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      Health, Economy, and Environment: Sustainable Energy Choices for a Nation

      editorial

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          Abstract

          Energy policies are in transition worldwide based on a convergence of factors including static oil production coupled with increased demand, a desire for energy independence, and growing awareness of climate change. Making energy choices that improve human health, the environment, and economic development is possible if we understand the complex interplay between systems for energy delivery and sustainable, healthy human environments. Reducing energy consumption should be the first step. According to the International Energy Agency (IEA 2006), the average American consumes about 7,800 kg of oil equivalent energy per year compared with Switzerland, where the average person consumes 3,700 kg. If we simply apply lessons learned in Switzerland to our energy use, we could conceivably cut consumption in half without altering the quality of life. This drop in consumption will reduce the incidence of a number of diseases affected by energy production (Figure 1). Energy alternatives lead to surprisingly complex analyses regarding efficiency. For example, some studies have found that substituting biofuels for gasoline will reduce greenhouse gases because biofuel feedstocks sequester carbon during growth. However, other analyses have found that by including land-use change in the analyses, biofuel production could result in a net doubling of greenhouse gases over the next 30 years (Fargione et al. 2008; Searchinger et al. 2008). Moreover, certain biofuels will have a significant impact on water use patterns, food crop production, and deforestation, all of which can have direct and indirect impacts on human health (Figure 1). In addition, biofuels will produce a new mix of air pollutants that have not been extensively studied and could lead to increased air pollution related mortality (Jacobson 2007). Even seemingly clean sources of energy can have implications on human health. Wind energy will undoubtedly create noise, which increases stress, which in turn increases the risk of cardiovascular disease and cancer. The manufacturing process for photovoltaic panels to produce solar energy results in occupational exposures to silica dust or cadium (Fthenakis et al. 2008). Increased reliance on nuclear fission carries known radiation risks during the generation of electricity and disposal of used fuel. Even hydroelectric energy affects human and environmental health, as noted in several recent articles about the Three Gorges Dam (e.g., Hwang et al. 2007). We must combine the lessons we have learned in systems approaches in biology, ecology, engineering, and economics to develop a new systems theory, one that, when properly implemented, can begin to identify how changes in our energy policies will impact the health of our nation. To this end, we provide a simple example exemplifying the utility of comparing global health impacts across energy sources (Table 1). Table 1 shows that the use of traditional biomass accounts for greater mortality than other energy sources. Current world consumption of oil has the greatest impact on climate change, whereas predictions suggest that coal-fired power plants account for > 90% of mortality associated with electricity generation. However, we cannot draw robust conclusions from current analyses of available quantitated health impacts of energy systems because they do not incorporate important factors known to mediate health. For example, health end points related to food shortages resulting from unsustainable biofuel production have not been measured. Links between mercury found in most coal stocks and a range of health end points have not been fully addressed, and combustion products of alternative fuels, including biodiesel and ethanol, as related to health are not fully understood. Occupational exposures in the development and distribution of new fuels is another area of priority and one that calls for expanded focus. Therefore, there is a critical need for a large-scale collaborative effort between social, environmental, physical, engineering, and human health scientists to evaluate risks and benefits associated with rapidly changing energy policies. The National Resource Council (2007) recently suggested that “an appropriate institutional structure that fosters multidisciplinary intramural and extramural research is needed” to take full advantage of the “revolutions in biology and biotechnology.” Their vision focused on systems biology and laboratory investigation. Expanding this vision to address broad environmental linkages to health will result in fuller descriptions of the health implications due to the social, ecological, and economic changes linked to our changing global environment.

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            Emissions from photovoltaic life cycles.

            Photovoltaic (PV) technologies have shown remarkable progress recently in terms of annual production capacity and life cycle environmental performances, which necessitate timely updates of environmental indicators. Based on PV production data of 2004-2006, this study presents the life-cycle greenhouse gas emissions, criteria pollutant emissions, and heavy metal emissions from four types of major commercial PV systems: multicrystalline silicon, monocrystalline silicon, ribbon silicon, and thin-film cadmium telluride. Life-cycle emissions were determined by employing average electricity mixtures in Europe and the United States during the materials and module production for each PV system. Among the current vintage of PV technologies, thin-film cadmium telluride (CdTe) PV emits the least amount of harmful air emissions as it requires the least amount of energy during the module production. However, the differences in the emissions between different PV technologies are very small in comparison to the emissions from conventional energy technologies that PV could displace. As a part of prospective analysis, the effect of PV breeder was investigated. Overall, all PV technologies generate far less life-cycle air emissions per GWh than conventional fossil-fuel-based electricity generation technologies. At least 89% of air emissions associated with electricity generation could be prevented if electricity from photovoltaics displaces electricity from the grid.
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              Effects of ethanol (E85) versus gasoline vehicles on cancer and mortality in the United States.

              Ethanol use in vehicle fuel is increasing worldwide, but the potential cancer risk and ozone-related health consequences of a large-scale conversion from gasoline to ethanol have not been examined. Here, a nested global-through-urban air pollution/weather forecast model is combined with high-resolution future emission inventories, population data, and health effects data to examine the effect of converting from gasoline to E85 on cancer, mortality, and hospitalization in the United States as a whole and Los Angeles in particular. Under the base-case emission scenario derived, which accounted for projected improvements in gasoline and E85 vehicle emission controls, it was found that E85 (85% ethanol fuel, 15% gasoline) may increase ozone-related mortality, hospitalization, and asthma by about 9% in Los Angeles and 4% in the United States as a whole relative to 100% gasoline. Ozone increases in Los Angeles and the northeast were partially offset by decreases in the southeast. E85 also increased peroxyacetyl nitrate (PAN) in the U.S. but was estimated to cause little change in cancer risk. Due to its ozone effects, future E85 may be a greater overall public health risk than gasoline. However, because of the uncertainty in future emission regulations, it can be concluded with confidence only that E85 is unlikely to improve air quality over future gasoline vehicles. Unburned ethanol emissions from E85 may result in a global-scale source of acetaldehyde larger than that of direct emissions.
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                Author and article information

                Journal
                Environ Health Perspect
                Environmental Health Perspectives
                National Institute of Environmental Health Sciences
                0091-6765
                June 2008
                : 116
                : 6
                : A236-A237
                Affiliations
                National Institute of Environmental Health Sciences, National Institutes of Health, Department of Health and Human Services, Research Triangle Park, North Carolina, E-mail: portier@ 123456niehs.nih.gov
                Author notes

                The authors declare they have no competing financial interests.

                Julia M Gohlke is a postdoctoral fellow focusing on computational approaches describing biological processes.

                Sharon Hrynkow is the former acting director of Fogarty International Center and is currently an associate director of the National Institute of Environmental Health Sciences (NIEHS).

                Christopher J. Portier heads Environmental Systems Biology and is an associate director of the NIEHS.

                Article
                ehp0116-a00236
                10.1289/ehp.11602
                2430245
                18560493
                32a8319d-020b-4c7c-b8d5-445b5a3c93e5
                This is an Open Access article: verbatim copying and redistribution of this article are permitted in all media for any purpose, provided this notice is preserved along with the article's original DOI.
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