江西农业大学学报:社会科学版
江西農業大學學報:社會科學版
강서농업대학학보:사회과학판
Journal of Jianxi Agricultural University :Social Sciences Edition
2013年
2期
170~177
,共null页
土地利用 碳蓄积 碳排放 低碳优化对策
土地利用 碳蓄積 碳排放 低碳優化對策
토지이용 탄축적 탄배방 저탄우화대책
land use; carbon accumulation; carbon emission; low-carbon optimizing measures
土地利用/覆被变化通过改变生态系统的结构和功能,对全球碳排放产生深刻的影响。以南昌市为例,采用生态系统类型法确定土地生态系统的有机碳排放,2005年南昌市碳排放总量为4.826 2 Tg,2010年为5.535 9 Tg。期间南昌市土地利用变化碳排放量呈现增长的趋势,2010年比2005年增长0.709 7 Tg,年均增长0.141 9 Tg。其中耕地和牧草地的碳排放量在2005—2010年间减少,园地、建设用地表现为增加,水域和其他未利用地的碳吸收功能减弱。根据土地利用规划预测计算得出,2020年为6.697 7 Tg,比2005年增长1.871 5 Tg,年均增长0.141 9 Tg。由于用地结构的差异性,南昌市的碳排放量也有所不同。2005—2010年,全市各县区的碳排放依次以南昌县、新建县、进贤县和青山湖区最多,碳排放总量排名基本保持不变。结合土地利用结构变化和发展规划,南昌市应该采取适度退耕还林、还水、限制建设用地过度扩张、优化城市用地布局、灵活调节土地供应政策、构建碳交易法律体系等碳减排措施,达到土地利用规划与生态建设相结合的目标。
土地利用/覆被變化通過改變生態繫統的結構和功能,對全毬碳排放產生深刻的影響。以南昌市為例,採用生態繫統類型法確定土地生態繫統的有機碳排放,2005年南昌市碳排放總量為4.826 2 Tg,2010年為5.535 9 Tg。期間南昌市土地利用變化碳排放量呈現增長的趨勢,2010年比2005年增長0.709 7 Tg,年均增長0.141 9 Tg。其中耕地和牧草地的碳排放量在2005—2010年間減少,園地、建設用地錶現為增加,水域和其他未利用地的碳吸收功能減弱。根據土地利用規劃預測計算得齣,2020年為6.697 7 Tg,比2005年增長1.871 5 Tg,年均增長0.141 9 Tg。由于用地結構的差異性,南昌市的碳排放量也有所不同。2005—2010年,全市各縣區的碳排放依次以南昌縣、新建縣、進賢縣和青山湖區最多,碳排放總量排名基本保持不變。結閤土地利用結構變化和髮展規劃,南昌市應該採取適度退耕還林、還水、限製建設用地過度擴張、優化城市用地佈跼、靈活調節土地供應政策、構建碳交易法律體繫等碳減排措施,達到土地利用規劃與生態建設相結閤的目標。
토지이용/복피변화통과개변생태계통적결구화공능,대전구탄배방산생심각적영향。이남창시위례,채용생태계통류형법학정토지생태계통적유궤탄배방,2005년남창시탄배방총량위4.826 2 Tg,2010년위5.535 9 Tg。기간남창시토지이용변화탄배방량정현증장적추세,2010년비2005년증장0.709 7 Tg,년균증장0.141 9 Tg。기중경지화목초지적탄배방량재2005—2010년간감소,완지、건설용지표현위증가,수역화기타미이용지적탄흡수공능감약。근거토지이용규화예측계산득출,2020년위6.697 7 Tg,비2005년증장1.871 5 Tg,년균증장0.141 9 Tg。유우용지결구적차이성,남창시적탄배방량야유소불동。2005—2010년,전시각현구적탄배방의차이남창현、신건현、진현현화청산호구최다,탄배방총량배명기본보지불변。결합토지이용결구변화화발전규화,남창시응해채취괄도퇴경환림、환수、한제건설용지과도확장、우화성시용지포국、령활조절토지공응정책、구건탄교역법률체계등탄감배조시,체도토지이용규화여생태건설상결합적목표。
Changes in land use/cover have a profound impact on the global carbon emissions through changing ecosystem structure and function.Taking Nanchang for example,this paper,by using ecosystem types,determines carbon emissions of land ecosystems between 2005 and 2010.It finds that,in 2005 the carbon emission of Nanchang was 4.826 2 Tg,which was increased to 5.535 9 Tg in 2010,indicating a trend of growth among the years.The carbon emission increased by 0.709 7 Tg in 2010 compared to that in 2005,with an average annual growth 0.141 9 Tg.The carbon emissions of cultivated land and grassland was reduced from 2005 to 2010 while those in garden and construction land were increased.The carbon accumulation function of water and other unused land abated.According to the estimate of land use planning,in 2020 the carbon emission of Nanchang will reach 6.697 7 Tg,1.871 5 Tg more than that in 2005,with an average annual growth of 0.141 9 Tg.Due to the differences of land use structure,the carbon emission of Nanchang City was also different.In the period of 2005—2010,the ranking of counties’carbon emission was Nanchang County,Xinjian County,Jinxian County,Qingshanhu District,and the ranking of carbon emission remained unchanged.The carbon emissions in the southern part of Nanchang was the highest,of which the most prominent was Nanchang County.Combined with the land use structure and development plan of Nanchang,it is urgent that the city take such measures to reduce carbon emission reduction as returning farmland to forests or water,limiting excessive expansion of construction land,optimizing the layout of urban land use,adjusting the land supply policy,and establishing a legal system to regulate carbon trading so that the combined goals of land-use planning and ecological construction can be achieved.