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2900 - Site Mitigation Program
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PR0541913
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Last modified
2/13/2020 7:07:47 PM
Creation date
2/13/2020 11:53:44 AM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2900 - Site Mitigation Program
File Section
WORK PLANS
RECORD_ID
PR0541913
PE
2960
FACILITY_ID
FA0024043
FACILITY_NAME
FRONTIER TRANSPORTATION FACILITY
STREET_NUMBER
425
STREET_NAME
LARCH
STREET_TYPE
RD
City
TRACY
Zip
95304
APN
21220009
CURRENT_STATUS
01
SITE_LOCATION
425 LARCH RD
P_LOCATION
03
QC Status
Approved
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EHD - Public
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g Addendum to Interim Corrective Action Plan <br /> Frontier Transportation, Inc. <br /> t April 14, 2006 <br /> - I Page 7 > <br /> Drawdown will be maintained at static level for 4 hours or until dewatering from (` <br /> the pumping well reaches asymptotic minimal flow levels for a period of at least 60 <br /> minutes. <br /> The aquifer test will be performed to identify lateral hydraulic conductivity, <br /> transmissivity, storativity and aquifer dewatering capability allowing technical and cost <br /> effective groundwater treatment. <br /> Variance in transmissivity (T), hydraulic conductivity (K), Specific Yield (S), the <br /> lateral extension of the cone of depression in this unconfined aquifer will be determined <br /> by pumping in two events at the two dewatering wells, MW-9 and MW4, near the <br /> contaminated area. <br /> The lateral variation of T within the aquifer unit will be determined using an <br /> average K determined by averaging conductivity data identified in the two wells. . <br /> The groundwater table will be measured in each of two pumping wellsand each of <br /> observation wells prior to equipment installation using an electronic water table <br /> measurement tape calibrated to 0 .01 -foot accuracy. The thickness of the aquifer will be <br /> determined from boring logs identifying the shallow groundwater retarding layer <br /> J underlying the first aquifer. The groundwater hydraulic gradient will be measured in all <br /> site-monitoring wells immediately prior to aquifer testing. <br /> Dedicated groundwater level indicators will be placed immediately above <br /> termination depth in each pumping and observation well and dedicated for the life of the <br /> aquifer test. The groundwater level loggers will be calibrated to 1 -minute test interval at <br /> 0.01 ` accuracy prior to installation of a submersible pump. Depth to groundwater will be <br /> measured throughout the pumping operation, proposed for a four hour and eight-hour :Ff 1+ <br /> period shouldrufficient. <br /> The pumping will be performed using an approximate 0.3 hp submersible pump <br /> with the discharge hose secured to a 2 thousand gallon portable tank on site and emptied <br /> ' by vacuum truck during aquifer testing. Pumping flow rate will be controlled and <br /> measured using a separate knife gate valve in each pumping well. Flow rate will be <br /> identified using a variable area rotameter with flow rate measurement range from 0.5 to <br /> 25 gallons per minute. Aggregate total discharge will be measured with a flow totalizer. <br /> Groundwater temperature and ambient pressure will be monitored periodically <br /> during the aquifer test. 1 . Contaminant mass, by measuring the pumping rate q, and <br /> knowing the water table depth in two observation wells, we can establish a value of k for <br /> field conditions. The equation in these conditions is <br /> i <br /> , i <br /> f 7 <br />
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