

喀什大学化学与环境科学学院,新疆生物质类固废资源化工程技术研究中心,新疆喀什 844006

收稿日期:2019-06-25 出版日期:2019-11-25 发布日期:2019-12-04
通讯作者: *,莫治新, E-mail: mzxzky@163.com
作者简介:韦良焕(1981—),女,陕西富平人,博士,副教授,研究方向为环境管理与经济。E-mail: weilianghuanabc@126.com
基金资助:
新疆维吾尔自治区自然科学基金(2017D01A11)

Inventory and characteristics of agricultural nitrous oxide emissions in China

WEI Lianghuan, LIN Ning, MO Zhixin^*

Xinjiang Biomass Solid Waste Resources Technology and Engineering Center, College of Chemistry and Environmental Science, Kashi University, Kashi 844006, China

Received:2019-06-25 Online:2019-11-25 Published:2019-12-04

摘要/Abstract

摘要： 对中国31个省(市、自治区)2000—2016年的农业源N₂O排放清单进行计算和分析。结果表明:中国(不含港、澳、台)农业源N₂O排放量从2000年的71.801 3×10⁴ t波动增加到2016年的95.354 9×10⁴ t,增幅为32.80%,年均增长1.79%,其中,农用地N₂O是农业源N₂O的主要来源,占农业源N₂O总排放量的63.47%~77.26%。省域农业源N₂O排放存在明显的区域差异性:广西、广东和云南的N₂O排放量最高,远高于北京、上海、天津等地。其中,农用地N₂O排放以广西最高,2016年为45.320 2×10⁴ t,西藏最少,2016年为0.005 3×10⁴ t。农用地N₂O排放以直接排放为主,所占比例为69%~87%。畜禽粪便管理N₂O排放以四川、河南、内蒙古、云南和山东最高,而上海、北京、天津、浙江、海南较少。

关键词: 农用地, 畜禽粪便, 温室气体

Abstract: In the present study, agricultural N₂O emissions inventory and characteristics of 31 provinces (municipalities, autonomous regions) were explored in 2000-2016 in China. It was shown that the agricultural N₂O emission in China (Hongkong, Macau, Taiwan excluded) increased from 71.801 3×10⁴ t in 2000 to 95.354 9×10⁴ t in 2016, with an increase of 32.80% and an average annual increase of 1.79%. The N₂O emission from agricultural land was the main source of agricultural N₂O emission, which accounted for 63.47%-77.26%. There were obvious regional differences for the agricultural N₂O emissions in 31 provinces (municipalities, autonomous regions). Guangxi, Guangdong and Yunnan showed the highest agricultural N₂O emission, which was higher than that in Beijing, Shanghai and Tianjin. The highest N₂O emission from agricultural land occurred in Guangxi, with an amount up to 45.320 2×10⁴ t in 2016, while the lowest N₂O emission from agricultural land occurred in Tibet, which was 0.005 3×10⁴ t. Besides, the direct emission accounted for 69%-87% in the case of N₂O emission from agricultural land. N₂O emission from livestock and poultry manure management was relatively high in Sichuan, Henan, Inner Mongolia, Yunnan and Shandong, while it was relatively low in Shanghai, Beijing, Tianjin, Zhejiang and Hainan.

Key words: farmland, livestock and poultry manure, greenhouse gas

中图分类号:

X511

韦良焕, 林宁, 莫治新. 中国省域农业源N₂O排放清单及特征分析[J]. 浙江农业学报, 2019, 31(11): 1909-1917.

WEI Lianghuan, LIN Ning, MO Zhixin. Inventory and characteristics of agricultural nitrous oxide emissions in China[J]. , 2019, 31(11): 1909-1917.

参考文献

[1] 魏民秀, 赵先贵. 1999—2011年鄂尔多斯市温室气体足迹动态分析[J]. 中国环境科学, 2014, 34(10): 2706-2713.
WEI M X, ZHAO X G.Dynamic changes of greenhouse footprint in Ordos City from 1999 to 2011[J]. China Environmental Science, 2014, 34(10): 2706-2713.(in Chinese with English abstract)
[2] 陈哲, 陈媛媛, 高霁, 等. 不同施肥措施对黄河上游灌区油葵田土壤N₂O排放的影响[J]. 应用生态学报, 2015, 26(1): 129-139.
CHEN Z, CHEN Y Y, GAO J, et al.Effects of different fertilization measures on N₂O emission in oil sunflower field in irrigation area of upper Yellow River[J]. Chinese Journal of Applied Ecology, 2015, 26(1): 129-139.(in Chinese with English abstract)
[3] RAVISHANKARA A R, DANIEL J S, PORTMANN R W.Nitrous oxide (N₂O): the dominant ozone-depleting substance emitted in the 21st Century[J]. Science, 2009, 326(5949): 123-125.
[4] 周涛, 王云鹏, 王芳, 等. 广东省农业氮足迹分析[J]. 中国环境科学, 2014, 34(9): 2430-2438.
ZHOU T, WANG Y P, WANG F, et al.Analysis of the nitrogen footprint of agriculture in Guangdong[J]. China Environmental Science, 2014, 34(9): 2430-2438. (in Chinese with English abstract)
[5] BARNARD R, LEADLEY P W, HUNGATE B A.Global change, nitrification, and denitrification: a review[J]. Global Biogeochemical Cycles, 2005, 19(1): 23-28.
[6] BABU Y J, LI C, FROLKING S, et al.Field validation of DNDC model for methane and nitrous oxide emissions from rice-based production systems of India[J]. Nutrient Cycling in Agroecosystems, 2006, 74(2): 157-174.
[7] 尹释玉. 农田N₂O排放研究进展[J]. 绿色科技, 2016(12): 152-154.
YIN S Y.The progress of study on N₂O emissions in cropland[J]. Journal of Green Science and Technology, 2016(12): 152-154.(in Chinese with English abstract)
[8] 尹高飞, 翟梦瑜, 苏帅, 等. 农田土壤氧化亚氮排放及其控制研究[J]. 河北农业科学, 2015, 19(3): 80-84
YIN G F, ZHAI M Y, SU S, et al. Study on emission and control of nitrous oxide from farmland soil[J]. Journal of Hebei Agricultural Sciences, 2015,19(3): 80-84.(in Chinese with English abstract)
[9] 汤勇华. 中国农田化学氮肥施用和生产中温室气体(N₂O、CO₂)减排潜力估算[D].南京: 南京农业大学, 2010.
TANG Y H.An estimate of green house gas (N₂O, CO₂) mitigation potential in nitrogenous fertilizer application and production in Chinese croplands[D]. Nanjing: Nanjing Agricultural University,2010.(in Chinese with English abstract)
[10] 营娜, 麻金继, 周丰, 等. 中国农田肥料N₂O直接和间接排放重新评估[J]. 环境科学学报, 2013, 33(10): 2828-2839.
YING N, MA J J, ZHOU F, et al.Re-quantification of the direct/indirect N₂O emissions from agricultural fertilizer in China[J]. Acta Scientiae Circumstantiae, 2013, 33(10): 2828-2839.(in Chinese with English abstract)
[11] 刘韵, 柳文丽, 朱波. 施肥方式对冬小麦-夏玉米轮作土壤N₂O排放的影响[J]. 土壤学报, 2016, 53(3): 735-745.
LIU Y, LIU W L, ZHU B.Effect of fertilization regime on soil N₂O emission from upland field under wheat-maize rotation system[J]. Acta Pedologica Sinica, 2016, 53(3): 735-745.(in Chinese with English abstract)
[12] 蒋光福, 张稳, 李昕, 等. 1980—2010年中国和印度农田化肥氮源氧化亚氮排放的比较[J]. 农业环境科学学报, 2016, 35(9): 1807-1815.
JIANG G F, ZHANG W, LI X, et al.Comparison of synthetic fertilizer N-induced direct nitrous oxide emissions from croplands between China and India during 1980-2010[J]. Journal of Agro-Environment Science, 2016, 35(9): 1807-1815.(in Chinese with English abstract)
[13] 张冉, 赵鑫, 濮超, 等. 中国农田秸秆还田土壤N₂O排放及其影响因素的Meta分析[J]. 农业工程学报, 2015, 31(22): 1-6.
ZHANG R, ZHAO X, PU C, et al.Meta-analysis on effects of residue retention on soil N₂O emissions and influence factors in China[J]. Transactions of the CSAE, 2015, 31(22): 1-6.(in Chinese with English abstract)
[14] 温慧洋, 焦燕, 杨铭德, 等. 不同盐碱程度土壤氧化亚氮(N₂O)排放途径的研究[J]. 农业环境科学学报, 2016, 35(10): 2026-2033.
WEN H Y, JIAO Y, YANG M D, et al.Studies on emission pathways of nitrous oxide from different salinization soils[J]. Journal of Agro-Environment Science, 2016, 35(10): 2026-2033.(in Chinese with English abstract)
[15] 张旭. 四川省和重庆市农田N₂O排放量估算[D].重庆: 西南大学, 2008.
ZHANG X.Estimation of N₂O emissions from cropland in Sichuan and Chongqing[D]. Chongqing: Southwest University, 2008. (in Chinese with English abstract)
[16] 吴宜珊. 宁夏回族自治区温室气体排放清单及核算研究[D].西安: 陕西师范大学,2013.
WU Y S.Greenhouse gas inventory and emission accounting of Ningxia Hui Autonomous Region[D]. Xi'an: Shaanxi Normal University, 2013. (in Chinese with English abstract)
[17] 郭树芳, 齐玉春, 尹飞虎, 等. 不同灌溉方式对华北平原冬小麦田土壤CO₂和N₂O排放通量的影响[J]. 环境科学, 2016, 37(5): 1880-1890.
GUO S F, QI Y C, YIN F H, et al.Effect of irrigation patterns on soil CO₂ and N₂O emissions from winter wheat field in North China Plain[J]. Environmental Science, 2016, 37(5): 1880-1890.(in Chinese with English abstract)
[18] 闫翠萍, 张玉铭, 胡春胜, 等. 不同耕作措施下小麦-玉米轮作农田温室气体交换及其综合增温潜势[J]. 中国生态农业学报, 2016, 24(6): 704-715.
YAN C P, ZHANG Y M, HU C S, et al.Greenhouse gas exchange and comprehensive global warming potential under different wheat-maize rotation patterns[J]. Chinese Journal of Eco-Agriculture, 2016, 24(6): 704-715.(in Chinese with English abstract)
[19] 张贺, 郭李萍, 谢立勇, 等. 不同管理措施对华北平原冬小麦田土壤CO₂和N₂O排放的影响研究[J]. 土壤通报, 2013, 44(3): 653-659.
ZHANG H, GUO L P, XIE L Y, et al.The effect of management practices on the emission of CO₂ and N₂O from the winter wheat field in North China Plain[J]. Chinese Journal of Soil Science, 2013, 44(3): 653-659.(in Chinese with English abstract)
[20] 薛建福, 濮超, 张冉, 等. 农作措施对中国稻田氧化亚氮排放影响的研究进展[J]. 农业工程学报, 2015, 31(11): 1-9.
XUE J F, PU C, ZHANG R, et al.Review on management-induced nitrous oxide emissions from paddy ecosystems[J]. Transactions of the CSAE, 2015, 31(11): 1-9.(in Chinese with English abstract)

中国省域农业源N₂O排放清单及特征分析

Inventory and characteristics of agricultural nitrous oxide emissions in China

RichHTML

PDF (PC)

可视化

摘要/Abstract

引用本文

使用本文

参考文献

相关文章 10

编辑推荐

Metrics

本文评价

[1]	吴承杰, 任兰天, 郝冰, 邵庆勤, 王泓, 陈峰, 代高峰, 梅世远, 张从军. 秸秆堆肥部分替代化肥配施硝化抑制剂对冬小麦温室气体排放的影响[J]. 浙江农业学报, 2020, 32(7): 1233-1240.
[2]	倪治华, 孙万春, 林辉, 钟杭, 朱伟锋, 陆若辉, 马军伟. 浙江省畜禽粪源有机肥质量安全风险与控制对策[J]. 浙江农业学报, 2020, 32(2): 299-307.
[3]	沈亚强, 陈龙骏, 金玉婷, 钱淑琼, 陈贵, 程旺大. 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.
[4]	陈红卫, 黄玲, 冯露, 李晓庆, 孟雨田, 代琳. 生物质炭基肥对农田土壤温室气体排放年际变化的影响[J]. 浙江农业学报, 2017, 29(6): 977-981.
[5]	王宏燕, 宋冰冰, 聂颖, 孙岩. 有机种植对盐碱土壤N₂O、CO₂排放通量的影响[J]. 浙江农业学报, 2016, 28(9): 1580-1587.
[6]	米松华1，黄祖辉2，*，朱奇彪1，黄河啸1，李宝值1 . 稻田温室气体减排成本收益分析[J]. 浙江农业学报, 2016, 28(4): 707-.
[7]	刘益曦1，胡春1，叶定池2，朱圣潮1，*. 基于GIS的珊溪库区畜禽废弃物污染风险评价与防治对策 [J]. 浙江农业学报, 2014, 26(6): 1602-.
[8]	郭冬生1，王文龙1,*，彭小兰2，龚群辉2. 湖南省畜禽粪便抗生素排放量估算与治理策略[J]. 浙江农业学报, 2014, 26(5): 1315-.
[9]	金国强1，徐攀峰1，方文英1，阮关海2，*，陈合云2，3，闫川2，3. 不同稻—麦栽培管理方式对稻季农田温室气体排放的影响[J]. 浙江农业学报, 2014, 26(4): 1015-.
[10]	郭冬生;彭小兰;龚群辉;夏维福. 畜禽粪便污染与治理利用方法研究进展[J]. , 2012, 24(6): 0-1170.