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air pollution

 
(¦er pə′lü·shən)

(ecology) The presence in the outdoor atmosphere of one or more contaminants such as dust, fumes, gas, mist, odor, smoke, or vapor in quantities and of characteristics and duration such as to be injurious to human, plant, or animal life or to property, or to interfere unreasonably with the comfortable enjoyment of life and property.


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Release into the atmosphere of gases, finely divided solids, or finely dispersed liquid aerosols at rates that exceed the capacity of the atmosphere to dissipate them or to dispose of them through incorporation into the biosphere. Dust storms in desert areas and smoke from forest and grass fires contribute to particulate and chemical air pollution. Volcanic activity is the major natural source of air pollution, pouring huge amounts of ash and toxic fumes into the atmosphere. Air pollution may affect humans directly, causing irritation of the eyes or coughing. More indirectly, its effects can be measured far from the source, as, for example, the fallout of tetraethyl lead from automobile exhausts, which has been observed in the oceans and on the Greenland ice sheet. Still less direct are possible effects on global climates. See also smog.

For more information on air pollution, visit Britannica.com.

The presence in the atmospheric environment of natural and artificial substances that affect human health or well-being, or the well-being of any other specific organism. Pragmatically, air pollution also applies to situations where contaminants impact structures and artifacts or esthetic sensibilities (such as visibility or smell). Most artificial impurities are injected into the atmosphere at or near the Earth's surface. The lower atmosphere (troposphere) cleanses itself of some of these pollutants in a few hours or days as the larger particles settle to the surface and soluble gases and particles encounter precipitation or are removed through contact with surface objects. Unfortunately, removal of some pollutants (for example, sulfates and nitrates) by precipitation and dry deposition results in acid deposition, which may cause serious environmental damage. Also, mixing of the pollutants into the upper atmosphere may dilute the concentrations near the Earth's surface, but can cause long-term changes in the chemistry of the upper atmosphere, including the ozone layer. See also Atmosphere; Troposphere.

Types of sources

Sources may be characterized in a number of ways. First, a distinction may be made between natural and anthropogenic sources. Another frequent classification is in terms of stationary (power plants, incinerators, industrial operations, and space heating) and moving (motor vehicles, ships, aircraft, and rockets) sources. Another classification describes sources as point (a single stack), line (a line of stacks), or area (city).

Different types of pollution are conveniently specified in various ways: gaseous, such as carbon monoxide, or particulate, such as smoke, pesticides, and aerosol sprays; inorganic, such as hydrogen fluoride, or organic, such as mercaptans; oxidizing substances, such as ozone, or reducing substances, such as oxides of sulfur and oxide s of nitrogen; radioactive substances, such as iodine-131; inert substances, such as pollen or fly ash; or thermal pollution, such as the heat produced by nuclear power plants.

Air contaminants are produced in many ways and come from many sources; it is difficult to identify all the various producers. Also, for some pollutants such as carbon dioxide and methane, the natural emissions sometimes far exceed the anthropogenic emissions.

Both anthropogenic and natural emissions are variable from year to year, depending on fuel usage, industrial development, and climate. In some countries where pollution control regulations have been implemented, emissions have been significantly reduced. For example, in the United States sulfur dioxide emissions dropped by about 30% between 1970 and 1992, and carbon monoxide (CO) emissions were cut by over 30% in the same period. However, in some developing countries emissions continually rise as more cars are put on the road and more industrial facilities and power plants are constructed. In dry regions, natural emissions of nitrogen oxides (NOx), carbon dioxide (CO2), and hydrocarbons can be greatly increased during a season with high rainfall and above-average vegetation growth.

The anthropogenic component of most estimates of the methane budget is about two-thirds. Ruminant production and emissions from rice paddies are regarded as anthropogenic because they result from human agricultural activities. The perturbations to carbon dioxide since the industrial revolution are also principally the result of human activities. These emissions have not yet equilibrated with the rest of the carbon cycle and so have had a profound effect on atmospheric levels, even though emissions from fossil fuel combustion are dwarfed by natural emissions.

Effects

The major concern with air pollution relates to its effects on humans. Since most people spend most of their time indoors, there has been increased interest in air-pollution concentrations in homes, workplaces, and shopping areas. Much of the early information on health effects came from occupational health studies completed prior to the implementation of general air-quality standards.

Air pollution principally injures the respiratory system, and health effects can be studied through three approaches, clinical, epidemiological, and toxicological. Clinical studies use human subjects in controlled laboratory conditions, epidemiological studies assess human subjects (health records) in real-world conditions, and toxicological studies are conducted on animals or simple cellular systems. Of course, epidemiological studies are the most closely related to actual conditions, but they are the most difficult to interpret because of the lack of control and the subsequent problems with statistical analysis. Another difficulty arises because of differences in response among different people. For example, elderly asthmatics are likely to be more strongly affected by sulfur dioxide than the teenage members of a hiking club. See also Epidemiology.

Damage to vegetation by air pollution is of many kinds. Sulfur dioxide may damage field crops such as alfalfa and trees such as pines, especially during the growing season (Fig. 1). Both hydrogen fluoride (HF) and nitrogen dioxide (NO2) in high concentrations have been shown to be harmful to citrus trees and ornamental plants, which are of economic, importance in central Florida. Ozone and ethylene are other contaminants that cause damage to certain kinds of vegetation.

Air pollution can affect the dynamics of the atmosphere through changes in longwave and shortwave radiation processes. Particles can absorb or reflect incoming short-wave solar radiation, keeping it from the Earth's surface during the day. Greenhouse gases can absorb long-wave radiation emitted by the Earth's surface and atmosphere.

Carbon dioxide, methane, fluorocarbons, nitrous oxides, ozone, and water vapor are important greenhouse gases. These represent a class of gases that selectively absorb long-wave radiation. This effect warms the temperature of the Earth's atmosphere and surface higher than would be found in the absence of an atmosphere (the greenhouse effect). Because the amount of greenhouse gases in the atmosphere is rising, there is a possibility that the temperature of the atmosphere will gradually rise, possibly resulting in a general warming of the global climate over a time period of several generations. See also Greenhouse effect.

Researchers are also concerned with pollution of the stratosphere (10–50 km or 6–30 mi above the Earth's surface) by aircraft and by broad surface sources. The stratosphere is important, because it contains the ozone layer, which absorbs part of the Sun's short-wave radiation and keeps it from reaching the surface. If the ozone layer is significantly depleted, an increase in skin cancer in humans is expected. Each 1% loss of ozone is estimated to increase the skin cancer rate 3–6%. See also Stratosphere.

Visibility is reduced as concentrations of aerosols or particles increase. The particles do not just affect visibility by themselves but also act as condensation nuclei for cloud or haze formation. In each of the three serious air-pollution episodes discussed above, smog (smoke and fog) were present with greatly reduced visibility.

Chemistry

Air pollution can be divided into primary and secondary compounds, where primary pollutants are emitted directly from sources (for example, carbon monoxide, sulfur dioxide) and secondary pollutants are produced by chemical reactions between other pollutants and atmospheric gases and particles (for example, sulfates, ozone). Most of the chemical transformations are best described as oxidation processes. In many cases these secondary pollutants can have significant environmental effects, such as acid rain and smog.

Smog is the best-known example of secondary pollutants formed by photochemical processes, as a result of primary emissions of nitric oxide (NO) and reactive hydrocarbons from anthropogenic sources such as transportation and industry as well as natural sources. Energy from the Sun causes the formation of nitrogen dioxide, ozone (O3), and peroxyacetalnitrate, which cause eye irritation and plant damage.

It has been shown that when emissions of sulfur dioxide and nitrogen oxide from tall power plant and other industrial stacks are carried over great distances and combined with emissions from other areas, acidic compounds can be formed by complex chemical reactions. In the absence of anthropogenic pollution sources, the average pH of rain is around 5.6 (slightly acidic). In the eastern United States, acid rain with a pH less than 5.0 has been measured and consists of about 65% dilute sulfuric acid, 30% dilute nitric acid, and 5% other acids.


air pollution

The addition of harmful chemicals to the atmosphere. The most serious air pollution results from the burning of fossil fuels, especially in internal-combustion engines.

Gale Encyclopedia of Public Health:

Ambient Air Quality

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Human exposures to airborne chemicals vary widely among inhalation microenvironment categories, which include workplaces, residences, outdoor ambient air, transportation, recreation areas, and public spaces. There are also wide variations in exposure within each category, depending on the number and strength of the sources of the airborne chemicals, the volume and mixing characteristics of the air within the defined microenvironment, the rate of air exchange between indoor and outdoor air, and the rate of loss to surfaces within the microenvironment.

Exposures to airborne chemicals in the workplace are extremely variable in terms of composition and concentration, depending on the materials being handled, the process design and operation, the kinds and degree of engineering controls applied to minimize releases to the air, work practices followed, and personal protection provided. Airborne chemicals in residential microenvironments are attributable to their presence in the air infiltrating from out of doors and to their release from indoor sources, such as unvented cooking stoves and space heaters, cigarettes, and consumer products, including volatile emissions from wallboard, textiles, carpets, and other materials. Indoor sources can release nitrogen dioxide (NO2), fine particle mass (FPM), and formaldehyde (HCHO) to such an extent that indoor concentrations for these chemicals can be much higher than those in ambient outdoor air.

For pollutants having National Ambient Air Quality Standards (NAAQS), such as particulate matter, NO2, carbon monoxide (CO), ozone (O2), lead (PB), and sulfur dioxide (SO2), there is an extensive network of fixed-site monitors, generally on rooftops. Although these devices generate large volumes of data, the concentrations at these sites may differ substantially from the concentrations that people breathe, especially for tailpipe pollutants such as carbon monoxide.

Transportation sources represent a significant source of exposures. Many people spend up to three hours each day in autos or buses as they go to work, to school, or shopping. Inhalation exposures to CO in vehicles and garages can represent a significant fraction of total CO exposures. Recreational exposure while exercising may also be important to total daily exposure because the increased respiratory ventilation associated with exercise can produce much more than proportional increases in delivered dose and functional responses.

Current concern regarding community air quality, is focused on particulate matter (PM) and ozone. A broad variety of processes produce suspended particulate matter (PM) in the ambient air in which we live and breathe, and there are statistically significant associations between the concentrations of airborne PM and the rates of mortality and morbidity in human populations. The PM concentrations have almost always been expressed in terms of mass. Also, in studies that reported on associations between health effects and more than one mass concentration, the strength of the association generally improves as one goes from total suspended particulate matter (TSP) to thoracic particulate matter (PM10 microns or less in aerodynamic diameter [PM10]), to fine particulate matter (PM2.5 microns or less in aerodynamic diameter [PM2.5]).

(SEE ALSO: Airborne Particles; Carbon Monoxide; Clean Air Act; Hazardous Air Pollutants; Inhalable Particles [Sulfates]; Lead; National Ambient Air Quality Standards; Smog [Air Pollution]; Sulfur-Containing Air Pollutants [Particulates]; Total Suspended Particles [TSP])

Bibliography

Lippmann, M., ed. (2000). Environmental Toxicants, 2nd edition. New York: Wiley.

U.S. Environmental Protection Agency (2001). Air Quality Criteria for Particulate Matter. EPA 600/P-99/002. Washington, DC: Author.

— MORTON LIPPMANN



The presence in the earth's atmosphere of man-caused, or man-made, contaminants which may adversely affect property, or the lives of plants, animals, or humans. Common air pollutants include: carbon dioxide, carbon monoxide, lead, nitrogen oxides, ozone, smoke, and sulphur dioxide. In 1988 the EC adopted a directive to limit emissions of sulphur dioxide, nitrogen oxides and dust from power stations above a certain capacity, and the most rigorous environmental protection targets in the 1990s have been set by the six founding states of the EC, together with Denmark. See ambient air standard. See also pollution.

Air Pollution became a matter of concern in the United States in the nineteenth century, when population growth and industrialization increased the number of wood and coal furnaces, which generated enough smoke to overwhelm natural air-filtering processes and threaten human health. Coal-burning facilities in industrial centers like Pittsburgh, Pennsylvania, and smelter towns like Butte, Montana, spewed tons of smoke, soot, ash, and gases into the atmosphere. Boosters often applauded the smoke as a sign of prosperity. But by the late nineteenth century the hazards of smoke were better understood. Airborne pollutants became especially dangerous when a so-called thermal inversion occurred, trapping the pollutants and allowing them to build up for days in warm air overlaid by a cold air mass. In these cases, human exposure could and did cause respiratory illnesses and deaths. As early as 1815 some local governments required that manufacturers control emissions, and during the Progressive Era most major cities passed ordinances to control the "smoke nuisance." However, events such as the Donora smog of 1948, a thermal inversion in which twenty residents of Donora, Pennsylvania, died and more than five thousand fell ill, suggested that local efforts to abate air pollution were not sufficiently safeguarding public health.

In 1955, Congress enacted the first federal air-quality legislation, providing research and technical assistance to states. States and localities remained responsible for regulating factory emissions and the brown automobile-induced "photochemical smog" over urban basins, but this act expanded federal authority over air-quality control. With the Clean Air Act of 1963 Congress increased aid to states and for the first time allowed federal control over automobile emissions. In 1965 Congress enacted a law requiring automakers to install emissions-reducing devices on all cars built and sold in the United States after 1967.

The Air Quality Act of 1967 dramatically expanded federal control. It authorized federal regulation of stationary as well as mobile pollution sources, required states to impose air-quality standards in problem regions, and allowed federal controls where states failed to act. The Clean Air Act of 1970, a centerpiece of the burgeoning environmental movement, directed the Environmental Protection Agency (EPA), established the previous year, to set National Ambient Air Quality Standards (NAAQS). Under this law the EPA identified the principal air pollutants (particulates, sulfur dioxide, carbon monoxide, hydrocarbons, nitrogen dioxide, ozone, and, after 1978, lead), set maximum allowable levels for each, and required that states draft plans for meeting the federal standards. The act also required that stationary polluters secure federal permits contingent on their use of "best available" abatement technology and mandated that automakers achieve a 90 percent decrease in vehicle emissions by 1985 (a timetable relaxed somewhat by amendments in 1977).

In general these laws set maximum pollutant levels but left it to the polluters to find ways to meet them. This tactic, called "technology forcing," spurred automakers to adopt catalytic converters in the 1970s and compelled the

"big three" automakers (GM, Ford, and Chrysler) in 1993 to launch their Clean Car Initiative, a joint pledge to develop vehicles averaging ninety miles per gallon by 2003. When California insisted that zero-emission vehicles account for 10 percent of all new cars in the state by 2003, setting a precedent that other large states like New York were likely to follow, automakers stepped up efforts to develop new emissions technology. Much research focused on the "hybrid," an electric car with a small, supplementary fuel-burning motor that could radically cut emissions and reduce gasoline consumption. The first mass-produced hybrid, a Honda, was available in the United States in 1999. Other research focused on hydrogen-fed fuel cells, whose only exhaust is water vapor.

Industrial interests pleaded for less-stringent standards, claiming air-pollution control is expensive and economically damaging. Industries blamed the soaring inflation of the 1970s on environmental-protection legislation. In response the EPA delayed requirements and devised strategies for reducing pollution without placing undue burdens on manufacturers. For example, the "bubble" concept, formally adopted in a 1979 amendment to the Clean Air Act, placed an imaginary bubble over an entire region and required the air in the bubble to meet NAAQS levels. Firms in the same bubble could trade pollution rights with each other, allowing excess pollution at one source as long as it was offset by lower emissions at another. (The previous approach had forced each individual "stack" to meet national standards.) By defining each factory as part of a larger air shed, the bubble concept was a step toward an ecosystem-oriented approach. Along these lines, the Clean Air Act of 1990 capped the nation's total sulfur oxide emissions and allowed firms to set up a nationwide market in pollution permits.

By the late 1990s, such measures had significantly reduced major air pollutants in most metropolitan areas. However, haze in scenic nonurban areas such as the Grand Canyon caused by nearby urban areas and power plants had emerged as a growing problem. Moreover, as environmentalists adopted an increasingly global perspective, they identified new air pollution issues. Among the issues was acid precipitation, sulfur dioxide and other chemicals that originate in industrial areas, drift across political borders, and wash out of the atmosphere with rain, snow, or fog, causing acid deposits in lakes and forests. Another new issue, especially following the discovery in 1985 of an "ozone hole" over Antarctica, was depletion of the Earth's ozone layer caused by chlorofluorocarbons (CFCs) used in aerosol propellants, foam plastics, refrigerants, and industrial processes. A third issue that entered environmental debates in the 1980s concerned the emission of "greenhouse gases," especially carbon dioxide, that trap heat in the Earth's atmosphere and, according to many scientists, cause global-scale climate changes. These transnational and global air-quality issues stoked the fears of the industrial interests regarding greater government intervention in their affairs. Such reactions reflect the "out of sight, out of mind" axiom that long characterized responses to air pollution. Efforts to control visible pollution, like smoke or smog, traditionally won widespread support. But the less visible and more theoretical problems attracted detractors, who questioned the scientific methods of pollution-control proponents and raised the specter of economic stagnation to forestall stricter regulations.

Along with global air quality, attention focused on indoor air quality. Radon, a naturally occurring radioactive gas that collects in basements across much of the nation, was identified as a significant carcinogen. Secondary tobacco smoke raised substantial alarm in the 1990s, when many businesses, municipalities, and even states (notably California in 1994) banned Smoking in indoor workplaces. Mold spores, chemical fumes, and other invisible pollutants that circulate indoors were identified as health hazards in the 1980s, giving rise to the term "sick building syndrome" and forcing businesses to listen more carefully when employees complained of "bad air" in the workplace. Thus despite massive government intervention and the hopes of some environmentalists, air pollution did not disappear. The most visible pollutants generally lessened, but research revealed that air pollution was more complex, widespread, and intimate than previously thought.

Bibliography

Andrews, Richard N. L. Managing the Environment, Managing Ourselves: A History of American Environmental Policy. New Haven, Conn.: Yale University Press, 1999.

Bailey, Christopher J. Congress and Air Pollution: Environmental Policies in the USA. Manchester, U.K., New York: Manchester University Press, 1998.

Grant, Wyn. Autos, Smog, and Pollution Control: The Politics of Air Quality Management in California. Aldershot, U.K., Brook-field, Vt.: Edward Elgar, 1995.

Hays, Samuel P. Beauty, Health, and Permanence: Environmental Politics in the United States, 1955–1985. New York: Cambridge University Press, 1987.

Miller, E. Willard, and Ruby M. Miller. Indoor Pollution: A Reference Handbook. Santa Barbara, Calif.: ABC–CLIO, 1998.

Stradling, David. Smokestacks and Progressives: Environmentalists, Engineers, and Air Quality in America, 1881–1951. Baltimore: Johns Hopkins University Press, 1999.

Switzer, Jacqueline Vaughn. Environmental Politics: Domestic and Global Dimensions. New York: St. Martin's Press, 1994.

—Dennis Williams/W. P.

Answer of the Day:

air pollution

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Smoggy London Town  
Smoggy London Town
Nowadays, cars are the main culprits responsible for air pollution; but, not so long ago, the blame lay with the burning of coal. One of the worst examples of this was London's Great Smog of 1952. Beginning on December 5 of that year, and lasting for about four days, the city was covered with smog. It was determined that the excessive burning of coal, combined with high pressure, near freezing temperatures and light winds, caused the smog to settle in over London. Thousands of untimely deaths due to respiratory failure were blamed on the smog, which entered the buildings, making it difficult to breathe and even to see.

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From our Archives: Today's Highlights, December 5, 2007

Columbia Encyclopedia:

air pollution

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air pollution, contamination of the air by noxious gases and minute particles of solid and liquid matter (particulates) in concentrations that endanger health. The major sources of air pollution are transportation engines, power and heat generation, industrial processes, and the burning of solid waste.

Sources of Air Pollution

The combustion of gasoline and other hydrocarbon fuels in automobiles, trucks, and jet airplanes produces several primary pollutants: nitrogen oxides, gaseous hydrocarbons, and carbon monoxide, as well as large quantities of particulates, chiefly lead. In the presence of sunlight, nitrogen oxides combine with hydrocarbons to form a secondary class of pollutants, the photochemical oxidants, among them ozone and the eye-stinging peroxyacetylnitrate (PAN). Nitrogen oxides also react with oxygen in the air to form nitrogen dioxide, a foul-smelling brown gas. In urban areas like Los Angeles where transportation is the main cause of air pollution, nitrogen dioxide tints the air, blending with other contaminants and the atmospheric water vapor to produce brown smog. Although the use of catalytic converters has reduced smog-producing compounds in motor vehicle exhaust emissions, studies have shown that in so doing the converters produce nitrous oxide, which contributes substantially to global warming.

In cities, air may be severely polluted not only by transportation but also by the burning of fossil fuels (oil and coal) in generating stations, factories, office buildings, and homes and by the incineration of garbage. The massive combustion produces tons of ash, soot, and other particulates responsible for the gray smog of cities like New York and Chicago, along with enormous quantities of sulfur oxides (which also may be result from burning coal and oil). These oxides rust iron, damage building stone, decompose nylon, tarnish silver, and kill plants. Air pollution from cities also affects rural areas for many miles downwind.

Every industrial process exhibits its own pattern of air pollution. Petroleum refineries are responsible for extensive hydrocarbon and particulate pollution. Iron and steel mills, metal smelters, pulp and paper mills, chemical plants, cement and asphalt plants-all discharge vast amounts of various particulates. Uninsulated high-voltage power lines ionize the adjacent air, forming ozone and other hazardous pollutants. Airborne pollutants from other sources include insecticides, herbicides, radioactive fallout, and dust from fertilizers, mining operations, and livestock feedlots.

Effects on Health and the Environment

Like photochemical pollutants, sulfur oxides contribute to the incidence of respiratory diseases. Acid rain, a form of precipitation that contains high levels of sulfuric or nitric acids, can contaminate drinking water and vegetation, damage aquatic life, and erode buildings. When a weather condition known as a temperature inversion prevents dispersal of smog, inhabitants of the area, especially children and the elderly and chronically ill, are warned to stay indoors and avoid physical stress. The dramatic and debilitating effects of severe air pollution episodes in cities throughout the world-such as the London smog of 1952 that resulted in 4,000 deaths-have alerted governments to the necessity for crisis procedures. Even everyday levels of air pollution may insidiously affect health and behavior. Indoor air pollution is a problem in developed countries, where efficient insulation keeps pollutants inside the structure. In less developed nations, the lack of running water and indoor sanitation can encourage respiratory infections. Carbon monoxide, for example, by driving oxygen out of the bloodstream, causes apathy, fatigue, headache, disorientation, and decreased muscular coordination and visual acuity.

Air pollution may possibly harm populations in ways so subtle or slow that they have not yet been detected. For that reason research is now under way to assess the long-term effects of chronic exposure to low levels of air pollution-what most people experience-as well as to determine how air pollutants interact with one another in the body and with physical factors such as nutrition, stress, alcohol, cigarette smoking, and common medicines. Another subject of investigation is the relation of air pollution to cancer, birth defects, and genetic mutations.

A relatively recently discovered result of air pollution are seasonal "holes" in the ozone layer in the atmosphere above Antarctica and the Arctic, coupled with growing evidence of global ozone depletion. This can increase the amount of ultraviolet radiation reaching the earth, where it damages crops and plants and can lead to skin cancer and cataracts. This depletion has been caused largely by the emission of chlorofluorocarbons (CFCs) from refrigerators, air conditioners, and aerosols. The Montreal Protocol of 1987 required that developed nations signing the accord not exceed 1986 CFC levels. Several more meetings were held from 1990 to 1997 to adopt agreements to accelerate the phasing out of ozone-depleting substances.

Solutions to Air Pollution

To combat pollution in the United States, the Clean Air Act Amendments of 1970 gave the Environmental Protection Agency (EPA) the authority to establish and enforce air pollution standards and to set emission standards for new factories and extremely hazardous industrial pollutants. The states were required to meet "ambient air quality standards" by regulating the emissions of various pollutants from existing stationary sources, such as power plants and incinerators, in part by the installation of smokestack scrubbers, electrostatic precipitators, and other filters. Auto manufacturers were mandated to install exhaust controls or develop less polluting engines. The Clean Air Act, as amended in 1977, authorized the EPA to impose stricter pollution standards and higher penalties for failure to comply with air quality standards.

In 1990 when the act was reauthorized it required most cities to meet existing smog reduction regulations by the year 2005. The 1990 amendments also expanded the scope and strength of the regulations for controlling industrial pollution. The result has been limited progress in reducing the quantities of sulfur dioxide, carbon monoxide, nitrogen oxide, ozone, particulate matter, and lead in the air. The EPA also regulated hazardous air pollutants, which in 1992 included mercury, beryllium, asbestos, vinylchloride, benzene, radioactive substances, and inorganic arsenic.

The most satisfactory long-term solutions to air pollution may well be the elimination of fossil fuels and the ultimate replacement of the internal-combustion engine. To these ends efforts have begun in the United States, Japan, and Europe to develop alternative energy sources (see energy, sources of), as well as different kinds of transportation engines, such as one powered by electricity. A system of pollution allowances based on trading emission rights has been established in the United States in an attempt to use the free market to reward pollution reductions, and the international sale of surplus emission rights is permitted under the Kyoto Protocol (see below). Other proposed solutions include raising electricity and gasoline rates to better reflect environmental costs and to discourage waste and inefficiency, and mechanical controls on coal-fired utility plants.

In 1992, 150 nations signed a treaty on global warming at the UN-sponsored summit on the environment in Rio de Janeiro. A UN Conference on Climate Change, held in Kyoto, Japan, in 1997, produced an international agreement to combat global warming by sharply reducing emissions of industrial gases. Although the United States abandoned the treaty in 2001, saying it was counter to U.S. interests, most other nations agreed that year on the details necessary to make the protocol a binding international treaty, and the necessary ratifications brought the treaty into force in 2005. Efforts to develop a new, more encompassing binding treaty that would build on Kyoto have been unsuccessful.

See environmentalism; pollution.

Bibliography

See R. G. Bond et al., Air Pollution (1972); U.S. Council on Environmental Quality, Environmental Quality (22d Annual Report, 1991); World Bank, World Development Report (1992).


This entry contains information applicable to United States law only.

Air pollution has plagued communities since the industrial revolution and even before. Airborne pollutants, such as gases, chemicals, smoke particles, and other substances, reduce the value of and ability to enjoy affected property and cause significant health and environmental problems. Despite the long history and significant consequences of this problem, effective legal remedies are relatively recent. Though some cities adopted air quality laws as early as 1815, air pollution at that time was seen as a problem best handled by local laws and ordinances. Only as the United States' cities continued to grow, and pollution and health concerns with them, did federal standards and a nationwide approach to air quality begin to emerge.

The earliest cases involving air pollution were likely to be brought because of a noxious smell, such as from a slaughterhouse, animal herd, or factory, that interfered with a landowner's ability to enjoy his or her property. These disputes were handled through the application of the nuisance doctrine, which provides that the possessor of land has a duty to make a reasonable use of his or her property in a manner that does not harm other individuals in the area. A person who polluted the air and caused harm to others was liable for breaching this duty and was required to pay damages or was enjoined (stopped through an injunction issued by a court) from engaging in the activities that created the pollution. In determining whether to enjoin an alleged polluter, courts balanced the damage to the plaintiff landowner's property against the hardship the defendant polluter would incur in trying to eliminate, or abate, the pollution. Courts often denied injunctions because the economic damage suffered by the defendant — and, by extension, the surrounding community, if the defendant was essential to the local economy — in trying to eliminate the pollution often outweighed the damage suffered by the plaintiff. Thus, in many cases, the plaintiff was left only with the remedy of money damages — a cash payment equal to the estimated monetary value of the damage caused by the pollution — and the polluting activities were allowed to continue.

Using the nuisance action to control widespread air pollution proved inadequate for other reasons as well. At common law, only the attorney general or local prosecutor could sue to abate a public nuisance (one that damages a large number of persons) unless a private individual could show "special" damage that was distinct from and more severe than that suffered by the general public. The private plaintiff with special damage had the necessary standing (legally protectible interest) to seek injunctive relief. The problem of standing has been corrected in some states through laws that allow a private citizen to sue to abate public nuisances such as air pollution, though these laws are by no means the norm. Yet another difficulty with the nuisance doctrine is the plaintiff's burden of showing that the harm she or he has experienced was caused by a particular defendant. Pollutants can derive from many sources. As a result, it can be difficult, if not impossible, to prove that a particular polluter is responsible for a particular problem. Lastly, nuisance law was useful only to combat particular polluters; it did not provide an ongoing and systematic mechanism for the regulation and control of pollution.

Early in the nineteenth century, a few U.S. cities recognized the shortcomings of common-law remedies and enacted local laws that attempted to address the problem of air pollution. Pittsburgh, in 1815, was one of the first to institute air quality laws. Others, like Chicago and Cincinnati, passed smoke control ordinances in 1881, and by 1912, twenty-three U.S. cities with populations of over two hundred thousand had passed smoke abatement laws.

Though the early court cases usually addressed polluted air as an interference with the enjoyment of property, scientists quickly discovered that air pollution also poses significant health and environmental risks. It is believed to contribute to the incidence of chronic diseases such as emphysema, bronchitis, and other respiratory illnesses and has been linked to higher mortality rates from other diseases, including cancer and heart disease.

The shortcomings associated with the common-law remedies to control air pollution and increasing alarm over the problem's long-range effects finally resulted in the development of state and federal legislation. The first significant legislation concerning air quality was the Air Pollution Control Act, enacted in 1955 (42 U.S.C.A. § 7401 et seq. [1955]). Also known as the Clean Air Act, it gave the secretary of health, education, and welfare the power to undertake and recommend research programs for air pollution control. Amendments passed during the 1960s authorized federal agencies to intervene to help abate interstate pollution in limited circumstances, to control emissions from new motor vehicles, and to provide some supervision and enforcement powers to states trying to control pollution. By the end of the 1960s, when it became clear that states had made little progress in combating air pollution, Congress toughened the Clean Air Act through a series of new laws, which were known as the Clean Air Act Amendments of 1970 (Pub. L. No. 91-604, 84 Stat. 1676 [Dec. 31, 1970]).

The 1970 amendments greatly increased federal authority and responsibility for addressing the problem of air pollution. They provided for, among other things, uniform national emissions standards for the hazardous air pollutants most likely to cause an increase in mortality or serious illness. Under the amendments, the states retained some regulatory authority, having "primary responsibility for assuring air quality within the entire geographic area comprising such state." Thus, states could not "opt out" of air pollution regulation and for the first time were required to attain certain air quality standards within a specified period of time. In addition, the amendments directed the administrator of the Environmental Protection Agency (EPA), which was also established in 1970, to institute national standards regarding ambient air quality for air pollutants endangering public health or welfare, in particular sulfur dioxide, carbon monoxide, and photochemical oxidants in the atmosphere. The EPA was also granted the authority to require levels of harmful pollutants to be brought within set standards before further industrial expansion would be permitted.

Despite the ambitious scope of the 1970 legislation, many of its goals were never attained. As a result, the Clean Air Act was extensively revised again in 1977 (Pub. L. No. 95-95, 91 Stat. 685 [Aug. 7, 1977]). One significant component of the 1977 amendments was the formulation of programs designed to inspect, control, and monitor vehicle emissions. The 1977 revisions also sought to regulate parking on the street, discourage automobile use in crowded areas, promote the use of bicycle lanes, and encourage employer-sponsored carpooling. Unlike the goals of several of the 1970 amendments, many of the 1977 reforms have become reality. Many states, with the help of federal funding, have developed programs that require automobiles to be tested regularly for emissions problems before they can be licensed and registered. The 1977 amendments also directed the EPA to issue regulations to reduce "haze" in national parks and other wilderness areas. Under these regulations the agency has sought to improve air quality in a number of areas, including the Grand Canyon in Arizona.

During the 1980s and 1990s, several environmental issues, including acid rain, global climate change, and the depletion of the ozone layer, gave rise to further federal regulation. Acid rain, which has caused significant damage to U.S. and Canadian lakes, is created when the sulfur from fossil fuels, such as coal, combines with oxygen in the air to create sulfur dioxide, a pollutant. The sulfur dioxide then combines with oxygen to form sulfate, which, when washed out of the air by fog, clouds, mist, or rain, becomes acid rain, with potentially catastrophic effects on vegetation and water. Amendments to the Clean Air Act in 1990 (Pub. L. No. 101-549, 104 Stat. 2399 [Nov. 15, 1990]) sought to address the challenges posed by acid rain by commissioning a number of federally sponsored studies, including an analysis of Canada's approach to dealing with acid rain and an investigation of the use of buffering and neutralizing agents to restore lakes and streams. The 1990 laws also directed the EPA to prepare a report on the feasibility of developing standards related to acid rain that would "protect sensitive and critically sensitive aquatic and terrestrial resources." In addition, the amendments provided for a controversial system of "marketable allowances," which authorize industries to emit certain amounts of sulfate and which can be transferred to other entities or "banked" for future use.

The problem of global climate change is linked to the accumulation of gases, including carbon dioxide and methane, in the atmosphere. Scientists disagree over the net effect of this pollution on the global climate: some argue that it produces global warming; others maintain that it gradually cools global temperatures. Scientists do agree that a sustained climate change in either direction could significantly affect the environment.

The 1990 amendments implemented a number of strategies to address changes in the global climate, including the commissioning of studies on options for controlling the emission of methane. The amendments also contain provisions to deal with the depletion of the ozone layer, which shields the earth from the harmful effects of the sun's radiation. Though the long-term consequences are hard to determine at this time, damage has already been seen in the form of a "hole" in the ozone layer over Antarctica. The destruction of the ozone layer is believed to be caused by the release into the atmosphere of chlorofluorocarbons (CFCs) and other similar substances. The 1990 laws include a ban on "nonessential uses" of ozone-depleting chemicals, and the placement of conspicuous warning labels on certain substances, indicating that their use harms public health and the environment by destroying the ozone in the upper atmosphere.

In the 1990s, the battle to control air pollution moved indoors, into homes and businesses. Studies have shown that people are exposed to higher concentrations of air pollution for longer periods of time inside buildings than out-of-doors. Furthermore, evidence indicates that this exposure is contributing to a rapidly increasing incidence of illness, thus costing businesses, taxpayers, and the government billions of dollars in health care costs and lost work time. The typical U.S. home contains many hazardous chemicals and substances, including radon, which has been linked to lung cancer and other ailments. Congress has responded to public concern about indoor air quality by requiring the EPA, with the Superfund Amendments and Reauthorization Act (SARA), to establish a program to study the problem and make appropriate recommendations (Superfund Amendments and Reauthorization Act of 1986, Pub. L. No. 99-499, 100 Stat. 1613 [codified as amended in scattered sections of 10 U.S.C.A., 26 U.S.C.A., 29 U.S.C.A., 33 U.S.C.A., and 42 U.S.C.A.]).

One contentious air pollution issue is the effect of smoking in public places, especially as it concerns the rights and health of nonsmokers. Many states have enacted legislation designed to protect nonsmokers in public places, and the battle between smokers and nonsmokers is also making its way into the courts. An increasing number of restaurants, airlines, and other public facilities have dealt with the problem by banning smoking completely.

See: Automobiles; Environmental Law; Environmental Protection Agency; Pollution; Surgeon General; Tobacco.

The addition of harmful chemicals to the atmosphere. The most serious air pollution results from the burning of fossil fuels, especially in internal-combustion engines.

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  • Disasters and Phenomena - air pollution: condition in which toxic substances are in atmosphere, esp. as a result of industrial and automobile emissions


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Air pollution is the introduction of chemicals, particulate matter, or biological materials that cause harm or discomfort to humans or other living organisms, or cause damage to the natural environment or built environment, into the atmosphere.

The atmosphere is a complex dynamic natural gaseous system that is essential to support life on planet Earth. Stratospheric ozone depletion due to air pollution has long been recognized as a threat to human health as well as to the Earth's ecosystems.

Indoor air pollution and urban air quality are listed as two of the world's worst pollution problems in the 2008 Blacksmith Institute World's Worst Polluted Places report.[1]

Contents

Pollutants

Before flue-gas desulfurization was installed, the emissions from this power plant in New Mexico contained excessive amounts of sulfur dioxide.
Schematic drawing, causes and effects of air pollution: (1) greenhouse effect, (2) particulate contamination, (3) increased UV radiation, (4) acid rain, (5) increased ground level ozone concentration, (6) increased levels of nitrogen oxides.

A substance in the air that can cause harm to humans and the environment is known as an air pollutant. Pollutants can be in the form of solid particles, liquid droplets, or gases. In addition, they may be natural or man-made.[2]

Pollutants can be classified as primary or secondary. Usually, primary pollutants are directly emitted from a process, such as ash from a volcanic eruption, the carbon monoxide gas from a motor vehicle exhaust or sulfur dioxide released from factories. Secondary pollutants are not emitted directly. Rather, they form in the air when primary pollutants react or interact. An important example of a secondary pollutant is ground level ozone — one of the many secondary pollutants that make up photochemical smog. Some pollutants may be both primary and secondary: that is, they are both emitted directly and formed from other primary pollutants.

Major primary pollutants produced by human activity include:

  • Sulphur oxides (SOx) - especially sulfur dioxide, a chemical compound with the formula SO2. SO2 is produced by volcanoes and in various industrial processes. Since coal and petroleum often contain sulfur compounds, their combustion generates sulfur dioxide. Further oxidation of SO2, usually in the presence of a catalyst such as NO2, forms H2SO4, and thus acid rain.[2] This is one of the causes for concern over the environmental impact of the use of these fuels as power sources.
  • Nitrogen oxides (NOx) - especially nitrogen dioxide are emitted from high temperature combustion, and are also produced naturally during thunderstorms by electrical discharge. Can be seen as the brown haze dome above or plume downwind of cities. Nitrogen dioxide is the chemical compound with the formula NO2. It is one of the several nitrogen oxides. This reddish-brown toxic gas has a characteristic sharp, biting odor. NO2 is one of the most prominent air pollutants.
  • Carbon monoxide (CO)- is a colourless, odorless, non-irritating but very poisonous gas. It is a product by incomplete combustion of fuel such as natural gas, coal or wood. Vehicular exhaust is a major source of carbon monoxide.
  • Carbon dioxide (CO2) - a colourless, odorless, non-toxic greenhouse gas also associated with ocean acidification, emitted from sources such as combustion, cement production, and respiration. It is otherwise recycled in the atmosphere in the carbon cycle.
  • Volatile organic compounds - VOCs are an important outdoor air pollutant. In this field they are often divided into the separate categories of methane (CH4) and non-methane (NMVOCs). Methane is an extremely efficient greenhouse gas which contributes to enhanced global warming. Other hydrocarbon VOCs are also significant greenhouse gases via their role in creating ozone and in prolonging the life of methane in the atmosphere, although the effect varies depending on local air quality. Within the NMVOCs, the aromatic compounds benzene, toluene and xylene are suspected carcinogens and may lead to leukemia through prolonged exposure. 1,3-butadiene is another dangerous compound which is often associated with industrial uses.
  • Particulate matter - Particulates, alternatively referred to as particulate matter (PM) or fine particles, are tiny particles of solid or liquid suspended in a gas. In contrast, aerosol refers to particles and the gas together. Sources of particulate matter can be man made or natural. Some particulates occur naturally, originating from volcanoes, dust storms, forest and grassland fires, living vegetation, and sea spray. Human activities, such as the burning of fossil fuels in vehicles, power plants and various industrial processes also generate significant amounts of aerosols. Averaged over the globe, anthropogenic aerosols—those made by human activities—currently account for about 10 percent of the total amount of aerosols in our atmosphere. Increased levels of fine particles in the air are linked to health hazards such as heart disease,[3] altered lung function and lung cancer.
  • Toxic metals, such as lead, cadmium and copper.
  • Chlorofluorocarbons (CFCs) - harmful to the ozone layer emitted from products currently banned from use.
  • Ammonia (NH3) - emitted from agricultural processes. Ammonia is a compound with the formula NH3. It is normally encountered as a gas with a characteristic pungent odor. Ammonia contributes significantly to the nutritional needs of terrestrial organisms by serving as a precursor to foodstuffs and fertilizers. Ammonia, either directly or indirectly, is also a building block for the synthesis of many pharmaceuticals. Although in wide use, ammonia is both caustic and hazardous.
  • Odors — such as from garbage, sewage, and industrial processes
  • Radioactive pollutants - produced by nuclear explosions, nuclear events, war explosives, and natural processes such as the radioactive decay of radon.

Secondary pollutants include:

  • Particulate matter formed from gaseous primary pollutants and compounds in photochemical smog. Smog is a kind of air pollution; the word "smog" is a portmanteau of smoke and fog. Classic smog results from large amounts of coal burning in an area caused by a mixture of smoke and sulfur dioxide. Modern smog does not usually come from coal but from vehicular and industrial emissions that are acted on in the atmosphere by ultraviolet light from the sun to form secondary pollutants that also combine with the primary emissions to form photochemical smog.
  • Ground level ozone (O3) formed from NOx and VOCs. Ozone (O3) is a key constituent of the troposphere. It is also an important constituent of certain regions of the stratosphere commonly known as the Ozone layer. Photochemical and chemical reactions involving it drive many of the chemical processes that occur in the atmosphere by day and by night. At abnormally high concentrations brought about by human activities (largely the combustion of fossil fuel), it is a pollutant, and a constituent of smog.
  • Peroxyacetyl nitrate (PAN) - similarly formed from NOx and VOCs.

Minor air pollutants include:

Persistent organic pollutants (POPs) are organic compounds that are resistant to environmental degradation through chemical, biological, and photolytic processes. Because of this, they have been observed to persist in the environment, to be capable of long-range transport, bioaccumulate in human and animal tissue, biomagnify in food chains, and to have potential significant impacts on human health and the environment.

Sources

Dust storm approaching Stratford, Texas
Controlled burning of a field outside of Statesboro, Georgia in preparation for spring planting

Sources of air pollution refer to the various locations, activities or factors which are responsible for the releasing of pollutants into the atmosphere. These sources can be classified into two major categories which are:

Anthropogenic sources (human activity) mostly related to burning different kinds of fuel

  • "Stationary Sources" include smoke stacks of power plants, manufacturing facilities (factories) and waste incinerators, as well as furnaces and other types of fuel-burning heating devices. In developing and poor countries, traditional biomass burning is the major source of air pollutants; traditional biomass includes wood, crop waste and dung.[6][7]
  • "Mobile Sources" include motor vehicles, marine vessels, aircraft and the effect of sound etc.
  • Chemicals, dust and controlled burn practices in agriculture and forestry management. Controlled or prescribed burning is a technique sometimes used in forest management, farming, prairie restoration or greenhouse gas abatement. Fire is a natural part of both forest and grassland ecology and controlled fire can be a tool for foresters. Controlled burning stimulates the germination of some desirable forest trees, thus renewing the forest.
  • Waste deposition in landfills, which generate methane. Methane is not toxic; however, it is highly flammable and may form explosive mixtures with air. Methane is also an asphyxiant and may displace oxygen in an enclosed space. Asphyxia or suffocation may result if the oxygen concentration is reduced to below 19.5% by displacement

Natural sources

  • Dust from natural sources, usually large areas of land with little or no vegetation
  • Methane, emitted by the digestion of food by animals, for example cattle
  • Radon gas from radioactive decay within the Earth's crust. Radon is a colorless, odorless, naturally occurring, radioactive noble gas that is formed from the decay of radium. It is considered to be a health hazard. Radon gas from natural sources can accumulate in buildings, especially in confined areas such as the basement and it is the second most frequent cause of lung cancer, after cigarette smoking
  • Smoke and carbon monoxide from wildfires
  • Vegetation, in some regions, emits environmentally significant amounts of VOCs on warmer days. These VOCs react with primary anthropogenic pollutants—specifically, NOx, SO2, and anthropogenic organic carbon compounds—to produce a seasonal haze of secondary pollutants.[8]
  • Volcanic activity, which produce sulfur, chlorine, and ash particulates

Emission factors

Industrial Air Pollution emissions

Air pollutant emission factors are representative values that people attempt to relate the quantity of a pollutant released to the ambient air with an activity associated with the release of that pollutant. These factors are usually expressed as the weight of pollutant divided by a unit weight, volume, distance, or duration of the activity emitting the pollutant (e.g., kilograms of particulate emitted per megagram of coal burned). Such factors facilitate estimation of emissions from various sources of air pollution. In most cases, these factors are simply averages of all available data of acceptable quality, and are generally assumed to be representative of long-term averages.

There are 12 compounds in the list of POPs. Dioxins and furans are two of them and are intentionally created by combustion of organics, like open burning of plastics. The POPs are also endocrine disruptor and can mutate the human genes.

The United States Environmental Protection Agency has published a compilation of air pollutant emission factors for a multitude of industrial sources.[9] The United Kingdom, Australia, Canada and many other countries have published similar compilations, as well as the European Environment Agency.[10][11][12][13]

Indoor air quality (IAQ)

A lack of ventilation indoors concentrates air pollution where people often spend the majority of their time. Radon (Rn) gas, a carcinogen, is exuded from the Earth in certain locations and trapped inside houses. Building materials including carpeting and plywood emit formaldehyde (H2CO) gas. Paint and solvents give off volatile organic compounds (VOCs) as they dry. Lead paint can degenerate into dust and be inhaled. Intentional air pollution is introduced with the use of air fresheners, incense, and other scented items. Controlled wood fires in stoves and fireplaces can add significant amounts of smoke particulates into the air, inside and out.[14] Indoor pollution fatalities may be caused by using pesticides and other chemical sprays indoors without proper ventilation.

Carbon monoxide (CO) poisoning and fatalities are often caused by faulty vents and chimneys, or by the burning of charcoal indoors. Chronic carbon monoxide poisoning can result even from poorly adjusted pilot lights. Traps are built into all domestic plumbing to keep sewer gas, hydrogen sulfide, out of interiors. Clothing emits tetrachloroethylene, or other dry cleaning fluids, for days after dry cleaning.

Though its use has now been banned in many countries, the extensive use of asbestos in industrial and domestic environments in the past has left a potentially very dangerous material in many localities. Asbestosis is a chronic inflammatory medical condition affecting the tissue of the lungs. It occurs after long-term, heavy exposure to asbestos from asbestos-containing materials in structures. Sufferers have severe dyspnea (shortness of breath) and are at an increased risk regarding several different types of lung cancer. As clear explanations are not always stressed in non-technical literature, care should be taken to distinguish between several forms of relevant diseases. According to the World Health Organisation (WHO), these may defined as; asbestosis, lung cancer, and Peritoneal Mesothelioma (generally a very rare form of cancer, when more widespread it is almost always associated with prolonged exposure to asbestos).

Biological sources of air pollution are also found indoors, as gases and airborne particulates. Pets produce dander, people produce dust from minute skin flakes and decomposed hair, dust mites in bedding, carpeting and furniture produce enzymes and micrometre-sized fecal droppings, inhabitants emit methane, mold forms in walls and generates mycotoxins and spores, air conditioning systems can incubate Legionnaires' disease and mold, and houseplants, soil and surrounding gardens can produce pollen, dust, and mold. Indoors, the lack of air circulation allows these airborne pollutants to accumulate more than they would otherwise occur in nature.

Health effects

Air pollution is a significant risk factor for multiple health conditions including respiratory infections, heart disease, and lung cancer, according to the WHO. The health effects caused by air pollution may include difficulty in breathing, wheezing, coughing and aggravation of existing respiratory and cardiac conditions. These effects can result in increased medication use, increased doctor or emergency room visits, more hospital admissions and premature death. The human health effects of poor air quality are far reaching, but principally affect the body's respiratory system and the cardiovascular system. Individual reactions to air pollutants depend on the type of pollutant a person is exposed to, the degree of exposure, the individual's health status and genetics.[citation needed]

The most common sources of air pollution include particulate matter, ozone, nitrogen dioxide, and sulfur dioxide. Both indoor and outdoor air pollution have caused approximately 3.3 million deaths worldwide. Children aged less than five years that live in developing countries are the most vulnerable population in terms of total deaths attributable to indoor and outdoor air pollution.[15]

The World Health Organization states that 2.4 million people die each year from causes directly attributable to air pollution, with 1.5 million of these deaths attributable to indoor air pollution.[16] "Epidemiological studies suggest that more than 500,000 Americans die each year from cardiopulmonary disease linked to breathing fine particle air pollution. . ."[17] A study by the University of Birmingham has shown a strong correlation between pneumonia related deaths and air pollution from motor vehicles.[18] Worldwide more deaths per year are linked to air pollution than to automobile accidents.[citation needed] Published in 2005 suggests that 310,000 Europeans die from air pollution annually.[citation needed] Causes of deaths include aggravated asthma, emphysema, lung and heart diseases, and respiratory allergies.[citation needed] The US EPA estimates that a proposed set of changes in diesel engine technology (Tier 2) could result in 12,000 fewer premature mortalities, 15,000 fewer heart attacks, 6,000 fewer emergency room visits by children with asthma, and 8,900 fewer respiratory-related hospital admissions each year in the United States.[citation needed]

The worst short term civilian pollution crisis in India was the 1984 Bhopal Disaster.[19] Leaked industrial vapours from the Union Carbide factory, belonging to Union Carbide, Inc., U.S.A., killed more than 25,000 people outright and injured anywhere from 150,000 to 600,000. The United Kingdom suffered its worst air pollution event when the December 4 Great Smog of 1952 formed over London. In six days more than 4,000 died, and 8,000 more died within the following months.[citation needed] An accidental leak of anthrax spores from a biological warfare laboratory in the former USSR in 1979 near Sverdlovsk is believed to have been the cause of hundreds of civilian deaths.[citation needed] The worst single incident of air pollution to occur in the United States of America occurred in Donora, Pennsylvania in late October, 1948, when 20 people died and over 7,000 were injured.[20]

A new economic study of the health impacts and associated costs of air pollution in the Los Angeles Basin and San Joaquin Valley of Southern California shows that more than 3800 people die prematurely (approximately 14 years earlier than normal) each year because air pollution levels violate federal standards. The number of annual premature deaths is considerably higher than the fatalities related to auto collisions in the same area, which average fewer than 2,000 per year.[21]

Diesel exhaust (DE) is a major contributor to combustion derived particulate matter air pollution. In several human experimental studies, using a well validated exposure chamber setup, DE has been linked to acute vascular dysfunction and increased thrombus formation.[22][23] This serves as a plausible mechanistic link between the previously described association between particulate matter air pollution and increased cardiovascular morbidity and mortality.

Effects on cardiovascular health

Air pollution is also emerging as a risk factor for stroke, particularly in developing countries where pollutant levels are highest.[24] A recent study also found an association in women between air pollution and ischemia, but not hemorrhagic stroke.[25] Air pollution has also been associated with increased incidence and mortality from coronary artery disease.[26]

Effects on cystic fibrosis

A study from around the years of 1999 to 2000, by the University of Washington, showed that patients near and around particulate matter air pollution had an increased risk of pulmonary exacerbations and decrease in lung function.[27] Patients were examined before the study for amounts of specific pollutants like Pseudomonas aeruginosa or Burkholderia cenocepacia as well as their socioeconomic standing. Participants involved in the study were located in the United States in close proximity to an Environmental Protection Agency.[clarification needed] During the time of the study 117 deaths were associated with air pollution. Many patients in the study lived in or near large metropolitan areas in order to be close to medical help. These same patients had higher level of pollutants found in their system because of more emissions in larger cities. As cystic fibrosis patients already suffer from decreased lung function, everyday pollutants such as smoke, emissions from automobiles, tobacco smoke and improper use of indoor heating devices could further compromise lung function.[28]

Effects on COPD and Asthma

Chronic obstructive pulmonary disease (COPD) includes diseases such as chronic bronchitis and emphysema.[29]

Researches have demonstrated increased risk of developing asthma [30] and COPD[31] from increased exposure to traffic-related air pollution. Additionally, air pollution has been associated with increased hosptializations and mortality from asthma and COPD.[32][33]

A study conducted in 1960-1961 in the wake of the Great Smog of 1952 compared 293 London residents with 477 residents of Gloucester, Peterborough, and Norwich, three towns with low reported death rates from chronic bronchitis. All subjects were male postal truck drivers aged 40 to 59. Compared to the subjects from the outlying towns, the London subjects exhibited more severe respiratory symptoms (including cough, phlegm, and dyspnea), reduced lung function (FEV1 and peak flow rate), and increased sputum production and purulence. The differences were more pronounced for subjects aged 50 to 59. The study controlled for age and smoking habits, so concluded that air pollution was the most likely cause of the observed differences.[34]

It is believed that much like cystic fibrosis, by living in a more urban environment serious health hazards become more apparent. Studies have shown that in urban areas patients suffer mucus hypersecretion, lower levels of lung function, and more self diagnosis of chronic bronchitis and emphysema.[35]

Possible links to cancer

A large Danish epidemiological study found an increased risk of lung cancer for patients who lived in areas with high nitrogen oxide concentrations. In this study, the association was higher for non-smokers than smokers.[36] There are also possible associations between air pollution and other forms of cancer, including cervical cancer and brain cancer.[37]

Effects on children

Cities around the world with high exposure to air pollutants have the possibility of children living within them to develop asthma, pneumonia and other lower respiratory infections as well as a low initial birth rate. Protective measures to ensure the youths' health are being taken in cities such as New Delhi, India where buses now use compressed natural gas to help eliminate the “pea-soup” smog.[38] Research by the World Health Organization shows there is the greatest concentration of particulate matter particles in countries with low economic world power and high poverty and population rates. Examples of these countries include Egypt, Sudan, Mongolia, and Indonesia. In the United States, the Clean Air Act was passed in 1970, however in 2002 at least 146 million Americans were living in non-attainment areas—regions in which the concentration of certain air pollutants exceeded federal standards.[39] Those pollutants are known as the criteria pollutants, and include ozone, particulate matter, sulfur dioxide, nitrogen dioxide, carbon monoxide, and lead. Because children are outdoors more and have higher minute ventilation they are more susceptible to the dangers of air pollution.

Health effects in relatively "clean" areas

Even in the areas with relatively low levels of air pollution, public health effects can be significant and costly, since a large number of people breathe in such pollutants. A 2005 scientific study for the British Columbia Lung Association showed that a small improvement in air quality (1% reduction of ambient PM2.5 and ozone concentrations) would produce a $29 million in annual savings in the Metro Vancouver region in 2010.[40] This finding is based on health valuation of lethal (death) and sub-lethal (illness) effects.

Reduction efforts

There are various air pollution control technologies and land use planning strategies available to reduce air pollution. At its most basic level land use planning is likely to involve zoning and transport infrastructure planning. In most developed countries, land use planning is an important part of social policy, ensuring that land is used efficiently for the benefit of the wider economy and population as well as to protect the environment.

Efforts to reduce pollution from mobile sources includes primary regulation (many developing countries have permissive regulations),[citation needed] expanding regulation to new sources (such as cruise and transport ships, farm equipment, and small gas-powered equipment such as lawn trimmers, chainsaws, and snowmobiles), increased fuel efficiency (such as through the use of hybrid vehicles), conversion to cleaner fuels (such as bioethanol, biodiesel, or conversion to electric vehicles).

Control devices

The following items are commonly used as pollution control devices by industry or transportation devices. They can either destroy contaminants or remove them from an exhaust stream before it is emitted into the atmosphere.

  • Particulate control
    • Mechanical collectors (dust cyclones, multicyclones)
    • Electrostatic precipitators An electrostatic precipitator (ESP), or electrostatic air cleaner is a particulate collection device that removes particles from a flowing gas (such as air) using the force of an induced electrostatic charge. Electrostatic precipitators are highly efficient filtration devices that minimally impede the flow of gases through the device, and can easily remove fine particulate matter such as dust and smoke from the air stream.
    • Baghouses Designed to handle heavy dust loads, a dust collector consists of a blower, dust filter, a filter-cleaning system, and a dust receptacle or dust removal system (distinguished from air cleaners which utilize disposable filters to remove the dust).
    • Particulate scrubbersWet scrubber is a form of pollution control technology. The term describes a variety of devices that use pollutants from a furnace flue gas or from other gas streams. In a wet scrubber, the polluted gas stream is brought into contact with the scrubbing liquid, by spraying it with the liquid, by forcing it through a pool of liquid, or by some other contact method, so as to remove the pollutants.
  • Mercury control
    • Sorbent Injection Technology
    • Electro-Catalytic Oxidation (ECO)
    • K-Fuel

Legal regulations

Smog in Cairo

In general, there are two types of air quality standards. The first class of standards (such as the U.S. National Ambient Air Quality Standards and E.U. Air Quality Directive) set maximum atmospheric concentrations for specific pollutants. Environmental agencies enact regulations which are intended to result in attainment of these target levels. The second class (such as the North American Air Quality Index) take the form of a scale with various thresholds, which is used to communicate to the public the relative risk of outdoor activity. The scale may or may not distinguish between different pollutants.

Canada

In Canada air pollution and associated health risks are measured with the The Air Quality Health Index or (AQHI). It is a health protection tool used to make decisions to reduce short-term exposure to air pollution by adjusting activity levels during increased levels of air pollution.

The Air Quality Health Index or "AQHI" is a federal program jointly coordinated by Health Canada and Environment Canada. However, the AQHI program would not be possible without the commitment and support of the provinces, municipalities and NGOs. From air quality monitoring to health risk communication and community engagement, local partners are responsible for the vast majority of work related to AQHI implementation. The AQHI provides a number from 1 to 10+ to indicate the level of health risk associated with local air quality. Occasionally, when the amount of air pollution is abnormally high, the number may exceed 10. The AQHI provides a local air quality current value as well as a local air quality maximums forecast for today, tonight and tomorrow and provides associated health advice.

1 2 3 4 5 6 7 8 9 10 +
Risk: Low (1-3) Moderate (4-6) High (7-10) Very high (above 10)

As it is now known that even low levels of air pollution can trigger discomfort for the sensitive population, the index has been developed as a continuum: The higher the number, the greater the health risk and need to take precautions. The index describes the level of health risk associated with this number as ‘low’, ‘moderate’, ‘high’ or ‘very high’, and suggests steps that can be taken to reduce exposure.

[41]

Health Risk Air Quality Health Index Health Messages
At Risk population *General Population
Low 1-3 Enjoy your usual outdoor activities. Ideal air quality for outdoor activities
Moderate 4-6 Consider reducing or rescheduling strenuous activities outdoors if you are experiencing symptoms. No need to modify your usual outdoor activities unless you experience symptoms such as coughing and throat irritation.
High 7-10 Reduce or reschedule strenuous activities outdoors. Children and the elderly should also take it easy. Consider reducing or rescheduling strenuous activities outdoors if you experience symptoms such as coughing and throat irritation.
Very high Above 10 Avoid strenuous activities outdoors. Children and the elderly should also avoid outdoor physical exertion. Reduce or reschedule strenuous activities outdoors, especially if you experience symptoms such as coughing and throat irritation.

[42]

It is measured based on the observed relationship of Nitrogen Dioxide (NO2), ground-level Ozone (O3) and particulate matter (PM2.5) with mortality from an analysis of several Canadian cities. Significantly, all three of these pollutants can pose health risks, even at low levels of exposure, especially among those with pre-existing health problems.

When developing the AQHI, Health Canada’s original analysis of health effects included five major air pollutants: particulate matter, ozone, and nitrogen dioxide (NO2), as well as sulfur dioxide (SO2), and carbon monoxide (CO). The latter two pollutants provided little information in predicting health effects and were removed from the AQHI formulation.

The AQHI does not measure the effects of odour, pollen, dust, heat or humidity.

Cities

Nitrogen dioxide concentrations as measured from satellite 2002-2004

Air pollution is usually concentrated in densely populated metropolitan areas, especially in developing countries where environmental regulations are relatively lax or nonexistent[citation needed]. However, even populated areas in developed countries attain unhealthy levels of pollution with Los Angeles and Rome[43] being two good examples.

NATA

The National-Scale Air Toxics Assessment (NATA) is EPA's ongoing comprehensive evaluation of air toxics in the U.S. EPA developed the NATA as a state-of-the-science screening tool for State/Local/Tribal Agencies to prioritize pollutants, emission sources and locations of interest for further study in order to gain a better understanding of risks. NATA assessments do not incorporate refined information about emission sources, but rather, use general information about sources to develop estimates of risks which are more likely to overestimate impacts than underestimate them. NATA provides estimates of the risk of cancer and other serious health effects from breathing (inhaling) air toxics in order to inform both national and more localized efforts to identify and prioritize air toxics, emission source types and locations which are of greatest potential concern in terms of contributing to population risk. This in turn helps air pollution experts focus limited analytical resources on areas and or populations where the potential for health risks are highest. Assessments include estimates of cancer and non-cancer health effects based on chronic exposure from outdoor sources, including assessments of non-cancer health effects for Diesel Particulate Matter (PM). Assessments provide a snapshot of the outdoor air quality and the risks to human health that would result if air toxic emissions levels remained unchanged.[44]

Governing Urban Air Pollution – a regional example (London)

In Europe, Council Directive 96/62/EC on ambient air quality assessment and management provides a common strategy against which member states can “set objectives for ambient air quality in order to avoid, prevent or reduce harmful effects on human health and the environment . . . and improve air quality where it is unsatisfactory”.[45]

On 25 July 2008 in the case Dieter Janecek v Freistaat Bayern CURIA, the European Court of Justice ruled that under this directive[45] citizens have the right to require national authorities to implement a short term action plan that aims to maintain or achieve compliance to air quality limit values.[46]

This important case law appears to confirm the role of the EC as centralised regulator to European nation-states as regards air pollution control. It places a supranational legal obligation on the UK to protect its citizens from dangerous levels of air pollution, furthermore superseding national interests with those of the citizen.

In 2010, the European Commission (EC) threatened the UK with legal action against the successive breaching of PM10 limit values.[47] The UK government has identified that if fines are imposed, they could cost the nation upwards of £300 million per year.[48]

In March 2011, the City of London remains the only UK region in breach of the EC’s limit values, and has been given 3 months to implement an emergency action plan aimed at meeting the EU Air Quality Directive.[49] The City of London has dangerous levels of PM10 concentrations, estimated to cause 3000 deaths per year within the city.[50] As well as the threat of EU fines, in 2010 it was threatened with legal action for scrapping the western congestion charge zone, which is claimed to have led to an increase in air pollution levels.[51]

In response to these charges, Boris Johnson, Mayor of London, has criticised the current need for European cities to communicate with Europe through their nation state’s central government, arguing that in future “A great city like London” should be permitted to bypass its government and deal directly with the European Commission regarding its air quality action plan.[49]

In part, this is an attempt to divert blame away from the Mayors office, but it can also be interpreted as recognition that cities can transcend the traditional national government organisational hierarchy and develop solutions to air pollution using global governance networks, for example through transnational relations. Transnational relations include but are not exclusive to national governments and intergovernmental organisations [52] allowing sub-national actors including cities and regions to partake in air pollution control as independent actors.

Particularly promising at present are global city partnerships.[53] These can be built into networks, for example the C40 network, of which London is a member. The C40 is a public ‘non-state’ network of the world’s leading cities that aims to curb their greenhouse emissions.[53] The C40 has been identified as ‘governance from the middle’ and is an alternative to intergovernmental policy.[54] It has the potential to improve urban air quality as participating cities “exchange information, learn from best practices and consequently mitigate carbon dioxide emissions independently from national government decisions”.[53] A criticism of the C40 network is that its exclusive nature limits influence to participating cities and risks drawing resources away from less powerful city and regional actors.

Carbon dioxide emissions

Most Polluted World Cities by PM[55]
Particulate
matter,
μg/m³ (2004)
City
168 Cairo, Egypt
150 Delhi, India
128 Kolkata, India (Calcutta)
125 Tianjin, China
123 Chongqing, China
109 Kanpur, India
109 Lucknow, India
104 Jakarta, Indonesia
101 Shenyang, China
Total CO2 emissions
Countries with the highest CO2 emissions
Country Carbon dioxide emissions per
year (106 Tons) (2006)
Percentage of global total Avg. emission
per Km2 of its land (Tons)
 China 6,103 21.5% 636
 United States 5,752 20.2% 597
 Russia 1,564 5.5% 91
 India 1,510 5.3% 459
 Japan 1,293 4.6% 3421
 Germany 805 2.8% 2254
 United Kingdom 568 2.0% 2338
 Canada 544 1.9% 54
 South Korea 475 1.7% 4758
 Italy 474 1.7% 1573


Per capita CO2 emissions[56]
Countries with the highest per capita CO2 emissions
Country Carbon dioxide emissions per year
(Tons per person) (2006)
 Qatar 56.2
 United Arab Emirates 32.8
 Kuwait 31.2
 Bahrain 28.8
 Trinidad and Tobago 25.3
 Luxembourg 24.5
 Netherlands Antilles 22.8
 Aruba 22.3
 United States 19
 Australia 18.1


Atmospheric dispersion

The basic technology for analyzing air pollution is through the use of a variety of mathematical models for predicting the transport of air pollutants in the lower atmosphere. The principal methodologies are:

Visualization of a buoyant Gaussian air pollution dispersion plume as used in many atmospheric dispersion models

The point source problem is the best understood, since it involves simpler mathematics and has been studied for a long period of time, dating back to about the year 1900. It uses a Gaussian dispersion model for buoyant pollution plumes to forecast the air pollution isopleths, with consideration given to wind velocity, stack height, emission rate and stability class (a measure of atmospheric turbulence).[57][58] This model has been extensively validated and calibrated with experimental data for all sorts of atmospheric conditions.

The roadway air dispersion model was developed starting in the late 1950s and early 1960s in response to requirements of the National Environmental Policy Act and the U.S. Department of Transportation (then known as the Federal Highway Administration) to understand impacts of proposed new highways upon air quality, especially in urban areas. Several research groups were active in this model development, among which were: the Environmental Research and Technology (ERT) group in Lexington, Massachusetts, the ESL Inc. group in Sunnyvale and California, California Air Resources Board group in Sacramento, California. The research of the ESL group received a boost with a contract award from the United States Environmental Protection Agency to validate a line source model using sulfur hexafluoride as a tracer gas. This program was successful in validating the line source model developed by ESL inc. Some of the earliest uses of the model were in court cases involving highway air pollution, the Arlington, Virginia portion of Interstate 66 and the New Jersey Turnpike widening project through East Brunswick, New Jersey.

Area source models were developed in 1971 through 1974 by the ERT and ESL groups, but addressed a smaller fraction of total air pollution emissions, so that their use and need was not as widespread as the line source model, which enjoyed hundreds of different applications as early as the 1970s. Similarly photochemical models were developed primarily in the 1960s and 1970s, but their use was more specialized and for regional needs, such as understanding smog formation in Los Angeles, California.

Environmental impacts of greenhouse gas pollutants

The greenhouse effect is a phenomenon whereby greenhouse gases create a condition in the upper atmosphere causing a trapping of heat and leading to increased surface and lower tropospheric temperatures. Carbon dioxide emissions from combustion of fossil fuels are a source of greenhouse gas emissions.

Other greenhouse gases include methane, hydrofluorocarbons, perfluorocarbons, chlorofluorocarbons, nitrogen oxides, and ozone.

This effect has been understood by scientists for about a century, and technological advancements during this period have helped increase the breadth and depth of data relating to the phenomenon. Currently, scientists are studying the role of changes in composition of greenhouse gases from natural and anthropogenic sources for the effect on climate change.

A number of studies have also investigated the potential for long-term rising levels of atmospheric carbon dioxide to cause increases in the acidity of ocean waters and the possible effects of this on marine ecosystems.

See also

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External links

Air quality science and general information
Air quality modelling
Effects on human health

 
 
Related topics:
smog (meteorology)
photochemical smog
airborne contaminants

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