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C ITY OF S AN L EANDRO <br />S AN L EANDRO S HORELINE D EVELOPMENT P ROJECT EIR <br />EXHIBIT A: WORK SCOPE AND COSTS <br /> <br />THE PLANNING CENTER | DC&E 15 <br />MAY 1, 2013 <br /> <br />capita transportation targets for the Metropolitan Transportation Commission (MTC) for the <br />Bay Area for passenger vehicles under Senate Bill 375 (SB 375). The EIR will also include a <br />discussion of the City of San Leandro’s Climate Action Plan, adopted December 2009. <br /> <br />ii. Existing Greenhouse Gas Emissions Inventory <br />The existing land uses within the project site generate GHG emissions from transportation <br />sources (vehicles and boats), energy (natural gas and indirect emissions from purchased <br />electricity), area sources (landscape emissions, consumer products), indirect emissions from <br />water use and wastewater generation, and indirect emissions from waste disposal. The <br />existing GHG emissions inventory will be developed for the project based on the existing land <br />uses on-site and modeled using the CalEEMod for both existing and future (“No Project <br />Future Conditions”) emissions rates. Trip generation data for existing land uses will be <br />incorporated into the model. Model results from CalEEMod will be supplemented using <br />OFFROAD2011 for pleasure-crafts (i.e., boats) based on an estimate of existing boat use at <br />the marina. At present, the 465-berth boat harbor is approximately 40 percent occupied. We <br />will work with the City to obtain an estimate of existing harbor usage (e.g. based on <br />diesel/gas sales at the harbor and/or estimate of average annual daily/weekly use of the <br />marina). <br /> <br />iii. Project Greenhouse Gas Emissions Inventory <br />The Planning Center | DC&E will prepare a quantitative evaluation of project-related GHG <br />emissions. The evaluation will include potential emissions from transportation sources <br />(vehicles), energy (natural gas and indirect emissions from purchased electricity), area <br />sources (landscape emissions, consumer products), indirect emissions from water use and <br />wastewater generation, and indirect emissions from waste disposal. GHG emissions from the <br />construction inventory developed for criteria air pollutants (see Task 1.c) will also be <br />identified. Cumulative air quality impacts will also be described. We assume that changes in <br />carbon sequestration associated with changes in land cover (vegetation) would compose a <br />de minimus portion of the GHG inventory; and are therefore, not included. The future GHG <br />inventory will be developed for each project phase-based on the proposed land uses on-site <br />and modeled using CalEEMod. Trip generation data for existing land uses will be <br />incorporated into the model. The model will also account for reductions in emissions as a <br />result of federal, state, and regional GHG regulations that have been adopted and/or are <br />identified in the CARB Scoping Plan. Additional reductions from Project Design Features <br />(such as mixed-use features, increase in energy efficiency, etc.) will be modeled, as available. <br />The GHG emissions inventory for the project will be compared to BAAQMD’s per capita GHG