EPA Comments on Biofuels Pathways Feb 6 2012-Final
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February 6, 2012 Air and Radiation Docket Docket No. EPA–HQ–OAR–2011–0542 Environmental Protection Agency Mailcode: 6406J 1200 Pennsylvania Ave. NW. Washington, DC 20460. Docket No. EPA–HQ–OAR–2011–0542 (RIN 2060-AR07) Re: Comments on Proposed and Direct Final Rules for “Regulation of Fuels and Fuel Additives: Identification of Additional Qualifying Renewable Fuel Pathways Under the Renewable Fuel Standard Program” To Whom It May Concern: Clean Air Task Force, Environmental Working Group, Friends of the Earth, National Wildlife Federation and the Natural Resources Defense Council appreciate the opportunity to submit comments on the Environmental Protection Agency’s proposed and direct final rules entitled “Regulation of Fuels and Fuel Additives: Identification of Additional Qualifying Renewable Fuel Pathways Under the Renewable Fuel Standard Program.” We disagree with EPA’s view that these rules are noncontroversial actions and therefore request that the agency carries out a full rulemaking. Our comments address three main issues: (1) an assumption that production of camelina and other biofuels feedstocks would not result in any land use change; (2) the potential for some of the proposed feedstocks to become invasive; and (3) impacts of corn stover removal. Analysis of Greenhouse Gas Emissions for Biofuels Produced from Camelina Oil and Other Feedstocks With the passage of the Energy Independence and Security Act (EISA) of 2007, EPA is required to include greenhouse gas (GHG) emissions from direct and indirect land use change in its analysis of new biofuels pathways. While some biofuel feedstocks like camelina, napier grass, giant reed and others are not predicted to result in large land use changes, even small changes, once summed up, can have a detrimental impact on our climate, water, air, soil and wildlife resources. We understand the difficulty in calculating GHG emissions from biomass production but as history has shown, scaling up biofuels production may result in numerous unintended consequences that either may or may not have been predicted years ago. As EPA noted in the direct final rule, research on biomass production from sources like camelina and giant reed is still in its early stages. As the University of Florida’s Cooperative Extension Service noted, “research related to [camelina] production is limited and will develop as its value increases as a renewable energy crop.”1 Despite limited information, EPA made an assumption 1 Wright, D. and Jim Marois. “Camelina Production in Florida.” Feb. 2011. Florida Cooperative Extension Service. Accessed online 6 Feb. 2012 at http://edis.ifas.ufl.edu/ag350. that all camelina used for biofuels production will be grown on fallow land and will thus result in no land use change from additional acres being brought into production.2 Unfortunately, the agency failed to cite adequate evidence to validate this assumption. By relying on one study that was co-authored by an industry official, EPA failed to explain how no land use change would occur if camelina production was significantly scaled up.3 Shonnard et al. (2010) state that, “Altogether more than 5 million U.S. acres have the potential to grow camelina in a sustainable manner with no impact on food supply.” 4 But, EPA assumes that almost twice that amount – 8 million acres – would be planted to camelina. With a near-record number of acres being planted to corn, primarily to produce ethanol to meet the Renewable Fuel Standard (RFS) mandate, increased pressure has been placed on the environment as more marginal and fallow land has been brought into production. EPA should analyze how many acres of marginal and fallow land are currently available for biofuels production and what impacts may occur at the margin after biofuels production from camelina or other feedstocks is scaled up. Additionally, EPA must provide a more robust and better-substantiated analysis of likely production practices. When analyzing the environmental consequences of increased production of camelina, giant reed, napier grass, and energy cane, it is not enough for the agency to describe the least damaging ways in which these crops might be grown.5 The fact that it may be physically possible to grow crops using a certain approach says nothing about whether that approach is the most economically efficient option available to farmers – particularly when production is scaled up to commercially relevant volumes. Growing practices will be determined largely according to a variety of economic factors, such as input costs and commodity prices. In its proposal, EPA failed to provide factual data that show how those economic factors will shape production practices, nor has it described the methodology it would use to analyze such data.6,7 Consequently, EPA has not provided an adequate basis for its assessment that an increase in biofuels-related production of camelina, giant reed, napiergrass and energy cane will not result in a significant increase in land use change-related GHG emissions. 2 “Regulation of Fuels and Fuel Additives: Identification of Additional Qualifying Renewable Fuel Pathways Under the Renewable Fuel Standard Program.” Federal Register Vol. 77, No. 3 (5 Jan. 2012): 700-727. Accessed online 6 Feb. 2012 at http://www.gpo.gov/fdsys/pkg/FR-2012-01-05/pdf/2011-31580.pdf. 3 Shonnard, D., L. Williams and T. Kalnes. “Camelina-Derived Jet Fuel and Diesel: Sustainable Advanced Biofuels.” Environmental Progress & Sustainable Energy 29.3 (2010): 382-392. Accessed online 6 Feb. 2012 at http://onlinelibrary.wiley.com/doi/10.1002/ep.10461/pdf. 4 Shonnard, D., L. Williams and T. Kalnes. “Camelina-Derived Jet Fuel and Diesel: Sustainable Advanced Biofuels.” Environmental Progress & Sustainable Energy 29.3 (2010): 382-392. Accessed online 6 Feb. 2012 at http://onlinelibrary.wiley.com/doi/10.1002/ep.10461/pdf. 5 See, e.g., 77 Fed. Reg. at 702, where EPA asserts that camelina “can be grown” during different growing seasons, “can also be used to break planting cycles,” and has certain attributes that “allow it to be grown” on marginal land – without indicating the economic likelihood that these options will be pursued. 6 Cf. CAA §307(d)(3), 42 U.S.C.A. § 7607(d)(3). 7 In fact, EPA acknowledged that it lacked key data concerning the impact that increased production of camelina would have on markets and market-mediated environmental effects. 77 Fed. Reg. at 702. The agency also states that, “The renewable biomass provisions under the Energy Independence and Security Act would prohibit direct land conversion into new agricultural land for camelina production for biofuel internationally.” But without proper monitoring and enforcement, this provision will not prevent farmers from converting new land to biomass production. By assuming no land use change, EPA may underestimate the increase in GHG emissions that could result from breaking new land. This assumption is not only an issue with camelina production but could also underestimate land use change emissions associated with biomass production from giant reed, napiergrass, energy cane and other feedstocks. EPA again assumes that these feedstocks will be grown on the least productive land without citing any specific models or studies that may have informed this decision. EPA also overestimated long-term camelina yields in the direct final rule. Its estimates are on the high end of the current yield range in states like Pennsylvania, Oregon and Montana.8 EPA assumes that U.S. yields will average 1650 pounds per acre and that investment in new seed technology could increase yields to 3000 pounds per acre.9 However, other researchers estimate that camelina’s yield potential ranges from 330 to 2400 pounds per acre without irrigation.10,11 Reaching yields of 3000 pounds per acre may be attainable in certain areas, but previous trials do not suggest that average yields could reach this level in just ten years. Even with nitrogen application rates at two to four times the EPA estimated rate of 40 pounds per acre in 2022, yields barely exceeded 2000 to 2200 pounds per acre in trials in Colorado.12 With the huge increase in corn ethanol production and corn acreage, new land has been brought into production with detrimental environmental consequences.13 As an example, in 2011, the 8 McKay, K.A. and P.F. Lamb. “Camelina Production in Montana.” March 2008. Montana State University Extension. Accessed online 6 Feb. 2012 at http://msuextension.org/publications/AgandNaturalResources/MT200701AG.pdf. 9 “Regulation of Fuels and Fuel Additives: Identification of Additional Qualifying Renewable Fuel Pathways Under the Renewable Fuel Standard Program.” Federal Register Vol. 77 No. 3 (5 Jan. 2012): 700-727. Accessed online 6 Feb. 2012 at http://www.gpo.gov/fdsys/pkg/FR-2012-01-05/pdf/2011-31580.pdf. 10 Ehrensing, D.T. and S.O. Guy. “Camelina.” Jan. 2008. Oregon State University Extension Service. Accessed online 6 Feb. 2012 at http://extension.oregonstate.edu/catalog/pdf/em/em8953-e.pdf. 11 McKay, K.A. and P.F. Lamb. “Camelina Production in Montana.” March 2008. Montana State University Extension. Accessed online 6 Feb. 2012 at http://msuextension.org/publications/AgandNaturalResources/MT200701AG.pdf. 12 Lafferty, R.M., C. Rife and G. Foster. “Spring Camelina Production Guide for the Central High Plains.” Dec. 2009. Blue Sun Agriculture Research and Development. Accessed online 6 Feb. 2012 at http://www.colorado.gov/cs/Satellite?blobcol=urldata&blobheader=application%2Fpdf&blobkey =id&blobtable=MungoBlobs&blobwhere=1251616501820&ssbinary=true. 13 Wallander, S., R. Claassen and C. Nickerson. “The Ethanol Decade: An Expansion of U.S. Corn Production, 2000-09.” Aug. 2011. United States Department of Agriculture’s Economic Research Service. Accessed online 6 Feb. 2012 at http://www.ers.usda.gov/Publications/EIB79/. U.S. produced about 13 billion gallons of ethanol by utilizing 40 percent of domestic corn production; U.S. farmers responded to near-record corn prices by planting 92 million acres of corn, the second-highest level since 1944.14 The RFS2 final rulemaking predicted that the U.S.