Surface Water, Flow and Water Level Monitoring
Second Quarter 2003
Neal's Landfill, Monroe County, Indiana
August 20, 2003
VIACOM
1.0 BACKGROUND
This report summarizes the results of surface water, flow and water level monitoring work
completed by Viacom Inc. during the second quarter of 2003 at the Neal's Landfill site.
Surface water monitoring was performed at a total of four locations (springs and streams) in
accordance with the April 2002 Long Term Groundwater Monitoring Plan (LTGWMP) and the
April 2002 Groundwater Investigation Plan (GIP) for this site. Continuous monitoring of flow
and water levels was also performed at four locations.
2.0 SURFACE WATER MONITORING
The monitoring work described in this report was performed on March 17, April 10 and May 14,
2003. The March-May time period constitutes the second reporting quarter for Realms Landfill
for 2003.
Scope of Work
The scope of water sampling for this monitoring period comprised monthly sampling at South
Spring and North Spring, as stipulated in the LTGWMP and GIP and summarized in Table 1.
Taylor Spring and Branam Spring, which are sampled on a semi-annual schedule, were sampled
April 10, 2003. The approximate locations of these stations are shown on Figure I, Monitoring
and Sampling Locations.
Sample Collection and Handling
Samples at the spring locations were collected by carefully filling a new disposable beaker. The
water was transferred from the beaker into pre-cleaned amber glass l-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 trillion (ppb) for all PCB parameters (except Aroclor 1221;
detection limit 0.2 ppb) by EPA SW-846 method 8082. Samples \vcre also analyzed for total
suspended solids (TSS) by EPA method 160.2.
Quality 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 chah~-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.
Field blank samples for these sampling events were NL1909, NL1913 and NL1984. No PCBs
were detected in any of these samples.
Analytical Results for Surface Water Samples
Field parameter measurements, PCB analytical results, and QA/QC results for samples collected
during this reporting period are reported in Tables 2 and 3. Historical data for the two
Northwest Spring System sampling stations specified in the LTGWMP, South Spring and North
Spring, are also reported in Tables 2 and 3, respectively. Historical data for the two Southwest
Spring System sampling stations, Branam Spring and Taylor Spring, are reported in Tables 4 and
5, respectively. Each table summarizes historical groundwater monitoring data collected since
the completion of the remedy in November 1999. Copies of the chain-oi:custodv tonics arc
provided in Appendix A. Copies of the certificates of analysis arc provided in Appendix R. A
validation summary for these samples appears in Appendix C. Copies of the field sampling data
sheets are on file at PSARA Technologies, Inc.'s Bloomington Branch Office.
3.0 CONTINUOUS FLOW AND WATER LEVEE 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 6.
Water lever transducers, water level data logging equipment, and piezometer crest gauges were
operated during all or part of the period from March 2003 through May 2003 at the following
locations:
| Monitoring: Location |
Equipment |
| Conard's Branch Weir |
In-Situ mini-Troll transducer/dataloggcr
EZLogger tipping rain gauge |
| MW EPA-5a
|
In-Situ mini-Troll transduccr/datalogger |
| Piezometer I |
In-Situ mini-troll trunsducer/datalogger |
| Piezometer 2 |
Crest gauge |
| Piezometer 3 |
Crest gauge |
| Piezometer 4 |
Crest gauge |
| Piezometer 5 |
Crest gauge |
The approximate locations of these flow and water level monitoring stations are shown on Figure 1.
Flow and Water Level Plots
The following plots for the monitored stations for this reporting period are attached:
-
Flow data and monthly cumulative rainfall at Conard's Branch weir
-
Water elevation at MW EPA-5a and PZ-1
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.html) 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 1). Airport rain events ot
approximately 0.25 inch or more are indicated on the flow and water level plots. In addition' the
plots for the Conard's Branch weir also show cumulative rainfall data from both the airport and
from a rain gauge at Neal's Landfill that is maintained by Viacom.
As a further data quality check, manual water level measurements were made during and after
significant storm events. The purpose of the manual checks 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.
A complete instrument maintenance log for all of the Neal's Landfill installations is attached.
This log details the installation, re-indexing, and maintenance histories of each transducer and
data logger present at Neal's Landfill during the First Quarter.
Discussion
Data for this period are complete except as follows:
The mini-Troll transducer at MW EPA-5a did not collect data from March 6-20. This
instrument began operating properly again on March 20, and has provided quality data
since that date. Therefore, this data gap was presumedly caused by operator error.
Crest Gauges
The purpose of these gauges is to provide an indication of maximum water level in the
piezometers that do not contain transducers. Crest gauge measurements appear in Table 7.
The crest gauges in Piezometers 2, 3, 4, and 5 showed no apparent movement during the second
quarter of 2003.
Scope of Non-Routine Activities
Pumping operations at the new Conard's Branch Pump (CBP) station continued during the
second quarter of 2003. The system operated in both `'continuous low flow" (CLF) mode and
full automatic mode during the quarter depending on daily temperature and flow.
Periodic maintenance of the system during this quarter involved the cleaning of accumulated
sediment and algae from the intake screens on several occasions. In addition, a replacement
(spare) set of intake screens was fabricated and a supplemental pumping system involving two
sump pumps was constructed to handle periods of high flow on Conard's Branch.
Continuous operation in automatic mode is expected to continue uninterrupted during the third
quarter of 2003.
Potentiometric Data
On April 23, 2003, water levels were measured by hand at eleven monitor wells at the site and
the Conard residential well. The depth to water in the Conard residential well was 2().45-ft. at
14:05 hours on this date. The other specific measurement locations are listed in the table insert
on Figure 1, which also depicts the resulting potentiometric surface across the site on this date.
If you have questions regarding the sampling and flow/water level monitoring activities or
findings for this reporting quarter, please call Mike McCann at (812) 335-0424.
Sincerely,
Dorothy M. Alke
Project Director
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