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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
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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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AGENCY NAME: Musco Family Olive Company and the Studley Company Page 4 <br /> FACILITY NAME: Wastewater Treatment &Land Disposal Facility <br /> Self-Monitoring Report Review. Discharger self-monitoring reports (SMRs) are timely, but continue to <br /> be incomplete. The Monitoring and Reporting Program(MRP)requires daily wastewater pond <br /> monitoring, but the Discharger only monitors on weekdays. The MRP requires daily flow <br /> measurements and BODS loading rate calculations of all land application areas receiving wastewater,but <br /> the Discharger does not measure the flow or calculate the BODS loading of fields that irrigate <br /> wastewater without using sprinklers. The MRP requires a daily estimate of the storm water flow into the <br /> storage reservoir based on the intensity of the storm and the drainage basin, but the Discharger only <br /> provides a monthly estimate of the storm water flow based on the change in surface elevation of the <br /> settling pond. The MRP requires the Discharger note and explain all violations, but the Discharger's <br /> summary does not include this information. <br /> Housekeeping Deficiencies. The Discharger's operation and maintenance of many areas within the <br /> facility exposed to rainfall was unsatisfactory. General housekeeping was poor in a manner that could <br /> degrade the quality of storm water runoff and of groundwater quality the facility. One of the sumps had <br /> several cracks in its concrete floor (Photo 1). When asked when the sump was last inspected for integrity, <br /> Mr. Hall could not say when. In the tank farm area, we noted a broken floor grate (Photo 2), pallets <br /> loaded with deteriorated bags of chemicals (Photos 3, 4), a clogged gutter grate (Photo 5), and multiples <br /> spills and leaks of storage solution (mostly acetic acid) from storage vessels and piping in the tank farms <br /> (Photos 6, 7). When asked about the leaks, Mr. Benjamin Hall replies, "You cannot stop the drips." In <br /> the facility's solid waste and materials storage area, we saw numerous spilled perforated cans that were <br /> draining brine canning solution onto the pavement (Photos 8, 9). Mr. Hall indicated the canning brine has <br /> a total dissolved solids concentration of about 10,000 mg/L. Also in the solid waste and materials storage <br /> area, we observed stained soil evidencing spill(s) from a diesel storage and filling station (Photo 10). Near <br /> the diesel filling station, we noted open and nearly full containers of what appeared to be spent motor oil <br /> (Photo 11). Mr. Hall said Musco had plans for sheltering chemical and petroleum storage areas from rain, <br /> but will not implement the plans for another two months or so. Water observed in the olive receiving area <br /> (Photos 12, 13) may be wastewater, storm water, or a combination of both. <br /> The above examples of poor housekeeping constitute a violation of Discharge Specification B.11, which <br /> requires the Discharger operate all systems and equipment to maximize treatment of wastewater and <br /> optimize the quality of the discharge. Onsite disposal of canning brine from damaged cans, if it is to <br /> occur at all, should be the Title 27 ponds. <br /> Wastewater Impoundments. Discharge Specifications B.S.a and c require the wastewater from 1 to 2 <br /> feet below the surface of the settling pond and the storage reservoir maintain a dissolved oxygen (DO) <br /> concentration greater than 2 mg/L and a pH between 7.5 and 8.5. Effluent Limitation C.1 establishes the <br /> following concentration limitations (in mg/L) for wastewater discharged to the settling pond: TDS <br /> 2,047, Sodium 597, and Chloride 601. The wastewater's chloride concentration exceeded this limit <br /> twice in December 2002. Recent SMRs (December 2002 and January 2003) reveal impounded <br /> wastewater consistently has a DO concentration below 2.0 mg/L, occasionally has a dissolved sulfide <br /> concentration greater than 0.1 mg/L, and frequently has a pH less than 7.5. <br /> We detected slight odors in the settling pond vicinity. A field measurement of settling pond wastewater <br /> taken at 2:43 pm revealed a DO concentration of 0.42 mg/L, an electrical conductivity (EC) of <br /> 2800 µmhos/cm and a pH of 6.75. Mr. Hall indicated an additional aerator for the 1-million gallon <br /> settling pond and ten 25-horsepower aerators for the 84-million gallon storage reservoir were on order. <br /> We observed the surface of wastewater in the settling pond to have a layer of oily scum (Photo 14), <br /> which is likely due to the presence of olive oil in the wastewater. The settling pond is unlined has steep <br />
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