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III. ENVIRONMENTAL SETTING,IMPACTS AND MITIGATION MEASURES <br /> B. AIR QUALITY <br /> Increases in particulate emissions associated with the project would primarily be related to new <br /> on-road motor vehicle trips, off-road mobile equipment use,increased municipal waste handling <br /> activities(up to 1,000 tpd)within the transfer station building, which includes construction and <br /> demolition debris handling(up to 400 tpd), and greenwaste operations(up to 150 tpd). Large- <br /> sized particulates typically fall out of the air within several hundred feet of the source. Based on <br /> the distance from the main transfer station operations to the nearest residences (approximately <br /> 400 feet), increases in large-sized particulates would not be considered to pose a significant <br /> nuisance impact. <br /> Respirable particulate matter(PM-10),including diesel particulates, are small enough to remain <br /> suspended in the air for longer periods and travel further than large-sized particulates. <br /> Table III.B-3 compares estimates of emissions of PM-10,a criteria air pollutant, and diesel <br /> particulates,a toxic air contaminant, under three scenarios. The first scenario represents existing <br /> (1999)conditions, where emissions are primarily a result of collection truck trips and employee <br /> trips. The second scenario represents existing plus project conditions in 2000 when project <br /> construction has been completed and operations at the site are at 60 percent of their full permitted <br /> capacity. The last scenario assumes that operation of the site at its full permitted capacity would <br /> begin in 2003. <br /> Emissions estimates shown in Table III.B-3 for on-road motor vehicles are based on daily trip <br /> generation information provided in the Transportation Circulation and Safety section,an assumed <br /> trip length of 10 miles for each type of one-way trip,except transfer truck trips,EMFAC7G <br /> composite vehicle emissions factors, and assumed average speeds(different speeds were assumed <br /> for different types of trips,e.g., 10 miles per hour for collection vehicles and 35 to 50 miles per <br /> hour for transfer truck trips). It is expected that initially transfer trucks would haul materials to <br /> Forward Landfill,North County Landfill,or Foothill Landfill, which are about 10 to 15 miles <br /> from the transfer station site. However,in the future refuse may be transferred to a more distant <br /> facility for disposal, such as WMI's landfill in Lockwood,Nevada, roughly 190 driving miles <br /> from the site. The emissions estimates shown in Table III.B-3 represent the worst case scenario <br /> when transfer trucks would travel the full distance to Nevada. Daily emissions from transfer <br /> trucks would be incrementally lower on the average day if loads were transferred to local landfills <br /> as is the case now. EMFAC7G is a motor vehicle emissions factor model developed by the state <br /> ARB. The estimates for on-road motor vehicles reflect the following number of daily vehicle <br /> one-way trips for each analytical scenario: 260 under existing conditions;482 under existing plus <br /> project conditions in 2000; and, 804 under existing plus project conditions in 2003. The <br /> estimates for"Total PM-10" shown in Table III.B-3 include exhaust,tire wear,brake wear, and <br /> entrained road dust. An emissions factor of 0.69 grams per vehicle-mile-traveled was used to <br /> estimate PM-10 emissions from entrained road dust for all vehicle types. Diesel-particulate <br /> emissions in Table III.B-3 reflect PM-10 exhaust emissions from diesel-powered vehicles and <br /> Storkton Scavenger Transfer Station Erpansion III.B.18 ESA/990190 <br />