My WebLink
|
Help
|
About
|
Sign Out
Home
Browse
Search
ARCHIVED REPORTS_XR0004902
EnvironmentalHealth
>
EHD Program Facility Records by Street Name
>
L
>
LOUISE
>
365
>
3500 - Local Oversight Program
>
PR0545431
>
ARCHIVED REPORTS_XR0004902
Metadata
Thumbnails
Annotations
Entry Properties
Last modified
3/9/2020 3:58:49 PM
Creation date
3/9/2020 11:58:34 AM
Metadata
Fields
Template:
EHD - Public
ProgramCode
3500 - Local Oversight Program
File Section
ARCHIVED REPORTS
FileName_PostFix
XR0004902
RECORD_ID
PR0545431
PE
3528
FACILITY_ID
FA0005191
FACILITY_NAME
FULLER MOBILE HOME PARK
STREET_NUMBER
365
Direction
E
STREET_NAME
LOUISE
STREET_TYPE
AVE
City
LATHROP
Zip
95330
APN
19627022
CURRENT_STATUS
02
SITE_LOCATION
365 E LOUISE AVE
P_LOCATION
07
P_DISTRICT
003
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.
/
53
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
Fuller Mobile Home Park <br /> 365 F- Louise Ave-, Lathrop, California December 20, 1993 <br /> Phase H Site Characterization Page. 4 <br /> 2 5 mg/Kg for gasoline and 10 mg/kg for diesel Analyses were conducted by Geo- <br /> Monitor, Inc, of Hesperia, California, a State certified laboratory <br /> 3.5 Groundwater Sampling <br /> A travel blank provided by the laboratory accompanied the sample vials from the time <br /> they were picked up from the lab to the tune they were delivered to the lab This travel <br /> blank was listed on the Chani of Custody but was analyzed only if all samples contained <br /> the same contaminants <br /> All sampling equipment, including the pump, bailer and cables used by sampling <br /> personnel was disassembled, if appropriate, and steam-cleaned prior to commencement <br /> of sampling These procedures were also followed between each well and sampling <br /> point, and at the end of the sampling day De-ionized or organic-free water (also <br />' provided by the laboratory)was then introduced into the pump or bailer as a final stage <br /> of cleaning This water ww,then pumped or gently poured into sample vials to be used <br /> as pump or bailer blanks These blanks were tested only if their corresponding samples <br /> were found to contain contanunants <br /> Immediately prior to sampling, water levels and well depth measurements were taken <br />' in all wells at the site Each well was evacuated using a stainless steel bladder pump <br /> (which does not introduce air into the water column) or a Teflon bailer The pH, <br /> temperature, acid electrical conduct-natty of the water was monitored as the well was <br />' evacuated, and were noted on the field logs (Table 3 & Appendix D) Instruments <br /> calibrated to known standards were used to monitor these parameters <br />' At least five well volumes (or more, if necessary) were evacuated from each well until <br /> the above parameters became stable Wells that are de-watered before the evacuation <br /> of five well volumes had been accomplished were sampled upon eighty percent <br />' recovery of the initial water level The wells or other sampling points were sampled in <br /> the order of least contaminated to most contaminated, as best known or estimated <br /> The samples were pumped from a stainless steel bladder pump or carefully poured <br />' from a Teflon bailer into clean glass vials with Teflon-lined screw caps and half gallon <br /> plastic containers provided by the laboratory Care was taken to ensure that no air <br />' space existed in the vials by inverting to check for bubbles and re-sampling if necessary <br /> The samples were analyzed or extracted within 14 days according to their EPA <br />' methods Water samples collected for analysis were analyzed by EPA method 602 for <br /> BTX&E compounds, method 5030/modified 8015 for gasoline range hydrocarbons <br /> and method 3510 for diesel range hydrocarbons The minimum detection limits used <br /> for each analyte were 0 5 ,ug/kg for BTX&E, 0 5 mg/l for gasoline and 0 05 mgfkg for <br /> diesel Analyses were conducted by Geo-Morutor of Hesperia, California, a State <br /> certified laboratory <br />
The URL can be used to link to this page
Your browser does not support the video tag.