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ARCHIVED REPORTS_XR0002483
Environmental Health - Public
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2900 - Site Mitigation Program
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PR0540859
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ARCHIVED REPORTS_XR0002483
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Last modified
1/15/2020 3:47:30 PM
Creation date
1/15/2020 3:07:38 PM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2900 - Site Mitigation Program
File Section
ARCHIVED REPORTS
FileName_PostFix
XR0002483
RECORD_ID
PR0540859
PE
2960
FACILITY_ID
FA0023361
FACILITY_NAME
PLAY N PARK (FORMER BARNES TRUCKING)
STREET_NUMBER
1817
Direction
S
STREET_NAME
FRESNO
STREET_TYPE
AVE
City
STOCKTON
Zip
95206
CURRENT_STATUS
01
SITE_LOCATION
1817 S FRESNO AVE
P_LOCATION
01
QC Status
Approved
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EHD - Public
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it Borin2 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 QjIsing. Screen and Filter Pack Construction <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 borings 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 <br /> unless site geochemistry or contamination necessitates an alternative material The wells are constructed with <br /> factory-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 level The screened interval may extend less than five feet above the <br /> maxunum 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 <br /> to two feet above the screen, as site conditions permit, so as to prevent extension of the sand pack into an overlying <br /> water-bearmg unit The well screen slot size is the maximum size capable of retammg 90% of the filter pack <br /> Typically, 0 010-mch screen is used where the formation is predominantly clay and/or silt or poorly-graded fine <br /> sand 0 020-inch screen is used where the formation is predominantly well-graded or medium to coarse sand and/or <br /> gravel <br /> . The filter pack grade(mean gram 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 tunes the 70% retained gram size Since results of particle 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 forest significantly thick layer of sediment to be screened Commonly selected grades are Lone Star®3,2/12 or <br /> 2/16(or equivalent)with 0 020-inch slotted screen and Lone Star® 1/20 with 0 010-mch slotted screen <br /> Well Seal and Colal2letion <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 If bentonite is used in the grout mixture, it does not exceed 5% by weight The grout is <br /> placed using a tremie pipe, if the top of the bentonite is more than 20 feet below grade, or if water is present in the <br /> boring above the bentonite seal A watertight locking cap and protective traffic-rated vault box is installed on top of <br /> each well Well construction details are presented on the Field Exploratory Soil Boring Log Following <br /> completion of a well, Clearwater completes and submits, or ensures that the driller has sufficient information to <br /> complete and 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 surgmg with a surge block and removing water from the well with either a pump or bailer,until the well is free of <br /> 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 <br /> potable water All data collected during development are recorded on the Well Development Data Sheet and, if <br /> necessary,the Purging Data Sheet <br /> CLEARWATER GROUP(WI/GWS) 2 revised dune 29, 2001 <br />
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