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2900 - Site Mitigation Program
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PR0506525
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Entry Properties
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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prior to installing the bentonite seal in order to maximize the filtering capacity of the <br />wells. <br />Full development of the wells will be performed a minimum of 48 hours after well <br />completion. This will include additional surging and bailing along the screened interval <br />to remove fine particles from the sandpack. After several volumes of the water have <br />been removed, the wells will be pumped (or bailed) until the discharge water is relatively <br />free of sand or silt. <br />' 5.0 SOIL AND GROUNDWATER SAMPLE HANDLING PROCEDURES <br />The following procedures will be used for soil and groundwater sample handling: <br />' 1. Each retained sample will be labeled using waterproof ink with the project name, <br />borehole I.D. number, sample depth (for soil samples), time and date collected, <br />and the initials of the sampler. <br />1 <br />401111,9111 A-5 <br />4.4 Monitoring Well Sampling Procedures <br />Each groundwater monitoring well will be purged prior to collecting groundwater <br />to five <br />' <br />samples for chemical analyses. During the purging process, approximately three <br />well volumes of groundwater will be discharged from the well using either a centrifugal <br />pump or bailer. The well will be properly purged when the physical parameters of the <br />groundwater (i.e., pH, temperature, and conductivity) have stabilized. If the well is <br />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 a <br />Teflon® or stainless steel bailer which has been washed in a solution of Alconox <br />' <br />followed by several rinses with potable or deionized water, or using a disposable bailer <br />which was removed from its factory protective cover immediately prior to sampling the <br />well. The groundwater samples collected from each well will be decanted into the <br />' <br />appropriate sample containers for each analyte. Sample containers will be chemically <br />preserved by the laboratory prior to going into the field. Care will be taken when <br />transferring the water from the bailer to the sample containers to avoid turbulence and all <br />' <br />VOA vials will be filled above the top of the opening to form a positive meniscus so that <br />no headspace will be present. <br />4.5 Water Level Measurements and Surveying Top of Casing of Monitoring Wells <br />After the water levels in the wells have stabilized, the depth to water in the wells will be <br />' <br />measured to an accuracy of 0.01 ft using an electronic immersion probe. The top of <br />casing of each well will also be surveyed to a common datum to convert depth -to -water <br />level measurements to relative groundwater elevations. All surveyed elevations will be <br />t <br />performed to an accuracy of 0.01 ft. All survey locations in the X -Y coordinate will be <br />taped to an accuracy of 0.1 ft. <br />' 5.0 SOIL AND GROUNDWATER SAMPLE HANDLING PROCEDURES <br />The following procedures will be used for soil and groundwater sample handling: <br />' 1. Each retained sample will be labeled using waterproof ink with the project name, <br />borehole I.D. number, sample depth (for soil samples), time and date collected, <br />and the initials of the sampler. <br />1 <br />401111,9111 A-5 <br />
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