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PR0521824
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Last modified
3/5/2020 12:23:11 PM
Creation date
3/5/2020 10:27:58 AM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2900 - Site Mitigation Program
File Section
FIELD DOCUMENTS
RECORD_ID
PR0521824
PE
2950
FACILITY_ID
FA0014819
FACILITY_NAME
CSU STANISLAUS / STKN MULTI-CAMPUS
STREET_NUMBER
510
Direction
E
STREET_NAME
MAGNOLIA
STREET_TYPE
ST
City
STOCKTON
Zip
95202
CURRENT_STATUS
01
SITE_LOCATION
510 E MAGNOLIA ST
QC Status
Approved
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EHD - Public
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• Preliminary Environmental Assessment Report <br /> Pittman Elementary School,Stockton,CA <br /> December 10,2003 <br /> Page 5 <br /> The paint chip samples were collected by removing the paint layers from the surface of the building. The <br /> paint on the warehouse building was chipping and peeling; therefore it was not necessary to use <br /> additional equipment to collect the paint chip samples. The paint chip samples were immediately placed <br /> in a resealable bag and shipped to EMSL Analytical, Inc. of Milpitas, California, which forwarded the <br /> samples to LA Testing of South Pasadena, California for analyses. <br /> 5.3 NATURAL GAS FIELD SAMPLES <br /> Soil vapor borings were installed at 15 locations on the site in a grid-like pattern, one location per acre. <br /> The borings were completed to approximately 20 feet bgs. Soil vapor.samples were collected at depths of <br /> 10 and 20 feet bgs in each boring for a total of 30 soil,vapor samples. Sample locations are indicated on <br /> Figure 6,Appendix A. <br /> The borings were advanced and samples collected using direct push technology. The borings were <br /> advanced using a Geoprobe percussion hammer driven sampler equipped with a two-inch outside <br /> diameter, four-foot long core barrel. Soil gas samples were collected from each direct push boring from a <br /> sample barrel fitted with a three-inch long, screened, expendable air sampling tip. The soil gas sampling <br /> tip was advanced to the target depth, opened, and the sample tubing purged of ambient air with a vacuum <br /> pump. One-liter Tedlar bags were checked for vacuum seal integrity, then connected to the purged <br /> sampling tube with a 10-micron filter and a soil gas sample was collected. Each Tedlar bag was labeled <br /> for sample identification. The soil vapor samples were analyzed for methane and hydrogen sulfide. The <br /> samples were shipped under chain-of-custody procedures via overnight carrier to Air Toxics Ltd. in <br /> • Folsom, Califomia, for analyses. Upon completion of the drilling and sampling, the borings were grouted <br /> with cement slurry containing three to five percent bentonite. The soil gas sampling equipment was <br /> cleaned prior to collecting each sample. The cleaning procedures consisted of washing in a solution of <br /> laboratory-grade, non-phosphate detergent and deionized water, and double rinsing with deionized water. <br /> 5.4 EASTERN FORMER UNDERGROUND STORAGE TANKS SITE SAMPLES <br /> Soil vapor borings (VB-5 through VB-6) were installed at four locations along the eastern site boundary. <br /> Three borings were installed approximately 30 feet apart from each other starting at the northern side of <br /> the warehouse building. One boring was installed approximately 30 feet west of the other borings. The <br /> borings were completed to groundwater, approximately 40 feet bgs..Soil vapor samples were collected at <br /> depths of five and 15 feet bgs in each boring for a total of eight soil vapor samples. Groundwater samples <br /> were also collected from the borings. Sample locations are indicated on Figure 5, Appendix A. <br /> The borings were advanced and samples collected using direct push technology. The borings were <br /> advanced using a Geoprobe percussion hammer driven sampler equipped with a two-inch outside <br /> diameter, four-foot long core barrel. Soil gas samples were collected from each direct push boring from a <br /> sample barrel fitted with a three-inch long, screened, expendable air sampling tip. The soil gas sampling <br /> tip was advanced to the target depth, opened, and the sample tubing purged of ambient air with a vacuum <br /> pump. Six-liter Summa canisters were checked for vacuum seal integrity, then connected to the purged <br /> sampling tube with a 10-micron filter and a soil gas sample was collected. The Summa canisters were <br /> checked for appropriate vacuum pressure after sample collection. Each Summa canister was labeled for <br /> sample identification. <br /> 4M , <br /> IL 41 CONDOR <br />
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