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WORK PLANS CASE 2
Environmental Health - Public
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WORK PLANS CASE 2
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Last modified
9/16/2019 3:16:55 PM
Creation date
9/16/2019 3:06:19 PM
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EHD - Public
ProgramCode
2900 - Site Mitigation Program
File Section
WORK PLANS
FileName_PostFix
CASE 2
RECORD_ID
PR0523856
PE
2965
FACILITY_ID
FA0016065
FACILITY_NAME
OAKWOOD SHORES
STREET_NUMBER
1699
STREET_NAME
BELLA LAGO
STREET_TYPE
WAY
City
MANTECA
Zip
95337
APN
24152013
CURRENT_STATUS
01
SITE_LOCATION
1699 BELLA LAGO WAY
P_LOCATION
99
P_DISTRICT
005
QC Status
Approved
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K L E I N FELDER <br /> EXPECT MORE <br /> 3 WELL DEVELOPMENT AND SURVEYING <br /> 3.1 WELL DEVELOPMENT METHODOLOGY <br /> During well installation the well sand pack will be surged for approximately 5 minutes, <br /> using surge block attached to a drill rod. The surging will be performed to prevent <br /> bridging and to settle the sand pack prior to placement of the bentonite seal. <br /> A minimum of 48 hours after installation, the monitoring wells will be developed to <br /> remove fine silt from the well bore and to effectively increase the hydraulic radius of <br /> each monitoring well. Surging along the screened interval of the well will be performed <br /> to draw the sediment from the formation into the filter pack and well and to further set <br /> the sand pack. Surging will be done with a suction pump equipped with new food- <br /> grade, ribbed tubing, surge block and foot valve. The bottom of the tubing will be fitted <br /> with the surge block attached to a ball-valve/foot valve. This valve is designed to allow <br /> water and sediment into the tubing, but prevents outflow from the tubing. The well <br /> screen interval will be surged for approximately 5-minutes followed by purging using a <br /> suction pump. Sediment can also be pumped directly from the bottom of the well using <br /> this method. This process will be repeated until the discharge runs relatively clear of <br /> fines. The discharge will be periodically monitored for pH, temperature, and specific <br /> conductance to evaluate and record groundwater parameters during the development <br /> task. The monitoring wells will otherwise be generally developed as described in <br /> Appendix D-3.2. <br /> 3.2 WELL SURVEY <br /> The locations of new monitoring wells, and the elevation of the top of the PVC well <br /> casings will be surveyed and tied into permanent markers, if readily available. At a <br /> minimum the well elevation survey will utilize a GPS coordinate system that meets the <br /> requirement/s of the RWQCB's Geotracker database. Survey accuracy will be <br /> approximately 0.1 foot for the "x" and "y" coordinates and .01 foot for the "z" coordinate. <br /> The measuring point will default to the north side of the PVC unless an obvious high <br /> point/irregularity is noted on the casing. These areas will be marked for the surveyors <br /> by the field geologist/water sampling technician prior to the well survey. The depth to <br /> static groundwater will be measured from the marked/surveyed point in subsequent <br /> water level surveys. The depth of water is then subtracted from the elevation of the top <br /> of the well casing to provide a groundwater elevation for each monitoring well location. <br /> The new wells will be tied into the existing monitoring well network elevations and <br /> locations. The well elevation survey will be conducted by a Licensed Land Surveyor or <br /> Engineering firm with the appropriate certifications for performing this work. <br /> 48093.E01/ST07R052/CJC/Iv Page 7 of 15 <br /> ©2007 Kleinfelder, Inc January 26, 2007 <br />
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