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ARCHIVED REPORTS XR0009635
EnvironmentalHealth
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3500 - Local Oversight Program
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PR0543393
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ARCHIVED REPORTS XR0009635
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Last modified
11/6/2018 3:26:42 AM
Creation date
11/5/2018 8:30:31 AM
Metadata
Fields
Template:
EHD - Public
ProgramCode
3500 - Local Oversight Program
File Section
ARCHIVED REPORTS
FileName_PostFix
XR0009635
RECORD_ID
PR0543393
PE
3528
FACILITY_ID
FA0006246
FACILITY_NAME
CITY OF STOCKTON/VICTORY PARK*
STREET_NUMBER
1201
Direction
N
STREET_NAME
PERSHING
STREET_TYPE
AVE
City
STOCKTON
Zip
95202
APN
13515001
CURRENT_STATUS
02
SITE_LOCATION
1201 N PERSHING AVE
P_LOCATION
01
P_DISTRICT
001
QC Status
Approved
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WNg
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EHD - Public
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City of Stockton A68104 01A <br /> October 25, 1995 Page A-3 <br /> registered geologist or certified professional engineer <br /> Soil borings for monitoring wells are drilled and sampled according to Twining's "Standard <br /> Operating Procedures for Drilling and Soil Sampling" Equipment used for drilling, <br />' sampling, and constructing wells, and well construction materials are thoroughly cleaned <br /> according to Twining's "Standard Operating Procedures for Equipment Decontamination" <br /> Groundwater monitoring wells are constructed of minimum Schedule 40 polyvinyl chloride <br /> (PVC), stainless steel, or other material casing. Screen may be machine-slotted or wire- <br /> wrapped Casing and well screen specifications will depend upon project objectives, site <br /> conditions, and project budgets The well screen and casing sections are joined by factory- <br /> made flush-threaded connections <br /> rThe well filter pack material consists of appropriately-sized pre-washed sand The filter <br /> material is placed in the annulus between the boring wall, from the bottom of the boring <br /> to approximately 2 feet above the top of the screen Subsequent to filter pack <br /> emplacement, preliminary development may be performed to provide a uniform filter pack <br /> about the casing Above the filter pack, a 3- to 4-foot thick bentonite seal is installed The <br /> bentonite may consist of 1/4- or 1/2-inch pellets, or may be in the form of a slurry If <br /> pellets are used, they are hydrated prior to grouting the well, by adding at least one gallon <br /> of water for every bucket of pellets The thickness of the bentonite seal depends upon local <br /> regulatory requirements <br /> The remainder of the well annulus is sealed with a 6-sack sand-cement, or cement grout <br /> slurry in one continuous operation from the bottom of the interval to be filled to the top <br /> For wells with a seal more than 15 feet deep, the grout is emplaced through the hollow <br /> augers, which will extend to within 15 feet of the bentonite seal if required by the local <br /> regulatory agency, the grout is emplaced by pumping through a tremie pipe which extends <br /> to within 15 feet of the seal The tremie pipe or augers are withdrawn from the boring in <br /> 10-foot increments as the boring fills with grout A watertight well cap is placed on top of <br /> each groundwater monitoring well, and a 3-foot steel standpipe with locking cover or a <br /> traffic-rated box is installed around the wellhead Monitoring wells are locked to restrict <br /> access to unauthorized personnel <br /> Monitoring well construction details are recorded on the field well construction form <br /> Construction information is transferred to Monitoring Well construction schematics for <br /> presentation in final reports <br /> A-3 Standard Operating Procedures for Groundwater Monitoring_Well Development <br /> When possible, initial well development is performed during installation of the sand pack <br /> A minimum of 48 hours following installation, groundwater monitoring wells are developed <br /> in order to remove sediment that may accumulate in the well during installation, and to <br /> settle the filter pack Groundwater monitoring well development is performed using a <br /> combination of either bailing, pumping, and surging <br />
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