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ARCHIVED REPORTS XR0006549
EnvironmentalHealth
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DURHAM FERRY
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4491
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3500 - Local Oversight Program
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PR0544625
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ARCHIVED REPORTS XR0006549
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Last modified
7/3/2019 8:13:12 PM
Creation date
7/3/2019 4:44:53 PM
Metadata
Fields
Template:
EHD - Public
ProgramCode
3500 - Local Oversight Program
File Section
ARCHIVED REPORTS
FileName_PostFix
XR0006549
RECORD_ID
PR0544625
PE
3528
FACILITY_ID
FA0003113
FACILITY_NAME
ZAPIEN MARKET
STREET_NUMBER
4491
Direction
W
STREET_NAME
DURHAM FERRY
STREET_TYPE
RD
City
TRACY
Zip
95376
APN
25504003
CURRENT_STATUS
02
SITE_LOCATION
4491 W DURHAM FERRY RD
P_LOCATION
99
P_DISTRICT
005
QC Status
Approved
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EHD - Public
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Soil Boring Abandonment <br /> Soil borings which are not to be converted into monitoring wells are sealed to the ground surface using neat cement <br /> or sand-cement slurry in accordance with federal,state and local regulations Native soil may be used to fill the top <br /> two to three feet for cosmetic purposes, as permitted <br /> Monitoring Well Installation <br /> Well Casing, Screen and Filter Pack Constnictton <br /> All well construction is performed in accordance with Department of Water Resources "California Well Standards" <br /> and all requirements of local oversight agencies Soil bonngs to be converted into single-cased monitoring wells are <br /> a minimum of eight inches in diameter for 2-inch diameter wells and a minimum of ten inches in diameter for 4-inch <br /> diameter wells Monitoring wells are constructed with schedule 40, threaded, polyvinyl chloride (PVC)casing unless <br /> site geochemistry or contamination necessitates an alternative material The wells are constructed with factory- <br /> slotted screen and threaded end caps <br /> The screened interval is placed such that it extends approximately ten feet into the water bearing zone and at least <br /> five feet above the expected maximum water le%el The screened interval may extend less than five feet above the <br /> maximum water level, only to prevent intersection of the screened interval with the top of the confining layer of a <br /> confined aquifer, or where the water table is too shallow to allow this construction <br /> A graded sand filter pack is placed in the annular space across the screened interval and extended approximately one to <br /> two feet above the screen, as site conditions permit so as to prevent extension of the sand pack into an overlying <br /> water-bearing unit The well screen slot size is the maximum size capable of retaining 9017c of the filter pact. <br /> Typically, 0 010-inch screen is used where the formation is predominantly clay and/or silt or poorly-graded fine sand <br /> 0 020-inch screen is used where the formation is predominantly well-graded or medium to coarse sand and/or gravel <br /> The filter pack grade (mean grain size) is selected according to native sediment type as follows a) for poorly graded <br /> fine sand or silt/clay - 4 times the 70% retained grain size of the formation b) for medium to coarse sand gravel or <br /> well graded sediments - 6 times the 70% retained grain size Since results of panicle size analysis are not always <br /> available, Clearwater often selects screen size and filter pack on the basis of general site stratigraphy, and specifically <br /> the finest significantly thick layer of sediment to be screened Commonly selected grades are Lone Stan? 3, 2/12 or <br /> 2116 (or equivalent) with 0 020-inch slotted screen and Lone Star(D 1/20 with 0 010-inch slotted screen <br /> Well Seal and <br /> A minimum two foot seal of bentonite is placed above the sand pack The bentonite seal is hydrated by either <br /> formation water or potable water Neat cement or a cement/bentonite grout mixture seals the remaining annular <br /> space to the surface Iā¬bentonite is used in the grout mixture, it does not exceed 5% by weight The grout is placed <br /> using a tremae pipe, if the top of the bentonite is more than 20 feet below grade, or if water is present in the boring <br /> above the bentonite seal A watertight locking cap and protective traffic-rated vault box is installed on [op of each <br /> well Well construction details are presented on the Field Exploratory Soil Bonng Log Following completion of a <br /> well, Clearwater completes and submits, or ensures that the driller has sufficient information to complete and <br /> submit,the state-required Well Completion Report or equivalent document <br /> Well Development <br /> All newly installed wells are developed prior to sampling to remove fine grained sediments from the well and <br /> stabilize the filter pack and the disturbed aquifer materials Development takes place prior to or at least 24 hours <br /> after setting the seal on the well, unless otherwise directed by a local oversight agency Well development consists <br /> of surging with a surge block and removing water from the well with either a pump or bailer, until the well is free <br /> of sediment, or until at least 10 well casing volumes have been removed Depth to bottom is measured to determine <br /> casing volume If the well is sampled immediately following development, temperature, pH, specific conductance <br /> and turbidity (qualitative) are monitored during well development (see section "Groundwater Sampling") All <br /> development equipment is cleaned prior to use and between wells with an Alconox® solution, then rinsed in potable <br /> water All data collected during development are recorded on the Well Development Data Sheet and, if necessary,the <br /> Purging Data Sheet <br /> CLEARWA'iER GROUP,INC (WVGWS) _ 2 revised November 15, 1999 <br />
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