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2900 - Site Mitigation Program
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PR0541913
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Last modified
2/13/2020 7:07:47 PM
Creation date
2/13/2020 11:53:44 AM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2900 - Site Mitigation Program
File Section
WORK PLANS
RECORD_ID
PR0541913
PE
2960
FACILITY_ID
FA0024043
FACILITY_NAME
FRONTIER TRANSPORTATION FACILITY
STREET_NUMBER
425
STREET_NAME
LARCH
STREET_TYPE
RD
City
TRACY
Zip
95304
APN
21220009
CURRENT_STATUS
01
SITE_LOCATION
425 LARCH RD
P_LOCATION
03
QC Status
Approved
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EHD - Public
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Frontier Transportation B23502.01A <br /> January 2, 1996 Page A4 <br /> free of sediment, and the values of pH, temperature, and specific electrical conductance <br /> (EC) have stabilized. Well development data will be recorded on the Sampling/Well <br /> Development Log (Attachment A). <br /> Purged water will be containerized in Department of Transportation-approved drums, and <br /> stored on site in an area inaccessible to the general public. The purged water is typically <br /> characterized either by sampling, or on the basis of the groundwater sample analytical <br /> results. Twining can recommend an appropriate method for disposition of the purged water. <br /> Disposal will be the responsibility of the client. <br /> A4 Standard Operating Procedures for Groundwater Monitoring Well Sampling <br /> Standard operating procedures (SOPS) used by The Twining Laboratories, Inc. (Twining) <br /> when sampling groundwater monitoring wells are presented below. Twining observes these <br /> procedures in order to obtain consistent, reliable data. <br /> Groundwater sampling will be performed a minimum of 24 hours following development, <br /> or when the post-development water level in the well has returned to the static level. before <br /> purging and sampling is performed, the depth to water and the total well depth will be <br /> measured. If floating hydrocarbons are suspected, a bottom-filling clear bailer, or _ <br /> hydrocarbon-detecting paste bailer, or interface probe may be used to record floating <br /> hydrocarbon thickness. Depth to water will be measured with an electric sounder, according <br /> to. Twining's "Standard Operating Procedures for Measuring Depths to Water and <br /> Calculating Groundwater Elevations". <br /> Prior to sampling a monitoring well, a minimum of 3 well casing volumes will be purged <br /> using a clean, stainless steel submersible pump or a disposable bailer equipped with a length <br /> of new rope. Disposable bailers and rope lengths will be used once, and discarded. After <br /> 3 casing_ volumes of water have been removed from the well, purging will continue until <br /> measured field parameters (pH, specific electrical conductivity, and temperature) have <br /> stabilized. Purging data will be recorded on the Well Sampling log. <br /> Some monitoring wells are expected to be evacuated to dryness after removing fewer than <br /> three casing volumes. These low-yield monitoring wells will be allowed to recharge for as <br /> long as 24 hours. Samples will be collected as soon as the monitoring wells have recharged <br /> sufficiently to allow sample collection. If insufficient water has recharged after 24 hours, <br /> the monitoring well will be recorded as "dry" for the sampling event. <br /> Purged water will be containerized in Department of Transportation-approved drums, and <br /> stored on site in an area inaccessible to the general public. The purged water is typically <br /> characterized either by sampling, or on the basis of the groundwater sample analytical <br /> results. Twining can recommend an appropriate method for disposition of the purged water. <br /> Disposal will be the responsibility of the client. <br />
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