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SITE INFORMATION AND CORRESPONDENCE
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Last modified
2/5/2020 12:26:47 PM
Creation date
2/5/2020 10:23:06 AM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2900 - Site Mitigation Program
File Section
SITE INFORMATION AND CORRESPONDENCE
RECORD_ID
PR0009051
PE
2960
FACILITY_ID
FA0000649
FACILITY_NAME
FORMER NESTLE USA INC FACILITY
STREET_NUMBER
230
STREET_NAME
INDUSTRIAL
STREET_TYPE
DR
City
RIPON
Zip
95366
APN
25938001
CURRENT_STATUS
01
SITE_LOCATION
230 INDUSTRIAL DR
P_LOCATION
05
P_DISTRICT
005
QC Status
Approved
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r' <br /> STATE OF CALIFORNIA-Environmental Protectio . ency • PETE WILSON, Governor <br /> CALIFORNIA REGIONAL WATER QUALITY CONTROL BOARD <br /> CENTRAL VALLEY REGION I ",L HEALTH <br /> 3443 Routier Road, Suite A <br /> Sacramento, CA 95827-3098 AUGn1 pyo ! <br /> PHONE: (916) 255-3000 Jai G 10 PH 1: 11 <br /> FAX: (916)255-3015 <br /> 9 August 1994 <br /> Mr. Frank Zumstein <br /> Nestles Beverage Company <br /> 230 Industrial Ave. <br /> Ripon, CA 95366 <br /> FINAL REMEDIAL INVESTIGATION REPORT, NESTLES BEVERAGE COMPANY, RIPON <br /> We have reviewed the Final Remedial Investigation Report, Nestles Ripon Facilitv. received <br /> February 1, 1994. The report is well written and the data are presented in easily discernable format. <br /> This report presents a good description of all past remedial work at this facility. Even though <br /> extensive investigative has been performed we believe, based on data presented, that further <br /> investigation is necessary to complete the remedial investigation. For example, the report discusses <br /> several possible source areas but, the vadose zone contamination has not been characterized. Also <br /> several ground water units are not well enough defined to describe the complete extent of the <br /> contaminant plume. This work will have to be done before remedial design can be completed. <br /> Below is specific comments on the Final Remedial Investigation Report: <br /> I. Section 4.1 Ground Water, Paragraph 2; <br /> The report states, "Non-detections in production wells, however, were considered in defining <br /> the extent of impacts in all units." This appears inappropriate. Many production wells cover <br /> several ground water units and nondetect in a well may represent dilution rather than no <br /> contamination in any of those units. In general production wells should not be used in plume <br /> definition. <br /> II. Section 4.2.2 Soil Gas Sampling Results, Paragraph 1; <br /> The report states, " Although the industrial sewer located along Industrial Avenue and Fourth <br /> Street has been considered as a possible explanation for elevated TCE in this area, samples <br /> taken from the sewer and wells near the sewer in 1992 indicate that the sewer is not a <br /> potential source." This statement does not appear to be supported by the data. Monitoring <br /> well M-8, which is adjacent to the sewer line, showed the highest TICE concentration in the <br /> first ground water unit. All monitoring wells adjacent to the sewer show detectable levels of <br /> TCE. Also since the TCE discharge to the sewer line occurred over 20 years ago, it is likely <br /> that samples directly from the sewer would not detect TCE. <br /> III. Section 4.2.3 Soil Vapor Extraction, Paragraph 4; <br /> This paragraph provides only a cursory description the eight months of vapor extraction <br /> system results following 10 January 1988 start-up at vapor extraction well VE-4. During <br /> those months the concentration leaving the extraction well increased from nondetect to over <br /> 10ppm of TCE. This increase indicates a source area within the sphere of influence of VE-4, <br /> but not right at the location of VE-4. This source area should be identified, and its lateral <br /> and vertical extent determined, in order to more effectively remediate it. <br /> IV. Section 5.1 Transport Media, Paragraph 1; <br />
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