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Cap-and-Trade versus the Alternatives for U.S. Climate Policy

Let’s credit Senator Lisa Murkowski (R-Alaska) for raising questions in the National Journal about the viability of cap-and-trade versus other approaches for the United States to employ in addressing CO₂ and other greenhouse gas emissions linked with global climate change.

Senator Murkowski says that only one approach – cap-and-trade – has received significant attention in the Congress. Let’s put aside for the moment the fact that most of the 1,428 pages of H.R. 2454 – the American Clean Energy and Security Act of 2009 (otherwise known as the Waxman-Markey bill) – are not about cap-and-trade at all, but about a host of other regulatory approaches (several of which are highly problematic, as I’ve discussed in a previous post). We can also put aside the fact that both conventional regulatory approaches and carbon taxes have been discussed repeatedly in numerous House and Senate committees over the past decade, and received detailed attention from a succession of U.S. administrations.

So, let’s not quibble about the Senator’s claim that cap-and-trade is the only approach that has received serious attention. Instead, let’s address the key substantive questions which Senator Murkowski raises, because they are important questions: Is cap-and-trade the most effective way of addressing climate change? And are there other approaches capable of achieving the same results at lower cost? From my perspective, as a card-carrying environmental economist, these are indeed the key questions.

While political leaders in the European Union, Canada, Australia, New Zealand, Japan, and the United States (Congress) move toward cap-and-trade systems as their preferred approach for achieving meaningful reductions in emissions of CO₂ and other greenhouse gases, many people – including some of my fellow economists — have been critical of the cap-and-trade approach in the climate context and have endorsed the use of carbon taxes. The Senator is correct that we should reflect on the merits of that alternative approach.

But, first, what about conventional regulatory approaches, that is, performance standards and technology standards?

Conventional Regulatory Standards

In short, experience has shown that such standards cannot ensure achievement of emissions targets, create problematic unintended consequences, and are very costly for what they achieve.

Why can conventional standard not ensure achievement of reasonable emissions targets? First, standards typically focus on new emissions sources, and do not address emissions from existing sources. Think about greenhouse gas standards for new cars and new power plants, for example. Second, standards cannot possibly address all types of new sources, given the ubiquity of energy generation and use (and hence CO₂ emissions) in a modern economy. Third, emissions depend upon many factors that cannot be addressed by standards, such as: emissions from existing sources and unregulated new sources; how quickly the existing capital stock is replaced; the growth in the number of new emissions sources; and how intensively emissions-generating plants and equipment are utilized.

Next, what about those unintended consequences? First, by reducing operating costs, energy-efficiency standards – for example — can cause more intensive use of regulated equipment (for example, air conditioners are run more often), leading to offsetting increases in emissions — the “rebound effect.” Second, firms and households may delay replacing existing equipment if standards make new equipment more costly. This is the well-known problem with vintage-differentiated regulations or “New Source Review.” Third, standards may encourage counterproductive, unintended shifts among regulated activities (for example, from purchasing cars to purchasing SUVs under the CAFE program). All of these unintended consequences result from the problematic incentives that standards can create, compared with the efficient incentives created by a cap-and-trade system (or a carbon-tax, for that matter).

If you favor a regulatory approach, then you may welcome what’s coming from EPA as a result of the Supreme Court ruling of a few years ago combined with the Administration’s endangerment finding. For my part, I don’t welcome it; I worry about it, because the set of regulatory approaches that could be forthcoming will accomplish relatively little, do so at an unnecessarily high cost, and hence play into the hands of opponents of progressive climate policy. (More about that in some other, future post.)

Putting a Price on Carbon

To virtually all participants in the policy world, it has become increasingly clear that the only approach that can do the job and do it cost-effectively is one which involves at its core putting a price on carbon. That leaves cap-and-trade and carbon taxes. Let me take these in turn.

Cap-and-Trade

Let’s step back from the debate regarding the details of the Waxman-Markey House bill or the new Senate proposal by Senators Boxer and Kerry, and think about the essence of the cap-and-trade approach. (For some of those details, however, please see my previous posts, where I have commented on various aspects of Waxman-Markey and described a proposal I developed for The Hamilton Project of an up-stream, economy-wide CO₂ cap-and-trade system to cost-effectively achieve meaningful greenhouse gas emissions reductions.)

Here are the basics. First, aggregate emissions from regulated sources are capped, and the cap is enforced through a requirement for affected firms to hold emissions allowances. Importantly, allowance trading minimizes costs of meeting the cap. It does this because allowances migrate to the highest-valued uses, covering emissions that are the most costly to reduce. So, the emission reductions undertaken are those that are least costly to achieve. In essence, the uniform market price of allowances creates incentives for all covered sources to reduce all emissions, and do so cost-effectively.

A cap-and-trade system can be more environmentally-effective and more cost-effective than standards. First, in terms of environmental-effectiveness, a cap-and-trade system can ensure achievement of emissions targets. Cap-and-trade allows policymakers to set specific overall emissions targets. And a well-enforced system guarantees achievement of those targets, because emissions will not exceed available allowances. An economy-wide, upstream cap-and-trade system on the carbon content of fossil fuels can cover all fossil-fuel-related CO₂ emissions without needing to regulate each emissions source individually.

In terms of cost-effectiveness, a well-designed cap-and-trade system minimizes emission reduction costs. Unlike NO_x, SO₂, and other pollutants, GHG emission reductions have the same effect no matter how, where, or when they are achieved. This makes the climate change problem unique in the degree to which compliance flexibility can be used to lower costs without compromising environmental integrity. Hence, a cap-and-trade system can minimize costs while still meeting environmental objectives by offering three forms of flexibility: what flexibility; where flexibility; and when flexibility.

In regard to “what flexibility,” many types of actions offer low-cost emission reductions, and a cap-and-trade system allows emission reductions through whatever measures are least costly. By contrast, standards can target only certain identified emission reduction measures, leaving other cost-effective opportunities untapped. Furthermore, predictions of what measures are cost-effective may be wrong.

In regard to “where flexibility,” the costs of emission reductions vary widely across industries, across facilities, and even across users of the same equipment. A cap-and-trade system exploits this variation in costs by achieving reductions wherever they are least costly. By contrast, standards would only be cost-effective if they accounted for all of the variation in costs across sectors, technologies, and regulated entities — but it is completely infeasible for standards to do this. Emission reduction costs across sectors and technologies change over time, making the flexibility offered by a cap-and-trade system even more valuable. Also, lower-cost opportunities to reduce emissions may exist in other countries. Importantly, a cap-and-trade system creates a common currency (emissions allowances) that makes it possible to link with other systems.

A cap-and-trade system also minimizes costs through “when flexibility.” Costs can be reduced through flexibility in the timing of emission reductions by avoiding: premature retirement of capital stock or lock-in of existing technologies; and unnecessarily costly reductions in one year due to unusual circumstances when less-costly offsetting reductions can be achieved in other years. A cap-and-trade can incorporate “when flexibility”
without compromising cumulative emissions targets through: allowance banking and borrowing; and multi-year compliance periods.

Beyond such “static cost-effectiveness,” cap-and-trade creates incentives for technology innovation, and thereby lowers long-run costs. By rewarding any means of reducing emissions, a cap-and-trade system provides broad incentives for any innovations that lower the cost of achieving emissions targets. Although standards may encourage development of lower cost means of meeting the standards’ specific requirements, they do not encourage efforts to exceed those standards.

Several cap-and-trade systems have been successful at achieving environmental goals and cost savings: the phase-out of leaded gasoline in the 1980s; the phase-out of ozone depleting substances; and the Clean Air Act amendments of 1990 SO₂ allowance trading program to cut acid rain by 50%. Perceived shortcomings in other cap-and-trade systems reflect design choices, not problems with the policy instrument itself. This applies both to California’s RECLAIM program, and the pilot phase of the EU Emissions Trading Scheme (which is operating successfully in its real, Kyoto phase).

In summary, compared with conventional standards, a cap-and-trade system can be more environmentally-effective and more cost-effective. As with any policy instrument, however, careful design is important.

Taxing Carbon

As I mentioned, it is clear that the only approach that can do the job and do it cost-effectively is one that involves putting a price on carbon. So, what about the other carbon-pricing approach — a carbon tax?

I am by no means opposed to the notion of a carbon tax, having written about such approaches for more than twenty years. Indeed, both cap-and-trade and carbon taxes are good approaches to the problem; they have many similarities, some tradeoffs, and a few key differences. I am opposed, however, to the confused and misleading straw-man arguments that have sometimes been used against cap-and-trade by carbon-tax proponents.

While there are tradeoffs between these two principal market-based instruments targeting CO₂ emissions — a cap-and-trade system and a carbon tax – the best (and most likely) approach for the short to medium term in the United States is a cap-and-trade system. I say this based on three criteria: environmental effectiveness, cost effectiveness, and distributional equity. So, my position is not capitulation to politics. On the other hand, sound assessments of environmental effectiveness, cost effectiveness, and distributional equity should surely be made in the real-world political context.

The key merits of the cap-and-trade approach I have described above are, first, the program can provide cost-effectiveness, while achieving meaningful reductions in greenhouse gas emissions levels. Second, it offers an easy means of compensating for the inevitably unequal burdens imposed by a climate policy. Third, it provides a straightforward means to harmonize with other countries’ climate policies. Fourth, it avoids the current political aversion in the United States to taxes. Fifth, it is unlikely to be degraded – in terms of its environmental performance and cost effectiveness – by political forces. And sixth, this approach has a history of successful adoption and implementation in this country over the past two decades.

Having said this, there are some real differences between taxes and cap-and-trade that need to be recognized. First, environmental effectiveness: a tax does not guarantee achievement of an emissions target, but it does provides greater certainty regarding costs. This is a fundamental tradeoff. Taxes provide automatic temporal flexibility, which needs to be built into a cap-and-trade system through provision for banking, borrowing, and possibly a cost-containment mechanism. On the other hand, political economy forces strongly point to less severe targets if carbon taxes are used, rather than cap-and-trade – this is not a tradeoff, and this is why environmental NGOs are opposed to the carbon-tax approach.

In principle, both carbon taxes and cap-and-trade can achieve cost-effective reductions, and – depending upon design — the distributional consequences of the two approaches can be the same. But the key difference is that political pressures on a carbon tax system will most likely lead to exemptions of sectors and firms, which reduces environmental effectiveness and drives up costs, as some low-cost emission reduction opportunities are left off the table. But political pressures on a cap-and-trade system lead to different allocations of allowances, which affect distribution, but not environmental effectives, and not cost-effectiveness.

Proponents of carbon taxes worry about the propensity of political processes under a cap-and-trade system to compensate sectors through free allowance allocations, but a carbon tax is sensitive to the same political pressures, and may be expected to succumb in ways that are ultimately more harmful: reducing environmental achievement and driving up costs.

The Bottom Line

The Hamilton Project staff concluded in an overview paper (which I highly recommend) that a well-designed carbon tax and a well-designed cap-and-trade system would have similar economic effects. Hence, they said, the two primary questions to use in deciding between them should be: which is more politically feasible; and which is more likely to be well-designed?

The answer to the first question is obvious; and I have argued here that given real-world political forces, the answer to the second question also favors cap-and-trade. In other words, it is important to identify and design policy that will be “optimal in Washington,” not just from the perspective of Cambridge, New Haven, or Berkeley.

In “policy heaven,” the optimal instrument to address climate-change emissions may well be a carbon tax (largely because of its simplicity), but in the real world in which policy is developed and implemented, cap-and-trade is the best approach if one is serious about addressing the threat of climate change with meaningful, effective, and cost-effective policies.

The Making of a Conventional Wisdom

Despite the potential cost-effectiveness of market-based policy instruments, such as pollution taxes and tradable permits, conventional approaches – including design and uniform performance standards – have been the mainstay of U.S. environmental policy since before the first Earth Day in 1970. Gradually, however, the political process has become more receptive to innovative, market-based strategies. In the 1980s, tradable-permit systems were used to accomplish the phasedown of lead in gasoline (at a savings of about $250 million per year), and to facilitate the phaseout of ozone-depleting chloroflourocarbons (CFCs); and in the 1990’s, tradable permits were used to implement stricter air pollution controls in the Los Angeles metropolitan region, and – most important of all – a cap-and-trade system was adopted to reduce sulfur dioxide (SO₂) emissions and consequent acid rain by 50 percent under the Clean Air Act amendments of 1990 (saving about $1 billion per year in abatement costs). Most recently, cap-and-trade systems have emerged as the preferred national and regional policy instrument to address carbon dioxide (CO₂) emissions linked with global climate change (see my previous posts of February 6^th on an “Opportunity for a Defining Moment” and March 7^th on “Green Jobs”).

Why has there been a relatively recent rise in the use of market-based approaches? For academics like me, it would be gratifying to believe that increased understanding of market-based instruments had played a large part in fostering their increased political acceptance, but how important has this really been? In 1981, my Harvard colleague, political scientist Steven Kelman surveyed Congressional staff members, and found that support and opposition to market-based environmental policy instruments was based largely on ideological grounds: Republicans, who supported the concept of economic-incentive approaches, offered as a reason the assertion that “the free market works,” or “less government intervention” is desirable, without any real awareness or understanding of the economic arguments for market-based programs. Likewise, Democratic opposition was based largely upon ideological factors, with little or no apparent understanding of the real advantages or disadvantages of the various instruments. What would happen if we were to replicate Kelman’s survey today? My refutable hypothesis is that we would find increased support from Republicans, greatly increased support from Democrats, but insufficient improvements in understanding to explain these changes. So what else has mattered?

First, one factor has surely been increased pollution control costs, which have led to greater demand for cost-effective instruments. By the late 1980’s, even political liberals and environmentalists were beginning to question whether conventional regulations could produce further gains in environmental quality. During the previous twenty years, pollution abatement costs had continually increased, as stricter standards moved the private sector up the marginal abatement-cost curve. By 1990, U.S. pollution control costs had reached $125 billion annually, nearly a 300% increase in real terms from 1972 levels.

Second, a factor that became important in the late 1980’s was strong and vocal support from some segments of the environmental community. By supporting tradable permits for acid rain control, the Environmental Defense Fund seized a market niche in the environmental movement, and successfully distinguished itself from other groups. Related to this, a third factor was that the SO₂ allowance trading program, the leaded gasoline phasedown, and the CFC phaseout were all designed to reduce emissions, not simply to reallocate them cost-effectively among sources. Market-based instruments are most likely to be politically acceptable when proposed to achieve environmental improvements that would not otherwise be achieved.

Fourth, deliberations regarding the SO₂ allowance system, the lead system, and CFC trading differed from previous attempts by economists to influence environmental policy in an important way: the separation of ends from means, that is, the separation of consideration of goals and targets from the policy instruments used to achieve those targets. By accepting – implicitly or otherwise – the politically identified (and potentially inefficient) goal, the ten-million ton reduction of SO₂ emissions, for example, economists were able to focus successfully on the importance of adopting a cost-effective means of achieving that goal.

Fifth, acid rain was an unregulated problem until the SO₂ allowance trading program of 1990; and the same can be said for leaded gasoline and CFC’s. Hence, there were no existing constituencies – in the private sector, the environmental advocacy community, or government – for the status quo approach, because there was no status quo approach. We should be more optimistic about introducing market-based instruments for “new” problems, such as global climate change, than for existing, highly regulated problems, such as abandoned hazardous waste sites.

Sixth, by the late 1980’s, there had already been a perceptible shift of the political center toward a more favorable view of using markets to solve social problems. The George H. W. Bush Administration, which proposed the SO₂ allowance trading program and then championed it through an initially resistant Democratic Congress, was (at least in its first two years) “moderate Republican;” and phrases such as “fiscally responsible environmental protection” and “harnessing market forces to protect the environment” do have the sound of quintessential moderate Republican issues. But, beyond this, support for market-oriented solutions to various social problems had been increasing across the political spectrum for the previous fifteen years, as was evidenced by deliberations on deregulation of the airline, telecommunications, trucking, railroad, and banking industries. Indeed, by the mid-1990s, the concept (or at least the phrase), “market-based environmental policy,” had evolved from being politically problematic to politically attractive.

Seventh and finally, the adoption of the SO₂ allowance trading program for acid rain control – like any major innovation in public policy – can partly be attributed to a healthy dose of chance that placed specific persons in key positions, in this case at the White House, EPA, the Congress, and environmental organizations. The result was what remains the golden era in the United States for market-based environmental strategies.

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If you would like to read more about the factors that have brought about the changes that have occurred in the political reception given to market-based environmental policy instruments over the past two decades, here are some references:

Stavins, Robert N. “What Can We Learn from the Grand Policy Experiment? Positive and Normative Lessons from SO2 Allowance Trading.” Journal of Economic Perspectives, Volume 12, Number 3, pages 69-88, Summer 1998.

Keohane, Nathaniel O., Richard L. Revesz, and Robert N. Stavins. “The Choice of Regulatory Instruments in Environmental Policy.” Harvard Environmental Law Review, volume 22, number 2, pp. 313-367, 1998.

Hahn, Robert W. “The Impact of Economics on Environmental Policy.” Journal of Environmental Economics and Management 39(2000):375-399.

Hahn, Robert W., Sheila M. Olmstead, and Robert N. Stavins. “Environmental Regulation During the 1990s: A Retrospective Analysis.” Harvard Environmental Law Review, volume 27, number 2, 2003, pp. 377-415.

Green Jobs

The January 12, 2009 issue of The New Yorker includes a well-written and in some ways inspiring article by Elizabeth Kolbert, profiling Van Jones, founder and president of Green for All. In the article, “Greening the Ghetto: Can a Remedy Serve for Both Global Warming and Poverty,” Kolbert includes the following passage:

When I presented Jones’s arguments to Robert Stavins, a professor of business and government at Harvard who studies the economics of environmental regulation, he offered the following analogy: “Let’s say I want to have a dinner party. It’s important that I cook dinner, and I’d also like to take a shower before the guests arrive. You might think, Well, it would be really efficient for me to cook dinner in the shower. But it turns out that if I try that I’m not going to get very clean and it’s not going to be a very good dinner. And that is an illustration of the fact that it is not always best to try to address two challenges with what in the policy world we call a single policy instrument.”

That brief quote generated a considerable amount of commentary in the blogosphere, much of it negative, and some of it downright hostile. This surprised me, because I didn’t consider the proposition to be controversial, and I had chosen my words carefully, simply stating that “it is not always best to try to address two challenges with … a single policy instrument.” Two activities — each with a sensible purpose — can be very effective if done separately, but sometimes combining them means that one does a poor job with one, the other, or even both.

In the policy world, such dual-purpose policy instruments are sometimes a good, even great idea (gas taxes are an example), but other times, they are not. Whether trying to kill two birds with one stone makes sense depends upon the proximity of the birds, the weapon being used, and the accuracy of the stoner. In the real world of important policy challenges — such as environmental degradation and economic recession — these are empirical questions and need to be examined case by case, which was my point in the brief quote. Since my further explanation of this point in the green jobs context (in an interview that lasted 30 to 60 minutes — I don’t recall) did not find its way into Ms. Kolbert’s article (no fault of hers — she had plenty of sources, plenty of material, and limited space), let me provide that explanation here.

In 1990, when Congress sought to cut sulfur dioxide (SO₂) emissions from coal-fired power plants by 50% to reduce acid rain, Senator Robert Byrd (West Virginia) argued against the proposal for a national cap-and-trade system, because it would displace Appalachian coal mining jobs through reduced demand for high-sulfur coal. He recommended instead a national requirement for all plants to install scrubbers, which would have increased costs nationally by $1 billion per year in perpetuity.

Fortunately, Senator Ted Kennedy (Massachusetts) recognized that these two problems (acid rain and displaced miners) called for two separate policy instruments. Simultaneous with the passage of the Clean Air Act amendments of 1990, which established the path-breaking SO₂ allowance trading program, Congress passed a job training and compensation initiative for Appalachian coal miners, at a one-time cost of $250 million. Acid rain was cut by 50%, $1 billion per year was saved for the economy, and sensible and meaningful aid was provided to the displaced miners. Two different policies were used to address two different purposes. Sometimes that is the wisest course.

What about two current challenges: concern about the environment, in particular global climate change, on the one hand, and the need to turn around the economy, on the other hand? Can “green jobs” be the answer to both?

Will an economic stimulus package — properly designed — lead to job creation in the short term? Yes, but to some degree this will be by moving forward in time the date of job creation, as opposed to creating additional jobs in the long run. Of course, at a time of recession and increasing unemployment, that can be a sensible thing to do. So, by expanding economic activity, an economic stimulus package can surely create jobs — green or otherwise — in the short term.

But will a stimulus package — such as subsidies for renewable energy — create net jobs from the change in the nature of economic activity? The key question here is whether the encouraged economic activities in green sectors are more labor-intensive than the discouraged economic activities in other sectors, such as with a shift to renewables from fossil fuels.

This is considerably less clear, but there are cases where it is likely to be valid. Solar rooftop installation, for example, is labor-intensive. And the greatest consistency between economic stimulus and greening the economy is within the energy-efficiency realm, in particular, activities such as the weatherization of homes and businesses. Such projects are highly labor-intensive, can be done quickly, and will save energy. And, importantly, they will reduce the long-term cost of meeting climate objectives.

But some other areas, such as new green infrastructure, will happen much more slowly — partly because of NIMBY (“not in my backyard”) problems — and so are less consistent with the purpose of economic stimulus. An example of the challenge is presented by the current interest in expanding and improving our national electricity grid.

A more interlinked and better grid is needed for increased reliance on renewable energy sources, which will be needed to address climate change. First, greater use of renewable resources will require an expanded grid just to transmit electricity from the Great Plains, for example, to cities with high demand for power. And, second, this will also require the use of a so-called “smart grid,” so that greater reliance on intermittent sources of electricity, such as from wind farms, can be balanced with cuts in consumer demand when power is scarce.

But the timing of grid expansion — important for the use of renewables and achieving climate goals — is not coincident with the appropriate timing of the economic stimulus. As was reported in an article by Matthew Wald in the New York Times (“Hurdles (Not Financial Ones) Await Electric Grid Update,” January 7, 2009, p. A11), the CEO of the American Transmission Company — which operates in four midwestern states — said that the firm’s most recent major project, a 200-mile transmission line from Minnesota to Wisconsin, took 2 years to build, but 8 years prior to that to win the necessary permits!

Likewise, an article by Peter Behr in Climate Wire (“Green Power Express line gets derailed by patchwork grid rules,” Feburary 12, 2009, p. 1) focuses on the dilemma facing ITC Holdings, the nation’s largest independent electric transmission company, which has been seeking permission from the Federal Energy Regulatory Commission to build a line to bring wind power from the Great Plains to the Midwest and East. The company’s chairman and CEO, Joseph Welch, indicates that a greater hurdle than the necessary money or “even the ever-present citizen opposition to new transmission projects” is a set of rules for interstate transmission lines that effectively prohibits projects that are not immediately required to maintain the grid’s reliability. A project intended to provide future green power does not meet the test.

These are just two examples of the unpleasant reality of the pace of investment and change in this important category of green infrastructure frequently talked about in the context of quick economic stimulus. Surely, economic recovery, increased reliance on renewable sources of energy, and a smarter, inter-connected grid are all important. But that does not mean they are best addressed with a single policy instrument – the economic stimulus package.

So, the strongest support for “green job creation” is with regard to economic expansion, as opposed to changes in the economy. Of course, the key economic question remains whether even more jobs would be created with a different sort of expansion. In any event, while we are expanding economic activity through the economic stimulus package, it makes sense to reduce any tendency to lock in new capital stock that would make it more difficult and costly to achieve long-term environmental goals. But that is very different from claiming that all substitution of green activities for brown activities creates jobs in the long-term.

As the government uses economic stimulus to expand economic activity, it can and should tilt the expansion in a green direction. But rather than a “broad-brush green painting of the stimulus,” this may call for some careful, selective, and well thought-through “green tinting.”

Addressing the worst economic recession in generations calls for the most effective economic stimulus package that can be devised, not a stimulus package that is diminished in effectiveness through excessive bells and whistles meant to address a myriad of other (legitimate) social concerns. And, likewise, getting serious about global climate change will require the enactment and implementation of meaningful, dedicated climate policies, most likely a comprehensive national CO₂ cap-and-trade system. These are two serious but different policy problems, and they call for two serious, carefully-crafted policy responses.

After I wrote this brief essay, someone brought to my attention an article posted at Slate by Michael Levi, a senior fellow at the Council on Foreign Relations(“Barking Up the Wrong Tree: Why ‘Green Jobs’ May Not Save the Economy or the Environment,” March 4, 2009). I found Levi’s assessment to be sensible and compelling, but I may be biased by two realities: one is that he and I are fundamentally in agreement; and the other is that we have been professionally affiliated, because he is the co-author of a paper (“Policies for Developing Country Engagement” ) which is part of the Harvard Project on International Climate Agreements, a global research and outreach initiative which I direct. Rather than summarize or repeat any of Michael Levi’s article, I urge you to read it in its entirety at the Slate web address above.