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Economics of the Environment

The Sixth Edition of Economics of the Environment: Selected Readings has just been published by W. W. Norton & Company of New York and London. Through five previous editions, Economics of the Environment has served as a valuable supplement to environmental economics texts and as a stand-alone book of original readings in the field of environmental economics. Nearly seven years have passed since the previous edition of this volume was published, and it is now more than three decades since the first edition appeared, edited by Robert and Nancy Dorfman. The Sixth Edition continues this tradition.

Motivation and Audience

Environmental economics continues to evolve from its origins as an obscure application of welfare economics to a prominent field in its own right, which combines elements from public finance, industrial organization, microeconomic theory, and many other areas of economics. The number of articles on the environment appearing in mainstream economics periodicals continues to increase, and more and more economics journals are dedicated exclusively to environmental and resource topics.

There has also been a proliferation of environmental economics textbooks for college courses. Many are excellent, but none can be expected to provide direct access to timely and original contributions by the field’s leading scholars. As most teachers of economics recognize, it is valuable to supplement the structure and rigor of a text with original readings from the literature.

Scope and Style

With that in mind, this new edition of Economics of the Environment consists of thirty-four chapters that instructors will find to be of great value as a complement to their chosen text and their lectures. The scope is comprehensive, and the list of authors is a veritable “who’s who” of environmental economics, including: Joseph Aldy, Kenneth Arrow, Trudy Cameron, Ronald Coase, Maureen Cropper, Peter Diamond, George Eads, Jeffrey Frankel, Rick Freeman, Don Fullerton, Lawrence Goulder, John Graham, Robert Hahn, Michael Hanemann, Jerry Hausman, Steven Kelman, Nathaniel Keohane, Alan Krupnick, Lester Lave, John Livernois, Eric Maskin, Leonardo Maugeri, Gilbert Metcalf, Richard Newell, Roger Noll, William Nordhaus, Wallace Oates, Sheila Olmstead, Elinor Ostrom, Karen Palmer, Ian Parry, Carl Pasurka, Robert Pindyck, William Pizer, Michael Porter, Paul Portney, Forest Reinhardt, Richard Revesz, Milton Russell, Michael Sandel, Richard Schmalensee, Steven Shavell, Jason Shogren, Kerry Smith, Robert Solow, Nicholas Stern, Laura Taylor, Richard Vietor, and myself.

The articles are timely, with more than 90 percent published since 1990, and half since 2005. There are two completely new sections of the book, “Economics of Natural Resources” and “Corporate Social Responsibility,” and all of the chapters in the section on global climate change are new to the sixth edition.

In order to make the readings in Economics of the Environment accessible to students at all levels, one criterion I use in the selection process is that articles should not only be original and well written — and meet the highest standards of economic scholarship — but also be non-technical in their presentations. Hence, readers will find virtually no formal mathematics in any of the book’s 34 chapters throughout its 733 pages.

The Path Ahead

Environmental economics is a rapidly evolving field. Not only do new theoretical models and improved empirical methods appear on a regular basis, but entirely new areas of investigation open up when the natural sciences indicate new concerns or the policy world turns to new issues. Therefore, this book remains a work in progress. I owe a great debt to the teachers and students of previous editions who have sent their comments and suggestions for revisions. Looking to future editions, I invite all readers — whether teachers, students, or practitioners — to send me any thoughts or suggestions for improvement.

In the meantime, if you’re interested finding out more about the book, immediately below is a chapter-by-chapter summary of the book. Alternatively, you can check out the W. W. Norton or Amazon web sites.

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Appendix: A Summary of Economics of the Environment, Sixth Edition

Part I of the volume provides an overview of the field and a review of its foundations. Don Fullerton and I start things off with a brief essay about how economists think about the environment (Nature 1998). This is followed by the classic treatment of social costs and bargaining by Ronald Coase (Journal of Law and Economics 1960), and a new article by Jason Shogren and Laura Taylor on the important, emerging field of behavioral environmental economics (Review of Environmental Economics and Policy 2008).

The Costs of Environmental Protection

Part II examines the costs of environmental protection, which might seem to be without controversy or current analytical interest. This is not, however, the case. This section begins with a survey article by Carl Pasurka that reviews the theory and empirical evidence on the relationship between environmental regulation and so-called “competitiveness” (Review of Environmental Economics and Policy 2008).

A somewhat revisionist view is provided by Michael Porter and Class van der Linde, who suggest that the conventional approach to thinking about the costs of environmental protection is fundamentally flawed (Journal of Economic Perspectives 1995). Karen Palmer, Wallace Oates, and Paul Portney provide a careful response (Journal of Economic Perspectives 1995).

The Benefits of Environmental Protection

In Part III, the focus turns to the other side of the analytic ledger — the benefits of environmental protection. This is an area that has been even more contentious — both in the policy world and among scholars. Here the core question is whether and how environmental amenities can be valued in economic terms for analytical purposes.

The book features a provocative debate on the stated-preference method known as “contingent valuation.” Paul Portney outlines the structure and importance of the debate, Michael Hanemann makes the affirmative case, and Peter Diamond and Jerry Hausman provide the critique (all three articles are from the Journal of Economic Perspectives 1994).

In the final article in Part III, the book turns to a concept that is both very important in assessments of the benefits of environmental regulations and is also very widely misunderstood — the value of a statistical life. In an insightful essay, Trudy Cameron seeks to set the record straight (Review of Environmental Economics and Policy 2010).

There are two principal policy questions that need to be addressed in the environmental realm: how much environmental protection is desirable; and how should that degree of environmental protection be achieved. The first of these questions is addressed in Part IV and the second in Part V.

The Goals of Environmental Policy: Economic Efficiency and Benefit-Cost Analysis

In an introductory essay, Kenneth Arrow, Maureen Cropper, George Eads, Robert Hahn, Lester Lave, Roger Noll, Paul Portney, Milton Russell, Richard Schmalensee, Kerry Smith, and I ask whether there is a role for benefit-cost analysis to play in environmental, health, and safety regulation (Science 1996).

Then, Lawrence Goulder and I focus on an ingredient of benefit-cost analysis that non-economists seem to find particularly confusing, or even troubling — intertemporal discounting (Nature 2002). Next, Robert Pindyck examines a subject of fundamental importance — the role of uncertainty in environmental economics (Review of Environmental Economics and Policy 2007). Steven Kelman provides an ethically-based critique of benefit-cost analysis, which is followed by a set of responses (Regulation 1981).

Part IV concludes with an up-to-date essay by John Graham on the critical role of the U.S. Office of Management and Budget in federal regulatory impact analysis (Review of Environmental Economics and Policy 2008).

The Means of Environmental Policy: Cost Effectiveness and Market-Based Instruments

Part V examines the policy instruments — the means — that can be employed to achieve environmental targets or goals. This is an area where economists have made their greatest inroads of influence in the policy world, with tremendous changes having taken place over the past twenty years in the reception given by politicians and policy makers to so-called market-based or economic-incentive instruments for environmental protection.

Lawrence Goulder and Ian Parry start things off with a broad-ranging essay on instrument choice in environmental policy (Review of Environmental Economics and Policy 2008). Following this, I examine lessons that can be learned from the innovative sulfur dioxide allowance trading program, set up by the Clean Air Act Amendments of 1990 (Journal of Economic Perspectives 1998). Finally, Michael Sandel provides a critique of market-based instruments, with responses offered by Eric Maskin, Steven Shavell, and others (New York Times 1997).

Economics of Natural Resources

Part VI consists of three essays on a new topic for this book — the economics of natural resources. First, John Livernois examines the empirical significance of a central tenet in natural resource economics, namely the Hotelling Rule — the proposition that under conditions of efficiency, the scarcity rent (price minus marginal extraction cost) of natural resources will rise over time at the rate of interest (Review of Environmental Economics and Policy 2009).

Essays by Leonardo Maugeri (Review of Environmental Economics and Policy 2009) and Sheila Olmstead (Review of Environmental Economics and Policy 2010), respectively, examine two particularly important resources: petroleum and water.

The next four sections of the book treat some timely and important topics and problems.

Corporate Social Responsibility and the Environment

Part VII examines corporate social responsibility and the environment, discussion of which has too often been characterized by more heat than light. Forest Reinhardt, Richard Vietor, and I provide an overview of this realm from the perspective of economics, examining the notion of firms voluntarily sacrificing profits in the social interest. In a second essay, Paul Portney provides a valuable empirical perspective (both are from the Review of Environmental Economics and Policy 2008).

Global Climate Change

Part VIII is dedicated to investigations of economic dimensions of global climate change, which may in the long term prove to be the most significant environmental problem that has arisen, both in terms of its potential damages and in terms of the costs of addressing it. First, a broad overview of the topic is provided in a survey article by Joseph Aldy, Alan Krupnick, Richard Newell, Ian Parry, and William Pizer (Journal of Economic Literature 2010).

Next, William Nordhaus critiques the well-known Stern Review on the Economics of Climate Change, and Nicholas Stern and Chris Taylor respond (both are from Science 2007). In the final essay in this section, Gilbert Metcalf examines market-based policy instruments that can be used to address greenhouse gas emissions (Journal of Economic Perspectives 2009).

Sustainability, the Commons, and Globalization

Part IX begins with Robert Solow’s economic perspective on the concept of sustainability. This is followed by Elinor Ostrom’s development of a general framework for analyzing sustainability (Science 2009), and my own historical view of economic analysis of problems associated with open-access resources (American Economic Review 2011). Then, Jeffrey Frankel draws on diverse sources of empirical evidence to examine whether globalization is good or bad for the environment (Council on Foreign Relations 2004).

Economics and Environmental Policy Making

The final section of the book, Part X, departs from the normative concerns of much of the volume to examine some interesting and important questions of political economy. It turns out that an economic perspective can provide useful insights into questions that might at first seem to be fundamentally political.

Nathaniel Keohane, Richard Revesz, and I utilize an economic framework to ask why our political system has produced the particular set of environmental policy instruments it has (Harvard Environmental Law Review 1998). Myrick Freeman reflects on the benefits that U.S. environmental policies have brought about since the first Earth Day in 1970 (Journal of Economic Perspectives 2002). Lastly, Robert Hahn addresses the question that many of the articles in this volume raise: what impact has economics actually had on environmental policy (Journal of Environmental Economics and Management 2000)?

Who Killed Cap-and-Trade?

In a recent article in the New York Times, John Broder asks “Why did cap-and-trade die?” and responds that “it was done in by the weak economy, the Wall Street meltdown, determined industry opposition and its own complexity.” Mr. Broder’s analysis is concise and insightful, and I recommend it to readers. But I think there’s one factor that is more important than all those mentioned above in causing cap-and-trade to have changed from politically correct to politically anathema in just nine months. Before turning to that, however, I would like to question the premise of my own essay.

Is Cap-and-Trade Really Dead?

Although cap-and-trade has fallen dramatically in political favor in Washington as the U.S. answer to climate change, this approach to reducing carbon dioxide (CO₂) emissions is by no means “dead.”

The evolving Kerry-Graham-Lieberman legislation has a cap-and-trade system at its heart for the electricity-generation sector, with other sectors to be phased in later (and it employs another market-based approach, a series of fuel taxes for the transportation sector linked to the market price for allowances). Of course, due to the evolving political climate, the three Senators will probably not call their system “cap-and-trade,” but will give it some other creative label.

The competitor proposal from Senators Cantwell and Collins — the CLEAR Act — has been labeled by those Senators as a “cap-and-dividend” approach, but it is nothing more nor less than a cap-and-trade system with a particular allocation mechanism (100% auction) and a particular use of revenues (75% directly rebated to households) — and, it should be mentioned, some unfortunate and unnecessary restrictions on allowance trading.

And we should not forget that cap-and-trade continues to emerge as the preferred policy instrument to address climate change emissions throughout the industrialized world — in Europe, Australia, New Zealand, and Japan (as I wrote about in a recent post).

But back to the main story — the dramatic change in the political reception given in Washington to this cost-effective approach to environmental protection.

A Rapid Descent From Politically Correct to Politically Anathema

Among factors causing this change were: the economic recession; the financial crisis (linked, in part, with real and perceived abuses in financial markets) which thereby caused great suspicion about markets in general and in particular about trading in intangible assets such as emission allowances; and the complex nature of the Waxman-Markey legislation (which is mainly not about cap-and-trade, but various regulatory approaches).

But the most important factor — by far — which led to the change from politically correct to politically anathema was the simple fact that cap-and-trade was the approach that was receiving the most serious consideration, indeed the approach that had been passed by one of the houses of Congress. This brought not only great scrutiny of the approach, but — more important — it meant that all of the hostility to action on climate change, mainly but not exclusively from Republicans and coal-state Democrats, was targeted at the policy du jour — cap-and-trade.

The same fate would have befallen any front-running climate policy.

Does anyone really believe that if a carbon tax had been the major policy being considered in the House and Senate that it would have received a more favorable rating from climate-action skeptics on the right? If there’s any doubt about that, take note that Republicans in the Congress were unified and successful in demonizing cap-and-trade as “cap-and-tax.”

Likewise, if a multi-faceted regulatory approach (that would have been vastly more costly for what would be achieved) had been the policy under consideration, would it have garnered greater political support? Of course not. If there is doubt about that, just observe the solid Republican Congressional hostility (and some announced Democratic opposition) to the CO₂ regulatory pathway that EPA has announced under its endangerment finding in response to the U.S. Supreme Court decision in Massachusetts vs. EPA.

(There’s a minor caveat, namely, that environmental policy approaches that hide their costs frequently are politically favored over policies that make their costs visible, even if the former policy is actually more costly. A prime example is the broad political support for Corporate Average Fuel Economy (CAFE) standards, relative to the more effective and less costly option of gasoline taxes. Of course, cap-and-trade can be said to obscure its costs relative to a carbon tax, but that hardly made much difference once opponents succeeded in labeling it “cap-and-tax.”)

In general, any climate policy approach — if it was meaningful in its objectives and had any chance of being enacted — would have become the prime target of political skepticism and scorn. This has been the fate of cap-and-trade over the past nine months.

Why is Political Support for Climate Policy Action So Low in the United States?

If much of the political hostility directed at cap-and-trade proposals in Washington has largely been due to hostility towards climate policy in general, this raises a further question, namely, why has there been so little political support in Washington for climate policy in general. Several reasons can be identified.

For one thing, U.S. public support on this issue has decreased significantly, as has been validated by a number of reliable polls, including from the Gallup Organization. Indeed, in January of this year, a Pew Research Center poll found that “dealing with global warming” was ranked 21^st among 21 possible priorities for the President and Congress. (It should be noted some polls are not consistent with these.) This drop in public support is itself at least partly due to the state of the national economy, as public enthusiasm about environmental action has — for many decades — been found to be inversely correlated with various measures of national economic well-being.

Although the lagging economy (and consequent unemployment) is likely the major factor explaining the fall in public support for climate policy action, other contributing factors have been the so-called Climategate episode of leaked e-mails from the University of East Anglia and the damaged credibility of the Intergovernmental Panel on Climate Change (IPCC) due to several errors in recent reports.

Furthermore, the nature of the climate change problem itself helps to explain the relative apathy among the U.S. public. Nearly all of our major environmental laws have been passed in the wake of highly-publicized environmental events or “disasters,” ranging from Love Canal to the Cuyahoga River.

But the day after Cleveland’s Cuyahoga River caught on fire in 1969, no article in The Cleveland Plain Dealer commented that “the cause was uncertain, because rivers periodically catch on fire from natural causes.” On the contrary, it was immediately apparent that the cause was waste dumped into the river by adjacent industries. A direct consequence of the “disaster” was, of course, the Clean Water Act of 1972.

But climate change is distinctly different. Unlike the environmental threats addressed successfully in past legislation, climate change is essentially unobservable. You and I observe the weather, not the climate (note the dramatic difference of opinion about the reality of climate change between climatologists and television weathercasters). Until there is an obvious and sudden event — such as a loss of part of the Antarctic ice sheet leading to a disastrous sea-level rise — it’s unlikely that public opinion in the United States will provide the bottom-up demand for action that has inspired previous Congressional action on the environment over the past forty years.

Finally, it should be acknowledged that the fiercely partisan political climate in Washington has completed the gradual erosion of the bi-partisan coalitions that had enacted key environmental laws over four decades. Add to this the commitment by the opposition party to deny the President any (more) political victories in this year of mid-term Congressional elections, and the possibility of progressive climate policy action appears unlikely in the short term.

An Open-Ended Question

There are probably other factors that help explain the fall in public and political support for climate policy action, as well as the changed politics of cap-and-trade. I suspect that readers will tell me about these.

Unintended Consequences of Government Policies: The Depletion of America’s Wetlands

Private land-use decisions can be affected dramatically by public investments in highways, waterways, flood control, or other infrastructure. The large movement of jobs from central cities to suburbs in the postwar United States and the ongoing destruction of Amazon rain forests have occurred with major public investment in supporting infrastructure. As these examples suggest, private land-use decisions can generate major environmental and social externalities – or, in common language, unintended consequences.

In an analysis that appeared in 1990 in the American Economic Review, Adam Jaffe of Brandeis University and I demonstrated that the depletion of forested wetlands in the Mississippi Valley – an important environmental problem and a North American precursor to the loss of South American rain forests – was exacerbated by Federal water-project investments, despite explicit Federal policy to protect wetlands.

Wetland Losses

Forested wetlands are among the world’s most productive ecosystems, providing improved water quality, erosion control, floodwater storage, timber, wildlife habitat, and recreational opportunities. Their depletion globally is a serious problem; and preservation and protection of wetlands have been major Federal environmental policy goals for forty years.

From the 1950s through the mid-1970s, over one-half million acres of U.S. wetlands were lost each year. This rate slowed greatly in subsequent years, averaging approximately 60 thousand acres lost per year in the lower 48 states from 1986 through 1997. And by 2006, the Bush administration’s Secretary of the Interior, Gale Norton, was able to announce a net gain in wetland acreage in the United Sates, due to restoration and creation activities surpassing wetland losses.

What Caused the Observed Losses?

What were the causes of the huge annual losses of wetlands in the earlier years? That question and our analysis are as germane today as in 1990, because of lessons that have emerged about the unintended consequences of public investments.

The largest remaining wetland habitat in the continental United States is the bottomland hardwood forest of the Lower Mississippi Alluvial Plain. Originally covering 26 million acres in seven states, this resource was reduced to about 12 million acres by 1937. By 1990, another 7 million acres had been cleared, primarily for conversion to cropland.

The owner of a wetland parcel faces an economic decision involving revenues from the parcel in its natural state (primarily from timber), costs of conversion (the cost of clearing the land minus the resulting forestry windfall), and expected revenues from agriculture. Agricultural revenues depend on prices, yields, and, significantly, the drainage and flooding frequency of the land. Needless to say, landowners typically do not consider the positive environmental externalities generated by wetlands; thus conversion may occur more often than is socially optimal.

Such externalities are the motivation for Federal policy aimed at protecting wetlands, as embodied in the Clean Water Act. Nevertheless, the Federal government engaged in major public investment activities, in the form of U.S. Army Corps of Engineers and U.S. Soil Conservation Service flood-control and drainage projects, which appeared to make agriculture more attractive and thereby encourage wetland depletion. The significance of this effect had long been disputed by the agencies which construct and maintain these projects; they attributed the extensive conversion exclusively to rising agricultural prices.

In an econometric (statistical) analysis of data from Arkansas, Mississippi, and Louisiana, from 1935 to 1984, Jaffe and I sought to sort out the effects of Federal projects and other economic forces. We discovered that these public investments were a very substantial factor causing conversion of wetlands to agriculture, with between 30 and 50 percent of the total wetland depletion over those five decades due to the Federal projects.

More broadly, four conclusions emerged from our analysis. First, landowners had responded to economic incentives in their land-use decisions. Second, construction of Federal flood-control and drainage projects caused a higher rate of conversion of forested wetlands to croplands than would have occurred in the absence of projects, leading to the depletion of an additional 1.25 million acres of wetlands. Third, Federal projects had this impact because they made agriculture feasible on land where it had previously been infeasible, and because, on average, they improved the quality of feasible land. Fourth, adjustment of land use to economic conditions was gradual.

Government Working at Cross-Purposes

The analysis highlighted a striking inconsistency in the Federal government’s approach to wetlands. In articulated policies, laws, and regulations, the government recognized the positive externalities associated with some wetlands, with the George H.W. Bush administration first enunciating a “no net loss of wetlands” policy. But public investments in wetlands – in the form of flood-control and drainage projects – had created major incentives to convert these areas to alternative uses. The government had been working at cross-purposes.

The conclusion that major public infrastructure investments affect private land-use decisions (thereby often generating negative externalities) may not be a surprise to some readers, but it was the 1990 analysis described here that first provided rigorous evidence which contrasted sharply with the accepted wisdom among policy makers.

The Ongoing Importance of Induced Land-Use Changes

As wetlands, tropical rain forests, barrier islands, and other sensitive environmental areas become more scarce, their marginal social value rises. In general, if induced land-use changes are not considered, the country will engage in more public investment programs whose net social benefits are negative.