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WORK PLANS FILE 2
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3500 - Local Oversight Program
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PR0544513
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WORK PLANS FILE 2
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Last modified
5/31/2019 5:00:53 PM
Creation date
5/31/2019 4:53:22 PM
Metadata
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Template:
EHD - Public
ProgramCode
3500 - Local Oversight Program
File Section
WORK PLANS
FileName_PostFix
FILE 2
RECORD_ID
PR0544513
PE
3528
FACILITY_ID
FA0024115
FACILITY_NAME
WEST CLAY PROPERTY
STREET_NUMBER
639
Direction
W
STREET_NAME
CLAY
STREET_TYPE
ST
City
STOCKTON
Zip
95209
APN
14707110
CURRENT_STATUS
02
SITE_LOCATION
639 W CLAY ST
P_LOCATION
01
QC Status
Approved
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EHD - Public
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27 October 2005 <br /> AGE-NC Project No. 96-0235 <br /> Page 5 of 11 <br /> Major element Initial to Final values changed as follows. Ca from 91 to 35 ppm; Mg from 34 to 16 <br /> ppm; Na from 430 to 350 ppm; Al from 9600 to 850 parts per billion(ppb); Fe from 8800 to 900 <br /> ppb; Mn from 2500 to 390 ppb. Ca and Mg probably decreased due to carbonate pptn, Fe and Mn <br /> to oxide pptn. The Na and Al changes are harder to explain but may be substitution/exchange <br /> reactions for divalent Fe and Mn that are displaced from silicate lattices during their oxidation. <br /> The aquifer water already contained some anomalous trace amounts of heavy metals,including 39 <br /> ppb As, 1.3 ppb Be,9.7 ppb Cr,23 ppb Co, 1.7 ppb Cd, 100 ppb Cu, 1.2 ppb Mo,27 ppb Pb,36 ppb <br /> Ni, 1.9 ppb Se,35 ppb V,69 ppb Zn,in addition to 8800 ppb Fe and 2500 ppb Mn.It is not apparent <br /> why this natural water contains such high concentrations of heavy metals,although complexing with <br /> organic ligands may be important. The high concentrations of Fe and Mn are most likely the result <br /> of bacteria-mediated oxidation of hydrocarbons.By the end of the experiment almost all of these had <br /> diminished significantly, possibly by their sorption on Fe and Mn oxides, or as trace substitutions <br /> into silicates in exchange for Fe and Mn or as substitutions into precipitated carbonates. Two trace <br /> elements increased, Se from 1.9 to 15ppb and Mo from 1.2 to 48 ppb. Both could have been have <br /> been oxidized up from less soluble lower valence solids such as Se°,s or MOODS, or alternatively <br /> may have been mobilized by the decrease in Ca and Mg, if their Ca or Mg salts were at saturation. <br /> In the Final water, TRM total chrome was less than hexachrome, 3.2 vs. 8.4 ppb, but the TTLC <br /> hexachrome value of 9.2 was in much better agreement. The TTLC Final water metals values are <br /> also reported, and the common elements that form oxide/hydroxide solids, Fe, Mn and Al are <br /> significantly higher than their TRM values.Trace element comparisons range from good to slightly <br /> higher to erratic (significantly higher or lower), indicating that sampling and sub-sampling <br /> techniques are extremely important for metals. <br /> Soil <br /> The Initial and Final soil metals values were generally in good agreement after correction for water <br /> content.The only trace metal disagreements are Cu initial value=82 vs.final=47 mg/kg,Zn initial <br /> = 78 vs. final=67. For major elements, Ca initial= 5600 vs. final= 6300,and Na initial=980 vs. <br /> final = 1200, which is opposite and therefore in agreement with their decrease in concentration in <br /> the aquifer water. <br /> Advanced GeoEnvironmental,Inc. <br />
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