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FIELD REPORT <br /> WELL INSTALLATION <br /> SAN JOAQUIN COUNTY MOSQUITO ABATEMENT DISTRICT <br /> LODI FACILITY, LODI, CALIFORNIA <br /> On July 14, 1992, ROY F WESTON, INC. (WESTON) conducted a site investigation at the <br /> San Joaquin County Mosquito Abatement District (SJCMAD) facility in Lodi, California <br /> (Figure A-1) This investigation was performed to gain further information on the extent of <br /> petroleum hydrocarbon compounds in soil and groundwater at the site All work was performed <br /> in accordance with the WESTON Work Plan dated April 1, 1992. <br /> Drilling and Sampling <br />' The monitoring well boring was drilled using 8-inch hollow-stem augers and a truck-mounted <br /> drill ng Soil samples for lithologic description were collected using a 5-foot-long continuous- <br /> core barrel sampler The sampler was placed inside the first 5 feet of auger and extended <br /> I approximately 6 inches below the end of the auger during drilling operations which allowed for <br /> the collection of relatively undisturbed soil samples Soil samples were collected for potential <br /> laboratory analyses at 10 foot intervals using a California-modified split-spoon sampler lined <br /> with three 2-inch-diameter by 6-inch-long brass liners These samples were field tested for <br /> organic compounds using an HNu photoionization detector (PID) Subsurface samples were <br /> collected by drilling to the appropriate depth and then driving the sampler ahead of the auger <br /> using a 140-pound drive hammer The number of blows required to advance the sample 6 <br /> inches was recorded on the boring logs The well log for BAW-4 is included at the end of this <br /> field report <br /> One brass liner from each sample interval was preserved for Potential shipment to the <br /> laboratory. The brass liner selected for shipment was preserved by sealing both ends with <br /> Teflon sheeting and tight-fitting plastic caps. Each liner was labeled with a unique sample <br /> number, boring number, depth of sample, site name, date, time of collection, and any other <br /> pertinent information. After sample preparation, the brass liner was placed in a ziplock plastic <br /> bag in a cooled ice chest pending delivery to the laboratory No soil samples were submitted <br /> to the laboratory for chemical analyses because there were no above-background volatile organic <br /> compound (VOC) levels detected with the PID field screening instrument <br /> Field screening for VOCs was performed on soil from one of the brass liners from each 10-foot <br /> sample interval. The headspace-screening technique involved placing a portion of each sample <br /> into a clean resealable plastic bag and promptly sealing the bag After a minimum of five <br /> minutes, to allow for volatilization of any constituents that may have been present, a PID probe <br /> was inserted into the bag and a measurement was recorded. Results of the screening are <br /> presented on the boring log The PID was calibrated daily using isobutylene as the calibration <br /> gas. <br />' MXC\R"S\S1CMAa WP A - 1 10/14192 <br />