Home > Forecasts & Analysis > Reducing Emissions of Sulfur Dioxide, Nitrogen Oxides, and Mercury from Electric Power Plants > Notes

Reducing Emissions of Sulfur Dioxide, Nitrogen Oxides, and Mercury from Electric Power Plants
 

Executive Summary

1 Emission leakage occurs when control programs in a sector that is covered lead to actions that increase emissions in sectors not covered by the programs.

Background and Methodology

1 For more discussion of proposed bills, see Energy Information Administration, Analysis of Strategies for Reducing Multiple Emissions from Electric Power Plants: Sulfur Dioxide, Nitrogen Oxides, Carbon Dioxide, and Mercury and a Renewable Portfolio Standard, SR/OIAF/2001-03 (Washington, DC, July 2001), web site www.eia.doe.gov/oiaf/servicerpt/epp/.

2 Industrial generators currently account for approximately 8 percent of total generation, with approximately two-thirds being generated from natural gas.

3 For benefit studies, see bibliography in Energy Information Administration, Analysis of Strategies for Reducing Multiple Emissions from Electric Power Plants: Sulfur Dioxide, Nitrogen Oxides, Carbon Dioxide, and Mercury and a Renewable Portfolio Standard, SR/OIAF/2001-03 (Washington, DC, July 2001), web site www.eia.doe.gov/oiaf/servicerpt/epp/.

4 For more information on the representation of emission caps in NEMS, see Chapter 2 in Energy Information Administration, Analysis of Strategies for Reducing Multiple Emissions from Electric Power Plants: Sulfur Dioxide, Nitrogen Oxides, Carbon Dioxide, and Mercury and a Renewable Portfolio Standard, SR/OIAF/2001-03 (Washington, DC, July 2001), web site www.eia.doe.gov/oiaf/servicerpt/epp/.

5 For more discussion of the treatment of environmental rules and regulations in the reference case, see page 9 of Energy Information Administration, Analysis of Strategies for Reducing Multiple Emissions from Electric Power Plants: Sulfur Dioxide, Nitrogen Oxides, Carbon Dioxide, and Mercury and a Renewable Portfolio Standard, SR/OIAF/2001-03 (Washington, DC, July 2001), web site www.eia.doe.gov/oiaf/ servicerpt/epp/.

6 Even when allowances are allocated at zero cost, there are opportunity costs associated with them. By using its own allowances, a company forgoes the revenue that could be made by selling them.

7 For an analysis of the potential impacts of different emission allowance approaches see D. Burtraw, K. Palmer, R. Bharvirkar, and A. Paul, “The Effect of Allowance Allocation on the Cost of Carbon Emissions Trading” (Washington, DC: Resources for the Future, Discussion Paper 01-30, August 2001); and C. Fischer, “Rebating Environmental Policy Revenues: Output-based Allocations and Tradable Performance Standards” (Washington, DC: Resources for the Future, Discussion Paper 01-22, July 2001). For a discussion of the impacts of a generation performance standard approach see, J.A. Beamon, T. Leckey, and L. Martin, “Power Plant Emissions Reductions Using a Generation Performance Standard,” web site www.eia.doe.gov/oiaf/servicerpt/gps/pdf/gpsstudy.pdf.

8 Banking decisions were estimated exogenously.

9 Output received from Pacific Northwest Laboratory August 30, 2001. Because the Second Generation Model is an energy sector model, offsets that might be available from non-energy sectors (such as agricultural changes or reforestation activities) are not represented.

Impacts on Electricity Generation and Key Fuel Markets

10 Power companies created “banked allowances” by overcomplying during the first phase of the CAAA90 SO2program, from 1995 to 1999. They can use those allowances in later years. (Return to Impacts on Electricity Generation and Key Fuel Markets)

11 Substantial uncertainty remains about the measurement and control of Hg emissions. For a discussion of this issue see pages 16 and 17 in Energy Information Administration, Analysis of Strategies for Reducing Multiple Emissions from Electric Power Plants: Sulfur Dioxide, Nitrogen Oxides, Carbon Dioxide, and Mercury and a Renewable Portfolio Standard, SR/OIAF/2001-03 (Washington, DC, July 2001), web site www.eia.doe.gov/oiaf/servicerpt/epp/.

12 The reference case includes the summer season NOx cap that begins in 2004 for 19 midwestern and eastern states and the District of Columbia. The analysis cases include only the annual NOx reduction programs requested.

13 The Hg allowance price in 2010 is $0 in each of the three analysis cases, because it is assumed that each plant must achieve a specified reduction—set to achieve half the total required reduction—by 2007. Because these reductions are sufficient to meet the 2010 overall cap, the allowance price is $0.

14 The examples given in this paragraph assume a 15-percent fixed charge factor, a 2.5-percent heat rate penalty, and a coal price of $1 per million Btu. They do not represent the costs for any particular plant but are meant to be illustrative.

15 The changes in resource costs reported here do not include the financing and profits typically associated with new investments. If the changes in capital investments are put in the form of annuities, the changes in resource costs are $3.1 billion, $5.7 billion, and $7.2 billion in 2010 in the 50-, 65-, and 75-Percent cases, respectively. In 2020 the corresponding values are $4.8 billion, $9.1 billion, and $12.3 billion.

16 Emission leakage occurs when control programs in a covered sector lead to actions that increase emissions in sectors not covered by the programs.

17 The SGM supply and demand curves were modified to be consistent with the Energy Information Administration’s International Energy Outlook 2001, DOE/EIA-0484(2001) (Washington, DC, March 2001).  Essentially the percentage change in carbon emissions reflected in the SGM curves at different allowance prices was applied to the International Energy Outlook emissions projections for various parts of the world to develop revised abatement demand and supply curves. For more information on the SGM model, see J.A. Edmonds, H.M. Pitcher, D. Barns, R. Baron, and M.A. Wise, “Modeling Future Greenhouse Gas Emissions: The Second Generation Model Description,” in Modeling Global Change, L.R. Klein and Fu-chen Lo, eds (New York, NY: United Nations University Press, 1993).

18 For discussion of an enhanced Hg control technology case and other emission cap sensitivity cases, see Energy Information Administration, Analysis of Strategies for Reducing Multiple Emissions from Electric Power Plants: Sulfur Dioxide, Nitrogen Oxides, Carbon Dioxide, and Mercury and a Renewable Portfolio Standard, SR/OIAF/2001-03 (Washington, DC, July 2001), web site www.eia.doe.gov/oiaf/servicerpt/epp/.