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ABC ONE HO
CLEANERS
NORTH CAROLINA
EPA ID# NCD024644494
EPA REGION 4
Onslow County
Jacksonville
Site Description
The 1-acre ABC One Hour Cleaners site has operated as a dry cleaning operation since
1954. Facilities previously consisted of three buildings, but two of the buildings were joined to
form one complex. Workers stored tetrachloroethylene (PCE), a dry-cleaning solvent, in a
250-gallon aboveground tank. The only hazardous wastes known to be generated at the site
were from the recycling wastes still that was used to reclaim spent solvents. Until about 1985,
wastes were buried on the site, although operators now send them to an EPA-approved
hazardous waste facility. A septic tank/soil absorption system, consisting of an underground
concrete tank and lid, has always been used to store wastewater. All these processes are
housed in the rear building. In 1984, the nearby Camp Lejeune Marine Corps Base, also
proposed for the NPL in 1988, sampled 40 community drinking water supply wells. Analysts
found organic compounds in three wells near two off-base dry cleaners. Investigations by the
North Carolina Department of Natural Resources and Community Development narrowed
the source of the contamination to ABC Cleaners. After inspecting the site, the State found
that the stored solvent was entering the septic tank/soil absorption system and was polluting
groundwater. This system since has been taken out of service. State analysts also identified
PCE in a monitoring well at ABC Cleaners and in two community wells near the site.
Approximately 41,000 people obtain drinking water from three public well systems within 3
miles of the site.
Site Responsibility: This site is being addressed through
Federal actions.
NPL LISTING HISTORY
Proposed Date: 06/24/88
Final Date: 03/31/89
Threats and Contaminants
The groundwater is contaminated with volatile organic compounds (VOCs), mainly
PCE. Nearby residents' health may be threatened if they drink or come in direct
contact with contaminated groundwater.
March 1992
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Cleanup Approach
This site is being addressed in a long-term remedial phase focusing on cleanup at the entire
site.
Response Action Status
Entire Site: The EPA began an intensive study of site conditions in 1989. This
investigation will explore the nature and extent of groundwater contamination and
wall recommend the best strategies for final cleanup. It is slated for completion in
1992, with cleanup activities scheduled to start soon thereafter.
Environmental Progress
After adding this site to the NPL, the EPA performed preliminary site investigations and
determined that the ABC One Hour Cleaners site was safe to the surrounding community
and the environment while the investigation leading to the selection of final cleanup remedies
is taking place.
Site Repository
Cnslow County Public Library, 58 Doris Avenue, East, Jacksonville, NC 28540
March 1992
ABC ONE HOUR CLEANERS
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ABERDEEN
PESTICIDE
DUMPS
NORTH CAROLIN
EPA ID# NCD980843346
EPA REGION 4
Moore County
Aberdeen
Other Names:
Fairway Six Dump
Twin Dumps
Mclver Pesticide Dump
Route 211 Dump
Farm Chemicals, Inc. Dump
Site Description
The Aberdeen Pesticide Dumps are a cluster of five pesticide dumps ranging in size from 1/2
to 1 1/2 acres within 2 miles of one another; all but one are privately owned. They were
discovered in 1984 during construction of a golf course. That same year, the North Carolina
Solid and Hazardous Waste Management Branch found several bags of pesticides and noted
a strong chemical odor at the site. State analysis revealed soil contamination caused by
various pesticides. Soils at two other properties also were found to be contaminated with
pesticides. One property is owned by the town of Aberdeen, and the other, 350 feet away, is
privately owned. Both are 500 feet from the Farm Chemicals operation, where a string of
owners has manufactured pesticides since the 1930s. A citizen tip led the State to the Mclver
dump in 1984, where officials found 200 to 300 55-gallon pesticide drums in a leased rubble
landfill. Further investigations disclosed another area where pesticides had been dumped.
Under a State order, Farm Chemicals and the lessee of the property removed the drums in
1985. After the EPA began emergency cleanup at three of the dumps, the owner of another
dump reported site contamination to authorities. The State found a pile of cardboard
containers, pesticide bags, powders, and tarry residues. The last discovered dump is located on
the site of the long-standing pesticide manufacturer. Soils at all five areas contain pesticide
residues and are permeable, facilitating movement of contaminants into groundwater. Nearby
Page's Lake also is threatened. Four of Aberdeen's 12 municipal wells are contaminated with
forms of lindane; two wells were shut down in 1986 and 1990 because levels were sufficiently
elevated to present a health risk. Approximately 15 other off-site wells contained various
forms of lindane. The surrounding area is rural. Approximately 3,500 people live within the
municipal well service area. In addition, approximately 2,000 people are served by private
wells in the area.
Site Responsibility: This site is being addressed through
Federal, State, and potentially
responsible parties' actions.
NPL LISTING HISTORY
Proposed Date: 01/22/87
Final Date: 03/31/89
March 1992
-------
Threats and Contaminants
Fifteen off-site wells contained various pesticides, as did soil in many unlined
trenches. On-site soils contain DDT and its components and toxaphene. People
may be exposed to contaminants through direct contact with pure pesticide
products in surface and subsurface soil. Other health risks include ingestion or
direct contact with contaminated groundwater.
Cleanup Approach
This site is being addressed in four stages: emergency actions and three long-term remedial
phases focusing on cleanup of the entire site, the Fairway Six Disposal Area, and the
environmental risks and groundwater cleanup.
Response Action Status
Emergency Actions: In 1985, EPA emergency workers removing surface
contamination at the Fairway Six Area uncovered three large trenches of buried,
concentrated pesticide wastes. Wastes, pure product, packing material, and
contaminated soil were excavated and transported to an EPA-approved disposal facility.
Wastes and contaminated soil were removed from the Twin Sites Area and the Mclver Dump
Area "B"; workers shipped more than 450 truckloads to an EPA-approved facility for disposal.
In 1985, under State order, two parties potentially responsible for contamination at the
Mclver Dump Area "B" steam-cleaned, triple-rinsed, and crushed nearly 700 drums and sent
them to the Moore County landfill. Another emergency action occurred in 1986 at the Route
211 Area. Five truckloads (100 tons) of pesticide-contaminated soil were shipped off site to
an EPA-approved facility for disposal. After pesticides were detected in Aberdeen's drinking
water in 1986, EPA emergency workers returned to discover four more trenches thought to
contain about 12 million pounds of pesticide wastes at the Fairway Six Area. An on-site
mobile incinerator conducted a test burn in which 12,000 pounds of contaminated soil and
debris were incinerated. Incinerator ash was stored in 27 on-site 55-gallon drums. In 1988,
EPA workers excavated, shredded, screened, and stockpiled about 55 million pounds of
pesticide-contaminated materials, which now await further long-term treatment through the
remedial program.
Entire Site: The EPA began an intensive study of contamination at this cluster
of dumps in 1987. The investigation was completed in mid-1991. The selected
remedy entails thermal treatment of approximately 124,000 cubic yards of
contaminated soil at one central location. This volume includes the 22,000 cubic yards of soil
at the Fairway Six Area.
March 1992 4 ABERDEEN PESTICIDE DUMPS
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Fairway Six Disposal Area: The EPA selected a cleanup remedy for this
portion of the site in 1989. It features: (1) excavating and blending stockpiled
pesticide-contaminated wastes; (2) burning them in a mobile incinerator on site;
(3) recycling wastes from this process back into the incinerator; (4) monitoring air emissions;
and (5) disposing of residual ash on the site. Union Carbide Corporation agreed to complete
the design and to conduct the cleanup activities. In 1991, the EPA amended the cleanup
remedy from incineration to thermal desorption.
Environmental Risks and Groundwater: The EPA is undertaking a study of
environmental risks associated with the site and of the nature and extent of
groundwater contamination. This study was completed in 1991, however, additional
field work is necessary in two areas of the site. A remedy for groundwater cleanup is
scheduled for selection in 1992.
Site Facts: Unilateral Administrative Orders were issued to four of the potentially
responsible parties, compelling them to implement the cleanup activities at the Fairway Six
Disposal Area. One party agreed to comply with the Order.
Environmental Progress
The emergency treatment and/or removal of solid and liquid wastes and soil, as well as the
installation of fences, have reduced the potential for exposure to hazardous materials at the
Aberdeen Pesticide Dumps site while further cleanup activities are taking place.
Site Repository
Aberdeen Town Hall, 115 North Poplar Street, Aberdeen, NC 28315
ABERDEEN PESTICIDE DUMPS
March 1992
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BENFIELD
INDUSTRIE
NORTH CAROLINA
EPA ID#NCD981026479
EPA REGION 4
Haywood County
Hazelwood
Site Description
Benfield Industries, Inc. began mixing and packaging bulk chemicals on this 5-acre site in
1976. The company listed a wide range of organic and inorganic chemicals for sale. In 1982, a
fire destroyed most of the plant; except for minor mixing operations and cleanup of debris
from the fire, operations ceased. In 1986, the owner removed other debris and usable
chemicals from the site in preparation to sell the land. The site lies in the flood plain of
Richland Creek, next to Browning Branch. Local surface water is used for recreational
activities. As of 1985, approximately 1,800 people used drinking water from private wells
within a 3-mile radius of the site.
Site Responsibility: This site is being addressed through
Federal actions.
NPL LISTING HISTORY
Proposed Date: 06/24/88
Final Date: 10/04/89
Threats and Contaminants
In 1985, the North Carolina Division of Health Services found high concentrations
of polycyclic aromatic hydrocarbons (PAHs), produced from chemical packaging
activities, in the soil on the western portion of the site and in other areas. If
contaminants enter groundwater, people who drink such water may be threatened.
March 1992
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Cleanup Approach
This site is being addressed in a single long-term remedial phase focusing on cleanup of the
entire site.
Response Action Status
Entire Site: The EPA initiated an intensive study to evaluate site contamination.
This investigation will examine the nature and extent of pollution problems on the
site and will recommend the best strategies for final cleanup. It began in early
1991 and is scheduled to conclude in 1992, at which time EPA will select the most effective
cleanup methods. As part of the remedial investigation, the site was surrounded by a six foot
chain linked fence.
Environmental Progress
After adding this site to the NPL, the EPA performed preliminary investigations and
determined that no immediate actions were needed at the Benfield Industries site while
further investigations and cleanup activities are taking place.
Site Repository
Hazelwood Town Hall, 101 West Georgia Avenue, Hazelwood, NC 28738
BENFIELD INDUSTRIES, INC.
March 1992
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BYPASS 601
GROUND
WATER
CONTAMINATION
NORTH CAROLINA
EPA ID# NCD044440303
Site Description
EPA REGION 4
Cabarrus County
Concord
Other Names:
Scrap Recycling, Inc.
The ByPass 601 Ground Water Contamination site is an area in Concord where the
ground-water is contaminated with lead from multiple sources. The best known source is the
Martin Scrap Recycling (MSR) Facility, which occupies approximately 13 acres. Past practices
included disposing of waste acid on site or selling it for reclamation and using spent battery
casings for fill material on site. In 1982, the Department of Health Services for North
Carolina notified the site owner that waste materials must be cleaned up or the facility must
be closed. In response, the owner removed 2 to 6 inches of soil in the operations area and
sold it for reclamation, along with process waste by-products. A permit for hazardous waste
disposal was granted to the facility in 1983; groundwater contamination was discovered that
same year. Ten other potential sources have been identified and are under investigation.
Approximately 3,000 people live in this rural community. Private wells are near the site, and
the closest home is within 500 feet.
Site Responsibility: This site is being addressed through
Federal actions.
NPL LISTING HISTORY
Proposed Date: 10/01/84
Final Date: 06/10/86
Threats and Contaminants
21AJ
The groundwater, soil, and surface water are contaminated with heavy metals
including lead and chromium. Human health could be threatened if people come in
direct contact with contaminated sediments or waters or ingest contaminated
groundwater. Public access to the site is restricted by a fence and difficult terrain.
March 1992
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Cleanup Approach
This site is being addressed in three stages: initial actions and two long-term remedial phases
focusing on cleanup of the Martin Scrap Recycling area and of the additional sources of
contamination.
Response Action Status
Initial Actions: The EPA sampled soil around battery casings in other disposal
areas around the MSR facility and is expected to remove the battery casings and
contaminated soil to the MSR facility for inclusion in the final remedy.
Martin Scrap Recycling Area: The EPA selected a remedy that entails
excavation, consolidation, and capping of contaminated soils. The engineering
design of the remedy was completed in 1991.
Additional Sources: In 1990, the EPA began a study to determine the nature
and extent of groundwater contamination. Additionally, the EPA is attempting to
identify sources of the groundwater contamination. To date, ten sources have been
identified. This study is scheduled for completion in 1993.
Environmental Progress
By performing site sampling and the expected removal of battery casings, the EPA will make
the ByPass 601 Ground Water Contamination site safer while investigations are being
completed and cleanup activities begin.
Site Repository
Charles A. Cannon Memorial Library, 27 Union Street, North Concord, NC 28025
BYPASS 601 GROUND WATER CONTAMINATION
March 1992
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CAMP LEJEU
MILITARY
RESERVATION
NORTH CAROLINA
EPA ID# NC6170022580
EPA REGION 4
Onslow County
Jacksonville
Other Names:
USMC Camp LeJeune Marine
Corps Base
USMC New River
Marine Corps Air Station
Site Description
Camp LeJeune Military Reservation, a U.S. Marine Corps Base established in 1941, covers
170 square miles in Onslow County. The complex has a number of facilities, including the
Marine Corps Air Station New River, which adjoins the base. The main functions of the base
are to provide housing, training, logistical, and administrative support for Fleet Marine Force
Units. The Navy has identified 77 potential waste disposal areas in Camp LeJeune and has
designated 23 as posing a potential threat to public health and the environment. The Navy
has detected pesticides in the soil and various contaminants in the groundwater. Several on-
base drinking water wells have been closed. Approximately 13,800 people obtain drinking
water from wells within 3 miles of the contamination on the site, with the nearest well being
3,500 feet away from one of the areas of contamination. Groundwater is the sole source of
drinking water for the base and the surrounding communities. Surface water from the base
drains into the Atlantic Ocean via the New River. Both bodies of water are used for fishing
and recreational activities.
Site Responsibility: This site is being addressed through
Federal actions.
NPL LISTING HISTORY
Proposed Date: 06/24/88
Final Date: 10/04/89
Threats and Contaminants
The groundwater is contaminated with volatile organic compounds (VOCs), such
as fuels and chlorinated solvents, from the former disposal activities. Soils are
contaminated with mercury, pesticides including DDT, DDE, and aldrin, and
polychlorinated biphenyls (PCBs). Because the soil at the site is permeable,
conditions are favorable for contaminants to move further into the groundwater.
Although several drinking water wells on the base have been shut down, the
contaminant plume may affect other wells. People who drink the contaminated
water may be at risk.
10
March 1992
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Cleanup Approach
The site is being addressed in nine long-term remedial phases focusing on cleanup of
seventeen sub-sites.
Response Action Status
Sub-site 21, Sub-site 24, and Sub-site 78: The U.S. Marine Corps is
currently studying the nature and extent of contamination at Sub-sites 21,24, and
78. Possible contaminants include pesticides, PCBs, fly ash, solvents, paint
stripping compounds, and VOCs such as PCE. The investigation is expected to be completed
in 1994, at which time a-remedy will be selected to address final cleanup of the contaminants.
An interim investigation addressing the PCE contamination of a shallow aquifer also is
underway. This study will determine the best alternatives for containing and cleaning up two
plumes in the shallow aquifer. The interim remedy is expected to be selected in 1992.
Sub-site 6 and Sub-site 9: Field work exploring possible sources of
contamination such as pesticides, PCBs, and solvents at Sub-site 6 and potential
oil, solvents, and contaminated fuels at the fire training pit on Sub-site 9 is
expected to begin in late 1992. Once the investigation is completed, expected in 1994,
alternative cleanup options will be selected.
Sub-site 48: Field work exploring the nature and extent of mercury
contamination at this Sub-site is expected to begin in late 1992. The investigation
is expected to be completed in 1994, at which time a final cleanup remedy will be
selected for the Sub-site.
Sub-site 69: Field work is expected to begin in late 1992 at this chemical dump
Sub-site. The study will be exploring the nature and extent, as well as the possible
sources of contamination, including pesticides and other chemical agents. Once
the investigation is completed, scheduled for 1995, final cleanup remedies will be selected to
address contamination at Sub-site 69.
Sub-site 2 and Sub-site 74: An investigation is scheduled to begin in 1993 to
explore the nature and extent of contamination at Sub-site 2 and Sub-site 74.
The study will be exploring potential contaminants at these sites including
pesticides, PCBs, and grease. Once the investigation is completed, expected in 1994,
alternative cleanup options will be selected.
Sub-site 35, Sub-site 36, and Sub-site 41: In 1995, an investigation is
expected to begin exploring the nature and extent of contamination at these Sub-
sites. The investigation will address potential sources of contamination including
municipal and industrial wastes, hydraulic fluids, solvents, and ordinances. The study will
identify alternative cleanup options for final remedy selection for the Sub-sites.
CAMP LEJEUNE MILITARY RESERVATION 11 March 1992
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Sub-site 1, Sub-site 28, and Sub-site 30: In 1994, an investigation is
planned to begin exploring the nature and extent of contamination at these Sub-
sites. Potential sources of contamination that will be addressed include petroleum
waste, oil, lubricants, battery acids, mixed industrial wastes, and sludge mixed with lead from
fuel storage tanks. The investigation is expected to be completed in 1995, at which time
alternative cleanup options will be identified to address the Sub-sites' contaminants.
Sub-site 16: An investigation is scheduled to begin in 1994 to explore the
nature and extent of waste oil contaminants at this tire debris site. The
investigation is expected to be completed in 1995, at which time alternative
cleanup options will be identified to address the Sub-site's contaminants.
Sub-site 73: In 1995, an investigation is scheduled to begin exploring the nature
and extent of contamination at Sub-site 73. The study will address the 400,000
gallons of waste oils and 20,000 gallons of waste battery acid that possibly
contaminate the Sub-site. Once the study is completed, expected in 1996, alternative cleanup
options will be selected.
Site Facts: Camp LeJeune is participating in the Installation Restoration Program, a
specially funded program established by the Department of Defense (DOD) in 1978, to
identify, investigate, and control the migration of hazardous contaminants at military and
other DOD facilities.
Environmental Progress
Presently, the DOD is monitoring drinking water supplies, and subsequently is closing wells
when contaminant levels exceed health standards. These practices have reduced risks from
contamination at this site. After placing the Camp LeJeune Military Reservation site on the
NPL, the EPA conducted an initial investigation and determined that the site does not
presently pose an immediate threat to the surrounding communities or the environment while
studies leading to a final cleanup remedy selection are being conducted by the U.S. Marine
Corps.
Site Repository
Onslow County Library, 58 Dorris Avenue, East, Jacksonville, NC 28540
March 1992 12 CAMP LEJEUNE MILITARY RESERVATION
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CAPE FEAR W
PRESERVI
NORTH CAROLI
EPA ID# NCD003188828
EPA REGION 4
Cumberland County
Fayetteville
Site Description
The 41-acre Cape Fear Wood Preserving site contains a 10-acre wood preserving facility.
From 1953 until 1983, wood was treated, using both the creosote and the chromated-copper-
arsenate (CCA) process. Process wastes were deposited in an unlined treatment lagoon and a
surface impoundment. Wastes also were allowed to discharge from a sump into a drainage
ditch. Contaminants have been found in the soil, groundwater, a drainage ditch, and a diked
pond on the site. Buildings contain asbestos, and CCA crystals were spilled under the process
building. The site is vacant, and access is unrestricted. Approximately 1,000 people live within
1/4 mile of the site. About 16,000 people living within 3 miles of the site depend on public
wells as a source of drinking water. Land across the road from the site is used for agricultural
purposes, and an unnamed creek is nearby.
Site Responsibility:
This site is being addressed through
Federal actions.
NPL LISTING HISTORY
Proposed Date: 06/10/86
Final Date: 07/22/87
Threats and Contaminants
IT
The groundwater is contaminated with heavy metals including arsenic and
chromium, as well as benzene and polycyclic aromatic hydrocarbons (PAHs). The
sediments from the pond and surface water from the drainage ditch also are
contaminated with PAHs. The soil is contaminated with PAHs and arsenic. People
who accidentally come in direct contact with or ingest contaminated soil,
sediments, groundwater, or surface water may be exposed to hazardous materials.
13
March 1992
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Cleanup Approach
This site is being addressed in two stages: initial actions and a long-term remedial phase
focusing on cleanup at the entire site.
Response Action Status
Initial Actions: In 1985, the EPA pumped water out of the pond and added fly
ash to solidify the sludge. The mixture was removed down to the water table,
which was about 7 feet below the surface. The pond then was filled in with soil
from the site. A portion of sediment from an unnamed creek also was removed. In addition,
sludge was removed from a septic tank. Soils from an unlined lagoon used for disposing CCA-
related waste also were removed, backfilled, and regraded. In 1986, the EPA removed
creosote from a tank, solidified the creosote with fly ash, and stored these residues on site,
under a covered shed. In 1987, the EPA repaired pipes from the tanks, pumped liquids from
the pond into on-site tanks, and backfilled the pit. In 1988, the owner dug up the drainage
ditch, installed several new drainage ditches, and removed the dike.
Entire Site: In 1989, the EPA selected a remedy for the site that includes:
excavating the soil, washing the soil to reduce the volume of contaminated soils,
treating contaminated soils by bioremediation to remove the organics, solidifying
soils as necessary to contain inorganics, and then placing it back in the excavated area; and
extracting the groundwater for treatment. The technical specifications and design for the
selected cleanup were approved by the Agency in late 1991. Cleanup is scheduled to begin in
late 1992.
Environmental Progress
Initial actions, including pumping and treating contaminated pond water, removing
contaminated sediments from a creek, and repairing pipes and drainage ditches, have made
the Cape Fear Wood Preserving site safe until further cleanup activities are completed.
Site Repository
Cumberland County Public Library, 300 Maiden Lane, Fayetteville, NC 28301
March 1992 14 CAPE FEAR WOOD PRESERVING
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CAROLINA
TRANSFO
NORTH CAROL
EPA ID# NCD0031888
EPA REGION 4
Cumberland County
Near East Fayetteville
Site Description
The Carolina Transformer Co. site is on an approximately 5-acre parcel located in a rural
area near East Fayetteville. The site formerly was used as an electrical transformer recycling
facility. In response to citizen concerns in 1978, the EPA conducted sampling which revealed
contamination of the soil and a shallow residential drinking water well near the site, and trace
contamination in Carolina Transformer's deep industrial well. The house with the
contaminated shallow well was connected to the public water system in 1979. In 1989, the
North Carolina Environmental Services Division inspected the abandoned site and found 98
capacitors, 18 of which were ruptured and leaking onto the soil. The nearest residence is
located approximately 250 feet from the site. An estimated 3,000 people reside within a 3-
mile radius of the site. A food processing facility also is located next to the site.
Site Responsibility: The site is being addressed through
Federal actions.
NPL LISTING HISTORY
Proposed Date: 01/22/87
Final Date: 07/22/87
Threats and Contaminants
Private wells near the site were sampled and contained volatile organic compounds
(VOCs); polychlorinated biphenyls (PCBs)-carrier compounds from the former
transformer recycling operations were found in a shallow residential drinking water
well about 250 feet west of the site. Soil on the site and nearby surface waters are
contaminated with PCBs and PCB-carrier compounds (chlorobenzenes). Removing
contaminated soils and filling in the excavated areas with clean fill have reduced
potential risks on site, but exposure to off-site contaminated soils, sediments, and
surface waters still may exist. Potential risks exist to individuals who come in direct
contact with or accidentally ingest contaminated surface water, groundwater, soils,
or sediments; inhale contaminated dusts; or consume agricultural crops that
contain bioaccumulated contaminants.
Cleanup Approach
The site is being addressed in two stages: immediate actions and a long-term remedial phase
directed at cleanup of the entire site.
15
March 1992
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Response Action Status
Immediate Actions: In 1984, the EPA removed 975 tons of contaminated soil,
transported it to a federally approved facility, and then fenced the area.
Residences with contaminated groundwater were connected to the public water
supply. In early 1990, the EPA completed a removal of 98 leaking capacitors that had been
disposed of at the site after the 1984 removal activities were completed.
Entire Site: The EPA completed an investigation into the nature and extent of
contamination at the site in mid-1991. The final cleanup remedy includes solvent
extraction of the contaminated soil; extraction and treatment of groundwater;
demolition of the roof and walls of the building remaining on site; and disposal of residual
solid waste and debris. The design phase for the remedy is expected to begin in late 1992.
Site Facts: The EPA has sued Carolina Transformer Co. for cost recovery and treble
damages for not complying with an Administrative Order to clean up the site.
Environmental Progress
The removal of contaminated soils from the site, the provision of a safe drinking water
source, and the construction of a fence have reduced the potential for exposure to hazardous
materials at the Carolina Transformer Co. site while the technical design phase for the final
cleanup remedy is being planned.
Site Repository
Cumberland County Public Library, 300 Maiden Lane, Fayetteville, NC 28301
March 1992 16 CAROLINA TRANSFORMER CO.
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CELANESE
CORP. (S
OPERATIONS)
NORTH CAROLINA
EPA ID# NCD003446721
EPA REGION 4
Cleveland County
Shelby
Other Names:
Fiber Industries, Inc.
Shelby Fiber Operations
Site Description
The Celanese Corporation began operations in 1983 on 450 acres of this site near Shelby.
The plant, a polyester raw material production facility, consists of a manufacturing area, a
wastewater treatment area, a waste disposal area, and a recreational and tree farming area.
Operations at the site began in 1960 by Fibers Industries, Inc., a manufacturer of polyester
polymer chips and filament yarn. Chemical wastes were disposed of directly into a drainage
ditch during the early years of operation, prior to completion of the wastewater treatment
plant. Treated effluent has been discharged to Buffalo Creek since the mid-1960s, when the
treatment plant was completed. In addition, there are several areas that have been used for
waste storage and disposal, including a buried waste area and a drum landfill. Oils and
solvents were burned in a small open area during the 1960s. When the storage of waste
chemicals and solvents ceased in the mid-1970s, drums were removed and properly disposed
of, and the landfill was covered. Approximately 21 acres of open area were used for
landfarming of non-hazardous sludge during the late 1970s for a project authorized by the
State and monitored by North Carolina State University. Monitoring wells on the site are
contaminated with organic chemicals. Approximately 500 people live within a mile of the site.
The closest well is about 1,500 feet away, and 47 wells are within 1/4 mile of the site. Buffalo
Creek is 3,500 feet away and is the source of the plant's drinking water. Land within 1/2 mile
is used for forestry and agricultural activities.
Site Responsibility:
This site is being addressed through
Federal and potentially responsible
parties' actions.
NPL LISTING HISTORY
Proposed Date: 10/15/84
Final Date: 06/10/86
Threats and Contaminants
ZEJ
Groundwater, soils, and sediments are contaminated with volatile organic
compounds (VOCs) including benzene and trichloroethene, semi-volatiles including
ethylene glycol, and heavy metals including chromium and arsenic. Surface water is
contaminated with chromium and phthalates. If nearby residents drink
contaminated groundwater from private wells, they may be at risk. People who
trespass on the site and come into direct contact with or accidentally ingest
contaminated groundwater, surface water, soil, or sediments may be at risk.
17
March 1992
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Cleanup Approach
The site is being addressed in two long-term remedial phases focusing on cleanup of the
groundwater and controlling the source of contamination.
Response Action Status
Groundwater: In 1988, the EPA selected a remedy to clean up the groundwater
that includes pumping the groundwater, removing contaminants with an air
stripper, and treating the air before releasing it into the atmosphere. In addition,
the water is subjected to treatment by microorganisms. It also is being treated by forcing the
groundwater through tanks containing activated carbon, a specially treated material that
attracts the contaminants. This is followed by discharging the water to the on-site wastewater
treatment plant. If the effluent contains metals, it is treated further by adding chemicals that
will cause the metals to collect at the bottom of the treatment container. The selected
remedy is treating contaminated groundwater successfully and controlling off-site migration.
Cleanup activities began in 1988 and are still in progress.
Source Control: The remedy selected by the EPA in 1989 to clean up the source
of contamination includes excavating the contaminated soils, sludges, and stream
sediments and incinerating them on site; mixing the incinerator ash and sediments
with a hardening agent, such as lime or cement, to form a solid and disposing of it on site;
filling the excavated areas with clean soil; and monitoring the site for contamination.
Construction of the incinerators is completed, and excavation of the source waste began in
early 1991. Cleanup activities are expected to be completed in 1992.
Environmental Progress
The groundwater treatment system construction is completed, and groundwater is being
treated, thus controlling contaminant migration. Incineration and solidification of the source
waste is near completion at the Celanese Corp. (Shelby Fiber Operations) site.
Site Repository
Cleveland County Library System, 104 Howie Drive, Shelby, NC 28151
March 1992 18 CELANESE CORP. (SHELBY FIBER OPERATIONS)
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CHARLES MACON
LAGOON & D
STORAG
NORTH CA
EPA ID# NCD980840409
Site Description
EPA REGION 4
Richmond County
11/2 miles southwest of Cordova
Other Names:
icon Site 1 Mile South of Cordova
The Charles Macon Lagoon & Drum Storage site is an abandoned, 16-acre hazardous waste
storage facility. According to a 1980 inspection by the State of North Carolina, there were 11
lagoons on the site containing waste oil and sludges and 2,175 drums containing various
chemicals. Eight of these lagoons were unlined and overflowing. Operations at the site ceased
in 1981. In 1982, the State ordered the owner's estate to clean up the site. The estate
removed 300 drums and installed two on-site monitoring wells. In 1985, the EPA detected
chemicals in monitoring wells downgradient of the site. Approximately 1,100 people draw
drinking water from private wells within 3 miles of the site, most of which are upgradient.
There are four residences within 100 yards of the facility. The Pee Dee River is a mile away;
and two ponds, two streams, and a swamp are located between the river and the site.
Site Responsibility: This site is being addressed through
Federal and potentially responsible
parties' actions.
NPL LISTING HISTORY
Proposed Date: 01/22/87
Final Date: 07/22/87
Threats and Contaminants
7V
Groundwater downstream from the site is contaminated with trichloroethylene
(TCE) and heavy metals including barium and chromium. Sediments from the pond
are contaminated with toluene. Sludge is contaminated with heavy metals and
creosote. People who accidentally come in direct contact with or ingest
contaminated groundwater, sediments, sludge, or soil may be at risk.
19
March 1992
-------
Cleanup Approach
The site is being addressed in two stages: immediate actions and a long-term remedial phase
focusing on cleanup of the entire site.
Response Action Status
Immediate Actions: In 1983, the EPA removed all the remaining drums on the
site and excavated and filled in 10 lagoons. The remaining lagoon contains
solidified waste sludge, crushed empty drums, and contaminated soil and is
covered with 3 feet of clay.
Entire site: The parties potentially responsible for the contamination on the site
are studying the type and extent of the contamination. Once the study is
completed, expected in 1991, alternatives for site cleanup will be recommended.
The final cleanup remedy for the site was selected in late 1991. Cleanup will involve
innovative technologies for on-site cleanup and pumping and treatment for the groundwater.
Site Facts: In 1982, the State issued an order to the owner to clean up the site. In 1987, the
EPA filed an action against several parties potentially responsible for contamination at the
site.
Environmental Progress
Removing the 55-gallon drums and filling in 10 of the 11 lagoons reduced the potential for
exposure to hazardous materials at the Charles Macon Lagoon and Drum Storage site while
the EPA is selecting the technical design to use for the final cleanup.
Site Repository
Thomas H. Leath Memorial Library, 412 East Franklin Street, Rackingham, NC 28379
March 1992 20 CHARLES MACON LAGOON &
DRUM STORAGE
-------
CHEMTRONICS, INC.
NORTH CAROLINA
EPA ID# NCD095459
Site Description
EPA REGION 4
Buncombe County
Swannanoa Township
Other Names:
I Production, Inc.
Amcel Propulsion, Inc.
Disposal activities at the Chemtronics, Inc. site involve 10 acres of a 1,027-acre parcel of
land. The active industrial plant has had several owners/operators since it was first developed
in 1952. A variety of products were manufactured at the site, including explosives, rocket fuel,
and Pharmaceuticals. By-products of these manufacturing activities were deposited in 23 areas
on site and three areas off site. Two areas were particularly involved: one area consisted of
eight abandoned acid and organic waste pits; the other contained two lined basins used for
the neutralization and equalization of waste before it was discharged into local wastewater
facilities. Solid wastes and solvents were burned on site before 1971. From 1971 to 1975,
liquid waste was disposed of in on-site pits and trenches, while solid and explosive wastes were
burned. Acid and organic wastes also were disposed of in pits and trenches starting in 1975.
In 1979, the disposal pits were closed. Two monitoring wells near the pits were found to be
contaminated. There are several residences within several hundred feet of the off-site
disposal areas. The site is adjacent to Bee Tree Creek, and the Pisgah National Forest is to
the north of the site. One of the reported waste disposal areas, a municipal landfill, has been
proposed for development as a mobile home park.
Site Responsibility: This site is being addressed through
Federal and potentially responsible
parties' actions.
NPL LISTING HISTORY
Proposed Date: 12/01/82
Final Date: 09/01/83
Threats and Contaminants
Groundwater and soils are contaminated with volatile organic compounds (VOCs),
explosives such as TNT, heavy metals including chromium, and benzylic acid.
Surface water is contaminated with VOCs, explosives, and bromoform. People who
come in direct contact with or accidentally ingest contaminated groundwater,
surface water, or soil may be at risk.
21
March 1992
-------
Cleanup Approach
The site is being addressed in two stages: immediate actions and a long-term remedial phase
focusing on cleanup of the entire site.
Response Action Status
Immediate Actions: In 1985, the EPA removed two drums of hazardous
materials and disposed of them in a federally approved facility.
Entire Site: The remedy selected by the EPA to clean up the site includes:
covering the waste disposal areas with a cap, which includes a high-density
polyethylene membrane, clean soil, and planting vegetation; installing a gas
collection and ventilation system, if necessary; pumping and treating groundwater by using air
stripping, carbon adsorption, or bioremediation and sedimentation; sampling of the pond
water and sediments, and, if necessary, cleanup; and sediment, groundwater, and surface
water monitoring. Treated groundwater will be discharged to a local treatment facility. The
parties potentially responsible for the site contamination prepared the technical specifications
for cleaning up the site which were approved by the EPA in 1991. A number of extraction
wells were installed in 1990, and the construction of a groundwater treatment system will
begin in 1992. Currently more extraction wells, piezometers, and additional monitoring wells
are being installed. The disposal areas are being prepared for capping. All drilling should be
completed by early 1992. Heavy earth moving operations (capping of the disposal areas)
began in early 1992 and are expected to be completed by mid-1992. All cleanup construction
activities are expected to be completed by late 1992.
Site Facts: The EPA and two of the potentially responsible parties signed an Administrative
Order on Consent on September 30, 1985 to perform a study of the nature and extent of
contamination on the site. The EPA issued an order on March 22, 1989 to all three of the
potentially responsible parties (Celanese, Chemtronics, and Northrop) to conduct the
engineering design and actual cleanup for the site. Each potentially responsible party is in
compliance with the Administrative Order.
Environmental Progress
By removing the drums of hazardous materials, the EPA eliminated any immediate threats
posed by the Chemtronics, Inc. site while cleanup activities begin.
Site Repository
Martha Ellison Library, Warren Wilson College, 701 Warren Wilson Road, Swannanoa, NC
28778
March 1992 22 CHEMTRONICS, INC.
-------
PCX, INC.
(STATES
PLANT)
NORTH CAROLINA
EPA ID# NCD095458527
EPA REGION 4
Iredell County
Statesville
Site Description
From 1940 through 1985, PCX, Inc. (Statesville Plant) repackaged and distributed agricultural
chemicals at this 5-acre site. Liquid and powdered pesticides were repackaged at the site until
1969. Reportedly, between 5,000 and 10,000 pounds of pesticides were buried under a
concrete warehouse floor some time before 1969. Also, spills occurred in areas where
pesticides were handled. Soil and groundwater collected at the site in 1986 are contaminated.
The company filed for bankruptcy in September of 1985 and began liquidating its assets.
Private and public wells within 3 miles of the site provide drinking water to an estimated
12,000 people. The site is bordered on its northern and western sides by Burlington Textile
Mill and Carnation Milk Company.
Site Responsibility: This site is being addressed through
Federal actions.
NPL LISTING HISTORY
Proposed Date: 06/24/88
Final Date: 02/16/90
Threats and Contaminants
The soil is contaminated with pesticides such as chlordane and DDT, as well as
with coal tar distillates and halogenated organic solvents. The groundwater
contains pesticides including lindane, chlordane and DDT, and halogenated organic
solvents. Human health would be threatened through direct contact with
contaminants or if contaminated groundwater were to enter private wells. A
private well upgradient of the site contains volatile organic compounds (VOCs)
including tetrachloroethylene.
23
March 1992
-------
Cleanup Approach
The site is being addressed in two stages: immediate actions and a long-term remedial phase
focusing on cleanup of the entire site.
Response Action Status
Immediate Actions: In 1989, the EPA installed four new monitoring wells
onsite and fenced the site. Results of sampling showed groundwater
contamination. Soil sampling outside the warehouse detected low levels of
pesticides, but suspected buried pesticides were not found.
Entire Site: The EPA has begun a study of the nature and extent of groundwater
and soil contamination remaining at the site and the alternative technologies
available for cleanup. Field work for these studies is expected to be completed in
1992, with cleanup actions scheduled to start in 1993.
Environmental Progress
Initial assessments indicate that the site does not pose an immediate hazard to human health
or the environment while investigations are underway and cleanup alternatives for the site are
being selected.
Site Repository
Not established.
March 1992 24 PCX, INC. (STATESVILLE PLANT)
-------
PCX, INC.
(WASHIN
PLANT)
NORTH CAROLINA
EPA ID# NCD981475932
PA REGION 4
Beaufort County
Washington
Other Names:
Washington Plant
Site Description
PCX, Inc. (Washington Plant) began repackaging and selling agricultural chemicals in 1945
on this 6-acre site. During these operations, a large trench was filled with pesticide wastes
and other agricultural chemicals in the early 1910s. The company filed for bankruptcy and
began liquidating its assets in 1985. The chemicals from the trench may move into shallow
groundwater connected to the underlying aquifer. This deeper aquifer is the major source of
drinking water in the area. Approximately 2,850 people draw drinking water from wells within
3 miles of the site. The area is mainly agricultural. The site is bordered by a railroad and a
wetland.
Site Responsibility:
This site is being addressed through
Federal and potentially responsible
parties' actions.
NPL LISTING HISTORY
Proposed Date: 06/24/88
Final Date: 03/31/89
Threats and Contaminants
The soil of the disposal trench contains pesticides, such as DDT and chlordane, as
well as mercury. Direct contact with the contaminated soil is a potential threat to
public health, but is unlikely since the area is fenced. If contamination spreads
from soils into the deeper aquifer, individuals may ingest contaminants in drinking
water.
Cleanup Approach
This site is being addressed in two stages: initial actions and a long-term remedial phase
focusing on cleanup of the entire site.
25
March 1992
-------
Response Action Status
Initial Actions: In 1988, the EPA began to excavate the contaminated soil and
analyze it on site. The site also was fenced. The EPA stored and covered all
contaminated soil on site and then backfilled the excavated area with clean soil.
In early 1992, an additional 2,000 yards of contaminated soil were excavated.
Entire Site: PCX, Inc. is conducting a study into the extent and nature of
contamination at the trench and main warehouse and the alternative technologies
for cleanup. The study began in 1990 and is scheduled to end in 1993.
Site Facts: The EPA filed an Administrative Order to compel PCX, Inc. and Fred Webb,
Inc. to remove pesticides from the trench area.
Environmental Progress
The initial actions, including excavating and storing contaminated soil and fencing the site,
have made the PCX, Inc. (Washington Plant) site safer while investigations leading to
cleanup activities are taking place.
Site Repository
Not established.
March 1992
26
PCX, INC. (WASHINGTON PLANT)
-------
GEIGY CHEM
CORPORA!
(ABERDEEN
NORTH CAROLINA
EPA ID# NCD981927502
PA REGION 4
Moore County
Aberdeen
Site Description
The Geigy Chemical Corporation (Aberdeen Plant) site covers 1 acre and has been occupied
by various chemical companies since 1947. From 1949 to 1955, Geigy produced solid and
liquid pesticides on the site. The facility includes four aboveground storage tanks, an office
building, and two warehouses. In 1985, the State detected pesticides in private and municipal
wells. In 1987, the EPA detected pesticides in the surface and subsurface soils on the site.
The aboveground storage tanks were removed in 1989, and two warehouses were removed in
1991. The Aberdeen Public Water Supply System and numerous private wells within 3 miles
of the site serve approximately 7,400 people. The Sandhill Aquifer underneath the site
supplies all the drinking water for Moore County. Drainage from the site collects in several
unnamed tributaries of Aberdeen Creek. The creek is used for recreational activities.
Site Responsibility: The site is being addressed through a
combination of Federal and
potentially responsible parties' action.
NPL LISTING HISTORY
Proposed Date: 06/24/88
Final Date: 10/04/89
Threats and Contaminants
ZGJ
The groundwater is contaminated with lindane and toxaphene. The soil is
contaminated with pesticides including toxaphene, DDT, and lindane. Trespassers
on this site who come in direct contact with or accidentally ingest contaminated
groundwater and soil may be at risk. Individuals frequenting Aberdeen may be
exposed to contaminants through direct contact with surface water.
27
March 1992
-------
Cleanup Approach
This site is being addressed in two stages: initial actions and a long-term remedial phase
focusing on cleanup of the entire site.
Response Action Status
Initial Actions: In 1989, the parties potentially responsible for the site
contamination removed approximately 460 tons of pesticide-contaminated soil and
debris to an approved facility. A second action was conducted in 1991, involving
the removal of 227 tons of pesticide-contaminated soil to an approved facility for disposal. Six
30-gallon drums containing concentrated surface debris were sent to an approved incinerator
facility for thermal treatment. The site also has been fenced.
Entire Site: The potentially responsible parties are studying the type and extent
of contamination at the site. Various alternatives for the cleanup will be
recommended once the study is completed in 1992. After the EPA selects the most
appropriate remedies, design and construction of the final site cleanup will begin.
Site Facts: In 1988, the EPA and Ciba-Geigy Corp., Olin Corp., and Kaiser Aluminum and
Chemical Corp. signed an Administrative Order. This agreement specified how these parties
would conduct the study into the type and extent of contamination at the site.
Environmental Progress
The initial actions to remove contaminated soils and debris, in addition to fencing the site,
have reduced the potential for exposure to hazardous materials at the Geigy Chemical
Corporation site while investigations and cleanup activities are taking place.
Site Repository
Aberdeen Town Hall, 115 North Poplar Street, Aberdeen, NC 28315
March 1992 28 GEIGY CHEMICAL CORPORATION
(ABERDEEN PLANT)
-------
FM ROCK
A REGION 4
erson
CO./SHEPHE
NORTH CAROLINA
EPA ID# NCD079044426
Site Description
The General Electric Co./Shepherd Farm site consists of the 50-acre General Electric
property and a 3-acre dry pond or ravine known as Shepherd Farm, located 2,500 feet
southwest of the General Electric plant. Since 1955, the Lighting System Division of General
Electric has manufactured various types of luminaire systems at the site. Wastes resulting
from these production processes were disposed of at Shepherd Farm from 1957 to 1970. The
disposal process involved burning the wastes and then bulldozing them into the ground.
Wastes were also disposed of at the Seldon Clark property, located across the street from
General Electric; other nearby areas may have received wastes from General Electric. The
EPA, the State, and General Electric conducted studies between 1976 and 1989 which
identified site contaminants and pathways of contaminant migration. Site contaminants were
later discovered in 19 off-site private wells. This migration of contaminants is believed to have
resulted from the rupture of a drainline that carried wastewater from the manufacturing plant
to the treatment ponds. Residences that used these wells were connected to the municipal
water supply. Other wells within 4 miles of the site once supplied drinking water to an
estimated 4,400 people; the nearest of these wells is within a mile of the site. A trailer park is
now located on a portion of the old dump.
Site Responsibility: This site is being addressed through
Federal, State, and the potentially
responsible parties' actions.
Threats and Contaminants
On-site and off-site groundwater and sediments are contaminated with various
heavy metals and volatile organic compounds (VOCs). On-site wastewater
treatment ponds and sludge impoundments are contaminated with polychlorinated
biphenyls (PCBs) and heavy metals, including chromium, copper, lead, nickel and
zinc. PCBs also were detected in the soil of the trailer park.
29 March 1992
-------
Cleanup Approach
This site is being addressed in two phases: immediate actions and one long-term remedial
phase focusing on cleanup of the entire site.
Response Action Status
Immediate Actions: Residences using contaminated water from 19 private wells
were connected to the municipal water supply.
Entire Site: General Electric, under EPA supervision, will undertake a study of
the nature and extent of site contamination. This study, scheduled to begin in
early 1993, will help determine the best alternatives for cleanup at the site.
Site Facts: Interim Status under Subtitle C of the Resource Conservation and Recovery Act
(RCRA) was granted to the General Electric plant in 1980, when they filed a RCRA Part A
permit application. In 1984, General Electric became a RCRA hazardous waste generator.
Because of this change, this site now qualifies for listing on the NPL, as stated in the EPA's
NPIVRCRA policy.
Environmental Progress
Municipal water has been provided to residents. Initial site investigations indicate that the
General Electric Co./Shepherd Farm site poses no immediate threat to the health and safety
of the nearby population while additional investigations are underway and activities are being
planned for permanent cleanup of the site.
Site Repository
Not established.
March 1992
30
GENERAL ELECTRIC CO./SHEPHERD FARM
-------
HEVI-DUTY
COMPA
NORTH CAROL
EPA ID# NCD039102951
EPA REGION 4
Wayne County
2 miles south of Goldsboro
Site Description
Beginning in 1968, Hevi-Duty Electric Company manufactured dry and liquid power
transformers on a portion of a 125-acre parcel of land. In 1979,1,000 gallons of transformer
oil containing polychlorinated biphenyls (PCBs) were spilled from an underground storage
tank. The company removed the soil from the spill area and buried it in an unlined pit on the
northern end of the property. In 1976, PCB-contaminated soil from an underground storage
tank area was removed and buried in a plastic-lined pit, under supervision of the State. In
1986, a spill from a cracked pipeline on a tanker truck resulted in 1,400 gallons of oil running
into culverts and an open drainage ditch. The majority of the oil was recovered. Another spill
of 1,500 gallons occurred when an underground oil line cracked. The State conducted tests in
1986 and found contaminants in the groundwater. Approximately 7,600 people obtain
drinking water from public wells within 3 miles of the site; the nearest well is 2,000 feet away.
Approximately 15,000 people live within 4 miles of the site. The site drains into the Neuse
River, which is nearly 4,700 feet from the plant. This river is used for recreational fishing.
Site Responsibility:
This site is being addressed through
Federal and potentially responsible
parties' actions.
NPL LISTING HISTORY
Proposed Date: 05/05/89
Final Date: 08/30/90
Threats and Contaminants
[HA]
The air, groundwater, soil, and surface water are contaminated with PCBs. People
who come in direct contact with or accidentally ingest contaminated groundwater
or soils may be at risk. Contaminated air on the site may pose a health threat to
those who breathe it. Because the site drains into the Neuse River, people who eat
fish from it may suffer adverse health effects.
31
March 1992
-------
Cleanup Approach
This site is being addressed in two stages: initial actions and a long-term remedial phase
focusing on cleanup of the entire site.
Response Action Status
Initial Actions: In 1976, contaminated soil was removed from an underground
storage tank area. In 1986, Hevi-Duty cleaned up an oil spill by pumping
groundwater to flush oil out of the ground.
Entire Site: Hevi-Duty is studying the environmental condition of the site. After
this study is completed, the EPA will select the most effective remedies, and
cleanup activities will begin soon thereafter.
Site Facts: In 1985, the EPA and Hevi-Duty signed a Consent Agreement, under which the
company paid a civil penalty for a PCB spill from an underground storage tank.
Environmental Progress
After proposing this site to the NPL> the EPA performed preliminary investigations and
determined that no additional immediate actions were needed at the Hevi-Duty Electric
Company site while further studies are being conducted.
Site Repository
Not established.
March 1992 32 HEVI-DUTY ELECTRIC COMPANY
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JADCO-HU
FACILITY
NORTH CAROLINA
EPA ID# NCD980729602
EPA REGION 4
Gaston County
Belmont
15 miles west of
Charlotte, NC
Site Description
From 1971 to 1975, C.A. Hughes operated a solvent reclamation and storage facility at this 6-
acre site in Belmont. Workers reprocessed chemical waste from industries to recover
whatever could be resold, storing the residues on the site. In 1975, Jadco, another firm,
leased the site, equipment, and operation. A large quantity of drums had accumulated by
1975, when operations ceased. The drums, in various stages of decay, were stacked at several
locations. The site also held several large storage tanks. By 1978, up to 18,000 drums were
removed. Contaminated soil and debris were placed in an unlined landfill on site, and the site
was regraded. In 1983, bulk storage tanks and other drums were removed; however, spillage
and leakage resulted in contamination of the soil predominantly with organic solvents and
partially with heavy metals. In 1984, an estimated 4,700 people used wells within 3 miles of
the site as a source of drinking water. Roughly 40 to 50 residences lie within a 1,000-foot
radius of the site, with the closest being 50 feet away. All homes have access to a public
water supply, although some residents may still be using water from private wells. Migration
of contaminants into groundwater is likely, because the landfill is unlined and only 6 feet
above the water table. A ditch that drains the site flows into the Catawba River, and
Belmont's drinking water intake is 2 1/2 miles downstream from the confluence of the river
and ditch. Trace amounts of site-related contaminants have been detected in a private well
that is no longer in use.
Site Responsibility:
This site is being addressed through
Federal and potentially responsible
parties' actions.
NPL LISTING HISTORY
Proposed Date: 10/01/84
Final Date: 06/01/86
33
March 1992
-------
Threats and Contaminants
II
On-site sediments contain heavy metals including chromium, lead, and nickel.
Polychlorinated biphenyls (PCBs) in contaminated sediments and soils were
cleaned up in one area of the site, but remain a concern site-wide. PCBs and
nickel have been found in sediments off site. The soil contains heavy metals and
volatile organic compounds (VOCs) including methylene chloride and toluene. On-
and off-site surface water has been shown to be contaminated with metals such as
barium and dichloroethane. Groundwater is contaminated with VOCs and heavy
metals including lead, nickel, barium, and beryllium. People may be harmed by
direct contact with contaminated surface water and sediment or by drinking
contaminated water. Migration of contaminants to the groundwater is a priority
concern.
Cleanup Approach
The site is being addressed in a two stages: initial actions and a long-term remedial phase
focusing on cleanup of the entire site.
Response Action Status
Initial Actions: In 1990, PCB-contaminated soils and sediments were removed
from the southeastern swale area of the site.
Entire Site: Under the EPA's monitoring, the parties potentially responsible for
contamination at the site began a study of its pollution problems in 1986. This
investigation was completed in 1990. The EPA selected a remedy which includes
treatment of soils using soil vacuum extraction and soil flushing techniques. Groundwater will
be pumped and treated and disposed of either in a local wastewater treatment plant or in a
tributary, in accordance with national discharge permits. Surface water is being re-routed and
culvert is being repaired to eliminate surface water contamination. Design of the cleanup
remedies is underway and is scheduled for completion in 1993.
Site Facts: The North Carolina Department of Justice issued a complaint requiring Jadco-
Hughes to remove waste from the site some time in or after 1975. The potentially responsible
parties conducted a study to determine the type and extent of contamination under a
Consent Order.
Environmental Progress
Excavation and disposal of the PCB-contaminated soil and sediments reduced the potential of
direct contact while engineering designs for the cleanup of the site are being planned.
March 199234 JADCO-HUGHES FACILITY
-------
Site Repository
Gaston County Public Library, Belmont Public Library Branch, 111 Central Avenue,
Belmont, NC 28012
JADCO-HUGHES FACILITY
35
March 1992
-------
JFD ELECT
CHANNEL
NORTH CAROLINA
EPA ID# NCD122263825
EPA REGION 4
Granville County
Oxford
Site Description
From 1962 to 1979, JFD Electronics manufactured television antennas at this 13-acre site on
Industrial Drive in Oxford. The owners built a 1/2-acre lagoon in 1964 to 1965 to dispose of
sludge generated by wastewater treatment. A chromate conversion process and copper/nickel
electroplating generated most of this wastewater. When Channel Master bought the property
in 1980, the company filled half the lagoon and used it as a truck parking lot. A local
department store rents a building on the property as a warehouse. Channel Master believes
that approximately 25 percent of the site is contaminated. The problem appears to be
associated with leaking underground tanks of waste oil used by the former owner and with an
area where trucks carrying waste oil had been rinsed. Approximately 2,500 people get their
drinking water from private wells within 3 miles of the site; the closest is about 2,000 feet to
the southeast. The site also drains to an unnamed tributary of Fishing Creek, which is used
for recreational fishing.
Site Responsibility: This site is being addressed through
Federal and potentially responsible
parties' actions.
NPL LISTING HISTORY
Proposed Date: 06/24/88
Final Date: 10/04/89
Threats and Contaminants
ZDJ
Volatile organic compounds (VOCs) were detected in both on- and off-site shallow
and deep monitoring wells. The current owner contracted for several studies of the
site, and chromium, lead, and other heavy metals were found in the sludge and
soils but were removed in 1988. VOCs are contaminating the surface water,
sediments, and groundwater. People could be at risk if they accidentally ingest or
come in direct contact with the contaminated groundwater, soil, and sludges.
36
March 1992
-------
Cleanup Approach
The site is being addressed in two stages: immediate actions and a long-term remedial phase
focusing on cleanup of the entire site.
Response Action Status
Immediate Actions: Channel Master has contracted for several studies of the
site. One study developed a plan for cleaning up the lagoon and contaminated
soil. Cleanup work was started in 1987 and completed in 1988.
Entire Site: In 1989, the EPA began an intensive study of groundwater
contamination at the site, exploring the nature and extent of its pollution
problems. This investigation, which also will recommend the best strategies for
final cleanup, is scheduled for completion in 1992.
Environmental Progress
The cleanup of the lagoon and contaminated soil has reduced the threat of continued
contamination of the groundwater. After adding the JFD Electronics site to the NPL, the
EPA performed preliminary evaluations of the site conditions and determined that the site
does not currently pose an immediate threat to the surrounding community or the
environment while cleanup activities continue and further studies into the final groundwater
remedy are taking place.
Site Repository
Granville County Library System, Richard H. Thorton Library, Main and Spring Streets,
Oxford, NC 27565
JFD ELECTRONICS/ CHANNEL MASTER
37
March 1992
-------
KOPPERS
COMPAN
(MORRISVILL
PLANT)
NORTH CAROLINA
EPA ID# NCD003200383
PA REGION 4
Wake County
1 mile northwest of
Morrisville
Site Description
The Koppers Company, Inc. (Morrisville Plant) site covers 52 acres and was used as a saw
mill until 1959 when it was sold to Unit Structures, Inc., which produced glue-laminated wood
products. Koppers Company purchased the site in 1962 and continued the glue-laminated
process. From 1968 to 1975, Koppers treated wood with pentachlorophenol (PCP) at the site.
Wastewater from the PCP process was discharged to an on-site pond for the first 6 months of
operation and then to two unlined lagoons nearby. The owners closed the lagoons in 1977
and sprayed the liquids that remained in them over a field on the northeastern corner of the
property. They mixed the sludge with soil and spread it over the lagoon area. In 1982, the
owners found PCP in on-site soil, wells, pond water, and sediment. Koppers sold the plant to
an unrelated company that retained the name Unit Structures, Inc. Koppers, however, kept
10 acres of the original site where PCP was used. Unit Structures, Inc. still is an active
facility. Groundwater within 3 miles of the site is a source of drinking water for 2,200 people.
The North Carolina Solid and Hazardous Waste Branch detected trace contaminants in some
off-site wells. Koppers installed over 3 miles of public water lines to residences where PCP or
isopropyl ether was detected in the drinking water. Water from the northeastern corner of
the site drains toward Crabtree Creek, 2 miles away. Water from the southeastern corner
drains to Koppers Pond, which was used for fire protection. Occasional overflow from
Koppers Pond reaches Medlin's Pond, which is used for fishing and irrigating garden crops.
Site Responsibility: This site is being addressed through
Federal and potentially responsible
parties' actions.
NPL LISTING HISTORY
Proposed Date: 06/24/88
Final Date: 03/31/89
38
March 1992
-------
Threats and Contaminants
The owner found soil, groundwater, surface water, and sediments contaminated
with PCP in the early 1980s. Dioxins and furans also are found on site. The site is
unfenced, making it possible for people and animals to come into direct contact
with contaminated soils or water. Possible health threats include coming into direct
contact with or accidentally ingesting any of these contaminated materials.
Cleanup Approach
This site is being addressed in two stages: emergency actions and a long-term remedial phase
focusing on cleanup of the entire site.
Response Action Status
Emergency Actions: In 1980 and 1986, Koppers removed soil contaminated
with PCP from the lagoon area and transported it to an EPA-approved hazardous
waste facility, although contaminated soil remained on the site. In 1989, under
EPA monitoring, more than 3 miles of public water supply lines were extended by Koppers to
affected homes near the site.
Entire Site: In 1989, under EPA monitoring, the parties potentially responsible
for site contamination began a thorough study of the type and extent of soil and
water pollution at the site. Additional fieldwork was conducted to define the
extent of dioxins in soils, and to confirm earlier groundwater results. Reports will be finalized
in mid-1992. The proposed remedy for groundwater is pumping and treatment, however, soil
cleanup methods are still under investigation.
Site Facts: An Administrative Order was issued to the potentially responsible party to install
a water line. A second Administrative Order was issued to conduct site investigations.
Environmental Progress
The emergency removal of soil and provision of an alternate water supply have reduced the
potential for exposure to contaminants at the site or through the drinking water supply while
investigations and cleanup activities are taking place.
KOPPERS COMPANY, INC. (MORRISVILLE PLANT) 39 March 1992
-------
Site Repository
Wake County Dept. of the Public Library, Gary Public Library Branch, 310 South Academy
St., Gary, NC 27511
March 1992
40
KOPPERS COMPANY, INC.
(MORRISVILLE PLANT)
-------
MARTIN-MA
SODYECO
NORTH CAROLINA
EPAID# NCD001810365
EPA REGION 4
Mecklenburg County
'10 miles west of Charlotte
Site Description
Chemical dyes have been made since 1936 on the 1,300-acre Martin-Marietta site. Opened by
Sodyeco, the plant was taken over by American Martin-Marietta in 1958 and sold to Sandoz
Chemicals Company in 1983. The plant has manufactured liquid sulfur and vat and disperse
dyes, as well as other chemicals from various industries. The first indication of potential
contamination at the site was the discovery in 1980 of organic solvents in the company's
drinking water well and nearby private wells. On-site disposal of distillation tars and dye
clarification cake resulted in extensive groundwater and soil pollution. Analysts traced the
source of contamination to three trenches of buried wastes. The company excavated the
wastes and disposed of them off site. It was later realized that five areas on the site are
probable sources of soil and groundwater contamination. Area A operated as a landfill
between the 1930s and 1974. It accepted sulfur residues and dyes, fiber clothes, empty metal
and cardboard drums and cartons, non-acidic and non-flammable chemicals, chemical wastes,
and construction debris. This area currently is covered with asphalt and buildings. Area B
operated as a landfill from 1973 to 1978 and received wastes previously sent to Area A. Area
B was being used as a parking lot covered with gravel. Area C, now a grassy area, once
contained the remains of laboratory and production samples, distillation tars, and waste
solvents. These are the trenches cleaned up in the early 1980s, but available analytical
techniques allowed some soil contamination to go undetected. Area D contained two
wastewater settling ponds that have been taken out of service. This area currently holds a
lined freshwater pond and a fuel oil storage tank. Area E is a drainage basin receiving
discharge from the old plant manufacturing area. No wastes are known to have been
deposited there. Approximately 4,500 people in Mount Holly live directly across the river
from the site, and the City of Belmont, with 4,600 people, is 3 1/2 miles downriver. Belmont's
public water intake is downstream of the site. The residents of Mount Holly and Belmont
depend upon local groundwater for drinking water.
Site Responsibility: This site is being addressed through
Federal and potentially responsible
parties' actions.
NPL LISTING HISTORY
Proposed Date: 12/01/82
Final Date: 09/01/83
41
March 1992
-------
Threats and Contaminants
On-site groundwater and soil are polluted with volatile organic compounds
(VOCs). Groundwater contamination is worst at Areas C, D, and E. Soil
contamination is highest in Areas C and D; the soil at Area E is uncontaminated.
Area residents are not at risk of being exposed to site contamination, as a result of
early excavation of dangerous wastes. However, the public drinking water supply
may become polluted as groundwater contamination migration occurs.
Groundwater discharges into the Catawba River, which is a source of drinking
water for the plant and area residents.
Cleanup Approach
This site is being addressed in two stages: initial actions and a long-term remedial phase
focusing on cleanup of the entire site.
Response Action Status
Initial Actions: Contaminated wastes and secondary soils were excavated and
removed from the site.
Entire Site: The EPA selected a remedy for this site in 1987, which includes:
(1) extracting contaminated groundwater and treating it on site; (2) discharging
treated groundwater to an off-site stream; (3) continuing cleanup until
contaminated water meets cleanliness goals; (4) capping Area B (the truck staging area) with
asphalt to keep rainfall and runoff from spreading contaminants; and (5) treating
contaminated soil in Area C (trench area) on site to remove organic contaminants. Cleanup
actions began in 1989 and are being performed by the potentially responsible parties, under
EPA monitoring. The asphalt cap has been completed in Area B. Extraction wells have been
installed and are operating. The groundwater pump and treatment process has been expanded
and may require operation until 1999. The cleanup of Areas C and D has begun. The
evaluation of results will be available for the EPA's review in early 1992.
Environmental Progress
The cleanup actions undertaken so far, including groundwater treatment, removal of highly
contaminated wastes and secondary soils, and capping of contaminated areas have reduced
the potential for exposure to hazardous substances at the Martin-Marietta Sodyeco site while
final cleanup actions are underway.
March 1992 42 MARTIN-MARIETTA, SODYECO, INC.
-------
Site Repository
Mt. Holly Public Library, 245 West Catawba Avenue, Mt. Holly, NC 28120
MARTIN-MARIETTA, SODYECO, INC.
43
March 1992
-------
NATIONAL
& CHEM
CORP.
NORTH CAROLINA
EPA ID# NCD991278953
A REGION 4
Rowan County
es south of Salisbury
Other Names:
roctor Chemical Co. Inc.
Site Description
The National Starch & Chemical Corporation (NSCC) site is located on a 500-acre parcel
occupied by the NSCC-owned Cedar Springs Road Plant that currently manufactures textile
finishing and specialty chemicals. From 1971 to 1978, NSCC disposed of approximately
350,000 gallons of reaction vessel wash waters in trenches constructed on a 5-acre tract of
land located behind the plant. Trenches in this area also received liquid waste from the plant,
and it was absorbed into the ground. After the absorption rate substantially declined, the
trenches were backfilled and seeded. Site monitoring in 1976 and 1977 revealed shallow
groundwater contamination adjacent to or within the trench area. Consequently, the North
Carolina Department of Natural and Economic Resources requested that NSCC stop on-site
waste disposal activities. Since 1978, production plant process waters have been pre-treated in
a facility near the production area and discharged to the Salisbury publicly owned treatment
works (POTW). The main area of contamination identified at the site is the trench area;
however, low levels of surface water contamination are currently under investigation. The
plant is located in a rural area that depends heavily on wells for drinking water.
Approximately 7,700 people use public and private wells within 3 miles of the site for drinking
water and other domestic purposes. Since the site and the surrounding areas lie above a
bedrock aquifer, residents drinking water from this source could become affected by site-
related contaminants; however, no off-site contamination of groundwater has been detected.
Site Responsibility: This site is being addressed through
Federal and potentially responsible
parties' actions.
NPL LISTING HISTORY
Proposed Date: 04/01/85
Final Date: 10/04/89
44
March 1992
-------
Threats and Contaminants
The groundwater, surface water, and sediments are contaminated with heavy
metals and volatile organic compounds (VOCs). Soil contaminated with VOCs
and lead has been cleaned up, making the site safer, but residual contamination
still remains in subsurface soils. The soil is contaminated with VOCs and lead.
People who come in direct contact with or accidentally ingest the contaminated
groundwater may be exposed to a potential health threat. Recreational uses of
Grants Creek or its tributaries also may cause a health threat due to possible
contamination of the water. The northeastern tributary shows very low levels of
contaminants at the site; however, these contaminants are removed prior to
leaving the site property.
Cleanup Approach
The site is being addressed in three long-term remedial phases focusing on groundwater, soil,
and surface water cleanup.
Response Action Status
Groundwater: Design technologies were completed by the party potentially
responsible for the site contamination, and cleanup action began in 1990. The
actions selected by the EPA for the cleanup of groundwater include: installation of
a groundwater interception and extraction system, a pre-treatment system, and final discharge
to the Salisbury POTW. In order to discharge the groundwater, effluent criteria defined in
the Salisbury National Pollutant Discharge Elimination System (NPDES) permit must be met.
Modifications were made to the pretreatment design to meet the POTW pretreatment
standards. Extraction wells have been installed, and off-site monitoring wells are to be
installed soon. Groundwater pumping and treatment continue over the long term.
Soil Contamination: The potentially responsible party conducted a study of the
type and extent of on-site soil contamination and evaluated alternative cleanup
actions. In 1990, a remedy was selected, which entails natural soil flushing, soil
monitoring, and deed restrictions on the site. The engineering design of the selected remedy
is currently being finalized.
Surface Water Contamination: Additional fieldwork will be conducted to
determine the nature and extent of surface water contamination and to explore
the best strategies for final cleanup. The study is expected to be completed in
mid-1993.
Site Facts: The State ordered a stop to on-site disposal activities after sampling in 1976 and
1977 showed shallow groundwater contamination.
NATIONAL STARCH & CHEMICAL CORP. 45 March 1992
-------
Environmental Progress
After adding the National Starch & Chemical Corp. site to the NPL, the EPA determined
that the site does not pose an imminent threat to the surrounding community or the
environment while the cleanup of groundwater and soil is taking place.
Site Repository
Rowan Public Library, 201 West Fisher Street, Salisbury, NC 28144
March 1992
46
NATIONAL STARCH & CHEMICAL CORP.
-------
NEW HANOV
COUNTY
BURN PIT
NORTH CAROLINA
EPA ID# NCD981021157
EPA REGION 4
New Hanover County
Wilmington
Site Description
The New Hanover County Airport Burn Pit was constructed by the County in 1968. From
1968 to 1979, the Cape Fear Technical Institute used the pit for fire-training purposes,
burning jet fuel and gasoline in the burn pit, and extinguishing the fires with water. The
Wilmington Fire Department used the burn pit for fire-training purposes from 1968 to 1976.
Jet fuel and drainage from petroleum fuel storage tanks in the area were burned, and the
fires were extinguished with water, carbon dioxide, and dry chemicals. Some time prior to
1982, materials used in river spill cleanups were dumped into the pit. In addition, fuel oil,
kerosene, and oil from oil spill cleanups were burned in the pit. The pit held approximately
22,500 gallons, of which 85 percent is water. In 1986, the North Carolina Division of Health
Services discovered heavy metals in the soil around the pit and numerous organics in other
soil samples. Surface water within 3 miles downstream of the site is used for recreational
activities, and there is an estuary wetland approximately 1 mile from the site at the probable
point of runoff from the site. Approximately 6,300 people obtain drinking water from public
and private wells within 3 miles of the site. A private well is approximately 1,500 feet to the
northwest of the site.
Site Responsibility:
This site is being addressed through
Federal actions.
NPL LISTING HISTORY
Proposed Date: 06/24/88
Final Date: 03/31/89
Threats and Contaminants
EDJ
The soil is contaminated with heavy metals, volatile organic compounds (VOCs),
and petrochemicals. Sludges are contaminated with barium. There is a possible
health threat from direct contact with the soil. Direct contact with contaminated
water in a nearby creek may be a health threat as well. Based on preliminary
investigations, groundwater contamination remains on site. An estuary wetland is
located approximately 1 mile from the site.
47
March 1992
-------
Cleanup Approach
The site is being addressed in two stages: initial actions and a long-term remedial phase
focusing on cleanup of the entire site.
Response Action Status
Initial Actions: In 1990, the potentially responsible parties, under EPA
supervision, removed approximately 2,000 cubic yards of sludge and soils, piping,
tanks, and training structures from the site.
Entire Site: An investigation of the nature and extent of site contamination and a
study of alternatives for cleaning up the site contaminants were started in 1990.
The investigation is scheduled for completion in 1992, with a decision on a cleanup
plan expected shortly thereafter.
Site Facts: A Consent Order for removal of the contaminants by the potentially responsible
parties was signed in June 1990.
Environmental Progress
Removal of sludge, soils, and debris from the New Hanover County Airport Burn Pit site has
reduced the threat of exposure to contaminants while investigations leading to final cleanup
activities are taking place.
Site Repository
New Hanover County Public Library, 201 Chestnut Street, Wilmington, NC 28401
March 1992
48
NEW HANOVER COUNTY
AIRPORT BURN PIT
-------
N.C. STATE
UNIVERSI
(LOT 86,
FARM UNIT #
NORTH CAROLINA
EPA ID# NCD980557656
EPA REGION 4
Wake County
Raleigh
Site Description
The 1 1/2-acre North Carolina State University site is situated to the north of Carter-Finley
Stadium in Raleigh. The site was used by the North Carolina State University science
laboratories and agricultural research facilities as a waste disposal area. From 1969 to 1980,
the University disposed of solvents, pesticides, heavy metals, acids, and some low-level
radioactive laboratory wastes. The wastes are buried in containers that are placed in 10-foot
trenches. Analysis of groundwater from the wells indicates the presence of high levels of
organic contamination. The site is completely fenced and is located approximately 100 feet
away from any public access point. The closest residence is approximately 2,000 feet away
from the site. Approximately 150,000 people live within 4 1/2 miles of the site. Most of these
residents use city-supplied water, which is not contaminated. However, there are a few
residents who use groundwater from private wells.
Site Responsibility:
This site is being addressed through
Federal and potentially responsible
parties' actions.
NPL LISTING HISTORY
Proposed Date: 10/05/84
Final Date: 06/10/86
Threats and Contaminants
The groundwater is contaminated with various volatile organic compounds (VOCs)
and heavy metals including lead. Ingesting and coming in direct contact with
contaminated groundwater is a potential health hazard.
49
March 1992
-------
Cleanup Approach
The site is being addressed in a single long-term remedial phase focusing on cleanup of the
entire site.
Response Action Status
Entire Site: The University's Department of Marine, Earth, and Atmospheric
Sciences has monitored the site extensively since 1981. One background and three
downgradient wells were drilled to a depth of about 10 feet below the water table.
The EPA currently is investigating the nature and extent of the contamination in the site. A
report of the study is expected in 1993. The selection of the remedies to be used for site
cleanup will be determined by the EPA that same year.
Environmental Progress
After adding this site to the NPL, the EPA performed preliminary investigations and
determined that the North Carolina State University site posed no immediate threats while
investigations are taking place.
Site Repository
Not established.
March 1992
50
N.C. STATE UNIVERSITY
(LOT 86, FARM UNIT #1)
-------
PCB SPILL
NORTH CA
EPA ID# NCD980602163
EPA REGION 4
Halifax and 13 counties
243 miles of N.C. highway
Site Description
The PCB Spills site falls along 243 miles of highway where 30,000 gallons of waste
transformer oil contaminated with polychlorinated biphenyls (PCBs) were deliberately
discharged in several areas along the shoulders of the highway in 14 counties of North
Carolina. The State conducted several studies and determined that contaminants did not
travel from the discharge areas into surrounding areas, including rivers, lakes, or streams.
Therefore, the populations surrounding these numerous locations and the plant and animal
life have not been affected.
Site Responsibility: This site was addressed through
Federal actions.
NPL LISTING HISTORY
Proposed Date: 12/30/82
Final Date: 09/08/83
Deleted: 03/07/86
Threats and Contaminants
The soil was contaminated with PCBs. After cleanup investigations were
completed, it was determined that contamination did not move from the discharge
areas into surface water, plant life, or groundwater; therefore, there is no health
threat associated with the spills.
Cleanup Approach
The site was addressed in a single long-term remedial phase focusing on cleanup of the entire
spill area.
51
March 1992
-------
Response Action Status
Entire Site Area: In 1982, the EPA and the State of North Carolina initiated
cleanup actions to: construct a landfill for disposal of PCB waste; remove,
transport, and dispose of contaminated soils; and reconstruct the highway
shoulders. The disposal of contaminated soil was completed in 1982, and the landfill was
capped, graded, and vegetated. Sampling was conducted during cleanup at the beginning and
ending points of the contaminated strips to ensure that all contaminated soils were removed.
Random samples were collected from the areas after soils were removed. No soils
contaminated with PCBs above the accepted levels were left in place. These areas then were
excavated and filled with clean soil. As a result of the completed cleanup actions and the
elimination of site contamination, the EPA, in consultation with the State, deleted the site
from the NPL on March 7, 1986.
Environmental Progress
The contaminated soil from the spill area has been excavated and moved to a closely
monitored landfill. Testing indicated no contamination was present in the groundwater,
surface water, or plant or animal life in the area of the PCB spill. The site is once again safe
for the public and the surrounding environment and has been deleted from the NPL.
Site Repository
Not established.
March 1992
52
PCB SPILLS
-------
POTTER'S SEPTIC
TANK SERVICE
PITS
NORTH CAROLINA
EPA ID# NCD981023260
EPA REGION 4
Brunswick County
Sandy Creek, approximately
18 miles west of Wilmington
Site Description
The Potter's Septic Tank Service Pits site covers 5 acres of land. In 1976, the U.S. Coast
Guard was notified of an oil spill in Rattlesnake Branch Creek. The Coast Guard and the
North Carolina Department of Natural and Economic Resources traced the oil spill to one of
the four disposal pits at the site. In 1983, the present owner informed the North Carolina
Department of Human Resources that he had uncovered sludge in his front yard. The State
found contaminants in his well and shut it down. The EPA found contaminants in the soil and
groundwater on the site. Approximately 1,800 people obtain drinking water from private wells
within 3 miles of the site.
Site Responsibility: This site is being addressed through
Federal and State actions.
NPL LISTING HISTORY
Proposed Date: 06/24/88
Final Date: 03/31/89
Threats and Contaminants
The groundwater is contaminated with volatile organic compounds (VOCs)
including benzene and xylene, phenols, and other petroleum compounds. The soil
is contaminated with heavy metals, chloroform, phenols, VOCs, and other
petroleum compounds. People who use contaminated well water may be at risk.
Direct contact with contaminated soil was a health threat, especially to children
playing in the area, before the removal of contaminated soil and sludge.
Cleanup Approach
This site is being addressed in two stages: initial actions and a long-term remedial phase
focusing on cleanup of the entire site.
53
March 1992
-------
Response Action Status
Initial Actions: The U.S. Coast Guard and the North Carolina Department of
Natural and Economic Resources removed 40,000 gallons of oil from the stream
and pits and 150 truckloads of oil sludge and oil-stained soil. Thick oil sludge that
could not be removed was mixed with sand and buried on the site. In 1984, the EPA removed
approximately 3 million pounds of contaminated soil from the site and transported it to a
federally approved hazardous waste facility.
Entire Site: The EPA began studying the nature and extent of contamination at
the site in 1989. Once their studies are completed, scheduled for mid-1992, the
EPA will determine the best strategies for cleanup.
Environmental Progress
The initial soil and sludge removal actions described above have eliminated the possibility of
contact threats from contaminated soil at the Potter's Septic Tank Service Pits site while
investigations and cleanup activities are taking place.
Site Repository
Columbus County Library, Route 2, Highway 87, Riegelwood, NC 28456
March 1992
54
POTTER'S SEPTIC TANK SERVICE PITS
-------
GLOSSARY
Terms Used in the NPL Book
This glossary defines terms used throughout the NPL Volumes. The terms and
abbreviations contained in this glossary apply specifically to work performed
under the Superfund program in the context of hazardous waste management. These
terms may have other meanings when used in a different context. A table of common
toxic chemicals found at NPL sites, their sources, and their potential threats is located
on page G-15
Acids: Substances, characterized by low pH
(less than 7.0), that are used in chemical manu-
facturing. Acids in high concentration can be
very corrosive and react with many inorganic
and organic substances. These reactions possi-
bly may create toxic compounds or release
heavy metal contaminants that remain in the
environment long after the acid is neutralized.
Administrative Order On Consent: A
legal and enforceable agreement between the
EPA and the parties potentially responsible for
site contamination. Under the terms of the
Order, the potentially responsible parties (PRPs)
agree to perform or pay for site studies or
cleanups. It also describes the oversight rules,
responsibilities, and enforcement options that
the government may exercise in the event of
non-compliance by potentially responsible
parties. This Order is signed by PRPs and the
government; it does not require approval by a
judge.
Administrative Order [Unilateral]: A
legally binding document issued by the EPA,
directing the parties potentially responsible to
perform site cleanups or studies (generally, the
EPA does not issue Unilateral Orders for site
studies). This type of Order is not signed by the
PRPs and does not require approval by a judge.
Aeration: A process that promotes breakdown
of contaminants in soil or water by exposing
them to air.
Agency for Toxic Substances and Dis-
ease Registry (ATSDR): The Federal
agency within the U.S. Public Health Service
charged with carrying out the health-related
responsibilities of CERCLA.
Air Stripping: A process whereby volatile
organic chemicals (VOCs) are removed from
contaminated material by forcing a stream of air
through the contaminated material in a pressur-
ized vessel. The containinants are evaporated
into the air stream. The air may be further
treated before it is released into the atmosphere.
Ambient Air: Anyunconfinedpartofthe
atmosphere. Refers to the air that may be
inhaled by workers or residents in the vicinity of
contaminated air sources.
Applicable or Relevant and Appropriate
Requirements (ARARs): Federal, State, or
local laws which apply to Superfund activities at
NPL sites. Both emergency and long-term
actions must comply with these laws or provide
sound reasons for allowing a waiver. ARARs
must be identified for each site relative to the
characteristics of the site, the substances found
at the site, or the cleanup alternatives being
considered for the site.
G-1
-------
GLOSSARY
Aquifer: An underground layer of rock, sand,
or gravel capable of storing water within cracks
and pore spaces, or between grains. When
water contained within an aquifer is of sufficient
quantity and quality, it can be tapped and used
for drinking or other purposes. The water
contained in the aquifer is called groundwater.
A "sole source aquifer" supplies 50 percent or
more of the drinking water of an area.
Artesian (Well): A well made by drilling into
the earth until water is reached, which, due to
internal pressure, flows up like a fountain.
Asbestos: A mineral fiber that can pollute air
or water and is known to cause cancer or
asbestosis when inhaled.
Attenuation: The naturally occurring process
by which a compound is reduced in concentra-
tion over time through adsorption, degradation,
dilution, or transformation.
Background Level: The amount of a sub-
stance typically found in the air, water, or soil
from natural, as opposed to human, sources.
Baghouse Dust: Dust accumulated in
removing particulates from the air by passing it
through cloth bags in an enclosure.
Bases: Substances characterized by high pH
(greater than 7.0), which tend to be corrosive in
chemical reactions. When bases are mixed with
acids, they neutralize each other, forming salts.
Berm: A ledge, wall, or a mound of earth used
to prevent the migration of contaminants.
Bioaccumulate: The process by which some
contaminants or toxic chemicals gradually
collect and increase in concentration in living
tissue, such as in plants, fish, or people, as they
breathe contaminated air, drink contaminated
water, or eat contaminated food.
Biological Treatment: The use of bacteria
or other microbial organisms to break down
toxic organic materials into carbon dioxide and
water.
Bioremediation: A cleanup process using
naturally occurring or specially cultivated
microorganisms to digest contaminants and
break them down into non-hazardous compo-
nents.
Bog: A type of wetland that is covered with
peat moss deposits. Bogs depend primarily on
moisture from the air for their water source, are
usually acidic, and are rich in plant residue [see
Wetland].
Boom: A floating device used to contain oil
floating on a body of water or to restrict the
potential overflow of waste liquids from
containment structures.
Borehole: A hole that is drilled into the
ground and used to sample soil or ground-water.
Borrow Pit: An excavated area where soil,
sand, or gravel has been dug up for use else-
where.
Cap: A layer of material, such as clay or a
synthetic material, used to prevent rainwater
from penetrating and spreading contaminated
materials. The surface of the cap generally is
mounded or sloped so water will drain off.
Carbon Adsorption: A treatment system in
which contaminants are removed from ground-
water and surface water by forcing water
through tanks containing activated carbon, a
specially treated material that attracts and holds
or retains contaminants.
Carbon Disulfide: A degreasing agent
formerly used extensively for parts washing.
This compound has both inorganic and organic
G-2
-------
GLOSSARY
properties, which increase cleaning efficiency.
However, these properties also cause chemical
reactions that increase the hazard to human
health and the environment.
Carbon Treatment: [see Carbon Adsorp-
tion].
Cell: In solid waste disposal, one of a series of
holes in a landfill where waste is dumped,
compacted, and covered with layers of dirt.
CERCLA: [see Comprehensive Environmen-
tal Response, Compensation, and Liability Act].
Characterization: The sampling, monitoring,
and analysis of a site to determine the extent and
nature of toxic releases. Characterization
provides the basis for acquiring the necessary
technical information to develop, screen, ana-
lyze, and select appropriate cleanup techniques.
Chemical Fixation: The use of chemicals to
bind contaminants, thereby reducing the poten-
tial for leaching or other movement.
Chromated Copper Arsenate: An insecti-
cide/herbicide formed from salts of three toxic
metals: copper, chromium, and arsenic. This
salt is used extensively as a wood preservative
in pressure-treating operations. It is highly toxic
and water-soluble, making it a relatively mobile
contaminant in the environment
Cleanup: Actions taken to eliminate a release
or threat of release of a hazardous substance.
The term "cleanup" sometimes is used inter-
changeably with the terms remedial action,
removal action, response action, or corrective
action.
Closure: The process by which a landfill stops
accepting wastes and is shut down under Federal
guidelines that ensure the protection of the
public and the environment.
Comment Period: A specific interval during
which the public can review and comment on
various documents and EPA actions related to
site cleanup. For example, a comment period is
provided when the EPA proposes to add sites to
the NPL. Also, there is minimum 3-week
comment period for community members to
review and comment on the remedy proposed to
clean up a site.
Community Relations: The EPA effort to
establish and maintain two-way communication
with the public. The goals of community
relations programs include creating an under-
standing of EPA programs and related actions,
assuring public input into decision-making
processes related to affected communities, and
making certain that the Agency is aware of, and
responsive to, public concerns. Specific com-
munity relations activities are required in
relation to Superfund cleanup actions [see
Comment Period].
Comprehensive Environmental Re-
sponse, Compensation, and Liability
Act (CERCLA): Congress enacted the
CERCLA, known as Superfund, in 19X0 to
respond directly to hazardous waste problems
that may pose a threat to the public health and
the environment. The EPA administers the
Superfund program.
Confluence: The place where two bodies of
water, such as streams or rivers, come together.
Confined Aquifer: An aquifer in which
groundwater is confined under pressure that is
significantly greater than atmospheric pressure.
G-3
-------
GLOSSARY
Consent Decree: A legal document, ap-
proved and issued by a judge, formalizing an
agreement between the EPA and the parties
potentially responsible for site contamination.
The decree describes cleanup actions that the
potentially responsible parties are required to
perform, or the costs incurred by the govern-
ment that the parties will reimburse, and the
roles, responsibilities, and enforcement options
that the government may exercise in the event of
non-compliance by potentially responsible
parties. If a settlement between the EPA and a
potentially responsible party includes cleanup
actions, it must be in the form of a Consent
Decree. A Consent Decree is subject to a public
comment period.
Consent Order: [see Administrative Order
on Consent].
Containment: The process of enclosing or
containing hazardous substances in a structure,
typically in a pond or a lagoon, to prevent the
migration of contaminants into the environment.
Contaminant: Any physical, chemical,
biological, or radiological material or substance
whose quantity, location, or nature produces
undesirable health or environmental effects.
Contingency Plan: A document setting
out an organized, planned, and coordinated
course of action to be followed in case of a
fire, explosion, or other accident that releases
toxic chemicals, hazardous wastes, or radioac-
tive materials into the environment.
Cooperative Agreement: A contract
between the EPA and the States, wherein a State
agrees to manage or monitor certain site cleanup
responsibilities and other activities on a cost-
sharing basis.
Cost Recovery: A legal process by which
potentially responsible parties can be required
to pay back the Superfund program for money
it spends on any cleanup actions [see Poten-
tially Responsible Parties].
Cover: Vegetation or other material placed
over a landfill or other waste material. It can
be designed to reduce movement of water into
the waste and to prevent erosion that could
cause the movement of contaminants.
Creosotes: Chemicals used in wood pre-
serving operations and produced by distilla-
tion of tar, including polycyclic aromatic
hydrocarbons and polynuclear aromatic
hydrocarbons [see PAHs and PNAs]. Con-
taminating sediments, soils, and surface
water, creosotes may cause skin ulcerations
and cancer through prolonged exposure.
Culvert: A pipe used for drainage under a
road, railroad track, path, or through an embank-
ment.
Decommission: To revoke a license to
operate and take out of service.
Degradation: The process by which a chemi-
cal is reduced to a less complex form.
Degrease: To remove grease from wastes,
soils, or chemicals, usually using solvents.
Deletion: A site is eligible for deletion from
the NPL when Superfund response actions at the
site are complete. A site is deleted from the
NPL when a notice is published in the Federal
Register.
De minimis: This legal phrase pertains to
settlements with parties who contributed small
amounts of hazardous waste to a site. This
process allows the EPA to settle with small, or
due minimis contributors, as a single group rather
than as individuals, saving time, money, and
effort.
Dewater: To remove water from wastes, soils,
or chemicals.
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GLOSSARY
Dike: A low wall that can act as a barrier to
prevent a spill from spreading.
Dioxin: An organic chemical by-product of
pesticide manufacture which is known to be one
of the most toxic man-made chemicals.
Disposal: Final placement or destruction of
toxic, radioactive, or other wastes; surplus or
banned pesticides or other chemicals; polluted
soils; and drums containing hazardous materials.
Disposal may be accomplished through the use
of approved secure landfills, surface impound-
ments, land farming, deep well injection, or
incineration.
Downgradient: A downward hydrologic
slope that causes groundwater to move toward
lower elevations. Therefore, wells downgradi-
ent of a contaminated groundwater source are
prone to receiving pollutants.
Ecological Assessment: A study of the
impact of man-made or natural activity on living
creatures and their environment
Effluent: Wastewater, treated or untreated,
that flows out of a treatment plant, sewer, or
industrial outfall. Generally refers to wastes
discharged into surface waters.
Emission: Pollution discharged into the
atmosphere from smokestacks, other vents, and
surface areas of commercial or industrial facili-
ties.
Emulsifiers: Substances that help in inking
materials that do not normally mix; e.g., oil and
water.
Endangerment Assessment: A study
conducted to determine the risks posed to public
health or the environment by contamination at
NPL sites. The EPA or the State conducts the
study when a legal action is to be taken to direct
the potentially responsible parties to clean up a
site or pay for the cleanup. An endangerment
assessment supplements an investigation of the
site hazards.
Enforcement: EPA, State, or local legal
actions taken against parties to facilitate
settlements; to compel compliance with laws,
rules, regulations, or agreements; or to obtain
penalties or criminal sanctions for violations.
Enforcement procedures may vary, depending
on the specific requirements of different
environmental laws and related regulatory
requirements. Under CERCLA, for example,
the EPA will seek to require potentially
responsible parties to clean up a Superfund
site or pay for the cleanup [see Cost Recov-
ery].
Erosion: The wearing away of land surface
by wind or water. Erosion occurs naturally
from weather or surface runoff, but can be
intensified by such land-related practices as
fanning, residential or industrial develop-
ment, road building, or timber-cutting. Ero-
sion may spread surface contamination to off-
site locations.
Estuary (estuarine): Areas where fresh
water from rivers and salt water from
nearshore ocean waters are mixed. These
areas may include bays, mouths of rivers, salt
marshes, and lagoons. These water ecosys-
tems shelter and feed marine life, birds, and
wildlife.
Evaporation Ponds: Areas where sewage
sludge or other watery wastes are dumped and
allowed to dry out.
Feasibility Study: The analysis of the
potential cleanup alternatives for a site. The
feasibility study usually starts as soon as the
remedial investigation is underway. In this
volume, the feasibility study is referred to as a
site study [see also Remedial Investigation].
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GLOSSARY
Filtration: A treatment process for remov-
ing solid (particulate) matter from water by
passing the water through sand, activated
carbon, or a man-made filter. The process is
often used to remove particles that contain
contaminants.
Flood Plain: An area along a river, formed
from sediment deposited by floods. Flood
plains periodically are innundated by natural
floods, which can spread contamination.
Flue Gas: The air that is emitted from a
chimney after combustion in the burner
occurs. The gas can include nitrogen oxides,
carbon oxides, water vapor, sulfur oxides,
particles, and many chemical pollutants.
Fly Ash: Non-combustible residue that results
from the combustion of flue gases. It can
include nitrogen oxides, carbon oxides, water
vapor, sulfur oxides, as well as many other
chemical pollutants.
French Drain System: A crushed rock drain
system constructed of perforated pipes, which is
used to drain and disperse wastewater.
Gasification (coal): The conversion of soft
coal into gas for use as a fuel.
General Notice Letter: [See Notice Letter].
Generator: A facility that emits pollutants
into the air or releases hazardous wastes into
water or soil.
Good Faith Offer: A voluntary offer, gener-
ally in response to a Special Notice letter, made
by a potentially responsible party, consisting of
a written proposal demonstrating a potentially
responsible party's qualifications and willing-
ness to perform a site study or cleanup.
Groundwater: Water that fills pores in soils
or openings in rocks to the point of saturation.
In aquifers, groundwater occurs in sufficient
quantities for use as drinking and irrigation
water and other purposes.
Groundwater Quality Assessment: The
process of analyzing the chemical characteris-
tics of groundwater to determine whether any
hazardous materials exist.
Halogens: Reactive non-metals, such as
chlorine and bromine. Halogens are very
good oxidizing agents and, therefore, have
many industrial uses. They are rarely found
by themselves; however, many chemicals
such as polychlorinated biphenyls (PCBs),
some volatile organic compounds (VOCs),
and dioxin are reactive because of the pres-
ence of halogens.
Hazard Ranking System (HRS): The
principal screening tool used by the EPA to
evaluate relative risks to public health and the
environment associated with abandoned or
uncontrolled hazardous waste sites. The HRS
calculates a score based on the potential of
hazardous substances spreading from the site
through the air, surface water, or groundwater
and on other factors such as nearby popula-
tion. The HRS score is the primary factor in
deciding if the site should be on the NPL.
Hazardous Waste: By-products of society
that can pose a substantial present or potential
hazard to human health and the environment
when improperly managed. Hazardous waste
possesses at least one of four characteristics
(ignitability, corrosivity, reactivity, or toxic-
ity), or appears on special EPA lists.
Heavy Metals: Metallic elements with high
atomic weights, such as arsenic, lead, mercury,
and cadmium. Heavy metals are very hazardous
even at low concentrations and tend to accumu-
late in the food chain.
Herbicide: A chemical pesticide designed to
control or destroy plants, weeds, or grasses.
G-6
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GLOSSARY
Hot Spot: An area or vicinity of a site contain-
ing exceptionally high levels of contamination.
Hydrocarbons: Chemical compounds that
consist entirely of hydrogen and carbon.
Hydrology: The properties, distribution, and
circulation of water.
Hydrogeology: The geology of groundwater,
with particular emphasis on the chemistry and
movement of water.
Impoundment: A body of water or sludge
confined by a dam, dike, floodgate, or other
barrier.
Incineration: A group of treatment technolo-
gies involving destruction of waste by controlled
burning at high temperatures, e.g., burning
sludge to reduce the remaining residues to a
non-burnable ash that can be disposed of safely
on land, in some waters, or in underground
locations.
Infiltration: The movement of water or
other liquid down through soil from precipita-
tion (rain or snow) or from application of
wastewater to the land surface.
Influent: Water, wastewater, or other liquid
flowing into a reservoir, basin, or treatment
plant.
Injection Well: A well into which waste
fluids are placed, under pressure, for purposes
of disposal.
Inorganic Chemicals: Chemical sub-
stances of mineral origin, not of basic carbon
structure.
Installation Restoration Program: The
specially funded program established in 1978
under which the Department of Defense has
been identifying and evaluating its hazardous
waste sites and controlling the migration of
hazardous contaminants from those sites.
Intake: The source from where a water supply
is drawn, such as from a river or water body.
Interagency Agreement: A written agree-
ment between the EPA and a Federal agency
that has the lead for site cleanup activities,
setting forth the roles and responsibilities of the
agencies for performing and overseeing the
activities. States often are parties to interagency
agreements.
Interim (Permit) Status: Conditions under
which hazardous waste treatment, storage,
and disposal facilities, that were operating
when regulations under the RCRA became
final in 1980, are temporarily allowed by the
EPA to continue to operate while awaiting
denial or issuance of a permanent permit. The
facility must comply with certain regulations
to maintain interim status.
Lagoon: A shallow pond or liquid waste
containment structure. Lagoons typically are
used for the storage of wastewaters, sludges,
liquid wastes, or spent nuclear fuel.
Landfarm: To apply waste to land or incor-
porate waste into the surface soil, such as
fertilizer or soil conditioner. This practice
commonly is used for disposal of composted
wastes and sludges.
Landfill: A disposal facility where waste is
placed in or on land. Sanitary landfills are
disposal sites for non-hazardous solid wastes.
The waste is spread in layers, compacted to the
smallest practical volume, and covered with soil
at the end of each operating day. Secure chemi-
cal landfills are disposal sites for hazardous
waste. They are designed to minimize the
chance of release of hazardous substances into
the environment [see Resource Conservation
and Recovery Act].
Leach, Leaching [v.t.]: The process by
which soluble chemical components are dis-
solved and carried through soil by water or
some other percolating liquid.
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GLOSSARY
Leachate [n]: The liquid that trickles through
or drains from waste, carrying soluble compo-
nents from the waste.
Leachate Collection System: A system
that gathers liquid that has leaked into a landfill
or other waste disposal area and pumps it to the
surface for treatment.
Liner: A relatively impermeable barrier
designed to prevent leachate (waste residue)
from leaking from a landfill. Liner materials
include plastic and dense clay.
Long-term Remedial Phase: Distinct,
often incremental, steps that are taken to solve
site pollution problems. Depending on the
complexity, site cleanup activities can be
separated into several of these phases.
Long-term Response Action: An action
which requires a continuous period of on-site
activity before cleanup goals are achieved.
These actions typically include the extraction
and treatment of groundwater and monitoring
actions.
Marsh: A type of wetland that does not
contain peat moss deposits and is dominated by
vegetation. Marshes may be either fresh or
saltwater and tidal or non-tidal [see Wetland].
Migration: The movement of oil, gas, con-
taminants, water, or other liquids through porous
and permeable soils or rock.
Mill Tailings: [See Mine Tailings].
Mine Tailings: A fine, sandy residue left from
mining operations. Tailings often contain high
concentrations of lead, uranium, and arsenic or
other heavy rnetals.
Mitigation: Actions taken to improve site
conditions by limiting, reducing, or controlling
toxicity and contamination sources.
Modeling: A technique using a mathematical
or physical representation of a system or theory
that tests the effects that changes on system
components have on the overall performance of
the system.
Monitoring Wells: Special wells drilled at
specific locations within, or surrounding, a
hazardous waste site where groundwater can be
sampled at selected depths and studied to obtain
such information as the direction in which
groundwater flows and the types and amounts of
contaminates present.
National Priorities List (NPL): The
EPA's list of the most serious uncontrolled or
abandoned hazardous waste sites identified
for possible long-term cleanup under Super-
fund. The EPA is required to update the NPL
at least once a year.
Natural Attenuation: [See Attenuation].
Neutrals: Organic compounds that have a
relatively neutral pH, complex structure and,
due to their organic bases, are easily absorbed
into the environment. Water is the most
commonly known neutral, however, naphtha-
lene, pyrene, and trichlorobenzene also are
examples of neutrals.
Nitroaromatics: Common components of
explosive materials, which will explode if
activated by very high temperatures or pres-
sures; 2,4,6-Trinitrotoluene (TNT) is a
nitroaromatic.
Notice Letter: A General Notice Letter
notifies the parties potentially responsible for
site contamination of their possible liability. A
Special Notice Letter begins a 60-day formal
period of negotiation during which the EPA is
not allowed to start work at a site or initiate
enforcement actions against potentially respon-
sible parties, although the EPA may undertake
certain investigatory and planning activities.
G-8
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GLOSSARY
The 60-day period may be extended if the EPA
receives a good faith offer from the PRPs
within that period. [See also Good Faith Offer].
On-Scene Coordinator (OSC): The
predesignated EPA, Coast Guard, or Depart-
ment of Defense official who coordinates and
directs Superfund removal actions or Clean
Water Act oil- or hazardous-spill corrective
actions.
Operation and Maintenance: Activities
conducted at a site after a cleanup action is
completed to ensure that the cleanup or
containment system is functioning properly.
Organic Chemicals/Compounds:
Chemical substances containing mainly
carbon, hydrogen, and oxygen.
Outfall: The place where wastewater is
discharged into receiving waters.
Overpacking: Process used for isolating
large volumes of waste by jacketing or encap-
sulating waste to prevent further spread or
leakage of contaminating materials. Leaking
drums may be contained within oversized
barrels as an interim measure prior to removal
and final disposal.
Pentachlorophenol (PCP): A synthetic,
modified petrochemical that may be used as a
wood preservative because of its toxicity to
termites and fungi. It is a common component
of creosotes and can cause cancer.
Perched (groundwater): Groundwater
separated from another underlying body of
groundwater by a confining layer, often clay or
rock.
Percolation: The downward flow or filtering
of water or other liquids through subsurface
rock or soil layers, usually continuing down-
ward to groundwater.
Pesticide: A substance or mixture of sub-
stances intended to prevent, destroy, or repel any
pest. If misused, pesticides can accumulate in
the foodchain and contaminate the environment.
Petrochemicals: Chemical substances
produced from petroleum in refinery operations
and as fuel oil residues. These include
fluoranthene, chrysene, mineral spirits, and
refined oils. Petrochemicals are the bases from
which volatile organic compounds (VOCs),
plastics, and many pesticides are made. These
chemical substances often are toxic to humans
and the environment.
Phenols: Organic compounds that are used in
plastics manufacturing and are by-products of
petroleum refining, tanning, textile, dye, and
resin manufacturing. Phenols are highly poison-
ous.
Physical Chemical Separation: The
treatment process of adding a chemical to a
substance to separate the compounds for further
treatment or disposal.
Pilot Testing: A small-scale test of a pro-
posed treatment system in the field to determine
its ability to clean up specific contaminants.
Plugging: The process of stopping the flow of
water, oil, or gas into or out of the ground
through a borehole or well penetrating the
ground.
Plume: A body of contaminated groundwater
flowing from a specific source. The movement
of the groundwater is influenced by such factors
as local groundwater flow patterns, the character
of the aquifer in which groundwater is con-
tained, and the density of contaminants [see
Migration].
Poll ution: Generally, the presence of matter
or energy whose nature, location, or quantity
produces undesired health or environmental
effects.
G-9
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GLOSSARY
Polycyclic Aromatic Hydrocarbons or
Polyaromatic Hydrocarbons (PAHs):
PAHs, such as pyrene, are a group of highly
reactive organic compounds found in motor oil.
They are a common component of creosotes and
can cause cancer.
Polychlorinated Biphenyls (PCBs): A
group of toxic chemicals used for a variety of
purposes including electrical applications,
carbonless copy paper, adhesives, hydraulic
fluids, microscope immersion oils, and caulking
compounds. PCBs also are produced in certain
combustion processes. PCBs are extremely
persistent in the environment because they are
very stable, non-reactive, and highly heat
resistant. Chronic exposure to PCBs is believed
to cause liver damage. It also is known to
bioaccumulate in fatty tissues. PCB use and
sale was banned in 1979 with the passage of the
Toxic Substances Control Act.
Polynuclear Aromatic Hydrocarbons
(PNAs): PNAs, such as naphthalene, and
biphenyls, are a group of highly reactive organic
compounds that are a common component of
creosotes, which can be carcinogenic.
Polyvinyl Chloride (PVC): A plastic made
from the gaseous substance vinyl chloride. PVC
is used to make pipes, records, raincoats, and
floor tiles. Health risks from high concentra-
tions of vinyl chloride include liver cancer and
lung cancer, as well as cancer of the lymphatic
and nervous systems.
Potable Water: Water that is safe for drink-
ing and cooking.
Potentially Responsible Parties (PRPs):
Parties associated with a Superfund site who
may be liable for the cost of remedying the
release of hazardous substances. This may
include owners or operators of the site or trans-
porters who disposed of materials at the site.
PRPs may admit liability, or liability may be
determined by a court of law. PRPs may sign a
Consent Decree or Administrative Order on
Consent to participate in the site cleanup without
admitting liability.
Precipitation: The removal of solids from
liquid waste so that the solid and liquid portions
can be disposed of safely; the removal of
particles from airborne emissions. Electro-
chemical precipitation is the use of an anode or
cathode to remove the hazardous chemicals.
Chemical precipitation involves the addition of
some substance to cause the solid portion to
separate.
Preliminary Assessment: The process of
collecting and reviewing available information
about a known or suspected waste site or release
to determine if a threat or potential threat exists.
Pump and Treat: A groundwater cleanup
• technique involving the extracting of contami-
nated groundwater from the subsurface and the
removal of contaminants, using one of several
treatment technologies.
Radionuclides: Elements, including radium
and uranium-235 and -238, which break down
and produce radioactive substances due to their
unstable atomic structure. Some are man-made,
and others are naturally occurring in the envi-
ronment. Radon, the gaseous form of radium,
decays to form alpha particle radiation, which
cannot be absorbed through skin. However, it
can be inhaled, which allows alpha particles to
affect unprotected tissues directly and thus cause
cancer. Radiation also occurs naturally through
the breakdown of granite.
RCRA: [See Resource Conservation and
Recovery Act].
Recharge Area: A land area where rainwater
saturates the ground and soaks through the earth
to reach an aquifer.
G-10
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GLOSSARY
Record of Decision (ROD): A public
document that explains which cleanup
alternative(s) will be used to clean up sites
listed on the NPL. It is based on information
generated during the remedial investigation
and feasibility study and consideration of
public comments and community concerns.
Recovery Wells: Wells used to withdraw
contaminants or contaminated groundwater.
Recycle: The process of minimizing waste
generation by recovering usable products that
might otherwise become waste.
Remedial Action (RA): The actual con-
struction or implementation phase of a
Superfund site cleanup following the remedial
design [see Cleanup].
Remedial Design: A phase of site cleanup
where engineers design the technical specifi-
cations for cleanup remedies and technolo-
gies.
Remedial Investigation: An in-depth
study designed to gather the data necessary to
determine the nature and extent of contamina-
tion at a Superfund site, establish the criteria
for cleaning up the site, identify the prelimi-
nary alternatives for cleanup actions, and
support the technical and cost analyses of the
alternatives. The remedial investigation is
usually done with the feasibility study. In this
volume, the remedial investigation is referred
to as a site study [see also Feasibility Study].
Remedial Project Manager (RPM): The
EPA or State official responsible for oversee-
ing cleanup actions at the site.
Remedy Selection: The selection of the
final cleanup strategy for the site. At the few
sites where the EPA has determined that
initial response actions have eliminated site
contamination, or that any remaining con-
tamination will be naturally dispersed without
further cleanup activities, a "No Action"
remedy is selected [see Record of Decision].
Removal Action: Short-term immediate
actions taken to address releases of hazardous
substances [see Cleanup].
Residual: The amount of a pollutant re-
maining in the environment after a natural or
technological process has taken place, e.g.,
the sludge remaining after initial wastewater
treatment, or the particulates remaining in air
after the air passes through a scrubber.
Resource Conservation and Recovery
Act (RCRA): A Federal law that established
a regulatory system to track hazardous sub-
stances from the time of generation to dis-
posal. The law requires safe and secure
procedures to be used in treating, transport-
ing, storing, and disposing of hazardous
substances. RCRA is designed to prevent
new, uncontrolled hazardous waste sites.
Retention Pond: A small body of liquid
used for disposing of wastes and containing
overflow from production facilities. Some-
times retention ponds are used to expand the
capacity of such structures as lagoons the
store waste.
Runoff: The discharge of water over land
into surface water. It can carry pollutants
from the air and land and spread contaminants
from its source.
Scrubber: An air pollution control device
that uses a spray of water or reactant or a dry
process to trap pollutants in emissions.
Sediment: The layer of soil, sand, and
minerals at the bottom of surface waters such
as streams, lakes, and rivers, that absorbs
contaminants.
G-11
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GLOSSARY
Seeps: Specific points where releases of
liquid, usually leachate, form from waste
disposal areas, particularly along the lower
edges of landfills.
Seepage Pits: A hole, shaft, or cavity in
the ground used for the storage of liquids,
usually in the form of leachate, from waste
disposal areas. The liquid gradually leaves
the pit by moving through the surrounding
soil.
Septage: Residue remaining in a septic tank
after the treatment process.
Sinkhole: A hollow depression in the land
surface in which drainage collects; associated
with underground caves and passages that
facilitate the movement of liquids.
Site Characterization: The technical pro-
cess used to evaluate the nature and extent of
environmental contamination, which is neces-
sary for choosing and designing cleanup mea-
sures and monitoring their effectiveness.
Site Inspection: The collection of informa-
tion from a hazardous waste site to determine
the extent and severity of hazards posed by the
site. It follows, and is more extensive than, a
preliminary assessment. The purpose is to
gather information necessary to score the site,
using the Hazard Ranking System, and to
determine if the site presents an immediate
threat that requires a prompt removal action.
Slag: The fused refuse or dross separated
from a metal in the process of smelting.
Sludge: Semi-solid residues from industrial
or water treatment processes that may be
contaminated with hazardous materials.
Slurry Wall: Barriers used to contain the flow
of contaminated groundwater or subsurface
liquids. Slurry walls are constructed by digging
a trench around a contaminated area and filling
the trench with an impermeable material that
prevents water from passing through it. The
groundwater or contaminated liquids trapped
within the area surrounded by the slurry wall
can be extracted and treated.
Smelter: A facility that melts or fuses ore,
often with an accompanying chemical change,
to separate the metal. Emissions from smelters
are known to cause pollution.
Soil Gas: Gaseous elements and compounds
that occur in the small spaces between par-
ticles of soil. Such gases can move through
or leave the soil or rock, depending on
changes in pressure.
Soil Vapor Extraction: A treatment
process that uses vacuum wells to remove
hazardous gases from soil.
Soil Washing: A water-based process for
mechanically scrubbing soils in-place to remove
undesirable materials. There are two ap-
proaches: dissolving or suspending them in the
wash solution for later treatment by conven-
tional methods, and concentrating them into a
smaller volume of soil through simple particle
size separation techniques [see Solvent Extrac-
tion].
Stabilization: The process of changing an
active substance into inert, harmless material,
or physical activities at a site that act to limit
the further spread of contamination without
actual reduction of toxicity.
Solidification/Stabilization: A chemical
or physical reduction of the mobility of
hazardous constituents. Mobility is reduced
through the binding of hazardous constituents
into a solid mass with low permeability and
resistance to leaching.
G-12
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GLOSSARY
Solvent: A substance capable of dissolving
another substance to form a solution. The
primary uses of industrial solvents are as
cleaners for degreasing, in paints, and in
Pharmaceuticals. Many solvents are flam-
mable and toxic to varying degrees.
Solvent Extraction: A means of separating
hazardous contaminants from soils, sludges,
and sediment, thereby reducing the volume of
the hazardous waste that must be treated. It
generally is used as one in a series of unit
operations. An organic chemical is used to
dissolve contaminants as opposed to water-
based compounds, which usually are used in
soil washing.
Sorption: The action of soaking up or
attracting substances. It is used in many
pollution control systems.
Special Notice Letter: [See Notice Let-
ter].
Stillbottom: Residues left over from the
process of recovering spent solvents.
Stripping: A process used to remove volatile
contaminants from a substance [see Air Strip-
ping]-
Sumps: A pit or tank that catches liquid
runoff for drainage or disposal.
Superfund: The program operated under the
legislative authority of the CERCLA and
Superfund Amendments and Reauthorization
Act (SARA) to update and improve environ-
mental laws. The program has the authority to
respond directly to releases or threatened re-
leases of hazardous substances that may endan-
ger public health, welfare, or the environment
The "Superfund" is a trust fund that finances
cleanup actions at hazardous waste sites.
Surge Tanks: A holding structure used to
absorb irregularities in flow of liquids, including
liquid waste materials.
Swamp: A type of wetland that is dominated
by woody vegetation and does not accumulate
peat moss deposits. Swamps may be fresh or
saltwater and tidal or non-tidal [see Wetlands].
Thermal Treatment: The use of heat to
remove or destroy contaminants from soil.
Treatability Studies: Testing a treatment
method on contaminated ground water, soil, etc.,
to determine whether and how well the method
will work.
Trichloroethylene (TCE): A stable, color-
less liquid with a low boiling point. TCE has
many industrial applications, including use as
a solvent and as a metal degreasing agent.
TCE may be toxic to people when inhaled,
ingested, or through skin contact and can
damage vital organs, especially the liver [see
Volatile Organic Compounds].
Unilateral [Administrative] Order: [see
Administrative Order].
Upgradient: An upward hydrologic slope;
demarks areas that are higher than contaminated
areas and, therefore, are not prone to contamina-
tion by the movement of polluted groundwater.
Vacuum Extraction: A technology used to
remove volatile organic compounds (VOCs)
from soils. Vacuum pumps are connected to a
series of wells drilled to just above the water
table. The wells are sealed tightly at the soil
surface, and the vacuum established in the soil
draws VOC-contaminated air from the soil
pores into the well, as fresh air is drawn down
from the surface of the soil.
G-13
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GLOSSARY
Vegetated Soil Cap: A cap constructed with
graded soils and seed for vegetative growth, to
prevent erosion [see Cap].
Vitrification: The process of electrically
melting wastes and soils or sludges to bind the
waste in a glassy, solid material more durable
than granite or marble and resistant to leaching.
Volatile Organic Compounds (VOCs):
VOCs are manufactured as secondary petro-
chemicals. They include light alcohols, acetone,
trichloroethylene, perchloroethylene,
dichloroethylene, benzene, vinyl chloride,
toluene, and methylene chloride. These poten-
tially toxic chemicals are used as solvents,
degreasers, paints, thinners, and fuels. Because
of their volatile nature, they readily evaporate
into the air, increasing the potential exposure to
humans. Due to their low water solubility,
environmental persistence, and widespread
industrial use, they are commonly found in soil
and groundwater.
Waste Treatment Plant: A facility that
uses a series of tanks, screens, filters, and
other treatment processes to remove pollut-
ants from water.
Wastewater: The spent or used water from
individual homes or industries.
Watershed: The land area that drains into a
stream or other water body.
Water Table: The upper surface of the
groundwater.
Weir: A barrier to divert water or other liquids.
Wetland: An area that is regularly saturated
by surface or groundwater and, under normal
circumstances, is capable of supporting
vegetation typically adapted for life in satu-
rated soil conditions. Wetlands are critical to
sustaining many species of fish and wildlife.
Wetlands generally include swamps, marshes,
and bogs. Wetlands may be either coastal or
inland. Coastal wetlands have salt or brackish
(a mixture of salt and fresh) water, and most
have tides, while inland wetlands are non-
tidal and freshwater. Coastal wetlands are an
integral component of estuaries.
Wildlife Refuge: An area designated for
the protection of wild animals, within which
hunting and fishing are either prohibited or
strictly controlled.
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GLOSSARY
Some Common Contaminants at NPL Sites
Contaminant
Category
Example
Chemical Types
Sources
Potential Health
Heavy Metals
Volatile Organic
Compounds
(VQCs)
Polychtarinated
(Pegs)
Creosotes
Radiatfon
(Radfonudkfes)
Arsenic, Barium, Beryllium,
Cadmium, Cobalt, Copper,
Chromium, Lead, Manga-
nese, Mercury, Nickel,
Silver, Selenium, Zinc
Trichloroethylene (TCE),
Perchloroethylene (PCE),
Acetone', Benzene,
Ketone, Methyl chloride,
Toluene, Vinyl Chloride,
Dichlorethylene
Chlordane, DDT 4-4, DDE,
Heptachlor, Aldrin, Endrin,
Atrazine, Dieldrin, Toxa-
phene
Polyaromatic hydrocar-
bons (PAHs), Polynuclear
aromatics (PNAs),
Phenolic Tars, Pentachlo-
rophenol (PCP)
Radium-226, Radon,
Uranium-235, Uranium-
238
Electroplating, batteries,
paint pigments, photogra-
phy, smelting, thermom-
eters, fluorescent lights,
solvent recovery
Solvents and degreasers,
gasoline octane enhanc-
ers, oils and paints, dry
cleaning fluids, chemical
manufacturing.
Agricultural applications,
pesticide and herbicide
production
Electric transformers and
capacitors, insulators and
coolants, adhesives,
caulking compounds,
carbonless copy paper,
hydraulic fluids.
Wood preserving, fossil
fuel combustion
Mine tailings, radium
products, natural decay of
granites
Tumors, cancers, and kidney,
brain, neurological, bone and
liver damage
Cancers, kidney and liver
damage, impairment of the
nervous system resulting in
sleepiness and headaches,
leukemia
Various effects ranging from
nausea to nervous disorders.
Dioxin is a common by-product
of the manufacture of pesti-
cides and is both highly toxic
and a suspected carcinogen.
Cancer and liver damage.
Cancers and skin ulcerations
with prolonged exposure
Cancer
Sources:
Toxic Chemicals—What They Are, How They Affect You (EPA, Region 5)
Glossary of Environmental Terms (EPA, 1988)
'The potential for risk due to these contaminants is linked to a number of factors; for example, the length and level of exposure
and environmental and health factors such as age.
*U.S. G.P.O.: 1993-341-835:81030
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