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Following
a property transfer in late 1995, this telecommunications industry client
initiated activities necessary for regulatory closure of this research and
development laboratory site, under New Jersey’s Industrial Site Recovery
Act (ISRA). Initial activities performed by the client included signing a
Remediation Agreement and submitting Preliminary Assessment (PA) Reports
for this and five other ISRA-subject sites. Since early 1996, Mr.
Peterson has provided all project management and technical consulting
services in connection with one of the project sites and Princeton
Geoscience has served as the project consultant since its formation in
February 2000.
Site Investigation
Site characterization activities included
developing, implementing, managing and reporting for work activities,
during ISRA Site Investigation (SI) and, Remedial Investigation (RI)
phases of work. The PA Report identified 28 potential Areas of Concern at
the site. Sampling and other evaluation required during the SI focused on
19 of these areas, including decommissioned septic systems, underground
chemical wastewater piping, sumps, underground storage tanks, stormwater
sewers, a detention basin, and transformers.
Remedial Investigation
Based on the SI results, Princeton Geoscience performed an RI to evaluate
the extent of contamination at four areas, and to evaluate hydrogeologic
conditions and groundwater quality across the site. Hydrogeologic
investigations required consideration of several Coastal Plain geologic
formations, multiple areas of aquifer recharge, complex flow conditions,
and groundwater discharge into two wetland areas. Naturally
elevated concentrations of several trace metals were associated with
minerals
of the aquifer matrix, which necessitated development of specialized
sampling and statistical evaluation procedures to obtain representative
characterization of natural vs. facility-related groundwater impacts. A
well search and water supply survey and a Baseline Ecological Evaluation
were conducted in conjunction with contaminant fate and transport
analysis, to assess potential impact to receptors.
Based on the completed SI and RI, No Further
Action status was obtained for 26 of the 28 Areas of Concern identified during
the PA. Active remediation was required in four areas, including:
· An area of PCB-contaminated soil adjacent to an active
transformer
· An area of pesticide-contaminated soil in a landscape bedding
area which was identified during sampling along delivery lines leading to a
septic system
· Groundwater impacted by nitrate, ammonia and trace levels of
chlorinated organic compounds near a decommissioned septic system leachfield
· Groundwater impacted by chloroform downgradient of a parking
lot and concrete walkway
Soil Remedial Actions
Princeton Geoscience designed and managed implementation of removal
actions to address the PCB- and pesticide-impacted soils at the
transformer and landscape bedding areas. Challenges included performing
excavation work safely in immediate proximity to the main facility
building and in an area of active, high-voltage electrical units and
subsurface
utilities, and ensuring effective containment of excavated soil and prevention
of dust transport of contaminants at this occupied facility. A total of
450 tons of non-hazardous waste soil were excavated and transported
offsite for recycling at a mine reclamation site in eastern Pennsylvania.
The excavation and restoration was completed over three weekends, allowing
facility activities to proceed without interruption during
the work week.
Groundwater Remedial Actions
Abandoned Septic System Area
Bench-scale treatability
and field pilot studies were completed to evaluate the feasibility of
implementing enhanced, in-situ bioremediation for nitrate, ammonia and
chlorinated organic compounds in groundwater near the abandoned septic
system leachfield. Based on the positive results of these innovative
studies, a full-scale remedy was considered which incorporated two
separate treatment zones (permeable reactive barriers) along the
groundwater flowpath. In the leachfield area, oxygen-releasing compounds
were to be injected to establish a nitrification enhancement zone, where
sorbed ammonium would be converted under aerobic conditions to nitrate, a
more mobile nitrogen compound. Downgradient of the leachfield, oxygen
scavenging compounds and a carbon source material would be injected to
create a denitrification enhancement zone, where nitrate formed in the
leachfield area would be “cut off” by anaerobic denitrification
processes. The anaerobic conditions and available carbon source would
also facilitate reductive dehalogenation of the chlorinated organic
compounds found at low concentrations near the leachfield. Excavation and
conventional pump and treat alternatives were also considered, but were
ruled out due to their cost and partial
effectiveness.
In 2004, the New Jersey Ground Water Quality Standard (GWQS) for ammonia
was increased by a factor of six, to 3.0 mg/L. In light of this
development, Princeton Geoscience determined that a simpler remedy based
on potable water discharge to the former leachfield piping might be
appropriate. Field pilot testing over a 90-day period indicated this
approach reduced nitrate and ammonia concentrations to below the GWQS,
with only limited rebound following the cessation of the potable water
discharge. We attributed the contaminant concentration reductions to
dilution, flushing, and geochemical and microbial changes coincident with
the potable water discharge. Based on these findings, potable water
discharge has been proposed as a source reduction remedy for the abandoned
leachfield area, in conjunction with monitored natural attenuation for
downgradient plume areas.
Chloroform Plume Area
The source of the chloroform in site groundwater was initially unclear, because
the plume appeared to originate in a relatively undisturbed, wooded area of the
site, away from any known or likely past chemical releases. To define the
extent and source of the chloroform concentrations in groundwater, Princeton
Geoscience conducted a detailed delineation program using direct-push (i.e.,
Geoprobe®) groundwater sampling techniques and in-field analyses by an NJDEP-certified
mobile laboratory. This effort showed that the plume in fact originates in a
wooded and grass-covered area traversed by a
concrete
sidewalk and stairway at the downgradient edge of a paved parking lot.
Potential sources such as leakage along sanitary sewer lines or water lines were
ruled out, based on locations of these utilities and the distribution of
chloroform in groundwater. Since their construction in the mid-1980s, the
parking lot and concrete walkway have been treated with salt for snow and ice
removal. Runoff of deicing meltwater to adjacent organic topsoil takes place in
this area.
Based on a literature search and review of site conditions, Princeton Geoscience
identified alternate mechanisms which explain the chloroform occurrence.
Specifically, we concluded that natural in-situ halogenation of soil organic
matter, augmented by influxes of low pH, chloride-containing runoff associated
with the deicing salt applications, caused enhanced formation of chloroform in
the soil zone, leading to the observed groundwater impact. This finding is
novel, because although halogenation of soil organic matter via both biological
and abiotic processes has been associated with natural chloride deposition in
precipitation, chloride-enhancement by road salt has not been considered
previously. Princeton Geoscience developed and is in the process of obtaining a
United States patent for a simple remedial process to treat primary and residual
sources of chlorinated VOC impacts resulting from salt-enhanced in-situ
halogenation of soil organic matter. We anticipate the process will be utilized
to remediate chloroform impacts at the site.
Current Status
Institutional controls will also be required as a component of the ISRA site
remediation. These will include development of a Classification Exception Area
for groundwater contamination and filing of a Deed Notice. NJDEP is currently
reviewing the Remedial Action Selection Report and Remedial Action Workplan for
the two areas of groundwater impact. Upon receipt of NJDEP’s comments on the
documents, final design of the remedies will be completed, followed by
implementation of the remedies and institutional controls.
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