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PR0523718
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Last modified
2/14/2019 12:48:06 PM
Creation date
2/14/2019 10:38:15 AM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2900 - Site Mitigation Program
File Section
FIELD DOCUMENTS
RECORD_ID
PR0523718
PE
2950
FACILITY_ID
FA0015997
FACILITY_NAME
SJ REGIONAL TRANSIT
STREET_NUMBER
0
STREET_NAME
CHANNEL
STREET_TYPE
ST
City
STOCKTON
Zip
95205
CURRENT_STATUS
01
SITE_LOCATION
0 CHANNEL ST
QC Status
Approved
Scanner
WNg
Tags
EHD - Public
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kn KLEINFELDER <br /> ' For additional details regarding g g soil sampling and handling methodology please refer to the <br /> section below. <br /> ' Based onrelimin <br /> p ary soil sampling results, additional soil samples were collected on December <br /> ' 16, 2004 at location TPI using the same equipment, operator and sampling methodology as <br /> previously described for the original test pits. A deeper soil sample was collected at location TP- <br /> 1 at depths of 9 and 15 feet bsg. A lense of discolored soil approximately 6-inches thick was <br /> ' noted at approximately 6 feet bsg. Based on the former sampling depth and location, it appeared <br /> the base of the former TPI soil sample (TP 1-4') was likely advanced into a portion of this lense. <br /> Test Pit 1 was advanced to depths of 9 and 15 feet bsg, and two additional samples were <br /> ' collected at these depths. Additional soil discoloration and odor was not noted at these depths or <br /> below the discolored lense noted at approximately 6 feet bsg. <br /> Sample Collection and Handling <br /> The stainless steel hand auger, sampler and sample tubes were cleaned between locations with a <br /> ' Liquinox® (laboratory-grade d etergent) w ash f ollowed b y a p otable w ater and d istilled w ater <br /> rinse. The stainless steel tubes used for collecting the samples were then sealed following <br /> collection of the sample with Teflon° sheeting and tight-fitting plastic end caps. After <br /> ' collection, the soil samples were labeled, logged on a chain-of-custody form, and immediately <br /> stored in an iced cooler pending transportation to the analytical laboratory. <br /> ' The soil samples collected on November 30, 2004 were transported under chain-of-custody <br /> control to Kleinfelder's office and then transported by courier in a chilled container to Alpha <br /> Analytical Laboratory, Inc. (Alpha) of Sparks, Nevada. The chain-of-custody form was signed <br /> ' by each individual who handled the samples, including the sampler and the receiving employee <br /> at Alpha Analytical. Alpha is certified by the State of California to perform the analyses <br /> requested. The samples were analyzed on a standard 10 working day turnaround schedule for <br /> ' completion. The four discrete soil samples collected at each stockpile were requested to be <br /> composited by Alpha. Based on a requested rush turn around time, the two samples collected on <br /> December 16, 2 004 were s ubmitted t o a l ocal 1 aboratory, P recision E nviro-Tech o f S tockton, <br /> ' California. Sample handling was the same as described above, only Kleinfelder transported the <br /> samples in a ice chest directly to the laboratory the same day as samples were collected. <br /> ' ANALYTICAL RESULTS <br /> A.total of nine soil samples, seven discrete and two four point composite samples collected on <br /> November 30, 2004 were submitted for the following analyses: <br /> • Total Purgeable Petroleum Hydrocarbons (Gasoline Range) [TPH-G] by EPA Method <br /> 8015B/DHS LUFT <br /> • Benzene, toluene, ethylbenzene, xylenes [BTEX] by EPA Method 8260B <br /> • Total Extractable Petroleum Hydrocarbons as referenced to Diesel and Motor Oil [TPH- <br /> D/TPH-MO] by EPA Method 8015B/DHS LUFT <br /> 51726/ST05R157/DH:ly Page 3 of 7 <br /> 2005,Kleinfelder,Inc. February 8,2005 <br />
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