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The Warsaw Climate Negotiations, and Reason for Cautious Optimism

The Nineteenth Conference of the Parties (COP-19) of the United Nations Framework Convention on Climate Change (UNFCCC) came to a close in Warsaw, Poland, on Saturday, November 23^rd, after what has become the norm – several all-night sessions culminating in last-minute negotiations that featured diplomatic haggling over subtle changes to the text on which countries were finally willing to agree. The key task of this COP was essentially to pave the way for the negotiations next year at COP-20 in Lima, Peru, as a lead-up to the real target, reaching a new international climate agreement at the 2015 negotiations in Paris to be implemented in 2020, when the second commitment period of the Kyoto Protocol comes to an end. If that was the key objective, then the Warsaw meetings must be judged to be at least a modest success – the baton was not dropped, rather it was passed successfully in this long relay race of negotiations.

Before going further, I would like to acknowledge something else about COP-19 in Warsaw, namely the excellent logistics. Anyone who suffered through the disastrous logistical arrangements for COP-15 in Copenhagen will not take this for granted. Perhaps ironically, in the years I’ve been participating in these annual events, the two best organized conferences (in terms of logistical arrangements) were the two Polish COPs – COP-14 in Poznan in 2008 and COP-19 in Warsaw this year.

As I have written in many previous essays at this blog, the challenges standing in the way of an effective international climate change agreement are numerous and severe. A brief historical account is necessary to explain the significance of what transpired in Warsaw. However, if you’re familiar with international climate policy, particularly the history of these international negotiations, I suggest you skip the next section and move directly to “Issue #1: Making Progress toward a Post-Kyoto Agreement.”

Some Historical Background to Place the Warsaw Talks in Context: the UNFCCC, the Berlin Mandate, the Kyoto Protocol, and the Durban Platform

The U.N. Framework Convention on Climate Change, adopted at the U.N. Conference on Environment and Development (the first “Earth Summit”) in Rio de Janeiro, Brazil, in 1992, contains what was to become a crucial passage: “The Parties should protect the climate system for the benefit of present and future generations of humankind, on the basis of equity and in accordance with their common but differentiated responsibilities and respective capabilities. Accordingly, the developed country Parties should take the lead in combating climate change and the adverse effects thereof.” [emphasis added] The countries considered to be “developed country Parties” were listed in an appendix to the 1992 Convention – Annex I.

The phrase – common but differentiated responsibilities – was given a specific interpretation three years after the Earth Summit by the first decision adopted by the first Conference of the Parties (COP-1) of the U.N. Framework Convention, in Berlin, Germany, April 7, 1995 – the all important Berlin Mandate, which interpreted the principle as: (1) launching a process to commit (by 1997) the Annex I countries to quantified greenhouse gas emissions reductions within specified time periods (targets and timetables); and (2) stating unambiguously that the process should “not introduce any new commitments for Parties not included in Annex I.”

Thus, the Berlin Mandate established the dichotomous distinction whereby the Annex I countries were to take on emissions-reductions responsibilities, and the non-Annex I countries were to have no such responsibilities whatsoever. This had wide-ranging and profound consequences, because it became the anchor that prevented real progress in international climate negotiations. With 50 non-Annex I countries coming to have greater per capita income than the poorest of the Annex I countries, the distinction was out of whack within a few years.

But, more important than that, this dichotomous distinction meant that: (a) half of global emissions would be from nations without constraints; (b) the world’s largest emitter – China – would be unconstrained; (c) aggregate compliance costs would be driven up to be four times their cost-effective level, because many opportunities for low-cost emissions abatement in emerging economies were taken off the table; and (d) an institutional structure was perpetuated that made change and progress virtually impossible.

The dichotomous Annex I/non-Annex I distinction remained a central – indeed, the central – feature of international climate negotiations from COP-1 in Berlin in 1995 continuously until COP-15 in 2009, when hints of possible change first appeared. The Copenhagen Accord (2009) and the Cancun Agreements (2010) began a process of blurring the Annex I/non-Annex I distinction. But this blurring was only in the context of the interim pledge-and-review system established at COP-15 in Copenhagen and certified at COP-16 in Cancun, not in the context of an eventual successor to the Kyoto Protocol. Thus, the Berlin Mandate retained its centrality.

Then, in December, 2011, at COP-17 in Durban, South Africa, the Durban Platform for Enhanced Action was adopted. Under some interpretations, it essentially eliminates the Annex I/non-Annex I (or industrialized/developing country) distinction. In the Durban Platform, the delegates decided to reach an agreement by 2015 that will be applicable to all countries by 2020.

Rather than adopting the Annex I/non-Annex I (or industrialized/developing country) distinction, the Durban Platform focuses instead on the pledge to create a system of greenhouse gas reductions including all Parties (what matters, really, is all key countries) by 2015 that will come into force by 2020. Nowhere in the text of the decision were phrases such as “Annex I,” “common but differentiated responsibilities,” “distributional equity,” “historical responsibility,” all of which had long since become code words for targets for the richest countries and blank checks for all others.

By replacing the Berlin Mandate, the Durban Platform opened an important window. National delegations from around the world took on the challenging task to identify a new international climate policy architecture that is consistent with the process, pathway, and principles laid out in the Durban Platform, namely to find a way to include all (key) countries (such as the 20 largest national and regional economies that together account for upwards of 80% of global carbon dioxide emissions) in a structure that brings about meaningful emissions reductions within an appropriate timetable at acceptable cost, while remaining within the overall framework provided by the UNFCCC, including the celebrated principle of common but differentiated responsibilities.

Issue #1: Making Progress toward a Post-Kyoto Agreement

In Warsaw, the negotiators were tasked under the Durban Platform track (the so-called “ADP” track) to develop a work plan of substantive topics and a related calendar that will lead to the development of the text of an agreement of a new comprehensive policy architecture that can be discussed at COP-20 in Lima one year from now and then subject to final consideration and adoption a year after that at COP-21 in Paris. This they did, and in the process they identified six components for the new architecture: mitigation, adaptation, finance, technology development and transfer, capacity-building, and transparency of action and support. Some of these are more necessary than others, but it was this package that generated agreement in Warsaw.

The actual agreement in Warsaw could only be achieved through carefully negotiated text. The delegates’ obligation is to eventually adopt “a protocol, another legal instrument or an agreed outcome with legal force under the Convention applicable to all Parties…” In truth, the phrase “under the Convention” is not necessary, because any decision by the UNFCCC is under the Convention, and therefore it is the case that any agreement produced under the Durban Platform is still subject to the UNFCCC principle of “common but differentiated responsibilities.” But the large emerging economies tend to view the phrase “under the Convention” as supporting the dichotomous distinction of, on the one hand, commitments for Annex I (industrialized) countries to reduce emissions, and, on the other hand, no obligations for non-Annex I (developing) countries, who would take actions only voluntarily and only with financial assistance from the Annex I countries. The same set of large emerging economies insisted that if they were to be included in the agreement, then the word “commitments” must be replaced by “contributions.”

It is looking increasingly likely that the 2015 agreement will take the form of a hybrid architecture, combining: (1) a bottom-up system of national commitments (sorry, national contributions) that arise from – or are at least consistent with – national policies and goals; plus (2) top-down, centralized management of oversight, guidance, and coordination, with an eye to increasing ambition over time. At the Harvard Project on Climate Agreements, we outlined such a hybrid international climate policy architecture four years ago (“A Portfolio of Domestic Commitments: Implementing Common but Differentiated Responsibilities”), and we explored it further just last month in a new report (“Identifying Options for a New International Climate Regime Arising from the Durban Platform for Enhanced Action”). In Warsaw, we co-hosted and participated in two sessions that explored these ideas in considerable detail (you can learn more about that here; we will soon place all of the slide decks from those sessions at the Harvard Project web site).

Issue #2: Loss and Damage

As I predicted at the conclusion of last year’s climate negotiations (COP-18) in Doha, Qatar, the issue that held the greatest potential for blowing up this year’s talks in Warsaw was the topic of “loss and damage,” which the delegates agreed to put on the agenda for discussion this year at COP-19. The phrase “loss and damage” is typically understood to refer to the range of damages and loss associated with climate change impacts in developing countries that are particularly vulnerable to the adverse effects of climate change. Discussions about potential international policy in this realm frequently bring up thoughts about who should pay for such loss and damages, presumably those most responsible for climate change.

Since climate change is a function not of current emissions, but of concentrations, responsibility for damages is presumably correlated with cumulative emissions. Hence, the industrialized countries, in particular, the United States, worry that negotiations on “loss and damage” would soon raise the specter of unlimited legal liability.

The link is less direct than one might think, however. First, there is the global commons nature of the problem, meaning that climate change cannot be linked to emissions from a specific country. Second, there is the highly stochastic link from climate change to changes in weather patterns, so that no specific weather incident – whether Superstorm Sandy in New York, Hurricane Katrina in New Orleans, or Typhoon Haiyan in the Philippines – can be deterministically linked with global climate change. These two scientific realities mean that moving from “loss and damage” to legal liability would be a long and perilous road.

But this is a very important issue in the climate negotiations for many developing countries, in particular, for the small island states that are most at risk. Hence, it should not be surprising that this area of discussion – in some ways only a sideshow of the primary talks on reducing emissions and the risk of climate change – almost caused the talks to collapse.

In the end, the delegates agreed to finesse the topic by creating the Warsaw International Mechanism for Loss and Damage, which does not mention liability or promise compensation, but rather states that this is a topic to be discussed further at future meetings, and under the general topic of adaptation to climate change.

Issue #3: Finance

Those are two – the Durban Platform, and Loss and Damage – of three major issues that were considered in Warsaw. The third was “finance,” that is, the question of when and how the industrialized countries will meet the commitment they made at COP-15 in Copenhagen in 2009 to begin delivering $100 billion per year of financial assistance to developing countries in 2020 to help with mitigation and adaptation. Not surprisingly, there was little or no progress on that front. More about this in a future essay. For now ….

The Path Ahead – Any Reason for Optimism?

Given my description above of the debates and “resolution” regarding the major issues, is there any cause for optimism regarding the path ahead. Regular readers of this blog will know that I tend to see the half-full glass (or one-tenth full glass) of water, and in this case I think there really is cause for cautious optimism regarding the path ahead.

This is based upon a singular reality – the growing convergence of interests between the two most important countries in the world when it comes to climate change and international policy to address it, namely, China and the United States.

First of all, 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.

Second, as I explained above, cumulative emissions are particularly important, because they are what cause climate change. Any discussion of distributional equity in the climate realm 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 is changing rapidly, because of the fact that 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 many other factors, China may top all countries in cumulative emissions within 10 to 20 years from now.

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 has been constrained by available infrastructure (i.e., lack of pipelines, but that will change).

Fourth, in both countries, sub-national climate policies – 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.

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 hope) that the twenty-first century will be the Chinese Century. And, as I was quoted by David Jolly in the New York Times as saying, “If it’s your century, you don’t obstruct, you lead.”

Conclusion

There was no fundamental setback in Warsaw to the stream of work that needs to be accomplished in Lima in 2014 in preparation for an agreement to be reached in Paris in 2015 under the Durban Platform for Enhanced Action. This, combined with the reality of increasing convergence of Chinese and U.S. perspectives and interests, leaves me cautiously optimistic (or perhaps, just hopeful) about the path ahead.

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You can view and listen to an assessment of the Warsaw negotiations in a discussion in which I participated on the PBS NewsHour on November 27^th, moderated by Judy Woodruff.

For other summaries and analyses of Warsaw’s COP-19 climate conference, I recommend:

Carraro, Carlo. “COP19: Between Weak Commitments and Tiny Successes.” International Center for Climate Governance. November 27, 2013.

Center for Climate and Energy Solutions. “Outcomes of the U.N. Climate Change Conference in Warsaw.” November, 2013.

Stowe, Robert. “COP-19: Different Strokes?”The Energy Collective, November 27, 2013.

Climate Change, Public Policy, and the University

Over the past year or more, across the United States, there has been a groundswell of student activism pressing colleges and universities to divest their holdings in fossil fuel companies from their investment portfolios. On October 3, 2013, after many months of assessment, discussion, and debate, the President of Harvard University, Drew Faust, issued a long, well-reasoned, and – in my view – ultimately sensible statement on “fossil fuel divestment,” in which she explained why she and the Corporation (Harvard’s governing board) do not believe that “university divestment from the fossil fuel industry is warranted or wise.” I urge you to read her statement, and decide for yourself how compelling you find it, and whether and how it may apply to your institution, as well.

About 10 days later, two leaders of the student movement at Harvard responded to President Faust in The Nation. Andrew Revkin, writing at the New York Times Dot Earth blog, highlighted the fact that the students responded in part by saying, “We do not expect divestment to have a financial impact on fossil fuel companies … Divestment is a moral and political strategy to expose the reckless business model of the fossil fuel industry that puts our world at risk.”

I agree with these students that fossil-fuel divestment by the University would not have financial impacts on the industry, and I also agree with their implication that it would be (potentially) of symbolic value only. However, it is precisely because of this that I believe President Faust made the right decision. Let me explain.

The Value of Symbolic Action

If divestment would at best be a symbolic action, without meritorious direct financial impacts, can it not nevertheless be important and of great value? More broadly, can’t symbolic actions be valuable?

One major problem is that symbolic actions often substitute for truly effective actions by allowing us to fool ourselves into thinking we are doing something meaningful about a problem when we are not.

But even if there are such opportunity costs of symbolic actions, can they not still be merited as part of moral crusades (as the students would presumably argue)? The answer is, in my view, yes. The problem, however, is that climate change is fundamentally a scientific, economic, and political challenge. Viewing it as a moral crusade, I fear, will only play into and exacerbate the terrible political polarization that is already paralyzing Washington, a topic about which I have written previously at this blog.

The Climate Impacts of Divestment

Divestment of fossil fuel stocks would hurt, not help efforts to address global climate change. First, natural gas is the crucial transition fuel to address climate change. A major reason for the drop in U.S. CO₂ emissions is the increased use of natural gas to generate electricity, as documented in this recent report from the U.S. Energy Information Administration.

Second, even if divestment were to reduce the financial resources of coal, oil, and gas companies (which it would not do), this would only serve to reduce research and development at those same companies of carbon capture and storage (CCS) technologies, as well as other potential technological breakthroughs; and could reduce the development of some renewable sources of energy (which the fossil fuel companies are carrying out as part of their financially rational diversification strategies).

The University’s Comparative Advantage

Most important, as I have argued for years, Harvard’s real contributions to fight climate change and promote sound climate change policies will be through our products: research, teaching, and outreach. That is how this great university has made a difference on other societal challenges for decades and centuries, and it is how we will make a real difference on this one.

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Three and a half years ago, I posted an essay at this blog about what I saw to be the proper role of individuals and institutions in addressing climate change. Frequently I refer to my previous blog posts, but today I’m going a step further, and reproducing that one from March, 2010, because it applies so directly to the topic at hand (including its Epilogue at the very end):

What’s the Proper Role of Individuals and Institutions in Addressing Climate Change?

Posted on March 8, 2010 by Robert Stavins

This may seem like a trivial question with an obvious answer. But what really is the proper role for individuals and institutions in addressing climate change? An immediate and natural response may be that everyone should do their part. Let’s see what that really means.

Decisions affecting carbon dioxide (CO₂) emissions, for example, are made primarily by companies and consumers. This includes decisions by companies about how to produce electricity, as well as thousands of other goods and services; and decisions by consumers regarding what to buy, how to transport themselves, and how to keep their homes warm, cool, and light.

However, despite the fact that these decisions are made by firms and individuals, government action is clearly key, because climate change is an externality, and it is rarely, if ever, in the self-interest of firms or individuals to take unilateral actions. That’s why the climate problem exists, in the first place. Voluntary initiatives – no matter how well-intended – will not only be insufficient, but insignificant relative to the magnitude of the problem.

So, the question becomes how to shift decisions by firms and individuals in a climate-friendly direction, such as toward emissions reductions. Whether conventional standards or market-based instruments are used, meaningful government regulation will be required.

But where does this leave the role and responsibility of individuals and institutions? Let me use as an example my employer, a university. A couple of years ago, I met with students advocating for a reduced “carbon foot-print” for the school. Here is what I told them.

“I was asked by a major oil company to advise on the design of an internal, voluntary tradable permit systems for CO₂ emissions. My response to the company was ‘fine, but the emissions from your production processes — largely refineries — are trivial compared with the emissions from the use of your products (combustion of fossil fuels). If you really want to do something meaningful about climate change, the focus should be on the use of your products, not your internal production process.’ (My response would have been different had they been a cement producer.) The oil company proceeded with its internal measures, which – as I anticipated – had trivial, if any impacts on the environment (and they subsequently used the existence of their voluntary program as an argument against government attempts to put in place a meaningful climate policy).”

My view of a university’s responsibilities in the environmental realm is similar. Our direct impact on the natural environment — such as in terms of CO₂ emissions from our heating plants — is absolutely trivial compared with the impacts on the environment (including climate change) of our products: knowledge produced through research, informed students produced through our teaching, and outreach to the policy world carried out by faculty.

So, I suggested to the students that if they were really concerned with how the university affects climate change, then their greatest attention should be given to priorities and performance in the realms of teaching, research, and outreach.

Of course, it is also true that work on the “greening of the university” can in some cases play a relevant role in research and teaching. And, more broadly — and more importantly — the university’s actions in regard to its “carbon footprint” can have symbolic value. And symbolic actions — even when they mean little in terms of real, direct impacts — can have effects in the larger political world. This is particularly true in the case of a prominent university, such as my own.

But, overall, my institution’s greatest opportunity — indeed, its greatest responsibility — with regard to addressing global climate change is and will be through its research, teaching, and outreach to the policy community.

Why not focus equally on reducing the university’s carbon foot-print while also working to increase and improve relevant research, teaching, and outreach? The answer brings up a phrase that will be familiar to readers of this blog – opportunity cost. Faculty, staff, and students all have limited time; indeed, as in many other professional settings, time is the scarcest of scarce resources. Giving more attention to one issue inevitably means – for some people – giving less time to another.

So my advice to the students was to advocate for more faculty appointments in the environmental realm and to press for more and better courses. After all, it was student demand at my institution that resulted in the creation of the college’s highly successful concentration (major) in environmental science and public policy.

My bottom line? Try to focus on actions that can make a real difference, as opposed to actions that may feel good or look good but have relatively little real-world impact, particularly when those feel-good/look-good actions have opportunity costs, that is, divert us from focusing on actions that would make a significant difference. Climate change is a real and pressing problem. Strong government actions will be required, as well as enlightened political leadership at the national and international levels.

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Epilogue: After I posted the above essay, I was reminded of an incident that took place many years ago (before I came to Harvard for graduate school, in fact) when I was working full-time for the Environmental Defense Fund in Berkeley, California, under the inspired leadership of the late (and truly great) Tom Graff, the long-time guru of progressive California water policy. EDF was very engaged at the time in promoting better water policies in California, including the use of trading mechanisms and appropriate pricing schemes for scarce water supplies. A prominent national newspaper which was not friendly to EDF’s work sent a reporter to EDF’s Berkeley office to profile the group’s efforts on water policy in the State. A staff member found the reporter in the office bathroom examining whether EDF had voluntarily installed various kinds of water conservation devices in its plumbing. Our reaction at the time was that whether or not EDF had voluntarily installed water conservation devices was simply and purely an (intentional) distraction from the important work the group was carrying out. After several decades, my view of that incident has not changed.

Economics and Politics in California: Cap-and-Trade Allowance Allocation and Trade Exposure

In my previous essay at this blog – The Importance of Getting it Right in California – I wrote about the precedents and lessons that California’s Global Warming Solutions Act (AB 32) and its greenhouse gas (GHG) cap-and-trade system will have for other jurisdictions around the world, including other states, provinces, countries, and regions. This is particularly important, given the failure of the U.S. Senate in 2009 to pass companion legislation to the Waxman-Markey bill, passed by the U.S. House of Representatives, highlighting the absence of a national, economy-wide carbon pricing policy.

In my previous essay, I focused on three pending design issues in the emerging rules for the AB-32 cap-and-trade system: (1) the GHG allowance reserve; (2) the role of offsets; and (3) proposals for allowance holding limits. I drew upon a presentation I made on “Offsets, Holding Limits, and Market Liquidity (and Other Factors Affecting Market Performance)” at the 2013 Summer Issues Seminar of the California Council for Environmental and Economic Balance.

At the same conference, I made another presentation, which was on “Allowance Value Distribution and Trade Exposure,” a topic that is of great importance both economically and politically, not only in the context of the design of California’s AB-32 cap-and-trade system, but for the design of any cap-and-trade instrument in any jurisdiction. It is to that topic that I turn today. (For a much more detailed discussion, please see a white paper I wrote with Dr. Todd Schatzki of Analysis Group, “Using the Value of Allowances from California’s GHG Cap-and-Trade System,” August, 2012).

Why Does Anyone Care About the Allowance Value Distribution?

A cap-and-trade policy creates a valuable new commodity – emissions allowances. In a well-functioning emissions trading market, the financial value of these allowances (per ton of emissions, for example) is approximately equivalent to their opportunity cost, which is the marginal cost of emissions reductions. This is because of the existence of the overall cap, which – if binding – fosters scarcity of available allowances, and hence generates their economic value.

It should not be surprising, then, that the initial allocation of these allowances can have important consequences both for environmental and for economic outcomes.

Environmental Consequences of the Initial Allowance Allocation

No matter how many times I meet with policy makers around the world to talk about alternative policy instruments (for climate change and other environmental problems), I never cease to be struck by the confusion that abounds regarding the environmental (and the economic) consequences of the initial allocation of allowances in a cap-and-trade system. As I have written many times in the past at this blog, the initial allocation does not directly affect environmental outcomes. Regardless of the allocation method used, aggregate emissions are limited by the emissions cap. This is true whether the allowances are sold (auctioned) or distributed without charge. Furthermore, which firms or sources receive the initial allocation of allowances has no effect on either aggregate emissions or the ultimate distribution of emissions reductions among sources.

This independence of a cap-and-trade system’s performance from the initial allowance allocation was established as far back as 1972 by David Montgomery in a path-breaking article in the Journal of Economic Theory (based upon his 1971 Harvard economics Ph.D. dissertation). It has been validated with empirical evidence repeatedly over the years. (More below about the initial allocation’s potential effects on economic performance.)

However, it is also true that the initial allocation method can indirectly affect emissions. In particular, emissions leakage can arise if economic activity shifts to unregulated sources – this risk is greatest with auctions or free fixed allocations. In contrast, an updating, output-based allocation (used in AB 32 for “industry assistance”) can reduce leakage risk by making the free allocation of allowances marginal, rather than infra-marginal (as is the case with a simple free allocation).

Economic Consequences of the Initial Allowance Allocation

A favorite topic of academic economists is that the allowance allocation method in a cap-and-trade system can affect the overall social cost of the policy if the allowances are auctioned (sold by government to compliance entities), and if the revenues are then used to reduce distortionary taxes (such as taxes on labor and investment), thereby eliminating some deadweight loss and cutting overall social cost. I discuss this a bit more below, but for now let’s recognize that the combination of two California propositions and subsequent court rulings means that the State is not permitted to use the auction proceeds to cut taxes (rather, any auction proceeds must be used to achieve the purposes of AB 32, that is, reducing GHG emissions).

So, within the set of feasible options, the initial allowance allocation will not directly affect the cost-effectiveness of actions taken by emission sources to reduce emissions. In other words, aggregate abatement costs will not be directly affected by the nature of the initial allocation.

I was careful to use the word, “directly,” because the initial allowance allocation can indirectly affect economic outcomes. In particular, the use of updating, output-based allocations can: (1) lower the costs seen by consumers, which can reduce incentives to conserve; (2) avoid reductions in economic activity within California, with associated distributional impacts; and (3) avoid potential shifts of production to less efficient, more distant producers.

Auction Revenue Use

Decisions about how auction revenues are used can have profound consequences for the potential benefits of auctioning. There are three basic options.

First, as I emphasized above, in theory, reducing distortionary taxes provides the greatest net economic benefit (by reducing the social cost of the policy). But California’s unique legal context takes this option off the table.

Second, funding programs to address other market failures that are not addressed by the price signals provided by the cap-and-trade system can be meritorious. For example, information spillovers can be addressed through financing of research and development activities, and the principal-agent problems that infect energy-efficiency adoption decisions in rental properties can be addressed — to some degree — through zoning and other local policies.

The third and final option, however, is highly problematic, if not completely without merit, and yet, ironically, there are strong incentives in place for policy makers to go this third route. This third option is to use auction revenues to fund programs to subsidize emission reductions. There is a strong incentive to do this, because of California’s legal constraint to employ any auction revenues in pursuit of the objectives of the statute, that is, reducing GHG emissions.

What’s the problem? The AB-32 cap-and-trade system will cover approximately 85% of the economy. In other words, the vast majority of sources are under the cap. As I have explained in detail in several previous essays at this blog, under the umbrella of a cap-and-trade mechanism, (successful) efforts to further reduce emissions of capped sources will have three consequences: (1) allowance prices will be supressed (take a look at the hand-wringing in Europe over allowance prices in its CO₂ Emissions Trading System); (2) aggregate compliance costs will be increased (cost-effectiveness is reduced because marginal abatement costs are no longer equated among all sources); and (3) nothing is accomplished for the environment, in the sense that there are no additional CO₂ emissions reductions (rather, the CO₂ emissions reductions are simply relocated among sources under the cap).

Economics, Policy, and Politics

As I concluded in my previous essay, the California Air Resources Board has done an impressive job in its initial design of the rules for its GHG cap-and-trade system. Of course, there are flaws, and therefore there are areas for improvement. A major issue continues to be the mechanisms used for the initial allocation of allowances. Because of the economics and politics of this issue, it will not go away. But, going forward, it would be helpful if those debating this issue could demonstrate better understanding of the allowance allocation’s real – as opposed to fictitious – environmental and economic consequences.