6/21/17

Dear Cook County Board,

As you know, climate change is rapidly emerging as a profound threat to the long-term health and safety of global civilization as well as the people of Cook County. You may also be aware of efforts within our community to address that threat including those of two local organizations, The Nordic Nature Group and the Citizen’s Climate Lobby.

The Nordic Nature Group is a local environmental advocacy youth group with a mission to: Help Nature in good ways and take care of the Earth.

The Citizen’s Climate Lobby (CCL) is a national non-profit with several chapters in Minnesota including one right here in fabulous Cook County. CCL advocates for a climate change solution know as “” which is a national, revenue-neutral, carbon pricing policy developed to appeal to conservative values.

Our two organizations thank you for the opportunity to make a joint presentation to you on Tuesday, June 27th about climate change and climate change solutions, and to ask for your help in addressing this monumental challenge.

Earlier this year the Grand Marais City Council unanimously passed two resolutions concerning climate change (attached). Resolution 2017-04 directs the City to create a Climate Action Plan and was brought forward by the Nordic Nature Group. On the 27th, the Nordic Nature Group will present an update on their work with the City of Grand Marais and discuss with you the possibility of creating a Cook County Climate Action Plan sometime in the near future.

City resolution 2017-03 recognizes climate change as a threat to the City of Grand Marais and endorses Carbon Fee and Dividend with the intent of influencing our federal congressional delegation to consider this imminently viable climate change solution. This resolution was also passed by the Grand Marais Public Utilities Commission.

On the 27th, your local chapter of CCL will present an overview of the national Carbon Fee and Dividend policy and ask the Cook County Board to consider passing a resolution of endorsement similar to that passed by the City. 6/21/17

Of course, it’s no fun to take up a divisive national issue over which you have no direct control. Why risk inflaming local animosities? However, we urge you to do so for two main reasons: One, given the extent and severity of the climate change crisis, and the difficulty of implementing solutions, it is simply too vital to the future of our community to ignore this issue. And two, the difficult change required — a national carbon pricing policy — can only be accomplished through a grassroots political movement of which your resolution would be a small but essential part.

As you (hopefully) become familiar with the CFD proposal you will find an ocean of complexity. We suggest that not all the details of CFD need be worked out at this stage. But rather, if you come to believe this concept has merit, your resolution would be to endorse the initiation of a national legislative process whereby the details of a CFD proposal would be developed with input from all stakeholders through their federal elected officials.

As for the CFD proposal itself, many, on the left and on the right, have been impressed with both its projected effectiveness and its political viability. The proposal is carefully crafted to be non-partisan. It doesn’t raise taxes, it’s market- based, and it would render obsolete a complicated mountain of governmental energy regulation and subsidies — all things that are appealing to a growing number of conservatives who are increasingly taking the issue of climate change more seriously.

Attached are Grand Marais City Council resolutions and selected supporting documents (the two lengthy studies do contain executive summaries). More information about CFD available, of course, on the web at: citizensclimatelobby.org.

For the good,

Olya Wright Nordic Nature Group 387 2968

George Wilkes Cook County Chapter, Citizen’s Climate Lobby Grand Marais Public Utilities Commissioner 387 2137

The Economic, Climate, Fiscal, Power, and Demographic Impact of a National Fee-and-Dividend

Prepared by Regional Economic Models, Inc. (REMI) – Washington, DC

Synapse Energy Economics, Inc. (Synapse) – Cambridge, MA

Prepared for Citizens’ Climate Lobby (CCL) – Coronado, CA

Scott Nystrom, M.A. Senior Economic Associate, REMI

Patrick Luckow, M.S. Associate, Synapse

1776 I St. NW Suite 750 Washington, DC (202) 716-1397

Monday, June 9, 2014 REMI * Synapse

Acknowledgments The authors would like to thank the following individuals and groups that made this research possible. They include Louis W. Allstadt, Cathy Carruthers of Environmental Tax Reform from Washington (ETR-WA) and the United States (ETR-US), Peter Fiekowsky, and Alan and Jessica Langerman from Massachusetts. In addition to these individuals, Mr. Fiekowsky acknowledges his father, Dr. Seymour Fiekowsky, for his twenty-five years of service as chief of the United States Department of the Treasury’s Office of Tax Analysis (OTA) and in his inspiration toward making a difference for his country. Grateful recognition also goes to his OTA colleagues Emil Sunley and Michael Kaufman, who contributed to the design of this study. The authors would also like to thank Ali Zaidi and Dr. Frederick Treyz of REMI for their editorial commentary, as well as Dr. Danny Richter, Dr. Marc Breslow, Roger Streit, Rebecca Morris, Jennifer Loftus, and, in particular, Tom Haw from California for proofreading. The organizations include Citizens’ Climate Lobby (CCL), Citizens’ Climate Education Corp (CCEC), the groups under the ETR aegis, and Climate XChange, an organization in Massachusetts. All of their contributions aided in the completeness and quality of the report and its results on economic, climate, fiscal, power, and demographic impacts of implementing a fee-and-dividend carbon tax system in the Untied States. These results do not reflect the institutional views of REMI or Synapse but rather the professional opinions of the authors and findings of the models.1

1 All images courtesy of Wikimedia and out of the public domain

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Executive Summary This report examines the economic, climate, budgetary, power generation, and demographic impacts of implementing a revenue-neutral carbon tax for nine regions of the United States. The carbon tax would begin in 2016 with a rate of $10 per metric ton of carbon dioxide and escalate in a linear manner at $10 per year. The point of assessment for this tax would be extraction, although, after significant pass-through of the cost from upstream producers to downstream consumers, everyone in the energy supply chain would feel the influence from the carbon tax. Every dollar—100% of proceeds—from the carbon tax would enter into a “fee-and-dividend” (F&D) system that refunds the money to all American households with checks or direct deposits on a monthly basis. Every household would receive its share based on the number of adults (over 18) living there with dependent children (under 18) counting half as much as adults (and two being the maximum). The policy would also include a border adjustment to correct for carbon leakage outside of American borders and preserve competitiveness.

The results of the study demonstrate that there are probable benefits to taxing carbon dioxide emissions and returning the money to consumers through F&D. The following are highlights of the national level results of the study in 2025.

 2.1 million more jobs under the F&D carbon tax than in the baseline  33% reduction in carbon dioxide emissions from baseline conditions  13,000 premature deaths saved from improvements in air quality

These principal results are not to say the outcome is universally positive, and there are certain industries and regions in the United States that may do better or worse under a carbon pricing system. For example, the industries tied directly to households, such as healthcare, retail, and housing construction, tend to do well because F&D increases the overall level of consumer spending. There are other important results in 2025. The F&D rebates return nearly $400 billion to households—or almost $300 per month for a family of four, and the carbon tax aids in retirements of coal plants and accelerates investments in wind, solar, and nuclear power. The impact to the total cost of living is less than 3% from the baseline, and (GDP) increases between $80 billion and $90 billion.

This study integrates three models with different, important perspectives on the economy and energy. The first is ReEDS (Regional Energy Deployment System) built by the National Renewable Energy Laboratory (NREL) and run by Synapse Energy Economics, Inc. from Cambridge, Massachusetts. The ReEDS model predicts the type of power generation in use (such as coal, gas, nuclear, wind, or solar) in different parts of the country after implementing a carbon tax. The second is the Carbon Analysis Tool (CAT), which draws its assumptions from the Annual Energy Outlook (AEO) produced by the Energy Information Administration (EIA). CAT forecasts carbon dioxide emissions and revenues from the carbon tax. The third is PI+, a dynamic, multiregional model of subnational units of the United States economy. PI+ includes variables describing the changing energy prices, investments, and air quality and produces an impact study with results on job creation, GDP, income, and the differential impacts between different income groups, industries, and regions.

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Table of Contents * * *

 Acknowledgements p. 1  Executive Summary p. 2  Table of Contents pp. 3-5  “Just the Facts” pp. 6-9 o Policy Design p. 6 o Economic Impact p. 7 o Climate Impact p. 8 o Electricity Impact p. 9  Word Cloud p. 10  Introduction pp. 11-15 o Figure 1.1 – Carbon Content p. 12 o Figure 1.2 – Nine Regions p. 15  Policy Design pp. 16-18 o Fee-and-Dividend (F&D) pp. 16-17 o Border Adjustment pp. 17-18 . Figure 2.1 – Modeling Flowchart p. 18  Simulation Results pp. 19-43 o Figure 3.1 – Results Categories p. 19 o Figure 3.2 – Total Employment (regional level) p. 20 o Figure 3.3 – Total Employment (national level) p. 20 o Figure 3.4 – Gross Regional Product (GRP) p. 21 o Figure 3.5 – Gross Domestic Product (GDP) p. 21 o Figure 3.6 – Total Employment (percentage change) p. 22 o Figure 3.7 – GRP and GDP (percentage change) p. 22 o Figure 3.8 – GDP by Major Industries (national level) p. 23 o Figure 3.9 – GDP by Manufacturing Industries (national level) p. 24 o Figure 3.10 – Employment by Major Industry (national level) p. 25 o Figure 3.11 – GDP by Industry (national level) p. 26 o Figure 3.12 – Employment by Industry (national level) p. 27 o Figure 3.13 – Employment by Occupation (national level) pp. 28-29 o Figure 3.14 – Carbon Dioxide Emissions (annual forecast) p. 30 o Figure 3.15 – Carbon Dioxide Savings by Source (annual forecast) p. 30 o Figure 3.16 – Carbon Dioxide Savings (cumulative, regional level) p. 32 o Figure 3.17 – Carbon Tax Revenues (total, national level) p. 33 o Figure 3.18 – Monthly Dividend by Family p. 32 o Figure 3.19 – Cost of Living (regional level) p. 33 o Figure 3.20 – Energy Commodity Prices (national level) p. 34 o Figure 3.21 – Cost of Living (by quintile, national level) p. 35 o Figure 3.22 – Total Employment (by quintile, national level) p. 36 o Figure 3.23 – Real Personal Income (regional level) p. 37 o Figure 3.24 – Real Personal Income (national level) p. 37 o Figure 3.25 – Real Personal Income (per capita, regional level) p. 38 o Figure 3.26 – Real Personal Income (per capita, national level) p. 38 o Figure 3.27 – Labor Share of Income (national level) p. 39 o Figure 3.28 – Labor Share of Income (regional level) p. 39 o Figure 3.29 – Electrical Power Capacity (national level) p. 40 o Figure 3.30 – Electrical Power Generation (national level) p. 40

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o Figure 3.31 – Improved Air Quality (regional level) p. 42 o Figure 3.32 – Saved Premature Deaths (annual, regional level) p. 43 o Figure 3.33 – Saved Premature Deaths (cumulative, regional level) p. 43 o Figure 3.34 – Population (regional level) p. 44 o Figure 3.35 – Economic Migration Determinants (regional level) p. 44  Alternative Fiscal Case: “Across-the-Board” (ATB) Tax Cuts pp. 45-46 o Figure 4.1 – Employment, GDP, and Real Personal Income p. 45  Congressional Budget Office (CBO) pp. 46-47  Technical Appendix pp. 48-67 o Figure 5.1 – Policy Variables p. 48 o The ReEDS Model pp. 49-54 . Technology Data pp. 49-50  Figure 5.2 – Costs p. 49  Figure 5.3 – Emissions Parameters (2015) p. 40  Figure 5.4 – Emissions Parameters (2050) p. 50 . Load Data pp. 50-51  Figure 5.5 – Load Requirements (national level) p. 51 . Resource Assumptions pp. 51-53  Wind p. 51  Concentrating Solar Power (CSP) p. 51  Utility-Scale and Distributed PV p. 51  Biomass p. 52  Geothermal p. 52  Hydroelectricity p. 52  Retirements p. 52  Integrating Renewable Resources pp. 52-53  Supplemental Discussion pp. 53-54 o The CAT Model pp. 54-62 . Figure 5.6 – Carbon Tax Analysis Model (CTAM) p. 56 . Border Adjustment p. 58 . Electrical Power Investments p. 58 . NOX and SOX Emissions p. 60 . Fossil Fuel Exports p. 61 o The PI+ Model pp. 62-65 . Figure 5.7 – Model Structure p. 64 o Integrating ReEDS, CAT, and PI+ pp. 65-67 . Figure 5.8 – Modeling Flowchart p. 66 . Figure 5.9 – Data, Sharing, and Policy Variables p. 67 . Figure 5.10 – Baseline and Alternative p. 67  Regional Appendix pp. 68-121 o New England (NE) pp. 68-73 . Figure 6.1 – Electrical Power Capacity (NE level) p. 69 . Figure 6.2 – Electrical Power Generation (NE level) p. 69 . Figure 6.3 – GRP by Industry p. 70 . Figure 6.4 – Employment by Industry p. 71 . Figure 6.5 – Employment by Occupation pp. 72-73 o Mid Atlantic (MA) pp. 74-79 . Figure 6.1 – Electrical Power Capacity (MA level) p. 75 . Figure 6.2 – Electrical Power Generation (MA level) p. 75 . Figure 6.3 – GRP by Industry p. 76

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. Figure 6.4 – Employment by Industry p. 77 . Figure 6.5 – Employment by Occupation pp. 78-79 o East North Central (ENC) pp. 80-85 . Figure 6.1 – Electrical Power Capacity (ENC level) p. 81 . Figure 6.2 – Electrical Power Generation (ENC level) p. 81 . Figure 6.3 – GRP by Industry p. 82 . Figure 6.4 – Employment by Industry p. 83 . Figure 6.5 – Employment by Occupation pp. 84-85 o West North Central (WNC) pp. 86-91 . Figure 6.1 – Electrical Power Capacity (WNC level) p. 87 . Figure 6.2 – Electrical Power Generation (WNC level) p. 87 . Figure 6.3 – GRP by Industry p. 88 . Figure 6.4 – Employment by Industry p. 89 . Figure 6.5 – Employment by Occupation pp. 90-91 o South Atlantic (SA) pp. 92-97 . Figure 6.1 – Electrical Power Capacity (SA level) p. 93 . Figure 6.2 – Electrical Power Generation (SA level) p. 93 . Figure 6.3 – GRP by Industry p. 94 . Figure 6.4 – Employment by Industry p. 95 . Figure 6.5 – Employment by Occupation pp. 96-97 o East South Central (ESC) pp. 98-103 . Figure 6.1 – Electrical Power Capacity (ESC level) p. 99 . Figure 6.2 – Electrical Power Generation (ESC level) p. 99 . Figure 6.3 – GRP by Industry p. 100 . Figure 6.4 – Employment by Industry p. 101 . Figure 6.5 – Employment by Occupation pp. 102-04 o West South Central (WSC) pp. 104-09 . Figure 6.1 – Electrical Power Capacity (WSC level) p. 105 . Figure 6.2 – Electrical Power Generation (WSC level) p. 105 . Figure 6.3 – GRP by Industry p. 106 . Figure 6.4 – Employment by Industry p. 107 . Figure 6.5 – Employment by Occupation pp. 108-09 o Mountain (MNT) pp. 110-15 . Figure 6.1 – Electrical Power Capacity (MNT level) p. 111 . Figure 6.2 – Electrical Power Generation (MNT level) p. 111 . Figure 6.3 – GRP by Industry p. 112 . Figure 6.4 – Employment by Industry p. 113 . Figure 6.5 – Employment by Occupation pp. 114-15 o Pacific (PAC) pp. 116-22 . Figure 6.1 – Electrical Power Capacity (PAC level) p. 117 . Figure 6.2 – Electrical Power Generation (PAC level) p. 117 . Figure 6.3 – GRP by Industry p. 118 . Figure 6.4 – Employment by Industry p. 119 . Figure 6.5 – Employment by Occupation pp. 120-21  Regional Economic Models, Inc. (REMI) pp. 122-23 o Figure 7.1 – Client Map p. 123  Synapse Energy Economics, Inc. p. 123  Authors’ Biographies and Contact Information p. 124 o Scott Nystrom, M.A. p. 124 o Patrick Luckow, M.S. p. 124  Notes p. 125

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“Just the Facts”

Policy Design This white paper examines the economic, climate, budgetary, electrical power, and demographic implications of a carbon tax at the national level for nine regions of the United States and its economy. Those nine regions are the “U.S. Census” regions used in a number of federal data sources and in the energy forecasts from the Energy Information Administration (EIA). The carbon tax under study here supposes a tax rate of $10 per metric ton of carbon dioxide in 2016 and then increasing at a linear rate upward of $10 per year. The tax would be at the point of extraction and entrance to the economy, but the interconnectivity of the energy supply chain would mean a significant amount (if not the whole weight) of the carbon tax would eventually make its way to end-use consumers in the residential, commercial, and industrial sectors of the economy. This policy design would take 100% of the revenues and send them into a “fee-and- dividend” (F&D) system in which all proceeds would return to households in the form of monthly checks or direct deposits. Rebate eligibility would be on a per capita basis for adults (over 18) with half-credit for dependent children in each household (under 18) up to a maximum of two. This would keep the system revenue-neutral and require no other changes to the tax code or expenditures by the federal government. The policy would also include a “border adjustment” based on the carbon dioxide emitted during the production of any goods or services for importation into the United States. This border adjustment would help prevent the leakage of emissions outside of the country, aid in preserving the competitiveness of American industry on the world market, and encourage other countries to adopt a similar policy.

Methodology This study integrates three models with different perspectives on the economy and energy markets. They are (1) the Regional Energy Deployment System (ReEDS) built by the National Renewable Energy Laboratory and ran by Synapse Energy Economics; (2) the Carbon Analysis Tool (CAT) built from the Annual Energy Outlook (AEO) from the EIA; and (3) REMI PI+, a dynamic model of subnational units of the United States’ economy. The ReEDS model shows potential future investment patterns for power generation capacity by technology type. A carbon tax might influence earlier retirements of coal plants and earlier or additional investments in low- or zero-carbon power sources such as nuclear, natural gas with carbon sequestration, or wind and solar—ReEDS explicitly models such power switching. CAT takes its data and its assumptions from the AEO in order to have a baseline of energy consumption in the United States by region and sector. CAT adjusts this forecast downwards based on the price elasticity of demand for energy commodities after the tax and a pass-through in the energy supply chain increases end-use energy costs. CAT uses this process to generate an alternative energy demand forecast with saved carbon dioxide emissions and revenues from carbon taxes to have fiscal results. CAT also includes concepts on power investments from ReEDS, air quality, the revenues from the border adjustment, and changing American exports of fossil fuel resources. PI+ combines input data from ReEDS and CAT in order to perform an economic impact study of the F&D carbon tax in its dynamic, multiregional structure, including the impacts on job creation, gross domestic product (GDP), personal income, the cost of living, and long-term regional demographics as households respond to new incentives.

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This map shows the nine regions in this study (Alaska and Hawaii are in the Pacific region).

New England (NE)

Mid-Atlantic (MA)

East North Central (ENC)

West North Central (WNC)

South Atlantic (SA)

East South Central (ESC)

West South Central (WSC)

Mountain (MNT)

Pacific (PAC)

Economic Impact Results

Total Employment (regional level)

700 600 NE 500 MA 400 ENC 300 WNC 200 SA ESC 100 WSC 0

Thousands from baseline from Thousands MNT

-100

PAC

2017

2015

2031

2021

2016 2019

2018

2027

2035

2025

2033

2023 2032

2022 2034

2024

2029 2026

2028 2030 2020 Almost all regions experience a positive impact to job creation relative to the baseline from the F&D carbon tax, and even the energy production-intensive WSC region (which includes Texas) has close to a net zero impact to total employment levels. The F&D carbon tax tends to generate jobs in labor-intensive industries like healthcare and retail, which helps explain these results of 2.1 million jobs in 2025 and 2.8 million jobs by 2035.

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Gross Regional Product (GRP) and Gross Domestic Product (GDP)

1.0% USA 0.5% NE MA 0.0% ENC -0.5% WNC -1.0% SA ESC -1.5% WSC

Percentage from baseline from Percentage -2.0%

MNT

PAC

2017

2015

2031

2021

2016 2019

2018

2027

2035

2025

2033

2023 2032

2022 2034

2024

2026 2029

2028 2030 2020 The sum of GRP for all regions is the same as GDP for the nation. Most regions have a positive impact to total output, though WSC does decline because of reduced output in capital-intensive sectors like oil and gas extraction, pipeline transportation, and petroleum refining. Job creation in WSC is still not significantly different from the baseline, however, and the net national result in 2025 is an additional $80 billion to $90 billion in GDP.

Climate Impact Results

Carbon Dioxide Emissions (annual forecast from baseline, national level)

6,000 5,000 4,000 3,000 2,000 1,000

Millions metric tons of Millions 0

2017

2015

2031

2021

2016 2019

2018

2027

2035

2025

2033

2023 2032

2022 2034

2024

2026 2029

2028

2030 2020 NEMS/ReEDS Baseline CAT/ReEDS Alternative

A $10 per metric ton carbon tax starting in 2016 and increasing at $10 per year would have a large influence on future carbon dioxide emissions, engendering a 33% decrease from baseline emissions by 2025 and a 52% decrease from baseline in 2035.

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Saved Premature Deaths (annual, regional level) -16

-14 PAC -12 MNT -10 WSC -8 ESC -6 SA -4 WNC ENC Thousands (annual) Thousands -2 MA

0

NE

2017

2015

2031

2021

2016 2019

2018

2027

2035

2025

2033

2023 2032

2034 2022

2024

2026 2029

2028 2030 2020 Reducing emissions of carbon dioxide (mostly from vehicles and power plants, as shown below) also indirectly reduces the emissions of noxious air pollutants such as mono-nitrogen oxides (or

NOX) and sulfur dioxide (SOX). According to the U.S. Environmental Protection Agency (EPA), both these compounds can cause respiratory problems and hospitalizations. The above results calculate saved premature deaths from reducing NOX and SOX emissions in a way consistent with guidelines from EPA and other federal agencies.

Electrical Power Generation (national level)

Baseline ($0/year) Alternative ($10/year) 5,000 5,000 Solar

4,500 4,500 Wind

4,000 4,000 Biopower

Geothermal

3,500 3,500 Hydro 3,000 3,000 Nuclear Oil-Gas-Steam 2,500 2,500 Gas-CC-CCS Gas-CT 2,000 2,000 Gas-CC 1,500 1,500 Coal-CCS

Generation Generation (TWh) Coal-IGCC

1,000 1,000 Coal-New 500 500 Cofiring Coal-Old Scrubbed

0 0 Coal-Old Unscrubbed 2010 2020 2030 2040 2010 2020 2030 2040

Baseline power generation continues to include a significant amount of coal and gas, while the alternative with the carbon tax reduces generation and emissions (of carbon, NOX, and SOX) from coal and gas while encouraging nuclear, solar, and wind power.

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Word Cloud

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Introduction This research takes a detailed look at the impacts to the United States’ economy, emission, federal budget, power generation capacity, and demographics from implementing a national system for a “fee-and-dividend” (F&D) carbon tax starting in 2016. To provide a synopsis, this system would apply a fee to the extraction or removal of any carbon dioxide-emitting fuels— such as petroleum, natural gas, or coal—from the Earth. Objectives include the discouragement of their usage in order to preserve future resource endowments, reduce emissions, and provide an income base for a monthly rebate check of any proceeds from the carbon tax to all American households.2 Such a carbon tax would begin at $10 per metric ton in 2016 and escalate in a linear fashion at $10 per year upward, although this study’s timeline ends with the models’ horizon in 2035. Carbon taxes are a form of a sales tax—they introduce an extra charge paid to the government during a regular market transaction that raises the price of the good or service and renders the buyer less likely to consume it.3 Carbon taxes are expressly “Pigouvian” in the sense they mean to help markets internalize the negative externalities unrealized by the parties directly involved in the transaction, such as the potential harm done to the atmosphere when combusting fossil fuels.4 However, a carbon tax’s nature as a fee and sales tax and its service as a revenue source for a governmental jurisdiction or a rebate fund make it a fiscal issue and therefore an appropriate topic for scrutiny with the traditional “tools of the trade” for economic and fiscal impact analysis. These include, in short, price elasticity of demand, network and dispatch modeling of electrical power generation, and regional impact modeling. This study integrates the three perspectives to allow a comprehensive portrait of a F&D carbon tax—what it means as budget, fiscal, and tax reform at the federal level. This includes implications on the national and regional economies, emissions by type, the federal budget, the electrical grid, and long-term industrial competitiveness and quality of life.

The fundamental objective of a price on carbon dioxide is to incentivize households and businesses to consider the total cost of carbon dioxide emission during prosaic purchasing decisions. Carbon dioxide, while harmless in dilute quantities and produced during normal respiration by many living organisms, may produce damages (an external social cost) when emitted in tremendous quantities across the globe. There is no shortage of literature postulating that higher atmospheric concentrations may disrupt existing human activities through rising sea levels, changing weather patterns, increase in the overall frequency and intensity of storms, and other factors.5 This analysis does not depend on a motive for why the United States may wish to reduce its emissions. The net of the benefits and costs from global warming or climate change are immaterial in examining carbon taxes and F&D as a sort of “mundane” budget or tax reform, and impacts on climate and air quality are truly secondary, indirect effects

2 For a full introduction to the fee-and-dividend (F&D) system for a carbon tax under consideration here, please see, , particularly the section “Therefore the following legislation” 3 For a longer introduction to the basics of carbon taxes, please see, , and especially this slideshow, 4 Named for Arthur Cecil Pigou, a British economist of the early Twentieth-Century and a founding figure of welfare economics who noted that markets did not account for public costs with issues such as littering and pollution, please see, 5 For a summary to the research and controversy about carbon externality and “climate change,” please see the UN Intergovernmental Panel on Climate Change (IPCC),

p. 11 REMI * Synapse in this type of modeling and policy design. To offer an example on the functioning of a carbon tax, a gallon of gasoline at retail weighs about 6.3 pounds on average. Those 6.3 pounds produce approximately 19.6 pounds of carbon dioxide in combustion when combining hydrocarbons with the oxygen in the air.6 After undertaking unit conversion,7 a $1 per metric ton carbon tax is the equivalent to a $0.009 per gallon excise tax on retail gasoline (literally “at the pump”). The exercise is the same for different fuels based on the inherent chemical “carbon content” of the fuel at whatever typical unit of sale at whatever point on the energy supply chain (such as extraction, first sale, refinement, wholesale, or retail). Many major corporations—including ExxonMobil, Wal-Mart, , General Electric, Walt Disney, Wells Fargo, DuPont, Duke Energy, , and Delta Airlines—already make similar calculations of the potential carbon tax on their energy usage in expectation of future carbon pricing policies at the regional or national level.8 These expectations help motivate and contribute to the research into the potential net impact of such a carbon tax with an F&D algorithm.

1 gal of Burning it 19.6 pounds Each $1/ton gasoline yields about of CO2 is in tax is weighs 6.3 19.6 pounds about 0.009 $0.009/gal pounds of CO2 metric tons for gasoline

Figure 1.1 – This process chart shows the basics of calculating a carbon tax once passed down through the energy supply chain to retail and end-use consumers. Chemistry determines the “carbon content” of a fuel or energy type, which becomes part of its price with an excise tax within a transaction to discourage its use and garner revenues for a rebate fund.

Citizens’ Climate Lobby (CCL), private citizens based in Coronado, California, engaged Regional Economic Models, Inc. (REMI) and its Washington, DC office to examine these issues and their interrelationships through the lens of modeling. This study uses three tools: the Regional Energy Deployment System (ReEDS), the Carbon Analysis Tool (CAT), and PI+. The ReEDS model, built by the National Renewable Energy Laboratory (NREL) in Golden, Colorado, but ran in this study by Synapse Energy Economics, Inc. of Cambridge, Massachusetts,9 is a long-term capacity deployment and investment tool for modeling the power sector in the United States.10 CAT is an evolution of the Carbon Tax Analysis Model (CTAM) initially developed by Keibun Mori for

6 Depending on the specific blend with ethanol, 7 1 pound = 0.00045359237 metric tons 8 In fact, these companies already factor in a future price on carbon in their strategic planning and their long-term investment decisions, please see Coral Davenport, “Large Companies Prepared to Pay Price on Carbon,” New York Times, December 5, 2013, 9 For more background on Synapse, please see their webpage, 10 For an introduction to ReEDS, please see the NREL website, , the technical appendix has more information on its specific application for this research

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Washington11 and later adapted by REMI for analyses in Massachusetts,12 the state of Washington, King County, Washington,13 and California.14 CAT takes CTAM and its construction on top of the Reference Case of the Annual Energy Outlook (AEO)15 from the National Energy Modeling System (NEMS)16 of the Energy Information Administration (EIA)17 and adds new emissions concepts for NOX and SOX, international imports and exports of energy, multiple regions, power switching (from ReEDS), and a fuller integration with REMI PI+. PI+ is a dynamic, multiregional, and integrated economic, demographic, and fiscal model inside of a Microsoft Windows-based software package of subnational units of the United States used to produce economic impact results from exogenous policy simulations such as the F&D carbon tax. The models work in tandem. ReEDS describes how the power grid and generation might respond to a carbon tax with fossil energy sources being more expensive relative to zero-carbon alternatives and CAT takes data from ReEDS and the AEO to forecast a baseline and alternative for emissions and carbon tax revenues. PI+ simulates the net impact of higher end-use energy prices versus increased consumer spending from F&D, investments in different power sources, and various other factors. This integrated approach highlights each model’s strengths in its core area (such as power generation in ReEDS and long-term demographics in PI+) before moving to the next step; the outputs from one model become the inputs for the next before finishing the chain inside of PI+ with economic impact analysis.

The results in this white paper cover several dimensions and topics, the era from 2016 to 2035 of twenty years, and a nine region subnational breakout of different segments of the United States. The broad areas include macroeconomic indicators, a baseline forecast and alternative for carbon dioxide emission from ReEDS and CAT, fiscal considerations for the federal budget and F&D system, the impact to the cost of living and socioeconomics, changes in the power generation profile, and any long-term changes to American demographics at the regional level on account of these policies. Macroeconomic indicators include employment and job creation, gross regional product (GRP) or gross domestic product (GDP),18 and distribution of jobs and

11 Please see the original article by Keibun Mori, “Washington State Carbon Tax: Fiscal and Environmental Impacts,” from the Evans School of Public Affairs at the University of Washington, , and see additional information on the construction of CTAM and CAT in the technical appendix 12 Scott Nystrom and Ali Zaidi, “Modeling the Economic, Demographic, and Climate Impact of a Carbon Tax in Massachusetts,” July 11, 2013, ; Erin Ailworth, “Environmentalists Call for Massachusetts Carbon Tax,” Boston Globe, June 23, 2013, 13 Technically a 2-region study of King County and the rest of the state, please see Scott Nystrom and Ali Zaidi, “The Economic, Demographic, and Climate Impact of Environmental Tax Reform in Washington and King County,” 14 Including a similar policy design to the F&D approach here, please see Scott Nystrom and Ali Zaidi, “Environmental Tax Reform in California: Economic and Climate Impact of a Carbon Tax Swap,” 15 This study used the AEO reference case for 2013, found here, 16 For an introduction to NEMS, please see, 17 For the EIA homepage, please see, 18 Sometimes called “value-added,” the market value of goods and services produced by labor and property in a region (GRP) or the United States (GDP) regardless of the nationality of its ownership

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GRP across different industries,19 occupations,20 and regions. The climate results involve a baseline forecast, a “$0 per ton” future case, contrasted with the $10 per year case to 2035 and potential emissions savings in power generation, the use of liquid and gaseous fuels, and reduced fossil fuel exports. Fiscal data includes a forecast of total carbon tax revenues, which is the anticipated remaining emissions multiplied by the rate in any given year, as well as the anticipated size of any annual or monthly rebate checks per capita or per household. The socioeconomics of the study look at changes to cost of living indices, energy and commodity prices, and changes by income strata in the labor market and the prospects of F&D serving as a nascent “guaranteed income.” Results for power include the anticipated capacity and generation for each technology type in each case and by year and by region. The power results combine with data from CAT on transportation-related emissions in order to consider the impact of improved 21 22 air quality via reduced emissions of mono-nitrogen oxides (NOX), sulfur dioxide (SOX), and the benefit-cost of health outcomes. Quality of life, the labor market, and cost of living adjusts the demographic forecast in PI+ through migration between regions in the model. The dynamic results for several categories on the impact of a F&D carbon tax offer a comprehensive portrait of the implications of fiscal and climate policy.

There are two appendices to the report. The first describes the technical foundation of the ReEDS model, CAT, PI+, and the integration between the three. The second has a surfeit of detailed tables on selected model results at the regional level. While this is a national level study of a proposed change in federal tax policy, the workings of the models are “bottom-up” for running at the regional level before agglomerating upward to the national whole. The United States’ economy and demographics total over $16 trillion in annual GDP and 318 million individuals. This is approximately the size of the whole European Union (EU) in terms of GDP (though with around 190 million fewer people). Just as in Europe between different countries, there is considerable variation within the United States. Energy is perhaps a quintessential example of regional inimitability. For instance, California produces almost no power from coal and instead relies on natural gas, nuclear, renewable power, and its uneven topography and adequate rivers to site hydroelectric dams.23 At the national level, on the other hand, coal-fired

19 By 70 sectors that approximate the 3-digit NAICS (North American Industrial Classification System) codes, the U.S. Census’ standard definition of what constitutes the hierarchy of industrial sectors in the economy, please see, 20 By the Standard Occupational Classification (SOC) codes from the Bureau of Labor Statistics (BLS), a similar concept to NAICS that instead looks at the type of job and tasks performed by the worker instead of the final product produced by the firm, please see, 21According to the “health” page of the U.S. Environmental Protection Agency (EPA), “Current scientific evidence links short-term exposures to SO2, ranging from five minutes to twenty-four hours, with an array of adverse respiratory conditions including bronchial construction and increased asthma symptoms… these effects are particularly important for asthmatics at elevated ventilation rates (e.g., while exercising or playing),” 22 According to EPA, “Current scientific evidence links short-term NO2 exposures, ranging from thirty minutes to twenty-four hours, with adverse respiratory effects including airway inflammation in healthy people and increased respiratory symptoms in people with asthma… breathing elevated short-term NO2 concentrations, and increased visits to emergency departments and hospital admissions for respiratory issues, especially asthma,” 23 California still imports electricity that may come from coal-fired generation in the western United States, although its internal power generation is nearly all gas and zero-carbon sources, please see,

p. 14 REMI * Synapse generation produces between 35% and 40% of all electricity.24 Thus, the modeling here of region-to-region has several advantages over a purely macroeconomic or “one region” setup—it takes into account of regional differences in industry mixtures, energy supply and demand, and provides results from the F&D carbon tax in terms of geographic units. It does not use “one number” to cover all the inherent heterogeneity and variability of the United States’ economy.25 The results presented in this study are the same as the nine regions of the NEMS model and the EIA data for the sake of consistency with federal sources.

New England (NE)

Mid-Atlantic (MA)

East North Central (ENC)

West North Central (WNC)

South Atlantic (SA)

East South Central (ESC)

West South Central (WSC)

Mountain (MNT)

Pacific (PAC)

Figure 1.2 – This map shows the nine regions in the PI+ model simulations for this work.26 The colors above are consistent with the coloration of the results tables and appendices. The states of Alaska and Hawaii are part of the PAC region with California, Oregon, and Washington. Each region has its own reaction to the F&D carbon tax before becoming part of the national whole through simple addition. For instance, the heavy concentration of coal-fired power plants in ENC and WNC (the Great Lakes and Great Plains states, respectively) make their economies more susceptible to switching from coal power to nuclear power than NE or PAC, neither of which have comparably much in terms of coal. On the other hand, ENC and WNC have potential for wind power given all their cheap, open land. These regions have their idiosyncrasies—these models specifically exist to take account of them.

24 According to EIA, please see, 25 There is always considerable variability between regions in response to policy, and some states can grow rapid while others are in recession—for example, in 2012, national real GDP grew at 2.5%, but ten states grew at 3.3% or faster (and North Dakota at 13.4%) while nine states grew less than 1.2% (with a small recession in Connecticut of -0.1%) according to the Bureau of Economic Analysis (BEA), 26 The regions above are the same as those in the NEMS modeling data and the same as the subnational units used by the U.S. Census in many of its data releases at the “Census Divisions” granularity, please see,

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Policy Design The results consider a primary scenario of a F&D carbon tax starting in 2016 at $10 per metric ton of carbon dioxide and increasing at a linear rate of $10 per year assessed at the point of extraction of any carbon dioxide-emitting fuels.27 The initial rate above is in 2016 dollars, and the tax rate would have indexing from the outset in order to prevent the divergence from its real value due to inflation. The rate per metric ton is an important consideration with a carbon tax because it captures market-based incentives toward switching out of carbon-intensive power generation, business practices, and item purchases and toward a trajectory for lower emissions. The linear, consistent increase in the tax rate sends a clear, predictable message to households, businesses, and investors about future costs and incentivizes them to investigate different ways of doing things. The embedded simplicity and expectedness of this system removes all ambiguity about future prices for any purchasing decisions—up from individuals doing straightforward benefit-cost analysis on things like appliance purchases to multinational corporations and their strategic plans. Assuming the carbon tax rate would continue increasing at $10 per year past 2035 and to at least 2040 is part of the illustration of the point. The ReEDS model runs to 2040 and has a structure that implicitly assumes the investors in electrical power capacity make rational decisions about cost competitiveness of plants and infrastructure not only now but in the future. “Investors” in 2035 will look for a return on investment (ROI) from 8% to 12% over the lifespan of a project, which means anticipated higher carbon prices in 2035 will matter for decisions made in the 2020s and the 2030s.

Fee-and-Dividend (F&D) The other main part of a carbon tax is considering of the final disposition of the revenues. This can have considerable influence on the final regional and macroeconomic impacts of the policy (given that the sums involved often total a few percentage points of GDP). The revenues from a carbon tax could see utilization in an infinite number of ways toward replacing current revenue sources, refunds, deficit reduction, or financing new expenditures. Nevertheless, the governing principle for this design is revenue-neutrality and the fee-and-dividend alone—all of monies paid into the U.S. Department of the Treasury from the carbon tax must return to households in the form of a monthly check or direct deposit. There would be limited eligibility requirements, and household size would determine each household’s share of the total, national dividend. To quote, “Equal, monthly, per-person dividend payments made to all American households (one-half payment per child under eighteen with a limit of two per household), and the total value of all monthly dividend payments shall represent 100% of the total carbon fees collected in each month.”28 A monthly check (as opposed to annual) assists families living “hand to mouth” in any transitional periods, prevents households from needing to carry a net loss from higher energy prices longer than thirty-one days, and makes it an easier part of family budget planning along with monthly car payments, mortgages, and similar fixed costs. Revenue-neutrality through F&D has several advantages from a policy design and a political standpoint. Revenue-neutrality implies there is no appreciable net increase in the level

27 For an outline of the full legislative proposal by CCL, please see, 28 This matters in the economic simulations, as well, given it helps determine some of the distribution of the impacts between regions of the country due to differing fertility rates and family sizes

p. 16 REMI * Synapse of total federal spending, which means the fiscal and climate issues behind the carbon tax are separate from any debates on the most appropriate or efficient level of spending relative to tax revenues, population, or GDP. The F&D approach avoids entanglement in ongoing debates about tax reform,29 individual income tax rates, corporate taxes, tax expenditures,30 capping deductions,31 or “base broadening” because F&D works as a separate system from general fiscal policy and the regular tax code. It also does not influence the structure, functioning, or financing of social entitlement programs, such as Social Security, Medicare, Medicaid, or unemployment insurance.32 These are all issues with infinite complications of their own, but F&D combined with revenue-neutrality leaves them as separate matters.

Border Adjustment Another feature of this design is its inclusion of a “border adjustment” on the potential carbon dioxide of any fuels or the emissions behind the production of goods brought into the United States for sale. It charges the same rate on manufactured goods, agricultural products, and fossil fuel imports as that charged domestic producers. The tariff would also apply to American exports of fossil fuels. The goal of the adjustment is to prevent the “leakage” of emissions for American consumption to foreign production, maintain competitiveness, and place upward pressure on the world price of coal, natural gas, and petroleum and incentivize other nations to design their own carbon pricing. The United States is a large country and an enormous energy producer, and therefore a higher cost for domestic resource extraction would have some effect on the world price for energy, although the scale of that effect is not part of the modeling. The border adjustment aids in preventing the movement of production lines and their emissions out of the United States in order to avoid the tax before exporting the goods back into the American market. For instance, consider an automobile assembly plant in Ontario or Chihuahua in competition with a similar one in Michigan or Alabama. Without a border tariff and ceteris paribus, the foreign lines could freely emit while domestic ones pay carbon taxes. However, the border adjustment means Canadian and Mexican producers pay a border tax comparable to the prevailing one in the United States. This design could have complications with international trade law, the World Trade Organization (WTO), and its goals of encouraging international commerce via lower tariffs. The models here presume any issues with the WTO have a happy resolution; there is an abundance of literature on possible routes.33 Revenues from the border adjustment would still meet revenue-neutrality criteria, but they would have a different

29 Perhaps the most important one at the moment is that of Representative Dave Camp, for a summary, please see, Martin Sullivan, “25 Interesting Features of Chairman Camp’s New Tax Reform Plan,” Forbes, March 3, 2014, 30 For an introduction to tax expenditures, the largest one being the deduction for employer-provided insurance, please see, “The Distribution of Major Tax Expenditures in the Individual Income Tax System,” Congressional Budget Office (CBO), May 29, 2013, 31 An approach favored by such economists at Dr. at Harvard and a favorite of Governor Mitt Romney during the presidential campaign of 2012, please see, Martin Feldstein, “It’s time to cap deductions,” Washington Post, March 12, 2013, 32 Some proposals imagine a carbon price supplementing or replacing current payroll taxes 33 For example, please see, Joost Pauwelyn, “Carbon Leakage Measures and Border Tax Adjustments Under WTO Law,” Graduate Institute of International and Development Studies (IHEID), March 21, 2012,

p. 17 REMI * Synapse treatment than domestic carbon tax revenues into the F&D system. Revenues from the tariff adjustment would go into a separate “jar” than the general F&D and help to rebate back the tax’s value to American manufacturers in order to support their ability to compete on international markets. This would assist in buttressing American competitiveness and reducing leakage of carbon emissions for American-consumed goods to foreign production locations or other nations without an analogous carbon dioxide pricing arrangement.

Figure 2.1 – This is an arc-and-node representation of the logical superstructure of the policy and the data involved in the model. The carbon tax rate in the upper left informs the initial simulations in ReEDS and CAT, which in turn generate results on power generation and capacity, air quality, carbon dioxide emissions, energy costs, the border adjustment, and fossil fuel exports. These serve as inputs to the economic study in PI+ in the bottom right.

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Simulation Results The results of the simulations in ReEDS, CAT, and PI+ cover the economic, climate/emissions, federal fiscal, electrical power, and demographic implications of a national, F&D carbon tax starting at $10 per year in 2016 (in 2016 dollars) and increasing linearly at $10 per year through 2035. As per F&D, all revenues gained from the carbon tax return to American households in the form of a monthly check in a system roughly similar to the Alaska Permanent Fund of annual rebates to individual taxpayers of state royalties and excise taxes on oil and gas extraction and mining.34 The results include simulation inputs for the border adjustment, as well. All the results below are against a “do-nothing” or “business as usual” baseline presuming no other changes to the economy, energy prices, or the tax code. The baseline represents the general drift of the United States’ economy by region into the future based on long-term trends within the economy, technological development, and demographics. The models simulate the net impact of implicitly higher end-use energy costs from the carbon tax versus the benefit of increased consumer spending (via F&D) with changing investments in power generation capacity and the border adjustment. It accounts for both the negatives and the positives of this potential policy with a ceteris paribus condition against the “null hypothesis” baseline. For the most part, results are against this baseline, although there are instances where a direct comparison between the baseline and alternative is appropriate rather than just the difference (or “delta”) between them.

Economic Emissions Budgetary Electrical Demo- •Jobs •Carbon •Revenues •Capacity by graphics •GDP emissions •Monthly technology •Population •Income •NOX, SOX dividend •Generation •Economic •Prices emissions •Per capita by type migration •By industry •Baseline •Per family •Investment •Saved in power •By region •Alternative •Border premature adjustment •By region deaths

Figure 3.1 – This summarizes the broad categories of the results, starting on the left with economic impacts and eventually ending with changing long-term demographics.

34 The Alaska Permanent Fund (or the “oil check”) serves as inspiration for CCL’s conception of a F&D system with a few differences, including narrower eligibility requirements for state residency and the existence of a permanent, interest-bearing sovereign wealth fund in Alaska, while F&D would carry no balance and immediately refund all revenues, please see,

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Total Employment (regional level)

700 600 NE 500 MA 400 ENC 300 WNC 200 SA ESC 100 WSC 0

Thousands from baseline from Thousands MNT

-100

PAC

2017

2015

2031

2021

2016 2019

2018

2027

2035

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2033

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2028 2030 2020 Figure 3.2 – This represents the net change in employment by region. The results are, again, consequences of the inputs built around conditions described in the policy design section and previous page. Speaking relative to the baseline, the net effect on job creation and employment is positive in most years and regions, and even the export-oriented and energy production- intensive WSC region has close to a net zero impact on its employment levels.

Total Employment (national level)

3,000

2,500

2,000

1,500

1,000

500

Thousands over baseline over Thousands 0

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2015

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2028 2030 2020 Figure 3.3 – This is the same data as that in Figure 3.2 agglomerated up from the regions to the nation. Thus, net employment levels at the national level from the F&D carbon tax are between 2 million and 3 million over baseline (approximately a 1% increase) when counting higher energy costs versus rebates to households and changed investments.

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Gross Regional Product (GRP)

$40,000

$30,000 NE $20,000 MA $10,000 $0 ENC -$10,000 WNC -$20,000 SA -$30,000 -$40,000 ESC -$50,000 WSC

Millions 2012dollars of Millions -$60,000 MNT

-$70,000

PAC

2017

2015

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2021

2016 2019

2018

2027

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2033

2023 2032

2022 2034

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2028 2030 2020 Figure 3.4 – This shows the impact to GRP for the nine regions from the F&D carbon tax. Most regions see a slight expansion in their economic output, although the ESC and WSC regions have either a neutral or a negative impact. This is a natural extension of the large energy production cluster present in the WSC’s economy. Its ability to maintain the same level of employment in the face of falling GRP involves a change in its industry mixture.

Gross Domestic Product (GDP)

$90,000

$80,000 $70,000 $60,000 $50,000 $40,000 $30,000 $20,000

$10,000 Millions 2012dollars of Millions

$0

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2028 2030 2020 Figure 3.5 – This is the sum of the regions’ GRP, which equals the United States’ GDP. The impact is still a net positive, although less so than the impact to employment in percentage terms—the above is a difference of 0.35% to 0.65% from baseline GDP. The difference in the scale of the impact between the two again comes down to the industry mixture.

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Total Employment (percentage change)

2.0% USA 1.5% NE MA 1.0% ENC WNC 0.5% SA 0.0% ESC WSC

Percentage from baseline from Percentage -0.5%

MNT

PAC

2017

2015

2031

2021

2016 2019

2018

2027

2035

2025

2033

2023 2032

2022 2034

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2026 2029

2028 2030 2020 Figure 3.6 – The above displays the percentage change from the baseline implied by the results in Figure 3.2 and Figure 3.3. The F&D carbon tax has a positive effect on employment in most regions, although over the scope and scale of the United States economy the impact in even the “best” region (PAC, MNT, or ENC) is still less than a 2% difference from the baseline.

Gross Regional/Domestic Product (percentage change)

1.0% USA 0.5% NE MA 0.0% ENC -0.5% WNC -1.0% SA ESC -1.5% WSC

Percentage from baseline from Percentage -2.0%

MNT

PAC

2017

2015

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2018

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2028 2030 2020 Figure 3.7– The percentage changes in GRP and GDP are less than that in the changes to total employment because of the labor-intensity of the industries tied to consumer spending and the F&D system in Figure 3.8. Most regions add GRP save WSC but, even then, the impact to GRP in the WSC region is less than 2% by 2035, which is a small change from baseline.

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GDP by Major Industries (national level)

Health Care and Social Assistance Finance and Insurance Retail Trade Real Estate and Rental and Leasing Information Other Services, except Public Administration Accommodation and Food Services Wholesale Trade Construction State and Local Government Administrative and Waste Management Services Arts, Entertainment, and Recreation Educational Services Professional, Scientific, and Technical Services Forestry, Fishing, and Related Activities Management of Companies and Enterprises Utilities Transportation and Warehousing Mining Manufacturing -$40,000 -$20,000 $0 $20,000 $40,000 Millions of 2012 dollars (annual average, 2016-2035)

Figure 3.8 – This distributes the impacts to national GDP between the 19 private sector industries that make the two-digit NAICS codes as well as state and local government. As in Figure 3.6 and Figure 3.7, most of this represents a small change versus the baseline of between 1% and 2% of total output over two decades for the service sectors and under a 10% decrease in mining output. Manufacturing has important patterns in Figure 3.9.

The F&D carbon tax renders the national economy larger than the one in the baseline, but perhaps just as vital is the composition of GDP under the policy. The above shows higher energy prices cause a decline in the value-added of the sectors directly related to energy production and distribution, such as mining or utilities, as well as energy-intensive sectors like manufacturing and transportation/logistics. This is an expected outcome of taxing those industries’ products or inputs via the carbon tax in order to incentivize a reduction in the consumption of carbon dioxide-emitting fuels, goods, and services. On the other hand, F&D increases demand from households for consumer staples like healthcare, food and drinks, electronics, media, entertainment, and housing. The industries in the blend at the top of the distribution all have close, direct, or indirect linkages with the consumption component (“C”) of GDP, and its expansion in the simulation due to the rebate increase their output and value-added. Carbon pricing would not yield a positive impact on all sectors or regions no matter its structure, and the results for the WSC region in Figure 3.4 and industries in Figure 3.8 reflect the expectation. The net is overwhelmingly positive, however, and there are trends within manufacturing and in Figure 3.8 that reflect higher national and regional employment levels.

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GDP by Manufacturing Industries (national level)

Motor vehicles, bodies and trailers, and parts Food Beverage and tobacco Printing and related support activities Fabricated metal Furniture and related Nonmetallic mineral Wood Machinery Apparel; Leather and allied Paper Textile mills; Textile mills Miscellaneous Other transportation equipment Plastics and rubber Electrical equipment and appliance Primary metal Computer and electronic Chemical Petroleum and coals -$20,000 -$10,000 $0 $10,000 Millions of 2012 dollars (annual average, 2016-2035)

Figure 3.9 – This is the same data as the manufacturing agglomeration in the previous figure subdivided into the three-digit manufacturing sectors in the NAICS codes. As before, most of these changes represent a marginal difference from the baseline of a few percentage points.

There are several key trends in the complicated picture for American manufacturing under the F&D carbon tax. Most sectors have close to a neutral impact, though some break this pattern. The largest losses are in “petroleum and coals,” which is an industry made up mostly of petroleum refineries.35 Declining output for this industry relative to the baseline is a natural expectation from a measure like a carbon tax. A price on emissions raises upstream costs of inputs and, after a “pass-through” in market prices, the downstream cost of its final products in wholesale and retail markets. Its decline is a significant loss in output but, as Figure 3.10 on the next page depicts, it does not represent a very significant loss in employment compared to the gains in other industries. The other industries at the bottom, including chemicals and primary metals (which produce steel and pipes), have a direct relationship to the decline in refinery output for being part of that industry’s supply chain. Conversely, manufacturing subsectors with a strong connection to consumers—such as automobiles, food products, printing, fabricated metals (mostly car parts), and furniture—increase their output relative to the baseline. In fact, if one subtracts petroleum and chemical manufacturing, the net change in the combined output under the F&D carbon tax from all of the other, “non-energy” American manufacturing sectors is close to zero.

35 This sector, which is NAICS 324, mostly involves refinement of crude petroleum; please see,

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Employment by Major Industry (national level)

Health Care and Social Assistance Retail Trade Other Services, except Public Administration Accommodation and Food Services Administrative and Waste Management Services Construction Finance and Insurance Real Estate and Rental and Leasing Educational Services Arts, Entertainment, and Recreation State and Local Government Wholesale Trade Professional, Scientific, and Technical Services Information Manufacturing Transportation and Warehousing Forestry, Fishing, and Related Activities Management of Companies and Enterprises Utilities Mining -200 -100 0 100 200 300 400 500 600 Thousands over baseline (annual average, 2016-2035)

Figure 3.10 – This chart recasts the total employment by region and nationally from previous figures into the difference in jobs by industry relative to the baseline. Most sectors, with the exception of mining and utilities, have a positive impact to their employment levels.

The main factors in the results for Figure 3.2, Figure 3.3, Figure 3.4, and Figure 3.5 on the regional and macroeconomic impacts to jobs, GDP, and GRP from F&D carbon tax are changes in demand by industry and labor productivity. As described, demand relates to the incentives inherent to the carbon tax. Labor productivity is a concept of the necessary labor units needed to perform a task—for instance, if a software company requires 50 workers for two years to complete a $20 million contract, this implies a labor productivity of $200,000 per worker every year.36 Technology and the nature of the production process for each industry determine the relative “labor-intensity,” or to what degree labor inputs and wages play a role in its operational enterprise. The positive results to employment levels under the carbon tax owe much to this policy’s propensity to shift output away from industries with low labor-intensity (such as petroleum refining, mining, transportation, and utilities) and toward consumer-centric industries that require larger labor inputs. The healthcare and retail sectors, in particular, receive many of the extra dollars and their labor-intensity means they create an outsized portion of the net new jobs. This explains why total employment can be positive or neutral in the face of stagnant or declining GRP or GDP in the model simulations.

36 50 workers * 2 years * $200,000 per worker = $20 million worth of completed project

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Figure 3.11 – GDP by Industry (millions of 2012 dollars) 70 sector NAICS 2020 2025 2030 2035 Forestry and logging; Fishing, hunting, and trapping -$156 -$430 -$646 -$794 Agriculture and forestry support activities -$11 -$42 -$64 -$74 Oil and gas extraction -$6,344 -$13,923 -$19,207 -$20,603 Mining (except oil and gas) -$3,380 -$10,396 -$15,971 -$16,872 Support activities for mining -$1,101 -$1,422 -$1,366 -$1,121 Utilities -$9,932 -$11,462 -$11,075 -$11,060 Construction $1,814 $6,292 $7,806 $10,390 Wood manufacturing $139 $212 $170 $156 Nonmetallic mineral manufacturing $165 $237 $167 $177 Primary metal manufacturing -$613 -$1,790 -$2,680 -$3,066 Fabricated metal manufacturing $921 $332 -$226 $394 Machinery manufacturing -$145 $438 $358 -$148 Computer and electronic manufacturing -$504 -$2,538 -$4,314 -$4,970 Electrical equipment and appliance manufacturing -$335 -$1,163 -$1,925 -$2,470 Motor vehicles, bodies and trailers, and parts manufacturing $1,264 $2,314 $3,081 $3,876 Other transportation equipment manufacturing -$179 -$693 -$1,190 -$1,557 Furniture and related manufacturing $338 $347 $201 $38 Miscellaneous manufacturing $58 -$467 -$875 -$1,022 Food manufacturing $944 $1,114 $983 $857 Beverage and tobacco manufacturing $483 $583 $532 $456 Textile mills; Textile mills -$20 -$208 -$401 -$459 Apparel manufacturing; Leather and allied manufacturing -$35 -$170 -$230 -$236 Paper manufacturing $91 -$120 -$364 -$532 Printing and related support activities $247 $318 $310 $316 Petroleum and coals manufacturing -$8,199 -$18,210 -$27,028 -$35,033 Chemical manufacturing -$1,016 -$5,341 -$9,824 -$13,374 Plastics and rubber manufacturing -$40 -$640 -$1,339 -$1,879 Wholesale trade $4,633 $6,327 $6,517 $7,582 Retail trade $9,893 $18,138 $23,935 $30,480 Air transportation -$3,937 -$10,395 -$17,408 -$23,916 Rail transportation -$288 -$647 -$1,028 -$1,234 Water transportation -$44 -$125 -$219 -$300 Truck transportation $492 $517 $277 $219 Couriers and messengers $222 $193 $24 -$122 Transit and ground passenger transportation $176 $237 $243 $261 Pipeline transportation -$508 -$838 -$979 -$988 Scenic and sightseeing transportation; Support activities for transportation -$869 -$2,232 -$3,788 -$5,438 Warehousing and storage $168 $162 $83 $49 Publishing industries, except Internet $1,389 $2,019 $2,271 $2,738 Motion picture and sound recording industries $1,301 $2,161 $2,875 $3,715 Internet publishing and broadcasting; ISPs, search portals, and data processing $616 $803 $810 $880 Broadcasting, except Internet $387 $536 $569 $643 Telecommunications $3,437 $5,408 $6,561 $7,767 Monetary authorities - central bank; Credit intermediation and related activities $9,636 $14,491 $16,689 $18,807 Securities, commodity contracts, investments $3,847 $5,189 $5,381 $5,641 Insurance carriers and related activities $3,813 $5,268 $5,425 $5,374 Real estate $13,816 $22,972 $27,708 $32,174 Rental and leasing services; Leasing of nonfinancial intangible assets -$1,164 -$4,245 -$7,656 -$10,299 Professional, scientific, and technical services $3,453 $2,614 $120 -$978 Management of companies and enterprises -$106 -$1,953 -$4,133 -$5,837 Administrative and support services $2,733 $3,753 $3,864 $4,288 Waste management and remediation services $277 $362 $353 $375 Educational services $1,516 $2,386 $2,849 $3,177 Ambulatory health care services $14,727 $23,715 $29,217 $34,358 Hospitals $3,872 $6,195 $7,672 $9,001 Nursing and residential care facilities $1,322 $2,142 $2,642 $3,075 Social assistance $1,071 $1,704 $2,073 $2,384 Performing arts and spectator sports $689 $1,067 $1,260 $1,481 Museums, historical sites, zoos, and parks $105 $174 $217 $253 Amusement, gambling, and recreation $972 $1,608 $1,977 $2,297 Accommodation $1,543 $2,587 $3,187 $3,731 Food services and drinking places $2,428 $3,944 $4,746 $5,405 Repair and maintenance $1,238 $1,864 $2,112 $2,379 Personal and laundry services $2,494 $4,052 $4,934 $5,649 Membership associations and organizations $985 $1,525 $1,802 $2,020 Private households $411 $737 $936 $1,092 State and local government $4,422 $5,021 $3,991 $3,966 TOTAL OF ALL SECTORS = $65,623 $72,609 $52,993 $53,536

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Figure 3.12 – Employment by Industry (thousands over baseline) 70 sector NAICS 2020 2025 2030 2035 Forestry and logging; Fishing, hunting, and trapping -1 -3 -4 -5 Agriculture and forestry support activities 0 -2 -2 -2 Oil and gas extraction -25 -56 -80 -91 Mining (except oil and gas) -13 -36 -47 -43 Support activities for mining -4 -3 -1 0 Utilities -15 -14 -10 -7 Construction 62 170 209 245 Wood manufacturing 3 5 6 7 Nonmetallic mineral manufacturing 3 5 7 9 Primary metal manufacturing -1 -2 -3 -2 Fabricated metal manufacturing 8 7 6 12 Machinery manufacturing 0 2 2 1 Computer and electronic manufacturing -2 -7 -9 -8 Electrical equipment and appliance manufacturing -1 -4 -6 -7 Motor vehicles, bodies and trailers, and parts manufacturing 7 9 10 10 Other transportation equipment manufacturing 0 -1 -2 -2 Furniture and related manufacturing 5 5 4 2 Miscellaneous manufacturing 1 -1 -2 -1 Food manufacturing 10 14 15 15 Beverage and tobacco manufacturing 1 2 2 2 Textile mills; Textile mills 0 -2 -4 -5 Apparel manufacturing; Leather and allied manufacturing -1 -3 -3 -2 Paper manufacturing 2 2 2 2 Printing and related support activities 3 5 4 4 Petroleum and coals manufacturing -2 -3 -3 -3 Chemical manufacturing 1 -2 -4 -4 Plastics and rubber manufacturing 2 0 -2 -3 Wholesale trade 34 49 52 56 Retail trade 172 289 342 387 Air transportation -14 -32 -48 -59 Rail transportation -1 -1 -1 0 Water transportation 0 1 2 3 Truck transportation 14 29 45 65 Couriers and messengers 5 9 13 18 Transit and ground passenger transportation 6 10 13 17 Pipeline transportation -1 -1 -1 -1 Scenic and sightseeing transportation; Support activities for transportation -8 -19 -28 -37 Warehousing and storage 4 5 5 6 Publishing industries, except Internet 6 8 8 8 Motion picture and sound recording industries 6 9 11 12 Internet publishing and broadcasting; ISPs, search portals, and data processing 2 3 3 2 Broadcasting, except Internet 2 3 3 4 Telecommunications 10 14 15 16 Monetary authorities - central bank; Credit intermediation and related activities 34 47 48 49 Securities, commodity contracts, investments 44 58 57 57 Insurance carriers and related activities 28 38 38 37 Real estate 62 105 121 130 Rental and leasing services; Leasing of nonfinancial intangible assets 6 7 6 5 Professional, scientific, and technical services 43 49 38 37 Management of companies and enterprises 0 -7 -13 -15 Administrative and support services 101 168 199 226 Waste management and remediation services 3 4 5 6 Educational services 46 81 101 115 Ambulatory health care services 190 311 387 459 Hospitals 57 95 118 136 Nursing and residential care facilities 35 61 77 91 Social assistance 42 71 89 103 Performing arts and spectator sports 16 24 27 30 Museums, historical sites, zoos, and parks 2 3 4 5 Amusement, gambling, and recreation 32 54 67 76 Accommodation 23 38 46 50 Food services and drinking places 91 155 185 201 Repair and maintenance 18 29 33 37 Personal and laundry services 56 88 101 110 Membership associations and organizations 34 55 66 74 Private households 49 82 96 104 State and local government 53 57 43 41 TOTAL OF ALL SECTORS = 1,344 2,140 2,458 2,785

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The data in Figure 3.13 examines the impact from the F&D carbon tax to the labor market at the national level not from the perspective of industry-by-industry but rather by each “occupation.” An occupation is a task or type of worker that may work in different industries depending on qualifications; all industries employ a number of occupations. For instance, a commercial bank in a city like Charlotte, North Carolina or Seattle, Washington will employ executives, analysts, records clerks, managers and supervisors, IT and HR professionals, sales representatives, receptionists, and maintenance personnel of any buildings and grounds. All these occupations have differing backgrounds in terms of education, position in the corporate hierarchy, and wages—hence, an examination of the impact by occupation is one means for approaching the socioeconomic aspects of PI+ analysis. In addition, occupation-by-occupation impacts are often a more accurate way to measure the net impacts on labor attributable to a policy than industry level impacts. After all, for most workers, finding a job or good pay is more important to them than the NAICS code of their employer. Some industries have a decline in their total level of employment relative to the baseline in Figure 3.12, but very few of the occupations have a similar result. These numbers represent small changes against a baseline over a long horizon, which implies hiring and natural attrition over time are the more likely means for the changes below to take place (rather than any surges in direct hiring or layoffs). For example, in the scenario of F&D carbon tax, a young engineering graduate or a certified welder is slightly more likely to find work in the automotive sector, in construction (of housing or commercial square footage), or in wind power instead of with mining, oil and gas extraction, or petroleum refining. Still other engineers might find themselves using their education to move into another quantitative occupation such as financial analysis, computer programming, research and development, professional sales, or management where jobs would be marginally more plentiful than in the baseline within several industries. This helps allow the economy and labor market to absorb these small changes over a decade’s experience.

Figure 3.13 – Employment by Occupation (thousands over baseline) 95-occupation SOC 2020 2025 2030 2035 Top executives 18 27 29 31 Advertising, marketing, promotions, public relations, and sales managers 5 8 8 9 Operations specialties managers 11 14 13 14 Other management occupations 21 34 39 44 Business operations specialists 28 41 43 47 Financial specialists 32 43 43 45 Computer occupations 17 19 16 15 Mathematical science occupations 1 1 1 1 Architects, surveyors, and cartographers 0 0 0 0 Engineers -3 -8 -13 -15 Drafters, engineering technicians, and mapping technicians 0 0 -1 -1 Life scientists 1 1 1 1 Physical scientists -1 -2 -4 -4 Social scientists and related workers 2 3 3 4 Life, physical, and social science technicians 0 -1 -2 -2 Counselors and Social workers 13 21 26 30 Miscellaneous community and social service specialists 8 13 16 19 Religious workers 0 1 1 1 Lawyers, judges, and related workers 4 5 4 4 Legal support workers 2 3 3 2 Postsecondary teachers 15 25 29 33 Preschool, primary, secondary, and special education school teachers 21 29 31 34 Other teachers and instructors 7 11 12 14 Librarians, curators, and archivists 2 2 2 3 Other education, training, and library occupations 9 14 16 18 Art and design workers 5 7 7 7

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Entertainers and performers, sports and related workers 8 13 15 17 Media and communication workers 8 12 13 14 Media and communication equipment workers 3 4 4 5 Health diagnosing and treating practitioners 78 128 158 186 Health technologists and technicians 46 75 93 109 Other healthcare practitioners and technical occupations 1 2 2 3 Nursing, psychiatric, and home health aides 32 54 68 81 Occupational therapy and physical therapist assistants and aides 4 7 9 11 Other healthcare support occupations 37 60 74 85 Supervisors of protective service workers 1 1 1 1 Fire fighting and prevention workers 1 1 1 1 Law enforcement workers 3 4 3 3 Other protective service workers 13 20 23 25 Supervisors of food preparation and serving workers 9 14 17 19 Cooks and food preparation workers 28 46 55 60 Food and beverage serving workers 63 107 128 141 Other food preparation and serving related workers 13 21 25 27 Supervisors of building and grounds cleaning and maintenance workers 6 11 13 15 Building cleaning and pest control workers 52 87 102 112 Grounds maintenance workers 43 80 100 116 Supervisors of personal care and service workers 3 5 6 6 Animal care and service workers 5 8 9 10 Entertainment attendants and related workers 9 15 18 20 Funeral service workers 1 1 1 1 Personal appearance workers 30 48 57 64 Baggage porters, bellhops, and concierges; Tour and travel guides 1 1 1 1 Other personal care and service workers 52 89 108 124 Supervisors of sales workers 17 27 32 36 Retail sales workers 102 170 201 225 Sales representatives, services 23 32 33 33 Sales representatives, wholesale and manufacturing 11 16 17 18 Other sales and related workers 15 24 28 31 Supervisors of office and administrative support workers 17 25 29 32 Communications equipment operators 1 2 2 2 Financial clerks 40 61 67 74 Information and record clerks 64 94 104 114 Material recording, scheduling, dispatching, and distributing workers 23 34 37 41 Secretaries and administrative assistants 51 80 91 103 Other office and administrative support workers 43 66 73 80 Supervisors of farming, fishing, and forestry workers 0 0 0 0 Agricultural workers 1 1 1 1 Fishing and hunting workers 0 -1 -1 -1 Forest, conservation, and logging workers 0 0 0 -1 Supervisors of construction and extraction workers 3 8 9 11 Construction trades workers 34 89 108 129 Helpers, construction trades 3 8 10 12 Other construction and related workers 2 3 4 4 Extraction workers -11 -22 -28 -28 Supervisors of installation, maintenance, and repair workers 3 5 6 7 Electrical and electronic equipment mechanics, installers, and repairers 4 6 7 7 Vehicle and mobile equipment mechanics, installers, and repairers 12 19 21 24 Other installation, maintenance, and repair occupations 23 41 47 54 Supervisors of production workers 2 1 1 1 Assemblers and fabricators 7 8 8 9 Food processing workers 6 9 10 11 Metal workers and plastic workers 5 4 3 5 Printing workers 2 3 2 2 Textile, apparel, and furnishings workers 5 6 5 5 Woodworkers 2 3 3 3 Plant and system operators -3 -5 -6 -6 Other production occupations 12 14 14 15 Supervisors of transportation and material moving workers 2 4 4 5 Air transportation workers -5 -13 -19 -24 Motor vehicle operators 30 52 68 88 Rail transportation workers 0 -1 -1 0 Water transportation workers 0 0 0 1 Other transportation workers 4 6 6 6 Material moving workers 25 35 37 45 Military 0 0 0 0 TOTAL OF ALL OCCUPATIONS = 1,344 2,140 2,458 2,785

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Carbon Dioxide Emissions (annual forecast, national level)

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Figure 3.14 – These lines illustrate a baseline for emissions without the tax from the Reference Case in the AEO and ReEDS (blue). The alternative (gold) after a $10 per year tax, price elasticity of demand in CAT, and grid optimization in ReEDS represents a significant reduction in emissions—of 52% by 2035. The baseline is not exactly the same as the one in the AEO because this projection uses ReEDS for the power generation portion of the emissions forecast. They are rather close, however. AEO 2013 projects a 2.4% increase in national emissions from 2015 to 2035 while the blue line above projects a 5.5% total increase.

Carbon Dioxide Savings by Source (annual from baseline, national level)

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Figure 3.15 – This shows the savings in carbon dioxide emissions by major source broken out into power generation, non-power domestic fuels, and reduced fossil fuel exports.

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The data in Figure 3.15 reveals trends about the disposition of the economy, technology, and their ability to find savings. The power sector, in particular, illustrates the initial likelihood to save emissions. There are full details in a later section. However, in summary, a relatively low tax rate in the 2010s and 2020s (of $50 per year to $100 per year) and the certainty of a higher rate in the 2030s (within the lifespan of any investments) means a large reduction in coal-fired generation and its replacement with gas, nuclear, and renewable sources. This greatly reduces emissions from power “early” in policy life. Reductions from residential or business consumers of natural gas and petroleum products (especially motor gasoline) are slower given changes in end-use prices and the relatively inelastic price responses.37 The response is slower when the impact to gasoline prices is less than $1 per gallon, although it does accelerate later when it approaches $2 per gallon. “Blue” and “gold” in Figure 3.15 represent mostly a net reduction in American and world emissions—the “red” section, however, shows only the implied savings from reduced exports of coal, natural gas, and petroleum products. “Red” does not necessarily represent a net world reduction, however, given that foreign production of fossil fuels (from the Middle East, Australia, or other regions) may increase to make up for reduced American exports.

Carbon Dioxide Savings (cumulative from baseline, regional level)

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37 For example, the average price elasticity of demand in this study for motor gasoline from the original CTAM and PI+ is -0.62, which means a 1% in gasoline prices only reduces demand by 0.62%

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Carbon Tax Revenues (total, national level)

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Figure 3.17 – The results above are for the revenues from the carbon tax in blue and receipts from the border adjustment in gold. These revenues are significant and robust despite a decline in emissions in CAT and ReEDS in the late 2020s and 2030s—the increasing tax rate keeps revenues robust through at least the two-decade window. For context, federal revenue in 2012 came in at $2.45 trillion (and corporate income tax receipts at $242.3 billion).38

Monthly Dividend by Family

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2028 2030 2020 Figure 3.18 – This divides the “blue” general carbon tax revenue in Figure 3.17 across all American households for their projected share of the monthly carbon tax dividend.

38 From CBO data, please see,

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Cost of Living (regional level)

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Figure 3.19 – This represents the change in the cost of living for households in PI+ from higher energy costs and any pass-through of higher prices from businesses because of a higher cost of production. PI+ utilizes an internal Personal Consumption Expenditure (PCE) index, which is similar to the Consumer Price Index (CPI) though different in some of its treatment of housing and local taxes. The carbon tax does elevate the cost of living in the model in every one of the nine regions. Energy-intensive regions such as ESC and WSC have the largest impacts while less energy-intensive regions like NE and PAC have smaller results. However, the above is a modest, “one-time” vector adjustment of less than 3% over a twenty-year period. This is the equivalent to adding one “extra” year of inflation between 2016 and 2025 before achieving price stability relative to the “do-nothing” baseline sometime in the late 2020s.

The next section and Figure 3.20 describe the average impact to energy prices by commodity attributable to the carbon tax. The results on average electricity prices are out of ReEDS, and the results for petroleum products and natural gas are the calculated differences in CAT based on the inherent carbon dioxide content of the fuels, the tax rate, and the price forecasts in the Reference Case of the AEO. The difference in natural gas prices are especially high in the results because the absolute price forecast for natural gas is lower than for petroleum products in the EIA data.39 The numbers, as in Figure 3.19, represent a one-time adjustment against the baseline and not any projected or assumed growth rate in energy prices of the future. In fact, retail energy prices might fall in the future if NEMS finds a market solution where such results are feasible. Most of the impacts by region are not divergent to any significant degree—a $1 per ton carbon tax still corresponds to an excise tax on retail gasoline of $0.009 per gallon anywhere in the country (given that chemistry does not vary between MA, SA, MNT, or other regions). Higher prices do have a negative impact by themselves. Contextualizing them with the cost of living in Figure 3.19 and the macroeconomic results in the previous section implies the total economy offsets some of the potential harms below.

39 In energy-equivalent units (such as dollars per MMBTU or other thermal measurements)

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Energy Commodity Prices (national level)

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Figure 3.20 – Most commodities see a linear increase in their prices relative to the baseline with the national level, linear increase in the rate. Electricity, on the other hand, can switch out of carbon-intensive coal and natural gas and into zero-carbon nuclear, wind, and solar, which reduces the impact in the 2020s and 2030s. All these have a negative effect, but the macroeconomic balance is positive, and it does generate revenues for the F&D and incentivize the significant reduction of national and regional level emissions.

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Cost of Living (by quintile, national level) 2.5% 2.0% Lowest 20% 1.5% Low-Middle 20% 1.0% Middle 20%

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2033 2023 2029 Figure 3.21 – This adapts the data in Figure 3.19 to display by income quintile (the 20% increments) instead of by region.40 The impact to the cost of living between different quintiles is nearly indistinguishable in the modeling’s net results.

A critical concern with a carbon tax is that it may behave regressively—cost of living spikes for low-income households disproportionately more than that for earners and households higher in the income spectrum. There is a bevy of literature on the topic.41 The general theory is such that lower-income households have much less flexibility with their spending and, unlike wealthier households, cannot cutback on luxury purchases (electronics, travel, and new vehicles) in order to cover the costs of necessities like food and fuel. This logic is sensible; however, consumption of energy is “income elastic” as wealthier people tend to live in larger dwellings, own more cars, use public transportation less, travel by air, and have more appliances and electronics. This aids in “leveling” the share of income for energy purchases across income quintiles. Other aspects of this policy help to equalize its socioeconomics. As demonstrated in Figure 3.22 ahead, the occupational mixture of new jobs over the baseline from F&D carbon tax tend to be in the lower 60% of the distribution. Increasing the quality of the labor market for workers—in terms of employment opportunity and wages—helps offset any of the negative effects from higher energy costs. The Congressional Budget Office (CBO) assessed a F&D-like idea (a refundable income tax rebate) as a means for offsetting the cost of higher energy prices for lower-income households under a carbon tax, concluding, “A refundable tax rebate of a fixed dollar amount would be progressive, providing greater relief as a percentage of income to low-income households.”42 Furthermore, “Based on earlier CBO work, fully offsetting the additional cost that a carbon tax

40 Above calculations in PI+ based on the Consumer Expenditure Survey 2011 by the BLS, , for the methodology of the calculations, please see, 41 There is some disagreement, although most “static” studies on this question look only at prices and not macroeconomic feedbacks in markets like in PI+, for example, please see Corbett A. Grainger and Charles D. Kolstad, “Who Pays a Price on Carbon,” National Bureau of Economic Research (NBER), NBER Working Paper #15239, August 2009, 42 CBO has a full discussion of the pros and cons of a refundable income tax credit (which has similar incentives to F&D though with a different structure, being nested in the existing tax code) on pp. 8-9 of Terry Dinan, “Offsetting a Carbon Tax’s Cost on Low-Income Households,” Congressional Budget Office (CBO), November 2012,

p. 35 REMI * Synapse would impose on households in the lowest income quintile would take roughly 12% of the gross revenue.”43 The F&D would approximate this distribution of the funds. Household size is not uniform across the spectrum, and, on average, more members for a household means there are more adults available for full-time employment and adolescents for part-time work. The median household with an income under $25,000 per year has less than two members, the median one from $25,000 per year to $100,000 per year has two to three, and the median household over $100,000 per year has three or more.44 If the average family has around 2.0 or 3.0 shares of the F&D (two adults and two children) and the average low-income family has 1.5 or 2.0 (two adults or one adult and one child), then low-income households would receive between 10% and 15% of F&D funds—satisfying CBO’s criteria to “make whole” the bottom 20%. A F&D design would also create an implicit “guaranteed income” system in the same way as the Alaska Permanent Fund, which would complement and supplement existing welfare benefits.45

Total Employment (by quintile, national level)

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43 Ibid., p. 13 44 For the raw data table from the U.S. Census on household size and income expectation, please see, 45 Please see Megan McArdle, “They’ll Pay You to Live in Switzerland,” Bloomberg, November 15, 2013, ; Annie Lowrey, “Switzerland’s Proposal to Pay People for Being Alive,” New York Times, November 12, 2013,

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Real Disposable Personal Income (regional level)

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2028 2030 2020 Figure 3.23 – This is the regional level impact to aggregate personal income. For example, if a hypothetical region had five income-earners each making $100,000 per year, then total real disposable personal income (RDPI) in the region would be $500,000 per year. Given that the above is real income, this means it is the net of increasing the number of jobs available and wages, the F&D rebates to households, and any negative impact from higher energy prices reflected in the price index in Figure 3.19. Most regions have a positive impact, although the WSC region has a neutral/slightly negative impact (with a smaller population).

Real Disposable Personal Income (national level)

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2028 2030 2020 Figure 3.24 – Total RDPI at the national level increases between $150 billion and $300 billion depending on the year, which is as much as 1.25% more than levels in the baseline.

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Real Disposable Personal Income (per capita, regional level)

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2028 2030 2020 Figure 3.25 – This recasts the results from Figure 3.23 in per capita terms. This means the above results take account of not only changes in RDPI—the net of the impact to the labor market, F&D checks, and energy prices—but also to population and demographic trends. For instance, the Midwestern regions, ENC and WNC, add $60 billion and $25 billion to annual RDPI by 2035, respectively, although here their per capita impact is close to zero. Therefore, each region must have experienced a large increase in its population relative to baseline, which is the happenstance under the F&D carbon tax simulations here.

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2028 2030 2020 Figure 3.26 – This aggregates the regional level results to the national level. Real per capita income is $500 more by 2025 and almost $800 more by the models’ sunset in 2035.

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Labor Share of Income (national level, RDPI/GDP) 76.2% 76.0%

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Figure 3.27 – Finishing the conversation at this time on the distributional aspects of carbon tax, this shows the labor share of income in the PI+ model—defined as the ratio of real disposable personal income to GDP here. The baseline has a decline in the labor share from around 76% in 2016 down to near 75% by 2035, but the alternative policy reverses this.

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2028 2030 2020 Figure 3.28 – This shows the “delta” to the labor share of income, RDPI/GRP, by region (the equivalent to the difference between “blue” and “gold” in Figure 3.27). All of the regions have an increase in their labor share of income relative to the baseline in the simulations. The increase in WSC is the most because it maintains a neutral level of employment (in the consumer-centric and labor-intensive service sectors) in the face of a decline in GRP.

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Electrical Power Capacity (national level)46

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Gas-CC Capacity Capacity (GW) 400 400 Coal-CCS Coal-IGCC 200 200 Coal-New Cofiring 0 0 Coal-Old Scrubbed 2010 2020 2030 2040 2010 2020 2030 2040 Coal-Old Unscrubbed

Figure 3.29 – This shows the total installed capacity by technology type at the national level from ReEDS. Power capacity and generation results for the nine regions are in the appendix.

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Figure 3.30 – This is also from ReEDS on national level generation. Results run to 2040 because ReEDS is “forward-looking” in its capacity installments vis-à-vis future prices.

46 Gas-CC-CCS = combined cycle-carbon capture and storage, Gas-CT = combustion turbine, Gas-CC = combined cycle, Gas-CCS = carbon capture and storage

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Several trends in Figure 3.29 and Figure 3.30 help drive the further economic, climate, fiscal, and demographic results elsewhere.47 The most notable trend is that a carbon tax at $10 per year starting in 2016 eliminates coal-related capacity and generation by the late 2020s. When assuming thermal equivalence, coal is a carbon-intensive resource—one MMBTU of energy from coal releases between 93.28 kilograms and 103.69 kilograms of carbon dioxide into the atmosphere.48 Natural gas, in contrast, averages 53.06 kilograms per MMBTU, which makes gas approximately twice as “carbon-efficient” as coal for energy.49 Aside from the carbon dioxide 50 reductions of less coal, coal plants are also large sources of NOX and SOX emissions, which influence air quality, quality of life, and amenity. Coal-derived capacity and generation gives way to some additional natural gas in the short- and medium-term in the model. However, ReEDS looks at anticipated future prices when making decisions about new investments, which means even natural gas seem less competitive in the future when optimizing for the higher tax rate in the late 2020s and 2030s. Some natural gas does remain for base-load purposes, however, and especially gas with carbon capture and carbon sequestration at scales in the 2030s. Replacing coal and natural gas on the grid are, to degrees, nuclear power, biomass, geothermal, wind, and solar. Gas-CT capacity also expands to meet needs for a few peak hours each year. As these plants see use so infrequently, little overall generation from them appears in Figure 3.30. Hydroelectricity is present and significant in both the baseline and the alternative, and especially in the MNT and PAC regions of the western United States. The paucity of major rivers with steep elevation changes that still lack a dam in North America prevents the hydroelectric sector from expanding much even with a carbon price. The baseline trend for nuclear power is such that the existing fleet ages in place before eventually retiring in the next few decades, its replacement being a mixture of gas and renewable energy.51 The carbon price helps in establishing price competitiveness for nuclear in the medium- and long-term. Instead of a decline, nuclear renews itself or even expands in the 2030s. Wind farms experience the greatest impact, and the additional wind replaces much of the decline in coal, although not in an equal manner. Solar follows in a similar direction for increasing as fossil-based generation declines. Additionally, the uptick for renewable power in the $10 per year alternative increases the total capacity in the United States for power generation—the intermittency of wind and solar means there needs to be more generation capacity and storage to make up for it. Generation in the alternative is less than that in the baseline, however, because of a price response to higher wholesale and retail electricity pricing. With carbon pricing, scale wind and solar would assume

47 Supplementary discussion to these results available in the technical appendix 48 According to the EPA table on fuel emissions factors by source, typically in kilograms per MMBTU, 49 This white paper considers only the impact of taxing carbon dioxide and not that of fugitive methane lost in natural gas extraction or deployment—the second is an important issue, although quantifying the total “leakage” from the system (including landfills) is much more uncertain at this point than working on carbon alone, and other EPA regulations are starting to address the issue, please see James Bradbury, Michael Obeiter, Laura Draucker, Amanda Stevens and Wen Wang, “Clearing the Air: Reducing Upstream Greenhouse Gas Emissions from U.S. Natural Gas Systems,” World Resources Institute (WRI), April 2013, 50 Over 65% of SOX emissions are from utility generation, particularly coal, for example 51 For example, please see Matthew D. Wald, “Economics Forcing Some Nuclear Plants into Retirement: Aging and Expensive, Reactors Face Mothballs,” New York Times, October 23, 2012,

p. 41 REMI * Synapse a comparable role to each other on the grid in providing variable generation during sunny and windy hours. Different cost assumptions on the relative cost of wind52 versus solar53 would lead to the “lime green” for wind and the “gold” for solar trading share with each other in the graphs in Figure 3.29 and Figure 3.30. In the alternative, by 2035, the ReEDS model shows nearly all American power generations coming from zero- or low-carbon sources such as solar, wind, geothermal, hydro, nuclear, and captured gas.

The next section covers improvements in air quality from changing sources in power generation and reduced combustion of transportation fuels. Specifically, it includes two compounds—NOX and SOX emissions—that are part of the ReEDS and CAT models. These emissions play no direct part in the carbon pricing of $10 per year, but they are implied, indirect effects of the emissions and power generation effects elsewhere. Social costs of NOX and SOX are the same here as those in REMI TranSight, the transportation-oriented version of PI+, which monetizes the social costs of emissions in a manner consistent with EPA guidelines.54 The values are $0.005 per gram for NOX and $0.0025 per gram for SOX (in 2012 dollars).

Improved Air Quality (regional level)

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Figure 3.31 – This illustrates the value of reduced NOX and SOX emissions from power generation, gasoline, and diesel. The lions’ shares of savings are in the ENC and the WNC, which have the heaviest proportion of coal-fired generation in the United States. Regions with a smaller share of coal power generation, such as NE or PAC, have less of an impact.

52 The source for the long-term cost assumptions about wind power in ReEDS is the ongoing research from U.S. Department of Energy (USDOE), “A New Vision for United States Wind Power,” 53 Long-term solar cost assumptions for ReEDS also come from an ongoing USDOE research project, “Sunshot Vision Study,” 54 Based on methodologies developed by Mark Delucchi at University of California-Irvine, please see,

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2028 2030 2020 Figure 3.32 – In continuation of the benefit-cost, the above is Figure 3.31 divided by $6.2 million for the average social cost of a premature death for air quality-related conditions or reduced quality of life. The exact figure for this calculation varies between federal sources;55 the $6.2 million is the “unadventurous” figure usually required by the U.S. Department of Transportation (USDOT) in accounting for air quality benefits.

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Figure 3.33 – These are annual saved lives summed over time to 230,000 in twenty years.

55 For a discussion of some of the values used by EPA and USDOT, please see Binyamin Appelbaum, “As U.S. Agencies Put More Value on a Life, Businesses Fret,” New York Times, February 16, 2011,

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2028 2030 2020 Figure 3.34 – This is the net change in population, over or under the baseline, for the nine regions after migration due to changes in the labor market, the regional cost of living, and quality of life/amenity benefits. The increase in population in ENC and WNC is from their large share of the improved air quality and quality of life, as Figure 3.35 demonstrates.

Economic Migration Determinants (regional level) NE 100 PAC 75 MA 50 Real Relative Wage Rate MNT 25 ENC Relative Job 0 Opportunity Quality of Life WSC WNC and Amenity

ESC SA

Figure 3.35 – This radar chart displays the determinants for economic migration and population. The factors are not of equal strength—amenity (“red”) is the strongest and dominates the results with the population increase in ENC and WNC. The regions are on a 100-point scale with the “best” region equal to 100, the relative “worst” at 0, and a hypothetical “average” region at 50 with the others scaled in the middle.

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Alternative Fiscal Case: “Across-the-Board” (ATB) Tax Cuts Dedicating the funds from a revenue-neutral carbon tax to a F&D system is just one of countless policy options, and the nature of the allocation of the revenues has strong implications for the net economic and demographic impacts. This alternative fiscal case, which means to test the models’ responsiveness and economy’s sensitivity, looks at the “most simple” of those options— an across-the-board (ATB), revenue-neutral tax cut to the largest federal revenue categories that are up for revision during tax reform periods. This considers the three categories that are the largest revenue items for the budget: (1) the personal income tax, (2) the payroll tax/FICA, and (3) the corporate income tax. Modifying the simulations to cover a contrasting utilization of the revenues from a carbon tax has little significant impact on the climate and air quality results above—the price incentive of $10 per year is still the same in coal, electricity, gas, and petroleum markets, after all—so the difference examined here is the economic impact. The comparison looks at three “headline” results of employment, GDP, and RDPI.

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2028 2030 2020 Figure 4.1 – The incentives for work and investment under ATB produce employment and GDP, although the rebates of F&D keep RDPI higher than in the alternative fiscal case.

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The results in Figure 4.1 follow from the economic reasoning inherent in the models. Increasing the return to labor and capital by lowering taxes on income and business entities encourages work and investment, although such a program has less influence on consumer spending (at least initially) compared to F&D. Reducing some business costs through cuts to the corporate income tax, however, increases the rate of investment in the United States, improves the trade balance by reducing imports and increasing exports, and expands GDP over time relative to the baseline and F&D. This result brings about the higher percentage impact to employment with ATB given the increased GDP encapsulates increased labor demand. Conversely, the F&D system, for reserving more of the funds for direct rebates to households and eventual consumer spending, has advantages in boosting spending in labor-intensive, localized industries, which keep the overall impact to employment roughly parallel amid the cases. It also increases the total household share of national income/GDP. Despite the differences in Figure 4.1, neither case is wholesale different from the other on a national scale. The economic models and general intuition of higher prices reducing energy demand, changing power investments away from fossil fuels, improving air quality, reducing the level of economic activity associated with the capital-intensive energy production and distributional supply chain, and increasing the output of relative labor-intensive, consumer-related industries holds for both. Relative to each other, ATB describes a slightly larger economic “pie” with more exports, although with a smaller share for households of national income. F&D illustrates a slightly smaller economy from ATB (not the baseline) with more consumer spending and overall RDPI for households. Each simulation has its respective story on a growing, less carbon-intensive economy.

Congressional Budget Office (CBO) In May 2013, the CBO released a report and literature review on several of the possible policy options regarding carbon taxes for Congress and the White House and likely economic, fiscal, and environmental effects.56 The study did not attempt to quantify the potential impacts of a carbon tax from either deficit reduction (“CBO has not estimated how a carbon tax combined with a deficit reduction policy would affect output”)57 nor revenue-neutrality (“CBO has not quantified the effects of a tax swap”).58 The overall directions of the results in this white paper are, nonetheless, broadly consistent with CBO’s finding and the literature. Most notably, CBO says that apt fiscal reform to the general tax code in combination with carbon pricing could potentially increase output or GDP. To quote, “However, various studies that have looked at different types of tax swaps have concluded that a well-designed swap would significantly lower the economic costs of a carbon tax, and a few studies have concluded that a tax swap could lead to a net increase in output.”59 Such a statement fits this study into the latter category where returning the funds to households to engender consumer spending leads to a net increase in employment and GDP from the tax swap or rebate. The main difference between the CBO research and this study is that CBO considered only marginal tax rate changes, while the prime

56 Available online, please see “Effects of a Carbon Tax on the Economy and Environment,” Congressional Budget Office (CBO), May 22, 2013, 57 Ibid., p. 10 58 Ibid., p. 11 59 Ibid., p. 10

p. 46 REMI * Synapse simulations here looked at a refund system.60 Both of the approaches would lead to an increase in consumption, but the guaranteed income of F&D would lose some of the positive incentives that come with changes to marginal rates. Adapting a CBO statement on lump-sum payments to lower-income households to adjust for their welfare losses, which is similar to the F&D, “Those payments would not increase people’s incentives to work or invest, and thus would not lead to greater economic productivity.”61 After all, if the “rebate” from the carbon tax goes to households only through lower income tax rates, then individuals would be more likely to “seek the benefit” by participating in the labor force or working longer hours. PI+ captures some of these differences in the results of Figure 4.1. Adjusting marginal rates leads to higher GDP and productivity (essentially the same quantity of labor for additional output) than relying on F&D by itself. The feedbacks in PI+, not necessarily present in other models at the same level of regional or industrial detail or with the same exact structure, lead to the “wash” in the results for employment and RDPI. Cutting marginal income taxes and F&D have differences in their welfare effects and short- and long-term incentives; yet, each still leads to a massive jump in aggregate consumer spending that dictates much of the macroeconomic results with a boost to the output of labor-intensive and service sectors.

CBO generally concurs with the other crucial results of CAT and PI+ on climate and economic impacts from carbon pricing. Foremost, CBO’s description of the likely industries to see a decline in their output match those in Figure 3.9 with coal mining, oil and gas, other types of metallic and nonmetallic mineral product mining, refining, chemical manufacturing, and other heavy manufacturing.62 With climate, CBO’s hypothetical $20 per ton carbon tax (with a 5.6% annual increase in the rate) would reduce national emissions in the first decade by 8%.63 Given adjustments take time, the emissions reduction in the final year of the decade window would have to be somewhat more than 8%. This is more than the 6% reduction from the CAT baseline in 2018 (the year of $30 per ton), although this reduction would be closer to 10% to 12% if it were a plateau and had more time to adjust, thus making it consistent with CBO numbers. Regarding fiscal implications, CBO comments, “Because rising tax rates would lead to a decline in emissions, the amount of revenues generated by a carbon tax would eventually decline, as well.”64 To continue, “However, if the tax rate grew slowly, it could produce rising revenues for many decades and allow the economy to adjust gradually to less emission-intensive ways of producing goods and services.” This statement is consistent with the results in Figure 3.15 and Figure 3.16 of a carbon tax phased at $10 per year serving as a robust revenue item for the federal government or F&D “trust” through at least 2035. The money would be enough to return significant amounts of cash to every household or even replace major revenue items such as the corporate income tax or much of FICA for Social Security, Medicare, and other programs. The results here have many more details, and they report the distributional aspects of this policy between regions and industries in a way not typical to CBO analyses.

60 “A well-designed tax swap would cut marginal tax rates (the rates on an additional dollar of income), thereby raising the after-tax returns that people receive from work or investment and leading to increases in those activities,” Ibid., p. 10 61 Ibid., p. 12 62 Ibid., p. 9 63 Ibid., p. 3 64 Ibid., p. 3

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Technical Appendix This section describes the details behind the quantification and the modeling of the results at the heart of this report. The descriptions are “input-oriented,” looking mostly at how the input variables and assumptions to ReEDS, CAT, and PI+ came out with references to the general documentation for the original construction of ReEDS and PI+. This technical appendix starts with the ReEDS model, inputs, assumptions, and how it generates the power technology data and information reported in this study. The portion on CAT covers the original methodology from CTAM and the additions made to CAT to take account of power switching (from ReEDS),

NOX and SOX emissions, multiple regions, the border adjustment, and the integration of this data into the policy simulation in PI+. The PI+ partition covers the basics of the model, its dynamic structure, and how each of the data inputs to policy variables influence the simulation and the results of the white paper. The final simulation looked at 160 sectors, twenty years, and nine regions, which is 28,800 potential results even before looking at the type of results (such as total employment, GDP, or income). This gives a comprehensive accounting of the potential impacts of a F&D carbon tax from many variable inputs.

Figure 5.1 – This is a screen capture from the PI+ software including all of the exogenous variables used for the final economic and demographic impact simulation. Many of those inputs—such as power generation investments or quality of life amenities—are significant results for their own sake and reported here from ReEDS and CAT. The fiscal inputs include the personal income tax, the payroll tax, and the corporate income tax for alternative fiscal cases, though, for the most part, those inputs were zero and all funds went into the F&D. Every variable set represents its own set of benefits and costs to the regional economies.

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The ReEDS Model This subsection provides a high-level overview of the costs and technology characteristics of the ReEDS model runs. A comprehensive outline of the methodology behind the model is available from NREL;65 the Renewable Electricity Future study thoroughly documents all assumptions at current inside the modeling system.66

The ReEDS model is a long-term capacity expansion and dispatch model of the electrical power system in the United States developed by NREL. It has a high-level of renewable resource detail with numerous wind and solar resource regions, each with availability by resource class and unique grid connection costs. Model outputs include generation, total capacity, transmission expansion, total system costs, electricity prices, and emissions of carbon dioxide, NOX, SOX, and mercury (Hg). The model operates out to 2050 in 2-year steps, with each 2-year period divided into 17 time slices representing morning, afternoon, evening, and night in each of the four seasons, plus an additional summer peak. The ReEDS model includes data on the existing fossil fuel facilities in each of the model’s 134 Power Control Areas (PCAs) based on data reported in EIA’s Form 860 Annual Electric Generator Report.67 Under a carbon tax, ReEDS will change both the dispatch of existing units and the build of new units, as well as transmission additions and interregional transfers. The resulting scenarios are a product of many input assumptions, several of which have definitions here.

Technology Data Most technology parameters come from the EIA’s AEO 2013.68

Capital Costs Fixed O&M Variable O&M Heat Rate (1000$/MW) ($/MW-year) ($/MWh) (MMBTU/MWh) Hydro $3,719 $14 $3 9.63 Gas-CT $817 $7 $13 9.89 Gas-CC $962 $14 $3 6.59 Gas-CC-CCS $2,088 $32 $3 7.41 Goal-Pulverized $2,924 $32 $4 8.66 Coal-IGCC $3,771 $51 $7 8.17 Coal-CCS $5,211 $66 $4 10.95 Oil-Gas-Steam $965 $24 $4 10.50 Nuclear $4,767 $93 $2 10.31 Geothermal $6,050 $112 $0 9.62 Biomass $4,098 $106 $5 13.31 Landfill Gas $8,492 $388 $9 13.46 Wind (onshore) $1,759 $48 $0 N/A Wind (shallow offshore) $4,436 $125 $0 N/A Wind (deep offshore) $5,732 $160 $0 N/A Utility PV $3,173 $16 $0 N/A CSP (no storage) $5,022 $52 $0 N/A

Figure 5.2 – These values provide technology costs and performance characteristics.

65 Please see, 66 Please see M.M. Hand, S. Baldwin, E. DeMeo, J.M. Reily, T. Mai, D. Arent, G. Porro, M. Meshek, D. Sandor, eds., “Renewable Electricity Futures Study,” 4 vols., NREL/TP-6A20-52409, National Renewable Energy Laboratory (NREL), 67 Please see, 68 Assumptions for wind in Figure 5.2 are for Class-3 resources and do not include the cost of interconnection, and hydro and geothermal costs represent the baseline costs for a new facility—costs will increase from this level for power control areas with resources harder to access

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LBS/MMBTU LBS/MWh (2015) NOX SOX Hg CO2 NOX SOX Hg CO2 Gas-CT 0.1 0.0 0.0 119 0.9 0.1 0.0 1,194 Gas-CC 0.0 0.0 0.0 119 0.2 0.0 0.0 795 Gas-CC-CCS 0.0 0.0 0.0 18 0.3 0.0 0.0 134 Coal-Old Scrubbed 0.1 0.2 0.0 205 1.1 1.9 0.0 2,047 Coal-Old Unscrubbed 0.1 1.2 0.0 205 1.1 12.8 0.0 2,103 Coal-New 0.1 0.1 0.0 205 1.0 0.5 0.0 1,800 Coal-IGCC 0.1 0.1 0.0 205 0.7 0.5 0.0 1,698 Coal-CCS 0.1 0.1 0.0 31 0.9 0.5 0.0 341 Oil-Gas-Steam 0.2 0.3 0.0 137 1.8 0.6 0.0 1,459 Biomass 0.0 0.1 0.0 0 0.0 3.2 0.0 0 Cofiring 0.1 0.2 0.0 205 1.2 1.1 0.0 2,202 Landfill Gas 0.0 0.0 0.0 -250 0.0 2.0 0.0 -3,408 Nuclear 0.0 0.0 0.0 0 0.0 0.0 0.0 0 Geothermal 0.0 0.0 0.0 0 0.0 0.0 0.0 0 Solar 0.0 0.0 0.0 0 0.0 0.0 0.0 0 Wind 0.0 0.0 0.0 0 0.0 0.0 0.0 0

Figure 5.3 – These are the electricity emissions rates (in 2015, national level averages).

LBS/MMBTU LBS/MWh (2015) NOX SOX Hg CO2 NOX SOX Hg CO2 Gas-CT 0.9 0.1 0.0 119 0.9 0.1 0.0 1,131 Gas-CC 0.2 0.0 0.0 119 0.2 0.0 0.0 781 Gas-CC-CCS 0.3 0.0 0.0 18 0.3 0.0 0.0 134 Coal-Old Scrubbed 1.1 1.9 0.0 205 1.1 1.9 0.0 2,047 Coal-Old Unscrubbed 1.1 12.8 0.0 205 1.1 12.8 0.0 2,103 Coal-New 1.0 0.5 0.0 205 1.0 0.5 0.0 1,792 Coal-IGCC 0.7 0.5 0.0 205 0.7 0.5 0.0 1,527 Coal-CCS 0.9 0.5 0.0 31 0.9 0.5 0.0 286 Oil-Gas-Steam 1.8 0.6 0.0 137 1.8 0.6 0.0 1,459 Biomass 0.0 3.2 0.0 0 0.0 3.2 0.0 0 Cofiring 1.2 1.1 0.0 205 1.2 1.1 0.0 2,202 Landfill Gas 0.0 2.0 0.0 -250 0.0 2.0 0.0 -3,408 Nuclear 0.0 0.0 0.0 0 0.0 0.0 0.0 0 Geothermal 0.0 0.0 0.0 0 0.0 0.0 0.0 0 Solar 0.0 0.0 0.0 0 0.0 0.0 0.0 0 Wind 0.0 0.0 0.0 0 0.0 0.0 0.0 0

Figure 5.4 – These are the electricity emissions rates (in 2050, national level averages).

Much of the benefits in this report are from moving out of capacity types at the top of the above distribution and toward the bottom in Figure 5.3 and Figure 5.4. The renewable, zero-carbon dioxide sources also have reduced NOX and SOX emissions.

Load Data The ReEDS model only covers the electrical power sector, and thus it takes its energy and peak load requirements from AEO 2013. There is no endogenous capability to add energy-efficient (EE) resources or capital, although it is likely that additional EE would come at the carbon tax levels under discussion here.69 Figure 5.5 shows the growth patterns assumed in the baseline from AEO 2013 and the alternative based on implicit price elasticity.

69 This would have some influence on the economic impact results, but they would be small compared to the gross results of placing a price on energy and recycling the revenue with F&D

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Figure 5.5 – These are the national level load requirements on the ReEDS model for the baseline—which is the same as in the Reference Case as the AEO 2013—and an alternative that assumes low load from reduced energy purchases due to higher electricity prices. Each has internal growth of around 4.0 TWh needed in 2014 to nearly 5.0 TWh needed by 2040.

Resource Assumptions “Renewable Electricity Futures: Volume 2” has detailed resource supply curve assumptions, and there is a summary of the methodology here for reference.70

Wind The ReEDS system models onshore wind, shallow offshore wind, and deep offshore resources. For each type, the model has data on five resource classes for wind power in every one of the 356-regions across the country. These resources come from GIS analysis of high-resolution wind speed data with exclusions for land-use, topographical constraints, and wildlife habitats. A stepwise supply curve accounts for the cost of connection individual wind sites to the existing power distribution and transmission grid.

Concentrating Solar Power (CSP) The ReEDS model considers CSP without storage and CSP with at least 5-hours of storage. Similar to wind, five resource classes are in each of the 356-regions for CSP based on a detailed GIS analysis—although most resources are in the Southwest and West.71

Utility-Scale and Distributed Rooftop Photovoltaic (PV) Characteristics for utility-scale resources are in each of the 134 PCAs with costs from the 2012 Sunshot Vision study.72 Generation profiles are averages from satellite data from 1998 to 2009.

70 Please see, 71 Portions of ENC, WSC, MNT, and PAC in the nine region breakout 72 Please see,

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Distributed rooftop photovoltaic deployments and performance are from another NREL model, SolarDS,73 and inputs exogenously into ReEDS. All scenarios use distributed rooftop deployment consistent with a 50% cost reduction from 2010 to 2020. This level does not change across the scenarios, although more aggressive cost reductions may take place at higher tax levels given further investments and research.

Biomass There are both dedicated biomass power plants and cofired power plants supplied with biomass in each of the 134 PCAs. Their supply curves come from the USDOE study, “U.S. Billion-Ton Update” from 2011, which estimated the potential biomass supplies within the contiguous United States based on assumptions about both sustainable residue biomass levels and new, dedicated feedstock that might come online in the future.74

Geothermal The ReEDS model includes supply curves for conventional geothermal, as well as near-field enhanced geothermal (EGS) and deep EGS. Near-field EGS resources are hot enough for electricity production but still relatively shallow, so they are substantially less expensive than deep EGS resources. A typical ReEDS run will allow conventional and near-field EGS, but exclude deep EGS due to substantial uncertainty with the technology.

Hydroelectricity NREL is in the process of updating hydroelectric resources based on recent work by Oak Ridge National Laboratory (ORNL). This work will explore the potential to add power production at existing non-powered dams as well as original research for the ongoing “Hydro Vision” study paired with the wind and solar research projects by USDOE.75

Retirements The ReEDS model retires existing conventional power plants based on assumed lifetimes. Fossil units can also have endogenous retirements. The assumptions are such that coal units under 100MW have a 65-year life and ones larger than that continue to operate for 75-years. Natural gas units have a 55-year life. Fossil units retire endogenously in the model if they do not see utilization beyond a minimum capacity for more than 4-years. Nuclear plants built before 1980 retire after 60-years. For those built after 1980, the model allows them two license renewals— that results in them having a de facto lifespan of 80-years.

Integrating Renewable Resources In addition to accounting for the cost to bring renewable power onto the grid, the model also accounts for several operational parameters of variable resources. The ReEDS model calculates

73 For an introduction and methodology to this additional modeling system, please see Paul Denholm, Easan Drury, and Robert Margolis, “The Solar Deployment System (SolarDS) Model: Documentation and Sample Results,” National Renewable Energy Laboratory (NREL), September 2009, 74 Please see “U.S. Billion-Ton Update: Biomass Supply for a Bio-energy and Bio-products Industry,” U.S. Department of Energy (USDOE), August 2011, 75 For an introduction, please see,

p. 52 REMI * Synapse curtailed energy, firm capacity value, storage resources, and the additional included operation reserve requirements (due to forecast errors) from variable resources.

Supplemental Discussion Total capacity grows substantially in the alternative, $10 per year case to meet both rising peak demand and to compensate for the reduced capacity contribution from intermittent resources, such as wind and solar, as compared to traditional fossil fuel generation. Nationally, capacity starts at 1,000 GW in 2010 and by 2040 grows to 1,300 GW in the baseline and 1,440 GW in the $10 per year case. This alternative case reflects a few key trends.

Between 2020 and 2030, most coal undergoes either conversion into co-fire with biomass or outright retirement. Natural gas and wind meet the need for capacity, and they appear the most economical resource to replace retiring coal plants and meet the underlying, baseline growth in demand over time. Due to reduced capacity contributions from wind resources, total nameplate capacity in the alternative case remains similar to or higher than the baseline despite reduced energy demand overall in the $10 per year carbon tax.

Integrating intermittent resources requires increasingly flexible capacity resources to meet load in periods where renewable output falls (or, conversely, to reduce their load when renewable output surges). The model endogenously determines the capacity value of wind and solar each year, which declines with increasing levels as increasingly marginal sites come online. For example, in the $10 per ton tax case the median percentage of wind capacity counted as “firm” decreases from 18% in 2010 to 7% in 2040. Additional wind and solar also require new, flexible, responsive reserve resources to guard against errors in the output forecast. By 2040, this results in building an extra 60 GW of dispatch reserve requirements. Toward the end of the study period, the demands placed on the system by increasingly intermittent resources—coupled with increasingly large carbon taxes—result in the reintroduction, beginning, and then the significant expansion of low-carbon base-load technologies such as nuclear plants and natural gas with carbon capture and storage (CCS) at an industrial scale.

Nationally, wind and solar represent about 5% of 2014 generation and, by 2040, this grows to 37% in the alternative case. Nuclear, which mostly retires in the baseline, expands from 20% at current to around 25% of total generation. Coverage for the remainder of the balance from the reductions in coal is from a combination of geothermal, hydroelectricity, and natural gas combined-cycle units (gas-CC, and many gas-CCS). The model can build coal with carbon capture and sequestration technology and retrofit old plants to the same standard; however, even with an assumed capture rate of 85%, the emissions from coal-CCS would still be high enough those hypothetical plants are uneconomical with these prices. While storage plays an important role, it is a net negative generation technology due to imperfect efficiency, and it does not appear on the generation chart to any significant degree.

The carbon tax results in a dramatic reduction in carbon dioxide emissions. In the baseline, emissions rise slowly, concurrent with the increase in the load, resulting in cumulative electrical-derived emissions of 85 gigatons from 2010 to 2050. With the $10 per year price, cumulative emissions by 2050 are closer to 27 gigatons, which is a 68% reduction over the period. As the tax level increases between scenarios, it quickly becomes clear the marginal cost

p. 53 REMI * Synapse of additional carbon abatement is rising rapidly. For example, a $15 per year carbon tax from 2016 to 2050 only results in 11% fewer emissions than $10 per year with a 50% increase in the cost for emitters throughout the whole of the economy.

A carbon tax represents a large departure from the current power system, resulting in significant turnover and replacement of many of today’s plants in the next twenty-five years. The rapid investment in resources in these scenarios—particularly wind—may seem difficult to imagine given today’s energy sector. However, a society that implements a significant carbon tax would presumably commit to solving the complex logistical, manufacturing, and regulatory challenges necessary to reduce emissions to this degree.

The results vary at the regional level, and the second appendix has the exact data. To discuss some basic trends in the baseline and alternative, however, most regions continue to use a substantial amount of coal out to 2040 without the carbon tax. Large portions of the existing nuclear fleet retire, and its replacement is either natural gas or wind. The $10 per ton case is sufficient to drive out coal in all regions. Those with limited wind resources, such as ESC, tend to replace coal with nuclear, while WNC (the farmlands of Iowa, Kansas, Minnesota, Missouri, Nebraska, North Dakota, and South Dakota) builds the largest amount of wind and couples it with base-load renewable power and transmission for balancing.

The CAT Model CAT is an evolution of CTAM for state carbon analysis to add dimensions and additional inputs for economic and fiscal models to its simulations. This section will cover the basic methodology of CTAM, its integration with ReEDS, and the added features to make it into the CAT system. A summary slide deck is available online,76 as well as a Microsoft Excel-based copy of the original CTAM for the state of Washington.77

The “core” of CTAM and CAT is an exogenous case, typically the Reference Case, from the AEO. This study used the Reference Case from AEO 2013 because the full AEO 2014 only became available late in this research’s projected timeline (on May 7, 2014 versus a planned release of the white paper in early June). The current NREL calibration of the ReEDS uses AEO 2013 and, for the sake of consistency between the models, this paper stays with AEO 2013. The most important table is “A2” for total energy consumption by sector and source.78 This table is also available at the regional level, which was a direct influence on the choice of the nine regions for assessment (and not, initially, states or cities, which PI+ can do, as well).79 The AEO baseline is

76 Please see Keibun Mori, Roel Hammerschlag, and Greg Nothstein, “Carbon Tax Modeling for Washington State,” 2013 Western Energy Policy Research Conference, September 5, 2013, 77 Please see, 78 Please see, 79 Here is, for example, table A2 for New England (NE), please see,

p. 54 REMI * Synapse in thermal units (quadrillions of BTUs), but an emissions factor allows these energy units to undergo conversion into carbon dioxide emissions.80 For example, the Reference Case forecast in AEO 2013 for NE has residential consumption of propane totaling 0.036 quadrillion BTUs. From the EPA table, the combustion of enough propane to release one MMBTU of energy81 emits 63.07 kilograms of carbon dioxide into the air. The 0.036 quadrillion BTUs in the AEO forecast is 36,000,000 MMBTUs. When multiplied by the EPA emissions factor, this means the AEO forecast implies carbon dioxide emissions from this sector, this source, and in this year equal about 2,270,000,000 kilograms. This is 2,270,000 metric tons and 2.270 million metric tons when converting by first thousands (103) and then millions (106). Finding carbon tax revenues by sector/source/year/region is a multiplication of the rate by the forecast, which would be $113.5 million in this case at $50 per ton.82 This “static” calculation off the Reference Case is not the whole story on how CTAM and CAT work, however, given this simple calculation fails to take account of any cutbacks in energy purchases by consumer because of higher prices. Without a price response, emissions in the baseline and alternative are the same and the implicit price elasticity of demand is zero—perfectly inelastic, there is no possible price change large enough to induce a change in spending habits. To deal with this involves another data set from AEO and another set of calculations off the baseline.

The main mechanism in CTAM and CAT to determine the impact to emission, and thereby to carbon tax revenues, is price elasticity of demand. The AEO also provides a price forecast for energy by sector and source in table A3.83 This forecast is in dollars per MMBTU. In order to find an alternative price, the model works backwards—it calculates the carbon tax per MMBTU of fuel by type from the EPA data and then adds the additional cost on top of the baseline one from the Reference Case. For example, one MMBTU of gasoline averages 71.26 kilograms of carbon dioxide.84 A carbon tax of $30 per ton would charge $2.13 per MMBTU of gasoline (which is 0.0713 metric tons multiplied by $30 per ton).85 The Reference Case has the price of gasoline in the MA region at $25.64 (in 2012 dollars) in 2018. The case’s carbon tax rate in that year is $30 per ton in 2016 dollars—or $28.66 per ton in 2012 dollars. 86 Finding the adjusted price for a simulation involves adding the carbon price ($2.04 per MMBTU in 2012 dollars)87 to the baseline price ($25.64 per MMBTU) to give an adjusted price of $27.68 per MMBTU. This is a 7.96% change in the market price from alternative to baseline, which factors into the price elasticity response. CTAM and CAT each include exogenous parameters for the price elasticity of demand for different fuel types—how much does a 1% increase in market prices decrease consumer spending. In the original CTAM, Mori included a literature survey of econometric analyses and meta-studies of price elasticity by fuel type, averaged them, and then included them as adjustable parameters. REMI either evaluated these parameters as probable or adjusted

80 Please see, 81 1 gallon of propane = 91,600 BTUs, so 1 MMBTU of propane would be approximately 10.92 gallons, or about 2.31 times the size of standard 4.73 gallon refillable steel tanks for backyard cooking 82 The primary case’s rate in 2020 was $50/ton, so $50/ton * 2,270,000 = $113.500 million 83 Please see, 84 1 gallon of gasoline, depending on the exact blend or mixture, averages 0.114 MMBTU of energy 85 $2.14/MMBTU * 0.114MMBTU/gallon = $0.27 gallon (adjusted for rounding) 86 $1.00 in 2016 is about $0.955 in 2012 according to the price index in PI+ 87 $2.13/MMBTU (the rate before adjusting for the price index) * (0.955/1.00) from the previous note

p. 55 REMI * Synapse them for consistency with the preexisting price elasticity of demand in research for PI+ and its treatment of energy.88 The critical one is gasoline, which this study kept from Mori at -0.62 (a 1% increase in price engenders a 0.62% decline in consumption) phased over a decade. Price response is not instantaneous but dynamic in order to give a more realistic sense of the time it takes consumers to adjust to new prices and for old, energy-intensive capital items to wear-out and see replacement by newer, more efficient equipment for final utilization. Transportation fuels take ten years to phase and non-transportation fuels take twenty years. To return to the example, a 7.96% increase in the cost of gasoline would reduce demand for the commodity by 4.94%.89 The new demand forecast becomes the factor in CAT’s forecast of emissions versus a baseline and, after multiplying it by the carbon tax rate, the potential fiscal effects in the economic model. Neither CTAM nor CAT include cross price elasticity for switching between liquid and gaseous fuel types where possible (such as the replacement of a fuel oil boiler with natural gas heating or a car powered by an internal combustion engine with an electric vehicle). There would be some of this switching on the margin, but the size of the effect would be diminutive compared to the overall response to higher prices. Price elasticity of demand would still handle the overall change in demand even with switching and, in light of inelasticity, in an analytically conservative manner.

Figure 5.6 – This is the structure of the original CTAM in a graphic designed by the Northwest Economic Research Council (NERC) at Portland State University.90 Much of the above remains intact in CAT, although a few changes to its structure and assumptions allow it to go “further back” in the energy supply chain, integrate electricity data from ReEDS, and take account of other effects like border adjustments, exports, and air quality concepts. Changes in these areas allow CAT to bring more to the analytical inputs to the economic impact model.

88 For a description of the estimation procedure of consumption elasticity in PI+, please see, 89 7.96% * -0.62 = -4.94% 90 Please see Jeff Renfro and Jenny Liu, “Carbon Tax and Shift: How to make it work for Oregon’s economy,” Northwest Economic Research Council (NERC), March 1, 2013,

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CTAM has strong concepts for price elasticity of demand, emissions forecasting, tax revenues, and the grounding of the AEO forecast, but there are several limitations to its approach at the national scale. First, because it uses only price elasticity off the Reference Case, CTAM has no concept of power switching from coal/gas toward wind/solar/nuclear. It can reduce aggregate demand for electricity in the forecast but not adjust for the carbon content of the power over time in response to price incentives for utilities and investors. For instance, if the baseline has 25% coal-derived generation in the AEO and, by extension CTAM, then 25% of the generation in the alternative will still come from coal, even though the ReEDS runs here show coal is unlikely to persist with a significant tax. In order to improve on this, the CAT model takes output data from ReEDS on power generation and capacity by type and adjusts the carbon tax on electricity to the changing levels of carbon-intensity in power generation, which ReEDS simulates in detail. The structure of CTAM alone makes it best for examining the fiscal and climate effects of a low carbon tax assessed at retail in a state or region with little in terms of power generation or resource extraction. States like Massachusetts or the rest of New England would be ideal for this sort of policy design and modeling. NE has little coal-based generation to switch away. The area’s status as a hydrocarbon importer with almost no extraction of its own would favor a retail tax because assessing the tax at the point of extraction would miss imports (nearly all of their energy), and taxing interstate trade of MMBTUs would have implementation problems and might conflict with the Commerce Clause. CTAM describes situations like this well, although the power switching in ReEDS and CAT are necessary to handle other parts of the country. CAT keeps CTAM’s original methodology of adjusting consumption, emissions, and revenues based on the price elasticity of demand for liquid and gaseous fuels, though, for electricity, it entirely replaces price elasticity and data from AEO with everything from ReEDS. This change along with others described below allow for CAT to conceive of the carbon tax at the point of extraction with an assumption of a “perfect,” 100% pass-through of energy prices down to end-use consumers in residencies, commerce, and industry. Reality would be more complicated as dynamic markets adjust to the carbon tax. The modeling here does take account of the aggregate, economy-wide effects after pass-through, and CAT illustrates how all energy consumers (the end-use above as well as utilities via ReEDS and exports) react to the price incentives of a tax early in the supply chain. CAT gives results for the downstream. Unlike CTAM, however, it does not miss on incorporating incentives for producers, which makes it analogous to assessing an upstream tax with a heavy or complete pass-through to consumers.

Besides accounting for endogenous power switching from ReEDS, here is a list of additional features in the CAT model intended as PI+ inputs.

 Border Adjustment  Electrical Power Investments

 NOX and SOX Emissions  Fossil Fuel Exports

The next subsection describes the methodology in CAT behind each of these before moving on to the PI+ model and the inputs into it from Figure 5.1. Overall, these processes aim to develop additional inputs for the economic model, PI+, for simulations.

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Border Adjustment Assessing the fiscal and economic impact of a border adjustment requires two inputs: (1) a robust forecast of imports to the United States by type and (2) a way to transform the import forecast into an explicit forecast of the carbon dioxide emissions behind any imports. From there, the next step is to multiply the carbon content of the imports by the tax rate and feed this back into the economic model. The adjustment decreases competitiveness of carbon-intensive imported goods on the American market and, using the funds gained at the port of entry, it increases the competitiveness of American exports to the rest of the world. This requires several data sources and the baseline forecast in the PI+ model.

PI+ includes a detailed forecast of imports by region, year, and industry, quantified in the form of all monetary value of the trade. Thus, this took care of step one, and the next step was to somehow change those dollar values into carbon quantities. For this, the resource was a report by the U.S. Department of Commerce on the ratio of the output of various NAICS industries to their carbon emissions.91 It reported, for example, that amongst the manufacturing industries the most “carbon-intensive” (defined as the ratio of output to carbon dioxide emissions) manufacturing sector was nonmetallic mineral products (NAICS 327)92 with 1.613 million metric tons of carbon dioxide emitted for $1 billion of output in 2006. The least carbon-intensive manufacturing sector was leather and allied products (NAICS 316)93 with 0.072 million metric tons for $1 billion in output. Unfortunately, detailed information on the carbon-intensity of imports from every other nation of the world and dozens of industries probably does not exist at the current time. Instead, the estimation procedure utilized the import forecast from PI+ (increasing monetary values of imports with a growing world economy and increasing levels of connectedness) with a few assumptions. The first is that foreign imports now have the same carbon intensity as American production from 2002, which is the median case from the data in the U.S. Department of Commerce report. The second is that the carbon-intensity of foreign imports improves at the same rate as the carbon-intensity of the American economy improves according to the AEO forecast.94 This places the average exporter to the United States a decade behind this country in terms of efficiency but gaining at the same technological rate as American industry. While an imperfect estimation, this does create a “stable” forecast of revenues from the border adjustment where increasing import volumes and the decreasing carbon-intensity of those imports “wash” each other out, and the increase in the carbon tax rate does mean a gentle, upward, linear slope in anticipated adjustment revenues to 2035.

91 Please see, “U.S. Carbon Dioxide Emissions and Intensities Over Time: A Detailed Accounting of Industries, Government and Households,” U.S. Department of Commerce (USDOC), September 10, 2010, 92 “The nonmetallic mineral product manufacturing subsector transforms mined or quarried nonmetallic minerals, such as sand, gravel, stone, clay, and refractory materials, into products for intermediate or final consumption,” please see, 93 “Establishments in the leather and allied product manufacturing subsector transform hides into leather by tanning or curing and fabricating the leather into products for final consumption,” please see, 94 The year-over-year growth rate in the energy-intensity row of this table,

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Electrical Power Investments One of the important economic development implications of a carbon tax is the potential for an expansion of the installation and maintenance of alternative energy resources in different areas of the country. Wind and solar projects, in addition, might be more labor-intensive or localized during the construction phase than the existing coal, natural gas, and nuclear fleets. Changing over from fossil-based generation to renewable power will require a number of requirements and an increased rate of new builds to make up for the difference, as well. The calculation involved looking at the year-to-year change in net capacity added or subtracted by region from the ReEDS results. The data in Figure 5.2 allowed for the conversation of electrical capacities into dollars based on the capital costs of a megawatt of different technology types. Regarding operations and maintenance expenses, the calculation was similar on multiplying the current difference in net capacity between the baseline and alternative and monetizing it with the information from Figure 5.2. It was the same for the variable cost (mostly fuel inputs) from the ReEDS data and results. The transaction data does not cover power generation beyond its generic type; the industry accounting data from the Bureau of Economic Analysis (BEA),95 for example, only goes down to the three-digit NAICS.96 Some concepts go to 388-industries, but even this does not cover the six-digit NAICS where different types of power generation make themselves at home.97 Hence, the simulations used the NAICS industries the most analogous to the unique sorts of production and economic activity associated with each of the power types. Natural gas vectored toward oil and gas extraction,98 coal toward coal mining,99 nuclear and hydroelectricity toward construction and custom turbine installation,100 wind power toward industrial wind turbine manufacturers,101 and solar panel power toward semiconductor manufacturing.102 The exact variable in PI+ was the “demand” for production from these industries, which is an important distinction from directly increasing the “output” of these sectors in the model. Demand is the purchase or utilization of a good and not its production. This means actual production could be local or it could take the form of imports from another region. PI+ can illustrate this difference with the preexisting trade flows of commodities from region-to-region and the rest of the world in the model. For instance, wind turbines built for a new offshore wind product (anticipated as cost-effective and needed by ReEDS) in SA might come from a production facility in ENC, WNC, or Germany. Solar cells for a CSP project in MNT (Arizona or New Mexico) might come from PAC (California) or another country (such as China, Japan, Mexico, or Canada).

95 Please see, 96 Please see, 97 NAICS 221111 for hydroelectric power through NAICS 221118 for “other” power generation 98 NAICS 211, 99 NAICS 2121, 100 NAICS 23, 101 NAICS 336, 102 NAICS 3344,

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NOX and SOX Emissions This involved integrating data from ReEDS and taking a few additional steps beyond the price elasticity of demand of the general CAT with additional data from the AEO and exogenous parameters on average vehicle emissions per mile traveled for various types of pollutants. As illustrated in Figure 5.3 and Figure 5.4, ReEDS includes results on NOX and SOX emissions in its simulations. Power-related emissions are oftentimes the deciding factor on the quality of the local atmosphere, although emissions from cars and trucks play a large part in urban centers in certain parts of the country. As described in the price elasticity of demand discussion before Figure 5.6, the AEO provides a forecast of the quantity of motor gasoline and diesel fuel purchased by region and by year in quadrillions of BTUs. CAT adjusts this to give a similar forecast only accounting for the price elasticity response from the carbon tax. The AEO also provides a forecast of total VMT for cars103 and trucks104 at the national level. This data is not available at the regional level, but the share of fuel demand in table A2 (motor gasoline for cars, diesel fuel for trucks) serves as an adequate proxy to share the national level VMT down to regional level VMT. This handles the baseline, and the alternative forecast for VMT by region simply has the same adjustment in percentage terms as the change in demand for gasoline and diesel MMBTUs from the price elasticity. That is, if CAT projected a 5% decrease in gasoline consumption in energy units in a region, then it also projected a 5% decline in car VMT relative to the baseline. This gives a forecast of baseline VMT by region and adjusted VMT by region for the two overarching modes with the assumption that most gasoline purchases are for cars and most diesel purchases are for medium or heavy trucks. EPA provides data on average emissions 105 106 by mode for the average VMT. For cars, this is 0.693 grams per VMT of NOX and 0.120 107 grams per VMT for SOX and, for trucks, 17.483 grams per VMT for NOX and 0.120 grams per

VMT for SOX. Multiplying these parameters by the derived VMT forecasts gives quantities of pollutants, and subtracting the baseline from the alternative gives the results. This methodology may miss some small efficiency improvements in terms of vehicular-sourced NOX and SOX emissions against the Reference Case baseline and the EPA data. Conversely, the price elasticity of demand calculations do capture and reductions in fuel purchases for any reason—including driving less, switching modes (public transportation, cycling, walking for individuals or onto railroads or water for freight), or buying cars or trucks with greater fuel-efficiency in the first place. The forecast in grams undergoes the same monetization as the results from ReEDS. CAT adds the two of them together, reports a monetary figure of the benefit-cost value of saved pollution, and divides them by a parameter for the value of a life to give a simple estimation of the saved premature deaths from regional air pollution.

103 Please see, 104 Please see, 105 The main page with the studies and information for these parameters, which are also in REMI TranSight, is here, please see, 106 Please see, “Average Annual Emission and Fuel Consumption for Gasoline-Fueled Passenger Cars and Light Trucks,” U.S. Environmental Protection Agency (USEPA), 107 Please see, “Average In-Use Emissions from Heavy-Duty Trucks,” U.S. Environmental Protection Agency (USEPA),

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Fossil Fuel Exports Energy trading oftentimes takes place in global markets, which means CAT needed concepts for international imports and exports of coal, natural gas, and petroleum to and from the United States. Petroleum has long had a “world market,” and coal and natural gas are beginning to have similar dynamics in North America with Canada and the United States gearing up to begin the export of coal and gas via LNG.108 Imports of fossil energy are implicitly part of the energy consumption forecast (table A2) from the Reference Case; many of those MMBTUs demanded at the regional level originally started in a foreign well or mine before they came to the United States for final consumption. PI+ already takes account of the fact much of the energy used in the United States comes from Canada or overseas. For instance, demand for coal mining or oil and gas exaction can find its supply in another region or the rest of world through the model’s trade tables. Rising demand for petroleum products in NE or MA can engender an increase in the output of related industries in ESC or WSC or increase imports from the rest of the world. Demand for industrial coal from processing facilities in ENC can come from mines in MNT or the SA region. While price elasticity eventually makes its way back to reduced imports through the trade tables in the structure of PI+, there still needs to be a way in CAT to indicate the decrease in the competitiveness of America fossil fuel exports on the world market because they are now subject to a carbon price. AEO 2013 provides a forecast of energy exports by type (for coal, natural gas, and petroleum) in the Reference Case in quadrillions of BTUs.109 This table is at the national level only, so data from PI+ on each regional estimated share of international exports by the relevant industries (coal mining and oil and gas extraction) serves as a means to subdivide to the regional level. The data and intuition match in this case. WSC dominates the share of natural gas exports, and it has a large portion of the petroleum ones (though the PAC region also has a significant amount given the large refinery clusters near Los Angeles, San Francisco, and Seattle). Coal exports come from SA (which includes West Virginia) and ESC (eastern Kentucky and Tennessee) with a rising share for MNT (Wyoming). The calculation of alternative exports from the United States under carbon pricing is similar to the “domestic” CAT—the price of these fuels increases based on their underlying carbon content and the carbon tax rate, and the world market through price elasticity by purchasing less of them from suppliers in the nine regions of the United States. The elasticity comes from implicit price elasticity of demand from the world market for American exports in PI+. This has an economic impact, too; regions like WSC lose a portion of their exports (“X”), which therefore lowers GRP. It may not have a significant impact on regional job creation given the high capital-intensity for these industries, but it does help to explain the negative impact to GRP in the WSC region and the neutral impact to GRP for ESC. Unfortunately, ReEDS, CAT, and PI+ collectively do not have detailed enough coverage of world energy markets to say how much foreign production of fossil fuels would make up for any decrease in the exports from the United States. Hence, this section is mostly for adjusting GDP to match for a decline in exports and not for any climate implications.

108 For example, please see Keith Johnson and Ben Lefebvre, “U.S. Approves Expanded Gas Exports,” Wall Street Journal, May 18, 2013, 109 Please see,

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The PI+ Model This study used a nine region, 160 sector PI+ model of the United States and constituent regions to perform this analysis. PI+ is a computerized, multiregional, dynamic model of regions, states, counties, or other subnational disaggregates of the United States in a Microsoft Windows-based program. PI+ relies on four quantitative methodologies to guide its overall approach to regional modeling. The different methodologies highlight each other’s strengths while compensating for any of their weaknesses when used individually.

1. Input-output tabulation (IO)110 – At the core of PI+ is an input-output table (also known as a Social Accounting Matrix, or SAM).111 An IO table captures the structure of the regional or national economy in terms of business-to-business transactions, wages, consumption, and can provide the “multiplier” from an additional dollar of spending or purchase. To provide a classic example, an automobile assembly plant in Michigan will have a lengthy supply chain across the rest of ENC and the rest of the United States. Vehicle assembly in Michigan requires parts from suppliers in Ohio and Wisconsin. Those suppliers need fabricated and primary metal products from steel mills in Indiana and Pennsylvania, drifting into the MA region. Railroads based in Omaha and Kansas City (WNC) move final and intermediate products around the Midwest, and Great Lakes boats based in Cleveland or bring in foreign supplies or iron ore from the Mesabi Range of northern Minnesota via Duluth. An IO model captures the effect of adding a dollar to car demand in Michigan and its echoing through the economy and into other industries. However, IO models have several weaknesses. They are very “rigid” in the computational sense, have no time horizon (only “before” and “after”), no concepts for the scarcity of labor and capital, and no internal concept for the competitiveness of different industries in dissimilar regions. They also sometimes lack trade flows between regions, they have no variables for energy prices or costs, and no adjustments to how the structure of supply chains and the overall economy responds to supply-side shocks. PI+ includes other modeling techniques to deepen the representation of the structure of the economy over time and include these various concepts.

2. Computable general equilibrium (CGE) – CGE models are a broad classification of models that rely on the principles of equilibrium economics. In essence, the addition of CGE principles to PI+ introduces market-based concepts and illustrations of the supply and demand for labor, housing, consumption, commuting, production, intermediate inputs, imports, exports, government spending, and other concepts. The CGE portion of the model demonstrates what happens after all markets have had a chance to “clear” in relation to each other back to a stable equilibrium. For example, the opening of a large manufacturer of wind turbines near a small city will cause more than just a multiplier at the local and regional level. The new plant will bring jobs with it, and, depending on the size and characteristics of the local labor pool, this will bid the price of labor up in the general economy of the area as more workers find a job at the plant. Certain technical

110 Also called Leontief modeling after its developer, Wassily Leontief, who won a Nobel Prize for it in 1973, please see, 111 The raw data for the IO table comes from BLS, please see, “Inter-industry relationships (Input/output matrix),”

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skills may be unavailable locally, so some households will move from other parts of the country in order to work there. This increases the city’s population and puts upward pressure on local housing prices, which has the benefit of increasing local property tax revenues for the school board but also discourages others from buying homes. Some households may locate in another city far away. Others will make a calculation based on time, distance, price, and square footage and then locate themselves in a neighboring town with lower housing prices and commute the distance back to the city in order to work there or in the turbine manufacturer. Higher housing prices might also induce a developer to build a new housing subdivision in the area, as well. All of these effects, as well as any consequential loss of competitiveness and output from higher energy costs for commercial and industrial enterprises, are not present in pure IO models but an endogenous part of the CGE structure of PI+.

3. New Economic Geography – Economic geography is the study of the idea that cities and interconnected industries are the engines of economic growth. PI+ utilizes this theory to illustrate how specialized labor pools and industry clusters given a region a competitive advantage relative to its competitors. For instance, for labor inputs, the “selection” of trained surgeons in cities known for university-attached medical schools or healthcare clusters (such as Baltimore, Boston, and Minneapolis/Rochester, Minnesota) is much higher than cities known more for agricultural services or leisure (such as Helena, Montana). Under ceteris paribus, a hospital in a city like Cleveland or Houston is going to have an easier time finding a qualified, productive worker than a similar facility in Las Cruces, New Mexico or Chattanooga, Tennessee. This forms part of the competitiveness measure in PI+, particularly for labor-intensive industries like healthcare, finance, insurance, entertainment, and professional and technical services. The same process is in effect for capital-intensive or intermediate input-reliant firms in terms of their relative access to a concentrated supply chain. These industries tend to cluster on top of each other in a certain niches across the country, such as with the textiles and furniture industries in SA, agribusiness in WNC, and shipbuilding on the Gulf Coast of ENC and WSC. The size and overall health of these clusters is important to the economic wellbeing of any region or city. Different parts of the United States tend to specialized in a handful of key industries—maintaining them is essential to maintaining local growth and the quality of the regional economy. PI+ assesses these clusters in the baseline and in any alternative simulations like a F&D carbon tax.

4. Econometrics – REMI uses historical data to determine the parameters necessary to populate the mathematics of the model. This includes estimating elasticity (the implicit slope of supply and demand curves), terms, and “time lags” on how long it takes an individual market to adjust back to equilibrium. Some markets, such as that for labor, tend to work relatively quickly as people and firms look for jobs and employees while other, such as housing, tend to take more time as buyers, sellers, developers, banks, and regulators are always trying to catch-up to a new set of incentives in regional and national housing markets. Some equations in the model are entirely econometric in nature, and this allows the IO and CGE portions of the model to work with each other in a truly dynamic, multiyear structure with multiple regions.

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The methodology and equations set in PI+ are peer-reviewed and available to the public.112 The initial publications by REMI’s founder, Dr. George I. Treyz, and his team have appeared in such publications as the Journal of Regional Science,113 the Review of Economics and Statistics,114 and the American Economic Review.115 The data inside PI+ comes from public data agencies such as the BEA, BLS, EIA, U.S. Census, the U.S. Department of Defense, the U.S. Department of Education, and several other sources.116 Trends in the macroeconomic portion of the model are from the BLS industry forecast and the Research Seminar in Quantitative Economics (RSQE) at the University of Michigan-Ann Arbor.117 This all provides the background data and methodologies for running exogenous policy simulations.

Figure 5.7 – This shows the explicit structure of PI+ with cause-and-effect linkages between different concepts and sectors of the economy and demographics.

112 For the full PDF of model equations, please see, 113 Dan S. Rickman, Gang Shao, and George I. Treyz, “Multiregional Stock Adjustment Equations of Residential and Nonresidential Investment in Structure,” Journal of Regional Science, Vol. 33 (2), 1993, pp. 207-2019 114 George I. Treyz, Dan S. Rickman, and Michael J. Greenwood, “The Dynamics of U.S. Internal Migration,” Review of Economics and Statistics, Vol. LXXV, No. 2, May 1993, pp. 209-214 115 Please see, 116 For a full accounting of the data sources and estimation procedures in the REMI model, please see, 117 Their homepage on the Michigan and American economies is here,

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Each block in the above structure of Figure 5.7 describes a different portion of the economy. Block 1 is the macroeconomics of the model with final demand and GDP by component. The calculations in Block 2 make up the “business” perspective on the economy where firms will maximize profits by minimizing costs in hiring decisions (employment) and capital (their investments). Block 3 is a full demographic model with natural changes, labor mobility within the United States, and international migration and emigration. Block 3 also includes the interactions of households with the general economy through labor force participation, wages, and consumer spending. Block 4 introduces equilibrium concepts to the labor market concepts, the cost of living (including energy prices), and production costs (for labor, capital, fuel inputs, and intermediate goods). Block 5 illustrates the competitiveness of a region with explicit regional purchase coefficients (RPCs), which quantify how likely an area is to keep imports away while moving its own exports out to other regions and countries.

Other applications of the REMI model in the energy sphere include the aforementioned carbon tax studies at the state level in Massachusetts, Washington, and California in integration with CTAM. It is also possible to integrate REMI with other models besides CTAM, ReEDS, and CAT, including grid and dispatch models such as GPCM®118 or IPM,119 or travel-demand models (TDMs) such as TransCAD and Cube Voyager.120 PI+ provides a flexible framework with a plethora of variables to make this level of integration typical.

Integrating ReEDS, CAT, and PI+ The ReEDS model and CAT in concert produced seven main types of exogenous inputs to PI+ in order to illustrate the direct costs and benefits of a F&D carbon tax. Each one of these inputs affected the economic model in different ways in the structure from Figure 5.7, and the results reported were for all inputs ran at the same time to give a net analysis. The seven categories included the following inputs, charted out in Figure 5.8 below.

1. Monthly rebate checks that increase consumer spending 2. Higher end-use energy costs for residential, commercial, and industrial sectors 3. Changing investments in power generation capacity and O&M expenses 4. Quality of life and amenity benefits from improved air quality 5. Decreased competitiveness for foreign products on the American market through the border adjustment’s assessment 6. Increased competitiveness for American products on foreign markets through the recycling of the border adjustment 7. Reduced fossil fuel exports by type and by region

118 Scott Nystrom and Robert Brooks, “The Macroeconomic Impact of LNG Exports: Integrating the GPCM Natural Gas Model and the PI+ Regional Model,” United States Association for Energy Economics (USAEE), presented at the annual conference 2012 in Austin, Texas, 119 Please see, 120 Described in the appendix of the TranSight documentation, please see,

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Figure 5.8 – This is the same chart as Figure 2.1 from earlier in the report. It shows the seven main types of inputs into PI+ to make the economic impact simulation reported here.

The next table, Figure 5.9, charts the source of the seven categories for PI+ from either ReEDS or CAT and any information from inside the baseline in PI+ necessary to share the information down to the regional level or 16o sectors. For example, the AEO only reports consumption of fuel types by broad sector (residential, consumer, and industrial) in table A2. PI+ needs inputs at its level of industrial detail. To rectify this, a multiplication of regional output by industry by the fuel share (by electricity, natural gas, and petroleum type) in the IO table gives an estimation of fuel demand by type for the various industries. This becomes a share by industry and region for breaking the high-level AEO data down to PI+ in a consistent manner.

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Data Source Sharing Procedure Policy Variable Population by region 1 CAT Personal taxes (amount) from PI+ Consumer price (fuel oil and other fuels, Industry output CAT (underlying data natural gas, electricity, and motor vehicle multiplied by fuel from AEO 2013 and fuels), electricity costs (by individual 2 absorption coefficient electricity results from industry), natural gas costs (by in IO table between ReEDS) individual industry), residual costs (by industries and regions individual industry) CAT (calculated off 3 N/A Exogenous final demand (by industry) results from ReEDS) CAT (transportation) Non-pecuniary amenity (amount, by 4 and ReEDS (from N/A region) power generation) CAT (with Share of imports to Production costs (by industry and 5 supplementary data different regions and region) from PI+) industries CAT (with Share of exports from Production costs (by industry and 6 supplementary data different regions and region) from PI+) industries Share of exports from CAT (calculated from Industry sales/exogenous exports (by 7 fossil fuel-related AEO baseline) region and industry) industries by region

Figure 5.9 – This shows the exact data transfers from ReEDS and CAT into PI+ in order to perform these simulations from the modeling flowchart in Figure 5.8. The ReEDS runs and the AEO 2013 form the backbone of the study before building up changes and exogenous inputs into PI+ to represent the net economic, fiscal, and demographic impact of F&D carbon taxes.

3,000

2,500 2,000 1,500 1,000

500 Economic Indicator Economic

0

2012

2014 2016

2018

2052

2054 2056

2032

2034

2022 2036

2024 2042

2044

2026 2058

2046

2050

2038

2028

2048

2030

2020

2040 2060 Control Forecast Policy A Policy B

Figure 5.10 – This last illustration shows the fundamental idea of the PI+ model, where the changes in Figure 5.9 induce the economy to change over time from a baseline (Policy A or Policy B versus the Control Forecast) in order to compare the difference.

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New England (NE)

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Electrical Power Capacity (NE level)

Baseline ($0/year) Alternative ($10/year) 50 50 Storage 45 45 Solar Wind

40 40 Biopower

35 35 Geothermal Hydro

30 30 Nuclear 25 25 Oil-Gas-Steam Gas-CC-CCS 20 20 Gas-CT

Gas-CC Capacity Capacity (GW) 15 15 Coal-CCS 10 10 Coal-IGCC Coal-New

5 5 Cofiring 0 0 Coal-Old Scrubbed 2010 2020 2030 2040 2010 2020 2030 2040 Coal-Old Unscrubbed

Figure 6.1 – The most notable change in power capacity in NE is a large addition of wind turbines at the expense of some natural gas capacity in the $10 per year scenario. The carbon tax also accelerates the retirement of the last few coal plants in the area by a decade or so.

Electrical Power Generation (NE level)

Baseline ($0/year) Alternative ($10/year) 180 180 Solar

160 160 Wind

Biopower 140 140 Geothermal 120 120 Hydro Nuclear 100 100 Oil-Gas-Steam Gas-CC-CCS

80 80 Gas-CT

Gas-CC

60 60 Coal-CCS Generation (TWh) Generation 40 40 Coal-IGCC Coal-New 20 20 Cofiring Coal-Old Scrubbed

0 0 Coal-Old Unscrubbed 2010 2020 2030 2040 2010 2020 2030 2040

Figure 6.2 – NE already has a “favorable” generation mix in terms of emissions with mostly gas, nuclear, hydroelectric, biomass, wind, and some solar. The carbon tax reduces the share dedicated to gas (or makes carbon sequestration with that gas economical).

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Figure 6.3 – GRP by Industry (millions of 2012 dollars) 70 sector NAICS 2020 2025 2030 2035 Forestry and logging; Fishing, hunting, and trapping -$21 -$71 -$110 -$134 Agriculture and forestry support activities -$1 -$3 -$4 -$4 Oil and gas extraction -$3 -$8 -$15 -$17 Mining (except oil and gas) $12 -$10 -$28 -$35 Support activities for mining $0 $0 $0 $0 Utilities -$208 -$387 -$416 -$387 Construction $437 $545 $572 $722 Wood manufacturing $9 $10 $8 $9 Nonmetallic mineral manufacturing $16 $18 $16 $19 Primary metal manufacturing -$6 -$29 -$41 -$37 Fabricated metal manufacturing $58 $53 $11 -$2 Machinery manufacturing $10 $43 $72 $67 Computer and electronic manufacturing -$22 -$204 -$356 -$440 Electrical equipment and appliance manufacturing -$11 -$77 -$137 -$181 Motor vehicles, bodies and trailers, and parts manufacturing $8 $11 $13 $15 Other transportation equipment manufacturing -$8 -$56 -$102 -$136 Furniture and related manufacturing $14 $14 $9 $4 Miscellaneous manufacturing $11 -$32 -$62 -$72 Food manufacturing $35 $38 $32 $29 Beverage and tobacco manufacturing $10 $9 $6 $5 Textile mills; Textile mills $0 -$11 -$24 -$27 Apparel manufacturing; Leather and allied manufacturing -$1 -$8 -$12 -$12 Paper manufacturing $14 $0 -$16 -$26 Printing and related support activities $17 $19 $17 $17 Petroleum and coals manufacturing -$15 -$63 -$94 -$111 Chemical manufacturing $78 -$47 -$183 -$268 Plastics and rubber manufacturing $15 -$7 -$32 -$50 Wholesale trade $310 $333 $319 $362 Retail trade $531 $774 $950 $1,178 Air transportation -$104 -$243 -$386 -$514 Rail transportation -$6 -$16 -$26 -$31 Water transportation -$2 -$6 -$10 -$14 Truck transportation $16 $12 $3 -$2 Couriers and messengers $11 $5 -$6 -$16 Transit and ground passenger transportation $12 $8 -$1 -$7 Pipeline transportation -$5 -$9 -$10 -$10 Scenic and sightseeing transportation; Support activities for transportation -$22 -$58 -$98 -$139 Warehousing and storage $8 $4 -$2 -$7 Publishing industries, except Internet $146 $205 $243 $305 Motion picture and sound recording industries $27 $43 $58 $76 Internet publishing and broadcasting; ISPs, search portals, and data processing $47 $48 $40 $41 Broadcasting, except Internet $23 $27 $26 $28 Telecommunications $173 $230 $246 $271 Monetary authorities - central bank; Credit intermediation and related activities $534 $726 $799 $873 Securities, commodity contracts, investments $427 $552 $550 $560 Insurance carriers and related activities $325 $419 $416 $403 Real estate $869 $1,010 $988 $1,108 Rental and leasing services; Leasing of nonfinancial intangible assets -$21 -$181 -$353 -$483 Professional, scientific, and technical services $398 $286 $68 -$32 Management of companies and enterprises $32 -$83 -$231 -$347 Administrative and support services $186 $218 $199 $199 Waste management and remediation services $23 $24 $21 $21 Educational services $151 $187 $193 $206 Ambulatory health care services $821 $1,239 $1,480 $1,682 Hospitals $307 $380 $378 $397 Nursing and residential care facilities $96 $115 $110 $112 Social assistance $67 $92 $102 $113 Performing arts and spectator sports $31 $37 $36 $39 Museums, historical sites, zoos, and parks $8 $9 $10 $10 Amusement, gambling, and recreation $52 $75 $86 $95 Accommodation $93 $116 $113 $116 Food services and drinking places $130 $117 $82 $74 Repair and maintenance $74 $81 $72 $71 Personal and laundry services $146 $217 $258 $289 Membership associations and organizations $43 $47 $41 $40 Private households $18 $28 $35 $40 State and local government $360 $285 $156 $112 TOTAL OF ALL SECTORS = $6,783 $7,100 $6,079 $6,167

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Figure 6.4 – Employment by Industry (thousands over baseline) 70 sector NAICS 2020 2025 2030 2035 Forestry and logging; Fishing, hunting, and trapping 0 0 -1 -1 Agriculture and forestry support activities 0 0 0 0 Oil and gas extraction 0 0 0 0 Mining (except oil and gas) 0 0 0 0 Support activities for mining 0 0 0 0 Utilities 0 -1 0 0 Construction 8 11 12 14 Wood manufacturing 0 0 0 0 Nonmetallic mineral manufacturing 0 0 0 0 Primary metal manufacturing 0 0 0 0 Fabricated metal manufacturing 0 0 0 0 Machinery manufacturing 0 0 0 0 Computer and electronic manufacturing 0 -1 -1 -1 Electrical equipment and appliance manufacturing 0 0 0 0 Motor vehicles, bodies and trailers, and parts manufacturing 0 0 0 0 Other transportation equipment manufacturing 0 0 0 0 Furniture and related manufacturing 0 0 0 0 Miscellaneous manufacturing 0 0 0 0 Food manufacturing 0 0 0 0 Beverage and tobacco manufacturing 0 0 0 0 Textile mills; Textile mills 0 0 0 0 Apparel manufacturing; Leather and allied manufacturing 0 0 0 0 Paper manufacturing 0 0 0 0 Printing and related support activities 0 0 0 0 Petroleum and coals manufacturing 0 0 0 0 Chemical manufacturing 0 0 0 0 Plastics and rubber manufacturing 0 0 0 0 Wholesale trade 2 2 2 2 Retail trade 9 12 14 15 Air transportation 0 -1 -1 -1 Rail transportation 0 0 0 0 Water transportation 0 0 0 0 Truck transportation 0 1 1 2 Couriers and messengers 0 0 1 1 Transit and ground passenger transportation 0 1 1 1 Pipeline transportation 0 0 0 0 Scenic and sightseeing transportation; Support activities for transportation 0 -1 -1 -1 Warehousing and storage 0 0 0 0 Publishing industries, except Internet 1 1 1 1 Motion picture and sound recording industries 0 0 0 0 Internet publishing and broadcasting; ISPs, search portals, and data processing 0 0 0 0 Broadcasting, except Internet 0 0 0 0 Telecommunications 0 1 1 1 Monetary authorities - central bank; Credit intermediation and related activities 2 2 2 2 Securities, commodity contracts, investments 3 4 4 4 Insurance carriers and related activities 2 2 2 2 Real estate 4 4 4 4 Rental and leasing services; Leasing of nonfinancial intangible assets 0 0 0 0 Professional, scientific, and technical services 4 4 3 2 Management of companies and enterprises 0 0 -1 -1 Administrative and support services 5 8 8 9 Waste management and remediation services 0 0 0 0 Educational services 4 6 6 7 Ambulatory health care services 10 16 19 22 Hospitals 4 5 6 6 Nursing and residential care facilities 2 3 3 4 Social assistance 2 3 4 4 Performing arts and spectator sports 1 1 1 1 Museums, historical sites, zoos, and parks 0 0 0 0 Amusement, gambling, and recreation 2 3 3 3 Accommodation 1 2 2 2 Food services and drinking places 4 5 5 5 Repair and maintenance 1 1 1 1 Personal and laundry services 3 5 5 6 Membership associations and organizations 1 2 1 2 Private households 2 3 4 4 State and local government 4 3 2 1 TOTAL OF ALL SECTORS = 81 107 113 123

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Figure 6.5 – Employment by Occupation (thousands over baseline) 95 occupation SOC 2020 2025 2030 2035 Top executives 1 1 1 1 Advertising, marketing, promotions, public relations, and sales managers 0 0 0 0 Operations specialties managers 1 1 1 1 Other management occupations 1 2 2 2 Business operations specialists 2 2 2 2 Financial specialists 2 3 2 2 Computer occupations 2 2 1 1 Mathematical science occupations 0 0 0 0 Architects, surveyors, and cartographers 0 0 0 0 Engineers 0 0 0 0 Drafters, engineering technicians, and mapping technicians 0 0 0 0 Life scientists 0 0 0 0 Physical scientists 0 0 0 0 Social scientists and related workers 0 0 0 0 Life, physical, and social science technicians 0 0 0 0 Counselors and Social workers 1 1 1 1 Miscellaneous community and social service specialists 0 1 1 1 Religious workers 0 0 0 0 Lawyers, judges, and related workers 0 0 0 0 Legal support workers 0 0 0 0 Postsecondary teachers 1 2 2 2 Preschool, primary, secondary, and special education school teachers 1 2 1 1 Other teachers and instructors 1 1 1 1 Librarians, curators, and archivists 0 0 0 0 Other education, training, and library occupations 1 1 1 1 Art and design workers 0 0 0 0 Entertainers and performers, sports and related workers 1 1 1 1 Media and communication workers 0 1 1 1 Media and communication equipment workers 0 0 0 0 Health diagnosing and treating practitioners 5 7 8 9 Health technologists and technicians 3 4 4 5 Other healthcare practitioners and technical occupations 0 0 0 0 Nursing, psychiatric, and home health aides 2 3 3 3 Occupational therapy and physical therapist assistants and aides 0 0 0 1 Other healthcare support occupations 2 3 4 4 Supervisors of protective service workers 0 0 0 0 Fire fighting and prevention workers 0 0 0 0 Law enforcement workers 0 0 0 0 Other protective service workers 1 1 1 1 Supervisors of food preparation and serving workers 0 0 0 1 Cooks and food preparation workers 1 2 2 2 Food and beverage serving workers 3 4 4 4 Other food preparation and serving related workers 1 1 1 1 Supervisors of building and grounds cleaning and maintenance workers 0 0 1 1 Building cleaning and pest control workers 3 4 4 4 Grounds maintenance workers 2 4 4 5 Supervisors of personal care and service workers 0 0 0 0 Animal care and service workers 0 0 0 0 Entertainment attendants and related workers 0 1 1 1 Funeral service workers 0 0 0 0 Personal appearance workers 2 3 3 3 Baggage porters, bellhops, and concierges; Tour and travel guides 0 0 0 0 Other personal care and service workers 3 4 4 5 Supervisors of sales workers 1 1 1 1 Retail sales workers 5 7 8 9 Sales representatives, services 2 2 2 2 Sales representatives, wholesale and manufacturing 1 1 1 1 Other sales and related workers 1 1 1 1 Supervisors of office and administrative support workers 1 1 1 1 Communications equipment operators 0 0 0 0 Financial clerks 2 3 3 3 Information and record clerks 4 5 5 5 Material recording, scheduling, dispatching, and distributing workers 1 2 2 2 Secretaries and administrative assistants 3 4 4 5 Other office and administrative support workers 3 3 3 4 Supervisors of farming, fishing, and forestry workers 0 0 0 0 Agricultural workers 0 0 0 0 Fishing and hunting workers 0 0 0 0 Forest, conservation, and logging workers 0 0 0 0

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Supervisors of construction and extraction workers 1 1 1 1 Construction trades workers 4 6 7 8 Helpers, construction trades 0 1 1 1 Other construction and related workers 0 0 0 0 Extraction workers 0 0 0 0 Supervisors of installation, maintenance, and repair workers 0 0 0 0 Electrical and electronic equipment mechanics, installers, and repairers 0 0 0 0 Vehicle and mobile equipment mechanics, installers, and repairers 1 1 1 1 Other installation, maintenance, and repair occupations 2 2 2 3 Supervisors of production workers 0 0 0 0 Assemblers and fabricators 0 0 0 0 Food processing workers 0 0 0 0 Metal workers and plastic workers 0 0 0 0 Printing workers 0 0 0 0 Textile, apparel, and furnishings workers 0 0 0 0 Woodworkers 0 0 0 0 Plant and system operators 0 0 0 0 Other production occupations 1 1 1 0 Supervisors of transportation and material moving workers 0 0 0 0 Air transportation workers 0 0 0 -1 Motor vehicle operators 2 2 3 3 Rail transportation workers 0 0 0 0 Water transportation workers 0 0 0 0 Other transportation workers 0 0 0 0 Material moving workers 2 2 2 2 Military 0 0 0 0 TOTAL OF ALL OCCUPATIONS = 80 108 111 120

Amherst, Massachusetts

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Mid-Atlantic (MA)

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Electrical Power Capacity (MA level)

Baseline ($0/year) Alternative ($10/year) 140 140 Storage

Solar

120 120 Wind

Biopower

Geothermal

100 100 Hydro 80 80 Nuclear Oil-Gas-Steam

Gas-CC-CCS

60 60 Gas-CT

Gas-CC Capacity (GW) Capacity 40 40 Coal-CCS

Coal-IGCC 20 20 Coal-New Cofiring 0 0 Coal-Old Scrubbed 2010 2020 2030 2040 2010 2020 2030 2040 Coal-Old Unscrubbed

Figure 6.6 – The capacity patterns in MA mimic many of the national level trends with steady coal and expanding gas in the baseline. The carbon tax helps to retire the coal and introduce a decent amount of new wind to take its place with more overall capacity in the system.

Electrical Power Generation (MA level)

Baseline ($0/year) Alternative ($10/year) 500 500 Solar

450 450 Wind 400 400 Biopower

Geothermal

350 350 Hydro 300 300 Nuclear Oil-Gas-Steam

250 250 Gas-CC-CCS

Gas-CT 200 200 Gas-CC

150 150 Coal-CCS Generation (TWh) Generation Coal-IGCC

100 100 Coal-New 50 50 Cofiring Coal-Old Scrubbed

0 0 Coal-Old Unscrubbed 2010 2020 2030 2040 2010 2020 2030 2040

Figure 6.7 – The carbon price of $10 per year reduces the baseline’s 100 TWh per year of power generation from coal to close to zero, although MA is one of the few regions where coal with carbon capture and sequestration proves economical to some degree.

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Figure 6.8 – GRP by Industry (millions of 2012 dollars) 70 sector NAICS 2020 2025 2030 2035 Forestry and logging; Fishing, hunting, and trapping -$3 -$9 -$14 -$17 Agriculture and forestry support activities $0 -$1 -$2 -$2 Oil and gas extraction -$86 -$224 -$341 -$409 Mining (except oil and gas) -$305 -$965 -$1,554 -$1,653 Support activities for mining -$14 -$14 $4 $23 Utilities -$1,078 -$1,484 -$1,306 -$1,228 Construction $662 $911 $1,166 $1,487 Wood manufacturing $16 $20 $20 $21 Nonmetallic mineral manufacturing $42 $44 $39 $41 Primary metal manufacturing -$68 -$253 -$389 -$437 Fabricated metal manufacturing $144 $103 $36 $120 Machinery manufacturing $3 $34 $63 $39 Computer and electronic manufacturing -$66 -$292 -$461 -$558 Electrical equipment and appliance manufacturing -$30 -$130 -$220 -$285 Motor vehicles, bodies and trailers, and parts manufacturing $35 $52 $62 $71 Other transportation equipment manufacturing $0 -$26 -$53 -$71 Furniture and related manufacturing $35 $32 $19 $4 Miscellaneous manufacturing $16 -$58 -$108 -$124 Food manufacturing $111 $113 $92 $78 Beverage and tobacco manufacturing $30 $29 $22 $17 Textile mills; Textile mills -$1 -$18 -$35 -$40 Apparel manufacturing; Leather and allied manufacturing -$9 -$42 -$60 -$65 Paper manufacturing $21 -$5 -$32 -$48 Printing and related support activities $39 $43 $40 $39 Petroleum and coals manufacturing -$355 -$932 -$1,364 -$1,714 Chemical manufacturing $196 -$283 -$793 -$1,167 Plastics and rubber manufacturing $15 -$45 -$109 -$157 Wholesale trade $761 $835 $858 $993 Retail trade $1,261 $1,947 $2,542 $3,189 Air transportation -$539 -$1,304 -$2,105 -$2,834 Rail transportation -$22 -$53 -$84 -$99 Water transportation -$4 -$13 -$22 -$30 Truck transportation $58 $50 $32 $34 Couriers and messengers $35 $25 $1 -$17 Transit and ground passenger transportation $50 $59 $59 $67 Pipeline transportation -$26 -$42 -$48 -$48 Scenic and sightseeing transportation; Support activities for transportation -$97 -$249 -$417 -$587 Warehousing and storage $28 $20 $3 -$5 Publishing industries, except Internet $264 $346 $386 $440 Motion picture and sound recording industries $245 $396 $535 $693 Internet publishing and broadcasting; ISPs, search portals, and data processing $113 $115 $107 $116 Broadcasting, except Internet $86 $99 $96 $104 Telecommunications $454 $602 $676 $772 Monetary authorities - central bank; Credit intermediation and related activities $1,813 $2,572 $2,960 $3,302 Securities, commodity contracts, investments $1,419 $1,863 $1,932 $2,015 Insurance carriers and related activities $644 $835 $846 $829 Real estate $1,988 $2,344 $2,605 $3,019 Rental and leasing services; Leasing of nonfinancial intangible assets -$168 -$725 -$1,292 -$1,743 Professional, scientific, and technical services $837 $522 $96 -$91 Management of companies and enterprises $28 -$366 -$817 -$1,177 Administrative and support services $372 $380 $325 $313 Waste management and remediation services $40 $37 $31 $31 Educational services $270 $345 $390 $437 Ambulatory health care services $1,975 $3,039 $3,695 $4,212 Hospitals $549 $682 $738 $828 Nursing and residential care facilities $192 $238 $254 $279 Social assistance $193 $270 $314 $358 Performing arts and spectator sports $112 $144 $161 $184 Museums, historical sites, zoos, and parks $17 $21 $24 $27 Amusement, gambling, and recreation $110 $164 $197 $225 Accommodation $147 $149 $139 $147 Food services and drinking places $228 $201 $162 $163 Repair and maintenance $146 $162 $159 $167 Personal and laundry services $364 $558 $682 $766 Membership associations and organizations $120 $138 $139 $149 Private households $37 $61 $81 $92 State and local government $856 $635 $386 $315 TOTAL OF ALL SECTORS = $14,306 $13,702 $11,548 $11,600

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Figure 6.9 – Employment by Industry (thousands over baseline) 70 sector NAICS 2020 2025 2030 2035 Forestry and logging; Fishing, hunting, and trapping 0 0 0 0 Agriculture and forestry support activities 0 0 0 0 Oil and gas extraction -1 -2 -3 -3 Mining (except oil and gas) -1 -4 -6 -5 Support activities for mining 0 0 0 0 Utilities -2 -2 -1 -1 Construction 12 18 23 28 Wood manufacturing 0 0 0 1 Nonmetallic mineral manufacturing 0 1 1 1 Primary metal manufacturing 0 0 -1 0 Fabricated metal manufacturing 1 1 1 2 Machinery manufacturing 0 0 0 0 Computer and electronic manufacturing 0 -1 -1 -1 Electrical equipment and appliance manufacturing 0 -1 -1 -1 Motor vehicles, bodies and trailers, and parts manufacturing 0 0 0 0 Other transportation equipment manufacturing 0 0 0 0 Furniture and related manufacturing 0 0 0 0 Miscellaneous manufacturing 0 0 0 0 Food manufacturing 1 1 1 1 Beverage and tobacco manufacturing 0 0 0 0 Textile mills; Textile mills 0 0 0 0 Apparel manufacturing; Leather and allied manufacturing 0 -1 -1 -1 Paper manufacturing 0 0 0 0 Printing and related support activities 0 1 1 0 Petroleum and coals manufacturing 0 0 0 0 Chemical manufacturing 1 0 0 0 Plastics and rubber manufacturing 0 0 0 0 Wholesale trade 5 6 7 7 Retail trade 22 32 38 42 Air transportation -2 -4 -6 -7 Rail transportation 0 0 0 0 Water transportation 0 0 0 0 Truck transportation 1 3 4 6 Couriers and messengers 1 1 2 2 Transit and ground passenger transportation 2 3 4 5 Pipeline transportation 0 0 0 0 Scenic and sightseeing transportation; Support activities for transportation -1 -2 -3 -4 Warehousing and storage 1 1 1 1 Publishing industries, except Internet 1 1 1 1 Motion picture and sound recording industries 1 2 2 2 Internet publishing and broadcasting; ISPs, search portals, and data processing 0 0 0 0 Broadcasting, except Internet 0 1 1 1 Telecommunications 1 1 2 2 Monetary authorities - central bank; Credit intermediation and related activities 5 7 7 7 Securities, commodity contracts, investments 9 12 12 11 Insurance carriers and related activities 4 6 5 5 Real estate 8 10 11 12 Rental and leasing services; Leasing of nonfinancial intangible assets 1 1 1 0 Professional, scientific, and technical services 8 8 6 5 Management of companies and enterprises 0 -1 -2 -3 Administrative and support services 12 18 22 25 Waste management and remediation services 0 1 1 1 Educational services 8 13 16 19 Ambulatory health care services 26 41 51 58 Hospitals 8 11 13 15 Nursing and residential care facilities 5 7 9 10 Social assistance 7 11 13 15 Performing arts and spectator sports 3 3 4 4 Museums, historical sites, zoos, and parks 0 1 1 1 Amusement, gambling, and recreation 4 6 7 8 Accommodation 2 3 3 3 Food services and drinking places 9 12 13 15 Repair and maintenance 2 2 3 3 Personal and laundry services 8 13 15 16 Membership associations and organizations 4 5 5 6 Private households 4 7 8 9 State and local government 9 7 4 3 TOTAL OF ALL SECTORS = 189 260 294 327

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Figure 6.10 – Employment by Occupation (thousands over baseline) 95 occupation SOC 2020 2025 2030 2035 Top executives 3 3 4 4 Advertising, marketing, promotions, public relations, and sales managers 1 1 1 1 Operations specialties managers 2 2 2 2 Other management occupations 3 4 5 5 Business operations specialists 5 6 6 6 Financial specialists 6 7 7 7 Computer occupations 3 3 3 3 Mathematical science occupations 0 0 0 0 Architects, surveyors, and cartographers 0 0 0 0 Engineers 0 0 0 -1 Drafters, engineering technicians, and mapping technicians 0 0 0 0 Life scientists 0 0 0 0 Physical scientists 0 0 0 0 Social scientists and related workers 0 0 0 0 Life, physical, and social science technicians 0 0 0 0 Counselors and Social workers 2 3 3 4 Miscellaneous community and social service specialists 1 2 2 2 Religious workers 0 0 0 0 Lawyers, judges, and related workers 1 1 1 1 Legal support workers 0 1 0 0 Postsecondary teachers 3 4 5 5 Preschool, primary, secondary, and special education school teachers 3 4 4 4 Other teachers and instructors 1 2 2 2 Librarians, curators, and archivists 0 0 0 0 Other education, training, and library occupations 2 2 2 2 Art and design workers 1 1 1 1 Entertainers and performers, sports and related workers 1 2 2 2 Media and communication workers 1 2 2 2 Media and communication equipment workers 0 1 1 1 Health diagnosing and treating practitioners 11 16 20 22 Health technologists and technicians 6 9 11 13 Other healthcare practitioners and technical occupations 0 0 0 0 Nursing, psychiatric, and home health aides 5 7 8 10 Occupational therapy and physical therapist assistants and aides 1 1 1 1 Other healthcare support occupations 5 8 10 11 Supervisors of protective service workers 0 0 0 0 Fire fighting and prevention workers 0 0 0 0 Law enforcement workers 1 0 0 0 Other protective service workers 2 2 3 3 Supervisors of food preparation and serving workers 1 1 1 2 Cooks and food preparation workers 3 4 5 5 Food and beverage serving workers 7 9 10 11 Other food preparation and serving related workers 1 2 2 2 Supervisors of building and grounds cleaning and maintenance workers 1 1 1 2 Building cleaning and pest control workers 6 8 10 11 Grounds maintenance workers 5 9 11 13 Supervisors of personal care and service workers 0 1 1 1 Animal care and service workers 1 1 1 1 Entertainment attendants and related workers 1 2 2 2 Funeral service workers 0 0 0 0 Personal appearance workers 5 7 9 10 Baggage porters, bellhops, and concierges; Tour and travel guides 0 0 0 0 Other personal care and service workers 7 10 12 14 Supervisors of sales workers 2 3 4 4 Retail sales workers 13 19 22 24 Sales representatives, services 4 5 5 5 Sales representatives, wholesale and manufacturing 2 2 2 2 Other sales and related workers 2 3 3 3 Supervisors of office and administrative support workers 2 3 4 4 Communications equipment operators 0 0 0 0 Financial clerks 6 8 8 9 Information and record clerks 9 12 13 14 Material recording, scheduling, dispatching, and distributing workers 3 4 4 5 Secretaries and administrative assistants 8 11 12 13 Other office and administrative support workers 7 8 9 10 Supervisors of farming, fishing, and forestry workers 0 0 0 0 Agricultural workers 0 0 0 0 Fishing and hunting workers 0 0 0 0 Forest, conservation, and logging workers 0 0 0 0

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Supervisors of construction and extraction workers 1 1 1 1 Construction trades workers 6 10 12 14 Helpers, construction trades 1 1 1 1 Other construction and related workers 0 0 0 0 Extraction workers -1 -1 -2 -2 Supervisors of installation, maintenance, and repair workers 0 1 1 1 Electrical and electronic equipment mechanics, installers, and repairers 1 1 1 1 Vehicle and mobile equipment mechanics, installers, and repairers 2 2 2 2 Other installation, maintenance, and repair occupations 3 4 5 6 Supervisors of production workers 0 0 0 0 Assemblers and fabricators 1 1 0 1 Food processing workers 1 1 1 1 Metal workers and plastic workers 1 0 0 0 Printing workers 0 0 0 0 Textile, apparel, and furnishings workers 1 0 0 0 Woodworkers 0 0 0 0 Plant and system operators 0 0 0 0 Other production occupations 2 2 1 1 Supervisors of transportation and material moving workers 0 0 1 1 Air transportation workers -1 -2 -2 -3 Motor vehicle operators 5 7 9 11 Rail transportation workers 0 0 0 0 Water transportation workers 0 0 0 0 Other transportation workers 1 1 1 1 Material moving workers 4 4 4 5 Military 0 0 0 0 TOTAL OF ALL OCCUPATIONS = 194 260 293 322

Poughkeepsie, New York

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East North Central (ENC)

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Electrical Power Capacity (ENC level)

Baseline ($0/year) Alternative ($10/year) 250 250 Storage

Solar

Wind

200 200 Biopower

Geothermal

Hydro

150 150 Nuclear

Oil-Gas-Steam

Gas-CC-CCS 100 100 Gas-CT

Gas-CC Capacity (GW) Capacity Coal-CCS 50 50 Coal-IGCC Coal-New

Cofiring 0 0 Coal-Old Scrubbed 2010 2020 2030 2040 2010 2020 2030 2040 Coal-Old Unscrubbed

Figure 6.11 – The heavy concentration of coal plants in the area east of the Mississippi River, north of the Ohio River, and west of Pittsburgh give ENC more capacity in coal-based generation than NE has overall (and nearly more than MA overall). The carbon tax, however, incentivizes its retirement and replacement with large-scale wind farms in this region.

Electrical Power Generation (ENC level)

Baseline ($0/year) Alternative ($10/year) 800 800 Solar 700 700 Wind Biopower

600 600 Geothermal Hydro 500 500 Nuclear Oil-Gas-Steam 400 400 Gas-CC-CCS

Gas-CT

300 300 Gas-CC

Coal-CCS Generation (TWh) Generation 200 200 Coal-IGCC

Coal-New

100 100 Cofiring

Coal-Old Scrubbed

0 0 Coal-Old Unscrubbed 2010 2020 2030 2040 2010 2020 2030 2040

Figure 6.12 – The ENC remains a leading region for power generation in both cases—just through coal in the baseline and wind (with some gas and nuclear) and the alternative.

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Figure 6.13 – GRP by Industry (millions of 2012 dollars) 70 sector NAICS 2020 2025 2030 2035 Forestry and logging; Fishing, hunting, and trapping -$7 -$15 -$22 -$28 Agriculture and forestry support activities $0 -$1 -$1 -$1 Oil and gas extraction -$141 -$300 -$418 -$474 Mining (except oil and gas) -$248 -$922 -$1,440 -$1,536 Support activities for mining -$17 -$14 -$2 $6 Utilities -$2,040 -$1,981 -$1,921 -$1,922 Construction $385 $1,837 $2,618 $3,216 Wood manufacturing $21 $45 $52 $56 Nonmetallic mineral manufacturing $32 $61 $65 $72 Primary metal manufacturing -$240 -$630 -$926 -$1,090 Fabricated metal manufacturing $225 $146 $20 $114 Machinery manufacturing -$32 $272 $287 $135 Computer and electronic manufacturing -$69 -$220 -$289 -$284 Electrical equipment and appliance manufacturing -$113 -$315 -$495 -$629 Motor vehicles, bodies and trailers, and parts manufacturing $690 $1,285 $1,738 $2,195 Other transportation equipment manufacturing $0 -$23 -$44 -$57 Furniture and related manufacturing $69 $73 $46 $13 Miscellaneous manufacturing -$13 -$129 -$206 -$228 Food manufacturing $187 $241 $240 $228 Beverage and tobacco manufacturing $43 $68 $77 $77 Textile mills; Textile mills -$2 -$15 -$29 -$32 Apparel manufacturing; Leather and allied manufacturing -$2 -$9 -$9 -$6 Paper manufacturing $17 -$12 -$51 -$82 Printing and related support activities $56 $82 $89 $95 Petroleum and coals manufacturing -$1,112 -$2,102 -$2,694 -$3,349 Chemical manufacturing -$200 -$805 -$1,351 -$1,800 Plastics and rubber manufacturing -$24 -$166 -$326 -$457 Wholesale trade $694 $1,259 $1,615 $2,064 Retail trade $1,422 $3,127 $4,470 $5,896 Air transportation -$434 -$1,091 -$1,845 -$2,570 Rail transportation -$48 -$105 -$163 -$193 Water transportation -$3 -$7 -$12 -$16 Truck transportation $95 $134 $131 $160 Couriers and messengers $31 $41 $37 $37 Transit and ground passenger transportation $28 $53 $71 $86 Pipeline transportation -$41 -$66 -$75 -$74 Scenic and sightseeing transportation; Support activities for transportation -$95 -$232 -$390 -$560 Warehousing and storage $31 $41 $39 $43 Publishing industries, except Internet $143 $235 $302 $386 Motion picture and sound recording industries $53 $90 $123 $162 Internet publishing and broadcasting; ISPs, search portals, and data processing $56 $108 $144 $174 Broadcasting, except Internet $29 $50 $61 $72 Telecommunications $387 $716 $964 $1,190 Monetary authorities - central bank; Credit intermediation and related activities $1,117 $1,819 $2,214 $2,580 Securities, commodity contracts, investments $336 $469 $504 $540 Insurance carriers and related activities $621 $910 $981 $997 Real estate $1,661 $3,767 $4,907 $5,589 Rental and leasing services; Leasing of nonfinancial intangible assets -$38 -$181 -$344 -$479 Professional, scientific, and technical services $337 $557 $604 $701 Management of companies and enterprises -$51 -$313 -$585 -$795 Administrative and support services $344 $617 $777 $953 Waste management and remediation services $37 $69 $86 $99 Educational services $245 $490 $645 $742 Ambulatory health care services $1,976 $3,302 $4,199 $5,176 Hospitals $743 $1,445 $2,003 $2,473 Nursing and residential care facilities $252 $508 $701 $858 Social assistance $166 $304 $400 $475 Performing arts and spectator sports $105 $198 $260 $317 Museums, historical sites, zoos, and parks $18 $38 $53 $64 Amusement, gambling, and recreation $121 $219 $284 $341 Accommodation $98 $208 $294 $358 Food services and drinking places $397 $937 $1,311 $1,572 Repair and maintenance $187 $371 $490 $582 Personal and laundry services $309 $530 $654 $772 Membership associations and organizations $168 $326 $431 $501 Private households $22 $47 $60 $76 State and local government $758 $1,560 $1,948 $2,203 TOTAL OF ALL SECTORS = $9,742 $19,001 $23,357 $27,784

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Figure 6.14 – Employment by Industry (thousands over baseline) 70 sector NAICS 2020 2025 2030 2035 Forestry and logging; Fishing, hunting, and trapping 0 0 0 0 Agriculture and forestry support activities 0 0 0 0 Oil and gas extraction -2 -4 -6 -7 Mining (except oil and gas) -1 -3 -4 -4 Support activities for mining 0 0 0 0 Utilities -3 -2 -1 -1 Construction 11 38 50 57 Wood manufacturing 0 1 1 1 Nonmetallic mineral manufacturing 0 1 1 2 Primary metal manufacturing 0 0 0 0 Fabricated metal manufacturing 2 2 2 3 Machinery manufacturing 0 1 1 1 Computer and electronic manufacturing 0 -1 -1 -1 Electrical equipment and appliance manufacturing 0 -1 -2 -2 Motor vehicles, bodies and trailers, and parts manufacturing 3 5 5 5 Other transportation equipment manufacturing 0 0 0 0 Furniture and related manufacturing 1 1 1 0 Miscellaneous manufacturing 0 0 0 0 Food manufacturing 2 3 3 3 Beverage and tobacco manufacturing 0 0 0 0 Textile mills; Textile mills 0 0 0 0 Apparel manufacturing; Leather and allied manufacturing 0 0 0 0 Paper manufacturing 0 1 1 1 Printing and related support activities 1 1 1 1 Petroleum and coals manufacturing 0 0 0 0 Chemical manufacturing 0 0 0 0 Plastics and rubber manufacturing 0 0 0 0 Wholesale trade 5 10 12 15 Retail trade 26 52 66 77 Air transportation -1 -3 -5 -6 Rail transportation 0 0 0 0 Water transportation 0 0 0 0 Truck transportation 2 5 8 12 Couriers and messengers 1 1 2 2 Transit and ground passenger transportation 1 2 3 3 Pipeline transportation 0 0 0 0 Scenic and sightseeing transportation; Support activities for transportation -1 -2 -3 -4 Warehousing and storage 1 1 1 2 Publishing industries, except Internet 1 1 1 1 Motion picture and sound recording industries 0 1 1 1 Internet publishing and broadcasting; ISPs, search portals, and data processing 0 0 1 0 Broadcasting, except Internet 0 0 0 1 Telecommunications 1 2 2 3 Monetary authorities - central bank; Credit intermediation and related activities 4 6 7 7 Securities, commodity contracts, investments 5 7 7 7 Insurance carriers and related activities 4 6 7 7 Real estate 8 18 23 25 Rental and leasing services; Leasing of nonfinancial intangible assets 1 2 2 2 Professional, scientific, and technical services 5 9 12 14 Management of companies and enterprises 0 -1 -1 -2 Administrative and support services 15 30 38 46 Waste management and remediation services 0 1 1 1 Educational services 8 17 22 26 Ambulatory health care services 26 45 58 72 Hospitals 12 23 31 38 Nursing and residential care facilities 7 14 20 25 Social assistance 7 13 18 21 Performing arts and spectator sports 2 4 5 6 Museums, historical sites, zoos, and parks 0 1 1 1 Amusement, gambling, and recreation 4 8 11 13 Accommodation 2 4 5 6 Food services and drinking places 17 36 48 54 Repair and maintenance 3 6 8 9 Personal and laundry services 8 13 15 17 Membership associations and organizations 6 12 16 19 Private households 3 5 6 7 State and local government 10 20 23 25 TOTAL OF ALL SECTORS = 207 412 524 612

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Figure 6.15 – Employment by Occupation (thousands over baseline) 95 occupation SOC 2020 2025 2030 2035 Top executives 3 5 7 8 Advertising, marketing, promotions, public relations, and sales managers 1 1 2 2 Operations specialties managers 2 3 3 4 Other management occupations 3 7 9 10 Business operations specialists 4 8 10 12 Financial specialists 4 7 8 9 Computer occupations 2 4 5 6 Mathematical science occupations 0 0 0 0 Architects, surveyors, and cartographers 0 0 0 0 Engineers 0 0 0 1 Drafters, engineering technicians, and mapping technicians 0 0 1 1 Life scientists 0 0 0 1 Physical scientists 0 0 0 0 Social scientists and related workers 0 1 1 1 Life, physical, and social science technicians 0 0 0 0 Counselors and Social workers 2 4 6 7 Miscellaneous community and social service specialists 1 3 4 4 Religious workers 0 0 0 0 Lawyers, judges, and related workers 1 1 1 1 Legal support workers 0 1 1 1 Postsecondary teachers 3 5 7 8 Preschool, primary, secondary, and special education school teachers 4 7 9 10 Other teachers and instructors 1 2 3 4 Librarians, curators, and archivists 0 1 1 1 Other education, training, and library occupations 2 3 4 5 Art and design workers 1 1 1 2 Entertainers and performers, sports and related workers 1 2 3 3 Media and communication workers 1 2 3 3 Media and communication equipment workers 0 1 1 1 Health diagnosing and treating practitioners 13 23 30 37 Health technologists and technicians 7 13 18 22 Other healthcare practitioners and technical occupations 0 0 1 1 Nursing, psychiatric, and home health aides 6 12 16 20 Occupational therapy and physical therapist assistants and aides 1 1 1 2 Other healthcare support occupations 5 9 11 14 Supervisors of protective service workers 0 0 0 0 Fire fighting and prevention workers 0 0 0 0 Law enforcement workers 1 1 1 2 Other protective service workers 2 4 4 5 Supervisors of food preparation and serving workers 1 3 4 5 Cooks and food preparation workers 5 10 13 15 Food and beverage serving workers 11 24 31 35 Other food preparation and serving related workers 2 5 6 7 Supervisors of building and grounds cleaning and maintenance workers 1 2 2 3 Building cleaning and pest control workers 5 11 14 16 Grounds maintenance workers 6 13 18 21 Supervisors of personal care and service workers 0 1 1 1 Animal care and service workers 1 1 1 2 Entertainment attendants and related workers 1 2 3 3 Funeral service workers 0 0 0 0 Personal appearance workers 4 8 9 11 Baggage porters, bellhops, and concierges; Tour and travel guides 0 0 0 0 Other personal care and service workers 6 12 16 20 Supervisors of sales workers 3 5 6 7 Retail sales workers 15 30 39 45 Sales representatives, services 3 5 5 6 Sales representatives, wholesale and manufacturing 2 3 4 5 Other sales and related workers 2 4 6 6 Supervisors of office and administrative support workers 2 4 5 6 Communications equipment operators 0 0 0 0 Financial clerks 6 11 13 15 Information and record clerks 9 16 19 22 Material recording, scheduling, dispatching, and distributing workers 4 7 9 10 Secretaries and administrative assistants 8 14 18 21 Other office and administrative support workers 7 12 15 17 Supervisors of farming, fishing, and forestry workers 0 0 0 0 Agricultural workers 0 0 0 0 Fishing and hunting workers 0 0 0 0 Forest, conservation, and logging workers 0 0 0 0

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Supervisors of construction and extraction workers 1 2 3 3 Construction trades workers 6 21 27 31 Helpers, construction trades 1 2 2 3 Other construction and related workers 0 1 1 1 Extraction workers -1 -2 -2 -2 Supervisors of installation, maintenance, and repair workers 1 1 2 2 Electrical and electronic equipment mechanics, installers, and repairers 0 1 1 2 Vehicle and mobile equipment mechanics, installers, and repairers 2 4 6 7 Other installation, maintenance, and repair occupations 4 9 11 13 Supervisors of production workers 0 1 1 1 Assemblers and fabricators 2 3 3 4 Food processing workers 1 2 2 2 Metal workers and plastic workers 2 2 2 2 Printing workers 0 1 1 1 Textile, apparel, and furnishings workers 1 1 1 1 Woodworkers 0 1 1 1 Plant and system operators 0 0 0 0 Other production occupations 2 4 4 5 Supervisors of transportation and material moving workers 0 1 1 1 Air transportation workers -1 -1 -2 -2 Motor vehicle operators 5 10 14 18 Rail transportation workers 0 0 0 0 Water transportation workers 0 0 0 0 Other transportation workers 1 1 1 1 Material moving workers 5 8 10 13 Military 0 0 0 0 TOTAL OF ALL OCCUPATIONS = 207 408 519 615

Lafayette, Indiana

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West North Central (WNC)

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Electrical Power Capacity (WNC level)

Baseline ($0/year) Alternative ($10/year) 140 140 Storage

Solar

120 120 Wind

Biopower

Geothermal

100 100 Hydro 80 80 Nuclear Oil-Gas-Steam

Gas-CC-CCS

60 60 Gas-CT

Gas-CC Capacity (GW) Capacity 40 40 Coal-CCS

Coal-IGCC 20 20 Coal-New Cofiring 0 0 Coal-Old Scrubbed 2010 2020 2030 2040 2010 2020 2030 2040 Coal-Old Unscrubbed

Figure 6.16 – The WNC region already has a significant portion of its power capacity in wind, although the $10 per year case triples current capacity to around 60 GW with significant storage to replace the retirement of most of the coal fleet by 2030 throughout the 2020s.

Electrical Power Generation (WNC level)

Baseline ($0/year) Alternative ($10/year) 500 500 Solar

450 450 Wind 400 400 Biopower

Geothermal

350 350 Hydro 300 300 Nuclear Oil-Gas-Steam 250 250 Gas-CC-CCS Gas-CT 200 200 Gas-CC

150 150 Coal-CCS Generation (TWh) Generation Coal-IGCC

100 100 Coal-New 50 50 Cofiring Coal-Old Scrubbed

0 0 Coal-Old Unscrubbed 2010 2020 2030 2040 2010 2020 2030 2040

Figure 6.17 – Emissions from power generation in WNC decline to nearly zero in the alternative case with wind in its open farmlands, biomass, hydroelectricity, and small amounts of nuclear and sequestered gas serving as the base-load.

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Figure 6.18 – GRP by Industry (millions of 2012 dollars) 70 sector NAICS 2020 2025 2030 2035 Forestry and logging; Fishing, hunting, and trapping -$7 -$13 -$18 -$23 Agriculture and forestry support activities -$1 -$2 -$3 -$3 Oil and gas extraction -$132 -$263 -$360 -$395 Mining (except oil and gas) -$5 -$208 -$331 -$372 Support activities for mining -$75 -$52 -$24 -$10 Utilities -$1,165 -$1,105 -$1,131 -$1,232 Construction -$41 $938 $1,281 $1,510 Wood manufacturing $8 $22 $21 $20 Nonmetallic mineral manufacturing -$2 $13 $7 $5 Primary metal manufacturing -$42 -$100 -$149 -$174 Fabricated metal manufacturing $53 $20 -$33 -$16 Machinery manufacturing -$18 $34 -$18 -$83 Computer and electronic manufacturing -$67 -$192 -$282 -$312 Electrical equipment and appliance manufacturing -$39 -$101 -$160 -$203 Motor vehicles, bodies and trailers, and parts manufacturing $78 $148 $198 $253 Other transportation equipment manufacturing -$31 -$84 -$131 -$167 Furniture and related manufacturing $21 $21 $7 -$8 Miscellaneous manufacturing $3 -$35 -$66 -$77 Food manufacturing $107 $133 $112 $86 Beverage and tobacco manufacturing $17 $29 $32 $31 Textile mills; Textile mills -$1 -$7 -$14 -$16 Apparel manufacturing; Leather and allied manufacturing -$2 -$7 -$8 -$7 Paper manufacturing $3 -$4 -$16 -$26 Printing and related support activities $24 $37 $37 $37 Petroleum and coals manufacturing -$723 -$1,404 -$2,053 -$2,723 Chemical manufacturing -$152 -$392 -$667 -$912 Plastics and rubber manufacturing -$23 -$77 -$148 -$208 Wholesale trade $219 $534 $679 $851 Retail trade $503 $1,346 $1,956 $2,600 Air transportation -$135 -$375 -$648 -$907 Rail transportation -$60 -$127 -$201 -$245 Water transportation -$1 -$2 -$4 -$5 Truck transportation $27 $20 -$20 -$42 Couriers and messengers $8 $5 -$6 -$17 Transit and ground passenger transportation $7 $12 $13 $13 Pipeline transportation -$27 -$44 -$52 -$52 Scenic and sightseeing transportation; Support activities for transportation -$40 -$97 -$164 -$238 Warehousing and storage $6 $7 $2 -$1 Publishing industries, except Internet $68 $119 $141 $165 Motion picture and sound recording industries $16 $27 $37 $48 Internet publishing and broadcasting; ISPs, search portals, and data processing $36 $85 $111 $129 Broadcasting, except Internet $14 $29 $35 $40 Telecommunications $202 $419 $568 $696 Monetary authorities - central bank; Credit intermediation and related activities $578 $996 $1,201 $1,389 Securities, commodity contracts, investments $127 $193 $209 $222 Insurance carriers and related activities $352 $531 $567 $571 Real estate $547 $1,914 $2,454 $2,624 Rental and leasing services; Leasing of nonfinancial intangible assets -$151 -$362 -$597 -$789 Professional, scientific, and technical services $28 $208 $229 $239 Management of companies and enterprises -$56 -$173 -$311 -$419 Administrative and support services $95 $256 $325 $381 Waste management and remediation services $10 $30 $38 $42 Educational services $99 $225 $299 $342 Ambulatory health care services $786 $1,331 $1,705 $2,139 Hospitals $291 $676 $973 $1,207 Nursing and residential care facilities $127 $294 $416 $510 Social assistance $89 $169 $222 $262 Performing arts and spectator sports $45 $97 $128 $154 Museums, historical sites, zoos, and parks $6 $16 $23 $28 Amusement, gambling, and recreation $56 $109 $142 $169 Accommodation $44 $145 $209 $249 Food services and drinking places $163 $492 $710 $848 Repair and maintenance $77 $197 $267 $315 Personal and laundry services $123 $220 $270 $319 Membership associations and organizations $71 $160 $217 $252 Private households $10 $20 $26 $33 State and local government $225 $729 $923 $1,017 TOTAL OF ALL SECTORS = $2,373 $7,780 $9,175 $10,114

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Figure 6.19 – Employment by Industry (thousands over baseline) 70 sector NAICS 2020 2025 2030 2035 Forestry and logging; Fishing, hunting, and trapping 0 0 0 0 Agriculture and forestry support activities 0 0 0 0 Oil and gas extraction -2 -3 -5 -6 Mining (except oil and gas) 0 -1 -2 -2 Support activities for mining 0 0 0 0 Utilities -2 -1 -1 -1 Construction 3 21 26 30 Wood manufacturing 0 1 1 1 Nonmetallic mineral manufacturing 0 1 1 1 Primary metal manufacturing 0 0 0 0 Fabricated metal manufacturing 1 1 1 1 Machinery manufacturing 0 0 0 0 Computer and electronic manufacturing 0 -1 -1 -1 Electrical equipment and appliance manufacturing 0 0 -1 -1 Motor vehicles, bodies and trailers, and parts manufacturing 1 1 1 1 Other transportation equipment manufacturing 0 0 0 0 Furniture and related manufacturing 0 0 0 0 Miscellaneous manufacturing 0 0 0 0 Food manufacturing 1 2 2 3 Beverage and tobacco manufacturing 0 0 0 0 Textile mills; Textile mills 0 0 0 0 Apparel manufacturing; Leather and allied manufacturing 0 0 0 0 Paper manufacturing 0 0 0 0 Printing and related support activities 0 1 1 1 Petroleum and coals manufacturing 0 0 0 0 Chemical manufacturing 0 0 0 0 Plastics and rubber manufacturing 0 0 0 0 Wholesale trade 2 4 5 7 Retail trade 10 23 30 35 Air transportation 0 -1 -2 -2 Rail transportation 0 0 0 0 Water transportation 0 0 0 0 Truck transportation 1 3 6 8 Couriers and messengers 0 1 1 1 Transit and ground passenger transportation 0 1 1 1 Pipeline transportation 0 0 0 0 Scenic and sightseeing transportation; Support activities for transportation 0 -1 -1 -2 Warehousing and storage 0 0 0 0 Publishing industries, except Internet 0 1 1 1 Motion picture and sound recording industries 0 0 0 0 Internet publishing and broadcasting; ISPs, search portals, and data processing 0 0 0 0 Broadcasting, except Internet 0 0 0 0 Telecommunications 1 1 1 1 Monetary authorities - central bank; Credit intermediation and related activities 2 3 4 4 Securities, commodity contracts, investments 2 3 3 4 Insurance carriers and related activities 3 4 4 4 Real estate 3 9 11 12 Rental and leasing services; Leasing of nonfinancial intangible assets 0 1 1 1 Professional, scientific, and technical services 1 4 5 6 Management of companies and enterprises 0 -1 -1 -1 Administrative and support services 5 12 15 18 Waste management and remediation services 0 0 1 1 Educational services 4 8 10 12 Ambulatory health care services 10 18 23 29 Hospitals 5 10 14 18 Nursing and residential care facilities 4 8 12 15 Social assistance 4 8 10 12 Performing arts and spectator sports 1 2 3 3 Museums, historical sites, zoos, and parks 0 0 0 0 Amusement, gambling, and recreation 2 4 5 6 Accommodation 1 3 4 4 Food services and drinking places 7 18 24 27 Repair and maintenance 1 3 4 5 Personal and laundry services 3 5 6 7 Membership associations and organizations 3 6 9 10 Private households 1 2 3 3 State and local government 3 10 13 13 TOTAL OF ALL SECTORS = 81 194 248 290

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Figure 6.20 – Employment by Occupation (thousands over baseline) 95 occupation SOC 2020 2025 2030 2035 Top executives 1 3 3 4 Advertising, marketing, promotions, public relations, and sales managers 0 1 1 1 Operations specialties managers 1 1 2 2 Other management occupations 1 3 4 5 Business operations specialists 2 4 5 6 Financial specialists 2 3 4 4 Computer occupations 1 2 2 2 Mathematical science occupations 0 0 0 0 Architects, surveyors, and cartographers 0 0 0 0 Engineers 0 0 0 0 Drafters, engineering technicians, and mapping technicians 0 0 0 0 Life scientists 0 0 0 0 Physical scientists 0 0 0 0 Social scientists and related workers 0 0 0 0 Life, physical, and social science technicians 0 0 0 0 Counselors and Social workers 1 2 3 4 Miscellaneous community and social service specialists 1 2 2 2 Religious workers 0 0 0 0 Lawyers, judges, and related workers 0 0 1 1 Legal support workers 0 0 0 0 Postsecondary teachers 1 3 3 4 Preschool, primary, secondary, and special education school teachers 1 4 5 5 Other teachers and instructors 1 1 2 2 Librarians, curators, and archivists 0 0 0 0 Other education, training, and library occupations 1 2 2 2 Art and design workers 0 1 1 1 Entertainers and performers, sports and related workers 1 1 1 2 Media and communication workers 1 1 1 2 Media and communication equipment workers 0 0 0 0 Health diagnosing and treating practitioners 5 10 13 17 Health technologists and technicians 3 6 8 10 Other healthcare practitioners and technical occupations 0 0 0 0 Nursing, psychiatric, and home health aides 3 6 9 11 Occupational therapy and physical therapist assistants and aides 0 0 1 1 Other healthcare support occupations 2 4 5 6 Supervisors of protective service workers 0 0 0 0 Fire fighting and prevention workers 0 0 0 0 Law enforcement workers 0 1 1 1 Other protective service workers 1 2 2 3 Supervisors of food preparation and serving workers 1 2 2 2 Cooks and food preparation workers 2 5 7 8 Food and beverage serving workers 5 12 16 18 Other food preparation and serving related workers 1 2 3 3 Supervisors of building and grounds cleaning and maintenance workers 0 1 1 1 Building cleaning and pest control workers 2 5 7 8 Grounds maintenance workers 2 6 8 9 Supervisors of personal care and service workers 0 0 0 1 Animal care and service workers 0 1 1 1 Entertainment attendants and related workers 1 1 1 2 Funeral service workers 0 0 0 0 Personal appearance workers 2 3 3 4 Baggage porters, bellhops, and concierges; Tour and travel guides 0 0 0 0 Other personal care and service workers 3 6 8 10 Supervisors of sales workers 1 2 3 3 Retail sales workers 6 14 18 21 Sales representatives, services 1 2 3 3 Sales representatives, wholesale and manufacturing 1 1 2 2 Other sales and related workers 1 2 3 3 Supervisors of office and administrative support workers 1 2 3 3 Communications equipment operators 0 0 0 0 Financial clerks 2 5 6 7 Information and record clerks 4 7 9 10 Material recording, scheduling, dispatching, and distributing workers 1 3 4 5 Secretaries and administrative assistants 3 6 8 9 Other office and administrative support workers 3 6 7 8 Supervisors of farming, fishing, and forestry workers 0 0 0 0 Agricultural workers 0 0 0 0 Fishing and hunting workers 0 0 0 0 Forest, conservation, and logging workers 0 0 0 0

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Supervisors of construction and extraction workers 0 1 2 2 Construction trades workers 2 11 14 16 Helpers, construction trades 0 1 1 1 Other construction and related workers 0 0 1 1 Extraction workers -1 -1 -1 -1 Supervisors of installation, maintenance, and repair workers 0 1 1 1 Electrical and electronic equipment mechanics, installers, and repairers 0 1 1 1 Vehicle and mobile equipment mechanics, installers, and repairers 1 2 3 4 Other installation, maintenance, and repair occupations 1 4 6 6 Supervisors of production workers 0 0 0 0 Assemblers and fabricators 0 1 1 1 Food processing workers 1 1 1 1 Metal workers and plastic workers 0 1 1 1 Printing workers 0 0 0 0 Textile, apparel, and furnishings workers 0 0 0 1 Woodworkers 0 0 0 0 Plant and system operators 0 0 0 0 Other production occupations 1 2 2 2 Supervisors of transportation and material moving workers 0 0 1 1 Air transportation workers 0 0 -1 -1 Motor vehicle operators 2 5 8 10 Rail transportation workers 0 0 0 0 Water transportation workers 0 0 0 0 Other transportation workers 0 0 1 1 Material moving workers 2 4 5 6 Military 0 0 0 0 TOTAL OF ALL OCCUPATIONS = 82 191 251 293

Ames, Iowa

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South Atlantic (SA)

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Electrical Power Capacity (SA level)

Baseline ($0/ton) Alternative ($10/year) 300 300 Storage

Solar 250 250 Wind Biopower

Geothermal

200 200 Hydro

Nuclear 150 150 Oil-Gas-Steam Gas-CC-CCS

Gas-CT

Gas-CC

Capacity (GW) Capacity 100 100 Coal-CCS

Coal-IGCC

50 50 Coal-New

Cofiring 0 0 Coal-Old Scrubbed 2010 2020 2030 2040 2010 2020 2030 2040 Coal-Old Unscrubbed

Figure 6.21 – SA lacks the geography, topography, and meteorology of the ENC and WNC to encourage much wind development, and therefore the region concentrates on replacing its reduction in coal output with renewals and expansions in its nuclear fleet.

Electrical Power Generation (SA level)

Baseline ($0/ton) Alternative ($10/year) 1,000 1,000 Solar

900 900 Wind 800 800 Biopower

Geothermal

700 700 Hydro 600 600 Nuclear Oil-Gas-Steam

500 500 Gas-CC-CCS

Gas-CT 400 400 Gas-CC

300 300 Coal-CCS Generation (TWh) Generation Coal-IGCC

200 200 Coal-New 100 100 Cofiring Coal-Old Scrubbed

0 0 Coal-Old Unscrubbed 2010 2020 2030 2040 2010 2020 2030 2040

Figure 6.22 – Nuclear overwhelms the alternative case and replaces the coal and gas in the baseline. Additionally, SA has a greater quantity of solar generation than is typical in the other regions owing to the bright sunlight in Florida and some of the other states.

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Figure 6.23 – GRP by Industry (millions of 2012 dollars) 70 sector NAICS 2020 2025 2030 2035 Forestry and logging; Fishing, hunting, and trapping -$38 -$102 -$139 -$160 Agriculture and forestry support activities -$4 -$12 -$15 -$17 Oil and gas extraction -$132 -$295 -$432 -$484 Mining (except oil and gas) -$1,157 -$3,308 -$5,290 -$5,555 Support activities for mining -$23 -$28 -$8 $13 Utilities -$1,903 -$2,251 -$1,695 -$1,591 Construction $631 $1,443 $2,589 $3,287 Wood manufacturing $27 $32 $33 $32 Nonmetallic mineral manufacturing $34 $42 $51 $62 Primary metal manufacturing -$59 -$182 -$261 -$288 Fabricated metal manufacturing $94 $66 $167 $447 Machinery manufacturing -$3 $64 $107 $60 Computer and electronic manufacturing -$104 -$382 -$531 -$582 Electrical equipment and appliance manufacturing -$66 -$214 -$337 -$424 Motor vehicles, bodies and trailers, and parts manufacturing $116 $205 $279 $352 Other transportation equipment manufacturing -$5 -$60 -$110 -$146 Furniture and related manufacturing $63 $57 $31 $0 Miscellaneous manufacturing $5 -$61 -$103 -$115 Food manufacturing $129 $136 $120 $111 Beverage and tobacco manufacturing $203 $222 $194 $157 Textile mills; Textile mills -$13 -$110 -$206 -$237 Apparel manufacturing; Leather and allied manufacturing -$6 -$26 -$33 -$33 Paper manufacturing $12 -$37 -$81 -$111 Printing and related support activities $32 $38 $41 $45 Petroleum and coals manufacturing -$415 -$955 -$1,305 -$1,639 Chemical manufacturing -$155 -$837 -$1,411 -$1,876 Plastics and rubber manufacturing -$6 -$121 -$233 -$322 Wholesale trade $751 $964 $1,270 $1,675 Retail trade $1,663 $2,967 $4,330 $5,661 Air transportation -$590 -$1,777 -$3,188 -$4,577 Rail transportation -$49 -$113 -$175 -$205 Water transportation -$12 -$33 -$58 -$79 Truck transportation $67 $60 $39 $45 Couriers and messengers $39 $29 $1 -$22 Transit and ground passenger transportation $22 $29 $33 $38 Pipeline transportation -$29 -$47 -$54 -$54 Scenic and sightseeing transportation; Support activities for transportation -$160 -$427 -$728 -$1,043 Warehousing and storage $27 $19 $4 -$1 Publishing industries, except Internet $169 $229 $306 $412 Motion picture and sound recording industries $76 $127 $176 $232 Internet publishing and broadcasting; ISPs, search portals, and data processing $85 $98 $127 $167 Broadcasting, except Internet $69 $89 $108 $135 Telecommunications $729 $1,094 $1,428 $1,778 Monetary authorities - central bank; Credit intermediation and related activities $1,772 $2,593 $3,146 $3,656 Securities, commodity contracts, investments $441 $568 $616 $674 Insurance carriers and related activities $604 $815 $861 $872 Real estate $2,641 $4,004 $6,141 $8,049 Rental and leasing services; Leasing of nonfinancial intangible assets -$117 -$583 -$1,025 -$1,350 Professional, scientific, and technical services $633 $290 $189 $368 Management of companies and enterprises -$37 -$423 -$807 -$1,083 Administrative and support services $569 $732 $956 $1,218 Waste management and remediation services $49 $58 $76 $97 Educational services $246 $366 $474 $557 Ambulatory health care services $2,962 $4,778 $6,057 $7,065 Hospitals $615 $894 $1,162 $1,413 Nursing and residential care facilities $212 $306 $398 $480 Social assistance $160 $244 $306 $361 Performing arts and spectator sports $127 $186 $235 $287 Museums, historical sites, zoos, and parks $15 $23 $31 $39 Amusement, gambling, and recreation $223 $363 $470 $560 Accommodation $281 $422 $638 $853 Food services and drinking places $406 $547 $797 $1,018 Repair and maintenance $221 $296 $384 $464 Personal and laundry services $509 $831 $1,075 $1,236 Membership associations and organizations $207 $288 $360 $424 Private households $106 $193 $264 $308 State and local government $740 $699 $831 $1,021 TOTAL OF ALL SECTORS = $13,699 $15,122 $18,676 $23,735

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Figure 6.24 – Employment by Industry (thousands over baseline) 70 sector NAICS 2020 2025 2030 2035 Forestry and logging; Fishing, hunting, and trapping 0 -1 -1 -1 Agriculture and forestry support activities 0 0 -1 -1 Oil and gas extraction -1 -3 -5 -6 Mining (except oil and gas) -3 -8 -12 -11 Support activities for mining 0 0 0 0 Utilities -3 -3 -1 -1 Construction 18 41 61 69 Wood manufacturing 1 1 1 1 Nonmetallic mineral manufacturing 1 1 1 2 Primary metal manufacturing 0 0 0 0 Fabricated metal manufacturing 1 1 2 4 Machinery manufacturing 0 0 0 0 Computer and electronic manufacturing 0 -1 -1 -1 Electrical equipment and appliance manufacturing 0 -1 -1 -1 Motor vehicles, bodies and trailers, and parts manufacturing 1 1 1 1 Other transportation equipment manufacturing 0 0 0 0 Furniture and related manufacturing 1 1 1 0 Miscellaneous manufacturing 0 0 0 0 Food manufacturing 1 2 2 2 Beverage and tobacco manufacturing 0 0 0 0 Textile mills; Textile mills 0 -1 -2 -2 Apparel manufacturing; Leather and allied manufacturing 0 0 0 0 Paper manufacturing 0 0 0 0 Printing and related support activities 0 1 1 1 Petroleum and coals manufacturing 0 0 0 0 Chemical manufacturing 0 0 -1 -1 Plastics and rubber manufacturing 0 0 0 0 Wholesale trade 6 8 9 10 Retail trade 29 49 62 71 Air transportation -2 -5 -9 -11 Rail transportation 0 0 0 0 Water transportation 0 0 0 1 Truck transportation 2 4 7 10 Couriers and messengers 1 2 2 3 Transit and ground passenger transportation 1 1 2 2 Pipeline transportation 0 0 0 0 Scenic and sightseeing transportation; Support activities for transportation -2 -4 -6 -7 Warehousing and storage 1 1 1 1 Publishing industries, except Internet 1 1 1 1 Motion picture and sound recording industries 1 1 1 1 Internet publishing and broadcasting; ISPs, search portals, and data processing 0 0 0 0 Broadcasting, except Internet 0 1 1 1 Telecommunications 2 3 3 4 Monetary authorities - central bank; Credit intermediation and related activities 6 9 9 10 Securities, commodity contracts, investments 7 9 9 9 Insurance carriers and related activities 5 6 7 6 Real estate 12 18 25 28 Rental and leasing services; Leasing of nonfinancial intangible assets 1 1 1 1 Professional, scientific, and technical services 8 8 9 11 Management of companies and enterprises 0 -2 -3 -3 Administrative and support services 23 37 48 55 Waste management and remediation services 1 1 1 1 Educational services 8 13 17 19 Ambulatory health care services 38 61 78 91 Hospitals 9 14 18 22 Nursing and residential care facilities 6 9 12 14 Social assistance 6 10 13 15 Performing arts and spectator sports 3 4 5 5 Museums, historical sites, zoos, and parks 0 0 1 1 Amusement, gambling, and recreation 7 12 15 17 Accommodation 4 7 9 11 Food services and drinking places 16 25 32 36 Repair and maintenance 3 5 6 7 Personal and laundry services 11 18 22 23 Membership associations and organizations 7 10 12 14 Private households 13 21 27 29 State and local government 10 9 10 12 TOTAL OF ALL SECTORS = 261 398 502 576

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Figure 6.25 – Employment by Occupation (thousands over baseline) 95 occupation SOC 2020 2025 2030 2035 Top executives 4 5 6 7 Advertising, marketing, promotions, public relations, and sales managers 1 1 2 2 Operations specialties managers 2 2 3 3 Other management occupations 4 6 8 9 Business operations specialists 5 8 9 10 Financial specialists 6 7 8 9 Computer occupations 3 3 3 4 Mathematical science occupations 0 0 0 0 Architects, surveyors, and cartographers 0 0 0 0 Engineers 0 0 0 0 Drafters, engineering technicians, and mapping technicians 0 0 0 0 Life scientists 0 0 0 0 Physical scientists 0 0 0 0 Social scientists and related workers 0 1 1 1 Life, physical, and social science technicians 0 0 0 0 Counselors and Social workers 2 3 4 5 Miscellaneous community and social service specialists 1 2 3 3 Religious workers 0 0 0 0 Lawyers, judges, and related workers 1 1 1 1 Legal support workers 1 1 1 1 Postsecondary teachers 3 4 5 6 Preschool, primary, secondary, and special education school teachers 4 5 6 7 Other teachers and instructors 1 2 2 2 Librarians, curators, and archivists 0 0 0 0 Other education, training, and library occupations 2 2 3 3 Art and design workers 1 1 1 1 Entertainers and performers, sports and related workers 1 2 3 3 Media and communication workers 1 2 2 3 Media and communication equipment workers 0 1 1 1 Health diagnosing and treating practitioners 15 23 30 35 Health technologists and technicians 8 14 17 20 Other healthcare practitioners and technical occupations 0 0 0 1 Nursing, psychiatric, and home health aides 5 8 11 13 Occupational therapy and physical therapist assistants and aides 1 1 2 2 Other healthcare support occupations 7 12 15 17 Supervisors of protective service workers 0 0 0 0 Fire fighting and prevention workers 0 0 0 0 Law enforcement workers 1 1 1 1 Other protective service workers 3 4 5 6 Supervisors of food preparation and serving workers 2 2 3 3 Cooks and food preparation workers 5 8 10 11 Food and beverage serving workers 11 18 23 26 Other food preparation and serving related workers 2 3 4 5 Supervisors of building and grounds cleaning and maintenance workers 1 2 3 4 Building cleaning and pest control workers 12 19 24 27 Grounds maintenance workers 10 19 25 29 Supervisors of personal care and service workers 1 1 1 1 Animal care and service workers 1 2 2 2 Entertainment attendants and related workers 2 3 4 4 Funeral service workers 0 0 0 0 Personal appearance workers 6 10 12 13 Baggage porters, bellhops, and concierges; Tour and travel guides 0 0 0 0 Other personal care and service workers 11 18 23 26 Supervisors of sales workers 3 5 6 7 Retail sales workers 18 29 37 42 Sales representatives, services 4 5 6 6 Sales representatives, wholesale and manufacturing 2 3 3 4 Other sales and related workers 3 4 6 6 Supervisors of office and administrative support workers 3 5 6 6 Communications equipment operators 0 0 0 0 Financial clerks 8 11 14 16 Information and record clerks 12 17 21 23 Material recording, scheduling, dispatching, and distributing workers 4 6 7 8 Secretaries and administrative assistants 10 15 19 21 Other office and administrative support workers 8 12 15 17 Supervisors of farming, fishing, and forestry workers 0 0 0 0 Agricultural workers 0 0 0 0 Fishing and hunting workers 0 0 0 0 Forest, conservation, and logging workers 0 0 0 0

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Supervisors of construction and extraction workers 1 2 3 4 Construction trades workers 10 21 32 36 Helpers, construction trades 1 2 3 3 Other construction and related workers 0 1 1 1 Extraction workers -1 -3 -4 -4 Supervisors of installation, maintenance, and repair workers 1 1 1 2 Electrical and electronic equipment mechanics, installers, and repairers 1 1 2 2 Vehicle and mobile equipment mechanics, installers, and repairers 2 3 4 4 Other installation, maintenance, and repair occupations 5 8 11 13 Supervisors of production workers 0 0 0 0 Assemblers and fabricators 1 1 1 2 Food processing workers 1 1 2 2 Metal workers and plastic workers 1 1 1 2 Printing workers 0 0 0 0 Textile, apparel, and furnishings workers 1 1 1 0 Woodworkers 0 1 1 1 Plant and system operators 0 0 0 0 Other production occupations 2 2 2 3 Supervisors of transportation and material moving workers 0 1 1 1 Air transportation workers -1 -2 -3 -4 Motor vehicle operators 5 8 11 15 Rail transportation workers 0 0 0 0 Water transportation workers 0 0 0 0 Other transportation workers 1 1 1 1 Material moving workers 5 6 7 9 Military 0 0 0 0 TOTAL OF ALL OCCUPATIONS = 258 396 505 576

Orlando, Florida

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East South Central (ESC)

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Electrical Power Capacity (ESC level)

0Baseline ($0/year) Alternative ($10/year) 140 140 Storage

Solar

120 120 Wind

Biopower

Geothermal

100 100 Hydro 80 80 Nuclear Oil-Gas-Steam

Gas-CC-CCS

60 60 Gas-CT

Gas-CC Capacity (GW) Capacity 40 40 Coal-CCS

Coal-IGCC 20 20 Coal-New Cofiring 0 0 Coal-Old Scrubbed 2010 2020 2030 2040 2010 2020 2030 2040 Coal-Old Unscrubbed

Figure 6.26 – ESC, like SA, lacks the conditions to add mass quantities of wind power in the $10 per year case (like the regions in the Midwest). It makes up the difference mostly with nuclear power and some natural gas with carbon sequestration technology included.

Electrical Power Generation (ESC level)

Baseline ($0/year) Alternative ($10/year) 600 600 Solar

Wind

500 500 Biopower

Geothermal 400 400 Hydro Nuclear

Oil-Gas-Steam 300 300 Gas-CC-CCS Gas-CT

Gas-CC

200 200 Coal-CCS Generation (TWh) Generation Coal-IGCC 100 100 Coal-New Cofiring

Coal-Old Scrubbed

0 0 Coal-Old Unscrubbed 2010 2020 2030 2040 2010 2020 2030 2040

Figure 6.27 – ESC retires nearly all its coal plants in the alternative case by 2030 and receives the majority of its power from nuclear generation. Wind plays almost no role in this region, although there is still some renewable production from hydroelectricity, solar, and biomass.

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Figure 6.28 – GRP by Industry (millions of 2012 dollars) 70 sector NAICS 2020 2025 2030 2035 Forestry and logging; Fishing, hunting, and trapping -$21 -$51 -$69 -$77 Agriculture and forestry support activities -$1 -$4 -$5 -$5 Oil and gas extraction -$92 -$195 -$269 -$302 Mining (except oil and gas) -$943 -$2,608 -$3,973 -$4,151 Support activities for mining -$28 -$38 -$26 -$8 Utilities -$713 -$872 -$842 -$845 Construction -$37 $186 $388 $664 Wood manufacturing $7 $7 $2 $3 Nonmetallic mineral manufacturing $4 $2 -$2 $3 Primary metal manufacturing -$95 -$256 -$366 -$403 Fabricated metal manufacturing $36 $2 -$31 $155 Machinery manufacturing -$9 $7 -$4 -$27 Computer and electronic manufacturing -$20 -$71 -$87 -$77 Electrical equipment and appliance manufacturing -$52 -$148 -$234 -$294 Motor vehicles, bodies and trailers, and parts manufacturing $206 $382 $520 $673 Other transportation equipment manufacturing $7 -$4 -$16 -$22 Furniture and related manufacturing $30 $26 $9 -$8 Miscellaneous manufacturing -$3 -$32 -$53 -$60 Food manufacturing $53 $57 $50 $47 Beverage and tobacco manufacturing $45 $56 $52 $46 Textile mills; Textile mills -$3 -$20 -$37 -$42 Apparel manufacturing; Leather and allied manufacturing -$3 -$13 -$17 -$17 Paper manufacturing -$4 -$42 -$76 -$96 Printing and related support activities $10 $12 $12 $13 Petroleum and coals manufacturing -$686 -$1,438 -$1,922 -$2,284 Chemical manufacturing -$315 -$800 -$1,180 -$1,455 Plastics and rubber manufacturing -$18 -$83 -$146 -$190 Wholesale trade $109 $97 $79 $162 Retail trade $442 $866 $1,260 $1,755 Air transportation -$168 -$401 -$618 -$797 Rail transportation -$23 -$51 -$79 -$94 Water transportation -$5 -$13 -$23 -$31 Truck transportation $23 $6 -$23 -$32 Couriers and messengers $19 $8 -$19 -$44 Transit and ground passenger transportation $3 $4 $4 $4 Pipeline transportation -$28 -$47 -$54 -$54 Scenic and sightseeing transportation; Support activities for transportation -$40 -$103 -$173 -$246 Warehousing and storage $8 $4 -$3 -$5 Publishing industries, except Internet $26 $35 $40 $49 Motion picture and sound recording industries $29 $49 $68 $89 Internet publishing and broadcasting; ISPs, search portals, and data processing $8 $10 $12 $17 Broadcasting, except Internet $11 $14 $16 $21 Telecommunications $123 $198 $256 $322 Monetary authorities - central bank; Credit intermediation and related activities $389 $573 $673 $790 Securities, commodity contracts, investments $66 $82 $83 $94 Insurance carriers and related activities $172 $238 $251 $254 Real estate $280 $563 $796 $1,123 Rental and leasing services; Leasing of nonfinancial intangible assets -$18 -$92 -$172 -$218 Professional, scientific, and technical services $3 -$111 -$209 -$199 Management of companies and enterprises -$26 -$117 -$209 -$275 Administrative and support services $96 $122 $138 $198 Waste management and remediation services $8 $7 $5 $9 Educational services $50 $87 $110 $128 Ambulatory health care services $868 $1,386 $1,749 $2,118 Hospitals $175 $286 $374 $462 Nursing and residential care facilities $60 $100 $129 $157 Social assistance $42 $69 $87 $103 Performing arts and spectator sports $28 $44 $55 $68 Museums, historical sites, zoos, and parks $3 $6 $8 $10 Amusement, gambling, and recreation $31 $52 $67 $82 Accommodation $50 $82 $120 $173 Food services and drinking places $89 $166 $235 $302 Repair and maintenance $49 $69 $84 $109 Personal and laundry services $113 $182 $232 $278 Membership associations and organizations $50 $82 $103 $122 Private households $25 $46 $62 $75 State and local government $54 -$4 -$45 $33 TOTAL OF ALL SECTORS = $549 -$1,344 -$2,853 -$1,647

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Figure 6.29 – Employment by Industry (thousands over baseline) 70 sector NAICS 2020 2025 2030 2035 Forestry and logging; Fishing, hunting, and trapping 0 0 0 0 Agriculture and forestry support activities 0 0 0 0 Oil and gas extraction -1 -2 -3 -3 Mining (except oil and gas) -3 -7 -9 -8 Support activities for mining 0 0 0 0 Utilities -1 -1 -1 -1 Construction 3 11 17 21 Wood manufacturing 0 1 1 1 Nonmetallic mineral manufacturing 0 0 1 1 Primary metal manufacturing 0 0 0 0 Fabricated metal manufacturing 0 0 0 2 Machinery manufacturing 0 0 0 0 Computer and electronic manufacturing 0 0 0 0 Electrical equipment and appliance manufacturing 0 -1 -1 -1 Motor vehicles, bodies and trailers, and parts manufacturing 1 2 2 2 Other transportation equipment manufacturing 0 0 0 0 Furniture and related manufacturing 0 0 0 0 Miscellaneous manufacturing 0 0 0 0 Food manufacturing 1 1 1 1 Beverage and tobacco manufacturing 0 0 0 0 Textile mills; Textile mills 0 0 0 0 Apparel manufacturing; Leather and allied manufacturing 0 0 0 0 Paper manufacturing 0 0 0 0 Printing and related support activities 0 0 0 0 Petroleum and coals manufacturing 0 0 0 0 Chemical manufacturing 0 -1 -1 0 Plastics and rubber manufacturing 0 0 0 0 Wholesale trade 1 2 2 2 Retail trade 8 15 19 23 Air transportation -1 -1 -2 -2 Rail transportation 0 0 0 0 Water transportation 0 0 0 0 Truck transportation 1 2 3 5 Couriers and messengers 0 1 1 2 Transit and ground passenger transportation 0 0 0 0 Pipeline transportation 0 0 0 0 Scenic and sightseeing transportation; Support activities for transportation 0 -1 -1 -2 Warehousing and storage 0 0 0 0 Publishing industries, except Internet 0 0 0 0 Motion picture and sound recording industries 0 0 0 0 Internet publishing and broadcasting; ISPs, search portals, and data processing 0 0 0 0 Broadcasting, except Internet 0 0 0 0 Telecommunications 0 1 1 1 Monetary authorities - central bank; Credit intermediation and related activities 2 2 2 2 Securities, commodity contracts, investments 1 1 1 1 Insurance carriers and related activities 1 2 2 2 Real estate 2 4 5 6 Rental and leasing services; Leasing of nonfinancial intangible assets 0 0 0 1 Professional, scientific, and technical services 1 0 0 1 Management of companies and enterprises 0 0 -1 -1 Administrative and support services 5 9 11 13 Waste management and remediation services 0 0 0 0 Educational services 2 3 4 5 Ambulatory health care services 11 18 23 28 Hospitals 3 5 6 7 Nursing and residential care facilities 2 3 4 5 Social assistance 2 3 4 5 Performing arts and spectator sports 1 1 1 1 Museums, historical sites, zoos, and parks 0 0 0 0 Amusement, gambling, and recreation 1 2 3 3 Accommodation 1 2 2 3 Food services and drinking places 4 8 11 12 Repair and maintenance 1 1 2 2 Personal and laundry services 3 4 5 6 Membership associations and organizations 2 4 4 5 Private households 3 5 6 7 State and local government 1 0 -1 0 TOTAL OF ALL SECTORS = 58 99 124 158

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Figure 6.30 – Employment by Occupation (thousands over baseline) 95 occupation SOC 2020 2025 2030 2035 Top executives 1 1 2 2 Advertising, marketing, promotions, public relations, and sales managers 0 0 0 0 Operations specialties managers 0 1 1 1 Other management occupations 1 2 2 3 Business operations specialists 1 2 2 3 Financial specialists 1 1 2 2 Computer occupations 0 0 0 1 Mathematical science occupations 0 0 0 0 Architects, surveyors, and cartographers 0 0 0 0 Engineers 0 0 -1 -1 Drafters, engineering technicians, and mapping technicians 0 0 0 0 Life scientists 0 0 0 0 Physical scientists 0 0 0 0 Social scientists and related workers 0 0 0 0 Life, physical, and social science technicians 0 0 0 0 Counselors and Social workers 1 1 1 2 Miscellaneous community and social service specialists 0 1 1 1 Religious workers 0 0 0 0 Lawyers, judges, and related workers 0 0 0 0 Legal support workers 0 0 0 0 Postsecondary teachers 1 1 1 1 Preschool, primary, secondary, and special education school teachers 1 1 1 1 Other teachers and instructors 0 0 1 1 Librarians, curators, and archivists 0 0 0 0 Other education, training, and library occupations 0 1 1 1 Art and design workers 0 0 0 0 Entertainers and performers, sports and related workers 0 1 1 1 Media and communication workers 0 1 1 1 Media and communication equipment workers 0 0 0 0 Health diagnosing and treating practitioners 4 7 9 11 Health technologists and technicians 2 4 5 6 Other healthcare practitioners and technical occupations 0 0 0 0 Nursing, psychiatric, and home health aides 1 2 3 4 Occupational therapy and physical therapist assistants and aides 0 0 1 1 Other healthcare support occupations 2 3 4 5 Supervisors of protective service workers 0 0 0 0 Fire fighting and prevention workers 0 0 0 0 Law enforcement workers 0 0 0 0 Other protective service workers 1 1 1 1 Supervisors of food preparation and serving workers 0 1 1 1 Cooks and food preparation workers 1 2 3 3 Food and beverage serving workers 3 5 7 8 Other food preparation and serving related workers 1 1 1 2 Supervisors of building and grounds cleaning and maintenance workers 0 1 1 1 Building cleaning and pest control workers 3 5 6 7 Grounds maintenance workers 2 5 6 7 Supervisors of personal care and service workers 0 0 0 0 Animal care and service workers 0 0 0 1 Entertainment attendants and related workers 0 1 1 1 Funeral service workers 0 0 0 0 Personal appearance workers 1 2 3 3 Baggage porters, bellhops, and concierges; Tour and travel guides 0 0 0 0 Other personal care and service workers 3 5 6 7 Supervisors of sales workers 1 1 2 2 Retail sales workers 5 9 11 13 Sales representatives, services 1 1 1 2 Sales representatives, wholesale and manufacturing 0 1 1 1 Other sales and related workers 1 1 1 2 Supervisors of office and administrative support workers 1 1 2 2 Communications equipment operators 0 0 0 0 Financial clerks 2 3 4 4 Information and record clerks 3 4 5 6 Material recording, scheduling, dispatching, and distributing workers 1 2 2 3 Secretaries and administrative assistants 2 4 5 6 Other office and administrative support workers 2 3 4 4 Supervisors of farming, fishing, and forestry workers 0 0 0 0 Agricultural workers 0 0 0 0 Fishing and hunting workers 0 0 0 0 Forest, conservation, and logging workers 0 0 0 0

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Supervisors of construction and extraction workers 0 0 1 1 Construction trades workers 1 5 8 10 Helpers, construction trades 0 1 1 1 Other construction and related workers 0 0 0 0 Extraction workers -1 -3 -3 -3 Supervisors of installation, maintenance, and repair workers 0 0 0 0 Electrical and electronic equipment mechanics, installers, and repairers 0 0 0 0 Vehicle and mobile equipment mechanics, installers, and repairers 0 1 1 1 Other installation, maintenance, and repair occupations 1 1 2 3 Supervisors of production workers 0 0 0 0 Assemblers and fabricators 1 1 1 1 Food processing workers 0 1 1 1 Metal workers and plastic workers 0 0 0 1 Printing workers 0 0 0 0 Textile, apparel, and furnishings workers 0 0 0 0 Woodworkers 0 0 0 0 Plant and system operators 0 0 0 0 Other production occupations 1 1 1 1 Supervisors of transportation and material moving workers 0 0 0 0 Air transportation workers 0 -1 -1 -1 Motor vehicle operators 1 3 4 6 Rail transportation workers 0 0 0 0 Water transportation workers 0 0 0 0 Other transportation workers 0 0 0 0 Material moving workers 1 1 1 2 Military 0 0 0 0 TOTAL OF ALL OCCUPATIONS = 55 100 129 158

Clarksville, Tennessee

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West South Central (WSC)

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Electrical Power Capacity (WSC level)

Baseline ($0/ton) Alternative ($10/ton) 300 300 Storage

Solar 250 250 Wind Biopower

Geothermal

200 200 Hydro

Nuclear 150 150 Oil-Gas-Steam Gas-CC-CCS

Gas-CT

Gas-CC

Capacity (GW) Capacity 100 100 Coal-CCS

Coal-IGCC

50 50 Coal-New

Cofiring 0 0 Coal-Old Scrubbed 2010 2020 2030 2040 2010 2020 2030 2040 Coal-Old Unscrubbed

Figure 6.31 – WSC relies on natural gas more in the baseline than other regions, and it still remains an important part of the base-load in the alternative forecast. The flat terrain of western Texas and western Oklahoma has strong potential for the wind capacity above.

Electrical Power Generation (WSC level)

Baseline ($0/year) Alternative ($10/year) 800 800 Solar 700 700 Wind Biopower

600 600 Geothermal Hydro 500 500 Nuclear Oil-Gas-Steam

400 400 Gas-CC-CCS

Gas-CT

300 300 Gas-CC

Coal-CCS Generation (TWh) Generation 200 200 Coal-IGCC

Coal-New

100 100 Cofiring

Coal-Old Scrubbed

0 0 Coal-Old Unscrubbed 2010 2020 2030 2040 2010 2020 2030 2040

Figure 3.32 – Natural gas replaces coal as the base-load source in the alternative, and wind and solar take the place as the variable generation resource. WSC behaves much like the national level results although with a larger proportion for natural gas than other regions.

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Figure 6.33 – GRP by Industry (millions of 2012 dollars) 70 sector NAICS 2020 2025 2030 2035 Forestry and logging; Fishing, hunting, and trapping -$23 -$63 -$94 -$111 Agriculture and forestry support activities -$2 -$6 -$9 -$10 Oil and gas extraction -$4,710 -$10,677 -$14,796 -$15,780 Mining (except oil and gas) $4 -$213 -$358 -$406 Support activities for mining -$770 -$1,226 -$1,315 -$1,170 Utilities -$1,544 -$2,173 -$2,285 -$2,241 Construction -$1,042 -$2,525 -$3,525 -$3,275 Wood manufacturing -$4 -$25 -$49 -$57 Nonmetallic mineral manufacturing -$25 -$76 -$126 -$134 Primary metal manufacturing -$77 -$240 -$385 -$459 Fabricated metal manufacturing $4 -$232 -$437 -$412 Machinery manufacturing -$50 -$46 -$166 -$298 Computer and electronic manufacturing -$160 -$551 -$905 -$1,117 Electrical equipment and appliance manufacturing -$43 -$126 -$201 -$247 Motor vehicles, bodies and trailers, and parts manufacturing $50 $73 $69 $76 Other transportation equipment manufacturing -$30 -$107 -$183 -$239 Furniture and related manufacturing $17 $6 -$15 -$32 Miscellaneous manufacturing -$23 -$86 -$139 -$168 Food manufacturing $83 $78 $45 $23 Beverage and tobacco manufacturing $27 $21 $7 -$1 Textile mills; Textile mills -$1 -$10 -$19 -$22 Apparel manufacturing; Leather and allied manufacturing -$4 -$15 -$22 -$23 Paper manufacturing -$7 -$55 -$104 -$133 Printing and related support activities $7 -$4 -$16 -$21 Petroleum and coals manufacturing -$3,559 -$8,941 -$13,939 -$17,985 Chemical manufacturing -$827 -$2,580 -$4,402 -$5,830 Plastics and rubber manufacturing -$38 -$158 -$288 -$377 Wholesale trade -$183 -$966 -$1,914 -$2,595 Retail trade $243 $96 -$116 $24 Air transportation -$656 -$1,831 -$3,132 -$4,348 Rail transportation -$42 -$95 -$150 -$181 Water transportation -$10 -$29 -$52 -$71 Truck transportation $20 -$40 -$138 -$196 Couriers and messengers $10 -$4 -$31 -$54 Transit and ground passenger transportation $8 $6 $2 -$1 Pipeline transportation -$277 -$465 -$546 -$553 Scenic and sightseeing transportation; Support activities for transportation -$150 -$400 -$694 -$1,011 Warehousing and storage $15 $13 $6 $3 Publishing industries, except Internet $23 -$44 -$142 -$212 Motion picture and sound recording industries $49 $82 $112 $149 Internet publishing and broadcasting; ISPs, search portals, and data processing $11 -$45 -$112 -$151 Broadcasting, except Internet $16 $10 -$2 -$4 Telecommunications $336 $432 $440 $515 Monetary authorities - central bank; Credit intermediation and related activities $781 $992 $983 $1,100 Securities, commodity contracts, investments $189 $224 $216 $241 Insurance carriers and related activities $323 $414 $396 $385 Real estate $1,081 $833 $616 $1,219 Rental and leasing services; Leasing of nonfinancial intangible assets -$478 -$1,367 -$2,317 -$3,025 Professional, scientific, and technical services -$354 -$1,389 -$2,518 -$3,220 Management of companies and enterprises -$105 -$381 -$691 -$942 Administrative and support services $77 -$154 -$459 -$627 Waste management and remediation services $3 -$33 -$74 -$96 Educational services $93 $101 $85 $85 Ambulatory health care services $1,234 $1,917 $2,351 $2,796 Hospitals $323 $376 $342 $351 Nursing and residential care facilities $97 $103 $78 $67 Social assistance $91 $132 $148 $166 Performing arts and spectator sports $38 $33 $12 $6 Museums, historical sites, zoos, and parks $7 $6 $4 $3 Amusement, gambling, and recreation $67 $102 $122 $145 Accommodation $102 $111 $115 $159 Food services and drinking places $192 $72 -$105 -$185 Repair and maintenance $76 $7 -$87 -$118 Personal and laundry services $181 $281 $351 $423 Membership associations and organizations $87 $98 $84 $85 Private households $34 $65 $89 $111 State and local government -$434 -$1,603 -$2,548 -$2,835 TOTAL OF ALL SECTORS = -$9,629 -$32,297 -$52,933 -$62,841

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Figure 6.34 – Employment by Industry (thousands over baseline) 70 sector NAICS 2020 2025 2030 2035 Forestry and logging; Fishing, hunting, and trapping 0 -1 -1 -1 Agriculture and forestry support activities 0 0 0 0 Oil and gas extraction -15 -33 -48 -54 Mining (except oil and gas) 0 -2 -2 -2 Support activities for mining -3 -3 -3 -1 Utilities -2 -3 -2 -2 Construction -11 -24 -30 -23 Wood manufacturing 0 0 0 0 Nonmetallic mineral manufacturing 0 0 0 1 Primary metal manufacturing 0 0 0 0 Fabricated metal manufacturing 0 -1 -2 -1 Machinery manufacturing 0 0 0 0 Computer and electronic manufacturing -1 -1 -1 -1 Electrical equipment and appliance manufacturing 0 -1 -1 -1 Motor vehicles, bodies and trailers, and parts manufacturing 0 0 0 0 Other transportation equipment manufacturing 0 0 0 0 Furniture and related manufacturing 0 0 0 0 Miscellaneous manufacturing 0 0 -1 0 Food manufacturing 1 2 2 2 Beverage and tobacco manufacturing 0 0 0 0 Textile mills; Textile mills 0 0 0 0 Apparel manufacturing; Leather and allied manufacturing 0 0 0 0 Paper manufacturing 0 0 0 0 Printing and related support activities 0 0 0 0 Petroleum and coals manufacturing -1 -2 -2 -2 Chemical manufacturing -1 -2 -3 -3 Plastics and rubber manufacturing 0 -1 -1 -1 Wholesale trade 0 -3 -6 -7 Retail trade 6 7 6 8 Air transportation -2 -6 -8 -11 Rail transportation 0 0 0 0 Water transportation 0 0 0 1 Truck transportation 1 3 4 6 Couriers and messengers 0 1 1 1 Transit and ground passenger transportation 0 0 0 1 Pipeline transportation -1 -1 -1 0 Scenic and sightseeing transportation; Support activities for transportation -1 -3 -5 -6 Warehousing and storage 0 0 0 1 Publishing industries, except Internet 0 0 0 0 Motion picture and sound recording industries 0 1 1 1 Internet publishing and broadcasting; ISPs, search portals, and data processing 0 0 0 0 Broadcasting, except Internet 0 0 0 0 Telecommunications 1 1 1 1 Monetary authorities - central bank; Credit intermediation and related activities 3 4 3 4 Securities, commodity contracts, investments 4 4 4 5 Insurance carriers and related activities 3 4 4 3 Real estate 5 6 6 7 Rental and leasing services; Leasing of nonfinancial intangible assets 0 0 -1 -2 Professional, scientific, and technical services -2 -9 -17 -21 Management of companies and enterprises 0 -2 -2 -3 Administrative and support services 6 7 6 5 Waste management and remediation services 0 0 0 0 Educational services 3 5 5 5 Ambulatory health care services 18 28 35 41 Hospitals 5 7 7 7 Nursing and residential care facilities 3 4 3 3 Social assistance 4 6 7 8 Performing arts and spectator sports 1 1 1 1 Museums, historical sites, zoos, and parks 0 0 0 0 Amusement, gambling, and recreation 2 4 5 5 Accommodation 2 2 3 3 Food services and drinking places 8 9 7 6 Repair and maintenance 1 1 1 1 Personal and laundry services 4 6 7 8 Membership associations and organizations 4 5 4 5 Private households 4 7 9 11 State and local government -6 -22 -33 -36 TOTAL OF ALL SECTORS = 43 5 -38 -27

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Figure 6.35 – Employment by Occupation (thousands over baseline) 95 occupation SOC 2020 2025 2030 2035 Top executives 0 -1 -2 -2 Advertising, marketing, promotions, public relations, and sales managers 0 0 0 0 Operations specialties managers 0 -1 -2 -2 Other management occupations 1 0 -1 -1 Business operations specialists 0 -2 -4 -5 Financial specialists 1 0 -1 -1 Computer occupations 0 -3 -6 -7 Mathematical science occupations 0 0 0 0 Architects, surveyors, and cartographers 0 0 -1 -1 Engineers -3 -8 -11 -12 Drafters, engineering technicians, and mapping technicians -1 -2 -2 -3 Life scientists 0 0 0 0 Physical scientists -1 -2 -3 -3 Social scientists and related workers 0 0 0 0 Life, physical, and social science technicians -1 -1 -2 -2 Counselors and Social workers 1 1 1 1 Miscellaneous community and social service specialists 1 1 1 1 Religious workers 0 0 0 0 Lawyers, judges, and related workers 0 0 -1 -1 Legal support workers 0 0 -1 -1 Postsecondary teachers 0 0 -1 -1 Preschool, primary, secondary, and special education school teachers 0 -3 -5 -5 Other teachers and instructors 0 0 0 0 Librarians, curators, and archivists 0 0 0 0 Other education, training, and library occupations 0 -1 -1 -1 Art and design workers 0 0 0 0 Entertainers and performers, sports and related workers 0 0 0 0 Media and communication workers 0 0 0 0 Media and communication equipment workers 0 0 0 0 Health diagnosing and treating practitioners 6 9 10 12 Health technologists and technicians 3 5 5 6 Other healthcare practitioners and technical occupations 0 0 0 0 Nursing, psychiatric, and home health aides 3 4 5 5 Occupational therapy and physical therapist assistants and aides 0 1 1 1 Other healthcare support occupations 3 5 5 6 Supervisors of protective service workers 0 0 0 0 Fire fighting and prevention workers 0 0 -1 -1 Law enforcement workers 0 -1 -2 -2 Other protective service workers 1 0 0 0 Supervisors of food preparation and serving workers 1 1 1 1 Cooks and food preparation workers 2 2 2 2 Food and beverage serving workers 5 6 5 4 Other food preparation and serving related workers 1 1 1 1 Supervisors of building and grounds cleaning and maintenance workers 0 1 1 1 Building cleaning and pest control workers 4 5 6 7 Grounds maintenance workers 3 5 6 7 Supervisors of personal care and service workers 0 0 0 0 Animal care and service workers 0 0 1 1 Entertainment attendants and related workers 1 1 1 1 Funeral service workers 0 0 0 0 Personal appearance workers 2 3 4 4 Baggage porters, bellhops, and concierges; Tour and travel guides 0 0 0 0 Other personal care and service workers 5 7 9 10 Supervisors of sales workers 1 1 0 1 Retail sales workers 4 5 4 5 Sales representatives, services 2 2 1 1 Sales representatives, wholesale and manufacturing 0 -1 -2 -3 Other sales and related workers 1 1 1 1 Supervisors of office and administrative support workers 1 1 0 0 Communications equipment operators 0 0 0 0 Financial clerks 2 1 0 0 Information and record clerks 4 3 2 2 Material recording, scheduling, dispatching, and distributing workers 0 -1 -2 -2 Secretaries and administrative assistants 2 1 0 1 Other office and administrative support workers 2 0 -1 -1 Supervisors of farming, fishing, and forestry workers 0 0 0 0 Agricultural workers 0 0 0 0 Fishing and hunting workers 0 0 0 0 Forest, conservation, and logging workers 0 0 0 0

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Supervisors of construction and extraction workers -1 -3 -4 -3 Construction trades workers -6 -13 -17 -14 Helpers, construction trades 0 -1 -1 -1 Other construction and related workers 0 -1 -1 -1 Extraction workers -4 -8 -10 -10 Supervisors of installation, maintenance, and repair workers 0 -1 -1 -1 Electrical and electronic equipment mechanics, installers, and repairers 0 0 -1 -1 Vehicle and mobile equipment mechanics, installers, and repairers 0 0 -1 -1 Other installation, maintenance, and repair occupations -1 -3 -5 -4 Supervisors of production workers 0 -1 -1 -1 Assemblers and fabricators 0 -1 -1 -1 Food processing workers 0 1 1 1 Metal workers and plastic workers 0 -1 -2 -2 Printing workers 0 0 0 0 Textile, apparel, and furnishings workers 0 0 0 0 Woodworkers 0 0 0 0 Plant and system operators -2 -3 -4 -4 Other production occupations 0 -1 -2 -2 Supervisors of transportation and material moving workers 0 0 0 0 Air transportation workers -1 -2 -3 -4 Motor vehicle operators 1 1 1 2 Rail transportation workers 0 0 0 0 Water transportation workers 0 0 0 0 Other transportation workers 0 0 0 0 Material moving workers -1 -3 -6 -6 Military 0 0 0 0 TOTAL OF ALL OCCUPATIONS = 42 6 -37 -28

Dallas, Texas

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Mountain (MNT)

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Electrical Power Capacity (MNT level)

Baseline ($0/year) Alternative ($10/year) 160 160 Storage

Solar 140 140 Wind

Biopower 120 120

Geothermal

Hydro 100 100 Nuclear 80 80 Oil-Gas-Steam Gas-CC-CCS 60 60 Gas-CT

Gas-CC Capacity (GW) Capacity 40 40 Coal-CCS Coal-IGCC 20 20 Coal-New Cofiring 0 0 Coal-Old Scrubbed 2010 2020 2030 2040 2010 2020 2030 2040 Coal-Old Unscrubbed

Figure 6.36 – Coal is steady in the MNT baseline, although the carbon price quickly makes it uneconomical in the 2020s. It sees replacement by larger capacities of wind and solar. The solar capacity of this region is higher than in any of the other under consideration.

Electrical Power Generation (MNT level)

Baseline ($0/year) Alternative ($10/year) 500 500 Solar

450 450 Wind 400 400 Biopower

Geothermal

350 350 Hydro 300 300 Nuclear Oil-Gas-Steam

250 250 Gas-CC-CCS

Gas-CT 200 200 Gas-CC

150 150 Coal-CCS Generation (TWh) Generation Coal-IGCC

100 100 Coal-New 50 50 Cofiring Coal-Old Scrubbed

0 0 Coal-Old Unscrubbed 2010 2020 2030 2040 2010 2020 2030 2040

Figure 6.37 – The removal of the coal generation in the area improves the quality of life and means more solar, wind, and geothermal resources take its place. The MNT region even has very little natural gas or nuclear power in its generation profile from the above results.

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Figure 6.38 – GRP by Industry (millions of 2012 dollars) 70 sector NAICS 2020 2025 2030 2035 Forestry and logging; Fishing, hunting, and trapping -$7 -$11 -$18 -$24 Agriculture and forestry support activities -$1 -$1 -$2 -$3 Oil and gas extraction -$542 -$1,148 -$1,521 -$1,589 Mining (except oil and gas) -$899 -$2,048 -$2,719 -$2,834 Support activities for mining -$181 -$107 -$69 -$58 Utilities -$712 -$598 -$736 -$845 Construction $206 $1,324 $1,262 $1,341 Wood manufacturing $7 $20 $16 $14 Nonmetallic mineral manufacturing $6 $32 $23 $18 Primary metal manufacturing -$29 -$60 -$86 -$95 Fabricated metal manufacturing $50 $57 $13 $3 Machinery manufacturing -$16 $11 $3 -$19 Computer and electronic manufacturing -$34 -$109 -$291 -$408 Electrical equipment and appliance manufacturing -$2 -$15 -$33 -$48 Motor vehicles, bodies and trailers, and parts manufacturing $16 $31 $37 $43 Other transportation equipment manufacturing -$34 -$84 -$132 -$170 Furniture and related manufacturing $18 $24 $15 $5 Miscellaneous manufacturing -$4 -$49 -$92 -$111 Food manufacturing $43 $61 $57 $50 Beverage and tobacco manufacturing $17 $28 $29 $27 Textile mills; Textile mills $0 -$4 -$8 -$9 Apparel manufacturing; Leather and allied manufacturing $0 -$1 -$1 $0 Paper manufacturing $3 $3 -$1 -$5 Printing and related support activities $13 $23 $23 $23 Petroleum and coals manufacturing -$730 -$1,152 -$1,626 -$2,197 Chemical manufacturing -$30 -$53 -$131 -$216 Plastics and rubber manufacturing -$2 -$10 -$31 -$50 Wholesale trade $433 $936 $1,087 $1,277 Retail trade $1,063 $2,314 $2,939 $3,630 Air transportation -$250 -$707 -$1,212 -$1,652 Rail transportation -$25 -$53 -$87 -$106 Water transportation $0 $0 -$1 -$1 Truck transportation $38 $56 $34 $24 Couriers and messengers $14 $14 $0 -$12 Transit and ground passenger transportation $13 $18 $14 $9 Pipeline transportation -$31 -$51 -$60 -$61 Scenic and sightseeing transportation; Support activities for transportation -$57 -$138 -$232 -$332 Warehousing and storage $8 $8 $1 -$4 Publishing industries, except Internet $77 $138 $145 $162 Motion picture and sound recording industries $33 $57 $77 $99 Internet publishing and broadcasting; ISPs, search portals, and data processing $32 $66 $69 $72 Broadcasting, except Internet $22 $41 $44 $47 Telecommunications $281 $534 $643 $738 Monetary authorities - central bank; Credit intermediation and related activities $788 $1,356 $1,524 $1,668 Securities, commodity contracts, investments $155 $244 $245 $247 Insurance carriers and related activities $206 $312 $319 $312 Real estate $913 $2,562 $2,901 $2,975 Rental and leasing services; Leasing of nonfinancial intangible assets -$101 -$268 -$518 -$713 Professional, scientific, and technical services $104 $314 $96 -$74 Management of companies and enterprises -$20 -$88 -$213 -$318 Administrative and support services $226 $453 $449 $446 Waste management and remediation services $19 $43 $46 $47 Educational services $95 $189 $228 $249 Ambulatory health care services $1,184 $2,071 $2,503 $2,957 Hospitals $246 $492 $624 $728 Nursing and residential care facilities $80 $163 $207 $241 Social assistance $75 $134 $164 $188 Performing arts and spectator sports $48 $94 $111 $128 Museums, historical sites, zoos, and parks $7 $16 $20 $23 Amusement, gambling, and recreation $95 $176 $210 $239 Accommodation $266 $625 $722 $742 Food services and drinking places $215 $499 $612 $681 Repair and maintenance $108 $229 $268 $298 Personal and laundry services $179 $326 $376 $423 Membership associations and organizations $66 $130 $156 $172 Private households $31 $60 $70 $79 State and local government $299 $725 $690 $679 TOTAL OF ALL SECTORS = $4,091 $10,254 $9,252 $9,150

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Figure 6.39 – Employment by Industry (thousands over baseline) 70 sector NAICS 2020 2025 2030 2035 Forestry and logging; Fishing, hunting, and trapping 0 0 0 0 Agriculture and forestry support activities 0 0 0 0 Oil and gas extraction -2 -5 -7 -8 Mining (except oil and gas) -4 -8 -9 -8 Support activities for mining -1 0 0 0 Utilities -1 -1 -1 -1 Construction 8 27 26 27 Wood manufacturing 0 0 0 0 Nonmetallic mineral manufacturing 0 1 1 1 Primary metal manufacturing 0 0 0 0 Fabricated metal manufacturing 0 1 0 1 Machinery manufacturing 0 0 0 0 Computer and electronic manufacturing 0 0 -1 -1 Electrical equipment and appliance manufacturing 0 0 0 0 Motor vehicles, bodies and trailers, and parts manufacturing 0 0 0 0 Other transportation equipment manufacturing 0 0 0 0 Furniture and related manufacturing 0 0 0 0 Miscellaneous manufacturing 0 0 0 0 Food manufacturing 1 1 1 1 Beverage and tobacco manufacturing 0 0 0 0 Textile mills; Textile mills 0 0 0 0 Apparel manufacturing; Leather and allied manufacturing 0 0 0 0 Paper manufacturing 0 0 0 0 Printing and related support activities 0 0 0 0 Petroleum and coals manufacturing 0 0 0 0 Chemical manufacturing 0 0 0 0 Plastics and rubber manufacturing 0 0 0 0 Wholesale trade 3 6 6 7 Retail trade 18 34 39 43 Air transportation -1 -2 -3 -4 Rail transportation 0 0 0 0 Water transportation 0 0 0 0 Truck transportation 1 2 4 5 Couriers and messengers 0 1 1 1 Transit and ground passenger transportation 0 1 1 1 Pipeline transportation 0 0 0 0 Scenic and sightseeing transportation; Support activities for transportation -1 -1 -2 -2 Warehousing and storage 0 0 0 0 Publishing industries, except Internet 0 1 1 1 Motion picture and sound recording industries 0 1 1 1 Internet publishing and broadcasting; ISPs, search portals, and data processing 0 0 0 0 Broadcasting, except Internet 0 0 0 0 Telecommunications 1 1 1 1 Monetary authorities - central bank; Credit intermediation and related activities 3 5 5 5 Securities, commodity contracts, investments 4 5 5 5 Insurance carriers and related activities 2 3 3 2 Real estate 6 13 14 15 Rental and leasing services; Leasing of nonfinancial intangible assets 1 1 1 1 Professional, scientific, and technical services 2 5 4 3 Management of companies and enterprises 0 0 -1 -1 Administrative and support services 8 16 18 20 Waste management and remediation services 0 0 1 1 Educational services 3 6 8 9 Ambulatory health care services 15 27 33 40 Hospitals 4 7 9 10 Nursing and residential care facilities 2 4 5 6 Social assistance 3 5 7 8 Performing arts and spectator sports 1 2 3 3 Museums, historical sites, zoos, and parks 0 0 0 0 Amusement, gambling, and recreation 3 6 7 8 Accommodation 4 8 9 9 Food services and drinking places 8 16 19 21 Repair and maintenance 2 3 4 4 Personal and laundry services 4 7 8 8 Membership associations and organizations 2 4 5 6 Private households 4 7 7 7 State and local government 4 10 9 8 TOTAL OF ALL SECTORS = 107 220 242 264

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Figure 6.40 – Employment by Occupation (thousands over baseline) 95 occupation SOC 2020 2025 2030 2035 Top executives 1 3 3 3 Advertising, marketing, promotions, public relations, and sales managers 0 1 1 1 Operations specialties managers 1 1 1 1 Other management occupations 2 4 4 4 Business operations specialists 2 4 4 5 Financial specialists 2 4 4 4 Computer occupations 1 2 1 1 Mathematical science occupations 0 0 0 0 Architects, surveyors, and cartographers 0 0 0 0 Engineers 0 0 -1 -1 Drafters, engineering technicians, and mapping technicians 0 0 0 0 Life scientists 0 0 0 0 Physical scientists 0 0 0 0 Social scientists and related workers 0 0 0 0 Life, physical, and social science technicians 0 0 0 0 Counselors and Social workers 1 2 2 3 Miscellaneous community and social service specialists 1 1 1 2 Religious workers 0 0 0 0 Lawyers, judges, and related workers 0 1 0 0 Legal support workers 0 0 0 0 Postsecondary teachers 1 2 3 3 Preschool, primary, secondary, and special education school teachers 1 3 3 3 Other teachers and instructors 0 1 1 1 Librarians, curators, and archivists 0 0 0 0 Other education, training, and library occupations 1 1 1 2 Art and design workers 0 1 1 1 Entertainers and performers, sports and related workers 1 1 1 2 Media and communication workers 1 1 1 1 Media and communication equipment workers 0 0 0 0 Health diagnosing and treating practitioners 6 11 13 16 Health technologists and technicians 4 7 8 10 Other healthcare practitioners and technical occupations 0 0 0 0 Nursing, psychiatric, and home health aides 2 4 5 6 Occupational therapy and physical therapist assistants and aides 0 1 1 1 Other healthcare support occupations 3 5 6 7 Supervisors of protective service workers 0 0 0 0 Fire fighting and prevention workers 0 0 0 0 Law enforcement workers 0 1 1 1 Other protective service workers 1 2 3 3 Supervisors of food preparation and serving workers 1 2 2 2 Cooks and food preparation workers 2 5 6 6 Food and beverage serving workers 6 12 14 15 Other food preparation and serving related workers 1 2 3 3 Supervisors of building and grounds cleaning and maintenance workers 1 1 1 1 Building cleaning and pest control workers 5 9 10 11 Grounds maintenance workers 4 7 9 10 Supervisors of personal care and service workers 0 0 1 1 Animal care and service workers 0 1 1 1 Entertainment attendants and related workers 1 2 2 2 Funeral service workers 0 0 0 0 Personal appearance workers 2 4 4 5 Baggage porters, bellhops, and concierges; Tour and travel guides 0 0 0 0 Other personal care and service workers 4 7 9 10 Supervisors of sales workers 2 3 4 4 Retail sales workers 10 20 23 25 Sales representatives, services 2 3 3 3 Sales representatives, wholesale and manufacturing 1 2 2 2 Other sales and related workers 1 3 3 3 Supervisors of office and administrative support workers 1 3 3 3 Communications equipment operators 0 0 0 0 Financial clerks 3 6 7 7 Information and record clerks 6 10 11 12 Material recording, scheduling, dispatching, and distributing workers 2 4 4 5 Secretaries and administrative assistants 4 8 9 9 Other office and administrative support workers 3 7 7 8 Supervisors of farming, fishing, and forestry workers 0 0 0 0 Agricultural workers 0 0 0 0 Fishing and hunting workers 0 0 0 0 Forest, conservation, and logging workers 0 0 0 0

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Supervisors of construction and extraction workers 0 1 1 1 Construction trades workers 4 13 13 13 Helpers, construction trades 0 1 1 1 Other construction and related workers 0 1 0 0 Extraction workers -2 -3 -4 -4 Supervisors of installation, maintenance, and repair workers 0 1 1 1 Electrical and electronic equipment mechanics, installers, and repairers 0 1 1 1 Vehicle and mobile equipment mechanics, installers, and repairers 1 2 2 3 Other installation, maintenance, and repair occupations 2 5 6 6 Supervisors of production workers 0 0 0 0 Assemblers and fabricators 0 1 1 1 Food processing workers 0 1 1 1 Metal workers and plastic workers 0 0 0 0 Printing workers 0 0 0 0 Textile, apparel, and furnishings workers 0 1 1 1 Woodworkers 0 0 0 0 Plant and system operators 0 0 0 0 Other production occupations 1 1 1 1 Supervisors of transportation and material moving workers 0 0 0 1 Air transportation workers 0 -1 -1 -2 Motor vehicle operators 2 5 6 8 Rail transportation workers 0 0 0 0 Water transportation workers 0 0 0 0 Other transportation workers 0 1 1 1 Material moving workers 2 3 4 4 Military 0 0 0 0 TOTAL OF ALL OCCUPATIONS = 104 219 241 266

Albuquerque, New Mexico

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Pacific (PAC)

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Electrical Power Capacity (PAC level)

Baseline ($0/year) Alternative ($10/year) 200 200 Storage 180 180 Solar Wind

160 160 Biopower

Geothermal 140 140 Hydro

120 120 Nuclear 100 100 Oil-Gas-Steam Gas-CC-CCS 80 80 Gas-CT

Gas-CC Capacity (GW) Capacity 60 60 Coal-CCS 40 40 Coal-IGCC Coal-New

20 20 Cofiring 0 0 Coal-Old Scrubbed 2010 2020 2030 2040 2010 2020 2030 2040 Coal-Old Unscrubbed

Figure 6.41 – PAC is unique among the nine regions for its large share of hydroelectric capacity and lack of coal in the baseline. The important difference in the alternative includes adding more wind, solar, and geothermal power sooner than in the baseline.

Electrical Power Generation (PAC level)

Baseline ($0/year) Alternative ($10/year) 600 600 Solar

Wind

500 500 Biopower

Geothermal 400 400 Hydro Nuclear

Oil-Gas-Steam 300 300 Gas-CC-CCS Gas-CT

Gas-CC

200 200 Coal-CCS Generation (TWh) Generation Coal-IGCC 100 100 Coal-New Cofiring

Coal-Old Scrubbed

0 0 Coal-Old Unscrubbed 2010 2020 2030 2040 2010 2020 2030 2040

Figure 6.42 – Geothermal has the largest increase in generation during the alternative simulation, and PAC has a special case of its base-load coming from hydroelectric dams and geothermal plants instead of nuclear facilities or gas with carbon sequestration.

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Figure 6.43 – GRP by Industry (millions of 2012 dollars) 70 sector NAICS 2020 2025 2030 2035 Forestry and logging; Fishing, hunting, and trapping -$31 -$94 -$163 -$221 Agriculture and forestry support activities -$2 -$13 -$23 -$29 Oil and gas extraction -$507 -$812 -$1,055 -$1,155 Mining (except oil and gas) $161 -$114 -$277 -$330 Support activities for mining $8 $56 $73 $83 Utilities -$570 -$612 -$744 -$768 Construction $614 $1,632 $1,457 $1,438 Wood manufacturing $47 $80 $68 $59 Nonmetallic mineral manufacturing $58 $100 $93 $92 Primary metal manufacturing $3 -$40 -$76 -$82 Fabricated metal manufacturing $256 $118 $29 -$15 Machinery manufacturing -$31 $20 $13 -$22 Computer and electronic manufacturing $39 -$516 -$1,111 -$1,191 Electrical equipment and appliance manufacturing $21 -$37 -$107 -$161 Motor vehicles, bodies and trailers, and parts manufacturing $67 $127 $164 $198 Other transportation equipment manufacturing -$77 -$250 -$419 -$549 Furniture and related manufacturing $72 $95 $81 $60 Miscellaneous manufacturing $66 $14 -$47 -$66 Food manufacturing $196 $256 $234 $205 Beverage and tobacco manufacturing $91 $121 $113 $98 Textile mills; Textile mills $2 -$12 -$30 -$35 Apparel manufacturing; Leather and allied manufacturing -$8 -$49 -$69 -$73 Paper manufacturing $33 $32 $13 -$4 Printing and related support activities $50 $69 $68 $68 Petroleum and coals manufacturing -$603 -$1,222 -$2,030 -$3,030 Chemical manufacturing $389 $456 $295 $149 Plastics and rubber manufacturing $41 $26 -$25 -$69 Wholesale trade $1,540 $2,335 $2,525 $2,793 Retail trade $2,766 $4,700 $5,603 $6,546 Air transportation -$1,061 -$2,665 -$4,274 -$5,716 Rail transportation -$14 -$35 -$63 -$79 Water transportation -$7 -$21 -$37 -$52 Truck transportation $146 $220 $219 $227 Couriers and messengers $57 $70 $46 $24 Transit and ground passenger transportation $33 $48 $51 $52 Pipeline transportation -$42 -$68 -$80 -$81 Scenic and sightseeing transportation; Support activities for transportation -$208 -$527 -$891 -$1,281 Warehousing and storage $38 $46 $33 $25 Publishing industries, except Internet $474 $754 $850 $1,031 Motion picture and sound recording industries $775 $1,288 $1,689 $2,168 Internet publishing and broadcasting; ISPs, search portals, and data processing $227 $319 $312 $314 Broadcasting, except Internet $117 $176 $185 $200 Telecommunications $752 $1,184 $1,342 $1,485 Monetary authorities - central bank; Credit intermediation and related activities $1,864 $2,863 $3,190 $3,449 Securities, commodity contracts, investments $686 $994 $1,027 $1,048 Insurance carriers and related activities $566 $795 $788 $751 Real estate $3,835 $5,975 $6,300 $6,469 Rental and leasing services; Leasing of nonfinancial intangible assets -$73 -$485 -$1,039 -$1,499 Professional, scientific, and technical services $1,467 $1,937 $1,565 $1,329 Management of companies and enterprises $129 -$9 -$269 -$481 Administrative and support services $769 $1,130 $1,155 $1,207 Waste management and remediation services $88 $127 $125 $124 Educational services $268 $397 $425 $431 Ambulatory health care services $2,921 $4,652 $5,476 $6,213 Hospitals $623 $964 $1,078 $1,142 Nursing and residential care facilities $205 $315 $350 $370 Social assistance $189 $291 $330 $357 Performing arts and spectator sports $154 $235 $262 $297 Museums, historical sites, zoos, and parks $24 $39 $45 $49 Amusement, gambling, and recreation $217 $348 $400 $442 Accommodation $462 $729 $839 $935 Food services and drinking places $606 $912 $943 $931 Repair and maintenance $301 $452 $476 $493 Personal and laundry services $570 $907 $1,036 $1,143 Membership associations and organizations $175 $257 $271 $276 Private households $128 $216 $250 $279 State and local government $1,564 $1,994 $1,651 $1,422 TOTAL OF ALL SECTORS = $23,716 $33,290 $30,709 $29,483

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Figure 6.44 – Employment by Industry (thousands over baseline) 70 sector NAICS 2020 2025 2030 2035 Forestry and logging; Fishing, hunting, and trapping 0 0 -1 -1 Agriculture and forestry support activities 0 0 -1 -1 Oil and gas extraction -2 -3 -4 -4 Mining (except oil and gas) 0 -2 -3 -3 Support activities for mining 0 0 0 0 Utilities -1 -1 -1 -1 Construction 11 26 23 23 Wood manufacturing 1 1 1 1 Nonmetallic mineral manufacturing 0 1 1 1 Primary metal manufacturing 0 0 0 0 Fabricated metal manufacturing 2 1 1 0 Machinery manufacturing 0 0 0 0 Computer and electronic manufacturing 0 -1 -2 -2 Electrical equipment and appliance manufacturing 0 0 0 0 Motor vehicles, bodies and trailers, and parts manufacturing 0 1 1 1 Other transportation equipment manufacturing 0 -1 -1 -1 Furniture and related manufacturing 1 1 1 1 Miscellaneous manufacturing 0 0 0 0 Food manufacturing 2 2 2 2 Beverage and tobacco manufacturing 0 1 1 1 Textile mills; Textile mills 0 0 0 0 Apparel manufacturing; Leather and allied manufacturing 0 -1 -1 -1 Paper manufacturing 0 0 0 0 Printing and related support activities 1 1 1 1 Petroleum and coals manufacturing 0 0 0 0 Chemical manufacturing 1 1 1 0 Plastics and rubber manufacturing 0 0 0 0 Wholesale trade 10 13 13 13 Retail trade 43 65 69 72 Air transportation -4 -9 -12 -14 Rail transportation 0 0 0 0 Water transportation 0 0 0 1 Truck transportation 3 6 8 10 Couriers and messengers 1 2 2 3 Transit and ground passenger transportation 1 2 2 2 Pipeline transportation 0 0 0 0 Scenic and sightseeing transportation; Support activities for transportation -2 -4 -7 -9 Warehousing and storage 1 1 1 1 Publishing industries, except Internet 1 2 2 2 Motion picture and sound recording industries 3 4 4 5 Internet publishing and broadcasting; ISPs, search portals, and data processing 1 1 1 0 Broadcasting, except Internet 1 1 1 1 Telecommunications 2 3 3 2 Monetary authorities - central bank; Credit intermediation and related activities 7 9 9 9 Securities, commodity contracts, investments 9 12 11 11 Insurance carriers and related activities 4 5 5 5 Real estate 15 22 22 21 Rental and leasing services; Leasing of nonfinancial intangible assets 1 2 1 1 Professional, scientific, and technical services 15 20 17 16 Management of companies and enterprises 1 0 -1 -1 Administrative and support services 21 31 33 35 Waste management and remediation services 1 1 1 1 Educational services 7 11 12 13 Ambulatory health care services 36 58 68 77 Hospitals 8 12 13 14 Nursing and residential care facilities 5 8 9 9 Social assistance 7 11 13 14 Performing arts and spectator sports 4 5 6 6 Museums, historical sites, zoos, and parks 0 1 1 1 Amusement, gambling, and recreation 6 10 12 13 Accommodation 6 8 9 10 Food services and drinking places 18 26 26 26 Repair and maintenance 4 6 6 6 Personal and laundry services 11 17 18 19 Membership associations and organizations 5 8 8 8 Private households 15 24 25 26 State and local government 17 21 17 14 TOTAL OF ALL SECTORS = 300 442 447 460

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Figure 6.45 – Employment by Occupation (thousands over baseline) 95 occupation SOC 2020 2025 2030 2035 Top executives 4 6 5 5 Advertising, marketing, promotions, public relations, and sales managers 1 2 2 2 Operations specialties managers 3 3 3 3 Other management occupations 4 6 6 6 Business operations specialists 7 9 9 9 Financial specialists 7 10 9 9 Computer occupations 5 6 5 5 Mathematical science occupations 0 0 0 0 Architects, surveyors, and cartographers 0 0 0 0 Engineers 1 1 0 0 Drafters, engineering technicians, and mapping technicians 0 1 0 0 Life scientists 0 0 0 0 Physical scientists 0 0 0 0 Social scientists and related workers 0 1 1 1 Life, physical, and social science technicians 0 0 0 0 Counselors and Social workers 2 4 4 4 Miscellaneous community and social service specialists 1 2 2 2 Religious workers 0 0 0 0 Lawyers, judges, and related workers 1 1 1 1 Legal support workers 1 1 1 1 Postsecondary teachers 3 4 4 4 Preschool, primary, secondary, and special education school teachers 5 7 6 6 Other teachers and instructors 1 2 2 2 Librarians, curators, and archivists 0 0 0 0 Other education, training, and library occupations 2 3 3 3 Art and design workers 1 2 2 2 Entertainers and performers, sports and related workers 2 3 3 3 Media and communication workers 2 3 3 3 Media and communication equipment workers 1 1 1 1 Health diagnosing and treating practitioners 14 22 25 28 Health technologists and technicians 9 14 16 17 Other healthcare practitioners and technical occupations 0 0 0 0 Nursing, psychiatric, and home health aides 5 7 8 9 Occupational therapy and physical therapist assistants and aides 1 1 2 2 Other healthcare support occupations 7 12 14 15 Supervisors of protective service workers 0 0 0 0 Fire fighting and prevention workers 0 0 0 0 Law enforcement workers 1 1 1 1 Other protective service workers 3 4 4 5 Supervisors of food preparation and serving workers 2 3 3 3 Cooks and food preparation workers 6 8 8 8 Food and beverage serving workers 13 19 20 19 Other food preparation and serving related workers 3 4 4 4 Supervisors of building and grounds cleaning and maintenance workers 1 2 2 2 Building cleaning and pest control workers 13 20 21 22 Grounds maintenance workers 8 13 14 15 Supervisors of personal care and service workers 1 1 1 1 Animal care and service workers 1 2 2 2 Entertainment attendants and related workers 2 3 3 4 Funeral service workers 0 0 0 0 Personal appearance workers 6 9 10 10 Baggage porters, bellhops, and concierges; Tour and travel guides 0 0 0 0 Other personal care and service workers 12 19 21 22 Supervisors of sales workers 4 6 6 7 Retail sales workers 25 37 40 41 Sales representatives, services 5 6 6 6 Sales representatives, wholesale and manufacturing 3 4 4 4 Other sales and related workers 3 5 5 5 Supervisors of office and administrative support workers 4 5 5 5 Communications equipment operators 0 0 0 0 Financial clerks 9 13 13 13 Information and record clerks 13 19 19 19 Material recording, scheduling, dispatching, and distributing workers 6 8 7 7 Secretaries and administrative assistants 11 16 17 17 Other office and administrative support workers 9 13 13 14 Supervisors of farming, fishing, and forestry workers 0 0 0 0 Agricultural workers 0 0 0 0 Fishing and hunting workers 0 0 0 0 Forest, conservation, and logging workers 0 0 0 0

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Supervisors of construction and extraction workers 1 2 1 1 Construction trades workers 7 15 13 13 Helpers, construction trades 1 1 1 1 Other construction and related workers 0 1 1 1 Extraction workers 0 -1 -1 -1 Supervisors of installation, maintenance, and repair workers 1 1 1 1 Electrical and electronic equipment mechanics, installers, and repairers 1 1 1 1 Vehicle and mobile equipment mechanics, installers, and repairers 3 4 4 4 Other installation, maintenance, and repair occupations 6 9 9 9 Supervisors of production workers 1 1 0 0 Assemblers and fabricators 1 1 1 1 Food processing workers 1 2 2 2 Metal workers and plastic workers 1 1 0 0 Printing workers 0 0 0 0 Textile, apparel, and furnishings workers 1 1 1 1 Woodworkers 1 1 1 1 Plant and system operators 0 0 0 0 Other production occupations 3 4 3 3 Supervisors of transportation and material moving workers 1 1 1 1 Air transportation workers -2 -3 -5 -6 Motor vehicle operators 7 10 12 14 Rail transportation workers 0 0 0 0 Water transportation workers 0 0 0 0 Other transportation workers 1 1 1 1 Material moving workers 7 9 9 9 Military 0 0 0 0 TOTAL OF ALL OCCUPATIONS = 297 436 442 456

San Francisco, California

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Regional Economic Models, Inc. (REMI) REMI is an economic and policy analysis firm specializing in services related to modeling. REMI’s headquarters is in Amherst, Massachusetts, although its research and consulting practice reside in Washington, DC. It initially began as a research project at the University of Massachusetts-Amherst by a professor named Dr. George I. Treyz. During the late 1970s, Dr. Treyz developed an economic model to study the potential impact of expanding the “MassPike” (I-90 through central Massachusetts from Boston to Worcester, Springfield, and connecting to the New York State Thruway in Albany to head out to Syracuse, Rochester, and eventually Buffalo). He later generalized the methodology to all counties in the United States and incorporated the firm in 1980. The current entity provides data, software, technical support, and issue-oriented expertise and consulting across the United States and the globe. There are users of the REMI model, its data, or studies in every state (and the District of Columbia) and foreign nations in North America, Europe, Asia, and the Middle East.121 Typical REMI clients include state or local governments, federal agencies, consulting firms, academic institutions, research groups, non-profits, labor unions, and trade associations.

Figure 7.1 – This map shows the REMI client base in the United States. Each point represents a current model subscriber in either the private sector or a level of government. The different colors are for different model types—teal is for the “standard” PI+ model, green is Tax-PI (an expansion for state level budget analysis), gold is for TranSight (and transportation), purple is Metro-PI (on subcounty planning), and red is the eREMI online forecasting tool.

Some of the notable REMI clients in the United States include the American Gas Association (AGA), the National Education Association (NEA), the National Federation of Independent

121 For the full list of clients, please see,

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Business (NFIB), the University of Michigan-Ann Arbor, Sandia National Laboratory (SNL), the Texas Comptroller of Public Accounts (CPA), and the California Department of Finance (CalFinance). Others include the Southern California Association of Governments (SCAG), the Atlanta Regional Commission (ARC), the city and county of San Francisco, California, the New York City Independent Budget Office (IBO), and the consulting firms Cambridge Systematics, CDM Smith, Booz Allen Hamilton, EY, and PWC. Clients outside of the United States include the provincial government of Alberta and the Korea Energy Economics Institute (KEEI). Prominent consulting studies by REMI in the past year include the state-by-state impact of immigration reform options, and featured the results.122 Another topic included the Medicaid expansion option for state governors and legislatures.123 This study is part of REMI’s record on analyzing the state level and federal level implications of changes in energy policies such as carbon taxes or renewable generation standards.

Synapse Energy Economics Synapse Energy Economics, Inc. is a research and consulting firm specializing in energy, economic, and environmental topics. Since inception in 1996, Synapse has become a leader in providing rigorous analysis of the electrical power sector for public interest and governmental clients. Synapse’s staff of thirty includes experts in energy and , resource planning, electricity dispatch and economic modeling, energy efficiency, renewable energy, transmission and distribution, rate design, cost allocation, risk management, and benefit-cost analysis. Other areas include rate design and cost allocation, climate science, and both regulated and competitive electricity and natural gas markets. Several senior staff members have more than thirty years of experience in the economics and regulation of the electricity and natural gas sectors. Many of them have held positions as regulators, economists, and as utility commissioners or ISO staff.

Synapse’s services include economic and technical analyses, regulatory support, research and report writing, policy analysis and development, representation in stakeholder committees, facilitation, development of analytical tools, and expert witnessing. Synapse commits to the idea that robust, transparent analyses can help to inform better policy and planning decisions. Many of Synapse’s clients seek expertise to help them participate effectively in planning, regulation, and litigation cases, as well as other forums requiring public involvement. Synapse’s clients include public utility commissions in American states and in Canada, offices of consumer advocates, attorney generals, environmental organizations, foundations, regional associations, public interest groups, and federal agencies such as the U.S. Environmental Protection Agency and the U.S. Department of Justice. International clients include projects for the United Nations Framework Convention on Climate Change (UNFCCC), the Global Environmental Facility, the International Joint Commission, and several others.124

122 Please see Sara Murray, “Immigration Overhaul Would Benefit Big States the Most: California, Texas, Florida Would Get Large Economic Boost, Study Says,” Wall Street Journal (WSJ), July 16, 2013, 123 Please see, 124 For the full list of clients, please see,

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Regional Economic Models, Inc. (REMI)

1776 I St. NW Suite 750 Washington, DC 20006 (202) 716-1397

Synapse Energy Economics, Inc.

485 Massachusetts Ave. Suite 2 Cambridge, MA 02139 (617) 661-3248

Scott Nystrom125 received B.A. in history, B.S. in economics, and M.A. in economic history from Iowa State University (ISU) in Ames, Iowa. He has worked at REMI since 2011, and he is the main point of contact in the Washington, DC office for training, technical support, and economic consulting. Mr. Nystrom works on a daily basis with clients across the United States and the rest of the world in state governments, federal agencies, provincial authorities, regional councils, consulting firms, academic institutions, and non-profit research groups. His major projects have included economic impact analyses of the federal “fiscal cliff” and sequestration, the TransCanada Keystone XL pipeline, the $500 billion long-range transportation plan of the Southern California Association of Governments (SCAG), the potential Medicaid expansion in North Carolina, and carbon tax studies in Massachusetts, Washington, and California. His other research and responsibilities include integrating regional models with PI+, modeling the impact of changing commuting patterns and intermodal transportation, and business development and travel throughout North America and Europe.

Patrick Luckow126 performs modeling analyses of power systems using industry-standard models to evaluate long-term energy plans and the environmental and economic impacts of policy initiatives. His recent work at Synapse includes modeling the market price impacts of adding high-level wind resources in PJM, modeling the New England electric system to calculate avoided costs associated with energy efficiency, modeling the cost and emissions impacts of transmission and renewable energy additions. His previous analyses with the ReEDS model include evaluating several clean energy futures for the Energy Foundation. Prior to joining Synapse, he worked as a scientist at the Joint Global Change Research Institute (JGCRI) in College Park, Maryland and evaluated the long-term implications of potential climate policies at the national and international level using a variety of energy and electricity models. He holds a B.S. in mechanical engineering from Northwestern University in Evanston, Illinois and a M.S. in mechanical engineering from the University of Maryland-College Park.

125 126

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Notes

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A Conservative Answer to Climate Change Enacting a carbon tax would free up private firms to find the most efficient ways to cut emissions.

By

GEORGE P. SHULTZ and

JAMES A. BAKER III

FEB 7, 2017

Thirty years ago, as the atmosphere’s protective ozone layer was dwindling at alarming rates, we were serving proudly under President Ronald Reagan. We remember his leading role in negotiating the Montreal Protocol, which continues to protect and restore the delicate ozone layer. Today the world faces a similar challenge: the threat of climate change.

Just as in the 1980s, there is mounting evidence of problems with the atmosphere that are growing too compelling to ignore. And, once again, there is uncertainty about what lies ahead. The extent to which climate change is due to man-made causes can be questioned. But the risks associated with future warming are so severe that they should be hedged.

The responsible and conservative response should be to take out an insurance policy. Doing so need not rely on heavy-handed, growth-inhibiting government regulations. Instead, a climate solution should be based on a sound economic analysis that embodies the conservative principles of free markets and limited government.

We suggest a solution that rests on four pillars. First, creating a gradually increasing carbon tax. Second, returning the tax proceeds to the American people in the form of dividends. Third, establishing border carbon adjustments that protect American competitiveness and encourage other countries to follow suit. And fourth, rolling back government regulations once such a system is in place.

PHOTO: DAVID GOTHARD The first pillar, a carbon tax, is the most cost-effective way to reduce emissions. Unlike the current cumbersome regulatory approach, a levy on emissions would free companies to find the most efficient way to reduce their carbon footprint. A sensibly priced, gradually rising tax would send a powerful market signal to businesses that want certainty when planning for the future.

A “carbon dividend” payment, the second pillar, would have tax proceeds distributed to the American people on a quarterly basis. This way, the revenue-neutral tax would benefit working families rather than bloat government spending. A $40-per-ton carbon tax would provide a family of four with roughly $2,000 in carbon dividends in the first year, an amount that could grow over time as the carbon tax rate increased.

A carbon dividends policy could spur larger reductions in greenhouse-gas emissions than all of President Obama’s climate policies. At the same time, our plan would strengthen the economy, help working-class Americans, and promote national security, all while reducing regulations and shrinking the size of government.

The third pillar is a border adjustment for carbon content. When American companies export to countries without comparable carbon pricing systems, they would receive rebates on the carbon taxes they have paid. Imports from such countries, meanwhile, would face fees on the carbon content of their products. Proceeds from such fees would also be returned to the American people through carbon dividends. Pioneering such a system would put America in the driver’s seat of global climate policy. It would also promote American competitiveness by penalizing countries whose lack of carbon-reduction policies would otherwise give them an unfair trade advantage.

The eventual elimination of regulations no longer necessary after the enactment of a carbon tax would constitute the final pillar. Almost all of the Environmental Protection Agency’s regulatory authority over carbon emissions could be eliminated, including an outright repeal of President Obama’s Clean Power Plan. Robust carbon taxes would also justify ending federal and state tort liability for emitters.

With these principles in mind, on Wednesday the Climate Leadership Council is unveiling “The Conservative Case for Carbon Dividends.” The report was co-authored by conservative thinkers Martin Feldstein, Jr., Gregory Mankiw,Ted Halstead,Tom Stephenson and Rob Walton.

This carbon dividends program would help steer the U.S. toward a path of more durable economic growth by encouraging technological innovation and large-scale substitution of existing energy sources. It would also provide much-needed regulatory relief to U.S. industries. Companies, especially those in the energy sector, finally would have the predictability they now lack, removing one of the most serious impediments to capital investment.

Perhaps most important, the carbon-dividends plan speaks to the increasing frustration and economic insecurity experienced by many working-class Americans. The plan would elevate the fortunes of the nation’s less-advantaged while strengthening the economy. A Treasury Department report published last month predicts that carbon dividends would mean income gains for about 70% of Americans.

This plan will also be good for the long-term prospects of the Republican Party. About two- thirds of Americans worry a “great deal” or “fair amount” about climate change, according to a 2016 Gallup survey. Polls often show concern about climate change is higher among younger voters, and among Asians and Hispanics, the fastest-growing demographic groups. A carbon- dividends plan provides an opportunity to appeal to all three demographics.

Controlling the White House and Congress means that Republicans bear the responsibility of exercising wise leadership on the defining challenges of our era. Climate change is one of these issues. It is time for the Grand Old Party to once again lead the way.

Mr. Shultz was secretary of state (1982-89) and Treasury secretary (1972-74). Mr. Baker was secretary of state (1989-92) and Treasury secretary (1985-88).

From: George Wilkes [email protected] Subject: Carbon Fee and Dividend Policy Date: January 29, 2017 at 9:56 AM To: Bill Hansen [email protected]

This is one of the more cogent explanations of CFD.

George

http://citizensclimatelobby.org/carbon-fee-and-dividend/

Carbon Fee and Dividend Policy

Below you’ll find the full-text version of Citizens’ Climate Lobby’s preferred climate solution, known as Carbon Fee and Dividend. A national, revenue-neutral carbon fee-and-dividend system (CF&D) would place a predictable, steadily rising price on carbon, with all fees collected minus administrative costs returned to households as a monthly energy dividend.

In just 20 years, studies show, such a system could reduce carbon emissions to 50% of 1990 levels while adding 2.8 million jobs to the American economy.

Download the full-text version or see answers to frequently asked questions.

Findings:

1. Causation: Whereas the weight of scientific evidence indicates that greenhouse gas emissions from human activities including the burning of fossil fuels and other sources are causing rising global temperatures,

2. Mitigation (Return to 350 ppm or below): Whereas the weight of scientific evidence also indicates that a return from the current concentration of more than 400 parts per million (“ppm”) of carbon dioxide (“CO2”) in the atmosphere to 350 ppm CO2 or less is necessary to slow or stop the rise in global temperatures,

3. Endangerment: Whereas further increases in global temperatures pose imminent and substantial dangers to human health, the natural environment, the economy, national security, and an unacceptable risk of catastrophic impacts to human civilization,

4. Co-Benefits: Whereas the measures proposed in this legislation will benefit the economy, human health, the environment, and national security, even without consideration of global human health, the environment, and national security, even without consideration of global temperatures, as a result of correcting market distortions, reductions in non-greenhouse-gas pollutants, reducing the outflow of dollars to oil-producing countries and improvements in the energy security of the United States,

5. Benefits of Carbon Fees: Whereas phased-in carbon fees on greenhouse gas emissions (1) are the most efficient, transparent, and enforceable mechanism to drive an effective and fair transition to a domestic-energy economy, (2) will stimulate investment in alternative-energy technologies, and (3) give all businesses powerful incentives to increase their energy-efficiency and reduce their carbon footprints in order to remain competitive,

6. Equal Monthly Per-Person Dividends: Whereas equal monthly dividends (or “rebates”) from carbon fees paid to every American household can help ensure that families and individuals can afford the energy they need during the transition to a greenhouse gas-free economy and the dividends will stimulate the economy,

Therefore the following legislation is hereby enacted:

1. Collection of Carbon Fees/Carbon Fee Trust Fund: Upon enactment, impose a carbon fee on all fossil fuels and other greenhouse gases at the point where they first enter the economy. The fee shall be collected by the Treasury Department. The fee on that date shall be $15 per ton of CO2 equivalent emissions and result in equal charges for each ton of CO2 equivalent emissions potential in each type of fuel or greenhouse gas. The Department of Energy shall propose and promulgate regulations setting forth CO2 equivalent fees for other greenhouse gases including at a minimum methane, nitrous oxide, sulfur hexafluoride, hydrofluorocarbons (HFCs), perfluorocarbons, and nitrogen trifluoride. The Treasury shall also collect the fees imposed upon the other greenhouse gases. All fees are to be placed in the Carbon Fees Trust Fund and be rebated to American households as outlined below.

2. Emissions Reduction Targets: To align US emissions with the physical constraints identified by the Intergovernmental Panel on Climate Change (IPCC) to avoid irreversible climate change, the yearly increase in carbon fees including other greenhouse gases, shall be at least $10 per ton of CO2 equivalent each year. Annually, the Department of Energy shall determine whether an increase larger than $10 per ton per year is needed to achieve program goals. Yearly price increases of at least $10 per year shall continue until total U.S. CO2- equivalent emissions have been reduced to 10% of U.S. CO2-equivalent emissions in 1990. 3. Equal Per-Person Monthly Dividend Payments: Equal monthly per-person dividend payments shall be made to all American households (½ payment per child under 18 years old, with a limit of 2 children per family) each month. The total value of all monthly dividend payments shall represent 100% of the net carbon fees collected per month.

4. Border Adjustments: In order to ensure there is no domestic or international incentive to relocate production of goods or services to regimes more permissive of greenhouse gas emissions, and thus encourage lower global emissions, Carbon-Fee-Equivalent Tariffs shall be charged for goods entering the U.S. from countries without comparable Carbon Fees/Carbon Pricing. Carbon-Fee-Equivalent Rebates shall be used to reduce the price of exports to such countries. The State Department will determine rebate amounts and exemptions if any. !

What is Carbon Fee and Dividend? Carbon Fee and Dividend is the policy proposal created by Citizens’ Climate Lobby (CCL) to put a federal price on carbon-based fuels so that their consumer cost reflects their true costs to society. It’s the policy that both climate scientists and economists say is the best first-step to reduce the likelihood of catastrophic climate change from global warming. Why Carbon Fee and Dividend? Currently, the price of fossil fuels does not reflect their true costs—including their impact on global climate. Correcting this market failure will require that their price account for the true social costs.

As long as fossil fuels remain artificially inexpensive, their use will rise. Correcting this market failure requires a federal price on carbon that accounts for their true costs. What Will Carbon Fee and Dividend Do? Carbon Fee and Dividend will do four things:

1. Add the social cost of carbon-based fossil fuels to the price consumers pay. 2. Cut emissions enough to stay below the 2C threshold for “dangerous” warming. 3. Grow jobs and GDP without growing government one bit. 4. Recruit global participation.

citizensclimatelobby.org

Cook County and Grand Marais Energy Conservation and Renewable Energy Plan

The Energy Summits were held in Grand Marais and Tofte in May 2011. They consisted of a short (approximately 15 minute) presentation of the Energy Planning process followed by a 2 hour question and answer period. A total of 19 people attended the Summits.

The analysis of the survey results is presented in detail in Appendix B. A few of the major findings are included here in the body of the report.

The survey indicated that the community is very concerned about energy; especially energy costs and environmental impacts. When polled on national issues of most concern, energy ranked first with 70% of the respondents selecting very concerned (Figure 1). Virtually all respondents were concerned or very concerned with the cost of energy while more than 90% were concerned or very concerned about environmental issues (Figure 2).

In the graphs that follow the legends represent the following:

Legend Title Grouping OL ‐ All On‐line survey; all responses OL – Less Ed On‐line survey; < 4 years post‐secondary education OL – More Ed On‐line survey; 4 or more years post‐secondary education OL – Lower Inc On‐line survey; <$50,000 annual income OL – Higher Inc On‐line survey; >$50,000 annual income Telephone Random telephone survey

Government leadership toward better energy utilization was viewed favorably. Approximately 80% of the respondents believe that government should be taking steps to address energy planning (Figure 3) and a majority support increased regulatory standards for increased energy efficiency (Figure 4).

Respondents overwhelmingly viewed movement toward use of renewable energy as very favorable (Figure 5) and indicated a willingness to pay a premium of about 6% for renewable energy (Figure 6).

Cost was seen as a big driver in making energy efficiency improvements. Educational programs and incentives toward improving energy efficiency were viewed favorably.

The responses of the different groups were similar with a few relatively minor exceptions. The telephone respondents and those with less formal education were more concerned with national security and dependence on foreign energy sources than with environmental issues and were less supportive of using government action to resolve energy issues. They were willing to pay a smaller premium for renewable energy than those with more formal education. Those with lower income were also willing to pay a smaller premium for renewable energy.

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Cook County and Grand Marais Energy Conservation and Renewable Energy Plan

Figure 1: Please choose whether you are not at all concerned, somewhat concerned or very concerned about each of the following issues

90 Not Concerned 80 Somewhat concerned Very Concerned 70

60

50

40

30

Fraction of respondentsof Fraction (%) 20

10

0 Energy Economy Education Climate change Health Security Category

Figure 2: If you are concerned about energy issues, which of the following issues concerns you the most?

90 Not Concerned 1 - Effect on the environment 80 Somewhat concerned 2 - Cost Very Concerned 3 - Dependency of fossil fuel 4 - Future availability 70 5 - Dependance on foreign sources 6 - Local Source 60 7 - Energy job losses

50

40

30

Fraction of respondents (%) respondents of Fraction 20

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0 1234567 Category

Page 9

Impact of CCL’s proposed carbon fee and dividend policy:

A high-resolution analysis of the financial effect on U.S. households

Kevin Ummel †

Research Scholar, Energy Program International Institute for Applied Systems Analysis (IIASA)

Prepared for Citizens’ Climate Lobby (CCL)

February, 2016

Working Paper v1.3

I am grateful for comments, advice, and data provided by Kevin Perese, Chad Stone, Robert Corea, Scott Curtin, Art Diem, Eric Wilson, Travis Johnson, James Crandall, Michael Mazerov, Danny Richter, Jerry Hinkle, and Tony Sirna. All remaining errors and omissions are mine.

† The analysis and opinions expressed here are those of the author alone and do not reflect the positions of CCL, IIASA, or any other organization. This document is released as a working paper subject to revision and improvement. 1 Executive summary

This study simulates a “carbon fee and dividend” policy similar to that proposed by the Citizens’ 1 Climate Lobby (CCL). The policy consists of a $15 per ton of CO2 “fee” (carbon tax) applied to domestic fossil fuel production and imports. Exports receive full tax rebates to maintain competitiveness of U.S. businesses. All remaining revenue is distributed to households as a taxable “dividend” (rebate) on a modified per-capita basis.

Assuming that firms pass the entire carbon fee on to consumers in the form of higher prices and there is no change in employment, technologies, or consumer behavior, the net financial effect of the policy for a given household is the difference between higher cost of goods and services and additional disposable income from the dividend.

Given these assumptions, the policy confers a net financial benefit on 54% of households nationwide (59% of individuals). The distributional effects are highly progressive. Ninety percent of households living below the Federal Poverty Level are benefited by the policy. The average net benefit in this group is $342 per household, equivalent to nearly 3% of pre-tax income. Overall, the primary distributional effect is to shift purchasing power from the top quintile to the bottom two quintiles of the income distribution (see figure on following page).

About two-thirds of younger (age 18-35) and older (age 80 and above) households are benefited, compared to 45% of households age 50 to 65. Over three-quarters of Latino households are benefited, compared to less than one-half of White households. The large household sample used here (5.8 million households) allows results to be generated for each of 30,000+ zip codes, revealing both regional and local spatial patterns (see figure on following page).

Differential impacts across space and household type highlight the ways in which “geo- demographic” factors combine with policy design to affect distributional outcomes. It is possible that a different dividend allotment formula with respect to household size and age, for example, could generate net positive benefits for a larger portion of the population.

This study introduces a number of methodological advances relevant to both carbon footprinting and carbon tax analysis. These include adjustments for expenditure under-reporting and variation in prices paid for goods and services across households, as well as improvements to input-output modeling of carbon tax price impacts. Overall, these enhancements suggest that rich households may be less exposed to carbon pricing than previously thought.

1 https://citizensclimatelobby.org/carbon-fee-and-dividend/

i Overall net financial benefit, by income quintile

Percent of households benefited by policy, by zip code

ii 2 Table of contents

1 Executive summary i 2 Table of contents iii 3 List of figures iv 4 Introduction 1 5 Estimation of household carbon footprints 3 5.1 Simulation and adjustment of household expenditures 4 5.2 Input-output modeling of national CIE 6 5.3 Modeling spatial variation in prices 9 5.4 Adjusting CIE for Manhattan and Gucci effects 13 5.5 Calculation of fuel-specific CIE 15 6 Simulation of carbon fee and dividend policy 17 6.1 Sources of gross revenue 17 6.2 Dispersal and taxation of dividend 19 6.3 Impact on government budget 20 7 Results 21 7.1 Costs and benefits across the income distribution 21 7.2 Spatial variation in net benefit 24 7.3 Net benefit across demographic groups 25 8 Conclusion 29 9 References 31 10 Additional graphics 33

iii 3 List of figures

Figure 1 - Gasoline price index (2012) 11 Figure 2 - Fruits and vegetables price index (2012) 12 Figure 3 - Services price index (2012) 12 Figure 4 - Estimated Gucci effect 14 Figure 5 - Carbon intensity of electricity supply (2012) 16 Figure 6 - Residential electricity price (2012) 16 Figure 7 - Assumed relationship between household income and marginal tax rate 20 Figure 8 - Percent of households benefited, by income quintile 22 Figure 9 - Total financial cost and benefit, by income decile 23 Figure 10 - Overall net financial benefit, by income quintile 24 Figure 11 - Percent of households benefited, by zip code 25 Figure 12 - Percent of households benefited, by age group 26 Figure 13 - Percent of households benefited, by household type 27 Figure 14 - Percent of households benefited, by race 28 Figure 15 - Typical per-person carbon footprint, by zip code 33 Figure 16 - Distribution of net financial benefit, by income quintile 34 Figure 17 - Distribution of net financial benefit, by age group 34 Figure 18 - Distribution of net financial benefit, by household type 35 Figure 19 - Distribution of net financial benefit, by race 35

iv 4 Introduction

Governments often seek to discourage harmful behavior by making such activity costlier. Second-hand smoke causes harm to innocent bystanders, prompting federal, state, and local politicians to impose a tax on cigarettes. The tax increases the price of cigarettes – discouraging consumption and improving public health – while providing a source of revenue.

Unmitigated burning of coal, oil, and gas causes harm via local air pollution and global climate change. A “carbon fee” – a tax on fossil fuels – is analogous to a cigarette tax, discouraging the use of goods, services, and technologies that rely on fossil fuels and encouraging clean alternatives.2

A carbon fee increases the price of carbon-intensive products. This “price signal” is key to the policy’s efficacy, as it incentivizes conservation and low-carbon choices among households and businesses. But the prospect of American families – especially low-income and elderly – facing higher costs is a central concern of carbon fee skeptics on both ends of the political spectrum.

Of course, a carbon fee also generates revenue that can be used to make households and/or businesses better off. Conservative economists have long argued that revenue from “environmental taxes” should be used to reduce other taxes – like income, capital, and corporate taxes – that hinder economic activity (Tullock 1967). Others argue that the revenue should be returned directly to households to help offset higher prices.

These differences reflect an inherent tradeoff between efficiency and equity when deciding how to “recycle” carbon fee revenue back into the economy. In general, reduction of capital and corporate taxes maximizes economy-wide efficiency (i.e. GDP growth), while the least-efficient recycling option is to return revenue directly to households. But the consequences for equity are reversed: reducing taxes on business disproportionately benefit the rich, while a rebate to consumers is more likely to benefit low-income households. Reducing taxes on labor generates effects somewhere in-between (Williams et al. 2014a).

While conceptually simple, carbon pricing can induce multiple and complex impacts on U.S. households. A reduction in economic efficiency might suppress employment and workers’ wages in some industries more than others (Ho, Morgenstern, and Shih 2008). Improved local air quality or lower long-term climate risk might benefit households in particular places (Jerrett et al. 2005). Revenue returned to households through rebates or lower taxes might benefit certain demographic groups or regions of the country, depending on the policy design (Metcalf 2007).

This study simulates a “carbon fee and dividend” policy similar to that proposed by the Citizens’ 3 Climate Lobby (CCL). The policy consists of a $15 per ton of CO2 “fee” (carbon tax) applied to domestic fossil fuel production and imports. Exports receive full tax rebates to maintain competitiveness of U.S. businesses. All remaining revenue is distributed to households on a

2 Readers are directed to Metcalf and Weisbach (2009), Marron et al. (2015), and Kennedy et al. (2015) for comprehensive reviews of the implementation and administrative details of such a policy. 3 https://citizensclimatelobby.org/carbon-fee-and-dividend/

1 modified per-capita basis as a taxable “dividend” (rebate). Specifically, every adult receives a full dividend “share” and each child (up to two per household) receives a half share.

Importantly, this analysis is “static” and does not consider “dynamic” effects of a carbon tax on economic growth, employment, wages, trade, production processes, or consumption patterns over time.4 Nor does it consider local or global environmental benefits. Instead, I calculate the short-term financial effect on families, assuming that the policy is implemented “overnight”, firms pass the entire carbon fee on to consumers in the form of higher prices, and there is no change in behavior, technologies, or emissions.

Under these assumptions, the net effect of the policy for a given household is the difference between additional costs due to higher prices and additional disposable income due to the dividend. The direct cost (tax burden) of the policy is related to a household’s “carbon footprint” – the amount of CO2 emitted as a result of consumption. This includes emissions associated with direct consumption of energy (e.g. electricity, natural gas, gasoline, etc.) as well as indirect CO2 that is emitted during the production of other goods and services (e.g. food, electronics, a visit to the doctor, etc.).

This basic technique is similar to those employed in prior research, including Metcalf (1999), Hassett, Mathur, and Metcalf (2007), Metcalf (2007), Burtraw, Sweeney, and Walls (2009), Hassett, Mathur, and Metcalf (2011), and Mathur and Morris (2014). This study differs in the level of socioeconomic, demographic, and spatial detail it provides. Household-level impacts can be assessed across almost any socioeconomic or demographic dimension, down to the level of individual zip codes. I also introduce a number of methodological improvements for estimating a household’s carbon footprint and, therefore, its tax burden due to higher consumer prices.

Section 5 describes how I estimate carbon footprints for each of 5.8 million households in a representative national sample over 2008-2012. This includes techniques to adjust for known under-reporting in household expenditure surveys and variation in prices paid for goods and services across households, as well as improvements to input-output modeling of carbon tax price impacts.

Section 6 explains how this information is used to simulate the specific carbon fee and dividend policy outlined above and determine the net financial gain or loss of each household. Section 7 presents results across the income distribution, space, and demographic groups. Section 8 concludes with a discussion of caveats, uncertainties, and policy design options.

4 Addressing dynamic effects requires a computable general equilibrium (CGE) model of the economy. Examples include, among others, Rausch and Reilly (2012) and Williams et al. (2014a; 2014b).

2 5 Estimation of household carbon footprints

I use an expenditure-based approach to estimate a household’s carbon footprint. This requires two pieces of information: 1) total expenditure for each kind of good or service; and 2) an estimate of the CO2 emitted per dollar spent on those same goods and services. I refer to the latter as the “carbon intensity of expenditure” – denoted by CIE in subsequent formulae – and it has units of kgCO2 per dollar.

A household’s carbon footprint is simply expenditure multiplied by CIE, summed across i categories of goods and services:

= ( ) ( 1 )

Household-level expenditure𝐻𝐻𝐻𝐻𝐻𝐻𝐻𝐻𝐻𝐻ℎ𝑜𝑜 𝑜𝑜𝑜𝑜by𝐶𝐶𝐶𝐶 category2 𝑓𝑓𝑓𝑓𝑓𝑓𝑓𝑓𝑓𝑓𝑓𝑓𝑓𝑓𝑓𝑓𝑓𝑓 is available∑𝑖𝑖 from𝐸𝐸𝑥𝑥𝑥𝑥𝑥𝑥𝑥𝑥𝑥𝑥𝑥𝑥𝑥𝑥𝑥𝑥𝑥𝑥𝑥𝑥 the Bureau𝑖𝑖 ∗ of𝐶𝐶𝐶𝐶 Labor𝐶𝐶𝑖𝑖 Statistics (BLS) Consumer Expenditure Survey (CEX). This ongoing survey uses interviews and diaries to continually collect expenditure, income, housing, and demographic data for a representative sample of American households. It is the primary source of information on how expenditure patterns vary across types of goods and services, space, and household characteristics.

However, household expenditure totals in the CEX are consistently lower than those in the Personal Consumption Expenditures (PCE) component of the Bureau of Economic Analysis (BEA) national accounts (National Research Council 2013).5 The latter provides aggregate household expenditure based on what businesses report to have sold, whereas the CEX provides what households report to have purchased.

When expenditure is summed across categories with comparable definitions, CEX totals are typically only 75% of PCE – and reporting rates vary widely across different kinds of goods and services. Discrepancies between expenditure surveys and national accounts are not uncommon. While there is no theoretical preference for one over the other, there are good practical reasons to prefer PCE as the accurate measure in rich countries (Deaton 2005).

This matters greatly for carbon footprinting, because the CIE term in Eq. 1 is calculated using data and techniques that assume national accounts provide the correct measure of expenditure and investment (see Section 5.2). Consequently, addressing the “under-reporting problem” is important for accurate analysis of carbon tax incidence.

Estimation of CIE also faces a number of methodological challenges. The standard approach (and the approach used here) relies on “input-output” tables from the BEA that detail monetary flows of commodities to and from industries (Leontief 1953). These tables are used to estimate CIE for individual commodities.6 The advantage of “I-O modeling” is that a single analytical

5 It is also likely that the CEX (like many surveys) underrepresents households at the upper end of the income distribution (Sabelhaus et al. 2013). 6 I believe one of the earliest extensions of I-O modeling to the energy context – from which an extension to emissions can then be made – is Herendeen (1973). Kok, Benders, and Moll (2006) provide an excellent overview of methodological issues in this area.

3 framework is used to measure all of the inputs (and, therefore, CO2 emissions) required to produce a wide range of goods and services.

However, a national I-O model can only provide national average CIE for each expenditure category. In reality, we know that CIE actually varies across households, and a primary reason for this is that prices vary across households.

Consider a household in Manhattan (New York City) that spends $2.00 for a 2-liter bottle of Coca-Cola. A household in Tulsa, Oklahoma spends only $1.33 for the same product. It is reasonable to assume that the real-world carbon footprints of each purchase are not significantly different. But using identical CIE for both transactions suggests that the household in Manhattan is responsible for 50% more carbon pollution. I refer to this complication – stemming from spatial variation in the price of identical products – as the “Manhattan effect”.

Further, consider the purchase of shoes. A pair purchased at Walmart might cost $30, while a pair of Gucci luxury brand shoes might cost $600.7 Both transactions are categorized as “Shoes and other footwear” for the purposes of Eq. 1. The Gucci shoes may, in fact, have a higher carbon footprint than those from Walmart – but probably not 20 times higher, which is what a uniform CIE implies. In practice, we expect CIE to vary with household income as wealthier households, on average, buy higher-priced versions of otherwise similar items. I refer to this complication – stemming from differences in price paid across households within a given expenditure category – as the “Gucci effect”.8

Both the Manhattan and Gucci effects suggest that conventional approaches may overestimate the carbon footprints of rich households. On the other hand, it is possible that rich households are disproportionately responsible for underreporting of expenditures in the CEX. These two factors push in opposite directions – with possibly important distributional consequences.

The following sections describe how I address the issues raised above, specifically 1) adjustment of household-level expenditures reported in the CEX to match associated PCE totals and 2) calculation and adjustment of national average CIE to account for both the Manhattan and Gucci effects.

5.1 Simulation and adjustment of household expenditures

The CEX sample size is not sufficient to allow an analysis of this kind at both high spatial and demographic resolution. However, it is possible to use CEX data to simulate household expenditure for the much larger American Community Survey (ACS), relying on the large overlap in household and geographic variables between the two surveys. This type of survey integration is sometimes referred to as “micro data fusion” (Pisano and Tedeschi 2014).

7 For the record, I (proudly) have no idea what a pair of luxury-brand shoes actually cost. 8 We can imagine a third effect that we might call the “Hawaii effect” or “Alaska effect”, reflecting the fact that prices are higher in some places due to geographic considerations and transportation costs, independent of the Manhattan and Gucci effects. In theory, a spatial econometric approach could isolate this effect using the data described in Section 5.3, but I leave this for future analysis.

4

The CEX-ACS fusion process was introduced and described by Ummel (2014). The technique relies on boosted quantile regression trees – a machine learning strategy – to estimate expenditure probability distributions conditional on observable household, climatic, and local economic characteristics (e.g. fuel prices). In conjunction with an algorithm to generate random uniform variates that exhibit observed correlation across spending categories (Schumann 2009), it is possible to simulate an expenditure dataset that preserves both micro and macro patterns in the original CEX data. Readers are directed to the original paper for details.9

This study takes the fused CEX-ACS dataset as its starting point. It contains inflation-adjusted expenditures (2012 dollars) for nearly 6 million households across 52 different expenditure categories over the period 2008-2012, along with the complete set of household-level variables inherent to the ACS. The main extension in this paper is to adjust expenditures for the aforementioned discrepancy between CEX and PCE expenditure total (i.e. under-reporting problem).

I rely on a comparison of CEX and PCE totals across comparable expenditure categories carried out by BLS and BEA staff.10 It provides the ratio of CEX-to-PCE expenditure (“reporting ratio”) for each category. Expenditures for rent, utilities, vehicle purchase, gasoline, and communication services (e.g. phone service) are all reported quite accurately. Outside of these categories, the aggregate reporting ratio for 2014 was just 53%.

To understand why this is problematic, consider the example of expenditures for meals consumed outside the home (i.e. fast food and restaurants). The reporting ratio is about 60%. I-O analysis produces a CIE for restaurants (kgCO2 per dollar of expenditure) based on total PCE expenditure for the category (see Section 5.2). If the CIE is applied to unadjusted CEX expenditure, it will underestimate total emissions from eating out by 40%.

To make matters worse, reported restaurant expenditure increases disproportionately with household income. Indeed, this is true of many of the categories with low reporting ratios. Without any adjustment, Eq. 1 will not only underestimate total restaurant emissions, it will disproportionately under-estimate emissions among rich households (assuming the rich report as accurately as the poor).

Clearly, it is necessary to adjust CEX expenditure upwards to match PCE totals and create compatibility with CIE derived from I-O tables. However, absent detailed survey data comparing household reported expenditure to actual expenditure (something that is very difficult to do), there is no way of knowing if the likelihood and/or magnitude of under-reporting is related to household demographics (e.g. income).

Consequently, I assume that under-reporting is uniform across the population. For each category, CEX expenditure for all households is divided by the category-specific reporting ratio. The net effect is to disproportionately increase expenditure among the rich – but only because the rich

9 http://www.cgdev.org/publication/who-pollutes-household-level-database-americas-greenhouse-gas-footprint- working-paper 10 http://www.bls.gov/cex/cecomparison.htm

5 disproportionately consume those categories where BLS/BEA analysis suggests under-reporting is most significant.11

To check that the adjustment for under-reporting produces plausible total expenditure, I compare aggregate PCE with aggregate (adjusted) expenditure in the household sample. Since the two are not directly comparable as is, I subtract-out the following PCE components from the national accounts data:

• Imputed rental of owner-occupied nonfarm housing • Rental value of farm dwellings • Health care • Health insurance • Pharmaceutical and other medical products • Final (net) consumption expenditures of nonprofit institutions serving households

For 2012, this leaves $7.2 trillion in the remaining PCE categories. I compare this figure with under-reporting-adjusted total expenditures in the household sample, excluding Health insurance, Drugs, Medical services, and Medical supplies, and Cash contributions. The resulting total expenditure is $7.17 trillion. Whether the adjustment procedure generates the correct distribution of expenditures remains an open question, but it does produce overall spending in agreement with the national accounts.

5.2 Input-output modeling of national CIE

The data and techniques used here to estimate national CIE across expenditure categories are similar to those employed by Fullerton (1996), Metcalf (1999), and others.12 My approach is most similar that of Perese (2010), and readers are directed to that paper for technical and mathematical details.13 This section describes where, why, and how I modify the conventional approach, and I assume the reader is familiar with the basics of I-O modeling.14

Estimation of CIE requires the analyst to pass a “tax matrix” into the I-O framework such that, when solved, the system of equations returns a vector of price increases for each commodity. These prices increases reveal the CIE, given the (static) state of economy described in the I-O

11 Cross-country analysis shows that the ratio of total household survey expenditure to total national account expenditure declines with rising income (Deaton 2005). If this observed pattern between countries were to hold within the U.S. – implying that rich households disproportionately under-report expenditures – then my assumption of uniform under-reporting across households will underestimate spending among the rich. 12 Strictly speaking, the analyses cited do not estimate CIE directly but, instead, estimate commodity relative price changes for a given carbon price. Mathematically, these are two sides of the same coin and analogous for our purposes. 13 https://www.cbo.gov/sites/default/files/111th-congress-2009-2010/workingpaper/2010-04-io_model_paper_0.pdf 14 In short, the I-O “framework” or model relies on “Use” and “Make” input tables that describe the monetary flow of commodities to and from industries. They report all inputs and outputs associated with the production of goods and services. The tables are consistent with one another and with the national account totals for consumption and investment across households and government, as well as imports and exports. See UN Statistics Division (1999).

6 tables. Each cell of the tax matrix should contain the revenue to be raised from the use of a given commodity by a given industry.

The tax matrix is typically constructed to reflect revenue from energy-related CO2 emissions for the year in question. However, this omits carbon embedded in fuel exports. Fossil fuel inputs (e.g. crude oil) used to produce fuel exports (e.g. fuel oil) are to be taxed at the well/mine mouth or border, but the associated carbon is not reflected in energy-related emissions since it remains embedded in fuel sent abroad.

To correct for this, I remove fuel exports from the Make and Use tables. I adjust all intermediate inputs to the respective industries proportionally, reflecting the share of fuel exports in total industry output. This reduces total output of fossil fuel commodities in the I-O framework to account for emissions embedded in fuel exports.

In practice, earlier research probably did not suffer too much from this omission, because U.S. fuel exports were relatively small. But fuel exports in the post-2008 period are not negligible. This is most pronounced in the case of petroleum product exports containing almost 500 MtCO2 of embedded carbon in 2012 (coal exports were also significant in CO2 terms).

It is also necessary to distribute the revenue in the tax matrix across specific commodity-industry cells. Typically, revenue is allocated across industries in proportion to input value, assuming that ad valorem tax rates are constant for a given fossil fuel commodity. However, in practice input prices can vary considerably across industries.

I address this, in part, by integrating EIA data on the amount of CO2 emitted, by fuel, in the “Electricity” and “Other” sectors. This allows me, for a given fossil fuel, to assign one ad valorem tax rate for the power sector and one rate for all other users. In the case of coal, for example, this leads to larger ad valorem rates in the electricity sector compared to industrial users, presumably reflecting the lower input prices of the former.

Unlike Perese (2010), I do not explicitly include rebates for carbon sequestered through non- combustive use of fuel (e.g. asphalt, lubricants, etc.). Technically, the CCL proposal would provide such rebates. However, since the size of the tax passed into the I-O model purposefully excludes sequestered CO2, the model captures the aggregate effect of such an adjustment but ignores differential effects across industries. Ideally, future work would include sequestered CO2 in the tax matrix alongside explicit rebates in the I-O framework per Perese (2010).

I multiply commodity-specific CIE values from the I-O model across all final uses in the Use table to calculate the total carbon associated with each commodity and end use. This effectively assumes that non-fuel imports have the same carbon-intensity (and, therefore, face the same tax rate) as their domestically-produced counterparts. This is a common assumption in such analyses and could well reflect real-world border tax adjustments under unilateral carbon pricing (Metcalf and Weisbach 2009).

In the case of fuel imports and exports, I calculate the associated carbon separately by integrating additional data on physical quantities of fossil fuel produced, imported, and exported in

7 15 conjunction with CO2 emission factors from the EPA. I find that the fuel import and export emissions implied by the I-O model do not consistently replicate the quantities calculated from physical fuel data. This may be due to differences in prices or other issues specific to the treatment of imports and exports in the BEA data. This is an area where additional work in needed. For now, I assume that the fuel import and exports emissions derived from physical fuel quantities are correct.

The remaining departure from previous research concerns the level of detail used in the I-O model itself.16 The BEA provides “benchmark” I-O tables every five years that contain detailed data for almost 400 commodities and industries (most recently for 2007). Annual “summary” tables contain analogous data for an aggregated set of about 70 commodities and industries (currently through 2014). Typically, researchers face a tradeoff between detail and timeliness, and all previous research has relied on the comparatively coarse product detail of the summary- level tables.

It is possible, however, to use the 2007 benchmark data to “expand” each cell of a summary year table. This results in new Make and Use tables for non-benchmark years that have the product detail of the benchmark tables but retain cell values consistent with the summary-level tables. Since this process can result in discrepancies in commodity and industry total output across the Use and Make tables, I use an iterative proportional fitting procedure (i.e. “matrix raking” or “RAS algorithm”) to adjust cell values and achieve identical margins across the two tables.17 I employ an analogous process to create detail-level versions of the PCE bridge matrices.

Using the expanded I-O tables, I compute CIE for each BEA commodity and year 2008-2012. The expanded PCE bridge matrices are used to calculate CIE for more than 200 PCE categories. Finally, CIE is calculated for each of the 51 expenditure categories contained in the fused CEX- ACS dataset, using a cross-walk provided by BLS and BEA that links CEX expenditure line item codes to PCE categories. National CEX expenditure at the line-item level is used to weight the relative contribution of different PCE categories when calculate final CIE for each expenditure category.

15 Both energy-related CO2 emission and physical fuel quantity data come from EIA’s Monthly Energy Review (http://www.eia.gov/totalenergy/data/monthly). Emission factors are from the EPA (http://www.epa.gov/energy/ghg-equivalencies-calculator-calculations-and-references). 16 I utilize the BEA Make and Use tables, in producer prices and after redefinitions, at both the summary and benchmark level of detail along with the commodity-PCE bridge data. For an introduction to the BEA Industry Accounts, see Streitwieser (2009). 17 Every carbon tax analysis using summary-level BEA I-O tables must take analogous steps to, at a minimum, disaggregate the “Coal mining” industry from the aggregated “Mining, except oil and gas” industry. The technique used here is simply a systematic extension of this process to the rest of the matrix.

8 5.3 Modeling spatial variation in prices

As indicated above, variation in consumer prices poses a challenge when computing household carbon footprints from expenditures alone. Previous analyses of CEX data in the context of carbon pricing and/or footprinting have ignored this fact. In order to account for both the Manhattan and Gucci effects, it is necessary to specify how prices for different kinds of goods vary across the country.

I rely on a proprietary dataset of consumer prices provided by the Council for Community and Economic Research (C2ER).18 The C2ER data used here provides reported consumer prices for 53 individual goods and services (referred to here as “items”) over 2008-2012 and for nearly 400 urban areas. These data indicate, for example, the retail price of a gallon of regular gasoline or a 2-liter bottle of Coca Cola, etc.

The C2ER data generally report consumer prices excluding state and local sales tax. However, prices for gasoline, beer, and wine include federal and state excise taxes paid by producers, and gasoline additionally includes sales tax when applicable.

Reported retail prices for gasoline, beer, and wine are first stripped of their sales and excise tax components. Per-gallon excise and applicable sales taxes for gasoline come from the American Petroleum Institute’s motor fuel tax reports.19 Excise taxes for beer and wine come from the Tax Foundation.20 This step removes spatial variation in prices due to differences in state tax policy. The resulting “tax-free” prices reflect the underlying cost of production, transport, and wholesale and retail trade margins for a given location.

For each item and year, I spatially interpolate observed prices using zip-code level data as regressors in a universal Kriging model. The zip-code level regressors include a measure of typical per-capita income created by combining information from multiple ACS 5-year (2010- 2014) estimate tables, along with population density and typical home value provided by Zillow Real Estate Research.21

Following spatial interpolation of tax-free prices, applicable sales and excise tax for each item is added to arrive at the tax-inclusive retail price in each zip code.22 Combined state and local sales tax rates for each zip code come from Avalara.23 Exclusion of certain items from the sales tax base is determined using guidance on state-specific exclusions of food and drugs from the Federation of Tax Administrators.24

18 https://www.coli.org 19 http://www.api.org/Oil-and-Natural-Gas-Overview/Industry-Economics/Fuel-Taxes 20 http://taxfoundation.org/tax-topics/alcohol-taxes 21 http://www.zillow.com/research/data/ 22 There is no dominant, large-scale spatial pattern underlying sales tax rates. While there is significant intra-state variation due to taxes imposed by local municipalities in addition to the statewide rate, there is effectively zero overall correlation (-0.024) between zip code sales tax rate and typical per-capita income. This suggests that explicit consideration of sales tax leads to place-specific (and somewhat random) adjustments to CIE rather than systematic adjustments along spatial or demographic lines. 23 http://salestax.avalara.com 24 http://www.taxadmin.org/assets/docs/Research/Rates/sales.pdf

9

The prevailing, tax-inclusive price in a given zip code ( ) may differ from the effective consumer price – i.e. the average price actually paid by residents ( ). This is most pronounced 𝑖𝑖 for locales and items where tax rates vary significantly across𝑝𝑝 political borders (e.g. gasoline 𝑖𝑖 prices across state borders). I assume that the effective price in a given𝑃𝑃 zip code resembles an average of local prices within some radius of residents’ homes.

To capture this effect, I convert the polygon zip code data to a raster grid and, for each cell, item and year, calculate the effective consumer price as the weighted mean price within 40 km (25 miles) of each grid cell. For cell k with j cells at distance and local population25 , the effective price is the weighted mean of local prices such that 𝑑𝑑𝑗𝑗 𝑦𝑦𝑗𝑗 𝑃𝑃𝑘𝑘 𝑝𝑝𝑗𝑗 = where = ( 2 ) ∑𝑗𝑗 𝑝𝑝𝑗𝑗𝑤𝑤𝑗𝑗 𝑦𝑦𝑗𝑗 𝑘𝑘 𝑗𝑗 𝑗𝑗 𝑗𝑗 𝑗𝑗 For each item and year, the effective𝑃𝑃 price∑ 𝑤𝑤 in zip code 𝑤𝑤 is then1+ 𝑑𝑑simply the population-weighted mean of associated grid cells k: 𝑖𝑖 = ( 3 ) ∑𝑘𝑘 𝑃𝑃𝑘𝑘𝑦𝑦𝑘𝑘 𝑖𝑖 For each item and year, the effective price 𝑃𝑃in zip code∑𝑘𝑘 𝑦𝑦𝑘𝑘 is then divided by the population- weighted mean national price for the item in question ( ), giving a ratio defined by: 𝑖𝑖 𝑃𝑃� 𝑅𝑅𝑖𝑖 = = ( 4 ) 𝑃𝑃𝑖𝑖 𝑃𝑃𝑖𝑖 ∑𝑖𝑖 𝑦𝑦𝑖𝑖 𝑖𝑖 Each of the items are then assigned to a CEX𝑅𝑅 UCC𝑃𝑃� ∑(line𝑖𝑖 𝑃𝑃𝑖𝑖𝑦𝑦-𝑖𝑖 item) code and one of 11 categories: Alcohol, Apparel, Consumer goods, Dairy, Fast food, Fruits and vegetables, Gasoline, Health care, Meat and eggs, Other food, and Services. For each category, a weighted relative price index is calculated ( ), where the associated item weights are equal to total U.S. expenditure for the associated UCC code ( ): 𝑉𝑉𝑖𝑖 𝑛𝑛 𝐸𝐸𝑛𝑛 = ( 5 ) ∑𝑛𝑛 𝑅𝑅𝑖𝑖𝐸𝐸𝑛𝑛 𝑖𝑖 The variable is computed for each year 2008𝑉𝑉 -2012∑𝑛𝑛 𝐸𝐸𝑛𝑛 and measures relative differences in price levels across zip codes. A value of = 1 indicates parity with national average prices for the 𝑖𝑖 category in question.𝑉𝑉 𝑖𝑖 𝑉𝑉 Figures 1-3 show the resulting zip-code level relative price indices for the Gasoline, Fruits and vegetables, and Services categories for the year 2012. In the case of gasoline, the differences largely reflect variation in state excise tax. But for Fruits and vegetables and Services, the patterns reflect other economic forces.

25 Grid-cell population provided by: http://beta.sedac.ciesin.columbia.edu/data/set/gpw-v4-population-density

10 Finally, for the purposes of subsequent analysis that integrates price index data with the fused CEX-ACS dataset, it is necessary to aggregate the zip code level results to the level of PUMA’s. This is accomplished using a linkage between zip codes and PUMA’s provided by the Missouri Census Data Center’s MABLE/Geocorr1226 system and constructing a population-weighted mean index value for each PUMA.

Figure 1 - Gasoline price index (2012)

26 http://mcdc.missouri.edu/websas/geocorr12.html

11 Figure 2 - Fruits and vegetables price index (2012)

Figure 3 - Services price index (2012)

12 5.4 Adjusting CIE for Manhattan and Gucci effects

With the price index data developed above, adjusting CIE for the Manhattan effect is straightforward. For a given expenditure category, the local CIE in PUMA m is simply:

= ( 6 ) 𝐶𝐶𝐶𝐶����𝐶𝐶� 𝑚𝑚 where is the national average CIE derived𝐶𝐶𝐶𝐶𝐶𝐶 from𝑉𝑉 the𝑚𝑚 I-O analysis in Section 5.2. That is, the local CIE results from adjusting national average CIE up (down) in places with below-average (above𝐶𝐶𝐶𝐶�-�average)��𝐶𝐶� prices.

However, adjusting for both the Manhattan and Gucci effects is more complicated. The Gucci effect implies that the average price paid for otherwise-similar products (i.e. products within a given expenditure category) varies with household characteristics – particularly income.

To estimate the size of this effect, I exploit the fact that households cannot consume infinite amounts of food. Assuming that richer individuals do not eat more calories (just more expensive ones), I estimate annual total calories consumed at the household level (C) by combining information on the number and age of household members with recommended daily calorie intake for different groups.27 Summing local-price-adjusted expenditure E across f food expenditure categories and dividing by C gives a measure of average price per calorie:

= ( 7 ) 1 𝐸𝐸𝑓𝑓 𝑓𝑓 𝑓𝑓 It is possible that Y increases with income because𝑌𝑌 𝐶𝐶 ∑ richer𝑉𝑉 households shift to more expensive categories of food (e.g. eating out) without any actual increase in the price paid for calories within a given category. Isolating the Gucci effect requires controlling for the composition of the household food basket.

I fit a boosted quantile (median) regression tree model where the response variable is the ratio of Y to its calorie-weighted mean (call the ratio G) over n households in the sample, and the predictors include household income percentile I and a vector of food category expenditure shares :

𝑋𝑋𝑓𝑓 = , where = ( 8 ) 𝑌𝑌 ∑𝑛𝑛 𝐶𝐶𝑛𝑛 𝑓𝑓 𝐺𝐺 𝐹𝐹�𝐼𝐼 𝑋𝑋 � 𝐺𝐺 ∑𝑛𝑛 𝑌𝑌𝑛𝑛𝐶𝐶𝑛𝑛 A monotonicity constraint is enforced on I and 10-fold cross-validation used to determine the optimal number of regression trees, as determined by minimizing the average root-mean-squared error across the folds.

27 http://www.cnpp.usda.gov/sites/default/files/usda_food_patterns/EstimatedCalorieNeedsPerDayTable.pdf

13 The marginal effect of I on G is given by the black curve in Figure 4. It describes the relationship between household income percentile and typical (median) price-per-calorie relative to the national average controlling for both local price levels and the composition of the food basket. In other words, a measure of the degree to which richer households buy more expensive versions of otherwise-similar calories – the Gucci effect (or, at least, a proxy for it). I assume that this relationship holds across all applicable expenditure categories.28

Figure 4 - Estimated Gucci effect

At this point, a simple adjustment to CIE might consist of including household-level predictions of G (based on I) in the denominator of Eq. 6. However, as mentioned earlier, it is possible that higher-price products and services are, in fact, more carbon-intensive than lower-price alternatives.29 Exactly how much more is unclear and probably not knowable outside of extremely detailed, item-specific expenditure surveys coupled to life-cycle analyses.

A practical approach is to assume that variation in G is due entirely to differences in trade margins. That is, Gucci and Walmart shoes are effectively identical at the factory gate, and the difference in consumer price is due to (much) higher transport, wholesale, and retail margins in the case of the former.

Under this assumption, for a given expenditure category and household located in PUMA m, the fully-adjusted CIE is a function of the predicted generic Gucci ratio (based on household’s

28 Utility and gasoline expenditure categories are excluded from the Gucci effect adjustment, because premium or luxury version of these goods are generally not available. 29 A relevant exception here is organic food, which may have both a lower carbon footprint and higher price.

14 observed I), the local price index ( ), the share of trade margins in total purchaser price ( ) and the national average CIE for the production and trade margin components ( and , 𝑚𝑚 𝑡𝑡 respectively). 𝑉𝑉 𝑆𝑆 �𝐶𝐶𝐶𝐶���𝐶𝐶�𝑝𝑝� 𝐶𝐶𝐶𝐶����𝐶𝐶��𝑡𝑡 = ( ) (1 ) + ( + 1) ( 9 ) −1 𝐶𝐶𝐶𝐶𝐶𝐶𝑚𝑚 𝑉𝑉𝑚𝑚𝐺𝐺 � − 𝑆𝑆𝑡𝑡 �𝐶𝐶𝐶𝐶���𝐶𝐶�𝑝𝑝� 𝑆𝑆𝑡𝑡 𝐺𝐺 − �𝐶𝐶𝐶𝐶���𝐶𝐶��𝑡𝑡� 5.5 Calculation of fuel-specific CIE

In the case of electricity, there is no need to rely on CIE from the I-O model. Instead, the EPA eGRID program provides CO2 emission factors for 26 power grid sub-regions in year 2012, reflecting emissions released at power plants during fuel combustion (zero in the case of renewable generators).30 I also include an adjustment for transmission and distribution losses between generators and consumers.31

Combined with a spatial dataset indicating the physical boundaries of grid sub-regions, it is possible to estimate the carbon intensity (kgCO2 per MWh) of individual zip codes. Figure 5 shows the results. A separate dataset from OpenIE, provides residential electricity rates for 2012 for individual zip codes (cents per kWh).32 Figure 6 displays this information. These two data sources allow the calculation of location-specific CIE for residential electricity.

In the case of natural gas, heating oil, and LPG, I use state-level residential prices from the EIA to adjust the national average CIE. Since this could lead to erroneous values (primarily because the I-O analysis CIE for these fuels will reflect all uses – not just residential), I include a further, final adjustment to ensure that total residential CO2 emissions from these fuels match totals reported by the EIA.

30 http://www.epa.gov/energy/egrid 31 The eGRID-derived emission factors do not account for inter-regional electricity flows that could impact the true GHG-intensity of electricity consumed. Up to 30% of electricity consumed in some grid sub-regions originates elsewhere (Diem and Quiroz 2012), but there is currently no simple way to account for these flows. 32 http://en.openei.org/datasets/dataset/u-s-electric-utility-companies-and-rates-look-up-by-zipcode-2013

15 Figure 5 - Carbon intensity of electricity supply (2012)

Figure 6 - Residential electricity price (2012)

16 6 Simulation of carbon fee and dividend policy

The simulated policy imposes a $15 per ton CO2 carbon fee on all domestic fossil fuel extraction and imported fuels and goods. I calculate that the average annual carbon tax base – that is, the total amount of CO2 subject to taxation– was 7,810 MtCO2 per year over the period 2008-2012 Assuming a static economy and no response to the tax, this yields gross revenue of $117 billion for simulation purposes.

About 20% of gross revenue is used to finance carbon tax rebates for businesses exporting goods abroad or using fossil fuel for non-combustive uses (see Section 6.1). The remaining ~80% is returned to households in the form of a taxable “dividend”. The revenue is disbursed to households, assuming that each adult receives a full dividend “share” and each child (up to two per household) receives a half share.

A measure of “net financial benefit” (NFB) is calculated for each household in the sample. Given a pre-tax dividend (D), marginal income tax rate (M; see Section 6.2 below), effective CO2 footprint (Z), and a nominal carbon tax rate of $15 per ton CO2 (T=15), a household’s NFB is given by:

= (1 ) ( 10 )

In the context of carbon pricing, revenue𝑁𝑁𝑁𝑁𝑁𝑁 and CO−2 𝑀𝑀emissions𝐷𝐷 − 𝑍𝑍𝑍𝑍 are analogous. The tax burden for a given entity – assuming that the tax is passed entirely on to consumers and there is no macroeconomic response to the policy – is proportional to that entity’s carbon footprint. Since a primary objective of this study is to assess the balance of costs (i.e. emissions or tax burden) and benefits (i.e. dividends) for individual households, it is important to ensure that the “sources and sinks” of these flows are clearly understood.

6.1 Sources of gross revenue

Results from the I-O model show that 12.8% of CO2 emissions (and, therefore 12.8% of gross revenue under carbon pricing) is attributable to local, state, and federal governments. These entities face higher prices when providing public services. In addition, 44% of health care services – ostensibly household consumption in PCE accounting – are, in fact, paid by governments (primarily through Medicare and Medicaid).33 I calculate that the government- financed portion of total health sector CO2 emissions averaged 201 MtCO2 per year over 2008- 2012, providing ~2.6% of gross revenue. All told, governments at all levels ultimately finance about 15% of gross revenue. See Table 1 for details.

Another 16.3% of gross revenue is derived from implicit taxation of fuel, goods, and services produced for export. This is higher than the result of ~10% reported by Perese (2010) using data from 2006. However, given the significant increase in U.S. fuel exports since that time, the

33 https://kaiserhealthnews.files.wordpress.com/2014/04/highlights.pdf

17 higher figure is reasonable. A policy with full border tax adjustments requires that exporters receive a rebate equal to the carbon tax embedded in their production costs.

Consequently, I assume that 16.3% of gross revenue is effectively a new cost (an export rebate) to be paid by the federal government.34 In addition, I estimate that nearly 4% of gross revenue is derived from taxation of carbon sequestered by nonfuel uses of energy (e.g. asphalt, petrochemicals, etc.). This revenue would also need to be rebated. Together, about 20% of gross revenue is directed back to business in the form of tax rebates.

The remaining ~65% of revenue must be sourced from households. However, total emissions/costs that can be assigned to households on the basis of actual expenditure only amount to about 54% of gross revenue. Part of the discrepancy is due to health care. Individuals rarely report (or know) the actual value of health care services received. Nor do most report (or know) the value of private health insurance premiums paid by employers. I estimate that private, non-government provision of health care is the source of ~3.3% of gross revenue.

I assume this cost is evenly distributed across the non-Medicare and non-Medicaid population. I make a rough estimate of participation in these programs on the basis of head-of-household age and household income relative to the Federal Poverty Level (133% being the general threshold for Medicaid eligibility). This effectively assumes that privately-insured individuals pay 3.3% of gross revenue through higher health insurance premiums, imposing an average cost of $19 per person.

Finally, 7.5% of gross revenue is attributable to taxation of fixed private investment – that is, construction of physical structures and purchase of durable equipment by both business and households.35 There is no agreement on how (or even whether, in some cases) revenue derived from fixed capital formation should be allocated to households. I assume this cost is distributed across households in proportion to total expenditure.

34 This is different than the border tax adjustment policy proposed by CCL. CCL proposes to make all exports eligible for a rebate except fossil fuel exports. I chose to simulate the more generic rebate policy since it is unclear how to assign the cost of the fossil fuel exemption across households (if at all). Additionally, CCL proposes the use of a separate government account where revenue from taxation of non-fuel imports is deposited and subsequently used to pay for rebates on non-fuel exports. Based on the I-O model output, I suspect this the account would generate a small positive balance. 35 From BEA NIPA Handbook (https://www.bea.gov/national/pdf/NIPAhandbookch6.pdf): “Private fixed investment (PFI) measures spending by private businesses, nonprofit institutions, and households on fixed assets in the U.S. economy. Fixed assets consist of structures, equipment, and software that are used in the production of goods and services. PFI encompasses the creation of new productive assets, the improvement of existing assets, and the replacement of worn out or obsolete assets.”

18 Table 1 - Sources of gross carbon tax revenue (annual avg. 2008-2012)

Revenue, $B Percent of MtCO2 ($15 per tCO2) total Consumption expenditures 4,188 $62.8 53.6% Households Private health care 256 $3.8 3.3% Private fixed investment 582 $8.7 7.5%

Government Consumption and investment 1,003 $15.0 12.8% (all levels) Medicare and Medicaid 201 $3.0 2.6%

Rebate-eligible Export of fuel and goods 1,270 $19.0 16.3% activities Non-combustive use of fuel 310 $4.8 3.9% TOTAL 7,810 $117.1 100%

6.2 Dispersal and taxation of dividend

The dividend is treated as fully taxable income at the federal level, and I assume that all households in the fused dataset receive a dividend and pay federal income tax. The policy has no impact on state income taxes. In reality, details of the rebate mechanism(s) could have significant practical and distributional consequences, both for welfare and tax revenue. Dinan (2012) and Stone (2015) provide excellent overviews of the relevant issues and concerns. For the purposes of this study, details of the rebate mechanism itself are ignored.

Each household pays a portion of the rebate back to the federal government, reflecting the household’s marginal income tax rate. I estimate the marginal rate of each household using results from the Urban-Brookings Tax Policy Center Microsimulation Model.36 The assumed relationship between household income percentile and marginal tax rate is given in Figure 7. This assumption results in about 18% of the gross dividend returning to the federal government as income tax revenue.

36 http://www.taxpolicycenter.org/numbers/displayatab.cfm?Docid=2503

19 Figure 7 - Assumed relationship between household income and marginal tax rate

6.3 Impact on government budget

The simulation results in a net cost to government of $1.1 billion. Given the allocation of the dividend across households and the assumed marginal tax rate relationship with income, about 18% of the gross dividend is recouped by the federal government as income tax revenue. This generates total income tax revenue of $17 billion, but the tax burden imposed on government through higher prices is $18.1 billion, leaving a $1.1 billion shortfall.

It should be noted (again) that this analysis does not consider any dynamics effects of the policy on macroeconomic outcomes. If the policy were to cause the economy to contract, the budget deficit could be greater than presented here.

20 7 Results

When assessing the results presented below, it is important to remember that this analysis is “static” and does not consider “dynamic” effects that a carbon tax would have on economic growth, employment, wages, trade, or consumption patterns over time. Nor does it consider local or global environmental benefits. Instead, I calculate the short-run financial effect on families, assuming that the policy is implemented “overnight” with 100% pass-through of the tax into consumer prices, no change in household behavior, and no change in production processes, technologies, or emissions. Throughout this section, a household that is said to be “benefited” by the policy is one that experiences a positive net financial benefit (NFB) given the assumptions and limitations noted above.

The policy’s $15 per ton CO2 carbon fee generates annual revenue of $117 billion for the purposes of the simulation. About 20% of gross revenue is used to finance carbon tax rebates for businesses exporting goods abroad or using fossil fuel for non-combustive uses. The remaining 80% ($93 billion) is returned to households in the form of a taxable “dividend”, assuming that every adult receives a full dividend “share” and each child (up to two per household) receives a half share.

This amounts to a pre-tax dividend of, on average, $811 per household ($323 per person).37 Given the assumed marginal tax rate relationship with income (Section 6.2), the average after-tax dividend – that is, the increase in disposable income due to the rebate – amounts to $664 per household ($264 per person).

7.1 Costs and benefits across the income distribution

Overall, 54% of U.S. households experience a positive NFB under the policy. Figure 8 shows the percent of households benefited overall and across income quintiles. Each quintile contains an equal number of people, ranked according to household income as a percentage of the Federal Poverty Level (FPL).38

Among households benefited, the typical (median) gain is $198 per household or about 0.4% of income. Among the 46% of households with a negative NFB, the typical loss is $196 per household. Across all households, the mean NFB is slightly positive ($17), reflecting the fact that the policy, as simulated, results in a small net transfer from government to households (Section 6.3).

37 All “per-person” results include both adults and children equally in the denominator. Also, the ACS sample excludes people living in “group quarters”, which includes correctional facilities, juvenile facilities, nursing homes, and health care facilities. Consequently, per-household and per-person results are slightly over-stated. 38 I use income as a percentage of FPL to rank households, because the latter incorporates an adjustment for household size that better reflects relative economic standing (https://aspe.hhs.gov/poverty-guidelines). Percent of FPL is also often used to determine eligibility for government programs, so distributional effects along this dimension have practical policy relevance.

21 The policy is highly progressive overall. Eighty-seven percent of households in the bottom quintile of the income distribution are benefited, compared to just 15% in the top quintile. On average, net benefit for households in the bottom quintile is $305 per household or about 1.9% of income. Households in the top quintile, on average, experience losses of a similar absolute magnitude ($324) but less relative to income (-0.2%). Households in the middle of the income distribution (Quintile 3) see a small overall benefit (mean value of $39 per household).

Figure 8 - Percent of households benefited, by income quintile

Figure 9 shows overall financial effects across income deciles. The size of the after-tax dividend (additional disposable income) received by each decile does not vary significantly across the income distribution, though it does decline slightly with rising income and higher marginal tax rates. Conversely, the tax burden imposed through higher prices for goods and services increases with income. Overall, the net distributional consequences of the policy are largely (but not exclusively; see Section 7.3) driven by differences in the exposure of households to carbon pricing (i.e. their carbon footprint).

Ummel (2014) estimated that per-person CO2 footprints in the top quintile were, on average, 2.9 times larger than those in the bottom quintile. Given the range of methodological improvements introduced in this study (Section 5), that ratio declines to about 2.2, suggesting that the rich are comparatively less exposed to carbon pricing than previously thought.

22 This pattern results in a net transfer of money from upper-income to lower-income households (Figure 10). Overall, households in Quintiles 3 and 4 exhibit comparatively small net gains and losses, respectively. The primary distributional effect is to shift purchasing power from the top quintile to the bottom two quintiles.

Figure 9 - Total financial cost and benefit, by income decile

23 Figure 10 - Overall net financial benefit, by income quintile

7.2 Spatial variation in net benefit

Figure 11 shows the percent of households benefited for each of 30,000+ zip codes. The typical value of ~54% is represented by white shading in the map. Blue (red) areas are those with higher (lower) than typical values.39

I do not provide a formal analysis of the drivers of these spatial patterns. However, it is possible to surmise three factors that explain at least some of the variation. First, areas with comparatively low-carbon electricity tend to fare better (compare with Figure 12 in Section 5.5). Second, households in suburban areas tend to fare worse, reflecting higher incomes/consumption and

39 Readers should consult Ummel (2014) for details regarding derivation of zip-code level results from the fused CEX-ACS dataset. From that paper: “In order to calculate statistics for alternative geographic regions (e.g. zip codes or congressional districts), it is necessary to compute new sample weights that reflect the likelihood of a given household being located in a given region. A sample weight “raking” algorithm is employed to assign and re-weight households for any given geographic region, using region-specific marginal household counts from ACS and 2010 Census summary files. This technique ensures that the subsample of households assigned to a given zip code or congressional district, for example, reflects the actual distribution of households across income, age, race, housing tenure, and household size…More details are provided in the Annex.”

24 carbon footprints (red “hotspots” around urban cores). Third, areas with comparatively mild climates tend to do better.

Figure 11 - Percent of households benefited, by zip code

The zip-code level results generally bear out trends hinted at in the state-level CGE modeling of Williams et al. (2014b). Namely, that small-scale variation in the distribution of benefits within geographic regions or states may well be more important than differences across regions. This is consistent with the finding of Ummel (2014) that household carbon footprints rise and then fall as one moves outward from urban cores (i.e. a suburban effect).

7.3 Net benefit across demographic groups

This section presents results by age group, household type, and race.

Figure 12 reports net effects across five age groups, based on age of the household head. Roughly two-thirds of younger (18-35) and older (80 and above) households are benefited, compared 45% of households age 50 to 65.

The pattern of benefits across groups makes sense given the impact of age on both carbon footprints and dividend received. Older households tend to have smaller footprints, reflecting reduced mobility and less consumption as a result of low fixed incomes. Younger households

25 tend to be larger – and therefore benefited by the dividend formula – in addition to less income/consumption in early career.

Households in the “35 to 50” and “50 to 65” groups, on the other hand, have higher incomes/consumption and, as children age and move out, smaller and less efficient households (from a carbon footprint perspective).

Figure 12 - Percent of households benefited, by age group

Figure 13 reports net effects across different household types. “Elderly” households are those with a household head age 65 or older, no more than two adults, and no children present. “Poverty” and “Low income” refer to households with income below 100% and 200% of FPL, respectively. Reflecting the strong progressivity seen earlier, 90% of households living below the poverty line are benefited by the policy. The mean NFB in this group is $342 per household (2.9% of income).

Household income is not the sole determinate of policy effects. This is evidenced by comparing results for the “Minority” and “Elderly” groups. Household income as a percentage of FPL is similar for the two groups, but minority households see significantly larger positive effects: mean NFB of $174 versus just $7 for elderly households. This is likely due to differences in household composition and resulting dividend allotment.

26 Figure 13 - Percent of households benefited, by household type

Figure 14 reports net effects by race, based on the self-identified race of the household head.

Most noticeable is the fact that over three-quarters of Latino households are benefited by the policy, compared to less than one-half of White households. On average, Latino households are not only poorer than White households (generally associated with a lower footprint) but also significantly larger in size. Since the dividend formula benefits larger households (and especially households with multiple adults), this leads to both higher pre-tax dividend and NFB.40

Overall, the results highlight the ways in which geographic and social differences can combine with the design of the policy to produce important – and sometimes unforeseen – distributional outcomes.

40 It is also possible that Latino households (and perhaps Asian households), on average, benefit from geographic concentration in parts of the country with comparatively mild climates, though this is not explicitly tested.

27 Figure 14 - Percent of households benefited, by race

28 8 Conclusion

This study simulates a “carbon fee and dividend” policy similar to that proposed by the Citizens’ Climate Lobby (CCL), assuming a “static” economy in which the policy is implemented “overnight” with 100% pass-through of the tax into consumer prices, no change in household behavior, and no change in production processes, technologies, or macroeconomic conditions.

I find that the policy confers a net financial benefit on 54% of households nationwide (59% of individuals). The overall distributional effects are highly progressive. Ninety percent of households living below the federal poverty line are benefited by the policy. The average net benefit in this group is $342 per household, equivalent to nearly 3% of income.

The typical size of the after-tax dividend (additional disposable income) does not vary considerably across the income distribution. As expected, the tax burden imposed through higher prices for goods and services increases with income – though the methodological improvements introduced here suggest that the rich are comparatively less exposed to carbon pricing than previously thought. Overall, the policy’s primary distributional effect is to shift purchasing power from the top quintile to the bottom two quintiles of the income distribution.

Impacts across different population subgroups highlight the ways in which “geo-demographic” differences combine with policy design to affect distributional outcomes. The results suggest that details of the dividend allotment formula with respect to household size and age, for example, could meaningfully impact the distribution of benefits. A different dividend design could prove equally simple to administer and explain while generating net positive benefits for a larger portion of the population.

Indeed, once the distribution of carbon tax burdens across households is accurately specified (and Section 5 makes significant progress here), a principle task – from a policy perspective – is to identify revenue distribution schemes that lead to micro and macro effects amenable to both sides of the political spectrum. Certainly, this task has not been ignored (e.g. Metcalf 2007; Williams et al. 2014a), but “high-resolution” data and analysis – whether used to simulate household rebates, more complex changes to the tax code, or simply “downscale” output from other models – may help communicate policy options in ways that are more meaningful to politicians and the broader public.

Further, the challenge of creating “fair” or “equitable” carbon tax policy – for example, policy that does not unduly harm vulnerable populations – requires not only being able to identify critical populations in modeling output but also go beyond simple mean effects. I focused in Section 7 on the presentation of “percent benefited” results, because I believe this metric is closer to what we should care about most: not leaving some people (literally) out in the cold. For those interested in the full detail that large-sample micro-simulations can provide, I include additional distributional results in Section 10.

It is also worth considering how the “static” household results presented here may differ from reality. From the perspective of workers and their families, the most important omission is the effect of carbon pricing on employment and wages. Whatever the aggregate size and direction of

29 this effect, it will not fall uniformly across industries (Ho, Morgenstern, and Shih 2008). Certain types of workers (e.g. coal miners) and their families and communities will be impacted more than others. It is not immediately clear how inclusion of largely place- and industry-specific employment effects would alter distributional outcomes.41 Since it is possible to observe the occupation of each worker in the fused CEX-ACS household sample, however, there is the possibility of gaining some clarity on this question in the future.

The static analysis also assumes no change in household consumption patterns in response to higher prices. While this approach approximates the formal welfare loss under carbon pricing (Metcalf 1999), it is effectively a worst-case scenario from a household financial perspective. In practice, some households could reduce their tax burden through changes that impose little or no inconvenience – for example, turning off lights in an unoccupied room. But others face taxation of activities that are not easily avoided or substituted for – for example, long commutes in places with no public transportation. As in the case of employment, the real-world financial effects are likely to vary considerably from one household to another.

41 For example, if those households most exposed to negative employment effects already experience net losses for unrelated reasons, then employment effects could make some households even worse off without significantly changing the overall proportion of households benefited.

30 9 References

Burtraw, Dallas, Richard Sweeney, and Margaret Walls. 2009. “The Incidence of U.S. Climate Policy.” Discussion Paper, Resources for the Future. Deaton, Angus. 2005. “Measuring Poverty in a Growing World (or Measuring Growth in a Poor World).” Review of Economics and Statistics 87 (1): 1–19. Dinan, Terry. 2012. “Offsetting a Carbon Tax’s Costs on Low-Income Households.” Working Paper 2012-16, Microeconomic Studies Division, Congressional Budget Office. Hassett, Kevin A., Aparna Mathur, and Gilbert E. Metcalf. 2007. “The Incidence of a US Carbon Tax: A Lifetime and Regional Analysis.” National Bureau of Economic Research. http://www.nber.org/papers/w13554. ———. 2011. “The Consumer Burden of a Carbon Tax on Gasoline.” Fuel Taxes and the Poor: The Distributional Effects of Gasoline Taxation and Their Implications for Climate Policy, Thomas Sterner, Ed., Resources for the Future Press. http://papers.ssrn.com/sol3/papers.cfm?abstract_id=2212939. Herendeen, R.A. 1973. “An Energy Input–Output Matrix for the United States, 1963: User’s Guide. Doc. No. 69.” Center for Advanced Computation, University of Illinois at Urbana-Champaign, Urbana. Ho, Mun S., Richard Morgenstern, and Jhih-Shyang Shih. 2008. “Impact of Carbon Price Policies on U.S. Industry.” Discussion Paper, Resources for the Future. Jerrett, Michael, Richard T. Burnett, Renjun Ma, C Arden Pope, Daniel Krewski, K Bruce Newbold, George Thurston, et al. 2005. “Spatial Analysis of Air Pollution and Mortality in Los Angeles:” Epidemiology 16 (6): 727–36. doi:10.1097/01.ede.0000181630.15826.7d. Kok, Rixt, René M.J. Benders, and Henri C. Moll. 2006. “Measuring the Environmental Load of Household Consumption Using Some Methods Based on Input–output Energy Analysis: A Comparison of Methods and a Discussion of Results.” Energy Policy 34 (17): 2744– 61. doi:10.1016/j.enpol.2005.04.006. Leontief, Wasily. 1953. Studies in the Structure of the American Economy; Theoretical and Empirical Explorations in Input-Output Analysis. New York: Oxford University Press. Mathur, Aparna, and Adele C. Morris. 2014. “Distributional Effects of a Carbon Tax in Broader U.S. Fiscal Reform.” Energy Policy 66 (March): 326–34. doi:10.1016/j.enpol.2013.11.047. Metcalf, Gilbert. 2007. “A Proposal for a U.S. Carbon Tax Swap.” Discussion Paper, The Hamilton Project. Metcalf, Gilbert E. 1999. “A Distributional Analysis of Green Tax Reforms.” National Tax Journal, 655–81. Metcalf, Gilbert E., and David Weisbach. 2009. “Design of a Carbon Tax, The.” Harv. Envtl. L. Rev. 33: 499.

31 National Research Council. 2013. “Measuring What We Spend: Toward a New Consumer Expenditure Survey.” Edited by Don A. Dillman and Carol C. House. Committee on National Statistics, Division of Behavioral and Social Sciences and Education. Pisano, Elena, and Simone Tedeschi. 2014. “Micro Data Fusion of Italian Expenditures and Incomes Surveys.” Working Paper No. 164, Sapienza University of Rome, Italy. http://www.dipecodir.it/upload/wp/pdf/wp164.pdf. Rausch, Sebastian, and John Reilly. 2012. “Carbon Tax Revenue and the Budget Deficit: A Win- Win-Win Solution?” MIT Joint Program on the Science and Policy of Global Change. http://18.7.29.232/handle/1721.1/72548. Sabelhaus, John, David Johnson, Stephen Ash, David Swanson, Thesia Garner, John Greenlees, and Steve Henderson. 2013. “Is the Consumer Expenditure Survey Representative by Income?” National Bureau of Economic Research. http://www.nber.org/papers/w19589. Schumann, Enrico. 2009. “Generating Correlated Uniform Variates.” COMISEF. http://comisef.wikidot.com/tutorial:correlateduniformvariates/. Stone, Chad. 2015. “Design and Implementation of Policies to Protect Low-Income Households under a Carbon Tax.” Issue brief, Resources for the Future. Streitwieser, Mary L. 2009. A Primer on BEA’s Industry Accounts. Bureau of Economic Analysis. Tullock, Gordon. 1967. “Excess Benefit.” Water Resources Research 3 (2). Ummel, Kevin. 2014. “Who Pollutes? A Household-Level Database of America’s Greenhouse Gas Footprint.” Working Paper No. 381, Center for Global Development. http://www.cgdev.org/sites/default/files/who_pollutes_greenhouse_gas_footprint_0.pdf. UN Statistics Division. 1999. “Handbook of Input-Output Table Compilation and Analysis.” Department of Economic and Social Affairs, United Nations. http://unstats.un.org/unsd/publication/SeriesF/SeriesF_74E.pdf. Williams, Roberton C., Hal G. Gordon, Dallas Burtraw, Jared C. Carbone, and Richard D. Morgenstern. 2014a. “The Initial Incidence of a Carbon Tax across Income Groups.” Resources for the Future Discussion Paper, no. 14-24. http://papers.ssrn.com/sol3/papers.cfm?abstract_id=2537839. ———. 2014b. “The Initial Incidence of a Carbon Tax across US States.” Resources for the Future Discussion Paper, no. 14-25. http://papers.ssrn.com/sol3/papers.cfm?abstract_id=2537847.

32 10 Additional graphics

Figure 15 - Typical per-person carbon footprint, by zip code

33 Figure 16 - Distribution of net financial benefit, by income quintile

Figure 17 - Distribution of net financial benefit, by age group

34 Figure 18 - Distribution of net financial benefit, by household type

Figure 19 - Distribution of net financial benefit, by race

35