Effects of Household Age and Size on the Elasticity of Energy Consumption Michael Dalton, U.S. National Oceanic and Atmospheric Administration, Seattle WA USA, +1 206 526 655, [email protected] Brian C. O'Neill, International Institute for Applied Systems Analysis, Laxenburg Austria, +43 2236 807 380, [email protected] Katarína Zigová, International Institute for Applied Systems Analysis, Laxenburg Austria, +43 2236 807 394, [email protected] Overview The contribution to climate change of emissions from the combustion of fossil fuels is a concern for scientists and policy makers. The energy-economic growth models used to project future energy demand and emissions usually assume that populations consist of a large number of identical (i.e. representative) households which consume a single good. These assumptions ignore potentially important differences in the composition of consumption among various households, which could affect projections of the aggregate demand for energy (Dalton et al. 2008). Household age and size appear to be the most important demographic factors to consider for energy demand in developed countries (Jiang and O'Neill 2007). In this paper, we present results from an econometric model that estimates substitution elasticities between energy-related (e.g. fuels, utilities) and other consumer goods using household level data from the U.S. Consumer Expenditure Survey (CEX) which are stratified by age and size. We find significant differences in substitution elasticities among these household types. Data and Methods Our econometric model is based on a system of demand equations that are derived from the constant elasticity of substitution (CES) utility function. The index i = 1,...,10 provides a reasonable number of household types. For simplicity, the model in this paper is restricted to 2-goods: energy-related and other. Thus there are 2 demand equations for each household type. The subscript e refers to the energy-related good, and n refers to the other good. Let e i and ni denote the share parameters in the CES utility function. Let denote the substitution parameter in each utility function such that i is the corresponding elasticity. The subscript t = 1,...,19 stands for time. Let p et and p nt represent the average prices in year t. One demand equation for each household is redundant because the two share equations add to unity. Let S nit denote the average share of non-energy related expenditures for households of type i in year t. By dropping equations for the energy-related good, we obtain a system with 10 equations. After adding an error term u it to each, the system takes the following stochastic form: i i = 1/ 1− ln S −nit1− 1 = i i −1 ln ni ei i i −1 ln pet p nt u it (1) For estimation and testing, we constructed time series of household expenditure shares for energy-related and other consumer goods from the U.S. CEX 1986-2004. The energy good comprises all fuels and household utilities. The U.S. Bureau of Labor Statistics provides consumer price indices that correspond directly to this definition. We stratified households in the CEX such that 4 size categories (1, 2, 3, 4+) are crossed with 4 age of the household head categories (15-24, 25-34, 35-64, 65+). Some eligible types are excluded due to under-representation at the extremes. The remaining 10 types are mutually exclusive and cover around 95% of all U.S. households. First, we used Zellner's seemingly unrelated regression (SURE) to estimate the simultaneous system of demand it ,∣ i∣ 1 , and the it are i.i.d. Next, equations in (1). Autocorrelation was not rejected. Thus we assumed that u it= i u it− 1 we used the four-stage Aitken method of Kmenta and Gilbert (1970) to estimate the system in (1) with autocorrelated disturbances. This method applies SURE twice. Residuals from the first round are used to estimate each i and then the Cochrane-Orcutt procedure is used to transform the system in (1) prior to the second round of estimation. Results Estimates of the substitution elasticity i range from 0.23 to 0.62 for the 10 household types. This parameter is significant for each type. A Wald test rejected the overall equality of the i at the 1% level, with a test statistic of F(9, 160) = 4.7. Point estimates of i imply that the goods are substitutes. Older households exhibit a greater elasticity of substitution between the goods, while younger households and larger households have lower values. The largest elasticity values belong to the old households (65+), regardless of their size; while the smallest values occur in cases with the household head in the 35-64 age group and at least 3 members in the household. In comparison, Goulder et al. (1999) use a value of = 0.85 for a representive household in the U.S., and Cremer et al. (2003) estimate a value of = 0.27 for a representative household in France. Conclusions Trends in population aging and shrinking household size will likely continue over the next 40-50 years in developed countries such as the U.S. Jiang and O’Neill (2007) project that the proportion of old households (65+) could reach as much as 25% of the U.S. population by 2050, while small households (one or two members) will peak around 2040 with 42% of the total U.S. population. These values compare with 12% and 35%, respectively, in 2000. Results from the econometric model in this paper imply that the elasticity of energy consumption is different for old and young households, as well as for small and large households. In future work, we intend to use these econometric results in the energy-economic growth model of Dalton et al. (2008) to gauge the effects of population aging and changes in household size on future energy demand and carbon emissions. References Cremer, H., F. Gahvari and N. Ladoux (2003). Environmental taxes with heterogeneous consumers: an application to energy consumption in France, Journal of Public Economics, 87, 2791-2815. Dalton, M., B. C. O'Neill, A. Prskawetz, L. Jiang, J. Pitkin (2008). Population aging and future carbon emissions in the United States. Energy Economics, 30, 642-675. Goulder, L.H., I.W.H. Parry, R.C. Williams and D. Burtraw (1999). The cost e ffectiveness of alternative instruments for environmental protection in a second-best setting, Journal of Public Economics, 72, 329360. Jiang, L. and B. C. O'Neill (2007). Impacts of demographic trends on US household size and structure, Population and Development Review, 33, 567-591. Kmenta, J. and R.F. Gilbert (1970). Estimation of seemingly unrelated regressions with autoregressive disturbances, Journal of the American Statistical Association, 65, 186-197.
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