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CFE agenda 091117
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CFE agenda 091117
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9/11/2017
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CFE minutes 091117
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The development of a biofuels economy can have <br />an impact on species and habitats at multiple stag- <br />es of production, from land conversion for biofuel <br />feedstocks and the logistics of harvest, to treatment <br />and transportation from field to refinery (Dale et al. <br />2010). Increased biofuel is associated with clear- <br />ing native habitat, displacing agricultural activi- <br />ties into new areas, and an increasing likelihood of <br />alien species introductions. As demand for ethanol <br />increases and corn prices rise, expanding corn acreage <br />could decrease area available for wildlife. Addition- <br />ally, the building of refineries and their associated <br />infrastructure can change the economic dynamics of <br />rural areas, and thus influence changes in land -use <br />that may impact wildlife and habitat. <br />Although corn is the dominant feedstock currently <br />used in the U.S. for biofuel, current research suggests <br />that there are important environmental drawbacks. <br />For example, Pimental and Pitzek (2005) found that <br />the energy outputs from ethanol produced using <br />corn, switchgrass, and wood biomass were each less <br />than their respective fossil energy inputs. For wild- <br />life, corn monocultures offer few habitat benefits and <br />may exacerbate the impact of fertilizers and pesticides <br />on aquatic systems. Thomas et al. (2009) modeled <br />the water quality impacts of shifting from a corn - <br />soybean rotation to more corn - intensive rotations to <br />simulate increasing demand for biofuels in Indiana. <br />They found that, when managing for continuous <br />corn production, mean annual erosion was signifi- <br />cantly greater than in corn - soybean rotation systems. <br />In conventional agriculture with high levels of chem- <br />ical inputs, erosion leads to water quality degrada- <br />tion as a result of agrochemicals attaching to soil <br />particles and washing into local waterways (Thomas <br />et al. 2009). These agrochemicals may persist in soil <br />sediments or biomagnify and accumulate as toxins in <br />the food chain. <br />Some researchers have suggested that the push to <br />develop and grow biofuel feedstocks may change <br />the way land is used in the U.S., while other studies <br />have demonstrated that biofuel targets can be met <br />with relatively minor adjustments (Dale et al. 2010). <br />Of particular concern is the conversion of currently <br />protected land to monoculture biofuel production. <br />Fargione et al. (2008) have argued that the conver- <br />sion of rainforests, peatlands, savannas, or grass- <br />lands would result in 17 to 420 times more carbon <br />dioxide being released than the annual greenhouse <br />gas reductions that these fuels would provide from <br />displacing fossil fuels. A recent paper by Eggers et <br />al. (2009) found that increasing European Union <br />biofuel production targets may have, on balance, a <br />negative impact on biodiversity. They suggested that <br />more of the 313 wildlife species they analyzed would <br />suffer from habitat losses, though the magnitude of <br />impacts varied spatially and with the feedstock type <br />(Eggers et al. 2009). In this same study, woody crops <br />(lignocellulosic) were found to be less detrimental to <br />wildlife than arable crops. Although cellulosic etha- <br />nol is not currently cost - competitive, the Depart- <br />ment of Energy (DOE) is investing in biorefineries <br />that will produce more than 130 million gallons of <br />cellulosic ethanol per year and projects that cellulosic <br />ethanol will be cost - competitive with gasoline by <br />2012 (DOE 2007). <br />These impacts may differ in the United States. Kline <br />and Dale (2008) argue that enough land is available <br />for biofuel production in the U.S., and that strategi- <br />cally using previously cleared or other marginal lands <br />would actually enhance environmental and econom- <br />ic sustamability. However, some conservationists <br />are concerned about the potential conversion of <br />privately -owned land that is currently enrolled in <br />federal habitat conservation programs to switchgrass <br />or other monocultures for biofuel production (Kline <br />and Dale 2008). As the financial benefits of biofuel <br />production increase, the incentives to keep privately - <br />owned land in federal conservation programs may <br />diminish. Over 300 million acres (25 million of which <br />are dominated by grasses) are currently enrolled in <br />
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