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ARCHIVED REPORTS_FIVE-YEAR WATER QUALITY REVIEW REPORT 11-17-2008
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ARCHIVED REPORTS_FIVE-YEAR WATER QUALITY REVIEW REPORT 11-17-2008
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Last modified
5/14/2020 4:35:22 PM
Creation date
5/14/2020 3:03:08 PM
Metadata
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Template:
EHD - Public
ProgramCode
2900 - Site Mitigation Program
File Section
ARCHIVED REPORTS
FileName_PostFix
FIVE-YEAR WATER QUALITY REVIEW REPORT 11-17-2008
RECORD_ID
PR0516727
PE
2965
FACILITY_ID
FA0012758
FACILITY_NAME
DIAMOND FOOD PROCESSORS OF RIPON
STREET_NUMBER
942
Direction
S
STREET_NAME
STOCKTON
STREET_TYPE
AVE
City
RIPON
Zip
95366
APN
25934012
CURRENT_STATUS
01
SITE_LOCATION
942 S STOCKTON AVE
P_LOCATION
05
P_DISTRICT
005
QC Status
Approved
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EHD - Public
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Five-Year Water-Quality Report November 17,2008 <br /> Neenah Paper FR LLC Ripon Mill Page 7 of 19 <br /> 10. July 2007 data for City of Ripon municipal well MW-4 shows a nitrate concentration of 9.2 <br /> mg/L(the June 2002 concentration was 38 mg/L), characteristic of local water quality <br /> (Appendix A). Ripon municipal well MW-9, located immediately east of the NP site was <br /> nondetect for nitrate in July 2007 (June 2002 showed nitrate concentration of 6.2 mg/L). <br /> GROUNDWATER MOVEMENT <br /> 11. In the semiperched zone during the period 2002 through 2007, the direction of the groundwater <br /> gradient varied on a seasonal basis, similar to historic patterns. In the first and third quarters, <br /> the gradient in the southeast part of the site(near the Stanislaus River) generally is from the site <br /> towards the river(to the south-southeast). In the second quarter, the gradient in the southeast <br /> part of the site (near the Stanislaus River) generally is from the river towards the site(to the <br /> north-northwest). In the fourth quarter, the gradient is often more or less parallel to the river in <br /> the southeast part of the site. In the northern and western parts of the site,the gradient <br /> generally is away from the site,ranging from northwest to west (Figure 3). <br /> 12. In the upper aquifer during the period 2002 through 2007,the groundwater gradient generally <br /> was always away from the central part of the site(to the southwest in the southwestern corner <br /> of the site,to the southeast or east along the eastern part of the site, to the northeast in the <br /> northeast part of the site, and to the northeast in the northwestern part of the site; Figure 4). <br /> 13. In the intermediate zone during the period 2002 through 2007,the groundwater gradient was <br /> similar to that in the upper zone, generally moving away from the site to the northwest and <br /> southeast(Figure 5). <br /> 14. Percolation of effluent in fields causes groundwater mounding in the semiperched zone to vary <br /> in location beneath the percolation areas. <br /> 15. Groundwater mounding in the semiperched zone is reflected,but muted, in the upper and <br /> intermediate zones. <br /> GROUNDWATER QUALITY <br /> 16. In the semiperched zone, areas of elevated TDS are associated with areas of groundwater <br /> mounding (high groundwater). The highest TDS generally is found in the vicinity of ASB-2 <br /> and in the northeast corner of the site (Figure 6). Elevated TDS beneath ASB-2 reflects <br /> percolation of effluent downward from the pond. Elevated TDS in the northeastern part of the <br /> site reflects concentration of constituents from evapotranspiration by the eucalyptus trees in <br /> this area. <br /> 17. In the upper zone, TDS concentrations are higher in areas of elevated groundwater. The <br /> highest concentrations are observed in the southwestern and northeastern corners of the site; <br /> concentration decreases to the southeast(Figure 7). The pattern of TDS in the upper aquifer <br /> reflects downward migration of applied effluent and clean irrigation water drawn towards the <br /> southeast by the active production wells there. <br /> 003044.02 Lawrence&Associates <br /> W.â˘IClientslFoxRiver-NeenahU year review reports Year Review 2008Weenah_5YearReview Aug2008.doc <br />
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