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Environmental Health - Public
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EHD Program Facility Records by Street Name
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LOWER SACRAMENTO
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7910
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3500 - Local Oversight Program
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PR0545441
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Last modified
3/9/2020 6:21:27 PM
Creation date
3/9/2020 2:39:21 PM
Metadata
Fields
Template:
EHD - Public
ProgramCode
3500 - Local Oversight Program
File Section
WORK PLANS
RECORD_ID
PR0545441
PE
3528
FACILITY_ID
FA0003733
FACILITY_NAME
NORTH SIDE SHELL
STREET_NUMBER
7910
STREET_NAME
LOWER SACRAMENTO
STREET_TYPE
RD
City
STOCKTON
Zip
95210
APN
07949006
CURRENT_STATUS
02
SITE_LOCATION
7910 LOWER SACRAMENTO RD
P_LOCATION
01
QC Status
Approved
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EHD - Public
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LM <br /> LO 1.0 METHOD <br /> 1.1 Soil Sampling and Contamination Reduglion <br /> * Soil borings and soil sampling will be performed under the direction of a Delta engineer or geologist. <br /> The soil borings will be advanced using a truck-mounted drill rig utilizing hollow-stem augers. <br /> Il. To reduce the chances of cross-contamination between boreholes, all downhole drilling equipment <br /> will be cleaned between borings. To reduce cross-contamination between samples, the spit-barrel <br /> sampler will be washed in a soap solution and double-rinsed between each sampling event. <br /> Soil sampling will be done in accordance with ASTM 1586-84. Using the procedure, a 2-inch <br /> �. outside diameter split-barrel sampler or a 2-inch inside diameter California-type sampler is driven <br /> into the soil by a 140-pound weight falling 30 inches. After an initial set of 6 inches, the number <br /> of blows required to drive the sampler an additional 12 inches is known as penetration resistance, <br /> or the "N" value. The N value is used as an empirical measure of the relative density of cohesionless <br /> 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 later <br /> screening with a portable photoionization detector (PID). Another portion of the soil sample will be <br /> used for classification and description. That part of the soil sample collected in brass tubes within <br /> the California-type sampler will be stored at approximately 4°C for transport to the laboratory. <br /> 1.2 Soil Classification <br /> As the samples are obtained in the filed, they will be classified by a geologist/engineer in accordance <br /> with ASTM: D2488-84. Representative portions of the samples will then be returned to the <br /> z laboratory for further examination and for verification of the field classification. Logs of the <br /> borings indicating the depth and identification of the various strata, the N value, water-level <br /> information, and pertinent information regarding the method of maintaining and advancing the <br /> ` borehole will be made. <br /> F1.2 Soil Sample Screenin P r able J!hotoignization DetectREh <br /> After soil sample jars have been brought to room temperature, the headspace vapors of the soil <br /> sample jars will be screened with a portable PID equipped with a 10.2 eV lamp calibrated to benzene <br /> for direct reading in parts per million (ppm). The sample jar lid will be opened and the probe <br /> immediately placed within the headspace of the jar. The highest observed reading will be recorded. <br /> 1.4 Monitorine Well Gravel Pak and Slot Size Selection <br /> The size of the gravel pack that will be placed adjacent to the well screen will be determined by the <br /> i.. project manager based on an estimation of the distribution of grain size in the formation which is <br /> likely to be encountered within the uppermost saturated zone at the site. Available geologic <br /> L. <br />
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