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Quantifying GHG Emissions <br /> 6.2 Operational GHG Emissions <br /> CaIEEMod estimates operational emissions of CO2, N20,and CH4 generated by area sources,energy <br /> use,vehicle trips (i.e., mobile sources),waste generation, and water use and conveyance. <br /> Operational emissions should be calculated for year 2030, rather than the plan/project buildout <br /> year, in order to provide an appropriate comparison of project emissions to the year 2030 <br /> threshold. <br /> Area Source Emissions <br /> Area sources include GHG emissions that would occur from the use of landscaping equipment, <br /> hearths,and woodstoves,which emit GHGs associated with the equipment's fuel combustion.The <br /> landscaping equipment emission values in CaIEEMod are derived from the 2011 Off-Road <br /> Equipment Inventory Model.31 Emission rates for combustion of wood and natural gas for wood <br /> stoves and fireplaces are based on those published by the U.S. EPA in Chapter 1.9 of AP-42. <br /> Typically, no adjustments to landscaping equipment inputs are necessary.The number of hearths <br /> and woodstoves should be adjusted in CaIEEMod to reflect the project design. <br /> Energy Use Emissions <br /> GHGs are emitted on-site during the combustion of natural gas for cooking, space and water <br /> heating, and decorative uses and off-site during the generation of electricity from fossil fuels in <br /> power plants. CaIEEMod estimates GHG emissions from energy use by multiplying average rates of <br /> residential and non-residential energy consumption by the quantities of residential units and non- <br /> residential square footage entered in the land use module to obtain total projected energy use.This <br /> value is then multiplied by electricity and natural gas GHG emission factors applicable to the <br /> plan/project location and utility provider. Building energy use is typically divided into energy <br /> consumed by the built environment and energy consumed by uses that are independent of the <br /> building,such as plug-in appliances. Non-building energy use, or"plug-in energy use,"can be further <br /> subdivided by specific end-use(refrigeration, cooking, office equipment, etc.). In California,Title 24 <br /> governs energy consumed by the built environment, mechanical systems, and some types of fixed <br /> lighting. <br /> Electricity emissions are calculated by multiplying the energy use by the carbon intensity of the <br /> utility district per kilowatt hour.32 Projects would be served either by EBCE or by PG&E. The specific <br /> energy intensity factors (i.e.,the amount of CO2, CH4, and N20 per kilowatt-hour)for the applicable <br /> utility should be used in the calculations of GHG emissions. <br /> As of publication of this guidance document,the current iteration of Title 24 included the 2019 <br /> Building Energy Efficiency Standards. In accordance with Section 150.1(b)14 of the 2019 Building <br /> Energy Efficiency Standards, all new residential uses three stories or less must install photovoltaic <br /> (PV)solar panels that generate an amount of electricity equal to expected electricity usage.The <br /> calculation method contained in Section 150.1(b)14 of the 2019 Building Energy Efficiency Standards <br /> should be utilized to estimate the number of kilowatts of PV solar panels that would be required for <br /> a residential project three stories or less. In addition, modeling should account for local regulations <br /> 311bid. <br /> 321bid. <br /> Draft 33 <br />