My WebLink
|
Help
|
About
|
Sign Out
Home
Browse
Search
COMPLIANCE INFO
EnvironmentalHealth
>
EHD Program Facility Records by Street Name
>
A
>
AMERICAN
>
820
>
4800 – General/Other Program
>
PR0543500
>
COMPLIANCE INFO
Metadata
Thumbnails
Annotations
Entry Properties
Last modified
6/11/2021 2:32:03 PM
Creation date
6/11/2021 2:00:43 PM
Metadata
Fields
Template:
EHD - Public
ProgramCode
4800 – General/Other Program
File Section
COMPLIANCE INFO
RECORD_ID
PR0543500
PE
2960
FACILITY_ID
FA0024694
FACILITY_NAME
SIEBOLD CONSTRUCTION
STREET_NUMBER
820
Direction
S
STREET_NAME
AMERICAN
STREET_TYPE
ST
City
STOCKTON
Zip
95206
APN
147292090, 110
CURRENT_STATUS
01
SITE_LOCATION
820 S AMERICAN ST
P_LOCATION
01
QC Status
Approved
Scanner
SJGOV\dsedra
Tags
EHD - Public
There are no annotations on this page.
Document management portal powered by Laserfiche WebLink 9 © 1998-2015
Laserfiche.
All rights reserved.
/
62
PDF
Print
Pages to print
Enter page numbers and/or page ranges separated by commas. For example, 1,3,5-12.
After downloading, print the document using a PDF reader (e.g. Adobe Reader).
View images
View plain text
4.2.2 Dermal Contact with Soil <br />Some soil contaminants may be absorbed across the skin into the bloodstream. Absorption will depend <br />upon the amount of soil in contact with the skin, the concentration of chemicals in soil, the skin surface <br />area exposed, and the potential for the chemical to be absorbed across the skin. Note, USEPA assumes <br />that benzene and ethylbenzene will not be on the skin long enough (due to volatilization) to absorb <br />through the skin. <br />4.2.3 Inhalation of Volatile and Particulate Emissions in Outdoor Air <br />The inhalation exposure route includes the inhalation of both volatile and particulate emissions. The <br />inhalation slope factors and noncarcinogenic inhalation reference doses are presented in Table 7. <br />4.3 Chemical Parameter and Toxicity Values Used <br />The default chemical parameter values came from the RWQCB 2 Environmental Screening Levels (2007). <br />The toxicity values for noncarcinogenic toxicity came from USEPA's On-line Risk Information System <br />(IRIS, 2011). The carcinogenic toxicity values for benzene, ethylbenzene, and naphthalene came from <br />OEHHA's list of cancer potency factors (OEHHA 2009). The carcinogenic oral slope factor for <br />benzo(a)pyrene came from OEHHA's Public Health Goals for Chemicals in Drinking Water for <br />Benzo(a)pyrene (OEHHA 2010). <br />5 SOIL SCREENING LEVELS <br />Table 8 shows the soil screening levels calculated for each exposure scenario. <br />Table 8: Summary of Soil Screening Levels for different Exposure Scenarios and Receptors <br />Chemical Residential Commercial/ Industrial Utility Worker <br />0 to 5 feet bgs <br />mg/kg <br />Volatilization to <br />outdoor air <br />(5 to 10 feet bgs) <br />mg/kg <br />0 to 5 feet bgs <br />mg/kg <br />Volatilization to <br />outdoor air <br />(5 to 10 feet bgs) <br />mg/kg <br />0 to 10 feet bgs <br />mg/kg <br />Benzene 1.9 2.8 8.2 12 14 <br />Ethylbenzene 21 32 89 134 314 <br />Naphthalene 9.7 9.7 45 45 219 <br />PAH* 0.063** NA 0.68 NA 4.5 <br />Notes; <br />* Based on the seven carcinogenic PAHs as benzo(a)pyrene toxicity equivalent [BaPe]. The PAH screening level <br />(applicable to total BaPe) is only applicable where soil was affected by either waste oil and/or Bunker C fuel. <br />** DTSC (2009) reports average ambient PAH concentrations (as BaPe) in California ranging from 0.16 to 0.21 <br />mg/kg, and upper tolerance limits (UTLs) ranging from 0.9 to 1.5 mg/kg. The screening level shown in this table is <br />"risk-based" and is far below the average ambient concentrations for PAHs in California. It is suggested that DTSC <br />citation (2009) be consulted for sites with PAH contamination. <br />8
The URL can be used to link to this page
Your browser does not support the video tag.