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Environmental Health - Public
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EHD Program Facility Records by Street Name
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HAMMER
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1120
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3500 - Local Oversight Program
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PR0545244
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Last modified
1/30/2020 9:21:34 AM
Creation date
1/30/2020 8:34:27 AM
Metadata
Fields
Template:
EHD - Public
ProgramCode
3500 - Local Oversight Program
File Section
WORK PLANS
RECORD_ID
PR0545244
PE
3526
FACILITY_ID
FA0024606
FACILITY_NAME
FORMER KNOWLES STATION
STREET_NUMBER
1120
Direction
W
STREET_NAME
HAMMER
STREET_TYPE
LN
City
STOCKTON
Zip
95209
APN
07749027
CURRENT_STATUS
02
SITE_LOCATION
1120 W HAMMER LN
P_LOCATION
01
QC Status
Approved
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EHD - Public
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GROUND ZERO ANALVMS, INC. <br /> FIELD PROCEDURES <br /> the relative consistency of the soil. Sampling equipment is cleaned between each use with a steam <br /> cleaner or with clean tap water and laboratory-grade detergent. <br /> Continuous core sampling during drilling with hollow stem augers is typically accomplished using <br /> a 94-millimeter diameter, 5-foot long split spoon sampler with no liners. <br /> The soil samples selected for possible laboratory analysis are removed from the sampler and <br /> quickly sealed in their brass sleeves with Teflon tape and plastic caps. Samples from the <br /> continuous core sampler are collected into 1-inch diameter brass sleeves and quickly sealed with <br /> Teflon tape and plastic caps. The respective sample containers are labeled in the field with the job <br /> number, sample location, sample depth, and date, and promptly placed in iced storage for <br /> transport to the laboratory. Chain of Custody records are initiated by field personnel and <br /> accompany the samples to a laboratory certified by the State of California to perform the analyses <br /> requested. <br /> "Grab" Groundwater Samplinz <br /> A direct push rig or a hollow stem auger rig equipped with continuous flight, hollow stem augers <br /> is used to drill borings to the first encountered groundwater. After the auger is terminated at <br /> groundwater, a Hydropunch or similar sampling device is driven into groundwater, which is <br /> allowed to flow into the sampling device. Groundwater samples are slowly transferred to <br /> laboratory-cleaned sample containers, which are labeled in the field with the job number, sample <br /> location and depth, and date and promptly placed in iced storage for transport to the laboratory. <br /> Chain of Custody records are initiated by field personnel and accompany the samples to a <br /> laboratory certified by the State of California to perform the analyses requested. <br /> Monitoring Well Construction <br /> Monitoring wells are typically constructed in the borings with thread-jointed, 2-inch (or 4-inch) <br /> inside diameter, Schedule 40 PVC casing. No chemical cements, glues or solvents are used in <br /> well construction. The screened portion of each well typically consists of factory-perforated <br /> casing with 0.010 to 0.020-inch wide slots. The well screen extends from the total depth of the <br /> well (typically 15 feet below the groundwater surface) to approximately 5-feet above the <br /> groundwater surface. This screened interval allows sampling at the air-water interface during <br /> seasonal and other fluctuations of the groundwater level. The annular space in the well is packed <br /> with sand compatible with well slot size to approximately 1- to 2-feet above the slotted interval. <br /> A 2-foot thick bentonite plug is added above the sand pack to prevent the cement from entering <br /> the well pack. The remaining annulus is backfilled to grade with neat cement slurry. <br /> Wells are protected with a traffic-rated utility box. The box has a water tight seal to protect <br /> against surface-water infiltration and must be opened with a special wrench. The design of this <br /> box discourages vandalism and reduces the possibility of accidental disturbance of the well. <br /> 2 <br /> groundze\forms\fld-proc.doc <br />
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