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Life Cycle Analysis Chapter j 10 193


                The Societal Test is structurally similar to the TRC Test. It goes beyond the
             TRC Test in that it attempts to quantify the change in the TRCs to society as a
             whole rather than to only the service territory (the utility and its ratepayers). In
             taking society’s perspective, the Societal Test utilizes essentially the same
             input variables as the TRC Test, but they are defined with a broader societal
             point of view. More specifically, the Societal Test differs from the TRC Test in
             at least one of five ways. First, the Societal Test may use higher marginal costs
             than the TRC Test if a utility faces marginal costs that are lower than other
             utilities in the state or than its out-of-state suppliers. Marginal costs used in the
             Societal Test would reflect the cost to society of the more expensive alternative
             resources. Second, tax credits are treated as a transfer payment in the Societal
             Test and thus are left out. Third, in the case of capital expenditures, interest
             payments are considered a transfer payment since society actually expends the
             resources in the first year. Therefore capital costs enter the calculations in the
             year in which they occur. Fourth, a societal discount rate should be used (refer
             to point 7 in Notes). Finally, marginal costs used in the Societal Test would
             also contain externality costs of power generation not captured by the market
             system. An illustrative and by no means exhaustive list of “externalities and
             their components” is given below (refer to the Limitations section for elabo-
             ration). These values are also referred to as “adders” designed to capture or
             internalize such externalities. The list of potential adders would include, for
             example:

             1. The benefit of avoided environmental damage: the CPUC policy specifies
                two “adders” to internalize environmental externalities, one for electricity
                use and one for natural gas use. Both are statewide average values. These
                adders are intended to help distinguish between cost-effective and non-
                cost-effective energy efficiency programs. They apply to an average sup-
                ply mix and would not be useful in distinguishing among competing supply
                options. The CPUC electricity environmental adder is intended to account
                for the environmental damage from air pollutant emissions from power
                plants. The CPUC-adopted adder is intended to cover the human and
                material damage from sulfur oxides, nitrogen oxides, volatile organic
                compounds (sometimes called reactive organic gases), particulate matter at
                or below 10 micron diameter, and carbon. The adder for natural gas is
                intended to account for air pollutant emissions from the direct combustion
                of the gas. In the CPUC policy guidance, the adders are included in the
                tabulation of the benefits of energy efficiency programs. They represent
                reduced environmental damage from displaced electricity generation and
                avoided gas combustion. The environmental damage is the result of the net
                change in pollutant emissions in the air basins, or regions, in which there is
                an impact. This change is the result of direct changes in power plant or
                natural gas combustion emission resulting from the efficiency measures,
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