Resources Science ›› 2020, Vol. 42 ›› Issue (4): 593-606.doi: 10.18402/resci.2020.04.01
PENG Hongsong1, GUO Lijia1, ZHANG Jinhe2, ZHONG Shien1(), YU Hu3, HAN Ya4
Received:
2019-07-03
Revised:
2019-10-21
Online:
2020-04-25
Published:
2020-06-25
Contact:
ZHONG Shien
E-mail:fgh1475@163.com
PENG Hongsong, GUO Lijia, ZHANG Jinhe, ZHONG Shien, YU Hu, HAN Ya. Research progress and implication of the relationship between regional economic growth and resource-environmental pressure[J].Resources Science, 2020, 42(4): 593-606.
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Table 1
Literature on Grainger causal relationship between regional economic growth and resource-environmental pressure"
作者 | 研究期 | 数据与方法 | 研究案例 | 基本结论 |
---|---|---|---|---|
Appiah[ | 1960—2015年 | 时间序列单位根、协整和格兰杰因果检验 | 加纳 | 真实GDP←能源消费 |
Alshehry等[ | 1980—2011年 | 时间序列单位根、协整和格兰杰因果检验 | 沙特阿拉伯 | GDP←能源消费、GDP?碳排 |
Cowan等[ | 1990—2010年 | 面板格兰杰因果检验 | 金砖国家 | GDP→耗电:南非;GDP?耗电:俄罗斯; GDP×耗电:中国、巴西、印度;GDP→碳排:南非;GDP←碳排:巴西;GDP?碳排:俄罗斯;GDP×碳排:印度、中国 |
Yoo等[ | 1975—2006年 | 时间序列单位根、协整和格兰杰因果检验 | 7个拉丁 美洲国家 | GDP←耗电:阿根廷、巴西、智利、哥伦比亚、厄瓜多尔;GDP?耗电:委内瑞拉; GDP×耗电:秘鲁 |
Chen等[ | 1971—2001年 | 时间序列单位根和格兰杰因果检验,面板单位根、协整和格兰杰因果检验 | 10个亚洲国家和地区 | GDP→耗电:印度、新加坡、马来西亚、菲律宾;GDP←耗电:香港;GDP×耗电:韩国、印度尼西亚、台湾、泰国;不明确:中国 |
彭新育等[ | 1990—2013年 | 时间序列单位根和格兰杰因果检验 | 中国广东省 | GDP←能源消费 |
陈桂月等[ | 1986—2009年 | 时间序列平稳性、协整和格兰杰因果检验 | 中国山西省 | GDP→工业废弃物排放 |
Table 2
Literature on environmental Kuznets curve (EKC) hypothesis between regional economic growth and resource-environmental pressure"
作者 | 研究期 | 数据与方法 | 研究案例 | 基本结论 |
---|---|---|---|---|
Xie等[ | 2015年 | 截面二次对数函数空间自回归模型 | 中国249个城市 | 人均GDP和PM2.5浓度呈倒U形关系,拐点为25336.47元 |
Bimonte等[ | 1980—2008年 | 面板二次对数函数回归模型 | 意大利20个地区 | 人均收入与人均土地消费呈倒U形关系 |
Zaman等[ | 2005—2013年 | 面板二次对数函数回归模型 | 亚太国家、欧盟与高收入OECD成员国、非OECD成员国3类集团 | 碳排量与人均GDP呈倒U形关系 |
Lee等[ | 2003—2010年 | 面板二次和三次函数固定效应模型 | 中国东、中、西、东北等4大地区 | 人均GDP和二氧化硫、废水排放呈倒U形或N形关系 |
Begum等[ | 1970—2009年 | 时间序列二次对数函数回归模型 | 马来西亚 | 人均GDP与人均碳排呈U形关系 |
张月等[ | 2002—2014年 | 面板三次对数函数回归模型 | 中国及中国8大地区 | 人均工业用水与人均GDP呈倒U形关系,各地区拐点因工业发展水平及经济状况而异 |
张宏等[ | 2009—2013年的60个月 | 时间序列三次对数函数回归模型 | 周庄、锦溪与千灯古镇 | 周庄的污水、粪便、垃圾排放量与人均旅游收入分别呈U形曲线、U形曲线、单调上升线性关系,锦溪分别是倒U形、N形、N形曲线,千灯则是单调上升线性、倒U形曲线、线性上升关系 |
Table 3
Comparison of decoupling analysis models between regional economic growth and resource-environmental pressure"
模型方法 | 基本理念与类型划分 | 优缺点 |
---|---|---|
OECD脱钩 指数模型 | 基本理念:单位GDP资源环境压力的下降率 类型划分:绝对脱钩、相对脱钩和未脱钩3类,相对脱钩与绝对脱钩的临界点即EKC拐点 | 优点:①容易理解;②对数据要求不高 缺点:①存在经济繁荣与衰退两种情境下的脱钩类型划分,具体细分也不详细,不利于直观判断脱钩的状态和程度;②指标敏感性较强,结果易受基期选择的影响发生波动;③未考虑总量变化 |
变化量综合 分析法 | 基本理念:经济增长与资源环境压力的弹性分析 类型划分:强脱钩、弱脱钩、衰退性脱钩、强复钩、弱复钩、扩张性复钩6类 | 优点:①综合考虑了总量变化与相对量变化;②克服了OECD脱钩指数模型在基期选择上的困境和脱钩类型难以识别的局限,更详细地反映了脱钩状态和程度;③容易理解;④数据要求不高 缺点:不能区分未脱钩与复钩的关系 |
Tapio脱钩 弹性模型 | 基本理念:经济增长与资源环境压力的弹性分析 类型划分:强脱钩、弱脱钩、衰退脱钩、强负脱钩、弱负脱钩、扩张负脱钩、增长连结、衰退连结8类 | 优点:①使用负脱钩的概念替换变化量综合分析法中的复钩,同时为避免过度解释脱钩弹性指数(DEI)的微小波动,将DEI=1±20%的变化仍视为未脱钩(连接);②容易理解;③数据要求不高 缺点:脱钩类型划分复杂,容易混淆 |
IGTX 模型 | 基本理念:基于IPAT方程的二者关系的定量表达 类型划分:绝对脱钩、相对脱钩与未脱钩3类 | 优点:指标易计算,结果更易识别 缺点:①很少使用,需要区分经济繁荣与衰退两种情境下的脱钩;②容易受到其他非环境因素的影响,研究周期越短,脱钩指数越易扭曲 |
计量分析 方法 | 基本理念:建模原理和思想与以上方法不同,除包含经济发展与资源环境的关系外,模型中还可涵盖城市化、工业化、家庭收入等解释变量 类型划分:无 | 优点:①方法更成熟,结果更精准;②函数方程形式多样 缺点:①数据质量要求高;②变量选取主观性强,难以进行横向比较研究 |
Table 4
Comparison of methods for measuring eco-efficiency between regional economic growth and resource-environmental pressure"
测度方法 | 方法亚类 | 优劣势与适用性 |
---|---|---|
单一 比值法 | ①产品/服务的价值(分子)与资源环境影响(分母)的比值 ②上述形式的倒数,类似于资源消耗和环境污染的强度指标 | 优点:①目前应用最广的测度方法,便于核算创造单位经济价值的资源环境成本,主要适用于研究单个项目或技术对象;②两种形式本质相同,物质流分析、能值分析、生命周期评价、生态足迹分析等方法,常用于测度产品/服务的价值或环境影响,也可归于此类 缺点:①环境影响指标涉及的范围比较有限,只能表征某一类环境影响;②未能提供生态效率最优值,难以指导实践 |
指标 体系法 | 熵权法 层次分析法 主成分分析法 模糊综合评价法 逼近理想解排序法 | 优点:构建包含经济和资源环境维度的指标体系,综合表征区域复合生态系统的发展水平和协调度 缺点:需使用赋权方法解决资源环境维度指标的集成问题,无论主观赋权还是客观赋权均有局限,并可能导致效率评价结果有偏 |
模型法 | 数据包络分析 | 优点:①能够处理多投入、多产出并分解综合效率;②无需事先假定方程、估计方程参数与赋权,最大限度地保留了数据的原始信息;③易于比较效率值 缺点:①将偏离生产前沿面即视为无效率,忽视了随机效应和测量误差,可能会高估无效率值;②有诸多技术细节易被忽视,如依据实际情况选择投入或产出导向,检验投入与产出变量的相关性,检验投入指标间、产出指标间的独立性,考虑决策单元的异质性,处置非期望产出及确保决策单元数是指标数的3倍等 |
随机前沿分析 | 优点:考虑了随机变量,并将与生产前沿的偏差分解为随机误差(白噪声)和无效率,克服了DEA高估无效率值的缺点 缺点:模型假设不当将直接导致结果有偏 |
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