Identifying ecological compensation areas for ecosystem services degradation on the Qinghai-Tibet Plateau

被引:2
|
作者
Liu, Hua [1 ]
Liu, Shiliang [1 ]
Wang, Fangfang [1 ]
Liu, Yixuan [1 ]
Liu, Yanxu [2 ]
Sun, Jian [3 ]
Mcconkey, Kim R. [4 ]
Tran, Lam-Son Phan [5 ,6 ]
Dong, Yuhong [7 ]
Yu, Lu [1 ]
Wang, Qingbo [1 ]
机构
[1] Beijing Normal Univ, Sch Environm, State Key Lab Water Environm Simulat, Beijing 100875, Peoples R China
[2] Beijing Normal Univ, Inst Land Surface Syst & Sustainable Dev, Fac Geog Sci, Beijing 100875, Peoples R China
[3] Chinese Acad Sci, Inst Tibetan Plateau Res, State Key Lab Earth Syst Resources & Environm Tibe, Beijing 100101, Peoples R China
[4] Univ Nottingham Malaysia, Sch Environm & Geog Sci, Jalan Broga, Kajang 43500, Selangor, Malaysia
[5] Duy Tan Univ, Inst Res & Dev, 03 Quang Trung, Da Nang, Vietnam
[6] Texas Tech Univ, Inst Genom Crop Abiot Stress Tolerance, Dept Plant & Soil Sci, Lubbock, TX 79409 USA
[7] Chinese Acad Forestry, Res Inst Forestry, Beijing 100091, Peoples R China
关键词
Ecological restoration; Pastoral area; Compensation area; Future scenarios; Qinghai-Tibet plateau; LAND-USE CHANGE; CLIMATE-CHANGE; TRADE-OFFS; COVER; RESTORATION; PROJECTIONS; MANAGEMENT; DYNAMICS; CHINA; CMIP6;
D O I
10.1016/j.jclepro.2023.138626
中图分类号
X [环境科学、安全科学];
学科分类号
08 ; 0830 ;
摘要
Ecological restoration is the most promising way to combat ecological degradation and improve ecological stability. However, it remains unclear at what scale ecological restoration is needed for the ecological degradation region related with ecosystem services under ongoing and future climate change. Based on that, this study assessed carbon sequestration (CS), water supply index (WSI), and mean species abundance (MSA) from 2000 to 2020 on the Qinghai-Tibet Plateau (QTP). Moreover, utilizing the Offset Portfolio Analyzer and Locator model to map and quantify the impacts of ecological degradation on CS, WSI, and MSA. Furthermore, this study explored the compensation area based on protection and restoration two compensation types under the shared socioeconomic pathway (SSP) and representative concentration pathway (RCP) scenarios between 2030 and 2060. The results showed that the spatial distribution of CS and WSI had a generally gradual declining trend, and MSA had an increasing trend from the southeast to the northwest. Ecological degradation of 1.21 x 10(6) ha has impacted 1.39 x 10(6) ha of terrestrial ecosystems on the QTP, and at least 7.47 x 10(6) ha of compensation area is needed. Regarding the protection scenario, the compensation area is mainly located in the western and northeastern parts of the QTP, with the highest CS of 8.05 x 10(5) Mg ha(-1) in the SSP1-RCP1.9 scenario and the highest WSI of 0.09 in the SSP4-RCP6.0 scenario. Regarding the restoration scenarios, SSP2-RCP4.5 showed a strong CS capacity with a value of 3.30 x 10(5) Mg ha(-1), while the SSP4-RCP6.0 scenario had an adequate water supply capacity with a WSI value of 0.61. Our findings indicate that a multifaceted assessment can determine the extent of ecological restoration required to mitigate different scales of degradation. This will help conservation managers develop more targeted sustainable management policies.
引用
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页数:12
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