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FIELD DOCUMENTS FILE 2
Environmental Health - Public
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EHD Program Facility Records by Street Name
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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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FIELD DOCUMENTS FILE 2
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Last modified
7/3/2019 7:49:05 PM
Creation date
7/3/2019 4:26:46 PM
Metadata
Fields
Template:
EHD - Public
ProgramCode
3500 - Local Oversight Program
File Section
FIELD DOCUMENTS
FileName_PostFix
FILE 2
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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s <br /> r I%Wle LI <br /> 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 Casine,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 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 level. 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 90% of the filter pack. <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 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 finest 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-inch slotted screen. <br /> Well Seal and Completion <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 placed <br /> using a tremie 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 top of each <br /> well. Well construction details are presented on the Field Exploratory Soil Boring 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 /> CLEARWATER GROUP,INC.(WI/GWS) 2 revised April 24, 2001 <br />
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