Constraints relationship of wetland ecosystem services in Chongqing
GUAN Dong-jie1, ZHOU Li-lei2, LI Qiu-yan1, HU Shuai1, YUAN Xing-zhong3, YANG Hua4
1. College of Architecture and Urban Planning, Chongqing Jiaotong University, Chongqing 400074, China;
2. College of Resources and Environmental Science, Chongqing University, Chongqing 400044, China;
3. State Key Laboratory of Coal Mine Disaster Dynamics and Control, Chongqing University, Chongqing 400044, China;
4. Institute of Geography and Tourism, Chongqing Normal University, Chongqing 401331, China
Wetlands in Chongqing were picked up as cases to elucidate constraint relationship of ecosystem services. First, we calculated the services of water supply and conservation of water and soil at the year nodes of 2000, 2005, 2010 and 2015 by using the InVEST model. Then, the constraint relationship between the service of water supply and the service of conservation of water and soil was investigated. The results indicated that from 2000 to 2015, service of water supply was first declined from 395.41×104mm in 2000 to 238.89×104mm in 2010 and then increased to 286.36×104mm in 2015; meanwhile, the service of conservation of water and soil was increased from 85.74×106t in 2000 to 364.73×106t in 2015. Specifically, from 2000 to 2015, the total water supply for lake wetlands and paddy wetlands showed a first decreased and then increased trend, that for river wetlands and reservoir wetlands exhibited a converse trend, and that for swamp wetland showed a decreasing trend. Differently, from 2000 to 2015, the service of conservation of water and soil for lake wetlands, reservoir wetlands and paddy wetlands was first increased, and then decreased and again increased, that for river wetlands showed an increasing trend, and that for swamp wetland showed a first increased and then decreased trend. In addition, at the landscape level, there was a hump-shaped constraint effect between services of water supply and services of conservation of water and soil from 2000 to 2015; at the ecological level, from 2000 to 2015, there were double hump restraint, index constraint and hump-shaped constraint effect between these two kinds of services in the reservoir wetlands, the double hump restraint and hump-shaped constraint effect in the river wetland, and the hump-shaped constraint effect in the paddy wetland.
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