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2900 - Site Mitigation Program
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PR0516611
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SITE HISTORY
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Last modified
1/15/2020 4:25:57 PM
Creation date
1/15/2020 4:15:38 PM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2900 - Site Mitigation Program
File Section
SITE HISTORY
RECORD_ID
PR0516611
PE
2965
FACILITY_ID
FA0012706
FACILITY_NAME
BEAR CREEK WINERY
STREET_NUMBER
11900
Direction
N
STREET_NAME
FURRY
STREET_TYPE
RD
City
LODI
Zip
95240
APN
06116026
CURRENT_STATUS
01
SITE_LOCATION
11900 N FURRY RD
P_LOCATION
99
P_DISTRICT
004
QC Status
Approved
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EHD - Public
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Vincent Westphal • - 3 - • 28 July 2003 , <br /> A Draft RWD prepared by FCE was submitted in February 2002; that report described an <br /> inadequate groundwater monitoring network. RWD Section 3.3, Groundwater Water Quality <br /> stated: <br /> "There are no wells that sample directly up and down gradient of the disposal field, <br /> therefore it is difficult to draw definitive conclusions about the effect of the Winery's disposal <br /> field on groundwater. However, the well that is most likely to be influenced by the <br /> wastewater disposal fields is monitoring well 3 (MW3), which is the southern most of the two <br /> monitoring wells to the west of the fields. " The report continues, "The concentration of total <br /> dissolved solids (TDS) measured in MW3 is higher than the concentration measured in the <br /> presumed up gradient well, MW2. The typical potassium concentration ofgrape juice is <br /> around 1,200 to 1,400 mg/L, while that of wine is around 800 mg/L. The Winery's <br /> wastewater is presumably enriched in this cation. Well 3, the presumptive "down gradient" <br /> well, has an elevated concentration ofpotassium compared to Well 2. " <br /> To reinforce those conclusions, in Section 3.4, of the same RWD, Summary of Findings states: <br /> "...the land disposal system may be causing some elevated mineralization to occur due to <br /> the elevated levels of potassium in the wastewater. " <br /> Staff notes that the RWD proposed adding 57 acres to the land areas used for application of <br /> wastewater and groundwater monitoring was not recommended in any of the new land areas. <br /> Additionally, new land application areas have already been developed and are in use prior to <br /> characterization of the groundwater quality. Active land application areas require installation of <br /> groundwater monitoring wells without further delay. <br /> On 15 April 2002 a Revised Report of Waste Discharge (dated March 2002)prepared by FCE was <br /> submitted. The Revised RWD Section 3.3 Groundwater Water Quality includes the same text <br /> quoted above. The Revised RWD states, "There are no wells that sample directly up and down <br /> gradient of the disposal fields, therefore it is difficult to draw definitive conclusions about the <br /> effect of the Winery's disposal field on groundwater. " The report goes on to state Well MW3 <br /> appears to be impacted by the wastewater application. <br /> Groundwater Monitoring Reports <br /> Revised Monitoring and Reporting Program (Revised MRP)No. 71-37 was issued on <br /> 25 September 2000 and requires groundwater monitoring. While either FCE or ASE has prepared <br /> the reports, both companies have reported higher concentrations of dissolved solids in Well MW-3. <br /> The First Quarter 2003 monitoring report prepared by FCE states, <br /> "The data show that monitoring well 3, which is best situated to be influenced by <br /> applications on the primary waste disposal area, carries a heavier burden of dissolved <br /> substances than does well 2 which is crossgradient from it and from the disposal area. <br /> Well 1, which is presumed to be upgradient of waste applications by Bear Creek Winery, <br /> also exceeds well 2 in TDS Thus, the differences between well 2 and well 3 are not <br /> unambiguously linked to the occasional disposal of wastewater between the two. " <br /> WSen_Joequin_Nonl 5%Stdfl06nenWm Joequin\Bear Creek\weStpIW 21 July 03.dm <br />
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