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County of San Diego 2005/2006 Greenhouse Gas Emissions Inventory

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Appendix D:<br />

Community <strong>Inventory</strong> Methodology<br />

This appendix expands on the description <strong>of</strong> methodology provided in Section 2, describing in more detail the data<br />

sources and processes used to calculate emissions in the community inventory.<br />

D.1 Overview <strong>of</strong> <strong>Inventory</strong> Contents and Approach<br />

The community inventory describes emissions <strong>of</strong> the major greenhouse gases from the residential,<br />

commercial/industrial, transportation, solid waste, and wastewater sectors. As explained in Section 2, emissions are<br />

calculated by multiplying activity data—such as kilowatt hours or gallons <strong>of</strong> gasoline consumed—by emissions<br />

factors, which provide the quantity <strong>of</strong> emissions per unit <strong>of</strong> activity. Activity data is typically available from electric<br />

and gas utilities, planning and transportation agencies and air quality regulatory agencies. <strong>Emissions</strong> factors are<br />

drawn from a variety <strong>of</strong> sources, including the California Climate Action Registry, the Local Governments<br />

Operations Protocol, and air quality models produced by the California Air Resources Board (CARB).<br />

In this inventory, all GHG emissions are converted into carbon dioxide equivalent units, or CO 2 e, per guidance in<br />

the Local Government Operations Protocol (LGOP). The LGOP provides standard factors to convert various<br />

greenhouse gases into carbon dioxide equivalent units; these factors are known as Global Warming Potential<br />

factors, representing the ratio <strong>of</strong> the heat-trapping ability <strong>of</strong> each greenhouse gas relative to that <strong>of</strong> carbon dioxide.<br />

The community inventory methodology is based on guidance from ICLEI’s draft International Local Government<br />

GHG <strong>Emissions</strong> Analysis Protocol (IEAP), as well as methods utilized in the <strong>San</strong> <strong>Diego</strong> <strong>County</strong> <strong>Greenhouse</strong> <strong>Gas</strong><br />

<strong>Inventory</strong> produced by the University <strong>of</strong> <strong>San</strong> <strong>Diego</strong>’s Energy Policy Initiatives Center (EPIC)—which evaluated<br />

emissions <strong>County</strong>-wide, both incorporated and unincorporated—and methods used in ongoing climate change<br />

planning work at SANDAG.<br />

D.1.1 <strong>Emissions</strong> Sources Included and Excluded<br />

In general, local jurisdictions should seek to measure all emissions <strong>of</strong> the six Kyoto Protocol greenhouse gases 30<br />

occurring within the jurisdictional boundaries. In practice, this level <strong>of</strong> detail may not be feasible for the local<br />

jurisdiction. The table below describes sources included in this community inventory, followed by sources that<br />

were excluded:<br />

30 CO 2, CH 4, N 2 O, SF 6 , perfluorocarbons (PFCs) and hydr<strong>of</strong>luorocarbons (HFCs)<br />

<strong>2005</strong>/<strong>2006</strong> <strong>San</strong> <strong>Diego</strong> <strong>County</strong> <strong>Greenhouse</strong> <strong>Gas</strong> <strong>Emissions</strong> <strong>Inventory</strong> XV

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