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Friday, November 25, 2022

Low-carbon fuel standard

A low-carbon fuel standard (LCFS) is an emissions trading rule designed to reduce the average carbon intensity of transportation fuels in a given jurisdiction, as compared to conventional petroleum fuels, such as gasoline and diesel. The most common methods for reducing transportation carbon emissions are supplying electricity to electric vehicles, supplying hydrogen fuel to fuel cell vehicles and blending biofuels, such as ethanol, biodiesel, renewable diesel, and renewable natural gas into fossil fuels. The main purpose of a low-carbon fuel standard is to decrease carbon dioxide emissions associated with vehicles powered by various types of internal combustion engines while also considering the entire life cycle ("well to wheels"), in order to reduce the carbon footprint of transportation.

The first low-carbon fuel standard mandate in the world was enacted by California in 2007, with specific eligibility criteria defined by the California Air Resources Board (CARB) in April 2009 but taking effect in January 2011. Similar legislation was approved in British Columbia in April 2008, and by European Union which proposed its legislation in January 2007 and which was adopted in December 2008. The United Kingdom is implementing its Renewable Transport Fuel Obligation Program, which also applies the concept of low-carbon fuels.

Several bills have been proposed in the United States for similar low-carbon fuel regulation at a national level but with less stringent standards than California. As of early 2010 none have been approved. The U.S. Environmental Protection Agency (EPA) issued its final rule regarding the expanded Renewable Fuel Standard (RFS2) for 2010 and beyond on February 3, 2010. This ruling, as mandated by the Energy Independence and Security Act of 2007 (EISA), included direct emissions and significant indirect emissions from land use changes.

California Low-Carbon Fuel Standard

Californian Governor Arnold Schwarzenegger issued Executive Order S-1-07 on January 19, 2007, to enact a low-carbon fuel standard (LCFS). The LCFS requires oil refineries and distributors to ensure that the mix of fuel they sell in the Californian market meets the established declining targets for greenhouse gas (GHG) emissions measured in CO2-equivalent grams per unit of fuel energy sold for transport purposes. The LCFS directive calls for a reduction of at least 10 percent in the carbon intensity of California's transportation fuels by 2020. These reductions include not only tailpipe emissions but also all other associated emissions from production, distribution and use of transport fuels within the state. Therefore, California LCFS considers the fuel's full life cycle, also known as the "well to wheels" or "seed to wheels" efficiency of transport fuels. The standard is also aimed to reduce the state's dependence on petroleum, create a market for clean transportation technology, and stimulate the production and use of alternative, low-carbon fuels in California.

The LCFS is a mix of command and control regulation and emissions trading, as it will use market-based mechanisms that allow providers to choose how they will reduce emissions while responding to consumer demand. Some believe that oil companies could opt for several actions to comply. For example, they state that refiners and producers could improve the efficiency of the refineries and upstream production, or may purchase and blend more low-carbon ethanol into gasoline products, or purchase credits from electric utilities supplying low carbon electrons to electric passenger vehicles, or diversifying and selling low carbon hydrogen for use by vehicles as a product, or any new strategy as the standard is being designed. The California Global Warming Solutions Act of 2006 authorized the establishment of emissions trading in California, with rules to be adopted by 2010, and taking effect no later than January 2012.

Regulatory proceedings

In accordance to the California Global Warming Solutions Act of 2006 and the Governor's Directive, the California Air Resources Board is the agency responsible for developing the "Low-Carbon Fuel Standard Program", and it was directed to initiate the regulatory proceedings to establish and implement the LCFS." CARB identified the LCFS as an early action item with a regulation to be adopted and implemented by 2010. Also Executive Order S-1-07 ordered the California Environmental Protection Agency to coordinate activities between the University of California, the California Energy Commission and other state agencies to develop and propose a draft compliance schedule to meet the 2020 target.

As mandated by the Executive Order, a University of California team, led by Daniel Sperling of UC Davis and the late Alexander E. Farrell (UC Berkeley), developed two reports that established the technical feasibility of an LCFS, proposed the methodology to calculate the full life cycle GHG emissions from all fuels sold in the state, identified technical and policy issues, and provided a number of specific recommendations, thus providing an initial framework for the development of CARB's LCFS. This study was presented by Governor Schwarzenegger in May 2007 and they were the backbone of CARB's initial efforts to develop the LCFS, even though not all of the specific recommendations were incorporated in the final LCFS staff's proposed regulation.

Public consultation process

During 2008 and until the April 2009 LCFS ruling, CARB published in its website all technical reports prepared by its staff and collaborators regarding the definition and calculations related to the proposed LCFS regulation, conducted 16 public workshops, and also submitted its studies for external peer review. Before the April 23, 2009 ruling, the Board held a 45-day public hearing that received 229 comments, 21 of which were presented during the Board Hearing.

Controversy about indirect land use impacts

Among relevant and controversial comments submitted to CARB as public letters, on June 24, 2008, a group of 27 scientists and researchers from a number of universities and national laboratories, expressed their concerns arguing that there "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." With a similar opposing position, on October 23, 2008, a letter submitted to CARB by the New Fuels Alliance, representing more than two-dozen advanced biofuel companies, researchers and investors, questioned the Board intention to include indirect land use change (ILUC). In another public letter just before the ruling meeting, more than 170 scientists and economists sent a letter to CARB, urging it to account for GHG emissions from indirect land use change for biofuels and all other transportation fuels. They argued that "...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."

2009 Ruling

On April 23, 2009, CARB approved the specific rules and carbon intensity reference values for the LCFS that will go into effect on January 1, 2011. The technical proposal was approved without modifications by a 9–1 vote, to set the 2020 maximum carbon intensity reference value for gasoline to 86 grams of carbon dioxide equivalent released per megajoule of energy produced. One standard was established for gasoline and the alternative fuels that can replace it, and a second similar standard is set for diesel fuel and its replacements. The regulation is based on an average declining standard of carbon intensity that is expected to achieve 16 million metric tons of greenhouse gas emission reductions by 2020. CARB expects the new generation of fuels to come from the development of technology that uses cellulosic ethanol from algae, wood, agricultural waste such as straw and switchgrass, and also natural gas from municipal solid waste. They also expect the standard to drive the availability of plug-in hybrid, battery electric and fuel-cell powered cars while promoting investment in infrastructure for electric charging stations and hydrogen fueling stations.

The ruling is controversial. Representatives of the US ethanol industry complained that this rule overstates the environmental effects of corn ethanol, and also criticized the inclusion of indirect effects of land-use changes as an unfair penalty to home-made corn ethanol because deforestation in the developing world is being tied to US ethanol production. The initial reference value set for 2011 for LCFS means that Mid-west corn ethanol will not meet the California standard unless current carbon intensity is reduced. Oil industry representatives complained that there is a cost associated to the new standard, as the LCFS will limit the use of corn ethanol blended in gasoline, thus leaving oil refiners with few available and viable options, such as sugarcane ethanol from Brazil, but this option means paying costly U.S. import tariffs. CARB officials and environmentalists reject such scenario because they think there will be plenty of time and economic incentive to developed inexpensive biofuels, hydrogen-based fuels, even ethanol from such cellulosic materials, or new ways to make ethanol out of corn with a smaller carbon footprint.

Brazilian ethanol producers (UNICA), though they welcomed the ruling as they consider their sugarcane ethanol have passed a critical test and expect their biofuel to enter the California market in the future, UNICA also urged CARB to update the data and assumptions used, which according to them, is excessively penalizing their ethanol and is not reflecting the technology and agricultural practices currently in use in Brazil. UNICA disagreed with the assertion that indirect land-use changes can be accurately calculated with the current methodologies. Canadian officials also complained the standard could become an entry barrier to their Alberta oil sands, as producers will have to significantly reduce their emissions or purchase expensive credits from alternative energy producers in order for their non-conventional oil to be sold in California. They complained that the measure could be discriminating against Canadian oil sands crude as a high carbon intensity crude oil, while other heavy crude oils from other sources were not evaluated by CARB's studies.

The only Board member who voted against the ruling explained that he had "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 indirect land use change penalty. "They said the model was not good enough... to use at this time as a component part of such an historic new standard." CARB adopted only one main amendment to the staff proposal to bolster the standard review process, moving up the expected date of an expert working group to report on indirect land use change from January 2012 to January 2011. This change is expected to provide for a thoroughly review of the specific penalty for indirect land use change and correct it if possible. The CARB staff is also expected to report back to the Board on indirect impacts of other fuel pathways before the commencement of the standard in 2011.

Fuels were rated based on their carbon intensity, estimated in terms of the quantity of grams of carbon dioxide equivalent released for every megajoule of energy produced for their full life cycle, also referred to as the fuel pathway. Carbon intensity was estimated considering the direct carbon footprint for each fuel, and for biofuels the indirect land-use effects were also included. The resulting intensities for the main biofuels readily available are the following:

California carbon intensity values for gasoline and fuels that substitute for gasoline
(grams of carbon dioxide equivalent released per megajoule of energy produced)
Fuel type Carbon
intensity
Carbon intensity
including land-use
changes
Comments
Midwest ethanol 75.10 105.10 Mainly made from corn. Includes some of the plant's power coming from coal.
California gasoline 95.86 95.86 Gasohol with 10% ethanol.
CARB LCFS 2011 n/a 95.61 Maximum allowed in 2011 (initial). Might be reviewed as more studies are available.
CARB LCFS 2020 n/a 86.27 Maximum allowed by 2020. Might be reviewed as more studies are available.
California ethanol 50.70 80.70 Considers plant's power coming from natural gas.
Brazilian ethanol 27.40 73.40 Made from sugarcane and ship transport Brazil-California included
CNG: via pipeline 67.70 67.70 North American natural gas compressed in California.
CNG: landfill gas 11.26 11.26 Derived from landfills in California.
Note: the complete lifecycle analysis for these fuels and others considered such as cellulosic ethanol (farmed trees and forest waste), electricity (California average electricity mix),
hydrogen (gaseous hydrogen from North American natural gas) and biodiesel (soybean) are available at CARB's website (see Lifecycle Analysis)

The LCFS standards established in CARB's rulemaking will be periodically reviewed. The first formal review will occur by January 1, 2011. Additional reviews are expected to be conducted approximately every three years thereafter, or as necessary. The 2011 review will consider the status of efforts to develop low carbon fuels, the compliance schedule, updated technical information, and provide recommendations on metrics to address the sustainable production of low carbon fuels.

According to CARB's ruling, providers of transportation fuels must demonstrate that the mix of fuels they supply meet the LCFS intensity standards for each annual compliance period. They must report all fuels provided and track the fuels’ carbon intensity through a system of "credits" and "deficits." Credits are generated from fuels with lower carbon intensity than the standard. Deficits result from the use of fuels with higher carbon intensity than the standard. A fuel provider meets its compliance obligation by ensuring that amount of credits it earns (or otherwise acquires from another party) is equal to, or greater than, the deficits it has incurred. Credits and deficits are generally determined based on the amount of fuel sold, the carbon intensity of the fuel, and the efficiency by which a vehicle converts the fuel into usable energy. Credits may be banked and traded within the LCFS market to meet obligations.

Two "lookup tables" (similar to the one above) and its carbon intensity values are part of the regulation, one for gasoline and another for diesel. The carbon intensity values can only be amended or expanded by regulatory amendments, and the Board delegated to the Executive Officer the responsibility to conduct the necessary rulemaking hearings and take final action on any amendments, other than amending indirect land-use change values included in the lookup tables.

Latest Developments

California-Modified GREET

Pathways for Brazilian sugarcane ethanol
(grams of CO2 equivalent released per megajoule of energy produced)

Fuel type Carbon
intensity
Carbon intensity
including land-use
changes
Comments
Average Brazilian ethanol 27.40 73.40 Baseline pathway
Mechanized harvesting and
co-product bioelectricity
12.20 58.20 Scenario 1
Mechanized harvesting 20.40 66.40 Scenario 2
Note: for all scenarios indirect land use change effects are the same and CARB estimate is 46 gCO2e/MJ.

On July 20, 2009, CARB published a Notice of Public Availability of modified text and availability of additional documents regarding the April 2009 rule making (Resolution 09–31), open for public comment until August 19. The supporting documents and information added to the rule making record include new pathways for Liquefied Natural Gas (LNG) from several sources, Compressed Natural Gas (CNG) from dairy digester biogas, biodiesel produced in California from used cooking oil, renewable diesel produced in California from tallow (U.S. sourced), and two additional new pathways for Brazilian sugarcane ethanol which reflect best practices already implemented in some regions of the country.

The two additional scenarios for sugarcane ethanol were requested by the Board in order to account for improved harvesting practices and the export of electricity from sugarcane ethanol plants in Brazil using energy from bagasse. These two scenarios are not to be considered average for all of Brazilian ethanol but specific cases when such practices are adopted in Brazil. Scenario 1 considers mechanized harvesting of cane which is gradually replacing the traditional practice of burning straw before harvesting cane, and the sale of electricity (co-generated) from power plants that are capable of exporting additional energy beyond that required for processing in the plant (co-product credit). Scenario 2 only considers the export of electricity (co-product) from power plants capable of producing the additional electricity for export. The assumptions or values for the baseline pathway published in February 2009 are the same, including the estimates of indirect land use change for all Brazilian sugarcane scenarios.

In December 2009 the Renewable Fuels Association (RFA) and Growth Energy, two U.S. ethanol lobbying groups, filed a lawsuit in the Federal District Court in Fresno, California, challenging the constitutionality of the California Low Carbon Fuel Standard (LCFS). The two organizations argued that the LCFS violates both the Supremacy Clause and the Commerce Clause of the US Constitution, and "jeopardizes the nationwide market for ethanol". In a press release both associations announced that "If the United States is going to have a low carbon fuel standard, it must be based on sound science and it must be consistent with the U.S. Constitution..." and that "One state cannot dictate policy for all the others, yet that is precisely what California has aimed to do through a poorly conceived and, frankly, unconstitutional LCFS." Additional lawsuits against the California regulation were filed by refiners and truckers including Rocky Mountain Farmers Union; Redwood County Minnesota Corn and Soybean Growers; Penny Newman Grain, Inc.; Red Nederend; Fresno County Farm Bureau; Nisei Farmers League; California Dairy Campaign; National Petrochemical and Refiners Association; American Trucking Associations; Center for North American Energy Security; and the Consumer Energy Alliance.

In December 2011 a federal judge granted a preliminary injunction against the implementation of California's LCFS. In three separate rulings the judge rejected CARB's defense as he concluded that the state acted unconstitutionally and the regulation "impermissibly treads into the province and powers of our federal government, reaches beyond its boundaries to regulate activity wholly outside of its borders." CARB announced it intends to appeal the decision. The Ninth Circuit Court of Appeals issued a stay of the injunction on 23 April 2012 during the tendency of the litigation. In other words, the challenge to the constitutionality of the LCFS continues, but until it is resolved there is no bar on the CARB continuing to enforce the LCFS. (While the stay did not specifically authorize a return to the LCFS, CARB argued in its briefs before the Court that a stay would "permit the LCFS to go back into effect as though the injunction had never been issued". That is the approach currently taken by CARB and it continues to refine carbon intensity standards and applicability).

In 2011, a provision was added to the LCFS that allows refiners to receive credits for the deployment of innovative crude production technologies, such as carbon capture and sequestration or solar steam generation. Solar thermal enhanced oil recovery is a form of enhanced oil recovery (EOR), which is key to harvesting California's heavy crude. Currently, California uses EOR to help produce about 60% of its crude output. By using solar power instead of natural gas to create steam for EOR, solar steam generation reduces the amount of emissions produced during oil extraction, thus lowering the overall carbon intensity of crude. California currently has two solar EOR projects in operation, one in McKittrick, operated by LINN Energy (formerly Berry Petroleum) using enclosed trough technology from GlassPoint Solar, and another in Coalinga operated by Chevron Corporation using BrightSource Energy power tower technology.

CARB is currently considering an amendment to allow upstream operators to receive credits for deploying innovative crude production technologies.

In 2015, California's LCFS was re-adopted in order to address some of the issues in the original proposed standard. A number of the changes were made, including updated crude provisions, a new model used to be used to calculate carbon intensity, the establishment of a "Credit Clearance" process that would take effect at the end of the year should the LCFS credit market become too competitive, and other provisions.

In May 2016, the Seneca Solar Project became the first facility to start earning LCFS credits. Located in the North Midway Sunset oil field in Taft, Kern County, California, this facility met the threshold of 0.10gCO2/ MJ carbon intensity (CI) reduction.

Shortly after that, in August 2016, the SB 32 was passed, which changed the target for green house gas (GHG) reduction to 40% below the levels in 1990, to be achieved by 2030. It is anticipated that this will lead to the tightening of LCFS standards from 2020 all the way through 2030.

In November 2017, GlassPoint announced a partnership with Aera Energy to bring its enclosed trough technology to the South Belridge Oil Field, near Bakersfield, California. When done, the facility will be California's largest solar EOR field. It is projected to produce approximately 12 million barrels of steam per year through a 850MW thermal solar steam generator. It will also cut carbon emissions from the facility by 376,000 metric tons per year.

US National Low-Carbon Fuel Standard

Using California's LCFS as a model, several bills have been presented to establish a national low-carbon fuel standards at the federal level.

2007

Senators Barbara Boxer, Dianne Feinstein, and future President Barack Obama introduced in 2007 competing bills with varying versions of California's LCFS.

  • In March 2007, Senator Dianne Feinstein sponsored the "Clean Fuels and Vehicles Bill", which would have reduced emissions from motor vehicle fuels by 10 percent below projected levels by 2030, and would have required fuel suppliers to increase the percentage of low-carbon fuels – biodiesel, E-85 (made with cellulosic ethanol), hydrogen, electricity, and others – in the motor vehicle fuel supply.
  • California Senator Barbara Boxer presented on May 3, 2007, the "Advanced Clean Fuels Act of 2007". This bill was an amendment to the Clean Air Act to promote the use of advanced clean fuels that help reduce air and water pollution and protect the environment.
  • Then Senator Obama introduced his bill on May 7, 2007. The "National Low Carbon Fuel Standard Act of 2007" would have required fuel refineries to reduce the lifecycle greenhouse gas emissions of the transportation fuels sold in the U.S. by 5 percent in 2015 and 10 percent in 2020.

2009

In March 2009, the Waxman-Markey Climate Bill was introduced in the U.S. House Committee on Energy and Commerce, and it has been praised by top Obama Administration officials. The bill requires a slightly higher targets for reductions in emissions of carbon dioxide, methane, and other greenhouse gases than those proposed by President Barack Obama. The bill proposed a 20-percent emissions reduction from 2005 levels by 2020 (Obama had proposed a 14 percent reduction by 2020). Both plans aim to reduce emissions by about 80 percent by 2050. The Climate Change Bill was approved by the U.S. House of Representatives on June 26, 2009. As approved, emissions would be cut 17 percent from 2005 levels by 2020, and 83 percent by 2050.

EPA Renewable Fuel Standard

The Energy Independence and Security Act of 2007 (EISA) established new renewable fuel categories and eligibility requirements, setting mandatory life cycle greenhouse gas emissions thresholds for renewable fuel categories, as compared to those of average petroleum fuels used in 2005. EISA definition of life cycle GHG emissions explicitly mandated the U.S. Environmental Protection Agency (EPA) to include "direct emissions and significant indirect emissions such as significant emissions from land use changes."

On May 5, 2009, the U.S. Environmental Protection Agency (EPA) released its notice of proposed rulemaking for implementation of the 2007 modification of the Renewable Fuel Standard (RFS). The draft of the regulations was released for public comment during a 60-day period. EPA's proposed regulations also included the carbon footprint from indirect land-use changes, which, as CARB's ruling, caused controversy among ethanol producers. On the same day, President Barack Obama signed a Presidential Directive with the aim to advance biofuels research and improve their commercialization. The Directive established a Biofuels Interagency Working Group which has the mandate to come up with policy ideas for increasing investment in next-generation fuels, such as cellulosic ethanol, and for reducing the environmental footprint of growing biofuels crops, particularly corn-based ethanol.

An amendment was introduced in the House Appropriations Committee during the discussion of the fiscal 2010 Interior and Environment spending bill, aimed to prohibit EPA to consider indirect land-use changes in the RFS2 ruling for five years. This amendment was rejected on June 18, 2009, by a 30 to 29 vote. A similar amendment to the Waxman-Markey Climate Bill was introduced in the U.S. House Committee on Energy and Commerce. The Climate Bill was approved by the U.S. House of Representatives with a vote of 219 to 212, and included a mandate for EPA to exclude any estimation of international indirect land use changes due to biofuels for a five-year period for the purposes of the RFS2. During this period, more research is to be conducted to develop more reliable models and methodologies for estimating ILUC. By 2010 the bill is awaiting approval by the U.S. Senate.

EISA Standards for 2010
Fuel Category Percentage of
Fuel Required
to be Renewable
Volume of
Renewable Fuel
(in billion gal)
Cellulosic biofuel 0.004% 0.0065
Biomass-based diesel 1.10%(1) 1.15(1)
Total Advanced biofuel 0.61% 0.95
Renewable fuel 8.25% 12.95
Notes: (1) Combined 2009/2010 biomass-based diesel volumes applied in 2010.

On February 3, 2010, EPA issued its final rule regarding the expanded Renewable Fuel Standard (RFS2) for 2010 and beyond. The final rule revises the annual renewable fuel standards, and the required renewable fuel volume continues to increase reaching 36 billion gallons (136.3 billion liters) by 2022. For 2010, EISA set a total renewable fuel standard of 12.95 billion gallons (49.0 billion liters). This total volume, presented as a fraction of a refiner's or importer's gasoline and diesel volume, must be renewable fuel. The final 2010 standards set by EPA are shown in the table in the right side.

As mandated by law, and in order to establish the fuel category for each biofuel, EPA included in its modeling direct emissions and significant indirect emissions such as emissions from land use changes related to the full lifecycle. EPA's modeling of specific fuel pathways incorporated comments received through the third-party peer review process, and data and information from new studies and public comments. EPA's analysis determined that both ethanol produced from corn starch and biobutanol from corn starch comply with the 20% GHG emission reduction threshold required to classify as a renewable fuel. EISA grandfathered existing U.S. corn ethanol plants, and only requires the 20% reduction in life cycle GHG emissions for any renewable fuel produced at new facilities that commenced construction after December 19, 2007.

EPA also determined that ethanol produced from sugarcane, both in Brazil and Caribbean Basin Initiative countries, complies with the applicable 50% GHG reduction threshold for the advanced fuel category. Both diesel produced from algal oils and biodiesel from soy oil and renewable diesel from waste oils, fats, and greases complies with the 50% GHG threshold for the biomass-based diesel category. Cellulosic ethanol and cellulosic diesel (based on currently modeled pathways) comply with the 60% GHG reduction threshold applicable to cellulosic biofuels.

The following table summarizes the mean GHG emissions estimated and the range of variations considering that the main source of uncertainty in the life cycle analysis is the emissions related to international land use change GHG emissions.

U.S. Environmental Protection Agency
Life cycle Year 2022 GHG emissions reduction results for RFS2 final rule
(includes direct and indirect land use change effects and a 30-year payback period at a 0% discount rate)
Renewable fuel Pathway
(for U.S. consumption)
Mean
GHG emission
reduction(1)
GHG emission
reduction
95% confidence
interval(2)
EISA
category
Assumptions/comments
Corn ethanol 21% 7-32% Renewable fuel Natural gas fired dry mill plant, drying 63% of the DGS it produces and employing corn oil fractionation technology.
Corn biobutanol 31% 20-40% Renewable fuel Natural gas fired dry mill plant, drying 63% of the DGS it produces and employing corn oil fractionation technology.
Sugarcane ethanol(3) 61% 52-71% Advanced biofuel 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 bringing ethanol from Brazil to the U.S. are included.
Cellulosic ethanol from switchgrass 110% 102-117% Cellulosic biofuel Ethanol produced using the biochemical process.
Cellulosic ethanol from corn stover 129% No ILUC Cellulosic biofuel Ethanol produced using the biochemical process. Ethanol produced from agricultural residues does not have any international land use emissions.
Soybean-based biodiesel 57% 22-85% Biomass-based diesel Plant using natural gas
Waste grease biodiesel 86% No ILUC Biomass-based diesel 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) EPA develop a new Brazil module 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).

UNICA, a Brazilian ethanol producers association, welcomed the ruling and commented that they hope the classification of Brazilian sugarcane ethanol as an advanced biofuel will contribute to influence those who seek to lift the trade barriers imposed against clean energy, both in the U.S. and the rest of the world. EPA's final ruling is expected to benefit Brazilian producers, as the blending mandate requires an increasing quota of advanced biofuels, which is not likely to be fulfill with cellulosic ethanol, and then it would force blenders to import more Brazilian sugarcane-based ethanol, despite the existing 54¢ per gallon tariff on ethanol imported directly from Brazil.

In the case of corn-based ethanol, EPA said that manufacturers would need to use “advanced efficient technologies” during production to meet RSF2 limits. The U.S. Renewable Fuels Association also welcomed the ruling, as ethanol producers "require stable federal policy that provides them the market assurances they need to commercialize new technologies." However, they complained that "EPA continues to rely on oft-challenged and unproven theories such as international indirect land use change to penalize U.S. biofuels to the advantage of imported ethanol and petroleum."

Other U.S. regional proposals and programs

Eleven U.S. Northeast and Mid-Atlantic states have committed to analyzing a single low-carbon fuel standard for the entire region, driving commercialization and creating a larger market for fuels with low carbon intensity. The standard is aimed to reduce greenhouse gas emissions from fuels for vehicles and other uses, including fuel used for heating buildings, industrial processes, and electricity generation. Ten of these states are members of the Regional Greenhouse Gas Initiative (RGGI). California Air Resources Board (CARB) staff has been coordinating with representatives of these States. The states developing a regional LCFS are Connecticut, Delaware, Maine, Maryland, Massachusetts, New Hampshire, New Jersey, New York, Pennsylvania, Rhode Island, and Vermont.

A Memorandum of Understanding concerning the development of the regional low carbon fuel standard program was signed by the Governors of each State on December 30, 2009, committing the states to an economic analysis of the program, consultation with stakeholders before ruling, and a draft model rule by early 2011.

The Oregon Clean Fuels Program

In 2009, Oregon's legislature authorized the state's Department of Environmental Quality to create a standard with the same essential structure as California's LCFS. DEQ began full implementation of the program starting in 2016. The Oregon Clean Fuels Standard (CFS) explicitly draws on life-cycle greenhouse gas intensity calculations created or approved by the California Air Resources Board for the LCFS.

By early 2019, the path of CFS credit prices seemed to suggest some de facto linkage between the California and Oregon programs. Although Oregon's credit prices have been generally lower, Oregon has experienced a similar upward movement in prices in the 2016-2018 period, in parallel with California credit price increases.

British Columbia Low-Carbon Fuel Requirements

The Legislative Assembly of British Columbia, Canada, approved in April 2008 the Renewable and Low Carbon Fuel Requirements Act, which mandates fuel suppliers in B.C. to sell gasoline and diesel containing 5% and 4% percent renewable fuels, respectively, by 2010, and allows the provincial government to set thresholds for the carbon intensity of fuels, taking into account their entire carbon footprint. The RLCFR Act also provides flexibility for regulated fuel suppliers to meet their obligations as they may receive notional transfers of renewable fuels and of attributable greenhouse gas emissions.

Europe

Existing regulations

The EU has mainly acted to mitigate road transport greenhouse emissions mainly through its voluntary agreement on CO2 emissions from cars and subsequently through Regulation 443/2009 which sets mandatory CO2 emission limits for new cars. The EU promoted the use of biofuels through the directive on the promotion of the use of biofuels and other renewable fuels for transport (2003/30/EC), also known as Biofuel Directive, which calls for countries across the EU aiming at replacing 5,75% of all transport fossil fuels (petrol and diesel) with biofuels by 2010. None of these regulations, however, were based on carbon intensity of fuel. Fuel quality standards in the European Union are regulated by Directive 98/70/EC.

Other European countries have their own mandates limiting consumption of conventional fossil fuels by substituting to cleaner fuels in order to reduce greenhouse gas emissions, such as the United Kingdom Renewable Transport Fuel Obligation Program (RTFO), requiring transport fuel suppliers to ensure that 5% of all road vehicle fuel comes from sustainable renewable sources by 2010.

UK Renewable Transport Fuel Obligation

The Renewable Transport Fuel Obligation is similar to California's LCFS in some aspects. Biofuel suppliers are required to report on the level of carbon savings and sustainability of the biofuels they supplied in order to receive Renewable Transport Fuel Certificates (RTFCs). Suppliers have to report on both the net GHG savings and the sustainability of the biofuels they supply according to the appropriate sustainability standards of the feedstocks from which they are produced and any potential indirect impacts of biofuel production, such as indirect land-use change or changes to food and other commodity prices that are beyond the control of individual suppliers. Suppliers that do not submit a report will not be eligible for RTFO certificates.

Certificates can be claimed when renewable fuels are supplied and fuel duty is paid on them. At the end of the obligation period, these certificates may be redeemed to the RTFO Administrator to demonstrate compliance. Certificates can be traded, therefore, if obligated suppliers don't have enough certificates at the end of an obligation period they have to 'buy-out' the balance of their obligation by paying a buy-out price. The buy out price will be 15 pence per litre in the first two years.

EU low-carbon fuel standard

On January 31, 2007, the European Commission (EC) proposed new standards for transport fuels to reduce full life cycle emissions by up to 10 percent between 2011 and 2020 This was three weeks after the California LCFS Directive was announced. The EU proposal aimed to encourage the development of low-carbon fuels and biofuels, considering reductions in greenhouse gas emissions caused by the production, transport and use of the suppliers fuels.

In December 2008 the European Parliament, among other measures to address climate change in the European Union, approved amendments to the fuel quality directive (98/70) as well as replacing the Biofuels Directive with a Directive on the promotion of Renewable Energy Sources as proposed by the European Commission. The revision of Directive 98/07/EC introduced a mechanism to monitor and reduce greenhouse gas emissions from the use of road transport fuels, requiring fuel suppliers to reduce GHG emissions by up to 10 percent by 2020 on a life cycle basis. Regarding land use changes, the EC was ordered to "develop a concrete methodology to minimise greenhouse gas emissions caused by indirect land use changes." The fuel directive includes provisions to promote sustainable biofuels which minimized the impacts of ILUC. The approved goal of 10 percent reduction in greenhouse gas emissions can be achieved in several ways, and not exclusively from low-carbon fuels:

  • At least 6% by 31 December 2020, compared to the EU-average level of life cycle greenhouse gas emissions per unit of energy from fossil fuels in 2010, obtained through the use of biofuels, alternative fuels and reductions in flaring and venting at production sites.
  • A further 2% reduction (subject to a review) obtained through the use of environmentally friendly carbon capture and storage technologies and electric vehicles.
  • An additional further 2% reduction obtained through the purchase of credits under the Clean Development Mechanism of the Kyoto Protocol.

The commission is continuing development of the EU LCFS, in particular on the methodology for fossil fuel emissions, has recently consulted on various aspects of the implementation and responses have been published. Further work is underway to address Indirect Land Use Change emissions. Two modelling exercises and a model comparison exercise are being carried out to better understand the scale and nature of indirect land use change due to biofuels before the Commission makes proposals to address it.

On June 10, 2010, the EC adopted guidelines explaining how the Renewable Energy Directive (RED) should be implemented, as the Directive came into effect in December 2010. Three measures focus on the criteria for sustainability of biofuels and how to control that only sustainable biofuels are used in the EU. First, the commission is encouraging E.U. nations, industry and NGOs to set up voluntary schemes to certify biofuel sustainability. Second, the EC laid down the rules to protect untouched nature, such as forests, wetlands and protected areas, and third, a set of rules to guarantee that biofuels deliver substantial reduction in well-to-wheel greenhouse gas emissions.

Sustainable biofuel certificates

The EC decided to request governments, industry and NGO's to set up voluntary schemes to certify biofuel sustainability for all types of biofuels, including those imported into the EU. According to the EC, the overall majority of biofuels are produced in the EU, and for 2007, only 26% of biodiesel and 31% of bioethanol consumed in the EU was imported, mainly from Brazil and the United States. The Commission set standards that must be met for these schemes to gain EU recognition. One of the main criteria is that the certification scheme must be interdependently audited and fraud-resistant. Auditors must check the whole production chain, from the farmer and mill to the filling station (well-to-wheel life cycle). Auditors must check all the paper and inspect a sample of the farmers, mills and traders, and also whether the land where the feedstock for the ethanol is produced has been indeed farm land before and not a tropical forest or protected area. The certificates are to guarantee that all the biofuels sold under the label are sustainable and produced under the criteria set by the Renewable Energy Directive. Several private certification systems originally designed for sustainability more generally have adapted their standards to qualify for recognition under the Renewable Energy Directive, including the Roundtable on Sustainable Biomaterials and Bonsucro.

Environmental groups complained the measures "are too weak to halt a dramatic increase in deforestation." According to Greenpeace "Indirect land use change impacts of biofuels (ILUC) production still are not properly addressed" because if not properly regulated, "ILUC impacts will continue causing major biodiversity loss and more greenhosuse gas emissions." On the other hand, industry representatives welcomed the introduction of a certification system and some dismissed the concerns regarding the lack of criteria about ILUC. UNICA, the Brazilian ethanol producers association welcome the rules more cautiously, as they consider "that gaps in the rules needed to be filled in so the "industry has a clear framework within which to operate". Some other industry organizations also said that further clarification is needed in order to implement the Renewable Energy Directive.

The EC clarified that it would publish a report on the impacts of indirect land use by the end of 2010, as requested in the Renewable Energy Directive and on the basis of recently released reports that suggest that biofuels are saving greenhouse gas emissions.

Protecting untouched nature

The rules set by the Commission establish that biofuels should not be made from feedstocks from tropical forests or recently deforested areas, drained peatland, wetland or highly biodiverse areas. The corresponding Communication explains how this should be assessed and as an example, it makes it clear that the conversion of a forest to a palm oil plantation would not meet the sustainability requirements.

Promote only biofuels with high greenhouse gas savings

The Commission reiterated that Member States have to meet binding, national targets for renewable energy and that only those biofuels with high greenhouse gas emission savings count for the national targets. The corresponding Communication explains how to make the calculation, which not only includes carbon dioxide (CO2), but also methane (CH4) and nitrous oxide (N2O), both stronger greenhouse gases than CO2. Biofuels must deliver greenhouse gas savings of at least 35% compared to fossil fuels, rising to 50% in 2017 and to 60%, for biofuels from new plants, in 2018.

Vehicle emission standard

From Wikipedia, the free encyclopedia

Emission standards are the legal requirements governing air pollutants released into the atmosphere. Emission standards set quantitative limits on the permissible amount of specific air pollutants that may be released from specific sources over specific timeframes. They are generally designed to achieve air quality standards and to protect human life. Different regions and countries have different standards for vehicle emissions.

Regulated sources

Many emissions standards focus on regulating pollutants released by automobiles (motor cars) and other powered vehicles. Others regulate emissions from industry, power plants, small equipment such as lawn mowers and diesel generators, and other sources of air pollution.

The first automobile emissions standards were enacted in 1963 in the United States, mainly as a response to Los Angeles' smog problems. Three years later Japan enacted their first emissions rules, followed between 1970 and 1972 by Canada, Australia, and several European nations. The early standards mainly concerned carbon monoxide (CO) and hydrocarbons (HC). Regulations on nitrogen oxide emissions (NOx) were introduced in the United States, Japan, and Canada in 1973 and 1974, with Sweden following in 1976 and the European Economic Community in 1977. These standards gradually grew more and more stringent but have never been unified.

There are largely three main sets of standards: United States, Japanese, and European, with various markets mostly using these as their base. Sweden, Switzerland, and Australia had separate emissions standards for many years but have since adopted the European standards. India, China, and other newer markets have also begun enforcing vehicle emissions standards (derived from the European requirements) in the twenty-first century, as growing vehicle fleets have given rise to severe air quality problems there, too.

Vehicle emission performance standard

An emission performance standard is a limit that sets thresholds above which a different type of vehicle emissions control technology might be needed. While emission performance standards have been used to dictate limits for conventional pollutants such as oxides of nitrogen and oxides of sulphur (NOx and SOx), this regulatory technique may be used to regulate greenhouse gases, particularly carbon dioxide (CO2). In the US, this is given in pounds of carbon dioxide per megawatt-hour (lbs. CO2/MWhr), and kilograms CO2/MWhr elsewhere.

Europe

Before the European Union began streamlining emissions standards, there were several different sets of rules. Members of the European Economic Community (EEC) had a unified set of rules, considerably laxer than those of the United States or Japan. These were tightened gradually, beginning on cars of over two liters displacement as the price increase would have less of an impact in this segment. The ECE 15/05 norms (also known as the Luxemburg accord, strict enough to essentially require catalytic converters) began taking effect gradually: the initial step applied to cars of over 2000 cc in two stages, in October 1988 and October 1989. There followed cars between 1.4 and 2.0 liters, in October 1991 and then October 1993. Cars of under 1400 cc had to meet two subsequent sets of regulations that applied in October 1992 and October 1994 respectively. French and Italian car manufacturers, strongly represented in the small car category, had been lobbying heavily against these regulations throughout the 1980s.

Within the EEC, Germany was a leader in regulating automobile emissions. Germany gave financial incentives to buyers of cars that met US or ECE standards, with lesser credits available to those that partially fulfilled the requirements. These incentives had a strong impact; only 6.5 percent of new cars registered in Germany in 1988 did not meet any emissions requirements and 67.3 percent were compliant with the strictest US or ECE standards.

Sweden was one of the first countries to instill stricter rules (for 1975), placing severe limitations on the number of vehicles available there. These standards also caused drivability problems and steeply increased fuel consumption - in part because manufacturers could not justify the expenditure to meet specific regulations that applied only in one very small market. In 1982, the European Community calculated that the Swedish standards increased fuel consumption by 9 percent, while it made cars 2.5 percent more expensive. For 1983 Switzerland (and then Australia) joined in the same set of regulations, which gradually increased the number of certified engines. One problem with the strict standards was that they did not account for catalyzed engines, meaning that vehicles thus equipped had to have the catalytic converters removed before they could be legally registered.

In 1985 the first catalyzed cars entered certain European markets such as Germany. At first, the availability of unleaded petrol was limited and sales were small. In Sweden, catalyzed vehicles became allowed in 1987, benefitting from a tax rebate to boost sales. By 1989 the Swiss/Swedish emissions rules were tightened to the point that non-catalyzed cars were no longer able to be sold. In early 1989 the BMW Z1 was introduced, only available with catalyzed engines. This was a problem in some places like Portugal, where unleaded fuel was still almost non-existent, although European standards required unleaded gasoline to be "available" in every country by 1 October 1989.

European Union

The main source of greenhouse gas emissions in the European Union is transportation. In 2019, it contributes to about 31% of global emissions and 24% of emissions in the EU. In addition, up to the COVID-19 pandemic, emissions have only increased in the transport economic sector. In 2019, about 95% of the fuel came from fossil sources.

The European Union has its own set of emissions standards that all new vehicles must meet. Currently, standards are set for all road vehicles, trains, barges and 'nonroad mobile machinery' (such as tractors). No standards apply to seagoing ships or airplanes.

EU Regulation No 443/2009 set an average CO2 emissions target for new passenger cars of 130 grams per kilometre. The target was gradually phased in between 2012 and 2015. A target of 95 grams per kilometre applies from 2021.

For light commercial vehicle, an emissions target of 175 g/km applies from 2017, and 147 g/km from 2020, a reduction of 16%.

The EU introduced Euro 4 effective 1 January 2008, Euro 5 effective 1 January 2010, and Euro 6 effective 1 January 2014. These dates had been postponed for two years to give oil refineries the opportunity to modernize their plants.

From January 2022, all new light vehicles must comply with Euro 6d.

From 1 January 2023, all new motorcycles must comply with Euro 5.

Germany

According to the German federal automotive office 37.3% (15.4 million) cars in Germany (total car population 41.3 million) conform to the Euro 4 standard from Jan 2009.

Russia

All new light vehicles must comply with Euro 5 since January 2016.

All new heavy vehicles must comply with Euro 5 since 2018.

UK

Several local authorities in the UK have introduced Euro 4 or Euro 5 emissions standards for taxis and licensed private hire vehicles to operate in their area. Emissions tests on diesel cars have not been carried out during MOTs in Northern Ireland for 12 years, despite being legally required.

From January 2022, all new light vehicles must comply with Euro 6d.

From 1 January 2023, all new motorcycles must comply with Euro 5.

North America

Canada

In Canada, the Canadian Environmental Protection Act, 1999 (CEPA 1999) transfers the legislative authority for regulating emissions from on-road vehicles and engines to Environment Canada from Transport Canada's Motor Vehicle Safety Act. The Regulations align emission standards with the U.S. federal standards and apply to light-duty vehicles (e.g., passenger cars), light-duty trucks (e.g., vans, pickup trucks, sport utility vehicles), heavy-duty vehicles (e.g., trucks and buses), heavy-duty engines and motorcycles.

Mexico

From 1 July 2019, all new heavy vehicles must comply with EPA 07 and Euro 5.

From 1 January 2025, all new heavy vehicles must comply with EPA 10 and Euro 6.

United States

The United States has its own set of emissions standards that all new vehicles must meet. In the United States, emissions standards are managed by the Environmental Protection Agency (EPA). Under federal law, the state of California is allowed to promulgate more stringent vehicle emissions standards (subject to EPA approval), and other states may choose to follow either the national or California standards. California had produced air quality standards prior to EPA, with severe air quality problems in the Los Angeles metropolitan area. LA is the country's second-largest city, and relies much more heavily on automobiles and has less favorable meteorological conditions than the largest and third-largest cities (New York and Chicago).

Some states have areas within the state that require emissions testing while other cities within the state do not require emission testing. Arizona emissions testing locations are located primarily in the two largest metropolitan areas (Phoenix and Tucson). People outside of these areas are not required to submit their vehicle for testing as these areas are the only ones that have failed the air quality tests by the state.

California's emissions standards are set by the California Air Resources Board (CARB). By mid-2009, 16 other states had adopted CARB rules; given the size of the California market plus these other states, many manufacturers choose to build to the CARB standard when selling in all 50 states. CARB's policies have also influenced EU emissions standards.

California is attempting to regulate greenhouse gas emissions from automobiles, but faces a court challenge from the federal government. The states are also attempting to compel the federal EPA to regulate greenhouse gas emissions, which as of 2007 it has declined to do. On 19 May 2009, news reports indicate that the Federal EPA will largely adopt California's standards on greenhouse gas emissions.

California and several other western states have passed bills requiring performance-based regulation of greenhouse gases from electricity generation.

In an effort to decrease emissions from heavy-duty diesel engines faster, CARB's Carl Moyer Program funds upgrades that are in advance of regulations.

The California ARB standard for light vehicle emissions is a regulation of equipment first, with verification of emissions second. The property owner of the vehicle is not permitted to modify, improve, or innovate solutions in order to pass a true emissions-only standard set for their vehicle driven on public highways. Therefore, California's attempt at regulation of emissions is a regulation of equipment, not of air quality. Vehicle owners are excluded from modifying their property in any way that has not been extensively researched and approved by CARB and still operate them on public highways.

The EPA has separate regulations for small engines, such as groundskeeping equipment. The states must also promulgate miscellaneous emissions regulations in order to comply with the National Ambient Air Quality Standards.

Latin America

Argentina

From 1 January 2016, all new heavy vehicles in Argentina must comply with Euro 5.

From 1 January 2018, all new light and heavy vehicles in Argentina must comply with Euro 5.

Brazil

From 1 January 2012, all new heavy vehicles in Brazil must comply with Proconve P7 (similar to Euro 5)

From 1 January 2015, all new light vehicles in Brazil must comply with Proconve L6 (similar to Euro 5).

From 1 January 2022, all new light vehicles in Brazil must comply with Proconve L7 (similar to Euro 6).

From 1 January 2023, all new heavy vehicles in Brazil must comply with Proconve P8 (similar to Euro 6).

From 1 January 2025, the new light vehicle fleets in Brazil must comply with the first stage of Proconve L8 (automaker average).

Chile

From September 2014, all new cars in Chile must comply with Euro 5.

From September 2022, all new light and medium vehicle models in Chile must comply with Euro 6b.

From September 2024, all new light and medium vehicle models in Chile must comply with Euro 6c.

Colombia

From 1 January 2023, all new vehicles in Colombia must comply with Euro 6.

Asia

China

Due to rapidly expanding wealth and prosperity, the number of coal power plants and cars on China's roads is rapidly growing, creating an ongoing pollution problem. China enacted its first emissions controls on automobiles in 2000, equivalent to Euro I standards. China's State Environmental Protection Administration (SEPA) upgraded emission controls again on 1 July 2004 to the Euro II standard. More stringent emission standard, National Standard III, equivalent to Euro III standards, went into effect on 1 July 2007. Plans were for Euro IV standards to take effect in 2010. Beijing introduced the Euro IV standard in advance on 1 January 2008, becoming the first city in mainland China to adopt this standard.

From 1 January 2018, all new vehicles must comply with China 5 (similar to Euro 5).

From 1 January 2021, all new vehicles in China must comply with China 6a (similar to Euro 6).

From 1 July 2023, all new vehicles in China must comply with China 6b (similar to Euro 6).

Hong Kong

From 1 January 2006, all new passenger cars with spark-ignition engines in Hong Kong must meet either Euro IV petrol standard, Japanese Heisei 17 standard or US EPA Tier 2 Bin 5 standard. For new passenger cars with compression-ignition engines, they must meet US EPA Tier 2 Bin 5 standard.

The current standard is Euro 6C, it has been phased in since 2019.

India

Bharat stage emission standards are emission standards instituted by the Government of India to regulate the output of air pollutants from internal combustion engine equipment, including motor vehicles. The standards and the timeline for implementation are set by the Central Pollution Control Board under the Ministry of Environment & Forests.

The standards, based on European regulations were first introduced in 2000. Progressively stringent norms have been rolled out since then. All new vehicles manufactured after the implementation of the norms have to be compliant with the regulations. By 2014, the country was under a combination of Euro 3 and Euro 4-based norms, with Euro 4 standards partly implemented in 13 major cities. Till April 2017, the entire country was under BS IV norms, which is based on Euro 4.

As of now manufacturing and registration of BS VI vehicles has started, from April 2020 all BS VI manufacturing is mandatory, respectively.

Israel

Since January 2012 vehicles which do not comply with Euro 6 emission values are not allowed to be imported to Israel.

Japan

Background

Starting 10 June 1968, the Japanese Government passed the (Japanese: Air Pollution Control Act) which regulated all sources of air pollutants. As a result of the 1968 law, dispute resolutions were passed under the 1970 (Japanese: Air Pollution Dispute Resolution Act). As a result of the 1970 law, in 1973 the first installment of four sets of new emissions standards were introduced. Interim standards were introduced on 1 January 1975, and again for 1976. The final set of standards were introduced for 1978. While the standards were introduced they were not made immediately mandatory, instead tax breaks were offered for cars which passed them. The standards were based on those adopted by the original US Clean Air Act of 1970, but the test cycle included more slow city driving to correctly reflect the Japanese situation. The 1978 limits for mean emissions during a "Hot Start Test" of CO, hydrocarbons, and NOx were 2.1 grams per kilometre (3.38 g/mi) of CO, 0.25 grams per kilometre (0.40 g/mi) of HC, and 0.25 grams per kilometre (0.40 g/mi) of NOx respectively. Maximum limits are 2.7 grams per kilometre (4.35 g/mi) of CO, 0.39 grams per kilometre (0.63 g/mi) of HC, and 0.48 grams per kilometre (0.77 g/mi) of NOx. One interesting detail of the Japanese emissions standards was that they were introduced in a soft manner; that is, 1978 model year cars could be sold that did not meet the 1978 standards, but they would suffer various tax penalties. This gave manufacturers breathing room to properly engineer solutions and also incentivized fixing the best-selling models first, leading to smoother adoption of clean air standards and fewer drivability concerns than in many other markets.

The "10 - 15 Mode Hot Cycle" test, used to determine individual fuel economy ratings and emissions observed from the vehicle being tested, use a specific testing regime.

In 1992, to cope with NOx pollution problems from existing vehicle fleets in highly populated metropolitan areas, the Ministry of the Environment adopted the (Japanese: Law Concerning Special Measures to Reduce the Total Amount of Nitrogen Oxides Emitted from Motor Vehicles in Specified Areas), called in short The Motor Vehicle NOx Law. The regulation designated a total of 196 communities in the Tokyo, Saitama, Kanagawa, Osaka and Hyogo Prefectures as areas with significant air pollution due to nitrogen oxides emitted from motor vehicles. Under the Law, several measures had to be taken to control NOx from in-use vehicles, including enforcing emission standards for specified vehicle categories.

The regulation was amended in June 2001 to tighten the existing NOx requirements and to add PM control provisions. The amended rule is called the "Law Concerning Special Measures to Reduce the Total Amount of Nitrogen Oxides and Particulate Matter Emitted from Motor Vehicles in Specified Areas", or in short the Automotive NOx and PM Law.

Emission Standards

The NOx and PM Law introduces emission standards for specified categories of in-use highway vehicles including commercial goods (cargo) vehicles such as trucks and vans, buses, and special purpose motor vehicles, irrespective of the fuel type. The regulation also applies to diesel powered passenger cars (but not to gasoline cars).

In-use vehicles in the specified categories must meet 1997/98 emission standards for the respective new vehicle type (in the case of heavy duty engines NOx = 4.5 g/kWh, PM = 0.25 g/kWh). In other words, the 1997/98 new vehicle standards are retroactively applied to older vehicles already on the road. Vehicle owners have two methods to comply:

  1. Replace old vehicles with newer, cleaner models
  2. Retrofit old vehicles with approved NOx and PM control devices

Vehicles have a grace period, between 8 and 12 years from the initial registration, to comply. The grace period depends on the vehicle type, as follows:

  • Light commercial vehicles (GVW ≤ 2500 kg): 8 years
  • Heavy commercial vehicles (GVW > 2500 kg): 9 years
  • Micro buses (11-29 seats): 10 years
  • Large buses (≥ 30 seats): 12 years
  • Special vehicles (based on a cargo truck or bus): 10 years
  • Diesel passenger cars: 9 years

Furthermore, the regulation allows fulfillment of its requirements to be postponed by an additional 0.5–2.5 years, depending on the age of the vehicle. This delay was introduced in part to harmonize the NOx and PM Law with the Tokyo diesel retrofit program.

The NOx and PM Law is enforced in connection with Japanese vehicle inspection program, where non-complying vehicles cannot undergo the inspection in the designated areas. This, in turn, may trigger an injunction on the vehicle operation under the Road Transport Vehicle Law.

Turkey

Diesel and gasoline sulphur content is regulated at 10 ppm. Turkey currently follows Euro VI for heavy duty commercial vehicles, and, in 2016 a couple of years after the EU, Turkey adopted Euro 6 for new types of light duty vehicles (LDV) and new types of passenger cars. Turkey is planning to use the worldwide harmonized light vehicles test procedure (WLTP).

However, despite these tailpipe emission standards for new vehicle types there are many older diesel vehicles, no low-emission zones and no national limit on PM2.5 particulates so local pollution, including from older vehicles, is still a major health risk in some cities, such as Ankara. Concentrations of PM2.5 are 41 µg/m3 in Turkey, making it the country with the worst air pollution in Europe. The regulation for testing of existing vehicle exhaust gases is Official Newspaper number 30004 published 11 March 2017.

An average of 135 g CO2/km for LDVs compared well with other countries in 2015, however unlike the EU there is no limit on carbon dioxide emissions.

Vietnam

From 1 January 2022, all new cars in Vietnam must comply with Euro 5.

Africa

Morocco

From 1 January 2024, all new vehicles in Morocco must comply with Euro 6b.

South Africa

South Africa's first clean fuels programme was implemented in 2006 with the banning of lead from petrol and the reduction of sulphur levels in diesel from 3,000 parts per million (ppm) to 500ppm, along with a niche grade of 50 ppm.

The Clean Fuels 2 standard, expected to begin in 2017, includes the reduction of sulphur to 10 ppm; the lowering of benzene from 5 percent to 1 percent of volume; the reduction of aromatics from 50 percent to 35 percent of volume; and the specification of olefins at 18 percent of volume.

Oceania

Australia

Australian emission standards are based on European regulations for light-duty and heavy-duty (heavy goods) vehicles, with acceptance of selected US and Japanese standards. The current policy is to fully harmonize Australian regulations with United Nations (UN) and Economic Commission for Europe (ECE) standards. In November 2013, the first stage of the stringent Euro 5 emission standards for light vehicles was introduced, which includes cars and light commercial vehicles. The development of emission standards for highway vehicles and engines is coordinated by the National Transport Commission (NTC) and the regulations—Australian Design Rules (ADR)—are administered by the Department of Infrastructure and Transport.

All new vehicles manufactured or sold in the country must comply with the standards, which are tested by running the vehicle or engine in a standardized test cycle.

Environmental standard

From Wikipedia, the free encyclopedia

Environmental standards are administrative regulations or civil law rules implemented for the treatment and maintenance of the environment. Environmental standards are typically set by government and can include prohibition of specific activities, mandating the frequency and methods of monitoring, and requiring permits for the use of land or water. Standards differ depending on the type of environmental activity.

Environmental standards may be used produce quantifiable and enforceable laws that promote environmental protection. The basis for the standards is determined by scientific opinions from varying disciplines, the views of the general population, and social context. As a result, the process of determining and implementing the standards is complex and is usually set within legal, administrative or private contexts.

The human environment is distinct from the natural environment. The concept of the human environment considers that humans are permanently interlinked with their surroundings, which are not just the natural elements (air, water, and soil), but also culture, communication, co-operation, and institutions. Environmental standards should preserve nature and the environment, protect against damage, and repair past damage caused by human activity.

Development of environmental standards

Historically, the development of environmental standards was influenced by two competing ideologies: ecocentrism and anthropocentrism. Ecocentrism frames the environment as having an intrinsic value divorced from the human utility, while anthropocentrism frames the environment as only having value if it helps humanity survive. This has led to problems in establishing standards.

In recent decades, the popularity and awareness of environmentalism has increased with the threat of global warming becoming more alarming than ever since the IPCC released their report in 2018. The report asserts that based on scientific evidence “if human activities continue to at this rate it is predicted to increase in-between 1.5-2 °C over pre industrial levels in-between 2030 and 2052”. Busby argues that Climate change will define this century and that it is no longer a faraway threat. In turn, the demand for protecting the environment has risen. Developments in science have been fundamental for the setting of environmental standards. Improved measurements and techniques have allowed scientists to better understand the impact of human-caused environmental damage on human health and the biodiversity which composes the natural environment.

Therefore, environmental standards in modern times are set with the view that humans do have obligations toward the environment, but they can be justified in terms of obligations toward other humans. This means it is possible to value the environment without discarding anthropocentrism. Sometimes called prudential or enlightened anthropocentrism. This is evident as environmental standards often characterize the desired state (e.g. the pH of a lake should be between 6.5 and 7.5) or limit alterations (e.g., no more than 50% of the natural forest may be damaged). Statistical methods are used to determine the specific states and limits the enforceable environmental standard.

Penalties and other procedures for dealing with regions out of compliance with the standard may be part of the legislation.

Governmental institutions setting environmental standards

Environmental standards are set by many different institutions.

United Nations (UN)

The UN, with 193 member states, is the largest intergovernmental organization. The environmental policy of the UN has a huge impact on the setting of international environmental standards. At the Earth summit in 1992, held in Rio, the member states acknowledged their negative impact on the environment for the first time. During this and the following Millennium Declaration, the first development goals for environmental issues were set.

Since then, the risk of the catastrophe caused by extreme weather has been enhanced by the overuse of natural resources and global warming. At the Paris Agreement in 2015, the UN determined 17 Goals for sustainable development. Besides the fight against global poverty, the main focus of the goals is the preservation of our planet. These goals set a baseline for global environmentalism. The environmental areas of water, energy, oceans, ecosystems, sustainable production, consumer behavior and climate protection were covered by the goals. The goals contained explanations on which mediums were required to reach them. Implementation and follow-up are controlled by non-enforceable voluntary national reviews. The main control is done by statistical values, which are called indicators. These indicators deliver information if the goals are reached.

European Union

(See also: Environmental policy of the European Union)

Within the Treaty on the Functioning of the European Union, the Union integrates a self-commitment towards the environment. In Title XX, Article 191.1, it is settled: “Union policy on the environment shall contribute to the pursuit of the following objectives: — preserving, protecting and improving the quality of the environment, — protecting human health, — prudent and rational utilization of natural resources, — promoting measures at international level to deal with regional or worldwide environmental; problems, and in particular combating climate change.” All environmental actions are based on this article and lead to a suite of environmental laws. European environmental regulation covers air, biotechnological, chemical, climate change, environmental economics, health, industry and technology, land use, nature and biodiversity, noise, protection of the ozone layer, soil, sustainable development, waste, and water.

The European Environment Agency (EEA) consults the member states about environmental issues, including standards.

The environmental standards set by European legislation include precise parametric concentrations of pollutants and also includes target environmental concentrations to be achieved by specific dates.

United States

In the United States, the development of standards is decentralized. These standards were developed by more than a hundred different institutions, many of which are private. The method of handling environmental standards is a partly fragmented plural system, which is mainly affected by the market. Under the Trump Administration, Climate standards have increasingly become a site of conflict in the politics of global warming.

Ambient air quality standards

The National Ambient Air Quality Standards (NAAQS) are set by the Environmental Protection Agency (EPA) to regulate pollutants in the air. The enforcement of these standards is designed to prevent further degradation of air quality.

States may set their own ambient standards, so long as they are lower than the national standard. The NAAQS regulates the six criteria for air pollutants: sulfur dioxide (SO2), particulate matter (PM10), carbon monoxide (CO), ozone (O3), nitrogen dioxide (NO2), and lead (Pb). To ensure that the ambient standards are met, the EPA uses the Federal Reference Method (FRM) and Federal Equivalent Method (FEM) systems to measure the number of pollutants in the air and check that they are within the legal limits.

Air emission standards

Emission standards are national regulations managed by the EPA  that control the amount and concentration of pollutants that can be released into the atmosphere to maintain air quality, human health, and regulate the release of greenhouse gases such as carbon dioxide (CO2), oxides of nitrogen and oxides of sulfur.

The standards are established in two phases to stay up-to-date, with final projections aiming to collectively save Americans $1.7 trillion in fuel costs and reduce the amount of greenhouse gas emissions (GHG) by 6 billion metric tons. Similar to the ambient standards, individuals states may also tighten regulations. For example, California set their own emissions standards through the California Air Resources Board (CARB), and these standards have been adopted by some other states. Emission standards also regulate the number of pollutants released by heavy industry and for electricity.

The technological standards set by the EPA do not necessarily enforce the use of specific technologies, but set minimum performance levels for different industries. The EPA often encourages technological improvement by setting standards that are not achievable with current technologies. These standards are always set based on the industry's top performers to promote the overall improvement of the industry as a whole.

Impact of non-governmental organizations on environmental standards

International Organization of Standardization

The International Organization of Standardization (ISO) develops a large number of voluntary standards. With 163 member states, it has a comprehensive outreach. The standards set by the ISO were often transmitted into national standards by different nations. About 363,000 companies and organizations worldwide have the ISO 14001 certificate, a standard for environmental management created to improve the environmental performance of an organization and legal aspects as well as reaching environmental aims. Most of the national and international environmental management standards include the ISO 14000 series. In light of the UN Sustainable Development Goals, ISO has identified several families of standards which help meet SDG 13 which is focused on Climate Action for global warming.

Greenpeace

Greenpeace is a popular non-governmental organization that deals with biodiversity and the environment. Their activities have had a great global impact on environmental issues. Greenpeace encourages public attention and enforces governments or companies to adapt and set environmental standards through activities recording special environmental issues. Their main focus is on forests, the sea, climate change, and toxic chemicals. For example, the organization set a standard about toxic chemicals together with the textiles sector, creating the concept 2020, which plans to banish all toxic chemicals from textile production by 2020.

World Wildlife Fund

The World Wide Fund is an international non-governmental organization founded in 1961 that works in the field of wilderness preservation and the reduction of human impact on the environment.

Economy

Environmental standards in the economy are set through external motivation. First, companies need to fulfill the environmental law of the countries in which they operate. Moreover, environmental standards are based on voluntary self-commitment which means companies implement standards for their business. These standards should exceed the level of the requirements of governmental regulations. If companies set further-reaching standards, they try to fulfill the wishes of stakeholders.

At the process of setting environmental standards, three different stakeholders have the main influence. The first stakeholder, the government, is the strongest determinate, followed by the influence of the customers. Nowadays, there is an increasing number of people, who consider environmental factors during their purchasing decision. The third stakeholder who forces companies to set environmental standards is industrial participants. If companies are part of industrial networks, they are forced to fulfill the codes of conduct of these networks. This code of conduct is often set to improve the collective reputation of an industry. Another driving force of industry participants could be a reaction to a competitors action.

The environmental standards set by companies themselves can be divided into two dimensions: operational environmental policies and the message sent in advertising and public communications.

Operational environmental policies

This can be the environmental management, audits, controls, or technologies. In this dimension, the regulations tend to be closely connected with other function areas, e.g. lean production. Furthermore, it could be understood that multinational companies tend to set cross-country harmonized environmental government regulations and therefore reach a higher performance level of environmental standards.

It is often argued that companies focus on the second dimension: the message sent in advertising and public communications. To satisfy the stakeholders' requirement, companies were focused on the public impression of their environmental self-commitment standards. Often the real implementation does not play an important role.

A lot of companies settle the responsibility for the implementation of low-budget departments. The workers, who were in charge of the standards missing time and financial resources to guarantee a real implementation. Furthermore, within the implementation, goal conflicts arise. The biggest concern of companies is that environmental protection is more expansive compared to the gained beneficial effects. But, there are a lot of positive cost-benefit-calculation for environmental standards set by companies themselves. It is observed that companies often set environmental standards after a public crisis. Sometimes environmental standards were already set by companies to avoid public crises. As to whether environmental self-commitment standards are effective, is controversial.

Psychology of climate change denial

From Wikipedia, the free encyclopedia https://en.wikipedia.org/wiki/Psychology_of_climate_change_denial   The ...