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ARCHIVED REPORTS_XR0009935
EnvironmentalHealth
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3500 - Local Oversight Program
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PR0545678
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ARCHIVED REPORTS_XR0009935
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Last modified
5/20/2020 11:43:54 AM
Creation date
5/20/2020 11:34:17 AM
Metadata
Fields
Template:
EHD - Public
ProgramCode
3500 - Local Oversight Program
File Section
ARCHIVED REPORTS
FileName_PostFix
XR0009935
RECORD_ID
PR0545678
PE
3528
FACILITY_ID
FA0005843
FACILITY_NAME
MASONITE CORPORATION
STREET_NUMBER
433
Direction
W
STREET_NAME
SCOTTS
STREET_TYPE
AVE
City
STOCKTON
Zip
95203
APN
14704044
CURRENT_STATUS
02
SITE_LOCATION
433 W SCOTTS AVE
P_LOCATION
01
P_DISTRICT
001
QC Status
Approved
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EHD - Public
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i <br /> ISite Background Information Prem Dor <br /> Page 4 of 7 <br /> STRATIGRAPHY <br /> IIn general, silty clay and clayey silt, with lesser, discontinuous layers of sandy material, were <br /> encountered from surface grade to approximately 23 feet to 25 feet bsg From between 23 feet and <br /> I 25 feet to approximately 29 feet bsg, silty sand and fine-to coarse-grained sand was identified,grain <br /> size appeared to increase with depth From 29 feet to approximately 67 feet bsg,silty clay and clayey <br /> silt were encountered,with a thin,discontmous layer of sandy material encountered at approximately <br /> I34 feet bsg in borings MW-4 and MW-5, a thin layer of sandy sediments and stiff, fine-grained <br /> material was encountered at approximately 52 feet bsg,as well From 67 feet bsg to 76 feet bsg,silty <br /> sand and sand,underlain by silt,was identified in boring CPT-1,with silty clay,clay,and stiff,fine- <br /> grained material encountered from 76 feet to the total depth of boring CPT-1 at 97 feet bsg <br />' SITE CONCEPTUAL MODEL <br />' Based on the data collected to date from soil borings and monitoring well installations, AGE has <br /> developed a conceptual site model (CSM) for the release, migration and distribution of the <br /> contaminants in the subsurface as described below <br /> I • The soil profile beneath the site is generally composed of silt with sand and gravel (fill material) <br /> from surface grade to 6 feet below surface grade (bsg), clays, clayey silts and clayey sands from <br />' 6 feet bsg to 21 feet bsg, fine to coarse sand and silty sand from 21 feet to 29 feet bsg (35 feet at <br /> MW-2),clay with medium to high toughness and plasticity from 29 feet bsg to 36 feet bsg, silt from <br /> 36 feet bsg to 49 feet bsg, and fine sand from 49 feet bsg to 52 feet bsg or beyond <br />' Since initiation of ground water monitoring in October 2003,depth to ground water measurements <br /> have fluctuated between approximately 18 5 feet and 21 feet below the top of the casing(btoc) The <br />' inferred ground water flow direction generally has been towards the northeast, four times, at <br /> gradients ranging between 0 005 ft/ft and 0 022 ft/ft, ground water flow was towards the east- <br /> northeast once at a gradient of 0 002 ft/ft <br />' <br /> Releases o p f petroleum hydrocarbons occurred from the former on-site USTs Once released to the <br />' subsurface,the contaminants migrated through the fine grained unit directly below the UST area to <br /> a vertical depth of approximately 20 feet bsg, at which point the contaminants encountered a more <br /> porous sand unit and the water table and began to migrate laterally as well as vertically,the direction <br />' of lateral migration should be towards the northeast, in the preferred ground water flaw direction, <br /> however, maps of contaminant distribution suggest a more uniform spread away from the former <br /> UST location The vertical migration of soil contamination appears to be slowed by the clay layer <br />' encountered from 29 to 36 feet bsg except at the location of boring B3, where significant <br /> concentrations are detected at this depth <br /> • <br />' .Advanced GeoEnvironmental,Inc. <br /> 1 <br />
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