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the material, the increase in distance would be: Clements 13.98 miles, Vernalis 5.58 miles, Table <br /> Mountain 30.08 miles, and Waterford 17.78 miles. (See Alternative Site Hauling Routes Map, <br /> ESA GIS 2012 and Final EIR Figure 2-1) <br /> Generally speaking an emission inventory can be summarized as the `product of an emission rate <br /> (e.g. grams per pollutant emitted over a mile)and vehicle activity(e.g. miles driven per day). (See <br /> Emmission Modeling User Guide EMFAC, CA Air Resources Board 2007) Reduction in miles <br /> directly translates to a reduction in emissions. If state wide transportation distances were reduced by <br /> even 15 miles,then diesel fuel consumption would be reduced by 44 million gallons annually,truck <br /> emissions by 835 tons per year and greenhouse gasses by 400,000 metric tons. (See California <br /> Department of Transportation; Construction Aggregate Supply Limitations, Economic Impact <br /> Analysis 2007)The EPA EMFAC Model for San Joaquin identifies an increase in emissions per <br /> mile. With Munn Perkins as a local supply providing materials to the local service area the average <br /> distance increase of the facilities that would be able to supply material is 16.86 miles. (See <br /> Alternative Site Hauling Routes Map and San Joaquin County Truck Emissions EMFAC) <br /> F.4. Shorter Haul Routes Reduce Noise Impacts <br /> The EIR has identified in section 3-4 that based on the significance threshold criteria that noise <br /> from project asphalt plant operations is LESS THAN Significant, however,the single-noise <br /> events, although not in excess of the County noise standards,has increased the probability of <br /> causing awakenings which is POTENTIALLY Significant. However,the EIR identifies <br /> mitigation measures to reduce the noise exposure through the implementation of"noise <br /> mitigating operating parameters". There are no other mitigation measurses which have not been <br /> evaluated in the EIR, and all mitigation measures have been adopted as part of the Mitigation <br /> Monitoring Program(Attachment D) (See Munn Perkins Final EIR at p. 3.4-16 and <br /> Environmental Noise Assessment, Bollard Acoustical Consultants, Inc. August 18, 2010.) <br /> As identified above Caltrans is relying more frequently on nighttime projects. If the Munn <br /> Perkins Facility cannot furnish this material, it must then come from other facilities located at <br /> Clements, Table Mountain, Waterford, or Vernalis all resulting in longer hauls. (See Alternative <br /> Site Hauling Routes Map) Consider a pending Highway 99 project and a facility other than <br /> Munn Perkins providing the material, the increase in distance would be: Clements 13.98 miles, <br /> Vernalis 5.58 miles, Table Mountain 30.08 miles, and Waterford 17.78 miles. (See Area Facility <br /> Distance Maps, ESA GIS 2012 and Final EIR Figure 2-1). These longer routes not only have the <br /> potential to increase the probability of additional awakenings, above the Munn Perkins Facility, <br /> but are also not obligated to utilize the"noise-mitigating operating parameters" and would likely <br /> exceed the noise significance criteria as no mitigation is required for these longer haul distances. <br /> F.S. Regional Economic Benefits Effects <br /> Federal and State funding for freeways, state highways, and local roads and streets has greatly <br /> decreased. Much roadway work in San Joaquin County is made possible even on freeways and <br /> state highways by the sales tax paid by the people of San Joaquin County to the San Joaquin <br /> Council of Governments which in turn distributes the money to freeway and state highway <br /> projects either as advances or as a partner as well as for local streets and roads. (See Regional <br /> Transportation Plan 2011 SJCOG) <br /> 20 <br />