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ARCHIVED REPORTS XR0011668
EnvironmentalHealth
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EHD Program Facility Records by Street Name
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EL DORADO
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2900 - Site Mitigation Program
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PR0009146
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ARCHIVED REPORTS XR0011668
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Entry Properties
Last modified
7/11/2019 1:16:59 PM
Creation date
7/11/2019 11:26:37 AM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2900 - Site Mitigation Program
File Section
ARCHIVED REPORTS
FileName_PostFix
XR0011668
RECORD_ID
PR0009146
PE
2960
FACILITY_ID
FA0004093
FACILITY_NAME
LIGHTHOUSE SCHOOL
STREET_NUMBER
222
Direction
N
STREET_NAME
EL DORADO
STREET_TYPE
ST
City
STOCKTON
Zip
95202
APN
13910022
CURRENT_STATUS
02
SITE_LOCATION
222 N EL DORADO ST
P_LOCATION
01
QC Status
Approved
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EHD - Public
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I <br /> LEEDSNILL-NERREkNo". INC_ <br /> Reference point (RP) elevations were established by licensed surveyors to within <br /> 0.01 foot at each of the monitoringwells. All <br /> and subsequent calculations are baed on these RPrsundwater level measurements <br /> 4. 2 GROUNOWATER SAMPLING <br /> As mentioned in Section 3 .1 Soil Sampling, grab water samples were collected on <br /> September 5 and 6, 1990 from soil borings SBI , SB4, and SB6 using either a bailer <br /> or a "hydropunch" . <br /> On October 1 , 1990, representative groundwater samples were collected from each <br /> of the monitoring wells using established protocol as specified in the USGS <br /> "National Handbook of Recommended Methods for Water Data Acquisition, " which <br /> provides guidelines for the collection of representative groundwater samples. <br /> The monitoring wells were sampled with a 3-inch diameter acrylic bailer. Several <br /> well volumes of water were removed prior to sampling, while field measurements <br /> of conductivity, pH, temperature, and visual observations were made to ensure the <br /> collection of stable, representative groundwater samples. Quantitative <br /> groundwater sampling field data sheets are included in Appendix E. <br /> All sampling equipment was cleaned with a trisodium phosphate (TSP) and water <br /> solution before sampling each monitoring well to prevent potential cross- <br /> contamination. <br /> Water samples were collected in sterile sampling <br /> labeled and preserved according to standard EPA ethds. All nsamples were rcooled <br /> to 4 degrees Celsius at the site and maintained at that temperature until <br /> received at the laboratory within 24 hours of collection under appropriate chain- <br /> of-custody procedures, and extracted prior to expiration of approved holding <br /> times. Chain-of-custody forms are presented in Appendix E. <br /> 4.3 SAMPLE ANALYSIS <br /> Groundwater samples were collected on September 5 and 6, 1990, from soil borings <br /> SBI using a hydropunch and SB4 and SB6 using a bailer. These samples were <br /> analyzed for benzene, toluene, ethyibenzene, and xylene (BTX&E) , total petroleum <br /> hydrocarbons (TPH) as gasoline and diesel , and total dissolved solids (TOS) . <br /> On October 1 , 1990, one week after well development, groundwater samples were <br /> collected from the monitoring wells and analyzed for BTX&E, TPH as gasoline, TDS, <br /> and total coliform. <br /> The analytical methods referred to above conform to EPA Test Methods for <br /> Evaluating Solid Waste: Physical Chemical Method (SW-846, 2nd Edition) , Methods <br /> for Organic Chemical Analysis of Municipal and Industrial Wastewater, USEPA 600- <br /> 14-057, applicable methodologies from Standard Methods for the Examination of <br /> Water and Wastewater, 16th Edition, and/or as specified in the Leaking <br /> Underground Fuel Tank Manual (LOFT) , modified EPA SW-845 Method 8015. <br /> i <br /> 18 <br />
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