My WebLink
|
Help
|
About
|
Sign Out
Home
Browse
Search
SITE INFORMATION AND CORRESPONDENCE
Environmental Health - Public
>
EHD Program Facility Records by Street Name
>
N
>
NAVY
>
0
>
2900 - Site Mitigation Program
>
PR0009171
>
SITE INFORMATION AND CORRESPONDENCE
Metadata
Thumbnails
Annotations
Entry Properties
Last modified
3/30/2020 11:50:21 AM
Creation date
3/30/2020 11:19:42 AM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2900 - Site Mitigation Program
File Section
SITE INFORMATION AND CORRESPONDENCE
RECORD_ID
PR0009171
PE
2960
FACILITY_ID
FA0004011
FACILITY_NAME
PORT OF STOCKTON-FUEL TERMINAL
STREET_NUMBER
0
STREET_NAME
NAVY
STREET_TYPE
DR
City
STOCKTON
Zip
95203
CURRENT_STATUS
01
SITE_LOCATION
NAVY DR
P_LOCATION
01
P_DISTRICT
001
QC Status
Approved
Scanner
SJGOV\sballwahn
Tags
EHD - Public
Jump to thumbnail
< previous set
next set >
There are no annotations on this page.
Document management portal powered by Laserfiche WebLink 9 © 1998-2015
Laserfiche.
All rights reserved.
/
577
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
Mr.Jeffrey D. Wingfield . -2- 29 July 201111 <br /> Port of Stockton California <br /> calculated arsenic concentration statistics using data from 93 wells across Rough & Ready <br /> Island, including all five Site 47 monitoring wells. Therefore, the Port cannot use the Navy <br /> background statistics to determine'whether or not Site 47 groundwater has been impacted by <br /> arsenic. <br /> Response #1: The Port must calculate background statistics for arsenic using a data set that <br /> does no include the Site 47 monitoring well concentration data. The Port must then compare <br /> the alternate arsenic background data to the arsenic data collected from the five Site 47 <br /> monitoring wells to determine if arsenic in soil has impacted groundwater. <br /> Comment #2: The Port has designated the uppermost fine-grained water-bearing zone <br /> beneath Rough & Ready Jsland as the CA Zone. The CA Zone varies in depth from <br /> 0 to 25 feet and is composed of organic matter, clay, and silt. CA Zone water surface contour <br /> maps are shown on Figures 10 through 12, and are based on triangulation of the water surface <br /> elevations measured in three shallow Monitoring Wells: W282, W284, and W285. However, <br /> one of the three (W285) is screened 15 feet deeper than the other two and may not be valid for <br /> contouring near-surface groundwater elevations. Furthermore, W284 and W285 are adjacent <br /> to each other, further reducing the validity of triangulating the water table. If one excludes the <br /> water surface elevation in W285, the actual flow direction during any give event could be <br /> interpreted to be any direction from northwest to southwest to southeast. <br /> Response #2: The Port must contour the CA Zone water surface elevation using at least <br /> three monitoring wells that have been screened between approximately 10 to 15 feet below the <br /> ground surface (bgs). Central Valley Water Board staff note that Monitoring Well W312, <br /> located north of Site 47, is screened between 10 and 15 feet bgs and could be utilized for this <br /> purpose. Based on inferred groundwater flow direction obtained from the CA Zone contours, <br /> the Port must install groundwater monitoring wells down-gradient of the three arsenic <br /> "hotspots" shown on Draft RI figures and first identified by the Navy in the 1990s. <br /> Comment #3: The Port has designated the uppermost coarse-grained water-bearing zone <br /> beneath Rough & Ready Island as the WA Zone. The WA Zone varies in depth from <br /> 15 to 30 feet and is composed of sand or silty sand. The Draft RI does not provide <br /> groundwater flow contour maps for the WA Zone beneath Site 47. Furthermore, the Draft RI <br /> does not provide adequate arsenic concentration data from groundwater in the WA Zone. The <br /> only monitoring well at Site 47 that is screened in the WA Zone is W280. <br /> Response #3: The Port must contour the WA Zone water surface elevation using at least <br /> three monitoring wells that have been screened within the coarse-grained material of this zone. <br /> Based on inferred groundwater flow direction obtained from the WA Zone contours, the Port <br /> must install groundwater monitoring wells down-gradient of the three arsenic "hotspots" shown <br /> on Draft RI figures. The Port should place Monitoring Well W280 on cross section <br /> D — D' in the Draft RI. Also, the Port should place groundwater arsenic concentration data on <br /> all of the cross sections provided in the Draft RI. <br /> Comment#4: The concentration of arsenic in WA Zone Monitoring Well W280 has increased <br /> between October 1999 and August 2008. The arsenic concentration during the first sampling <br /> event, conducted on 21 January 2000, was 228 micrograms per liter (Ng/L); the concentration <br /> during the last event, conducted on 13 August 2008, was 400 pg/L. This well is on the western <br /> edge of one of the arsenic "hot spots" shown on Draft RI figures. The well is also <br /> approximately 200 feet northwest of the Site 47 roadway relocation project constructed by the <br />
The URL can be used to link to this page
Your browser does not support the video tag.