National Oil and Hazardous Substances Pollution Contingency Plan; National Priorities List, 9023-9028 [05-3452]
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Federal Register / Vol. 70, No. 36 / Thursday, February 24, 2005 / Proposed Rules
implications.’’ This proposed rule does
not have tribal implications, as specified
in Executive Order 13175. As described
elsewhere in this preamble, today’s
proposed rule would only have the
effect of providing continual use of an
ocean disposal site pursuant to section
102(c) of MPRSA. Thus, Executive
Order 13175 does not apply to this
proposed rule.
7. Executive Order 13045
Executive Order 13045, Protection of
Children from Environmental Health
Risks and Safety Risks (62 FR 19885,
April 23, 1997) applies to any rule that:
(1) Is determined to be ‘‘economically
significant’’ as defined under Executive
Order 12866, and (2) concerns an
environmental health or safety risk that
EPA has reason to believe may have a
disproportionate effect on children. If
the regulatory action meets both criteria,
EPA must evaluate the environmental
health or safety effects of the planned
rule on children, and explain why the
planned regulation is preferable to other
potentially effective and reasonably
feasible alternatives considered by EPA.
This proposed rule is not subject to
the Executive Order because it is not
economically significant as defined in
Executive Order 12866, and because
EPA does not have any reason to believe
the environmental health or safety risks
addressed by this action present a
disproportionate risk to children. As
described elsewhere in this preamble,
today’s proposed rule would only have
the effect of providing continual use of
an ocean disposal site pursuant to
section 102(c) of MPRSA.
8. Executive Order 13211
This proposed rule is not subject to
Executive Order 13211, ‘‘Actions
Concerning Regulations That
Significantly Affect Energy Supply,
Distribution, or Use’’ (66 FR 28355 (May
22, 1001)) because it is not a significant
regulatory action under Executive Order
12866.
9. National Technology Transfer
Advancement Act
Section 12(d) of the National
Technology Transfer Advancement Act
of 1995 (‘‘NTTAA’’), Public Law 104–
113, section 12(d) (15 U.S.C. 272 note),
directs EPA to use voluntary consensus
standards in its regulatory activities
unless doing so would be inconsistent
with applicable law or otherwise
impractical. Voluntary consensus
standards are technical standards (e.g.,
materials specifications, test methods,
sampling procedures, and business
practices) that are developed or adopted
by voluntary consensus bodies. The
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NTTAA directs EPA to provide
Congress, through OMB, explanations
when the Agency decides not to use
available and applicable voluntary
consensus standards. This proposed
rule does not involve technical
standards. Therefore, EPA did not
consider the use of any voluntary
consensus standards.
10. Executive Order 12898
Executive Order 12898 requires that,
to the greatest extent practicable and
permitted by law, each Federal agency
must make achieving environmental
justice part of its mission. Executive
Order 12898 provides that each Federal
agency must conduct its programs,
policies, and activities that substantially
affect human health or the environment
in a manner that ensures that such
programs, policies, and activities do not
have the effect of excluding persons
(including populations) from
participation in, denying persons
(including populations) the benefits of,
or subjecting persons (including
populations) to discrimination under
such programs, policies, and activities
because of their race, color, or national
origin.
No action from this proposed rule
would have a disproportionately high
and adverse human health and
environmental effect on any particular
segment of the population. In addition,
this rule does not impose substantial
direct compliance costs on those
communities. Accordingly, the
requirements of Executive Order 12898
do not apply.
List of Subjects in 40 CFR Part 228
Environmental protection, Water
pollution control.
Dated: February 7, 2005.
J. I. Palmer, Jr.,
Regional Administrator for Region 4.
In consideration of the foregoing,
Subchapter H of Chapter I of Title 40 is
proposed to be amended as follows:
PART 228—[AMENDED]
1. The authority citation for part 228
continues to read as follows:
Authority: 33 U.S.C. 1412 and 1418.
2. Section 228.15 is amended by
adding paragraph (h)(23) to read as
follows:
§ 228.15 Dumping sites designated on a
final basis.
*
*
*
*
*
(h) * * *
(23) Port Royal, SC; Ocean Dredged
Material Disposal Site.
(i) Location (NAD83): 32°05.00′ N.,
80°36.47′ W.; 32° 05.00′ N., 80°35.30′
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W.; 32°04.00′ N., 80° 35.30′ W.;
32°04.00′ N., 80°36.47′ W.
(ii) Size: Approximately 1.0 square
nautical miles.
(iii) Depth: Averages 36 feet.
(iv) Primary use: Dredged material.
(v) Period of use: Continuing use.
(vi) Restriction: Disposal shall be
limited to suitable dredged material
from the greater Port Royal, South
Carolina vicinity. Disposal shall comply
with conditions set forth in the most
recent approved Site Management and
Monitoring Plan.
*
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*
*
*
[FR Doc. 05–3525 Filed 2–23–05; 8:45 am]
BILLING CODE 6560–50–P
ENVIRONMENTAL PROTECTION
AGENCY
40 CFR Part 300
[FRL–7874–8]
National Oil and Hazardous
Substances Pollution Contingency
Plan; National Priorities List
Environmental Protection
Agency.
ACTION: Notice of intent for partial
deletion at the Peterson/Puritan, Inc.
site from the National Priorities List.
AGENCY:
SUMMARY: The Environmental Protection
Agency (EPA) Region 1 announces its
intent to delete a portion of the
Peterson/Puritan, Inc. Superfund Site
(the Site), owned by Macklands Realty,
Inc. and Berkeley Realty, Co. (herein
Macklands and Berkeley properties),
from the National Priorities List (NPL).
EPA requests public comment on this
action. The NPL constitutes appendix B
to the National Oil and Hazardous
Substances Pollution Contingency Plan
(NCP), 40 CFR part 300, which EPA
promulgated pursuant to section 105 of
the Comprehensive Environmental
Response, Compensation, and Liability
Act (CERCLA). This partial deletion at
Operable Unit Two (OU 2) of the
Peterson/Puritan, Inc. Site is proposed
in accordance with 40 CFR 300.425(e)
and the Notice of Policy Change: Partial
Deletion of Sites Listed on the National
Priorities List 60 FR 55466 (November 1,
1995).
The Site is made up of two formally
designated operable units. This proposal
for partial deletion pertains only to a
portion of OU 2 consisting of 19.8 acres
of the estimated 217 acres contained in
OU 2. Macklands Realty, Inc. owns Plat
14, Lot 2 which consists of
approximately 10.1 acres proposed for
deletion while Berkeley Realty, Co.
owns Plat 15, Lot 1 which consists of
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approximately 9.7 acres proposed for
deletion. These properties are also
known locally as the proposed Berkeley
Commons and River Run developments,
located along the eastern slope of the
Blackstone River Valley between State
Route 122 and the Blackstone River in
Cumberland, Rhode Island. The western
extent of the Macklands and Berkeley
properties also makes up a portion of
the northeastern boundary of OU 2. The
remaining portions of OU 2 will stay on
the NPL, and the Remedial Investigation
and Feasibility Study (RI/FS) will
continue as planned at OU 2. EPA bases
its intent to delete this portion at OU 2
on the determination by EPA and Rhode
Island Department of Environmental
Management (RIDEM) that
investigations have shown that the area
proposed for deletion poses no
significant threat to human health or the
environment and, therefore, currently
warrants that no further response action
is required at the Macklands and
Berkeley properties.
DATES: EPA will accept comments
concerning its intent for partial deletion
on or before March 28, 2005 and a
newspaper of record.
ADDRESSES: Comments may be mailed
to: Mr. David J. Newton, Remedial
Project Manager, Office of Site
Remediation and Restoration, U.S. EPA,
Region 1, 1 Congress Street, Suite 1100,
Boston, MA 02114–2023.
Information Repositories:
Comprehensive information on the
Peterson/Puritan, Inc. Site as well as an
administrative record specific to this
proposed partial deletion is available for
review at EPA’s Region 1 office in
Boston, MA, and at the information
repositories listed below. The EPA
Region 1’s Superfund Records Center is
located at 1 Congress Street, Boston,
MA, 02114–2023. A review of the
records can be conducted by
appointment by calling (617) 918–1440
between 8:30 a.m. until 4:30 p.m.,
Monday–Friday.
Other information repositories where
the deletion docket and comprehensive
site records are available for public
review include: Cumberland Public
Library at 1464 Diamond Hill Road in
Cumberland, Rhode Island, and Lincoln
Public Library, Old River Road, Lincoln,
Rhode Island.
FOR FURTHER INFORMATION CONTACT:
David J. Newton, Remedial Project
Manager at (617) 918–1243, or Sarah
White, Community Involvement
Coordinator, U.S. EPA, Region 1, Office
of Site Remediation and Restoration, 1
Congress Street, Suite 1100, Boston, MA
02114–2023, Telephone: (617) 918–
1026.
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SUPPLEMENTARY INFORMATION:
Table of Contents
I. Introduction
II. NPL Deletion Criteria
III. Deletion Procedures
IV. Basis for Intended Partial Site Deletion
I. Introduction
The United States Environmental
Protection Agency (EPA) Region 1
announces its intent to delete a portion
of Operable Unit Two (OU 2) at the
Peterson/Puritan, Inc. Superfund Site,
(the Site) located in Cumberland, Rhode
Island from the National Priorities List
(NPL), which constitutes appendix B of
the National Oil and Hazardous
Substances Pollution Contingency Plan
(NCP), 40 CFR part 300, and requests
comments on this proposal. This
proposal for partial deletion pertains to
the properties designated on the town of
Cumberland Tax Assessor’s Map Plat
14, Lot 2 and Plat 15, Lot 1, known
locally as the proposed Berkeley
Commons and River Run developments,
and owned by Macklands Realty, Inc.
and Berkeley Realty, Co. respectively
(herein Macklands and Berkeley
properties). This partial deletion
involves 19.8 acres designated within
the OU 2 boundary (see Figure 1; a map
showing the areas proposed for deletion;
which is located in the Administrative
Record (AR) under section 5.4).
A. Peterson/Puritan Site Description
The Site consists of two formally
designated operable units totaling over
two linear miles of mixed industrial/
commercial/residential property. The
Site is located along the Blackstone
River and includes a portion of the
Blackstone River Valley National
Heritage Corridor. The Site is located in
the towns of Cumberland and Lincoln,
in the north-central corner of Rhode
Island. Land use within and adjacent to
the Site is mixed having interspersed
industrial, commercial, and residential
uses typical of an enduring suburban
community with a past textile mill
heritage in Providence County. A more
residential to rural setting is found
immediately west of the river in
Lincoln. The Blackstone River forms a
shared town boundary between
Cumberland and Lincoln.
The OU 2 portion of the Site, which
principally contains the J.M. Mills
Landfill, is surrounded by industrial,
residential and semi-rural properties.
Bordering OU 2 to the north is the Hope
Global company, located at 88 Martin
Street in Cumberland. To the south of
OU 2 is the Stop and Shop Market (and
strip mall) on Mendon Road. The Pratt
Dam across the Blackstone River and the
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southern extent of the former transfer
station property (also known as the
Nunes Parcel) partially forms the
southern boundary of OU 2. The eastern
boundary of OU 2 includes a portion of
the former Mackland Sand and Gravel
operations and wetlands known locally
as the New River. Finally, the western
boundary of OU 2 includes the
Blackstone River and the Quinnville
wellfield in Lincoln.
OU 2 contains many different parcels
totaling an estimated 217 acres. EPA
believes that the most contaminated
parcel is the privately owned 38 acre
J.M. Mills Landfill which accepted
mixed municipal and industrial waste
from 1954 through 1986. Adjacent to the
J.M. Mills Landfill is a privately owned
28 acre unnamed island located in the
Blackstone River. EPA recently
discovered solid wastes disposed of on
this island and believes that the island’s
soils were used to provide daily cover
materials for the landfill and, perhaps,
was even used as an additional disposal
location during the time the landfill was
operating. Down river from the
unnamed island is the Pratt Dam, which
provides an access point to the island.
The Site also includes the 26 acre
Lincoln Quinnville wellfield and the
Cumberland Lenox Street municipal
well. These wells were used by the
towns as a municipal water supply until
1979 when they were closed by the
Rhode Island Department of Health due
to the presence of volatile organic
contaminants found in the water. A
section of the Providence and Worcester
Railroad line runs through OU 2 and
forms the eastern extent of the landfill
slope while the river forms the landfill’s
western boundary. A former privately
owned transfer station is located on the
southern portion of the Site. Other areas
of OU 2 include portions of the
Blackstone River and an adjacent canal,
the Blackstone River Bikeway, and
wetlands.
When the northeasterly boundary of
OU 2 for the RI/FS was created, it
clipped a portion (19.8 acres) of
residential and commercially zoned
properties in Plats 14 and 15 developed
by the Macklands and Berkeley
properties. The remaining two thirds of
these developments are not included
within the OU 2 boundary as drawn.
The 19.8 acres included by the OU 2
boundary are the subject of this
proposed partial deletion (see Figure 1
contained in the AR).
Preliminary samples taken from
suspected source areas within OU 2
(such as the J.M. Mills Landfill and
other associated disposal locations and
excluding the properties proposed for
deletion) indicate the presence of
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volatile organic contaminants
(including, but not limited to,
trichloroethylene, freon 11, 1,2dichloroethene, 1,1,1-trichloroethane,
and benzene), and also chromium,
nickel and lead in the groundwater.
Contaminants found in the soil and
sediment include benzo(a)pyrene,
chrysene, indeno(1,2,3+cd)pyrene,
bis(2-ethylhexyl)phthalate,
polychlorinated biphenyls (PCBs) and
asbestos insulation/transite. In addition,
preliminary sampling of the soils along
the river have been found to be
contaminated with PCBs, polyaromatic
hydrocarbons and heavy metals.
EPA included the Site on the NPL on
September 8, 1983. EPA conducted a
removal action at OU 2 in 1992 to
construct a fence around the former J.M.
Mills Landfill and to remove drums
containing contaminated materials from
the base of the landfill. In November
1997, a second removal action was
conducted at the J.M. Mills Landfill to
address recently disposed asbestoscontaining material found outside of the
fenced-in area. The security fence was
also extended to limit further dumping
and restrict access to additional portions
of the Site.
An investigation into the nature and
extent of contamination at the J.M. Mills
Landfill and surrounding areas is
currently underway. Following the
completion of this study, a final cleanup
remedy will be selected, a remedial
design will be completed and the
remedial action will be initiated.
B. Area Proposed for Deletion
The properties owned by Macklands
Realty, Inc. and Berkeley Realty, Co.
were historically run as a family owned
and operated sand and gravel mining
operation. In 1939, a portion of the
property was subdivided into
residential lots; the remaining portion
became a working sand and gravel
mining operation from 1939 to the early
1970s. The Macklands and Berkeley
properties, with the majority of the
property under a single family’s
ownership for approximately 70 years,
has no known history of industrial or
manufacturing activities involving
hazardous substances. Future
development plans for the Macklands
and Berkeley properties include: (1)
Macklands Realty, Inc., a residential
subdivision covering approximately 32
acres with approximately 10.1 acres
proposed for deletion; and (2) Berkeley
Realty, Co., a mixed use development
including duplexes, townhouses, and
office/retail buildings covering
approximately 30 acres of which 9.7
acres is proposed for deletion from the
site. Each of these proposed
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developments are located off of Mendon
Road in Cumberland, Rhode Island.
The only known use of oil or
potentially hazardous materials on
portions of the development properties
was the application of ‘‘MC–2,’’ an oilbased dust suppression material, along
haul roads at the height of the sand and
gravel mining operations in the 1950s
and 1960s.
In June 2003, a Phase 1
Environmental Site Assessment of the
Macklands and Berkeley properties
revealed no evidence of observed
environmental conditions associated
with hazardous substances or petroleum
products, asbestos-containing material,
radon, lead-based paints, or areas of
special natural resource concern at the
properties. Interviews and review of
past records (including old aerial
photographs) also provide no evidence
of the generation or disposal of
hazardous substances or waste on the
properties.
Based upon currently available
information obtained and submitted for
the Agency’s review, EPA finds that no
further action is necessary to protect
human health and the environment in
relation to the Macklands and Berkeley
properties designated in the town of
Cumberland’s Tax Assessor’s Map as
Plat 14, Lot 2 and Plat 15, Lot 1 in
Cumberland Rhode Island. The
information supporting this finding is
contained in an Administrative Record
established for this purpose (see
Administrative Record Index for the
Macklands and Berkeley properties,
Peterson/Puritan, Inc. Operable Unit 2,
November 2004).
EPA proposes to delete the Macklands
and Berkeley properties from the
Peterson/Puritan, Inc. Site because all
appropriate CERCLA response activities
have been completed for these
properties. Moreover, focused site
investigations have determined that
these properties are not currently
impacted by, nor are they contributing
to, the contamination responsible for
Superfund response actions at OU 2.
Response obligations at the rest of OU
2 are not yet complete, and the Site will
remain on the NPL and is not the
subject of this partial deletion. The
remaining portions of OU 2 include, but
are not limited to, the J.M. Mills
Landfill, the unnamed island, the Nunes
parcel, and a portion of the Blackstone
River and the associated wetlands.
The NPL is a list of sites that EPA has
determined present a significant risk to
human health, welfare, or the
environment. Sites on the NPL may be
the subject of remedial actions financed
by the Hazardous Substance Superfund
(Fund). Pursuant to 40 CFR 300.425(e)
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of the NCP, any site or portion of a site
deleted from the NPL remains eligible
for Fund-financed remedial actions if
conditions at the site warrant such
action.
EPA will accept comments
concerning its intent for partial deletion
for thirty (30) days after publication of
this notice in the Federal Register and
a newspaper of record.
II. NPL Deletion Criteria
The NCP establishes the criteria that
EPA uses to delete sites from the NPL.
In accordance with 40 CFR 300.425(e),
sites may be deleted from the NPL
where no further response is
appropriate to protect human health or
the environment. In making such a
determination pursuant to § 300.425(e),
EPA will consider, in consultation with
the State, whether any of the following
criteria have been met:
Section 300.425(e)(1)(i). Responsible
parties or other persons have
implemented all appropriate response
actions required; or
Section 300.425(e)(1)(ii). All
appropriate Fund-financed responses
under CERCLA have been implemented,
and no further response action by
responsible parties is appropriate; or
Section 300.425(e)(1)(iii). The
remedial investigation has shown that
the release poses no significant threat to
human health or the environment and,
therefore, taking of remedial measures is
not appropriate.
Deletion of a portion of a site from the
NPL does not preclude eligibility for
subsequent Fund-financed actions for
the area deleted if future site conditions
warrant such actions. Section
300.425(e)(3) of the NCP provides that
Fund-financed actions may be taken at
sites that have been deleted from the
NPL. A partial deletion of a site from the
NPL does not affect or impede EPA’s
ability to conduct CERCLA response
activities at areas not deleted and
remaining on the NPL. In addition,
deletion of a portion of a site from the
NPL does not affect the liability of
responsible parties or impede agency
efforts to recover costs associated with
response efforts.
III. Deletion Procedures
Deletion of a portion of a site from the
NPL does not itself create, alter, or
revoke any person’s rights or
obligations. The NPL is designed
primarily for informational purposes
and to assist Agency management.
The following procedures were used
for the proposed deletion of portions of
the Macklands and Berkeley
development properties that are
included within the defined boundary
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of the Peterson/Puritan, Inc. Site as
shown on Figure 1 (contained in the
AR):
(1) EPA has recommended the partial
deletion and has prepared the relevant
documents.
(2) The State of Rhode Island through
the Rhode Island Department of
Environmental Management (RIDEM)
concurs with this partial deletion.
(3) Concurrent with this Notice of
Intent for Partial Deletion, a notice has
been published in a newspaper of
record and has been distributed to
appropriate Federal, State, and local
officials, and other interested parties.
These notices announce a thirty (30) day
public comment period on the deletion
package, which commences on the date
of publication of this notice in the
Federal Register and a newspaper of
record.
(4) EPA has made all relevant
documents available at the information
repositories listed previously.
This Federal Register notice, and a
concurrent notice in a newspaper of
record, announce the initiation of a
thirty (30) day public comment period
and the availability of the Notice of
Intent for Partial Deletion. The public is
asked to comment on EPA’s proposal to
delete the Macklands and Berkeley
properties (as identified on Figure 1
contained in the AR) from the NPL. All
critical documents needed to evaluate
EPA’s decision are included in the
Deletion Docket and are available for
review at the EPA Region 1’s Superfund
Record Center in Boston, Massachusetts,
RIDEM, and at the established
information repositories for the Site.
Upon completion of the thirty (30)
day public comment period, EPA will
evaluate all comments received before
issuing the final decision on the partial
deletion. EPA will prepare a
Responsiveness Summary for comments
received during the public comment
period and will address concerns
presented in the comments. The
Responsiveness Summary will be made
available to the public at the
information repositories listed
previously. Members of the public are
encouraged to contact EPA Region 1 to
obtain a copy of the Responsiveness
Summary.
If, after review of all public
comments, EPA determines that the
partial deletion from the NPL is
appropriate, EPA will publish a Notice
of Partial Deletion in the Federal
Register. Deletion of the Macklands and
Berkeley properties does not actually
occur until the Notice of Partial Deletion
is published in the Federal Register.
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IV. Basis for Intended Partial Site
Deletion
The following provides EPA’s
rationale for deletion of the Macklands
and Berkeley properties from the NPL
and EPA’s finding that the criteria in 40
CFR 300.425(e) are satisfied.
A. Background
RIDEM classifies the Blackstone River
as a Class B1 stream throughout the Site.
This classification has an established
use goal of ‘‘fishable and swimmable,’’
and the State of Rhode Island has an
overall objective to ‘‘restore impaired
sections of the Blackstone River and its
tributaries’’ that do not fully support the
river’s designated uses. (Source: Draft
Blackstone River Action Plan, Rhode
Island Department of Environmental
Management (RIDEM), September 2001).
The B1 classification indicates that
while all Class B uses must be
supported by water quality, primary
contact recreation may be ‘‘impacted
due to pathogens from approved
wastewater discharges’’ (RI WQR, Rule
8(B)(1)).
Sources of surface water impairments
for the Blackstone River, including the
area encompassed by the Site and not
otherwise found to be in association
with disposal practices identified at the
Site, are understood to be point and
non-point sources such as Combined
Sewer Overflows, seepage from failing
septic systems, runoff during storm
events and other lesser sources. Under
the Clean Water Act, permitted
discharges under the National Pollution
Discharge Elimination System and
storm water abatement using Best
Management Practices (BMPs) under the
implementation of Storm Water Phase II
are two examples of regulation geared to
manage, control, and mitigate such
impairments.
The current groundwater
classification at the Site is GAA–NA.
The GAA classification, as designated
by the Rhode Island Department of
Environmental Management Rules and
Regulations for Ground Water Quality,
is defined as ‘‘those ground water
resources which the Director has
designated to be suitable for public
drinking water use without treatment.’’
The ‘‘NA’’ classification is defined as
‘‘those areas that have pollutant
concentrations greater than the ground
water quality standards for the
applicable classification.’’ The
groundwater at and around the Site
remains a viable potential drinking
water resource.
On behalf of the owner of the
Macklands and Berkeley properties, a
limited site investigation was conducted
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by EA Engineering, Science and
Technology (EA). The purpose of this
investigation was to evaluate
groundwater, surface water quality, and
the hydraulic relationship of the
properties to known sources of
groundwater contamination to the
southwest and northwest. In June of
2003, the owner directed the installation
of four (4) monitoring wells strategically
placed to monitor groundwater flow (see
Figure 2; a map illustrating relevant
sampling locations; which is located in
the AR under section 5.4). Of the four
wells, three were completed in shallow
bedrock due the thin, non-water bearing
veneer of overburden that was found to
be present at these locations. The most
southern well was completed in
overburden. Groundwater samples were
collected from each of the wells using
low-flow sampling methods and
procedures in accordance with EPA
protocols. Duplicate samples were also
taken for quality assurance purposes.
All samples were analyzed for volatile
organic compounds (VOCs) and total
metals. The samples were analyzed
using EPA approved methods and
compared to Project Action Limits
(PALs) as approved for use in the
Peterson/Puritan, Inc. OU 2 Quality
Assurance Project Plan. (See: (1) Phase
1 Environmental Site Assessment, Plat
14 Lot 2, Plat 15 Lot 1, Macklands and
Berkeley properties, and (2) Limited
Investigation Report, prepared by EA
Engineering, Science and Technology,
June and August 2003, respectively).
In addition, one surface water sample
and one sediment sample was collected
from both an intermittent stream and
Monastery Brook (see Figure 2
contained in the AR). A duplicate
surface water sample was taken from the
intermittent stream for quality assurance
purposes. Both streams run westerly
through the Macklands and Berkeley
properties where the confluence of each
enters into wetlands located east of the
Blackstone River and within OU2. Each
sample was analyzed for semi-volatile
organic compounds (SVOCs), VOCs and
total metals.
In August 2003, these results were
presented to EPA and RIDEM in a
document entitled, ‘‘Limited
Investigation [for] Berkeley Commons/
River Run Development.’’ The owner of
the properties also requested that his
properties be deleted from the Site so
that ongoing development plans would
not be impacted. In addition, the OU 2
remedial investigation (RI) began in the
fall of 2003.
B. Response Actions
As part of a preliminary screening
evaluation for potential ecological
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threats, surface water data were
compared with the Federal Ambient
Water Quality Criteria (AWQC) with
appropriate adjustment for site-specific
water hardness (calculated using
calcium and magnesium concentrations
in site water). Calculations and criteria
followed EPA AWQC documentation
(EPA, 1999). No chemicals exceeded the
AWQC chronic values, which are
designed to be broadly protective of
aquatic life.
Sediment data were evaluated using
the Consensus-Based Threshold Effect
Concentrations (TECs) from MacDonald
et al., 2000 (MacDonald, D.D., C.G.
Ingersoll, and T.A. Berger. 2000.
Development and evaluation of
Consensus-Based Sediment Quality
Guidelines for Freshwater Ecosystems.
Archives of Environmental
Contamination and Toxicology, 39, 20–
31. Springer-Verlag, New York Inc.).
Chemicals below their respective TECs
generally would not be expected to pose
a risk to sediment-dwelling organisms,
but may warrant further evaluation. Of
the detected chemicals found in
sediment, only lead exceeded the TEC
value in one sample. Sediment taken
from sample location WT–02 had a lead
concentration of 43.9 mg/Kg. The TEC
for lead is 35.8 mg/Kg. It should also be
noted that lead at this location is well
below the Probable Effect Concentration
of 128 mg/Kg, which is the
concentration above which adverse
effects would be considered likely.
Sampling location WT–02 is located
at the end of Monastery Brook.
Monastery Brook is known to receive
storm water from Mendon Road and the
immediate surrounding community.
Based on topography and other
observations made to date within OU 2
of the Site, it is likely that the presence
of lead at WT–02 is associated with
storm run-off from Mendon Road and
the local surroundings. On the basis of
a single detection of lead slightly above
the TEC, and no exceedence of surface
water quality criteria, there does not
appear to be a need for further
evaluation of potential source areas on
the Macklands and Berkeley properties.
A preliminary screening evaluation of
the data for potential human health
concerns was also conducted by EPA.
For groundwater, surface water and
sediment a few metals were detected at
levels above EPA Project Action Limits
(PALs), which were based on either the
risk-based values from EPA Region 9
PRG tables or EPA National Secondary
Drinking Water Standards for the OU 2
RI/FS. Among those metals detected,
iron, aluminum and copper are
considered essential nutrients by EPA
and therefore did not warrant further
VerDate jul<14>2003
18:21 Feb 23, 2005
Jkt 205001
risk evaluation. However, manganese,
arsenic and barium were detected in
some samples at levels exceeding the
PALs. For chemicals with noncancer
health effects, the PALs used were the
EPA Region 9 PRG values (based on
hazard quotient of 1) divided by 10. A
hazard quotient of 1 is considered by
EPA a threshold below which
noncancer adverse health effects do not
likely occur. Therefore, it is EPA Region
1’s policy to use hazard quotient of 0.1
to account for the additive effects of
multiple chemicals. For manganese and
barium, the detected levels were slightly
above the PALs at less than 1 order of
magnitude. Therefore, the assumed
noncancer hazard index from
manganese and barium are acceptable
and below EPA’s noncancer hazard
index of 1. For arsenic in sediment,
detected levels were slightly above the
risk-based PAL, at about 1 order of
magnitude, but would result in an
excess risk falling within the EPA
acceptable risk range. The same
conservative assumptions for exposure
parameters that were used to develop
the risk-based Region 9 values were
used to determine this risk evaluation.
In summary, based on the information
provided in the EA report, the cancer
risks and noncancer hazards from a few
detected metals at the Macklands and
Berkeley properties would be acceptable
for an EPA Superfund site and therefore,
there is no need for any further risk
evaluation or response action.
Therefore, EA’s finding that the levels of
compounds found at the Macklands
Realty, Inc. and Berkeley Realty, Co.
properties do not pose any unacceptable
risk or hazard to the human health
based on EPA standards, is reasonable.
EPA Region 1’s preliminary screening
evaluation of risk also concur with the
findings presented by EA.
C. 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
this intent for partial deletion of this
Site from the NPL are available to the
public in the information repositories.
D. Current Status
Among other documents, the Phase 1
Environmental Site Assessment of
Macklands and Berkeley properties
revealed no evidence of recognized
environmental conditions associated
with hazardous substances or petroleum
products, asbestos-containing material,
radon, lead-based paints, or areas of
special natural resource concern at the
PO 00000
Frm 00028
Fmt 4702
Sfmt 4702
9027
properties. From the Limited
Investigation Report of Berkeley
Commons/River Run and other
corroborating Site information gathered
to date, the Macklands and Berkeley
properties are not contributing to the
VOC contamination of groundwater
associated with the Site nor is it
apparent that the Macklands and
Berkeley properties are being affected
currently by the documented release, or
releases, associated with the Site. Based
on limited testing, groundwater is in
compliance with RIDEM’s GAA
standards at the Macklands and
Berkeley properties. It should be noted
that groundwater is not intended for
direct consumption at the Macklands
and Berkeley properties, as the
development is scheduled to be serviced
by municipal water. EPA may require
access to the Macklands and Berkeley
properties to monitor groundwater or
sample wetlands in association with the
Superfund response actions to the
immediate south and west of the
Macklands and Berkeley properties.
Future consideration for the placement
of institutional controls (in the form of
deed restrictions for the future use, or
hydraulic alteration of groundwater)
adjacent to, or onto the Macklands and
Berkeley properties, are possible once
the RI/FS for OU 2 is complete and a
remedy has been selected.
While EPA does not believe that any
future response actions will be needed
on the Macklands and Berkeley
properties, if future conditions warrant
such action, the proposed deletion areas
of OU 2 remain eligible for future
response actions. Further, this action
does not preclude the State of Rhode
Island from taking any response actions
under State authority, nor others taking
actions governed by other Federal
statutes, should future conditions
warrant such actions. This intent for
partial deletion does not alter the status
of the remainder of the Peterson/
Puritan, Inc. Superfund Site, which is
not proposed for deletion and remains
on the NPL.
EPA, with concurrence from the State
of Rhode Island, has determined that the
release impacting the Site poses no
significant threat to human health or the
environment at the Macklands and
Berkeley properties and therefore
warrants no current response action at
the properties. Therefore, EPA makes
this proposal to delete the properties
owned by Macklands Realty, Inc. and
Berkeley Realty, Co., designated on the
town of Cumberland tax assessor’s map
as Plat 14, Lot 2 and Plat 15, Lot 1 from
the NPL.
E:\FR\FM\24FEP1.SGM
24FEP1
9028
Federal Register / Vol. 70, No. 36 / Thursday, February 24, 2005 / Proposed Rules
Dated: February 1, 2005.
Robert W. Varney,
Regional Administrator, Region 1.
[FR Doc. 05–3452 Filed 2–23–05; 8:45 am]
BILLING CODE 6560–50–P
DEPARTMENT OF COMMERCE
National Oceanic and Atmospheric
Administration
50 CFR Part 622
[I.D. 021705A]
RIN 0648–AS19
Fisheries of the Caribbean, Gulf of
Mexico, and South Atlantic; Reef Fish
Fishery of the Gulf of Mexico;
Vermilion Snapper Rebuilding Plan
National Marine Fisheries
Service (NMFS), National Oceanic and
Atmospheric Administration (NOAA),
Commerce.
ACTION: Notice of availability of
Amendment 23 to the Fishery
Management Plan (FMP) for Reef Fish
Resources of the Gulf of Mexico
(Amendment 23); request for comments.
AGENCY:
NMFS announces the
availability of Amendment 23 prepared
by the Gulf of Mexico Fishery
Management Council (Council) that
would establish a 10–year rebuilding
plan for vermilion snapper in the
exclusive economic zone (EEZ) of the
Gulf of Mexico. The rebuilding plan
seeks to achieve a 25.5–percent
reduction in harvest based on the 2003
predicted landings. Measures to
accomplish this reduction equitably for
the commercial and recreational sectors
of this fishery include increases in
minimum size, a decreased recreational
bag limit, and a closed commercial
season. Amendment 23 would also
establish biological reference points and
stock status determination criteria for
vermilion snapper (i.e., maximum
sustainable yield (MSY), optimum yield
(OY), maximum fishing mortality
threshold (MFMT), and minimum stock
size threshold (MSST), consistent with
the requirements of the MagnusonStevens Fishery Conservation and
Management Act (Magnuson-Stevens
Act). The intended effect of these
measures is to end overfishing and
rebuild the vermilion snapper resource
consistent with the requirements of the
Magnuson-Stevens Act.
DATES: Written comments must be
received no later than 5 p.m., eastern
time, April 25, 2005.
SUMMARY:
VerDate jul<14>2003
18:21 Feb 23, 2005
Jkt 205001
You may submit comments
on Amendment 23 by any of the
following methods:
• E-mail: 0648–AS19NOA@noaa.gov.
Include in the subject line the following
document identifier: 0648–AS19.
• Federal e-Rulemaking Portal: http:/
/www.regulations.gov. Follow the
instructions for submitting comments.
• Mail: Peter Hood, Southeast
Regional Office, NMFS, 9721 Executive
Center Drive N., St. Petersburg, FL
33702.
• Fax: 727–570–5583, Attention:
Peter Hood.
Copies of Amendment 23, which
includes a Regulatory Impact Review,
Initial Regulatory Flexibility Analyses,
and a Supplemental Environmental
Impact Statement, may be obtained from
the Gulf of Mexico Fishery Management
Council, The Commons at Rivergate,
3018 U.S. Highway 301 North, Suite
1000, Tampa, FL 33619–2266;
telephone: 813–228–2815; fax: 813–
225–7015; e-mail:
gulfcouncil@gulfcouncil.org. Copies of
Amendment 23 can also be downloaded
from the Council’s website at
www.gulfcouncil.org.
ADDRESSES:
FOR FURTHER INFORMATION CONTACT:
Peter Hood, telephone: 727–570–5305;
fax: 727–570–5583; e-mail:
peter.hood@noaa.gov.
The reef
fish fishery in the EEZ of the Gulf of
Mexico is managed under the FMP. The
FMP was prepared by the Council under
the authority of the Magnuson-Stevens
Act by regulations at 50 CFR part 622.
SUPPLEMENTARY INFORMATION:
Background
In October 2003, NMFS declared the
Gulf of Mexico stock of vermilion
snapper to be overfished and
undergoing overfishing. This
determination was based in part on the
results of a 2001 NMFS vermilion stock
assessment and review by the Council’s
Reef Fish Stock Assessment Panel that
found the stock to be undergoing
overfishing. Subsequently, NMFS
reexamined the assessment, as well as
more recent data that ultimately
supported the findings of the
assessment, and declared the Gulf of
Mexico vermilion snapper stock
overfished. Therefore, measures to end
overfishing and a rebuilding plan to
restore the stock to the biomass needed
to allow harvest at maximum
sustainable yield (BMSY) in 10 years or
less are necessary.
Amendment 23 contains measures for
vermilion snapper designed to end
overfishing and initiate implementation
of the rebuilding plan that allocates the
necessary restrictions fairly and
PO 00000
Frm 00029
Fmt 4702
Sfmt 4702
equitably between the recreational and
commercial sectors of the fishery,
consistent with the requirements of the
Magnuson-Stevens Act.
Rebuilding Plan
Amendment 23 would establish a 10–
year vermilion snapper rebuilding plan,
structured in one 4–year interval
followed by two 3 year intervals, that
would end overfishing and rebuild the
stock to BMSY. In Amendment 23, the
rebuilding plan begins in 2004 and
continues through 2013. However, due
to the time required to complete
supporting documentation,
implementation of this amendment will
not occur until 2005. Therefore, the
rebuilding plan has been moved forward
one year and will begin in 2005. The
intervals are intended to provide shortterm stability for the management and
operation of the fishery, correlate more
closely with the timing of future stock
assessments, and provide a more
reasonable time period for assessing the
impacts of prior management actions.
The appropriate parameters for each
time interval, consistent with the overall
objectives of the rebuilding plan, would
be determined based upon the most
recent stock assessment.
Initial (2005–2008) Implementation of
the Rebuilding Plan
Based on the results of the 2001
vermilion snapper stock assessment and
updated indices of abundance, the
allowable harvest for the first 4–year
interval starting in 2005 is 1.475 million
lb (0.664 million kg). This equates to a
25.5–percent reduction in harvest based
on the 2003 predicted landings.
Measures to accomplish this reduction
are:
(1) a minimum size limit for
recreationally caught vermilion snapper
of 11 inches (27.9 cm) total length (TL);
(2) a bag limit of 10 fish within the
20–reef fish aggregate bag limit. The
increase in the size limit, from 10 inches
(25.4 cm) TL to 11 inches (27.9 cm) TL,
and the further restriction of the bag
limit would achieve approximately a
21.5–percent reduction relative to the
predicted 2003 harvest;
(3) a minimum size limit for
commercially caught vermilion snapper
of 11 inches (27.9 cm) TL; and
(4) a closed commercial season from
April 22 through May 31 each year. This
would achieve a 26.3–percent harvest
reduction from the estimated 2003
landings.
The reduction in harvest achieved by
these measures is slightly more than the
target 25.5 percent needed by the
rebuilding plan. Increasing harvest by
the commercial sector is believed to
E:\FR\FM\24FEP1.SGM
24FEP1
Agencies
[Federal Register Volume 70, Number 36 (Thursday, February 24, 2005)]
[Proposed Rules]
[Pages 9023-9028]
From the Federal Register Online via the Government Printing Office [www.gpo.gov]
[FR Doc No: 05-3452]
-----------------------------------------------------------------------
ENVIRONMENTAL PROTECTION AGENCY
40 CFR Part 300
[FRL-7874-8]
National Oil and Hazardous Substances Pollution Contingency Plan;
National Priorities List
AGENCY: Environmental Protection Agency.
ACTION: Notice of intent for partial deletion at the Peterson/Puritan,
Inc. site from the National Priorities List.
-----------------------------------------------------------------------
SUMMARY: The Environmental Protection Agency (EPA) Region 1 announces
its intent to delete a portion of the Peterson/Puritan, Inc. Superfund
Site (the Site), owned by Macklands Realty, Inc. and Berkeley Realty,
Co. (herein Macklands and Berkeley properties), from the National
Priorities List (NPL). EPA requests public comment on this action. The
NPL constitutes appendix B to the National Oil and Hazardous Substances
Pollution Contingency Plan (NCP), 40 CFR part 300, which EPA
promulgated pursuant to section 105 of the Comprehensive Environmental
Response, Compensation, and Liability Act (CERCLA). This partial
deletion at Operable Unit Two (OU 2) of the Peterson/Puritan, Inc. Site
is proposed in accordance with 40 CFR 300.425(e) and the Notice of
Policy Change: Partial Deletion of Sites Listed on the National
Priorities List 60 FR 55466 (November 1, 1995).
The Site is made up of two formally designated operable units. This
proposal for partial deletion pertains only to a portion of OU 2
consisting of 19.8 acres of the estimated 217 acres contained in OU 2.
Macklands Realty, Inc. owns Plat 14, Lot 2 which consists of
approximately 10.1 acres proposed for deletion while Berkeley Realty,
Co. owns Plat 15, Lot 1 which consists of
[[Page 9024]]
approximately 9.7 acres proposed for deletion. These properties are
also known locally as the proposed Berkeley Commons and River Run
developments, located along the eastern slope of the Blackstone River
Valley between State Route 122 and the Blackstone River in Cumberland,
Rhode Island. The western extent of the Macklands and Berkeley
properties also makes up a portion of the northeastern boundary of OU
2. The remaining portions of OU 2 will stay on the NPL, and the
Remedial Investigation and Feasibility Study (RI/FS) will continue as
planned at OU 2. EPA bases its intent to delete this portion at OU 2 on
the determination by EPA and Rhode Island Department of Environmental
Management (RIDEM) that investigations have shown that the area
proposed for deletion poses no significant threat to human health or
the environment and, therefore, currently warrants that no further
response action is required at the Macklands and Berkeley properties.
DATES: EPA will accept comments concerning its intent for partial
deletion on or before March 28, 2005 and a newspaper of record.
ADDRESSES: Comments may be mailed to: Mr. David J. Newton, Remedial
Project Manager, Office of Site Remediation and Restoration, U.S. EPA,
Region 1, 1 Congress Street, Suite 1100, Boston, MA 02114-2023.
Information Repositories:
Comprehensive information on the Peterson/Puritan, Inc. Site as
well as an administrative record specific to this proposed partial
deletion is available for review at EPA's Region 1 office in Boston,
MA, and at the information repositories listed below. The EPA Region
1's Superfund Records Center is located at 1 Congress Street, Boston,
MA, 02114-2023. A review of the records can be conducted by appointment
by calling (617) 918-1440 between 8:30 a.m. until 4:30 p.m., Monday-
Friday.
Other information repositories where the deletion docket and
comprehensive site records are available for public review include:
Cumberland Public Library at 1464 Diamond Hill Road in Cumberland,
Rhode Island, and Lincoln Public Library, Old River Road, Lincoln,
Rhode Island.
FOR FURTHER INFORMATION CONTACT: David J. Newton, Remedial Project
Manager at (617) 918-1243, or Sarah White, Community Involvement
Coordinator, U.S. EPA, Region 1, Office of Site Remediation and
Restoration, 1 Congress Street, Suite 1100, Boston, MA 02114-2023,
Telephone: (617) 918-1026.
SUPPLEMENTARY INFORMATION:
Table of Contents
I. Introduction
II. NPL Deletion Criteria
III. Deletion Procedures
IV. Basis for Intended Partial Site Deletion
I. Introduction
The United States Environmental Protection Agency (EPA) Region 1
announces its intent to delete a portion of Operable Unit Two (OU 2) at
the Peterson/Puritan, Inc. Superfund Site, (the Site) located in
Cumberland, Rhode Island from the National Priorities List (NPL), which
constitutes appendix B of the National Oil and Hazardous Substances
Pollution Contingency Plan (NCP), 40 CFR part 300, and requests
comments on this proposal. This proposal for partial deletion pertains
to the properties designated on the town of Cumberland Tax Assessor's
Map Plat 14, Lot 2 and Plat 15, Lot 1, known locally as the proposed
Berkeley Commons and River Run developments, and owned by Macklands
Realty, Inc. and Berkeley Realty, Co. respectively (herein Macklands
and Berkeley properties). This partial deletion involves 19.8 acres
designated within the OU 2 boundary (see Figure 1; a map showing the
areas proposed for deletion; which is located in the Administrative
Record (AR) under section 5.4).
A. Peterson/Puritan Site Description
The Site consists of two formally designated operable units
totaling over two linear miles of mixed industrial/commercial/
residential property. The Site is located along the Blackstone River
and includes a portion of the Blackstone River Valley National Heritage
Corridor. The Site is located in the towns of Cumberland and Lincoln,
in the north-central corner of Rhode Island. Land use within and
adjacent to the Site is mixed having interspersed industrial,
commercial, and residential uses typical of an enduring suburban
community with a past textile mill heritage in Providence County. A
more residential to rural setting is found immediately west of the
river in Lincoln. The Blackstone River forms a shared town boundary
between Cumberland and Lincoln.
The OU 2 portion of the Site, which principally contains the J.M.
Mills Landfill, is surrounded by industrial, residential and semi-rural
properties. Bordering OU 2 to the north is the Hope Global company,
located at 88 Martin Street in Cumberland. To the south of OU 2 is the
Stop and Shop Market (and strip mall) on Mendon Road. The Pratt Dam
across the Blackstone River and the southern extent of the former
transfer station property (also known as the Nunes Parcel) partially
forms the southern boundary of OU 2. The eastern boundary of OU 2
includes a portion of the former Mackland Sand and Gravel operations
and wetlands known locally as the New River. Finally, the western
boundary of OU 2 includes the Blackstone River and the Quinnville
wellfield in Lincoln.
OU 2 contains many different parcels totaling an estimated 217
acres. EPA believes that the most contaminated parcel is the privately
owned 38 acre J.M. Mills Landfill which accepted mixed municipal and
industrial waste from 1954 through 1986. Adjacent to the J.M. Mills
Landfill is a privately owned 28 acre unnamed island located in the
Blackstone River. EPA recently discovered solid wastes disposed of on
this island and believes that the island's soils were used to provide
daily cover materials for the landfill and, perhaps, was even used as
an additional disposal location during the time the landfill was
operating. Down river from the unnamed island is the Pratt Dam, which
provides an access point to the island. The Site also includes the 26
acre Lincoln Quinnville wellfield and the Cumberland Lenox Street
municipal well. These wells were used by the towns as a municipal water
supply until 1979 when they were closed by the Rhode Island Department
of Health due to the presence of volatile organic contaminants found in
the water. A section of the Providence and Worcester Railroad line runs
through OU 2 and forms the eastern extent of the landfill slope while
the river forms the landfill's western boundary. A former privately
owned transfer station is located on the southern portion of the Site.
Other areas of OU 2 include portions of the Blackstone River and an
adjacent canal, the Blackstone River Bikeway, and wetlands.
When the northeasterly boundary of OU 2 for the RI/FS was created,
it clipped a portion (19.8 acres) of residential and commercially zoned
properties in Plats 14 and 15 developed by the Macklands and Berkeley
properties. The remaining two thirds of these developments are not
included within the OU 2 boundary as drawn. The 19.8 acres included by
the OU 2 boundary are the subject of this proposed partial deletion
(see Figure 1 contained in the AR).
Preliminary samples taken from suspected source areas within OU 2
(such as the J.M. Mills Landfill and other associated disposal
locations and excluding the properties proposed for deletion) indicate
the presence of
[[Page 9025]]
volatile organic contaminants (including, but not limited to,
trichloroethylene, freon 11, 1,2-dichloroethene, 1,1,1-trichloroethane,
and benzene), and also chromium, nickel and lead in the groundwater.
Contaminants found in the soil and sediment include benzo(a)pyrene,
chrysene, indeno(1,2,3+cd)pyrene, bis(2-ethylhexyl)phthalate,
polychlorinated biphenyls (PCBs) and asbestos insulation/transite. In
addition, preliminary sampling of the soils along the river have been
found to be contaminated with PCBs, polyaromatic hydrocarbons and heavy
metals.
EPA included the Site on the NPL on September 8, 1983. EPA
conducted a removal action at OU 2 in 1992 to construct a fence around
the former J.M. Mills Landfill and to remove drums containing
contaminated materials from the base of the landfill. In November 1997,
a second removal action was conducted at the J.M. Mills Landfill to
address recently disposed asbestos-containing material found outside of
the fenced-in area. The security fence was also extended to limit
further dumping and restrict access to additional portions of the Site.
An investigation into the nature and extent of contamination at the
J.M. Mills Landfill and surrounding areas is currently underway.
Following the completion of this study, a final cleanup remedy will be
selected, a remedial design will be completed and the remedial action
will be initiated.
B. Area Proposed for Deletion
The properties owned by Macklands Realty, Inc. and Berkeley Realty,
Co. were historically run as a family owned and operated sand and
gravel mining operation. In 1939, a portion of the property was
subdivided into residential lots; the remaining portion became a
working sand and gravel mining operation from 1939 to the early 1970s.
The Macklands and Berkeley properties, with the majority of the
property under a single family's ownership for approximately 70 years,
has no known history of industrial or manufacturing activities
involving hazardous substances. Future development plans for the
Macklands and Berkeley properties include: (1) Macklands Realty, Inc.,
a residential subdivision covering approximately 32 acres with
approximately 10.1 acres proposed for deletion; and (2) Berkeley
Realty, Co., a mixed use development including duplexes, townhouses,
and office/retail buildings covering approximately 30 acres of which
9.7 acres is proposed for deletion from the site. Each of these
proposed developments are located off of Mendon Road in Cumberland,
Rhode Island.
The only known use of oil or potentially hazardous materials on
portions of the development properties was the application of ``MC-2,''
an oil-based dust suppression material, along haul roads at the height
of the sand and gravel mining operations in the 1950s and 1960s.
In June 2003, a Phase 1 Environmental Site Assessment of the
Macklands and Berkeley properties revealed no evidence of observed
environmental conditions associated with hazardous substances or
petroleum products, asbestos-containing material, radon, lead-based
paints, or areas of special natural resource concern at the properties.
Interviews and review of past records (including old aerial
photographs) also provide no evidence of the generation or disposal of
hazardous substances or waste on the properties.
Based upon currently available information obtained and submitted
for the Agency's review, EPA finds that no further action is necessary
to protect human health and the environment in relation to the
Macklands and Berkeley properties designated in the town of
Cumberland's Tax Assessor's Map as Plat 14, Lot 2 and Plat 15, Lot 1 in
Cumberland Rhode Island. The information supporting this finding is
contained in an Administrative Record established for this purpose (see
Administrative Record Index for the Macklands and Berkeley properties,
Peterson/Puritan, Inc. Operable Unit 2, November 2004).
EPA proposes to delete the Macklands and Berkeley properties from
the Peterson/Puritan, Inc. Site because all appropriate CERCLA response
activities have been completed for these properties. Moreover, focused
site investigations have determined that these properties are not
currently impacted by, nor are they contributing to, the contamination
responsible for Superfund response actions at OU 2. Response
obligations at the rest of OU 2 are not yet complete, and the Site will
remain on the NPL and is not the subject of this partial deletion. The
remaining portions of OU 2 include, but are not limited to, the J.M.
Mills Landfill, the unnamed island, the Nunes parcel, and a portion of
the Blackstone River and the associated wetlands.
The NPL is a list of sites that EPA has determined present a
significant risk to human health, welfare, or the environment. Sites on
the NPL may be the subject of remedial actions financed by the
Hazardous Substance Superfund (Fund). Pursuant to 40 CFR 300.425(e) of
the NCP, any site or portion of a site deleted from the NPL remains
eligible for Fund-financed remedial actions if conditions at the site
warrant such action.
EPA will accept comments concerning its intent for partial deletion
for thirty (30) days after publication of this notice in the Federal
Register and a newspaper of record.
II. NPL Deletion Criteria
The NCP establishes the criteria that EPA uses to delete sites from
the NPL. In accordance with 40 CFR 300.425(e), sites may be deleted
from the NPL where no further response is appropriate to protect human
health or the environment. In making such a determination pursuant to
Sec. 300.425(e), EPA will consider, in consultation with the State,
whether any of the following criteria have been met:
Section 300.425(e)(1)(i). Responsible parties or other persons have
implemented all appropriate response actions required; or
Section 300.425(e)(1)(ii). All appropriate Fund-financed responses
under CERCLA have been implemented, and no further response action by
responsible parties is appropriate; or
Section 300.425(e)(1)(iii). The remedial investigation has shown
that the release poses no significant threat to human health or the
environment and, therefore, taking of remedial measures is not
appropriate.
Deletion of a portion of a site from the NPL does not preclude
eligibility for subsequent Fund-financed actions for the area deleted
if future site conditions warrant such actions. Section 300.425(e)(3)
of the NCP provides that Fund-financed actions may be taken at sites
that have been deleted from the NPL. A partial deletion of a site from
the NPL does not affect or impede EPA's ability to conduct CERCLA
response activities at areas not deleted and remaining on the NPL. In
addition, deletion of a portion of a site from the NPL does not affect
the liability of responsible parties or impede agency efforts to
recover costs associated with response efforts.
III. Deletion Procedures
Deletion of a portion of a site from the NPL does not itself
create, alter, or revoke any person's rights or obligations. The NPL is
designed primarily for informational purposes and to assist Agency
management.
The following procedures were used for the proposed deletion of
portions of the Macklands and Berkeley development properties that are
included within the defined boundary
[[Page 9026]]
of the Peterson/Puritan, Inc. Site as shown on Figure 1 (contained in
the AR):
(1) EPA has recommended the partial deletion and has prepared the
relevant documents.
(2) The State of Rhode Island through the Rhode Island Department
of Environmental Management (RIDEM) concurs with this partial deletion.
(3) Concurrent with this Notice of Intent for Partial Deletion, a
notice has been published in a newspaper of record and has been
distributed to appropriate Federal, State, and local officials, and
other interested parties. These notices announce a thirty (30) day
public comment period on the deletion package, which commences on the
date of publication of this notice in the Federal Register and a
newspaper of record.
(4) EPA has made all relevant documents available at the
information repositories listed previously.
This Federal Register notice, and a concurrent notice in a
newspaper of record, announce the initiation of a thirty (30) day
public comment period and the availability of the Notice of Intent for
Partial Deletion. The public is asked to comment on EPA's proposal to
delete the Macklands and Berkeley properties (as identified on Figure 1
contained in the AR) from the NPL. All critical documents needed to
evaluate EPA's decision are included in the Deletion Docket and are
available for review at the EPA Region 1's Superfund Record Center in
Boston, Massachusetts, RIDEM, and at the established information
repositories for the Site.
Upon completion of the thirty (30) day public comment period, EPA
will evaluate all comments received before issuing the final decision
on the partial deletion. EPA will prepare a Responsiveness Summary for
comments received during the public comment period and will address
concerns presented in the comments. The Responsiveness Summary will be
made available to the public at the information repositories listed
previously. Members of the public are encouraged to contact EPA Region
1 to obtain a copy of the Responsiveness Summary.
If, after review of all public comments, EPA determines that the
partial deletion from the NPL is appropriate, EPA will publish a Notice
of Partial Deletion in the Federal Register. Deletion of the Macklands
and Berkeley properties does not actually occur until the Notice of
Partial Deletion is published in the Federal Register.
IV. Basis for Intended Partial Site Deletion
The following provides EPA's rationale for deletion of the
Macklands and Berkeley properties from the NPL and EPA's finding that
the criteria in 40 CFR 300.425(e) are satisfied.
A. Background
RIDEM classifies the Blackstone River as a Class B1 stream
throughout the Site. This classification has an established use goal of
``fishable and swimmable,'' and the State of Rhode Island has an
overall objective to ``restore impaired sections of the Blackstone
River and its tributaries'' that do not fully support the river's
designated uses. (Source: Draft Blackstone River Action Plan, Rhode
Island Department of Environmental Management (RIDEM), September 2001).
The B1 classification indicates that while all Class B uses must be
supported by water quality, primary contact recreation may be
``impacted due to pathogens from approved wastewater discharges'' (RI
WQR, Rule 8(B)(1)).
Sources of surface water impairments for the Blackstone River,
including the area encompassed by the Site and not otherwise found to
be in association with disposal practices identified at the Site, are
understood to be point and non-point sources such as Combined Sewer
Overflows, seepage from failing septic systems, runoff during storm
events and other lesser sources. Under the Clean Water Act, permitted
discharges under the National Pollution Discharge Elimination System
and storm water abatement using Best Management Practices (BMPs) under
the implementation of Storm Water Phase II are two examples of
regulation geared to manage, control, and mitigate such impairments.
The current groundwater classification at the Site is GAA-NA. The
GAA classification, as designated by the Rhode Island Department of
Environmental Management Rules and Regulations for Ground Water
Quality, is defined as ``those ground water resources which the
Director has designated to be suitable for public drinking water use
without treatment.'' The ``NA'' classification is defined as ``those
areas that have pollutant concentrations greater than the ground water
quality standards for the applicable classification.'' The groundwater
at and around the Site remains a viable potential drinking water
resource.
On behalf of the owner of the Macklands and Berkeley properties, a
limited site investigation was conducted by EA Engineering, Science and
Technology (EA). The purpose of this investigation was to evaluate
groundwater, surface water quality, and the hydraulic relationship of
the properties to known sources of groundwater contamination to the
southwest and northwest. In June of 2003, the owner directed the
installation of four (4) monitoring wells strategically placed to
monitor groundwater flow (see Figure 2; a map illustrating relevant
sampling locations; which is located in the AR under section 5.4). Of
the four wells, three were completed in shallow bedrock due the thin,
non-water bearing veneer of overburden that was found to be present at
these locations. The most southern well was completed in overburden.
Groundwater samples were collected from each of the wells using low-
flow sampling methods and procedures in accordance with EPA protocols.
Duplicate samples were also taken for quality assurance purposes. All
samples were analyzed for volatile organic compounds (VOCs) and total
metals. The samples were analyzed using EPA approved methods and
compared to Project Action Limits (PALs) as approved for use in the
Peterson/Puritan, Inc. OU 2 Quality Assurance Project Plan. (See: (1)
Phase 1 Environmental Site Assessment, Plat 14 Lot 2, Plat 15 Lot 1,
Macklands and Berkeley properties, and (2) Limited Investigation
Report, prepared by EA Engineering, Science and Technology, June and
August 2003, respectively).
In addition, one surface water sample and one sediment sample was
collected from both an intermittent stream and Monastery Brook (see
Figure 2 contained in the AR). A duplicate surface water sample was
taken from the intermittent stream for quality assurance purposes. Both
streams run westerly through the Macklands and Berkeley properties
where the confluence of each enters into wetlands located east of the
Blackstone River and within OU2. Each sample was analyzed for semi-
volatile organic compounds (SVOCs), VOCs and total metals.
In August 2003, these results were presented to EPA and RIDEM in a
document entitled, ``Limited Investigation [for] Berkeley Commons/River
Run Development.'' The owner of the properties also requested that his
properties be deleted from the Site so that ongoing development plans
would not be impacted. In addition, the OU 2 remedial investigation
(RI) began in the fall of 2003.
B. Response Actions
As part of a preliminary screening evaluation for potential
ecological
[[Page 9027]]
threats, surface water data were compared with the Federal Ambient
Water Quality Criteria (AWQC) with appropriate adjustment for site-
specific water hardness (calculated using calcium and magnesium
concentrations in site water). Calculations and criteria followed EPA
AWQC documentation (EPA, 1999). No chemicals exceeded the AWQC chronic
values, which are designed to be broadly protective of aquatic life.
Sediment data were evaluated using the Consensus-Based Threshold
Effect Concentrations (TECs) from MacDonald et al., 2000 (MacDonald,
D.D., C.G. Ingersoll, and T.A. Berger. 2000. Development and evaluation
of Consensus-Based Sediment Quality Guidelines for Freshwater
Ecosystems. Archives of Environmental Contamination and Toxicology, 39,
20-31. Springer-Verlag, New York Inc.). Chemicals below their
respective TECs generally would not be expected to pose a risk to
sediment-dwelling organisms, but may warrant further evaluation. Of the
detected chemicals found in sediment, only lead exceeded the TEC value
in one sample. Sediment taken from sample location WT-02 had a lead
concentration of 43.9 mg/Kg. The TEC for lead is 35.8 mg/Kg. It should
also be noted that lead at this location is well below the Probable
Effect Concentration of 128 mg/Kg, which is the concentration above
which adverse effects would be considered likely.
Sampling location WT-02 is located at the end of Monastery Brook.
Monastery Brook is known to receive storm water from Mendon Road and
the immediate surrounding community. Based on topography and other
observations made to date within OU 2 of the Site, it is likely that
the presence of lead at WT-02 is associated with storm run-off from
Mendon Road and the local surroundings. On the basis of a single
detection of lead slightly above the TEC, and no exceedence of surface
water quality criteria, there does not appear to be a need for further
evaluation of potential source areas on the Macklands and Berkeley
properties.
A preliminary screening evaluation of the data for potential human
health concerns was also conducted by EPA. For groundwater, surface
water and sediment a few metals were detected at levels above EPA
Project Action Limits (PALs), which were based on either the risk-based
values from EPA Region 9 PRG tables or EPA National Secondary Drinking
Water Standards for the OU 2 RI/FS. Among those metals detected, iron,
aluminum and copper are considered essential nutrients by EPA and
therefore did not warrant further risk evaluation. However, manganese,
arsenic and barium were detected in some samples at levels exceeding
the PALs. For chemicals with noncancer health effects, the PALs used
were the EPA Region 9 PRG values (based on hazard quotient of 1)
divided by 10. A hazard quotient of 1 is considered by EPA a threshold
below which noncancer adverse health effects do not likely occur.
Therefore, it is EPA Region 1's policy to use hazard quotient of 0.1 to
account for the additive effects of multiple chemicals. For manganese
and barium, the detected levels were slightly above the PALs at less
than 1 order of magnitude. Therefore, the assumed noncancer hazard
index from manganese and barium are acceptable and below EPA's
noncancer hazard index of 1. For arsenic in sediment, detected levels
were slightly above the risk-based PAL, at about 1 order of magnitude,
but would result in an excess risk falling within the EPA acceptable
risk range. The same conservative assumptions for exposure parameters
that were used to develop the risk-based Region 9 values were used to
determine this risk evaluation.
In summary, based on the information provided in the EA report, the
cancer risks and noncancer hazards from a few detected metals at the
Macklands and Berkeley properties would be acceptable for an EPA
Superfund site and therefore, there is no need for any further risk
evaluation or response action. Therefore, EA's finding that the levels
of compounds found at the Macklands Realty, Inc. and Berkeley Realty,
Co. properties do not pose any unacceptable risk or hazard to the human
health based on EPA standards, is reasonable. EPA Region 1's
preliminary screening evaluation of risk also concur with the findings
presented by EA.
C. 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 this intent for partial deletion of this Site from
the NPL are available to the public in the information repositories.
D. Current Status
Among other documents, the Phase 1 Environmental Site Assessment of
Macklands and Berkeley properties revealed no evidence of recognized
environmental conditions associated with hazardous substances or
petroleum products, asbestos-containing material, radon, lead-based
paints, or areas of special natural resource concern at the properties.
From the Limited Investigation Report of Berkeley Commons/River Run and
other corroborating Site information gathered to date, the Macklands
and Berkeley properties are not contributing to the VOC contamination
of groundwater associated with the Site nor is it apparent that the
Macklands and Berkeley properties are being affected currently by the
documented release, or releases, associated with the Site. Based on
limited testing, groundwater is in compliance with RIDEM's GAA
standards at the Macklands and Berkeley properties. It should be noted
that groundwater is not intended for direct consumption at the
Macklands and Berkeley properties, as the development is scheduled to
be serviced by municipal water. EPA may require access to the Macklands
and Berkeley properties to monitor groundwater or sample wetlands in
association with the Superfund response actions to the immediate south
and west of the Macklands and Berkeley properties. Future consideration
for the placement of institutional controls (in the form of deed
restrictions for the future use, or hydraulic alteration of
groundwater) adjacent to, or onto the Macklands and Berkeley
properties, are possible once the RI/FS for OU 2 is complete and a
remedy has been selected.
While EPA does not believe that any future response actions will be
needed on the Macklands and Berkeley properties, if future conditions
warrant such action, the proposed deletion areas of OU 2 remain
eligible for future response actions. Further, this action does not
preclude the State of Rhode Island from taking any response actions
under State authority, nor others taking actions governed by other
Federal statutes, should future conditions warrant such actions. This
intent for partial deletion does not alter the status of the remainder
of the Peterson/Puritan, Inc. Superfund Site, which is not proposed for
deletion and remains on the NPL.
EPA, with concurrence from the State of Rhode Island, has
determined that the release impacting the Site poses no significant
threat to human health or the environment at the Macklands and Berkeley
properties and therefore warrants no current response action at the
properties. Therefore, EPA makes this proposal to delete the properties
owned by Macklands Realty, Inc. and Berkeley Realty, Co., designated on
the town of Cumberland tax assessor's map as Plat 14, Lot 2 and Plat
15, Lot 1 from the NPL.
[[Page 9028]]
Dated: February 1, 2005.
Robert W. Varney,
Regional Administrator, Region 1.
[FR Doc. 05-3452 Filed 2-23-05; 8:45 am]
BILLING CODE 6560-50-P