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ARCHIVED REPORTS XR0000940
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PR0544127
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ARCHIVED REPORTS XR0000940
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Last modified
2/8/2019 4:52:01 PM
Creation date
2/8/2019 4:35:27 PM
Metadata
Fields
Template:
EHD - Public
ProgramCode
3500 - Local Oversight Program
File Section
ARCHIVED REPORTS
FileName_PostFix
XR0000940
RECORD_ID
PR0544127
PE
3528
FACILITY_ID
FA0009518
FACILITY_NAME
GEORGE F SCHULER INC
STREET_NUMBER
1705
Direction
N
STREET_NAME
BROADWAY
STREET_TYPE
AVE
City
STOCKTON
Zip
95205
APN
14315007
CURRENT_STATUS
02
SITE_LOCATION
1705 N BROADWAY AVE
P_LOCATION
99
P_DISTRICT
001
QC Status
Approved
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WNg
Tags
EHD - Public
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George F. Schuler, Inc <br /> 1705 N. Broadivay, Stockton, California August l7, 1993 <br /> Phase I Remedial Report Page: 3 <br /> The borings were logged under the direct supervision of a registered professional <br /> using the Unified Soil Classification System (Appendix D). The color, texture, <br /> moisture, plasticity, consistency of the earth materials, pertinent soil or bedrock <br /> characteristics, and any evidence of contamination were noted. All water-bearing <br /> zones and the depths at which they were encountered were noted on these logs. <br /> i <br /> All borings were drilled in such a manner as to prevent cross contamination <br /> i between strata. Exploratory soil borings within the unsaturated zone were <br /> backfilled with a cement and three percent (3%) Bentonite mixture. Borings into <br /> the saturated zone were terminated approximately 8 feet beneath the top of the <br /> aquifer in a clay to prevent penetration into a deeper aquifer. Upon termination., <br /> the boring into the saturated zone was completed as a monitoring well and <br /> backfilled with concrete grout, after a Bentonite seal had been placed. The boring <br /> for the monitoring well was of a diameter at least 4 inches greater than the 2 inch <br /> diameter of the well casing to be used. <br /> The cuttings from the drilling operation were containerized on-site during drilling <br /> for proper disposition. The proper method of disposal will be dependent upon <br /> results of laboratory analysis. This disposal will be the responsibility of the client <br /> unless other arrangements have been made. <br /> 3.2 Well Construction <br /> All materials used in well construction were thoroughly cleaned prior to <br /> introduction into the boring. A 2- inch diameter well casing (PVC) with end cap <br /> and factory perforations for placement in the saturated zone was placed in the <br /> boring. The screen and filter pack sizes are as noted in the well construction <br /> drawing. The casing and end caps were threaded; no PVC cement was used. The <br /> filter pack extends two feet above the perforated zone. A Bentonite seal 2- to 3- <br /> feet thick was placed in the annular space above the filter pack followed by a <br />' cement grout to the surface. Seal and filter pack elevations may vary based on the <br /> underlying geology (Appendix D). <br /> 3.3 Well Development and Sampling <br /> The wells were developed until the well water appeared clear of sediment, or until <br /> an appropriate number of well volumes (based upon the judgment of the <br /> responsible professional) had been evacuated. The water produced during well <br /> development was containerized and left on-site in 55-gallon drums for disposal as <br /> hazardous waste if deemed necessary upon receipt of laboratory results. Disposal <br /> will be the responsibility of the client unless other arrangements have been made. <br /> The wells were allowed to stabilize for twenty-four (24) hours prior to sampling. <br />
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