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WORK PLANS_CASE 1
Environmental Health - Public
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WORK PLANS_CASE 1
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Last modified
3/6/2020 3:53:57 PM
Creation date
3/6/2020 3:00:01 PM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2900 - Site Mitigation Program
File Section
WORK PLANS
FileName_PostFix
CASE 1
RECORD_ID
PR0506313
PE
2950
FACILITY_ID
FA0000514
FACILITY_NAME
MAIN STREET SHELL*
STREET_NUMBER
1071
Direction
N
STREET_NAME
MAIN
STREET_TYPE
ST
City
MANTECA
Zip
95336
APN
21707011
CURRENT_STATUS
02
SITE_LOCATION
1071 N MAIN ST
P_LOCATION
04
P_DISTRICT
003
QC Status
Approved
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METHODS <br /> Soil Sampling <br /> Soil borings and soil sampling will be performed under the direction of a State of <br /> California registered professional engineer or geologist. The soil borings will be advanced <br /> to a depth of approximately five below grade by using a hand auger. The soil borings will <br /> be advanced, below five feet to final depth, using a truck-mounted hollow-stem auger <br /> drilling rig. <br /> To reduce the possibility of cross-contamination between boreholes, all downhole drilling <br /> equipment will be steamed cleaned between each boring. To reduce cross-contamination <br /> between samples, the split-barrel sampler will be washed in a soap solution and double- <br /> rinsed between each sampling event. <br /> Soil sampling will be done in accordance with ASTM 1586-84. Using this procedure, a <br /> two-inch O.D. split-barrel sampler or a two-inch I.D. California-type sampler is driven into <br /> the soil by a 140-pound weight falling 30 inches. After an initial set of 6 inches, the <br /> number of blows required to drive the sampler an additional 12 inches is known as <br /> penetration resistance, or the "N" value. The N value is used as an empirical measure of <br /> the relative density of cohesionless soils and the consistency of cohesive soils. <br /> Upon recovery, a portion of the soil sample will be placed into a glass jar and sealed for <br /> later screening with a PID/OVA. Another portion of the soil sample will be used for class- <br /> ification and description. That part of the soil sample collected in a brass tube within the <br /> California-type sampler will be stored at approximately <br /> 4° C for transport to the laboratory. <br /> Soil Classification <br /> .r <br /> As the samples are obtained in the field, they are classified by the engineer or geologist <br /> in accordance with the Unified Soil Classification System (USCS). Representative portions <br /> — of the samples are then returned to the laboratory for further examination and for <br /> verification of the field classification. Logs of the borings indicating the depth and iden- <br /> tification of the various strata, the <br /> N value, and pertinent information regarding the method of maintaining and advancing the <br /> borehole are also made. <br /> Soil Sample Screening: Portable Photoionization Detector Method <br /> After soil sample jars have been brought to ambient temperature, the head space of the <br /> y soil sample jars will be screened with a portable photoionization detector equipped with <br /> a 10.2 eV lamp calibrated to benzene for direct reading in ppm. The sample jar lid will be <br /> opened and the detector probe immediately placed within the head space of the jar. The <br /> highest observed reading will be recorded. <br />
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