Laserfiche WebLink
i <br /> Kennedy/Jenks/Chilton <br /> i <br /> DRUM CONTENTS SAMPLING <br /> ' On 10 May 1990 and 11 May 1990, fluid samples were collected from the <br /> drums. Field activities were performed by Peregren and Kennedy/Jenks/ <br /> Chilton. All sampling personnel were health and safety trained in <br /> ' compliance with 29 CFR 1910 120 Fluid samples were collected using a <br /> Composite Liquid Waste Sampler (COLIWASA) which is an EPA recommended <br /> sampler for drums containing liquids. The COLIWASA allows for the <br /> 1 collection of a sample which is representative of potential vertical <br /> stratification of liquid waste contained within a drum Fluid collected <br /> from an individual drum was placed in two 100-milliliter amber glass <br /> ' vials with tight fitting caps. During sampling, a small amount of the <br /> fluid from each drum was placed into clear disposal containers for <br /> visual purposes. On the basis of a visual inspection, the drum contents <br /> were grouped according to visual characteristics. A total of nine <br /> groups were identified Composite fluid samples were then collected <br /> from each group. A total of nine groups were identified. Composite <br /> fluid samples were then collected from each group. The composite drum <br /> ' samples (CS-1 through CS-9) were collected in one-liter glass bottles <br /> for laboratory analyses. Composite fluid sample 55A/55B was collected <br /> from the one-gallon glass container in two 100-milliter amber glass <br /> vials for laboratory analyses. A strong pesticide-like odor was noted <br /> t while sampling the fluid contained within the glass bottle that was <br /> found in the warehouse Table 7 provides the schedule used for <br /> compositing drum samples <br /> After sample collection, the glass sampling containers were secured with <br /> tight fitting caps. A completed label was attached to each container <br /> 1 with the following information site name, collection date/time, sample <br /> number, sample depth, and collector's initials. Samples were temporari- <br /> ly stored and transported in a chilled ice-chest under Chain-of-Custody <br /> to the Kennedy/Jenks/Chilton Laboratory Division in San Francisco, <br /> California. <br /> LABORATORY ANALYSES RESULTS <br /> ' Drums <br /> Composite fluid samples CS-1 through CS-9, collected from the drums, <br /> ' were analyzed for organochlorine pesticides by EPA 8080 and for Total <br /> Petroleum Hydrocarbons by modified EPA Method 8015 Organochlorine <br /> pesticides were not detected above method detection limits in these <br /> ' samples However, the detection limits were elevated due to sample <br /> dilution required by the laboratory sample preparation procedures TPH <br /> were detected at concentrations ranging from 1) 0.40 mg/L to 6 7 mg/L <br /> as gasoline, 2) 23 mg/L to 650 mg/L as diesel fuel , and 3) 190 mg/L to <br /> 3,500 mg/L as motor oil . Table 8 provides the concentrations of TPH <br /> detected in the nine fluid samples collected A copy of the laboratory <br /> reports is included in Appendix A, Part 5. <br /> WPI13 5 2 882526.01 <br /> i <br />