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ARCHIVED REPORTS XR0011281
Environmental Health - Public
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EHD Program Facility Records by Street Name
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FREMONT
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2050
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3500 - Local Oversight Program
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PR0543791
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ARCHIVED REPORTS XR0011281
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Last modified
10/1/2018 5:27:01 AM
Creation date
9/28/2018 5:01:37 PM
Metadata
Fields
Template:
EHD - Public
ProgramCode
3500 - Local Oversight Program
File Section
ARCHIVED REPORTS XR0011281
FileName_PostFix
XR0011281
RECORD_ID
PR0543791
PE
3526
FACILITY_ID
FA0003592
FACILITY_NAME
Aries Tek, LLC
STREET_NUMBER
2050
Direction
E
STREET_NAME
FREMONT
STREET_TYPE
St
City
Stockton
Zip
95205
CURRENT_STATUS
02
SITE_LOCATION
2050 E Fremont St
P_LOCATION
01
P_DISTRICT
001
QC Status
Approved
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EHD - Public
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EMCON will recommend an appropriate method for disposition of the cuttings based on <br /> the analytical results The client will be responsible for disposal of the drill cuttings <br /> Soil samples for chemical analysis will be collected in brass or stainless steel liners, sealed <br /> with Teflon® tape and plastic end caps, labeled, placed on ice, and delivered to a <br /> state-certified analytical laboratory, along with the appropriate chain-of-custody <br /> documentation Soil samples selected for chemical analysis will be determined from a <br /> head-space analysis using a hand-held photoaonization detector (PID) The soil will be <br /> placed in a glass Jar, sealed, and placed in a warm atmosphere After approximately <br /> 15 minutes, which is generally sufficient for volatiles to escape from the soil, the PID <br /> probe will be inserted into the glass Jar The total volatile hydrocarbons present are <br /> detected by the PID and reported in parts per million (ppm) The PID will be calibrated to <br /> an isobutylene standard <br /> Generally two soil samples from each soil boring will be submitted for chemical analysis <br /> Soil samples selected for analysis typically represent the highest PID reading recorded for <br /> each soil boring and the sample Just above first-encountered groundwater <br /> Monitoring Well Installation <br /> Monitoring wells will be completed by installing 2- -inch-diameter Schedule 40 polyvinyl <br /> chloride (PVC) casing The 2-inch-diameter flush-threaded casing is generally used for <br /> wells dedicated for groundwater monitoring purposes The screened sections of casing are <br /> factory machine slotted and will be installed approximately 5 feet above and 10 feet below <br /> first-encountered water level The screened interval will allow for seasonal fluctuation in <br /> water level and for monitoring floating product A filter pack of graded sand will be placed <br /> in the annular space between the PVC casing and the borehole wall Sand will be added to <br /> the borehole through the hollow stem of the augers to provide a uniform filter pack around <br /> the casing and to stabilize the borehole The sand pack will be placed to a maximum of 2 <br /> feet above the screens followed by a minimum 1-foot seal consisting of bentonite pellets <br /> Cement grout containing 5 percent bentonite or concrete will be placed above the bentonite <br /> seal to the ground surface A concrete traffic-rated vault box will be installed over the <br /> monitoring well(s) A watertight locking cap will be installed over the top of the well <br /> casing Reference elevations for each monitoring well will be surveyed when more than <br /> two wells will be located on site Monitoring well elevations will be surveyed by EMCON <br /> or a subcontractor to the nearest 0 01 foot relative to mean sea level (MSL) or a site datum <br /> Exploratory boring logs (Figure A-1) and well construction details (Figure A-2) will be <br /> prepared for the final written report <br /> • <br /> CP1E IAPACERREPORTSWACP1dI DOC-9811sg 1 Fmcon <br /> A-2 <br />
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