MOVE TO BREATHE
CLEAN AIR ACT BASICS
Learn the basic outline of the Clean Air Act and how it works.
MOVING BEYOND THE REQUIREMENTS OF THE CLEAN AIR ACT
Learn how Neighbors for Clean Air is working with communities to get industrial sources to move beyond the requirements of the Clean Air Act to minimize emissions.
DIESEL PARTICULATES
Learn about sources and effects of diesel particulate emissions and what you can do to help us reduce diesel particulates in Oregon.
NUISANCE ODORS
Learn what a nuisance is and how DEQ is beginning to implement its prohibition on regulated facilities creating a nuisance.
CLEAN AIR ACT BASICS
The modern version of the Clean Air Act came into existence in 1970 with the passage of the Clean Air Act. The Act has undergone two major revisions in 1977 and 1990. The Act is broken down into Titles, Parts, and individual Sections. With all of its interconnections and technically complex programs, the Clean Air Act is the most complex environmental law in the United States; in fact it is probably one of the most complex laws ever passed by Congress. It is therefore impossible to give an “overview” of the entire Act. This overview will focus on the basics of some of the most used or important sections.
The Clean Air Act has six major Titles:
Title I contains requirements for stationary sources and airsheds.
Title I of the Clean Air Act regulates stationary sources of air pollution. Most regulations and requirements under the Clean Air Act find their basis in Title I. In Part A of Title I, Sections 107 through 110 require the United States Environmental Protection Agency (EPA) to create National Ambient Air Quality Standards (NAAQS) for “criteria” pollutants. Currently there are six criteria pollutants:
– nitrogen oxides (NOx),
– sulfur dioxide (SO2),
– carbon monoxide (CO),
– ozone (O3),
– lead (Pb),
– and particulate matter (PM), which is broken down into particulates less than 10 microns (PM10) and particulates less than 2.5 microns (PM2.5).
The NAAQS standards are set based on the best available data concerning the pollutant’s affect on human health; the cost of achieving these standards is not considered in setting the standards themselves. States must undertake monitoring and modeling to determine whether the airsheds in the state are in “attainment,” are “nonattainment,” or “unclassifiable.” States must then adopt a State Implementation Plan (SIP) that sets out the state’s plan for achieving or maintaining compliance with the NAAQS in these airsheds. These plans must be submitted to and approved by EPA. Once approved by EPA these state regulations become federal law in that state, which, as discussed below under Title III, makes them enforceable by citizens.
Also found in Part A are the New Source Performance Standards (NSPS) and National Emission Standards for Hazardous Air Pollutants (NESHAPs). Section 111 sets out the requirements for NSPS; Section 112 sets out the requirements for NESHAPs.
NSPS
NSPS regulations set out minimum control requirements for new air pollution sources in specific source categories. These standards are set based on the best system of emissions reduction that, accounting for cost and non-air impacts, has been adequately demonstrated. The NSPS set emission limits and do not require a source to install a specific control technology though in practice sources usually meet these requirements by installing the control technology EPA based the NSPS on. If an existing source would be subject to an NSPS but is not currently regulated under the NAAQS or NESHAPs, EPA can ask states to develop plans to address these existing sources. It is this authority that EPA is currently exploring to regulate green house gas (GHG) emissions from existing coal-fired power plants. NESHAP NESHAP regulations set standards for the most prevalent industrial sources of air toxics. The original NESHAP program was a health-based standard. Unfortunately due to its narrow scope and continuous litigation involving EPA’s judgment on the health effects, this original program was very ineffective. While the regulations passed under this program remain, the only one of real consequence is the regulation of asbestos. Part of the problem with the original program is that EPA first had to determine whether or not a chemical was toxic.
Congress remedied this situation with the 1990 Clean Air Act Amendments. Congress set out a list of 188 hazardous air pollutants (HAPs) and gave EPA the authority to add or remove from this list. This list is much broader than simply 188 chemicals since many are sets of compounds, like “chromium compounds,” that contain hundreds or even thousands of different chemicals. There have been some changes to this list over the years, but most of the list remains as Congress wrote it in 1990.
Congress also worked to create a more concrete standard for EPA to implement than a health-based standard that was subject to constant litigation. Congress required EPA to set out a list of the major and area sources of HAPs. A major source is a source that has the potential to emit more than 25 tons/year of HAPs or 10 tons/year of an individual HAP. An area source is a source other than a major source. The list of regulated source categories is revised every 8 years to ensure the appropriate source categories are regulated.
Congress also modified the NESHAP program to be essentially a pure technology based standard. New major sources must meet the best level of control achieved in practice. Existing major sources are required to meet a level of control that is the average of the best performing 12 percent of existing sources. If there are less than 30 sources in a category, an existing major source must meet a level of control that is the average of the top 5 sources. These standards are known as the maximum achievable control technology (MACT). Much like the NSPS, the NESHAP program does not require the installation of specific control technology only an emission limit. If EPA determines that a source category meets certain requirements, it can pass regulations for area sources that require the sources to implement generally available control technology (GACT).
Risk Management Planning
Section 112 also includes the Risk Management Planning (RMP) program. The RMP program is contained in Section 112r. This program was passed in response to the Bhopal disaster in India. It requires sources that store or use large amounts of potentially dangerous chemicals to develop plans that include a risk assessment, a program for preventing accidental releases, and a response plan for accidental releases.
New Source Review
The review of emissions from new or modified major sources is found in two separate parts of Title I. Part B, Subpart I sets out the Prevention of Siginficant Deterioration (PSD) program. Part D sets out the Nonattainment New Source Review (NaNSR) program. Both of these programs are often referred to as simply “New Source Review.” PSD applies in areas that are designated as attainment or unclassifiable. NaNSR applies in areas that are designated as nonattainment. Both programs only apply to the largest sources. For a designated list of source categories the trigger level is 100 tons per year of a single pollutant. Outside of that designated list, the trigger level is 250 tons per year of a single pollutant.
Generally, under PSD a source has to do modeling to ensure that it won’t cause a violation of the NAAQS. The source must also install the Best Available Control Technology (BACT). The determination of BACT is made on a case-by-case basis and accounts for “energy, environmental, and economic impacts and other costs,” but must be at least as stringent as any NSPS or NESHAP that are applicable to the source.
For NaNSR, a source must comply with the lowest achievable emission rate which is either the most stringent standard included in a SIP or the most stringent standard achieved in practice, whichever is lower. The source must also receive “offsets” from other sources of pollution so that there is no net increase in air emissions within the airshed.
Visibility Protection
The last major program in Title I is Visibility Protection. This program is aimed at curbing visibility impairment at “mandatory Class I Federal areas” which are places like National Parks and Wilderness areas. A full list can be found here. The Visibility Program requires states to develop plans to reduce the impact of anthropogenic emissions on visibility in these areas. Among other requirements, the largest sources that were “grandfathered” under the New Source Review programs (i.e., built prior to 1977) must install the best achievable retrofit technology (BART).
Title II contains requirements for mobile sources, both “on road” and “non road” sources.
Title II regulates mobile sources of air pollution like cars, trucks, and airplanes. EPA can set standards for these mobile sources. With a notable exception, states are prohibited from adopting their own standards. The purpose of this preemption was to allow car companies and engine manufacturers reliability and prevent a patchwork of state regulations from making interstate sales of cars and engines more difficult. However, because it had adopted standards prior to the Clean Air Act and had and has serious problems with air pollution, California was allowed to adopt more stringent standards that those passed by EPA. Other states are then allowed to adopt the California standards in lieu of the federal standards, but are still prohibited from adopting their own, different, standards.
Regulations under Title II have become important in EPA’s actions to address climate change. During the Bush Administration, several states and environmental groups petitioned EPA asking it to regulate GHGs emissions from motor vehicles. EPA denied the petition claiming that it lacked authority to regulate carbon dioxide and other GHGs and even if it did, policy considerations supported not regulating these emissions. The petitioners challenged this decision in court, which eventually lead to the landmark case of Massachusetts v. EPA. In Massachusetts, the Supreme Court ruled that carbon dioxide and other GHGs were “pollutants” under the Clean Air Act and that EPA may not look outside the text of the Clean Air Act and refuse to issue regulations for other “policy” considerations.
During the Obama Administration, EPA issued its first GHGs standards for new cars. Interestingly, under a long standing EPA regulation and interpretation, this meant that major new stationary sources of GHGs were now subject to New Source Review. The regulation of GHGs under Title II has also lead to EPA proposing New Source Performance Standards for GHGs from electric generating units like coal and natural gas power plants.
Title III contains general provisions, including enforcement provisions.
Title III contains the general provisions of the Clean Air Act. The most important part of this Title is the citizen suit provision. When first passed in 1970, the citizen suit provision of the Clean Air Act was a bold first. Prior to the 1970’s Clean Air Act, there were very few opportunities for citizens to be directly involved with the enforcement of laws and regulations. Now citizens can be there to step in when the state and federal governments can’t or simply won’t enforce the requirements of the Clean Air Act. The citizen suit provision allows any “person” to file suit in federal court. “Person” is defined very broadly to include individuals, corporations, partnerships, municipalities, and States.
The citizen suit provision has a couple of important caveats. First, to sue a violator in federal court under the Clean Air Act, the requirement must be part of the State Implementation Plan (SIP) approved by EPA. Not all requirements under state law are incorporated into the SIP. For instance, in Oregon there are additional requirements in the Portland Metro area that have not been incorporated into the Oregon SIP; citizens therefore cannot sue a source in federal court for violating these requirements.
In most circumstances citizens also have to give the source, the state, and the federal government “notice” before filing suit. This is done in an “Intent to Sue” letter that lays out why the citizen believes the source violated the Clean Air Act. The citizen must wait 60 days after giving notice to file in federal court. This gives the state and federal governments an opportunity to bring their own lawsuit, which preempts filing a citizen suit, though citizens can join the state or federal lawsuit under most circumstances. The notice also gives the violator an opportunity to fix the violation or negotiate a settlement with the citizen. The notice requirement does not apply if the source is proposing to construct or constructing in violation of New Source Review permitting requirements or is violating the terms New Source Review construction permit.
The citizen suit provision allows citizens to seek injunctive relief in which a federal judge orders a company or individual to undertake some action or prohibits them from taking some action. In other words, remedy the violation. Violations of the Clean Air Act also subject sources to civil penalties, currently up to $37,500 per day per violation.
The citizen suit provision also gives citizens the right to sue the Environmental Protection Agency (EPA) for failure to perform a non-discretionary duty. For instance, the Clean Air Act requires EPA to update NSPS and NESHAPs on a set time table. If EPA fails to meet this time table, which it often does, citizens can sue EPA to force the updates.
Title IV addresses the problem of acid rain.
Added with the 1990 Clean Air Act Amendments, Title IV is aimed at addressing the problem of acid rain. Acid rain is caused by the presence of sulfur and nitrogen oxides. These pollutants, when trapped in the water vapor of clouds, form sulfuric and nitric acid. Acid rain causes significant damage to plants and wildlife. Title IV regulates the emissions of sulfur and nitrogen oxides, mainly from electric generating units like coal and natural gas power plants through a cap-and-trade system of allowances. The first phase, implemented in 1995, targeted the largest sources in the East and Midwest. The second phase, implemented in 2000, expanded the scope of the program.
Title V contains the major source operating permit program.
Title V was added to the Clean Air Act with the 1990 Amendments and is probably the most visible part of the Clean Air Act to the general public. However, the role of Title V is often misunderstood. Title V was added to address a very specific problem. Prior to 1990, a large number of facilities had multiple construction or modification permits. For instance, if an existing facility added a large emergency generator, it would get a construction permit, but only for that generator. This meant that the requirements a facility was subject to were contained in multiple permits. This made it hard for sources to know for sure that they were doing everything they were supposed to be doing and it made it hard for regulators and citizens to assess whether a source was in compliance with the Clean Air Act.
Congress’s solution, at least for large sources, was Title V. Title V establishes an operating permit requirement for large sources. These large sources are required to apply for a Title V operating permit. This operating permit includes all of the applicable requirements for that source, making it much easier to assess compliance. Title V does not add any new requirements, it simply rolls all existing requirements into one place.
Despite the fact that it does not add any new requirements, Title V is important for a number of reasons. It makes it much easier to assess compliance with Clean Air Act requirements. The five year permit term means that the regulators and sources must assess changes to regulations on a regular, if extended, basis. Title V also includes public notice and comment requirements which allow the public to review regulators’s determinations of applicable requirements. Title V also allows citizens to petition EPA to object to state regulators’ determinations.
On the whole, while not adding any new requirements, Title V is an important part of the Clean Air Act because it aggregates all requirements in one place and provides more public oversight of the regulation of the largest sources of air pollution.
Title VI implements the requirements of the Montreal Protocol on Ozone Depleting Substances.
Most people born after 1990 wouldn’t even know that at one point the international community was concerned about ozone depletion and something called the “Ozone Hole.” The Ozone Layer is a portion of the upper atmosphere that contains ozone (O3). Unlike ground-level ozone which is a health hazard, this atmospheric ozone is vitally important in blocking ultraviolet (UV) radiation from the sun. In the 1970’s, data showed a small but steady decrease in the concentration of ozone in this layer of the stratosphere. In the 1980’s researchers discovered a large area over Antarctica where ozone levels were significantly depressed, a phenomenon referred to as the Ozone Hole.
Response to ozone depletion was tepid until the the discovery of the Ozone Hole. In 1987, representatives from 43 countries signed the Montreal Protocol. The Montreal Protocol froze production levels of chlorofluorocarbons (CFCs) and signatories agreed to reduce production levels by 50% by 1999. These requirements where later strengthened to include the phase-out of CFCs except in “essential” cases. CFCs have generally been replaced by less damaging hydrochlorofluorocarbons (HCFCs). Title VI of the Clean Air Act implements all of the requirements that the United States has signed onto and regulates ozone depleting substances (ODS).
As a result of the international implementation of the Montreal Protocol and subsequent agreements, the concern over the worsening of the Ozone Hole and ozone depletion has for the most part subsided. Given the long atmospheric life of CFCs, recovery will take decades.
Good Neighbor
GOOD NEIGHBOR AGREEMENT
Industrial Sources of Hazardous Air Pollutants Neighbors for Clean Air has pushed for many industrial point sources to improve operations and go beyond the minimum requirements of the Clean Air Act and adopt what we call “best practices” for the control of hazardous air pollutants (HAPs, sometimes referred to as “toxic” air pollutants). We model our approach after the success Neighbors for Clean Air, working with the Northwest Environmental Defense Center (NEDC) and the local neighborhood association, had in negotiating a Good Neighbor Agreement with ESCO Corporation. This process relies upon an open and transparent evaluation of available emissions reduction opportunities, rather than the more common refrain from businesses that the “are doing everything we can.” When ESCO invested the energy in a transparent process with its neighbors it found over 20 different emission reductions opportunities, including changes to a process that had been going on for over 100 years. Neighbors for Clean Air is committed to pushing for all industrial point sources to undertake similar analyses with their neighbors and committing to undertake economically feasible emission reduction projects. Learn more about specific projects Neighbors for Clean Air has undertaken:
ESCO Corporation
Intel
Vigor Industrial

DIESEL PARTICULATE POLLUTION
Oregon becomes dumping ground for California’s old, polluting diesel big rigs
Stop Oregon from being a dumping ground for dirty diesel: Sign the petition!
Diesel = Needless Deaths
What Can You Do?
Data from the Portland Air Toxics Study shows that nonroad sources of diesel account for 39% of all diesel particulate matter and on-road diesel accounts for 49%. So we’re starting by asking Oregon to join our west coast neighbors in adopting more stringent standards for non-road and on-road diesel engines. You can help out by signing our petition and calling your legislator to urge them to support adopting California’s diesel standards.
Sign the petition!
Contact your legislator!
The Effect of Diesel Particulates
One of the most serious current threats to public health from air pollution comes from the burning of diesel oil. The burning of diesel produces ultra-fine particulate matter, or PM2.5 (particulate matter less than 2.5 microns). This diesel particulate matter is small enough that it can penetrate deep into the lungs and even cross over into the blood stream. Long-term exposure to diesel emissions is linked to both lung and bladder cancer. Children are particularly vulnerable to the impacts of diesel pollution because their lungs are still developing and they breathe, on average, 50 percent more air per pound of body weight than do adults.
Modeling by the Oregon Department of Environmental Quality (DEQ) showed that diesel particulates are a significant problem in the Portland Metro Area. On average, diesel particulates would need to be reduced by 86% in order to meet the benchmarks, which are set based on “acceptable risk” of 1 excess cancer in a million. And that’s using Oregon’s benchmark. Both Washington and California have standards that are at least 33 times lower.
Based on data from EPA, diesel particulate matter is responsible for approximately 460 premature deaths a year in Oregon. That’s more than those who die from homicide and drunk driving, combined. In total, it costs the State $2 to 4 billion a year in death, medical costs, disease, and lost work days. The Clean Air Task Force in Boston estimates that Oregonians have the sixth highest health risk from diesel soot in the country.
Where We Stand in Oregon
While Oregon has adopted California’s standards for new light- and medium-duty motor vehicles, we have not adopted the more stringent standards for heavy-duty motor vehicles or California’s more stringent standards for a variety of non-road engines, including more stringent standards for construction equipment.
EPA’s current standards for new heavy duty on-road diesel engines and new non-road diesel engines require large reductions in diesel particulate. Through the installation of filters, other control devices and using ultra-low sulfur diesel fuel, diesel particulate can be reduced by 90-99%. However, these standards only apply to new engines, not the engines that have already been manufactured and are in use. EPA is relying upon a presumed turnover rate, the rate at which old diesel engines are retired and new engines pressed into service, of approximately 10% per year.
California’s standards on the other hand, require fleets to meet certain percentages of clean diesel engines by certain dates, forcing the engines to be phased out or retrofitted. Unfortunately for Oregon, we’ve become the dumping ground for these old, dirtier diesel engines. These engines are sold into Oregon, where they can still be used, and newer, cleaner engines replace them in California. And unlike Washington, Oregon has not adopted an aggressive approach to helping business retrofit older engines – Oregon has relied on federal grants while Washington has added state dollars to their program. As a result, Oregon has retrofitted many fewer engines than Washington. This can be seen by Oregon’s actual turnover rate, which is only about 4%. That means that in Oregon it will take even longer to phase out or retrofit the old, dirty diesel engines with engines that would produce 90-99% less diesel particulate.

Why Should Oregon DEQ Enforce Nuisance?
Most, if not all, of the facilities that DEQ can regulate under its nuisance authority could also be subject to a civil tort suit for creating a private or public nuisance. So why has Neighbors for Clean Air been pushing DEQ to implement its authority when we could have filed a state tort lawsuit?
Two, interrelated, reasons are cost and environmental justice. Tort lawsuits can be very expensive between lawyers, experts, depositions, and all the other costs associated with filing, prosecuting, and winning the suit. Total costs are typically estimated in the tens of thousands of dollars. This also means that poorer communities are less likely to be able to afford to bring a tort suit for nuisance while more wealthy areas may be able to raise the funds, potentially creating different outcomes based on income levels.
Nuisance Odors
The Oregon Department of Environmental Quality (DEQ) revised its regulations in 2001 to prohibit any source subject to DEQ regulation to emit emissions that caused a nuisance (OAR 340-208-0300). This rule change included factors to consider and established the Best Work Practices program to deal with nuisance odors. While sometimes used colloquially a refer to a something not rising to a level of true concern (i.e., “the fly was just a nuisance”), in the law, “nuisance” is “a substantial and unreasonable interference with the use or enjoyment of property.” There are a variety of factors to be considered in determining whether a source is creating a nuisance. The non-inclusive list that is included in DEQ’s regulations include frequency, strength, duration, number of people affected, the character of the neighborhood, and the ability of the source to prevent or reduce the odor.
However, 12 years after the regulations were passed, Neighbors for Clean Air confronted DEQ on behalf of members in North Portland who were dealing with nuisance odors caused by a facility run by Daimler Trucks North America. In response to Neighbors for Clean Air’s claim that Daimler was causing a nuisance, DEQ said that they did not know how to implement their own regulations.
Thanks to public pressure and the involvement of elected officials, DEQ moved forward on developing a “Nuisance Odor Strategy” to give their inspectors a mechanism to implement DEQ’s regulations. DEQ’s Nuisance Odor Strategy was put out for public comment between April and July 2013 and finalized on July 31, 2013. After training management and permit writers/inspectors on the Nuisance Odor Strategy, DEQ announced the “full” implementation of the program on January 21, 2014, nearly thirteen years after the regulations were revised to prohibit nuisances.
It is still too early to tell whether or how successful DEQ’s implementation of its Nuisance Odor Strategy will be. Neighbors for Clean Air noted many deficiencies with the proposed program during the public comment period in 2013, including the fact that individual residents are still required to be responsible for determining the source of nuisance odors. While in some instances the source of odors is obvious, in others, especially near industrial sanctuaries, it is far from clear where the odor is coming from. Neighbors for Clean Air takes nuisance odors seriously: even if non-toxic, these odors can cause headaches or dizziness, ruin enjoyment of outdoor activities, or even force people inside. We continue to push DEQ to truly implement its regulations and protect Oregonians from nuisance odors.
Links
Oregon Department of Environmental Quality (DEQ)
Oregon DEQ is the state agency charged with implementing environmental laws including the Clean Air Act, the Clean Water Act, the Resource Conservation and Recovery Act (RCRA), and the Comprehensive Environmental Response, Compensation and Liability Act (CERCLA) (sometimes referred to as Superfund).
Oregon DEQ Facility Locator
Find facilities in your area
Portland Air Toxics Solution Project
The Portland Air Toxics Solution (PATS) was DEQ’s attempt to address air toxics in the Portland Metro area. While no regulations came out of the decade long process, the PATS does show clearly that we have a problem with air toxics in Portland.
The Smokestack Effect
The Smokestack Effect is a study conducted jointly between researched at University of Massachusetts-Amherst, Johns Hopkins, and the University of Maryland. Using data from the Toxic Release Inventory (TRI), the researches estimated the impact of industrial emissions on schools around the United States. In Oregon, 116 schools ranked in the bottom 10%. In Portland, many schools were in the bottom 5% and no school was better than the bottom 30%.

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