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External Costs and Environmental Policy

External Costs and Environmental Policy. P R E P A R E D B Y. In 2001, a group of students from an economics course at Hobart and William Smith Colleges joined an auction for the right to discharge sulfur dioxide into the atmosphere.

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External Costs and Environmental Policy

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  1. External Costs andEnvironmental Policy P R E P A R E D B Y In 2001, a group of students from an economics course at Hobart and William Smith Colleges joined an auction for the right to discharge sulfur dioxide into the atmosphere. Economics: Principles, Applications, and Tools O’Sullivan, Sheffrin, Perez 6/e. FERNANDO QUIJANO, YVONN QUIJANO, AND XIAO XUAN XU

  2. A P P L Y I N G T H E C O N C E P T S How do we determine the optimum level of pollution? Reducing Methane Emissions What is the economic approach to global warming? The Effects of a Carbon Tax Are there different ways to reduce pollution or mitigate its effects? Mercury in Tuna What are the benefits of giving firms options for reducing greenhouse gases? Chicago Climate Exchange What is the external cost of young drivers? Young Drivers and Collisions 1 2 3 4 5

  3. THE OPTIMAL LEVEL OF POLLUTION 31.1 Using the Marginal Principle M A R G I N A L P R I N C I P L E Increase the level of an activity as long as its marginal benefit exceeds its marginal cost. Choose the level at which the marginal benefit equals the marginal cost. • From society’s perspective, there are many benefits from pollution abatement: • Better health. • Increased enjoyment of the natural environment. • Lower production costs.

  4. THE OPTIMAL LEVEL OF POLLUTION 31.1 Example: The Optimal Level of Sulfur Dioxide FIGURE 31.1The Optimal Level of Sulfur Dioxide Emissions in 2010 The marginal-benefit curve is horizontal at $3,500, because for each additional ton of SO2 discharged into the atmosphere, the costs increase by about $3,500. The marginal-cost curve is positively sloped, because the more pollution we abate, the higher the marginal cost of abatement. The optimum level of pollution abatement is shown by point a, where the marginal benefit of abatement equals its marginal cost.

  5. 1 A P P L I C A T I O N REDUCING METHANE EMISSIONS APPLYING THE CONCEPTS #1: How do we determine the optimum level of pollution? ►FIGURE 31.2The Marginal Cost of Reducing Methane Emissions The marginal cost of reducing methane emissions increases with the volume reduced. What is the optimal level of methane abatement? It depends on the marginal benefit of abatement. If, for example, the marginal benefit is $10, the optimum level is about 36 million metric tons. But if the marginal benefit is much higher, say $150, the optimum level of abatement is about 69 million metric tons.

  6. TAXING POLLUTION 31.2 ●private cost of productionThe production cost borne by a producer, which typically includes the costs of labor, capital, and materials. ●external cost of productionA cost incurred by someone other than the producer. ●social cost of productionPrivate cost plus external cost. ●pollution taxA tax or charge equal to the external cost per unit of pollution.

  7. TAXING POLLUTION 31.2 A Firm’s Response to a Pollution Tax • FIGURE 31.3The Firm’s Response to an SO2 Tax From the perspective of a firm subject to a pollution tax, the marginal benefit of abatement is the $3,500 pollution tax that can be avoided by cutting pollution by one ton. The firm satisfies the marginal principle at point c, with six tons of abatement, leaving two tons of SO2 discharged into the atmosphere.

  8. TAXING POLLUTION 31.2 The Market Effects of a Pollution Tax • The production of electricity generates two major pollutants: • Sulfur dioxide. • Nitrogen oxides (NOx ).

  9. TAXING POLLUTION 31.2 ►FIGURE 31.4The Effects of SO2 and NOx Taxes on the Electricity Market The pollution tax increases the cost of producing electricity, shifting the market supply curve up. The equilibrium moves from point a to point b. The tax increases the equilibrium price from $64.90 to $67.60 per megawatt-hour and decreases the equilibrium quantity.

  10. 2 A P P L I C A T I O N THE EFFECTS OF A CARBON TAX APPLYING THE CONCEPTS #2: What is the economic approach to global warming? A carbon tax would reduce greenhouse emissions in several ways: • The price of gasoline would increase, causing people to drive less and buy more energy-efficient vehicles. • The tax would increase the price of electricity, decreasing the quantity of electricity demanded and the quantity of fossil fuels burned. • The higher price of home heating would cause people to turn down their thermostats and improve the heating efficiency of their homes, perhaps by installing energy-efficient windows or more insulation. • Some electricity producers would switch from coal to natural gas, which has a lower carbon content, and thus a lower carbon tax. Others would switch to noncarbon energy sources such as wind power, solar power, and geothermal sources.

  11. TAXING POLLUTION 31.2  FIGURE 31.5Responses to SO2 and NOx Taxes on Electricity Generation Taxes on SO2 and NOx cause electricity generators to switch to low-sulfur coal and to alternative energy sources that generate less SO2 and NOx.

  12. 31.3 TRADITIONAL REGULATION Uniform Abatement with Permits Consider an area with two electricity generators, firm L (for low cost) and firm H (for high cost). Suppose that in the absence of pollution-abatement efforts, each firm would discharge five tons of pollution per hour. The government sets a target abatement level of two tons of SO2 per hour, divided equally between the two firms. Under this uniform abatement policy, the government will issue four pollution permits to each firm, forcing each firm to cut pollution from five tons to four tons.

  13. 31.3 TRADITIONAL REGULATION Command and Control • The problem with this approach is that the mandated abatement technology—the control part of the policy—is unlikely to be the most efficient technology for two reasons: • The regulatory policy specifies a single abatement technology for all firms. Because the producers of a polluting good often use different materials and production techniques, an abatement technology that is efficient for one firm may be inefficient for others. • The regulatory policy decreases the incentives to develop more efficient abatement technologies. The command part of the policy specifies a maximum volume of waste for each firm, so there is no incentive to cut the volume of waste below the maximum allowed.

  14. 31.3 TRADITIONAL REGULATION Market Effects of Pollution Regulations How do the market effects of pollution regulation compare to the effects of a pollution tax? Recall that the uniform abatement policy achieves the same reduction in pollution at a higher cost because it doesn’t exploit differences in abatement costs across firms. In addition, the control part of command and control may lead to relatively costly abatement techniques because there’s no incentive to develop better ones. This will cause the supply curve for the polluting good to shift upward by a larger amount than it would with a tax. A larger supply shift causes a larger increase in the equilibrium price and a larger reduction in quantity. The inefficiency of regulations is passed on to consumers, who pay higher prices. One advantage of the command-and-control policy is its predictability. The policy specifies how much waste each firm can produce, so we can predict the total volume of waste. In contrast, we don’t know exactly how firms will respond to the pollution tax— they could pollute a little or a lot, depending on the tax and the cost of abating pollution—so it is difficult to predict the total volume of waste that will be emitted.

  15. A P L I C A T I O N 3 MERCURY IN TUNA APPLYING THE CONCEPTS #3: Are there different ways to reduce pollution or mitigate its effects? • Recent studies have reported dangerously high levels of mercury in tuna served in sushi restaurants. In one study, one-third of the samples had more than one part of mercury per million, the level that allows the Food and Drug Administration (FDA) to take fish off the market. • Our exposure to mercury from all sources could be reduced in a number of ways, at vastly different costs. • • Mercury is released into the environment when blood-pressure monitors break and spill their mercury. The cost of a proper cleanup of a spill is about $35,000 per kilogram of mercury spilled. Alternatively, a switch to nonmercury monitors would cost about $597 per kilogram of mercury avoided. • • Many vehicles contain mercury in switches for lights and antilock braking systems, and mercury is released when the vehicles are recycled and incinerated. The cost of a system that prevents releases during incineration is about $27,000 per kilogram of mercury captured. Alternatively, the cost of removing the switches prior to incineration is only about $590 per kilogram of mercury captured. • • The cost of reducing mercury emissions from power generation is about $27,000 per kilogram avoided.

  16. 31.3 TRADITIONAL REGULATION Lesson from Dear Abby: Options for Pollution Abatement • The readers of “Dear Abby” offered the following suggestions to Dreading Winter: • • Buy the neighbors a catalytic add-on for the wood stove or a wood-chip gasifier for an oil furnace. In either case, there would be much less air pollution from burning wood. • • Soak a towel in water, swish it around the room, and watch the smoke disappear. • • Leave a saucer of vinegar in each room to eliminate the smoke odor. • • Pay your neighbors to hire a chimney sweep to clean their flue. • • Seal and caulk your windows to keep the smoke outside at a cost of less than $500. • • Use the $500 to purchase an air purifier for your home. • There is usually more than one way to deal with a pollution problem.

  17. 31.4 MARKETABLE POLLUTION PERMITS ●marketable pollution permits A system under which the government picks a target pollution level for a particular area, issues just enough pollution permits to meet the pollution target, and allows firms to buy and sell the permits; also known as a cap-and-trade system.

  18. 31.4 MARKETABLE POLLUTION PERMITS Voluntary Exchange and Marketable Permits Making pollution permits marketable is sensible because it allows mutually beneficial exchanges between firms with different abatement costs. P R I N C I P L E O F V O L U N T A R Y E X C H A N G E A voluntary exchange between two people makes both people better off.

  19. 31.4 MARKETABLE POLLUTION PERMITS Supply, Demand, and the Price of Marketable Permits  FIGURE 31.6The Market for Pollution Permits The equilibrium price of permits is shown by the intersection of the demand curve and the vertical supply curve. The supply curve is vertical because each year the government specifies a fixed number of permits. A decrease in the number of permits shifts the supply curve to the left, increasing the equilibrium price.

  20. A P L I C A T I O N 4 CHICAGO CLIMATE EXCHANGE APPLYING THE CONCEPTS #4: What are the benefits of giving firms options for reducing greenhouse gases? • The Chicago Climate Exchange (CCX) allowsfirms to cut their emissions of greenhouse gases in different ways: • Cutting its own emissions. • (2) Paying for extra reductions by other firms. • (3) Paying for projects such as reforestation that offset the firm’s emissions. • The experience of American Electric Power (AEP), the nation’s largest electricity producer, illustrates how CCX works. AEP bought 10,000 acres of fallow land and planted walnut trees, which each year will withdraw about 71,000 tons of carbon dioxide from the air and convert it into solid wood. As long as the wood doesn’t burn or decompose, AEP can use the trees to offset some of its carbon emissions.

  21. 31.5 EXTERNAL COSTS FROM AUTOMOBILES External Costs from Pollution • FIGURE 31.7The Market Effects of a Gasoline Tax A gasoline tax of $0.68 per gallon shifts the supply curve upward by the amount of the tax. The equilibrium price increases by $0.40. The tax is shifted forward onto consumers, who pay $0.40 more per gallon, and backward onto input suppliers, who receive lower prices for crude oil.

  22. 31.5 EXTERNAL COSTS FROM AUTOMOBILES External Costs from Congestion The economic approach to congestion is to internalize the external cost by imposing a tax on drivers equal to the external costs they impose on others. Modern technology allows the efficient collection of congestion taxes. The use of congestion taxes and other time-sensitive pricing of highways is spreading. External Costs from Collisions In the United States, the annual cost of property damage, injuries, and deaths from traffic collisions is about $300 billion per year. About two-thirds of these costs are incurred by the driver who causes the accident, and the other third is borne by someone else. In other words, traffic collisions have substantial external costs. On average, the collision-related external cost of travel is about 4.4 cents per mile driven. By way of comparison, the fuel cost per mile is about 10 to 15 cents. The direct approach to internalize this externality would be to impose a tax of 4.4 cents per vehicle-mile traveled, a VMT tax. Such a tax would improve traffic safety by reducing the number of miles driven. Alternatively, the premium for automobile insurance could be based on miles driven or a gasoline tax could be imposed.

  23. A P L I C A T I O N 5 YOUNG DRIVERS AND COLLISIONS APPLYING THE CONCEPTS #5: What is the external cost of young drivers? A VMT tax of 4.4 cents per mile would internalize the external cost from collisions on average, but the external cost varies with the age of the driver. As shown in Table 31.1, the external cost of young drivers is over three times the external cost of middle-aged drivers. A precise VMT tax would have higher tax rates for the drivers with higher external cost. For example, the tax for young drivers would be 11 cents per mile, compared to 3.4 cents per mile for a middle-aged driver. Such a tax would reduce the miles driven by all drivers, but the reductions would be larger for young drivers, the group with the highest collision rates and external costs.

  24. K E Y T E R M S pollution tax private cost of production social cost of production external cost of production marketable pollution permits

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