My WebLink
|
Help
|
About
|
Sign Out
Home
Browse
Search
ARCHIVED REPORTS XR0000757
EnvironmentalHealth
>
EHD Program Facility Records by Street Name
>
B
>
BEVERLY
>
104
>
2900 - Site Mitigation Program
>
PR0540667
>
ARCHIVED REPORTS XR0000757
Metadata
Thumbnails
Annotations
Entry Properties
Last modified
2/8/2019 9:49:27 AM
Creation date
2/8/2019 9:25:10 AM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2900 - Site Mitigation Program
File Section
ARCHIVED REPORTS
FileName_PostFix
XR0000757
RECORD_ID
PR0540667
PE
2960
FACILITY_ID
FA0023252
FACILITY_NAME
WELDON CHURCH PROPERTY
STREET_NUMBER
104
Direction
W
STREET_NAME
BEVERLY
STREET_TYPE
PL
City
TRACY
Zip
95376
CURRENT_STATUS
01
SITE_LOCATION
104 W BEVERLY PL
QC Status
Approved
Scanner
WNg
Tags
EHD - Public
There are no annotations on this page.
Document management portal powered by Laserfiche WebLink 9 © 1998-2015
Laserfiche.
All rights reserved.
/
52
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
09 August 2000 . . <br /> AGE-NC Project No.'95-0106 , <br /> Page 4 of 10 <br /> Contaminant Level (MCL)for drinking water. In general, the hydrocarbon concentrations in samples <br />'. collected from monitoring well MW-4 fluctuate somewhat but.appear <br /> to be gradually declining over , <br /> time, Hydrocarbon concentrations in samples.from MW-I also fluctuate, appeared to decline up,to <br /> early 1999; at which time the concentrations rebounded; since that time, concentrations appear to <br /> have stabilized`or-declined slightly. <br /> The occurrence of TPH-g and BTEX in ground water encountered in an off-site; down-gradient well , <br /> (MW4) Indicates that dissolved hydrocarbons had migrated north of the site: The lateral extent of <br /> the impacted ground water around MW4 has not been delineated in all directions. The plume is ' <br /> generally constrained on the West-by monitoring well MW-5, on the northeast and east by MW-6 and. <br /> MW-3, respectively, and on the eastand south by MW-7_and.MW-2, respectively..However,-the <br /> plume is not'coristrained north and westf MW-4., <br /> AGE interprets the-data,to show that plume migration had reached its present extent at the time the <br /> monitoring wells were installed, and additional migration has not been detected since the.monitoring <br /> system was installed. The concentrations in MW-4 are probably declining as a result of natural Y ' <br /> attenuation processes affecting the"stabilized"plume. Hydrocarbon concentrations in samples from <br /> MW-I' may fluctuate more due to the well's close proximity to impacted soil left in place near the,farmer UST site. <br /> 2.5. STRATIGRAPHY <br /> Tan, silty clay soils-'were encountered from the surface to depths of approximately six feet bsg, in,,, <br /> each boring. Gray,'silty clay was encountered between six and"ten feet bsg during the installation of. <br /> the ground water monitoring well's and borings. <br />' Coarse sand.was locallyencountered below .the clay,-between 10-and 23 feet bsg" iri the borings <br /> Y' , <br /> established to that depth. Gravel occurred below the sand,from 23 feet bsg to-25 feet bsg, in boring' <br />' MW-6. <br /> Based"upon soil samples submitted for geotechnical analysis,'the upper clay layer appears to have . <br />' a lower permeability'than the saturated, sand and gravel locally.encountered below approximately . <br /> 10 feet bsg. Ground water is present in the sand, however it,appears that the clay immediately. <br /> overlaying 'the, sand may retard the vertical migration.'of ground water and hydrocarbons. A" <br /> I' stratigraphic cross section of the soils at the site;including the area of unsaturated impacted-soil, is <br /> depicted in Figure 3 - Stratigraphic Cross Section. . <br /> Advanced GeoEnvironmental,Inc. <br />
The URL can be used to link to this page
Your browser does not support the video tag.