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Groundwater, Surface Water, Flow and Water Level Monitoring
Second Quarter 2002
Bennett's Dump, Monroe County, Indiana

September 24, 2002

1.0 BACKGROUND

This report summarizes the results of groundwater, surface water, flow and water level monitoring work completed by Viacom Inc. during the second quarter of 2002 at the Bennett's Dump site.

Groundwater and surface water monitoring was performed at a total of nine locations (springs, streams and monitor wells) in accordance with the April 2002 Long Term Groundwater Monitoring Plan (LTGWMP) and the March 2002 Groundwater Investigation Plan (GIP) for this site. Continuous monitoring of flow and water levels was also performed at six locations selected by Viacom to promote the understanding of relationships between flows under storm and non-storm conditions, and the resulting PCB concentrations in groundwater and surface water at this site.

2.0 GROUNDWATER AND SURFACE WATER MONITORING

The monitoring work described in this report was performed on April 30, May 22 and June 14, 2002. This three month time period constitutes the second reporting quarter for Bennett's Dump for 2002.
Scope of Work
The scope of groundwater sampling for this monitoring period comprised a combination of monthly and quarterly sampling stipulated in the LTGWMP and GIP, as summarized in Table 1.

Groundwater and surface water sampling was performed at the following locations:

  • Stout's Creek Upstream
  • Stout's Creek Downstream
  • Mound Spring
  • Middle Spring
  • Mid-North Spring
  • North Spring
The approximate locations of these stations are shown on Figure 1, Groundwater and Surface Water Sampling Locations. Exceptions to the routine scope of sampling outlined in Table 1 for this reporting quarter were as follows:
  • No samples were collected at Mid-North Spring on April 30, or at North Spring on May 22 or June 14, since there was no flow at these locations on these sampling dates.
  • Beginning with the April 30 sampling event (the initial event under the LTGWMP), the Stout's Creek Downstream station was changed from its previous location at the Hunter Road culvert to a position just upstream of the confluence of Stout's Creek and the West Branch of Stout's Creek.
  • Sampling was not performed at monitor wells MW-6I and MW-6D since semi-annual sampling is specified at these locations.

Sample Collection and Handling

Samples at the spring and stream locations were collected by carefully filling a new disposable beaker. The water was transferred from the beaker into pre-cleaned amber glass 1-liter bottles supplied by the analytical laboratory. Routine sampling parameters including temperature and conductivity were measured and recorded.

Samples were analyzed by Heritage Lab of Indianapolis, Indiana. The samples were analyzed to a detection limit of 0.1 parts per billion (ppb) for all PCB parameters (except Aroclor 1221; detection limit 0.5 ppb) by EPA SW-846 method 8082. Samples were also analyzed for total suspended solids (TSS) by EPA method 160.2.

Oualitv Assurance

For quality assurance purposes a duplicate sample and a field blank were collected during each sampling event. All environmental and blank samples were labeled and logged onto a chain-of- custody form. The samples were stored and transported on ice in insulated coolers. Custody of the water samples was maintained by Viacom until shipment to the analytical laboratory.

Analytical Results for Groundwater Samples

Per the sampling requirements outlined in Table 1, no groundwater (monitor well) samples were collected during this reporting period. Historical data for the two groundwater sampling stations specified in the LTGWMP, MW-6I and MW-6D, are reported in Table 2, and Table 3 (Part I)(Part II) & 3-2, respectively (attached). In addition, historical data for monitor well MW-03 is attached as Table 4, although this well is not included in the LTGWMP and no further sampling is planned.

Analvtical Results for Surface Water Samples

Field parameter measurements, PCB analytical results, and QA/QC results for surface water samples collected during this reporting period are reported in Table 5, Table 6, Table 7, Table 8(Part I)/(Part II), Table 9, Table 10, Table 1(Part I)/(Part II) Each table summarizes historical groundwater monitoring data collected since the completion of the remedy in November 2000. Table 7 reports historical data for the Stout's Creek West Branch monitoring station, although this station is not included in the LTGWMP and no further sampling is planned. Copies of the chain-of-custody forms are provided in Appendix A. Copies of the certificates of analysis are provided in Appendix B. A validation summary for these samples appears in Appendix C. Copies of the field sampling data sheets are on file at PSARA's Bloomington Branch Office.

3.0 CONTINUOUS Flow AND WATER LEVEL MONITORING

The purpose of flow and water level monitoring is to evaluate site-specific data characterizing site hydrologic response under storm and non-storm conditions, and to evaluate correlations between PCB concentrations, spring flow and Groundwater elevations.

Scope of Work

The scope of Groundwater level and flow monitoring during this reporting period involved the use of dedicated instrumentation to record water level and other parameters as summarized in Table 12.

Water lever transducers, water level data logging equipment, and piezometer crest gauges were operated during all or part of the period from April 2002 through June 2002 at the following locations:

Monitoring Location Equipment Middle SpringIn-Situ mini-Troll transducer/datalogger Mound SpringIn-Situ mini-Troll transducer/datalogger (4/13-6/30) MOO-1In-Situ mini-Troll transducer/datalogger (411-4/26) In-Situ Troll 4000 transducer/datalogger (4/26-6/30) Icebox QuarryIn-Situ Troll 4000 transducer/datalogger Wedge QuarryIn-Situ Troll 4000 transducer/datalogger Stout's CreekIn-Situ mini-Troll transducer/datalogger Pi ezometer HIn-Situ mini -Troll transducer/datalogger Middle Spring Crest gauge Mound Spring Crest gauge Mid-North Spring Crest gauge

The approximate locations ofthe stations listed in Table 12 are shown on Figure 2, Flow and Water Level Monitoring Locations.

Flow and Water Level Plots

The following plots for the monitored stations for this reporting period are attached:
  • water level elevation at Stout's Creek Downstream and Piezometer H;
  • water level elevation at Stout's Creek Downstream and Piezometer H; water elevation and temperature at Icebox Quarry, Wedge Quarry, and MW-01 (elevation only at MW-01 in April);
  • water level elevation at Stout's Creek Downstream and Piezometer H; flow data for the weirs at Middle Spring and Mound Spring.

Quality Assurance

As a quality assurance check in documenting rain events and changes in flow, rainfall records for this time period were obtained from the Purdue University State Climatologist's web site (shadow.agru.purdue.edu/sc.index.htTnl) for the rain gauge station at the Monroe County Airport. This record was obtained for comparison to the downloaded transducer data at the various monitoring locations. Raw rainfall data from the web site appears in Appendix D. Rain events of approximately 0.25- in. or more are indicated on the flow and water level plots. In addition, the plots for Stout's Creek Downstream also show cumulative rainfall data at the PSARA office rain gauge, which is the nearest location to the Bennett's Dump site where a continuous rainfall record is maintained.

As a further data quality check, manual water level measurements were made and crest gauges at Middle Spring, Mound Spring and Mid-North Sprig were monitored during and after significant storm events. The purpose of the manual checks and crest gauge monitoring was to verify instrument readings, in particular those for installations susceptible to the accumulation of silt and/or algae growth. Manual field check data collected this reporting quarter are shown on the data plots. Crest gauge measurements appear in Table 13.

A complete instrument maintenance log for all of the Bennett's Dump installations is attached. This log details the installation, re-indexing, and maintenance histories of each transducer and data logger present at Bennett's Dump during the 2nd Quarter.

Discussion

Data for this period are complete except as follows:
  • the mini-Troll at Mound Spring was installed on April 13; no data are available prior to this date;
  • the Troll 4000 at Wedge Quarry malfunctioned from April 1 to April 18, resulting in no data collected during that time period;
  • the mini-Troll at Stout's Creek Downstream was relocated to a Lemon Lane station for short-term investigation activities from April 4 to April 13;
  • the mini-Troll installation at Stout's Creek Downstream was damaged during a strong storm on June S that resulted in the loss of data through June 30.

The malfunction of the mini-Troll at Wedge Quarry during the first half of April was due to an incorrect initialization time for measurements by the instrument, which was either set incorrectly or not recognized by the instrument. It cannot be determined whether this was the result of operator error or a programming fault. However, the instrument began recording data properly again on April 18 after re-initialization, and continued to do so for the remainder of the reporting period.

The Stout's Creek Downstream station was damaged during a brief but strong storm on June 5. A routine post-storm inspection on June 7 revealed that the instrument had been dislodged from its anchorage and was in the creek tethered to its anchor point by the instrument cable. This instrument was subsequently reinstalled at the precise same location (index datum) on June 13.

The data collected from that date through the end of the month suggested minor diurnal fluctuations in creek stage. A second inspection of the instrument cable revealed possible damage attributable to the June 5 storm event. The cable was returned to the manufacturer for evaluation and was determined to be beyond repair. The cable was replaced in July and the instrument appears to have operated reliably since that time.

The foregoing technical problems represent interruptions in the continuous monitoring operation at these locations. The problems are briefly noted on the flow and water level plots presented hereafter. In addition however, the plots for Middle Spring and Mound Spring appear to contain some questionable data. Both instruments record unusually rapid increases and decreases in flow during the May 7 rain event. The Middle Spring instrument often recorded water level values that, when converted to flow, were negative or zero during this relatively wet period. No particular explanation is apparent, although these same fluctuations do not appear in the subsequent data for June.

Crest Gauges

The crest gauge at Middle Spring was installed on May 2, and the gauge at Mid-North Spring on June 14. The purpose of the crest gauge at Middle Spring was to provide an additional indication of maximum flow to help evaluate the extreme fluctuations in flow recorded by the mini-Troll instrument at this location. The purpose of the crest gauge at Mid-North Spring was to provide an indication of maximum flow only, since there was no other instrument installed at this location. As stated previously, monitoring data for these crest gages are presented in Table 13.

Crest gauge readings during the second quarter of 2002 ranged from 0.08-in. to 0.1 8-in. above the bottom of the V-notch weir at these two locations. These values represent flows ranging from 5.6 to 15.4 gallons per minute (gpm), as shown in Table 13. In general, the crest gauge data for Middle Spring compare favorably (within 17%, on average) with the maximum transducer value recorded at this location for the same time periods. In several cases, however, the transducer at Middle Spring recorded extreme high and low (below zero) values that were viewed as unreasonable. These relatively extreme conditions occurred on May 2, May 7, May 18 through 25, and June 13. For these dates the mini-troll data were compared to the crest gauge data in an attempt to validate or discount the data extremes recorded by the mini-Troll. In all cases, the crest gauge data, which is an upper limit value, was substantially less than the data from the mini-Troll. For this reason, the mini-Troll data for these dates was regarded as suspect and was removed from the attached flow plots for Middle Spring. The reason for the periodic erratic behavior of the mini-Troll at Middle Spring has not been established at this time.

Potentiometric Data

On April 29, 2002, water levels were measured by hand at 5 monitor wells, 2 quarries and 4 springs at the site. The specific measurement locations are listed in the table insert on Figure 3, which also depicts the resulting potentiometric surface across the site on this date.


Warning! Eat no fish from Clear Creek, Pleasant Run, Salt or Richland Creeks.

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