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2900 - Site Mitigation Program
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PR0522097
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Last modified
5/27/2021 1:37:56 AM
Creation date
5/26/2021 4:05:44 PM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2900 - Site Mitigation Program
File Section
WORK PLANS
RECORD_ID
PR0522097
PE
2960
FACILITY_ID
FA0015058
FACILITY_NAME
SCHMIEDT SOIL SERVICE
STREET_NUMBER
2096
Direction
S
STREET_NAME
MAIN
STREET_TYPE
ST
City
MANTECA
Zip
95337
APN
22404021
CURRENT_STATUS
01
SITE_LOCATION
2096 S MAIN ST
QC Status
Approved
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SJGOV\dsedra
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EHD - Public
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NICKLEINFELDER <br /> Following completion of the drilling, a 2-inch diameter PVC well will be installed in each of the <br /> borings. The soil borings will be advanced approximately 10 feet into groundwater. The wells will <br /> be constructed with Schedule 40 PVC, a 15 foot long 0.010 inch screened section surrounded by <br /> and covered by clean sand filter pack (#2/16), 3 foot thick bentonite transition seal above the filter <br /> pack, and grouted to the surface. The wells will be finished with a locking pressure cap situated <br /> within a monument or flush style well box (depending on surface conditions). See the proposed <br /> Diagram of Well Construction(Plate 3). <br /> Once the monitoring wells have been installed, the top of each well will be surveyed so that depth <br /> to groundwater measurements in the wells can be converted to groundwater elevations used to <br /> assess groundwater gradients. The wells will be surveyed relative to a local benchmark. If a local <br /> benchmark is not available near the site, the wells will be surveyed relative to an onsite, assumed <br /> benchmark with an assigned elevation. The wells will be surveyed as described in Appendix A-3.4. <br /> 3.1.3 Monitoring Well Development <br /> A minimum of 48 hours after installation, the monitoring wells will be developed to remove fine <br /> silt from the well bore and to effectively increase the hydraulic radius of each monitoring well. <br /> Surging along the screened interval of the well will be performed to draw the sediment from the <br /> formation into the filter pack and the well and to set the sand filter pack. The monitoring wells <br /> will be developed as described in Appendix A.3.2. In addition to developing the monitoring <br /> wells until the discharge runs relatively clear of fines, the discharge will be periodically <br /> monitored for turbidity, pH, temperature, and specific conductance to record stable groundwater <br /> parameters during the development task. <br /> The well development purge water will be contained in 55-gallon drums pending analytical <br /> results. <br /> 3.1.4 Initial Groundwater Sampling <br /> Water level measurements will be made in the monitoring wells prior to purging and sampling the <br /> wells. The depth to groundwater will then be measured in each well according to the protocol <br /> described in Appendix A-4.1. <br /> Approximately three to five well volumes will be purged and samples will be collected as described <br /> in Appendix A-4.2. Each of the water samples collected for quantitative analyses will be <br /> submitted under chain-of-custody control to a laboratory certified by the State of California <br /> Department of Health Services (DHS) for the requested analyses. <br /> 3.2 SHALLOW SOIL SAMPLING <br /> There were numerous areas of concern identified in the ESA that required shallow soil sampling. <br /> Kleinfelder proposes to collect shallow soil samples from the orchard area and vehicle parking <br /> areas, ground surface depression near the eastern edge of the site where stormwater runoff <br /> 27125.E01/ST03R657 Page 6 of 15 <br /> Copyright 2003,Kleinfelder,Inc. May 23,2003 <br />
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