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Quarterly ground water sampling results, Livingston Rail Yard, Livingston, Montana PDF

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628.161 M26gsr 1992 ^ I l li i THIRD QUARTER 1992 GROUND WATER SAMPLING RESULTS LIVINGSTON RAIL YARD LIVINGSTON MONTANA STATE DOCUMENTS COLLECTIGJ, DEC 11992 SouubDmiimtttteeda MONTANA STATE library ttoo'. 1515 £ 6th AVE HELENA, MONTANA 59620 Montana Department of Health and Environmental Sciences Solid and Hazardous Waste Bureau Cogswell Building Helena, Montana 59620 Submitted by: Burlington Northern Railroad Co. 9401 Indian Creek Parkway Overland Park, KS 66201 Prepared by: Envirocon, Inc. P.O. Box 8243 Missoula, Montana 59807 Submittal Date: November 11, 1992 ENVIROCON, INC INTRODUCTION 1.0 This report presents the results of ground water samples collected during the third quarter of 1992. Ground water sampling for this quarter consisted of the August quarterly sampling event. The Montana Department of Health and Environmental Sciences (MDHES) approved Burlington Northern Railroad’s May 1992 draft Ground Water Sampling Plan, which does not require ground water sampling during July or September. RESULTS 2.0 The samples were analyzed by Energy Laboratories, Inc. in Billings, Montana. Results for the August 1992 quarterly sampling event are presented below. 2.1 August 1992 Quarterly Ground Water Sampling Event The August 1992 quarterly sampling event was conducted on August 27 through September 1992. Twenty-two samples were analyzed as part ofthis 1, event: twenty samples were primary and duplicate samples collected at monitoring wells within and around the Livingston Rail Yard, and two samples were trip blanks. All samples were analyzed for purgeable halocarbons by EPA Method 601. Tables 1, 2, 3, and 4 summarize quarterly analytical results for tetrachloroethene (PCE), trichloroethene (TCE), cis-l,2-dichloroethene (DCE), and chlorobenzene. Laboratory analytical results and a data validation report for this sampling event are in Appendix A. Most of the ground water samples collected during the August 1992 VOC quarterly sampling round contained dissolved chlorinated concentrations 1 Digitized by the Internet Archive 2015 in https://archive.org/details/quarterlyground1992mont_1 that continued the general decline observed during the past three years. A few notable sample results are described below. The PCE concentration in the sample from Monitoring Well 89-3 was 170 parts per billion (ppb). Well 89-3 is located immediately downgradient from the Electric Shop SVE system around the former degreasing area, as shown on Figure 1.0. This is a concentration decline from previous sample results and would be interpreted as resulting from removal ofover 300 pounds ofPCE from soil above the water table at this source area. However, the field duplicate sample contained a PCE concentration of 420 ppb. This poor correlation between primary and duplicate samples invalidates both samples. Further sampling will be necessary to determine the impact of the Electric Shop SVE system. Well 92-1 is located immediately downgradient from the SVE system at the Locomotive Shop manways, as shown on Figure 1.0. The PCE concentration of 220 ppb in the sample from Monitoring Well 92-1 is significantly lower than concentrations found in previous quarterly ground water samples collected at this location. The previous two samples from this well, collected in February and May 1992, contained 850 ppb and 520 ppb of PCE, respectively. The August 1992 results probably reflect the removal of over 110 pounds of PCE from the upgradient source at the Locomotive Shop manways by SVE. Monitoring Well 92-2 is located 160 feet east of the Yellowstone River, immediately south of the railroad tracks, as shown on Figure 1.0. As shown by the results in Appendix A, the August 1992 sample from this well contained 41 ppb of PCE, along with 18 ppb of DCE and 8.4 ppb of TCE. These concentrations are higher than those found in the only previous sample from this well, collected in May 1992. Further investigation is planned to determine 2 ) whether VOCs in the ground water on the east side of the river are due to sources east of the river or underflow of ground water beneath the river. Monitoring Well 92-3 was installed in July 1992 along the railroad tracks near the intersection of Park and E Streets, as shown on Figure 1.0. The August 1992 sample from this well contained 1.2 ppb of PCE. This indicates that low concentrations of PCE are present in the ground water in this area. The source of these low detections is not presently known. Monitoring Well 92-4 was installed in August 1992 to more accurately determine the position ofthe VOC plume boundary on the north side ofthe rail yard. Figure 1.0 shows the location of Well 92-4. The August 1992 sample collected from Well 92-4 contained only 2.2 ppb ofPCE. No other chlorinated VOCs were detected. This result indicates that the north boundary of the plume is farther south than is shown on plume maps in the Draft Remedial Investigation Report. 3 Table 1: Tetrachloroethene Analytical Results for Ground-Water Samples Collected During the November 1991, February 1992, May 1992, and August 1992 Sampling Rounds, Livingston Rail Yard, Livingston, Montana. Chemical Parameter: Tetrachloroethene Units: ug/L 1991 1992 1 Monitoring November February May August Well Quarterly Quarterly Quarterly quarterly 5 < 0.5 B 0.52 B < 0.5 B < 0.5 B 89-2 < 0.5 B < 0.5 B < 0.5 B < 0.5 B 89-3 280.0 B 180.0 B 260.0 B 170.0 U 89-4 210.0 B 240.0 B 210.0 B 160.0 B 89-9 190.0 B 200.0 B 180.0 B 170.0 B 90-6 - - < 0.5 B 0.54 B 92-1 - 850.0 B 520.0 B 220.0 B 92-2 - - 15.0 B 41.0 B 92-3 - - - 1.2 B 92-4 - - - 2.2 B HRO-17 - - 62.0 B 86.0 B L-87-2 0.83 B 2.2 B - < 0.5 B L-87-3 130.0 B 140.0 B 140.0 A 80.0 B L-87-5 160.0 B 150.0 B - 160.0 B L-87-8 < 0.5 B 16.0 B 11.0 B 6.2 B L-88-10 65.0 B 115.0 B - 71.0 B LS-11 8.0 B 38.0 B 75.0 B 14.0 B LS-8 40.0 B 74.0 B 73.0 B 66.0 B '

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