Pigouvian compendium

We’ve already established that I’m a fan of Pigouvian taxes and correcting externalities. The harms I visit on my neighbor should be the result of malice aforethought; we should have to look each other in the eye rather than shrug in world-weary acknowledgment of systemic perversities. Because of that interest, I wanted a sense of the total magnitude of Pigouvian taxation possible. Are American GDP numbers the result of accounting fraud that would put Enron to shame? How much would American production numbers decrease if we accounted for externalities? If the federal government shared my zeal for technocratic delights, how much of the federal budget could be funded by Pigouvian taxes? How much would an individual’s annual expenses increase if they’d internalized all their externalities and been absolved of their sins?

To answer those questions, I reviewed the academic literature and found every proposed Pigouvian tax I could. I did not include:

General sin taxes
Public health practitioners and others sometimes talk about taxing certain goods on the grounds that they correct for irrationality. Plebes People don’t know about the long-term harmful effects of sugary drinks or lack self-control, for example. Or cigarette taxes should be increased to stop people from enjoying themselves killing themselves prematurely. While there are reasonable arguments (despite the snark above) in support of such taxes, these aren’t the same as Pigouvian taxes. Pigouvian taxes correct for externalities and arise even with rAtIoNaL actors due to inherent failures of markets; these other taxes try to nudge toward actions that don’t create externalities and wouldn’t occur with rAtIoNaL actors.
Uncalibrated taxes
There are many jurisdictions that have taxes on externality-producing consumption—think cigarette taxes or alcohol taxes. However, these are just as likely to be the result of smoky backroom deals as of analysis grounded in an estimation of the externalities imposed by consumption. Thus, I excluded them and only looked for taxes (real or proposed) where numbers were intended to precisely ‘internalize’ externalities.

The results of this review are presented in the table below. The externalities associated with emitting carbon and driving are the largest by far. If we sum up all the known externalities listed in the table, we find that they come to $679 billion per year in the US. This is around 3.5% of US GDP and around 15% of US federal spending. The per capita cost of these externalities is around over $2150 per year. (The sum of externalities is described on annual basis and so excludes quantities which are stocks rather than annual flows. In particular, obesity and SME debt are current totals rather than annual changes.)

Taxable externalities in the US
Activity Externalities $ per unit Unit Total quantity Total $ Total $ as % of GPD Total $ per capita Data year
Driving Local pollution, global warming, crashes, congestion 2.15 Gallon 143 billion per year 307 billion per year 1.6 943
per year
Emitting carbon Global warming 144 Tonne 1.46 billion per year 210 billion per year 1.1 644
per year
Obesity Socialized healthcare spending 192 BMI 990 million 190 billion N/A 583 2012
Drinking alcohol Lost productivity, medical care, car crashes, crime 37 Liter 2.5 billion per year 92.5 billion per year 0.5 284
per year
Agriculture Damage to natural capital and human health 80 Hectare 431 million per year 34.5 billion per year 0.17 104
per year
Municipal waste Environmental costs 77 Ton 262 million per year 20.1 billion per year 0.1 62
per year
Smoking Medical issues, fires 0.54 Pack 13.35 billion per year 7.21 billion per year 0.04 22
per year
Antibiotic use Antibiotic resistance 110 Pound 25.4 million per year 2.79 billion per year 0.01 8.57
per year
Household debt Social borrowing constraint 0.0048 Dollar 557 billion per year 2.67 billion per year 0.001 8.20
per year
SME debt Social borrowing constraint 0.0056 Dollar 5.34 trillion 29.9 billion N/A 90 2009
Guns Unintentional killings 138 Gun 16.2 million per year 2.26 billion per year 0.01 6.90
per year
Drinking soda Obesity-related publicly-provided healthcare costs Unknown Liter 4.82 billion per year Unknown Unknown Unknown 2013
Gambling Problem gamblers, undermining government authority, organized crime Unknown Dollar 137 billion per year Unknown Unknown Unknown 2014
Finance Speculation, races, insolvency Unknown Unknown Unknown Unknown Unknown Unknown N/A
Total 679 billion 3.6 2156


A truck with an evil green goblin on the front
A direct regulation alternative—mandatory goblin masks for all motor vehicles—to Pigouvian taxes could also help us understand the evils of driving.

Everyone knows they’re killing the planet one mile at a time when they drive. What’s perhaps less obvious is that this is the least terrible thing about driving. The table below shows estimates of the many external costs of driving1. While driving’s contribution to global warm costs 8.5 cents per gallon, the external costs of collisions clock in at 73 cents per gallon. The proper Pigouvian tax that would internalize all the externalities is estimated at $2.15 per gallon. This is substantially larger than the current fuel tax in the US which averages 48 cents per gallon and is, interestingly, substantially lower than the current fuel tax in many European countries.

Summary of external costs of driving
cents/gal cents/mile
Central values for marginal external costs
 Fuel-related costs
  Greenhouse warming 8.5 0.4
  Oil dependency 15 0.7
  Sum 23 1.2
 Mileage-related costs
  Local pollution 56 2.8
  Congestion 85 4.3
  Accidents 73 3.7
  Sum 215 11
Data from (Parry, Walls, and Harrington 2007) and updated to 2018 dollars. The original source assumes an on-road fuel economy of 20 miles per gallon for the purpose of converting between cents/gal and cents/mile. That seems somewhat dubious to me, but we’ll go with it.

Brief explanation of the less obvious externalities:

When I pile into a traffic jam, everyone behind me is slowed down yet more.
“[W]hen I drive, I make it more likely that you will be in an accident. That is an external cost, which from an economic standpoint is equivalent to pollution. The numbers here are staggering. According to the US National Highway Traffic Safety Administration, there are more than 30 million traffic accidents a year. It estimates that the annual dollar cost of accidents, including property damage and personal injury, amounts to more than $400 billion a year.” (Parry, Walls, and Harrington 2007)

Okay, I lied when I said $2.15 per gallon “would internalize all the externalities”. There are more externalities not in that table (omitted because their harms don’t track fuel and mileage very well) because driving is a slow-motion apocalypse:

  • Noise
  • Highway maintenance costs
  • Urban sprawl
  • Parking subsidies
  • Other environmental externalities


William Nordhaus was one of this year’s fake Nobel Prize winners for his work on climate change. In (Nordhaus 2007), he suggests an initial carbon tax of $50 per tonne of carbon which would increase by 2-3% a year in real terms until 2050 and steeper increases after that.

Such a carbon tax is, of course, intended to correct for the external harms of global warming.

But Nordhaus isn’t the only person working to produce such inconvenient truths. There’s a whole slew of estimates of the social cost of carbon. Toward the other end of the spectrum is (Stern and others 2007) which estimates a social cost of carbon around $340 per tonne. Because global warming plays out over decades and centuries, the pure rate of time preference2 is one of the key determinants of the final number.

Weighted summary of estimates of social cost of carbon in $/tonne
All 0% 1% 3%
Mean 249 233 198 82
Std Dev 447 256 244 101
Mode 68 134 81 41
Median 144 191 150 59
95th %tile 884 804 676 338
Data from (Tol 2009) and update to 2018 prices

The median from this table is the number that made it into the table at the top.


America has, variously, a crisis, an epidemic (Wang and Beydoun 2007), and an apocalypse of obesity. Regardless of the descriptor, (Finkelstein et al. 2009) finds that the obese spend almost $1,500 more per year on medical services and that Medicare and Medicaid account for at least half of this increased spending3. “We estimate that a 1-unit increase in BMI for every adult in the United States would increase annual public medical expenditures (i.e., direct medical costs) by $38.7 billion; an average marginal cost of $175 per year per unit of BMI for each adult in the United States.” (Parks et al. 2012)

This is probably the right moment to bring up (again) that Pigouvian taxes are not a good response to all externalities (Fleischer 2015). In particular, a one point increases in BMI is very harmful to the health of some while it’s healthful for others. Thus, a tax which penalizes all weight gain equally could be called a Procrustean Pigouvian tax. It’s also worth pointing out that the optimal weight from a public health perspective isn’t settled (Afzal et al. 2016).


Coming next in our countdown is a classic sin tax—alcohol. There’s yet more double-counting between this and driving because the biggest alcohol-related externality is drunk driving. With a 5% discount rate, the cost breakdown is as follows:

External costs of heavy drinkers
External costs $/excess ounce
Medical and pension costs per excess ounce 0.00
 Medical care 0.23
 Sick leave 0.12
 Group life insurance 0.05
 Nursing home ~0
 Retirement pension 0.07
Lost taxes on earnings 0.14
Net medical and pension costs per excess ounce 0.60
Motor-vehicle accidents and criminal justice costs 0.00
 Lives of nondrinkers 1.33
 All other costs 0.81
Total net costs 2.74
Data from (Manning et al. 1989) updated to 2018 dollars.

(One very dubious part of (Manning et al. 1989) is that it counts harms to family members as internal rather than external.)

Because “nearly all external costs are caused by 10% of the drinking population who consume one-third to one-half of all alcohol sold” (Cnossen 2007) a targeted tax on excess drinking as (Manning et al. 1989) calculates would be the first best option. Alas, it’s far from obvious how this targeting would be implemented. We adjust the tax to look at total alcohol consumption then. (Manning et al. 1989) reports that 40% of alcohol consumption is in excess of two drinks per day (their definition of ‘excess drinking’). Multiplying “Total net costs” by 0.4 gets us the final cost of $1.10 per ounce ($37 per liter) which appears in the top table. ((Harwood 2000) gives a broadly similar estimate of $62 per liter.)


I know we’re not supposed to speak ill of that most sacred American—the farmer—but modern intensive agriculture creates lots of external harms in the process of food production. Broadly, these harms can be categorized as harms to natural capital and harms to human health. They total up to $34 billion and are broken down in more detail in the following table:

The annual external costs of modern agriculture in the USA
Cost Category $ million
1. Damage to natural capital: water
 a) Pesticides in sources of drinking water 851
 b) Nitrate, phosphate and soil in sources of drinking water 1170
 c) Zoonoses (esp. Cryptosporidum) in sources of drinking water * 360
 d) Eutrophication, pollution incidents, fish deaths, monitoring costs 244
2. Damage to natural capital: air
Emissions of methane, ammonia, nitrous oxide and carbon dioxide 15720
3. Damage to natural capital: soil
 a) Off-site damage caused by erosion 0
  i) Flooding, blocked ditches and lost water storage 3288
  ii) Damage to industry, navigation and fisheries 8287
 b) Organic matter and carbon dioxide losses from soils * 1286
4. Damage to natural capital: biodiversity and landscape
 a) Biodiversity/wildlife losses 313
 b) Hedgerows and drystone wall losses 1
 c) Bee colony losses and damage to domestic pets 218
5. Damage to human health: pesticides 126
6. Damage to human health: nitrate 1
7. Damage to human health: micro-organisms/disease agents
 a) Bacterial and viral outbreaks in food * 2648
 b) BSE and new variant CJD 1
 c) Overuse of antibiotics 1
Total annual external costs 34516
Total costs per hectare of arable and grassland 0.000080

Data from (Pretty et al. 2001) and updated to 2018 dollars using a 1996 exchange rate of 1.12 €/$ and inflation adjustment of 1.61 $2018/$1996

Rows marked with * are interpolated from UK figures using £9.9 billion of UK agricultural output, $138 billion of US agricultural ouptut and an exchange rate of 1.27 $/£.

The figures above are likely to underestimate the true size of external harms in agriculture:

  • some costs are known to be substantial underestimates (for example, acute and chronic pesticide poisoning of humans, monitoring costs, eutrophication of reservoirs and restoration of all hedgerow losses);
  • some costs currently cannot be calculated (for example, dredging to maintain navigable water, flood defences, marine eutrophication and poisoning of domestic pets);
  • the costs of returning the environment or human health to pristine conditions were not calculated;
  • treatment and prevention costs may be underestimates of how much people might be willing to pay to see positive externalities created;
  • the data do not account for time lags between the cause of a problem and its expression as a cost (i.e. some processes long since stopped may still be causing costs; some current practices may not yet have caused costs);
  • this study did not include the externalities arising from transporting food from farms to manufacturers, processors, retailers and finally to consumers.
(Pretty et al. 2001)

Municipal waste

As the malodor makes obvious when passing by a garbage dump, municipal solid waste isn’t entirely inert. It leaches into water and off-gases. These environmental harms are external to the initial disposal.

Unfortunately, as we get further down the list, finding good estimates of these costs gets harder and harder. (Repetto et al. 1992) estimates non-market costs of $135/ton of municipal solid waste in high-cost areas and $81/ton in low-cost areas, but doesn’t really show the work that leads up to this conclusion. The table below has a more detailed breakdown but the numbers are focused on Puerto Rico. Regardless, the final estimate of $77 in the table up top is the average of the average estimates from both sources (that is, $108/ton from (Repetto et al. 1992) and $46/ton from (Miranda and Hale 1999)).

Environmental Cost Estimates for a Landfill (2018 dollars per ton)
Cost No methane flaring Methane flaring
Water emissions
 Leachate 0.0 1.6
Air emissions
 Methane 13.8–93.4 3.3–10.8
 Carbon dioxide 0.6–2.2 1.1–3.1
 Vinyl chloride 6.8–7.5 6.8–7.5
 Benzene 0.2–4.4 0.2–4.4
 Others 0.5–7.5 0.5–7.5
Total 21.7–116.7 11.8–35.0
Data found in (Fullerton 2005), originally from (Miranda and Hale 1999) and adjusted to 2018 dollars. (Miranda and Hale 1999) seems to be focusing exclusively on municipal solid waste in Puerto Rico. If that’s the case, it’s not obvious to me these numbers will generalize to the continental U.S. (Fullerton 2005) doesn’t note this limitation so perhaps he knows something I don’t?


We finally reach the other classic sin tax—smoking. Surprisingly, there seems to be fairly widespread belief that cigarette taxes are, if anything, too high to be justified on purely Pigouvian grounds. (Manning et al. 1989) is the seminal paper in this area and it answers its titular question in the affirmative—smokers do pay their way. The basic mechanism is that while “nonsmokers subsidize smokers’ medical care and group life insurance, smokers subsidize nonsmokers’ pensions and nursing home payments” (Manning et al. 1989). The breakdown showing this follows:

External cost per pack of cigarettes, 2018 dollars
Category 0% discount rate 3% discount rate 5% discount rate
Medical care 1.25 0.96 0.89
Sick leave 0.00 0.02 0.03
Group life insurance 0.42 0.24 0.16
Nursing home care -1.04 -0.40 -0.14
Retirement pension -5.03 -2.07 -0.64
Fires 0.02 0.03 0.03
Lost payroll taxes 1.53 0.70 0.21
Total net cost per pack -2.85 -0.52 0.54
Data from (Viscusi 1995) which calls it a reanalysis of (Manning et al. 1989). Adjusted to 2018 dollars.

Even at a 5% discount rate, which produces the highest estimate of external harms (other discount rates actually suggest that cigarette consumption has net positive externalities), $0.54 per pack is less than the current federal cigarette tax of $1.01 per pack.

All that said, there are several acknowledged omissions in these estimates. The big one is environmental tobacco smoke (ETS; secondhand smoke). At the time of the studies (and perhaps still?), the precise health effects of ETS were unknown so the costs weren’t included in the above estimates. (Chaloupka and Warner 2000) explains:

The potential role of ETS costs in reevaluating the net negative externalities associated with smoking is seen by considering the following figures. Manning et al. (1991) noted that inclusion of the costs of 2,400 lung cancers from ETS (a fairly conservative estimate of this toll (Environmental Protection Agency, 1992) ) as external costs would add approximately 19 cents per pack in external costs (updated to 1994 dollars). In addition, inclusion of the costs of neonatal care for smoking-related low- birth-weight babies would add 3 cents to the total, while including fetal deaths attributable to smoking would add yet another 19 cents. Deaths from smoking-related fires would add a further 9 cents. The ETS costs would skyrocket if one included the estimated 30,000-60,000 heart disease deaths recently associated with ETS (Glantz and Parmley, 1995), adding perhaps 70 cents to the total social costs per pack. Similarly, inclusion of the smoking-induced respiratory tract infections and cases of aggravated asthma in children (Environmental Protection Agency, 1992) would boost the total further, as would inclusion of the long-term developmental disabilities in smoking-related low-birth-weight babies (Hay, 1991). All told, the social costs per pack could easily mount toward several dollars if all of the health hazards associated with ETS are real, many are treated as external to the basic consuming unit, and if all or even a significant fraction of the associated costs are included.


The majority of antibiotics used in the US are used for animal agriculture (it’s those beloved farmers again)—18.4 million pounds in agriculture compared to 7.0 million pounds in human medicine. Regardless, antibiotic use leads to antibiotic resistance. This externality should be priced at “between 29 and 287€ per kilogram active substance or between 9 and 86% of the average price of commonly used antibiotics” (Vågsholm and Höjgård 2010). Using the 2010 exchange rate EUR/USD exchange rate of 0.75 and adjusting for inflation, we find that this works out to $20–$201/lb of active substance. Picking the middle of the range produces the estimate of $110/lb used in the top table. The total cost calculated is in broad agreement with the estimated national cost of between $100 million and $30 million reported in (Rudholm 2002).


Somewhat non-obviously, borrowing also has external costs. “A borrower who has one more dollar of liquid net worth when the economy experiences a bust relaxes not only his private borrowing constraint but also the borrowing constraints of all other insiders. Not internalizing this spillover effect, the insider takes on too much debt during good times.” (Jeanne and Korinek 2010)

On a percentage basis, this externality is small and procyclical—0.56 percent of outstanding debt for small and medium enterprises in a boom and 0.48 percent of outstanding debt for households in a boom (Jeanne and Korinek 2010). It only amounts to a sizable cost because the quantities of debt involved are so enormous. American households took on $556 billion of new debt in the year up through Q3 of 2018. SME outstanding debt totaled 5.34 trillion in 2009 (Jeanne and Korinek 2010) (I couldn’t find info on the current rate of SME debt increase.).


I couldn’t find any direct estimates of the externalities of firearms so I threw together my own estimate. The key number I sought was the number of accidental firearm killings of another person. I ruled out self-killings as internalities (Which is not strictly correct. If a child accidentally kills themselves with their parent’s gun, that’s an externality.). I ruled out intentional killings on the grounds that some unknown fraction of these would still occur even in the absence of guns. Clearly though, the resulting estimate is a conceptual lower bound.

(Xu et al. 2016) records 505 deaths from accidental discharge. (Hemenway, Barber, and Miller 2010) reports that in half of such fatalities, the victim was shot by another person.

In 2016, 16 million guns entered circulation in the U.S. (base on 11.5 million manufactured in the U.S., 376 thousand exported and 5.1 million imported).

Using an even $9 million as the value of a statistical life, we find that the estimated cost of 252 deaths is around $2.26 billion. We divide by the 16 million guns entering circulation to get $134 per gun sale as an order of magnitude estimate of the appropriate Pigouvian tax.


Even though the soda tax is a ‘popular’ policy, I couldn’t find any serious attempts to estimate the optimal Pigouvian tax for soda. Any attempt would be complicated by the fact that the marginal cost of soda consumption varies widely but systematically across consumers (Fleischer 2015)—it would be much higher for those at risk of type 2 diabetes, for example.


The three categories of external costs highlighted in (Clotfelter 2005) are:

Problem gamblers
Problems gamblers constitute ~2% of the adult population. They “driving themselves into bankruptcy, their families into hardship, and their personal relationships into ruin”. Their are inevitably social costs which accompany these problems.
Undermines government credibility
“Government, through its schools, laws, and public pronouncements, advocates certain beliefs, including the value of productive work. To the extent that the sponsorship and, particularly, the promotion of gambling undercut that traditional message, legalized gambling creates a second category of external costs.”
Organized crime
Lotteries don’t seem to do much to encourage organized crime but other forms of legalized gambling may.


The three categories of external costs highlighted in (Masur and Posner 2015) are:

“A transfer of money does not generate social value unless it is part of a transaction that reduces risk or otherwise enables people to spread receipts of money across times or states of the world in a way that advances their interests.”
“When new information about [current] events […] comes into existence, market participants will scramble to be the first to trade on the information. […] This activity is socially wasteful. […] [T]he broader market will not benefit at all if information about terrorism, as embodied in market prices, reaches them a nanosecond quicker than it otherwise does.”
“Short-term debt creates a negative externality. When a depositor or other short-term lender withdraws money, it increases the probability that the borrower will not have enough funds to pay other lenders when the loans are due or demanded. Those lenders will not be able to recover in full because of bankruptcy.”

Afzal, Shoaib, Anne Tybjærg-Hansen, Gorm B Jensen, and Børge G Nordestgaard. 2016. “Change in Body Mass Index Associated with Lowest Mortality in Denmark, 1976-2013.” Jama 315 (18). American Medical Association: 1989–96. https://jamanetwork.com/journals/jama/fullarticle/2520627.

Chaloupka, Frank J, and Kenneth E Warner. 2000. “The Economics of Smoking.” Handbook of Health Economics 1. Elsevier: 1539–1627. https://fjc.people.uic.edu/Presentations/Papers/handfinal.pdf.

Clotfelter, Charles T. 2005. “Gambling Taxes.” Theory and Practice of Excise Taxation: Smoking, Drinking, Gambling, Polluting, and Driving, 84–119.

Cnossen, Sijbren. 2007. “Alcohol Taxation and Regulation in the European Union.” International Tax and Public Finance 14 (6). Springer: 699–732. https://link.springer.com/content/pdf/10.1007/s10797-007-9035-y.pdf.

Cropper, Maureen L, Sema K Aydede, and Paul R Portney. 1994. “Preferences for Life Saving Programs: How the Public Discounts Time and Age.” Journal of Risk and Uncertainty 8 (3). Springer: 243–65. https://www.econ.umd.edu/sites/www.econ.umd.edu/files/pubs/jc25.pdf.

Finkelstein, Eric A, Justin G Trogdon, Joel W Cohen, and William Dietz. 2009. “Annual Medical Spending Attributable to Obesity: Payer-and Service-Specific Estimates.” Health Affairs 28 (5). Project HOPE-The People-to-People Health Foundation, Inc.: w822–w831. https://www.healthaffairs.org/doi/full/10.1377/hlthaff.28.5.w822.

Fleischer, Victor. 2015. “Curb Your Enthusiasm for Pigovian Taxes.” Vand. L. Rev. 68. HeinOnline: 1673. https://digital.sandiego.edu/cgi/viewcontent.cgi?referer=https://scholar.google.com/&httpsredir=1&article=1004&context=law_fac_works.

Fullerton, Don. 2005. “An Excise Tax on Municipal Solid Waste.” Theory and Practice of Excise Taxation: Smoking, Drinking, Gambling, Polluting, and Driving. Oxford University Press, 155–92.

Harwood, Hendrick. 2000. “Updating Estimates of the Economic Costs of Alcohol Abuse in the United States: Estimates, Update Methods, and Data.” The National Institute on Alcohol Abuse and Alcoholism, 2000.

Hemenway, David, Catherine Barber, and Matthew Miller. 2010. “Unintentional Firearm Deaths: A Comparison of Other-Inflicted and Self-Inflicted Shootings.” Accident Analysis & Prevention 42 (4). Elsevier: 1184–8.

Manning, Willard G, Emmett B Keeler, Joseph P Newhouse, Elizabeth M Sloss, and Jeffrey Wasserman. 1989. “The Taxes of Sin: Do Smokers and Drinkers Pay Their Way?” Jama 261 (11). American Medical Association: 1604–9. https://www.rand.org/content/dam/rand/pubs/notes/2009/N2941.pdf.

Masur, Jonathan S, and Eric A Posner. 2015. “Toward a Pigouvian State.” U. Pa. L. Rev. 164. HeinOnline: 93. https://chicagounbound.uchicago.edu/cgi/viewcontent.cgi?referer=https://scholar.google.com/&httpsredir=1&article=12110&context=journal_articles.

Miranda, Marie Lynn, and Brack Hale. 1999. “Re-Covering All the Bases: A Comparison of Landfills and Resource Recovery Facilities in Puerto Rico.” Nickolas School of the Environment, Duke University. Citeseer. http://citeseerx.ist.psu.edu/viewdoc/download?doi=

Nordhaus, William D. 2007. “A Review of the Stern Review on the Economics of Climate Change.” Journal of Economic Literature 45 (3): 686–702. http://piketty.pse.ens.fr/files/Nordhaus2007b.pdf.

Parks, Joanna C, Julian M Alston, Abigail M Okrent, and others. 2012. “The Marginal External Cost of Obesity in the United States.” Robert Mondavi Institute Center for Wine Economics Working Paper 1201. https://ageconsearch.umn.edu/bitstream/162519/2/cwe1201.pdf.

Parry, Ian WH, Margaret Walls, and Winston Harrington. 2007. “Automobile Externalities and Policies.” Journal of Economic Literature 45 (2): 373–99. http://citeseerx.ist.psu.edu/viewdoc/download?doi=

Pretty, Jules, Craig Brett, David Gee, Rachel Hine, Chris Mason, James Morison, Matthew Rayment, Van Der BijlGert, and Thomas Dobbs. 2001. “Policy Challenges and Priorities for Internalizing the Externalities of Modern Agriculture.” Journal of Environmental Planning and Management 44 (2). Taylor & Francis: 263–83. http://citeseerx.ist.psu.edu/viewdoc/download?doi=

Repetto, Robert, Roger C Dower, Robin Jenkins, and Jacqueline Geoghegan. 1992. Green Fees: How a Tax Shift Can Work for the Environment and the Economy. World Resources Institutes. http://www.actrees.org/files/Policy_Alerts/wri_greenfees.pdf.

Rudholm, Niklas. 2002. “Economic Implications of Antibiotic Resistance in a Global Economy.” Journal of Health Economics 21 (6). Elsevier: 1071–83.

Stern, Nicholas, and others. 2007. “The Economics of Climate Change: The Stern Report.” Cambridge, UK. http://mudancasclimaticas.cptec.inpe.br/~rmclima/pdfs/destaques/sternreview_report_complete.pdf.

Tol, Richard SJ. 2009. “The Economic Effects of Climate Change.” Journal of Economic Perspectives 23 (2): 29–51. https://pubs.aeaweb.org/doi/pdfplus/10.1257/jep.23.2.29.

Vågsholm, Ivar, and Sören Höjgård. 2010. “Antimicrobial Sensitivity—a Natural Resource to Be Protected by a Pigouvian Tax?” Preventive Veterinary Medicine 96 (1-2). Elsevier: 9–18.

Viscusi, W Kip. 1995. “Cigarette Taxation and the Social Consequences of Smoking.” Tax Policy and the Economy 9. National Bureau of Economic Research; The MIT Press: 51–101. https://core.ac.uk/download/pdf/6853452.pdf.

Wang, Youfa, and May A Beydoun. 2007. “The Obesity Epidemic in the United States—Gender, Age, Socioeconomic, Racial/Ethnic, and Geographic Characteristics: A Systematic Review and Meta-Regression Analysis.” Epidemiologic Reviews 29 (1). Oxford University Press: 6–28. https://academic.oup.com/epirev/article/29/1/6/440773.

Xu, Jiaquan, Kenneth D Kochanek, Sherry L Murphy, and Brigham Bastian. 2016. “Deaths: Final Data for 2013.”

  1. There is some double counting here—the externalities generated by driving already include the externalities of emitting carbon. But the bulk of driving externalities aren’t actually from carbon emission.

  2. See the recently linked (Cropper, Aydede, and Portney 1994) if you too want to marvel at the fact that the average Marylander would let you and your best friend die in five years to save one person today.

  3. If the one thing you take from this post is that stigma against fat people is deserved, you’re a bad person. The point of this post is that we’re all deserving of moral condemnation. Wait, no. That our politicians are deserving of condemnation for failing to implement good policy. Wait, no. That capitalism is deserving of condemnation.