1. Other greenhouse gases include methane (CH4) and nitrous oxide (N2O), but carbon dioxide (CO2) accounts for 80 percent of U.S. greenhouse gas emissions. Throughout this brief, we use “carbon” as a stand-in for carbon dioxide and the other greenhouse gases. See “Overview of Greenhouse Gases,” Environmental Protection Agency, July 27, 2021.
2. Degrowth proponent Jason Hickel calls for stabilizing world GDP in order to prevent environmental catastrophe. As for concerns that degrowth freeze poverty and reduce welfare, Hickel says that an interventionist approach would achieve both environmental improvement and welfare enhancement that capitalism is unable to provide. Hickel states: “This should not come as a surprise, because the point of capitalism is surplus extraction, elite accumulation, and reinvestment for expansion—not meeting human needs. To the extent that the system does meet human needs, this is generally the result of political interventions (i.e., unions, labour rights, public provisioning, etc.).” Jason Hickel, “Degrowth,” jasonhickel.org (blog), October 27, 2020.
3. A report by the Breakthrough Institute, a climate think tank, says that climate change “now represents a near- to mid-term existential threat to human civilization” and that “to reduce or avoid such risks and to sustain human civilisation, it is essential to build a zero-emissions industrial system very quickly. This requires the global mobilization of resources on an emergency basis, akin to a wartime level of response.” See David Spratt, Ian Dunlop, and Admiral Chris Barrie, “Existential Climate-Related Security Risk: A Scenario Approach,” Breakthrough Institute Policy Paper, May 2019.
4. In fact, the higher bid increases welfare, since the seller now gets a higher price and the winner bidder’s willingness to pay for the auctioned good should be higher than the outbid party.
5. William Nordhaus, “Estimates of the Social Cost of Carbon: Concepts and Results from the DICE-2013R Model and Alternative Approaches,” Journal of the Association of Environmental and Resource Economists 1, nos. 1/2 (2014): 273–312.
6. In this example we are assuming perfect competition, so the price equals the marginal costs to producers. More generally, prices could be anywhere between $4.00 and $4.50 for the transaction to happen.
7. Total economic surplus is the difference between total benefits and total costs in dollar terms ($4.50 benefits to the driver minus the $4.00 costs to the retailer and the $1.00 negative externalities).
8. Ronald Coase, “The Problem of Social Cost,” in Classic Papers in Natural Resource Economics, ed. Chennat Gopalakrishnan (London: Palgrave Macmillan, 1960), pp. 87–137.
9. In our example, the driver gets a surplus of $0.50 ($4.50 worth of benefits minus the $4.00 paid to the retailer); likewise, the retailer gets $0 worth of surplus ($4.00 price minus the $4.00 of costs). Adding externalities of −$1.00, this yields a surplus of −$0.50. When the filter is installed, negative externalities disappear, but the driver gets a surplus of $0, since he must pay an extra $0.50 per gallon for the filter.
10. Federal and state governments regulate energy efficiency standards for all household appliances, including boilers, ceiling fans, refrigerators, furnaces, TVs, and more, not to mention water savings standards for dishwashers, faucets, toilets, and showerheads. See National Appliance Energy Conservation Act of 1987, Pub. L. No. 100–12, 101 Stat. 103 (1987); and Energy Policy Act of 2005, Pub. L. No. 109–58, 119 Stat. 594 (2005).
11. See, for example, “Greenhouse Gas Reporting Program (GHGRP),” Environmental Protection Agency, November 9, 2021, https://www.epa.gov/ghgreporting.
12. For a comprehensive review of state and federal tax credits, check “Database of State Incentives for Renewables and Efficiency (DSIRE),” N.C. Clean Energy Technology Center (North Carolina State University), November 16, 2021, https://www.dsireusa.org/. There are 30 federal policies in place and 170 state policies in California.
13. Federal Support for Developing, Producing, and Using Fuels and Energy Technologies, Before the Subcommittee on Energy Committee on Energy and Commerce U.S. House of Representatives, 115th Cong. (March 29, 2017) (testimony of Terry Dinan, Senior Adviser of the Microeconomic Studies Division of the Congressional Budget Office).
14. “FEDS Notes: Climate Change and Financial Stability,” Board of Governors of the Federal Reserve, March 19, 2021.
15. Going back to our earlier example, we had a driver willing pay up to $4.50 for an extra gallon and a retailer willing to accept $4.00 to sell it, but this had a marginal negative externality of burning the fuel of $1.00. A government-mandated emissions filter would cost this driver an average of $0.50 per gallon to prevent $1.00 worth of negative externalities. This is clearly efficient, but the emissions filter involves a fixed cost. If another buyer drives significantly less, it could be that the filter now costs more than $1.00 per gallon to prevent only $1.00 of externalities. In this case, the filter mandate would be inefficient.
16. Meredith Fowlie, Michael Greenstone, and Catherine Wolfram, “Do Energy Efficiency Investments Deliver? Evidence from the Weatherization Assistance Program,” NBER Working Paper no. 21331, July 2015.
17. Steven E. Sexton et al., “Heterogeneous Environmental and Grid Benefits from Rooftop Solar and the Costs of Inefficient Siting Decisions,” NBER Working Paper no. 25241, November 2018.
18. Severin Borenstein, “Private Net Benefits of Residential Solar PV: The Role of Electricity Tariffs, Tax Incentives, and Rebates,” Journal of the Association of Environmental and Resource Economists 4, no. S1 (2017): S85–122.
19. Stephen P. Holland et al., ”Environmental Benefits from Driving Electric Vehicles?,” NBER Working Paper no. 21291, June 2015.
20. Jianwei Xing, Benjamin Leard, and Shanjun Li, “What Does an Electric Vehicle Replace?,” Journal of Environmental Economics and Management 107 (2021): 102432.
21. S. Panero et al., “Impact of Household Batteries in Landfills,” Journal of Power Sources 57, nos. 1–2 (1995): 9–12. Energy storage provided by EVs can also increase carbon emissions because it makes sources that are more expensive to turn on and off, such as coal, relatively cheaper (for example, by absorbing cheap coal energy overnight and discharging it during the day when other cleaner sources are used). See Eric S. Hittinger and Inês M.L. Azevedo, “Bulk Energy Storage Increases United States Electricity System Emissions,” Environmental Science and Technology 49, no. 5 (2015): 3203–10.
22. We are assuming the benefits of the emissions filter go to $0 in this case. It is important to note that it makes no difference whether nominally the retailer or the driver is forced to bear the cost of the improvement. Economic incidence of costs depends on elasticities of demanders and suppliers.
23. Bento et al. survey recent evidence on rebound effects and find estimates varying from a 0 to 15 percent rebound (a 15 percent rebound means that a 100 percent efficiency gain would translate only to a 85 percent decrease in fuel savings). See Antonio M. Bento et al., “Estimating the Costs and Benefits of Fuel-Economy Standards,” Environmental and Energy Policy and the Economy 1, no. 1 (2020): 129–57.
24. Roger H. Bezdek and Robert M. Wendling, “Potential Long-term impacts of changes in US vehicle fuel efficiency standards,” Energy Policy 33, no. 3 (2005): 407–19.
25. Mark R. Jacobsen and Arthur A. Van Benthem, “Vehicle Scrappage and Gasoline Policy,” American Economic Review 105, no. 3 (2015): 1312–38.
26. Valerie J. Karplus et al., “Should a Vehicle Fuel Economy Standard Be Combined with an Economy-Wide Greenhouse Gas Emissions Constraint? Implications for Energy and Climate Policy in the United States,” Energy Economics 36 (2013): 322–33.
27. Arik Levinson, “How Much Energy Do Building Energy Codes Save? Evidence from California Houses,” American Economic Review 106, no. 10 (2016): 2867–94.
28. “Carbon Tax,” IGM Forum, University of Chicago, December 20, 2011, https://www.igmchicago.org/surveys/carbon-tax/.
29. Discount rates are a way to compare benefits and costs across time. For the social cost of carbon estimates, see Kevin Rennert et al., “The Social Cost of Carbon: Advances in Long-Term Probabilistic Projections of Population, GDP, Emissions, and Discount Rates,” Resources for the Future Working Paper no. 28, September 2021.
30. Using mean estimates of social costs of carbon $125 per metric ton of CO2 and the fact that one gallon of gasoline emits 8.887 x 10−3 metric tons of CO2, one gets a rough estimate of $1.00 (more precisely, $1.11) worth of carbon costs per extra gallon of fuel burnt.
31. In Brazil, for example, gasoline costs roughly $4.18 per gallon (Brazilian Real (BRL) 22.74 per 3.79 liters, using an exchange rate of 5.44 BRL/USD), 39 percent of which are taxes, amounting to a total tax bill of approximately $1.60 per gallon. See “Preços de Venda de Combustíveis,” Petrobras, October 4, 2021.
32. Economist Greg Mankiw has created the “Pigou Club,” named after economist Arthur Cecil Pigou, who lends his name to Pigouvan taxes (externality correcting taxes). The informal club, whose members include Daron Acemoglu, Noam Chomsky, Bill Gates, and Leonardo DiCaprio, publicly advocates for carbon and other Pigouvian taxes.
33. Some economists favor an approach where governments set targets or objectives and award prizes for them to sponsor innovation. Alternatively, government could precommit to buy a product, say carbon dioxide capture and storage, at a given price; these are called advanced markets commitments (AMCs). This approach has the advantage of avoiding government micromanagement and incentivizing private firms to innovate. The main problem, of course, is knowing what to award the prize for and how to set an appropriate award amount. For more details on these mechanisms, see Michael Kremer, Jonathan Levin, and Christopher M. Snyder, “Advance Market Commitments: Insights from Theory and Experience,” AEA Papers and Proceedings 110 (2020): 269–73; and Alexander Tabarrok, “Grand Innovation Prizes to Address Pandemics: A Primer,” Mercatus Center Special Edition Policy Brief, March 19, 2020.
34. Arianna Di Paola, et al., “The Expansion of Wheat Thermal Suitability of Russia in Response to Climate Change,” Land Use Policy 78 (2018): 70–77; and Charles A. Taylor and Wolfram Schlenker, “Environmental Drivers of Agricultural Productivity Growth: CO2 Fertilization of US Field Crops,” NBER Working Paper no. 29320, October 2021.
35. Because internal costs (i.e., costs to parties to a transaction) are already factored into prices, a carbon tax should reflect only the external costs of carbon intensive activities. So, the marginal social cost of carbon, for the purposes of carbon taxation, should only take into account external costs.
36. It is unclear whether uncertainty should lead us to take earlier and stronger action as a form of insurance, since reducing emissions also requires sunk investment costs, prompting us to postpone actions. For more details, see Robert S. Pindyck, “What We Know and Don’t Know about Climate Change, and Implications for Policy,” Environmental and Energy Policy and the Economy 2, no. 1 (2021): 4–43.
37. Pei Wang et al., “Estimates of the Social Cost of Carbon: A Review Based on Meta-Analysis,” Journal of Cleaner Production 209 (2019): 1494–507.
38. Rennert et al., “The Social Cost of Carbon.”
39. Duty drawbacks are refunds on duties, taxes, and fees paid on goods that are imported and subsequently exported, either unused or after processing. Taking our example, where country A imports from country B, this would amount to an intermediary country C importing from country B and reexporting the good to A. As a result, country A would carbon tax the imported good as if it were coming from C, but it would in fact be produced in B and pay no fees or taxes in C due to drawbacks.
40. A businessman, for example, was found guilty in 2020 of a $1 billion biodiesel tax fraud scheme that worked by creating fake paperwork for biodiesel production to collect IRS tax credits. See “Jury Finds Los Angeles Businessman Guilty in $1 Billion Biodiesel Tax Fraud Scheme,” Justice News, March 16, 2020.
41. See, for example, Michael Greenstone and Ishan Nath, “Do Renewable Portfolio Standards Deliver Cost-Effective Carbon Abatement?,” University of Chicago, Becker Friedman Institute for Economics Working Paper no. 2019–62 (2020). The paper finds that renewable portfolio standards (i.e., mandating renewable sources to produce a specified share of electricity) caused electricity prices to be 11 percent higher after seven years of being enacted.
42. Soren T. Anderson, Ioana Marinescu, and Boris Shor, “Can Pigou at the Polls Stop Us Melting the Poles?,” NBER Working Paper no. 26146, August 2019.
43. David Roberts, “Washington Votes No on a Carbon Tax—Again,” Vox, November 6, 2018.
44. Lucas W. Davis, “The Environmental Cost of Global Fuel Subsidies,” Energy Journal 38, KAPSARC Special Issue (2017): 7–27.
45. Gary M. Lucas Jr., “Voter Psychology and the Carbon Tax,” Temple Law Review 90 (2017): 1.