Homework 1

Externalities, Resource Access, and Public Goods

Author

Byeong-Hak Choe

Instructions

ImportantDue and submission

Due: Wednesday, September 23, 2026, at 9:30 A.M. Eastern Time.

Bring a written paper copy and submit it at the beginning of class.

Show your equations, algebra, and units. Label graph axes, curves, prices, and quantities; a neat hand-drawn graph is sufficient. Use areas of triangles, rectangles, and trapezoids to calculate welfare; calculus is not required. For short essays, explain the economic mechanism and support your reasoning with the case details. Suggested lengths apply to each response, not to the entire question set.

We use the lecture notation: MB for marginal benefit, PMC for private marginal cost, EMC for external marginal cost, and SMC=PMC+EMC for social marginal cost. For positive externalities, EMB is external marginal benefit and SMB is social marginal benefit. Prices and marginal values are in dollars per unit; total surplus, damage, revenue, and spending are in dollars for the stated period.

WarningGenerative AI is not permitted

Do not use generative AI for any part of this homework, including reading or summarizing sources, solving calculations, drafting or revising answers, or generating graphs. Standard calculators and ordinary spelling checkers that do not generate or rewrite content are permitted. Submit only your own reasoning, calculations, graphs, and writing.

This assignment is independent practice in close reading, quantitative reasoning, and evidence-based writing. The OECD’s PISA 2025 Results (Volume I) reports that, among participating 15-year-olds and after accounting for socio-economic status, students who did not use AI for specific schoolwork tasks tended, on average, to outperform users in science. The OECD cautions that these associations do not establish causation and depend on who uses AI and how. See Figure I.4.13, printed p. 239 and the Wall Street Journal summary.

1. Riparian restoration and positive spillovers (25 points)

A landowner plants native vegetation along a stream that flows past farms toward a downstream community where people use the cleaner water.

Landowners buy restoration services to plant native vegetation along streams. Each unit is one acre restored this year. Landowners receive private benefits such as reduced erosion on their own land. Downstream residents receive additional, unpriced water-quality benefits.

MB(Q)=100-Q,\qquad PMC(Q)=20+Q,\qquad EMB(Q)=20.

Here, MB represents only the purchasing landowners’ marginal benefits, and EMB represents only the external marginal benefits received by other people. This is a positive externality: restoring an additional acre creates a benefit for downstream residents who are outside the market transaction. Social marginal benefit, SMB(Q), is the benefit that one additional restored acre creates for everyone affected. In this problem,

SMB(Q)=MB(Q)+EMB(Q),

so SMB includes both the landowners’ private marginal benefit and the downstream residents’ external marginal benefit. Assume SMC=PMC and adequate land for all quantities considered. The market outcome equates MB with PMC, whereas the efficient outcome equates SMB with SMC.

(a) Market and social outcomes (5 points). Find the unregulated quantity and price. Using the definition above, write the numerical equation for SMB(Q) and find the efficient quantity. Explain the direction of the market failure.

100-Q=20+Q\quad\Rightarrow\quad Q_M=40,\quad P_M=60.

SMB(Q)=MB(Q)+EMB(Q)=120-Q.

120-Q=20+Q\quad\Rightarrow\quad Q^*=50.

The market restores too few acres because purchasing landowners do not count the additional benefits received by downstream residents.

(b) Subsidy and prices (5 points). Determine the corrective subsidy per acre. Suppose the government pays restoration suppliers for every acre sold. Find the price landowners pay, the amount suppliers receive per acre including the subsidy, and total government spending.

The corrective subsidy is s^*=EMB(Q^*)=20 per acre. Suppliers receive the buyer’s payment plus the subsidy:

P_S=P_B+s^*,\qquad MB(Q)+s^*=PMC(Q).

100-Q+20=20+Q\quad\Rightarrow\quad Q=50.

P_B=100-50=50,\qquad P_S=50+20=70.

Government spending is G=s^*Q=20(50)=1{,}000.

(c) Welfare accounting (6 points). Calculate CS, PS, external benefits (EB), and SW before and after the subsidy. Write the appropriate welfare formula. Why must government spending be subtracted when PS includes subsidy receipts?

Use SW=CS+PS+EB-G, where PS includes the subsidy received by suppliers.

Before the subsidy:

CS_M=\tfrac12(100-60)(40)=800,\qquad PS_M=\tfrac12(60-20)(40)=800,

EB_M=20(40)=800,\qquad SW_M=2{,}400.

With the subsidy:

CS_S=\tfrac12(100-50)(50)=1{,}250,\qquad PS_S=\tfrac12(70-20)(50)=1{,}250,

EB_S=20(50)=1{,}000,\qquad SW_S=1{,}250+1{,}250+1{,}000-1{,}000=2{,}500.

Two restoration-market panels show welfare accounting before and after a corrective subsidy. The subsidy panel plots private and social marginal benefit, underlying private marginal cost, and the supply curve shifted down by the subsidy. It shades consumer surplus, producer surplus, and one thousand dollars of external benefits, equal to government spending.

The purple line is the supply curve under the corrective subsidy. It lies 20 below the orange underlying supply curve because the government pays suppliers 20 for each restored acre. The subsidy does not lower the physical marginal cost of restoration; it lowers the amount buyers must pay to make each quantity worthwhile to suppliers.

At 50 acres, buyers pay 50 and suppliers receive 70 in total. The green area represents the $1,000 external benefit from those acres. Government subsidy spending is also $1,000 in this example. These values are equal here, but external benefits and government spending remain different concepts.

Annual measure Unregulated Corrective subsidy
Consumer surplus 800 1,250
Producer surplus, including subsidy receipts 800 1,250
External benefits 800 1,000
Government spending 0 1,000
Social welfare 2,400 2,500

The subsidy receipts benefit suppliers but are funded by others. Subtracting government spending offsets that transfer; otherwise the same public money would be counted as a new net social benefit. Under the exercise’s assumptions, the spending is not itself an additional real resource cost. Restoration’s real cost is already reflected by the supply curve.

(d) Graph (4 points). Plot MB, SMB, and PMC. Mark both quantities and shade the welfare gain from correcting underprovision. Calculate the shaded area.

Compare social welfare at the market quantity with social welfare at the efficient quantity. In this problem, SMC=PMC because restoration creates an external benefit, not an external cost. At Q^*=50, SMB=SMC=70. The 70 is the marginal social value and marginal cost at the efficient quantity—not the price buyers pay under the subsidy. Buyers pay 50, while suppliers receive 70.

Step 1: Start from the market allocation

The first graph repeats the unregulated panel from part (c). At Q_M=40, the three shaded areas sum to social welfare of 2{,}400.

At the unregulated restoration-market quantity of 40 acres, shaded consumer surplus, producer surplus, and external benefit sum to social welfare of 2,400 dollars.

Step 2: Identify maximum social welfare

For society, each acre is worthwhile while SMB exceeds SMC. The curves meet at Q^*=50, so the entire shaded area through 50 acres is the maximum social welfare: 2{,}500.

Social marginal benefit and social marginal cost meet at 50 acres and 70 dollars per acre. The area between the curves through 50 acres is maximum social welfare of 2,500 dollars.

Step 3: Isolate what the market leaves unrealized

The welfare through the first 40 acres is common to both outcomes. Once that common area is set aside, the only difference is the triangle between SMB and SMC from 40 to 50 acres.

Private marginal benefit is shown in the same blue as Step 1. The welfare-gain triangle lies between social marginal benefit and social marginal cost from 40 to 50 acres. Its width is 10 acres, height is 20 dollars per acre, and area is 100 dollars.

The same gain appears in both calculations:

SW(Q^*)-SW(Q_M)=2{,}500-2{,}400=100,

\Delta SW=\tfrac12(50-40)(80-60)=100.

(e) Policy design (5 points; 100–140 words). Suppose two restored acres have very different downstream benefits. Explain why paying the same subsidy for every acre may not produce an efficient allocation. Identify one observable site characteristic that could help target payments, one outcome the agency should verify, and one reason it may be difficult to determine whether the credited improvement was caused by the subsidy.

A uniform subsidy rewards acres equally even when their external benefits differ. It could encourage low-benefit restoration while leaving more valuable sites unrestored. Distance to a stream, slope, or the number of downstream water users could help target payments. For example, a steep field beside a tributary may have greater potential to reduce delivered sediment. The agency should verify an outcome such as survival of the planted buffer or a measured reduction in sediment or nutrient loss. Causal attribution remains difficult because weather varies and some landowners might have restored the acreage without the subsidy.

2. Effort in an open-access fishery (25 points)

Four boats fish from one shared bay, drawing from the same fish stock.

Consider the simplified total and marginal framework from Lecture 4. Let E be total seasonal fishing effort, measured in boat-days, with 0\leq E\leq120. Total catch revenue and total opportunity cost are

TB(E)=120E-E^2,\qquad TC(E)=20E.

For E>0, average benefit is AB(E)=120-E. The marginal schedules are supplied so that you do not need calculus:

MB(E)=120-2E,\qquad MC(E)=AC(E)=20.

Effort is divisible. In the open-access model, entrants expect the average revenue per boat-day and may enter freely. Costs include the opportunity cost of labor and equipment. For this exercise, the given revenue curve summarizes the resource constraints; do not add a separate damage curve or solve a dynamic stock model.

(a) Efficient effort (5 points). Find E^*, total revenue, total cost, and economic rent TB-TC at the efficient outcome. Explain the marginal condition.

MB=MC:\quad120-2E=20\quad\Rightarrow\quad E^*=50.

TB(50)=120(50)-50^2=3{,}500,\qquad TC(50)=20(50)=1{,}000.

\text{Rent}^*=TB-TC=2{,}500.

The last boat-day adds $20 to total catch revenue and costs $20 in resources. Additional effort would add less revenue than its cost, reducing aggregate rent.

(b) Open-access effort (5 points). Find the positive open-access equilibrium E_{OA}, total revenue, total cost, and economic rent. Explain why entry is governed by AB=AC, rather than MB=MC.

For positive effort, entry stops where AB=AC:

120-E=20\quad\Rightarrow\quad E_{OA}=100.

TB(100)=2{,}000,\qquad TC(100)=2{,}000,\qquad \text{Rent}_{OA}=0.

An entrant compares its expected average revenue per boat-day with its own cost. It does not account for the reduction in other users’ returns. Consequently, the marginal contribution to total revenue is below the return the entrant expects to capture. At E^*=50, AB=70>20, so entry is still privately attractive.

(c) Two-panel graph (6 points). Draw TB and TC in a top panel, and AB, MB, and MC=AC in a bottom panel. Align the effort axes and mark E^* and E_{OA}. Calculate the rent lost under open access. Does zero economic rent mean that boats catch no fish or that fishers receive no income?

The efficient quantity maximizes the vertical gap TB-TC in the top panel and satisfies MB=MC below. The positive open-access outcome occurs where TB=TC and AB=AC.

Aligned fishery panels show total revenue and cost above and average benefit, marginal benefit, and marginal cost below. Efficient effort is 50 boat-days and positive open-access effort is 100.

Open access loses 2{,}500 in rent. The lower panel gives the same result: between 50 and 100, MC-MB rises from 0 to 100, so \tfrac12(100-50)(100)=2{,}500. Zero economic rent means receipts cover opportunity costs, including labor and equipment. It does not mean zero catch or zero gross income. The model still has $2,000 in catch revenue at open access.

(d) Resource type and rules (4 points; 100–140 words). Explain why a fish stock is a common-pool resource. Distinguish this physical characteristic from common property and open access. Would a defined community with enforceable access and effort rules necessarily reach E_{OA}? Explain.

A fish stock is rival because a fish caught by one boat is unavailable to another, and excluding users can be costly. These features make it a common-pool resource. Common property describes a governance arrangement: a defined community controls access and establishes rules. Open access instead means no effective exclusion. A community that monitors entry and enforces effort limits need not reach the open-access outcome. It could retain positive rents by limiting effort, although its success depends on compliance and enforcement. The physical characteristics of fish do not by themselves determine the rules or the final effort level.

(e) Costs through time (5 points; 100–140 words). A boat’s wake damages a shoreline today, and its catch leaves fewer fish available for later use. Distinguish Lecture 3’s externality cost from stock-scarcity cost in these examples. Explain why secure ownership could make a user account for future scarcity, yet still leave harm to shoreline owners outside that user’s decision.

Wake damage is a current externality cost when the boat does not bear the shoreline owner’s loss. Catching fish also creates a stock-scarcity cost by giving up later opportunities to use the stock. A secure owner who expects to receive future returns has an incentive to consider that opportunity cost. With shared or insecure access, part of the scarcity cost may fall on others and remain external to the current user’s decision. Secure ownership of the fishing resource does not automatically internalize wake damage to somebody else’s property; that separate effect still needs to enter the user’s incentives.

3. Lake Erie: algae, economic losses, and institutions (50 points)

A monitoring crew samples Lake Erie near a research buoy as a green algal bloom approaches a water intake, city shoreline, beach, and recreational boats.

Read Kaylee Wells’s Marketplace report, “How algae can crater Lake Erie’s economy” (July 6, 2026). The corresponding audio report appears in the July 6 episode, Back-to-school shopping? Already? A complete, lightly edited transcript of the Lake Erie report is provided below.

Transcribed from the supplied audio transcript and lightly edited for punctuation, speaker labels, and obvious automated-transcription errors.

Host (Kai Ryssdal): Every year, the National Oceanic and Atmospheric Administration predicts just how bad the algae are going to be on Lake Erie. The latest forecast is just out: a moderate harmful algal bloom is the estimate for the year. Those blooms are obviously a bummer for fish and for kids who want to go swimming, but they have massive economic implications, too, for people living nearby and for visitors. From the warm, slightly green waters of Lake Erie, Marketplace’s Kaylee Wells explains.

Reporter (Kaylee Wells): The blooms are a big enough deal that Lake Erie is dotted with little buoys constantly monitoring how much algae are in the water. It takes several minutes in a zippy speedboat to travel far enough offshore to see one up close. On the way, one of the scientists captures a jar full of water and holds it up to the light. It looks clear enough to drink. But then she throws a net with a filter on the end overboard and drags it through roughly a thousand gallons of water to reveal all the stuff we cannot see. The liquid remaining in the filter is murky, yellow-green, and scuzzy, with tiny zooplankton buzzing around and nipping at the green bits. In summer, the water temperature is near 70 degrees.

Scientist: We are certainly catching a lot of living stuff in the water.

Reporter: Ed Verhamme is our captain on today’s voyage. He is also a principal and senior engineer at LimnoTech, a consulting firm that helps make water cleaner.

Ed Verhamme: What we do not want is the harmful algae.

Reporter: That is the kind of algae that can cause diarrhea, vomiting, and rashes, and it is what his company helps monitor. Verhamme keeps driving until we arrive at a buoy. He pulls up the data it is capturing on his phone and relays the good news.

Ed Verhamme: Yep, really nothing going on out there right now, so these are very low readings.

Reporter: The recipe for high readings? Extremely heavy rainy periods, which pull nutrient-rich agricultural runoff into the lake, followed by extremely dry and sunny periods that help the algae form. This year has not been very extreme, which is why NOAA says it will be a moderate year for harmful algae. Verhamme says an especially bad year, like 2014, when algae contaminated Toledo’s water supply, would show readings 20 or 25 times higher than these, and the blooms would be very visible.

Ed Verhamme: That is noticeable scum. The water looks like paint, really.

Reporter: This year’s moderate forecast is not just good news for Lake Erie’s ecosystem. It means algae will not tank whole chunks of the Great Lakes economy this year. Lake Erie is the main source of drinking water for Northeast Ohio. Alex Margevicius, commissioner of Cleveland’s Water Division, says an algal bloom like the one in Toledo would be a doomsday scenario.

Alex Margevicius: I do not even know where to begin to calculate the economic impact of something like that. If greater Cleveland had to be under a do-not-drink-water advisory, what would happen?

Reporter: The background chatter comes from the State of the Great Lakes, an annual gathering of water experts and community members in downtown Cleveland. Clean water is a big deal here. The cost of algal blooms is calculated in more than bottled water and health-care bills.

Reporter: The $6 trillion economy of the Great Lakes Basin includes a huge tourism economy. Chris Ronayne is the executive of Cuyahoga County, which includes Cleveland.

Chris Ronayne: Lake Erie is the walleye capital of the world. People come here to fish. There are fishing tournaments and recreational anglers.

Reporter: When the algae get bad, they use up oxygen in the water, which causes mass fish kills—not an appealing feature in the walleye capital of the world. A hit to the tourism industry can have ripple effects, says Scott Hardy, an earth scientist with the Ohio State University.

Scott Hardy: That is not only going to affect the people who come to recreate. You have to think about the hotels where people stay. You have to think about the gas stations that fill the cars people drive to the water.

Reporter: Hardy says climate change is making the extreme weather, and the algal blooms that follow it, more common. But he also says we are getting better at mitigating the runoff that causes the blooms in the first place. Every year is therefore a toss-up in terms of how bad it will be. From the waters of Lake Erie, I am Kaylee Wells for Marketplace.

(a) Identify and explain the negative externality (8 points; 160–200 words)

Using Kaylee Wells’s Marketplace report, “How algae can crater Lake Erie’s economy”, the transcript provided above, and course terminology, explain why nutrient runoff associated with agricultural production is a negative production externality. Identify the private decision-maker and activity, at least two groups outside the market transaction that bear costs, and the external marginal cost (EMC) omitted from PMC. State how SMC, PMC, and EMC are related.

Using specific details, explain how nutrient loading creates the potential for harm, heavy rain transports nutrients into Lake Erie, and later dry, sunny weather affects bloom formation, timing, and severity. Conclude by explaining why an activity can be privately profitable but socially inefficient.

Agricultural producers are the private decision-makers in this application. They compare their own revenues and costs, but downstream water users, anglers, visitors, and tourism businesses may bear losses. Those losses are an external marginal cost omitted from PMC, so SMC=PMC+EMC. Heavy rain transports nutrient-rich runoff into the lake; later dry, sunny weather helps a bloom form. Thus nutrient loading supplies material for the bloom, while weather affects delivery, timing, and severity. Specific evidence includes the 2014 contamination of Toledo’s water supply, severe readings that could be 20 or 25 times higher, health symptoms, monitoring buoys, and possible fish kills. A privately profitable activity can therefore be socially inefficient when part of its marginal cost falls on others.

(b) Analyze rising marginal damage (10 points)

For parts (b)–(c), use this separate hypothetical watershed model. Q is units of agricultural output per season. Assume each unit creates one unit of nutrient runoff delivered to the lake, with no abatement option. The model is an illustration inspired by the reading, not an estimate reported by Marketplace:

MB(Q)=120-Q,\qquad PMC(Q)=20+Q,\qquad EMC(Q)=2Q.

Find Q_M, write SMC(Q), and find Q^*. Calculate total external damage at each quantity using the area under EMC. Find the constant per-unit tax that implements Q^* and the prices buyers pay and suppliers retain under it. On one graph, draw MB, PMC, SMC, and the supply curve with the tax; mark Q_M, Q^*, and the tax wedge.

The unregulated market has

120-Q=20+Q\quad\Rightarrow\quad Q_M=50,\quad P_M=70.

Social cost and the efficient quantity are

SMC(Q)=20+Q+2Q=20+3Q,

120-Q=20+3Q\quad\Rightarrow\quad Q^*=25.

Total damage is the triangle under EMC(Q)=2Q:

ED(Q)=\tfrac12 Q(2Q)=Q^2.

Thus ED_M=50^2=2{,}500 and ED^*=25^2=625.

t^*=EMC(25)=50,\qquad P_B=MB(25)=95,\qquad P_S=PMC(25)=45.

The fixed per-unit tax shifts private supply to PMC+t^*=70+Q. This taxed supply intersects MB at Q=25. It is not identical to SMC=20+3Q at every quantity; the two curves coincide at the desired quantity.

Hypothetical watershed curves show market quantity 50 and efficient quantity 25. Fixed-tax supply and social marginal cost meet demand at 25 but have different slopes. A vertical segment labels the 50-dollar tax wedge, and the shaded deadweight loss is 1250 dollars.

(c) Account for welfare (10 points)

Calculate tax revenue and remaining external damage at Q^*. Are they equal? Explain why a Pigouvian tax need not equal total remaining damage when EMC rises with Q. Calculate the welfare gain using the deadweight-loss triangle. Then verify it by calculating CS, PS, tax revenue, external damage, and SW before and after the tax in a table.

TR=t^*Q^*=50(25)=1{,}250,\qquad ED^*=625.

Tax revenue is twice remaining damage in this example. The tax charges the marginal harm at the efficient quantity on every unit, whereas total damage sums the harm over all units. Because marginal harm rises from zero, the tax rectangle is twice the damage triangle. Equality between revenue and remaining damage is neither a general property nor a requirement of an efficient Pigouvian tax.

At Q_M=50, SMC=170 and MB=70. Therefore

DWL_M=\tfrac12(50-25)(170-70)=1{,}250.

The surplus calculations verify this:

CS_M=\tfrac12(120-70)(50)=1{,}250,\qquad PS_M=\tfrac12(70-20)(50)=1{,}250,

SW_M=1{,}250+1{,}250-2{,}500=0.

CS_T=\tfrac12(120-95)(25)=312.5,\qquad PS_T=\tfrac12(45-20)(25)=312.5,

SW_T=312.5+312.5+1{,}250-625=1{,}250.

Seasonal measure Unregulated Corrective tax
Quantity 50 25
Consumer surplus 1,250 312.5
Producer surplus 1,250 312.5
Tax revenue 0 1,250
External damage 2,500 625
Social welfare 0 1,250

(d) Classify information and the fishery (6 points; 120–160 words)

Case assumption: Suppose the buoy readings are posted online for anyone to use. Apply rivalry and excludability to classify the posted information. Contrast it with a walleye removed from the lake and explain why the fish stock is a common-pool resource. Finally, explain whether better public information alone gives upstream producers an incentive to include downstream runoff damage in their production decisions.

Openly posted buoy readings are nonrival because one person’s use does not reduce their usefulness to another, and they are effectively nonexcludable when anyone can access them. The information therefore has public-good characteristics under the case assumption. A harvested walleye is rival because the same fish cannot be caught by another person. Because fish are rival and controlling access to a mobile stock can be difficult, the stock is a common-pool resource. Better information can help water managers, residents, and visitors respond to a bloom. By itself, however, it does not require upstream producers to bear downstream damage or reward them for reducing nutrient loss, so it does not internalize the runoff externality.

(e) Recommend an institution (10 points; 200–250 words)

Case assumptions: Nutrient runoff comes from many farms, individual contributions are not directly observed, and rainfall changes how much nutrient reaches the lake. Compare these three approaches:

  • a charge on measured runoff;
  • a required protective farming practice; and
  • judicial liability for downstream harm.

For each approach, identify what must be measured or verified and who initially pays. Explain why lakewide buoy readings reveal lake conditions but do not identify each farm’s contribution. Recommend one approach as the main policy, state one important limitation, and explain why a tax on agricultural output becomes an imperfect substitute for a runoff charge when the assumed one-to-one relationship between output and runoff is relaxed.

A runoff charge makes avoiding an additional unit of measured pollution privately valuable while allowing producers to choose how to respond. Producers initially remit the charge and pay adjustment costs, though some costs may be passed to buyers. A credible charge requires a defensible measure of each source’s delivered runoff. A required protective practice offers a more observable compliance target, though compliance may produce different environmental benefits across sites. Farms initially bear its installation, maintenance, and compliance costs unless a subsidy or cost-sharing program shifts part of those costs. Judicial liability can reward prevention when producers expect to pay for attributable harm, but courts must establish causation and damages.

Lakewide buoy readings show ambient conditions; they do not identify which farm contributed each unit of nutrient. Many sources and variable rainfall therefore make attribution difficult. Given weak source-level measurement, I would begin with targeted, verifiable protective-practice requirements in high-risk locations, inspections, and credible penalties. This approach sacrifices some flexibility for observability. Its limitation is that the same practice can be costly or ineffective at different sites, so verified equivalent practices should be allowed where feasible. An output tax becomes a poor runoff proxy when farms can alter practices or when the same output produces different nutrient losses: it gives no direct reward for cleaner production at unchanged output.

(f) Interpret claims about economic losses (6 points; 130–170 words)

The report describes the Great Lakes Basin as a $6 trillion economy and notes possible effects on hotels and gas stations. Explain why $6 trillion is not an estimate of damage from a Lake Erie bloom. Explain why adding every affected firm’s lost sales could overstate welfare loss. Your answer must include examples to support your explanation.

The $6 trillion figure describes the scale of economic activity in the Great Lakes Basin, not the change in welfare caused by a bloom. Only the portion affected by the event is relevant. Lost sales also differ from welfare loss because a hotel that serves fewer guests may avoid housekeeping or supply costs, and visitors may spend at another destination. Adding a hotel’s lost sale, the visitor’s entire forgone trip spending, and the gas station’s lost sale can count related transactions more than once. A careful estimate measures changes in surplus and real resource costs. Sales records can also miss direct or nonmarket losses, including drinking-water disruption, health risk, fish mortality, and the lost enjoyment of swimming or fishing.

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