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2900 - Site Mitigation Program
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PR0009004
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Last modified
9/17/2020 5:34:49 PM
Creation date
9/17/2020 4:58:08 PM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2900 - Site Mitigation Program
File Section
WORK PLANS
RECORD_ID
PR0009004
PE
2954
FACILITY_ID
FA0004061
FACILITY_NAME
MCCORMICK & BAXTER CREOSOTING
STREET_NUMBER
1214
Direction
W
STREET_NAME
WASHINGTON
STREET_TYPE
ST
City
STOCKTON
Zip
95201
APN
14520001
CURRENT_STATUS
01
SITE_LOCATION
1214 W WASHINGTON ST
P_LOCATION
01
P_DISTRICT
001
QC Status
Approved
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EHD - Public
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Jeff Van Slooten <br /> Page 4 <br /> November 29 , 1989 <br /> level of 7 . 9 mg/ml. Errors of this sort must be <br /> corrected in order to make a correct assessment of <br /> potential health hazards. Since this document will be <br /> a matter of public record, it is very important that <br /> data be presented in a manner that will allow the <br /> public to have confidence in the information. In this <br /> same part of the report, it is stated that PCP levels <br /> in storm water have decreased over time due to changing <br /> procedures. However, the values on Table 3-8 still <br /> show a great deal of variability. Are there data for <br /> 1988 and 1989? The text (RAP 4-8) discusses further <br /> reductions in PCP discharges in 1989 but the data do <br /> not appear to be presented in the report. This <br /> document should "stand alone" and include, or <br /> reference, all data needed to characterize the site and <br /> its potential hazards. <br /> 6 . PCP is considered by the DHS to be a carcinogen (see <br /> Toxic Substances Control Program Scientific Guidance <br /> Memo 89-3) and must be addressed as such in the <br /> assessment of risk. Chromium VI (PHA 5-7) is <br /> considered by EPA to be a carcinogen by the inhalation <br /> route. This will require that all estimates of excess <br /> cancer risk be recalculated. The text PHA, page 3-5 , <br /> states that pentachlorophenol (PCP) was detected at <br /> 0. 010 mg/1 in OSSB near Gold Bond. Data to support <br /> this could not be located in the current PHA. <br /> 7 . All routes and all chemicals must be sunned (for the <br /> same toxic endpoint) in order to determine total risk <br /> to the biological receptor. <br /> 8 . It is very difficult to follow the rationale used in <br /> calculating the excess cancer risk and the comparison <br /> of the estimated daily intake to the reference dose <br /> (Tables in Appendix C of the PHA) . Text Tables 3-1 <br /> through 3-7 present the arithmetic mean concentration <br /> of chemicals in the soil. However, in Appendix C the <br /> geometric mean is used. What is the rationale f---- <br /> this? <br /> orthis? It seems that based on the range of sample <br /> concentrations, either the arithmetic or geometric mean <br /> should be used throughout the document. All chemicals <br /> that are identified in the soils are not found on the <br /> Tables in Appendix C. Specifically, chromium does not <br /> appear on any table in Appendix C, however, it is <br /> present in virtually all soil areas. Tables 6-1 <br /> through 6-4 present the excess cancer risk using the <br /> mean concentrations only. The maximum values should <br /> also be presented. <br />
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