National Oil and Hazardous Substances Pollution Contingency Plan; National Priorities List, 5930-5932 [05-2058]
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5930
Federal Register / Vol. 70, No. 23 / Friday, February 4, 2005 / Rules and Regulations
§ 52.519 Identification of plan-conditional
approval.
National Oil and Hazardous
Substances Pollution Contingency
Plan; National Priorities List
Comments may be mailed
to: Robert Sanchez, Remedial Project
Manager, U.S. EPA Region III (3HS23),
1650 Arch Street, Philadelphia, PA
19103–2029, (215) 814–3451.
Information Repositories:
Comprehensive information about the
Site is available for viewing and copying
at the Site information repositories
located at: U.S. EPA Region III, Regional
Center for Environmental Information
(RCEI), 1650 Arch Street (2nd Floor),
Philadelphia, PA 19103–2029, (215)
814–5254, Monday through Friday, 8
a.m. to 5 p.m.; and in Maryland at the
St. Mary’s County Library, 23250
Hollywood Road, Leonardtown, MD
20650 (301) 475–2846, Monday through
Friday, 8 a.m. to 4 p.m.
FOR FURTHER INFORMATION CONTACT:
Robert Sanchez, Remedial Project
Manager, U.S. EPA Region III (3HS23),
1650 Arch Street, Philadelphia, PA
19103–2029, (215) 814–3451 or 1–800–
553–2509.
SUPPLEMENTARY INFORMATION:
AGENCY:
Environmental Protection
Agency.
ACTION: Direct final rule of deletion of
the Southern Maryland Wood Treating
Superfund Site from the National
Priorities List.
Table of Contents
I. Introduction
II. NPL Deletion Criteria
III. Deletion Procedures
IV. Basis for Site Deletion
V. Deletion Action
SUMMARY: The Environmental Protection
Agency (EPA) Region III is publishing a
direct final rule of deletion of the
Southern Maryland Wood Treating
Superfund Site (Site), located in
Hollywood (St. Mary’s County),
Maryland, from the National Priorities
List (NPL).
The NPL, promulgated pursuant to
section 105 of the Comprehensive
Environmental Response,
Compensation, and Liability Act of
1980, as amended (CERCLA), is
Appendix B of 40 CFR part 300, which
is the National Oil and Hazardous
Substances Pollution Contingency Plan
(NCP). This direct final rule of deletion
is being published by EPA with the
concurrence of the State of Maryland,
through the Maryland Department of the
Environment (MDE), because EPA has
determined that all appropriate
response actions under CERCLA have
been completed and, therefore, further
remedial action pursuant to CERCLA is
not appropriate.
DATES: This direct final rule deletion
will be effective April 5, 2005, unless
EPA receives adverse comments by
March 7, 2005. If adverse comments are
received, EPA will publish a timely
withdrawal of the direct final rule
deletion in the Federal Register
informing the public that the deletion
will not take effect.
I. Introduction
EPA Region III is publishing this
direct final notice of deletion of the
Southern Maryland Wood Treating
Superfund Site from the NPL.
The EPA identifies sites that appear to
present a significant risk to public
health or the environment and
maintains the NPL as the list of those
sites. As described in § 300.425(e)(3) of
the NCP, sites deleted from the NPL
remain eligible for remedial actions if
conditions at a deleted site warrant such
action.
Because EPA considers this action to
be noncontroversial and routine, EPA is
taking it without prior publication of a
notice of intent to delete. This action
will be effective April 5, 2005, unless
EPA receives adverse comments by
March 7, 2005, on this document or the
parallel notice of intent to delete
published in the ‘‘Proposed Rules’’
section of today’s Federal Register. If
adverse comments are received within
the 30-day public comment period on
this notice or the notice of intent to
delete, EPA will publish a timely
withdrawal of this direct final notice of
deletion before the effective date of the
deletion and the deletion will not take
effect. EPA will, as appropriate, prepare
a response to comments and continue
with the deletion process on the basis of
the notice of intent to delete and the
EPA is conditionally approving a
revision to the Florida State
Implementation Plan (SIP) consisting of
a new citrus statute (Florida Statute
403.08725), as well as implementing
regulations (62–210.340 F.A.C.) based
upon a commitment from the State to
adopt specific enforceable measures by
March 7, 2006. If the State fails to meet
its commitment by March 7, 2006, the
approval is treated as a disapproval.
[FR Doc. 05–2072 Filed 2–3–05; 8:45 am]
BILLING CODE 6560–50–P
ENVIRONMENTAL PROTECTION
AGENCY
40 CFR Part 300
[FRL–7868–6]
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ADDRESSES:
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comments already received. There will
be no additional opportunity to
comment.
Section II of this document explains
the criteria for deleting sites from the
NPL. Section III discusses procedures
that EPA is using for this action. Section
IV discusses the Southern Maryland
Wood Treating Superfund Site and
demonstrates how it meets the deletion
criteria. Section V discusses EPA’s
action to delete the Site from the NPL
unless adverse comments are received
during the public comment period.
II. NPL Deletion Criteria
Section 300.425(e) of the NCP
provides that releases may be deleted
from the NPL where no further response
is appropriate. In making a
determination to delete a Site from the
NPL, EPA shall consider, in
consultation with the State, whether any
of the following criteria have been met:
i. Responsible parties or other persons
have implemented all appropriate
response actions required;
ii. All appropriate Fund-financed
(Hazardous Substance Superfund
Response Trust Fund) response under
CERCLA has been implemented, and no
further response action by responsible
parties is appropriate; or
iii. The remedial investigation has
shown that the release poses no
significant threat to public health or the
environment and, therefore, the taking
of remedial measures is not appropriate.
Even if a site is deleted from the NPL,
where hazardous substances, pollutants,
or contaminants remain at the deleted
site above levels that allow for
unlimited use and unrestricted
exposure, CERCLA section 121(c), 42
U.S.C. 9621(c), requires that a
subsequent review of the site be
conducted at least every five years after
the initiation of the remedial action at
the deleted site to ensure that the action
remains protective of public health and
the environment. If new information
becomes available which indicates a
need for further action, EPA may initiate
remedial actions. Whenever there is a
significant release from a site deleted
from the NPL, the deleted site may be
restored to the NPL without application
of the hazard ranking system.
III. Deletion Procedures
The following procedures apply to
deletion of the Site:
(1) EPA consulted with the State of
Maryland on the deletion of the Site
from the NPL prior to developing this
direct final notice of deletion.
(2) The State of Maryland has
concurred with deletion of the Site from
the NPL.
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Federal Register / Vol. 70, No. 23 / Friday, February 4, 2005 / Rules and Regulations
(3) Concurrently with the publication
of this direct final notice of deletion, a
notice of the availability of the parallel
notice of intent to delete published
today in the ‘‘Proposed Rules’’ section
of the Federal Register is being
published in a major local newspaper of
general circulation at or near the Site
and is being distributed to appropriate
Federal, State, and local government
officials and other interested parties; the
newspaper notice announces the 30-day
public comment period concerning the
notice of intent to delete the Site from
the NPL.
(4) EPA placed copies of documents
supporting the deletion in the Site
information repositories identified
above.
(5) If adverse comments are received
within the 30-day public comment
period on this notice or the companion
notice of intent to delete also published
in today’s Federal Register, EPA will
publish a timely notice of withdrawal of
this direct final notice of deletion before
its effective date. EPA will, as
appropriate, prepare a response to
comments and continue with the
deletion process on the basis of the
notice of intent to delete and the
comments already received.
Deletion of a site from the NPL does
not itself create, alter, or revoke any
individual’s rights or obligations.
Deletion of a site from the NPL does not
in any way alter EPA’s right to take
enforcement actions, as appropriate.
The NPL is designed primarily for
informational purposes and to assist
EPA management. Section 300.425(e)(3)
of the NCP states that the deletion of a
site from the NPL does not preclude
eligibility for future response actions,
should future conditions warrant such
actions.
IV. Basis for Site Deletion
The following information provides
EPA’s rationale for deleting the Site
from the NPL:
Site History and Characteristics
Land and Resource Use
The Southern Maryland Wood
Treating Site is approximately 25 acres
in size and is located on a 94-acre parcel
of land just west of Maryland Route 235
approximately one mile north of
Hollywood, Maryland. The upland
portion of the Site where most of the
remedial work took place is
approximately 25 acres. The remainder
of the Site is situated in or near a flood
plain area. Title of the property which
constitutes the Site is being held by a
bankruptcy trustee. The Site is bounded
by residential, agricultural and wooded
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tracts of land. The Site is the head
waters of Old Tom’s Run which
eventually flows into Breton Bay and
then into the Potomac River.
History of Contamination/Response
Actions
The Site was owned and operated by
the Southern Maryland Wood Treating
Corporation from 1965 to 1978 as a
pressure treatment wood preservation
facility. Creosote and
pentachlorophenol (PCP) were used as
wood preservatives by the facility. Six
unlined lagoons were used for disposal
of liquid wastes from the process. As a
result of such disposal practices, onsite
soils and ground water beneath the
lagoons became contaminated. Nonaqueous phase liquids (NAPLs), both
light (LNAPLs) and dense (DNAPLs),
were found in the subsurface beneath
the lagoons and above the underlying
clay layer. Additionally, due to ground
water discharge to the onsite pond from
the lagoon area, surface water and
sediments in the onsite pond and
sediments in Old Tom’s Run (east and
west tributaries) became contaminated.
Storage of treated wood onsite resulted
in surface soil contamination in the
northern section of the site and
northeast tank area.
On March 14, 1985, EPA initiated its
first response action, namely a removal
action, at the Site after the discovery of
contaminated material seeping into the
onsite freshwater pond. During the
removal action EPA excavated 1,400
cubic yards of contaminated sediments
from the freshwater pond. The
sediments were stabilized with cement
kiln dust and encapsulated on the Site,
and remained on the Site until a final
treatment. The Site was promulgated on
the National Priorities List on June 10,
1986. In 1988, EPA concluded a
Remedial Investigation (RI) and
Feasibility Study (FS) for the Site. Based
on the findings of these studies, EPA
issued a Record of Decision on June 29,
1988 (1988 ROD). In the 1988 ROD
EPA’s selected remedy consisted of the
construction of a subsurface barrier wall
around the former lagoon area,
excavation and onsite incineration of
contaminated soil and pumping and
treatment of contaminated ground
water. Construction of the substance
barrier (sheet pile wall) was completed
in November of 1990. By May 1992,
design of the incinerator and the ground
water treatment system were 95%
complete. At that point, local citizens
and local government entities expressed
opposition to an onsite incinerator. The
design work was suspended and EPA
proposed to conduct a Focused
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Feasibility Study (FFS) to reevaluate the
remedy for the Site.
On June 29, 1993, a second removal
action was initiated to address certain
immediate threats at the Site while the
FFS was being conducted. This action
included the demolition of several
buildings that were in danger of
collapse; the removal and off-site
disposal of liquid and solid waste in
numerous tanks and retorts; maintaining
the pile of previously excavated and
stabilized sediment; the construction of
an underflow dam to reduce the amount
of contaminated material migrating from
the onsite pond into the west tributary
stream; the construction of a trench
upgradient of the pond to collect
contaminated ground water, and the
construction of a water treatment
facility. The water treatment plant
(WTP–1) became fully operational in
1995.
The Focused Feasibility Study (FFS)
was completed in February 1995. Based
on the FFS, the EPA issued a second
Record of Decision on September 8,
1995 (1995 ROD). In this 1995 ROD,
EPA revised the remedy selected in the
1988 ROD from incineration to thermal
desorption which the community
accepted as the remedy. In addition to
excavation of the upland area, some
excavation in the small tributary stream
that receives storm water runoff from
the former lagoon area was conducted.
Two large continuous thermal
desorption units with vapor recovery
units were constructed on-site and
became operational in June 1998. Soil
treatment operations continued until
October 6, 2000. At that point,
approximately 270,600 tons of
contaminated soils and sediments had
been successfully treated. The Site was
re-graded and re-vegetated with a
diverse mixture of wildflowers and
grains suitable for wildlife habitant.
Demobilization activities began in
October 2000 and continued until
December 2000.
Cleanup Standards
During the excavation and thermal
desorption process, but before
backfilling was conducted, all treated
soil was sampled to determine if
contaminants had been properly
removed from the soils and sediments.
Based on this sampling, EPA
determined that all of the treated Site
soils were cleaned to the required
performance standards. These standards
were established in the 1995 ROD as
Remedial Action Objectives (‘‘RAOs’’).
The RAOs set soil clean-up levels of 0.1
ppm Benzo (a) Pyrene (B(a)P) equivalent
for surface soils (within two feet of the
surface) and 1.0 ppm B(a)P equivalent
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Federal Register / Vol. 70, No. 23 / Friday, February 4, 2005 / Rules and Regulations
for subsurface soils (below two feet from
the surface). However, during the
remedial action data showed that in
areas where the Site soils were below
the Benzo (a) Pyrene (B(a)P) clean-up
levels there were still high levels of
pentachlorophenol (PCP) in the soil. To
assure that the soil in these areas was
treated, a non-significant change to the
1995 ROD was issued by EPA on March
5, 1999. This non-significant change
established a cleanup level of 5.0 ppm
PCP. In addition, another nonsignificant change was the use of treated
soils from the Site as backfill below the
water table. These treated soils were
required to meet a clean-up level of 1.7
ppm PCP. This change from the 1995
ROD was announced during the public
meeting on November 7, 1996 and
documented in the ‘‘Site Specific Work
Plan,’’ dated July 1997.
Post Closure Monitoring
A Post Closure Monitoring Plan, dated
November 2000, was prepared to verify
the success of the cleanup. The plan
required sampling a network of
monitoring wells throughout the Site
including one well at the center of the
former lagoon area. In addition the plan
required the evaluation of the restored
uplands and wetlands areas that had
undergone excavation, backfilling, and
re-vegetation. The monitoring wells
were sampled quarterly from October
2000 to September 2002. Samples were
analyzed for target compounds such as
semi-volatiles, polynuclear aromatic
hydrocarbons (PAH), and
pentachlorophenol (PCP). All the
sampling results showed that levels for
these contaminants were well below
their respective Maximum Contaminant
Levels (MCLs) established under the
Safe Drinking Water Act, 42 U.S.C. 300f
et seq. Formal inspections of the
wetland and upland areas were
conducted concurrently with the
monitoring well sampling effort. These
areas showed no signs of erosion. All
disturbed wetland areas have stabilized.
The disturbed uplands areas are
currently stabilized with grass, and the
overall upland area is showing 95
percent total herbaceous coverage. After
completion of sampling in September
2002 all monitoring wells and the 600foot deep production well were
subsequently closed out in accordance
with MDE regulations for well
abandonment. The production well
required special close-out procedures
involving blasting. The concern for this
very deep well was that ground water
from the upper non-potable aquifer
could migrate down to the lower potable
aquifer along possible voids on the
outside of the well sleeve. Complete
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separation of these two aquifers was
assured by blasting the well sleeve open
at a point where there was an
impervious clay layer between the
upper and lower aquifers and then
pumping in grout material to seal the
well.
Five-Year Review
EPA has completed two Five-Year
Reviews for this Site. The first was
completed on September 30, 1994 and
the second on September 30, 1999.
Since the clean-up was ongoing these
reviews were not required by statute,
but were conducted as a matter of
policy.
Five-Year Reviews are required at
sites where the remedial action results
in hazardous substances, pollutants or
contaminants remain at the site above
levels that allow for unrestricted use
and unrestricted exposure. The response
actions conducted at the Southern
Maryland Wood Treating Site are now
complete, and allow for unlimited use
and unrestricted exposure, thus no
additional Five-Year Reviews will be
conducted for this Site.
Community Involvement
Public participation activities have
been satisfied as required in CERCLA
section 113(k), 42 U.S.C. 9613(k), and
CERCLA section 117, 42 U.S.C. 9617.
Documents in the Site docket which
EPA relied on for recommendation of
the deletion of the Site from the NPL are
available to the public in the
information repositories.
V. Deletion Action
EPA, with the concurrence of the
State of Maryland, has determined that
all appropriate responses under
CERCLA have been completed at the
Site, and that no further response
actions are necessary. Therefore, EPA is
deleting the Site from the NPL.
Because EPA considers this action to
be noncontroversial and routine, EPA is
taking it without prior publication of a
notice of intent to delete. This action
will be effective April 5, 2005, unless
EPA receives adverse comments by
March 7, 2005, on this notice or the
parallel notice of intent to delete
published in the ‘‘Proposed Rules’’
section of today’s Federal Register. If
adverse comments are received within
the 30-day public comment period, EPA
will publish a timely withdrawal of this
direct final notice of deletion before the
effective date of the deletion and it will
not take effect and EPA will also
prepare a response to comments and
continue with the deletion process on
the basis of the notice of intent to delete
and the comments already received.
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There will be no additional opportunity
to comment.
List of Subjects in 40 CFR Part 300
Environmental protection, Air
pollution control, Chemicals, Hazardous
waste, Hazardous substances,
Intergovernmental relations, Penalties,
Reporting and recordkeeping
requirements, Superfund, Water
pollution control, Water supply.
Dated: January 26, 2005.
Richard J. Kampf,
Acting Regional Administrator, Region III.
For the reasons set out in the preamble,
40 CFR part 300 is amended as follows:
I
PART 300—[AMENDED]
1. The authority citation for part 300
continues to read as follows:
I
Authority: 33 U.S.C. 1321(c)(2); 42 U.S.C.
9601–9657; E.O. 12777, 56 FR 54757, 3 CFR,
1991 Comp., p. 351; E.O. 12580, 52 FR 2923,
3 CFR, 1987 Comp., p. 193.
Appendix B—[Amended]
2. Table 1 of Appendix B to Part 300
is amended under Maryland (‘‘MD’’) by
removing the site name ‘‘Southern
Maryland Wood Treating, Hollywood.’’
I
[FR Doc. 05–2058 Filed 2–3–05; 8:45 am]
BILLING CODE 6560–50–P
GENERAL SERVICES
ADMINISTRATION
41 CFR Chapter 301
[FTR Amendment 2005–01; FTR Case 2005–
301]
RIN 3090–AI03
Federal Travel Regulation; Privately
Owned Vehicle Mileage
Reimbursement
AGENCY:
Office Governmentwide Policy,
GSA.
ACTION:
Final rule.
SUMMARY: This final rule amends the
mileage reimbursement rate for use of a
privately owned vehicle on official
travel to reflect current costs of
operation as determined in cost studies
conducted by the General Services
Administration (GSA). The governing
regulation is revised to increase the
mileage allowance for advantageous use
of a privately owned airplane from
$0.995 to $1.07 per mile, the cost of
operating a privately owned automobile
from $0.375 to $0.405 per mile, and the
cost of operating a privately owned
motorcycle from $0.285 to $0.305 per
mile.
E:\FR\FM\04FER1.SGM
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Agencies
[Federal Register Volume 70, Number 23 (Friday, February 4, 2005)]
[Rules and Regulations]
[Pages 5930-5932]
From the Federal Register Online via the Government Printing Office [www.gpo.gov]
[FR Doc No: 05-2058]
-----------------------------------------------------------------------
ENVIRONMENTAL PROTECTION AGENCY
40 CFR Part 300
[FRL-7868-6]
National Oil and Hazardous Substances Pollution Contingency Plan;
National Priorities List
AGENCY: Environmental Protection Agency.
ACTION: Direct final rule of deletion of the Southern Maryland Wood
Treating Superfund Site from the National Priorities List.
-----------------------------------------------------------------------
SUMMARY: The Environmental Protection Agency (EPA) Region III is
publishing a direct final rule of deletion of the Southern Maryland
Wood Treating Superfund Site (Site), located in Hollywood (St. Mary's
County), Maryland, from the National Priorities List (NPL).
The NPL, promulgated pursuant to section 105 of the Comprehensive
Environmental Response, Compensation, and Liability Act of 1980, as
amended (CERCLA), is Appendix B of 40 CFR part 300, which is the
National Oil and Hazardous Substances Pollution Contingency Plan (NCP).
This direct final rule of deletion is being published by EPA with the
concurrence of the State of Maryland, through the Maryland Department
of the Environment (MDE), because EPA has determined that all
appropriate response actions under CERCLA have been completed and,
therefore, further remedial action pursuant to CERCLA is not
appropriate.
DATES: This direct final rule deletion will be effective April 5, 2005,
unless EPA receives adverse comments by March 7, 2005. If adverse
comments are received, EPA will publish a timely withdrawal of the
direct final rule deletion in the Federal Register informing the public
that the deletion will not take effect.
ADDRESSES: Comments may be mailed to: Robert Sanchez, Remedial Project
Manager, U.S. EPA Region III (3HS23), 1650 Arch Street, Philadelphia,
PA 19103-2029, (215) 814-3451.
Information Repositories: Comprehensive information about the Site
is available for viewing and copying at the Site information
repositories located at: U.S. EPA Region III, Regional Center for
Environmental Information (RCEI), 1650 Arch Street (2nd Floor),
Philadelphia, PA 19103-2029, (215) 814-5254, Monday through Friday, 8
a.m. to 5 p.m.; and in Maryland at the St. Mary's County Library, 23250
Hollywood Road, Leonardtown, MD 20650 (301) 475-2846, Monday through
Friday, 8 a.m. to 4 p.m.
FOR FURTHER INFORMATION CONTACT: Robert Sanchez, Remedial Project
Manager, U.S. EPA Region III (3HS23), 1650 Arch Street, Philadelphia,
PA 19103-2029, (215) 814-3451 or 1-800-553-2509.
SUPPLEMENTARY INFORMATION:
Table of Contents
I. Introduction
II. NPL Deletion Criteria
III. Deletion Procedures
IV. Basis for Site Deletion
V. Deletion Action
I. Introduction
EPA Region III is publishing this direct final notice of deletion
of the Southern Maryland Wood Treating Superfund Site from the NPL.
The EPA identifies sites that appear to present a significant risk
to public health or the environment and maintains the NPL as the list
of those sites. As described in Sec. 300.425(e)(3) of the NCP, sites
deleted from the NPL remain eligible for remedial actions if conditions
at a deleted site warrant such action.
Because EPA considers this action to be noncontroversial and
routine, EPA is taking it without prior publication of a notice of
intent to delete. This action will be effective April 5, 2005, unless
EPA receives adverse comments by March 7, 2005, on this document or the
parallel notice of intent to delete published in the ``Proposed Rules''
section of today's Federal Register. If adverse comments are received
within the 30-day public comment period on this notice or the notice of
intent to delete, EPA will publish a timely withdrawal of this direct
final notice of deletion before the effective date of the deletion and
the deletion will not take effect. EPA will, as appropriate, prepare a
response to comments and continue with the deletion process on the
basis of the notice of intent to delete and the comments already
received. There will be no additional opportunity to comment.
Section II of this document explains the criteria for deleting
sites from the NPL. Section III discusses procedures that EPA is using
for this action. Section IV discusses the Southern Maryland Wood
Treating Superfund Site and demonstrates how it meets the deletion
criteria. Section V discusses EPA's action to delete the Site from the
NPL unless adverse comments are received during the public comment
period.
II. NPL Deletion Criteria
Section 300.425(e) of the NCP provides that releases may be deleted
from the NPL where no further response is appropriate. In making a
determination to delete a Site from the NPL, EPA shall consider, in
consultation with the State, whether any of the following criteria have
been met:
i. Responsible parties or other persons have implemented all
appropriate response actions required;
ii. All appropriate Fund-financed (Hazardous Substance Superfund
Response Trust Fund) response under CERCLA has been implemented, and no
further response action by responsible parties is appropriate; or
iii. The remedial investigation has shown that the release poses no
significant threat to public health or the environment and, therefore,
the taking of remedial measures is not appropriate.
Even if a site is deleted from the NPL, where hazardous substances,
pollutants, or contaminants remain at the deleted site above levels
that allow for unlimited use and unrestricted exposure, CERCLA section
121(c), 42 U.S.C. 9621(c), requires that a subsequent review of the
site be conducted at least every five years after the initiation of the
remedial action at the deleted site to ensure that the action remains
protective of public health and the environment. If new information
becomes available which indicates a need for further action, EPA may
initiate remedial actions. Whenever there is a significant release from
a site deleted from the NPL, the deleted site may be restored to the
NPL without application of the hazard ranking system.
III. Deletion Procedures
The following procedures apply to deletion of the Site:
(1) EPA consulted with the State of Maryland on the deletion of the
Site from the NPL prior to developing this direct final notice of
deletion.
(2) The State of Maryland has concurred with deletion of the Site
from the NPL.
[[Page 5931]]
(3) Concurrently with the publication of this direct final notice
of deletion, a notice of the availability of the parallel notice of
intent to delete published today in the ``Proposed Rules'' section of
the Federal Register is being published in a major local newspaper of
general circulation at or near the Site and is being distributed to
appropriate Federal, State, and local government officials and other
interested parties; the newspaper notice announces the 30-day public
comment period concerning the notice of intent to delete the Site from
the NPL.
(4) EPA placed copies of documents supporting the deletion in the
Site information repositories identified above.
(5) If adverse comments are received within the 30-day public
comment period on this notice or the companion notice of intent to
delete also published in today's Federal Register, EPA will publish a
timely notice of withdrawal of this direct final notice of deletion
before its effective date. EPA will, as appropriate, prepare a response
to comments and continue with the deletion process on the basis of the
notice of intent to delete and the comments already received.
Deletion of a site from the NPL does not itself create, alter, or
revoke any individual's rights or obligations. Deletion of a site from
the NPL does not in any way alter EPA's right to take enforcement
actions, as appropriate. The NPL is designed primarily for
informational purposes and to assist EPA management. Section
300.425(e)(3) of the NCP states that the deletion of a site from the
NPL does not preclude eligibility for future response actions, should
future conditions warrant such actions.
IV. Basis for Site Deletion
The following information provides EPA's rationale for deleting the
Site from the NPL:
Site History and Characteristics
Land and Resource Use
The Southern Maryland Wood Treating Site is approximately 25 acres
in size and is located on a 94-acre parcel of land just west of
Maryland Route 235 approximately one mile north of Hollywood, Maryland.
The upland portion of the Site where most of the remedial work took
place is approximately 25 acres. The remainder of the Site is situated
in or near a flood plain area. Title of the property which constitutes
the Site is being held by a bankruptcy trustee. The Site is bounded by
residential, agricultural and wooded tracts of land. The Site is the
head waters of Old Tom's Run which eventually flows into Breton Bay and
then into the Potomac River.
History of Contamination/Response Actions
The Site was owned and operated by the Southern Maryland Wood
Treating Corporation from 1965 to 1978 as a pressure treatment wood
preservation facility. Creosote and pentachlorophenol (PCP) were used
as wood preservatives by the facility. Six unlined lagoons were used
for disposal of liquid wastes from the process. As a result of such
disposal practices, onsite soils and ground water beneath the lagoons
became contaminated. Non-aqueous phase liquids (NAPLs), both light
(LNAPLs) and dense (DNAPLs), were found in the subsurface beneath the
lagoons and above the underlying clay layer. Additionally, due to
ground water discharge to the onsite pond from the lagoon area, surface
water and sediments in the onsite pond and sediments in Old Tom's Run
(east and west tributaries) became contaminated. Storage of treated
wood onsite resulted in surface soil contamination in the northern
section of the site and northeast tank area.
On March 14, 1985, EPA initiated its first response action, namely
a removal action, at the Site after the discovery of contaminated
material seeping into the onsite freshwater pond. During the removal
action EPA excavated 1,400 cubic yards of contaminated sediments from
the freshwater pond. The sediments were stabilized with cement kiln
dust and encapsulated on the Site, and remained on the Site until a
final treatment. The Site was promulgated on the National Priorities
List on June 10, 1986. In 1988, EPA concluded a Remedial Investigation
(RI) and Feasibility Study (FS) for the Site. Based on the findings of
these studies, EPA issued a Record of Decision on June 29, 1988 (1988
ROD). In the 1988 ROD EPA's selected remedy consisted of the
construction of a subsurface barrier wall around the former lagoon
area, excavation and onsite incineration of contaminated soil and
pumping and treatment of contaminated ground water. Construction of the
substance barrier (sheet pile wall) was completed in November of 1990.
By May 1992, design of the incinerator and the ground water treatment
system were 95% complete. At that point, local citizens and local
government entities expressed opposition to an onsite incinerator. The
design work was suspended and EPA proposed to conduct a Focused
Feasibility Study (FFS) to reevaluate the remedy for the Site.
On June 29, 1993, a second removal action was initiated to address
certain immediate threats at the Site while the FFS was being
conducted. This action included the demolition of several buildings
that were in danger of collapse; the removal and off-site disposal of
liquid and solid waste in numerous tanks and retorts; maintaining the
pile of previously excavated and stabilized sediment; the construction
of an underflow dam to reduce the amount of contaminated material
migrating from the onsite pond into the west tributary stream; the
construction of a trench upgradient of the pond to collect contaminated
ground water, and the construction of a water treatment facility. The
water treatment plant (WTP-1) became fully operational in 1995.
The Focused Feasibility Study (FFS) was completed in February 1995.
Based on the FFS, the EPA issued a second Record of Decision on
September 8, 1995 (1995 ROD). In this 1995 ROD, EPA revised the remedy
selected in the 1988 ROD from incineration to thermal desorption which
the community accepted as the remedy. In addition to excavation of the
upland area, some excavation in the small tributary stream that
receives storm water runoff from the former lagoon area was conducted.
Two large continuous thermal desorption units with vapor recovery
units were constructed on-site and became operational in June 1998.
Soil treatment operations continued until October 6, 2000. At that
point, approximately 270,600 tons of contaminated soils and sediments
had been successfully treated. The Site was re-graded and re-vegetated
with a diverse mixture of wildflowers and grains suitable for wildlife
habitant. Demobilization activities began in October 2000 and continued
until December 2000.
Cleanup Standards
During the excavation and thermal desorption process, but before
backfilling was conducted, all treated soil was sampled to determine if
contaminants had been properly removed from the soils and sediments.
Based on this sampling, EPA determined that all of the treated Site
soils were cleaned to the required performance standards. These
standards were established in the 1995 ROD as Remedial Action
Objectives (``RAOs''). The RAOs set soil clean-up levels of 0.1 ppm
Benzo (a) Pyrene (B(a)P) equivalent for surface soils (within two feet
of the surface) and 1.0 ppm B(a)P equivalent
[[Page 5932]]
for subsurface soils (below two feet from the surface). However, during
the remedial action data showed that in areas where the Site soils were
below the Benzo (a) Pyrene (B(a)P) clean-up levels there were still
high levels of pentachlorophenol (PCP) in the soil. To assure that the
soil in these areas was treated, a non-significant change to the 1995
ROD was issued by EPA on March 5, 1999. This non-significant change
established a cleanup level of 5.0 ppm PCP. In addition, another non-
significant change was the use of treated soils from the Site as
backfill below the water table. These treated soils were required to
meet a clean-up level of 1.7 ppm PCP. This change from the 1995 ROD was
announced during the public meeting on November 7, 1996 and documented
in the ``Site Specific Work Plan,'' dated July 1997.
Post Closure Monitoring
A Post Closure Monitoring Plan, dated November 2000, was prepared
to verify the success of the cleanup. The plan required sampling a
network of monitoring wells throughout the Site including one well at
the center of the former lagoon area. In addition the plan required the
evaluation of the restored uplands and wetlands areas that had
undergone excavation, backfilling, and re-vegetation. The monitoring
wells were sampled quarterly from October 2000 to September 2002.
Samples were analyzed for target compounds such as semi-volatiles,
polynuclear aromatic hydrocarbons (PAH), and pentachlorophenol (PCP).
All the sampling results showed that levels for these contaminants were
well below their respective Maximum Contaminant Levels (MCLs)
established under the Safe Drinking Water Act, 42 U.S.C. 300f et seq.
Formal inspections of the wetland and upland areas were conducted
concurrently with the monitoring well sampling effort. These areas
showed no signs of erosion. All disturbed wetland areas have
stabilized. The disturbed uplands areas are currently stabilized with
grass, and the overall upland area is showing 95 percent total
herbaceous coverage. After completion of sampling in September 2002 all
monitoring wells and the 600-foot deep production well were
subsequently closed out in accordance with MDE regulations for well
abandonment. The production well required special close-out procedures
involving blasting. The concern for this very deep well was that ground
water from the upper non-potable aquifer could migrate down to the
lower potable aquifer along possible voids on the outside of the well
sleeve. Complete separation of these two aquifers was assured by
blasting the well sleeve open at a point where there was an impervious
clay layer between the upper and lower aquifers and then pumping in
grout material to seal the well.
Five-Year Review
EPA has completed two Five-Year Reviews for this Site. The first
was completed on September 30, 1994 and the second on September 30,
1999. Since the clean-up was ongoing these reviews were not required by
statute, but were conducted as a matter of policy.
Five-Year Reviews are required at sites where the remedial action
results in hazardous substances, pollutants or contaminants remain at
the site above levels that allow for unrestricted use and unrestricted
exposure. The response actions conducted at the Southern Maryland Wood
Treating Site are now complete, and allow for unlimited use and
unrestricted exposure, thus no additional Five-Year Reviews will be
conducted for this Site.
Community Involvement
Public participation activities have been satisfied as required in
CERCLA section 113(k), 42 U.S.C. 9613(k), and CERCLA section 117, 42
U.S.C. 9617. Documents in the Site docket which EPA relied on for
recommendation of the deletion of the Site from the NPL are available
to the public in the information repositories.
V. Deletion Action
EPA, with the concurrence of the State of Maryland, has determined
that all appropriate responses under CERCLA have been completed at the
Site, and that no further response actions are necessary. Therefore,
EPA is deleting the Site from the NPL.
Because EPA considers this action to be noncontroversial and
routine, EPA is taking it without prior publication of a notice of
intent to delete. This action will be effective April 5, 2005, unless
EPA receives adverse comments by March 7, 2005, on this notice or the
parallel notice of intent to delete published in the ``Proposed Rules''
section of today's Federal Register. If adverse comments are received
within the 30-day public comment period, EPA will publish a timely
withdrawal of this direct final notice of deletion before the effective
date of the deletion and it will not take effect and EPA will also
prepare a response to comments and continue with the deletion process
on the basis of the notice of intent to delete and the comments already
received. There will be no additional opportunity to comment.
List of Subjects in 40 CFR Part 300
Environmental protection, Air pollution control, Chemicals,
Hazardous waste, Hazardous substances, Intergovernmental relations,
Penalties, Reporting and recordkeeping requirements, Superfund, Water
pollution control, Water supply.
Dated: January 26, 2005.
Richard J. Kampf,
Acting Regional Administrator, Region III.
0
For the reasons set out in the preamble, 40 CFR part 300 is amended as
follows:
PART 300--[AMENDED]
0
1. The authority citation for part 300 continues to read as follows:
Authority: 33 U.S.C. 1321(c)(2); 42 U.S.C. 9601-9657; E.O.
12777, 56 FR 54757, 3 CFR, 1991 Comp., p. 351; E.O. 12580, 52 FR
2923, 3 CFR, 1987 Comp., p. 193.
Appendix B--[Amended]
0
2. Table 1 of Appendix B to Part 300 is amended under Maryland (``MD'')
by removing the site name ``Southern Maryland Wood Treating,
Hollywood.''
[FR Doc. 05-2058 Filed 2-3-05; 8:45 am]
BILLING CODE 6560-50-P