LvEPA
      United States
      Environmental Protection
      Agency
Solid Waste And
Emergency Response
(5102G)
SUPERFUND:
EPA/540/R-93/045
December 1992
PB93-963247
                      Progress at
                      National
                      Priority
                      List Sites
    WEST VIRGINIA
      1992 UPDATE
• nntt'd on Recyrled Paper

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                                        Publication #9200.5-7476
                                              December 1992
     NATIONAL PRIORITIES LIST SITES:
                 West Virginia
UNITED STATES ENVIRONMENTAL PROTECTION AGENCY
       Office of Emergency & Remedial Response
            Office of Program Management
               Washington, DC 20460
                                   U s Environmental Protection Agency

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If you wish to purchase copies of any additional State volumes, contact:


                  National Technical Information Service (NTIS)
                         U.S. Department of Commerce
                            5285 Port Royal Road
                             Springfield, VA 22161
                                (703) 486-4650


The complete set of the 49 State reports may be ordered as PB93-963250.

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        TABLE OF CONTENTS
INTRODUCTION
   A Brief Overview of Superfund	v
   Streamlining Superfund: The Superfund Accelerated Cleanup Model	ix
   How Superfund Works	x


THE VOLUME
   How to Use the State Book	xi
A SUMMARY OF THE STATE PROGRAM
.XV
THE NPL REPORT
    Progress to Date	xix
THE NPL FACT SHEETS                      i
THE GLOSSARY
    Terms used in the NPL Book	G-l

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                     INTRODUCTION
           A BRIEF OVERVIEW OF SUPERFUND
      During the second half of the Twentieth
      Century, the environmental conse-
quences of more than 100 years of industrial-
ization in the United States became increas-
ingly clear. Authors such as Rachel Carson
wrote passionately about the often-hidden en-
vironmental effects of our modern society's
widespread use of chemicals and other haz-
ardous materials. Their audience was small at
first, but gradually their message spread.
Growing concern turned to action, as people
learned more about the environment and be-
gan to act on their knowledge

The 1970s  saw environmental issues burst
onto the national  scene and take hold in the
national consciousness. The first Earth Day
was observed in 1970, the year that the U.S.
Environmental Protection Agency (EPA) was
founded. By the end  of the 1970s, Love Canal
in New York and the Valley of the Drums in
Kentucky had entered the popular lexicon as
synonyms for pollution and environmental
degradation.
Superfund Is Established

The industrialization that gave Americans the
world's highest standard of living also created
problems that only a national program could
address. By 1980, the U.S. Congress had
passed numerous environmental laws, imple-
mented by the EPA, but many serious hazard-
ous waste problems were slipping through the
cracks.

Responding to growing concern about public
health and environmental threats from uncon-
trolled releases of hazardous materials, the
U.S. Congress passed the Comprehensive En-
vironmental Response, Compensation, and
Liability Act (CERCLA). Popularly known as
Superfund, CERCLA had one seemingly
simple job—to uncover and clean up hazard-
ous materials spills and contaminated sites.
A Big Job

Few in Congress, the EPA, the environmen-
tal community, or the general public knew in
1980 just how big the nation's hazardous ma-
terials problem is. Almost everyone thought
that Superfund would be a short-lived pro-
gram requiring relatively few resources to
clean up at most a few hundred sites. They
were quite mistaken.

As the EPA set to work finding sites and
gauging their potential to harm people and
the environment, the number of sites grew.
Each discovery seemed to lead to another,
and today almost 36,000 hazardous waste
sites have been investigated as potential haz-
ardous waste  sites. They are catalogued in
the EPA's computerized database, CERCLIS
(for the Comprehensive Environmental Re-

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INTRODUCTION
sponse, Compensation, and Liability Informa-
tion System).

The damage to public health and the environ-
ment that each site in CERCLIS might cause
is evaluated; many sites have been referred to
State and local governments for cleanup. The
EPA lists the nation's most serious hazardous
waste sites on the National Priorities List, or
NPL.  (These Superfund sites are eligible for
federally-funded cleanup, but whenever pos-
sible the EPA makes polluters pay for the
contamination they helped create.) The NPL
now numbers 1,275 sites, with 50 to 100
added each year. By the end of the century,
the NPL may reach as many as 2,100 sites.

Superfund faces some of the most complex
pollution problems ever encountered by an
environmental program. Improperly stored or
disposed chemicals and the soil they contami-
nate are one concern. More difficult to correct
are the wetlands and bays, and the groundwa-
ter, lakes, and rivers often used for drinking
water that are contaminated by chemicals
spreading through the soil or mixing with
storm water runoff. Toxic vapors contaminate
the air at some sites, threatening the health of
people living and working near by.

Superfund aims to control immediate public
health and environmental threats by tackling
the worst problems at the worst sites first.
Wherever possible, Superfund officials use
innovative treatment techniques—many de-
veloped or refined by the EPA—to correct
hazardous materials problems once and for
all. Many of the treatment techniques they use
did not exist when the program was created.

The EPA Administrator had challenged Su-
perfund to complete construction necessary
for cleanup work at 130 NPL sites by the end
of the 1992 federal fiscal year. By September
30, 1992, the end of fiscal year 1992, con-
struction had been completed at a total of 149
NPL sites. Superfund is well on its way of
meeting the Administrator's goal of complet-
ing construction at 200 NPL sites by the end
of fiscal year 1993, and 650 sites by the end
of fiscal year 2000.
Quick Cleanup at
Non-NPL Sites

Long-standing hazardous waste sites are not
Superfund's only concern. The EPA also re-
sponds to hazardous spills and other emergen-
cies, hauling away chemicals for proper treat-
ment or disposal. Superfund teams perform or
supervise responses at rail and motor vehicle
accidents, fires, and other emergencies in-
volving hazardous substances. They also
evacuate people living and working near by,
if necessary, and provide clean drinking water
to people whose own water is contaminated.
Removal crews also post warning signs and
take other precautions to keep people and ani-
mals away from hazardous substances.
                                             Superfund employee prepares equipment for groundwater
                                             treatment.
                                           VI

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                                                              INTRODUCTION
Quick Cleanups, or Removals, are not limited
to emergencies. When cleanup crews at con-
taminated sites find hazardous substances that
immediately threaten people or the environ-
ment, they act right away to reduce the threat
or to remove the chemicals outright.  As the
EPA implements the Superfund Accelerated
Cleanup Model (SACM), more and more sites
will undergo quick cleanups, and many of
these will be cleaned up completely without
ever being included on the NPL. (See
"Streamlining Superfund: The Superfund Ac-
celerated Cleanup  Model.")

Some of Superfund's most significant gains in
public health and environmental protection
have been won by  the removal program. As of
March 31,1992, the Emergency Response
Superfund employee removing drums from a Superfund site.

Program had logged more than 2,300 removal
completions since Superfund was established.
The Public's Role

Superfund is unique among federal programs
in its commitment to citizen participation. Al-
though the EPA is responsible for determin-
ing how dangerous a site is and how best to
clean it up, the Agency relies on citizen input
as it makes these decisions.

Community residents are often invaluable
sources of information about a hazardous
waste site, its current and previous owners,
and the activities that took place there. Such
information can be crucial to experts evaluat-
ing a site and its potential dangers.

Residents also comment on EPA cleanup
plans by stating their concerns and prefer-
ences at public meetings and other forums and
in formal, written comments to Agency pro-
posals. The EPA takes these comments and
concerns seriously, and has modified many
proposals in response to local concerns. For,
ultimately, it is the community and its citizens
that will live with the results of the EPA's de-
cisions and actions; it is only fair that citizens
participate in the process.
A Commitment to
Communication

The Superfund program is very serious about
public outreach and communication. Com-
munity relations coordinators are assigned to
each NPL site to help the public understand
the potential hazards present, as well as the
cleanup alternatives. Local information re-
positories, such as libraries or other public
buildings, have been  established near each
NPL site  to ensure that the public has an op-
portunity to review all relevant information
and the proposed cleanup plans.

The individual State volumes contain sum-
mary fact sheets on NPL sites in each State
and territory. Together, the fact sheets provide
a concise report on site conditions and the
progress made toward site cleanups as of
March  1992. The EPA revises these volumes
periodically to provide an up-to-date record of
program activities. A  glossary of key terms
relating to hazardous  waste management and
Superfund site cleanup is provided at the back
of this book.
                                          VII

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INTRODUCTION
Superfund is, of course, a public program, and
as such it belongs to everyone of us. This vol-
ume, along with other State volumes, com-
prises the EPA's report on Superfund
progress to the program's owners for the year
1992.
                                         VIII

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                                                           INTRODUCTION
  STREAMLINING SUPERFUND: THE SUPERFUND
             ACCELERATED CLEANUP MODEL
      Historically, critics and supporters alike
      have measured Superfund's progress
by the number of hazardous waste sites de-
leted from the NPL. Although easy enough to
tally, this approach is too narrow. It misses
the major gains Superfund makes by reducing
major risks at the nation's worst hazardous
sites long before all clean-up work is done
and the site deleted. It also ignores the Re-
moval Program's contributions to meeting
Superfund's twin mandates of maximizing
public health and environmental protection.

Renewing Superfund's commitment to rapid
protection from hazardous materials, the EPA
is streamlining the program. The Superfund
Accelerated Cleanup Model, or SACM, will
take Early Actions, such as removing hazard-
ous wastes or contaminated materials, while
experts study the site. SACM also will com-
bine similar site studies to reduce the time re-
quired to evaluate a site and its threats to
people and the environment. This way, imme-
diate public health and environmental threats
will be addressed while long-term cleanups
are being planned.

Emergencies such as train derailments and
motor vehicle accidents will continue to be
handled expeditiously. Teams of highly
trained technicians will swing into action
right away, coordinating the cleanup and re-
moval of hazardous substances to ensure pub-
lic safety as quickly as possible.

Breaking With Tradition

The traditional Superfund process begins with
a lengthy phase of study and site assessment,
but SACM will save time by combining sepa-
rate, yet similar, activities. Each EPA Region
will form a Decision Team of site managers,
risk assessors, community relations coordina-
tors, lawyers, and other experts to monitor the
studies and quickly determine whether a site
requires Early Action (taking less than five
years), Long-term Action, or both.

While the site studies continue, the Decision
Team will begin the short-term work required
to correct immediate public health or environ-
mental threats from the site. Besides remov-
ing hazardous materials, Early Actions in-
clude taking precautions to keep contaminants
from moving off the site and restricting access
to the site. Early Actions could eliminate most
human risk from these sites, and Superfund
will further focus its public participation and
public information activities on site assess-
ment and Early  Action.

Long-Term Solutions

While Early Actions can correct many hazard-
ous waste problems—and provide the bulk of
public health and environmental protection—
some contamination will take longer to cor-
rect. Cleanups of mining sites, wetlands, estu-
aries, and projects involving incineration of
contaminants or restoration of groundwater
can take far longer than the three to five years
envisioned for Early Actions.  Under SACM,
these sites will be handled much as they are
now.

Also under SACM, the EPA will continue its
pursuit of potentially responsible parties who
may have caused or contributed to site con-
tamination. Expedited enforcement  and
procedures for negotiating potentially respon-
sible party settlements will secure their par-
ticipation. Superfund personnel will continue
to oversee clean-up work performed by poten-
tially responsible parties.
                                        IX

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INTRODUCTION
                    HOW SUPERFUND WORKS
     Each Superfund site presents a different
     set of complex problems. The same haz-
ardous materials and chemicals often con-
taminate many sites, but the details of each
site are different. Almost always, soil is con-
taminated with one or more chemicals. Their
vapors may taint the air over and around the
site. Contaminants may travel through the soil
and reach underground aquifers which may be
used for drinking water, or they may spread
over the site to contaminate streams, ponds,
and wetlands. The contaminating chemicals
may interact with each other, presenting even
more complicated cleanup problems.

Superfund's cleanup process is arduous and
exacting. It requires the best efforts of hun-
dreds of experts in science and engineering,
public health, administration and manage-
ment, law, and many other fields.

The average NPL site takes from seven to ten
years to work its way through the system,
from discovery to the start of long-term
cleanup. Actual  cleanup work can take years,
decades if contaminated groundwater must
be treated. Of course, imminent threats to
public health or  the environment are cor-
rected right away.

The diagram to the right presents a simplified
view of the cleanup process. The major steps
in the Superfund process are:

  • Site discovery and investigation to iden-
   tify contaminants and determine whether
   emergency action is required;

  • Emergency site work such  as removing
   contaminants for proper treatment or dis-
   posal, and securing the site to keep people
   and animals away, if warranted by condi-
   tions at the site;

  • Site evaluation to determine how people
   living and working nearby, and the envi-
   ronment, may be exposed to site contami-
   nants;
 • Detailed studies to determine whether con-
  ditions are serious enough to add the site to
  the National Priorities List of sites eligible
  for federally funded cleanup under Super-
  fund;

 • Selection, design, and implementation of a
  cleanup plan, after a thorough review of
  the most effective cleanup options, given
  site conditions, contaminants present, and
  their potential threat to public health or the
  environment.

 • Follow-up to ensure that the cleanup work
  done at the site continues to be effective
  over the long term.
  The Superfund Process
From the earliest stages, EPA investigators
work hard to identify those responsible for the
contamination. As their responsibility is es-
tablished, the EPA negotiates with these "re-
sponsible parties" to pay for cleaning up the
problem they helped create. This "enforce-
ment first" policy saves Superfund Trust Fund
monies for use in cleanups where the respon-
sible parties cannot be identified,  or where
they are unable to fund cleanup work.

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                          THE VOLUME
                    How to Use the State Book
     The site fact sheets presented in this book
     are comprehensive summaries that cover
a broad range of information.  The fact sheets
describe hazardous waste sites on the NPL and
their locations, as well as the conditions
leading to their listing ("Site Description").
The summaries list the types of contaminants
that have been discovered and related threats
to public and ecological health ("Threats and
Contaminants"). "Cleanup Approach" pres-
ents an overview of the cleanup activities
completed,  underway, or planned. The fact
sheets conclude with a brief synopsis of how
much progress has been made in protecting
public health and the environment. The
summaries also pinpoint other actions,  such as
legal efforts to involve polluters responsible
for site contamination and community con-
cerns.

The fact sheets are arranged in alphabetical
order by site name.  Because site cleanup is a
dynamic and gradual process, all site informa-
tion is accurate as of the date shown on the
bottom of each page. Progress always is being
made at NPL sites, and the EPA periodically
will update the site fact sheets to reflect recent
actions and will publish updated State vol-
umes. The following two pages show a ge-
neric fact sheet and briefly describe the infor-
mation under each section.
How Can You Use
This State Book?
You can use this book to keep informed about
the sites that concern you, particularly ones
close to home.  The EPA is committed to
involving the public in the decision making
process associated with hazardous waste
cleanup. The Agency solicits input from area
residents in communities affected by Super-
fund sites. Citizens are likely to be affected
not only by hazardous site conditions, but also
by the remedies that combat them. Site clean-
ups take many forms and can affect communi-
ties in different ways. Local traffic may be
rerouted, residents may be relocated, tempo-
rary water supplies may be necessary.

Definitive information on a site can help
citizens sift through alternatives and make
decisions.  To make good choices, you must
know what the threats are and how the EPA
intends to clean up the site. You must under-
stand the cleanup alternatives being proposed
for site cleanup and how residents may be
affected by each one.  You also need to have
some idea of how your community intends to
use the site in the future, and you need to know
what the community can realistically expect
once the cleanup is complete.

The EPA wants to develop cleanup methods
that meet community needs, but the Agency
only can take local concerns into account if it
understands what they are.  Information must
travel both ways in order for cleanups to be
effective and satisfactory.  Please take this
opportunity to learn more, become involved,
and assure that hazardous waste cleanup at
"your" site considers your community's
concerns.
                                           XI

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THE VOLUME
   NPL LISTING HISTORY

 Provides the dates when the
 site was Proposed, made Final,
 and Deleted from the NPL.
   SITE RESPONSIBILITY

  Identifies the Federal, State,
  and/or potentially responsible
  parties taking responsibility
  for cleanup actions at the site.
      ENVIRONMENTAL
          PROGRESS

  Summarizes the actions to
  reduce the threats to nearby
  residents and the surrounding
  environment and the progress
  towards cleaning up the site.
  SITE NAME
  STATE
  EPA ID# ABCOOOOOOO
                                 Site Description
                                   EPA REGION XX
                                      COUNTY NAME
                                       LOCATION

                                      Other Names:
                                         : xxxxxxxxxx xxxx xxxxxxxx xxxx xx xxxxxxxxx xx xxxxxx xxxxx
  xxxxxxxxxxxx xxxxx



  Site Responsibility:

  Threats and Contaminants
                                 xxxx xxxx xxxxx xxxxxxx
                                 Cleanup Approach
                                 XXXXXX XXX XXXXX XXXXXX3CXXXXX XXXXXX XXXXXXXXX XXXXXXXX XXXXXXXXXXXXX XXXXX:

                                 XXXXXXXXXXXXX XXXXXXXXXJt XXXX XXXXXXXX XXXX XX XXXXXXXXX XX XXXXXX XXXXXXXX
                                 Response Action Status
  Site Facts:

  XXXXX XI
^^HXxxxx:

  Environmental Progress
:xx xxxxxxxxxxxxx xxxxxxxxxx xxxx xxxxxxxx xxxx xx xxxxxxxxx xx xx:

                                 Site Repository
                                 xxxxxx xxx xxxxx xxxxxxxx
                                                          SITE REPOSITORY

                                         Lists the location of the primary site repository. The site
                                         repository may include community relations plans, public
                                         meeting announcements and minutes, fact sheets, press
                                         releases, and other site-related documents.
                                                 XII

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                                                    THE VOLUME
                         SITE DESCRIPTION

This section describes the location and history of the site. It includes descrip-
tions of the most recent activities and past actions at the site that have con-
tributed to the contamination. Population estimates, land usages, and nearby
resources give readers background on the local setting surrounding the site.
                   THREATS AND CONTAMINANTS

The major chemical categories of site contamination are noted, as well as
which environmental resources are affected. Icons representing each of the
affected resources (may include air, groundwater, surface water, soil, and
contamination to environmentally sensitive areas) are included in the margins
of this section. Potential threats to residents and the surrounding environ-
ments arising from the site contamination also are described.
                        CLEANUP APPROACH

This section contains a brief overview of how the site is being cleaned up.
                     RESPONSE ACTION STATUS

Specific actions that have been accomplished or will be undertaken to clean
up the site are described here. Cleanup activities at NPL sites are divided
into separate phases, depending on the complexity and required actions at the
site.  Two major types of cleanup activities often are described: initial,
immediate, or emergency actions to quickly remove or reduce imminent
threats to the community and surrounding areas; and long-term remedial
phases directed at final cleanup at the site.  Each stage of the cleanup strategy
is presented in this section of the summary. Icons representing the stage of
the cleanup process (initial actions, site investigations, EPA selection of the
cleanup remedy, engineering design phase, cleanup activities underway, and
completed cleanup) are located in the margin next to each activity descrip-
tion.
                             SITE FACTS

Additional information on activities and events at the site are included in this
section. Often details on legal or administrative actions taken by the EPA to
achieve site cleanup or other facts pertaining to community involvement with
the site cleanup process are reported here.

                          xiii

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THE VOLUME
The "icons," or symbols, accompanying the text allow the reader to see at a glance which envi-
ronmental resources are affected and the status of cleanup activities at the site.
   Icons in the Threats
     and  Contaminants
             Section
       Contaminated Groundwater resources
       in the vicinity or underlying the site.
       (Groundwater is often used as a drink-
       ing water source.)

       Contaminated Surface Water and
       Sediments on or near the site.  (These
       include lakes, ponds, streams, and
       rivers.)

        Contaminated Air in the vicinity of
        the site. (Air pollution usually is
        periodic and involves contaminated
        dust particles or hazardous gas emis-
        sions.)

       Contaminated Soil and Sludges on or
       near the site. (This contamination
       category may include bulk or other
       surface hazardous wastes found on the
       site.)

       Threatened or contaminated Environ-
       mentally Sensitive Areas in the vicinity
       of the  site.  (Examples include wet-
       lands and coastal areas or critical
       habitats.)
Icons in the Response
Action Status Section
       Initial, Immediate, or Emergency
       Actions have been taken or are
       underway to eliminate immediate
       threats at the site.

      Site Studies at the site to determine
      the nature and extent of contamination
      are planned or underway.

     Remedy Selected indicates that site
     investigations have been concluded,
     and the EPA has selected a final
     cleanup remedy for the site or part of
     the site.

       Remedy Design means that engineers
       are preparing specifications and
       drawings for the selected cleanup
       technologies.

      Cleanup Ongoing indicates that the
      selected cleanup remedies for the
      contaminated site, or part of the site,
      currently are underway.

       Cleanup Complete shows that all
       cleanup goals have been achieved for
       the contaminated site or part of the
       site.
                                        XIV

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A SUMMARY OF THE STATE PROGRAM
             xv

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                                          Superfund
                                          Activities in
                                          West Virginia
                                    The State of West Virginia is located within EPA
                              Region 3, which includes the five mid-Atlantic States and
                            the District of Columbia. The State covers 24,232 square
                         miles. According to the 1990 Census, West Virginia experienced
                       an 8 percent decrease in population between 1980 and 1990, and is
                     ranked thirty-fourth in U.S. population with approximately 1,797,000
                   residents.
      The Hazardous Waste Emergency Response Fund Act provides funding for emergency
response actions. The statute limits State authority to cost recovery from polluters who fail to
conduct site cleanup and collection of interest from unpaid or late generator fees. Additional
enforcement actions may be taken pursuant to the State equivalent of the Federal Resource,
Conservation, and Recovery Act (RCRA). In practice, the State attempts to secure an agreement
from the polluter to pay cleanup and remedial action costs. In addition to the 10 percent contri-
bution required from the State under the Federal Superfund program, the State Fund provides for
emergency response, site investigation, and operation and maintenance activities relating only to
hazardous wastes, not hazardous substances. The Fund also may be used for studies, design
activities, and other cleanup preparations as long as the Fund balance remains above $1,000,000.
Currently, five sites in the State of West Virginia have been listed as final on the NPL. No new
sites have been proposed for listing in 1992.

         The Department of Commerce, Labor, and Natural Resources
          implements the Superfund Program in the State of West Virginia
Activities responsible for hazardous
waste contamination in the State of
West Virginia include:
    Pesticides
    Manufacturers
 Chemical
Production
 Facilities
 Manufacturing
 Facilities
                  Federal Facilities
Facts about the five NPL sites
in West Virginia:

        Immediate Actions (such as removing
        hazardous substances or restricting
        site access) were performed at four
        sites.
                                                One site endangers sensitive environ-
                                                ments.
                 Four sites are located near residential
                 areas.
                                      XVII
                                                                       March 1992

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WEST VIRGINIA
Most Sites Have Multiple Contaminants and
Contaminated Media:
Media Contaminated at Sites
Air


Surface
Water

Sediments
Soil


Ground-
water
       OE+O 10  20 30  40  50 60  70 80  90 100

               Percentage of Sites
     Contaminants Found at Sites
Percentage of Sites
Heavy Metals
VOCs
Creosotes
Dioxin
Pesticides/Herbicides
Petrochemicals/Explosives
60%
40%
40%
20%
20%
20%
The Potentially Responsible
Party Pays...
In the State of West Virginia, potentially re-
sponsible parties are paying for or conducting
cleanup activities at four sites.
           For Further Information on NPL Sites and
        Hazardous Waste Programs in the State of West
          	Virginia Please Contact:	^^
      EPA Region 3 Environmental
      Education and Outreach Branch

      National Response Center
      The Department of Commerce,
      Labor, and Natural Resources:
      Waste Management Section, Site
      Investigation and Response Office

      EPA Region 3 Site Assessment
      Section

      EPA Superfund Hotline
For Information concerning
community involvement

To report a hazardous
waste emergency

For information about the
State's responsibility in the
Superfund Program
For information about the
Regional Superfund Program

For information about the
Federal Superfund Program
(215) 597-9370



(800} 424-8802



(304) 558-2745





(215) 597-8229



(800) 424-9068
 March 1992
  xviii

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                    THE NPL  REPORT
                         PROGRESS TO DATE
     The following Progress Report lists all
     sites currently on, or deleted from, the
NPL and briefly summarizes the status of ac-
tivities for each site at the time this report was
prepared. The steps in the Superfund cleanup
process are arrayed across the top of the chart,
and each site's progress through these steps is
represented by an arrow (O) indicating the
current stage of cleanup.

Large and complex sites often are organized
into several cleanup stages.  For example,
separate cleanup efforts may be required to
address the source of the contamination,
hazardous substances in the groundwater, and
surface water pollution, or to clean up differ-
ent areas of a large site.  In such cases, the
chart portrays cleanup progress at the site's
most advanced stage, reflecting the status of
site activities rather than administrative ac-
complishments.

   O An arrow in the "Initial Response" cate-
     gory indicates that an emergency
     cleanup, immediate action,  or initial ac-
     tion has been completed or currently is
     underway.  Emergency or initial actions
     are taken as an interim measure to pro-
     vide immediate relief from exposure to
     hazardous site conditions or to stabilize
     a site to prevent further contamination.

   O A final arrow in the "Site Studies" cat-
     egory indicates that an investigation to
     determine the nature and extent of the
     contamination at the site currently is on-
     going or planned.

   O A final arrow in the "Remedy Selection"
     category means that the EPA has se-
     lected 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 contamination will
     be naturally dispersed without further
     cleanup activities, a "No Action" rem-
     edy has been selected. In these cases,
     the aiTows are discontinued at the
     "Remedy Selection" step and resume in
     the "Construction Complete" category.

  ^ A final arrow at the "Remedial Design"
     stage indicates that engineers currently
     are designing the technical specifica-
     tions for the selected cleanup remedies
     and technologies.

  ^ A final arrow in the "Cleanup Ongoing"
     column means that final cleanup actions
     have been started at the site and cur-
     rently are  underway.

  O A final arrow in the "Construction Com-
     plete" category is used only when all
     phases of the site cleanup plan have
     been performed, and the EPA has deter-
     mined that no additional construction
     actions are required at the site. Some
     sites in this category currently may be
     undergoing long-term operation and
     maintenance or monitoring to ensure
     that the cleanup actions continue to pro-
     tect human health and the environment.

  / A check in the "Deleted" category indi-
     cates that the site cleanup has met all
     human health and environmental goals
     and that the EPA has deleted the site
     from the NPL.

Further information on the activities and
progress at each site is given in the site "Fact
Sheets" published in this volume.
                                         XIX

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FIKE  CHE
INC.
WEST VIRGINIA
EPA ID# WVD0479892I
  EPA REGION 3
Kanawha and Putnam Counties
 itro Industrial Complex in Nitro
      Other Names:
    Fike Chemical/Artel
        Artel Site
Site Description
The 12-acre Fike Chemical, Inc. site consists of Fike Chemicals, Inc. (now Artel Chemicals)
and the Cooperative Sewage Treatment, Inc. (CST) property, which is a facility designed to
treat Pike's stormwater and wastewater. The Fike Chemical plant was a small volume batch
formulator that specialized in the development of over 60 chemicals, custom chemical
processing, and specialty chemicals. The plant was purchased by Artel Chemical in 1986 and
was subsequently abandoned in 1988. Site activities leading to contamination include improper
storage of drums containing hazardous substances, on-site disposal of hazardous wastes
through drum burial and unlined surface lagoons, and tank storage of various chemical stock,
products, and wastes. Treated water from the CST property is discharged into the Kanawha
River. Approximately 8,000 people live within a 1-mile radius of the site, and an estimated
25,000 people live within a 10-mile radius of the industrial complex.
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
         The groundwater and soil are contaminated with various organic compounds from
         the chemical plant's process wastes. Dioxin has been detected in on-site soils.
         There is a potential for release of volatile chemicals into the air that would pose
         risks if inhaled. Potential human health threats exist if contaminated groundwater
         or soil is accidentally ingested. The Kanawha River, located 2,000 feet east of the
         site, is threatened by contaminated runoff from the plant.
                                                                         March 1992

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Cleanup Approach
This site is being addressed in six stages: immediate actions and five long-term remedial
phases focusing on removal of tanks, drums, and other materials; cleanup of the process plant
equipment and chemicals; cleanup of buried containers; cleanup of the soil, sludge, and
groundwater; and cleanup of the wastewater treatment facility. Additional phases will be
added as needed as the cleanup process continues.
Response Action Status
           Immediate Actions: In June 1988, the EPA initiated an emergency cleanup
           action to address immediate threats posed by the site. By 1988, immediate
           threats had been eliminated.

          Tanks, Drums, and Other Materials: Additional activities to address
          contaminated materials on site currently are underway and are expected to be
          completed in late 1992. These activities include: removal, off-site incineration, and
disposal of the contaminated contents of a tank; removal of drums and other containers to
EPA-approved disposal facilities; operation of an on-site water treatment facility; and removal
and disposal of cyanides. The parties potentially responsible for site contamination have
assisted in certain cleanup tasks.

           Process Plant Equipment and Chemicals: A  study addressing process plant
           equipment and associated chemicals was completed in 1990, when the EPA
           selected  a remedy of dismantling, decontamination, and removal of the facility.
Design work for the cleanup activities began in early 1992.

           Buried  Containers:  In 1992, the remedy to clean up the buried containers at
           the site was selected.  The buried containers will be excavated  and their contents
           will be incinerated.  Design work for the cleanup activities is expected to begin in
1993.

          Soil, Sludge, and  Groundwater: A study to determine the extent and nature of
          contamination and to identify alternatives for addressing contaminated soil, sludge,
          and groundwater is underway. The first phase of the investigation has been
completed including installation of wells and soil sampling.  The second phase of the study is
expected to begin soon.  Once  the investigation is completed,  alternative cleanup options will
be selected.

          Wastewater Treatment Facility:  Once contaminants have  been addressed
          through the on-site wastewater treatment facility, a plan will be put in place to
          dismantle the facility.
March 1992                                 2                          FIKE CHEMICAL, INC.

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Environmental Progress
By removing surface drums, tank contents, and other containers, the EPA, with assistance
from the potentially responsible parties, has eliminated immediate threats to the surrounding
area while final studies and cleanup activities are undertaken at the Fike Chemical, Inc. site.
Site Repository
Nitro Public Library, 1700 Park Avenue, Nitro, WV 25143
FIKE CHEMICAL, INC.
March 1992

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FOLLANSBEE
SITE
WEST VIRGINIA
EPA ID# WVD004336749
 EPA REGION 3
     Brooke County
 1/4 mile from Follansbee

     Other Names:
  Irs Disposal Site Coketown
 Koppers Chemical Co.
 Koppers Industries, Inc.
Wheeling Pittsburgh Steel
Site Description
The Follansbee site covers 26 1/2 acres on the Ohio River in Follansbee. The site is an
operating coal tar processing plant owned by Koppers Industries, Inc. and consists of process
and storage facilities for the manufacture of coal tar by-products. Koppers acquired the site
from American Tar Products, the operators of the facility from 1914 to 1926. In 1929, a tar
pitch plant was built, and in the 1930s, a caustic plant was installed. A pencil pitch plant was
built in 1962 to convert liquid pencil pitch to solid pitch. There also is a wastewater treatment
plant on site. Contamination of the site potentially is due to leaking tanks, spills, surface
impoundments, and poor operation cleanup practices. Numerous springs and seeps are in the
area. There are an estimated 5,900 people living within a 3-mile radius of the site. Fifty
private residential water supply wells are within the 3-mile radius, and there are public wells
located 5 miles downstream that may be affected by this site, although limited data  exists.
The site is underlain by three aquifers, two of which are contaminated.
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
         Two of the three aquifers are contaminated with polycyclic aromatic hydrocarbons
         (PAHs), volatile organic compounds (VOCs) such as benzene and toluene, and
         metals. Surface water springs and riverbank seeps are contaminated with phenols.
         Potential health risks exist from drinking or coming in direct contact with
         contaminated groundwater and surface water. The Ohio River could be a threat to
         those who use it for recreational purposes or as a source for domestic water
         supplies. However, the effect of the site on the Ohio River has yet to  be assessed.
                                                                         March 1992

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Cleanup Approach
The site is being addressed in two stages: initial actions and a single long-term remedial phase
directed at cleanup of the entire site.
Response Action Status
           Initial Actions: The EPA conducted a field investigation at the site in 1982,
           resulting in its inclusion on the NPL. In 1983, Koppers installed a trench to
           intercept contaminated groundwater. The groundwater is pumped to the
company's wastewater treatment facility. The company installed a second pump in an attempt
to prevent the contaminated groundwater from reaching the Ohio River, as well as to control
the groundwater flow.

          Entire Site: Based on the results from the alluvial aquifer study conducted by
          Koppers, the EPA and Koppers agreed that an evaluation of the site is needed to
          determine the extent of the contamination at the site and to identify alternative
technologies for cleanup. Koppers has submitted a revised plan for the schedule and
objectives of the study to EPA. The investigation began in 1990; however, the Resource
Conservation and Recovery Act (RCRA) program acquired the lead on the site because it is
an active facility.

Site Facts: A Consent Decree was signed in August 1984, between the EPA, Koppers, and
Wheeling-Pittsburgh Steel, with the State of West Virginia as intervenor. The Consent
Decree called for: paving of Kopper's property; installation of five recovery wells on Kopper's
property to eliminate seepage from Koppers to the Wheeling-Pittsburgh Steel coal pits and to
prevent future groundwater contamination; and Koppers to conduct an alluvial aquifer study.
On September 27, 1990, Koppers and the EPA signed an Administrative Order on Consent,
placing site cleanup responsibility under the RCRA program.
Environmental Progress
Various measures have been taken to eliminate the spread of contamination in the
groundwater and to the Ohio River. The EPA has evaluated the Follansbee Site and
determined that conditions at the site do not pose an immediate threat while the
investigations leading to the selection of a final cleanup remedy are taking place.
FOLLANSBEE SITE                           5                                 March 1992

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Site Repository
Follansbee City Building, Main and Penn Streets, Follansbee, WV 26037
March 1992                                6                          FOLLANSBEE SITE

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LEETOWN  PESTCIDE             ^PA REGION 3
WEST VIRGINIA/   f.Vv  i    .^r^  8 miles south of Martinsbur9
EPA ID# WVD980693#fe  °  JSIPyV^O^       Other Names:
                                                           Robinson Property
Site Description
Leetown Pesticide is a 1-acre site that contains three specific areas that have been
contaminated by the agricultural use of pesticides, pesticide disposal, and landfilling. These
three areas are the former Pesticide Pile Area, the former Jefferson Orchard Mixing Area,
and the former Crimm Orchard Packing Shed. The former Pesticide Pile Area allegedly
resulted from the disposal of pesticide-contaminated debris from a 1975 chemical plant fire.
Debris  from the fire had been landfarmed in a pasture as donated "soil conditioners" to local
farms. The pasture currently is not in use. The Jefferson Orchard Mixing Area was used to
prepare pesticides during  active operation of the orchard. The orchard was abandoned during
the late 1950s or early 1960s. When the Crimm Orchard was in operation, the packing shed
was used to process the fruit crop and to  mix pesticides. Portions of the watershed areas for
the Bell Spring Run and Blue and Gray Spring Run are on the site. There are a number of
private residences in the area that rely on groundwater wells for drinking water.
Approximately 140 people live within a mile of the site. Land use in the area is predominantly
agricultural, dedicated to  pasture or forage crop production for dairy cattle operations.
Site Responsibility:  This site is being addressed through a       NPL LISTING HISTORY
                     combination of Federal, State, and
                     potentially responsible parties' actions.
Proposed Date: 12/01/82
  Final Date: 09/01/83
Threats and Contaminants
         Sediment from Bell Creek Run and Link Spring Run contained detectable
         concentrations of the pesticide DDT from former site activities. Soil in the
         pesticide pile area contained DDT, arsenic, and lead. The pesticide mixing area
         and Crimm Orchard Packing Shed soils also contained DDT, along with
         endosulfan, another pesticide. Since the removal of wastes and contaminated soils
         in 1983, the threats posed by DDT are within the EPA's acceptable risk range.
         The arsenic and lead contamination was caused by the spraying of lead arsenate
         during the active operations of the orchard and not from disposal operations.
                                                                          March 1992

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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.
Response Action Status
           Immediate Actions: In 1983, under the guidance of the EPA and the State, a
           party potentially responsible for the site contamination removed and disposed of a
           contaminated pile consisting of 160 cubic yards of waste and soil.

          Entire Site: In 1986, cleanup technologies were selected to address contamination
          including: dismantling and removing contaminated materials; excavating and
          consolidating of 3,600 cubic yards of contaminated soil from the former Pesticide
Pile Area, the former Jefferson Orchard Mixing Area, and the former Crimm Packing Shed
Area; placing contaminated soils in a specially constructed treatment bed; and constructing
surface water diversion, sedimentation channels, and diversion dikes. In 1988, a packing shed
containing broken bags of DDT was dismantled and contaminated flooring, a spray wagon,
and drums of pesticide were removed.  A soil cap was placed over the shed area after
contaminants were disposed of in a licensed hazardous waste facility. In 1992, the EPA re-
evaluated the site and determined that the soils no longer posed an unacceptable risk.
Therefore, it was concluded that no additional actions were necessary to clean up the site.
Environmental Progress
The removal of contaminated materials from the Leetown Pesticide site and the safe
destruction and subsequent capping of a packing shed have reduced the potential for
exposure to contaminants at the site.
Site Repository
Old Charles Town Library, 200 East Washington Street, Charles Town, WV 25414
March 1992
LEETOWN PESTICIDE

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ORDNANCE WO
DISPOSAL ARE
WEST VIRGINIA
EPA ID# WVD000850
  EPA REGION 3
    Monongalia County
 mile southeast of Morgantown

      Other Names:
Morgantown Ordnance Works
Site Description
The 826-acre Ordnance Works Disposal Areas site is located on the west bank of the
Monongahela River. Many private companies have operated chemical manufactories here
since 1941, when E.I. Du Pont de Nemours began producing ammonia and methanol for the
Department of War. Between 1946 and 1958, Sharon Steel operated a coke plant, Heyden
Chemical operated an ammonia production facility, and Olin Mathieson produced various
organic chemicals on the site. The site was sold in 1962 to Morgantown Ordnance Works
and, in 1982, to Morgantown Industrial Park. Disposal of contaminated materials from the
manufacturing process has been noted in several locations including a landfill, a scraped area,
a former lagoon area,  three streams traversing the site, and an industrial area in the northern
portion of the site. Testing has shown contamination of these spots with heavy metals and
polycyclic aromatic hydrocarbons (PAHs). The site is in the rural outskirts southwest of
Morgantown; the population within a mile is only 100. The Monongahela River supplies
drinking water to approximately 60,000 residents, and the water intake is less than a mile
downstream of the site.
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
Threats and Contaminants
         Sediments and soil adjacent to the landfill, scraped area, and the former lagoon
         area are contaminated with heavy metals and PAHs from surface runoff. Potential
         health hazards include accidentally ingesting or direct contact with contaminants.
                                                                     March 1992

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Cleanup Approach
This site is being addressed in three stages: immediate actions and two long-term remedial
phases focusing on the cleanup of the landfill, scraped area, and the former lagoon sections
of the site and the cleanup of the industrial complex areas.
Response Action Status
an approved facility.
           Immediate Actions: In 1984, to alleviate the immediate threat at a portion of
           the site, the current owner removed drums containing polychlorinated biphenyls
           (PCBs) to a secured storage area within the site. They later were disposed of in
           Landfill, Scraped Area, and Former Lagoons: In 1989, the EPA selected
           the following remedies for site cleanup at these areas: (1) consolidation of the
           existing landfill waste and construction of a multi-layer cap to keep rainfall and
runoff from spreading contaminants; (2) bioremediation of the former lagoons, scraped area
soil, and contaminated stream sediments; (3) drainage and sedimentation control on the
surface in the landfill area; and (4) post-treatment air monitoring to ensure the effectiveness
of the cleanup. The engineering design  is expected to be completed in 1993, with final
cleanup scheduled for completion in 1994.

          Industrial Complex Areas: The potentially responsible parties will conduct a
          study to determine the nature and extent of contamination and to identify
          alternatives for cleanup at the industrial complex areas and cool residue storage
areas in the northern and central portions of the site, respectively. The parties have
developed a work plan for the studies, which is under review by the EPA. Field work is
expected  to begin in late 1992.

Site Facts: The EPA and the potentially responsible parties signed a Consent Order on
June 4, 1990 for conducting site studies.
Environmental  Progress
The removal of drums containing PCBs has eliminated immediate threats to the surroundings
at the Ordnance Works Disposal Areas site while studies and cleanup activities are underway
at the industrial complex areas, landfill scraped area, and former lagoon sections of the site.
Site Repository
Morgantown Public Library, 373 Spruce Street, Morgantown, WV 26505
March 1992                                10            ORDNANCE WORKS DISPOSAL AREAS

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WEST VIRGINIA
ORDNANCE
WEST VIRGINIA
EPAID#WVD980713Q3<
     EPA REGION 3
         Mason County
6 miles north of Point Pleasant on the
         bank of the Ohio River

         Other Names:
 McClintlc Wildlife Refuge Station
  West Virginia Ordnance Works
Site Description
From 1942 to 1945, the Army produced TNT (trinitrotoluene) at West Virginia Ordnance, a
8,320-acre site. Soils around the operation's industrial area, process facilities, and industrial
wastewater disposal system were contaminated with the TNT explosive, its by-products, and
asbestos. When the site was decontaminated and decommissioned in 1945, the Army deeded
the industrial portion to West Virginia, stipulating that it be used for wildlife management.
The State created the McClintic State Wildlife Station on 2,785 acres, and the area now is
used for public hunting, fishing, camping, and day-time recreational use. Other non-industrial
portions of the original parcel are owned by the County or by private citizens. In 1989,
redwater seepage (liquid waste produced during the TNT manufacturing process) was
observed near Pond 13 on the wildlife station. EPA and State investigations revealed that the
groundwater and surface water were contaminated with  explosive nitroaromatics. Buried lines
associated with TNT manufacturing contained some crystalline TNT. The ground was littered
with residues and chunks of nitroaromatic compounds. About 11,000 people visit the
McClintic Wildlife Station each year. Surrounding areas  include residential communities, the
West Virginia University (WVU) Experimental Station, Mason County Airport, National
Guard facilities, the county fairgrounds, cropland, pastures,  and forests.
Site Responsibility:  This site is being addressed through
                     Federal actions.
Threats and  Contaminants
     NPL LISTING HISTORY
      Proposed Date: 10/01/81
       Final Date: 09/01/83
         Groundwater, seepage, soils, and the surface water on site are contaminated with
         explosive nitroaromatic compounds including TNT, trinitrobenzene, and
         dinitrotoluene from former site operations. Visitors to the wildlife refuge may be
         exposed to contaminants by direct contact with or accidental ingestion of
         contaminated surface water or soils. The shallow groundwater has been shown to
         be contaminated and is moving toward nearby private residences with wells. No
         nitroaromatics have been detected in any of the 13 local water supply wells, but
         sewer lines and open manholes contain reactive wastes, which may pose a safety
         and chemical hazard to people entering them. The site is a wildlife refuge.
                                        11
                     March 1992

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Cleanup Approach
The site is being addressed in six long-term remedial phases focusing on source control and
cleanup of Red Water Reservoir, Yellow Water Reservoir, groundwater contamination, Pond
13, and wetlands mitigation.

Response Action Status  	

          Source Control: The remedy selected to address the source of contamination is:
          (1) in-place flaming of reactive TNT residue on soil surfaces and installation of a
          2-foot soil cover over highly contaminated areas; (2) disposal of asbestos off site;
and (3) excavation of reactive sewer lines, flashing of explosives, and backfilling of trenches
from which lines are removed. These site cleanup activities were completed in 1989. After
completing these cleanup activities,  the Army conducted an investigation and determined that
damages occurred to natural resources (wetlands) during cleanup.  A second phase of cleanup
activities is expected to begin in 1993 to address this damage.

          Red Water Reservoir: In 1991, cleanup activities began at the Red Water
          Reservoir.  Remedies include relocating Ponds 1  and 2, filling and capping the
          original Ponds 1 and 2, and extracting and treating the groundwater. All cleanup
activities except the groundwater treatment for the Red Water Reservoir, Yellow Water
Reservoir, and Pond 13 will be  addressed in  one  action.

          Yellow Water Reservoir:  Designs  for  the cleanup actions at Yellow Water
          Reservoir began in  1991 and are expected to be completed in late 1992.
          Remedies selected include capping the contaminated areas and extracting and
treating the groundwater. Cleanup activities are scheduled to begin in  1993.
           Groundwater: The EPA and the Army are addressing groundwater
           contamination at the Red Water Reservoir, Yellow Water Reservoir, and Pond
           13.  Design of the pump and treat system for cleaning up the groundwater began
in 1991 and is expected to  be completed in late 1993.

           Pond 13: The remedies selected to treat the Pond 13 wet well include capping
           contaminated areas and extracting and treating the groundwater.  The design of
           the  cap is expected to begin in late 1992.

           Wetlands Mitigation: This action will be addressing the wetlands loss that will
           occur from capping the Red and Yellow Water Reservoirs and Pond 13. All
           wetlands are expected to be replaced by late 1994.

Site Facts: In  1984, the EPA concurred with the Army's request to assume responsibility for
cleanup actions at the site.  The West Virginia Ordnance site 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.
March 1992                                 12                    WEST VIRGINIA ORDNANCE

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Environmental Progress
While the West Virginia Ordnance site is awaiting the completion of cleanup activities begun
in 1988, the EPA and the Army have evaluated site threats and have determined that the site
does not currently pose an immediate risk to health or the environment.
Site Repository
Mason County Public Library, Sixth and Viand Streets, Point Pleasant, WV 25550
WEST VIRGINIA ORDNANCE
13
March 1992

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                             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 contaminants are evaporated
into the air stream. The air may be further
treated before it is released into the atmosphere.

Ambient Air:  Any unconfined part of the
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

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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
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                                                                       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  1980 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.
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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
de 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 fanning, 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.

Emulsiflers:  Substances that help in mixing
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
farming,  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.
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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.
                                           G-7

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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 metals.

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.
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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].

Pollution: 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.
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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.
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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 groundwater, 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.
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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
    Category
      Example
  Chemical Types
      Sources
    Potential Health
        Threats*
  r-teavy Metafe
  I Volatile Organic
  : Compounds
  ; Creosotes
  fiadiatfon
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.:1993-341-835:81027
                            G-15

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