Difficulties and Solutions of Emissions Trading in China [Author] Shi Qinghao, associate professor of Shanghai Administration Institute [Abstract] Emissions trading is a market-based instrument used to cope with environmental issues, especially the market failure of externality. In implementing emissions trading, there are difficulties in setting the cap, monitoring, information disclosure, punishment, etc. But these difficulties can be overcome, and pilot programs may be carried out by local governments. [Key Words] emissions trading, difficulties, solutions Emissions trading is also called “cap and trade”, which is a market-based approach used to control pollution by providing economic incentives for achieving reductions in the emissions of pollutants. In the world, economists consistently have urged the use of “market-based” or “economic-incentive” instruments to address environmental problems, rather than so-cal “command-and-control” instruments.1 In the past, the “command and control” regulation was mainly used in China to address environmental problems instead of “market-based” instruments. Command and control regulation is criticized for being excessively rigid, insensitive to geographical and technological differences, and inefficient. Since 2008, the local government of Pudong Shanghai has prepared to implement emissions trading. Difficulties have been come across by the local government of Pudong, and solutions must be found. Introduction of Emissions Trading Due to the theoretical contribution of Coase, Crocker, Dales, Montgomery etc, emissions trading over the course of its history can be divided into several phases: 1. Externality In 1920, the British economist Arthur Cecil Pigou published his work Welfare Economics. He put forward a new concept “externality”------an activity of one entity that affects the welfare of another entity in a way that is outside the market mechanism. For example, when a private firm polluted the environment, the cost of pollution is paid by the whole society. Such a phenomenon is regarded as one of the market failures-----the market mechanism fails to impose the environmental cost on the polluter, which provides the reasons for government intervention. In order to compensate the market failure, Pigou proposed a well-designed pollution tax. 2. Property Rights In 1960, Ronald Harry Coase published his paper The Problem of Social Cost, in which Coase developed Pigou’s viewpoint that the function of the government is not to take the place of the market but to help the market to overcome its failures. In order to overcome the failure of externality, the government should help the market to define the property rights, and if the transaction cost is low enough, the market mechanism will restore its function. 1 Stavins, Robert N: "What Can We Learn from the Grand Policy Experiment? Lessons from SO2 Allowance Trading", The Journal of Economic Perspectives.1998. 3, p69. 1 3. Proof of Principle In 1968, John H Dales published his work Land, Water, and Ownership. Dales put the theoretical principles into practice. Beginning in the 1970s, the political process has gradually become more receptive to market-oriented environmental tools. The Environmental Protection Agency (EPA of U.S.A.) offered states the option of employing variants of tradeable permits for the control of localized air pollutants. Tradeable-permit systems were used in the 1980s to phase leaded gasoline out of the market and to phase out ozone-depleting chlorofluorocarbons (CFCs). But by far the most ambitious application of these instruments has been for the control of acid rain under Title IV of the Clean Air Act amendments of 1990, which established a sulfur dioxide (S02) allowance trading program intended to cut nationwide emissions of S02 by 50 percent below 1980 levels by the year 2000.1 4. Prototype In the 1990s, “cap-and-trade” became the prototype worldwide. Especially, in 1997, the Kyoto Protocol was adopted, which came into force in 2005. According to the treaty, most developed nations (“Annex I” countries) agreed to reduce the overall emissions of six major greenhouse gases by 5.2% from their 1990 levels by the end of 2012, while the developing countries (“non-Annex I” countries) are not subject to caps on emissions. Annex I countries may also use International Emissions Trading (IET). Annex I countries that exceed their quotas can buy quotas from countries that emit less than their quota. It is also possible for Annex I countries to sponsor carbon projects that reduce greenhouse gas emissions in other countries. These projects generate tradable carbon credits that can be used by Annex I countries in meeting their caps. The project-based Kyoto Mechanisms are the Clean Development Mechanism (CDM) and Joint Implementation (JI). In the 1990s, China has started the research on emissions trading. Since 2001, trades were tried in the cities such as Nantong, Taicang, Nanjing in Jiangsu province. In 2007, the first Climate Exchange was established in Jiaxing, Zhejiang province. And In 2008, Climate Exchanges were also established in Beijing, Tianjin, Shanghai. Under such a situation, “cap-and-trade” method was going to be implemented since 2008 in Pudong Shanghai. The paper is based on the investigations in Pudong. The Necessity for Emissions Trading Emissions trading is an important measure to protect the environment. There are several reasons to implement emissions trading: 1. The “cap-and-trade” method can help the market to overcome the failure of externality. Environmental capacity is an important productive factor, which is the welfare of the people. Now since the property rights of environmental capacity are not defined, so the capacity of environment has no prices, the public welfare is polluted at the will of the polluters. The producer can reduce cost by polluting the environment to gain more profit; one the contrary, for an environmental-friendly enterprise, it would increase its cost to protect the environment, and thus profit is cut off. As a result, the market is expelling the environmental-friendly enterprise, while 1 Stavins, Robert N: "What Can We Learn from the Grand Policy Experiment? Lessons from SO2 Allowance Trading", The Journal of Economic Perspectives.1998. 3, pp 69-70. 2 encouraging the polluter. Such a phenomenon is called externality of the market. Under such a situation, the enterprises can gain profit by polluting, so they don’t have the drive to innovate. So it is necessary for the government to use its “visible hand” to help the “invisible hand” of the market to overcome the market failure, and emissions trading is an instrument to cope with the market failure of externality. By the mechanism of the “cap-and-trade”, enterprises are forced to innovate, to adopt measures to reduce pollution, to turn from polluters into environmental-friendly enterprises. 2. The property rights of environmental capacity are not defined, which increases the opportunities for the government officials to make mistakes. The market is encouraging the polluters while driving off environmental-friendly enterprises; but the government should protect the environment. It means that the “visible hand” of the government and the “invisible hand” of the market are fighting against each other. The “invisible hand” is so powerful that it is impossible for the “visible hand” to win. So in the official circle, there happen the same stories: those officials tolerating pollutions are promoted while those officials insisting on environmental protection are driven off-----since GDP plays a very important role in officials’ record of achievements. So it is necessary to use “two hands” to construct ecological civilization, and emissions trading is a solution. 3. The property rights of environmental capacity are not defined, which causes the public welfare vulnerable to violations. In public decision-makings, the people’s environmental rights are not fully considered. These decisions would be strongly opposed by the masses in implementation, such as the “the PX Issue in Xiamen”, “the Landfill Issue at Panyu Guangdong”, “the Issue of Magnetic Suspension in Shanghai”. Even if the government attached importance to the environmental rights of the relative interest groups, there isn’t a mechanism to evaluate and compensate the loss of the relative interest groups; the more radical they are, the more they get, so the masses are encouraged to act more radically. In order to build up a harmonic society, it is necessary to establish the “cap-and-trade” mechanism, which will evaluate and compensate the environmental loss in market-based way. Difficulties and Solutions of Emissions Trading in China Both the 12th Five-Year Plan1 of China and the report of the 18th Congress of the CPC2 make it clear that market-based instruments should be employed to cope with the environmental issues. Emissions trading is one of the market-based instruments besides the extended producer’s responsibility and the ecological compensation mechanism, etc. Emissions trading is also called “Cap-and-trade”, which is used to address environmental problems such as green-house effect, acid rain and eutrophication in waters. “Cap-and-trade” method is composed of the following steps: 1. Cap Usually by a political process, a government sets a limit (or a cap) on the total amount of a 1 2 the 12th Five-Year Plan of China,http://news.qq.com/a/20101027/001797_2.htm。 the report of the 18th Congress of the CPC, Beijing China, the People’s Publishing House 2012, p41. 3 pollutant that may be emitted, and the individual companies are free to choose how or if they will reduce their emissions. The cap is usually lowered over time according to the national emissions reduction target. Firms are required to hold a number of permits (or allowances or credits) equivalent to their emissions. The total number of permits cannot exceed the cap, limiting total emissions to that level. 2. Allocation of the cap The limit (or cap) is allocated freely or sold to firms in the form of emissions permits, which represent the right to emit a specific volume of the specified pollutant. 3. Measurement In order to trade, precise measurement is requested. The traditional method of hand-sampling can’t meet the request of “cap-and-trade”, on-line monitors are to be used to meet the demand. 4. Punishment After a cap has been set, firms emitting more than its permits would be punished at progressive rate by government, which increases the costs of production. Firms will choose the least-cost way to comply with the pollution regulation, which will lead to emissions trade in the market. 5. Trade: Firms who require fewer permits can sell them in the market. Who will buy? Firms that need to increase their volume of emissions would have to buy more permits; new firms should buy enough permits; organizations which do not pollute and therefore have no obligations may also participate in trading to purchase emission permits and hence drive up the price of the remaining permits according to the law of demand; firms can also donate emission permits to a nonprofit entity and then be eligible for a tax deduction; the government can also buy-back the extra permits as reward to firms that emit less. In effect, the buyer is paying a charge for polluting, while the seller is being rewarded for having reduced emissions, which forms a market mechanism encouraging those who can reduce emissions most cheaply. The above-mentioned steps compose an integrated chain of “cap-and-trade”. Difficulty or barrier at any step would cause the whole trade unaccomplished. Since 2008, Shanghai is preparing to implement emissions trading in Pudong. Investigation shows that there are difficulties to be overcome: 1. How to define the cap Theoretically speaking, the environmental capacity of an area is limited. There exists a valve in the ecological system, which would be under pressure or even collapse when emissions of pollutants exceed the valve. But in practice, how the cap is defined? According to the reality in China, there several ways to define the cap: (1) Pollution Source Census: From December 31, 2007 to February 9, 2010, China launched the first Pollution Source Census at the cost of 4.1 billion RMB Yuan. Databases have been established covering 4 levels: nation, province, city and county. Information can be retrieved according to the category of industry, area, polluting factor etc. The Pollution Source Census provided scientific base to set the cap. (2) The National Five-Year Plan: Cap is to be set according to the National Five-Year Plans in China. For example, the 11th Five-Year Plan set up an aim that the main pollutants should reduced by 10% at end of 2010; the 12th Five-Year Plan set up an aim that the consumption of 4 non-fossil energy will cover 11.4% of the total energy consumption, the energy consumption per unit GDP is to be reduced by 16% while the CO2 emission per unit GDP is to be reduced by 17%, the emission of the main pollutants is to be reduced by 8-10%.1 (3) Legislation of the People’s Congress: When the cap is set, it should not be changed. If it were changed, the permits would lose scarcity, and trade becomes impossible. So it is necessary for the People’s Congress to set the cap through legislative procedure, then the cap becomes law, which can’t be changed easily. Without permits, no firms can be established, even if it is very profitable; the only way to attract new investment is to close down backward productions to make space for advanced productions. Up to now, the national People’s Congress and the local People’s Congress still lack of such legislative activities on “cap-and-trade”. 2. The Ability of Monitoring “Cap-and-trade” requests precise monitoring. In China, emissions are mainly monitored by the government, whose ability of monitoring is far from “cap-and-trade” requests. For example, in 2008, Pudong Shanghai covers an area of about 570km2, with over 6000 pollution sources; while the Pudong Environmental Monitoring Station has a staff of less than 60. On average, a person should have to monitor 100 polluting firms in an area about 10km2. Furthermore, according to the regulation on monitoring, 2 staff members must be present at hand-sampling in order to avoid corruption. It is impossible for so few staff to get precise data by hand-sampling. In reality, what the Pudong Environmental Monitoring Station can do is to classify the polluting firms into several classes: the seriously polluting firms may be monitored twice every month, the average polluting ones may be monitored once a month, while the “good” ones are monitored once 2 months. So it is crystal clear that it is impossible for so few staff to get accurate data in such a primitive hand-sampling method. On-line monitoring is the solution, which can save monitoring staff and provide accurate data. But another difficulty occurs----now the on-line digital data doesn’t have legal validity in China mainly because there are so many different types of on-line monitors in China: some use the U.S. system, some use the European system, some use the Japanese system, and some use the Chinese system. The different system use different standards, different chemical agents and different testing methods. Which system should be regarded as the standard in law-making on the legal validity of on-line data? So before the on-line digital data have legal validity, it is necessary for China to establish the technical standard for the various types of monitors. Now it is still not the time to establish the same standard throughout China, but some local government can carry out some pilot project. 3. Information Disclosure Symmetry of information is a premise for trade. If information is not fully disclosed, people are unwilling to trade. Now the environmental information disclosure in China still can’t meet the demand of emissions trade. For example, from May1 2008, the Regulations on Government Information Disclosure of the People’s Republic of China took effect. According to the explanation of the Ministry of Environmental Protection, the government may disclose a firm’s polluting information only under 2 situations: firstly, the government has punished a firm for pollution; secondly, the firm itself is willing to disclose pollution information------it is clear that 1 the 12th Five-Year Plan of China,http://news.qq.com/a/20101027/001797_2.htm。 5 most firms are not willing to disclose their pollution information. So such a regulation on environmental information disclosure can’t meet the demand for emissions trading. Why is the government hesitating to disclose environmental information? The most important reason is that the government’s environmental data is undependable because of the above-mentioned hand-sampling method. Information disclosure would cause law case against the government, and the government has little confidence in its data. But such a situation will be changed if on-line monitors are installed. So some local government may carry out pilot project to install large amount of on-line monitors, and amend the regulations on information disclosure that the government has the authority to disclose the over-all information of the polluter. Or the government can entrust the third party (some monitoring institution) to monitor the emission of the producer. 4. Punishment Emissions trading requests the government imposing aggressive punishment on the polluters so as to force the polluter to reduce emission or buy permits in the market. But the current environmental punishment is too light. For example, according to the relative environmental law, the highest punishment is only 1000,000 RMB Yuan, which is nothing to a large firm; and according to latest law on water protection, the highest punishment is 500,000 RMB Yuan, but such a punishment needs a lot of harsh conditions------too harsh to make the punishment possible. So long as the cost of breaking the law is low, illegal behavior will thrive. The current environmental laws are encouraging the producers to pollute. Such environmental laws cannot meet the demand for emissions trading. In order to implement emissions trading, the current environmental laws have to be amended, especially more severe punishment are to be imposed on the polluters. Such amendments of law may be tried by some local governments. In implementation of emissions trading, there are difficulties in setting the cap, monitoring, information disclosure, punishment, etc. These difficulties can be overcome, but some concern various departments of the government and are beyond the power of the Environmental Protection Department. For example, some difficulties are to be overcome by amending the current law, which needs the joint efforts of the relative departments. China is a large country, different area has different situation, so it is reasonable for pilot programs to be carried out by local governments, such as Beijing, Shanghai, Tianjin and Guandong Province. Shi Qinghao shiqinghaopku@163.com 0086-18918989173 6