LOCAL GROWTH COALITIONS 9In this period, and leading into the 1970s, the substantive politics andpolicies dealing with air pollution were taking place in various localities. Itwas those areas in particular that had a heavy dependence on coal that facedthe most significant air pollution problem. Moreover, it was those areas thatwere most dependent on soft coal where air pollution was most acute and persistent.Not surprisingly, it is in these areas where the politics of air pollutionwere most intense. Major cities that were plagued with extremely poor airquality, and with the highest level of political activity surrounding the issueof air quality, included New York, Pittsburgh, Chicago, St. Louis, Cincinnati,and Birmingham (Grinder 1980; Stradling 1999; Dewey 2000).Once industrial manufacturers, utilities, and railroads in the post–WorldWar II period moved in large part to oil and natural gas as a source of fuel,cities like Chicago and Pittsburgh experienced drastically improved air quality.During this period, however, a new threat to clean air emerged—the automobile.Now cities such as Los Angeles began to face serious air pollutionproblems. It was the air pollution politics arising from Los Angeles that ledto the first serious effort to address airborne pollution from the automobile.Again, the federal government remained largely on the sidelines in the 1950sand 1960s while states like California undertook major efforts to curb automobileemissions (Krier and Ursin 1977).It was only after the environmental social movement of the late 1960sand early 1970s that the federal government assumed a direct role on theissue of air pollution. The federal government’s post-1970s effort in thisarea, however, has been criticized as weak. Matthew Cahn (1995), drawinginspiration from the work of Murray Edelman (1964; 1988), goes so far asto label federal air pollution policies as “symbolic.” He holds that they servemore as a mechanism to assuage public opinion than a concerted attemptto remedy the nation’s air quality problems. Indicative of the weak federalresponse to air pollution is the fact that leading into 1990, the federalagency responsible for regulating air pollution emissions, the EnvironmentalProtection Agency (EPA), had only set regulations for seven hazardousor toxic airborne emissions. The Clean Air Act of 1990 was designed torectify this. It specifies that the EPA must set standards for 189 hazardousor toxic chemicals (Bryner 1995). In this, as well as in other pollutionabatement efforts, however, the EPA is hampered by an inadequate budget(Yeager 1991; Mintz 1995; Rosenbaum 1998; Weber 1998; Seelye 2003).Moreover, in the central area of automobile emissions, the federal governmentonly took a direct role in regulating these emissions in 1980. Additionally,federal automobile emission standards have always lagged behindCalifornia’s, and they currently are not as strong as those in major states asNew York and Massachusetts.On the issue of policy implementation, the federal government relies primarilyon state and local agencies to formulate clean air implementation
10THE POLITICS OF AIR POLLUTIONstrategies. As set under the terms of the Federal Clean Air Act of 1970, statesmust submit State Implementation Plans (SIPs) to the EPA for its approval.These plans must outline how the individual states are going to meet federalclean air standards. The individual states are offered discretion in certainareas to develop standards that exceed federally mandated standards.More significant is the fact that states are responsible for implementingor enforcing air pollution regulations (Game 1979; Wood 1988; 1992;Scheberle 1997; Morag-Levine 2003). States, however, have varied recordsconcerning the enforcement of their clean air regulations. While some statesmay be aggressive on enforcement issues, others have been found to be verylax—even failing to enforce the minimum federal standards (Game 1979;Cushman 1998 June 7; Seelye 2001; “Lung Association” 2002).Thus, the reliance on states to formulate and implement air pollutionabatement programs has lead to an uneven clean air regulatory regime.Defenders of this approach hold that it does have its benefits. Most specifically,it is averred that the use of state agencies to formulate and enforce theclean air regulatory regime allows government regulators to be sensitive tostate and local conditions, and hence it leads to a more efficient and effectivepolicy regime (Nice 1987). Little or no empirical evidence, however, hasbeen generated to substantiate this oft-repeated claim.Much more likely is that state and local officials guard their discretionover federal environmental policies (e.g., Cushman 1998 August 5) becausethey can calibrate environmental regulatory regimes to growth strategies.Those areas with high levels of investment and growth can use environmentalpolicies, including clean air policies, to mitigate the environmental negativeexternalities of economic activity and growth, thereby seeking to insurethat existing growth and investment levels are not jeopardized by such externalities.Whereas those states and localities that have comparatively lowerlevels of growth and investment simply may not have the political will ordesire to regulate emissions, because these emissions, to the extent that theydo exist in these areas, do not present a perceived threat to growth. In otherwords, the pollution “load” has not reached a threshold that represents athreat to the local business climate. Local growth boosters in less developedareas may also perceive pollution abatement politics and policies as a disincentiveto potential local investment.These hypotheses are supported by the aforementioned statistical analysescomparing the “strength” of air pollution regulations in the various states.Such studies have measured and compared the restrictive content of state airpollution regulations as well as expenditures toward the enforcement of theseregulations (Game 1979; Kemp 1981; Lowry 1992; Ringquist 1993; Potoski2001). What these studies have found is that the strength of clean air regulatoryregimes vary positively with the level of wealth and economic activityin a state. Thus, those states with high levels of wealth and economic activ-
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SIXDemocratic Ethics,Environmental
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DEMOCRATIC ETHICS 91At the core of
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BibliographyAcher, Robin. 2001. “
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BIBLIOGRAPHY 119Brienes, Marvin. 19
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BIBLIOGRAPHY 121Cole, Luke W., and
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BIBLIOGRAPHY 123——— . 2002. W
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BIBLIOGRAPHY 133Perez-Pena, Richard
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BIBLIOGRAPHY 135Runte, Alfred. 1997
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BIBLIOGRAPHY 137Tarr, Joel A. 1996.
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BIBLIOGRAPHY 139Wiewel, Wim, and Jo
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144THE POLITICS OF AIR POLLUTIONTuc