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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
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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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CvvATC <br /> • <br /> A S S O C I A T E S I N C <br /> 37 feet The soil samples collected from beneath Vault 8 will be analyzed for total and hexavalent chronuum, <br /> alkalinity, ammonium/ammonia, arsenic, total organic carbon, copper, dissolved and total iron, dissolved and <br /> total manganese, methane, nitrate, dissolved oxygen, oxidation-reduction potential, sulfate, and zinc Soil <br /> collected from beneath Vault 8 will also be used for bench scale testing as described below <br /> All of the groundwater monitoring wells (MW-1 through MW-9) will be sampled for the constituents listed <br /> in the preceding paragraph to provide for baseline constituent concentrations Sampling of the monitoring <br /> wells for baseline characterization can be conducted commensurate with quarterly groundwater monitoring <br /> activities An unpreserved groundwater sample (3 liters) will be collected from MW-3 after the well has <br /> been purged of three well volumes using a submersible pump, and one liter of unpreserved tap water will be <br /> collected from the facility and delivered to the laboratory to be utilized for bench scale testing as described <br /> below The volume of soil and groundwater samples collected will be based on laboratory requirements <br /> BENCH SCALE TESTING <br /> Recent groundwater samples collected from the site contained up to 3 8 mg/1 of CrVL Two compounds that <br /> can reduce and stabilize CrVI and are suitable for infection into the subsurface are ferrous iron(Feil)solution <br /> and calcium polysulfide(Cascade solution) The following discussion is based on information was obtained <br /> from PRIMA Environmental <br /> • Ferrous Iron Solution <br /> Fell is prepared by dissolving ferrous sulfate heptahydrate in pH2 water (acidified with sulfuric acid) <br /> Generally, concentrated stock solution is prepared and a small amount is added to soil and groundwater <br /> to obtain the desired initial concentration FeII reacts with CM to form CrIH, which co-precipitates as <br /> an iron/chromium hydroxide when the pH is greater than about 5 (Eqn 1) <br /> CrVI+3Fell—> CrIlI+3FeM —i' iron/chromium hydroxides Eqn 1 <br /> Based on this stoichiometry, 3 2 grams (g) Fell are needed to reduce 1 g of CrV1 Fell must be added <br /> as an acidic solution (pH 2-4) in order to prevent it from oxidizing to FeIII, which is ineffective for <br /> treating CrVI In general, the buffering capacity of site soil and groundwater will allow pH to return to <br /> normal once application is complete As the pH increases to greater than about pH 5, the CrIII will co- <br /> precipitate with iron to form tron/chromium hydroxides, which are typically more stable (less soluble) <br /> than chromium hydroxide Excess iron will also precipitate as iron hydroxide [Fe(OH)3] <br /> Calcium Polysulfide(Cascade <br /> I <br /> Cascade is a purchased product that is used as received Cascade reduces CM to CrIII by a variety <br /> of chemical reactions that ultimately produce solid chromium hydroxide, sulfate, and sulfur <br /> Intermediate products may include sulfide and thiosulfates Concentrated Cascade is basic (pH <br /> 10), but the injection pH will be lower because Cascade is normally diluted prior to use In addition, <br /> the natural buffering capacity of site soil and groundwater will often minimize long-term changes in <br /> pH <br /> S lenvirornnentai1625831repoetSaCVLsedWKP-Bench testdoc 4 <br />
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