My WebLink
|
Help
|
About
|
Sign Out
Home
Browse
Search
SITE INFORMATION AND CORRESPONDENCE
Environmental Health - Public
>
EHD Program Facility Records by Street Name
>
G
>
GRANT LINE
>
575
>
2900 - Site Mitigation Program
>
PR0542420
>
SITE INFORMATION AND CORRESPONDENCE
Metadata
Thumbnails
Annotations
Entry Properties
Last modified
1/23/2020 9:31:51 AM
Creation date
1/23/2020 9:24:33 AM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2900 - Site Mitigation Program
File Section
SITE INFORMATION AND CORRESPONDENCE
RECORD_ID
PR0542420
PE
2960
FACILITY_ID
FA0024376
FACILITY_NAME
FORMER CHEVRON 98632
STREET_NUMBER
575
Direction
W
STREET_NAME
GRANT LINE
STREET_TYPE
RD
City
TRACY
Zip
95376
CURRENT_STATUS
01
SITE_LOCATION
575 W GRANT LINE RD
P_LOCATION
03
QC Status
Approved
Scanner
SJGOV\sballwahn
Tags
EHD - Public
There are no annotations on this page.
Document management portal powered by Laserfiche WebLink 9 © 1998-2015
Laserfiche.
All rights reserved.
/
106
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
Former Chevron Service Station No. 98632 September 5, 2014 <br /> 575 West Grant Line Road Page 2 of 4 <br /> Tracy, California 95376 <br /> human health (criteria [b] or [c] above). The site has been occupied by a used car lot <br /> since the 1990s with no permanent structures . The only structure onsite is a portable <br /> office trailerwith crawl space beneath that would likely allow any upward migrating vapor <br /> to dissipate. Therefore, there do not appear to be any current receptors at the site at <br /> risk of potential vapor intrusion to indoor air. If the site is redeveloped , potential vapor <br /> intrusion concerns can be addressed or mitigated by the Responsible Parties (RPs) at <br /> that time, through measures such as additional excavation or installation of active or <br /> passive ventilation equipment as warranted . Additional evaluation would be needed to <br /> determine what would be necessary. Such a condition could be included in the case <br /> closure documentation ." <br /> In response to the third bulleted LTCP criterion above , CRA stated in LTC Evaluation: <br /> "The maximum detected concentrations of benzene and ethylbenzene in soil samples <br /> collected in the 0 to 5 fbg interval do not exceed the commercial limits shown above. No <br /> soil samples collected in the 0 to 5 fbg interval were analyzed for naphthalene or PAHs; <br /> however, extensive excavation was performed to 10 to 10. 5 fbg in the former used-oil <br /> UST/sump/hoist area (Figure 2) and the soil disposed offsite. Therefore , these <br /> constituents are not expected to be present in soil from 0 to 5 fbg ." <br /> "With regard to the 5 to 10 fbg interval , for which the only potential exposure pathway of <br /> concern for commercial receptors is inhalation of volatile emissions from soil to outdoor <br /> air, the detected benzene and ethylbenzene concentrations generally do not exceed the <br /> limits above with the exception of two or three samples collected in 1995 (Table 2) . The <br /> concentrations do not significantly exceed the limits, and are expected to have <br /> decreased in the almost 20 years since the samples were collected due to natural <br /> attenuation processes. Although naphthalene was detected in a sample collected at 7.5 <br /> fbg beneath the former used-oil UST, as mentioned above this area was excavated to at <br /> least 10 fbg. In addition , no naphthalene was detected in a sample collected at 6 fbg <br /> from the boring for nearby well MW-1 . Regarding vo atilizafion of enzene an <br /> ethylbenzene from soil to outdoor air, as stated in the LTCP technical justification for this <br /> pathway, the assumptions under which this exposure pathway would be a concern are <br /> very conservative and the actual exposure assumed in the risk calculations would be <br /> impossible to achieve. For example , it is assumed that the receptor is located onsite, <br /> directly over the impacted soil 24 hour/day for the entire exposure duration (30 years for <br /> a commercial worker) . Also, vertical dispersion (mixing with outdoor air) above the <br /> height of the breathing zone is not considered . Thus, given this information and the site <br /> conditions, this does not appear to be a realistic exposure pathway of concern and it is <br /> unlikely it would pose a significant risk to the health of commercial workers at the site. " <br /> "With regard to utility worker concerns, of the numerous soil samples collected within 0 <br /> to 10 fbg , only the benzene concentrations in three samples (up to 24 mg/kg) collected <br /> at 6 or 6. 5 fbg in 1995 exceeded the limit (14 mg/kg) . Again, the concentrations do not <br /> significantly exceed the limit and likely have decreased since sample collection . Given <br /> the information and the limited extent, the benzene in soil does not appear to be a <br /> significant concern for potential future utility workers. However, to provide further <br /> assurance a soil management plan could be prepared to provide notification and <br /> management procedures for any future subsurface work." <br /> The following are EHD responses to CRA's arguments presented in LTC Evaluation : <br />
The URL can be used to link to this page
Your browser does not support the video tag.