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EHD Program Facility Records by Street Name
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12 (STATE ROUTE 12)
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2900 - Site Mitigation Program
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PR0545713
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Last modified
11/19/2024 3:47:20 PM
Creation date
6/15/2020 2:29:09 PM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2900 - Site Mitigation Program
File Section
COMPLIANCE INFO
RECORD_ID
PR0545713
PE
2965
FACILITY_ID
FA0013507
FACILITY_NAME
VAN RUITEN FAMILY WINERY
STREET_NUMBER
340
Direction
W
STREET_NAME
STATE ROUTE 12
City
LODI
Zip
95242
APN
05802005
CURRENT_STATUS
02
SITE_LOCATION
340 W HWY 12
P_LOCATION
99
P_DISTRICT
004
QC Status
Approved
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EHD - Public
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INFORMATION SHEET <br /> ORDER NO. R5-2003-0179 <br /> VAN RUITEN - TAYLOR RANCH LTD. <br /> VAN RUITEN - TAYLOR WINERY LLC <br /> SAN JOAQUIN COUNTY <br /> Van Ruiten—Taylor Ranch Ltd. operates Van Ruiten—Taylor Winery LLC at 340 West Highway 12, <br /> Lodi. The Discharger developed the 200-acre winery and vineyard in 2000. Buildings at the facility <br /> consist of a 4,000 square foot winery and a 1,200 square foot tasting room. The winery will process <br /> approximately 800 to 900 tons of grapes annually to produce approximately 60,000 cases of wine <br /> (approximately 144,000 gallons of wine). <br /> Wastewater is generated in tank cleaning, grape crushing,barrel washing, and equipment/floor <br /> cleaning. A mobile contract wine bottling service will perform bottling, therefore, bottling activities <br /> will not generate a high strength waste stream. Domestic wastewater is discharged to a septic tank and <br /> leachfield system. The domestic system is regulated by San Joaquin County Environmental Health <br /> Department. <br /> Process wastewater treatment consists of collection of wastewater in floor drains, discharge to a <br /> settling sump, rotary screening, biological treatment in a bioreactor, pH neutralization, clarification, <br /> and land application. Applied wastewater will be mixed with supplemental irrigation water. Sludge <br /> from the clarifier will be recirculated to the bioreactor or wasted. The treatment system is anticipated <br /> to reduce the concentration of Biochemical Oxygen Demand (BOD) from 10,000 mg/L to 600 mg/L. <br /> Combined with the size of the land application area, it is anticipated odors will not be generated by the <br /> discharge. Biological treatment is also likely to reduce total nitrogen concentrations and volatile <br /> dissolved solids resulting in a lower concentration of TDS discharged to the land application area. <br /> The water balance estimates the maximum daily process wastewater flow rate at 3,600 gallons per day <br /> (gpd) during the peak grape processing period, with estimated peak daily process flow rates during the <br /> off-season of approximately 1,500 gpd. <br /> Because the site does not have a wastewater storage pond, there is no means to store wastewater during <br /> rain events. The facility has adequate land area to accept wastewater and rainfall (100-year annual <br /> return rainfall amounts). Staff estimates the wastewater discharge is less than one-percent of the land <br /> application area's available hydraulic capacity. Because adequate land application areas are available, <br /> a wastewater storage pond is not required. The Discharger is allowed to discharge wastewater to the <br /> land application areas during rain events provided all requirements of the WDRs are complied with. <br /> It is anticipated that the cropping activities in the land application area will utilize all the nitrogen <br /> applied in the wastewater. Dissolved solids in the wastewater should not cause an increase in the <br /> dissolved solids concentration in the underlying groundwater based on the size of the land application <br /> area, cropping activities, and use of chemicals that are also plant micronutrients when applied to land. <br /> The Discharger has replaced some products (i.e.potassium hydroxide for sodium hydroxide) to <br /> maximize the uptake of the dissolved solids by crops. Nevertheless, groundwater monitoring is <br />
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