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COMPLIANCE INFO_PR0440063_1990-2019
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COMPLIANCE INFO_PR0440063_1990-2019
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Last modified
7/12/2021 3:46:00 PM
Creation date
7/3/2020 11:20:36 AM
Metadata
Fields
Template:
EHD - Public
ProgramCode
4400 - Solid Waste Program
File Section
COMPLIANCE INFO
FileName_PostFix
PR0440063_1990-2019
RECORD_ID
PR0440063
PE
4467
FACILITY_ID
FA0002971
FACILITY_NAME
MUSCO FAMILY OLIVE CO
STREET_NUMBER
17950
Direction
W
STREET_NAME
VIA NICOLO
City
TRACY
Zip
95377
APN
20911032
CURRENT_STATUS
02
SITE_LOCATION
17950 W VIA NICOLO
P_LOCATION
99
P_DISTRICT
005
QC Status
Approved
Scanner
SJGOV\sfrench
Supplemental fields
FilePath
\MIGRATIONS\SW\SW_4467_PR0440063_17950 W VIA NICOLO_.tif
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EHD - Public
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WASTE DISCHARGE REQUIREMENTS -2- <br /> MUSCO OLIVE PRODUCTS, INC. <br /> CLASS II SURFACE IMPOUNDMENTS <br /> SAN JOAQUIN COUNTY <br /> return of perched water. The Discharger has indicated that the perched ground water zone <br /> does not extend beneath the entire site as verified by surface and subsurface soil conditions <br /> explored by boring and backhoe test pits as described in a report, dated 21 December 1992. <br /> 6. Due to the confined nature of the aquifers beneath the surface impoundments and the thick <br /> sequences of clay, ground water monitoring would not provide early detection of a leak from <br /> the surface impoundments. Therefore, a system of lysimeters is used as the primary leak <br /> detection system in the vadose(unsaturated) zone beneath the surface impoundments. <br /> 7. The Discharger has installed 38 lysimeters under Ponds A and B at 5 and 10 foot depths to <br /> monitor the vadose zone. Two additional lysimeters are functioning as background vadose <br /> zone monitoring points. Attachment C shows the lysimeter designations. Based on <br /> monitoring reports, the lysimeters are normally dry with the exception of LY#17, 18, 23, and <br /> 24. The vacuum pumps for the lysimeters are left on for up to 30 days. When there is a <br /> sufficient amount of fluids available, sampling is performed. Because TDS levels sampled <br /> from the lysimeters are higher than TDS results (5440 mg/1) in W2 (920 mg/1), it is <br /> recommended that further investigation is needed to determine the cause. <br /> WASTES AND THEIR CLASSIFICATION <br /> 8. `Designated waste' is defined in Chapter 15, Section 2522(x)(1), as a nonhazardous waste <br /> which consists of, or contains pollutants which, under ambient environmental conditions at <br /> the waste management unit,could be released at concentrations in excess of applicable water <br /> quality standards, or'which,-could cause degradation of watersofthe state:- <br /> 9. The discharge,especially after evaporative concentration,poses a significant threat to water <br /> quality. Therefore, the discharge is a `designated waste' and as such must be discharged to a <br /> Class II surface impoundment as required by Chapter 15. <br /> 10. The Report of Waste Discharge described the waste as dilute salt brine, sodium hydroxide, <br /> and ferrous gluconate. The Discharger has stated that the chemical makeup will be as follows: <br /> Constituent Concentration <br /> pH 8-9 <br /> EC 19,000 µmhos/cm <br /> TDS 14,000 mg/l <br /> COD 9,000 mg/1 <br /> CLASS II SURFACE IMPOUNDMENTS <br /> 11. Kenneth Kjeldsen, a California Registered Civil Engineer has certified that,for all three <br /> surface impoundments,the surface impoundment design(including leachate collection and <br /> removal system), vadose zone monitoring design and ground water monitoring system design <br /> comply with Chapter 15 for a Class II surface impoundment. <br /> 12. The design of all three surface impoundments consist of an outer compacted clay liner two feet <br /> thick with a permeability to the brine waste of less than 1 x 10-6 cm/sec, a sand and geonet <br /> leachate collection system,and a 40-mil synthetic inner liner. The leachate collection system <br /> drains to a sump where leachate is pumped back to the surface impoundment. <br />
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