环境与生态

基于能源消费的江苏省土地利用碳排放与碳足迹

展开
  • 1. 南京大学地理与海洋科学学院,南京 210093;
    2. 华北水利水电学院资源与环境学院,郑州 450011
赵荣钦(1978-),男,河南孟津人,讲师,博士研究生。主要从事土地利用与碳偱环研究。E-mail:zhaorq234@163.com ;
黄贤金(1968-),男,江苏扬中人,教授,博导。主要从事资源经济与政策研究。E-mail:hxj369@nju.edu.cn

收稿日期: 2009-10-27

  修回日期: 2010-06-14

  网络出版日期: 2010-09-20

基金资助

国土资源部公益性行业科研专项经费项目(200811033);江苏省环保科技基金(2009037)

Carbon emission and carbon footprint of different land use types based on energy consumption of Jiangsu Province

Expand
  • 1. School of Geographic and Oceanographic Sciences, Nanjing University, Nanjing 210093, China;
    2. College of Resources and Environment,North China Institute of Water conservancy and Hydroelectric Power, Zhengzhou 450011, China

Received date: 2009-10-27

  Revised date: 2010-06-14

  Online published: 2010-09-20

摘要

采用2003~2007年江苏省能源消费和土地利用等数据,通过构建能源消费的碳排放模型,对江苏省5年来能源消费碳排放进行了核算,并通过土地利用类型和碳排放项目的对应,对不同土地利用方式的碳排放及碳足迹进行了定量分析。结论如下:(1)江苏省能源消费碳排放总量从2003年的8794.24万t上升到2007年的16329.85万t,涨幅达86%。其中,终端能源消费碳排放占53.6%。(2)江苏全省土地单位面积碳排放从2003年8.24t/hm2上升到2007年15.53 t/hm2,增幅为88.5%。其中,居民点及工矿用地单位面积碳排放最大,为95.62 t/hm2。(3)江苏全省能源消费碳足迹大于生产性土地的实际面积,由此造成的生态赤字达1351.285万hm2。(4)不同土地利用类型的碳足迹大小顺序为:居民点及工矿用地>交通用地>未利用地及特殊用地>农用地和水利用地,其中居民点及工矿用地的碳足迹高达10.89 hm2/ hm2。(5)江苏全省单位面积碳足迹也呈明显的扩大趋势,从2003年的0.938 hm2/ hm2上升到2007年的1.769 hm2/ hm2

本文引用格式

赵荣钦, 黄贤金 . 基于能源消费的江苏省土地利用碳排放与碳足迹[J]. 地理研究, 2010 , 29(9) : 1639 -1649 . DOI: 10.11821/yj2010090010

Abstract

The impact of anthropogenic activities on carbon cycle is fulfilled through land use change. It is helpful to study the impacts of land use change on carbon cycle through linking carbon emissions to different land use types. By using data of energy consumption and land use of Jiangsu province from 2003 to 2007, this paper estimated carbon emission by energy consumption through carbon emission model, and analyzed the carbon emission and carbon footprint of different land use types through linking carbon emission to different land use types. The conclusions can be drawn as follows.(1) Total carbon emission from energy consumption of Jiangsu province increased from 8792.24×104 t (2003) to 16329.85×104 t (2007) with an annual rate of 86%, of which carbon emission from terminal fossil energy use accounted for 53.6%. Because carbon emission from fossil energy use was the main reason for the increase of total carbon emission, developing clean energy and improving energy efficiency are the key methods to decreasing total carbon emission. (2) Per unit area carbon emission of Jiangsu increased from 8.24 t/hm2 (2003) to 15.53 t/hm2 (2007) with an annual rate of 88.5%, of which per unit area carbon emission from residential and industrial areas was the highest (95.62 t/hm2), indicating that dwelling districts and industrial parks were the regions that contributed carbon emission mostly. So, improving energy structure and improving energy efficiency of the above regions was crucial in carbon emission reduction. (3) Carbon footprint of energy consumption was greater than the area of ecological productive land, and the ecological deficit was 1351.28×104 hm2 in Jiangsu in 2007. It is indicated that the carbon absorption of terrestrial ecosystems of Jiangsu Province cannot compensate the carbon emission of energy use. So strengthening environmental protection and enhancing carbon sequestration rate could effectively decrease the carbon emission intensity. (4) The descending order of carbon footprint of different land use types was: residential and industrial area, transportation area, unused land and special use area, agricultural land and water conservancy area. So, adjusting the land use pattern and introducing carbon footprint and carbon emission reduction into land use planning is one of the effective methods to reduce regional carbon footprint. (5) Per unit area carbon footprint of Jiangsu increased from 0.938 hm2/hm2 (2003) to 1.769 hm2/hm2 (2007), which indicates that the carbon footprint of land use had been expanded since 2003.

参考文献


[1] Soytasa U, Sari R,Ewing B T. Energy consumption, income, and carbon emissions in the United States. Ecological Economics, 2007,(3-4)62:482~489.

[2] 齐玉春,董云社.中国能源领域温室气体排放现状及减排对策研究.地理科学,2004,24(5): 528~534.

[3] 张雷.中国一次能源消费的碳排放区域格局变化.地理研究,2006,25(1):1~9.

[4] 刘慧,成升魁,张雷.人类经济活动影响碳排放的国际研究动态.地理科学进展,2002, 21(5):420~429.

[5] 朱永彬,王铮,庞丽,等.基于经济模拟的中国能源消费与碳排放高峰预测.地理学报,2009,64(8):935~944.

[6] Schipper L, Murtishaw S, Khrushch M, et al. Carbon emissions from manufacturing energy use in 13 IEA countries:long-term trends through 1995,Energy Policy,2001,29(9):667~688.

[7] Casler S D, Rose A. Carbon dioxide emissions in the U.S. economy: A structural decomposition analysis. Environmental and Resource Economics, 1998,11(3-4): 349~363.

[8] 陈红敏.包含工业生产过程碳排放的产业部门隐含碳研究.中国人口·资源与环境,2009,19(3):25~30.

[9] IPCC. Land-use, land-use change and forestry. In: Watson R T, Noble I R, Bolin B, et al. A Special Report of the IPCC. Cambridge: Cambridge University Press, 2000.

[10] DeFries R S, Field C B, Fung I, et al. Combining satellite data and biogeochemical models to estimate global effects of human-induced land cover change on carbon emissions and primary productivity.Globle Biogeochemical Cycle, 1999, 13(3): 803~815.

[11] McGuire 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. Globle Biogeochem Cycle, 2001, 15(1): 183~206.

[12] 葛全胜,戴君虎,何凡能,等.过去300 年中国土地利用、土地覆被变化与碳循环研究.中国科学(D辑):地球科学,2008,38(2):197~210.

[13] Quay P D,Tilbrook B,Wong C S.Oceanic uptake of fossil fuel CO2:carbon-13 evidence.Science, 1992,256(5053):74~79.

[14] 陈广生,田汉勤.土地利用/覆盖变化对陆地生态系统碳循环的影响.植物生态学报,2007,31(2): 189~204.

[15] Wiedmann T, Minx J. A Definition of Carbon Footprint.2007. http://www.censa.org.uk/docs/ISA-UK_Report_07-01_carbon_footprint.pdf.

[16] Sovacool, B K,Brown M A.Twelve metropolitan carbon footprints: A preliminary comparative global assessment. Energy Policy,2010,38(9):4856~4869.

[17] Kenny T, Gray N F. Comparative performance of six carbon footprint models for use in Ireland. Environmental Impact Assessment Review,2009,29(1):1~6.

[18] 黄贤金,葛杨,叶堂林,等.循环经济学.南京:东南大学出版社,2009.147~159.

[19] 郭运功.特大城市温室气体排放量测算与排放特征分析——以上海为例.上海:华东师范大学硕士论文,2009.19~20.

[20] 赖力,黄贤金,刘伟良.基于投入产出技术的区域生态足迹调整分析——以2002年江苏为例.生态学报, 2006, 26(4) :1285~1292.

[21] IPCC.2006 IPCC Guidelines for National Greenhouse Gas Inventory,2006.

[22] 汪刚,冯霄.基于能量集成的 CO2减排量的确定.化工进展,2006, 25 (12): 1467~1470.

[23] 徐国泉,刘则渊,姜照华.中国碳排放的因素分解模型及实证分析:1995~2004.中国人口·资源与环境,2006,16(6):158~161.

[24] 谭丹,黄贤金.我国东、中、西部地区经济发展与碳排放的关联分析及比较.中国人口·资源与环境, 2008,18(3):54~57.

[25] 高树婷.我国温室气体排放量估测初探.环境科学研究,1994,7(6):56~59.

[26] 王雪娜.我国能源类碳源估算方法研究.北京:北京林业大学硕士毕业论文,2006,28.

[27] 何介南,康文星.湖南省化石燃料和工业过程碳排放的估算.中南林业科技大学学报,2008,28(5):52~58.

[28] ORNL. Estimate of CO2 emission from fossil fuel burning and cement manufacturing. ORNL/CDIAC-25. Carbon Dioxide Information Analysis Center, Oak Ridge National Laboratory, Oak Ridge,Tennessee, USA,1990.

[29] 李璞.低碳情景下建设用地结构优化研究——以江苏省为例.南京:南京大学硕士毕业论文,2009,27.

[30] 谢鸿宇,陈贤生,林凯荣,等.基于碳循环的化石能源及电力生态足迹.生态学报,2008,28(4):1729~1735.

[31] 李克让.土地利用变化和温室气体净排放与陆地生态系统碳循环.北京:气象出版社,2000,260.

[32] 赵荣钦,秦明周.中国沿海地区农田生态系统部分碳源/汇时空差异.生态与农村环境学报,2007,23(2):1~6,11.

文章导航

/