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HOWLAND
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16777
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2900 - Site Mitigation Program
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PR0546589
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Entry Properties
Last modified
3/12/2026 12:15:26 PM
Creation date
3/12/2026 12:04:09 PM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2900 - Site Mitigation Program
File Section
WORK PLANS
RECORD_ID
PR0546589
PE
2965 - RWQCB LEAD AGENCY WASTE DISCHARGE SITE
FACILITY_ID
FA0026428
FACILITY_NAME
SIMPLOT LATHROP
STREET_NUMBER
16777
STREET_NAME
HOWLAND
STREET_TYPE
RD
City
LATHROP
Zip
95330
CURRENT_STATUS
Active, billable
QC Status
Approved
Scanner
SJGOV\gmartinez
Supplemental fields
Site Address
16777 HOWLAND RD LATHROP 95330
Tags
EHD - Public
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wood. <br /> The original field logs will be retained by the Wood office for review by the responsible <br /> professional and for storage in the project files. <br /> 4.0 GEOPHYSICAL LOGS <br /> Following completion of drilling, downhole geophysical logs may be performed after the drilling <br /> fluid has been circulated to decrease the amount of suspended sediment in the return fluid. <br /> Geophysical methods and equipment will be selected to provide stratigraphic or hydrogeologic <br /> data appropriate for the project. Geophysical logging will be done as quickly and promptly after <br /> drilling as feasible, while the boring sidewall is still in stable condition, to reduce the possibility <br /> of bridging. Instruments on the logging unit will be adjusted to try to give the maximum defini- <br /> tion of strata boundaries. All downhole geophysical equipment will be cleaned before and after <br /> use in each borehole. <br /> 5.0 FIELD SCREENING <br /> Soil samples collected from the borings may be screened using a portable meter such as a <br /> photoionization detector (PID), a flame ionization detector (FID), a lower explosion limit (LEL) <br /> meter or other organic vapor meter. The meter may be used to assess the presence of volatile <br /> organic compounds (VOCs) or other gases in soil samples. Additional field screening <br /> techniques for chemical characterization of soils may include x-ray fluorescence (XRF) and <br /> thin-layer chromatography(TLC). Procedures for field screening are described in the protocol <br /> SOIL SAMPLING FOR CHEMICAL ANALYSIS. <br /> 6.0 DESTROYING SOIL BORINGS <br /> Soil borings that are not completed as monitoring wells will be destroyed by filling the holes <br /> with a neat cement grout, cement/sand grout, or cement/bentonite grout. A high-solids bento- <br /> nite grout may be used if appropriate. Wood field staff will calculate the borehole volume and <br /> compare it to the volume of grout used to evaluate whether bridging has occurred. These <br /> calculations and the actual volume emplaced will be noted on the BORING LOG. The grout <br /> will be placed in continuous lifts from the bottom of the boring to a depth of 20 feet above the <br /> water table. The grout will be emplaced by pumping it through the hollow stem augers, drill <br /> pipe, tremie pipe, or flexible hose initially lowered to the bottom of the borings and raised in- <br /> crementally as placement proceeds. If hollow stem augers are used, the augers should be <br /> raised incrementally as grout emplacement proceeds. Augers will not be raised in increments <br /> greater than 20 feet or greater than allowed by borehole stability. Borings that are terminated <br /> above the water table and not greater than 20 feet deep may be destroyed by continuous lifts <br /> originating at the ground surface. The grout will be pumped or poured until a return of fresh <br /> H:\AMEC\Field Protocols\Wood Protocols\PROTO-DD 0802.doc DRILLING AND DESTRUCTION OF SOIL BORINGS <br /> REVISION DATE:February 2015 Page 4 of 5 <br />
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