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SITE INFORMATION AND CORRESPONDENCE
Environmental Health - Public
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2900 - Site Mitigation Program
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PR0009011
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SITE INFORMATION AND CORRESPONDENCE
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Last modified
5/19/2020 3:01:33 PM
Creation date
5/19/2020 1:47:19 PM
Metadata
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Template:
EHD - Public
ProgramCode
2900 - Site Mitigation Program
File Section
SITE INFORMATION AND CORRESPONDENCE
RECORD_ID
PR0009011
PE
2954
FACILITY_ID
FA0004080
FACILITY_NAME
NAVCOMSTA
STREET_NUMBER
305
Direction
W
STREET_NAME
FYFFE
STREET_TYPE
ST
City
STOCKTON
Zip
952035000
CURRENT_STATUS
01
SITE_LOCATION
305 W FYFFE ST
P_LOCATION
01
P_DISTRICT
001
QC Status
Approved
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Sediment Quality Guidelines DRAFT <br /> Derived Through Equilibrium Partitioning <br /> Principles: <br /> 1. Concentrations of pollutants in sediment interstitial (pore)water have been shown <br /> empirically to be predictive of biological effects. <br /> 2. Water column criteria, such as the USEPA National Ambient Water Quality <br /> Criteria, may be used to determine the degree of biological effects from pollutants <br /> in water. <br /> 3. The equilibrium between pollutants in pore water and in sediment can be used to <br /> derive sediment quality guidelines (SQGs). <br /> 4. For non-ionic organic pollutants, partitioning between pore water and sediment is <br /> influenced largely by the association between the pollutant and organic carbon in <br /> the sediment. Therefore, the degree of association between a non-ionic organic <br /> pollutant and sediment is dependent on the fraction of organic carbon in bulk <br /> sediment (fo,). <br /> 5. The octanol-water partition coefficient (Kaw) for a pollutant can be used to <br /> estimate organic carbon-water partition coefficient (K,) for the pollutant using <br /> the following relationship: <br /> KOC = 0.983(K,,,)+ 0.00028 <br /> 6. Equilibrium partitioning may be applied to mixtures of toxic pollutants in sediment. <br /> 7. The toxicity of some metallic pollutants in sediment is largely dependent on their <br /> association with dissociable sulfides in the sediment. Unassociated metallic <br /> pollutants in pore water are available to cause biological effects. Sulfide bound <br /> metallic pollutants are not available to cause biological effects. <br /> 8. Dissociable sulfides are produced by bacterial breakdown of organic matter in <br /> sediment. Sulfide levels in sediment are lower in winter and early spring and <br /> increase with depth in the sediment. Sampling of the top 2.0 cm is recommended <br /> for"in-place" sediments. <br /> 9. Dissociable sulfides in sediment may be measured as acid volatile sulfide (AVS). <br /> Sediments are extracted with cold 1N HCl, producing H,S. <br /> 10. Metals extracted during the AVS procedure include Cadmium, Copper, Lead, <br /> Nickel, and Zinc, collectively called simultaneously extracted metal(SEM). <br /> Silver may also be included in SEM. <br />
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