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2900 - Site Mitigation Program
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PR0506525
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Last modified
10/24/2018 10:03:43 PM
Creation date
10/24/2018 2:11:53 PM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2900 - Site Mitigation Program
File Section
WORK PLANS
RECORD_ID
PR0506525
PE
2960
FACILITY_ID
FA0007475
FACILITY_NAME
MCMULLIN DEHYDRATOR STATION
STREET_NUMBER
26250
Direction
S
STREET_NAME
AIRPORT
STREET_TYPE
WAY
City
MANTECA
Zip
95336
APN
25703010
CURRENT_STATUS
01
SITE_LOCATION
26250 S AIRPORT WAY
P_LOCATION
99
P_DISTRICT
005
QC Status
Approved
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EHD - Public
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0 <br />11 <br />2. Selected soil samples collected at various depths will be retained in the <br />sample liners (the sample liner containing the desired sample will be <br />cut into a 12 -inch or shorter length with a clean knife blade or clean <br />hacksaw blade), and the ends covered with Teflon® sheets and plastic <br />end caps. <br />3.2 Borehole Abandonment Procedures <br />After the soil samples have been collected from each soil boring, the boreholes will be <br />grouted to the surface using neat cement. The cement will be pumped or tremied into the <br />borehole. <br />4.0 GROUNDWATER SAMPLING <br />4.1 Groundwater Grab Sampling Procedures <br />Groundwater grab samples will be collected from boreholes by lowering 1 -inch diameter <br />PVC screen and casing to the total depth of the borehole. The proper lengths of screen <br />and blank casing will be cleaned and threaded above the ground prior to lowering inside <br />the borehole. The well screen will be 5 to 10 ft in length and will extend across the water <br />table surface. The bottom of the screened interval will be fitted with an end plug. <br />Samples of the groundwater will be collected from each temporary well using a Teflon® <br />bailer or a pump which has be washed in a solution of Alconox or non -phosphate TSP <br />followed by several rinses with potable water, or by using a disposable bailer which was <br />removed from its factory protective cover immediately prior to sampling the well. The <br />groundwater samples collected from each well will be decanted into the appropriate <br />sample containers for each analyte. Care will be taken when transferring the water from <br />a bailer to the sample containers to avoid turbulence and all VOA vials will be filled <br />above the top of the opening to form a positive meniscus so that no headspace will be <br />present. <br />4.2 Monitoring Well Sampling Procedures <br />Each groundwater monitoring well will be purged using a low flow peristaltic pump prior <br />to collecting groundwater samples for chemical analyses. During the purging process, <br />approximately three well volumes of groundwater will be discharged from the well using <br />either a pump or bailer. The well will be properly purged when the physical parameters <br />of the groundwater (i.e., pH, temperature, and conductivity) have stabilized. If the well <br />is evacuated prior to the removal of three to five well volumes, a sample of the <br />groundwater will be collected when the water level is sufficient to provide a <br />representative sample (i.e., return to 80% or more of the static water level). <br />Samples of the groundwater will be collected from each monitoring well using the <br />peristaltic pump for inorganic and non-volatile organic constituents and a bailer for the <br />volatile organic constituents. The bailer used for sampling may be a Teflon® or stainless <br />steel bailer which has been washed in a solution of Alconox followed by several rinses <br />with potable or deionized water, or a disposable bailer which was removed from its <br />factory protective cover immediately prior to sampling the well. The groundwater <br />samples collected from each well will be decanted into the appropriate sample containers <br />
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