market-based environmental policies Archives - Page 15 of 37

What are the Benefits and Costs of EPA’s Proposed CO2 Regulation?

On June 2^nd, the Obama Administration’s Environmental Protection Agency (EPA) released its long-awaited proposed regulation to reduce carbon dioxide (CO₂) emissions from existing sources in the electricity-generating sector. The regulatory (rule) proposal calls for cutting CO₂ emissions from the power sector by 30 percent below 2005 levels by 2030. This is potentially significant, because electricity generation is responsible for about 38 percent of U.S. CO₂ emissions (about 32 percent of U.S. greenhouse gas (GHG) emissions).

On June 18^th, EPA published the proposed rule in the Federal Register, initiating a 120-day public comment period. In my previous essay at this blog, I wrote about the fundamentals and the politics of this proposed rule (EPA’s Proposed Greenhouse Gas Regulation: Why are Conservatives Attacking its Market-Based Options?). Today I take a look at the economics.

Cost-Effective, Perhaps – but Efficient?

The proposed rule grants freedom to implementing states to achieve their specified emissions-reduction targets in virtually any way they choose, including the use of market-based instruments (the White House has referenced cap-and-trade in this context, although somewhat obliquely as “market-based programs,” and state-level carbon taxes might also be acceptable – if any states were to include them in their plans to implement the regualtion). Also, the proposal allows for multistate proposals and for states and regions to establish linkages among their state and multi-state market-based instruments. Some questions remain regarding the temporal flexibility (banking and borrowing) that the proposed rule will allow, but it’s reasonable to conclude at this point that although EPA may not be guaranteeing cost-effectiveness, it is allowing for it, indeed facilitating it. As Dallas Burtraw of Resources for the Future has said, the proposed rule ought to be judged to be potentially cost-effective.

Cost-effectiveness (achieving a given target at the lowest possible aggregate cost) is one thing, but economists – and possibly some other policy wonks – may wonder if the proposal is likely to be efficient (maximizing the difference between benefits and costs). This is a much higher mountain to climb, and a particularly challenging one for a regional, national, or sub-national climate-change policy, given the global commons nature of the problem.

The Challenge of this Global Commons Problem

GHGs mix globally in the atmosphere, and so damages are spread around the world and are unaffected by the location of emissions. This means that any jurisdiction taking action – a region, a country, a state, or a city – will incur the direct costs of its actions, but the direct benefits (averted climate change) will be distributed globally. Hence, the direct climate benefits a jurisdiction reaps from its actions will inevitably be less than the costs it incurs, despite the fact that global climate benefits may be greater – possibly much greater – than global costs.

(An Aside: This presents the classic free-rider problem of this ultimate global commons problem: It is in the interest of no country to take action, but each can reap the benefits of any countries that do take action. This is why international, if not global, cooperation is essential. See the extensive work of the Harvard Project on Climate Agreements.)

On June 2^nd, EPA released its 376-page Regulatory Impact Analysis (RIA) of the proposed “Clean Power Plan” rule, the same day it released the 645-page proposed rule itself. An RIA is essentially a benefit-cost analysis, required for significant new Federal rules by a series of Executive Orders going back to the presidency of Jimmy Carter, and reaffirmed by every President since, including most recently President Obama.

Given the fundamental economic arithmetic of a global commons problem, it would be surprising – to say the least – if EPA were to find that the expected benefits of the proposed rule would exceed its expected costs, but this is precisely what EPA has found. Indeed, its central estimate is of positive net benefits (benefits minus costs) of $67 billion annually in the year 2030 (employing a mid-range 3% discount rate). How can this be?

Two Answers to the Conundrum

First, EPA does not limit its estimate of climate benefits to those received by the United States (or its citizens), but uses an estimate of global climate benefits.

Second, in addition to quantifying the benefits of climate change impacts associated with CO₂ emissions reductions, EPA quantifies and includes (the much larger) benefits of human-health impacts associated with reductions in other (correlated) air pollutants.

Of course, even if benefits exceed costs at the given level of stringency of the proposed rule, it does not mean that the rule is economically efficient, because it could be the case that benefits would exceed costs by an even greater amount with a more stringent or with a less stringent rule. However, if benefits are not greater than costs (negative net benefits), then the rule cannot possibly be efficient, so I will stick with the all-too-common Washington practice and simply ask whether the analysis indicates a winner or a loser at the proposed rule’s given level of stringency. In other words, the question becomes, “Is the proposed rule welfare-enhancing (even if it is not welfare-maximizing)?”

Now, let’s take a look at the numbers from these two key aspects of EPA’s economic analysis and the issues surrounding the calculations.

U.S. versus Global Damages

There are surely ethical arguments (and possibly legal arguments) for employing a global damage estimate, as opposed to a U.S. damage estimate, in a benefit-cost analysis of a U.S. climate policy, but until recently all Regulatory Impact Analyses over several decades had focused exclusively on U.S. impacts.

In a recent working paper, “Determining the Proper Scope of Climate Change Benefits,” Ted Gayer, Vice President and Director of Economic Studies at the Brookings Institution, and Kip Viscusi, University Distinguished Professor of Law, Economics, and Management at Vanderbilt University, review the history of RIAs, including their virtually exclusive focus on national impacts (defined by geography or U.S. citizenship) in benefit and cost estimates of regulations.

In the context of a conventional RIA, it does seem strange – at least at first blush – to use a global measure of benefits of a U.S. regulation. If this practice were applied in a consistent manner – that is, uniformly in all RIAs – it would result in some quite bizarre findings. For example, a Federal labor policy that increases U.S. employment while cutting employment in competitor economies might be judged to have zero benefits!

Another example, this one courtesy of Tim Taylor via Ted Gayer: Under global accounting, if a domestic climate policy had the unintended consequence of causing emissions and economic leakage (through relocation of some manufacturing to other countries), that would not be considered a cost of the regulation (and with diminishing marginal utility of income, it might be counted as a benefit)!

On the other hand, a counter-argument to this line of thinking is that the usual narrow U.S.-only geographic scope of an RIA is simply not appropriate for a global commons problem. Otherwise, we would simply restate in economic terms the free-rider consequences of a global commons challenge. In other words, a domestic-only RIA of a climate policy could have the effect of “institutionalizing free riding,” to quote my Harvard Kennedy School colleague, Professor Joseph Aldy. Of course, if global benefits are to be included in a regulatory assessment, it can be argued that global costs (such as leakage) should also be considered.

I leave it to legal scholars and lawyers to debate the law, and I defer to the philosophers among us to debate the ethics, but let’s at least ask what the consequences would be for EPA’s analysis if a U.S climate benefits number were used, rather than a global number. For this purpose, we can start with EPA’s estimates (from Table ES-7 on page ES-19 and Table ES-10 on page ES-23 of its Regulatory Impact Analysis of the proposed rule) for 2030 benefits and costs, using a mid-range 3% real discount rate. The estimated (global) climate benefits of the rule are $31 billion.

In order to think about what the domestic climate benefits might be, we can turn to the Obama administration’s original calculation of the Social Cost of Carbon in 2010, where the Interagency Working Group estimated a central global value for 2010 of $19 per ton of CO₂, and noted (and explained in more detail in a subsequent scholarly paper by several members of the Working Group) that U.S. benefits from reducing GHG emissions would be, on average, about 7 to 10 percent of global benefits across the scenarios analyzed with the one model that permitted such geographic disaggregation.

(The Interagency Working Group also suggested that if climate damages are simply proportional to GDP, then the U.S. share would be about 23%. However, given the IPCC’s prediction of highly unequal geographic distribution of climate change effects worldwide, combined with the exceptionally heterogeneous nature of climate sensitivity among the world’s economies, which vary from those with trivial reliance on agriculture to those dominated by their agricultural sectors, I find the argument behind this second approach unconvincing.)

Taking the midpoint of the Obama Working Group’s 7-10% range, U.S. damages (benefits) may be estimated to be 8.5% of global damages, which would reduce the $31 billion reported in the new RIA to about $2.6 billion, which is considerably less than the RIA’s estimated total annual compliance costs of $8.8 billion (assuming that the states facilitate cost-effective actions). This validates the intuition, explained above, that for virtually any jurisdiction, the direct climate benefits it reaps from its actions will be less than the costs it incurs (again, despite the fact that global climate benefits may be much greater than global costs).

There are plenty of caveats on both sides of this simple analysis. One of the most important is that if the proposed U.S. policy were to increase the probability of other countries taking climate policy actions (which I believe is probably the case), then the impacts on U.S. territory of such foreign policy actions would merit inclusion even in a traditional U.S.-only benefit-cost analysis. More broadly, although it has been traditional to use a U.S.-only benefits measure in RIAs, the current guidelines for carrying out these analyses from the Office of Information and Regulatory Affairs of the U.S. Office of Management and Budget (Circular A-4) requires that geographic U.S. benefit and cost estimates be provided, but also allows for the optional inclusion of global estimates.

Pending resolution (or more likely, discussion and debate) from lawyers and philosophers regarding the legal and ethical issue of employing domestic benefits versus global benefits in a climate regulation RIA, it is essential to recognize that there is an even more important factor that explains how EPA came up with estimates of significant positive net benefits (benefits exceeding costs) for the proposed rule (and would have even if a domestic climate benefits number had been employed), namely, the inclusion of (domestic) health impacts of other air pollutants, the emissions of which are correlated with those of CO₂.

Correlated Pollutants and Co-Benefits

The Obama Administration’s proposed regulation to reduce CO₂ emissions from the electric power sector is intended to achieve its objectives through a combination of less electricity generated (compared with a business-as-usual trajectory), greater dispatch of electricity from less CO₂-intensive sources (natural gas, nuclear, and renewable sources, instead of coal), and more investment in low CO₂-intensive sources. Hence, it is anticipated that less coal will be burned than in the absence of the regulation (and more use of natural gas, nuclear, and renewable sources of electricity). This means not only less CO₂ being emitted into the atmosphere, but also decreased emissions of correlated local air pollutants that have direct impacts on human health, including sulfur dioxide (SO₂), nitrogen oxides (NO_x), particulate matter (PM), and mercury (Hg).

It is well known that higher concentrations of these pollutants in the ambient air we breathe – particularly smaller particles of particulate matter (PM_2.5) – have very significant human health impacts in terms of increased risk of both morbidity and mortality. The numbers dwarf the climate impacts themselves. Whereas the U.S. climate change impacts of CO₂ reductions due to the proposed rule in 2030 are probably less than $3 billion per year (see above), the health impacts (co-benefits) of reduced concentrations of correlated (non-CO₂) air pollutants are estimated by EPA to be some $45 billion/year (central estimate)! (By the way, I assume that the co-benefits estimated by EPA are based upon a comparison with a business-as-usual baseline that includes the effects of all existing EPA and state regulations for these same local air pollutants. If not, the RIA will need to be revised.)

The Bottom Line

The combined U.S.-only estimates of annual climate impacts of CO₂ ($3 billion) and health impacts of correlated pollutants ($45 billion) greatly exceed the estimated regulatory compliance costs of $9 billion/year, for positive net benefits amounting to $39 billion/year in 2030. This is the key argument related to the possible economic efficiency of the proposed rule from the perspective of U.S. welfare. If EPA’s global estimate of climate benefits ($31 billion/year) is employed instead, then, of course, the rule looks even better, with total annual benefits of $76 billion, leading to EPA’s bottom-line estimate of positive net benefits of $67 billion per year. See the summary table below.

The Obama Administration’s proposed regulation of existing power-sector sources of CO₂ has the potential to be cost-effective, and if you accept these numbers, it can also be welfare-enhancing, if not welfare-maximizing.

That said, I assume that proponents of the Obama Administration’s proposed rule will take this assessment of EPA’s Regulatory Impact Analysis as evidence of the sensibility of the rule, and opponents of the Administration’s proposed actions will claim that my assessment of the RIA provides evidence of the foolishness of EPA’s proposal. So it is in our pluralistic system (not to mention, in the context of the political polarization that has gripped Washington on this and so many other issues).

————————————————————————————————————————–

Benefits and Costs of EPA’s Proposed Clean Power Plan Rule in 2030

(Mid-Point Estimates, Billions of Dollars)

	Climate Change Impacts		Health Impacts (Co-Benefits) of Correlated Pollutants plus …
	Domestic	Global	Domestic Climate Impacts	Global Climate Impacts
Benefits
Climate Change	$ 3	$ 31	$3	$31
Health Co-Benefits			$45	$45
Total Benefits	$ 3	$ 31	$48	$76
Total Compliance Costs	$ 9	$ 9	$ 9	$ 9
Net Benefits (Benefits – Costs)	– $ 6	$ 22	$ 39	$ 67

————————————————————————————————————————–

EPA’s Proposed Greenhouse Gas Regulation: Why are Conservatives Attacking its Market-Based Options?

This week, the Obama Administration’s Environmental Protection Agency (EPA) released its long-awaited proposed regulation to reduce carbon dioxide (CO₂) emissions from existing sources in the electricity-generating sector. The regulatory (rule) proposal calls for cutting CO₂ emissions from the power sector by 30 percent below 2005 levels by 2030.

The Fundamentals in Brief

Through a carefully designed formula, EPA’s proposal lists specific targets for each state, under Section 111(d) of the Clean Air Act. States are given broad flexibility for how to meet their targets, including: increasing the efficiency of fossil-fuel power plants; switching electricity dispatch from coal-fired generating plants to natural gas-fired generating plants; developing new low-emissions generation, such as new natural gas combined cycle plants, more renewable sources (wind and solar), nuclear, or coal with carbon capture and storage; and more efficient end-use of electricity.

States are also given flexibility to employ (in their implementation plans to be submitted to EPA) any of a wide variety of policy instruments, including but by no means limited to market-based trading systems. Furthermore, states can work together to submit multi-state plans.

The proposed regulation will be finalized after receipt of comments one year from now (June 30, 2015). Then states will have until July 2016 to submit their plans, and can request one-year extensions (or two-year extensions for multi-state plans). Compliance commences in 2020.

A Big-Picture Assessment of the Proposed Rule

Let’s start by acknowledging that the proposed policy will be less effective environmentally and less cost-effective economically than the economy-wide approach the Administration previously tried with the Waxman-Markey bill, which passed the U.S. House of Representatives in 2009, but failed to receive a vote in the U.S. Senate. Electricity generation is responsible for about 38 percent of U.S. CO₂ emissions, and about 32 percent of U.S. greenhouse gas (GHG) emissions.

Given ongoing political polarization in Washington and the inability of Congress to approve that more comprehensive and more cost-effective approach, this is probably the best the administration could do. Together with the motor-vehicle fuel efficiency and appliance energy efficiency standards previously put in place, this is certainly a step in the right direction.

More broadly, the importance of these U.S. moves in the international context should not be underestimated. Although the United States accounts for only about 17% of global CO₂ emissions (second to China’s 26% in 2010), these steps by the U.S. government can help international efforts to bring the large emerging economies (China, India, Brazil, Korea, South Africa, and Mexico) on board for a future (Paris, 2015) agreement under the Durban Platform for Enhanced Action.

Domestically, EPA’s proposed state-by-state approach does not guarantee cost-effectiveness, because under the formula employed, marginal abatement costs will initially vary across states. However, freedom is given to the states to employ market-based instruments, in particular, cap-and-trade systems (with carbon taxes presumably also an option). And EPA has emphasized its willingness to consider multi-state implementation plans (think, for example, of the existing Regional Greenhouse Gas Initiative – RGGI – the cap-and-trade system operating in nine northeast states; and the likelihood of a future linked policy bringing together California’s AB-32 cap-and-trade system with policies in Oregon and Washington).

The ability of states to develop under EPA’s rule such linked systems of market-based instruments, as well as the freedom for states and regions to subsequently establish linkages means that although EPA may not be guaranteeing cost-effectiveness, it is certainly allowing for it, indeed it is facilitating it.

Response from Environmental Advocacy Groups and Industry

Much of the response this week has not been surprising. The major environmental advocacy groups have been supportive of the proposed rule, despite the fact that they would prefer even greater ambition. Many in industry have also offered praise for the approach, particularly because of the flexibility that EPA has given for the means of achieving emissions reductions. In fact, some electricity-sector executives have been supportive, precisely for this reason, and appear to be encouraging the adoption of cap-and-trade systems. At a minimum, leading electric utilities, including some that are fossil-heavy, such as FirstEnergy Corporation and American Electric Power, Inc., have taken a “wait-and-see” attitude, rather than attacking the proposal.

Also not surprising has been strong opposition from the coal industry, as well as some prominent industry trade associations, including the U.S. Chamber of Commerce. Once the rule has become final (about a year from now), lawsuits will surely be filed by some of these private industry opponents and by a number of resistant states.

I will leave it to the lawyers to comment on the likely grounds of those anticipated lawsuits, as well as their probabilities of success. But, clearly, for the plan to succeed it will need to survive those legal challenges, which will work their way through the courts over several years.

Also, a significant change in the senate majority and in the party holding power after the next presidential election could result in progress being slowed to a crawl, if not the abandonment of the approach proposed by the current administration.

None of that is particularly surprising, but what should be surprising is the fact that conservative attacks on EPA’s proposed rule have focused, indeed fixated, on one of the options that is given to the states for implementation, namely the use of market-based instruments, that is, cap-and-trade systems. Given the demonization of cap-and-trade as “cap-and-tax” over the past few years by conservatives, why do I say that this fixation should be surprising?

The Irony of Conservatives Targeting Cap-and-Trade

Not so long ago, cap-and-trade mechanisms for environmental protection were popular in Congress. Now, such mechanisms are denigrated. What happened? Professor Richard Schmalensee (MIT) and I recently told the sordid tale of how conservatives in Congress who once supported cap and trade had come to lambast climate change legislation as “cap-and-tax.” Ironically, in doing this, conservatives have chosen to demonize their own market-based creation.

In the late 1980s, there was growing concern that acid precipitation – the result of SO₂ and, to a lesser extent, nitrogen oxides (NOx) reacting in the atmosphere to form sulphuric and nitric acids – was damaging forests and aquatic ecosystems, particularly in the northeast U.S. and southern Canada. In response, the U.S. Congress passed (and President George H.W. Bush signed into law) the Clean Air Act Amendments of 1990. Title IV of this law established the SO₂ allowance-trading system.

By the close of the 20th century, the SO₂ allowance-trading system had come to be seen as both innovative and successful. However, the successful enactment and implementation of the SO₂ cap-and-trade system in 1990 combined with the subsequent Congressional defeat of CO₂ cap-and-trade legislation 20 years later has produced a striking irony. Market-based, cost-effective policy innovation in environmental regulation – in particular, cap-and-trade – was originally championed and implemented by Republican administrations from that of President Ronald Reagan to that of President George W. Bush. But in recent years, Republicans have led the way in demonizing cap-and-trade, particularly as an approach to limiting carbon emissions.

For a long time, market-based approaches to environmental protection, such as cap-and-trade, bore a Republican label. In the 1980s, President Ronald Reagan’s EPA put in place a trading program to phase out leaded gasoline. It produced a more rapid elimination of leaded gasoline from the marketplace than had been anticipated, and at a saving of some $250 million per year, compared with a conventional no-trade, command-and-control approach. Not only did President George H.W. Bush successfully propose the use of cap-and-trade to cut SO₂ emissions, his administration advocated in international forums the use of emissions trading to cut global CO₂ emissions (a proposal initially resisted but ultimately adopted by the European Union). In 2005, President George W. Bush’s EPA issued the Clean Air Interstate Rule, aimed at reducing SO₂ emissions by a further 70% from their 2003 level. Cap-and-trade was again the policy instrument of choice.

From Bi-Partisan Support to Ideological Polarization

When the Clean Air Act Amendments were being considered in the Congress in 1989-1990, political support was not divided on partisan lines. Indeed, environmental and energy debates from the 1970s through much of the 1990s typically broke along geographic lines, rather than partisan lines, with key parameters being degree of urbanization and reliance on specific fuel types. Thus, the Clean Air Act Amendments of 1990 passed the Senate by a vote of 89-11 with 87% of Republican members and 91% of Democrats voting yea, and passed the House of Representatives by a vote of 401-21 with 87% of Republicans and 96% of Democrats voting in support.

But twenty years later, when climate change legislation was receiving serious consideration in Washington, environmental politics had changed dramatically, with Congressional support for environmental legislation coming mainly to reflect partisan divisions. In 2009, the House of Representatives passed the American Clean Energy and Security Act of 2009 (H.R. 2454) – the Waxman-Markey bill – that included an economy-wide cap-and-trade system to cut CO₂ emissions. The Waxman-Markey bill passed the House by a narrow margin of 219-212, with support from 83% of Democrats, but only 4% of Republicans. In July 2010, the Senate abandoned its attempt to pass companion legislation. In the process of debating this legislation, conservatives (largely Republicans and some coal-state Democrats) attacked the cap-and-trade system as “cap-and-tax,” much as an earlier generation of liberals had denigrated cap-and-trade as “selling licenses to pollute.”

It may be that some conservatives in Congress opposed climate policies because of disagreement about the threat of climate change or the costs of the policies, but instead of debating those risks and costs, they chose to launch an ultimately successful campaign to demonize and thereby tarnish cap-and-trade as an instrument of public policy, rendering it “collateral damage” in the wider climate policy battle.

Today that “scorched-earth” approach may have come back to haunt conservatives. Have they now boxed themselves into a corner, unable to support the power of the marketplace to reduce their own states’ compliance costs under the new EPA CO₂ regulation? I hope not, but only time will tell.

Can There Be a Positive Prognosis for Climate Negotiations?

I’m writing this brief essay on board my flight to the USA from Europe (where I participated in a workshop at the Center for European Economic Research (ZEW) in Mannheim, Germany). It was an interesting event, the substance of which (the “energy-efficiency paradox”) I will write about in the future, but today’s post is stimulated by a news article I read on board my flight, titled, “U.S. and China May Find Agreements Outside Stymied Climate Talks.”

Bad News from Bonn

In Bonn this past week, international negotiations continued under the United Nations Framework Convention on Climate Change (UNFCCC). The two most important countries in terms of greenhouse gas (GHG) emissions – China and the United States – apparently engaged in a war of words on the fundamental question of who should do what. In particular, these two giants – and their respective allies in the developed and developing worlds – bickered over their very different interpretations of the Durban Platform for Enhanced Action’s call for an agreement to be reached in Paris in 2015 that is “applicable to all Parties” (countries).

The United States and other industrialized countries have insisted that this calls for an agreement with emissions reduction pledges by all countries (in particular, by the industrialized countries plus the large emerging economies of China, India, Brazil, Korea, Mexico, and South Africa). But China, India, and most countries in the developing world have maintained that because the Durban Platform was adopted under the auspices of the UNFCCC, it calls only for emission reduction commitments by the industrialized countries. In previous essays at this blog, I’ve written about the potential promise that the Durban Platform can offer for a departure from the paralysis that has characterized the past 15 years under the Kyoto Protocol with its dichotomous distinction between emissions-reductions commitments for industrialized (Annex I) countries and no such commitments for other nations. But it is difficult to claim that the rhetoric in Bonn has been encouraging in that regard.

Better News from Beijing and Washington

At the same time, U.S. government officials back in Washington were quoted in the news article I read on board my flight as saying that bilateral negotiations with China – possibly outside of the UNFCCC – are where real progress is most likely to be made. This caught my eye, because it may be the major – and perhaps only — cause for (cautious) optimism regarding the path ahead. I wrote about this reality shortly after the UNFCCC negotiations concluded in Warsaw, Poland, in November, 2013, and recent developments merit returning to it today. My premise is what I perceive to be the potential emerging convergence of interests between these two most important countries in the world when it comes to climate change and international policy to address it – China and the United States. Five factors stand out: emissions, historical responsibility, fuel sources, policy approaches, and geopolitics.

Emissions

First, the annual carbon dioxide (CO₂) and greenhouse gas (GHG) emissions of these two countries have already converged. Whereas U.S. CO₂ emissions in 1990 were almost twice the level of Chinese emissions, by 2006 China had overtaken the United States. We are the world’s two largest emitters.

Historical Responsibility

Second, cumulative emissions are particularly important, because it is the accumulated stock of GHGs in the atmosphere that cause climate change. Any discussion of distributional equity in the climate realm therefore inevitably turns to considerations of historic responsibility. Looking at the period 1850-2010, the United States led the pack, accounting for nearly 19% of cumulative global emissions of GHGs, with the European Union in second place with 17%, and China third, accounting for about 12% of global cumulative emissions. But that picture is rapidly changing, because emissions are flat to declining throughout the industrialized world, but increasingly rapidly in the large emerging economies, in particular, China. Depending upon the relative rates of economic growth of China and the United States, as well as other factors, China may top all countries in cumulative emissions within 10 to 20 years.

Fuel Sources

Third, China and the United States both have historically high reliance on coal for generating electricity. At a time at which U.S. dependence on coal is decreasing (due to increased supplies of unconventional natural gas and hence lower gas prices ), China continues to rely on coal, but is very concerned about this, partly because of localized health impacts of particulates and other pollutants. Importantly, both countries have very large shale gas reserves. U.S. output (and use for electricity generation) has been increasing rapidly, bringing down CO₂ emissions, whereas Chinese exploitation and output have been constrained by available infrastructure (that is, lack of pipelines, but that will change).

Policy Approaches

Fourth, in both countries, sub-national market-based climate policies – in particular, cap-and-trade systems – are moving forward. In the case of the China, seven pilot CO₂ cap-and-trade regimes at the local level are under development, while in the United States, California’s ambitious AB-32 cap-and-trade system continues to make progress, and in the northeast, the Regional Greenhouse Gas Initiative (RGGI) is witnessing higher allowance auction prices due to the more severe targets the RGGI states recently adopted.

Geopolitics

Fifth and finally, there is the reality of global geopolitics. If the twentieth century was the American Century, then many observers, including leaders in China, anticipate (or at least hope) that the twenty-first century will be the Chinese Century. In this regard, I’m reminded that I was quoted by David Jolly in the New York Times, as saying, “If it’s your century, you don’t obstruct, you lead.”