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ARCHIVED REPORTS_XR0012626
EnvironmentalHealth
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EHD Program Facility Records by Street Name
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2900 - Site Mitigation Program
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PR0543041
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ARCHIVED REPORTS_XR0012626
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Last modified
5/18/2020 3:03:14 PM
Creation date
5/18/2020 2:45:25 PM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2900 - Site Mitigation Program
File Section
ARCHIVED REPORTS
FileName_PostFix
XR0012626
RECORD_ID
PR0543041
PE
2960
FACILITY_ID
FA0024604
FACILITY_NAME
HUMAN SERVICES AGENCY
STREET_NUMBER
145
Direction
S
STREET_NAME
SUTTER
STREET_TYPE
ST
City
STOCKTON
Zip
95202
APN
14912016
CURRENT_STATUS
01
SITE_LOCATION
145 S SUTTER ST
P_LOCATION
01
QC Status
Approved
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E `n <br /> monitoring wells (MW-5, MW-6, MW-7, and MW-8) are located based <br /> on the presently known compound distribution and apparent shallow <br /> groundwater gradient direction. <br /> MW-5 and MW-6 are placed to define the lateral plume boundaries <br /> �- to the northwest and the southeast, respectively. <br /> Monitoring well MW-7 is located northeast of MW-2 and will <br /> monitor for compound presence directly downgradient from the <br /> source area. MW-8 is also located directly downgradient and <br /> should provide an indication of the rate at which the compounds <br /> decrease downgradient due to dispersion or natural biological <br /> degradation. If the new downgradient wells MW-7 and MW-8 contain <br /> more compound concentrations than M11-2, additional wells may be <br /> required to define the extent of the plume. The decision to <br /> construct monitoring wells in addition to the five proposed above <br /> will be made only after an analysis of the data acquired by the <br /> Phase II Program is completed. <br /> 2.4 MONITORING WELL CONSTRUCTION <br /> The limited geologic data currently available for the site <br /> �• indicates that the aquifer is composed of fine to coarse-grained <br /> sand interlayered with discontinuous clay lenses. The aquifer is <br /> unconfined and contains no significant continuous aquicludes, at <br /> least within the upper 100 feet below the ground surface (person- <br /> al communication with the CRWQCB, August, 1989) . <br /> The monitoring wells will be drilled using hollow stem auger <br /> (HSA) techniques and split-spoon sampling at 5-foot intervals for <br /> lithologic control. The wells will be drilled to a total depth <br /> -' equal to approximately 20 feet below the top of the water table. <br /> Actual depths will vary depending on the elevation of the ground <br /> surface at each well. Wells drilled from street level will be <br /> -� approximately 60 feet deep. Based on presently available data, a <br /> total well depth of approximately 60 feet will provide a 20 foot <br /> water column in the wells. <br /> The wells will be constructed of 4-inch diameter schedule 40 PVC <br /> pipe with 20 feet of 4-inch diameter schedule 40, 0.010 inch <br /> slotted screen. The pipe will be flush-threaded; no glues or <br /> solvents will be used in constructing the wells. The well <br /> construction method will be as follows: <br /> o Screen and casing will be suspended within the hollow stem <br /> augers to the total depth so that the screen extends from 5 <br /> feet above the water table to 15 feet below the water table. <br /> This will leave a 5 foot sand plug beneath the screened <br /> section. <br /> o An appropriate sized sand/gravel pack will be placed around <br /> the well screen while removing the augers. The sand pack <br /> will extend 3 to 5 feet above the top of the screen. <br /> 2 - 3 <br />
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