National Oil and Hazardous Substance Pollution Contingency Plan; National Priorities List, 2454-2458 [E7-694]
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shall provide a standby towing vessel
that is FiFi class 1 equipped with a
minimum capacity of 100,000 pounds of
bollard pull and 4,000 horsepower that
is available to assist as directed by the
LNG vessel bridge watch required in
paragraph (d)(5) of this section.
(4) Requirements while LNG tankships
are moored both inside the LNG facility
slip and outside the LNG facility slip—
(i) When one LNG tankship is moored
inside and one LNG tankship is moored
outside of the LNG facility slip, the LNG
tankship moored outside of the LNG
facility slip shall have on-scene a
minimum of two escort towing vessels
each with a minimum of 100,000
pounds of bollard pull, 4,000
horsepower and capable of safely
operating in the indirect mode in order
to escort transiting vessels 1,600 gross
tons or greater past the moored LNG
tankship. At least one of these towing
vessels shall be FiFi Class 1 equipped.
In addition, the LNG tankship moored
inside of the slip shall have at least one
standby towing vessel with a minimum
of 100,000 pounds of bollard pull, 4,000
horsepower and FiFi Class 1 equipped
to take appropriate actions in an
emergency as directed by the LNG
vessel bridge watch required in
paragraph (d)(5) of this section.
(ii) When one LNG tankship is
moored outside and two LNG tankships
are moored inside the LNG facility slip,
the LNG tankship moored outside of the
LNG facility slip shall have on-scene a
minimum of two escort towing vessels
each with a minimum of 100,000
pounds of bollard pull, 4,000
horsepower and capable of safely
operating in the indirect mode in order
to escort transiting vessels 1,600 gross
tons or greater past the moored LNG
tankship. At least one of these towing
vessels shall be FiFi Class 1 equipped.
In addition, the LNG tankships moored
inside of the slip shall have at least one
standby towing vessel between the two
ships with a minimum of 100,000
pounds of bollard pull, 4,000
horsepower and FiFi Class 1 equipped
to take appropriate actions in an
emergency as directed by the LNG
vessel bridge watch required in
paragraph (d)(5) of this section.
(iii) In the event of an actual
emergency, escort towing vessels can be
utilized as stand-by towing vessels to
take appropriate actions as directed by
the LNG vessel bridge watch required in
paragraph (d)(5) of this section.
(5) Requirements for moored LNG
tankships—(i) While moored within the
RNA, each LNG tankship shall maintain
a bridge watch consisting of a docking
pilot or licensed deck officer who shall
monitor all vessels transiting past the
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LNG facility. In addition, the LNG
Bridge Watch shall communicate with
the pilots of vessels greater than 1600
gross tons at the points identified in
section (d)(6)(iii) of this section prior to
passing the LNG facility in order to take
actions of the towing vessel(s) required
in paragraphs (d)(2) through (4) of this
section.
(ii) While moored within the RNA,
LNG tankships shall have emergency
towing wires (fire wires) positioned one
meter above the waterline, both on the
off-shore bow and quarter of the ship.
LNG vessels equipped with waterline
bollards are exempt from this
requirement.
(6) Requirements for other vessels
while within the RNA—(i) Transiting
vessels 1,600 gross tons or greater, when
passing an LNG tankship moored
outside of the LNG facility slip, shall
have a minimum of two towing vessels
with a minimum capacity of 100,000
pounds of bollard pull, 4,000
horsepower, and the ability to operate
safely in the indirect mode, made-up in
such a way as to be immediately
available to arrest and control the
motion of an escorted vessel in the
event of steering, propulsion or other
casualty. At least one of the towing
vessels shall be FiFi Class 1 equipped.
While it is anticipated that vessels will
utilize the towing vessel services
required in paragraphs (d)(2)(i) and
(d)(4)(i) of this section, this section does
not preclude escorted vessel operators
from providing their own towing vessel
escorts, provided they meet the
requirements of this part.
(A) Outbound vessels shall be madeup and escorted from Bight Channel
Light 46 until the vessel is safely past
the LNG dock.
(B) Inbound vessels shall be made-up
and escorted from Elba Island Light 37
until the vessel is safely past the LNG
dock.
(ii) The requirements in paragraph
(d)(6)(i) of this section do not apply
when one or more LNG tankships are
moored in the LNG facility slip and no
LNG tankship is moored at the pier
outside of the LNG facility slip.
(iii) Vessels 1,600 gross tons or greater
shall make a broadcast on channel 13 at
the following points on the Savannah
River:
(A) Buoy ‘‘33’’ in the vicinity of Fields
Cut for inbound vessels;
(B) Buoy ‘‘53’’ in the vicinity of Fort
Jackson for outbound vessels.
(iv) Vessels 1,600 gross tons or greater
shall at a minimum, transit at bare
steerageway when within an area 1,000
yards on either side of the LNG facility
slip to minimize potential wake or surge
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damage to the LNG facility and vessel(s)
within the slip.
(v) Vessels 1,600 gross tons or greater
shall not meet nor overtake within an
area 1,000 yards on either side of the
LNG facility slip when an LNG tankship
is present within the slip.
(vi) All vessels less than 1,600 gross
tons shall not approach within 70 yards
of an LNG tankship, carrying LNG in
excess of heel, without the permission
of the Captain of the Port.
(vii) Except for vessels involved in
those operations noted in paragraph (c)
of this section entitled Applicability, no
vessel shall enter the LNG facility slip
at any time without the permission of
the Captain of the Port.
(e) Waivers. (1) The COTP may waive
any requirement in this section, if the
COTP finds that it is in the best interest
of safety or in the interest of national
security. Such waivers may be verbal or
in writing.
(2) An application for a waiver of
these requirements must state the
compelling need for the waiver and
describe the proposed operation and
methods by which adequate levels of
safety are to be obtained.
(f) Enforcement. Violations of this
section should be reported to the
Captain of the Port, Savannah, at (912)
652–4353. In accordance with the
general regulations in § 165.13 of this
part, no person may cause or authorize
the operation of a vessel in the regulated
navigation area contrary to the
provisions of this section.
Dated: January 5, 2007.
D. W. Kunkel,
Rear Admiral, U.S. Coast Guard, Commander,
Seventh Coast Guard District.
[FR Doc. E7–728 Filed 1–18–07; 8:45 am]
BILLING CODE 4910–15–P
ENVIRONMENTAL PROTECTION
AGENCY
40 CFR Part 300
[EPA–HQ–SFUND–1986–0005; FRL–8271–2]
National Oil and Hazardous Substance
Pollution Contingency Plan; National
Priorities List
Environmental Protection
Agency (EPA).
ACTION: Direct final notice of deletion of
the Avenue E Groundwater
Contamination Superfund Site from the
National Priorities List.
AGENCY:
SUMMARY: The Environmental Protection
Agency (EPA), Region V is publishing a
direct final notice of deletion of the
Avenue E Groundwater Contamination
Superfund Site (Site), located in
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Federal Register / Vol. 72, No. 12 / Friday, January 19, 2007 / Rules and Regulations
Traverse City, Michigan from the
National Priorities List (NPL). The NPL,
promulgated pursuant to section 105 of
the Comprehensive Environmental
Response, Compensation, and Liability
Act (CERCLA) of 1980, as amended, is
appendix B of 40 CFR part 300, which
is the National Oil and Hazardous
Substances Pollution Contingency Plan
(NCP). This direct final deletion is being
published by EPA with the concurrence
of the State of Michigan, through the
Michigan Department of Environmental
Quality (MDEQ), because EPA has
determined that all appropriate
response actions under CERCLA have
been completed, and, therefore, further
remedial action pursuant to CERCLA is
not necessary at this time.
DATES: This direct final notice of
deletion will be effective March 20,
2007 unless EPA receives adverse
comments by February 20, 2007. If
adverse comments are received, EPA
will publish a timely withdrawal of the
direct final notice of deletion in the
Federal Register informing the public
that the deletion will not take effect.
ADDRESSES: Submit your comments,
identified by Docket ID No. EPA–HQ–
SFUND–1986–0005 by one of the
following methods:
• https://www.regulations.gov: Follow
the on-line instructions for submitting
comments.
• E-mail: beard.gladys@epa.gov.
• Fax: Gladys Beard at (312) 886–
4071.
• Mail: Dave Novak, Community
Involvement Coordinator, U.S. EPA (P–
19J), 77 W. Jackson, Chicago, Il 60604,
312–886–0269 or 1–800–621–8431.
• Hand Delivery: Dave Novak,
Community Involvement Coordinator,
(P–19J), U.S. Environmental Protection
Agency, 77 West Jackson Boulevard,
Chicago, Illinois 60604. Such deliveries
are only accepted during the Regional
Office normal hours of operation, and
special arrangements should be made
for deliveries of boxed information. The
Regional Office official hours of
business are Monday through Friday,
8:30 a.m. to 4:30 p.m. excluding Federal
holidays.
Instructions: Direct your comments to
Docket ID No. EPA–HQ–SFUND–1986–
0005. EPA’s policy is that all comments
received will be included in the public
docket without change and may be
made available online at https://
www.regulations.gov, including any
personal information provided, unless
the comment includes information
claimed to be Confidential Business
Information (CBI) or other information
whose disclosure is restricted by statute.
Do not submit information that you
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consider to be CBI or otherwise
protected through https://
www.regulations.gov or e-mail. The
https://www.regulations.gov Web site is
an ‘‘anonymous access’’ system, which
means EPA will not know your identity
or contact information unless you
provide it in the body of your comment.
If you send an e-mail comment directly
to EPA without going through https://
www.regulations.gov your e-mail
address will be automatically captured
and included as part of the comment
that is placed in the public docket and
made available on the Internet. If you
submit an electronic comment, EPA
recommends that you include your
name and other contact information in
the body of your comment and with any
disk or CD-ROM you submit. If EPA
cannot read your comment due to
technical difficulties and cannot contact
you for clarification, EPA may not be
able to consider your comment.
Electronic files should avoid the use of
special characters, any form of
encryption, and be free of any defects or
viruses. For additional instructions on
submitting comments, go to Section I of
the SUPPLEMENTARY INFORMATION section
of this document.
Docket: All documents in the docket
are listed in the https://
www.regulations.gov index. Although
listed in the index, some information is
not publicly available, e.g., CBI or other
information whose disclosure is
restricted by statute. Certain other
material, such as copyrighted material,
will be publicly available only in hard
copy. Publicly available docket
materials are available either
electronically in https://
www.regulations.gov or in hard copy at
the Environmental Protection Agency,
Region 5, Superfund Division, 77 West
Jackson Boulevard, Chicago, Illinois
60604. This Facility is open from 8:30
a.m. to 4:30 p.m., Monday through
Friday, excluding legal holidays. We
recommend that you telephone Gladys
Beard, State NPL Deletion Process
Manager at (312) 886–7253, before
visiting the Region 5 office.
Information Repositories:
Comprehensive information about the
Site is available for viewing and copying
at the Site information repositories
located at: EPA Region V Record Center,
77 W. Jackson, Chicago, Il 60604, (312)
353–5821, Monday through Friday 8:30
a.m. to 4:30 p.m.
FOR FURTHER INFORMATION CONTACT:
Linda Martin, Remedial Project Manager
at (312) 886–3854,
Martin.Lindab@epa.gov or Gladys
Beard, State NPL Deletion Process
Manager at (312) 886–7253,
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Beard.Gladys@epa.gov or 1–800–621–
8431, (SR–6J), U.S. EPA Region V, 77 W.
Jackson, Chicago, IL 60604.
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 V is publishing this direct
final notice of deletion of the Avenue E
Groundwater Contamination 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 section
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 non-controversial and routine, EPA is
taking it without prior publication of a
notice of intent to delete. This action
will be effective March 20, 2007 unless
EPA receives adverse comments by
February 20, 2007 on this document. If
adverse comments are received within
the 30-day public comment period on
this document, EPA will publish a
timely withdrawal of this direct final
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 Avenue E Groundwater
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 release 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;
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ii. All appropriate Fund-financed
(Hazardous Substance Superfund
Response Trust Fund) responses under
CERCLA have 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 this Site:
(1) The EPA consulted with the State
of Michigan on the deletion of the Site
from the NPL prior to developing this
direct final notice of deletion.
(2) Michigan concurred with deletion
of the Site from the NPL.
(3) Concurrently with the publication
of this direct final notice of deletion a
notice of intent to delete is 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) The 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 document, EPA will
publish a timely notice of withdrawal of
this direct final notice of deletion before
its effective date and will prepare a
response to comments and continue
with a decision on the deletion based on
the notice of intent to delete and the
comments already received.
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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 remedy at the Avenue E Site was
found to be protective of human health
and the environment. This
determination was documented in the
five year review conducted in 2005. All
groundwater contaminants associated
with the Coast Guard facility have
reached the clean up standards
specified in the 1987 agreement
between the Coast Guard and the State
of Michigan. All active remediation has
been completed and no further actions
are required for this Site. The following
sections outline additional information
reviewed as part of an NPL deletion
determination.
Site Location
The Avenue E Groundwater
Contamination Superfund Site was a
groundwater contamination plume
located in East Bay Township in
Traverse County, Traverse City,
Michigan. The source of the
contamination was located on the U.S.
Coast Guard (USCG) Air Station. The
plume was located west of the
intersection of Parsons Road and Aero
Park Drive. It was traced to the
northwest corner of an industrial park
back lot located southwest of Nish-NahBee Industries. The plume eventually
extended to the East Arm of the Grand
Traverse Bay.
Site History
In 1980, residents of Avenue E in East
Bay Township complained of odors and
foaming in their well water. Subsequent
investigation by the Michigan
Department of Public Health (MDPH)
and the Michigan Department of Natural
Resources (MDNR) revealed the
existence of a plume of contamination
in the underlying aquifer. The plume
consisted primarily of hydrocarbons
found in petroleum distillates,
including benzene and toluene, and
some solvents.
Removal Actions Performed
On June 10, 1982, members of the
USCG District 9 air station met with
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Region V removal staff to discuss the
possibilities and procedures for
receiving CERCLA funds to pay for the
connection of the homes within the
Avenue E area of concern to the existing
public water supply system while the
USCG conducted a hydrogeologic
investigation to further determine the
source of contamination identified by
MDNR and MDPH. According to the On
Scene Coordinator’s (OSC) report, the
USCG could not pay for such
connections without knowing their
extent of responsibility. The Coast
Guard agreed to enter into a
Memorandum of Understanding (MOU)
with USEPA assuring to reimburse the
Agency for all costs incurred for the
connections should the USCG be found
to be the responsible party. USEPA then
proceeded with the removal action and
all home connections to the existing
public water supply were completed on
December 12, 1982. A total of 59 homes
received city water with nine home
owners declining to receive full
hookups. A total of 67 homes received
some level of service from this action.
The total cost reimbursed by the USCG
to USEPA was $137,540. Although not
all residents received full hookups to
the public water supply system, the
plume associated with the Coast Guard
property no longer exists and therefore
would indicate that no risk currently
exists to those not fully connected to the
public water supply from the
contamination associated with the Coast
Guard property.
Remedial Investigation and Feasibility
Study (RI/FS)
Groundwater
The first investigation of the site was
conducted by the MDNR in 1982. The
State Agency’s study objectives were to
locate and delineate the contaminant
plume, identify and determine the
distribution of its component parts and
locate the probable source area of the
plume. The MDNR drilled 24 wells and
two auger holes along Parsons Road and
around the lots of Jacklyn Steel and
Nish-Nah-Bee Industries.
As a result of this investigation, the
MDNR determined that the USCG Air
Station property was part of the
suspected source area. The USCG
contracted with the United States
Geological Service (USGS) in July 1982
to undertake a study of the area’s
hydrogeologic conditions. Objectives of
this study were:
(1) To determine the rate and
direction of groundwater flow;
(2) locate the source or sources of
contaminants;
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(3) determine the extent and
distribution of contaminants;
(4) evaluate hydrologically suitable
locations for installing purge wells
should that be necessary.
The USCG installed a total of 138
wells on the Coast Guard property, up
and down gradient of the base in and
around the industrial areas and
residential area. Five wells were
installed to conduct a pump test for
determining aquifer characteristics.
At the request of the USCG, a team
from the University of Michigan
conducted a study of the site from
February through August 1984. Building
on the data and results given in the
USCG report, the study was to be
complementary to the USCG effort. By
providing data and analysis on the time
variation of contaminants, the effect of
soil adsorptive characteristics on
contaminant distribution and
movement, and the potential risk posed
by the contamination to public health,
probable contaminant sources could be
determined and remedial action
alternatives developed.
A total of 24 wells including 15
existing and nine new wells were
selected for analysis based on previous
information. These wells were sampled
six times at 21-day intervals. Statistical
analysis was performed on the data and
various data plots were generated. This
information was used to provide
supporting information for developing
response alternatives. A preliminary
risk assessment was made for the
various chemical components found in
the plume. A contaminant transport
computer model was used to help
determine the possible origin of the
plume and the effectiveness of various
purge well combinations. Finally,
several cleanup alternatives were
identified and discussed.
Following the 1982 removal action,
the Coast Guard also contracted and
supervised additional groundwater
investigations complementing those
conducted earlier by the MDNR to aid
in the planning of a long term response.
Results of these investigations
concluded the following:
• A plume of contamination was
found stretching from near the Hanger/
Administration (HA) building on the
Coast Guard Property to East Bay. It was
approximately 4300 feet long and from
180 to 400 feet wide. Hydrocarbon
spectra of the contamination were
consistent with that of 115/145 aviation
gasoline. Major components were
benzene, toluene and xylene with a
maximum concentration of 3640 µg/l,
553000 µg/l and 5410 µg/l, respectively.
• An additional contaminant plume
was discovered on the Coast Guard
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property with parent origin near the
Coast Guard’s fueling station. Around
the fueling station several inches of pure
JP–4 jet fuel product were found floating
on the water table.
• A third contaminant plume was
found along the Coast Guard’s south
fence line up-gradient from the fuel
farm area. Possible origins include a
1979 Republic Airlines jet fuel spill and
various underground storage tanks in
the area that had since been removed.
• The contaminants were located in a
sandy aquifer of high permeability.
Groundwater flow is to the northeast
with a velocity of approximately five
feet per day.
• A probable source of the original
plume was a fuel spill in 1969 at the
Coast Guard base in which about 2500
gallons of aviation gasoline leaked into
the ground at a fuel station located
under the northwest corner of the new
HA building. The second plume may
have originated from leaking JP4 fuel
tanks at the current fuel station.
To mitigate adverse effects discovered
during the investigation, interim
responses were implemented. In
addition to providing city water
connections to affected residents in the
Avenue E area, the USCG also installed
and operated interdiction and purge
systems with treatment capability to
prevent additional offsite contaminant
migration and removed and/or repaired
tanks at the Coast Guard fueling station.
In addition to the investigation of
groundwater, the USGS and the
University of Michigan (UM) reported
numerous measurements of organics in
the soils at the Coast Guard Air Station.
The UM study found maximum
concentrations of 25.4 µg/g benzene,
27.6 µg/g toluene, and 229 µg/g xylene.
Analyses were made for seven other
hydrocarbons with negative results. Soil
borings indicate that much of the
organic material was adsorbed on the
soil in a 6’’ to 12’’ thick layer in the
capillary zone immediately above the
water table. The UM suggested that this
zone was slowly leaking organic
contaminants into the groundwater over
time and was serving as a source for the
plume.
Record of Decision Findings
There was no Record of Decision
(ROD) for this site. In 1987, an
agreement between the State of
Michigan and the USCG was negotiated.
USCG agreed to pay the cost of
implementing the cleanup of
contamination emanating from the
USCG air station. All clean up activities
associated with the Ave E site were
conducted as part of this Settlement
agreement.
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Characterization of Remaining Risk
The municipal water supply system
serving the East Bay township
residences and business currently meets
federal and state drinking water
standards and is safe for human
consumption. The source of the
township’s municipal water system is
groundwater wells located in East Bay
Township and monitored every three
years. The wells used to supply water to
East Bay Township are quite a distance
up-gradient of the Coast Guard Facility,
and the monitoring frequency for these
wells is adequate.
Currently, soil vapor intrusion is not
considered a possible problem at the
Site. Down gradient monitoring wells
placed along Avenue E in the residential
area where the plume was traced, have
found no detectable levels of
contaminants of concern associated
with the USCG plume.
Response Actions
In 1987, an agreement between the
State of Michigan and the USCG was
negotiated. USCG agreed to pay the cost
of implementing the cleanup of
contamination emanating from the site.
The cleanup involved extraction and
treatment of contaminated groundwater.
Some of the other remedial actions
included enhanced biodegradation
using hydrogen peroxide and nitrates to
reduce plume contaminates. The USCG
also implemented groundwater sparging
with vapor extraction, venting with
vapor extraction, soil venting, natural
attenuation and surfactant injection and
extraction. All of these additional
remedial measures helped to reduce the
contaminant source in the soil and
speed treatment of the groundwater
through the pump and treatment
system. The contaminated groundwater
was treated by activated carbon prior to
discharge to the Traverse City Sewer
system. By 1996, the contaminant levels
rarely exceeded the cleanup criteria
stipulated in the 1987 settlement
agreement. In 1999, the wells remained
clean.
A Preliminary Closeout Report
(PCOR) was completed by U.S. EPA in
September 2000. The purpose of the
PCOR was to document that all
construction activity had been
completed at the Site.
Institutional Controls
There were no provisions for
institutional controls in any of the
agreements associated with the clean up
and monitoring of this site as the
groundwater was to be remediated to
unrestricted use.
E:\FR\FM\19JAR1.SGM
19JAR1
2458
Federal Register / Vol. 72, No. 12 / Friday, January 19, 2007 / Rules and Regulations
Cleanup Standards
The cleanup standards in the 1987
Settlement Agreement were designed to
meet the contaminant levels for
benzene, tetrachloroethylene and
trichloroethylene as required by the
State of Michigan (MDNR), based on
acceptable standards in place at the time
the Settlement Agreement was issued.
This was an agreement between the
MDNR and USCG. If these standards
were not met, then additional measures
would be taken. This Site is being
deleted because the remedial response
met all cleanup standards outlined in
the 1987 Settlement Agreement.
Operation and Maintenance
USCG has completed monitoring
groundwater at the site in accordance
with the Settlement Agreement between
the State of Michigan and the USCG
filed on June 1, 1987. Per the Settlement
Agreement with the State of Michigan,
the USCG operated two interdiction
fields (pump and treatment systems).
There was one at the North of the base
and one at the South of the base. They
consisted of wells IN2, IN3, IN4, IN5,
and IN6 in the North field (avgas plume)
and PP5, PP7, and PP8 in the South
Field (JP–4 field). Each interdiction
point had point of compliance wells
along the USCG property boundary. The
North field point of compliance wells
were M56, M1, M4, M3, and M55. The
South field point of compliance wells
were M22, M61, M62, and M64. There
were a number of other wells installed
over the course of the project for various
reasons. In 2000, with consent of
MDEQ, the USCG removed wells PP5,
PP6, PP7 and PP8. In 2001, with the
consent of MDEQ, wells IN2, IN3, IN4,
IN5 and IN6 were removed along with
the associated piping, manifolds, carbon
treatment units, and discharge lines for
both the North and South interdiction
fields. The remaining monitoring wells
will be removed after the 10 year post
closure period. The post closure period
started in October 2005.
frosa on PROD1PC71 with RULES
Five-Year Review
EPA conducted a five-year review of
the Site in 2005. In the review, EPA
concluded that all remedial actions are
complete and monitoring indicates that
all clean up goals have been reached in
connection with the 1987 Settlement
Agreement. Therefore, no future fiveyear review, are required 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 deletion docket which
VerDate Aug<31>2005
17:42 Jan 18, 2007
Jkt 211001
EPA relied on for recommendation of
the deletion of this Site from the NPL
are available to the public in the
information repositories, and in https://
www.regulations.gov.
V. Deletion Action
List of Subjects in 40 CFR Part 300
Environmental protection, Air
pollution control, Chemicals, Hazardous
waste, Hazardous substances,
Intergovernmental relations, Penalties,
Reporting and record keeping
requirements, Superfund, Water
pollution control, Water supply.
Dated:January 9, 2007.
Mary A. Gade,
Regional Administrator, U.S. EPA Region V.
For the reasons set out in this
document, 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 ‘‘MI’’ by removing the
entry for ‘‘Avenue E Groundwater
Contamination’’ and the city ‘‘Traverse
City.’’
I
[FR Doc. E7–694 Filed 1–18–07; 8:45 am]
BILLING CODE 6560–50–P
Frm 00038
Fmt 4700
National Oceanic and Atmospheric
Administration
50 CFR Part 648
RIN 0648–AT60
The EPA, with concurrence of the
State of Michigan, determined that all
appropriate responses under CERCLA
have been completed, and that no
further response actions under CERCLA
are necessary. Therefore, EPA is
deleting the Site from the NPL.
Because EPA considers this action to
be non-controversial and routine, EPA is
taking it without prior publication. This
action will be effective March 20, 2007
unless EPA receives adverse comments
by February 20, 2007. If adverse
comments are received within the 30day 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. EPA will prepare a
response to comments and, as
appropriate, 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.
PO 00000
DEPARTMENT OF COMMERCE
Sfmt 4700
[Docket No.061020273–7001–03; I.D.
010307A]
Fisheries of the Northeastern United
States; Summer Flounder Fishery;
Emergency Rule
National Marine Fisheries
Service (NMFS), National Oceanic and
Atmospheric Administration (NOAA),
Commerce.
ACTION: Temporary rule; emergency
action; request for comments.
AGENCY:
SUMMARY: NMFS is implementing,
through this emergency rule, revised
summer flounder total allowable
landings (TAL) for the 2007 fishing year.
This emergency rule specifies allowed
harvest limits for both the commercial
and recreational summer flounder
fisheries. The TAL contained within
this emergency rule supersedes the
previous harvest limits for summer
flounder that became effective on
January 1, 2007. This action continues
the prohibition on federally permitted
commercial vessels landing summer
flounder in Delaware in 2007 due to
continued quota repayment of previous
year’s overages.
This emergency rule is necessary to
increase the 2007 summer flounder
harvest levels consistent with the
recently enacted Magnuson-Stevens
Fishery Conservation and Management
Reauthorization Act of 2006
(Reauthorized Magnuson-Stevens Act),
while ensuring compliance with
regulations implementing the Summer
Flounder, Scup, and Black Sea Bass
Fishery Management Plan (FMP). In
addition, this action will continue to
ensure that fishing mortality rates (F) or
exploitation rates, as specified in the
FMP, are not exceeded.
DATES: Effective from January 19, 2007
through July 18, 2007. Comments must
be received at the appropriate address or
fax number (see ADDRESSES) by 5 p.m.,
local time, on February 20, 2007.
ADDRESSES: Written comments should
be submitted by any of the following
methods:
• Mail: Patricia A. Kurkul, Regional
Administrator, NMFS, Northeast
Regional Office, One Blackburn Drive,
Gloucester, MA 01930. Mark the outside
of the envelope, ‘‘Comments on Summer
Flounder Emergency Action.’’
• E-mail:
SummerFlounderEmergency@noaa.gov
E:\FR\FM\19JAR1.SGM
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Agencies
[Federal Register Volume 72, Number 12 (Friday, January 19, 2007)]
[Rules and Regulations]
[Pages 2454-2458]
From the Federal Register Online via the Government Printing Office [www.gpo.gov]
[FR Doc No: E7-694]
-----------------------------------------------------------------------
ENVIRONMENTAL PROTECTION AGENCY
40 CFR Part 300
[EPA-HQ-SFUND-1986-0005; FRL-8271-2]
National Oil and Hazardous Substance Pollution Contingency Plan;
National Priorities List
AGENCY: Environmental Protection Agency (EPA).
ACTION: Direct final notice of deletion of the Avenue E Groundwater
Contamination Superfund Site from the National Priorities List.
-----------------------------------------------------------------------
SUMMARY: The Environmental Protection Agency (EPA), Region V is
publishing a direct final notice of deletion of the Avenue E
Groundwater Contamination Superfund Site (Site), located in
[[Page 2455]]
Traverse City, Michigan from the National Priorities List (NPL). The
NPL, promulgated pursuant to section 105 of the Comprehensive
Environmental Response, Compensation, and Liability Act (CERCLA) of
1980, as amended, is appendix B of 40 CFR part 300, which is the
National Oil and Hazardous Substances Pollution Contingency Plan (NCP).
This direct final deletion is being published by EPA with the
concurrence of the State of Michigan, through the Michigan Department
of Environmental Quality (MDEQ), because EPA has determined that all
appropriate response actions under CERCLA have been completed, and,
therefore, further remedial action pursuant to CERCLA is not necessary
at this time.
DATES: This direct final notice of deletion will be effective March 20,
2007 unless EPA receives adverse comments by February 20, 2007. If
adverse comments are received, EPA will publish a timely withdrawal of
the direct final notice of deletion in the Federal Register informing
the public that the deletion will not take effect.
ADDRESSES: Submit your comments, identified by Docket ID No. EPA-HQ-
SFUND-1986-0005 by one of the following methods:
https://www.regulations.gov: Follow the on-line
instructions for submitting comments.
E-mail: beard.gladys@epa.gov.
Fax: Gladys Beard at (312) 886-4071.
Mail: Dave Novak, Community Involvement Coordinator, U.S.
EPA (P-19J), 77 W. Jackson, Chicago, Il 60604, 312-886-0269 or 1-800-
621-8431.
Hand Delivery: Dave Novak, Community Involvement
Coordinator, (P-19J), U.S. Environmental Protection Agency, 77 West
Jackson Boulevard, Chicago, Illinois 60604. Such deliveries are only
accepted during the Regional Office normal hours of operation, and
special arrangements should be made for deliveries of boxed
information. The Regional Office official hours of business are Monday
through Friday, 8:30 a.m. to 4:30 p.m. excluding Federal holidays.
Instructions: Direct your comments to Docket ID No. EPA-HQ-SFUND-
1986-0005. EPA's policy is that all comments received will be included
in the public docket without change and may be made available online at
https://www.regulations.gov, including any personal information
provided, unless the comment includes information claimed to be
Confidential Business Information (CBI) or other information whose
disclosure is restricted by statute. Do not submit information that you
consider to be CBI or otherwise protected through https://
www.regulations.gov or e-mail. The https://www.regulations.gov Web site
is an ``anonymous access'' system, which means EPA will not know your
identity or contact information unless you provide it in the body of
your comment. If you send an e-mail comment directly to EPA without
going through https://www.regulations.gov your e-mail address will be
automatically captured and included as part of the comment that is
placed in the public docket and made available on the Internet. If you
submit an electronic comment, EPA recommends that you include your name
and other contact information in the body of your comment and with any
disk or CD-ROM you submit. If EPA cannot read your comment due to
technical difficulties and cannot contact you for clarification, EPA
may not be able to consider your comment. Electronic files should avoid
the use of special characters, any form of encryption, and be free of
any defects or viruses. For additional instructions on submitting
comments, go to Section I of the SUPPLEMENTARY INFORMATION section of
this document.
Docket: All documents in the docket are listed in the https://
www.regulations.gov index. Although listed in the index, some
information is not publicly available, e.g., CBI or other information
whose disclosure is restricted by statute. Certain other material, such
as copyrighted material, will be publicly available only in hard copy.
Publicly available docket materials are available either electronically
in https://www.regulations.gov or in hard copy at the Environmental
Protection Agency, Region 5, Superfund Division, 77 West Jackson
Boulevard, Chicago, Illinois 60604. This Facility is open from 8:30
a.m. to 4:30 p.m., Monday through Friday, excluding legal holidays. We
recommend that you telephone Gladys Beard, State NPL Deletion Process
Manager at (312) 886-7253, before visiting the Region 5 office.
Information Repositories: Comprehensive information about the Site
is available for viewing and copying at the Site information
repositories located at: EPA Region V Record Center, 77 W. Jackson,
Chicago, Il 60604, (312) 353-5821, Monday through Friday 8:30 a.m. to
4:30 p.m.
FOR FURTHER INFORMATION CONTACT: Linda Martin, Remedial Project Manager
at (312) 886-3854, Martin.Lindab@epa.gov or Gladys Beard, State NPL
Deletion Process Manager at (312) 886-7253, Beard.Gladys@epa.gov or 1-
800-621-8431, (SR-6J), U.S. EPA Region V, 77 W. Jackson, Chicago, IL
60604.
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 V is publishing this direct final notice of deletion of
the Avenue E Groundwater Contamination 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 section 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 non-controversial and
routine, EPA is taking it without prior publication of a notice of
intent to delete. This action will be effective March 20, 2007 unless
EPA receives adverse comments by February 20, 2007 on this document. If
adverse comments are received within the 30-day public comment period
on this document, EPA will publish a timely withdrawal of this direct
final 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 Avenue E Groundwater
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 release 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;
[[Page 2456]]
ii. All appropriate Fund-financed (Hazardous Substance Superfund
Response Trust Fund) responses under CERCLA have 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 this Site:
(1) The EPA consulted with the State of Michigan on the deletion of
the Site from the NPL prior to developing this direct final notice of
deletion.
(2) Michigan concurred with deletion of the Site from the NPL.
(3) Concurrently with the publication of this direct final notice
of deletion a notice of intent to delete is 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) The 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 document, EPA will publish a timely notice of
withdrawal of this direct final notice of deletion before its effective
date and will prepare a response to comments and continue with a
decision on the deletion based on 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 remedy at the Avenue E Site was found to be protective of human
health and the environment. This determination was documented in the
five year review conducted in 2005. All groundwater contaminants
associated with the Coast Guard facility have reached the clean up
standards specified in the 1987 agreement between the Coast Guard and
the State of Michigan. All active remediation has been completed and no
further actions are required for this Site. The following sections
outline additional information reviewed as part of an NPL deletion
determination.
Site Location
The Avenue E Groundwater Contamination Superfund Site was a
groundwater contamination plume located in East Bay Township in
Traverse County, Traverse City, Michigan. The source of the
contamination was located on the U.S. Coast Guard (USCG) Air Station.
The plume was located west of the intersection of Parsons Road and Aero
Park Drive. It was traced to the northwest corner of an industrial park
back lot located southwest of Nish-Nah-Bee Industries. The plume
eventually extended to the East Arm of the Grand Traverse Bay.
Site History
In 1980, residents of Avenue E in East Bay Township complained of
odors and foaming in their well water. Subsequent investigation by the
Michigan Department of Public Health (MDPH) and the Michigan Department
of Natural Resources (MDNR) revealed the existence of a plume of
contamination in the underlying aquifer. The plume consisted primarily
of hydrocarbons found in petroleum distillates, including benzene and
toluene, and some solvents.
Removal Actions Performed
On June 10, 1982, members of the USCG District 9 air station met
with Region V removal staff to discuss the possibilities and procedures
for receiving CERCLA funds to pay for the connection of the homes
within the Avenue E area of concern to the existing public water supply
system while the USCG conducted a hydrogeologic investigation to
further determine the source of contamination identified by MDNR and
MDPH. According to the On Scene Coordinator's (OSC) report, the USCG
could not pay for such connections without knowing their extent of
responsibility. The Coast Guard agreed to enter into a Memorandum of
Understanding (MOU) with USEPA assuring to reimburse the Agency for all
costs incurred for the connections should the USCG be found to be the
responsible party. USEPA then proceeded with the removal action and all
home connections to the existing public water supply were completed on
December 12, 1982. A total of 59 homes received city water with nine
home owners declining to receive full hookups. A total of 67 homes
received some level of service from this action. The total cost
reimbursed by the USCG to USEPA was $137,540. Although not all
residents received full hookups to the public water supply system, the
plume associated with the Coast Guard property no longer exists and
therefore would indicate that no risk currently exists to those not
fully connected to the public water supply from the contamination
associated with the Coast Guard property.
Remedial Investigation and Feasibility Study (RI/FS)
Groundwater
The first investigation of the site was conducted by the MDNR in
1982. The State Agency's study objectives were to locate and delineate
the contaminant plume, identify and determine the distribution of its
component parts and locate the probable source area of the plume. The
MDNR drilled 24 wells and two auger holes along Parsons Road and around
the lots of Jacklyn Steel and Nish-Nah-Bee Industries.
As a result of this investigation, the MDNR determined that the
USCG Air Station property was part of the suspected source area. The
USCG contracted with the United States Geological Service (USGS) in
July 1982 to undertake a study of the area's hydrogeologic conditions.
Objectives of this study were:
(1) To determine the rate and direction of groundwater flow;
(2) locate the source or sources of contaminants;
[[Page 2457]]
(3) determine the extent and distribution of contaminants;
(4) evaluate hydrologically suitable locations for installing purge
wells should that be necessary.
The USCG installed a total of 138 wells on the Coast Guard
property, up and down gradient of the base in and around the industrial
areas and residential area. Five wells were installed to conduct a pump
test for determining aquifer characteristics.
At the request of the USCG, a team from the University of Michigan
conducted a study of the site from February through August 1984.
Building on the data and results given in the USCG report, the study
was to be complementary to the USCG effort. By providing data and
analysis on the time variation of contaminants, the effect of soil
adsorptive characteristics on contaminant distribution and movement,
and the potential risk posed by the contamination to public health,
probable contaminant sources could be determined and remedial action
alternatives developed.
A total of 24 wells including 15 existing and nine new wells were
selected for analysis based on previous information. These wells were
sampled six times at 21-day intervals. Statistical analysis was
performed on the data and various data plots were generated. This
information was used to provide supporting information for developing
response alternatives. A preliminary risk assessment was made for the
various chemical components found in the plume. A contaminant transport
computer model was used to help determine the possible origin of the
plume and the effectiveness of various purge well combinations.
Finally, several cleanup alternatives were identified and discussed.
Following the 1982 removal action, the Coast Guard also contracted
and supervised additional groundwater investigations complementing
those conducted earlier by the MDNR to aid in the planning of a long
term response. Results of these investigations concluded the following:
A plume of contamination was found stretching from near
the Hanger/Administration (HA) building on the Coast Guard Property to
East Bay. It was approximately 4300 feet long and from 180 to 400 feet
wide. Hydrocarbon spectra of the contamination were consistent with
that of 115/145 aviation gasoline. Major components were benzene,
toluene and xylene with a maximum concentration of 3640 [mu]g/l, 553000
[mu]g/l and 5410 [mu]g/l, respectively.
An additional contaminant plume was discovered on the
Coast Guard property with parent origin near the Coast Guard's fueling
station. Around the fueling station several inches of pure JP-4 jet
fuel product were found floating on the water table.
A third contaminant plume was found along the Coast
Guard's south fence line up-gradient from the fuel farm area. Possible
origins include a 1979 Republic Airlines jet fuel spill and various
underground storage tanks in the area that had since been removed.
The contaminants were located in a sandy aquifer of high
permeability. Groundwater flow is to the northeast with a velocity of
approximately five feet per day.
A probable source of the original plume was a fuel spill
in 1969 at the Coast Guard base in which about 2500 gallons of aviation
gasoline leaked into the ground at a fuel station located under the
northwest corner of the new HA building. The second plume may have
originated from leaking JP4 fuel tanks at the current fuel station.
To mitigate adverse effects discovered during the investigation,
interim responses were implemented. In addition to providing city water
connections to affected residents in the Avenue E area, the USCG also
installed and operated interdiction and purge systems with treatment
capability to prevent additional offsite contaminant migration and
removed and/or repaired tanks at the Coast Guard fueling station. In
addition to the investigation of groundwater, the USGS and the
University of Michigan (UM) reported numerous measurements of organics
in the soils at the Coast Guard Air Station. The UM study found maximum
concentrations of 25.4 [mu]g/g benzene, 27.6 [mu]g/g toluene, and 229
[mu]g/g xylene. Analyses were made for seven other hydrocarbons with
negative results. Soil borings indicate that much of the organic
material was adsorbed on the soil in a 6'' to 12'' thick layer in the
capillary zone immediately above the water table. The UM suggested that
this zone was slowly leaking organic contaminants into the groundwater
over time and was serving as a source for the plume.
Record of Decision Findings
There was no Record of Decision (ROD) for this site. In 1987, an
agreement between the State of Michigan and the USCG was negotiated.
USCG agreed to pay the cost of implementing the cleanup of
contamination emanating from the USCG air station. All clean up
activities associated with the Ave E site were conducted as part of
this Settlement agreement.
Characterization of Remaining Risk
The municipal water supply system serving the East Bay township
residences and business currently meets federal and state drinking
water standards and is safe for human consumption. The source of the
township's municipal water system is groundwater wells located in East
Bay Township and monitored every three years. The wells used to supply
water to East Bay Township are quite a distance up-gradient of the
Coast Guard Facility, and the monitoring frequency for these wells is
adequate.
Currently, soil vapor intrusion is not considered a possible
problem at the Site. Down gradient monitoring wells placed along Avenue
E in the residential area where the plume was traced, have found no
detectable levels of contaminants of concern associated with the USCG
plume.
Response Actions
In 1987, an agreement between the State of Michigan and the USCG
was negotiated. USCG agreed to pay the cost of implementing the cleanup
of contamination emanating from the site. The cleanup involved
extraction and treatment of contaminated groundwater. Some of the other
remedial actions included enhanced biodegradation using hydrogen
peroxide and nitrates to reduce plume contaminates. The USCG also
implemented groundwater sparging with vapor extraction, venting with
vapor extraction, soil venting, natural attenuation and surfactant
injection and extraction. All of these additional remedial measures
helped to reduce the contaminant source in the soil and speed treatment
of the groundwater through the pump and treatment system. The
contaminated groundwater was treated by activated carbon prior to
discharge to the Traverse City Sewer system. By 1996, the contaminant
levels rarely exceeded the cleanup criteria stipulated in the 1987
settlement agreement. In 1999, the wells remained clean.
A Preliminary Closeout Report (PCOR) was completed by U.S. EPA in
September 2000. The purpose of the PCOR was to document that all
construction activity had been completed at the Site.
Institutional Controls
There were no provisions for institutional controls in any of the
agreements associated with the clean up and monitoring of this site as
the groundwater was to be remediated to unrestricted use.
[[Page 2458]]
Cleanup Standards
The cleanup standards in the 1987 Settlement Agreement were
designed to meet the contaminant levels for benzene,
tetrachloroethylene and trichloroethylene as required by the State of
Michigan (MDNR), based on acceptable standards in place at the time the
Settlement Agreement was issued. This was an agreement between the MDNR
and USCG. If these standards were not met, then additional measures
would be taken. This Site is being deleted because the remedial
response met all cleanup standards outlined in the 1987 Settlement
Agreement.
Operation and Maintenance
USCG has completed monitoring groundwater at the site in accordance
with the Settlement Agreement between the State of Michigan and the
USCG filed on June 1, 1987. Per the Settlement Agreement with the State
of Michigan, the USCG operated two interdiction fields (pump and
treatment systems). There was one at the North of the base and one at
the South of the base. They consisted of wells IN2, IN3, IN4, IN5, and
IN6 in the North field (avgas plume) and PP5, PP7, and PP8 in the South
Field (JP-4 field). Each interdiction point had point of compliance
wells along the USCG property boundary. The North field point of
compliance wells were M56, M1, M4, M3, and M55. The South field point
of compliance wells were M22, M61, M62, and M64. There were a number of
other wells installed over the course of the project for various
reasons. In 2000, with consent of MDEQ, the USCG removed wells PP5,
PP6, PP7 and PP8. In 2001, with the consent of MDEQ, wells IN2, IN3,
IN4, IN5 and IN6 were removed along with the associated piping,
manifolds, carbon treatment units, and discharge lines for both the
North and South interdiction fields. The remaining monitoring wells
will be removed after the 10 year post closure period. The post closure
period started in October 2005.
Five-Year Review
EPA conducted a five-year review of the Site in 2005. In the
review, EPA concluded that all remedial actions are complete and
monitoring indicates that all clean up goals have been reached in
connection with the 1987 Settlement Agreement. Therefore, no future
five-year review, are required 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 deletion docket which EPA relied on for
recommendation of the deletion of this Site from the NPL are available
to the public in the information repositories, and in https://
www.regulations.gov.
V. Deletion Action
The EPA, with concurrence of the State of Michigan, determined that
all appropriate responses under CERCLA have been completed, and that no
further response actions under CERCLA are necessary. Therefore, EPA is
deleting the Site from the NPL.
Because EPA considers this action to be non-controversial and
routine, EPA is taking it without prior publication. This action will
be effective March 20, 2007 unless EPA receives adverse comments by
February 20, 2007. 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. EPA will prepare a response to
comments and, as appropriate, 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 record keeping requirements, Superfund, Water
pollution control, Water supply.
Dated:January 9, 2007.
Mary A. Gade,
Regional Administrator, U.S. EPA Region V.
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For the reasons set out in this document, 40 CFR part 300 is amended as
follows:
PART 300--[AMENDED]
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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]
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2. Table 1 of Appendix B to Part 300 is amended under ``MI'' by
removing the entry for ``Avenue E Groundwater Contamination'' and the
city ``Traverse City.''
[FR Doc. E7-694 Filed 1-18-07; 8:45 am]
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