50 results match your criteria: "National Center for Environmental Economics.[Affiliation]"
Environ Res
March 2019
National Center for Environmental Economics, Office of Policy, US Environmental Protection Agency, 1200 Pennsylvania Ave. NW, Washington, D.C. 20460, USA.
Preterm birth (PTB) is a predictor of infant mortality and later-life morbidity. Despite recent declines, PTB rates remain high in the United States. Growing research suggests a possible relationship between a mother's exposure to common air pollutants, including fine particulate matter (PM), and PTB of her baby.
View Article and Find Full Text PDFEnviron Resour Econ (Dordr)
January 2018
U.S. EPA, Office of Water, Washington, DC, USA.
Empir Econ
January 2018
U.S. EPA National Center for Environmental Economics, 1200 Pennsylvania Ave NW, MC 1809T, Washington, DC 20460.
Like many agricultural commodities, fish and shellfish are highly perishable and producers cannot easily adjust supply in the short run to respond to changes in demand. In these cases it is more appropriate to conduct welfare analysis using inverse demand models that take quantities as given and allow prices to adjust to clear the market. One challenge faced by economists conducting demand analysis is how to limit the number of commodities in the analysis while accounting for the relevant substitutability and complementarity among goods.
View Article and Find Full Text PDFEnviron Resour Econ (Dordr)
January 2018
U.S. EPA, Office of Water.
Analysts often extrapolate estimates of the value of environmental improvements reported in prior studies to evaluate new policy proposals, a practice sometimes referred to as "benefit transfer." Benefit transfer functions are frequently specified based on statistical considerations alone. However, such a purely statistical approach can lead to willingness-to-pay functions that fail to satisfy some aspects of theoretical consistency that may be especially important for policy evaluations.
View Article and Find Full Text PDFJ Environ Econ Manage
January 2018
Landcare Research, New Zealand.
Incomplete information can lead households to underprice environmental disamenities in the housing market. To bound true implicit prices, researchers sometimes turn to high-profile cases involving significant media and community attention. However, prior research also finds that high-profile cases can lead to "stigma" effects that may confound interpretation of implicit prices.
View Article and Find Full Text PDFEnviron Int
May 2017
University of California San Francisco, Program on Reproductive Health and the Environment, CA, USA.
Environ Int
January 2018
University of California San Francisco, Program on Reproductive Health and the Environment, Oakland, CA, USA.
Background: There are reports of developmental and reproductive health effects associated with the widely used biocide triclosan.
Objective: Apply the Navigation Guide systematic review methodology to answer the question: Does exposure to triclosan have adverse effects on human development or reproduction?
Methods: We applied the first 3 steps of the Navigation Guide methodology: 1) Specify a study question, 2) Select the evidence, and 3) Rate quality and strength of the evidence. We developed a protocol, conducted a comprehensive search of the literature, and identified relevant studies using pre-specified criteria.
Risk Anal
March 2015
National Center for Environmental Economics, US Environmental Protection Agency, Washington, DC, USA.
Hedonic models are a common nonmarket valuation technique, but, in practice, results can be affected by omitted variables and whether homebuyers respond to the assumed environmental measure. We undertake an alternative stated preference approach that circumvents these issues. We examine how homeowners in the United Kingdom and Italy value mortality risk reductions by asking them to choose among hypothetical variants of their home that differ in terms of mortality risks from air pollution and price.
View Article and Find Full Text PDFEnviron Health Perspect
October 2014
Oak Ridge Institute for Science and Education (ORISE) Postdoctoral Fellow, National Center for Environmental Economics, Office of Policy, U.S. Environmental Protection Agency, Washington, DC, USA.
Background: The Navigation Guide is a novel systematic review method to synthesize scientific evidence and reach strength of evidence conclusions for environmental health decision making.
Objective: Our aim was to integrate scientific findings from human and nonhuman studies to determine the overall strength of evidence for the question "Does developmental exposure to perfluorooctanoic acid (PFOA) affect fetal growth in humans?"
Methods: We developed and applied prespecified criteria to systematically and transparently a) rate the quality of the scientific evidence as "high," "moderate," or "low"; b) rate the strength of the human and nonhuman evidence separately as "sufficient," "limited," "moderate," or "evidence of lack of toxicity"; and c) integrate the strength of the human and nonhuman evidence ratings into a strength of the evidence conclusion.
Results: We identified 18 epidemiology studies and 21 animal toxicology studies relevant to our study question.
Environ Health Perspect
October 2014
Oak Ridge Institute for Science and Education (ORISE) Postdoctoral Fellow, National Center for Environmental Economics, Office of Policy, U.S. Environmental Protection Agency, Washington, DC, USA.
Background: In contrast to current methods of expert-based narrative review, the Navigation Guide is a systematic and transparent method for synthesizing environmental health research from multiple evidence streams. The Navigation Guide was developed to effectively and efficiently translate the available scientific evidence into timely prevention-oriented action.
Objectives: We applied the Navigation Guide systematic review method to answer the question "Does fetal developmental exposure to perfluorooctanoic acid (PFOA) or its salts affect fetal growth in animals ?" and to rate the strength of the experimental animal evidence.
Mar Biol
August 2012
Woods Hole Oceanographic Institution, Woods Hole, MA USA.
Ocean acidification is increasingly recognized as a component of global change that could have a wide range of impacts on marine organisms, the ecosystems they live in, and the goods and services they provide humankind. Assessment of these potential socio-economic impacts requires integrated efforts between biologists, chemists, oceanographers, economists and social scientists. But because ocean acidification is a new research area, significant knowledge gaps are preventing economists from estimating its welfare impacts.
View Article and Find Full Text PDFRisk Anal
May 2012
U.S. EPA, National Center for Environmental Economics, 1301 Constitution Ave NW, Washington, DC 20460, USA.
Int J Environ Res Public Health
May 2011
National Center for Environmental Economics, US Environmental Protection Agency, 1200 Pennsylvania Ave, NW, MC 1809T, Washington, DC 20460, USA.
Economists have long been interested in measuring distributional impacts of policy interventions. As environmental justice (EJ) emerged as an ethical issue in the 1970s, the academic literature has provided statistical analyses of the incidence and causes of various environmental outcomes as they relate to race, income, and other demographic variables. In the context of regulatory impacts, however, there is a lack of consensus regarding what information is relevant for EJ analysis, and how best to present it.
View Article and Find Full Text PDFEcol Appl
October 2009
U.S. Environmental Protection Agency, National Center for Environmental Economics, Washington, DC 20460, USA.
In recent years a large literature on reserve site selection (RSS) has developed at the interface between ecology, operations research, and environmental economics. Reserve site selection models use numerical optimization techniques to select sites for a network of nature reserves for protecting biodiversity. In this paper, we develop a population viability analysis (PVA) model for salmon and incorporate it into an RSS framework for prioritizing conservation activities in upstream watersheds.
View Article and Find Full Text PDFJ Environ Manage
August 2009
U.S. Environmental Protection Agency, National Center for Environmental Economics, 1200 Pennsylvania Avenue, NW (MC 1809T), Washington, DC 20460, United States.
The choice of survey mode in contingent valuation research has long been debated in the literature. However, there is limited evidence as to how mode impacts behavior. Using an identical survey administered with telephone, mail, and in-person interviews, this is the first research to examine mode effects using all three commonly employed modes in contingent valuation research.
View Article and Find Full Text PDFChemosphere
March 2008
National Center for Environmental Economics, Office of Policy, Economics and Innovation, United States Environmental Protection Agency, 1200 Pennsylvania Avenue, N.W., EPA West 4339-M, MC 1809T, Washington, DC 20460, USA.
Managers of human biosolids have been incorporating the practice of waste pelletization for use as fertilizer since the mid 1920s, and waste pelletization has recently been embraced by some poultry producers as a way to move nutrients away from saturated agricultural land. However, the presence of arsenic in pelletized poultry house waste (PPHW) resulting from the use of organoarsenical antimicrobial drugs in poultry production raises concerns regarding additional incremental population exposures. Arsenic concentrations were determined in PPHW and pelletized biosolids fertilizer (PBF) samples.
View Article and Find Full Text PDFEcol Appl
March 2007
U.S. Environmental Protection Agency, National Center for Environmental Economics, Washington, D.C. 20046, USA.
A wide variety of environmental stresses can cause density-independent mortality in species populations. One example is cooling-water withdrawals, which kill or injure many aquatic organisms near power plants and other industrial facilities. In the United States alone, hundreds of facilities withdraw trillions of gallons from inland and coastal waters every year to cool turbines and other manufacturing equipment.
View Article and Find Full Text PDFEnviron Sci Technol
April 2007
U.S. EPA, National Center for Environmental Economics, 1200 Pennsylvania Avenue Northwest, Washington, DC, USA.
Trillions of gallons are withdrawn every year from U.S. rivers, estuaries, lakes, and coastal waters to cool the turbines of power plants and other equipment in manufacturing facilities.
View Article and Find Full Text PDFEnviron Health
May 2006
US Environmental Protection Agency, Public Health and Environmental Policy Team, National Center for Environmental Economics, 75 Hawthorne St, MC PPA-1 San Francisco, CA 94105, USA.
Background: Residential-use pesticides have been shown to be a major source of pesticide exposure to people in the United States. However, little is understood about the exposures to household pesticides and the resultant health effects. One reason that little is known about home-use pesticide exposure is the lack of comprehensive data on exposures to pesticides in the home.
View Article and Find Full Text PDFAccid Anal Prev
January 2005
US EPA -- National Center for Environmental Economics, 1200 Pennsylvania Ave., N.W., MC 1809T, Washington, DC 20460, USA.
This paper examines the relationship between traffic fatality risk and per capita income and uses it to forecast traffic fatalities by geographic region. Equations for the road death rate (fatalities/population) and its components--the rate of motorization (vehicles/population) and fatalities per vehicle (F/V)--are estimated using panel data from 1963 to 1999 for 88 countries. The natural logarithm of F/P, V/P, and F/V are expressed as spline (piecewise linear) functions of the logarithm of real per capita GDP (measured in 1985 international prices).
View Article and Find Full Text PDFHum Exp Toxicol
June 2004
National Center for Environmental Economics, US EPA, Washington, DC 20004-2403, USA.
Economists face no fundamental problem in calculating the optimal exposure of a hormetic substance and this could potentially be set as a regulatory level. This level would be where the marginal cost of control is equal to the slope of the exposure-response function. There are a number of reasons, however, to expect public resistance to assuming hormesis.
View Article and Find Full Text PDFJ Toxicol Environ Health A
June 2004
U.S. Environmental Protection Agency, National Center for Environmental Economics, Washington, DC, USA.
Benefit-cost analysis relies heavily upon risk assessment. The extent to which benefits can be quantitatively included in an economic analysis is frequently determined by risk assessment methods. Therefore, interdisciplinary collaboration between economists and experts in risk assessment-related disciplines is critical to further development of quantitative human health benefits analysis.
View Article and Find Full Text PDFEnviron Health Perspect
June 2003
National Center for Environmental Economics, U.S. Environmental Protection Agency, San Francisco, California 94105, USA.
Previous research shows poorer birth outcomes for racial and ethnic minorities and for persons with low socioeconomic status (SES). We evaluated whether mothers in groups at higher risk for poor birth outcomes live in areas of higher air pollution and whether higher exposure to air pollution contributes to poor birth outcomes. An index representing long-term exposure to criteria air pollutants was matched with birth certificate data at the county level for the United States in 1998-1999.
View Article and Find Full Text PDFRisk Anal
August 2002
U.S. EPA, National Center for Environmental Economics, Washington, DC 20460, USA.
To quantify the health benefits of environmental policies, economists generally require estimates of the reduced probability of illness or death. For policies that reduce exposure to carcinogenic substances, these estimates traditionally have been obtained through the linear extrapolation of experimental dose-response data to low-exposure scenarios as described in the U.S.
View Article and Find Full Text PDFRisk Anal
April 2002
United States Environmental Protection Agency, National Center for Environmental Economics, Washington, DC 20460, USA.
This article explores two problems analysts face in determining how to estimate values for children's health and safety risk reductions. The first addresses the question: Do willingness-to-pay estimates for health risk changes differ across children and adults and, if so, how? To answer this question, the article first examines the potential effects of age and risk preferences on willingness to pay. A summary of the literature reporting empirical evidence of differences between willingness to pay for adult health and safety risk reductions and willingness to pay for health and safety risk reductions in children is also provided.
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