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Draft Removal Action Completion Report <br /> Neighborhood C, <br /> Mountain House,CA <br /> Page 7 <br /> soil movement activities for a total of 18 days between October 18 and November 27, 2013. The last two <br /> days (November 26 and 27), air monitoring was conducted because waste soil encapsulated in Great <br /> Valley Parkway was being excavated to make room for utility crossings. <br /> 3.6.1 Air Monitoring <br /> In consultation with DTSC, air monitoring was performed during Site activities in which contaminated or <br /> potentially contaminated materials were being disturbed, moved, or otherwise exposed to wind. The Air <br /> Monitoring Officer was responsible for implementing the Air and Meteorological Monitoring Plan. <br /> Chemical air monitoring procedures and results are discussed in Section 4 and 5 on the following pages. <br /> 3.6.1.1 Responsibilities of the Air Monitoring Officer <br /> The Air Monitoring Officer was properly trained in the use and maintenance of air monitoring and <br /> meteorological monitoring equipment. Responsibilities of the Air Monitoring Officer included: <br /> • Monitoring and documentation of dust levels at the work zone and property fencelines. The Site Air <br /> Monitoring Officer had the authority to stop work in the event that on Site activities generated dust <br /> levels that exceed the dust monitoring action levels defined below. The Air Monitoring Officer <br /> maintained on-Site meteorological instrumentation, documented meteorological conditions, and <br /> coordinated with off-Site meteorological professionals to identify conditions that may have required <br /> cessation of work(e.g., excessive winds). If wind speeds exceeded 25 miles per hour instantaneously <br /> or there was visual evidence of wind carrying dust off-Site, then a more aggressive approach to dust <br /> control was implemented immediately. Increased dust controls included additional spray-applied <br /> water from water trucks. <br /> • Assured that all air sampling equipment and media were properly calibrated and in good working <br /> condition. Real-time, data-logging dust monitors, Thermo Electron Corp. personaldataRAM, model <br /> pDR-1000AN/1200, were used to measure dust levels. The personaldataRAM instruction manual is <br /> included in Appendix D. Real-time information was posted daily and discussed with Site workers. <br /> • Recordkeeping activities and general Site safety support of the Site Manager. <br /> 3.6.1.2 Air Monitoring Strategy and Methods <br /> Prior to use each day, air and dust monitors were calibrated according to manufacturer's specifications. <br /> The Air Monitoring Officer monitored dust and dieldrin levels in the following general locations (Figure <br /> 6, Appendix A): <br /> • One fenceline monitoring location upwind using a real-time data-logging (15-minute intervals) <br /> dust monitor and an air sampler for dieldrin(west of the Site boundary,"upwind"). <br /> • Two fenceline monitoring locations downwind using real-time data-logging dust monitors and air <br /> samplers for dieldrin(at western Site boundary, "residences") and along Grant Line Road"Grant <br /> Line". <br /> • Work Zone: by a real-time mobile personal dust monitor at various locations where daily <br /> activities were taking place in the exclusion zone"work zone". <br /> The Air Monitoring Officer monitored and recorded the dust concentrations at the work zone and at the <br /> fenceline monitoring locations at approximately 30-minute intervals in general accordance with the <br /> RAW. The Air Monitoring Officer regularly checked the functionality of the dust monitors and air <br /> samplers. Work Zone and Fenceline Action Levels specified in the RAW are included in Table 1 on the <br /> following page. <br />