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ARCHIVED REPORTS_XR0003248
Environmental Health - Public
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3500 - Local Oversight Program
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PR0545289
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ARCHIVED REPORTS_XR0003248
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Last modified
2/11/2020 9:55:31 PM
Creation date
2/11/2020 8:39:58 AM
Metadata
Fields
Template:
EHD - Public
ProgramCode
3500 - Local Oversight Program
File Section
ARCHIVED REPORTS
FileName_PostFix
XR0003248
RECORD_ID
PR0545289
PE
3528
FACILITY_ID
FA0003828
FACILITY_NAME
VAN BUSKIRK GOLF COURSE
STREET_NUMBER
1740
STREET_NAME
HOUSTON
STREET_TYPE
AVE
City
STOCKTON
Zip
95206
APN
16307036
CURRENT_STATUS
02
SITE_LOCATION
1740 HOUSTON AVE
P_LOCATION
01
P_DISTRICT
001
QC Status
Approved
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SJGOV\sballwahn
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EHD - Public
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City of Stockton - Van Buskirk Park Golf Course TL 394-0074-01 <br /> July 29, 1994 PWA-5 <br /> • Standards are prepared using the applicable reference materials; <br /> ' • Matrix spikes are analyzed in duplicate to validate the accuracy and precision of the <br /> method; and <br /> ' • During groundwater sampling, a travel blank sample consisting of organic-free water <br /> is prepared and containerized in the laboratory, transported to the site, and handled <br /> and transported in the same manner as the groundwater samples. <br /> A-8 Standard Operating Procedures for Groundwater Monitoring Well Installation: <br /> I <br /> Twining is a C-57 licensed water well drilling contractor (Contractor's License No. 546159). <br /> The groundwater monitoring wells are installed under the direction of a California <br /> registered geologist or certified professional engineer. <br /> Soil borings for monitoring wells are drilled and sampled according to Twining's "Standard. <br /> iOperating 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 /> The 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 2- 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 containing 3 to 5 percent bentonite. For wells with a seal more than 15 feet deep, <br /> the grout is emplaced through the hollow augers, which will extend to within 15 feet of the <br /> bentonite seal. If required by the local regulatory agency, the grout is emplaced by pumping <br /> through a tremie pipe which extends to within 15 feet of the seal. The tremie pipe or <br /> augers are withdrawn from the boring in 10-foot increments as the boring fills with grout. <br /> A watertight well cap is placed on top of each groundwater monitoring well, and a 3-foot <br /> steel standpipe with locking cover or a traffic-rated box is installed around the wellhead. <br /> Monitoring wells are locked to restrict access to unauthorized personnel. <br />
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