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49 Pages·2017·0.78 MB·English
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Clean Competition: How Competitive Elections Clean-up the Air in Mexican Municipalities. Anthony Pezzola Instituto de Ciencia Política Pontificia Universidad Católica de Chile Amanda Fidalgo Department of Political Science Penn State University Xun Cao Department of Political Science Penn State University July 26, 2017 Abstract: This paper evaluates whether and how electoral competition across Mexico’s municipalities influences local air quality. Past research suggests that greater electoral competition makes politicians more accountable to voters and stimulates a shift towards the provision of public goods. Most recent studies use social spending or infrastructure to measure public goods. However, the ability to target social programs and infrastructure projects to specific constituencies can reduce their “public” nature. Instead, we study the relationship between electoral competition and air pollution. The disperse nature of clean air and the trade-off faced by local politicians between providing clean-air and promoting the local economy makes the provision of clean air a more difficult public good. Using satellite data to capture air quality across Mexico’s municipalities, our main finding is that electoral competition measured by the effective number of parties is associated with lower level of PM 2.5 air pollution. 1 Introduction Electoral competition and government responsiveness is hardly a new topic for students of politics. There is often thought to be a positive link between electoral competition and the provision of public goods. The basic argument rests on theories of electoral accountability, which posit that elections offer citizens the opportunity to influence policy outcomes by removing representatives that perform poorly (Austen-Smith and Banks 1989; Ferejohn 1986). Most studies use the level of social spending and infrastructure projects as measures of public goods. However, the ability to target social programs and infrastructure projects to specific constituencies can reduce their “public” nature. Environmental public goods, such as air quality, on the other hand, are some of the purest types of public goods. They are both non-excludable and non-rival. Moreover, the disperse nature of clean air as well as the trade-off, often faced by politicians, between providing environmental public goods and protecting the vibrancy of the local economy makes the provision of clean air a more difficult public good to target and to politicize for electoral benefit. Our first contribution, therefore, is to assess the relationship between electoral competition and the provision of a less studied, pure(r) public good. This paper makes a second important contribution by studying a public good that has significant distributive implications that stem from regulatory enforcement rather than fiscal outlays that provide jobs, services, or cash transfers. Regulating pollution can negatively affect businesses, especially small enterprises and those in the informal sector, resulting in increased poverty (Dasputa et al 1998). Small and informal producers tend to emit far more particulate emissions than their larger counterpart, making them targets for anti-pollution policies. However, small and informal enterprises also tend to have far more difficulty reducing contamination even when the need capital investments are small. For example, in the 1990s, a typical brick kiln in 2 Ciudad Juárez, Mexico used tires and other debris as fuel, making kilns one of the most important sources of air pollution. On average, kilns employed six people and had weekly profits of only $100 (Backman and Barrister 1998). Low profits and a lack of credit make it almost impossible for operators to adjust production methods. As such, programs in Ciudad Juárez and numerous other municipalities to regulate and reduce emissions from kilns jeopardized the livelihood of thousands of already impoverished individuals. The clear distributional consequences for small and informal businesses makes properly regulating pollution politically difficult, especially in Latin America. This is partly because individuals in the informal sector participate more in politics than their formal counterparts (Thornton 2000) and strongly link their evaluations of politicians to their economic circumstances (Singer 2016). Individuals in the informal sector are also likely to belong to trade or other local associations that allow them to lobby against pollution control efforts. Regulating the informal sector may also threaten existing clientelistic relationships. Tendler (2002) finds that local Brazilian politicians often enter into an unspoken deal with small enterprises, keeping police and inspectors from harassing them in exchange for political support. This paper makes a third significant and empirical contribution to environmental studies in international and comparative politics by using satellite air pollution data to study the relationship between electoral competition and air pollution at the municipal level within Mexico. Large-N studies of environmental politics often adopt a country-level approach. This is understandable because theories often focus on the environmental effects of national-level political institutions (Fredriksson and Millimet 2004; Scruggs 2003), and because most cross- national data on pollution is only available at the national level. Data on air pollution at the 3 monitoring station level are available;1 however, most monitoring stations are in the OECD countries.2 Fined-grained data on sub-national level environmental outcomes, especially for developing countries, are difficult to find and limits our ability to study within country variation in environmental outcomes. Studying subnational level variation is important for students of environmental politics, because ultimately pollution is a function of local characteristics such as climate conditions, geography, and economic and social conditions. The use of satellite data, such as those provided in grid-cells as small as 0.1 × 0.1 decimal degree cell resolutions (about 11 km by 11 km at the Equator) allows us to model and test within country variation in air pollution. The relationship between electoral competition and the provision of public goods is likely to be a complex one. We argue that there might be mediating factors that influence the provision of environmental public goods. For instance, it is likely that electoral competition can only lead to the greater provision of public goods if the public prioritizes it. If voters prioritize economic growth, competitive elections may increase government investments in areas such as infrastructure (e.g., building roads and bridges) which is sometimes associated with more pollution. At the same time, encumbers in poorer municipalities may find it more politically efficient to provide private goods to ensure electoral victory. Therefore, we also examine whether electoral competition has a stronger effect on the provision of clean air in wealthier municipalities. 1 For example, see Bernauer and Koubi (2009). 2 Even within some of the richest countries, there are not enough stations to cover the ground. 4 Mexico is a useful and interesting case for a few reasons. First, it presents a particularly difficult test because it is a newly democratic regime (after the single-party rule of the PRI) and a country still eager to develop its economy. As such, a culture of electoral accountability is not as fully developed among voters as in more established democracies and we should expect voters’ preferences to be more geared towards economic growth. Additionally, there is significant variation in the level of electoral competition at the municipal level, which provides us with significant leverage to uncover the role of local politics in providing environmental public goods. The connection between pollution and electoral competition may seem tenuous, especially in a developing country and at the local level. However, there is good reason to believe that municipal governments play an active role in and care about air pollution in Mexico. The Mexican constitution grants municipalities the ability to develop ecological policies, the power to deal with low-level ecological emergencies and risks, the responsibility of regulating and preventing air and water pollution, managing the disposal of solid waste, and evaluating and regulating the environmental impacts of urban growth (Assetto, Hajba and Mumme 2003). They are also responsible for zoning and have the power to create ecological zones (Grindle 2007). The environmental law passed in 1988 decentralized significant authority over environmental policy to the municipal level. It charges municipalities with monitoring and ensuring the application of federal environmental regulations; it entrusts municipalities with the responsibility 5 to address all environmental problems within their jurisdiction not already specifically reserved for federal or state authorities.3 Additionally, while Mexico is a country that is eager to develop economically it is also a country in which people care about air pollution. Survey data from the World and European Value Surveys (WEVS) reveal the saliency of environmental preferences in the Mexican public. In 1996 and 2000, Mexican respondents indicated a preference for protecting the environment with a ratio close to 3:2; in 2005, the ratio of Mexicans choosing the environment to those choosing economic development almost reached 2:1: these were well above the response ratio of citizens in similar Latin American countries.4 Rodríguez-Sánchez (2014) more recently shows 3 While the specific policy responsibilities of municipalities vary by state, most have the ability to pass environmental regulatory ordinances and sanction violations of those ordinances (Assetto, Hajba and Mumme 2003). 4 The WEVS provides a question on citizens’ relative preference regarding “protecting environment vs. economic growth.” It asks respondents to choose from two statements: “Protecting the environment should be given priority, even if it causes slower economic growth and some loss of jobs” vs. “Economic growth and creating jobs should be the top priority, even if the environment suffers to some extent.” We consider respondents choosing the first statement as having environmental preferences. 6 that Mexicans are willing to pay to reduce air pollution: on average, a household head would pay $46.90 to $283.61 for a one-unit reduction in particulate matter emissions per year.5 To explain air quality across time and across Mexico’s municipalities, we use the Effective Number of Parties and the Margin of Victory in city council (ayuntamiento) elections to measure electoral competitiveness. We test both its marginal effect on air pollution and its interactive effect with local environmental demands (using GDP per-capita as a proxy). We find that party dominance on city councils (a lower Effective Number of Parties) is associated with poorer air quality, while a lower Margin of Victory by the leading party has no clear relationship with cleaner air. We find no evidence for the interactive effect between GDP per-capita and either measure of electoral competition. The rest of the paper is organized as follows: First, we discuss theoretical connections between electoral competition and public goods provisions. Second, we provide a brief discussion of actions municipal government can and have taken to impact air pollution in Mexico We then present the data and the empirical findings. Finally, we conclude and discuss directions of future research. Electoral Competition and Public Goods Provisions We aim to explain subnational variation in air pollution. While there are numerous potential factors that can explain air quality including climate, geographic conditions, and the nature of the local economy, we focus on political explanations. We treat air quality as a public good and rely 5 In constant 2000 dollars. In Rodríguez-Sánchez (2014), the mean of the PM emissions per area variable is about 0.80 and the standard deviation is 0.95. This suggests that one-unit reduction in PM is close to one standard deviation reduction. 7 on theories regarding public goods provisions to explain variation in air quality across Mexican municipalities. Such theories often implicitly assume pure public goods that are fully non-rival and non-excludable. Yet, in reality, most studies focus on public goods or services that suffer from some degree of rivalry and some crowding effects (e.g., infrastructure, education, health care, and social welfare). The enjoyment of a unit of an impure public good goes down with the number of people consuming it. Air quality, on the other hand, is one of the purest public goods. Clean air is less subject to crowding effects or rivalry. Non-excludability is also less of a concern for air quality. Moreover, almost all social spending and infrastructure projects can be targeted to specific groups making them essentially club goods. While the location of high polluting activities may be strategically placed (Monogan, Konisky, and Woods 2015), air quality at the municipal level is much more difficult to direct towards a specific constituency. There are a number of theories linking political factors to the provision of public goods. Some, such as the selectorate theory,6 are not directly relevant to subnational regimes that have similar institutions. Rather than review all of these theories, we focus on an approach related to electoral competition and government responsiveness. This approach often predicts a positive link between electoral competitiveness and the provision of public goods. The basic argument originates from the electoral democratic theory, which posits that competitive elections offer citizens the opportunity to influence government representatives by threatening to remove the 6 Selectorate theory posits that as the size of the winning coalition increases, a ruler will rely more on the provision of public goods because the relative price of doing so falls compared to buying support with private good transfers (Bueno de Mesquita et al. 2003). The theory predicts that regimes with large winning coalitions (often democracies) typically provide more public goods. 8 incumbent for poor performance and by selecting representatives who are competent and share the public's preferences (Austen-Smith & Banks 1989; Ferejohn 1986). Higher Electoral Competition, More Public Goods? It is generally thought that democracies, which are presumed to be more competitive, tend to provide more public goods than other forms of government. Competitive elections force politicians to address constituent demands. Ambitious politicians hoping to maintain their office and advance their political careers face a constant threat of removal. Political survival requires that they perform well. For instance, Fox (1994) argues that competition breaks down clientelist bonds, leading to more social spending as candidates and officials come under greater scrutiny. Wittman (1989) shows that political competition pushes governments toward efficient outcomes by lowering the opportunism of politicians. Becker (1983) finds that even in the presence of successful pressure groups, competition should cause governments to correct market failures (reflected in lower pollution), since policies that raise efficiency should win out because they produce gains rather than deadweight costs to society. Brown and Hunter (1999) show that democracies tend to spend more in general, and specifically on education.7 However, the aforementioned theoretical predictions following this electoral democratic thesis have received mixed empirical support, particularly when studying developing countries. 7 Treating education, especially primary education, as a public good, many studies suggest that democracy increases government education spending and improves educational outcomes (Ansell 2008; Nooruddin and Simmons 2009; Stasavage 2005; Hecock 2006; Huber, Mustillo and Stephens 2008). 9 In the Mexican context, studies conducted at the state level often find a positive connection between electoral competition and public goods (or government performance). For instance, Hecock (2006) finds that higher electoral competition is associated with more education spending. Studies conducted at the municipal level, on the other hand, often reveal null results. For instance, Cleary (2007) finds no connection between electoral competition and public goods (sewer and water coverage). Grindle (2007) finds no clear relationship between competition and government performance, with the latter measured as an index measuring efficiency, effectiveness, responsiveness, change initiatives, and development orientation. Moreno-Jaimes (2007) is also unable to find a discernable relationship between electoral competition (measured by margin of victory) and basic service provision (water drainage) in Mexico. Euler (2014) shows that competition (margin of victory) has no positive relationship with the provision of public services. The only exception that we know of is Hiskey (2003), which shows that municipalities that lack political competition and were dominated by the PRI are associated with lower public service provisions. Similarly, studies based on non-Mexican cases show mixed empirical results at the subnational level. Arvate (2013) shows that electoral competition increases student enrollment, teachers, and free immunizations in Brazil. Pereira and Melo (2009), on the other hand, find that the influence of competition on social spending depends on the degree of checks and balances within Brazilian states, while Cavalcante (2013) finds no effect for electoral competition. Chhibber and Nooruddin (2004) show that in India, greater competition is not necessarily beneficial because states with more than three effective parties provide fewer public goods. Elsewhere, Sánchez Torres and Pachón (2013) find political competition increases public goods at the municipal level in Columbia; Galasso and Nannicili (2011) and Paola and Scoppa (2010) 10

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Clean Competition: How Competitive Elections Clean-up the Air in Mexican. Municipalities. "Urban Armageddon or Politics as Usual? The Case of
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