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FIELD DOCUMENTS_2000-2003
Environmental Health - Public
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EHD Program Facility Records by Street Name
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2900 - Site Mitigation Program
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PR0009002
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FIELD DOCUMENTS_2000-2003
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Last modified
6/17/2020 3:11:07 PM
Creation date
6/17/2020 1:43:21 PM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2900 - Site Mitigation Program
File Section
FIELD DOCUMENTS
FileName_PostFix
2000-2003
RECORD_ID
PR0009002
PE
2960
FACILITY_ID
FA0004040
FACILITY_NAME
SPX COOLING TECHNOLOGIES INC
STREET_NUMBER
200
Direction
N
STREET_NAME
WAGNER
STREET_TYPE
AVE
City
STOCKTON
Zip
95215
APN
14331007
CURRENT_STATUS
02
SITE_LOCATION
200 N WAGNER AVE
P_LOCATION
99
P_DISTRICT
002
QC Status
Approved
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EHD - Public
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SPX Corporation <br /> incorporated into the Basin Plan. The Stockton Diverting Canal _ not connected to the Calaveras River <br /> during the dry period and therefore does not exchange water wit: tie Calaveras River during this period. <br /> We believe that during the dry period the Canal should not be cons:L.'red part of the Calaveras River. <br /> ✓ Application of the drinking water standards to the Stockton Dive—; Canal makes no sense. To the best of <br /> our knowledge no drinking water intakes are downstream of the MCTC discharge. The Canal is essentially <br /> dry during 6 months of the year and therefore the Canal is an unre-le drinking water supply. <br /> ✓ Groundwater is a source of drinking and irrigation water supplies zownstream of MCTC discharge and in <br /> the vicinity of the Stockton Diverting Canal and the MCTC facili As the RWQCB has noted during the <br /> dry period the MCTC discharge evaporates and/or percolates to He groundwater, which is a source of <br /> drinking and irrigation water. The RWQCB also agrees that the --aturally occurring groundwater TDS <br /> levels are higher than the 500 mg/1 limit proposed for the MC—,: wastewater discharge permit. If the <br /> groundwater that is used for drinking and irrigation has TDS level =eater than 500 mg 1. it makes no sense <br /> for RWQCB to require the MCTC discharge cleanup the natura:: xcurring levels of TDS that obviously <br /> have not adversely impacted the use of groundwater for drinking -=irigation. <br /> We are submitting specific comments on the conditions, monitoring, lits::= and terms of the tentative wastewater <br /> discharge requirements as follows: <br /> • Findings: <br /> ➢ Item 2: MCTC has ceased all operations at the facility exce`: -or the operation of the Groundwater <br /> Extraction and Treatment System. <br /> ➢ Item 4: Because an impermeable cap was placed over the con?--.inated soil area, we believe that the <br /> requirement for reinjecting 5% of the treated water into the shaicw soil to flush contaminants defeats the <br /> purpose of an impermeable cap and should therefore be eliminate;_ 3etuming 5% of the-treated water will <br /> not have a significant impact on minimizing the dewatering of the as-Mier. <br /> • Item 19: The Stockton Diverting Canal is a man-made canal cos_xted to divert the natural river flow to <br /> provide irrigation water and flood control from October 1 to Apr _ of each year. During the period from <br /> April 1 to October 1 of each year the Stockton Diverting Canal has plaited or no flow except for the MCTC <br /> Stockton CA wastewater discharge. If the MCTC, Stockton C; facility wastewater discharge were <br /> eliminated there would be no aquatic organisms because there mould be insufficient water to support <br /> aquatic life. Therefore, we believe that establishing the effluent '----s for Copper (Cu) 'cased on the acute <br /> and/or chronic aquatic life toxicity without the dilution is in_.^ropriate. The dilution factor of the <br /> Calaveras River should be the appropriate dilution factor, i.e. the nt at which the Canal reconnects with <br /> the Calaveras River. The purpose of the groundwater extraction �d treatment system is to cleanup the <br /> groundwater and capping the contaminated soil areas was intended:o prevent stormwater contamination. In <br /> fact, a pilot test of an insitu groundwater treatment is planned that=ay lead to cleanup of the contaminated <br /> groundwater to meet the groundwater quality criteria in the next ' vears. The discharge will then cease <br /> and the Stockton Diverting Canal will be dry each year during A7-- : to October 1. We do not believe that <br /> MCTC should be required to maintain an unnatural aquatic env, c—ent. Therefore, we don't think that it <br /> is appropriate to impose the Cu limit based on acute and chronic -,:aric toxicity criteria for the undiluted <br /> waste discharge. In addition, aquatic toxicity testing to date _as demonstrated that the discharge <br /> consistantly meets the criteria. <br /> ➢ Item 20: Our objections to the proposed new limit Cr-6based on:he acute and chronic aquatic toxicity are <br /> the same as our objections for the proposed new Cu limit. <br /> ➢ Item 23: See previous comments on pages 1 and 2. <br /> • Monitoring Requirements <br /> ➢ Influent Monitoring: We have been operating the groundwaw extraction and treaanent system and <br /> monitoring the groundwater and the influent to the treatment s}s m for over 10 year. We believe the <br /> Page 2 of J <br /> 01/C <br /> C:\WINDOWS\TEMPWrafl NPDES wmmenu.Jrc <br />
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