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Indirect land use change impacts of biofuels

The indirect land use change impacts of biofuels, also known as ILUC or iLUC (pronounced as i-luck), relates to the unintended consequence of releasing more carbon emissions due to land-use changes around the world induced by the expansion of croplands for ethanol or biodiesel production in response to the increased global demand for biofuels.[1][2]

As farmers worldwide respond to higher crop prices in order to maintain the global food supply-and-demand balance, pristine lands are cleared to replace the food crops that were diverted elsewhere to biofuels' production. Because natural lands, such as rainforests and grasslands, store carbon in their soil and biomass as plants grow each year, clearance of wilderness for new farms translates to a net increase in greenhouse gas emissions. Due to this off-site change in the carbon stock of the soil and the biomass, indirect land use change has consequences in the greenhouse gas (GHG) balance of a biofuel.[1][2][3][4]

Other authors have also argued that indirect land use changes produce other significant social and environmental impacts, affecting biodiversity, water quality, food prices and supply, land tenure, worker migration, and community and cultural stability.[3][5][6][7]

History

The estimates of carbon intensity for a given biofuel depend on the assumptions regarding several variables. As of 2008, multiple full life cycle studies had found that corn ethanol, cellulosic ethanol and Brazilian sugarcane ethanol produce lower greenhouse gas emissions than gasoline.[8][9][10][11][12][13][14] None of these studies, however, considered the effects of indirect land-use changes, and though land use impacts were acknowledged, estimation was considered too complex and difficult to model.[2][9] A controversial paper published in February 2008 in Sciencexpress by a team led by Searchinger from Princeton University concluded that such effects offset the (positive) direct effects of both corn and cellulosic ethanol and that Brazilian sugarcane performed better, but still resulted in a small carbon debt.[1]

After the Searchinger team paper, estimation of carbon emissions from ILUC, together with the food vs. fuel debate, became one of the most contentious issues relating to biofuels, debated in the popular media,[15][16][17][18][19][20][21][22][23] scientific journals,[1][2][7][24][25][26] op-eds and public letters from the scientific community,[4][27][28][29] and the ethanol industry, both American and Brazilian.[30][31][32] This controversy intensified in April 2009 when the California Air Resources Board (CARB) set rules that included ILUC impacts to establish the California Low-Carbon Fuel Standard that entered into force in 2011.

In May 2009 U.S. Environmental Protection Agency (EPA) released a notice of proposed rulemaking for implementation of the 2007 modification of the Renewable Fuel Standard (RFS).[33] EPA's proposed regulations also included ILUC, causing additional controversy among ethanol producers.[34][35][36][37][38] EPA's February 3, 2010 final rule incorporated ILUC based on modelling that was significantly improved over the initial estimates.[39][40]

The UK Renewable Transport Fuel Obligation program requires the Renewable Fuels Agency (RFA) to report potential indirect impacts of biofuel production, including indirect land use change or changes to food and other commodity prices.[14] A July 2008 RFA study, known as the Gallager Review, found several risks and uncertainties, and that the "quantification of GHG emissions from indirect land-use change requires subjective assumptions and contains considerable uncertainty", and required further examination to properly incorporate indirect effects into calculation methodologies.[41] A similarly cautious approach was followed by the European Union. In December 2008 the European Parliament adopted more stringent sustainability criteria for biofuels and directed the European Commission to develop a methodology to factor in GHG emissions from indirect land use change.[42]

Studies and controversy

[relevant?]

 
UK figures for the carbon intensity of bioethanol and fossil fuels. Graph assumes all bioethanols are burnt in country of origin and prior cropland was used to grow feedstock. No ILUC effects were included.[14]

Before 2008, several full life cycle ("Well to Wheels" or WTW) studies had found that corn ethanol reduced transport-related greenhouse gas emissions. In 2007 a University of California, Berkeley team led by Farrel evaluated six previous studies, concluding that corn ethanol reduced GHG emissions by only 13 percent.[8][9][12] However, 20 to 30 percent reduction for corn ethanol, and 85 to 85 percent for cellulosic ethanol,[9][10] both figures estimated by Wang from Argonne National Laboratory, are more commonly cited. Wang reviewed 22 studies conducted between 1979 and 2005, and ran simulations with Argonne's GREET model. These studies accounted for direct land use changes.[11][12] Several studies of Brazilian sugarcane ethanol showed that sugarcane as feedstock reduces GHG by 86 to 90 percent given no significant land use change.[9][13][14] Estimates of carbon intensity depend on crop productivity, agricultural practices, power sources for ethanol distilleries and the energy efficiency of the distillery. None of these studies considered ILUC, due to estimation difficulties.[2][9] Preliminary estimates by Delucchi from the University of California, Davis, suggested that carbon released by new lands converted to agricultural use was a large percentage of life-cycle emissions.[9][43]

Searchinger and Fargione studies

In 2008 Timothy Searchinger, a lawyer from Environmental Defense Fund,[44] concluded that ILUC affects the life cycle assessment and that instead of saving, both corn and cellulosic ethanol increased carbon emissions as compared to gasoline by 93 and 50 percent respectively. Ethanol from Brazilian sugarcane performed better, recovering initial carbon emissions in 4 years, while U.S. corn ethanol required 167 years and cellulosic ethanol required a 52 years payback period.[1] The study limited the analysis a 30-year period, assuming that land conversion emits 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 converted to cultivation in these countries during the 1990s.[1]

Summary of Searchinger et al.
comparison of corn ethanol and gasoline GHG emissions
with and without land use change
(Grams of CO2 released per megajoule of energy in fuel)[1][45]
Fuel type
(U.S.)
Carbon
intensity
Reduction
GHG
Carbon
intensity
+ ILUC
Reduction
GHG
Gasoline
92
-
92
-
Corn ethanol
74
-20%
177
+93%
Cellulosic ethanol
28
-70%
138
+50%
Notes: Calculated using default assumptions for 2015 scenario for ethanol in E85.
Gasoline is a combination of conventional and reformulated gasoline.[45]

Fargione and his team published a separate paper in the same issue of Science claiming that clearing lands to produce biofuel feedstock created a carbon deficit. This deficit applies to both direct and indirect land use changes. The study examined six conversion scenarios: 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 palm biodiesel, and U.S. Central grassland to corn ethanol.[46] The carbon debt was defined as the amount of CO2 released during the first 50 years of this process of land conversion. For the two most common ethanol feedstocks, the study found that sugarcane ethanol produced on natural cerrado lands would take about 17 years to repay its carbon debt, while corn ethanol produced on U.S. central grasslands would result in a repayment time of about 93 years. The worst-case scenario is converting Indonesian or Malaysian tropical peatland rainforest to palm biodiesel production, which would require about 420 years to repay.[46]

Criticism and controversy

The Searchinger and Fargione studies created controversy in both the popular media[4][15][16][17][18][19][21] and in scientific journals. Robert Zubrin observed that Searchinger's "indirect analysis" approach is pseudo-scientific and can be used to "prove anything".[47]

Wang and Haq from Argonne National Laboratory claiming: the assumptions were outdated; they ignored the potential of increased efficiency; and no evidence showed that "U.S. corn ethanol production has so far caused indirect land use in other countries." They concluded that Searchinger demonstrated that ILUC "is much more difficult to model than direct land use changes".[2] In his response Searchinger rebutted each technical objection and asserted that "... any calculation that ignores these emissions, however challenging it is to predict them with certainty, is too incomplete to provide a basis for policy decisions."[25][48]

Another criticism, by Kline and Dale from Oak Ridge National Laboratory, held that Searchinger et al. and Fargione et al. "... do not provide adequate support for their claim that bioufuels cause high emissions due to land-use change", as their conclusions depends on a misleading assumption because more comprehensive field research found that these land use changes "... are driven by interactions among cultural, technological, biophysical, economic, and demographic forces within a spatial and temporal context rather than by a single crop market".[26] Fargione et al. responded in part that although many factors contributed to land clearing, this "observation does not diminish the fact that biofuels also contribute to land clearing if they are produced on existing cropland or on newly cleared lands". Searching disagreed with all of Kline and Dale arguments.[26]

The U.S. biofuel industry also reacted, claiming that the "Searchinger study is clearly a 'worst case scenario' analysis ..." and that this study "relies on a long series of highly subjective assumptions ..."[49] Searchinger rebutted each claim, concluding that NFA's criticisms were invalid. He noted that even if some of his assumptions are high estimates, the study also made many conservative assumptions.[48]

 
Slash and burn forest removal in Brazil
 
Cattle ranching in Brazil

Brazil

In February 2010, Lapola estimated that planned expansion of Brazilian sugarcane and soybean biofuel plantations through 2020 would replace rangeland, with small direct land-use impact on carbon emissions.[50][51] However, the expansion of the rangeland frontier into Amazonian forests, driven by cattle ranching, would indirectly offset the savings.[51] "Sugarcane ethanol and soybean biodiesel each contribute to nearly half of the projected indirect deforestation of 121,970 km2 by 2020, creating a carbon debt that would take about 250 years to be repaid..."[50]

The research also found that oil palm would cause the least land-use changes and associated carbon debt. The analysis also modeled livestock density increases and found that "a higher increase of 0.13 head per hectare in the average livestock density throughout the country could avoid the indirect land-use changes caused by biofuels (even with soybean as the biodiesel feedstock), while still fulfilling all food and bioenergy demands."[50][51] The authors conclude that intensification of cattle ranching and concentration on oil palm are required to achieve effective carbon savings, recommending closer collaboration between the biofuel and cattle-ranching sectors.[50][51]

The main Brazilian ethanol industry organization (UNICA) commented that such studies missed the continuing intensification of cattle production already underway.[52]

A study by Arima et al. published in May 2011 used spatial regression modeling to provide the first statistical assessment of ILUC for the Brazilian Amazon due to soy production. Previously, the indirect impacts of soy crops were only anecdotal or analyzed through demand models at a global scale, while the study took a regional approach. The analysis showed a strong signal linking the expansion of soybean fields in settled agricultural areas at the southern and eastern rims of the Amazon basin to pasture encroachments for cattle production on the forest frontier. The results demonstrate the need to include ILUC in measuring the carbon footprint of soy crops, whether produced for biofuels or other end-uses.[53]

The Arima study is based on 761 municipalities located in the Legal Amazon of Brazil, and found that between 2003 and 2008, soybean areas expanded by 39,100 km2 in the basin's agricultural areas, mainly in Mato Grosso. The model showed that a 10% (3,910 km2) reduction of soy in old pasture areas would have led to a reduction in deforestation of up to 40% (26,039 km2) in heavily forested municipalities of the Brazilian Amazon. The analysis showed that the displacement of cattle production due to agricultural expansion drives land use change in municipalities located hundreds of kilometers away, and that the Amazonian ILUC is not only measurable but its impact is significant.[53]

Implementation

United States

California LCFS

California carbon intensity values
for gasoline, diesel and fuels that substitute them[22][54][55]
(grams of CO2 equivalent released per MJ of energy produced)
Fuel type Carbon
intensity
Carbon
intensity
+ land-use
changes
Intensity
change
respect to
2011 LCFS
Midwest corn ethanol
75.10
105.10
+10%
California gasoline
95.86
95.86
+0.2%
CARB LCFS 2011 for gasoline[54]
-
95.61
-
California diesel (ULSD)
94.71
94.71
+0.2%
CARB LCFS 2011 for diesel[54]
-
94.47
-
California ethanol
50.70
80.70
-16%
Brazilian sugarcane ethanol
27.40
73.40
-23%
Biodiesel (B100) Midwest soybeans(1)
26.93
68.93
-27%
Renewable diesel Midwest soybeans(1)
28.80
68.93
-27%
Cellulosic ethanol (farmed trees)(1)
2.40
20.40
-79%
Compressed natural gas (bio-methane)
11.26
11.26
-88%
Note: the complete lifecycle analysis for these fuels and others evaluated are available
at CARB's website (see Lifecycle Analysis). (1) Preliminary values of fuels not included
in the 2009 LCFS ruling and subject to refining.

On April 23, 2009, California Air Resources Board (CARB) approved the specific rules and carbon intensity reference values for the California Low-Carbon Fuel Standard (LCFS) that take effect January 1, 2011.[56][57] CARB's rulemaking included ILUC. For some biofuels, CARB identified land use changes as a significant source of additional GHG emissions.[54][58] It established one standard for gasoline and alternative fuels, and a second for diesel fuel and its replacements.[55]

Controversy

The public consultation process before the ruling, and the ruling itself were controversial, yielding 229 comments.[59] ILUC was one of the most contentious issues. On June 24, 2008, 27 scientists and researchers submitted a letter saying, "As researchers and scientists in the field of biomass to biofuel conversion, we are convinced that there simply is not enough hard empirical data to base any sound policy regulation in regards to the indirect impacts of renewable biofuels production. The field is relative new, especially when compared to the vast knowledge base present in fossil fuel production, and the limited analyses are driven by assumptions that sometimes lack robust empirical validation."[60][61] The New Fuels Alliance, representing more than two-dozen biofuel companies, researchers and investors, questioned the Board intention to include indirect land use change effects into account, wrote "While it is likely true that zero is not the right number for the indirect effects of any product in the real world, enforcing indirect effects in a piecemeal way could have very serious consequences for the LCFS.... The argument that zero is not the right number does not justify enforcing a different wrong number, or penalizing one fuel for one category of indirect effects while giving another fuel pathway a free pass."[61][62]

On the other side, more than 170 scientists and economists urged that CARB, "include indirect land use change in the lifecycle analyses of heat-trapping emissions from biofuels and other transportation fuels. This policy will encourage development of sustainable, low-carbon fuels that avoid conflict with food and minimize harmful environmental impacts.... There are uncertainties inherent in estimating the magnitude of indirect land use emissions from biofuels, but assigning a value of zero is clearly not supported by the science."[63][64]

Industry representatives complained that the final rule overstated the environmental effects of corn ethanol, and also criticized the inclusion of ILUC as an unfair penalty to domestic corn ethanol because deforestation in the developing world was being tied to U.S. ethanol production.[22][57][65][66][67][68] The 2011 limit for LCFS means that Mid-west corn ethanol failed, unless current carbon intensity was reduced.[56][67][69][70] Oil industry representatives complained that the standard left oil refiners with few options, such as Brazilian sugarcane ethanol, with its accompanying tariff.[68][70] CARB officials and environmentalists counter that time and economic incentives will allow produces to adapt.[68][70]

UNICA welcomed the ruling,[71] while urging CARB to better reflect Brazilian practices, lowering their estimates of Brazilian emissions.[32][71][72]

The only Board member who voted against the ruling explained that he had a "hard time accepting the fact that we're going to ignore the comments of 125 scientists", referring to the letter submitted by a group of scientists questioning the ILUC penalty. "They said the model was not good enough ... to use at this time as a component part of such an historic new standard."[67][69] CARB advanced the expected date for an expert working group to report on ILUC with refined estimates from January 2012 to January 2011.[65][67][69]

In December 2009 the Renewable Fuels Association (RFA) and Growth Energy, two U.S. ethanol lobbying groups, filed a lawsuit challenging LCFS' constitutionality. The two organizations argued that LCFS violated both the Supremacy Clause and the Commerce Clause, jeopardizing the nationwide ethanol market.[73][74][75]

EPA Renewable Fuel Standard

U.S. Environmental Protection Agency
Draft life cycle GHG emissions reduction results
for different time horizon and discount rate approaches[76]
(includes indirect land use change effects)
Fuel Pathway 100 years +
2% discount
rate
30 years +
0% discount
rate
Corn ethanol (natural gas dry mill)(1)
-16%
+5%
Corn ethanol (Best case NG DM)(2)
-39%
-18%
Corn ethanol (coal dry mill)
+13%
+34%
Corn ethanol (biomass dry mill)
-39%
-18%
Corn ethanol (biomass dry mill with
combined heat and power)
-47%
-26%
Soybean-based biodiesel
-22%
+4%
Waste grease biodiesel
-80%
-80%
Sugarcane ethanol
-44%
-26%
Cellulosic ethanol from switchgrass
-128%
-124%
Cellulosic ethanol from corn stover
-115%
-116%
Notes: (1) Dry mill (DM) plants grind the entire kernel and generally produce
only one primary co-product: distillers grains with solubles (DGS).
(2) Best case plants produce wet distillers grains co-product.

The Energy Independence and Security Act of 2007 (EISA) established new renewable fuel categories and eligibility requirements, setting mandatory lifecycle emissions limits.[76][77] EISA explicitly mandated EPA to include "direct emissions and significant indirect emissions such as significant emissions from land use changes."[76][77][78]

EISA required a 20% reduction in lifecycle GHG emissions for any fuel produced at facilities that commenced construction after December 19, 2007, to be classified as a "renewable fuel"; a 50% reduction for fuels to be classified as "biomass-based diesel" or "advanced biofuel", and a 60% reduction to be classified as "cellulosic biofuel". EISA provided limited flexibility to adjust these thresholds downward by up to 10 percent, and EPA proposed this adjustment for the advanced biofuels category. Existing plants were grandfathered in.[76][77][78]

On May 5, 2009, EPA released a notice of proposed rulemaking for implementation of the 2007 modification of the Renewable Fuel Standard, known as RFS2.[78][79] The draft of the regulations was released for public comment during a 60-day period, a public hearing was held on June 9, 2009, and also a workshop was conducted on June 10–11, 2009.[77][78]

EPA's draft analysis stated that ILUC can produce significant near-term GHG emissions due to land conversion, but that biofuels can pay these back over subsequent years. EPA highlighted two scenarios, varying the time horizon and the discount rate for valuing emissions. The first assumed a 30-year time period uses a 0 percent discount rate (valuing emissions equally regardless of timing). The second scenario used a 100-year time period and a 2% discount rate.[76][77][78]

On the same day that EPA published its notice of proposed rulemaking, President Obama signed a Presidential Directive seeking to advance biofuels research and commercialization. The Directive established the Biofuels Interagency Working Group, to develop policy ideas for increasing investment in next-generation fuels and for reducing their environmental footprint.[34][80][81][82]

 
Maize is the main feedstock for the production of ethanol fuel in the U.S.
 
Sugarcane is the main feedstock for the production of ethanol fuel in Brazil.

The inclusion of ILUC in the proposed ruling provoked complaints from ethanol[34][35][36][37][38] and biodiesel producers.[83] Several environmental organizations welcomed the inclusion of ILUC but criticized the consideration of a 100-year payback scenario, arguing that it underestimated land conversion effects.[36][84][85][86][87] American corn growers, biodiesel producers, ethanol producers and Brazilian sugarcane ethanol producers complained about EPA's methodology,[87][88][89][90] while the oil industry requested an implementation delay.[87][91]

On June 26, 2009, the House of Representatives approved the American Clean Energy and Security Act 219 to 212, mandating EPA to exclude ILUC for a 5-year period, vis a vis RFS2. During this period, more research is to be conducted to develop more reliable models and methodologies for estimating ILUC, and Congress will review this issue before allowing EPA to rule on this matter.[92][93][94][95][96] The bill failed in the U.S. Senate.[97][98]

On February 3, 2010, EPA issued its final RFS2 rule for 2010 and beyond.[39] The rule incorporated direct and significant indirect emissions including ILUC. EPA incorporated comments and data from new studies.[40] Using a 30-year time horizon and a 0% discount rate,[99] EPA concluded that multiple biofuels would meet this standard.[100]

EPA's analysis accepted both ethanol produced from corn starch and biobutanol from corn starch as "renewable fuels". Ethanol produced from sugarcane became an "advanced fuel". Both diesel produced from algal oils and biodiesel from soy oil and diesel from waste oils, fats, and greases fell in the "biomass-based diesel" category. Cellulosic ethanol and cellulosic diesel met the "cellulosic biofuel" standard.[40]

The table summarizes the mean GHG emissions 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.[99]

U.S. Environmental Protection Agency
Life cycle Year 2022 GHG emissions reduction results for RFS2 final rule[99]
(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)
Mean
GHG emission
reduction(1)
GHG emission
reduction
95% confidence
interval(2)
Assumptions/comments
Corn ethanol
21%
7–32%
New or expanded natural gas fired dry mill plant, 37% wet and 63% dry DGS it produces, and employing corn oil fractionation technology.
Corn biobutanol
31%
20–40%
Natural gas fired dry mill plant, 37% wet and 63% dry DGS it produces, and employing corn oil fractionation technology.
Sugarcane ethanol(3)
61%
52–71%
Ethanol is produced and dehydrated in Brazil prior to being imported into the U.S. and the residue is not collected. GHG emissions from ocean tankers hauling ethanol from Brazil to the U.S. are included.
Cellulosic ethanol from switchgrass
110%
102–117%
Ethanol produced using the biochemical process.
Cellulosic ethanol from corn stover
129%
No ILUC
Ethanol produced using the biochemical process. Ethanol produced from agricultural residues does not have any international land use emissions.
Biodiesel from soybean
57%
22–85%
Plant using natural gas.
Waste grease biodiesel
86%
No ILUC
Waste grease feedstock does not have any agricultural or land use emissions.
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.
(3) A new Brazil module was develop to model the impact of increased production of Brazilian sugarcane ethanol for use in the U.S. market and the international impacts of Brazilian sugarcane ethanol production. The Brazil module also accounts for the domestic competition between crop and pasture land uses, and allows for livestock intensification (heads of cattle per unit area of land).
Reactions

UNICA welcomed the ruling, in particular, for the more precise lifecycle emissions estimate and hoped that classification the advanced biofuel designation would help eliminate the tariff.[101][102]

The U.S. Renewable Fuels Association (RFA) also welcomed the ruling, as ethanol producers "require stable federal policy that provides them the market assurances they need to commercialize new technologies", restating their ILUC objection.[103]

RFA also complained that corn-based ethanol scored only a 21% reduction, noting that without ILUC, corn ethanol achieves a 52% GHG reduction.[103][104] RFA also objected that Brazilian sugarcane ethanol "benefited disproportionally" because EPA's revisions lowered the initially equal ILUC estimates by half for corn and 93% for sugarcane.[105]

Several Midwestern lawmakers commented that they continued to oppose EPA's consideration of the "dicey science" of indirect land use that "punishes domestic fuels".[104] House Agriculture Chairman Collin Peterson said, "... to think that we can credibly measure the impact of international indirect land use is completely unrealistic, and I will continue to push for legislation that prevents unreliable methods and unfair standards from burdening the biofuels industry."[104]

EPA Administrator Lisa P. Jackson commented that the agency "did not back down from considering land use in its final rules, but the agency took new information into account that led to a more favorable calculation for ethanol".[104] She cited new science and better data on crop yield and productivity, more information on co-products that could be produced from advanced biofuels and expanded land-use data for 160 countries, instead of the 40 considered in the proposed rule.[104]

Europe

As of 2010, European Union and United Kingdom regulators had recognized the need to take ILUC into account, but had not determined the most appropriate methodology.

UK Renewable Transport Fuel Obligation

The UK Renewable Transport Fuel Obligation (RTFO) program requires fuel suppliers to report direct impacts, and asked the Renewable Fuels Agency (RFA) to report potential indirect impacts, including ILUC and commodity price changes.[14] The RFA's July 2008 "Gallager Review", mentioned several risks regarding biofuels and required feedstock production to avoid agricultural land that would otherwise be used for food production, despite concluding that "quantification of GHG emissions from indirect land-use change requires subjective assumptions and contains considerable uncertainty".[41] Some environmental groups argued that emissions from ILUC were not being taken into account and could be creating more emissions.[106][107][108]

European Union

On December 17, 2008, the European Parliament approved the Renewable Energy Sources Directive (COM(2008)19) and amendments to the Fuel Quality Directive (Directive 2009/30),[109] which included sustainability criteria for biofuels and mandated consideration of ILUC. The Directive established a 10% biofuel target. A separate Fuel Quality Directive set the EU's Low Carbon Fuel Standard, requiring a 6% reduction in GHG intensity of EU transport fuels by 2020. The legislation ordered the European Commission to develop a methodology to factor in GHG emissions from ILUC by December 31, 2010, based on the best available scientific evidence.[42][54][110]

In the meantime, the European Parliament defined lands that were ineligible for producing biofuel feedstocks for the purpose of the Directives. This category included wetlands and continuously forested areas with canopy cover of more than 30 percent or cover between 10 and 30 percent given evidence that its existing carbon stock was low enough to justify conversion.[42]

The Commission subsequently published terms of reference for three ILUC modeling exercises: one using a General Equilibrium model;[111] one using a Partial Equilibrium model[112] and one comparing other global modeling exercises.[113] It also consulted on a limited range of high-level options for addressing ILUC[114] to which 17 countries[115] and 59 organizations responded.[116] The United Nations Special Rapporteur on the Right to Food and several environmental organizations complained that the 2008 safeguards were inadequate.[117][118][119][120] UNICA called for regulators to establish an empirical and "globally accepted methodology" to consider ILUC, with the participation of researchers and scientists from biofuel crop-producing countries.[121]

In 2010 some NGOs accused the European Commission of lacking transparency given its reluctance to release documents relating to the ILUC work.[122] In March 2010 the Partial and General Equilibrium Modelling results were made available, with the disclaimer that the EC had not adopted the views contained in the materials.[123] These indicate that a 1.25% increase in EU biofuel consumption would require around 5,000,000 hectares (12,000,000 acres) of land globally.[124]

The scenarios for varied from 5.6 to 8.6% of road transport fuels. The study found that ILUC effects offset part of the emission benefits, and that above the 5.6% threshold, ILUC emissions increase rapidly increase.[125][126] For the expected scenario of 5.6% by 2020, the study estimated that biodiesel production increases would be mostly domestic, while bioethanol production would take place mainly in Brazil, regardless of EU duties.[125] The analysis concluded that eliminating trade barriers would further reduce emissions, because the EU would import more from Brazil.[124] Under this scenario, "direct emission savings from biofuels are estimated at 18 Mt CO
2
, additional emissions from ILUC at 5.3 Mt CO
2
(mostly in Brazil), resulting in a global net balance of nearly 13 Mt CO
2
savings in a 20 years horizon".[125] The study also found that ILUC emissions were much greater for biodiesel from vegetable oil and estimated that in 2020 even at the 5.6% level were over half the greenhouse gas emissions from diesel.[125][126]

As part of the announcement, the Commission stated that it would publish a report on ILUC by the end of 2010.[127]

Certification system

On June 10, 2010, the EC announced its decision to set up certification schemes for biofuels, including imports as part of the Renewable Energy Directive. The Commission encouraged E.U. nations, industry and NGOs to set up voluntary certification schemes.[128][129] EC figures for 2007 showed that 26% of biodiesel and 31% of bioethanol used in the E.U. was imported, mainly from Brazil and the United States.[130]

Reactions

UNICA welcomed the EU efforts to "engage independent experts in its assessments" but requested that improvements because "... the report currently contains a certain number of inaccuracies, so once these are corrected, we anticipate even higher benefits resulting from the use of Brazilian sugarcane ethanol."[131] UNICA highlighted the fact that the report assumed land expansion that "does not take into consideration the agro-ecological zoning for sugarcane in Brazil, which prevents cane from expanding into any type of native vegetation."[131]

Critics said the 10% figure was reduced to 5.6% of transport fuels partly by exaggerating the contribution of electric vehicles (EV) in 2020, as the study assumed EVs would represent 20% of new car sales, two and six times the car industry's own estimate.[132] They also claimed the study "exaggerates to around 45 percent the contribution of bioethanol—the greenest of all biofuels—and consequently downplays the worst impacts of biodiesel."[132]

Environmental groups found that the measures "are too weak to halt a dramatic increase in deforestation".[130][133] According to Greenpeace, "indirect land-use change impacts of biofuel production still are not properly addressed", which for them was the most dangerous problem of biofuels[133]

Industry representatives welcomed the certification system and some dismissed concerns regarding the lack of land use criteria.[130][134][135] UNICA and other industry groups wanted the gaps in the rules filled to provide a clear operating framework.[134][135]

The negotiations between the European Parliament and the Council of European Ministers continue. A deal is not foreseen before 2014.[136]

See also

References

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  2. ^ a b c d e f Michael Wang; Zia Haq (2008-03-14). (PDF). Argonne National Laboratory. Archived from the original (PDF) on 2013-02-15. Retrieved 2009-06-07. The published version on Science Letters is included in Searchinger E-Letter responses 2008-08-12
  3. ^ a b Gnansounou; et al. (March 2008). "Accounting for indirect land-use changes in GHG balances of biofuels: Review of current approaches" (PDF). École Polytechnique Fédérale de Lausanne. Retrieved 2009-06-07. Working Paper REF. 437.101
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External links

  • Amendments to the European Renewable Energy Sources Directive (approved December 17, 2008.
  • CARB: Detailed California-modified GREET pathway for U.S. corn ethanol (February 27, 2009, version 2.1)
  • CARB: Detailed California-modified GREET pathway for Brazilian sugarcane ethanol (February 27, 2009, version 2.1)
  • CARB: Proposed Regulation to Implement the Low Carbon Fuel Standard (approved April 23, 2009)

indirect, land, change, impacts, biofuels, this, article, needs, updated, please, help, update, this, article, reflect, recent, events, newly, available, information, august, 2021, indirect, land, change, impacts, biofuels, also, known, iluc, iluc, pronounced,. This article needs to be updated Please help update this article to reflect recent events or newly available information August 2021 The indirect land use change impacts of biofuels also known as ILUC or iLUC pronounced as i luck relates to the unintended consequence of releasing more carbon emissions due to land use changes around the world induced by the expansion of croplands for ethanol or biodiesel production in response to the increased global demand for biofuels 1 2 Brazilian cerrado Amazon rainforest As farmers worldwide respond to higher crop prices in order to maintain the global food supply and demand balance pristine lands are cleared to replace the food crops that were diverted elsewhere to biofuels production Because natural lands such as rainforests and grasslands store carbon in their soil and biomass as plants grow each year clearance of wilderness for new farms translates to a net increase in greenhouse gas emissions Due to this off site change in the carbon stock of the soil and the biomass indirect land use change has consequences in the greenhouse gas GHG balance of a biofuel 1 2 3 4 Other authors have also argued that indirect land use changes produce other significant social and environmental impacts affecting biodiversity water quality food prices and supply land tenure worker migration and community and cultural stability 3 5 6 7 Contents 1 History 2 Studies and controversy 2 1 Searchinger and Fargione studies 2 1 1 Criticism and controversy 2 2 Brazil 3 Implementation 3 1 United States 3 1 1 California LCFS 3 1 1 1 Controversy 3 1 2 EPA Renewable Fuel Standard 3 1 2 1 Reactions 3 2 Europe 3 2 1 UK Renewable Transport Fuel Obligation 3 2 2 European Union 3 2 2 1 Certification system 3 2 2 2 Reactions 4 See also 5 References 6 External linksHistory EditThe estimates of carbon intensity for a given biofuel depend on the assumptions regarding several variables As of 2008 multiple full life cycle studies had found that corn ethanol cellulosic ethanol and Brazilian sugarcane ethanol produce lower greenhouse gas emissions than gasoline 8 9 10 11 12 13 14 None of these studies however considered the effects of indirect land use changes and though land use impacts were acknowledged estimation was considered too complex and difficult to model 2 9 A controversial paper published in February 2008 in Sciencexpress by a team led by Searchinger from Princeton University concluded that such effects offset the positive direct effects of both corn and cellulosic ethanol and that Brazilian sugarcane performed better but still resulted in a small carbon debt 1 Malaysian cloud forest After the Searchinger team paper estimation of carbon emissions from ILUC together with the food vs fuel debate became one of the most contentious issues relating to biofuels debated in the popular media 15 16 17 18 19 20 21 22 23 scientific journals 1 2 7 24 25 26 op eds and public letters from the scientific community 4 27 28 29 and the ethanol industry both American and Brazilian 30 31 32 This controversy intensified in April 2009 when the California Air Resources Board CARB set rules that included ILUC impacts to establish the California Low Carbon Fuel Standard that entered into force in 2011 In May 2009 U S Environmental Protection Agency EPA released a notice of proposed rulemaking for implementation of the 2007 modification of the Renewable Fuel Standard RFS 33 EPA s proposed regulations also included ILUC causing additional controversy among ethanol producers 34 35 36 37 38 EPA s February 3 2010 final rule incorporated ILUC based on modelling that was significantly improved over the initial estimates 39 40 The UK Renewable Transport Fuel Obligation program requires the Renewable Fuels Agency RFA to report potential indirect impacts of biofuel production including indirect land use change or changes to food and other commodity prices 14 A July 2008 RFA study known as the Gallager Review found several risks and uncertainties and that the quantification of GHG emissions from indirect land use change requires subjective assumptions and contains considerable uncertainty and required further examination to properly incorporate indirect effects into calculation methodologies 41 A similarly cautious approach was followed by the European Union In December 2008 the European Parliament adopted more stringent sustainability criteria for biofuels and directed the European Commission to develop a methodology to factor in GHG emissions from indirect land use change 42 Studies and controversy Edit relevant UK figures for the carbon intensity of bioethanol and fossil fuels Graph assumes all bioethanols are burnt in country of origin and prior cropland was used to grow feedstock No ILUC effects were included 14 Before 2008 several full life cycle Well to Wheels or WTW studies had found that corn ethanol reduced transport related greenhouse gas emissions In 2007 a University of California Berkeley team led by Farrel evaluated six previous studies concluding that corn ethanol reduced GHG emissions by only 13 percent 8 9 12 However 20 to 30 percent reduction for corn ethanol and 85 to 85 percent for cellulosic ethanol 9 10 both figures estimated by Wang from Argonne National Laboratory are more commonly cited Wang reviewed 22 studies conducted between 1979 and 2005 and ran simulations with Argonne s GREET model These studies accounted for direct land use changes 11 12 Several studies of Brazilian sugarcane ethanol showed that sugarcane as feedstock reduces GHG by 86 to 90 percent given no significant land use change 9 13 14 Estimates of carbon intensity depend on crop productivity agricultural practices power sources for ethanol distilleries and the energy efficiency of the distillery None of these studies considered ILUC due to estimation difficulties 2 9 Preliminary estimates by Delucchi from the University of California Davis suggested that carbon released by new lands converted to agricultural use was a large percentage of life cycle emissions 9 43 Searchinger and Fargione studies Edit In 2008 Timothy Searchinger a lawyer from Environmental Defense Fund 44 concluded that ILUC affects the life cycle assessment and that instead of saving both corn and cellulosic ethanol increased carbon emissions as compared to gasoline by 93 and 50 percent respectively Ethanol from Brazilian sugarcane performed better recovering initial carbon emissions in 4 years while U S corn ethanol required 167 years and cellulosic ethanol required a 52 years payback period 1 The study limited the analysis a 30 year period assuming that land conversion emits 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 converted to cultivation in these countries during the 1990s 1 Summary of Searchinger et al comparison of corn ethanol and gasoline GHG emissionswith and without land use change Grams of CO2 released per megajoule of energy in fuel 1 45 Fuel type U S Carbon intensity ReductionGHG Carbonintensity ILUC ReductionGHGGasoline 92 92 Corn ethanol 74 20 177 93 Cellulosic ethanol 28 70 138 50 Notes Calculated using default assumptions for 2015 scenario for ethanol in E85 Gasoline is a combination of conventional and reformulated gasoline 45 Fargione and his team published a separate paper in the same issue of Science claiming that clearing lands to produce biofuel feedstock created a carbon deficit This deficit applies to both direct and indirect land use changes The study examined six conversion scenarios 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 palm biodiesel and U S Central grassland to corn ethanol 46 The carbon debt was defined as the amount of CO2 released during the first 50 years of this process of land conversion For the two most common ethanol feedstocks the study found that sugarcane ethanol produced on natural cerrado lands would take about 17 years to repay its carbon debt while corn ethanol produced on U S central grasslands would result in a repayment time of about 93 years The worst case scenario is converting Indonesian or Malaysian tropical peatland rainforest to palm biodiesel production which would require about 420 years to repay 46 Criticism and controversy Edit The Searchinger and Fargione studies created controversy in both the popular media 4 15 16 17 18 19 21 and in scientific journals Robert Zubrin observed that Searchinger s indirect analysis approach is pseudo scientific and can be used to prove anything 47 Wang and Haq from Argonne National Laboratory claiming the assumptions were outdated they ignored the potential of increased efficiency and no evidence showed that U S corn ethanol production has so far caused indirect land use in other countries They concluded that Searchinger demonstrated that ILUC is much more difficult to model than direct land use changes 2 In his response Searchinger rebutted each technical objection and asserted that any calculation that ignores these emissions however challenging it is to predict them with certainty is too incomplete to provide a basis for policy decisions 25 48 Another criticism by Kline and Dale from Oak Ridge National Laboratory held that Searchinger et al and Fargione et al do not provide adequate support for their claim that bioufuels cause high emissions due to land use change as their conclusions depends on a misleading assumption because more comprehensive field research found that these land use changes are driven by interactions among cultural technological biophysical economic and demographic forces within a spatial and temporal context rather than by a single crop market 26 Fargione et al responded in part that although many factors contributed to land clearing this observation does not diminish the fact that biofuels also contribute to land clearing if they are produced on existing cropland or on newly cleared lands Searching disagreed with all of Kline and Dale arguments 26 The U S biofuel industry also reacted claiming that the Searchinger study is clearly a worst case scenario analysis and that this study relies on a long series of highly subjective assumptions 49 Searchinger rebutted each claim concluding that NFA s criticisms were invalid He noted that even if some of his assumptions are high estimates the study also made many conservative assumptions 48 Slash and burn forest removal in Brazil Cattle ranching in Brazil Brazil Edit In February 2010 Lapola estimated that planned expansion of Brazilian sugarcane and soybean biofuel plantations through 2020 would replace rangeland with small direct land use impact on carbon emissions 50 51 However the expansion of the rangeland frontier into Amazonian forests driven by cattle ranching would indirectly offset the savings 51 Sugarcane ethanol and soybean biodiesel each contribute to nearly half of the projected indirect deforestation of 121 970 km2 by 2020 creating a carbon debt that would take about 250 years to be repaid 50 The research also found that oil palm would cause the least land use changes and associated carbon debt The analysis also modeled livestock density increases and found that a higher increase of 0 13 head per hectare in the average livestock density throughout the country could avoid the indirect land use changes caused by biofuels even with soybean as the biodiesel feedstock while still fulfilling all food and bioenergy demands 50 51 The authors conclude that intensification of cattle ranching and concentration on oil palm are required to achieve effective carbon savings recommending closer collaboration between the biofuel and cattle ranching sectors 50 51 The main Brazilian ethanol industry organization UNICA commented that such studies missed the continuing intensification of cattle production already underway 52 A study by Arima et al published in May 2011 used spatial regression modeling to provide the first statistical assessment of ILUC for the Brazilian Amazon due to soy production Previously the indirect impacts of soy crops were only anecdotal or analyzed through demand models at a global scale while the study took a regional approach The analysis showed a strong signal linking the expansion of soybean fields in settled agricultural areas at the southern and eastern rims of the Amazon basin to pasture encroachments for cattle production on the forest frontier The results demonstrate the need to include ILUC in measuring the carbon footprint of soy crops whether produced for biofuels or other end uses 53 The Arima study is based on 761 municipalities located in the Legal Amazon of Brazil and found that between 2003 and 2008 soybean areas expanded by 39 100 km2 in the basin s agricultural areas mainly in Mato Grosso The model showed that a 10 3 910 km2 reduction of soy in old pasture areas would have led to a reduction in deforestation of up to 40 26 039 km2 in heavily forested municipalities of the Brazilian Amazon The analysis showed that the displacement of cattle production due to agricultural expansion drives land use change in municipalities located hundreds of kilometers away and that the Amazonian ILUC is not only measurable but its impact is significant 53 Implementation EditSee also Low carbon fuel standard United States Edit California LCFS Edit California carbon intensity values for gasoline diesel and fuels that substitute them 22 54 55 grams of CO2 equivalent released per MJ of energy produced Fuel type Carbonintensity Carbon intensity land usechanges Intensitychangerespect to 2011 LCFSMidwest corn ethanol 75 10 105 10 10 California gasoline 95 86 95 86 0 2 CARB LCFS 2011 for gasoline 54 95 61 California diesel ULSD 94 71 94 71 0 2 CARB LCFS 2011 for diesel 54 94 47 California ethanol 50 70 80 70 16 Brazilian sugarcane ethanol 27 40 73 40 23 Biodiesel B100 Midwest soybeans 1 26 93 68 93 27 Renewable diesel Midwest soybeans 1 28 80 68 93 27 Cellulosic ethanol farmed trees 1 2 40 20 40 79 Compressed natural gas bio methane 11 26 11 26 88 Note the complete lifecycle analysis for these fuels and others evaluated are available at CARB s website see Lifecycle Analysis 1 Preliminary values of fuels not included in the 2009 LCFS ruling and subject to refining On April 23 2009 California Air Resources Board CARB approved the specific rules and carbon intensity reference values for the California Low Carbon Fuel Standard LCFS that take effect January 1 2011 56 57 CARB s rulemaking included ILUC For some biofuels CARB identified land use changes as a significant source of additional GHG emissions 54 58 It established one standard for gasoline and alternative fuels and a second for diesel fuel and its replacements 55 Controversy Edit The public consultation process before the ruling and the ruling itself were controversial yielding 229 comments 59 ILUC was one of the most contentious issues On June 24 2008 27 scientists and researchers submitted a letter saying As researchers and scientists in the field of biomass to biofuel conversion we are convinced that there simply is not enough hard empirical data to base any sound policy regulation in regards to the indirect impacts of renewable biofuels production The field is relative new especially when compared to the vast knowledge base present in fossil fuel production and the limited analyses are driven by assumptions that sometimes lack robust empirical validation 60 61 The New Fuels Alliance representing more than two dozen biofuel companies researchers and investors questioned the Board intention to include indirect land use change effects into account wrote While it is likely true that zero is not the right number for the indirect effects of any product in the real world enforcing indirect effects in a piecemeal way could have very serious consequences for the LCFS The argument that zero is not the right number does not justify enforcing a different wrong number or penalizing one fuel for one category of indirect effects while giving another fuel pathway a free pass 61 62 On the other side more than 170 scientists and economists urged that CARB include indirect land use change in the lifecycle analyses of heat trapping emissions from biofuels and other transportation fuels This policy will encourage development of sustainable low carbon fuels that avoid conflict with food and minimize harmful environmental impacts There are uncertainties inherent in estimating the magnitude of indirect land use emissions from biofuels but assigning a value of zero is clearly not supported by the science 63 64 Industry representatives complained that the final rule overstated the environmental effects of corn ethanol and also criticized the inclusion of ILUC as an unfair penalty to domestic corn ethanol because deforestation in the developing world was being tied to U S ethanol production 22 57 65 66 67 68 The 2011 limit for LCFS means that Mid west corn ethanol failed unless current carbon intensity was reduced 56 67 69 70 Oil industry representatives complained that the standard left oil refiners with few options such as Brazilian sugarcane ethanol with its accompanying tariff 68 70 CARB officials and environmentalists counter that time and economic incentives will allow produces to adapt 68 70 UNICA welcomed the ruling 71 while urging CARB to better reflect Brazilian practices lowering their estimates of Brazilian emissions 32 71 72 The only Board member who voted against the ruling explained that he had a hard time accepting the fact that we re going to ignore the comments of 125 scientists referring to the letter submitted by a group of scientists questioning the ILUC penalty They said the model was not good enough to use at this time as a component part of such an historic new standard 67 69 CARB advanced the expected date for an expert working group to report on ILUC with refined estimates from January 2012 to January 2011 65 67 69 In December 2009 the Renewable Fuels Association RFA and Growth Energy two U S ethanol lobbying groups filed a lawsuit challenging LCFS constitutionality The two organizations argued that LCFS violated both the Supremacy Clause and the Commerce Clause jeopardizing the nationwide ethanol market 73 74 75 EPA Renewable Fuel Standard Edit See also Energy Policy Act of 2005 and Energy Independence and Security Act of 2007 U S Environmental Protection AgencyDraft life cycle GHG emissions reduction results for different time horizon and discount rate approaches 76 includes indirect land use change effects Fuel Pathway 100 years 2 discountrate 30 years 0 discount rateCorn ethanol natural gas dry mill 1 16 5 Corn ethanol Best case NG DM 2 39 18 Corn ethanol coal dry mill 13 34 Corn ethanol biomass dry mill 39 18 Corn ethanol biomass dry mill with combined heat and power 47 26 Soybean based biodiesel 22 4 Waste grease biodiesel 80 80 Sugarcane ethanol 44 26 Cellulosic ethanol from switchgrass 128 124 Cellulosic ethanol from corn stover 115 116 Notes 1 Dry mill DM plants grind the entire kernel and generally produce only one primary co product distillers grains with solubles DGS 2 Best case plants produce wet distillers grains co product The Energy Independence and Security Act of 2007 EISA established new renewable fuel categories and eligibility requirements setting mandatory lifecycle emissions limits 76 77 EISA explicitly mandated EPA to include direct emissions and significant indirect emissions such as significant emissions from land use changes 76 77 78 EISA required a 20 reduction in lifecycle GHG emissions for any fuel produced at facilities that commenced construction after December 19 2007 to be classified as a renewable fuel a 50 reduction for fuels to be classified as biomass based diesel or advanced biofuel and a 60 reduction to be classified as cellulosic biofuel EISA provided limited flexibility to adjust these thresholds downward by up to 10 percent and EPA proposed this adjustment for the advanced biofuels category Existing plants were grandfathered in 76 77 78 On May 5 2009 EPA released a notice of proposed rulemaking for implementation of the 2007 modification of the Renewable Fuel Standard known as RFS2 78 79 The draft of the regulations was released for public comment during a 60 day period a public hearing was held on June 9 2009 and also a workshop was conducted on June 10 11 2009 77 78 EPA s draft analysis stated that ILUC can produce significant near term GHG emissions due to land conversion but that biofuels can pay these back over subsequent years EPA highlighted two scenarios varying the time horizon and the discount rate for valuing emissions The first assumed a 30 year time period uses a 0 percent discount rate valuing emissions equally regardless of timing The second scenario used a 100 year time period and a 2 discount rate 76 77 78 On the same day that EPA published its notice of proposed rulemaking President Obama signed a Presidential Directive seeking to advance biofuels research and commercialization The Directive established the Biofuels Interagency Working Group to develop policy ideas for increasing investment in next generation fuels and for reducing their environmental footprint 34 80 81 82 Maize is the main feedstock for the production of ethanol fuel in the U S Sugarcane is the main feedstock for the production of ethanol fuel in Brazil The inclusion of ILUC in the proposed ruling provoked complaints from ethanol 34 35 36 37 38 and biodiesel producers 83 Several environmental organizations welcomed the inclusion of ILUC but criticized the consideration of a 100 year payback scenario arguing that it underestimated land conversion effects 36 84 85 86 87 American corn growers biodiesel producers ethanol producers and Brazilian sugarcane ethanol producers complained about EPA s methodology 87 88 89 90 while the oil industry requested an implementation delay 87 91 On June 26 2009 the House of Representatives approved the American Clean Energy and Security Act 219 to 212 mandating EPA to exclude ILUC for a 5 year period vis a vis RFS2 During this period more research is to be conducted to develop more reliable models and methodologies for estimating ILUC and Congress will review this issue before allowing EPA to rule on this matter 92 93 94 95 96 The bill failed in the U S Senate 97 98 On February 3 2010 EPA issued its final RFS2 rule for 2010 and beyond 39 The rule incorporated direct and significant indirect emissions including ILUC EPA incorporated comments and data from new studies 40 Using a 30 year time horizon and a 0 discount rate 99 EPA concluded that multiple biofuels would meet this standard 100 EPA s analysis accepted both ethanol produced from corn starch and biobutanol from corn starch as renewable fuels Ethanol produced from sugarcane became an advanced fuel Both diesel produced from algal oils and biodiesel from soy oil and diesel from waste oils fats and greases fell in the biomass based diesel category Cellulosic ethanol and cellulosic diesel met the cellulosic biofuel standard 40 The table summarizes the mean GHG emissions 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 99 U S Environmental Protection AgencyLife cycle Year 2022 GHG emissions reduction results for RFS2 final rule 99 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 MeanGHG emissionreduction 1 GHG emissionreduction95 confidence interval 2 Assumptions commentsCorn ethanol 21 7 32 New or expanded natural gas fired dry mill plant 37 wet and 63 dry DGS it produces and employing corn oil fractionation technology Corn biobutanol 31 20 40 Natural gas fired dry mill plant 37 wet and 63 dry DGS it produces and employing corn oil fractionation technology Sugarcane ethanol 3 61 52 71 Ethanol is produced and dehydrated in Brazil prior to being imported into the U S and the residue is not collected GHG emissions from ocean tankers hauling ethanol from Brazil to the U S are included Cellulosic ethanol from switchgrass 110 102 117 Ethanol produced using the biochemical process Cellulosic ethanol from corn stover 129 No ILUC Ethanol produced using the biochemical process Ethanol produced from agricultural residues does not have any international land use emissions Biodiesel from soybean 57 22 85 Plant using natural gas Waste grease biodiesel 86 No ILUC Waste grease feedstock does not have any agricultural or land use emissions 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 3 A new Brazil module was develop to model the impact of increased production of Brazilian sugarcane ethanol for use in the U S market and the international impacts of Brazilian sugarcane ethanol production The Brazil module also accounts for the domestic competition between crop and pasture land uses and allows for livestock intensification heads of cattle per unit area of land Reactions Edit UNICA welcomed the ruling in particular for the more precise lifecycle emissions estimate and hoped that classification the advanced biofuel designation would help eliminate the tariff 101 102 The U S Renewable Fuels Association RFA also welcomed the ruling as ethanol producers require stable federal policy that provides them the market assurances they need to commercialize new technologies restating their ILUC objection 103 RFA also complained that corn based ethanol scored only a 21 reduction noting that without ILUC corn ethanol achieves a 52 GHG reduction 103 104 RFA also objected that Brazilian sugarcane ethanol benefited disproportionally because EPA s revisions lowered the initially equal ILUC estimates by half for corn and 93 for sugarcane 105 Several Midwestern lawmakers commented that they continued to oppose EPA s consideration of the dicey science of indirect land use that punishes domestic fuels 104 House Agriculture Chairman Collin Peterson said to think that we can credibly measure the impact of international indirect land use is completely unrealistic and I will continue to push for legislation that prevents unreliable methods and unfair standards from burdening the biofuels industry 104 EPA Administrator Lisa P Jackson commented that the agency did not back down from considering land use in its final rules but the agency took new information into account that led to a more favorable calculation for ethanol 104 She cited new science and better data on crop yield and productivity more information on co products that could be produced from advanced biofuels and expanded land use data for 160 countries instead of the 40 considered in the proposed rule 104 Europe Edit As of 2010 European Union and United Kingdom regulators had recognized the need to take ILUC into account but had not determined the most appropriate methodology UK Renewable Transport Fuel Obligation Edit See also Renewable transport fuel obligation The UK Renewable Transport Fuel Obligation RTFO program requires fuel suppliers to report direct impacts and asked the Renewable Fuels Agency RFA to report potential indirect impacts including ILUC and commodity price changes 14 The RFA s July 2008 Gallager Review mentioned several risks regarding biofuels and required feedstock production to avoid agricultural land that would otherwise be used for food production despite concluding that quantification of GHG emissions from indirect land use change requires subjective assumptions and contains considerable uncertainty 41 Some environmental groups argued that emissions from ILUC were not being taken into account and could be creating more emissions 106 107 108 European Union Edit See also Directive on the Promotion of the use of biofuels and other renewable fuels for transport On December 17 2008 the European Parliament approved the Renewable Energy Sources Directive COM 2008 19 and amendments to the Fuel Quality Directive Directive 2009 30 109 which included sustainability criteria for biofuels and mandated consideration of ILUC The Directive established a 10 biofuel target A separate Fuel Quality Directive set the EU s Low Carbon Fuel Standard requiring a 6 reduction in GHG intensity of EU transport fuels by 2020 The legislation ordered the European Commission to develop a methodology to factor in GHG emissions from ILUC by December 31 2010 based on the best available scientific evidence 42 54 110 In the meantime the European Parliament defined lands that were ineligible for producing biofuel feedstocks for the purpose of the Directives This category included wetlands and continuously forested areas with canopy cover of more than 30 percent or cover between 10 and 30 percent given evidence that its existing carbon stock was low enough to justify conversion 42 The Commission subsequently published terms of reference for three ILUC modeling exercises one using a General Equilibrium model 111 one using a Partial Equilibrium model 112 and one comparing other global modeling exercises 113 It also consulted on a limited range of high level options for addressing ILUC 114 to which 17 countries 115 and 59 organizations responded 116 The United Nations Special Rapporteur on the Right to Food and several environmental organizations complained that the 2008 safeguards were inadequate 117 118 119 120 UNICA called for regulators to establish an empirical and globally accepted methodology to consider ILUC with the participation of researchers and scientists from biofuel crop producing countries 121 In 2010 some NGOs accused the European Commission of lacking transparency given its reluctance to release documents relating to the ILUC work 122 In March 2010 the Partial and General Equilibrium Modelling results were made available with the disclaimer that the EC had not adopted the views contained in the materials 123 These indicate that a 1 25 increase in EU biofuel consumption would require around 5 000 000 hectares 12 000 000 acres of land globally 124 The scenarios for varied from 5 6 to 8 6 of road transport fuels The study found that ILUC effects offset part of the emission benefits and that above the 5 6 threshold ILUC emissions increase rapidly increase 125 126 For the expected scenario of 5 6 by 2020 the study estimated that biodiesel production increases would be mostly domestic while bioethanol production would take place mainly in Brazil regardless of EU duties 125 The analysis concluded that eliminating trade barriers would further reduce emissions because the EU would import more from Brazil 124 Under this scenario direct emission savings from biofuels are estimated at 18 Mt CO2 additional emissions from ILUC at 5 3 Mt CO2 mostly in Brazil resulting in a global net balance of nearly 13 Mt CO2 savings in a 20 years horizon 125 The study also found that ILUC emissions were much greater for biodiesel from vegetable oil and estimated that in 2020 even at the 5 6 level were over half the greenhouse gas emissions from diesel 125 126 As part of the announcement the Commission stated that it would publish a report on ILUC by the end of 2010 127 Certification system Edit On June 10 2010 the EC announced its decision to set up certification schemes for biofuels including imports as part of the Renewable Energy Directive The Commission encouraged E U nations industry and NGOs to set up voluntary certification schemes 128 129 EC figures for 2007 showed that 26 of biodiesel and 31 of bioethanol used in the E U was imported mainly from Brazil and the United States 130 Reactions Edit UNICA welcomed the EU efforts to engage independent experts in its assessments but requested that improvements because the report currently contains a certain number of inaccuracies so once these are corrected we anticipate even higher benefits resulting from the use of Brazilian sugarcane ethanol 131 UNICA highlighted the fact that the report assumed land expansion that does not take into consideration the agro ecological zoning for sugarcane in Brazil which prevents cane from expanding into any type of native vegetation 131 Critics said the 10 figure was reduced to 5 6 of transport fuels partly by exaggerating the contribution of electric vehicles EV in 2020 as the study assumed EVs would represent 20 of new car sales two and six times the car industry s own estimate 132 They also claimed the study exaggerates to around 45 percent the contribution of bioethanol the greenest of all biofuels and consequently downplays the worst impacts of biodiesel 132 Environmental groups found that the measures are too weak to halt a dramatic increase in deforestation 130 133 According to Greenpeace indirect land use change impacts of biofuel production still are not properly addressed which for them was the most dangerous problem of biofuels 133 Industry representatives welcomed the certification system and some dismissed concerns regarding the lack of land use criteria 130 134 135 UNICA and other industry groups wanted the gaps in the rules filled to provide a clear operating framework 134 135 The negotiations between the European Parliament and the Council of European Ministers continue A deal is not foreseen before 2014 136 See also Edit Renewable energy portal Energy portal Environment portalBiodiesel Biofuels by region Carbon emissions reporting Carbon footprint Carbon leakage Deforestation in Brazil Environmental effects of biodiesel Ethanol fuel Food vs fuel Issues relating to biofuels Land use land use change and forestry Life cycle assessment Low carbon fuel standardReferences Edit a b c d e f g Timothy Searchinger et al 2008 02 29 Use of U S Croplands for Biofuels Increases Greenhouse Gases Through Emissions from Land Use Change Science 319 5867 1238 1240 Bibcode 2008Sci 319 1238S doi 10 1126 science 1151861 PMID 18258860 S2CID 52810681 Originally published online in Science Express on 7 February 2008 available here Archived 2009 12 11 at the Wayback Machine a b c d e f Michael Wang Zia Haq 2008 03 14 Letter to Science about Searchinger et al article PDF Argonne National Laboratory Archived from the original PDF on 2013 02 15 Retrieved 2009 06 07 The published version on Science Letters is included in Searchinger E Letter responses 2008 08 12 a b Gnansounou et al March 2008 Accounting for indirect land use changes in GHG balances of biofuels Review of current approaches PDF Ecole Polytechnique Federale de Lausanne Retrieved 2009 06 07 Working Paper REF 437 101 a b c Alexander E Farrell 2008 02 13 Better biofuels before more biofuels San Francisco Chronicle Retrieved 2009 06 07 Donald Sawyer 2008 05 27 Climate change biofuels and eco social impacts in the Brazilian Amazon and Cerrado Philosophical Transactions of the Royal Society 363 1498 1747 1752 doi 10 1098 rstb 2007 0030 PMC 2373893 PMID 18267903 Published on line 2008 02 11 Naylor et al November 2007 The Ripple Effect Biofuels Food Security and the Environment Environment Retrieved 2009 06 07 a b Renton Righelato Dominick V Spracklen 2007 08 17 Carbon Mitigation by Biofuels or by Saving and Restoring Forests Science 317 5840 902 doi 10 1126 science 1141361 PMID 17702929 S2CID 40785300 a b Farrel Plevin RJ Turner BT Jones AD O Hare M Kammen DM et al 2006 01 27 Ethanol Can Contribute to Energy and Environmental Goals Science 311 5760 506 508 Bibcode 2006Sci 311 506F doi 10 1126 science 1121416 PMID 16439656 S2CID 16061891 a b c d e f g Sperling Daniel Deborah Gordon 2009 Two billion cars driving toward sustainability Oxford University Press New York pp 98 99 ISBN 978 0 19 537664 7 For more detail see also the Notes 27 and 28 for Chapter 4 pp 272 a b Goettemoeller Jeffrey Adrian Goettemoeller 2007 Sustainable Ethanol Biofuels Biorefineries Cellulosic Biomass Flex Fuel Vehicles and Sustainable Farming for Energy Independence Prairie Oak Publishing Maryville Missouri pp 40 41 ISBN 978 0 9786293 0 4 a b Michael Wang Updated Energy and Greenhouse Gas Emission Results of Fuel Ethanol PDF Center for Transportation Research Argonne National Laboratory Archived from the original PDF on 2013 02 15 Retrieved 2009 06 07 Presented at the 15th International Symposium on Alcohol Fuels San Diego California a b c Michael Wang Updated Energy and Greenhouse Gas Emission Results of Fuel Ethanol PDF Center for Transportation Research Argonne National Laboratory Archived from the original PDF on 2013 02 16 Retrieved 2009 06 07 This is a public presentation of Michael Wang 2005 paper summarizing the results of the ANL study a b Macedo Isaias M Lima Verde Leal and J Azevedo Ramos da Silva 2004 Assessment of greenhouse gas emissions in the production and use of fuel ethanol in Brazil PDF Secretariat of the Environment Government of the State of Sao Paulo Archived from the original PDF on 2008 05 28 Retrieved 2008 05 09 a b c d e Carbon and Sustainability Reporting Within the Renewable Transport Fuel Obligation PDF Department of Transport United Kingdom January 2008 Archived from the original PDF on June 25 2008 Retrieved 2009 04 25 a b Bryan Walsh 2008 02 14 The Trouble With Biofuels Time Magazine Archived from the original on November 3 2012 Retrieved 2009 06 07 a b Michael Grunwald 2008 03 27 The Clean Energy Scam Time Magazine Archived from the original on March 30 2008 Retrieved 2009 06 07 This article was the cover story of the April 7 2008 print edition entitled The Clean Energy Myth a b Joe Jobe 2008 04 10 The Debate on Clean Energy Time Magazine Archived from the original on April 15 2008 Retrieved 2009 06 07 Reply letter by Joe Jobe CEO of the National Biodiesel Board published in the Inbox section in Time s April 21 issue a b Tom Zeller Jr 2008 11 03 The Biofuel Debate Good Bad or Too Soon to Tell The New York Times Retrieved 2009 06 07 a b Renewable Fuels Association 2008 11 08 Executive Summary Understanding Land Use Change and U S Ethanol Expansion PDF The New York Times Retrieved 2009 06 07 Biofuel Companies Question ARB s Inclusion of Indirect Effects in Low Carbon Fuel Standard Green Car Congress 2008 10 24 Retrieved 2009 06 07 a b Stephen Power 2008 11 11 If a Tree Falls in the Forest Are Biofuels To Blame It s Not Easy Being Green The Wall Street Journal Retrieved 2009 06 07 a b c David R Baker 2009 04 22 State readies stringent fuel standards San Francisco Chronicle Retrieved 2009 06 07 Maized and confused Does ethanol in Iowa cause deforestation in Brazil The Economist 2009 08 10 Retrieved 2009 08 12 Kurt Kleiner 2007 12 12 The backlash against biofuels Science 1 801 9 11 doi 10 1038 climate 2007 71 Focus Feature published online a b Timothy Searchinger 2008 08 12 E Letter response to M Wang and Z Haq s E Letter Ethanol s Effects on Greenhouse Gas Emissions Science 319 5867 Retrieved 2009 06 07 permanent dead link a b c Keith L Kline Virginia H Dale 2008 07 11 Biofuels Effects on Land and Fire PDF Letters to Science Archived from the original PDF on 2008 12 04 Retrieved 2009 06 11 This reference also includes Timothy Searching and Joseph Fargione responses to Kline and Dale Science Vol 321 Public letter to Mary D Nichols Chairman California Air Resources Board PDF BioenergyWiki 2008 06 24 Archived from the original PDF on 2011 07 23 Retrieved 2009 06 07 Public letter to Mary D Nichols Chairman California Air Resources Board PDF Union of Concerned Scientists 2009 04 21 Retrieved 2009 06 07 Group of Scientists and Economists Urge Inclusion of Indirect Land Use Change Effects for Biofuels and All Transportation Fuels in California LCFS Green Car Congress 2009 04 21 Retrieved 2009 06 07 Maized and confused The Economist 2009 08 10 Retrieved 2009 08 10 New Fuels Alliance 2008 10 23 Letter to Mary D Nichols CARB Chairman PDF California Air Resources Board Retrieved 2009 06 07 a b UNICA 2009 04 16 UNICA s Comments to CARB on Sugarcane Ethanol PDF California Air Resources Board Retrieved 2009 06 07 Renewable Fuel Standard Program RFS2 Notice of Proposed Rulemaking U S Environmental Protection Agency 2009 05 05 Retrieved 2009 05 06 a b c Jim Tankersley 2009 05 06 New standards could cut tax breaks for corn based ethanol Los Angeles Times Retrieved 2009 05 06 a b Suzanne Goldenberg 2009 05 06 Barack Obama s 1 8bn vision of greener biofuel The Guardian London Retrieved 2009 05 06 a b c Steven Mufson Juliet Eilperin 2009 05 06 EPA Proposes Changes To Biofuel Regulations The Washington Post Retrieved 2009 05 06 a b Jennifer Kho 2009 05 05 Corn Ethanol Crew Cries Foul Over EPA Emissions Ruling earth2tech com Archived from the original on 2009 05 09 Retrieved 2009 05 06 a b UNICA Press Release 2009 05 05 Sugarcane Ethanol Industry Eager to Implement U S Renewable Fuel Standard National Press Release Retrieved 2009 05 06 a b Renewable Fuel Standard Program RFS2 Final Rule U S Environmental Protection Agency 2010 02 03 Retrieved 2010 02 09 a b c Greenhouse Gas Reduction Thresholds U S Environmental Protection Agency 2010 02 03 Retrieved 2010 02 09 a b Ed Gallagher July 2008 The Gallagher Review of the indirect effects of biofuels production PDF Renewable Fuels Agency Archived from the original PDF on 2009 10 18 Retrieved 2009 06 09 See Chapter 2 The effect of land use change on GHG savings from biofuels a b c European Parliament 2008 12 17 Texts adopted Wednesday 17 December 2008 Monitoring and reduction of greenhouse gas emissions from fuels Retrieved 2009 06 09 For ILUC see Whereas items 11 through 18 Mark A Delucchi May 2006 Lifecycle Analyses of Biofuels Draft Report PDF University of California Davis Retrieved 2009 06 11 Institute of Transportation Studies UCD ITS RR 06 08 See pp 13 14 Timothy D Searchinger Retrieved April 5 2013 a b Searchinger et al 2008 Supporting Materials for Use of U S Croplands for Biofuels Increases Greenhouse Gases Through Emissions from Land Use Change PDF Princeton University Archived from the original PDF on 2011 10 10 Retrieved 2009 06 11 Data taken from Table 1B pp 21 a b Fargione Hill J Tilman D Polasky S Hawthorne P et al 2008 02 29 Land Clearing and the Biofuel Carbon Debt Science 319 5867 1235 1238 Bibcode 2008Sci 319 1235F doi 10 1126 science 1152747 PMID 18258862 S2CID 206510225 Originally published online in Science Express on 7 February 2008 available here Archived 2010 10 29 at the Wayback Machine For example using Searchinger s indirect analysis approach you can prove that increasing the mileage standards for vehicles contributes to global warming Consider Every gallon of gasoline not used by a motorist saves him 3 50 at today s prices He can use that money to buy other things For example at current prices about 80 per ton 3 50 could buy him about 90 pounds of coal Burning that coal would obviously produce far more carbon dioxide emissions than burning the 6 pounds of carbon in one gallon of gas So higher mileage standards for cars cause global warming Q E D in Zubrin Robert 2012 Merchants of Despair Radical Environmentalists Criminal Pseudo Scientists and the Fatal Cult of Antihumanism New Atlantis Books ISBN 978 1594034763 a b Timothy Searchinger 2008 02 26 Response to New Fuels Alliance and DOE Analysts Criticisms of Science Studies of Greenhouse Gases and Biofuels PDF BioenergyWiki Archived from the original PDF on 2008 05 16 Retrieved 2009 06 11 New Fuels Alliance Statement in Response to Science Articles on Biofuels PDF Renewable Fuels Association Archived from the original PDF on July 27 2008 Retrieved 2009 06 11 a b c d Lapola Schaldach R Alcamo J Bondeau A Koch J Koelking C Priess JA et al 2010 02 08 Indirect land use changes can overcome carbon savings from biofuels in Brazil Proceedings of the National Academy of Sciences 107 8 3388 93 Bibcode 2010PNAS 107 3388L doi 10 1073 pnas 0907318107 PMC 2840431 PMID 20142492 Published online before print a b c d Rhett A Butler 2010 02 08 Amazon rainforest will bear cost of biofuel policies in Brazil Mongabay com Retrieved 2010 02 09 Philip Brasher 2010 02 08 Brazil biofuels land use issue Des Moines Register Archived from the original on 2016 05 16 Retrieved 2010 02 09 a b Arima E Richards P Walker R and Caldas M M 2011 05 24 Statistical Confirmation of Indirect Land Use Change in the Brazilian Amazon Environmental Research Letters 6 1498 1747 1752 Bibcode 2011ERL 6b4010A doi 10 1088 1748 9326 6 2 024010 a href Template Cite journal html title Template Cite journal cite journal a CS1 maint multiple names authors list link a b c d e Proposed Regulation to Implement the Low Carbon Fuel Standard Volume I Staff Report Initial Statement of Reasons PDF California Air Resources Board 2009 03 05 Retrieved 2009 04 26 a b Draft Attachment B Public Hearing to Consider Adoption of a Proposed Regulation to Implement the Low Carbon Fuel Standard Staff s Suggested Modifications to the Original Proposal PDF CARB 2003 04 23 Archived from the original PDF on 2009 06 13 Retrieved 2009 04 30 a b Wyatt Buchanan 2009 04 24 Air Resources Board moves to cut carbon use San Francisco Chronicle Retrieved 2009 04 25 a b California Low Carbon Fuels Mandate The New York Times The Associated Press 2009 04 24 Retrieved 2009 05 21 Air Resources Board Resolution 09 31 April 23 2009 PDF California Air Resources Board 2009 04 23 Retrieved 2009 05 31 Final resolution pp 8 Comment Log for Low Carbon Fuel Standard LCFS09 California Air Resources Board Retrieved 2009 04 28 All letters and attachments are posted for public view of this site Public letter to Mary D Nichols Chairman California Air Resources Board PDF BioenergyWiki 2008 06 24 Archived from the original PDF on 2011 07 23 Retrieved 2009 04 28 a b Biofuel Companies Question ARB s Inclusion of Indirect Effects in Low Carbon Fuel Standard Green Car Congress 2008 10 24 Retrieved 2009 04 28 Leading Advanced Biofuel Companies Researchers Investors Call on Air Resources Board to Reconsider Draft Low Carbon Fuel Regulations PDF New Fuels Alliance 2008 10 23 Archived from the original PDF on 2009 05 09 Retrieved 2009 04 26 Public letter to Mary D Nichols Chairman California Air Resources Board PDF Union of Concerned Scientists 2009 04 21 Retrieved 2009 04 26 Group of Scientists and Economists Urge Inclusion of Indirect Land Use Change Effects for Biofuels and All Transportation 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Sugarcane Ethanol Passes Critical Test in California World Wire Archived from the original on 2009 04 26 Retrieved 2009 04 25 UNICA 2009 04 17 UNICA Sugarcane Ethanol Meets CARB Low Carbon Fuel Standard Biofuels Journal Retrieved 2009 04 29 Power Stephen 2009 12 24 Ethanol Groups Sue California Over Low Carbon Rule The Wall Street Journal Retrieved 2009 12 29 Ethanol Groups File Suit Challenging Constitutionality of California Low Carbon Fuel Standard Green Car Congress 2009 12 25 Retrieved 2009 12 29 Ethanol Groups Challenge Constitutionality of California LCFS Renewable Fuels Association 2009 12 24 Retrieved 2009 12 29 a b c d e EPA Lifecycle Analysis of Greenhouse Gas Emissions from Renewable Fuels Technical Highlights PDF Retrieved 2009 06 07 See Table 1 a b c d e EPA Proposes New Regulations for the National Renewable Fuel Standard Program for 2010 and Beyond U S Environmental Protection Agency 2009 05 05 Retrieved 2009 06 16 a b c d e EPA Proposes New Regulations for Renewable Fuel Standard to Implement Requirements of EISA GHG Reduction and Indirect Land Use Change Effects Included Green Car Congress 2009 05 05 Retrieved 2009 06 16 Renewable Fuel Standard Program RFS2 Notice of Proposed Rulemaking U S Environmental Protection Agency May 2009 Retrieved 2009 06 16 President Obama Announces Steps to Support Sustainable Energy Options Departments of Agriculture and Energy Environmental Protection Agency to Lead Efforts whitehouse gov 2009 05 05 Retrieved 2009 05 05 via National Archives Matthew L Wald 2009 05 05 White House Steps Up Support for Biofuels The New York Times Retrieved 2009 05 05 Ben Geman 2009 05 05 Obama Administration Prepares to Push Biofuels Scientific American Retrieved 2009 05 05 Kate Galbraith 2009 07 09 Biodiesel Makers Lash Out at E P A Rule The New York Times Retrieved 2009 06 16 EPA Confirms Most Corn Ethanol Worsens Global Warming Pollution Friends of the Earth 2009 05 05 Archived from the original on 2009 05 08 Retrieved 2009 06 17 EPA s RFS Proposal One Step Forward and Another Step Back PDF Clean Air Task Force 2009 05 05 Archived from the original PDF on February 15 2010 Retrieved 2009 06 17 Vincent Carroll 2009 05 09 Coddling the ethanol industry The Denver Post Retrieved 2009 06 16 a b c Difficult EPA Public Hearing on Biofuels Mandate SugarcaneBlog com 2009 06 09 Retrieved 2009 06 17 Biofuel Producers Give EPA an Earful on Renewable Fuel Standard Environment News Service 2009 06 09 Retrieved 2009 06 17 BIO asks EPA to maintain flexibility in life cycle analysis for RFS Biomass Magazine 2009 06 06 Retrieved 2009 06 17 Public Hearing on EPA s Proposed RFS Rule Renewable Fuels Association 2009 06 09 Retrieved 2009 06 17 Nick Snow 2009 06 09 API NPRA ask EPA to consider delay of RFS 2 implementation Oil amp Gas Journal Retrieved 2009 06 17 Jim Lane 2009 06 29 Climate change bill passes with five year punt on indirect land use change Biofuels Digest Archived from the original on 2011 08 09 Retrieved 2009 07 05 Kirsten Korosec 2009 06 27 Climate Change Bill Passes on Razor Thin Margin Tougher Battle Lies Ahead BNET Energy Archived from the original on July 3 2009 Retrieved 2009 07 05 House passes historic climate bill Renewable Fuels Association 2009 06 26 Retrieved 2009 07 05 Bravender Robin Geman Ben Luntz Taryn 2009 06 19 Farm Interests Use EPA Spending Bill to Fight Climate Regs The New York Times Retrieved 2009 06 26 Compromise Amendment to Waxman Markey Bill Prohibits EPA From Using Indirect Land Use Change Metrics on Biofuels for 5 Years While National Academies Research the Issue Green Car Congress 2009 06 26 Retrieved 2009 06 26 A squeaker with more to come The Economist 2009 07 02 Retrieved 2009 07 05 John M Broder 2009 06 30 With Something for Everyone Climate Bill Passed The New York Times Retrieved 2009 07 05 a b c Renewable Fuel Standard Program RFS2 Regulatory Impact Analysis PDF U S Environmental Protection Agency February 2010 Archived from the original PDF on February 2 2011 Retrieved 2010 02 12 See pp 480 and 489 and Tables 2 6 1 to 2 6 11 James Kanter 2010 02 11 Questions About Biofuels Environmental Costs Could Alter Europe s Policies The New York Times Retrieved 2010 02 14 Agencia ambiental dos EUA reconhece etanol de cana como biocombustivel avancado in Portuguese UNICA 2010 02 03 Archived from the original on 2011 07 06 Retrieved 2010 02 14 EPA Deems Sugarcane Ethanol an Advanced Biofuel DOMESTICFUEL com 2010 02 04 Retrieved 2010 02 14 a b RFS Rules Workable ILUC Inclusion Still Problematic Renewable Fuels Association 2010 02 03 Retrieved 2010 02 14 a b c d e Allison Winter 2010 02 04 New Biofuels Regs Could Still Face Fight From Capitol Hill The New York Times Retrieved 2010 02 16 Issue Brief Summary of RFS2 Final Rule PDF Renewable Fuels Association 2010 02 04 Archived from the original PDF on February 15 2010 Retrieved 2010 02 14 Alok Jha 2009 04 15 UK biofuels target creating more emissions environmentalists claim The Guardian London Retrieved 2009 06 16 Green fuels produce twice as much carbon as fossil fuels The Daily Telegraph London 2009 04 15 Archived from the original on 2009 04 20 Retrieved 2009 06 16 Petrol must now include biofuels BBC News 2008 04 15 Retrieved 2009 06 16 Directive 2009 30 EC of the European Parliament and of the Council of 23 April 2009 EUR Lex Retrieved 2010 01 29 Europe to Study Indirect Land Use Biofuels and Climate Change 2008 12 31 Retrieved 2009 06 13 Annex A Terms of Reference The indirect land use change impact of biofuels PDF European Commission 2009 06 29 Retrieved 2010 01 29 Annex 1 Terms of Reference PDF European Commission Retrieved 2010 01 29 Terms of Reference Administrative arrangement between JRC and DG ENV on Indirect Land Use Change emissions from biofuels PDF European Commission Retrieved 2010 01 29 Indirect land use change Possible elements of a policy approach preparatory draft for stakeholder expert comments PDF European Commission Retrieved 2010 01 29 ILUC Consultation comments by country European Commission Retrieved 2010 01 29 Download zip file with comments from 17 countries in PDF format ILUC Consultation comments by organisation European Commission Retrieved 2010 01 29 Download zip file with comments from 59 organisations in PDF format James Kanter 2009 06 12 Biofuels and Land Grabs in Poor Nations The New York Times Retrieved 2009 06 13 WWF European Policy Office EU Renewable Energy Directive 2008 Summary of WWF position PDF World Wide Fund for Nature Retrieved 2009 06 07 a href Template Cite web html title Template Cite web cite web a author has generic name help Final Biofuel Directive limits impact on wetlands Wetlands International Archived from the original on 2010 07 04 Retrieved 2009 06 13 Inadequacy of the Renewable Energy Directive BirdLife International Retrieved 2009 06 13 UNICA calls for globally harmonized methodologies to assess Indirect Land Use Change in IEA conference in Rotterdam UNICA 2009 05 28 Retrieved 2009 06 17 Green groups sue Commission over withheld biofuels docs Transport amp Environment 2010 03 09 Retrieved 2010 03 29 Renewable Energy Studies Land Use Change European Energy Commission 2010 03 26 Retrieved 2010 03 29 a b Biofuels and global trade study goes online European Commission Chief Economist March 2010 Retrieved 2010 03 29 a b c d International Food Policy Research Institute IFPRI 2010 03 25 Global Trade and Environmental Impact Study of the EU Biofuels Mandate PDF Directorate General for Trade of the European Commission Archived from the original PDF on 2011 01 13 Retrieved 2010 03 29 a href Template Cite web html title Template Cite web cite web a author has generic name help a b Analysis Finds That First Generation Biofuel Use of Up to 5 6 in EU Road Transport Fuels Delivers Net GHG Emissions Benefits After Factoring in Indirect Land Use Change Green Car Congress 2010 03 26 Retrieved 2010 03 29 Commission sets up system for certifying sustainable biofuels MEMO 10 247 European Commission 2010 06 10 Retrieved 2010 06 13 Commission sets up system for certifying sustainable biofuels European Commission 2010 06 10 Retrieved 2010 06 13 European Commission Sets Up System for Certifying Sustainable Biofuels Green Car Congress 2010 06 10 Retrieved 2010 06 13 a b c Mark Kinver 2010 06 10 EU biofuels need to be certified for sustainability EU biofuels need to be certified for sustainability BBC News Retrieved 2010 06 13 a b Report highlights benefits of Brazilian sugarcane ethanol confirms highest emissions savings UNICA 2010 03 29 Retrieved 2010 03 29 a b EU report signals U turn on biofuels target AlertNet Reuters 2010 03 25 Retrieved 2010 03 29 a b Broken biofuel policies still driving rainforest destruction Greenpeace European unit 2010 06 10 Retrieved 2010 06 13 a b James Kanter 2010 06 11 Parsing Europe s New Biofuel Rules The New York Times Retrieved 2010 06 13 a b Platts Commodity News 2010 06 11 Trade bodies welcome EU biofuels rules but call for more guidance UNICA Brazil Archived from the original on 2011 07 06 Retrieved 2010 06 13 EU Biofuels amp ILUC No deal before 2014 says Irish EU Presidency Archived from the original on 2013 11 03 Retrieved 2013 11 02 External links EditAmendments to the European Renewable Energy Sources Directive approved December 17 2008 CARB Detailed California modified GREET pathway for U S corn ethanol February 27 2009 version 2 1 CARB Detailed California modified GREET pathway for Brazilian sugarcane ethanol February 27 2009 version 2 1 CARB Proposed Regulation to Implement the Low Carbon Fuel Standard approved April 23 2009 Retrieved from https en wikipedia org w index php title Indirect land use change impacts of biofuels amp oldid 1137799966, wikipedia, wiki, book, books, library,

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