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ARCHIVED REPORTS_XR0005449
Environmental Health - Public
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99 (STATE ROUTE 99)
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19256
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2900 - Site Mitigation Program
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PR0540323
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ARCHIVED REPORTS_XR0005449
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Entry Properties
Last modified
11/19/2024 1:50:27 PM
Creation date
4/8/2020 2:38:27 PM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2900 - Site Mitigation Program
File Section
ARCHIVED REPORTS
FileName_PostFix
XR0005449
RECORD_ID
PR0540323
PE
2950
FACILITY_ID
FA0023049
FACILITY_NAME
TELFER HIGHWAY TECHNOLOGIES
STREET_NUMBER
19256
Direction
N
STREET_NAME
STATE ROUTE 99
City
ACAMPO
Zip
95220
CURRENT_STATUS
01
SITE_LOCATION
19256 N HWY 99
QC Status
Approved
Scanner
SJGOV\sballwahn
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EHD - Public
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Limited Soil and Groundwater Report-05/24/99 Page 8 <br /> Western 0,1,11 Spreading1preal,ng Site Project No 024 98 <br /> 6.0 SI'Z'E SOILS <br /> The site soils encountered beneath the site property during drilling consisted of brown silty sand to <br /> a depth between 8 to 9 314 feet bgs followed by an underlying layer of grey to brown sand, with the <br /> exception of boring B-3,which did not contain a sand seam at that elevation Below these layers of <br /> soil at a depth of between 12 and 13 feet bgs, a brownish-grey to brown clayey sand to silty sand was <br /> encountered to a depth of approximately 40 feet bgs However, a grey sand layer approximately 9 <br /> feet thick(at B-2) and a half-foot thick grey silty clay layer(at B-4), were encountered followed by <br /> a grey silty clay and grey-brown sand layer(at B-2) or a grey sand, grey-brown silty sand, and light <br /> ' grey sand layer (at B-4) At the time of sampling, petroleum hydrocarbon odors and soil <br /> discoloration were noted in the soil samples collected from borings B-1, B-2, and B-4 commencing <br /> at a depth of approximately 14, 4, and 12 feet bgs, respectively Analytical results later confirmed <br /> petroleum hydrocarbons within the soil at these three locations No indication of impacted soil was <br /> observed or confirmed by analytical results at borings B-3 and B-5 <br /> 7.0 SOIL. SAMPLING <br /> A total of 20 soil samples were selected during the drilling of borings B-1 through B-5 and submitted <br /> for laboratory analysis of TPH-d, TPH-k, TPH-g, MTBE, and BTEX The soil samples for borings <br /> B-2 through B-5 were collected using a 2 '/2-foot long, 2-inch 1 D steel split-spoon sampler <br /> containing three six-inch long stainless-steel or brass liners, while soul samples for boring B-1 were <br /> ' collected using a three-inch diameter, five-foot long split-spoon sampler containing no brass liners <br /> Each sampler used was decontaminated before and after each use by using a Tri-Sodium Phosphate <br /> ' wash solution and tap water The sampler was placed down the boring and driven into the ground <br /> approximately 18-inches using a 140-pound hammer, with the exception of boring B-1, which was <br /> continuously-cored <br /> ' Soil sampling intervals and initial sampling runs were used for visual classification of the underlying <br /> soil The soil sampling intervals were generally at depths of approximately 5, 10, 15, 20, 25, 30, 35, <br /> and 40 feet bgs Soil samples not submitted for laboratory analysis were used for visual identification <br /> of the underlying lithology <br /> ' 8.0 GROUNDWATER SA1J,IPII 2MG <br /> Because groundwater was encountered in only one of the exploratory soil borings, a total of one <br /> groundwater "grab"sample was collected from boring B-4 After boring B-4 was completed, the <br /> hollow-stem augers were left in-place for approximately one hour to prevent collapsing of the <br /> borehole and to assure that a representational groundwater "grab"sample could be collected from <br /> rthe borehole Groundwater samples were collected by placing a disposable bailer down the center <br /> of the auger to allow for an in-situ water sample collection The water sample was placed in three <br /> 40 rnl VOA vials containing HCL as a preservative for TPH-g and MTBE analysis and a one-liter <br /> amber bottle for TPH-d and TPH-k analysis The sample vials were filled with the collected <br /> groundwater until they overflowed, and were then sealed with Teflon-lined septa caps so that no air <br /> was trapped in the vial or bottle Once filled, each of the samples were inverted and tapped to test <br /> for air bubbles The groundwater water samples were contained in vials approved by the US EPA <br /> and the SFBRWQCB in accordance with EPA SW 849 Each sample container was properly labeled <br /> and contained the sample number, and date of sampling <br />
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