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SITE INFORMATION AND CORRESPONDENCE
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Last modified
2/6/2019 2:18:16 PM
Creation date
2/6/2019 2:06:35 PM
Metadata
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Template:
EHD - Public
ProgramCode
2900 - Site Mitigation Program
File Section
SITE INFORMATION AND CORRESPONDENCE
RECORD_ID
PR0518187
PE
2960
FACILITY_ID
FA0013750
FACILITY_NAME
CPL/RENOWN/TAOC
STREET_NUMBER
800
Direction
W
STREET_NAME
BEECHNUT
City
TRACY
Zip
95376
APN
23407004
CURRENT_STATUS
01
SITE_LOCATION
800 W BEECHNUT
P_LOCATION
03
QC Status
Approved
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EHD - Public
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C. Dean Hubbard <br /> October 13, 2006 <br /> Page 6 <br /> phenanthrene were considered volatiles (based on Henry's Law Constant greater than 10-5 atm- <br /> m3/mole and molecular weight less of 200 g/mole), while the rest were considered non-volatiles. <br /> Based on the above cited criteria three more PAHs should be considered volatiles, namely <br /> benzo(b)fluoranthene, chrysene, and pyrene. I have modified the list of PAHs accordingly and <br /> followed it in the exposure and risk calculations. <br /> Indoor Air Modeling <br /> 7. Geomatrix used the Johnson @ Ettinger model-based spreadsheet to calculate the indoor air <br /> concentrations resulting from migration of vapors from soil only. The rationale for many of the <br /> modeling assumptions is not provided in the report. The main deficiencies are discussed below: <br /> a) Geomatrix did not provide the rationale for selecting representative soil concentration <br /> (two sets—surface and surface plus subsurface) as input to the model (e.g., please refer to <br /> pyrene,Tables 2 and 3 and spreadsheet Iof 3 in Appendix B). As already stated, I used <br /> the concentrations from the surface plus subsurface set. <br /> b) As you are probably aware, using soil bulk concentrations will add additional uncertainty <br /> and is not recommended by CalEPA. Collection of soil-gas samples would result in <br /> much more realistic indoor air concentration modeling. In addition, soil contamination <br /> exists below 10 feet bgs at this site (higher soil concentrations might result in higher <br /> indoor air concentrations), but is not considered in this risk assessment. <br /> c) Geomatrix used unknown depth below grade to bottom of contamination. However, the <br /> groundwater(which is probably another source of vapors) is determined to be between 7 <br /> and 15 feet bgs. <br /> d) According to Geomatrix, VOCs were identified in previous site groundwater <br /> investigations and free product is currently being removed from ground water(see Site <br /> Conceptual Model section above). Despite these ongoing product removal activities, it <br /> remains unclear why the Johnson &Ettinger-based NAPL spreadsheet was not used to <br /> model the vapor migration indoors. <br /> e) Geomatrix used the default soil properties for loamy soil claiming it to be site-specific. <br /> However, my review of the boring logs provided as Appendix C of the "Soil <br /> Investigation and Groundwater Monitoring Report"shows a mix of sandy silt, silty sand <br /> to clayey sand. I am not in a position to determine whether this mix of different soil types <br /> may be conservatively(with respect to the soil vapor permeability) represented by a <br /> loamy soil. I have assumed that the above assumption is correct and used loamy soil type <br /> input parameters in my modeling. However, if you think that this assumption is incorrect, <br /> recalculation may be necessary. <br />
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