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SITE INFORMATION AND CORRESPONDENCE_FILE 2
EnvironmentalHealth
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2900 - Site Mitigation Program
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PR0535112
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SITE INFORMATION AND CORRESPONDENCE_FILE 2
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Last modified
4/15/2020 3:28:03 PM
Creation date
4/15/2020 2:17:32 PM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2900 - Site Mitigation Program
File Section
SITE INFORMATION AND CORRESPONDENCE
FileName_PostFix
FILE 2
RECORD_ID
PR0535112
PE
2957
FACILITY_ID
FA0020296
FACILITY_NAME
CHAPIN BROTHERS INC
STREET_NUMBER
1766
STREET_NAME
MONTE DIABLO
STREET_TYPE
AVE
City
STOCKTON
Zip
95203
APN
13505050
CURRENT_STATUS
01
SITE_LOCATION
1766 MONTE DIABLO AVE
P_LOCATION
01
P_DISTRICT
001
QC Status
Approved
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Mr.Russell Chapin <br /> 1766 W.Monte Diablo Avenue <br /> Page 2 of 7 <br /> Good cross sections can be utilized as the basis to infer initial values and characteristics for a <br /> hydrological model, as is illustrated under point 2 below, but must be augmented with sufficient <br /> site-specific data to generate a valid model. The cross sections allow some intuitive estimates <br /> of hydrological conductivity differences between the sand unit and the fine-grained units, but <br /> give no useful insight to the variation of hydrological conductivity within the sand that may lead <br /> to preferred migration pathways - even oblique or counter to the groundwater flow direction <br /> inferred from field data. For these reasons, the EHD disagrees with ATC's statement that the <br /> cross sections are sufficient to determine groundwater flow characteristics. A model utilized to <br /> justify leaving a large mass of contamination in place should utilize all the site-specific <br /> hydrological characteristics that are practicable to obtain. <br /> Point 2: A one-layer Modflow model could be sufficient to characterize groundwater flow and <br /> contaminant migration, if the layer attributes are properly defined for the model, and the model <br /> is representative of the site. The EHD does not believe that all attributes for this site are or can <br /> be properly characterized with the one-layer model presented, the layer thickness and hydraulic <br /> conductivities being examples of poorly characterized attributes. <br /> ATC utilized a single layer model with a thickness of 25 feet for the Modflow model. The EHD <br /> believes that the characteristics of the sand unit and overlying fine-grained unit require a two- <br /> layer model at a minimum. The sand unit can be anticipated to provide the dominant <br /> contaminant migration pathway in the subsurface, while the hydraulic conductivity and <br /> retardation effects of the overlying fine-grained unit is likely to slow contaminant migration <br /> several orders of magnitude compared to the sand unit. Conversely, the upper fine-grained unit <br /> more likely provides the predominant contaminant flux from both the vadose and saturated <br /> zones. <br /> As shown on the cross sections, the sand unit thickness varies from 3 to 17 feet and averages <br /> 9.5 feet, based on the sand thickness shown on the boring traces in the cross sections. In the <br /> cross sections, ATC shows a laterally continuous sand unit that displays abrupt variations of <br /> thickness and depth. Following the common practice utilized in the environmental field, the <br /> cross sections were constructed utilizing the ground surface as a datum from which to hang the <br /> soil data and were not corrected for elevation differences. The sand unit varies in apparent <br /> thickness from approximately 3 feet (VE-1/ASO-3) to 17 feet (MW-2), the depth to the top of the <br /> sand unit varies from 7 feet below surface grade (bsg, MW-5) to 20 feet bsg (VE-2), and the <br /> depths to the bottom of the sand varies from 17 feet bsg (VE-1/ASO-3) to 26 feet bsg (MW-2). <br /> Therefore, the EHD believes the model should consist of a minimum of two layers with the sand <br /> layer thickness locally varying from 3 to 17 feet and a variable total model thickness up to 26 <br /> feet. Modflow can accommodate layers of variable thickness. <br /> Point 3: Selection of the dominant flow direction based on the contaminant distribution does not <br /> seem unreasonable to the EHD, but reconciling the observed groundwater elevation data and <br /> inferred flow direction with the selected flow direction has implications regarding the hydraulic <br /> characteristics of the site. The EHD did not intend to question the flow direction selected for the <br /> model, but does not have a clear understanding of the interplay of factors that controls <br /> contaminant migration in the subsurface at this site, and did not see the controlling relationship <br /> of factors demonstrated in the ATC model. The basic questions are: How does the plume move <br /> in a subordinate flow direction oblique or counter to the dominant flow directions inferred from <br /> field data, and what are the implications to both the model variables and to possible future <br /> plume migration? Also, how does one select with confidence a hydraulic gradient for use in the <br /> model? <br />
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