Marketbased strategies Cap trade brainpickings org Marketbased strategies

Market-based strategies: Cap & trade brainpickings. org

Market-based strategies: Cap & trade Known by many names: marketable/tradable/transferable + permit/right/allowance/quota Generically: “marketable permit”, “tradable permit system” • Pollution: “tradable emissions allowances”, “transferable discharge permit” • Development: “transferable development right” • Fishing: “individual transferable quota” brainpickings. org

Instrument taxonomy

Transferable discharge permit system (TDP) • The most frequently employed market-based environmental instruments in the United States (Stavins, 1998)

The goal of C&T is to costeffectively control the aggregate level of activity (pollution, resource use) by letting agents sort out who most values permit use. Key regulator design decisions – scope: who’s regulated – cap: quantity of permits – initial allocation of permits Regulator allocates permits & sets up a market for permit trade between agents who decide how many permits to use how many they need to buy/sell.

How TDP works – “simple” example • 2 emitters (A, B) • What is the level of total unregulated emissions? • Suppose: – policy goal: 50% overall cut – allocation rule: proportional to pre-existing emissions. – A: 0. 5*120 = 60 permits – B: 0. 5*90 = 45 permits • Under the initial allocation, is the equimarginal principle satisfied? • Who would have an incentive to buy permits? Sell permits? (Think marginally!) • Note: A is the lower cost abater, B is the higher cost abater Are there gains to be had from trade? • The last unit abated by B cost ~ $4 K • B would be WTP <= ~$4 K to avoid abating that last unit • The next unit abated by A would cost ~$1. 2 K • A would be WTA >= ~$1. 2 K to abate another unit freeing up a permit for B to use

How TDP works – “simple” example From the initial allocation, A (LCA) reduces emissions by one unit to free up a permit to sell to B (HCA). E. M. P. satisfied? If no, repeat…. s n i a de g ll tra i t s m fro

How TDP works – “simple” example • 2 emitters (A, B) • What is the level of total unregulated emissions? • Suppose: – policy goal: 50% overall cut – allocation rule: proportional to pre-existing emissions. – A: 0. 5*120 = 60 permits – B: 0. 5*90 = 45 permits • At the predicted equilibrium of the permit market between these two: • Is the equimarginal principle satisfied? Why should we care? • After trading, has the total quantity of emissions changed?

2006: a California law known as AB 32 set a goal of reducing GHG emissions to 1990 levels (427 MMT CO 2 e) by 2020. n 2 6 = 1 10 x 5 3 /37. rso e p / MT 450 (NRDC, 2013)

Later: executive orders by the CA governor & an additional bill have set additional goals: 2020: 0% below 1990 (AB 32) 2030: 40% below 1990 (first by Exec Order then permanently in SB 32 [2016]) 2050: 80% below 1990 (climatepolicyinitiative. org)

Non-C&T based, complementary measures to reduce GHGs are led by (1) clean cars, (2) RPS, and (3) LCFS. (Clean Car Stds)

Most of the abatement to reach the 2020 target (1990 levels) is achieved by “complementary measures” outside of C&T. abatement comp. meas. cap abatement & tr. 2020 goal: 427 MMT (Burtraw, 2012)

California’s C&T policy recently (2015) completed planned expansion to cover trans. /nat. gas http: //calcarbondash. org/

California’s C&T policy: prices have settled at about $15/tonne http: //calcarbondash. org/

“Meager auction results in May and August 2016 had people fretting that the cap-and-trade program was failing; but buying was vigorous through most of 2017. (LAO)” LA Times (2018)

Carbon offsets • Carbon offsets: a tradable credit for reducing carbon emissions by some amount (e. g. ton) generated outside a regulated system, recognized within a regulated system (e. g. a cap -and-trade regime) as a substitute for holding and using an emissions permit. "Regulatory" offset. – "Retail offset": An offset marketed to individual consumers. Possibly but not necessarily recognized by any institutional authority.

Retail offset:

Attributes for carbon offset effectiveness Offset issues: is the offset… • Real: has the unit of emissions actually been avoided and not just claimed? • Additional: was the unit avoided due to the offset policy or would it have been avoided regardless of the offset mechanism? (Was this criteria satisfied in the “Cheat Neutral” ‘example’? ) • Permanent: is the unit avoided permanently or only temporarily (e. g. will a planted tree just be burned in 10 years)? • Verifiable: can we ensure that each attribute above is actually attained so that stakeholders in the over-arching climate policy can ensure that the policy is not being undermined?

Some markets are unequivocally unacceptable.

“Cheat Neutral”

“Cheat Neutral” • 0: 18 - 2: 40 – Q: "Have you ever cheated on your girlfriend? " A: "…No, certainly not. Cause that would be wrong. " – “…The total levels of heartbreak have not gone up. “ • 3: 25 - 5: 12 – ". . . cheating and jealousy are just a natural part of most modern relationships, and what we needed was a market-based solution to dealing with that. " – Q: "Does that make sense? " A: “…No. " – "What we're making sure is that the total amount of cheating doesn't go up. So if you want to cheat it's no longer something you have to feel bad about…" – Offset price: $5. – "All we're doing is taking this well-established concept of carbon offsetting and moving it into the arena of cheating and relationships. "

Agreement with moral precepts: Where should the limit be on the use of markets? • Costello et al (2012): “A market approach to saving the whales”. – Are individual tradable quotas a way forward from the current impasse in controlling international take of whales? • Sandel (1997): “It’s Immoral to Buy the Right to Pollute” – What do we lose when we commodify the environment?

Criteria for policy evaluation: Efficiency vs. Moral precepts "A tax on child pornography, for example, might be more efficient than certain criminal penalties in limiting the prevalence and severity of such activity; however, taxation would be considered a morally unacceptable policy in this instance because laws are important instruments forming and communicating ethical values” (Sterner, 2003, p. 198).

Cost effectiveness comparison over alternative instruments

“Myth of market solutions” • Another myth about how economists see the environment: “economists always recommend a market solution to a market problem. ” (Fullerton and Stavins, 1998) – Economists do tend to “search for instruments of public policy that can fix one market, essentially by introducing another (market)” (e. g. marketable permits, tax) … “allowing each to operate efficiently on its own” – However, the market fix is only efficient if there are no market failures associated with the market-based policy itself • Sale of permits in a cap & trade market monopolized by a small number of buyers/sellers • Inadequate information or high transactions costs? (e. g. costly to measure emissions? )

Results from congestion externality lab

Lab Section 1 Lab Section 3 Lab Section 2 Lab Section 4

Compare Agg. NB Between Treatments • Section 1 – Aggregate NB without entry fee: 1. 60 person, per round – Aggregate NB with entry fee: 3. 56 person, per round • Section 2 – Aggregate NB without entry fee: 1. 58 person, per round – Aggregate NB with entry fee: 2. 08 person, per round • Section 3 – Aggregate NB without entry fee: 2. 28 person, per round – Aggregate NB with entry fee: 3. 64 person, per round • Section 4 – Aggregate NB without entry fee: 1. 75 person, per round – Aggregate NB with entry fee: 3. 76 person, per round

Optional additional slides

State and regional programs (Hahn, 2000)

Example: SO 2 tradable emissions allowance market The problem: • 1980 s: scientists discovered that lakes, streams, and forests - even buildings and statues - were being damaged by acid rain. – Effects: robs soil of nutrients, can make lakes uninhabitable for aquatic life, damages man made objects. – Congress authorized a ten-year, $570 -million study to determine the cause, and a major culprit was found: sulfur dioxide (SO 2), • air pollutant generated by power plants and other industrial facilities. From US EPA website: http: //www. epa. gov/acidrain/images/origins. gif Effect of acid rain on a forest, Jizera Mountains, Czech Republic, http: //en. wikipedia. org/wiki/Acid_rain Sources: http: //www. etei. org/case_study_1. htm, http: //www. rff. org/documents/RFF-DP-00 -38. pdf

SO 2 Allowance Market The policy response • 1990: Congress revises the Clean Air Act – A yearly cap on SO 2 emissions was established (also NOx) • Scope: Began with the largest emitters (1995) then expanded to cover all fossil-fuel electric power producers (2000) • Ratcheting: Yearly cap decreased with an ultimate target of 50% of 1980 levels by 2010 (17. 5 million tons of SO 2 were emitted in 1980). – Also instituted an emission allowance trading program • The industry is allocated a fixed number of total allowances • Firms are required to hold one allowance for each ton of sulfur dioxide they emit. • Firms are allowed to transfer allowances among facilities or to other firms or to bank them for use in future years – The Environmental Defense Fund helped to write the revision Sources: http: //www. etei. org/case_study_1. htm, http: //www. rff. org/documents/RFF-DP-00 -38. pdf

SO 2 Allowance Market SO 2 Allowances Transferred Under the Acid Rain Program Allowance Prices (1994 -2010) http: //www. epa. gov/airmarkets/progress/ Schmalensee & Stavins 2012

SO 2 Allowance Market • B = 10*C: Overall the benefits of the program are around 10 times greater than the costs – The prediction was: B = C (Portney 1990) • Compliance cost: one-half or less of what was anticipated in 1990 (Burtraw, 2000) – Some savings from trading – Primary source of savings: flexibility in choosing abatement strategy in the firm (Hahn, 2000) • Fuel switching (e. g. low-sulfur coal made cheaper through railroad deregulation), • Innovation -- Not typically patentable discoveries, but rather subtle process changes and changes in markets and organizational behavior • Most of the estimated benefits have come through reduced risk of premature mortality by reducing exposure to sulfates (Burtraw, 2000)

SO 2 market surprises • put in place to curb acid rain, but main source of benefits from it was unexpected • main source of cost-effectiveness was an unanticipated consequence of earlier railroad deregulation • cap-and-trade now demonized by conservative politicians (yet, initially championed and implemented by Republicans) • court decisions and regulatory responses have led to the collapse of the SO 2 market (what the government gives, the government can take away) (Schmalensee & Stavins 2012)

Setting the level – the cap • Similar thought process to setting a performance standard or Pigovian tax (if efficiency is the goal). • The total cap is often ratcheted/reduced over time by the regulator (e. g. S 02) – Reasons: • technological improvements lower the efficient level • softens initial impact on industry (gradual adjustment to stringent ultimate target believed less costly).

Initial allocation of permits • As long as the initial allocation is fairly well dispersed (to avoid a permit trading monopoly), the resulting trading market should not be greatly affected. (Cost-effectiveness likely not affected. ) • The particular rule or formula will have distributional impacts • Example allocations – Give them away • Equal number of permits per firm – BUT firms differ in size • According to firms’ share of pre-existing emissions – BUT rewards bad actors • According to firms’ share of goods market – Sell them • Auction – Involves a transfer to government – Hybrid (give away fraction then sell remainder)

Political economy of cap and trade • C&T has emerged in the U. S. as most likely the lead instrument to control GHG emissions. WHY? • Political economic story over next slides summarized by J. Broder (2009. “From a Theory to a Consensus on Emissions” (5/16/09) New York Times). http: //www. nytimes. com/2009/05/17/us/politics/17 cap. html? _r=4&scp=1&sq=cap%20 and%20 trade&st=cse

Political economy of C&T • Previous take on C&T from many of those support C&T today: – “an industry-inspired Republican scheme to avoid the real costs of cutting air pollution. ” • The preferred approach they said (previously) was: – “strict government regulation, state-of-the-art technology and a federal tax on every ton of harmful emissions”

Political economy of C&T • Congressional history: – 1993: President Clinton “proposed a tax on all forms of energy, a plan that went down to defeat and helped take the Democratic majority in Congress down with it a year later. ” • Horse trading: – C&T is highly amenable to the “buying and selling of political support” through the permit allocation process (to industries and particular congressional districts).

Political economy of C&T • Previous success: the SO 2 model – During the Bush (Sr. ) administration a C&T plan for SO 2 reductions was outlined in the White House and sent to Congress. – This C&T plan became a critical component of the amendments to the Clean Air Act in 1990, “considered by many to be the most successful domestic environmental legislation ever enacted. ” – Even after vigorous debate in congress the target held: “roughly 50 percent reduction in emissions over the next decade”

Is a C&T system essentially equivalent to a tax? • W. David Montgomery (1971 doctoral thesis on emissions trading) – “It [a C&T approach to GHG control] is a steel fist of regulation covered by a velvet glove of emission trading…. ” – “Why not just impose a carbon tax? ”

“Companies Earn Big Profits From Free Carbon Credits”* • “During his election campaign, President Barack Obama pledged to institute a system in the United States where all permits would be auctioned. That could avoid the mind bogglingly large windfall profits made by utilities in Europe. ” • “The head of the nation’s largest burner of coal for power generation last week signaled his group’s determination to fight for a significant chunk of free allowances under any United States system, according to Reuters. ” – Michael Morris (chief executive of American Electric Power): “If you auction all of the credits, then it’s just a carbon tax, ”… “So let’s forget the game. Let’s call it a carbon tax, and let’s see if the populace wants to have a carbon tax. ” • *Source: New York Times (03/09/09): http: //greeninc. blogs. nytimes. com/2009/03/09/companies-earn-big-profits-from-freecarbon-credits/

Setting up the market for permit trade • General rule: simple and clear rules (keeps “transactions costs” low) • Single overall market for permits where buyers and sellers can interact openly and where information on prices is publicly available to all participants. • Added transactions costs will likely hurt the efficiency of the market – If trades require regulator approval, the additional bureaucracy and uncertainty will generate transactions costs. • Who is allowed to trade? – Just polluters? Third parties (e. g. private citizens, NRDC) who’d like to buy/retire permits?

Setting up the market for permit trade • Normal forces of competition would bring about a single price • Permits would tend to flow LAC HAC polluters • LAC: Low abatement cost polluters would be those with better preexisting technologies AND/OR those who have invested in better abatement technologies. • Our equilibrium prediction is that MACA = MACB = p* What is the predicted MAC of each firm after trade? Supply: LAC polluters or firms leaving the business Demand: HAC polluters, expanding firms, or new firms

TDP and Incentives for R&D Under performance standard at e 1 • What is the incentive to innovate (to MAC 2)? Model for an individual firm: Under a TDP system, with market permit price p • Suppose initial allocation of permits is A=0 (firm must buy all permits it needs on the open permit market) • What is level of abatement? Permits required? (Under MAC 1? MAC 2 ? ) • What is the total cost of compliance (TCC) for the firm including total abatement cost (TAC) and total permit cost (TPC)? TCC = TAC + TPC • What is the incentive to innovate? • How does the incentive to innovate under TDP compare to that under emissions charges (at least in theory)? -------------------------------- • Alternatively, suppose that A = e 1. Does the abatement level change? Does the TCC go up or down? Does the incentive to innovate change? Note: when many firms are involved, we will assume that each firm treats the permit price as fixed, i. e. their own buying and selling of permits is too minor to affect the market permit price. This is different then the simple 2 firm example previously discussed.