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Stormwater Management and Roadways  

Nigel Pickering and Somayeh Nassiri

Nonpoint source pollution is common in highly developed areas worldwide, degrading downstream water quality conditions and causing algal growth, aquatic toxicity, and sometimes fish kills. Stormwater runoff that results from rainfall or snowmelt events creates high-flow runoff from impervious surfaces and adjacent areas transporting multiple pollutants to the receiving waters. Although water quality regulations in the developed world have been effective in cleaning up wastewater discharges, their success with remediating stormwater discharges has not been consistent. An exploration of the sources, characteristics, and treatment of roadway runoff, a type of runoff that can be toxic and more difficult to manage because of the linear nature of the road network, is necessary. Since 1975, there have been more than 50 major roadway studies quantifying the sources and types of runoff contaminants like sediment, metals, inorganic salts, and organic compounds. Vehicle sources of pollutants are considered the most pernicious of all roadway contaminants, with brakes and tires being major sources. In the last decade, the leachate from tire wear particles has been linked to toxicity in coho salmon. Nonstructural stormwater management minimizes contamination by using source controls; for example, the elimination of almost all lead in automotive fuel has reduced roadway lead contamination significantly and the introduction of low-copper brake pads in the United States is expected to reduce roadway copper contamination over time. Structural stormwater management practices treat contaminated roadway runoff using small natural treatment systems; this is due in large part to the linear nature of roadways that makes larger regional systems more difficult. Since 2000, treatment performance has improved; however, there is still a great need for further improvement. Suggestions for treatment improvements include designing with low maintenance in mind; applying machine learning to the existing data; improving the understanding of road-land pollutant dynamics; using a transdisciplinary applied research approach to identify the means to improve treatment and reduce toxicity; improving the media used in treatment systems to enhance performance; improving structural strength of permeable pavement; and increasing implementation by facilitating ways to allow/encourage small, effective, and less costly alternatives.


Agricultural Nitrogen and Phosphorus Pollution in Surface Waters  

Marianne Bechmann and Per Stålnacke

Nutrient pollution can have a negative impact on the aquatic environment, with loss of biodiversity, toxic algal blooms, and a deficiency in dissolved oxygen in surface waters. Agricultural production is one of the main contributors to these problems; this article provides an overview of and background for the main biogeochemical processes causing agricultural nutrient pollution of surface waters. It discusses the main features of the agricultural impact on nutrient loads to surface waters, focusing on nitrogen and phosphorus, and describes some of the main characteristics of agricultural management, including processes and pathways from soil to surface waters. An overview of mitigation measures to reduce pollution, retention in the landscape, and challenges regarding quantification of nutrient losses are also dealt with. Examples are presented from different spatial scales, from field and catchment to river basin scale.


Mining and the Environment  

George Vrtis and Kirke Elsass

Human societies have always depended upon minerals. Even a cursory glance at any world history textbook reveals the centrality of minerals—and thus mining—in forging human cultures in antiquity. The stone age, the bronze age, the iron age—each of these complex periods are, in part, defined by the increasing human engagement with the minerals used to characterize them. In the history of the United States, mineral extraction has also been fundamental to the nature and evolution of the nation, as well as its colonial and Indigenous pasts. It was present in Native American societies prior to European contact, accelerated with European colonization, became foundational with the advent of the industrial revolution, was renegotiated with the rise of the environmental movement, and has influenced the United States’ relationship with many parts of the world. As these developments have unfolded, mining and mineral use have radically altered the natural world and profoundly shaped people’s relationships with the environment and with one another.


Environmental and Conservation Movements in Metropolitan America  

Robert R. Gioielli

By the late 19th century, American cities like Chicago and New York were marvels of the industrializing world. The shock urbanization of the previous quarter century, however, brought on a host of environmental problems. Skies were acrid with coal smoke, and streams ran fetid with raw sewage. Disease outbreaks were as common as parks and green space was rare. In response to these hazards, particular groups of urban residents responded to them with a series of activist movements to reform public and private policies and practices, from the 1890s until the end of the 20th century. Those environmental burdens were never felt equally, with the working class, poor, immigrants, and minorities bearing an overwhelming share of the city’s toxic load. By the 1930s, many of the Progressive era reform efforts were finally bearing fruit. Air pollution was regulated, access to clean water improved, and even America’s smallest cities built robust networks of urban parks. But despite this invigoration of the public sphere, after World War II, for many the solution to the challenges of a dense modern city was a private choice: suburbanization. Rather than continue to work to reform and reimagine the city, they chose to leave it, retreating to the verdant (and pollution free) greenfields at the city’s edge. These moves, encouraged and subsidized by local and federal policies, provided healthier environments for the mostly white, middle-class suburbanites, but created a new set of environmental problems for the poor, working-class, and minority residents they left behind. Drained of resources and capital, cities struggled to maintain aging infrastructure and regulate remaining industry and then exacerbated problems with destructive urban renewal and highway construction projects. These remaining urban residents responded with a dynamic series of activist movements that emerged out of the social and community activism of the 1960s and presaged the contemporary environmental justice movement.


The Environmental History of Russia  

Stephen Brain

Russian environmental history is a new field of inquiry, with the first archivally based monographs appearing only in the last years of the 20th century. Despite the field’s youth, scholars studying the topic have developed two distinct and contrasting approaches to its central question: How should the relationship between Russian culture and the natural world be characterized? Implicit in this question are two others: Is the Russian attitude toward the non-human world more sensitive than that which prevails in the West; and if so, is the Russian environment healthier or more stable than that of the United States and Western Europe? In other words, does Russia, because of its traditional suspicion of individualism and consumerism, have something to teach the West? Or, on the contrary, has the Russian historical tendency toward authoritarianism and collectivism facilitated predatory policies that have degraded the environment? Because environmentalism as a political movement and environmental history as an academic subject both emerged during the Cold War, at a time when the Western social, political, and economic system vied with the Soviet approach for support around the world, the comparative (and competitive) aspect of Russian environmental history has always been an important factor, although sometimes an implicit one. Accordingly, the existing scholarly works about Russian environmental history generally fall into one of two camps: one very critical of the Russian environmental record and the seeming disregard of the Russian government for environmental damage, and a somewhat newer group of works that draw attention to the fundamentally different concerns that motivate Russian environmental policies. The first group emphasizes Russian environmental catastrophes such as the desiccated Aral Sea, the eroded Virgin Lands, and the public health epidemics related to the severely polluted air of Soviet industrial cities. The environmental crises that the first group cites are, most often, problems once prevalent in the West, but successfully ameliorated by the environmental legislation of the late 1960s and early 1970s. The second group, in contrast, highlights Russian environmental policies that do not have strict Western analogues, suggesting that a thorough comparison of the Russian and Western environmental records requires, first of all, a careful examination of what constitutes environmental responsibility.


Monitoring and Modeling of Outdoor Air Pollution  

Stefan Reis

Air pollution has been a major threat to human health, ecosystems, and agricultural crops ever since the onset of widespread use of fossil fuel combustion and emissions of harmful substances into ambient air. As a basis for the development, implementation, and compliance assessment of air pollution control policies, monitoring networks for priority air pollutants were established, primarily for regulatory purposes. With increasing understanding of emission sources and the release and environmental fate of chemicals and toxic substances into ambient air, as well as atmospheric transport and chemical conversion processes, increasingly complex air pollution models have entered the scene. Today, highly accurate equipment is available to measure trace gases and aerosols in the atmosphere. In addition, sophisticated atmospheric chemistry transport models—which are routinely compared to and validated and assessed against measurements—are used to model dispersion and chemical processes affecting the composition of the atmosphere, and the resulting ambient concentrations of harmful pollutants. The models also provide methods to quantify the deposition of pollutants, such as acidifying and eutrophying substances, in vegetation, soils, and freshwater ecosystems. This article provides a general overview of the underlying concepts and key features of monitoring and modeling systems for outdoor air pollution.


Exploring Air Pollution and COVID-19 Linkages in South Asia  

Muthukumara Mani and Takahiro Yamada

South Asia is at the epicenter of the global air pollution problems and still evolving in COVID-19 cases and fatalities. There is growing evidence of increased rates of COVID-19 in areas with high levels of air pollution. Air pollution is found to cause cellular damage and inflammation throughout the body and has been linked to higher rates of diseases, including cancer, heart disease, stroke, diabetes, asthma, and other comorbidities. All these conditions also potentially increase the risk of death in COVID-19 patients. The causal link between the exposure to air pollution and COVID-19 is still under investigation around the world, underpinned by rigorous scientific research and peer-review processes. However, in terms of the approach after a careful review of the literature, the instrumental variable (IV) approach is a prospective candidate to establish causality in a reduced-form analysis to overcome endogeneity and measurement errors of air pollution level. An analysis, therefore, using sufficiently anonymized individual and household level information on COVID-19, household air pollution, and other individual and household socioeconomic endowments in the same primary sampling unit (PSU) of the individual and household survey would be necessary to establish the causality. The PSU data are usually available from demographic health surveys (DHS) with randomly displaced location information to maintain anonymity. Also, for the instrument of the exposure to ambient air pollution, the use of thermal inversions is suggested conditional on weather-related variables—for example, temperature, precipitation, wind velocity and direction, and humidity.


Absent Information in Integrative Environmental and Health Risk Communication  

Jari Lyytimäki and Timo Assmuth

Communication is typically understood in terms of what is communicated. However, the importance of what is intentionally or unintentionally left out from the communication process is high in many fields, notably in communication about environmental and health risks. The question is not only about the absolute lack of information. The rapidly increasing amount and variability of available data require actors to identify, collect, and interpret relevant information and screen out irrelevant or misleading messages that may lead to unjustified scares or hopes and other unwanted consequences. The ideal of balanced, integrative, and careful risk communication can only rarely be seen in real-life risk communication, shaped by competition and interaction between actors emphasizing some risks, downplaying others, and leaving many kinds of information aside, as well as by personal factors such as emotions and values, prompting different types of responses. Consequently, risk communication is strongly influenced by the characteristics of the risks themselves, the kinds of knowledge on them and related uncertainties, and the psychological and sociocultural factors shaping the cognitive and emotive responses of those engaged in communication. The physical, economic, and cultural contexts also play a large role. The various roles and factors of absent information in integrative environmental and health risk communication are illustrated by two examples. First, health and environmental risks from chemicals represent an intensively studied and widely debated field that involves many types of absent information, ranging from purposeful nondisclosure aimed to guarantee public safety or commercial interests to genuinely unknown risks caused by long-term and cumulative effects of multiple chemicals. Second, light pollution represents an emerging environmental and health issue that has gained only limited public attention even though it is associated with a radical global environmental change that is very easy to observe. In both cases, integrative communication essentially involves a multidimensional comparison of risks, including the uncertainties and benefits associated with them, and the options available to reduce or avoid them. Public debate and reflection on the adequacy of risk information and on the needs and opportunities to gain and apply relevant information is a key issue of risk management. The notion of absent information underlines that even the most widely debated risk issues may fall into oblivion and re-emerge in an altered form or under different framings. A typology of types of absent information based on frameworks of risk communication can help one recognize its reasons, implications, and remediation.


Potosí Mines  

Kris Lane

This article examines the long history of Potosí, Bolivia, home of the world’s most productive silver mines. The mines, discovered in 1545 and still active today, are discussed in terms of their geology, discovery, productivity, labor history, and technological development. The article also treats the social and environmental consequences of nearly five hundred years of continuous mining and refining.


Cultivation, Improvement, and Environmental Impacts of Tea  

Mainaak Mukhopadhyay and Tapan Kumar Mondal

Tea, the globally admired, non-alcoholic, caffeine-containing beverage, is manufactured from the tender leaves of the tea [Camellia sinensis (L.)] plant. It is basically a woody, perennial crop with a lifespan of more than 100 years. Cultivated tea plants are natural hybrids of the three major taxa or species, China, Assam (Indian), or Cambod (southern) hybrids based on the morphological characters (principally leaf size). Planting materials are either seedlings (10–18 months old) developed from either hybrid, polyclonal, or biclonal seeds, or clonal cuttings developed from single-leaf nodal cuttings of elite genotypes. Plants are forced to remain in the vegetative stage as bushes by following cultural practices like centering, pruning, and plucking, and they are harvested generally from the second year onward at regular intervals of 7–10 days in the tropics and subtropics, with up to 60 years as the economic lifespan. Originally, the Chinese were the first to use tea as a medicinal beverage, around 2000 years ago, and today, around half of the world’s population drink tea. It is primarily consumed as black tea (fermented tea), although green tea (non-fermented) and oolong tea (semifermented) are also consumed in many countries. Tea is also used as vegetables such as “leppet tea” in Burma and “meing tea” in Thailand. Green tea has extraordinary antioxidant properties, and black tea plays a positive role in treating cardiovascular ailments. Tea in general has considerable therapeutic value and can cure many diseases. Global tea production (black, green, and instant) has increased significantly during the past few years. China, as the world’s largest tea producer, accounts for more than 38% of the total global production of made tea [i.e. ready to drink tea] annually, while production in India, the second-largest producer. India recorded total production of 1233.14 million kg made tea during 2015–2016, which is the highest ever production so far. Since it is an intensive monoculture, tea cultivation has environmental impacts. Application of weedicides, pesticides, and inorganic fertilizers creates environmental hazards. Meanwhile, insecticides often eliminate the fauna of a vast tract of land. Soil degradation is an additional concern because the incessant use of fertilizers and herbicides compound soil erosion. Apart from those issues, chemical runoff into bodies of water can also create problems. Finally, during tea manufacturing, fossil fuel is used to dry the processed leaves, which also increases environmental pollution.


The Environmental Kuznets Curve  

David I. Stern

The environmental Kuznets curve (EKC) is a hypothesized relationship between environmental degradation and GDP per capita. In the early stages of economic growth, pollution emissions and other human impacts on the environment increase, but beyond some level of GDP per capita (which varies for different indicators), the trend reverses, so that at high income levels, economic growth leads to environmental improvement. This implies that environmental impacts or emissions per capita are an inverted U-shaped function of GDP per capita. The EKC has been the dominant approach among economists to modeling ambient pollution concentrations and aggregate emissions since Grossman and Krueger introduced it in 1991 and is even found in introductory economics textbooks. Despite this, the EKC was criticized almost from the start on statistical and policy grounds, and debate continues. While concentrations and also emissions of some local pollutants, such as sulfur dioxide, have clearly declined in developed countries in recent decades, evidence for other pollutants, such as carbon dioxide, is much weaker. Initially, many understood the EKC to imply that environmental problems might be due to a lack of sufficient economic development, rather than the reverse, as was conventionally thought. This alarmed others because a simplistic policy prescription based on this idea, while perhaps addressing some issues like deforestation or local air pollution, could exacerbate environmental problems like climate change. Additionally, many of the econometric studies that supported the EKC were found to be statistically fragile. Some more recent research integrates the EKC with alternative approaches and finds that the relation between environmental impacts and development is subtler than the simple picture painted by the EKC. This research shows that usually, growth in the scale of the economy increases environmental impacts, all else held constant. However, the impact of growth might decline as countries get richer, and richer countries are likely to make more rapid progress in reducing environmental impacts. Finally, there is often convergence among countries, so that countries that have relatively high levels of impacts reduce them more quickly or increase them more slowly, all else held constant.


The Economics of Marine Plastic Pollution  

Clemens W. Gattringer

Ubiquitous marine plastic pollution has become a prominent ecological issue, as it provokes implications that threaten marine species, induces health concerns, and causes vast economic damages. The complex dynamics behind its pervasive occurrence are multipronged and multidimensional, and simple clear-cut causal chains cannot always be identified. Analytical appraisals aiming to advance the understanding of pervasive plastic pollution need to address these complexities and acknowledge the interconnectedness of social and ecological systems. Orthodox economic analyses have insufficiently addressed this integration and are frequently characterized by shallow transdisciplinary and monodisciplinary approaches. As a result, several mechanisms that are highly relevant in constituting the problem tend to be neglected by presuming simplistic assumptions about human agency and inadequate nature-economy relationships. This reductionism in the conceptualization is mirrored in the policy responses that are advocated to address the issue. A broader perspective and the integration of different disciplinary concepts (such as biophysical limits as a result of the laws of thermodynamics, the notion of power, cognitive biases, institutions, and incommensurability) can underpin a more holistic perspective that considers the issue’s inherent complexities. While in a market idealist world consumers can “vote with their wallets” and transcend their values into purchasing decisions on the market, in reality there are essential difficulties to such an approach. Marine plastic pollution thus challenges economic thinking to address this real-world ecological challenge with insights that are compatible with and noncontradictory to the broad body of knowledge already elaborated by natural sciences. These perspectives are essential not only for forming a substantive interdisciplinary analysis and understanding the underlying institutions of consumption and production, clear key drivers of the problem, but also to identify promising political solutions for meaningful change.


The Car and the City  

David Blanke

The relationship between the car and the city remains complex and involves numerous private and public forces, innovations in technology, global economic fluctuations, and shifting cultural attitudes that only rarely consider the efficiency of the automobile as a long-term solution to urban transit. The advantages of privacy, speed, ease of access, and personal enjoyment that led many to first embrace the automobile were soon shared and accentuated by transit planners as the surest means to realize the long-held ideals of urban beautification, efficiency, and accessible suburbanization. The remarkable gains in productivity provided by industrial capitalism brought these dreams within reach and individual car ownership became the norm for most American families by the middle of the 20th century. Ironically, the success in creating such a “car country” produced the conditions that again congested traffic, raised questions about the quality of urban (and now suburban) living, and further distanced the nation from alternative transit options. The “hidden costs” of postwar automotive dependency in the United States became more apparent in the late 1960s, leading to federal legislation compelling manufacturers and transit professionals to address the long-standing inefficiencies of the car. This most recent phase coincides with a broader reappraisal of life in the city and a growing recognition of the material limits to mass automobility.


Housing, Indoor Air Pollution, and Health in High-Income Countries  

Richard Sharpe, Nicholas Osborne, Cheryl Paterson, Timothy Taylor, Lora Fleming, and George Morris

Despite the overwhelming evidence that living in poor-quality housing and built environments are significant contributors to public health problems, housing issues persist and represent a considerable societal and economic burden worldwide. The complex interaction between multiple behavioral, lifestyle, and environmental factors influencing health throughout the “life-course” (i.e., from childhood to adulthood) in high-income countries has limited the ability to develop more salutogenic housing interventions. The resultant, usually negative, health outcomes depend on many specific housing factors including housing quality and standards, affordability, overcrowding, the type of tenure and property. The immediate outdoor environment also plays an important role in health and wellbeing at the population level, which includes air (indoor and outdoor), noise pollution and the quality of accessible natural environments. These exposures are particularly important for more vulnerable populations, such as the elderly or infirm, and those living in insecure accommodation or in fuel poverty (i.e., being unable to heat the home adequately). Being homeless also is associated with increased risks in a number of health problems. Investigating pathways to protecting health and wellbeing has led to a range of studies examining the potential benefits resulting from accessing more natural environments, more sustainable communities, and housing interventions such as “green construction” techniques. Built environment interventions focusing on the provision of adequate housing designs that incorporate a “life-course” approach, affordable and environmentally sustainable homes, and urban regeneration along with active community engagement, appear capable of improving the overall physical and mental health of residents. While some interventions have resulted in improved public health outcomes in more high-income countries, others have led to a range of unintended consequences that can adversely affect residents’ health and wellbeing. Furthering understanding into four interrelated factors such as housing-specific issues, the immediate environment and housing, vulnerable populations, and natural spaces and sustainable communities can help to inform the development of future interventions.


Atmospheric Brown Clouds  

Sumit Sharma, Liliana Nunez, and Veerabhadran Ramanathan

Atmospheric brown clouds (ABCs) are widespread pollution clouds that can at times span an entire continent or an ocean basin. ABCs extend vertically from the ground upward to as high as 3 km, and they consist of both aerosols and gases. ABCs consist of anthropogenic aerosols such as sulfates, nitrates, organics, and black carbon and natural dust aerosols. Gaseous pollutants that contribute to the formation of ABCs are NOx (nitrogen oxides), SOx (sulfur oxides), VOCs (volatile organic compounds), CO (carbon monoxide), CH4 (methane), and O3 (ozone). The brownish color of the cloud (which is visible when looking at the horizon) is due to absorption of solar radiation at short wavelengths (green, blue, and UV) by organic and black carbon aerosols as well as by NOx. While the local nature of ABCs around polluted cities has been known since the early 1900s, the widespread transoceanic and transcontinental nature of ABCs as well as their large-scale effects on climate, hydrological cycle, and agriculture were discovered inadvertently by The Indian Ocean Experiment (INDOEX), an international experiment conducted in the 1990s over the Indian Ocean. A major discovery of INDOEX was that ABCs caused drastic dimming at the surface. The magnitude of the dimming was as large as 10–20% (based on a monthly average) over vast areas of land and ocean regions. The dimming was shown to be accompanied by significant atmospheric absorption of solar radiation by black and brown carbon (a form of organic carbon). Black and brown carbon, ozone and methane contribute as much as 40% to anthropogenic radiative forcing. The dimming by sulfates, nitrates, and carbonaceous (black and organic carbon) species has been shown to disrupt and weaken the monsoon circulation over southern Asia. In addition, the ozone in ABCs leads to a significant decrease in agriculture yields (by as much as 20–40%) in the polluted regions. Most significantly, the aerosols (in ABCs) near the ground lead to about 4 million premature mortalities every year. Technological and regulatory measures are available to mitigate most of the pollution resulting from ABCs. The importance of ABCs to global environmental problems led the United Nations Environment Programme (UNEP) to form the international ABC program. This ABC program subsequently led to the identification of short-lived climate pollutants as potent mitigation agents of climate change, and in recognition, UNEP formed the Climate and Clean Air Coalition to deal with these pollutants.


International Political Economy and the Environment  

Gabriele Spilker, Vally Koubi, and Thomas Bernauer

How does liberalization of trade and investment (i.e., economic globalization) as well as membership in international organizations (i.e., political globalization) affect the natural environment? Does economic and/or political globalization lead to ecological improvement or deterioration? This article reviews the existing literature on international political economy (IPE) and the environment in view of these and related questions. While globalization has various dimensions—economic, social, and political—IPE focuses mainly on the economic dimension when analyzing the effect of globalization on the environment. In particular, IPE puts most emphasis on the environmental implications of trade in goods and services as well as foreign direct investment (FDI). Even though both trade and investment are thought to have a substantial impact on the natural environment, the existing literature demonstrates that the effects of economic globalization on the environment are neither theoretically nor empirically one-dimensional. This means that existing research does not allow for a clear-cut overall assessment in terms of whether globalization leads to an improvement or deterioration of the environment. This is the case because the impact of economic globalization on the environment materializes via different mechanisms, some of which are supposedly good for the environment, and some of which are bad. On the one hand, economic globalization may improve environmental quality via its positive effect on economic growth, since trade and FDI facilitate specialization among countries according to their comparative advantage and the transfer of resources across countries. On the other hand, relevant economic theory gives little reason to believe that free trade and FDI will influence all countries in the same way. Instead, when considering the relationship between economic globalization and the environment, it is important to consider the interactions between scale, composition, and technique effects created by different national characteristics and trade and investment opportunities. In particular, the scale effect of openness to trade and capital mobility increases environmental degradation through more intensive production. The technique effect predicts a positive effect of trade and FDI on the environment through the use of cleaner techniques of production. And the change in the sectoral composition of a country as a consequence of trade and FDI, the composition effect, could positively or negatively affect the environment of a country (e.g., a change from agriculture to industry may lead to higher energy consumption and air pollution while a change from industry or agriculture to service is expected to decrease environmental degradation). Consequently, the overall effect of trade and FDI on environmental quality can be positive, negative, or nonexistent strongly depending on the specific situation of the country under investigation. Furthermore, both theory and empirical research highlight the potential for government policy and environmental regulations to affect the relationship between trade/FDI and the environment. On the one hand, increased competition between economic actors (usually companies) due to increased market openness (globalization) might cause a race to the bottom or at least regulatory chill in formal and informal environmental standards as well as pollution havens attracting foreign direct investment. The reason is that countries might weaken (or at least not increase) their environmental policies in order to protect industries from international competition or attract foreign firms and FDI motivated by the expectation of lower costs of environmental protection. Hence the (theoretical) expectation here is that developed countries will refrain from adopting more stringent environmental regulations and might even reduce existing standards due to competition with countries that have laxer environmental regulation. And less-developed countries will adopt lax environmental standards to attract FDI flowing into pollution-intensive sectors and export the respective goods to jurisdictions with higher environmental standards. In contrast, the Porter hypothesis states that a tightening of environmental regulations may stimulate technological innovation and thus help improve economic competitiveness. In addition, trade openness may induce an international ratcheting up of environmental standards (trading up) as higher environmental standards of richer and greener countries spread—via trade and investment relationships—to countries starting out with lower environmental standards. Furthermore, multinational corporations engaging in FDI and applying universal environmental standards throughout their operations tend to transfer greener technology and management practices to host countries, thus promoting the upgrade of local environmental standards and improving the environmental quality in those countries (the so-called pollution halo effect). Echoing the many theoretical pathways through which globalization can affect the natural environment, empirical studies estimating the impact of trade and FDI on environmental standards and environmental quality deliver quite heterogeneous results. In particular, the literature points to various factors mediating the effect of trade and FDI on the environment, such as differences in technology between industrial and developing countries, stringency of environmental regulations, property rights and political institutions, corruption levels as well as the pollution intensity of multinationals. More recently, IPE scholars have started to study the political dimensions of globalization and how they are related to environmental protection efforts. Memberships in international organizations are at the center of this research and recent studies analyze, for example, how they may affect the quality of the environment. Other studies focus more on specific organizations, such as the World Trade Organization, and, for instance, evaluate whether in trade disputes over environmental standards economic or environmental concerns prevail. Finally, a new strand of the IPE and environment literature deals with the micro level and studies how citizens evaluate economic openness in light of potential environmental concerns.


Environmental Health Concerns From Unconventional Natural Gas Development  

Irena Gorski and Brian S. Schwartz

Unconventional natural gas development (UNGD), which includes the processes of horizontal drilling and hydraulic fracturing to extract natural gas from unconventional reservoirs such as shale, has dramatically expanded since 2000. In parallel, concern over environmental and community impacts has increased along with the threats they pose for health. Shale gas reservoirs are present on all continents, but only a small proportion of global reserves has been extracted through 2016. Natural gas production from UNGD is highest in the United States in Pennsylvania, Texas, Louisiana, Oklahoma, and Arkansas. But unconventional production is also in practice elsewhere, including in eighteen other U.S. states, Canada, and China. Given the rapid development of the industry coupled with its likelihood of further growth and public concern about potential cumulative and long-term environmental and health impacts, it is important to review what is currently known about these topics. The environmental impacts from UNGD include chemical, physical, and psychosocial hazards as well as more general community impacts. Chemical hazards commonly include detection of chemical odors; volatile organic compounds (including BTEX chemicals [benzene, toluene, ethylbenzene, and xylene], and several that have been implicated in endocrine disruption) in air, soil, and surface and groundwater; particulate matter, ozone, and oxides of nitrogen (NOx) in air; and inorganic compounds, including heavy metals, in soil and water, particularly near wastewater disposal sites. Physical hazards include noise, light, vibration, and ionizing radiation (including technologically enhanced naturally occurring radioactive materials [TENORMs] in air and water), which can affect health directly or through stress pathways. Psychosocial hazards can also operate through stress pathways and include exposure to increases in traffic accidents, heavy truck traffic, transient workforces, rapid industrialization of previously rural areas, increased crime rates, and changes in employment opportunities as well as land and home values. In addition, the deep-well injection of wastewater from UNGD has been associated with increased seismic activity. These environmental and community impacts have generated considerable concern about potential health effects and corresponding political debate over whether UNGD should be promoted, regulated, or banned. For several years after the expansion of the industry, there were no well-designed, population-based studies that objectively measured UNGD activity or associated exposures in relation to health outcomes. This delay is inherent after the introduction of new industries, but hundreds of thousands of wells were drilled before any health studies were completed. By 2017, there were a number of important, peer-reviewed studies published in the scientific literature that raised concern about potential ongoing health impacts. These studies have reported associations between proximity to UNGD and pregnancy and birth outcomes; migraine headache, chronic rhinosinusitis, severe fatigue, and other symptoms; asthma exacerbations; and psychological and stress-related concerns. Beyond its direct health impacts, UNGD may be substantially contributing to climate change (due to fugitive emissions of methane, a powerful greenhouse gas), which has further health impacts. Certain health outcomes, such as cancer and neurodegenerative diseases, cannot yet be studied because insufficient time has passed in most regions since the expansion of UNGD to allow for latency considerations. With the potential for tens of thousands of additional wells across large geographic areas, these early health studies should give pause about whether and how UNGD should proceed. Citing health concerns, several U.S. states and nations in Europe have already decided to not allow UNGD.


The Harms and Crimes of Water Theft and Pollution  

Katja Eman

Water is a natural resource vital for the sustenance of life. Any harm against water resources should thus be recognized as a crime—defined in procedural and moral terms as wrongdoings determined within the legal justice system and social norms. With water scarcity and related crises, water protection has become a crucial concept, one impacting political, social, economic, and other fields. Therefore, identifying, defining, and prosecuting different forms of water crimes are essential. In this context, even the use of the term “water crimes” communicates the severe consequences of such activities for society. Water theft and water pollution are only two among various forms of crime against water resources, causing irreparable harm and damage, mainly due to the multiple dimensions of such crimes, in many areas. Water theft is understood as any form of stealing water from the natural water resources or water supply system to obtain an economic advantage by physically altering the supply system. Water pollution means any intentional contamination of water. The consequences of both crimes are a reduction in the quantity (and quality) of water, causing harm to the natural environment and its inhabitants (i.e., plants, animals, and humans). Moreover, most cases of serious water theft or pollution can end in the loss of life, including human life.


Environmental Regulations in India  

Rama Mohana R Turaga and Anish Sugathan

Pollution is one of the greatest causes of premature deaths and morbidity in the world, and this burden of pollution is disproportionately borne by the lower and middle income countries such as India—home to more than one-sixth of humanity. In India, due to the compound effect of its large population and high levels of environmental pollution, the human cost of pollution is among the highest in the world. The environmental degradation is partly a consequence of the development model pursued after independence in 1947 based on large-scale industrialization and exploitative resource utilization, with scant consideration for sustainability. Moreover, it is also due to the failure of the environmental administration, governance, and regulatory infrastructure to keep pace with the magnitude and pace of economic growth in India since economic liberalization in 1991. Ironically, India was also one of the early pioneers of integrating environmental considerations into its legislative and policy-making process beginning in the early 1970s. The federal and state environmental regulation and policy framing institutions set up during this era, along with environmental legislation such as the Environment (Protection) Act 1986, are comparable in design, stringency, and comprehensiveness to other contemporary command-and-control environmental regulatory regimes in many industrially developed economies. However, the widening gap between de jure expectations of environmental compliance and the de facto state of affairs has been a great concern for environmental governance in the country. The ongoing debates discuss several mechanisms to address the regulatory failures. The first is a greater emphasis on strengthening institutions and mechanisms that foster transparency and public disclosure by pollution sources with the intent to increase access to and credibility of information on pollution. Proponents argue this will help mobilize groups such as non-governmental organizations (NGOs) and the general public to pressure the industry and government to improve regulatory enforcement. Second, there have been calls for wider adoption of market-based instruments that are more efficient than the traditional command-and-control approaches on which India relies. Again, information is a prerequisite for the functioning of such market-based regulatory mechanisms. Third, the legal infrastructure to facilitate expedited hearing of environmental litigation is being created. With the establishment of the National Green Tribunal in 2010, India is one of only three other countries in the world to have an exclusive judicial body to hear environmental cases. This is potentially a significant step in providing greater access to environmental justice. An emerging view, however, argues that the prevailing economic development model is incompatible with ensuring sustainable development and requires a radical rethink.


Economics of Hazardous Waste Management  

Hilary Sigman

Hazardous waste management involves treatment, disposal, or recycling of a wide range of different waste streams from industry, households, and others. The diversity of wastes and management methods means that many choices affect its environmental harms, which result from possible contamination of groundwater, surface water, soil, and air. Efficient public policies that would fully reflect such varied external costs are unlikely to be feasible. In practice, governments principally apply three policy approaches to hazardous waste: taxes on hazardous waste, liability for environmental damages, and standards-based regulation of waste management facilities. Hazardous waste taxes may help internalize environmental costs but do not reflect all the variability in these costs. By contrast, liability for environmental damage can make waste generators and managers confront environmental costs that vary with their particular choices. However, environmental liability is often linked to programs for cleanup of contaminated sites and may not create efficient incentives for active waste management because this liability does not reflect the social costs of the contamination. Regulation usually takes the form of technology and performance standards applied to treatment, storage, and disposal facilities (TSDFs) and affects generation decisions only indirectly. Research finds that public policies that raise costs of hazardous waste management, such as taxes and regulation, encourage less waste generation, but may also provoke detrimental responses. First, facilities may substitute illegal waste dumping for legal management and thus exacerbate environmental damage. Second, generators may ship waste to jurisdictions with weaker environmental protections, especially developing countries, giving rise to a “waste haven” effect. This effect may create offsetting environmental damage, facilitate destructive policy competition among jurisdictions, and worsen inequities in exposure to environmental harm from hazardous waste.