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FINAL Supplemental EIS/EIR

Acquisition of Additional Water for Meeting the San Joaquin River Agreement Flow Objectives, 2000 – 2010


11. ENERGY PRODUCTION

Index

11.1 AFFECTED ENVIRONMENT

Energy resources in the Project Area consist of hydroelectric power generation. Hydroelectric power generation plants provide approximately 24 percent of California’s electrical generation capacity. The Central Valley Project (CVP) hydropower system provides a significant portion of the available energy to the San Joaquin Valley. The CVP system of power plants and pumping plants has an installed capacity of 749 megawatts (MW). Most of the power that is generated from the CVP system is used to operate CVP pumping plants or is sold to public agencies.

The major storage reservoirs that supply water for hydroelectric power generation located in the Project Area are New Don Pedro Reservoir and Lake McClure. Hydroelectric power generation facilities located downstream of these reservoirs include the New Don Pedro Project located on the Tuolumne River and the Exchequer, McSwain, and Merced Falls projects located on the Merced River.

11.1.1 New Don Pedro Project

The New Don Pedro Project (NDPP) is located at the western edge of Tuolumne County on the Tuolumne River. It is owned and operated jointly by Modesto Irrigation District (MID) and Turlock Irrigation District (TID). The NDPP consists of the New Don Pedro Dam, New Don Pedro Reservoir, and the New Don Pedro Powerhouse (FERC 1996). In addition to providing water, flood control, and recreational opportunities, the NDPP system produces hydropower. The system has four dams and associated powerhouses, as described in Table 11-1. MID and TID own 31.54 percent and 68.46 percent, respectively, of the New Don Pedro hydroelectric plant. This equates to approximately 63 and 136.2 MW, respectively, of the power produced.

Table 11-1
Hydroelectric Power Facilities Located on the Lower Tuolumne River

Reservoir operations at NDPP are controlled by various agreements between the City and County of San Francisco, MID and TID, the U.S. Army Corps of Engineers, and California Department of Fish and Game as well as Federal Energy Regulatory Commission license articles. The NDPP has a minimum flow requirements schedule below New Don Pedro Dam to protect fishery resources.

11.1.2 Exchequer, McSwain, and Merced Falls Projects

The Exchequer, McSwain, and Merced Falls projects (Table 11-2) are located downstream of Lake McClure on the Merced River in Mariposa County. The Exchequer and McSwain projects are owned and operated by Merced Irrigation District. The Merced Falls Project is owned by Pacific Gas & Electric Company. Both the Exchequer and McSwain projects include storage facilities, but the Merced Falls Project does not.

Table 11-2
Hydroelectric Power Facilities Located on the Lower Merced River

11.2 ENVIRONMENTAL CONSEQUENCES AND MITIGATION MEASURES

The production of electricity from falling water is a significant source of energy in the Project Area. Major factors that influence hydrogeneration operations include reservoir storage and upstream water regulation and supply, downstream water needs, applicable license and permit requirements, and electricity demand (which fluctuates according to the time of the year, weather conditions, and the economics of the energy market). Releases from upstream reservoirs are dependent on not only upstream water sources (principally from snow melt), and the nature and extent of droughts, but also electricity demand, water rights agreements, other water supply contracts, and minimum downstream streamflow requirements.

11.2.1 Key Impact Issues and Evaluation Criteria

This section of the SEIS/EIR examines the issues associated with potential power production from reservoir releases to meet the Project purpose. Power consumption from activities such as pumping are not addressed in this SEIS/EIR because the Proposed Action does not call for a significant amount of pumping of water over what already occurs under existing conditions to deliver surface water and groundwater. There is no potential for indirect impacts to groundwater pumping to occur. The key issue is to what extent the early release of water (to meet Project objectives) would affect hydroelectric power production.

Hydroelectric generation projects depend upon an upstream water source, such as a storage reservoir and the change in elevation between the source and the discharge point. The electricity is generated in the powerhouse, which may be located at the base of the dam forming the reservoir or farther downstream. The amount of energy generated directly depends upon both the amount of water run through the powerhouse turbines and on the difference in elevation between the water in the reservoir and the powerhouse. Thus, the higher the elevation of the water in the storage reservoir, the greater the potential for power production.

Power produced during the peak energy demand period is more valuable than that produced during lower demand periods. Hydropower is an energy source that can be turned on and off quickly, and is therefore employed to meet peak loads when possible. In California, these peak loads typically occur in the summer when maximum groundwater pumping, industrial, and air conditioning demands occur. Reductions in a hydroelectric plant’s ability to meet peak load requirements accelerates the need for additional peaking resources and increases utility costs (McCann 1994, cited in State Board 1998).

11.2.2 Environmental Consequences

The Proposed Action would result in higher flows in April or May in some years than would occur under the No Action Alternative. The model estimates that supplemental water would come entirely from either New Don Pedro Reservoir or Lake McClure; in reality, the water could come from either one reservoir or the other or a combination of both, up to 47,000 acre-feet total. The model results show that achieving these flows requires a shift in reservoir operation that includes "borrowing" from storage to make these spring releases and "paying back" the borrowed water during some future winter or spring months when water in excess of present commitments is available.

The projected reservoir storage capacity and flow figures were obtained from the hydrologic model results, contained in Appendix A. Of concern to the energy impact analyses is the fact that the model results include the New Melones Interim Plan of Operation (Reclamation 1997b), which has been in effect for over 2 years.

11.2.2.1 Proposed Action on the Tuolumne River

The changes in water storage based on the Proposed Project from the No Action Alternative were determined for both the April and May model results, as reported in Appendix A. In the supplemental Hydrologic Analysis (Appendix A), the model results indicate that Proposed Project releases would only occur during approximately 10 percent of the years during the modeled period of 1922 through 1992. The additional releases would range from 2,000 acre-feet to 46,000 acre-feet during those years affected by the Proposed Project.

New Don Pedro Reservoir

An elevation difference was calculated from the difference in storage for New Don Pedro Reservoir during those months affected by the supplementary Vernalis Adaptive Management Plan (VAMP) releases. The energy production (GWh) was calculated using values provided by TID that related kilowatt-hours per acre-foot for each foot of reservoir elevation.

No Action. The No Action Alternative represents current conditions. The average annual generation for the New Don Pedro power plant is 618 GWh. The average annual generation for the entire state of California in 1995 was a total of 51,660 GWh. In other words, the New Don Pedro plant produces approximately 1.2 percent of the state’s total power.

Proposed Action. The Proposed Action would result in changes in calculated energy production from the No Action Alternative as follows:

  • Supplementary VAMP Release: During the months with a supplemental VAMP release, energy production would increase (up to the capacity of the New Don Pedro and La Grange Auxiliary powerhouses) as more water is made available for generation. The Turlock Lake and Stone Drop powerhouses would be unaffected because no change in flow or head would result from the supplementary VAMP release at these facilities.
  • Head Effects: During the months following a supplemental VAMP release, energy production at New Don Pedro Powerhouse would decrease because of the reduced reservoir elevation. No other generating facilities would be impacted.
  • Replacement of Supplementary VAMP Releases: During months when runoff is available such that New Don Pedro Reservoir can be refilled, energy production at New Don Pedro Reservoir and La Grange Auxiliary powerhouses would decrease (typically during periods when in the absence of supplementary VAMP, releases would be made to prevent encroachment into the flood control pool).

The net results for the New Don Pedro Powerhouse for the years affected are presented in Table 11-3 assuming an April supplemental VAMP release, and Table 11-4 assuming a May supplemental VAMP release. These results show a total net loss of generation of 22 GWh (May releases) and 26 GWh (April releases) over the 71 years studied, or if equated to an annual basis, a loss of  0.31 and 0.36 GWh/year. This is approximately 0.05 percent of the average annual generation at this facility.  This potential loss in generation translates into an average loss of supply for 400 to 500 homes for 1 month. Given that the current energy situation in California affects the entire state, these values would be considered insignificant when compared to California’s total housing units that number over 10.3 million (Gaquin and Littman 2000). This change in energy production is considered insignificant in terms of effects on the California energy market. The monetary loss to the reservoir owners due to the decreased energy production could be offset in some years by the sale of the supplemental water, and is therefore considered insignificant.

Detailed calculations were not performed for the La Grange Auxiliary Powerhouse. By inspection the impacts were determined to be insignificant because of the relative size of La Grange compared to New Don Pedro, and because there are no decreased head elevation effects at LaGrange.

11.2.2.2 Proposed Action on the Merced River

The changes in water storage based on the Proposed Project from the No Action Alternative were determined for both the April and May model results, as reported in Appendix A. In the supplemental Hydrologic Analysis (Appendix A), the model results indicate that Proposed Project releases would only occur during approximately 10 percent of the years during the modeled period of 1922 through 1992. The additional releases would range from 2,000 acre-feet to 46,000 acre-feet.

Table 11-3
Change in Energy Production for New Don Pedro Reservoir with April Releases, Affected Months Only

Lake McClure

An elevation difference was calculated from the difference in storage for Lake McClure during those months affected by the supplemental VAMP releases. The energy production (GWh) was estimated for Lake McClure using values developed by URS based on the procedure provided by TID for New Don Pedro Reservoir relating kilowatt-hours per acre-foot for each foot of reservoir elevation.

No Action. The No Action Alternative represents current conditions. The average annual generation for the Exchequer Power Plant is 316 GWh. The average annual generation for the entire state of California in 1995 was a total of 51,660 GWh. In other words, the Exchequer Plant produces less than one percent of the state’s total power.

Proposed Action. The Proposed Action would result in changes in calculated energy production from the No Action Alternative as follows:

  • Supplementary VAMP Release: During the months with a supplemental VAMP release, energy production would increase (up to the capacity of the Exchequer, McSwain, and Merced Falls powerhouse) as more water is made available for generation. Due to limitations on the Exchequer generator capacity, supplemental VAMP releases in May would often result in no increase in energy production.)

Table 11-4
Change in Energy Production for New Don Pedro Reservoir with May Releases, Affected Months Only

  • Head Effects: During the months following a supplemental VAMP release, energy production at Exchequer would decrease because of the reduced reservoir elevation. No other generating facilities would be imported.
  • Replacement of Supplementary VAMP Releases: During months when runoff is available such that Lake McClure can be refilled, energy production of Exchequer, McSwain, and Merced Falls powerhouses would decrease (typically during periods when in the absence of supplementary VAMP, releases would be made to prevent encroachment into the flood control pool).

The net results for the Exchequer Powerhouse for the years affected are presented in Table 11-5, assuming an April supplemental VAMP release and Table 11-6, assuming a May supplemental VAMP release. These results show a total net loss of generation of 19 GWh (May releases) and 78 GWh (April releases) over the 71 years studied (for both April and May releases), or if equated on an annual basis, a loss of 0.26 GWh and 1.10 GWh/year. This is an average of approximately 0.21 percent of the average annual generation at this facility.  This potential loss in generation translates into an average loss of supply for 350 to 1,500 homes for 1 month. Given that the current energy situation in California affects the entire state, these values would be considered insignificant when compared to California’s total housing units that number over 10.3 million (Gaquin and Littman 2000).  This change in energy production is considered insignificant in terms of effects on the California energy market. The monetary loss to the reservoir owners due to the decreased energy production could be offset in some years by the sale of the supplemental water and is, therefore, considered insignificant.

Table 11-5
Change in Energy Production for Exchequer (Lake McClure) with April Releases, Affected Months Only

Detailed calculations were not performed for the McSwain and Merced Falls powerhouse. By inspection, the impacts were determined to be insignificant because of the relative size of these facilities compared to Exchequer, because of the changes in flow offset and because there are no decreased reservoir elevation effects at McSwain and Merced falls.

11.2.3 Impact Summary and Mitigation of Impacts

  • If the supplemental water was released entirely from New Don Pedro Reservoir, the net loss in generation from the New Don Pedro Power Plant would be between 22 GWh and 26 GWh over the model study period, or from 0.31 GWh/year to 0.36 GWh/year. This change in energy production is considered insignificant, and no mitigation is necessary.
  • If the supplemental water was released entirely from Lake McClure, the net loss in generation from the Exchequer Powerhouse would be between 19 GWh and 78 GWh over the model study period, or from 0.26 GWh/year to 1.10 GWh/year. This change in energy production is considered insignificant, and no mitigation is necessary.
  • Impacts at the smaller downstream powerhouses were determined by inspection to be insignificant, with minor increases possible during periods of supplemental VAMP release offset by decreases during periods when storage in replaced in the upstream reservoir(s).

Table 11-6
Change in Energy Production for Exchequer (Lake McClure) with May Releases, Affected Months Only

Final SEIS/EIR
CH 11

March 13, 2001

 


Dennis W. Westcot, Project Administrator
San Joaquin River Group
716 Valencia Ave.
Davis, CA 95616-0153
(530) 758-8633
westcot-sjrga@sbcglobal.net

For information regarding this web site, contact the Modesto Irrigation District.