Air Pollution Research Paper

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The economy extracts natural resources from the environment to be used as inputs in production processes (the source function of the environment). The output of these production processes may be either produced inputs for yet other production  processes or final products to  be directly consumed. Yet these produced inputs and final products are not the entirety of the output; there are also residual by-products of these processes (waste).

Just as the economy extracts natural resources from the environment, the economy in turn dumps many residual by-products, or waste, back into the environment (the sink function of the environment). There is waste at each stage of the economic process: waste from extracting and refining natural resources, waste emanating from production processes, waste in the marketing of products, and waste in the sphere of consumption. Wastes may be solid, airborne, or waterborne. Air pollution describes airborne wastes that can harm the environment and human health due to their accumulation in the atmosphere, their concentration  geo-spatially, and/or  their  synergistic effects when combining with other wastes.

There is an interesting relationship between the total natural resources utilized and the total waste produced by the economy. That is, they are ultimately equivalent. This is due to the first law of thermodynamics, which states that matter-energy can neither be created nor destroyed; only the form of matter-energy can change. Of course, it is  more  complicated  than  a  simple equality.  Natural resources are frozen in the form of capital goods during the depreciation process (and capital goods from previous periods are at differing stages in the depreciation process), and there is a time element in the consumption of many final products as well. At a fundamental level, however, the equality holds.

Resources and Pollution

Some wastes are recyclable or reusable and others are not. The fact that all waste is not recyclable or reusable is due to the second law of thermodynamics, which states that any utilization of matter-energy decreases the total available matter-energy. In other words, some of the forms into which matter-energy is transformed can no  longer be accessed. This is also known as the entropy law, and put differently means that not all the forms into which matter and  energy are transformed are recyclable or  reusable. That waste which is not recycled or reused is dumped into the environment.

The environment has an assimilative capacity, which is the ability of the environment to transform waste into harmless (or  even beneficial) forms. This  assimilative capacity, however, is not infinite. Waste at some level is not only incapable of being assimilated, but will damage or even destroy the assimilative capacity itself.

It is not simply the level of homogeneous waste in relation to the assimilative capacity that needs to be considered, but additionally what specific types of waste are being emitted.  Some types of waste (e.g., mercury) are not assimilable in any quatity, and at some stock level can result in various detrimental effects, including damage to the assimilative capacity itself. In addition, it is not sufficient to simply look at each type of waste and the quantity of it emitted in isolation, one must consider also its synergistic effects. The combinations of different forms of waste have effects that are more damaging than the sum of the component waste products independent of one another. A classic case here is sulfur dioxide and nitric oxide resulting in acid precipitation (acid rain, fog, and snow).

The qualities and quantities of waste globally along with spatial considerations concerning the local concentration of wastes are crucial. And it is not simply the case that the  assimilative capacity detoxifies or  degrades waste instantaneously, or  even within  some set time  period. There are cumulation effects that have to be dealt with. So in assessing the ability of the assimilative capacity to deal with industrial and other waste, combination effects, concentration effects, and cumulation effects all need to be carefully considered.

Furthermore, nothing guarantees that all waste that is capable of being recycled or reused is  being recycled or reused. All waste, whether recyclable or  not,  which is dumped into the environment, may impact on the assimilative capacity. Therefore, when considering the quantities and qualities of wastes confronting the assimilative capacity, only those residuals may be exempted that are actually recycled. Generally speaking, the technologies do not yet exist to capture and recycle airborne emissions.

 

Evolution of Air Pollution Regulation

In the United States, early air pollution laws were enacted locally in Chicago and Cincinnati. These were smoke control laws that addressed only smoke emissions from coal burning. Before 1948, there was almost no real government intervention in the environment, which means that there  was, by  default,  a  market  approach  to  natural resource use and environmental protection.

An early recorded disaster resulting from air pollution occurred in Belgium in 1930. A thermal inversion occurred in an area characterized by concentrated industry with substantial amounts of sulfur dioxide emissions and discharges of particulate matter.  Air circulation, which requires horizontal or vertical air currents, is one of the keys to the dispersal of air pollution. If there is no horizontal wind movement, then vertical air currents will usually disperse the pollutants due to the fact that atmospheric temperature is inversely related to height. The temperature falls by 5.4 degrees Fahrenheit every thousand feet above the Earth’s surface. So normally, the warm polluted air, being lighter, will rise and disperse into the cooler air.

However, if the temperature decrease is less than 5.4 degrees Farenheit per thousand feet, warm air, unable to rise because of the existence of even warmer air above it, hovers over the source of the pollution, trapping concentrated pollutants in the lower stratum. This phenomenon is called thermal inversion.

The thermal inversion in Belgium in 1930 resulted in sixty-three deaths and  five thousand  people becoming seriously ill.  A  similar  episode  occurred  in  Donora, Pennsylvania, a small industrial town thirty miles south of Pittsburgh, in 1948. Twenty people died and six thousand became ill. Thermal inversion combined with pollution and fog killed four thousand and caused numerous respiratory illnesses in London in 1952.

In the United States, the Donora incident led to a greater awareness of the problem of air pollution,  and eventually to the Air Pollution Act of 1955. Although this act did little more than  authorize and provide limited funding  for research, it  served as the  basis for future amendments  to  the  Act. The  Clean  Air Act of 1963 authorized the Public Health  Service to take corrective action in addressing problems of interstate air pollution, and  1965  amendments  gave the  federal program  the authority to curb auto emissions. The first standards for motor vehicle emissions were applied in 1968.

The Air Quality Act of 1967 strengthened the powers of state and local as well as federal authorities to set and enforce standards on a regional basis. This paved the way for the Clean Air Act of 1970, which was the first legislation to call for uniform air quality standards based on geographic regions.

The newly created Environmental Protection Agency (EPA) was given the authority to enforce two sets of standards: primary and secondary. Primary air quality standards concern the minimum air quality necessary to keep people from  getting ill. These standards are based on proven harmful effects of individual pollutants. Secondary standards are intended to promote the general public welfare and prevent damage to plants, animals, and property in general. Within  each geographic region, states determine how these standards are to be met.

Market Approaches to Air Pollution

Direct regulation or standards have been criticized on a number of grounds and have given rise to market approaches. Pollution taxes have been used, which it has been argued gives firms an incentive to reduce their emissions and is a lower cost method than command and control. The problem with such taxes or fees is identifying and calculating the social costs, and even if that is possible, there is no guarantee that they will reduce emissions to levels consistent with assimilative capacity.

These problems resulted in the market permits and emissions trading approach, which entails a market in pollution  rights. The  government makes some maximum allowable emissions standards, but then auctions off pollution permits to the highest bidders. Firms could purchase in the original market directly from the government or in secondary markets from other firms or individuals who purchased directly from the government, or in secondary markets themselves. Only after having acquired the right to pollute could a firm discharge polluting emissions. Here  there is a tax incentive: The  firm pays to reduce emissions and to seek ways of producing that pollute less, but the difference is that the total amount of pollution is fixed. In this sense, the market permit approach combines the strengths of both direct regulation and market approaches.

The market permits approach is not without its critics however. Many see the practice as government auctioning off clean air to the highest bidder. These issues are becoming particularly important  as scientific evidence about problems such as global climate change becomes more reliable and available.

Bibliograhy:

  1. Baumol, W 1972. On Taxation and the Control of Externalities. American Economic Review. 62 (3): 307–322.
  2. Georgescu-Roegen, N 1971. The Entropy Law and the Economic Process. Cambridge, MA: Harvard University Press.
  3. Heilbroner, Rober 1950. What Goes Up the Chimney. Harper’s (January): 61–69.
  4. Intergovernmental Panel on Climate Change (IPCC). Climate Change 2007: The Physical Science Basis. Geneva: WMO, IPCC Secretariat.
  5. Kapp, Karl W. The Social Costs of Private Enterprise. Cambridge, MA: Harvard University Press.
  6. Tietenberg, 1985. Emissions Trading: An Exercise in Reforming Pollution Policy. Washington, DC: Resources for the Future.

See also:

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