My WebLink
|
Help
|
About
|
Sign Out
Home
Browse
Search
WORK PLANS
EnvironmentalHealth
>
EHD Program Facility Records by Street Name
>
T
>
TENTH
>
65
>
2900 - Site Mitigation Program
>
PR0544562
>
WORK PLANS
Metadata
Thumbnails
Annotations
Entry Properties
Last modified
2/27/2026 10:21:34 AM
Creation date
2/27/2026 10:20:32 AM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2900 - Site Mitigation Program
File Section
WORK PLANS
RECORD_ID
PR0544562
PE
2950 - ENVIRON ASSESS
FACILITY_ID
FA0025330
FACILITY_NAME
BORDEN TRUST PROPERTY
STREET_NUMBER
65
Direction
E
STREET_NAME
TENTH
STREET_TYPE
ST
City
TRACY
Zip
95376
CURRENT_STATUS
Active, billable
QC Status
Approved
Scanner
SJGOV\gmartinez
Supplemental fields
Site Address
65 E TENTH ST TRACY 95376
Tags
EHD - Public
There are no annotations on this page.
Document management portal powered by Laserfiche WebLink 9 © 1998-2015
Laserfiche.
All rights reserved.
/
19
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
i <br /> 10 June 2019 AdvancedGeo <br /> AGE Project No. 19-4705 Environmental <br /> Page 4 of 6 M..aIV. <br /> For sample collection, a selected portion of the liner will be cut and covered with Teflon <br /> sheets, capped and sealed with tape. Appropriately sealed and labeled samples will be <br /> placed in a chilled container under ice and transported under chain-of-custody <br /> procedure to a CELAP-certified laboratory. Samples will be analyzed for the <br /> constituents listed in Section 2.2. Each sample will be labeled with boring designation, <br /> depth, time, date and sampler's initials. Soils encountered in the boring will be visually <br /> classified by AGE personnel in accordance with the Unified Soil Classification System <br /> (USCS). Additionally, soil samples will be field-screened for presence of volatile organic <br /> compounds using an organic vapor meter (OVM), equipped with a photo-ionization <br /> detector (PID) pre-calibrated to isobutylene. <br /> 3.2. GRAB GROUNDWATER SAMPLING <br /> For collection of grab groundwater samples, soil borings will be,advanced to the top of <br /> the groundwater table as identified by collection of a saturated soil sample. Once <br /> groundwater has been encountered, a Geoprobe (or similar) push-driven water <br /> sampling device will be advanced four feet into the water-bearing zone. Grab <br /> groundwater samples will be collected using a Geoprobe water sampling assembly <br /> fitted with a pre-cleaned, one-inch diameter 0.01-slotted temporary well screen. Each <br /> groundwater sample will be extracted by dedicated disposable polyethylene tubing <br /> through the hollow center of the push rods into the screen section. Samples will be <br /> analyzed for the constituents listed in Section 2.2. and will be collected into laboratory- <br /> supplied, non-preserved amber liters and preserved 40-ml Volatile Organic Analysis <br /> (VOA) vials. <br /> Appropriately sealed and labeled samples will be placed in a chilled container under ice <br /> and transported under chain-of-custody procedure to a CELAP-certified laboratory. <br /> Each sample container will be labeled with sample designation, time, date and <br /> sampler's initials. <br /> 3.3. SOIL-VAPOR SAMPLING & ANALYSIS <br /> At each of the two (2) proposed soil-vapor sampling locations, borings will be advanced <br /> to 6.5 feet bsg using 1.25" probing rods. Once the total depth is reached a semi- <br /> permanent soil-vapor sampling well will be installed within the boring. The temporary <br /> sampling point will consist of 8.5 feet of %-inch Teflon tubing and a sampling tip <br /> (generally inert ceramic stone). Prior to installing the tubing and sampling stone, 0.5 <br /> feet of #2/12 sand will be poured in the annuals of the boring for the sample tip to rest <br /> on. The tubing and sampling tip will then be lowered to a depth of six feet bsg and one- <br /> foot of #2/12 sand will be poured around the tip to create a filter pack. Above the sand, <br /> 0.75 feet of dry granular bentonite will be placed to a depth of 4.5 feet bsg.Thefeafter,, <br /> o se ent aiF intrusiousludng_ <br /> —saw#Rng <br />
The URL can be used to link to this page
Your browser does not support the video tag.