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SITE INFORMATION AND CORRESPONDENCE
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Last modified
5/29/2019 11:58:23 AM
Creation date
5/29/2019 11:10:41 AM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2900 - Site Mitigation Program
File Section
SITE INFORMATION AND CORRESPONDENCE
RECORD_ID
PR0508450
PE
2960
FACILITY_ID
FA0008087
FACILITY_NAME
DDJC-TRACY
STREET_NUMBER
25700
STREET_NAME
CHRISMAN
STREET_TYPE
RD
City
TRACY
Zip
95376
APN
25207002
CURRENT_STATUS
01
SITE_LOCATION
25700 CHRISMAN RD
P_LOCATION
99
P_DISTRICT
005
QC Status
Approved
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STATE OF CALIFORNIA -Environmental ProtecAMAgency PETE WILSON Governor <br /> CALIFORNIA REGIONAL WATER QUAMY CONTROL BOARD <br /> CENTRAL VALLEY REGION <br /> 3443 Routier Road, Suite A <br /> Sacramento, CA 95827-3098 <br /> PHONE: (916) 255-3000 <br /> DOD FAX: (916) 255-3052 <br /> 29 December 1993 <br /> Mr. Jim Pinasco <br /> Department of Toxic Substances Control <br /> 10151 Croydon Way, Suite 3 <br /> Sacramento, CA 95827-2106 <br /> GROUND WATER MODELING INTERIM TECHNICAL MEMORANDUM, DEFENSE <br /> DISTRIBUTION REGION WEST (DDRW), TRACY, SAN JOAQUIN COUNTY <br /> We have reviewed the Ground Water Modeling Interim Technical Memorandum (ITM) for DDRW, <br /> Tracy submitted 1 November 1993. We approve of this document and request that DDRW, Tracy <br /> proceed with development of the ground water flow and contaminant transport models. We believe <br /> that development of these models will aid in the design of effective extraction and disposal systems <br /> for the ground water remedial action. We commend Montgomery-Watson for preparing a well <br /> organized document and producing graphics of high quality. Our specific comments to the Ground <br /> Water ITM are presented below. <br /> 1. Section 5.3 MODEL GRID, subsection 5.3.0.3, page 11: We concur with the use of a <br /> variable grid size to optimize the resolution of results in the study area while reducing the <br /> total number of model nodes. However, the base grid of 100 feet by 100 feet used to cover <br /> the DDRW, Tracy site may be too dense and extensive. A less dense fine grid spacing <br /> (perhaps 200 feet by 200 feet) covering approximately the northern one third of the DDRW, <br /> Tracy site is adequate. In addition, a larger grid (increased by a factor of 1.5) should be <br /> used across the entire model domain. The larger nodes/grid pattern should produce similar <br /> modeling results and significantly reduce model manipulation and associated computer time. <br /> 2. Section 5.4 MODEL LAYERS, subsection 5.4.0.1, page 11: This section describes the <br /> uppermost geologic horizon for model layer 1 as the relatively coarse Upper Horizon of the <br /> Upper Tulare Formation. Model layer 1 does not include the siltier saturated Above Upper <br /> Horizon in which the highest levels TCE and PCE concentrations have been recorded. The <br /> Above Upper Horizon must be considered the shallowest model layer. Inclusion of the <br /> Above Upper Horizon as a model layer is necessary to develop the optimum remedial design <br /> for the cleanup of contaminants in the Upper Tulare Formation. <br /> 3. Section 5.5 BOUNDARY CONDITIONS, pages 11 and 12: This section describes the <br /> ground water model boundary conditions as illustrated in Figure 9. We concur with the <br /> boundaries selected for the northern and eastern edges of the study area. However, data <br /> collected from monitoring wells at Triple E Produce and Georgia Pacific, located southwest <br /> of DDRW, Tracy indicate a ground water flow direction in the northwesterly direction in the <br /> shallow zone; as opposed to the northeasterly general regional flow.direction shown in <br /> Figure 16. Maps (prepared by Roy F. Weston, 1992, and Brown & Caldwell, 1991 and <br />
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