nav emailalert searchbtn searchbox tablepage yinyongbenwen piczone journalimg journalInfo journalinfonormal searchdiv searchzone qikanlogo popupnotification paper paperNew
2018, 04, v.35;No.118 95-100
基于LMDI的中国SO2排放驱动因素分解
基金项目(Foundation): 国家科学基金规划项目(14BJY165);; 西南财经大学重大基础理论研究项目(JBK151122)资助
邮箱(Email):
DOI: 10.14096/j.cnki.cn34-1069/n/1004-4329(2018)04-095-06
摘要:

文章基于Kaya恒等式,运用LMDI方法将2006-2015年全国30个省市、自治区的SO2排放量分解为规模效应、能源强度效用、能源结构效应、产污系数效应四个因素,在此基础上,将SO2去除量变化分解为投资效率效应、经济结构效应和经济规模效应,分析投资等因素对SO2减排的贡献。研究结果表明:经济规模是导致SO2排放量增加最主要的因素,而产污系数则对SO2排放量的变化呈现最大的负向作用。针对SO2去除量的分解结果显示经济效应始终呈现正向效应,投资力度和效率则有所波动。

关键词: SO2; LMDI; 减排;
Abstract:

Using the LMDI method based on Kaya identities, the data of the country's sulfur dioxide emissions in 30 provinces from 2006 to 2015, is decomposed into scale effect, energy intensity, energy utility structure effect, production factor effect. On this basis, the change of sulfur dioxide removal is decomposed into investment efficiency effect, economic structure effect and economic scale effect, revealing their contribution to reduce the emissions. The results show that the economic scale is the most important factor for the increase of SO2 emissions, while the pollution coefficient has the greatest negative effect on the change of SO2 emission. The decomposition results of SO2 removal show that the economic effects are always positive, and the investment intensity and efficiency fluctuate.

参考文献

[1] YANG X, WANG S, ZHANG W Z, et al. Impacts of energy consumption,enenrgy struction,and treatment technology on SO2emissions:A multi-scale LMDI decomposition analysis in China[J]. Applied Energy,2016, 184:714-726.

[2] WANG Y, YING Q, HU J, et al. Spatial and temporal variations of six criteria air pollutants in 31 provincal capital cities in China during 2013-2014[J].Environment, 2014:413-422.

[3] HSU A.2016 environmental performance index[M].Yale University:New Haven, 2016.

[4] QU Y, AN J, HE Y, et al. An overview of emissions of SO2and NOxand the long-range transport of oxidized sulfur and nitrogen pollutants in East Asia[J]. Environ Sci-China, 2016:13-25.

[5] MING Z, SONG X, MINGIUAN M, et al.New energy bases and sustainable development in China[J].Renew Sustain Energy Rev, 2013:169-185.

[6] CHEN Y, AVRANHAM E, MICHEAL G, et al. Evidence on the impact of sustained exposure to air pollution on life expectancy from China’s Huai River policy[C]//Proceedings of the National Academy of Sciences of the United States of America, 2013, 12936-12941.

[7]陈仁杰,陈秉衡,阚海东.我国113个城市大气颗粒物污染的健康经济学评价[J].中国环境科学, 2010,30(3):410-415.

[8]杨冕,杨君甜.中国制造业SO2排放驱动因素分解研究[J].华东经济管理, 2017, 31(2):113-117.

[9]高彩玲,高歌,冯爱云.基于LMDI的中国SO2排放区域变化的因素分解[J].生态环境学报, 2012, 21(3):470-474.

[10]刘满芝,杨继贤,马丁,等.基于LMDI模型的中国主要大气污染物的空间差异及其影响因素分析[J].资源科学, 2015, 37(2):0333-0341.

[11] FUJII S M, SHINJI K. Decomposition analysis of air pollution abatement in China:Empirical study for ten industrial sectors from 1998 to 2009[J]. Journal of Cleaner Production, 2013, 59:22-31.

[12] HE J. What is the role of openness for China’s aggregate industrial SO2emission?:A structual analysis based on the Divisia decomposition method[J]. Ecological Economice, 2010, 69:868-886.

[13]夏艳清.我国工业能源消费及污染排放演变机理研究[J].软科学, 2011, 25(10):59-64.

[14]李荔,毕军,杨金田.我国SO2排放强度地区分解差异研究[J].中国人口.资源与环境, 2010, 20(3):34-38.

[15]程钰,徐成龙,刘雷,等.1991-2011年山东省工业经济增长的大气污染效应及其时空格局——以SO2和粉尘为例[J].地理科学进展, 2013(11):1703-1711.

基本信息:

DOI:10.14096/j.cnki.cn34-1069/n/1004-4329(2018)04-095-06

中图分类号:X701

引用信息:

[1]黄钢.基于LMDI的中国SO_2排放驱动因素分解[J].阜阳师范学院学报(自然科学版),2018,35(04):95-100.DOI:10.14096/j.cnki.cn34-1069/n/1004-4329(2018)04-095-06.

基金信息:

国家科学基金规划项目(14BJY165);; 西南财经大学重大基础理论研究项目(JBK151122)资助

发布时间:

2018-12-15

出版时间:

2018-12-15

检 索 高级检索

引用

GB/T 7714-2015 格式引文
MLA格式引文
APA格式引文