|The Cost Containment Mechanisms in the California Cap-and-Trade Program – why absent in the EUETS?|
|Thursday, 17 February 2011 16:40|
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In the European cap-and-trade the cap is established on the volume of allowances and, unfortunately, not on the price. But as the experience shows there are interesting concepts, how to mitigate not only the impact of climate change, but also the price risks inherent in the scheme. Direct quarterly sales of allowances from the Allowance Price Containment Reserve and the fixed Auction Reserve Price cause (providing that the Reserve won’t be prematurely exhausted) that in the California cap-and-trade the regulatory-fixed price range from 10$ to 75$ per metric ton of CO2 can be specified in the perspective 2012 – 2020 (with appropriate modifications in each year of the period).
The California Cap-and-Trade Program (see: California Environmental Protection Agency Proposed Regulation to Implement the California Cap-and-Trade Program PART I Volume I Staff Report: Initial Statement of Reasons, Release Date: October 28, 2010,
http://www.arb.ca.gov/cc/capandtrade/capandtrade.htm, last visited 10.02.2011) scheduled to start in 2012 envisages pivotal cost containment mechanisms. Some of them are similar, or equivalent to those present in the EUETS, but others seem to be original in their design.
The fundamental feature of the European Union Emissions Trading Scheme relative to management of price risk as regards allowances follows from Article 16(3) and (4) of the Directive 2003/87 and consists in that any operator who does not surrender sufficient allowances by 30 April of each year to cover its emissions during the preceding year shall be held liable for the payment of an excess emissions penalty which amounts to EUR 100 for each tonne of carbon dioxide equivalent emitted for which the operator or aircraft operator has not surrendered allowances. The pivotal element is that the payment of the excess emissions penalty shall not release the operator from the obligation to surrender an amount of allowances equal to those excess emissions when surrendering allowances in relation to the following calendar year (the excess emissions penalty relating to allowances issued from 1 January 2013 onwards shall increase in accordance with the European index of consumer prices). Consequently, the amount of 100 EUR is not a cap on the price of EUAs in the EUETS and theoretically, the possibility of price movement of EUAs beyond 100 EUR is not excluded. This uncertainty influences on the investments decisions with respect to the choice of the fuel for the future power plants and seems to be the one of the main reasons, why the share of renewables in the European electricity production sources have risen recently so sharply, and the planned coal – fired power plants face big difficulties in the drafting of business plans.
The Directive 2003/87 provides for some mechanisms in the event of excessive price fluctuations of allowances (see: box), but these provisions are intended to increase the quantity of allowances available on the market (and in this way indirectly influence on the price) rather than directly put restrictions on free price discovery by the market itself.
Cost Containment Mechanisms in the California Cap-and-Trade Program
The specification of the compliance periods does not seem extremely original, taking into account that the EUETS as well as the Kyoto Protocol used such a concept. The differences in the length of the specific compliance periods (EUETS: first - 3 years, second (convergent with Kyoto Protocol) - 5 years, third – 8 years, California cap-and-trade: 3 years, first starting in 2012) are of minor importance. There are however differences in the proportion of emissions against which allowances must be surrendered in each year of the compliance period (annual compliance obligation consists in that a covered entity is be required to surrender compliance instruments in each of the first two years of a compliance period equal to 30 percent of its verified emissions for that year. For a covered entity that reports emissions in April, the proposed surrender will be due by May 15 of the same year. For a covered entity that reports in June, the surrender will be due by July 15 of the same year). Comparing these provisions to that in the EUETS, the differences are visible in timing (30 April as a uniform surrendering date for every compliance unit in the EUETS) and the volume of yearly settlement (100% in the EUETS against 30% in California cap-and-trade).
According to the staff of the ARB three-year compliance cycle is to help smooth out annual variations in production, and to provide sources with greater flexibility to reduce emissions.
Equally similar to EUETS are the provisions on banking of allowances (which allows participants to hold spare allowances and use them for compliance in a later period), staff of the Californian ARB proposes to allow banking of allowances without restriction.
As a result, California compliance instruments do not expire. This allows an entity to hold the instrument until it is needed - across compliance periods. In the EUETS banking was not allowed as regards transition from the first compliance period (2005-2007) to the second (2008-2012), because the first compliance period had a “trial” character.
Contrary to the European Union Emissions Trading Scheme allowances issued in the California cap-and-trade for a future year cannot be used for surrender in an earlier compliance period (borrowing). The one exception is an allowance purchased from the Allowance Price Containment Reserve, which may be used as soon as it is bought. According to the staff of ARB, this approach is proposed to prevent the threat of “cascading borrowing.” This situation occurs when entities are able to use future allowances for current compliance, and it creates a growing shortage of instruments in later compliance periods.
In the EUETS allowances issued, for instance, in the year 2011 (in February 2011) may be used for surrendering as regards CO2 emitted into the atmosphere in 2010 (with the settlement date 30 April 2011). In the EUETS it can really lead to the cascading borrowing with the “point of truth” on 30 April 2013 (final settlement date for the entire second period).
California cap-and-trade envisages specific provisions on offset credits (which in themselves are instrument of providing necessary price elasticity). In the Californian model provisions on offsets are different from EUETS, it is sufficient to mention, that only American projects seem to be eligible to participate (apart from many other differences in the design), in this article the intention is only to mention this issue.
California cap-and-trade seems to be strongly designed to link in the near future with WCI (Western Climate Initiative) partner jurisdictions. In this article I mention the linkage to other greenhouse gas emissions trading systems as an instrument of providing the price elasticity, but the issue is generally worth of separate considerations.
Direct Quarterly Sales of Allowances from the Allowance Price Containment Reserve
Pursuant to the above-cited Initial Statement of Reasons the Reserve is an account that is filled with a specified number of allowances removed from the overall cap at the beginning of the program. Covered entities may purchase reserve allowances at specified prices during direct quarterly sales. Covered entities gain flexibility through access to the Reserve if prices are high or entities expect prices to be high in the future. Staff proposes that the Reserve be filled with 123.5 million allowances out of the total of approximately 2.7 billion issued for the years 2012 to 2020. A greater percentage of allowances come from later years of the program to provide more flexibility in the early years of the program. The Reserve will be filled with 1 percent of allowances from each year from 2012 through 2014, 4 percent of allowances from each year from 2015 through 2017, and 7 percent of allowances from each year from 2018 through 2020. This is equal to approximately 5 percent of total allowances in the program from 2012 through 2020.
Covered entities will have the option of buying from the reserve pool at fixed prices. The reserve allowances will not be available to voluntarily associated entities. Sales from the Reserve will take place three weeks after each quarterly auction. The Reserve will be organized into three equal tiers. Allowances in each tier will be available for purchase at fixed prices. Reserve allowances will be sold at prices of $40/metric ton for the first tier, $45/metric ton for the second tier, and $50/metric ton for the third tier in 2012. These prices will escalate by 5 percent plus the cost of inflation each year, such that the reserve prices are approximately $60/ metric ton, $67/ metric ton, and $75/ metric ton in 2020.
Covered entities will place bids for the number of allowances they wish to buy from each tier. The Reserve administrator will award allowances from each tier until the tier is exhausted. Empty tiers will not be refilled. If too many bids are submitted for a tier, the Reserve administrator will prorate the available allowances to the bidders.
Purchases from the Reserve will be subject to the Holding Limit (further mentioned). In addition, allowances purchased from the Reserve will be transferred by the administrator directly to the purchasing entity’s Compliance Account, from which it cannot be removed until it is surrendered. It is to ensure that allowances are only purchased to meet compliance needs, not to provide a supply of allowances for speculative activity.
The mechanisms similar to those as the Reserve are absent in the European Union Emissions Trading Scheme. There is New Entrant Reserve but it has different purpose. The European legislators intended probably that the market should be the one that discovers the price for CO2 allowances and that market forces shouldn’t be restricted in that process (excepting provisions of Article 29a of the Directive 2002/87 mentioned at the beginning).
But it seems that providing a little certainty with respect to the price risk in the EUETS would have a positive impact on the EU economy as a whole. Providing, that the Reserve won’t be prematurely exhausted, in the California cap-and-trade there is specified price range from 10$ to $75 per metric ton of CO2 in the perspective 2012 – 2020 (with appropriate modifications in each year of the period) and this regulatory specification is of important value in every investment projections. Unfortunately, in the EUETS even such general price range can’t be construed taking into account the text of law only.
|Last Updated on Saturday, 04 August 2012 15:30|