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2900 - Site Mitigation Program
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PR0518364
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Last modified
6/14/2019 4:50:17 PM
Creation date
6/14/2019 4:48:56 PM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2900 - Site Mitigation Program
File Section
FIELD DOCUMENTS
RECORD_ID
PR0518364
PE
2950
FACILITY_ID
FA0013868
FACILITY_NAME
KRETH PROPERTY
STREET_NUMBER
11781
Direction
E
STREET_NAME
COMSTOCK
STREET_TYPE
RD
City
STOCKTON
Zip
95215
CURRENT_STATUS
01
SITE_LOCATION
11781 E COMSTOCK RD
P_LOCATION
01
P_DISTRICT
000
QC Status
Approved
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EHD - Public
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• <br /> • Mr. Harlin Knoll <br /> ' May 9, 2002 <br /> Page 2 of 3 <br /> push rig to <br /> advance the borings and collect soil samples. Soil samples were collected at 5-foot <br /> us a 13/a inch diameter by 24-inch long core sampler The valuation sampler <br /> was lined with contamination.clear <br /> A <br /> intervals g <br /> acetate sleeves, affording soil identification and subjective e <br /> ounds in <br /> photoiomzatio <br /> n detector (PID) was used to monitor the presence of volatileorganic <br /> omediately placed in <br /> the soil. Soil samples collected from each <br /> °of g4oC r for transport to a state-certified analytical <br /> on <br /> an ice chest refrigerated to a temperature <br /> laboratory under chain of custody protocol. Soil samples selected for analysis were ase <br /> observations and field screening results. <br /> The completed borings were backfilled to the ground surface with neat cement grout. No soil <br /> generated. All down-hole drilling and sampling equi nt Boriwas ngclocations are <br /> ontaminated <br /> cuttings were g rade detergent and rinsing with water <br /> by washing with a laboratory g <br /> shown on Figure 2. Soil boring logs are included in Attachment B. <br /> three soil samples were analyzed by Argon Laboratories (ELAP #2359) for gasoline <br /> A total oft hydrocarbons as gasoline <br /> oxygenate additives using EPA method 8260,toluene, ethylbenzene, xylenes (BTEX) using <br /> (TPHg) using EPA method 8015M, benzene, <br /> EPA method 8020, and total lead using EPA method 7420. <br /> RESULTS OF INVESTIGATION <br /> 1 from the ground surface to approximately 15 feet bgs was al soillds olorationsas silt. nore <br /> rlying the <br /> Soil <br /> silt, a bed of silty clay extends to at least 21 feet bgs. No abnormal <br /> h drocarbon odors were noted, and PID readings were at background levels in all samples collected <br /> y <br /> from both borings. Soil boring logs are included in Attachment . <br /> No TPHg, BTEX or gasoline oxygenate additives were detectedilin amdhe lessoil samples collected from <br /> rranged from 11 parts per <br /> borings SBI and SB2. Total lead concentration m the s p <br /> million (ppm) to 13 ppm, which are naturally-occurring levels. Analytical results of soil samples <br /> are summarized in Table 1. Laboratory reports and chain of custody documentation are included in <br /> Attachment C. <br /> SUMMARY <br /> Two soil borings were drilled and sampled in the former tankpit area. Soil in the investigation area <br /> was classified as silt and silty clay. No abnormal soil discoloration, petroleum hydrocarbon odors <br /> or elevated PID readings were noted in either boring SBI or SB2. No TPHg,s were conTEX s stent owrth <br /> line <br /> oxygenate additives were detected in soil samples and lead concentrations <br /> naturally occurring levels. <br /> \\GZA FS\SYSOl\Data\GROUNDZE\KRETH\swnletter.doc <br />
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