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ARCHIVED REPORTS XR0003284
EnvironmentalHealth
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2900 - Site Mitigation Program
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PR0001781
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ARCHIVED REPORTS XR0003284
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Last modified
7/3/2019 12:04:47 PM
Creation date
7/3/2019 10:39:34 AM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2900 - Site Mitigation Program
File Section
ARCHIVED REPORTS
FileName_PostFix
XR0003284
RECORD_ID
PR0001781
PE
2960
FACILITY_ID
FA0004090
FACILITY_NAME
DIAMOND WALNUT GROWERS INC
STREET_NUMBER
1050
STREET_NAME
DIAMOND
STREET_TYPE
ST
City
STOCKTON
Zip
95205
APN
155 320 19 5
CURRENT_STATUS
01
SITE_LOCATION
1050 DIAMOND ST
P_LOCATION
01
QC Status
Approved
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EHD - Public
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ASSOCIATES(YVATC <br /> I NC <br /> 2Cr04+ 3CaS5 + 8H2O -> 2Cr(OH)3 +3Ca(OH)2+4(OH)-+ 15S Eqn 2 <br /> CrT17 Cascade Crill <br /> S52-+31202 -+ S2032-+3S Eqn 3a <br /> 2Cr04_+ 3 S2032-+5H2O -> 2Cr(OH)3 +3SO42 +3S +4(OH)- Eqn 3b <br /> CrP7 Crill <br /> For CrVI reduction and stabilization, the manufacturer recommends using a sulfur to CrVI molar ratio <br /> of 10 According to the product literature Cascade (concentrated, as obtained from the manufacturer) <br /> contains 14 moles sulfur/gallon Thus, 0 071 gallons of Cascade is needed to treat 1 kg of CrVL <br /> which is equivalent to 0 27 ml Cascade/g CrVI However, Cascade is a non-selective reducing <br /> agent and may also react with soil, air and other metals <br /> It should be noted that the chronuum hydroxide formed by this treatment method is more soluble than <br /> an iron/chromium hydroxide However, better subsurface transport may be possible with Cascade® <br /> because it is slower to decompose than Is FeII <br /> The goals of the proposed treatability testing are to estimate the dose requirements for each reductant <br /> and to evaluate the effect of treatment on downgradient water quality <br /> . Methodology <br /> Sort and Water Buffermg Curves <br /> Because the reducing agents proposed can affect the pH of the soil and groundwater, buffering curves <br /> will be generated to determine how much reagent can be added without causing long-term effects Soil <br /> will be combined with dilute sulfuric acid (pH 1, pH 2, and pH 3) dilute sodium hydroxide (pH 9, 10, <br /> 11) in a 1 1 soil to liquid ratio and the pH of the aqueous phase monitored over time Groundwater will <br /> be titrated with dilute sulfuric acid and with dilute sodium hydroxide Clean site tap water will be <br /> titrated with dilute sulfuric acid (Groundwater will be titrated to estimate how much residual soil <br /> acidity or alkalinity it may neutralize, while clean site tap water will be titrated in order to determine <br /> how much acid will be needed if FeII is used as the reducing agent) <br /> Estinxa ion of Dose Requiremen&Effect on Downgra&ent Water Quality <br /> Batch tests will be conducted to estimate the amount of each reducing agent needed to reduce CrVI to <br /> below the clean-up criterion Tests will be performed on groundwater and on soil-groundwater slumes <br /> in order to determine whether soil affects the amount of reagent required The use of soil columns is <br /> not proposed based on the laboratory's experience (soil columns often do not exhibit sufficient <br /> permeability - even using pumping, it can take several hours or days to get enough water through a <br /> column to allow for all of the analyses required The correct number of pore volumes to pass through <br /> the column prior to collecting samples Is another issue) and the composition of the subsurface soils at <br /> the site which generally consist of silt and clayey silt <br /> . Two doses of each reducing agent will be used Controls in which clean water rather than reducing <br /> agent is added will also be performed After approximately 24 hours, the aqueous phases will be <br /> s lenvironmental1625$3\reportslRevisedWU-Bench testdoc 5 <br />
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