Environmental economics
Environmental economics is a sub-field of economics concerned with environmental issues. It has become a widely studied subject due to growing environmental concerns in the twenty-first century. Environmental economics "undertakes theoretical or empirical studies of the economic effects of national or local environmental policies around the world. Particular issues include the costs and benefits of alternative environmental policies to deal with air pollution, water quality, toxic substances, solid waste, and global warming."
Environmental Versus Ecological Economics
Environmental economics is distinguished from ecological economics in that ecological economics emphasizes the economy as a subsystem of the ecosystem with its focus upon preserving natural capital. While environmental economics focuses on human preferences, by trying to balance protecting natural resources with people's needs for products and services. Due to these differences it can be seen that ecological economics takes a more holistic approach to traditional economic theories, while environmental economics fits within traditional economic theories.One survey of German economists found that ecological and environmental economics are different schools of economic thought, with ecological economists emphasizing "strong" sustainability and rejecting the proposition that human-made capital can substitute for natural capital, and environmental economics focusing on the efficient allocation of natural resources in order to fulfill human wants.
History
18th and 19th Century
Although the term "environmental economics" became popular beginning in the 1960s, the entwinement of the two fields of environmentalism and economics started much earlier. Starting with economist Marquis de Condorcet in the 18th century, who had an interest in the link between economic activity and environmental issues. This was seen in his usage of externalities while analyzing environmental issues.During the classical period of economics, Adam Smith realized while the market is able to allocate private goods efficiently for most goods, it fails to do so in some environmental circumstances. It is within these scenarios where the market fails, that the government needs to take action. This is seen in his quote "Erecting and maintaining certain public works and certain public institutions which it can never be for the interest of any individual, or small number of individuals to erect and maintain; because the profit would never repay the expense to any individual or small number of individuals, though it may frequently do much more than repay it to a great society." Thomas Robert Malthus also was another classical economist whose work led to the beginnings of environmental economists. Malthus' theory of population argued that agricultural productivity faces diminishing returns, which ultimately limits the exponential growth of human populations. This thought process later led economists to think about the relationship between resource scarcity and economic development. David Ricardo's writings connected the natural environment and the standard of living which further helped to develop environmental economics later on. He stressed that the value of land varies based on how fertile it is. The last classical economist to add to environmental economics was John Stuart Mill. In his Principles of Political Economy, he wrote that the management of the environment cannot be done by the market and individuals, and is instead a governmental obligation, "s there not the earth itself, its forests and waters, and all other natural riches, above and below the surface? These are the inheritance of the human race, and there must be regulations for the common enjoyment of it. What rights, and under what conditions, a person shall be allowed to exercise over any portion of this common inheritance cannot be left undecided. No function of government is less optional than the regulation of these things, or more completely involved in the idea of civilized society."
20th Century
Environmental economics became increasingly more popular in the 19th century. This is when the Resources for the Future to tax the creator of the polluter and to create regulation that put the burden of action on the polluter or 2) the sufferer must pay the polluter to not pollute.Topics and concepts
Market failure
Central to environmental economics is the concept of market failure. Market failure means that markets fail to allocate resources efficiently. As stated by Hanley, Shogren, and White : "A market failure occurs when the market does not allocate scarce resources to generate the greatest social welfare. A wedge exists between what a private person does given market prices and what society might want him or her to do to protect the environment. Such a wedge implies wastefulness or economic inefficiency; resources can be reallocated to make at least one person better off without making anyone else worse off." This results in an inefficient market that needs to be corrected through avenues such as government intervention. Common forms of market failure include externalities, non-excludability and non-rivalry.Externality
An externality exists when a person makes a choice that affects other people in a way that is not accounted for in the market price. An externality can be positive or negative but is usually associated with negative externalities in environmental economics. For instance, water seepage in residential buildings occurring in upper floors affect the lower floors. Another example concerns how the sale of Amazon timber disregards the amount of carbon dioxide released in the cutting. Or a firm emitting pollution will typically not take into account the costs that its pollution imposes on others. As a result, pollution may occur in excess of the 'socially efficient' level, which is the level that would exist if the market was required to account for the pollution. A classic definition influenced by Kenneth Arrow and James Meade is provided by Heller and Starrett, who define an externality as "a situation in which the private economy lacks sufficient incentives to create a potential market in some good and the nonexistence of this market results in losses of Pareto efficiency". In economic terminology, externalities are examples of market failures, in which the unfettered market does not lead to an efficient outcome.Common goods and public goods
When it is too costly to exclude some people from access to an environmental resource, the resource is either called a common property resource or a public good. In either case of non-exclusion, market allocation is likely to be inefficient.These challenges have long been recognized. Hardin's concept of the tragedy of the commons popularized the challenges involved in non-exclusion and common property. "Commons" refers to the environmental asset itself, "common property resource" or "common pool resource" refers to a property right regime that allows for some collective body to devise schemes to exclude others, thereby allowing the capture of future benefit streams; and "open-access" implies no ownership in the sense that property everyone owns nobody owns.
The basic problem is that if people ignore the scarcity value of the commons, they can end up expending too much effort, over harvesting a resource. Hardin theorizes that in the absence of restrictions, users of an open-access resource will use it more than if they had to pay for it and had exclusive rights, leading to environmental degradation. See, however, Ostrom's work on how people using real common property resources have worked to establish self-governing rules to reduce the risk of the tragedy of the commons.
The mitigation of climate change effects is an example of a public good, where the social benefits are not reflected completely in the market price. Because the personal marginal benefits are less than the social benefits the market under-provides climate change mitigation. This is a public good since the risks of climate change are both non-rival and non-excludable. Such efforts are non-rival since climate mitigation provided to one does not reduce the level of mitigation that anyone else enjoys. They are non-excludable actions as they will have global consequences from which no one can be excluded. A country's incentive to invest in carbon abatement is reduced because it can "free ride" off the efforts of other countries. Over a century ago, Swedish economist Knut Wicksell first discussed how public goods can be under-provided by the market because people might conceal their preferences for the good, but still enjoy the benefits without paying for them.
Valuation
Assessing the economic value of the environment is a major topic within the field. The values of natural resources often are not reflected in prices that markets set and, in fact, many of them are available at no monetary charge. This mismatch frequently causes distortions in pricing of natural assets: both overuse of them and underinvestment in them. Economic value or tangible benefits of ecosystem services and, more generally, of natural resources, include both use and indirect. Non-use values include existence, option, and bequest values. For example, some people may value the existence of a diverse set of species, regardless of the effect of the loss of a species on ecosystem services. The existence of these species may have an option value, as there may be the possibility of using it for some human purpose. For example, certain plants may be researched for drugs. Individuals may value the ability to leave a pristine environment for their children.Use and indirect use values can often be inferred from revealed behavior, such as the cost of taking recreational trips or using hedonic methods in which values are estimated based on observed prices. These use values can also be predicted through defensive behavior against pollution or environmental hazards, which can reveal how much people are willing to spend on healthcare and other preventative measures to avoid these hazards. Another health-based predictor of environmental use value is the value of a statistical life, which provides an estimate of how much people are willing to pay for small reductions in their risk of dying from environmental hazards. Non-use values are usually estimated using stated preference methods such as contingent valuation or choice modelling. Contingent valuation typically takes the form of surveys in which people are asked how much they would pay to observe and recreate in the environment or their willingness to accept compensation for the destruction of the environmental good. Hedonic pricing examines the effect the environment has on economic decisions through housing prices, traveling expenses, and payments to visit parks.