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Ethanol fuel in the United States

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Ethanol fuel in the United States

Summary

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Main article: Biofuel in the United States, Ethanol fuel

Corn vs Ethanol production in the United States

]]

E15]], E30 and [[E85]] in [[East Lansing, Michigan
Ethanol fuel production by state
Ethanol plants in the US

The United States became the world's largest producer of ethanol fuel in 2005. The U.S. produced 15.8 billion U.S. liquid gallons of ethanol fuel in 2019, up from 13.9 billion gallons (52.6 billion liters) in 2011, and from 1.62 billion gallons in 2000. The U.S. government subsidizes ethanol production.

The ethanol market share in the U.S. gasoline supply grew by volume from just over 1 percent in 2000 to more than 3 percent in 2006 to 10 percent in 2011. Domestic production capacity increased fifteen times after 1990, from 900 million US gallons to 1.63 billion US gal in 2000, to 13.5 billion US gallons in 2010. The Renewable Fuels Association reported 209 ethanol distilleries in operation located in 29 states in 2011.

By 2012 most cars on U.S. roads could run on blends of up to 10% ethanol(E10), and manufacturers had begun producing vehicles designed for much higher percentages. However, the fuel systems of cars, trucks, and motorcycles sold before the ethanol mandate may suffer substantial damage from the use of 10% ethanol blends. Flexible-fuel cars, trucks, and minivans use gasoline/ethanol blends ranging from pure gasoline up to 85% ethanol (E85). By early 2013 there were around 11 million E85-capable vehicles on U.S. roads. Regular use of E85 is low due to lack of fueling infrastructure, but is common in the Midwest. In January 2011 the U.S. Environmental Protection Agency (EPA) granted a waiver to allow up to 15% of ethanol blended with gasoline (E15) to be sold only for cars and light pickup trucks with a model year of 2001 or later. The EPA waiver authorizes, but does not require stations to offer E15. Like the limitations suffered by sales of E85, commercialization of E15 is constrained by the lack of infrastructure as most fuel stations do not have enough pumps to offer the new E15 blend, few existing pumps are certified to dispense E15, and no dedicated tanks are readily available to store E15.

Historically most U.S. ethanol has come from corn, and the required electricity for many distilleries came mainly from coal. There is a debate about ethanol's sustainability and environmental impact. The primary issues related to the large amount of arable land required for crops and ethanol production's impact on grain supply, indirect land use change (ILUC) effects, as well as issues regarding its energy balance and carbon intensity considering its full life cycle.

History

Typical label at the gas pumps warning drivers of ethanol content up to 10%, used as oxygenate additive instead of [[MTBE]]. [[Miami]], [[Florida]].

In 1826 Samuel Morey experimented with an internal combustion chemical mixture that used ethanol (combined with turpentine and ambient air then vaporized) as fuel. At the time, his discovery was overlooked, mostly due to the success of steam power. Ethanol fuel received little attention until 1860 when Nicholas Otto began experimenting with internal combustion engines. In 1859, oil was found in Pennsylvania, which decades later provided a new kind of fuel. Popular fuels in the U.S. before petroleum were a purified form of spirits of turpentine called camphene, and a blend of turpentine and alcohol known as burning fluid. The discovery of a ready supply of oil and Civil War taxation on burning fluid made kerosene a more popular fuel.

In 1896, Henry Ford designed his first car, the "Quadricycle" to run on pure ethanol. In 1908, the revolutionary Ford Model T was capable of running on gasoline, ethanol or a combination. Ford continued to advocate for ethanol fuel even during the prohibition, but lower prices caused gasoline to prevail.

Typical manufacture's warning placed in the fuel filler of U.S. vehicles regarding the capability of using up to E10, and warning against the use of blends between E20 and E85.

Gasoline containing up to 10% ethanol began a decades-long growth in the United States in the late 1970s. The demand for ethanol produced from field corn was spurred by the discovery that methyl tertiary butyl ether (MTBE) was contaminating groundwater. MTBE's use as an oxygenate additive was widespread due to mandates in the Clean Air Act amendments of 1992 to reduce carbon monoxide emissions. MTBE in gasoline had been banned in almost 20 states by 2006. Suppliers were concerned about potential litigation and a 2005 court decision denying legal protection for MTBE. MTBE's fall from grace opened a new market for ethanol, its primary substitute. Corn prices at the time were around US$2 a bushel. Farmers saw a new market and increased production. This demand shift took place at a time when oil prices were rising.

The steep growth in twenty-first century ethanol consumption was driven by federal legislation aimed to reduce oil consumption and enhance energy security. The Energy Policy Act of 2005 required use of 7500000000 USgal of renewable fuel by 2012, and the Energy Independence and Security Act of 2007 raised the standard, to 36000000000 USgal of annual renewable fuel use by 2022. Of this requirement, 21000000000 USgal had to be advanced biofuels, defined as renewable fuels that reduce greenhouse gas emissions by at least 50%.

Energy security

Ethanol fuel plant in [[West Burlington, Iowa]].

One rationale for ethanol production in the U.S. is increased energy security, from shifting supply from oil imports to domestic sources. Ethanol production requires significant energy, and current U.S. production derives most of that energy from domestic coal, natural gas and other non-oil sources. Because in 2006, 66% of U.S. oil consumption was imported, compared to a net surplus of coal and just 16% of natural gas (2006 figures), the displacement of oil-based fuels to ethanol produced a net shift from foreign to domestic U.S. energy sources.

Effect on gasoline prices

The effect of ethanol use on gasoline prices is the source of conflicting opinion from economic studies, further complicated by the non-market forces of tax credits, met and unmet government quotas, and the dramatic recent increase in domestic oil production. According to a 2012 Massachusetts Institute of Technology analysis, ethanol, and biofuel in general, does not materially influence the price of gasoline, while a runup in the price of government mandated Renewable Identification Number credits has driven up the price of gasoline.{{cite news|url=https://www.bloomberg.com/news/2013-03-21/gasoline-price-inflated-by-ethanol-in-oil-boom-energy-markets.html|title=Gasoline Price Inflated by Ethanol in Oil Boom: Energy Markets

The U.S. consumed 138.2 e9USgal of gasoline in 2008, blended with about 9.6 e9USgal of ethanol, representing a market share of almost 7% of supply by volume. Given its lower energy content, ethanol fuel displaced about 6.4 e9USgal of gasoline, representing 4.6 percent in equivalent energy units.

The EPA announced in November 2013, a reduction in mandated U.S. 2014 ethanol production, due to "market conditions".

Tariffs and tax credits

Since the 1980s until 2011, domestic ethanol producers were protected by a 54-cent per gallon import tariff, mainly intended to curb Brazilian sugarcane ethanol imports. Beginning in 2004 blenders of transportation fuel received a tax credit for each gallon of ethanol they mix with gasoline. Several countries in the Caribbean Basin imported and reprocessed Brazilian ethanol, usually converting hydrated ethanol into anhydrous ethanol, for re-export to the United States. They avoided the 2.5% duty and the tariff, thanks to the Caribbean Basin Initiative (CBI) and free trade agreements. This process was limited to 7% of U.S. ethanol consumption.

As of 2011, blenders received a per gallon tax credit, regardless of feedstock; small producers received an additional on the first 15 million US gallons; and producers of cellulosic ethanol received credits up to . Tax credits to promote the production and consumption of biofuels date to the 1970s. For 2011, credits were based on the Energy Policy Act of 2005, the Food, Conservation, and Energy Act of 2008, and the Energy Improvement and Extension Act of 2008.

A 2010 study by the Congressional Budget Office (CBO) found that in fiscal year 2009, biofuel tax credits reduced federal revenues by around billion, of which corn and cellulosic ethanol accounted for billion and million, respectively.

In 2010, CBO estimated that taxpayer costs to reduce gasoline consumption by one gallon were $1.78 for corn ethanol and $3.00 for cellulosic ethanol. In a similar way, and without considering potential indirect land use effects, the costs to taxpayers of reducing greenhouse gas emissions through tax credits were about $750 per metric ton of -equivalent for ethanol and around $275 per metric ton for cellulosic ethanol.

On June 16, 2011, the U.S. Congress approved an amendment to an economic development bill to repeal both the tax credit and the tariff, but this bill did not move forward. Nevertheless, the U.S. Congress did not extend the tariff and the tax credit, allowing both to end on December 31, 2011. Since 1980 the ethanol industry was awarded an estimated billion in subsidies.

Feedstocks

Corn

Main article: Corn ethanol

Corn is the main feedstock used for producing ethanol fuel in the United States. Most of the controversies surrounding U.S. ethanol fuel production and use is related to corn ethanol's energy balance and its social and environmental impacts.

Cellulose

Main article: Cellulosic ethanol

Cellulosic sources have the potential to produce a renewable, cleaner-burning, and carbon-neutral alternative to gasoline. In his State of the Union Address on January 31, 2006, President George W. Bush stated, "We'll also fund additional research in cutting-edge methods of producing ethanol, not just from corn, but from wood chips and stalks or switchgrass. Our goal is to make this new kind of ethanol practical and competitive within six years."

On July 7, 2006, DOE announced a new research agenda for cellulosic ethanol. The 200-page scientific roadmap cited recent advances in biotechnology that could aid use of cellulosic sources. The report outlined a detailed research plan for additional technologies to improve production efficiency. The roadmap acknowledged the need for substantial federal loan guarantees for biorefineries.

The 2007 federal budget earmarked $150 million for the research effort – more than doubling the 2006 budget. DOE invested in enzymatic, thermochemical, acid hydrolysis, hybrid hydrolysis/enzymatic, and other research approaches targeting more efficient and lower–cost conversion of cellulose to ethanol.

The first materials considered for cellulosic biofuel included plant matter from agricultural waste, yard waste, sawdust and paper. Professors R. Malcolm Brown Jr. and David Nobles, Jr. of the University of Texas at Austin developed cyanobacteria that had the potential to produce cellulose, glucose and sucrose, the latter two easily converted into ethanol. This offers the potential to create ethanol without plant matter.

Sugar

fuel ethanol
imports by country (2002–2007)
(Millions of U.S. liquid gallons)Country20072006200520042003
188.8433.731.290.30
75.266.836.336.639.3
73.338.523.75.76.9
Trinidad and Tobago42.724.810.000
39.335.933.425.414.7

Producing ethanol from sugar is simpler than converting corn into ethanol. Converting sugar requires only a yeast fermentation process. Converting corn requires additional cooking and the application of enzymes. The energy requirement for sugar conversion is about half that for corn. Sugarcane produces more than enough energy to do the conversion with energy left over. A 2006 U.S. Department of Agriculture report found that at market prices for ethanol, converting sugarcane, sugar beets and molasses to ethanol would be profitable. As of 2008 researchers were attempting to breed new varieties adapted to U.S. soil and weather conditions, as well as to take advantage of cellulosic ethanol technologies to also convert sugarcane bagasse.

U.S. sugarcane production occurs in Florida, Louisiana, Hawaii, and Texas. The first three plants to produce sugarcane-based ethanol went online in Louisiana in mid-2009. Sugar mills in Lacassine, St. James and Bunkie were converted to sugarcane ethanol production using Colombian technology to enable profitable ethanol production. These three plants planned to produce 100 e6USgal of ethanol per year within five years.

By 2009 two other sugarcane ethanol production projects were being developed in Kauai, Hawaii and Imperial Valley, California. The Hawaiian plant was projected to have a capacity of between 12 - a year and to supply local markets only, as shipping costs made competing in the continental US impractical. This plant went online in 2010. The California plant was expected to produce 60 e6USgal a year in 2011.

Presidents George W. Bush and [[Luiz Inácio Lula da Silva]] during Bush's visit to Brazil, March 2007.

In March 2007, "ethanol diplomacy" was the focus of President George W. Bush's Latin American tour, in which he and Brazil's president, Luiz Inácio Lula da Silva, promoted the production and use of sugarcane ethanol throughout the Caribbean Basin. The two countries agreed to share technology and set international biofuel standards. Brazilian sugarcane technology transfer was intended to permit various Central American, such as Honduras, El Salvador, Nicaragua, Costa Rica and Panama, several Caribbean countries, and various Andean Countries tariff-free trade with the U.S., thanks to existing trade agreements. The expectation was that such countries would export to the United States in the short-term using Brazilian technology.

In 2007, combined exports from Jamaica, El Salvador, Trinidad and Tobago and Costa Rica to the U.S. reached a total of 230.5 e6USgal of sugarcane ethanol, representing 54.1% of imports. Brazil began exporting ethanol to the U.S. in 2004 and exported 188.8 e6USgal representing 44.3% of U.S. ethanol imports in 2007. The remaining imports that year came from Canada and China.

Other feedstocks

Cheese whey, barley, potato waste, beverage waste, and brewery and beer waste have been used as feedstocks for ethanol fuel, but at a far smaller scale than corn and sugarcane ethanol, as plants using these feedstocks have the capacity to produce only 3 to per year.

Comparison with Brazilian ethanol

Sugarcane ethanol has an energy balance seven times greater than corn ethanol. As of 2007, Brazilian distiller production costs were 22 cents per liter, compared with 30 cents per liter for corn-based ethanol.{{cite news

Comparison of key characteristics between
the ethanol industries in the United States and Brazil
Characteristic
Main feedstock
Total ethanol fuel production (2011)
url=http://veja.abril.com.br/300408/p_058.shtmltitle=Ele é o falso vilãoauthor=Julia Duailibiwork=Vejalanguage=ptdate=April 27, 2008access-date=May 3, 2008archive-url=https://web.archive.org/web/20080506103110/http://veja.abril.com.br/300408/p_058.shtmlarchive-date=May 6, 2008 }}
Total area used for ethanol crop (2006)
url=http://revistaepoca.globo.com/Revista/Epoca/0,,EMI5865-15273.htmltitle=Por que a cana é melhor que o milhowork=Épocaauthor=Maria Helena Tachinardidate=June 13, 2008language=ptaccess-date=August 6, 2008archive-url=https://web.archive.org/web/20080707090818/http://revistaepoca.globo.com/Revista/Epoca/0%2C%2CEMI5865-15273.htmlarchive-date=July 7, 2008 }} Print edition pp. 73
url=http://www.eners.ch/plateforme/medias/macedo_2004.pdfauthor= Macedo Isaias, M. Lima Verde Leal and J. Azevedo Ramos da Silvatitle= Assessment of greenhouse gas emissions in the production and use of fuel ethanol in Brazilpublisher=Secretariat of the Environment, Government of the State of São Pauloyear=2004access-date=May 9, 2008archive-url = https://web.archive.org/web/20080528051443/http://www.eners.ch/plateforme/medias/macedo_2004.pdfarchive-date = May 28, 2008}}
title=Use of U.S. Croplands for Biofuels Increases Greenhouse Gases Through Emissions from Land-Use Changeauthor=Timothy Searchingerjournal=Sciencevolume=319issue=5867pages=1238–1240doi=10.1126/science.1151861date=February 29, 2008pmid=18258860bibcode=2008Sci...319.1238Ss2cid=52810681display-authors=etaldoi-access=free}} Originally published online in Science Express on February 7, 2008. See Letters to Science by Wang and Haq. There are critics to these findings for assuming a worst-case scenario.
EPA's estimated 2022 GHG reduction for RFS2.
CARB's full life-cycle carbon intensity
url=http://www.oxfam.org/files/bp114-inconvenient-truth-biofuels-0806.pdftitle=Another Inconvenient Truthpublisher=Oxfamdate=June 28, 2008access-date=August 6, 2008archive-url=https://web.archive.org/web/20080819214631/http://www.oxfam.org/files/bp114-inconvenient-truth-biofuels-0806.pdfarchive-date=August 19, 2008 }}Oxfam Briefing Paper 114, figure 2 pp.8
url=http://wheels.blogs.nytimes.com/2012/03/01/flex-fuel-amendment-makes-for-strange-bedfellows/?ref=automobilestitle=Flex-Fuel Amendment Makes for Strange Bedfellowsauthor=Jim Motavalliwork=The New York Timesdate=March 1, 2012access-date=March 18, 2012}}
Ethanol fueling stations in the country
url=http://br.invertia.com/noticias/noticia.aspx?idNoticia=200807152306_ABR_77211977title=ANP: consumo de álcool combustível é 50% maior em 2007author=Agência Brasildate=July 15, 2008publisher=Invertiaaccess-date=August 9, 2008language=ptarchive-url=https://web.archive.org/web/20081226014527/http://br.invertia.com/noticias/noticia.aspx?idNoticia=200807152306_ABR_77211977archive-date=December 26, 2008 }}
Cost of production (USD/US gallon)
Notes: (1) Assuming no land use change. (2) Estimate is for U.S. consumption and sugarcane ethanol is imported from Brazil. Emissions from sea transport are included. Both estimates include land transport within the U.S.

Environmental and social impact

Environmental effects

Energy balance and carbon intensity

Until 2008, several full life cycle ("Well to Wheels") studies had found that corn ethanol reduces greenhouse gas emissions as compared to gasoline. In 2007 a team led by Farrel from the University of California, Berkeley evaluated six previous studies and concluded corn ethanol reduces greenhouse gas emissions by only 13 percent. Both figures were estimated by Wang from Argonne National Laboratory, based on a comprehensive review of 22 studies conducted between 1979 and 2005, and simulations with Argonne's GREET model. All of these studies included direct land use changes. However, further research examining the actual effects of the Renewable Fuel Standard from 2008 to 2016 has concluded that corn ethanol produces more carbon emissions per unit of energy – likely more than 24% more – than gasoline, when factoring in fertilizer use and land use change.

The reduction estimates on carbon intensity for a given biofuel depend on the assumptions regarding several variables, including crop productivity, agricultural practices, and distillery power source and energy efficiency. None of these earlier studies considered the effects of indirect land-use changes, and though their impact was recognized, its estimation was considered too complex and more difficult to model than direct land use changes.

Effects of land use change

Summary of Searchinger et al. (2008)
comparison of corn ethanol and gasoline GHG emissions
with and without land use change
(CO2 release rate (g/MJ))
Gasoline
Corn ethanol
Cellulosic ethanol
Notes: Calculated using default assumptions for 2015 scenario for ethanol in E85.
Gasoline is a combination of conventional and reformulated gasoline.

Two 2008 studies, both published in the same issue of Scienceexpress, questioned the previous assessments. A team led by Searchinger from Princeton University concluded that once direct and indirect effect of land use changes (ILUC) are considered, both corn and cellulosic ethanol increased carbon emissions as compared to gasoline by 93 and 50 percent respectively. The study limited the analysis to a 30-year time horizon, assuming that land conversion emitted 25 percent of the carbon stored in soils and all carbon in plants cleared for cultivation. Brazil, China and India were considered among the overseas locations where land use change would occur as a result of diverting U.S. corn cropland, and it was assumed that new cropland in each of these regions correspond to different types of forest, savanna or grassland based on the historical proportion of each natural land converted to cultivation in these countries during the 1990s.

A team led by Fargione from The Nature Conservancy found that clearing natural lands for use as agricultural land to produce biofuel feedstock creates a carbon debt. Therefore, this carbon debt applies to both direct and indirect land use changes. The study examined six scenarios of wilderness conversion, Brazilian Amazon to soybean biodiesel, Brazilian Cerrado to soybean biodiesel, Brazilian Cerrado to sugarcane ethanol, Indonesian or Malaysian lowland tropical rainforest to palm biodiesel, Indonesian or Malaysian peatland tropical rainforest to oil palm forest, and U.S. Central grassland to corn ethanol.

Growing corn to fuel internal combustion vehicles is a highly inefficient use of land. A solar farm generating electricity to power an electric vehicle would power around 85 times as much distance as corn ethanol grown on the same area.

Low-carbon fuel standards

Main article: Low-carbon fuel standard

On April 23, 2009, the California Air Resources Board approved specific rules and carbon intensity reference values for the California Low-Carbon Fuel Standard (LCFS) that was to go into effect on January 1, 2011. The consultation process produced controversy regarding the inclusion and modeling of indirect land use change effects. After the CARB's ruling, among other criticisms, representatives of the ethanol industry complained that the standard overstated the negative environmental effects of corn ethanol, and also criticized the inclusion of indirect effects of land-use changes as an unfair penalty to home-made corn ethanol because deforestation in the developing world had been tied to U.S. ethanol production. The emissions standard for 2011 for LCFS meant that Midwest corn ethanol would not meet the California standard unless current carbon intensity is reduced.

A similar controversy arose after the U.S. Environmental Protection Agency (EPA) published on May 5, 2009, its notice of proposed rulemaking for the new Renewable Fuel Standard (RFS). EPA's proposal included the carbon footprint from indirect land-use changes. On the same day, President Barack Obama signed a Presidential Directive with the aim to advance biofuel research and commercialization. The Directive asked a new Biofuels Interagency Working Group comprising the Department of Agriculture, EPA, and DOE, to develop a plan to increase flexible fuel vehicle use, assist in retail marketing and to coordinate infrastructure policies.

The group also was tasked to develop policy ideas for increasing investment in next-generation fuels, and for reducing biofuels' environmental footprint.

In December 2009 two lobbying groups, the Renewable Fuels Association (RFA) and Growth Energy, filed a lawsuit challenging LCFS's constitutionality. The two organizations argued that LCFS violates both the Supremacy Clause and the Commerce Clause of the US Constitution, and "jeopardizes the nationwide market for ethanol." In a press release the associations announced that "If the United States is going to have a low carbon fuel standard, it must be based on sound science and it must be consistent with the U.S. Constitution".

On February 3, 2010, EPA finalized the Renewable Fuel Standard Program (RFS2) for 2010 and beyond. EPA incorporated direct emissions and significant indirect emissions such as emissions from land use changes along with comments and data from new studies. Given average production conditions it expected for 2022, EPA estimated that corn ethanol would reduce GHGs an average of 21% compared to the 2005 gasoline baseline. A 95% confidence interval spans a 7-32% range reflecting uncertainty in the land use change assumptions.

The following table summarizes the mean GHG emissions for ethanol using different feedstocks estimated by EPA modelling and the range of variations considering that the main source of uncertainty in the life cycle analysis is the GHG emissions related to international land use change.

U.S. Environmental Protection Agency
Life cycle year 2022 GHG emissions reduction results for RFS2 final rule
(includes direct and indirect land use change effects and a 30-year payback period at a 0% discount rate)Renewable fuel pathway
(for U.S. consumption)style="background:#cfc;"Mean
GHG emission
reduction(1)style="background:#cfc;"GHG emission
reduction
95% confidence
interval(2)style="background:#cfc;"Assumptions/comments
Corn ethanol
Corn biobutanol
Cellulosic ethanol from switchgrass
Cellulosic ethanol from corn stover
Notes: (1) Percent reduction in lifecycle GHG emissions compared to the average lifecycle GHG for gasoline or diesel sold or distributed as transportation fuel in 2005.
(2) Confidence range accounts for uncertainty in the types of land use change assumptions and the magnitude of resulting GHG emissions.

Water footprint

Water-related concerns relate to water supply and quality, and include availability and potential overuse, pollution, and possible contamination by fertilizers and pesticides. Several studies concluded that increased ethanol production was likely to result in a substantial increase in water pollution by fertilizers and pesticides, with the potential to exacerbate eutrophication and hypoxia, particularly in the Chesapeake Bay and the Gulf of Mexico.

Growing feedstocks consumes most of the water associated with ethanol production. Corn consumes from 500 - of water per liter of ethanol, mostly for evapotranspiration. In general terms, both corn and switchgrass require less irrigation than other fuel crops. Corn is grown mainly in regions with adequate rainfall. However, corn usually needs to be irrigated in the drier climates of Nebraska and eastern Colorado. Further, corn production for ethanol is increasingly taking place in areas requiring irrigation. A 2008 study by the National Research Council concluded that "in the longer term, the likely expansion of cellulosic biofuel production has the potential to further increase the demand for water resources in many parts of the United States. Biofuels expansion beyond current irrigated agriculture, especially in dry western areas, has the potential to greatly increase pressure on water resources in some areas."

A 2009 study estimated that irrigated corn ethanol implied water consumption at between 50 USgal/mi and 100 USgal/mi for U.S. vehicles. This figure increased to 90 USgal/mi for sorghum ethanol from Nebraska, and 115 USgal/mi for Texas sorghum. By contrast, an average U.S. car effectively consumes between 0.2 USgal/mi to 0.5 USgal/mi running on gasoline, including extraction and refining.

In 2010 RFA argued that more efficient water technologies and pre-treated water could reduce consumption. It further claimed that non-conventional oil "sources, such as tar sands and oil shale, require far more water than conventional petroleum extraction and refining."

Dead zone]] in the Gulf of Mexico.

U.S. standard agricultural practices for most crops employ fertilizers that provide nitrogen and phosphorus along with herbicides, fungicides, insecticides, and other pesticides.

Some part of these chemicals leaves the field. Nitrogen in forms such as nitrate (NO3) is highly soluble, and along with some pesticides infiltrates downwards toward the water table, where it can migrate to water wells, rivers and streams. A 2008 National Research Council study found that regionally the highest stream concentrations occur where the rates of application were highest, and that these rates were highest in the Corn Belt. These flows mainly stem from corn, which as of 2010 was the major source of total nitrogen loading to the Mississippi River.

Several studies found that corn ethanol production contributed to the worsening of the Gulf of Mexico dead zone. The nitrogen leached into the Mississippi River and out into the Gulf, where it fed giant algae blooms. As the algae died, it settled to the ocean floor and decayed, consuming oxygen and suffocating marine life, causing hypoxia. This oxygen depletion killed shrimp, crabs, worms and anything else that could not escape, and affected important shrimp fishing grounds.

Social implications

Effect on food prices

Main article: Food vs fuel

Some environmentalists, such as George Monbiot, expressed fears that the marketplace would convert crops to fuel for the rich, while the poor starved and biofuels caused environmental problems. The food vs fuel debate grew in 2008 as a result of the international community's concerns regarding the steep increase in food prices. In April 2008, Jean Ziegler, back then United Nations Special Rapporteur on the Right to Food, repeated his claim that biofuels were a "crime against humanity",{{cite news|url=https://news.bbc.co.uk/1/hi/sci/tech/7351766.stm|title=Brazil president defends biofuels|author=Emilio San Pedro

Corn is the main feedstock for the production of ethanol fuel in the U.S.

A July 2008 World Bank report found that from June 2002 to June 2008 "biofuels and the related consequences of low grain stocks, large land use shifts, speculative activity and export bans" accounted for 70–75% of total price rises. The study found that higher oil prices and a weak dollar explain 25–30% of total price rise. The study said that "large increases in biofuels production in the United States and Europe are the main reason behind the steep rise in global food prices." The report argued that increased production of biofuels in these developed regions was supported by subsidies and tariffs, and claimed that without such policies, food price increases worldwide would have been smaller. It also concluded that Brazil's sugarcane ethanol had not raised sugar prices significantly, and recommended that both the U.S. and E.U. remove tariffs, including on many African countries.

An RFA rebuttal said that the World Bank analysis was highly subjective and that the author considered only "the impact of global food prices from the weak dollar and the direct and indirect effect of high petroleum prices and attribute[d] everything else to biofuels."

A 2010 World Bank study concluded that its previous study may have overestimated the impact, as "the effect of biofuels on food prices has not been as large as originally thought, but that the use of commodities by financial investors (the so-called 'financialization of commodities') may have been partly responsible for the 2007/08 spike."

A July 2008 OECD economic assessment agreed about the negative effects of subsidies and trade restrictions, but found that the impact of biofuels on food prices was much smaller. The OECD study found that existing biofuel support policies would reduce greenhouse gas emissions by no more than 0.8 percent by 2015. It called for more open markets in biofuels and feedstocks to improve efficiency and lower costs. The OECD study concluded that "current biofuel support measures alone are estimated to increase average wheat prices by about 5 percent, maize by around 7 percent and vegetable oil by about 19 percent over the next 10 years."

During the 2008 financial crisis corn prices, fell 50% from their July 2008 high by October 2008, in tandem with other commodities, including oil, while corn ethanol production continued unabated. "Analysts, including some in the ethanol sector, say ethanol demand adds about 75 cents to $1.00 per bushel to the price of corn, as a rule of thumb. Other analysts say it adds around 20 percent, or just under 80 cents per bushel at current prices. Those estimates hint that $4 per bushel corn might be priced at only $3 without demand for ethanol fuel."

Reviewing eight years of actual implementation of the Renewable Fuel Standard, researchers from the University of Wisconsin found the standard increased corn prices by 30% and prices of other crops by 20%.

References

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