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Four firms located at different points on a river dump various quantities of effluent into it. The effluent adversely affects the quality of swimming for homeowners who live downstream. These people can build swimming pools to avoid swimming in the river, and the firms can purchase filters that eliminate harmful chemicals dumped in the river. As a policy adviser for a regional planning organization, how would you compare and contrast the following options for dealing with the harmful effect of the effluent: a. An equal-rate effluent fee on firms located on the river. b. An equal standard per firm on the level of effluent that each can dump. c. A transferable effluent permit system in which the aggregate level of effluent is fixed and all firms receive identical permits.

Short Answer

Expert verified
Each policy option comes with its own strengths and weaknesses. An equal-rate effluent fee is straightforward and incentivizing, but potentially unfair and might encourage illicit disposal. An equal standard per firm controls the total effluent but doesn't necessarily incentivize reduction. A transferable permit system could encourage pollution reduction but its success is dependent on rigorous enforcement; moreover, it could disadvantage smaller firms.

Step by step solution

01

Option A Analysis: Equal-rate effluent fee

An equal-rate effluent fee would mean that each firm pays the same fee for every unit of effluent they dump. This method is straightforward and could incentivize firms to reduce their pollution in order to minimize fees. However, it may be unfair to those firms who naturally produce less effluent. The potential economic burden might also encourage illicit disposal practices.
02

Option B Analysis: Equal standard per firm

An equal standard per firm means each company is allowed to dump the same amount of effluent. This method can be effective in controlling the total amount of effluent but may not necessarily incentivize companies to reduce their pollution, especially if their output is far below the limit. This policy also doesn't account for the disparity in production capacity between firms.
03

Option C Analysis: Transferable effluent permit system

A transferable effluent permit system would involve issuing identical permits to all firms, thereby setting a cap on the amount of effluent each firm can dump. Firms that can reduce their pollution would then have the option to sell their surplus permits to those that can't. This could encourage an overall reduction in pollution. However, the success of this system depends on proper regulation and enforcement. Furthermore, smaller firms might be disadvantaged if larger firms outbid them for additional permits.

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Key Concepts

These are the key concepts you need to understand to accurately answer the question.

Effluent Fee
An effluent fee is a policy tool used in environmental economics to control pollution from companies by charging them for the contaminants they release into natural water bodies. With this approach, each business along the river pays a fee proportional to the amount of effluent they discharge. This fee acts as an incentive for companies to reduce their pollution levels, as they would want to lower their expenses by minimizing effluent production.


  • Pros: The effluent fee system is relatively simple to implement and understand.
  • It provides a financial motivation for firms to reduce pollution.
  • Firms have the flexibility to innovate solutions to cut down on effluents.

Despite its benefits, the system might be perceived as unfair to firms that already produce less pollution. These smaller firms may bear a similar economic burden as larger firms due to the uniform fee rate. Consequently, there could also be unintended outcomes, where firms engage in illegal dumping to evade the fees. Thus, while an effluent fee can effectively reduce pollution levels, it requires robust monitoring and compliance mechanisms to prevent such practices.
Permit System
The permit system, specifically a transferable effluent permit system, is a strategy that allows for market-driven pollution control by allotting fixed pollution rights to firms. Each business along the river receives permits allowing a certain level of effluent discharge. Importantly, these permits are marketable, meaning they can be bought and sold among firms.


  • Trading Efficiency: This creates a secondary market where firms with lower pollution costs can sell their extra permits to firms facing higher costs.
  • Flexibility: Firms can choose either to reduce their emissions or to trade permits.

This system benefits the environment by maintaining an overall cap on pollution while providing economic efficiency. Companies that can cut emissions cheaply will do so and sell permits for profit. However, monitoring and enforcement are crucial to prevent breaches of permit conditions.

One downside is that prevailing market conditions can drive the price of permits up, making them inaccessible for smaller firms, potentially disadvantaging them. Also, market mechanisms must be effectively managed to ensure no firm exceeds its permit limit.
Pollution Control Policies
Pollution control policies encompass a wide range of strategies aimed at reducing the negative environmental impacts of industrial effluents. These policies can take various forms, such as regulation, taxation, and market-based mechanisms, all seeking to encourage limited waste production and cleaner manufacturing processes.


  • Regulatory Policies: Mandating specific limits on pollutants is common, where standards are set per firm.
  • Economic Instruments: These include taxes (like effluent fees) and cap-and-trade systems (like transferable permits), which are designed to internalize the environmental costs of pollution into the decision-making processes of firms.

The goal of these policies is ultimately to achieve sustainable economic growth with minimized environmental harm. Each approach has its strengths and challenges. Regulatory approaches are direct and straightforward but can be inflexible. Economic instruments can be highly effective, encouraging innovation but require proper oversight to work efficiently.
Pollution control policies must therefore be tailored to the specific context, considering the industry's characteristics, the local environment, and community needs to achieve the best outcomes.

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Most popular questions from this chapter

The Georges Bank, a highly productive fishing area off New England, can be divided into two zones in terms of fish population. Zone 1 has the higher population per square mile but is subject to severe diminishing returns to fishing effort. The daily fish catch (in tons) in Zone 1 is $$F_{1}=200\left(X_{1}\right)-2\left(X_{1}\right)^{2}$$ where \(X_{1}\) is the number of boats fishing there. Zone 2 has fewer fish per mile but is larger, and diminishing returns are less of a problem. Its daily fish catch is \\[ F_{2}=100\left(X_{2}\right)-\left(X_{2}\right)^{2} \\] where \(X_{2}\) is the number of boats fishing in Zone \(2 .\) The marginal fish catch MFC in each zone can be represented as \\[ \begin{array}{l} \mathrm{MFC}_{1}=200-4\left(X_{1}\right) \\ \mathrm{MFC}_{2}=100-2\left(X_{2}\right) \end{array} \\] There are 100 boats now licensed by the U.S. government to fish in these two zones. The fish are sold at \(\$ 100\) per ton. Total cost (capital and operating) per boat is constant at \(\$ 1000\) per day. Answer the following questions about this situation: a. If the boats are allowed to fish where they want, with no government restriction, how many will fish in each zone? What will be the gross value of the catch? b. If the U.S. government can restrict the number and distribution of the boats, how many should be allocated to each zone? What will be the gross value of the catch? Assume the total number of boats remains at 100 c. If additional fishermen want to buy boats and join the fishing fleet, should a government wishing to maximize the net value of the catch grant them licenses? Why or why not?

Assume that scientific studies provide you with the following information concerning the benefits and costs of sulfur dioxide emissions: Benefits of abating (reduc- \\[ \mathrm{MB}=500-20 A \\] ing ) emissions: costs of abating emissions: \\[ \mathrm{MC}=200+5 A \\] where \(A\) is the quantity abated in millions of tons and the benefits and costs are given in dollars per ton. a. What is the socially efficient level of emissions abatement? b. What are the marginal benefit and marginal cost of abatement at the socially efficient level of abatement? c. What happens to net social benefits (benefits minus costs) if you abate one million more tons than the efficient level? One million fewer? d. Why is it socially efficient to set marginal benefits equal to marginal costs rather than abating until total benefits equal total costs?

The market for paper in a particular region in the United States is characterized by the following demand and supply curves: \\[ Q_{D}=160,000-2000 P \quad \text { and } \quad Q_{S}=40,000+2000 P \\] where \(Q_{D}\) is the quantity demanded in 100 -pound lots, \(Q_{\mathrm{S}}\) is the quantity supplied in 100 -pound lots, and \(P\) is the price per 100 -pound lot. Currently there is no attempt to regulate the dumping of effluent into streams and rivers by the paper mills. As a result, dumping is widespread. The marginal external cost (MEC) associated with the production of paper is given by the curve \(\mathrm{MEC}=0.0006 Q_{S}\) a. Calculate the output and price of paper if it is produced under competitive conditions and no attempt is made to monitor or regulate the dumping of effluent. b. Determine the socially efficient price and output of paper. c. Explain why the answers you calculated in parts (a) and (b) differ.

In a market for dry cleaning, the inverse market demand function is given by \(P=100-Q\), and the (private) marginal cost of production for the aggregation of all dry-cleaning firms is given by \(\mathrm{MC}=10+Q\) Finally, the pollution generated by the dry cleaning process creates external damages given by the marginal external cost curve \(\mathrm{MEC}=Q\) a. Calculate the output and price of dry cleaning if it is produced under competitive conditions without regulation. b. Determine the socially efficient price and output of dry cleaning. c. Determine the tax that would result in a competitive market producing the socially efficient output. d. Calculate the output and price of dry cleaning if it is produced under monopolistic conditions without regulation. e. Determine the tax that would result in a monopolistic market producing the socially efficient output. f. Assuming that no attempt is made to monitor or regulate the pollution, which market structure vields higher social welfare? Discuss.

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