A Discrete-Continuous Choice Model of Climate Change Impacts on Energy* Erin T. Mansur Yale University School of Management and School of Forestry and Environmental Studies New Haven, CT erin.mansur@yale.edu Robert Mendelsohn Edwin Weyerhaeuser Davis Professor Yale University School of Forestry and Environmental Studies. New Haven, CT robert.mendelsohn@yale.edu Wendy Morrison Texas A&M University El Paso Agricultural Research Center El Paso, TX mmorrison@elp.rr.com January 2, 2005 * We would like to thank Arnulf Grübler, Nat Keohane, and Sheila Olmstead for helpful comments. This work was supported in part by a grant from the Department of Energy. Abstract This paper estimates a multinomial discrete-continuous fuel choice model of both households and firms in order to determine the sensitivity of national energy demand to climate change. We find that consumers switch from natural gas, oil, and other fuels to electricity as climate warms and that overall energy demand—especially electricity demand—increases. The model implies that warming will increase American energy expenditures, resulting in welfare damages that increase as temperatures rise. Increases in electricity expenditures for cooling are partially offset by reductions in expenditures on other fuels for heating. Given a five degree Celsius increase in temperature by 2100, we predict an annual welfare loss of $40 billion, borne primarily by residential customers. 1 Introduction While many have studied the impacts of energy consumption on climate change, few have examined how changing the climate is likely to impact the demand for energy. Energy has been identified as one of the more vulnerable economic sectors to climate change (McCarthy et al., 2001). This paper develops a multinomial discrete-continuous choice model of joint decisions regarding fuel choice and energy demand. We then apply this model to examine the interface between climate and energy demand. Although discrete-continuous modeling has been used to examine numerous consumption decisions, it has received relatively little attention in the energy literature. Further, whereas most consumption decisions involve only two choices, there are many choices of fuels, requiring a multinomial first stage choice. Using the methodology of Dubin and McFadden (1984), we estimate a multinomial logit model of fuel choice followed by fuel-specific conditional demand functions. In the specific case of energy, we find that there is another important distinction to make between houses that have access to natural gas (“pipeable”) and households that do not (“non-pipeable”). These two groups of households make very different fuel and energy choices. Climate warming is expected to affect the demand for space conditioning energy by reducing heating needs and increasing cooling needs. Using the estimated relationship between fuel choice and energy demand across current households and firms, we measure the climate sensitivity of both the fuel choice and conditional demand equations. The estimated model is then used to predict the US energy impacts of alternative future climate change scenarios. 1 Despite the widespread interest in global warming, few studies have calibrated the impact of climate on energy demand. Most energy-climate studies have focused on measuring energy use as a source of greenhouse gases (Metz et al., 2001), not as a potential impact of climate change (McCarthy et al., 2001). Most of the studies that do consider the impacts of climate on the energy sector rely mainly on expert opinion (Nordhaus, 1991; Cline, 1992), engineering models (Rosenthal et al., 1995) or case studies of electricity (Crocker, 1976; Linder et al., 1987; Smith and Tirpak, 1989). The few empirical studies that consider the entire energy sector use an aggregate expenditure model that examines all fuels without distinction (Morrison and Mendelsohn, 1999; Mendelsohn, 2001). Our study analyzes how climate change will alter consumers' fuel choice and subsequent consumption of energy. The study is based on a special data set that combines climate and energy information from individual residences and firms across the United States. The paper proceeds as follows. The discrete-continuous model is presented in Section 2. Section 3 presents the theory describing the welfare measurement of long run climate impacts on energy. Section 4 presents the empirical methodology and data. Section 5 presents the results of the empirical modeling on fuel choice and conditional demand. The estimated model is then used, in Section 6, to project the energy impacts for future climate scenarios. The paper concludes in Section 7 with a discussion of the energy model results and the welfare implications of climate change for the US energy sector. 2 2 Discrete-Continuous Choice Model of Energy Modeling techniques that explicitly consider the discrete and continuous components of consumer choice are found widely in the literature. Researchers have used this method to examine a wide range of topics including demand for transportation, housing, and water.1 For many consumer choices, total demand can be broken down into a discrete component involving choice over alternatives and a corresponding continuous component describing demand conditional on that choice. While energy demand includes a discrete fuel choice and a continuous choice of consumption level, this approach has received relatively little attention in the energy literature. Baughman and Joskow (1976) develop a model of fuel choice and energy consumption for electricity, natural gas, and oil in the commercial and residential sectors of the United States. Their study, however, does not account for potential interactions between fuel choice and consumption decisions. As noted by Heckman (1979), if the decisions are not independent, then the model will suffer from selection bias. For many consumer choice occasions, the error term in the choice equation is correlated with the error term in the continuous equation, requiring a selection correction estimation method. Dubin and McFadden (1984) (hereafter, DM) develop a methodology for estimating a discrete-continuous model in the polychotomous choice setting that accounts for section correction. DM apply their method to electricity demand and the choice of appliance holdings. More recently, Vaage (2000) examines household energy consumption using a discrete-continuous choice model using Norwegian data. 1 Several studies use this method to examine questions of transportation (see Abdelwahab and Sargious, 1992; Mannering and Winston, 1985; and Hensher and Milthorpe, 1987). Lee and Trost (1978) and King (1980) look at housing choices with this methodology. Other research examines food and drink (Pompelli and Heien, 1991; Haines, Guilkey, and Popkin, 1988), shopping (Barnard and Hensher, 1992), and water (Hewitt and Hanneman, 1995; Olmstead et al., 2004). 3 Households make discrete choices of which appliances to purchase and then how much energy to use conditional on these choices. He finds a large price elasticity in both modeling stages and substantial, observed household heterogeneity. Our paper uses the DM model to perform a comprehensive analysis of fuel choice and energy consumption in the residential and commercial energy sectors in the United States. The model tests how climate affects current energy decisions. We then use the model to forecast how climate change will affect both fuel choice and the level of energy consumption. 3 Welfare Impacts Of Climate Change In response to climate change, households and firms may alter: 1) fuel choice, 2) the quantity of fuel, 3) expenditures on building characteristics, and/or 4) interior comfort levels. For households, a measure of the welfare impacts of climate change on energy can be described as the change in income necessary to keep utility constant given climate change: ∂Y U *(T *, R*), ∂C (1) where Y is income, C is climate, U is utility, T is interior temperature, and R is an index of all other goods. Interior temperature is assumed to be a function of climate, energy use (Qf conditional on fuel choice f), and building characteristics (Z): T = T (C , Q f , Z ), where C is exogenous and Qf and Z are purchased inputs. 4 If people maintain optimal interior temperatures regardless of climate, there will be no loss of comfort from climate change. A survey of interior temperatures conducted across households in the winter revealed that households in all regions of the country maintained the same winter temperatures (EIA, 1993). If, with increased air conditioning penetration in the future, the same result holds for the summer, future households and firms will not alter their interior comfort in response to climate change. The welfare effect from climate change will simply be the change in expenditure required to maintain these desired temperatures.2 Increases (decreases) in energy and building expenditures will measure the welfare loss (gain) from climate change. The change in welfare (∆W) equals: ∆W = ∫ C0 C1 ∂Y ≅ Pq Q0 + Pz Z 0 −Pq Q1 − Pz Z1 , ∂C (2) where Pq and Pz are the prices of energy and building attributes, respectively, and subscripts 0 and 1 represent the baseline case and climate change scenario, respectively. As long as firms also hold interior temperatures constant, (2) applies to them as well. Although changes in both energy and building expenditures provide the desired measure of welfare change, only energy expenditure data and detailed data about building characteristics are available. We propose to estimate the long run impacts of climate change. We consequently do not control for building choices that are climate sensitive in our energy model. This will yield accurate long run measures of how energy will change as climate changes because it treats these building characteristics as endogenous. However, the approach will not capture the change in costs associated with changes in 2 To the extent that comfort levels fall or rise with warming, our measures of the impacts of climate change will be attenuated. 5 buildings. With changes such as cooling capacity, this will lead to an underestimate of the costs of warming. With changes such as insulation for winter, it will overestimate the costs of warming. In earlier analyses of energy expenditures, the analysis compared the energy costs associated with controlling for endogenous building characteristics (short run) and omitting them (long run). The analyses found that the energy expenditures did not change dramatically (Morrison and Mendelsohn, 1999; Mendelsohn, 2001). These results imply that the bias from omitting endogenous building characteristics is likely to be small. Because warming reduces heating costs but increases cooling costs, we expect that energy has a nonlinear relationship with climate. In very cold places, the heating effects will dominate and in hot places, the cooling effects will dominate. Somewhere between is a temperate climate that minimizes both heating and cooling. Climate, of course, is not a single dimension variable. In addition to annual mean temperatures, seasonal temperature distribution may also be important. In this study, we will distinguish between winter and summer temperatures. We will also explore the less important but still significant role of precipitation. In the discrete-continuous model, we define the welfare impacts of changes in climate as the change in the expected value of energy expenditures. The probability that a particular fuel portfolio, f ∈ F , is chosen is defined as θf. Expenditures are the product of prices Pq and the conditional demand Qf. 6 In this discrete-continuous situation, the estimate of the expected change in welfare corresponding to (2) is: ∆W ≅ Ε Pq Q f (C0 ) − Ε Pq Q f (C1 ) = ∑ θ f ∈F f (3) (C0 ) Pq Q f (C0 ) − θ f (C1 ) Pq Q f (C1 ) where E[·] identifies the expected value. Therefore, expenditures over all alternatives are defined as the sum of prices Pq times the conditional quantities Qf, weighted by the choice probabilities θf. The link between the model components determining θf and Qf is further described in Section 4. For most of the analysis, we assume that energy prices do not change as a result of climate change. Partially because we do not expect them to change very much and partially because it is very difficult to project how prices across fuels will actually change given our results.3 However, if energy prices do change, the welfare calculations are more complicated. One must estimate the consumer and producer welfare before and after the warming. Assuming a linear supply response, this will be equivalent to the estimate above with an additional term equal to one half of the change in price times the change in quantity for each fuel. So if energy supply is inelastic and warming increases summer (decreases winter) energy demand; prices will increase (decrease) and the welfare estimate of damages (benefits) will be slightly higher. We estimate the magnitude of this endogenous price effect in the sensitivity analysis. 3 The prices for electricity will rise while the prices of other fuels (used for heating) might decline. However, if the other fuels are used to produce electricity instead, then their prices will not decline. 7 One must estimate the consumer and producer welfare before and after the warming. The welfare effect will be approximately equivalent to (3) with an additional term equal to one half of the change in price times the change in quantity for each fuel: ∆W ≅ ∑ θ f ∈F f 1 (C0 ) Pq Q f (C0 ) − θ f (C1 ) Pq Q f (C1 ) − ( Pq* − Pq ) Q f (C1 ) − Q*f (C1 ) 2 ( ), (4) where Pq* and Q*f (C1 ) are the equilibrium price and quantity after climate change. The addition term captures the lost consumer surplus that results from the higher prices. So, if energy supply is not perfectly elastic and warming increases energy demand, both equilibrium prices and the welfare estimate of damages will increase. If energy demand falls, then prices will fall and the benefits will be even greater. We estimate the magnitude of the effect of endogenous prices on our welfare calculations in the sensitivity analysis of Section 6. 4 Empirical Methodology and Data 4.1 Empirical Methodology We model fuel choice and fuel consumption using a discrete-continuous model based on Dubin and McFadden (1984). This model is a generalization of Heckman's (1979) two-step selection model. The DM two-step estimation uses a multinomial logit model in the first stage to choose fuels and then estimates the conditional demand model for each fuel using ordinary least squares (OLS) with selection terms. Lee (1983) proposes an alternative polychotomous choice two-step selection model. Both the DM and the Lee models are widely used. 8 However, Schmertmann (1994) shows that the Lee model places substantial restrictions on the covariances between the continuous demand and selection choice models. Schmertmann further finds, using a Monte Carlo study, that the Lee model is significantly biased when this assumption is violated. Bourguignon, Fournier, and Gurgand (2004) (hereafter, BFG) support these findings with their own Monte Carlo study of these polychotomous choice two-step selection models. Both studies find the DM model to be more robust to various data generating processes. This section outlines our discrete-continuous DM model using the notation of BFG. We model energy consumption Qf for fuel choice f among F alternatives: Qf = x f β f + u f Q*f = z f γ f + η f , (5) f = 1...F (6) where all the variables xf and zf are exogenous, and the disturbance uf has the properties: E (u f | x, z ) = 0 and V (u f | x, z ) = σ 2f . Energy consumption Qf will be positive only when fuel f is chosen. This occurs if: Q*f > max(Q*j ). j≠ f (7) Hence, Q*f is a latent variable of fuel consumption. If the disturbance terms uf and (ηf)’s are independent, estimation of the parameters βf and γf is straightforward. When they are not independent, some correlation between the explanatory variables and the disturbance terms may be introduced into (5) and OLS βf estimates would be inconsistent. As noted by BFG, condition (7) is equivalent to z f γ f > ε f , where: 9 ε f = max(Q*j − η f ). (8) j≠ f Following McFadden (1973), we assume the (ηf)’s are i.i.d. with an extreme value type I distribution. This specification implies the multinomial logit model such that: θ f ≡ Pr( z f γ f > ε f ) = exp( z f γ f ) ∑ j =1 exp( z jγ j ) F (9) . The (γf)'s can be estimated by maximum likelihood. However, the estimation of the (βf)'s requires further assumptions. The DM model assumes the following linearity condition: E (u f | η1...η F ) = σ f ∑ j ≠ f rj (η j − E (η j )), with the correlations between uf and ηf summing to zero: (10) ∑ F r = 0 . With this j =1 j assumption, the conditional demand function for each fuel, as given in (5), can be written: θ j ln(θ j ) F Q f = x f β f + σ f ∑ j =1 rj + ln(θ f ) + w f , 1−θ j (11) where wf is an independent error term. This equation can be estimated using OLS. 4.2 Data The data come from the Department of Energy's Commercial Buildings Energy Consumption Survey (EIA, 1992) and Residential Energy Consumption Survey (EIA, 1993). These surveys provide detailed data on energy expenditures and consumption as well as demographics, and building characteristics. The data include several thousand buildings distributed in random clusters across the continental US and are weighted to 10 represent the true population of buildings. Data are available for the five major residential fuels: electricity, natural gas, fuel oil, liquid petroleum gas (LPG), and kerosene, as well as the four major commercial fuels: electricity, natural gas, fuel oil, and district heat. The original data do not disaggregate energy uses. Although space-conditioning energy is expected to be most sensitive to climate change, other commercial and residential energy uses may be affected. Hence, the model is estimated for fuel portfolio choice and consumption across all energy uses. The DOE data sets originally measured only degree-days as a proxy for climate. However, by definition, degree-days go to zero as one approaches an arbitrarily chosen temperature. For example, heating degree-days using 60°F as a base, assume that there would be no warming if temperatures rose above 60°F. We wish to test what temperature leads to the minimum expenditures, not assume it. Consequently, in cooperation with EIA, climate data from each county was merged with the DOE data sets. The climate data include average monthly temperature and precipitation for January, April, July, and October. The climate data were originally collected from the National Climatic Data Center as 30-year averages for 5,511 meteorological stations in the US. The data by meteorological station were interpolated to US counties using weighted regressions of all weather stations within 500 miles of each county (see Mendelsohn et al., 1994). A number of explanatory variables are expected to influence fuel choice and consumption. The variables used to predict residential and commercial fuel choice and consumption are described in Table A1 of the Appendix. In general, explanatory variables include climate, demographic and firmographic information, and building characteristics. The building characteristics are divided into climate sensitive and non- 11 sensitive categories. Non-climate sensitive building characteristics such as building size, type of occupancy, and building age are used to control for exogenous non-climatic factors that affect energy consumption. Climate sensitive characteristics affecting thermal efficiency include building material, conservation, the choice of heating and cooling equipment, and some aspects of the household structure. Recall that we are estimating the long run welfare impacts of climate change. Therefore, these characteristics are not included in our model as they are assumed to be endogenous in the long run. We divide residential customers into two groups: the pipeable and non-pipeable customers. The distinction between pipeable and non-pipeable households partially reflects a different set of choices since one group has gas and the other does not. However, it should be noted that pipeable households might also be systematically different in other respects as well. For example, these households may be more likely to be in a metropolitan area. When natural gas is available, households can choose electricity only, natural gas and electricity (“gas”), or fuel oil and electricity (“oil”). Of the 3,747 pipeable consumers, 82% opt for gas, 9% pick oil, and the rest choose electricity only. When gas is not available, they can choose electricity only, fuel oil and electricity, or other fuels (like LPG and kerosene) and electricity (“other”). Of the 1,283 non-pipeable consumers, 44% choose electricity only, 26% pick oil, and the rest opt for kerosene or LPG. Commercial customers are estimated jointly. Of the 5,605 firms, 55% opt for natural gas, 27% pick electricity only, 10% choose oil, and the rest use district heat (“other”). 12 Table 1 reports the actual expenditures for each customer class. For each fuel, expenditures equal the sum over all households of the fuel price, the household's demand of that fuel, and the population weight of the household (ωi). For N households: Expend f = ∑ i =1 Pqi Q fiωi . N (12) Based on our sample, of the $179 billion (in 1990 dollars) that the residential and commercial sectors spend on energy, 71% is for electricity. Furthermore, of the overall expenditures on electricity, 75% is by customers who use other fuels as well. Thus, even though a large portion of the sample is labeled “natural gas” consumers, most of the expenditures are on electricity. The share of total expenditures that is for either electricity or natural gas is over 90%. 5 Results In this section, we report our estimation results in four subsections and then examine the sensitivity of the national energy model to climate change. First we discuss the selection model results for the residential customers. We separately estimate those households that have access to natural gas and those who do not. Then the residential conditional demand models are explored for each fuel choice and each subgroup. Next the commercial selection model results are examined. We do not have information concerning whether firms have access to natural gas so all firms are estimated in one common multinomial model. Then the commercial conditional demand models' results are reported. Finally, we test the sensitivity of energy expenditures in the current economy to climate change. 13 5.1 Residential Fuel Choice Results The results of the multinomial logit fuel choice estimation for the residential sector are shown in Table 2. We report the γf coefficients from estimating the latent variable model, (6). For both pipeable and non-pipeable groups, the electricity alone portfolio is the base category where the normalization γ1=0 is imposed. The models fit the data relatively well. The pseudo-R2 is 0.39 for the pipeable households and is 0.41 for the others. Temperature and precipitation variables suggest that climate change will impact households’ choice of fuel. Many households in warmer regions rely on electricity alone since, on the cooling side, it is virtually the only option. On the heating side, it has a high marginal cost but a low fixed cost, making it desirable in moderate winters. The model results suggest that more households will prefer to move to electricity alone as temperatures warm. Given the nonlinearity of the choice model, Table 3 reports the marginal impacts of temperature and precipitation for January, July, and overall.4 For the pipeable households, greater January temperatures are likely to result in more households choosing natural gas instead of oil. A marginal increase in July temperatures increases households' probability of choosing electricity only but this effect is just weakly significant at the 10% level. Overall, the marginal impact of an increase in temperature is a reduction in 4 The marginal effects are calculated in the following manner: ∂ Pj ∂Cj = Pj [γ j − ∑ k ≠ j γ k ] (Green 1993, 666). Marginal effects are calculated at the sample mean of each independent variable. We assume independence of the linear and quadratic terms when estimating the standard errors of the marginal effects. A marginal increase in temperature is measured in degrees Celsius. A marginal increase in precipitation is measured in inches. 14 the probability of choosing oil of 0.4%. Greater precipitation is likely to result in fewer of the pipeable households selecting natural gas and more opting for electricity only. For the households that do not have access to natural gas, the marginal impact of temperature is substantially larger than for the pipeable households. A marginal increase in July temperatures results in a 3.5% reduction in the probability of selecting oil and a 5.1% increase in the probability of selecting electricity only. The overall temperature effects are similar. For these non-pipeable households, precipitation has a negligible impact. Table 2 also reports the coefficient estimates for the other factors including electricity and fuel prices, as well as a number of demographic and structural characteristics. The price variables significantly influence the choice probabilities. The own-price effects are negative while the cross price effects are positive, suggesting that the other options are substitutes. We also note that newer buildings, multi-unit buildings, and wood burning residents are more likely to select electricity only. Higher income households are less likely to choose kerosene or LPG. Larger homes select either gas or oil with greater frequency. Mobile homes tend to use gas or other fuels. 5.2 Residential Conditional Consumption Results Table 4 presents the results of the residential conditional consumption analysis for the climate and price variables. Because of nonlinearity of the climate variables, we report the marginal impact of temperature and precipitation at the sample mean of each variable. When natural gas is available, the marginal impact of a one degree Celsius increase in January temperatures, relative to a mean of zero, is a reduction in electricity 15 consumption of 3% for electricity only consumers (the impact is -0.028 on the natural log of kWh's consumed). Natural gas consumption falls 2% given a similar marginal increase. When July temperatures are increased one degree Celsius (relative to a mean of 24°C), electricity consumption increases substantially for all pipeable customers: electricity only customers increase their consumption 5%, gas customers increase their demand for electricity by 6%, and oil customers buy 15% more electricity. Consumption of natural gas falls 2% given a marginal increase in July temperatures, resulting in an overall reduction of 4%. A one-inch increase in monthly precipitation, relative to a means of 2.6 inches in January and 3.6 inches in July, results in more consumption by gas users of both electricity (7%) and of gas (2%). Of the non-pipeable customers, January temperatures reduce the consumption of oil by 6%. July temperatures increase electricity consumption for electricity only (4%) and oil (12%) customers, but decrease consumption for consumers of other fuels (4%). The overall impact of precipitation is insignificant at the 5% level for these customers. Overall, the climate variables are behaving as we expect with warmer summers increasing energy and warmer winters decreasing energy consumption. The own-price elasticities for electricity consumption range from -0.24 to -1.32 for the six customer groups. The own-price elasticities are -0.5 for natural gas consumption and -1.3 for the other fuel consumers based on the LPG price. For both the pipeable and non-pipeable oil consumers, the own price elasticities are 0.5. These positive oil price elasticities may reflect problems in collecting price data for oil. Consumers report expenditures and quantities of oil and prices are inferred for oil. It is 16 possible that consumers remember their last oil delivery rather than their monthly consumption rates. In general, the cross price fuel elasticities are positive. The other characteristics of the residence, household, and selection control variables are shown in the Appendix. We report all of the coefficient estimates for the pipeable (see Table A2) and non-pipeable (see Table A3) customers. In general, consumption is increasing in home size, income, and age of head of household. At least one selection term in half of the regressions is weakly significant at the 10% level. To interpret the coefficients, consider the following case. For households selecting gas, the coefficient on the electricity-only error term from the selection model is positive. This implies there is a positive correlation between the error in the conditional demand models for gas and the error in the choice of electricity only in the selection model. Households with a greater probability of selecting electricity only tend to consume more gas. 5.3 Commercial Fuel Choice Results Table 5 presents the results of the multinomial logit fuel choice model for the commercial sector. Here, all customers are modeled jointly. Electricity alone is the base category relative to selecting gas, oil, or other (here, other is district heat). The pseudo-R2 is 0.35. Many of the climate variables are significant, particularly for choosing oil. Table 6 reports the marginal effects of the temperature variables. Most of the climate impacts result from changes in July temperatures. A one-degree increase results in a 1.6% increase in the probability of selecting electricity only, while the probability of selecting 17 oil falls by 1.3%. Greater precipitation reduces the number of firms selecting gas and increases the number selecting electricity only or oil. Table 5 also reports the coefficient estimates for the other firm characteristics. The gas and district heat own-price effects are negative while the own price effect of oil selection is insignificant. Most of the cross price effects are positive. However, greater electricity and gas prices increase the probability of choosing district heat, suggesting these are complements relative to the other options. We also note that newer and smaller buildings are more likely to select electricity only. Multi-building facilities tend to choose electricity only and district heat. Commercial firms with alternative fuels not listed are more likely to select electricity only. Buildings with more establishments and more indoor parking tend to select electricity only. Finally, firms in metropolitan areas tend to select gas or district heat. 5.4 Commercial Conditional Consumption Results Table 7 presents the results of the commercial conditional consumption analysis for the climate and price variables. The marginal impact of a one degree Celsius increase in January temperatures is a reduction in electricity consumption of 3% for electricity only firms but an increase in electricity consumption of 2% for natural gas firms. The marginal effect also reduces gas consumption by 3% and oil demand a sizeable 12%. Marginal increases in July temperatures further reduce gas consumption an additional 3%. A one-inch increase in January and July precipitation results in more consumption of gas (6%) and of oil (40%). 18 Overall, firms are relatively sensitive to the prices of the fuels they consume. For electricity consumption, the own-price elasticities range from -1.01 to -1.98 for the four groups of firms. The own-price elasticities are relatively large in magnitude for natural gas, -1.8, and for oil, -3.6. In contrast, district heat consumption is inelastic, -0.3. District heat is characteristically used in non-profit institutions that have multiple buildings such as universities and hospitals.5 One explanation for the lack of observed price effects for district heat is that it is a difficult and costly task to change to another fuel. Another explanation is that the non-profits that dominate this fuel type are poor managers and fail to respond to prices by encouraging conservation. The cross price elasticities tend to be insignificant though gas and electricity seem to be complements. Table A4 reports the coefficients on the other covariates. The size of the building in square feet strongly influences consumption in all models as expected. The quantity demanded decreases with the age of the building, suggesting new buildings use more, not less, energy. Despite the fact that new buildings include more insulation, they also provide many services such as central air, computer facilities, and vending operations that could explain the higher energy expenditures. We also note that firms demand more fuel if their buildings are open for business more months of the year. Demand also increases if the firm has multi-building facilities. Metropolitan location has a strong positive influence on consumption for most fuel portfolios, identifying the potential for a heat island effect in cities. Firms with “alternative fuels” demand less of the selected fuel. Both the percentage of assembly activities and the percent of the building used as a warehouse or vacant space have a strong negative influence on consumption across 5 83% of commercial buildings that consume district heat are multi-complex facilities and 93% are in designated “urban” areas. In addition, the mean energy consumption in BTUs exceeds the mean of the sample by almost 3 times. 19 portfolios, probably due to lower space conditioning costs. Sample selection variables impact consumption of electricity and gas. For customers selecting electricity only, the greater the selection error for choosing gas the greater the electricity consumption while larger oil selection errors result in less demand. 5.5 Climate Sensitivity Measures In order to measure the sensitivity of current energy expenditures to climate, we explore what would happen to the current system with a small increase in warming and precipitation. For each class of residential customer, as determined by fuel choice and availability of natural gas, we calculate the predicted change in expenditures from climate change, using (12). We define the marginal impact of climate change to be a 1°C increase in temperature, which is approximately an 8% increase in average temperature, and a 7% increase in precipitation. The energy system is not particularly sensitive to precipitation so that most of the change will be due to warming. This allows us to determine the overall sensitivity of each customer class to climate changes holding all else constant. Given the complexity of the linkages between the variance-covariance matrices of the climate variable estimates in both stages, we measure the uncertainty over our predictions using a bootstrapping method. We create 1000 data sets by drawing, with replacement, from the original residential data. For each sample drawn, we calculate the discrete-continuous DM model and use the estimated coefficients to measure the changes in expenditures associated with climate change. In Table 8, we report the median, 5%, and 95% of the draws. With these last two measures, we construct the 90% confidence 20 interval. We then repeat the exercise for the commercial data. All expenditures are represented in 1990 dollars. The overall residential expenditures increase $2.0 billion with a 90% confidence interval of $1.1 to $2.7 billion. This is about a 2% change, suggesting a relatively small elasticity of approximately 0.25. Most of the impacts are in electricity expenditures (an average increase of $3.8 billion for all customers). This is partially offset by less consumption of oil and natural gas. Throughout the analysis, we note several interesting patterns. We consistently observe that consumers spend more on electricity because of greater needs for cooling but they spend less on other fuels that are primarily used for heating. Another consistent result is that the increases in expenditures associated with more cooling exceed the decreases in expenditures associated with less heating as the climate changes. Another interesting result is that pipeable and non-pipeable customers have very different responses to warming. The pipeable consumers are sensitive to climate change. In contrast, the energy expenditures of the non-pipeable consumers hardly change. Namely, the 90% confidence interval for the non-pipeable response (-0.1 to 1.0 billion) spans zero. In fact, the only significant impact for these customers is that the electricity only customers are expected to increase expenditures by $1.2 billion. In contrast, all of the energy expenditure responses to warming of the pipeable customers are significant at the 10% level. We also report the marginal sensitivity of the commercial expenditures to climate change in Table 8. Warming causes firms to spend more on electricity if it is their only fuel. When the firm relies on more than one fuel, there is no change in electricity 21 expenditures with warming. Commercial natural gas, oil, and district heat expenditures are predicted to fall with climate change. These climate change impacts cancel each other so there is little response from the commercial energy sector.6 6 Climate Change Simulation We use our discrete-continuous DM model estimates to simulate the impacts of climate change on energy expenditures under various future scenarios. The early literature on impacts focused on how climate might affect the current economy as shown in the exercise above. In practice, climate change will be occur far into the next century. In this section, we begin by introducing our base case scenarios for 2050 and 2100. For several climate change scenarios, we discuss how warming would impact these future economies. Then, we examine the robustness of our main findings to alternative economic assumptions regarding energy prices (including endogeneity), population growth, and economic growth. 6.1 Base Case Scenario of Climate Impacts Population in the United States is projected to grow annually by approximately 0.3% (IPCC, 1990). We assume similar growth of the number of firms. Based on historic averages, we model income per capita as continuing to grow at 2% per year. We assume that these changes are proportional across the country. We assume that the age distribution of the building stock will not change. 6 The median of the bootstrap draws reports a reduction in expenditures of 0.3 billion with a 90% confidence interval of -1.1 to 0.6 billion. 22 We also predict that fuel prices will increase over the next century. These changes are likely to occur due to expected reductions in fossil fuel supplies (Hotelling, 1931). In our base case scenario, we assume that oil, natural gas, and other fuel prices increase 50% by 2050. We assume that electricity prices will increase only 25% because of the presence of relatively plentiful coal and nuclear power. As oil and gas prices rise, we assume that synthetic gases and oils will be made from coal. This backstop technology is assumed to be abundant, so our prices do not change from 2050 to 2100. All of these changes will affect the fuel choice, conditional consumption, and the total expenditures of the forecasts. Given these baselines, we simulate how climate change may impact the economies of 2050 and 2100. The scenarios test the change in welfare with and without the climate changing given baseline conditions. For 2050, we test the impacts of changes in temperature of 1°C and 2°C with a 7% increase in precipitation. For 2100, we study increases of 2.5°C and 5°C with a 15% increase in precipitation. All of our climate change scenarios assume uniform climate change across the US. Current scientific evidence suggests that changes in climate are not likely to be uniform, and instead are expected to vary across regions, climate zones and countries. However, climate models do not agree on within-country variation and their results are difficult to compare. In contrast, the uniform scenarios for a country are a reasonable approximation of the expected climate effects (Williams et al., 1998) and they are easy to interpret. Table 9 reports our base case findings for the four climate scenarios. We focus on the changes in expenditures. We use our main coefficient estimates shown in Tables 2 to 23 7 to predict our expected change in expenditures from climate change, rather than the 1000 bootstrap estimates. In the 2050 low climate scenario of a one-degree change, residential expenditures are predicted to increase by $4 billion while commercial expenditures are not predicted to change. By doubling the climate impacts in 2050 (from a one to a two degree change), the expenditures more than double (increasing to $9 billion). For 2100, the low climate scenario of 2.5C predicts an increase in expenditures of $16 billion, most of which is attributable to residential consumers. Finally, given a five-degree increase in temperature and a 15% increase in precipitation, total expenditures are predicted to increase by $40 billion. Almost all of these expenditures, 93%, are attributed to residential consumption. In the next subsection, we test the sensitivity of our main findings to our key assumptions regarding the future economy. 6.2 Simulation Results and Sensitivity Analysis Our sensitivity analysis reveals the interaction between assumptions about the base case changes in energy and the impact of climate change. The analysis tests whether the results of the 2100 high climate case are sensitive to alternative assumptions. We begin by testing the importance of having endogenous energy prices in the welfare calculation. We also examine the impact of alternative assumptions about price changes, fuel availability, population growth, and rising income. Table 10 provides several sensitivity tests. The first row repeats our base case findings of $40 billion. Our first sensitivity analysis, shown in the second row, explores what difference it makes if energy prices are endogenous. Obviously, if the supply is 24 relatively elastic, then prices will change very little and there will be almost no additional effect. Namely, equations (3) and (4) would predict similar changes in welfare. In this scenario, we assume that the long run supply of every fuel type is unit elastic (the price elasticity equals 1.0).7 Overall demand for electricity will increase as a result of climate change.8 In this scenario, we assume that the first resources that power plants would use in order to meet this increase in demand would be any reductions in the quantities demanded of oil, natural gas, and other fuels associated with climate change. For each fuel, we convert the Btu’s of energy into electricity. We assume an efficiency rate of 40%, or equivalently, a “heat rate” of 8530 Btu/kWh. As consistent with our findings on total expenditures, the increase in electricity demand is greater than the reduction in energy from the other sources (converted into kWh’s). The increase in demand of electricity—net of the new supply from oil, gas, and other fuels’ reserves—will increase the market price for electricity. However, no other fuel prices will be impacted. We solve for the equilibrium electricity prices and quantities for all fuels iteratively. For a given percent increase in electricity prices, we measure the equilibrium quantities of all fuels. We then calculate the percent increase in net electricity demand. As we assume unit elastic supply, the equilibrium will exist when the two percent changes equate. In our model, electricity prices will increase by 9.65% if electricity supply is unit elastic. Using (4), the change in welfare approximately equals the $39.8 billion from the base case, plus one half times the change in average electricity prices 7 Note that these supply elasticities are for the residual residential and commercial US market only, ignoring international and industrial customers’ responses. 8 Table 8 shows that overall electricity expenditures increase for a marginal change in climate. In our base case, a temperature rise of 5°C in 2100 results in the total quantity of electricity demanded increasing by 34%. 25 ( ) ($0.0084 per kWh) times the reduction in consumption of electricity, Q f (C1 ) − Q*f (C1 ) . This reduction is the change in consumption that can be attributed to the price increase, given that temperatures have risen. For the residential consumers, electricity consumption decreases 87.3 billion kWh, implying an increase in welfare loss of $367 million. For commercial customers, consumption decreases 85.1 billion kWh and welfare falls $358 million. The overall additional impact of 0.72 billion that is due to the endogeneity of prices goes from $39.8 billion in the base case to $40.5 billion. The remaining sensitivity analyses are focused on changing baseline conditions. For example, we test the robustness of our main results with two exogenous price counterfactuals. First, we assume that all energy prices uniformly increase by 50%, including the electricity prices. Here, expenditures increase $44 billion. The second exogenous price case allows the prices to increase as in the base case but imposes that oil supplies, and synthetic oil substitutes, are exhausted. We set oil shares to zero and allow the other fuel shares to increase proportionally. This is consistent with the independence of irrelevant alternatives assumption made in multinomial logit models. Expenditures increase $55 billion as a result of climate change in this case. We then test the sensitivity of the welfare impacts to other characteristics of the economy. The fifth row is similar to the base case but we double the population growth rate. The change in expenditures is $54 billion, a 35% increase over the base case. The next row doubles the income per capita for residential customers relative to the base case. Welfare falls by $55 billion as a result of climate change. In the last row, we see that if 26 this substantial amount of climate change occurred in today’s economy, the change in expenditures would be only $17 billion, less than half of the effect seen in the base case.9 Overall, we conclude that the impacts of climate change on energy expenditures are quite sensitive to the assumptions of the future. Our base case simulation of the annual welfare loss associated with a 5°C increase in temperature for 2100 is approximately $40 billion. In contrast, our predictions that allow for different assumptions regarding changes in prices, population growth, and income growth range from $17 to $55 billion. 7 Conclusions This discrete-continuous model of the impact of climate change on fuel choice and energy expenditures provides valuable insights regarding the nature of climate change adjustment in the US energy sector. This is the first study to explicitly consider how climate change impacts fuel choice in each energy market. The model results indicate that the fuel choice component is an important aspect of the climate adjustment. Warming leads both firms and homes to move towards choosing only electricity to heat and cool. This fuel switch is sometimes more important than changes in the quantities of fuels chosen. The model projects that climate change will cause damages in the energy sector and especially in the residential energy sector. If warming is in the neighborhood of 2.5°C, these damages will be approximately $16 billion in 2100. With a 5°C warming, 9 Note that Tables 7 and 8 report the median of 1000 bootstrap draws while Table 10 is based on the initial sample only. Both methods provide consistent estimates of expenditures but need not be exactly equal. 27 residential energy damages are expected to rise to $37 billion with another $3 billion of damages in the commercial side. We find that these estimates are sensitive to assumptions about price changes, population growth, and economic growth. Our estimated impacts exceed those predicted by previous studies. Nordhaus (1991) and Cline (1992) predict electricity damages ranging from $2.4 billion to $11.2 billion and non-electric benefits ranging from $1.7 billion to $1.2 billion, respectively. Using an engineering methodology, Rosenthal et al. (1995) predict net benefits on the order of $5 billion. Morrison and Mendelsohn (1999) predict damages of $4 billion with a 2.5°C warming and $13 billion with a 5°C warming. Partly, our overall welfare impacts are more severe because our fuel specific model predicts large swings in fuel choice towards electricity as a result of warming. The explicit modeling of fuel choice allows for more accurate and more detailed insights into the effects of climate change on energy demand. The other major reason why our damage estimates are higher than the earlier literature is because we are projecting the impacts on a 2100 economy. Nordhaus, Cline, and Rosenthal all relied on a 1990 economy. 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Mendelsohn. 1998. “Evaluating GCM Output With Impact Models,” Climatic Change, 39: 111-133. 31 Table 1: Actual Energy Expenditures by Customer Type Residential Natural Gas is Available $5.8 Residential Natural Gas is Not Available $14.0 Residential Total Commercial Total $19.8 $12.1 Electricity Others $40.1 $11.0 $51.1 $43.6 Natural Gas $26.4 $26.4 $8.5 $3.9 $7.7 $1.6 $4.0 $4.0 Electricity Only Oil $3.8 LPG/Kerosene District Heat Total $3.9 $76.2 $32.9 $109.1 $69.6 Total expenditures are measured in billions of 1990 dollars. For a given fuel, expenditures equal the sum across households, or firms, of each consumer’s price times total annual consumption, weighted by the population weights for the sample. 32 33 We note significance by ** at the 1% level, * at the 5% level, and # at the 10% level. January temp January temp2 July temp July temp2 January precip January precip2 July precip July precip2 log elec. price log n. gas price log fuel oil price log lpg price log kero. price log building age log no. floors log age of head log home area log income log family size mobile home multi unit metropolitan burn wood constant Table 2: Selection Model for Residential Customers Natural Gas is Available Natural Gas is Not Available Gas Oil Oil Other 0.029 -0.238 ** -0.045 -0.004 -0.001 -0.009 * -0.002 -0.003 -0.092 # -0.197 -0.502** -0.131 # -0.012 -0.059 * -0.066** 0.010 -0.233 ** 0.042 -0.192 -0.061 # 0.014 0.034 -0.062 0.025 # -0.101 # -0.051 0.515** -0.052 -0.026 0.103 * -0.139* 0.014 3.500 ** 2.566 ** 3.327** 3.292** -2.471 ** 4.674 ** -0.317 -2.180 * 1.053 0.208 1.648** -2.747** 1.161 -2.819** 0.761 ** 2.103 ** 1.358** 0.523** -0.322 * 0.698 ** -0.283 -1.420 0.551 ** 0.784 * 0.544 0.273 0.431 ** 0.488 * 0.854** -0.146 0.007 -0.027 -0.122 -0.427** 0.633 ** 0.806 ** 0.268 0.571** 1.259 * -0.014 0.624 1.175** # -0.481 * -1.375 ** -0.755 -2.012** -0.109 -0.667 ** 0.116 -0.367 -0.677 ** -0.298 -0.705** -0.414* 2.582 -5.278 # -3.973 12.301** Table 3: Marginal Effects of Selection Model for Residential Customers Panel A: Natural Gas is Available January temp July temp Annual temp January precip July precip Annual precip Electricity -0.1% 0.3% # 0.2% 0.9% ** 0.3% 1.2% ** Gas 0.4%** -0.2% 0.2% Oil -0.3%** -0.1% -0.4%* -1.2%** -0.3% -1.5%** 0.3%* 0.0% 0.3% Panel B: Natural Gas is Not Available January temp July temp Annual temp January precip July precip Annual precip Electricity 0.4% 5.1% ** 5.6% ** 2.1% -2.1% 0.0% Oil -0.4% -3.5%* -3.9%** Other 0.0% -1.7% -1.7% -2.0% 5.5%** 3.5% -0.1% -3.4% # -3.5% We note significance by ** at the 1% level, * at the 5% level, and # at the 10% level. Marginal effects are calculated at the sample mean of each independent variable. We assume independents of the linear and quadratic terms when estimating the standard errors of the marginal effects. A marginal increase in temperature is measured in degrees Celsius. A marginal increase in precipitation is measured in inches. 34 Table 4: Marginal Climate Effects and Price Elasticity Estimates of the Conditional Demand Models for Residential Customers Panel A: Natural Gas is Available January temp July temp Annual temp Electricity consumption Only Gas Oil -0.028 ** 0.000 -0.041 0.045 ** 0.060** 0.153 * 0.017 0.060** 0.113 ** Other fuels Gas Oil -0.020** -0.029 -0.022** -0.048 -0.042** -0.077 January precip July precip Annual precip 0.043 # -0.004 0.039 -0.011 0.035** 0.024** log elec. price -0.759 ** log n. gas price log fuel oil price 0.036** 0.034** 0.070** 0.103 -0.043 0.060 -0.765** -0.929 ** 0.122* 0.217** -0.041 0.002 -0.038 0.274 # -0.511** 0.529 ** 0.487* Panel B: Natural Gas is Not Available January temp July temp Annual temp January precip July precip Annual precip log elec. price log fuel oil price log lpg price log kero. price Electricity consumption Only Oil Other -0.008 0.007 0.017 0.039 ** 0.122* -0.043 * 0.031 ** 0.129** -0.027 # 0.009 0.010 0.018 -0.244 ** Other fuels Oil Other -0.057* -0.018 0.102 -0.016 0.045 -0.034 -0.088 -0.064 -0.152 # -0.002 0.060 * 0.058 # -0.003 -0.018 -0.021 -1.324** -0.736 ** 0.125 0.369 0.522 -0.107 -0.131 -0.071 -0.053 -0.124 # 0.370 # -1.253** 0.805 Notes: Consumption in ln(kWh) for electricity, ln(therms) for natural gas, and ln(gallons) for oil and other fuels. Marginal increases are measured at the sample means. A marginal increase is measured in degrees Celsius for temperature and in inches for precipitation. We note significance by ** at the 1% level, * at the 5% level, and # at the 10% level. Regressions include quadratic functions of climate variables, log building age, log no. floors, log age of head, log home area, log income, log family size, mobile home, multi unit, metropolitan, burn wood, selection variables for each fuel not chosen, and a constant. 35 Oil -0.064 * 0.003 -0.391 ** -0.039 ** 0.499 ** -0.069 ** 0.277 ** -0.081 ** 0.385 * 0.497 ** 0.873 0.395 -1.995 ** 0.519 ** 0.410 ** 0.192 ** -0.771 ** 0.240 0.145 ** -0.021 ** 0.000 0.011 ** 0.005 -0.024 ** -0.011 ** -0.007 ** -5.206 ** 36 We note significance by ** at the 1% level, * at the 5% level, and # at the 10% level. The excluded percentage of space is for retail or service. January temp January temp2 July temp July temp2 January precip January precip2 July precip July precip2 log elec. price log n. gas price log fuel oil price log dist. heat price alt. fuel used log building age log no. floors log square feet multi-bldg facility metropolitan months open/year no. establishments % assembly % educational activities % food service activities % in-door parking % warehouse/vacant % office constant Gas 0.004 -0.001 -0.065 * -0.006 # 0.053 -0.019 ** -0.127 ** 0.017 0.476 ** -3.381 ** 2.709 ** 0.442 -2.530 ** 0.402 ** 0.001 0.199 ** -0.581 ** 0.561 ** 0.111 ** -0.008 * 0.000 0.003 # 0.010 ** -0.032 ** -0.013 ** -0.005 ** -3.454 ** Table 5: Selection Model for Commercial Customers Other -0.012 -0.006** -0.149** -0.007 -0.163* -0.001 0.000 -0.002 -0.501* -0.494** 2.908** -1.250** -3.376** 1.040** 1.086** 0.417** 1.800** 0.894** 0.030 -0.018** -0.001 0.004 # 0.002 -0.039** -0.018** -0.005** -8.882** Table 6: Marginal Effects of Selection Model for Commercial Customers January temp July temp Annual temp January precip July precip Annual precip Electricity 0.1% 1.6% ** 1.7% ** -1.0% 1.9% ** 0.9% Gas 0.2% 0.1% 0.3% -0.1% -3.7%** -3.8%** Oil -0.2% # -1.4%** -1.6%** Other -0.1% -0.3%* -0.3%* 1.7%** 1.6%** 3.4%** -0.6%** 0.2% -0.4% We note significance by ** at the 1% level, * at the 5% level, and # at the 10% level. Marginal effects are calculated at the sample mean of each independent variable. We assume independents of the linear and quadratic terms when estimating the standard errors of the marginal effects. A marginal increase in temperature is measured in degrees Celsius. A marginal increase in precipitation is measured in inches. 37 Table 7: Marginal Climate Effects and Price Elasticity Estimates of the Conditional Demand Models for Commercial Customers Panel A: Electricity consumption Only January temp -0.026 * July temp 0.046 # Annual temp 0.020 January precip July precip Annual precip 0.011 -0.050 # -0.039 log elec. price -1.982 ** log n. gas price log fuel oil price log dist. heat price Gas 0.020** -0.022 # -0.002 0.011 0.013 0.024 -1.683** Other 0.004 -0.010 -0.005 0.140 -0.130 # 0.009 0.057 0.011 0.068 -1.558 ** -1.009** -0.248* -0.638 # 0.126 Panel B: Consumption of other fuels Gas January temp -0.030 ** July temp -0.025 * Annual temp -0.055 ** January precip July precip Annual precip Oil -0.031 0.138 # 0.106 0.030 0.031 # 0.060 ** log elec. price -0.073 log n. gas price log fuel oil price log dist. heat price -1.816 ** Oil -0.118** 0.000 -0.117 # Other 0.020 -0.029 -0.010 0.312** 0.085 0.397** -0.009 0.013 0.004 0.090 0.017 -3.649** -0.259 * Notes: Consumption in ln(kWh) for electricity, ln(therms) for natural gas, ln(gallons) for oil, and ln(pounds of steam) for district heat. We note significance by ** at the 1% level, * at the 5% level, and # at the 10% level. Marginal increases are measured at the sample means. A marginal increase is measured in degrees Celsius for temperature and in inches for precipitation. Regressions include quadratic functions of climate variables, alt. fuel used, log building age, log no. floors, log square feet, multi-bldg facility, metropolitan, months open/year, no. establishments, selection variables for each fuel not chosen, and a constant. In addition, the regression includes shares of space for assembly, educational activities, food service activities, indoor parking, warehouse/vacant, and office. 38 Table 8: Sensitivity of Energy Expenditures to Climate Change (in billions of 1990 dollars) Electricity Only Electricity Others Natural Gas Oil Other* Total Residential Natural Gas is Available 0.8 Residential Natural Gas is Not Available 1.2 Commercial Total [0.5, 1.1] 14% [0.8, 1.6] 9% [0.8, 1.5] 9% 1.1 2.1 -0.3 -0.6 [1.7, 2.5] [-0.8, 0.2] [-1.3, 0.0] 5% -3% -1% -0.9 n/a -0.2 [-1.1, -0.7] [-0.4, -0.1] -3% -2% -0.5 -0.2 -0.3 [-0.8, -0.3] [-0.5, 0.0] [-0.4, -0.2] -13% -5% -19% n/a -0.1 -0.2 [-0.4, 0.1] [-0.4, 0.0] -3% -5% 1.5 0.5 -0.3 [1, 1.9] [-0.1, 1] [-1.1, 0.6] 2% 2% 0% Notes: The table reports the marginal impact of climate change: a one degree Celsius increase in all temperatures and a 7% increase in precipitation. We show the median change, 90% confidence interval of the change, and the percent change in expenditures. The statistics are calculated using a bootstrapping method with 1000 draws as described in the text. “Other” is LPG and kerosene for residential and district heat for commercial. 39 Table 9: Base Case Simulation of Welfare Loss Due to Climate Impacts (in billions of 1990 dollars) Scenarios Residential Commercial Total 2050 Low Climate 4.0 0.0 4.0 2050 High Climate 8.8 0.3 9.0 2100 Low Climate 15.5 0.5 16.0 2100 High Climate 37.1 2.7 39.8 Notes: For the 2050 and 2100 predictions, we assume that electricity prices will increase 25%, and that other fuel prices will increase 50%. We assume annual growth rates of 0.3% for population and 2% for income per capita. Simulations assume the 1990 distribution of building ages. For each year, a low and high range of temperature change is given. In 2050, the low and high estimates of change in degrees Celsius are 1 and 2. In 2100, the range is 2.5 and 5. For the 2050 simulations, precipitation increases 7%. For the 2100 simulations, precipitation increases 15%. 40 Table 10: Sensitivity Tests of Welfare Loss to Climate Change for the 2100 High Climate Case (in billions of 1990 dollars) Scenarios Residential Commercial Total Base case 37.1 2.7 39.8 Endogenous prices 37.5 3.1 40.5 Exogenous prices I 42.1 1.5 43.6 Exogenous prices II 39.2 16.2 55.4 Population growth 50.1 3.6 53.6 Income growth 52.1 2.7 54.7 Current economy 14.8 2.0 16.9 Notes: This table reports sensitivity analysis to the aggregate expenditure effects for the 2100 high climate change case from Table 9. In the base case, we assume that electricity prices will increase 25%, and that other fuel prices will increase 50%. We assume annual growth rates of 0.3% for population and 2% for income per capita. Temperature increases five degrees Celsius and precipitation increases 15%. As these changes are based on projections for 2100, we test the robustness of our findings to various changes that could occur by 2100. The endogenous price case allows for long run supply functions that are unit elastic. The first exogenous price case allows all prices to increase by 50%. The second exogenous case allows the prices to increase as in the base case but imposes that we will run out of oil. We force the oil shares to be zero and allow the other fuel shares to increase proportionally (as consistent with the independence of irrelevant alternatives assumption made in multinomial logit models). The population growth case increases the number of households and firms based on an annual growth rate of 0.6%. The income growth increases the income per capita assuming an annual growth rate of 4%. The current economy is assumes no change in population, income, or prices. All simulations assume the 1990 distribution of building ages. 41 APPENDIX Table A1: Data Definitions Panel A: Definitions of Independent Variables in Residential Regression Models Variable burn wood January temp January temp2 January precip July temp July temp2 July precip log age of head log elec. price log fuel oil price log kero. price log income log lpg price log nat. gas price log no. floors log family size log square feet log building age metropolitan mobile home more than 1 unit select gas Definition 1 if wood is burned as alternative heat source average January temperature(demeaned) – degrees C average January temperature(demeaned) squared average January precipitation(demeaned) – inches average July temperature(demeaned) – degrees C average July temperature(demeaned) squared average July precipitation(demeaned) – inches head householder age average electricity price average fuel oil price average kerosene price average household income for relevant income range average liquid petroleum gas price average natural gas price number of floors number of household members size of building in square feet age of building 1 if in a city (metropolitan statistical area) 1 if home is mobile type 1 if more than 1 unit sample selection variables for fuel type x Panel B: Additional Independent Variables in Commercial Regression Models Variable alt. fuel used log dist. heat price months open/year multi-bldg facility no. establishments % assembly % educational activities % food service activities % in-door parking % office space % retail/service % warehouse/vacant Definition 1 if alternate fuel is used average district heat price number of months open 1 if facility has multiple buildings number of establishments in building percent assembly operations percent non-refrigerated warehouse and vacant percent food service percent in-door parking garage percent office percent retail/services percent warehouse/vacant 42 Table A2: Conditional Demand for Residential Customers when Natural Gas is Available using the Dubin-McFadden Method Electricity consumption by fuel type Only January temp January temp2 July temp July temp2 January precip 2 January precip July precip July precip2 log elec. price log n. gas price log fuel oil price log building age log no. floors log age of head log home area log income log family size mobile home multi unit metropolitan burn wood select elec. select gas select oil constant Gas -0.029 ** 0.000 0.051 ** 0.006 ** Oil Consumption of other fuels Natural Gas -0.018** -0.002** -0.021** 0.001 -0.025 -0.003 -0.044 0.005 0.048 # 0.039 ** 0.109 -0.008 ** -0.005 ** -0.008 -0.003 0.035 ** -0.041 0.001 0.001 0.004 -0.759 ** -0.765 ** -0.929 ** -0.013 0.003* 0.029** -0.012** 0.217** -0.038 -0.004 -0.001 -0.008 0.274 # 0.122 * -0.511** # 0.105 -0.068 # 0.100 0.257 ** 0.108 ** 0.351 ** 0.057 -0.049 -0.022 0.051 0.000 -0.041 0.000 0.000 0.060 ** 0.164 * 0.001 0.011 Fuel Oil -0.077 ** 0.014 0.105 ** 0.257 ** 0.146 ** 0.299 ** -0.050 -0.177 ** -0.019 0.087 ** 0.138 # 0.160 # -0.103 -0.079 3.860 ** 3.287 ** 0.529 ** -0.095 0.079 -0.117 0.180 ** 0.076 * 0.317 ** -0.184 -0.369 ** -0.041 0.100 -0.043 0.015 5.000 ** 0.126** -0.219** 0.060* 0.323** 0.045** 0.184** 0.145** -0.008 0.062** -0.011 0.160* 0.033 3.394** 0.487* 0.072 -0.142* 0.159 # 0.355** 0.022 0.069 0.194 0.094 -0.027 -0.070 -0.004 0.074 3.207** We note significance by ** at the 1% level, * at the 5% level, and # at the 10% level. Consumption of electricity in ln(kWh), natural gas in ln(therms), and fuel oil in ln(gallons). 43 Table A3: Conditional Demand for Residential Customers when Natural Gas is Not Available using the Dubin-McFadden Method Electricity consumption by fuel type Only January temp January temp2 July temp July temp2 January precip Oil -0.007 0.010 0.000 -0.002 0.037** 0.139 * -0.002 0.017 # Other Fuel Oil # 0.018 -0.001 # -0.036 # 0.007* 0.006 -0.102 0.000 # January precip 0.020 -0.003 0.004 July precip 0.009 -0.040 0.058* July precip2 -0.001 0.048 * -0.005 log elec. price -0.244** -1.324 ** -0.736** log fuel oil price 0.369 2 log lpg price log kero. price log building age log no. floors log age of head log home area log income log family size mobile home multi unit metropolitan burn wood select elec. select oil select other constant 0.120** -0.188** 0.010 0.420** 0.087** 0.261** 0.314** -0.119 # -0.029 -0.182** 0.012 0.160 # 4.687** Consumption of other fuels -0.107 -0.131 -0.163 * 0.035 -0.115 -0.886 -0.076 -0.036 0.207 ** 0.329** 0.199 ** 0.129** 0.235 ** 0.309** -0.012 0.130 -0.064 0.208 0.073 0.272** 0.063 -0.069 # 0.406 -0.279 0.240 -0.204 3.238 ** 3.233** Other Fuels -0.050* -0.004* 0.123 0.020 # -0.019 0.001 -0.022 -0.005 -0.020 0.024 -0.023 -0.010 0.125 0.522 # -0.067 -0.006 -0.050 0.006 0.370 0.078 -0.251 -0.023 0.395** 0.052 -0.040 0.047 0.100 0.086 -0.092 0.113 -0.006 3.122** -1.253** 0.805 0.105 1.325 0.605** 0.054 0.088 0.174 0.187 0.740 -0.672** -0.490** 0.275 -0.044 2.862 # We note significance by ** at the 1% level, * at the 5% level, and # at the 10% level. Consumption of electricity in ln(kWh), fuel oil in ln(gallons), and other fuels in ln(gallons). 44 Table A4: Conditional Demand for Commercial Customers using the Dubin-McFadden Method Electricity consumption by fuel type Only Gas Oil Other January temp -0.033* 0.018 ** -0.038 0.005 2 January temp 0.002* 0.000 0.002 0.000 July temp 0.046 # -0.022 # 0.137 # -0.010 July temp2 0.000 0.004 # -0.004 0.000 January precip 0.016 0.023 0.155 0.065 January precip2 -0.006 -0.015 ** -0.020 -0.011 July precip -0.042 0.013 -0.130 # 0.005 July precip2 0.032** -0.001 -0.001 -0.027 log elec. price -1.982** -1.683 ** -1.558** -1.009** log n. gas price -0.248 * log fuel oil price -0.638 # log dist. heat price 0.126 # alt. fuel used -0.283 -0.199 -0.143 -0.143 log building age -0.162** -0.246 ** -0.169 -0.114 log no. floors 0.105 0.088 * 0.139 0.079 log square feet 0.719** 0.858 ** 0.885** 1.000** multi-bldg facility -0.037 0.101 # 0.196 0.143 metropolitan 0.559** 0.395 ** 0.460** 0.023 months open/year 0.029* 0.049 ** 0.135** 0.084** no. establishments 0.000 0.002 0.009 0.000 % assembly -0.005** -0.007 ** -0.011** -0.004* % educational activities 0.000 -0.004 ** -0.004* -0.006** % food service activities 0.005 # 0.010 ** 0.010** 0.005 % in-door parking -0.007** -0.008 * -0.003 -0.012 # % warehouse/vacant -0.011** -0.009 ** -0.004 -0.006* % office 0.004** 0.001 * 0.003 0.003* select elec. 0.220 -0.319 -0.388 select gas 0.337* -0.356 0.231 select oil -0.558* -0.184 -0.043 select other 0.020 -0.132 0.795 # constant -0.782* -1.075 ** -2.319 # -1.489 Consumption of other fuels Gas Oil Other -0.029** -0.126** 0.015 0.000 0.002 0.001 -0.025* -0.005 -0.028 0.004* -0.032** 0.005 0.036 0.323** -0.007 -0.009** -0.014 -0.002 # 0.033 0.080 0.008 0.009 -0.017 -0.023 -0.073 0.090 0.017 -1.816** -3.649** -0.259* -0.157 -0.907* -0.079 -0.049 # 0.424** -0.139 0.102* -0.088 -0.103 0.622** 0.599** 0.899** 0.163** 0.170 0.359 # 0.057 0.448** -0.288 0.010 -0.009 0.115** -0.005** 0.000 0.003 -0.003** -0.003 # -0.005** -0.001* 0.004* -0.004** 0.008** 0.003 -0.008 0.000 -0.003 0.001 -0.003** -0.004 -0.003 -0.003** -0.003 # -0.003* 0.605** -0.786 0.489 0.076 -0.119 -0.200 -0.280 -0.389* 0.587 1.432** -0.311 -1.375 We note significance by ** at the 1% level, * at the 5% level, and # at the 10% level. Shares are relative to percent retail or service. Consumption of electricity in ln(kWh) natural gas in ln(therms), fuel oil in ln(gallons), and other (district steam heat) in ln(pounds). 45