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Assessment of private economic benefits and positive environmental externalities of tea plantation in China
Authors:Hui Xue  Xiaoyi Ren  Shiyu Li  Xu Wu  Hao Cheng  Bin Xu  Baojing Gu  Guofu Yang  Changhui Peng  Ying Ge  Jie Chang
Institution:1. College of Life Sciences, Zhejiang University, 866 Yuhangtang Road, Hangzhou, 310058, Zhejiang Province, People’s Republic of China
2. International Colleges, Qingdao University, Qingdao, 266061, People’s Republic of China
3. Institute of Engineering Research, Yunnan University, 2 North Green Lake Road, Kunming, Yunnan, 650091, China
4. Institute of Tea, China Academy of Agricultural Science, Hangzhou, 310008, People’s Republic of China
5. Department of Public Administration, Zhejiang Gongshang University, Hangzhou, 310018, People’s Republic of China
6. Institut des sciences de l’environnement, Département des sciences biologiques, Université du Quebec à Montréal, Case postale 8888, Montreal, Canada
Abstract:Tea plantations are rapidly expanding in China and other countries in the tropical and subtropical zones, driven by relatively high private economic benefit. However, the impact of tea plantations on the regional environment, including ecosystem services and disservices are unclear. In this study, we developed an assessment framework for determining the private economic benefits and environmental externalities (the algebraic sum of the regulating services and disservices) of tea plantations in China. Our results showed that tea plantations provided private economic benefits of 5,652 yuan ha?1 year?1 (7.6 yuan?=?1 USD in 2007) for tea farmers, plus positive environmental externalities of 6,054 yuan ha?1 year?1 for the society. The environmental externalities were calculated as the sum of the value of four regulating services, including carbon sequestration (392 yuan ha?1 year?1); soil retention (72 yuan ha?1 year?1); soil fertility protection (3,189 yuan ha?1 year?1) and water conservation (2,685 yuan ha?1 year?1), and three disservices, including CO2 emission (?39 yuan ha?1 year?1), N2O emission (?137 yuan ha?1 year?1) and nonpoint source pollution (?108 yuan ha?1 year?1). Before the private optimal level, the positive environmental externalities can be maintained by private economic benefits; if a social optimal level is required, subsidies from government are necessary.
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