Abstract
The emerging notion of emissions inequality expands the idea of sustainability by incorporating economic opportunity as well as social needs and rights into environmental costs and benefits. In China, increasing inequality among urban households in terms of both income and housing wealth establishes a pattern of social stratification. An understanding of the association of social and environmental inequality is thus critical for urban sustainability. Based on the Chinese urban household survey from 2002 to 2009, this article employs the lifestyle approach to calculate and analyse the inequality of households by direct and indirect carbon emissions. The correlations among carbon emission inequality with income and housing wealth inequality are estimated with a Heckman procedure. We find that not only income distribution but also housing wealth distributionis an important consideration in understanding environmental inequality in China.
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Notes
EJ = 1018 Joules (J).
The Gini Index (Gastwirth 1972) is used in this test with the formula:
\({\text{GI}} = \left[ {\left( {2/N\mathop \sum \limits_{i = 1}^{N} y_{i} } \right)\mathop \sum \limits_{i = 1}^{N} i \cdot y_{i} } \right] - 1 - 1/N\)
where N represents the number of households in the sample, and \(y_{i}\) is the per household head income or housing wealth of each year, ordered by the per household head’s income or per household head’s housing wealth, respectively.
Head of the household refers to the individual in one family who is the representative of the family. In traditional China, normally the husband was the head of the household. Nowadays, the person who has the relatively higher income is likely to be the head of the family.
These include food, clothes, residence, housing facilities and services, medical care, transport and communication, education, cultural events and recreation, and miscellaneous goods and services.
Lambda can be expressed as
$$\lambda_{i} = \frac{{\phi \left( { - X_{2i} /\sigma_{2} } \right)}}{{\phi \left( {X_{2i} /\sigma_{2} } \right)}}$$where ϕ demonstrates the normal density function.
The consumer price index (CPI) was used as the deflator of the housing wealth and the disposable income, with the CPI of 2000 as the constant price.
The average disposable income of the top 10 % of urban Chinese households is 135,796 RMB in 2009.
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Appendices
Appendix 1: Coefficients of direct and indirect carbon emissions
Direct carbon emissions of households are calculated by the formula,
where \({\text{CE}}_{D}\) is direct carbon emissions, \(C_{{{\text{Coef}}_{D} }}\) is the carbon coefficient of each type of fuel, and \({\text{fuel}}_{D}\) refers to households’ indoor and outdoor direct energy consumption. The indoor direct energy includes electricity, coal, LPG and natural gas, and the outdoor direct energy is the vehicle fuel of gasoline. The data source and calculation formula of household direct carbon emissions is shown in Table 6.
The carbon coefficient of each type of fuel is calculated based on the IPCC (2006). The IPCC’s calculation of the coefficients follows a rigorous method with a comprehensive and transparent calculation process. To support the methodology used in obtaining carbon coefficients, the IPCC published ‘Good Practice Guidance and Uncertainty Management’, references for national calculations to prevent uncertainty and over- or under-estimations. The IPCC also considered regional variations by introducing regional differences in energy production into the calculation process. These coefficients are widely adopted in carbon emission research (Clarke-Sather et al. 2011; Wei et al. 2011) because of the high reliability of the data sources and the high applicability of the coefficients, and the IPCC (2006) is the most widely used by researchers in China.
Indirect carbon emissions of households are estimated based on the method from Wei et al. (2007). Indirect carbon emissions are calculated by the formula
where \({\text{CE}}_{I}\) refers to indirect carbon emissions, \(X_{I}\) refers to household consumption from the survey, and \(C_{{{\text{Coef}}_{I} }}\) is carbon intensity to proxy for the carbon coefficients of the eight major types of consumption. The eight-category classification of household consumption is the method used in the China Statistics Bureau, and this classification has been widely used in Chinese households’ carbon emissions (Wei et al. 2007; Zhang et al. 2011; Wang and Yang 2014). The data source and calculation formula of household indirect carbon emissions is shown in Table 7.
The carbon intensity is taken from the calculation of Wang and Yang (2014), estimated according to the method suggested by IPCC (2006) and Chinese households’ expenditure pattern. The specific method is to divide the sum of carbon emissions for the specific sectors by the sum of the value added of the sectors. Because improvements in technology lead to improvements in energy efficiency, the carbon intensity of each sector generally drops year by year. Residence, being the sector with the highest carbon intensity, reduces the most because of the increasing proportion of recycled materials adopted in industry. Clothing and miscellaneous goods and services only reduce a little because of the unchangeable production process with almost fixed carbon emissions.
Appendix 2: Robust tests: income, housing wealth and carbon emissions across three regions
As a robustness test, we estimated the correlation among income, housing wealth and carbon emissions across three regions: the eastern, central and western regions. Regional development in China presents significant differences in economy, income and housing wealth. The household survey found that the average housing wealth in the eastern area in 2002 was around 100,000 RMB, higher than that in the central and western areas, which averaged 50,000 RMB (China Statistical Yearbook 2003). The gap widened in 2009, with the housing wealth of each household in the eastern area being around 340,000 RMB and that of the western and central areas around 140,000 RMB (China Statistical Yearbook 2010). Annual disposable income of each household in the eastern area, which increased from 30,000 RMB to 60,000 RMB from 2002 to 2009, is also higher than that in the western and central areas, which increased from 19,000 RMB to 40,000 RMB (China Statistical Yearbook 2003–2010).
Housing wealth and income had significant effects in the regression across the three regions (Table 8). Consistent with what we found on the marginal effect of income and housing wealth on emissions, on average, we found the lowest marginal effect of income on direct carbon, the highest marginal effect of housing wealth on direct carbon and the highest marginal effect of both income and housing wealth on indirect carbon in the eastern region. The effects of inequality in housing and income on inequality of carbon emissions are highlighted.
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Yang, Z., Wu, S. & Cheung, H.Y. From income and housing wealth inequalities to emissions inequality: carbon emissions of households in China. J Hous and the Built Environ 32, 231–252 (2017). https://doi.org/10.1007/s10901-016-9510-9
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DOI: https://doi.org/10.1007/s10901-016-9510-9