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ARCHIVED REPORTS PHASE II FIELD INVESTIGATION AND LNAPL MOBILITY EVALUATION REPORT
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ARCHIVED REPORTS PHASE II FIELD INVESTIGATION AND LNAPL MOBILITY EVALUATION REPORT
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Last modified
12/14/2018 4:37:48 PM
Creation date
11/6/2018 1:47:45 PM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2900 - Site Mitigation Program
File Section
ARCHIVED REPORTS
FileName_PostFix
PHASE II FIELD INVESTIGATION AND LNAPL MOBILITY EVALUATION REPORT
RECORD_ID
PR0009049
PE
2960
FACILITY_ID
FA0004041
FACILITY_NAME
UP TRACY RAIL YARD
STREET_NUMBER
720
Direction
E
STREET_NAME
SIXTH
STREET_TYPE
ST
City
TRACY
Zip
95376
APN
25001014
CURRENT_STATUS
01
SITE_LOCATION
720 E SIXTH ST
P_LOCATION
03
P_DISTRICT
005
QC Status
Approved
Scanner
WNg
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\MIGRATIONS\S\SIXTH\720\PR0009049\PHASE II FIELD INVESTIGATION AND LNAPL MOBILITY EVALUATION REPORT.PDF
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' Phase II Field <br /> ARCADES Investigation and LNAPL <br /> Mobility Evaluation Report <br /> Union Pacific Railroad Company <br /> Former Maintenance Facility <br /> Tracy, California <br /> increased above historical maximums in the last year in several on-site wells <br /> (MW-08A, MW-11, PZ-01, TW-01, TW-02, and TW-04),which is due to a drop in <br /> groundwater elevation at these wells. LNAPL was observed recently in MW-08A during <br /> March 2009; however, LNAPL has not recently migrated into this area because 0.12 <br /> inch of LNAPL was observed once in March 2004.Also, LNAPL is not presently <br /> accumulating in wells with no historical LNAPL detections and plume fringe wells MW- <br /> 14A and MW-22A have not had any observable LNAPL since they were installed in <br /> 1991 These two findings indicate that the LNAPL plume is stable and not migrating. <br /> ' LNAPL mobility at the pore-scale is dependent upon the presence of a sufficient driving <br /> head and hydraulic gradient. Therefore, accumulation of LNAPL in monitoring wells is <br /> ' not a stand-alone indicator of LNAPL mobility. <br /> 5.2.2 LNAPL Field and Residual Saturations <br /> LNAPL saturation was assessed on soil cores collected from the Site through the <br /> petrophysical laboratory analyses PFS, FPM, and RSWD. Residual saturation values <br /> are generated through the latter two laboratory tests. LNAPL is immobile when field <br /> saturation equals residual saturation. <br /> LNAPL saturation data are presented in Table 7 and on Figures 12 and 13. LNAPL <br /> saturation data provided by PFS testing,which does not provide a residual saturation <br /> value,were compared to the residual saturation data from RSWD testing at the same <br /> ' site location. Field LNAPL saturation exceeded residual LNAPL saturation during the <br /> RSWD test at site locations LIF-02, LIF-06, LIF-10, and LIF-25. These results indicate <br /> that LNAPL is mobile at the pore-scale, as defined by ITRC, at these four site locations. <br /> LNAPL pore velocity calculations were performed when LNAPL field saturation <br /> exceeded the residual saturation. <br /> ' 5.2 3 LNAPL Pore Velocity Calculations <br /> There is potential for LNAPL movement in the subsurface at the pore-scale wherever <br /> measured field LNAPL saturations exceed residual saturation. LNAPL seepage <br /> velocity was calculated at each of the four locations (LIF-02, LIF-06, LIF-10, and <br /> LIF-25)where field saturation was greater than residual. LNAPL seepage velocity was <br /> ' calculated as a function of LNAPL saturation. Figure 14 presents LNAPL pore velocity <br /> for each location at all possible LNAPL saturation values(from residual LNAPL <br /> saturation on the left side of the figure to the irreducible water saturation on the right <br /> side). The measured field LNAPL saturation values from each soil core sample are <br /> rpt-upm_#acy�navi moUirty(91-29-201 o)dw 25 <br />
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