Note: ECAR- East Central Area Rellability Coordination Agreement Region: ERCOT Electric Reliability Council of Texas; MAAC - MidAtlantic Area Council; MAIN= Mid-America Interconnected Network; MAPP Mid-Continent Area Power Pool, NY - New York Power Pool, NE New England Power Pool, FL- Florida subregion of the Southeastern Electric Reliability Council; STV-Southeastern Electric Fleliability Council excluding Florida; SPP Southwest Power Pool, NWP- Northwest Pool subregion of the Western Systems Coordinat ing Council; RA= Rocky Mountain and Arizona-New Mexico Power Areas; CNV California-Southem Nevada Power Area.

Source: Office of Integrated Analysis and Forecasting, National Energy Modeling System runs KYCOMP.D080598A and FD03COMP 0080698C

Sensitivity Cases

Technological Progress

The development and market penetration of new technologies for consumer use (new air conditioners, furnaces, refrigerators, etc.) and for supplier use (new generation, transmission, and distribution equipment) will have a significant impact on the feasibility and costs of meeting the Kyoto Protocol targets in the U.S. electricity sector. All the carbon reduction cases in this analysis include substantial improvements in technology, mainly as a function of market penetration. For example, in the reference case the cost of new advanced combinedcycle plants declines from a starting point of $572 per kilowatt to $400 per kilowatt, a 30-percent improvement. In addition, the thermal efficiency of the same technology improves by roughly 10 percent. The situation is similar for wind plants, the cost of which falls from around $1,000 per kilowatt to under $750 per kilowatt. It is possible that further improvements might occur; however, it is impossible to predict to what

degree a concerted effort to reduce carbon emissions might stimulate the development of new technologies reduce the costs of existing ones.

As described in Chapter 2, to look at the potential impacts of technological innovation, development, and market penetration, a set of low (currently available technology and high technology sensitivity cases wer developed. In the 1990+9% low technology case, the new generating options available were limited to technab gies available in 1998. In the 1990+9% high technolog case, cost and performance characteristics wer assumed to improve at rates consistent with those used in the high technology sensitivity cases in the Anma Energy Outlook 1998.

The performance and cost data used in the high technol ogy cases are considered optimistic but not unreason able. In addition, two new plant types, coal gasification with carbon sequestration and natural gas combined cycle with carbon sequestration were made availabl beginning in 2010 in the high technology case. The uncertainty involved in selecting aggressive cost and performance values for different technologies is consid erable. Thus, the results of these sensitivity cases should not be viewed as indicating which technologies are most promising but, rather, as indicative of the extent to which technological innovation might lower the costs of meeting carbon emission reduction targets.

The key result of the high technology cases is that if new. more efficient, lower cost technologies evolve, the cast of meeting the Kyoto Protocol targets could be lowered significantly. The most important of the generating technologies appears to be the advanced natural gas combined cycle; however, as pointed out above, this is product of the high technology assumptions, and it is impossible to say which technology might progress the

most.

Figure 90 shows the average heat rate (number of Bu needed to generate each kilowatthour of electricity) for all natural-gas-fired generating plants. Even in the low technology case, the average heat rates for natural gas plants are expected to improve significantly. The improvement is greater in the 1990+9% case and even greater in the 1990+9% high technology case.

The effects of assuming lower and higher rates of technological progress on electricity prices in the carbon reduction cases are significant. For example, in 2010. projected electricity prices in the 1990+9% low technology case are more than 70 percent higher than those in the reference case (Figure 91). In the 1990-9% case and the 1990+9% high technology sensitivity case. they still are higher than in the reference case, but by only 49 and 36 percent, respectively. In 2020 the price difference remains quite high in the low technology case but is only 45 percent and 13 percent in the 1990+9% and

990+9% high technology cases, respectively. Neither of he carbon sequestration technologies penetrates the narket in the 1990+9% high technology case, because he projected carbon price is relatively low, and other igh-technology options are more attractive.

Nuclear Power

One carbon-free technology around which there is considerable uncertainty is new nuclear power plants. Currently nuclear power accounts for 20 percent of the power produced in the United States; however, no new nuclear power plants have been ordered since 1978, and the last one to come on line was Watts Bar 1 in 1996. In recent years, the overall performance of existing plants has improved dramatically (although several older units Figure 90. Projections of Average Heat Rates for Natural-Gas-Fired Power Plants In High and Low Technology Cases, 1996-2020 Btu per Kilowatthour

were retired before their 40-year operating licenses expired). In addition, manufacturers are now working on designs for a new generation of nuclear power plants, which are expected to be safer and less costly. As with any new technology the first few newly designed units are likely to be quite expensive, but costs should fall as manufacturers and regulators gain experience with them.

A special sensitivity case was used in this analysis to examine the possible impacts of new nuclear power plants on the carbon reduction cases. Because new nuclear plants are not economical in the 1990+9% case, this sensitivity was analyzed against the 1990-3% case. The 1990-3% nuclear sensitivity case assumes a carbon emissions target 3 percent below 1990 levels and new nuclear plant costs about 8 percent lower than the costs typically associated with the early units of new technologies, with rapidly declining costs as the new technology penetrates the market.

In the 1990-3% nuclear sensitivity case, about 40 gigawatts of new nuclear capacity is built, mostly in the later part of the projection period (Figure 92). With higher carbon prices and lower initial construction costs, the new plants are becoming competitive with other generating technologies. Nuclear electricity generation in the 1990-3% nuclear sensitivity case is only 9 billion kilowatthours higher than in the 1990-3% case in 2010 but is 248 billion kilowatthours higher in 2020.

As discussed above, increases in nuclear capacity and generation will result in greater amounts of spent nuclear fuel discharged from nuclear generating units. The waste must ultimately be moved to a permanent storage facility. The 1990-3% nuclear sensitivity case results in a 15-percent increase in projected cumulative Figure 92. Projections of Nuclear Generating Capacity in the 1990-3% Nuclear Sensitivity Case, 2000-2020

1990+9% Low Technology

1990+9%

spent fuel discharges by 2020, relative to the reference

case.

The future of nuclear power in the United States is uncertain. Indeed, it may depend on the extent to which limits are set on carbon emissions in response to the Kyoto Protocol. The reference and carbon reduction cases in this analysis assume no new nuclear construction, for several reasons. One is concern about the future of nuclear waste disposal. The Nuclear Waste Policy Act of 1982 directed the U.S. Department of Energy (DOE) to begin accepting spent fuel for permanent disposal in 1998. As yet, however, no permanent waste storage site is available, and most of the waste is still being stored on-site by the utilities that operate nuclear power plants. The current schedule projects 2010 as the earliest that the proposed site at Yucca Mountain could begin accepting waste. Given the history of schedule slippage in the waste repository project, new investors may not commit to new nuclear power construction until they are certain that DOE will be prepared to handle the waste. In addition, public concerns about the safety of both plant operations and waste disposal will need to be addressed. The public's association of nuclear power with its weapons origin, along with highly publicized accidents at Three Mile Island and Chernobyl, have heightened safety concerns. Public opposition can cause delays in project approval, adding risk to investments in nuclear power.

Another uncertainty is the cost of new nuclear construction. If another nuclear reactor is built in the United States, it will be one of several new designs that have been approved by the U.S. Nuclear Regulatory Commission (NRC). Two evolutionary designs have received final approval from the NRC, and one "passively safe" design is still being reviewed. The nuclear industry hopes that creating relatively few, standardized designs

will bring down construction costs and reduce the time needed to build future plants. However, past experien: suggests that there will be considerable uncertainty unti the first new units have actually been completed. No nuclear plant operating in the United States today wa built at its initial estimated cost or schedule. Instead, a faced both cost overruns and delays in completion.

There is also uncertainty about the useful lifetimes s currently operating nuclear reactors. In recent years i number of nuclear plants have been permanently shu down well before their license expiration dates, man because of the availability of more economical gener tion. Operating a nuclear unit for a full 40 years license life) will generally require additional capia expenditures over the last 10 to 15 years of the plant: life. Whether or not it is economical to incur such cost will depend on factors specific to each plant, such a location, other types of generation available, and fue prices.

If limitations are placed on carbon emissions in de future, the relative costs of electricity generation cont shift in favor of nuclear power. This analysis assumes that license renewal for nuclear plants will be consid ered, if economical, in all cases with restrictions on carbon emissions. Operators of nuclear power plants that are economical will renew the plant licenses. incurring the costs assumed to be necessary to prepar the plant for an additional 20 years of operation. In 1958 two utilities-Baltimore Gas & Electric and Duke Power-filed applications to renew the operating licenses of existing plants, the Calvert Cliffs units in Maryland and the Oconee plant in South Carolina. The approval process is likely to be lengthy for the first few plants, but as the NRC develops a standard review process, more utilities may consider license renewal a viable option.

Reducing the Impact on the Coal Industry

Coal is the most carbon intensive fuel used for electricity production. The carbon emission rate for coal is 78 percent higher than that for natural gas, which has the lowest rate among the fossil fuels. Consequently, carbon reduction strategies are expected to affect coal more than other energy sources. Because of their heavy reliance on coal, electricity generators have historically produced more carbon than the other energy sectors. In 1996, more than one-third of U.S. carbon emissions resulted from electricity production.

Reductions in carbon emissions in the electricity sector are expected to occur primarily as a result of switching from coal to fuels with lower emission rates, such as natural gas and renewables. Initially, fuel switching occurs mostly by changing the utilization of existing capacity. That is, coal-fired plants are operated less frequently and gas-fired units are used more extensively. Later on,

additional fuel switching results as new capacity is buft to replace electricity from existing coal units. Historically, electric utilities have accounted for most of the coal consumption in the United States. Therefore, fur switching to reduce carbon would seriously affect the co Industry. In the 1990+9% case, utility coal use in 2020 is projected to be 78 percent lower than in the reference case. In the 1990-3% case, coal consumption for electricity pro duction would be nearly eliminated in 2020. Absent s nificant changes in other sectors, continued use of coal i the electricity generation sector is not economical in the 1990+9% case. Substantially lower coal use would likely have dramatic impacts on mining employment, as fewer i miners would be needed, and on the railroads, whose transportation of the coal used in power plants would decline dramatically.

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The impacts on fossil fuel suppliers of policies to limit carbon emissions will depend on how much carbon is in each type of fuel: the more carbon in the fuel, the more severe the impact. If the Kyoto Protocol carbon emissions reduction targets were imposed, the U.S. coal and oil industries would see lower consumption and production than in the reference case, which does not incorporate the Protocol, whereas the natural gas industry would expand. Natural gas wins out over coal and oil in the carbon reduction cases used for this analysis. because its carbon content per British thermal unit (Btu) is only 55 percent of that for coal and 70 percent of that for oil. As a result of higher natural gas consumption and lower oil and coal consumption, carbon emissions from natural gas are projected to be higher in the carbon reduction cases, while emissions from oil and coal are lower.

Natural Gas Industry

Natural gas is a clean, economical, widely-available fuel used in more than 58 million homes and more than 60 percent of the manufacturing plants in the United States. Almost one-quarter of the energy consumed in the United States comes from natural gas. Most of the natural gas consumed in the United States is produced domestically from wells in the central part of the Nation. Gas is transported from the Central United States by pipelines throughout the country and becomes more expensive the farther it must be shipped. Yet natural gas is generally cheaper than oil products, though more expensive than coal on the basis of heating values.

In 1996 the combustion of natural gas produced 318 million metric tons of carbon emissions in the United States, about one-fifth of the U.S. total. The industrial sector was responsible for the biggest share of those emissions, about 45 percent, followed by residential, commercial, and electricity generation in order of magnitude. Twelve years from now, if no carbon reduction measures are put in place, emissions from natural gas combustion are expected to be about 100 million metric tons higher than they were in 1996. Even though the projected emissions are higher in 2010, the natural gas share of total emissions increases only slightly from 1996.

Natural gas consumption, production, imports, and prices are all expected to rise in the reference case.

Natural gas consumption increases more rapidly tu consumption of any other major fuel in the refem case from 1996 to 2010. Natural gas use increases a sectors, but consumption by electricity generators than doubles to take advantage of the high efficience. combined-cycle units and the low capital costs of r bustion turbines. By 2010 the generating capabiny: combined-cycle plants increases more than sixfait, as the generating capability of combustion turbines m than doubles. More than four-fifths of the new sumption is supplied by increased domestic products The remainder comes from increased imports, prine from Canada.

Two-thirds of the production increase between 1986 an 2010 is expected to come from onshore resources in de lower 48 States; the rest is expected to come from Alast and lower 48 offshore resources. More producti comes from onshore lower 48 resources, becaus roughly 75 percent of current proved reserves in located onshore, and continued technology improve ments make development of the vast onshore unconver tional resources more economical. Wellhead prices moderately in the reference case through 2010, reflecting increased consumption and its impact on resources, 2 each type of production progresses from larger, man profitable fields to smaller, less economical ones.

Policies designed to reduce carbon emissions would boost natural gas consumption, production, impors. and prices, principally because natural gas consumption would displace coal consumption in the electricity sup ply sector. In response, gas production and imports would increase, pushing up prices. In the 3-percent below-1990 (1990-3%) case, for example, the natural gas share of the U.S. energy market is projected to increase from 24 percent in 1996 to 35 percent in 2010, compared with an increase of only 2 percentage points in the refer ence case. Following the imposition of a carbon pric higher prices for natural gas eventually would bring gas into competition with conservation (i.e., demand reduc tion) and renewable fuels, slowing the growth of gas consumption and prices.

Natural Gas Consumption

Natural gas plays a key role in the transition to lower carbon emissions, because it allows fuel users to consume the same number of Btu, while emitting less carbon. Thus, one strategy for fuel users seeking t