My WebLink
|
Help
|
About
|
Sign Out
Home
Browse
Search
SITE INFORMATION AND CORRESPONDENCE_1993-2003
Environmental Health - Public
>
EHD Program Facility Records by Street Name
>
R
>
ROTH
>
850
>
2900 - Site Mitigation Program
>
PR0506824
>
SITE INFORMATION AND CORRESPONDENCE_1993-2003
Metadata
Thumbnails
Annotations
Entry Properties
Last modified
4/7/2020 3:15:47 PM
Creation date
4/7/2020 2:41:40 PM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2900 - Site Mitigation Program
File Section
SITE INFORMATION AND CORRESPONDENCE
FileName_PostFix
1993-2003
RECORD_ID
PR0506824
PE
2960
FACILITY_ID
FA0007648
FACILITY_NAME
DDRW - SHARPES
STREET_NUMBER
850
Direction
E
STREET_NAME
ROTH
STREET_TYPE
RD
City
LATHROP
Zip
95330
APN
19802001
CURRENT_STATUS
01
SITE_LOCATION
850 E ROTH RD BLDG S-108
P_LOCATION
07
P_DISTRICT
003
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.
/
491
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
Water QualitySite Assessment• -3- • D tr� 5 November 1992 <br /> Determination of Water Quality Limits <br /> To determine whether past waste management activities have degraded or have the po- <br /> tential to degrade water quality, applicable water quality limits need to be determined for <br /> the contaminants involved. Water quality limits are numerical contaminant concentra- <br /> tions, above which contaminants are considered to have adversely impacted beneficial <br /> uses (to have limited certain uses) of waters of the state. Water quality limits are used to <br /> implement the numerical and narrative water quality objectives contained in the state <br /> and regional Water Quality Control Plans. <br /> To select water quality limits, determine the following: <br /> ❑ beneficial uses of the water body being investigated; <br /> ❑ applicable water quality objectives to protect those beneficial uses; <br /> ❑ numerical water quality limits that will implement all applicable water quality ob- <br /> jectives (i.e. drinking water standards,water quality criteria for agriculture,health <br /> advisories, Proposition 65 No-Significant-Risk Levels,etc.); and finally, <br /> ❑ choose the most limiting value to be the water quality limit for each particular con- <br /> stituent,because it is protective of all beneficial uses. <br /> During the site assessment phase of a site investigation, detected constituent concentra- <br /> tions are compared to numerical water quality limits to determine if beneficial uses have <br /> been impacted. During the cleanup level determination phase,the background concen- <br /> tration is selected as the initial cleanup level,based on State Board Resolution Nos. 92-49 <br /> (Policies and Procedures for Investigation and Cleanup and Abatement of Discharges under <br /> Water Code Section 13304) and 68-16 (Antidegradation Policy). If the discharger demon- <br /> strates that it is technologically and/or economically infeasible to achieve background <br /> concentrations, then some achievable cleanup level between background and the water <br /> quality limit can be negotiated. However, any cleanup level greater background based on <br /> feasibility must still comply with all applicable statutes and regulations,and must not <br /> cause risk to human health and the environment, including beneficial uses of water. <br /> Site-wide Background Assessment of Soils <br /> 1. Select a minimum of four soil sampling sites that,based on available information, <br /> appear to be out of the influence of past waste management activities. Off-site sam- <br /> pling may be necessary if unimpacted areas cannot be found on-site. <br /> 2. Collect a soil sample at each location from each lithology type present above the <br /> water table. Each soil sample must be large enough to perform the Waste Extraction <br /> Test (WET) procedure with deionized water,' and to analyze the extract for all of the <br /> following: <br /> The standard citrate buffer should be used if the soils are significantly acidic our could become acidic. <br />
The URL can be used to link to this page
Your browser does not support the video tag.