Market-Oriented Environmental Tools
Read this section to learn more about how permits and the Coase theorem can be applied to solve environmental problems by defining user and property rights in society. Make sure to answer the "Try It" questions.
1. Market-Oriented Environmental Tools
- Show how pollution charges or marketable permits can impact firm decisions
- Explain the significance of marketable permits and property rights (the Coase theorem)
- Evaluate which government and market policies are most appropriate for various situations
Market-oriented environmental policies create incentives for firms to reduce pollution. The three main categories of market-oriented approaches to pollution control are pollution charges, marketable permits, and better-defined property rights. All of
these policy tools, discussed below, address the shortcomings of command-and-control regulation - albeit in different ways.
An effluent (or pollution) charge is a tax imposed on the quantity of pollution that a firm emits. Under an effluent charge system, firms are allowed to pollute, as long as they pay the charge for every unit of pollution.
A pollution charge gives a profit-maximizing firm an incentive to figure out ways to reduce its emissions - as long as the marginal cost of reducing the emissions is less than the tax.
For example, consider a small firm that emits 50 pounds per year of small particles, such as soot, into the air. Particulate matter, as it is called, causes respiratory illnesses and also imposes costs on firms and individuals.
Figure 1 illustrates the marginal costs that a firm faces in reducing pollution. The marginal cost of pollution reduction, like most most marginal cost curves increases with output, at least in the short run. Reducing the first 10 pounds of particulate emissions costs the firm $300. Reducing the second 10 pounds would cost $500; reducing the third ten pounds would cost $900; reducing the fourth 10 pounds would cost $1,500; and the fifth 10 pounds would cost $2,500. This pattern for the costs of reducing pollution is common, because the firm can use the cheapest and easiest method to make initial reductions in pollution, but additional reductions in pollution become more expensive.
Figure 1. A Pollution Charge. If a pollution charge is set equal to $1,000, then the firm will have an incentive to reduce pollution by 30 pounds because the $900 cost of these reductions would be less than the cost of paying the pollution charge.
Imagine the firm now faces a pollution tax of $1,000 for every 10 pounds of particulates emitted. The firm has the choice of either polluting and paying the tax, or reducing the amount of particulates they emit and paying the cost of abatement as shown
in the figure. How much will the firm pollute and how much will the firm abate? The first 10 pounds would cost the firm $300 to abate. This is substantially less than the $1,000 tax, so they will choose to abate. The second 10 pounds would cost $500
to abate, which is still less than the tax, so they will choose to abate. The third 10 pounds would cost $900 to abate, which is slightly less than the $1,000 tax. The fourth 10 pounds would cost $1,500, which is much more costly than paying the tax.
As a result, the firm will decide to reduce pollutants by 30 pounds, because the marginal cost of reducing pollution by this amount is less than the pollution tax. With a tax of $1,000, the firm has no incentive to reduce pollution more than 30 pounds.
A firm that has to pay a pollution tax will have an incentive to figure out the least expensive technologies for reducing pollution. Firms that can reduce pollution cheaply and easily will do so to minimize their pollution taxes, whereas firms that will incur high costs for reducing pollution will end up paying the pollution tax instead. If the pollution tax applies to every source of pollution, then no special favoritism or loopholes are created for politically well-connected producers.
For an example of a pollution charge at the household level, consider two ways of charging for garbage collection. One method is to have a flat fee per household, no matter how much garbage a household produces. An alternative approach is to have several levels of fees, depending on how much garbage the household produces - and to offer lower or free charges for recyclable materials. As of 2006 (latest statistics available), the EPA had recorded over 7,000 communities that have implemented "pay as you throw" programs. When people have a financial incentive to put out less garbage and to increase recycling, they find ways of doing so.
A number of environmental policies are really pollution charges, although they often do not travel under that name. For example, the federal government and many state governments impose taxes on gasoline. We can view this tax as a charge on the air pollution that cars generate as well as a source of funding for maintaining roads. Indeed, gasoline taxes are far higher in most other countries than in the United States.
Similarly, the refundable charge of five or 10 cents that only 10 states have for returning recyclable cans and bottles works like a pollution tax that provides an incentive to avoid littering or throwing bottles in the trash. Compared with command-and-control regulation, a pollution tax reduces pollution in a more flexible and cost-effective way.
When a city or state government sets up a marketable permit program, it must start by determining the overall quantity of pollution it will allow as it tries to meet national pollution standards. Then, a number of permits allowing only
this quantity of pollution are divided among the firms that emit that pollutant. These permits to pollute can be sold or given to firms free.
Now, add two more conditions. Imagine that these permits are designed to reduce total emissions over time. For example, a permit may allow emission of 10 units of pollution one year, but only nine units the next year, then eight units the year after that, and so on down to some lower level. In addition, imagine that these are marketable permits, meaning that firms can buy and sell them.
To see how marketable permits can work to reduce pollution, consider the four firms listed in Table 1. The table shows current emissions of lead from each firm. At the start of the marketable permit program, each firm receives permits to allow this level of pollution. However, these permits are shrinkable, and next year the permits allow the firms to emit only half as much pollution. Let's say that in a year, Firm Gamma finds it easy and cheap to reduce emissions from 600 tons of lead to 200 tons, which means that it has permits that it is not using that allow emitting 100 tons of lead. Firm Beta reduces its lead pollution from 400 tons to 200 tons, so it does not need to buy any permits, and it does not have any extra permits to sell. However, although Firm Alpha can easily reduce pollution from 200 tons to 150 tons, it finds that it is cheaper to purchase permits from Gamma rather than to reduce its own emissions to 100. Meanwhile, Firm Delta did not even exist in the first period, so the only way it can start production is to purchase permits to emit 50 tons of lead.
The total quantity of pollution will decline. But the buying and selling of the marketable permits will determine exactly which firms reduce pollution and by how much. With a system of marketable permits, the firms that find it least expensive to do so will reduce pollution the most.
Table 1. How Marketable Permits Work
|Current emissions - permits distributed free for this amount||200 tons
|How much pollution will these permits allow in one year?||100 tons
|Actual emissions one year in the future||150 tons
|Buyer or seller of marketable permit?||Buys permits for 50 tons||Doesn't buy or sell permits||Sells permits for 100 tons||Buys permits for 50 tons|
- the government policy will be effective in encouraging ChemUnited to reduce the amount of pollutant released in the river.
- it is more effective to rely on ChemUnited to self regulate rather than use taxation.
- the government policy will be ineffective for ChemUnited because cost of complying is higher than the cost of not complying.
Source: Lumen Learning, https://courses.lumenlearning.com/wmopen-microeconomics/chapter/market-oriented-environmental-tools/
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