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SITE INFORMATION AND CORRESPONDENCE
Environmental Health - Public
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2900 - Site Mitigation Program
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PR0516772
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SITE INFORMATION AND CORRESPONDENCE
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Last modified
6/1/2020 12:44:39 PM
Creation date
6/1/2020 12:23:17 PM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2900 - Site Mitigation Program
File Section
SITE INFORMATION AND CORRESPONDENCE
RECORD_ID
PR0516772
PE
2965
FACILITY_ID
FA0012793
FACILITY_NAME
MUSCO OLIVE LAND APP/TITLE 27
STREET_NUMBER
17950
Direction
W
STREET_NAME
VIA NICOLO
STREET_TYPE
RD
City
TRACY
Zip
95377
APN
20911032
CURRENT_STATUS
01
SITE_LOCATION
17950 W VIA NICOLO RD
P_LOCATION
99
P_DISTRICT
005
QC Status
Approved
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ORDER NO.R5-2002-0148 10 - <br /> INFORMATION SHEET <br /> MUSCO FAMILY OLIVE COMPANY AND THE STUDLEY COMPANY <br /> WASTEWATER TREATMENT AND LAND DISPOSAL FACILITY <br /> SAN JOAQUIN COUNTY <br /> The Discharger has submitted two quarters (April 2002 and July 2002) of water quality data for the site. <br /> With limited data, staff calculated the background groundwater monitoring wells in each zone by <br /> calculating the average value, and adding two standard deviations to establish a background water <br /> quality for the site. This procedure is consistent with CCR Title 27 Section 20415. <br /> Because two saturated zones have been identified at the site, each zone must include a unique water <br /> quality value. Wells MW-1 and MW-8 were selected as the background wells for the water table aquifer <br /> (i.e., Kleinfelder's "perched zone") and the confined unit(Kleinfelder's "deep zone") respectively. Well <br /> MW-1 was selected because it is the furthest upgradient shallow zone well. Although MW-8 is not the <br /> furthest upgradient confined zone well, it is downgradient of the processing facility which is not <br /> considered a source area, and it is located in an area that has not historically been used for land <br /> application until recently. The other confined zone wells were evaluated for use and determined to be <br /> inappropriate for the following reasons: Well MW-12 is located adjacent to the Title 27 surface <br /> impoundments, Well MW-9 is dry, and Well MW-4 is located adjacent to the 1 Mgal settling pond. <br /> Well MW-7 might be appropriate, however it is located downgradient of the Title 27 surface <br /> impoundments and therefore it was not selected. <br /> Staff calculated background groundwater quality values for both the water table and confined zones, as <br /> shown on the table below. For the water table aquifer, the limits are: TDS 850 mg/L, chloride 150 <br /> mg/L, and sodium 260 mg/L; for the confined aquifer they are: TDS 1,300 mg/L, chloride 400 mg/L, <br /> and sodium 300 mg/L. <br /> Well Date Units TDS Chloride Sodium <br /> Water Table Aquifer <br /> MW-1 4/10/02 mg/L 690 67 240 <br /> MW-1 6/24/02 mg/L 770 110 250 <br /> Average -- mg/L 730 88.5 245 <br /> St. Dev. mg/L 57 30 7 <br /> Background -- mg/L 850 150 260 <br /> Confined Aquifer <br /> MW-8 4/10/02 mg/L 1,300 130 280 <br /> MW-8 6/24/02 mg/L 1,300 270 290 <br /> Average -- mg/L 1,300 200 285 <br /> St. Dev. -- mg/L 0 99 7 <br /> Background mg/L 1,300 400 300 <br /> Alternative No. 4—Use of Regional Wells <br /> The 7 August 2002 Revised Background Water Quality Preliminary Evaluation Report described <br /> problems with the use of the onsite monitoring wells, and instead proposes the use of regional <br /> domestic/agricultural/industrial wells to determine the background groundwater quality. Staff disagree <br /> with a number of the conclusions in the report and consider a number of the conclusions unsupported <br /> based on the technical information presented in the reports. For example: <br />
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