Taicang port (31°39’N, 121°12’E), located on the south bank of the Yangtze River in southeastern Jiangsu province, is adjacent to Shanghai city, 53 km from Shanghai business center and 46 km from Shanghai ...Taicang port (31°39’N, 121°12’E), located on the south bank of the Yangtze River in southeastern Jiangsu province, is adjacent to Shanghai city, 53 km from Shanghai business center and 46 km from Shanghai Hongqiao International Airport. With over 20 kmof deep-water front (water depth 】10 m) and only 100 km from the mouth of the Yangtze River, it is most favored for the development of ocean shipping. In ancient times, the port, known as Liujia port, was located on the mouth of the Liuhe, a smalltributary of the Yangtze River, east of the present port. During the Ming dynasty (1368-1644), it was an important trading port, famous in the Chinese history especially for the fact that the great Chinese navigator of the early Ming dynasty, Mr. Zheng He (late 14th to early展开更多
The Environmental Kuznets Curve(EKC) model was applied to investigate the relationship between economic growth and water environment quality based on panel data of Taicang during 2010–2017. The typical inversed-U sha...The Environmental Kuznets Curve(EKC) model was applied to investigate the relationship between economic growth and water environment quality based on panel data of Taicang during 2010–2017. The typical inversed-U shaped relationship has been obtained between GDP(gross domestic product) and indicators of ammonia, total nitrogen(TN) and total phosphorus(TP), respectively. The EKC turning point appeared when the GDP per capita was around US$2270, which was much lower than those in some developed countries(US$11,200). However, the decoupling between chemical oxygen demand(COD) and GDP per capita occurred even before this period, which should be attributed to the strict COD emission regulation being implemented since 2010. Further, analysis based on the Tapio decoupling coefficient elasticity model analyzed the ammonia nitrogen and economic development of each industry. We found that the agriculture no-point was strong decoupling in 2011–2014, then came to Recessive decoupling. The domestic wastewater had been in a strong decoupling state;Both urban non-point and industry experienced expansive negative decoupling, due to strict policy that prioritizes the environment over development and the investment in improvement of environment and techniques, both of them gradually came to strong decoupling. The result demonstrated that the EKC turning point could be appear in earlier economic stage and the decoupling coefficient elasticity could be improved through taking strong regulation measures.展开更多
文摘Taicang port (31°39’N, 121°12’E), located on the south bank of the Yangtze River in southeastern Jiangsu province, is adjacent to Shanghai city, 53 km from Shanghai business center and 46 km from Shanghai Hongqiao International Airport. With over 20 kmof deep-water front (water depth 】10 m) and only 100 km from the mouth of the Yangtze River, it is most favored for the development of ocean shipping. In ancient times, the port, known as Liujia port, was located on the mouth of the Liuhe, a smalltributary of the Yangtze River, east of the present port. During the Ming dynasty (1368-1644), it was an important trading port, famous in the Chinese history especially for the fact that the great Chinese navigator of the early Ming dynasty, Mr. Zheng He (late 14th to early
基金supported by water pollution control and treatment of the National Major Science and Technology project (No. 2017ZX07106003-002-001)。
文摘The Environmental Kuznets Curve(EKC) model was applied to investigate the relationship between economic growth and water environment quality based on panel data of Taicang during 2010–2017. The typical inversed-U shaped relationship has been obtained between GDP(gross domestic product) and indicators of ammonia, total nitrogen(TN) and total phosphorus(TP), respectively. The EKC turning point appeared when the GDP per capita was around US$2270, which was much lower than those in some developed countries(US$11,200). However, the decoupling between chemical oxygen demand(COD) and GDP per capita occurred even before this period, which should be attributed to the strict COD emission regulation being implemented since 2010. Further, analysis based on the Tapio decoupling coefficient elasticity model analyzed the ammonia nitrogen and economic development of each industry. We found that the agriculture no-point was strong decoupling in 2011–2014, then came to Recessive decoupling. The domestic wastewater had been in a strong decoupling state;Both urban non-point and industry experienced expansive negative decoupling, due to strict policy that prioritizes the environment over development and the investment in improvement of environment and techniques, both of them gradually came to strong decoupling. The result demonstrated that the EKC turning point could be appear in earlier economic stage and the decoupling coefficient elasticity could be improved through taking strong regulation measures.
文摘以江苏太仓作为研究区域,基于生态系统服务评估确定生态源地,采用最小累积阻力模型(MCR)和重力模型构建生态廊道,提出生态网络优化模式和对应管控策略。经计算和分析,提取面积30365.46 hm 2的重要生态功能区作为生态源地;识别生态源地161.46 km 2,其中水域生态源50个、陆域生态源地47个;提取水域生态廊道53条、陆域生态廊道56条,且水域生态廊道相较于陆域生态廊道更为完善,连通性和稳定性更高;识别需优先保护的生态夹点25个,优先修复的生态障碍点18个。研究成果可为系统性开展国土空间生态保护修复提供借鉴和指导。
