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ARCHIVED REPORTS_RPT OF WASTE DISCHARGE FOR WASTEWATER DISPERSAL 2011
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ARCHIVED REPORTS_RPT OF WASTE DISCHARGE FOR WASTEWATER DISPERSAL 2011
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Last modified
5/14/2020 4:47:20 PM
Creation date
5/14/2020 3:11:49 PM
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EHD - Public
ProgramCode
2900 - Site Mitigation Program
File Section
ARCHIVED REPORTS
FileName_PostFix
RPT OF WASTE DISCHARGE FOR WASTEWATER DISPERSAL 2011
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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REPORT OF WASTE DISCHARGE- APPENDIX D <br /> Diamond Pet Food Processors of Ripon,LLC June 30,2011 <br /> Report of Waste Discharge—Antidegradation Analysis Page 7 of 14 <br /> The highest TDS level in the intermediate aquifer was across the central part of the site and in the <br /> northeast quadrant of the site in PW-5 (1,100 µmhos/cm). The area of lowest conductivity was in <br /> the northwest quadrant of the site in well M-11-C (130 mg/L; Figure 15). <br /> Infiltration of plant process water is responsible for the elevated TDS levels measured in the <br /> semiperched, upper, and intermediate aquifer over most of the site. The elevated TDS levels in the <br /> semiperched aquifer in the northeastern quadrant of the site, however,which have been up to three <br /> times higher than effluent TDS levels, are likely caused by the eucalyptus trees' concentrating effect <br /> on TDS.6 The elevated TDS levels observed along the western portion of the site,particularly in the <br /> southwest corner of the site,probably reflect the infiltration of higher TDS water originating at the <br /> City of Ripon's MWWTF encroaching onto the DP site. <br /> Stiff patterns are graphic representations of water quality and are created by plotting the <br /> concentrations of anions and cations (in meq/L) in a sample on a horizontal axis and then connecting <br /> the dots to create a unique pattern for each well. Stiff patterns for all wells are presented in Figure <br /> 16. <br /> The patterns illustrate that the best groundwater quality is in the southeast part of the site and the <br /> most degraded groundwater quality is in the northeastern part of the site. As with analysis of <br /> groundwater quality contour maps, the poorest water quality in the northeast can be attributed to the <br /> concentration of constituents from evapotranspiration by the eucalyptus trees in this area.7 <br /> For the second-half 2010 monitoring report, Mann-Kendall trend analysis was perform for all <br /> analytes in all wells. Figure 17 shows a summary of the trend analyses. Trend analyses for TDS <br /> show more improvements in water quality in the southeastern part of the site, reflecting application <br /> of the higher quality surface or groundwater to the east percolation field. The trend analyses also <br /> show more degradation of groundwater quality in the northeastern part of the site, reflecting <br /> concentration of constituents from evapotranspiration by the eucalyptus trees,$ and in the <br /> southwestern part of the site from the inflow of high TDS water from the City of Ripon's MWWTF. <br /> In order to meet the WQPS adopted by the CVRWQCB for the site (Table 3), Diamond predecessor <br /> Neenah Paper chose to import low TDS water from the South San Joaquin Irrigation District <br /> (SSJID) as the preferred corrective action method for reducing TDS levels in Plant effluent water <br /> 6 G.S.Jorgensen,Kenneth H. Solomon,and V. Cervinka,March 1993,Agroforestry Systems for On-Farm Drain Water <br /> Management. <br /> 7 lbid.P. 8 <br /> 8 L&A,November 17,2008,Five-Year Water Quality Review Report. <br /> 010070.00, Task I Lawrence&Associates <br /> w:I clients)diamond pet foods1010107.00-ripon rowdldiamondpet_rowdjune2011_draft.docx <br />
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