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 | | Hilary Sigman | | Nonresident Fellow | |
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PROFILE | Hilary Sigman is a professor of economics at Rutgers University and a research associate of the National Bureau of Economic Research (NBER). She conducts research on the empirical effects of environmental policy.
Her current work, funded by grants from the National Science Foundation and the Environmental Protection Agency (EPA), focuses on the law and economics of brownfields, international water resources, and the environmental implications of decentralization of public policies. She has served on the Environmental Economics Advisory Committee of EPA’s Science Advisory Board and the Board of Directors of the Association of Environmental and Resource Economists.
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| Featured Publications | | The Effect of Allowing Pollution Offsets with Imperfect Enforcement | | Hilary Sigman, Howard F. Chang | | American Economic Review Papers and Proceedings | 101 | | | | Environmental Liability and Redevelopment of Old Industrial Land | | Hilary Sigman | | Journal of Law and Economics | 53 | 289–306 | | | | Economics of Hazardous Waste and Contaminated Land | | Hilary Sigman | | Cheltenham, UK: Edward Elgar | 2008 | | | | Transboundary Spillovers and Decentralization of Environmental Policies | | Hilary Sigman | | Journal of Environmental Economics and Management | 50 | 82–101 | | | | International Spillovers and Water Quality in Rivers: Do Countries Free Ride? | | Hilary Sigman | | American Economic Review | 92 | 1152–1159 | | | | View All Related Publications |
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DISCUSSION PAPERS | | The Incidence of Pollution Control Policies | | Ian W.H. Parry, Hilary Sigman, Margaret A. Walls, Roberton C. Williams III | | RFF Discussion Paper 05-24 | June 2005 | Abstract: This paper reviews theoretical and empirical literature on the household distribution of the costs and benefits of pollution control policies, and ways of integrating distributional issues into environmental cost–benefit analysis. Most studies find that policy costs fall disproportionately on poorer groups, though this is less pronounced when lifetime income is used, and policies affect prices of inputs used pervasively across the economy. The policy instrument itself is also critical; freely allocated emission permits may hurt the poor the most, as they transfer income to shareholders via scarcity rents created by higher prices, while emissions taxes offer opportunities for progressive revenue recycling. And although low-income households appear to bear a disproportionate share of environmental risks, policies that reduce risks are not always progressive, for example, they may alter property values in ways that benefit the wealthy. The review concludes by noting a number of areas where future research is badly needed. | | | | The Cost of Reducing Municipal Solid Waste | | Karen L. Palmer, Hilary Sigman, Margaret A. Walls | | RFF Discussion Paper 96-35 | September 1996 | | Related journal article | Abstract: This paper explores public policies for reduction of municipal solid waste. We parameterize a simple model of waste disposal using supply and demand elasticities from the economics literature and 1990 prices and quantities of recyclable and recycled materials. Using this model, we calculate the waste reduction in response to three public policies: (i) deposit/ refunds, (ii) advance disposal fees, and (iii) recycling subsidies. The results illustrate the effects of the three policies on source reduction and recycling of five recyclable materials that comprise 56 percent of municipal solid waste: aluminum, glass, paper, plastic, and steel. The calculated responses provide information about the cost of reducing municipal solid waste through various policies. This analysis suggests that a 7.5 percent reduction in disposal of the solid wastes in the model might have been optimal in 1990 from a benefit-cost perspective. | | | | The Cost of Reducing Municipal Solid Waste: Comparing Deposit-Refunds, Advance Disposal Fees, Recycling Subsidies, and Recycling Rate Standards | | Karen L. Palmer, Hilary Sigman, Margaret A. Walls, Ken Harrison, Steve Puller | | RFF Discussion Paper 95-33 | July 1995 | Abstract: A number of recent theoretical studies have shown that, in the presence of illegal disposal opportunities, an optimal policy for reducing solid waste is a combination of a final product tax and a recycling subsidyi.e., a deposit/refund system. A deposit/refund is equivalent to a charge on disposal: the deposit is refunded if the product is recycled, so the consumer only bears a cost if the product is discarded. As a result, the deposit/refund ensures that the least-cost method of reducing disposal is used, whether it be through source reduction or recycling. By contrast, other policies take advantage of only source reduction or only recycling as opportunities for waste reduction. This study provides empirical estimates of the costs of deposit/refunds, along with advance disposal fees (ADFs), recycling subsidies, and recycling rate standards. The estimates are generated through calibration of a simple two-equation model of the supply and demand for secondary materials and a mass balance condition describing waste disposal. The calibration is performed using supply and demand elasticity estimates from the extant economics literature and 1990 baseline prices and quantities of materials in the municipal solid waste stream. These empirical estimates have two kinds of policy implications. First, they allow a comparison of the relative costs of the different approaches. Although previous research has shown that the deposit/refund provides the best incentives, other policies may be more politically or administratively feasible. Our comparison of the relative costs of the policies will allow policy- makers to assess the trade-off between political and administrative considerations and the incentives the policies create. Second, the paper evaluates the absolute magnitude of the costs of waste reductions. Thus, these costs may be compared with the benefits of waste reduction to decide if any policy intervention is desirable, and if so, how much waste should be reduced. We find that, indeed, the deposit/refund is the least-cost approach. For a 10 percent reduction in waste disposal, the deposit/refund has a marginal cost of only $45 per ton of waste reduced. By comparison, the ADF at $85 per ton and the recycling subsidy at $98 per ton are almost twice as costly as the deposit/refund. Setting recycling rate standards to achieve a 10 percent reduction has a marginal cost of $61 per ton of waste reduced. The larger the desired percentage reduction in disposal, the greater the absolute divergence in costs between the deposit/refund and the other approaches. Even allowing for uncertainty in the elasticity estimates, through a Monte Carlo simulation approach, the deposit/refund is still found to be cheaper than the other three alternatives. A remaining concern, however, is the administrative costs of the deposit/refund. Existing estimates suggest that traditional "bottle-bill" states have high administrative costs--so high that the ADF, which is essentially a deposit without the refund, would appear to be cheaper. Estimates of the administrative costs of the more centralized California system, on the other hand, are low enough to make the deposit/refund still the preferred approach. Nonetheless, we feel that more research into administrative costs by material is needed. We find that a policy that requires a uniform percentage reduction in each material in the solid waste stream is substantially more costly than an approach where materials are allowed to be reduced in the least-cost fashion. A 10 percent reduction in each material in the solid waste stream, for example, would be achieved with a set of deposit/refunds that cost $70 per ton of waste reduced. We argue that the principal benefits of waste reduction are the avoided landfill disposal costs. In this case, we find that a deposit/refund of approximately $33 per ton would be optimali.e., would provide a reduction in waste disposal to the point where the marginal benefits of that reduction just equals the marginal costs. A $33 per ton deposit/refund yields about a 7.5 percent reduction in waste disposal for the wastes that we address in our model. We qualify this finding, however, by noting that our model is calibrated on 1990 data. There have been significant changes in recycling markets in the mid-1990sprices for many secondary materials have risen as demand for those materials has increased. As a result, further increases in demand (and reductions in waste disposal) could be more costly than predicted by our model. This would imply a smaller optimal reduction in disposal. Updating the data is a topic for future research. | | | |
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