Laserfiche WebLink
3.0 FIELD INVESTIGATION AND RATIONALE <br /> This section describes the field activities and methods employed to obtain data through the collection <br /> of soil and/or groundwater samples Well boring N1W-12 was installed at the location proposed in <br /> the approved workplan dated January 6, 1999 <br /> 3.1 Soil Boring Methods and Installation of Groundwater Monitoring Wells <br />' One(1) soil boring, completed as groundwater monitoring well MW-12, was advanced to total depth <br /> of 73 feet bgs The location of the well bonng is shown on Figure 2 <br /> The Iocation of the boring was chosen based upon review of prior Site assessment data, discussions <br /> with PHS-EHD's personnel, and the accessibility to conduct field work The boring was advanced <br /> by Spectrum Drilling, Inc of Stockton, California, using a truck-mounted drill ng (CME-85), <br />' equipped with 8'/4-inch outside diameter (OD), hollow-stem, continuous-flight augers The augers <br /> were steam-cleaned pnor to drilling the boring The soil types encountered and other pertinent data <br /> were recorded on a field boring log, and described in accordance with the Unified Soil Classification <br />' System (USCS) Field boring logs are presented in Appendix A <br /> Soil cuttings generated during the drilling activities were placed in Department of Transportation- <br /> (DOT-) approved 55-gallon drums and stored on-site, pending disposal by Thrifty <br /> 3.2 Soil Sampling <br /> Soil samples were collected at 5-foot intervals through the hollow-stem auger using a California- <br /> modified spht-spoon sampler lined with 2-inch OD brass sleeves The samples were driven into the <br /> underlying soil by dropping a 140-pound hammer a distance of 30 inches (blow count) The brass <br /> sample tubes and split-spoon sampler were washed in an Alconox solution and double-nnsed with <br /> distilled water prior to each use <br /> The blow counts, recovery, and soil descriptions were recorded on the field logs One (1) brass <br /> sleeve filled with soil was capped, sealed, and labeled in accordance with EPA protocol, recorded on <br /> a chain-of-custody from, placed in a cooler at 4°C or less, and submitted to a California <br /> State-certified laboratory for the specified analyses <br />' 3.3 Field Screening of Soil Samples <br />' The material from the top brass sample sleeve was used for field screening The soil from this sleeve <br /> was placed in a sample container to approximately 50% capacity, shaken, and stored for a period of <br /> 15 minutes A standard head space reading was obtained for each soil sample using an HNu Systems <br /> Incorporated photoionization detector(PID) calibrated with isobutylene gas <br /> 1 <br /> A.11528J1 ASA 7 <br />