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Page IV.E-7ort Pa <br /> Draft Environmental Impact Report g <br /> Forward Inc. Landfill Expansion Project <br /> leachate. The existing Forward Landfill has a separate permit for land discharge of cannery <br /> wastes,but cannery wastes are not accepted for disposal. <br /> From an air quality perspective,the implementation of the project would potentially affect landfill <br /> gas(LFG)-related emissions (i.e., fugitive LFG and emissions from LFG control devices) and <br /> mobile source emissions from the increased haul vehicle activity(i.e.fugitive dust from roads and <br /> diesel particulate emissions). <br /> Based upon data from other landfills,toxic air contaminants(TAC) constituents within LFG <br /> typically consist of benzene, chloroform,methylene chloride,perchloroethylene (PCE), <br /> trichloroethylene(TCE),vinyl chloride(VC), as well as other TACs. Mobile sources emit diesel <br /> particulate matter (DPM), a TAC. TACs are also known as HAPS. Information about current TAC <br /> emissions from the landfill is presented in various tables provided in the SCS (2008) HRA. <br /> The anticipated closure date for the existing Forward Landfill is 2017. The expanded project <br /> would dispose a total of 8,668 tons per day, the same as currently permitted.In addition,the <br /> expanded project would accept 500 tons per day of recoverable materials at the MRF,5,487 tons <br /> per day of beneficial reuse materials,and 40,000 gallons of high moisture content waste. The <br /> proposed project assumes 960 versus 620 vehicles per day. This would occur over 7 days a <br /> week, as is the baseline case, with closure of the combined landfill being in extended 2032. <br /> These changes could affect the health and safety of workers at the landfill by potentially <br /> exposing them to a variety of contaminants in air, soil or water that are associated with the <br /> materials brought into the landfill. Fugitive dust with airborne contaminants could be inhaled, <br /> dermal contact and ingestion of contaminated soil and/or water could occur. <br /> As described earlier, the risk assessment completed by SCS was most sensitive to the diesel <br /> particulate emissions. Most of the increased cancer risk is due to the increased diesel particulate <br /> emissions from haul vehicles. The risk from moving haul vehicles accounts for over 80% of risk <br /> attributable to diesel particulate at the maximally exposed receptor and the maximally exposed <br /> occupied receptor. <br /> A summary of the key landfill operational commitments that result in a lessening of the risk <br /> factors in the proposed project are shown in Table IV.E-1, below, which compares the baseline <br /> assumptions with the proposed project assumptions. <br /> In addition, the following procedures are proposed as part of the project: <br /> • Use a total of 17 <br /> ieces of equipment (at any given time) over the life of the project to <br /> P <br /> minimize particulate discharge, will remain unchanged. <br /> • Operations at the combined landfill would be limited to a single working area at any <br /> given time. <br /> • All employees would be given appropriate training regarding the potential for exposure <br /> to hazardous materials. This training will include a 24-hour hazardous waste operations <br /> course and an annual 8-hour refresher course for personnel involved in the "load <br /> checking" program where the incoming loads are screened for hazardous materials. <br /> • The landfill would not accept any special waste that may potentially contain hazardous <br /> levels of regulated substances. <br /> • Dust control procedures specified in the Site Operations Plan (per the JTD) would use <br /> the application of fine water spray at a minimum of twice daily on the active soil- <br /> covered work areas, soil excavation areas, and soil stockpile areas where fugitive dust <br /> may exist. <br />