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sbl 6.2.1 Direct Reading Instrumentation <br /> As a precautionary measure, on-site worker exposure to airborne contaminants may be <br /> ' monitored during intrusive site activities. When pyroytic oil is encountered, a <br /> calibrated photoionization detector [PID] with a lamp strength of 10.6 eV] will be used <br /> onsite. The PID will not be used to determine changes in respiratory protection, <br /> however it will be used as a scanning device, to monitor and document changes in <br /> exposure to volatile organic compounds [VOCs]. The meter detects total hydrocarbons <br /> in parts per million. Specific chemical compounds are not detected, although some <br /> extrapolation of data may occur through familiarity of the instrument as well as <br /> expertise in industrial hygiene practices and the appropriate sampling strategy program. <br /> ' Note: Real time dust monitoring will not be conducted at the site. Instead the use of <br /> samples collected for laboratory analyses will be instituted at the project to <br /> ,j determine the migration of particulates. <br /> ' 6.2.2 Employee Exposure Assessment <br /> ,i SBES developed an air monitoring strategy, which includes the collection of personal <br /> i air samples. Prior to collection, and in keeping with good standards of industrial <br /> hygiene practice, the laboratory was consulted as to the best sampling methods for <br /> detecting the suspected contaminants. The sampling strategy was developed in <br /> accordance with the collection criteria outlined in the NIOSH [National Institute of <br /> '} Occupational Safety and Health], OSHA [Occupational Safety and Health <br /> -} Administration] and EPA [Environmental Protection Agency] Methodologies. This <br /> section details the sampling strategy, methodologies and analyses that will be used to <br /> -i monitor the following contaminants and document their levels in the exclusion and <br /> ;) contamination reduction zones. [Refer to Table 6-1 for details]. <br /> The selective monitoring of high-risk workers [i.e., heavy eQuipment operators, <br /> laborers, etc. approximating contaminated areas], will be conducted. This approach is <br /> based on the rationale that the probability of significant exposure varies directly with <br /> distance from the source. If workers closest to the source are not significantly exposed, <br /> than all other workers are, presumably, also not significantly exposed and therefore do <br /> not reQuire daily monitoring. <br />.' Since occupational exposures are linked closely with active material handling, personal <br /> v air sampling should not be necessary until site mitigation has begun. Personal <br /> monitoring samples will be collected in the breathing zone (placed on the worker's <br /> lapel]. These samples represent the actual inhalation exposure of workers who are not <br />-j wearing respiratory protection and the potential exposure of workers who are wearing <br /> .,r respirators. <br /> Samples will be collected every day during the Tracy Tire Fire Remediation Project. <br /> j <br /> Each day samples will be collected for antimony, arsenic, cadmium, chromium lead, <br /> Sb Environmental Services,ALC O October,2003 California Integrated Waste Management Board <br />- Site Specific Health and safety Plan Page 39 or 62 Tracy Tire Fire Remediation Project <br />