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scales. The ppm scale was used for structure monitoring. The <br /> instrument was calibrated with a 2.5% methane mixture and was <br /> warmed up for approximately 10 minutes prior to monitoring. The <br /> methane level in open air at the labor camp varied from 0 - 20 ppm. <br /> Each building contains two apartments. Monitoring consisted of a <br /> complete walk-through of each apartment with an emphasis on <br /> incoming plumbing, electrical outlets, baseboards, behind stoves, <br /> and cracks (if encountered) . <br /> Results of the structure monitoring are shown on Table 1. Nineteen <br /> structures were monitored. The first 13 structures listed on table <br /> 1 are along the east edge of the labor camp from north to south. <br /> Structures 14-16 are along the north edge from east to west. <br /> Structures 17-19 are in the interior of the labor camp. Due to the <br /> low levels found in structures 14-19, the remainder of the interior <br /> structures were not monitored. <br /> It should be noted that a strong cleanser odor was detected in <br /> structures 1 and 2 . A pine sol type cleanser was used in both <br /> cases. We put the Gas Tech probe near an open bottle of the <br /> cleanser, and the needle exceeded 500 ppm. Therefore, we believe <br /> the cleanser had a significant impact on the readings. <br /> The tenants were using the gas range in the west half of structure <br /> #6. It is not clear whether this would cause the 85 ppm reading <br /> found in the kitchen area. <br />