Ocean Disposal; Temporary Modification of an Ocean Dredged Material Disposal Site in Massachusetts Bay, 24408-24414 [2018-11322]
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Federal Register / Vol. 83, No. 103 / Tuesday, May 29, 2018 / Rules and Regulations
EPA-APPROVED ILLINOIS REGULATIONS AND STATUTES—Continued
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[FR Doc. 2018–11324 Filed 5–25–18; 8:45 am]
BILLING CODE 6560–50–P
ENVIRONMENTAL PROTECTION
AGENCY
40 CFR Part 228
[EPA–R01–OW–2017–0528; FRL–9978–51—
Region 1]
Ocean Disposal; Temporary
Modification of an Ocean Dredged
Material Disposal Site in
Massachusetts Bay
Environmental Protection
Agency (EPA).
ACTION: Final rule.
jstallworth on DSKBBY8HB2PROD with RULES
AGENCY:
The Environmental Protection
Agency (EPA) is approving a temporary
modification of the boundaries of the
Massachusetts Bay Dredged Material
Disposal Site (MBDS) pursuant to the
Marine Protection, Research, and
Sanctuaries Act (MPRSA), as amended.
The purpose of this temporary site
SUMMARY:
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modification is to allow for the
environmental restoration of a particular
area adjacent to the MBDS (Potential
Restoration Area) by temporarily
expanding the boundaries of the
existing MBDS. The temporary
expansion is a circular area that
contains the Potential Restoration Area,
which includes most of the historic
Industrial Waste Site (IWS). Decades
ago, the IWS was used for the disposal
of barrels containing industrial,
chemical and low-level radioactive
waste, as well as for the disposal of
munitions, ordnance, construction
equipment, and contaminated dredged
material. The modification of the
disposal site boundary will enable the
U.S. Army Corps of Engineers (USACE)
to place suitable dredged material
generated from the Boston Harbor Deep
Draft Navigation Project at the Potential
Restoration Area in order to cover the
barrels and other wastes disposed there
in the past. This is expected to improve
environmental conditions at the site.
The Deep Draft Navigation Project
includes improvement dredging of the
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main ship channel, which will generate
approximately 11 million cubic yards
(cy) of dredged material. The existing
MBDS will continue to be used for
disposal of other dredging projects, as
usual. The expansion area will
permanently close upon completion of
the Boston Harbor Deep Draft
Navigation Project, while the existing
MBDS will remain open for the disposal
of other suitable dredged material. Like
the MBDS, however, the expansion area
will be subject to ongoing monitoring
and management to monitor the
recovery of the area and to ensure
continued protection of the marine
environment.
The effective date of this rule is
June 28, 2018.
ADDRESSES: The EPA has established a
docket for this action under Docket ID
No. EPA–R01–OW–2017–0528. All
documents in the docket are listed on
the https://www.regulations.gov website
or on the EPA Region 1 MBDS web page
at https://www.epa.gov/ocean-dumping/
massachusetts-bay-industrial-waste-siterestoration-project. Although listed in
DATES:
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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,
is not placed on the internet and will be
publicly available only in hard copy
form. Publicly available docket
materials are available electronically
through https://www.regulations.gov.
They are also available in hard copy
during normal business hours at the
EPA Region 1 Library, 5 Post Office
Square Boston, MA 02109.
The supporting document for this site
modification is the Final Environmental
Assessment on the Proposed Expansion
of the Massachusetts Bay Ocean
Dredged Material Disposal Site and
Finding of No Significant Impact, May
2018, which was prepared by EPA.
FOR FURTHER INFORMATION CONTACT:
Alicia Grimaldi, U.S. Environmental
Protection Agency, Region 1, 5 Post
Office Square, Suite 100, Mail Code:
OEP 6–1, Boston, MA 02109;
telephone—(617) 918–1806; fax—(617)
918–0806; email address—
grimaldi.alicia@epa.gov.
SUPPLEMENTARY INFORMATION:
jstallworth on DSKBBY8HB2PROD with RULES
I. Potentially Affected Persons
The expansion of the MBDS is a
temporary modification made in order
to improve environmental conditions at
the Potential Restoration Area by
allowing suitable dredged material from
the USACE Boston Harbor improvement
project to be placed over wastes
dumped in the past at the historic IWS.
The USACE are persons potentially
affected by this action, as they are
responsible for the Boston Harbor Deep
Draft Navigation Project and the
disposal of dredged material into ocean
waters under MPRSA. The existing
MBDS will continue to be used for the
disposal of dredged material from other
projects that is suitable for ocean
disposal pursuant to the MPRSA. This
action will also impact those fishermen
who utilize the historic IWS for fishing,
despite posted warnings, by helping to
reduce the risk of potential injury
resulting from the inadvertent retrieval
of wastes from the IWS in their nets.
There have been documented instances
of fishermen trawling up barrels in the
IWS area and this action will lower the
risk of that occurring in the future.
II. Background
a. History of Disposal Sites in
Massachusetts Bay
The IWS is a disposal site in
Massachusetts Bay approximately 20
nautical miles (nmi) east of Boston that
was used in the past for disposal of a
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variety of wastes that would not be
permitted for disposal today. The IWS is
a circular site with its center at 42°25.7′
N, 70°35.0′ W and a radius of 1 nmi. It
is believed that disposal of derelict
vessels, construction debris, commercial
waste, and dredged material at the area
may have begun in the early 1900s.
There are records dating back to the
1940s documenting the disposal of
radioactive, chemical and hospital
waste, ordnance, munitions, etc. Use of
the IWS was discontinued in 1977 and
the site was officially de-designated in
1990 (55 FR 3688, February 2, 1990).
From 1977 through 1993, there was an
Interim Massachusetts Bay Disposal Site
for dredged material disposal with a
center 1 nmi east of the IWS at 42°25.7′
N, 70°34.0′ W and a radius of 1 nmi. In
1993, the existing MBDS was designated
by EPA with a center at 42°25.1′ N,
70°35.0′ W and a radius of 1 nmi, an
area of 3.14 nmi2, and depth ranges
from 82 to 92 meters (m). The MBDS
overlaps the southern portion of the
IWS, but avoids the known densest
concentration of barrels, also known as
the barrel field. The MBDS is used
solely for the disposal of dredged
material, primarily from Boston Harbor,
but also from smaller harbors and
navigation channels north and south of
Boston.
The USACE will begin the Boston
Harbor improvement dredging project in
2018. The project is expected to
generate approximately 11 million cy of
suitable dredged material consisting
primarily of Boston blue clay and glacial
till. EPA and USACE are proposing to
use this dredged material beneficially by
covering the area in and around the
historic IWS barrel field to a depth of
one to two meters. This will be
accomplished utilizing a method of
disposal developed and tested by the
USACE, which is designed to prevent
direct impact of sediment onto waste
containers. This method of disposal is
intended to reduce the risk of breaking
barrels and resuspending potentially
contaminated seafloor sediment.
Before any entity can dispose of
dredged material at the MBDS, EPA and
the USACE must evaluate the project
according to the ocean dumping
regulatory criteria (40 CFR 227) and
determine whether to authorize the
disposal. Under Section 103 of the
MPRSA, disposal projects are
authorized by the USACE and EPA
independently evaluates proposed
disposal projects and has the right to
restrict and/or reject the disposal of
dredged material if it determines that
the environmental protection
requirements under the MPRSA have
not been met. This modification to the
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MBDS site boundaries does not
constitute an approval by EPA or
USACE for open-water disposal of
dredged material from any specific
project. Thus, although the plan is that
suitable material from the USACE’s
Boston Harbor improvement project
would be placed at the temporary
expansion area, any material proposed
for disposal will have to go through
project-specific review and approval.
b. Location and Configuration of the
Modified Ocean Dredged Material
Disposal Site
This Final Rule temporarily modifies
the MBDS by expanding it to include
the Potential Restoration Area, which
encompasses the IWS barrel field. The
expansion will be temporary, opening
upon the effective date of the Final Rule
and closing upon completion of the
Boston Harbor Deep Draft Navigation
Project. The temporarily expanded site
will consist of two partially overlapping
circles:
• Center 1—42°25.1′ N, 70°35.0′ W, 1
nautical mile radius (existing MBDS)
• Center 2—42°26.417′ N, 70°35.373′ W,
0.75 nautical mile radius (temporary
expansion)
The area of the temporarily modified
MBDS is 4.60 nmi2 and the western
edge is approximately 19 nmi east of
Boston. Water depths at the modified
site range from 70 to 91 m. Like the
existing MBDS, the modified MBDS will
not overlap, and is not expected to
impact, the Stellwagen Bank National
Marine Sanctuary (SBNMS).
c. Response to Comments
On September 22, 2017, EPA
published a Proposed Rule proposing to
temporarily modify the MBDS with a
supporting Draft Environmental
Assessment and opened a public
comment period under Docket ID EPA–
R01–OW–2017–0528. The comment
period ended on October 23, 2017. EPA
received eleven comments on the
Proposed Rule and Draft Environmental
Assessment. The comments received are
listed below:
• Support of the temporary expansion
of the MBDS (6 commenters);
• Boundaries of the temporary
expansion of the MBDS overlap with the
Neptune Deepwater Port (1 commenter);
• Importance of proceeding with
disposal carefully to prevent breakage of
barrels (4 commenters);
• Barrels may no longer exist on the
seafloor (1 commenter);
• Sewage sludge should not be
disposed in the ocean or used for
capping (1 commenter);
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• There is no evidence of
contamination at the IWS (1
commenter);
• Disposing material further out into
the ocean is a cheaper solution (1
commenter);
• Other disposal sites were not
considered (1 commenter);
• The temporary expansion of the
MBDS will eliminate fishable bottom (2
commenters);
• How to stay informed on the status
of the project (2 commenters);
• Disposal could impact the health of
the ecosystem (1 commenter);
• Typographic errors in Draft EA (1
commenter);
• Modification of the MBDS will
change the size of the SBNMS (1
commenter);
• The Potential Restoration Area will
increase with additional dredged
material (1 commenter);
• The removal of barrels from the
IWS was not considered as an
alternative (2 commenters);
• Ensure that the disposal of dredged
material and the temporary expansion is
monitored (2 commenters);
• The Massachusetts Department of
Marine Fisheries (MDMF) would like to
consult on disposal time-of-year
restrictions to minimize impact to cod
spawning (1 commenter); and
• MDMF would like the USACE and
EPA to continue participating in a
working group exploring other
opportunities for beneficial use of
dredged material (1 commenter).
The responses to these comments can
be found in the Final Environmental
Assessment on the Proposed Expansion
of the Massachusetts Bay Ocean
Dredged Material Disposal Site and
Finding of No Significant Impact, which
is available on Regulations.gov and the
EPA Region 1 MBDS web page: https://
www.epa.gov/ocean-dumping/
massachusetts-bay-industrial-waste-siterestoration-project.
jstallworth on DSKBBY8HB2PROD with RULES
d. Management and Monitoring of the
Site
There will be two distinct areas of the
modified MBDS: The existing MBDS
and the temporary expansion. The
existing MBDS will continue to be
utilized as a dredged material disposal
site for those projects generating
dredged material suitable for open-water
disposal under the MPRSA. The
temporary expansion will be used solely
for the disposal of suitable dredged
material generated from the Boston
Harbor improvement dredging project.
Management of both the existing MBDS
and the temporary expansion will abide
by the Site Management and Monitoring
Plan (SMMP) for the MBDS. The SMMP
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includes management and monitoring
requirements to ensure that the any
dredged material placed at the sites is
suitable for ocean disposal and that the
adverse impacts of disposal, if any, are
addressed to the maximum extent
practicable. The SMMP for the MBDS
includes restrictions on disposal vessel
speeds, requirements for the presence of
a marine mammal observer for each
disposal event, and other guidelines to
minimize any potential conflicts with
threatened or endangered species and
other uses or activities in this area.
e. MPRSA Criteria
EPA has assessed the temporary
modification to the MBDS according to
the criteria of the MPRSA, with
particular emphasis on the general and
specific regulatory criteria of 40 CFR
228.5 and 228.6, to determine whether
the site modification satisfies those
criteria. The Final Environmental
Assessment of the Proposed Expansion
of the Massachusetts Bay Ocean
Dredged Material Disposal Site and
Finding of No Significant Impact
provides an extensive evaluation of the
site selection criteria and other related
factors considered for the modification
of the MBDS, and a summary is
included below.
General Criteria (40 CFR 228.5)
(a) The dumping of materials into the
ocean will be permitted only at sites or
in areas selected to minimize the
interference of disposal activities with
other activities in the marine
environment, particularly avoiding
areas of existing fisheries or
shellfisheries, and regions of heavy
commercial or recreational navigation.
Since its designation in 1993, disposal
at the MBDS has not interfered with
other activities in the marine
environment. It is anticipated that this
also will be the case for the temporarily
modified MBDS. The IWS has been
closed by the National Oceanic and
Atmospheric Administration’s (NOAA)
National Marine Fisheries Service
(NMFS) since 1980 to the harvesting of
surf clams and ocean quahogs. There is
also a warning from NOAA and the
Food and Drug Administration (FDA) on
all nautical charts against harvesting
fish and shellfish in the area. The
expanded MBDS area has low
recreational boater density and does not
overlap with the shipping lanes into and
out of Boston Harbor.
(b) Locations and boundaries of
disposal sites will be so chosen that
temporary perturbations in water
quality or other environmental
conditions during initial mixing caused
by disposal operations anywhere within
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the site can be expected to be reduced
to normal ambient seawater levels or to
undetectable contaminant
concentrations or effects before reaching
any beach, shoreline, marine sanctuary,
or known geographically limited fishery
or shellfishery.
The modified MBDS will be used only
for dredged material suitable for ocean
disposal under the MPRSA. USACE also
models disposal projects to evaluate
their potential to violate water quality
standards. The nearest shoreline to the
modified MBDS is approximately eight
nmi to the north. The prevailing current
is not expected to transport dredged
material to surrounding beaches or
shores. Temporary changes caused by
the physical movement of sediment
through the water column will be
reduced to ambient conditions before
reaching any environmentally sensitive
area. The SBNMS is immediately east of
the site, but a steep bathymetric rise
between the two features provides
containment of dredged material in the
deeper area known as Stellwagen Basin.
There are no known geographicallylimited fisheries or shellfisheries in the
project area.
(d) The sizes of ocean disposal sites
will be limited in order to localize for
identification and control any
immediate adverse impacts and permit
the implementation of effective
monitoring and surveillance programs
to prevent adverse long-range impacts.
The size, configuration, and location of
any disposal site will be determined as
a part of the disposal site evaluation or
designation study.
The size and configuration of the
temporarily modified MBDS is
specifically designed to allow for the
IWS barrel field to be covered by
suitable dredged material generated
during the USACE Boston Harbor
improvement project. The MBDS area
has been monitored under the USACE
Disposal Area Monitoring System
(DAMOS) program since the late 1970s.
Monitoring will continue at the
temporarily expanded MBDS to prevent
adverse long-range impacts.
(e) EPA will, wherever feasible,
designate ocean dumping sites beyond
the edge of the continental shelf and
other such sites that have been
historically used.
The continental shelf is over 220 nmi
east of Boston. Therefore, transporting
material to, and performing long-term
monitoring at, a site located off the
continental shelf is not economically or
operationally feasible. Moreover, taking
material somewhere off the continental
shelf will not help to isolate the wastes
previously placed at the IWS. The
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jstallworth on DSKBBY8HB2PROD with RULES
project area has been used for ocean
disposal since at least the early 1900s.
Specific Criteria (40 CFR 228.6(a))
(1) Geographical position, depth of
water, bottom topography and distance
from coast.
The temporarily expanded MBDS is
located in an area of Massachusetts Bay
known as Stellwagen Basin and is
approximately eight nmi from the
nearest coastline in Gloucester, MA. The
depth of the temporarily expanded site
ranges from 70–91 m. The seafloor in
the area is primarily flat and consists
primarily of silt and clay. There are two
large glacial knolls included within the
boundaries of the temporary expansion,
both roughly 20 m high. These knolls
are not included in the Potential
Restoration Area and, therefore, no
disposal will take place on them. There
is a smaller glacial knoll, approximately
six m high, included within the
boundaries of the Potential Restoration
Area. The USACE is drafting a project
design that will ensure that this feature
will be avoided by disposal operations.
(2) Location in relation to breeding,
spawning, nursery, feeding, or passage
areas of living resources in adult or
juvenile phases.
The MBDS area contains Essential
Fish Habitat (EFH) for various fish
species, and certain species of whale
and sea turtle listed as either threatened
or endangered under the Endangered
Species Act (ESA) have been sighted in
the vicinity of the MBDS. Furthermore,
the entirety of Massachusetts Bay and
most of the larger Gulf of Maine are
designated as critical foraging habitat for
the North Atlantic Right Whale by
NMFS. At the same time, NMFS has
determined that dredged material
disposal at the MBDS would not impact
any of these species and restrictions are
in place to ensure their safety, including
vessel speed limitations and the
requirement that marine mammal
observers accompany the USACE on
vessels during disposal operations.
Furthermore, any risk of contaminants
entering the food web is expected to be
minimized by the covering of the IWS
barrel field.
(3) Location in relation to beaches
and other amenity areas.
The closest beach to the temporarily
expanded MBDS is 10 nmi away. The
SBNMS is just east of the MBDS. Past
dredged material disposal has not
impacted the SBNMS and no impact to
the SBNMS is expected with the
temporary expansion of the MBDS.
(4) Types and quantities of wastes
proposed to be disposed of, and
proposed methods of release, including
methods of packing the waste, if any.
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The MBDS is only to be used for the
disposal of dredged material that is
suitable for ocean disposal under the
MPRSA. The temporary expansion of
the MBDS will only be used for suitable
dredged material generated during the
USACE Boston Harbor improvement
project. Disposal within the temporary
expansion will utilize a berm-building
technique devised by the USACE in
order to minimize the risk of barrel
breakage or resuspension of potentially
contaminated seafloor sediment.
(5) Feasibility of surveillance and
monitoring.
The MBDS is monitored through the
DAMOS program under the guidance of
the SMMP. Disposal is also monitored
through the National Dredging Quality
Management Program to confirm
accurate placement of dredged material.
The area of temporary expansion will be
included in the monitoring of the MBDS
under the DAMOS program from the
time of first disposal for as long as
MBDS monitoring continues.
(6) Dispersal, horizontal transport and
vertical mixing characteristics of the
area, including prevailing current
direction and velocity, if any.
Current velocities range from 0–30
cm/s in the MBDS area. Currents are
influenced by tides in a rotational
manner, but net water movement is to
the southeast. Regional dredged material
is primarily made up of fine sand, silt,
and clay. Dredged material generated
during the USACE Boston Harbor
improvement project is primarily
Boston blue clay, which is cohesive and,
therefore, settles rapidly. Minimal
horizontal mixing or vertical
stratification of dredged material occurs,
resulting in low suspended sediment
concentrations. Previous modeling of
initial disposal indicates no adverse
impacts in the water column or
violations of water quality criteria.
Previous studies have demonstrated the
relative immobility of dredged material
at the MBDS. Storms with the potential
to cause sediment resuspension at the
MBDS are rare in Massachusetts Bay.
(7) Existence and effects of current
and previous discharges and dumping
in the area (including cumulative
effects).
Beginning in the early 1900s, the
historic IWS was used for the disposal
of industrial, chemical, medical, lowlevel radioactive, and other hazardous
wastes, in addition to contaminated
dredged material, construction debris,
derelict vessels, etc. An Interim MBDS
was designated in 1977 for the disposal
of dredged material and it was closed in
1993, when the existing MBDS was
designated following all the
requirements of the MPRSA and
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National Environmental Policy Act
(NEPA). Studies and monitoring of the
area have shown no significant impacts
on water quality, sediment quality, or
marine resources. More information
regarding the effects of disposal in the
area can be found in the Final
Environmental Assessment on the
Proposed Expansion of the
Massachusetts Bay Ocean Dredged
Material Disposal Site and Finding of
No Significant Impact. The bermbuilding disposal technique designed by
USACE is intended to limit the
resuspension of potentially
contaminated seafloor sediment or
hazardous materials in the area.
Furthermore, placing suitable dredged
material generated during the USACE
Boston Harbor improvement project on
top of potentially contaminated
materials dumped at the IWS in the past
will isolate these potential contaminants
under a protective layer of suitable
sediments, consisting primarily of clay.
(8) Interference with shipping, fishing,
recreation, mineral extraction,
desalination, fish and shellfish culture,
areas of special scientific importance
and other legitimate uses of the ocean.
Extensive shipping, fishing,
recreational, and scientific research
activities take place in Massachusetts
Bay throughout the year. Dredged
material disposal operations at the
MBDS have not interfered with these
activities and temporarily expanding the
MBDS is not expected to interfere with
these activities either. Due to the
hazardous nature of material historically
disposed in the IWS, a warning to
fishermen against fishing and
shellfishing in the area is already
included on all nautical charts, and the
area is closed for the harvesting of ocean
quahogs and surf clams. Therefore,
disposal operations in the area are not
expected to interfere with any existing
fishing activity. To the extent that
fishermen ignore the warnings regarding
the IWS, the proposed action will not
create any greater interference because,
as stated above, both fishing and
dredged material disposal activities
have long been carried out in the area
of the MBDS without interference.
Moreover, once the IWS barrel field is
covered, the area should be safer for any
fishermen who drag their nets through
that area.
(9) The existing water quality and
ecology of the site as determined by
available data or by trend assessment or
baseline surveys.
Monitoring at the disposal area has
taken place since the late 1970s under
the DAMOS program. Surveys at the
MBDS have detected no significant
differences in water quality or biological
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characteristics in the disposal site and
adjacent reference areas. A Baseline
Seafloor Assessment Survey for the
Proposed Expansion of the
Massachusetts Bay Disposal Site was
completed by the USACE in
anticipation of this project and is
available on the USACE DAMOS
webpage at https://
www.nae.usace.army.mil/Missions/
Disposal-Area-Monitoring-SystemDAMOS/.
(10) Potentiality for the development
or recruitment of nuisance species in
the disposal site.
There are no known components of
dredged material or consequences of its
disposal that would attract or result in
the recruitment or development of
nuisance species at the expanded
MBDS. Nuisance species have not been
detected in any survey of the area.
(11) Existence at or in close proximity
to the site of any significant natural or
cultural features of historical
importance.
There are two known shipwrecks
within the boundaries of the existing
MBDS: a Coast Guard vessel and a 55foot fishing boat. Both were
intentionally sunk in 1981 and are not
considered to be historically significant.
Additional shipwrecks have been
revealed in the general area during
subsequent surveys, although there are
no identified shipwrecks within the
Potential Restoration Area. Disposal
operations have avoided and will
continue to avoid any shipwrecks in the
project area by implementing a fiftymeter buffer around known shipwrecks
within which no disposal will occur.
III. Environmental Statutory Review
jstallworth on DSKBBY8HB2PROD with RULES
a. National Environmental Policy Act
(NEPA)
Section 102 of the National
Environmental Policy Act of 1969, as
amended (NEPA), 42 U.S.C. 4321 to
4370f, requires federal agencies to
prepare an Environmental Impact
Statement (EIS) for major federal actions
significantly affecting the quality of the
human environment. When a federal
agency evaluates an action that it plans
to take and finds that it will not
significantly affect the environment, it
may issue an Environmental
Assessment and a Finding of No
Significant Impact (i.e., an ‘‘EA/
FONSI’’).
NEPA does not apply to EPA
designations of ocean disposal sites
under the MPRSA because EPA’s
actions under the MPRSA are exempt
from the procedural requirements of
NEPA through the functional
equivalence doctrine. Nevertheless, as a
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matter of policy, EPA undertakes a
NEPA review for certain of its regulatory
actions, including the designation of
dredged material disposal sites under
Section 102 of the MPRSA. The EPA’s
‘‘Notice of Policy and Procedures for
Voluntary Preparation of NEPA
Documents’’ (Voluntary NEPA Policy),
63 FR 58045 (October 29, 1998), sets out
both the policy and procedures the EPA
uses when preparing such
environmental review documents.
The EPA’s primary voluntary NEPA
document addressing the temporary
expansion of the MBDS is the Final
Environmental Assessment on the
Proposed Expansion of the
Massachusetts Bay Ocean Dredged
Material Disposal Site and Finding of
No Significant Impact (Final EA),
prepared by EPA in cooperation with
USACE. Anyone desiring a copy of the
Final EA may obtain one using the
methods provided above in the Docket
section. The Draft Environmental
Assessment on the Expansion of the
Massachusetts Bay Ocean Dredged
Material Disposal Site (ODMDS) (Draft
EA) was released for public review
concurrently with the Proposed Rule.
The Final EA, which is part of the
Docket for this action, provides the
environmental review for the temporary
modification of the MBDS. Information
from the Final EA is used in the above
discussion of the ocean dumping
criteria.
b. Magnuson-Stevens Fishery
Conservation & Management Act (MSA)
EPA integrated the EFH assessment
into the Draft EA, pursuant to Section
305(b), 16 U.S.C. 1855(b)(2), of the
Magnuson-Stevens Act, as amended
(MSA), 16 U.S.C. 1801–1891d, and
submitted that assessment to NMFS on
September 28, 2017. NMFS responded
via letter with a recommendation to
avoid disposal on the glacial knoll that
is within the boundaries of the Potential
Restoration Area. EPA and USACE have
adopted this recommendation and will
avoid the disposal of any dredged
material on this feature. This
recommendation has also been
incorporated into the Final EA.
c. Coastal Zone Management Act
(CZMA)
EPA determined that the modification
of the MBDS is consistent to the
maximum extent practicable with the
enforceable policies of the
Massachusetts coastal management
program, and a letter was submitted to
the Massachusetts Office of Coastal
Zone Management (MCZM) on
September 28, 2017. MCZM submitted a
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letter of concurrence to EPA on
November 30, 2017.
d. Endangered Species Act (ESA)
The Endangered Species Act, as
amended (ESA), 16 U.S.C. 1531 to 1544,
requires federal agencies to consult with
NMFS and the U.S. Fish and Wildlife
Service (FWS) to ensure that any action
authorized, funded, or carried out by the
federal agency is not likely to jeopardize
the continued existence of any
endangered species or threatened
species or result in the destruction or
adverse modification of any critical
habitat. The EPA incorporated an
assessment of the potential effects of
temporarily modifying the MBDS on
aquatic and wildlife species, including
any species listed under the ESA, into
the Draft EA, and EPA has submitted
that assessment to NMFS and FWS. EPA
concluded that this action is not likely
to adversely affect any threatened or
endangered species, nor would it
adversely modify any designated critical
habitat. EPA submitted a letter to NMFS
on October 30, 2017, that stated that the
re-initiation of consultation was not
necessary for this action. NMFS
submitted a letter of concurrence to EPA
on November 21, 2017. EPA sent a letter
to FWS on September 22, 2017, and
confirmed that no consultation was
necessary.
e. National Historic Preservation Act
(NHPA)
The National Historic Preservation
Act, as amended (NHPA), 16 U.S.C. 470
to 470a–2, requires federal agencies to
take into account the effect of their
actions on districts, sites, buildings,
structures, or objects, included in, or
eligible for inclusion in, the National
Register of Historical Places. EPA
submitted a letter to the Massachusetts
State Historic Preservation Office
(SHPO) on September 28, 2017,
outlining the plan to avoid the historic
shipwrecks in the area during disposal
operations. The Massachusetts SHPO
provided a letter of concurrence with
the avoidance plan to EPA on October
19, 2017.
IV. Statutory and Executive Order
Reviews
This rulemaking proposes the
modification of an ODMDS pursuant to
Section 102 of the MPRSA. This action
complies with applicable Executive
Orders and statutory provisions as
follows:
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a. Executive Order 12866: Regulatory
Planning and Review; Executive Order
13563: Improving Regulation and
Regulatory Review
This action is not a ‘‘significant
regulatory action’’ under the terms of
Executive Order 12866 (58 FR 51735,
October 3, 1993) and is, therefore, not
subject to review under Executive
Orders 12866 and 13563 (76 FR 3821,
January 21, 2011).
b. Paperwork Reduction Act
This action does not impose an
information collection burden under the
provisions of the Paperwork Reduction
Act, 44 U.S.C. 3501 et seq. This
temporary site modification does not
require persons to obtain, maintain,
retain, report, or publicly disclose
information to or for a federal agency.
c. Regulatory Flexibility Act
The Regulatory Flexibility Act (RFA)
generally requires federal agencies to
prepare a regulatory flexibility analysis
of any rule subject to notice and
comment rulemaking requirements
under the Administrative Procedure Act
or any other statute unless the agency
certifies that the rule will not have a
significant economic impact on a
substantial number of small entities
(businesses, organizations, or
jurisdictions). EPA has determined that
this action will not have a significant
economic impact on small entities.
jstallworth on DSKBBY8HB2PROD with RULES
d. Unfunded Mandates Reform Act
This action contains no federal
mandates under the provisions of Title
II of the Unfunded Mandates Reform
Act (UMRA) of 1995, 2 U.S.C. 1531 to
1538, for state, local, or tribal
governments or the private sector. This
action imposes no new enforceable duty
on any state, local or tribal governments
or the private sector. Therefore, this
action is not subject to the requirements
of sections 202 or 205 of the UMRA.
This action is also not subject to the
requirements of section 203 of the
UMRA because it contains no regulatory
requirements that might significantly or
uniquely affect small government
entities. Those entities are already
subject to existing permitting
requirements for the disposal of dredged
material in ocean waters.
e. Executive Order 13132: Federalism
This action does not have federalism
implications. It does not have
substantial direct effects on the states,
on the relationship between the national
government and the states, or on the
distribution of power and
responsibilities among various levels of
government, as specified in Executive
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Order 13132. Thus, Executive Order
13132 does not apply to this action. In
the spirit of Executive Order 13132, and
consistent with EPA policy to promote
communications between the EPA and
state and local governments, EPA has
coordinated with, and specifically
solicited comments from, state and local
officials with regard to this action.
f. Executive Order 13175: Consultation
and Coordination With Indian Tribal
Governments
This action does not have tribal
implications, as specified in Executive
Order 13175. The modification of the
MBDS will not have a direct effect on
Indian tribes, on the relationship
between the federal government and
Indian tribes, or on the distribution of
power and responsibilities between the
federal government and Indian tribes.
Thus, Executive Order 13175 does not
apply to this action.
g. Executive Order 13045: Protection of
Children From Environmental Health &
Safety Risks
This action is not subject to Executive
Order 13045 because it is not
economically significant as defined in
Executive Order 12866 and because the
EPA does not believe the environmental
health or safety risks addressed by this
action present a disproportionate risk to
children.
h. Executive Order 13211: Actions That
Significantly Affect Energy Supply,
Distribution, or Use
This action is not subject to Executive
Order 13211 (66 FR 28355) because it is
not a ‘‘significant regulatory action’’ as
defined under Executive Order 12866.
i. National Technology Transfer and
Advancement Act
This rulemaking does not involve
technical standards and, therefore, the
National Technology Transfer and
Advancement Act does not apply.
j. Executive Order 12898: Federal
Actions To Address Environmental
Justice in Minority Populations and
Low-Income Populations
Executive Order 12898 (59 FR 7629)
establishes federal executive policy on
environmental justice. Its main
provision directs federal agencies, to the
greatest extent practicable and
permitted by law, to make
environmental justice part of their
mission by identifying and addressing,
as appropriate, disproportionately high
and adverse human health or
environmental effects of their programs,
policies, and activities on minority
populations and low-income
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24413
populations in the United States. The
EPA determined that this action will not
have disproportionately high and
adverse human health or environmental
effects on minority or low-income
populations. This action is expected to
be protective of human health because
it will enable the wastes already within
the Potential Restoration Area to be
isolated under a protective layer of
sediment. This should help prevent any
accidental recovery of barrels by
fishermen and prevent contaminants
from the historic disposal from entering
the food web. The EPA has assessed the
overall protectiveness of modifying the
MBDS against the criteria established
pursuant to the MPRSA to ensure that
any adverse impact to the environment
will be mitigated to the greatest extent
practicable. No adverse impacts are
expected. The action is, instead,
expected to improve environmental
conditions in Massachusetts Bay by
enabling contaminated material dumped
at the IWS in the past to be covered with
suitable dredged material in order to
isolate the former from the environment.
k. Executive Order 13158: Marine
Protected Areas
Executive Order 13158 (65 FR 34909,
May 31, 2000) requires EPA to
‘‘expeditiously propose new sciencebased regulations, as necessary, to
ensure appropriate levels of protection
for the marine environment.’’ EPA may
take action to enhance or expand
protection of existing marine protected
areas and to establish or recommend, as
appropriate, new marine protected
areas. The purpose of the Executive
Order is to protect the significant
natural and cultural resources with the
marine environment, which includes,
‘‘those areas of coastal and ocean
waters, the Great Lakes and their
connecting waters, and submerged lands
thereunder, over which the United
States exercises jurisdiction, consistent
with international law.’’
EPA anticipates that this action will
afford additional protection to the
waters of Massachusetts Bay and
organisms that inhabit them. By
covering the barrel field and
surrounding seafloor sediment of the
historic IWS, potential contaminants
should be prevented from entering the
water column or food web in
Massachusetts Bay. This should
provide, if anything, greater protection
for the natural resources of the SBNMS,
which is in the vicinity of the
temporarily expanded MBDS.
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Federal Register / Vol. 83, No. 103 / Tuesday, May 29, 2018 / Rules and Regulations
l. Executive Order 13547: Stewardship
of the Ocean, Our Coasts, and the Great
Lakes
Section 6(a)(i) of Executive Order
13547, (75 FR 43023, July 19, 2010)
requires, among other things, EPA and
certain other agencies ‘‘ . . . to the
fullest extent consistent with applicable
law [to] . . . take such action as
necessary to implement the policy set
forth in section 2 of this order and the
stewardship principles and national
priority objectives as set forth in the
Final Recommendations and subsequent
guidance from the Council.’’ The
policies in section 2 of Executive Order
13547 include, among other things, the
following: ‘‘ . . . it is the policy of the
United States to: (i) Protect, maintain,
and restore the health and biological
diversity of ocean, coastal, and Great
Lakes ecosystems and resources; [and]
(ii) improve the resiliency of ocean,
coastal, and Great Lakes ecosystems,
communities, and economies. . . .’’ As
with Executive Order 13158 (Marine
Protected Areas), the overall purpose of
the Executive Order is to promote
protection of ocean and coastal
environmental resources.
EPA anticipates that this action will
afford additional protection to the
waters of Massachusetts Bay and
organisms that inhabit them. By
covering the barrel field and
surrounding seafloor sediment of the
historic IWS, potential contaminants
should be prevented from entering the
water column or food web in
Massachusetts Bay.
m. Executive Order 13771 Reducing
Regulation and Controlling Regulatory
Costs
jstallworth on DSKBBY8HB2PROD with RULES
This action would not be a
‘‘significant regulatory action’’ under
the terms of Executive Order 12866 (58
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FR 51735, October 3, 1993) and is,
therefore, not subject to review under
Executive Order 13771. See OMB,
‘‘Guidance Implementing Executive
Order 13771, Titled ‘‘Reducing
Regulation and Controlling Regulatory
Costs’’ (M–17–21) (April 5, 2017), p. 3
(‘‘An ‘E.O. 13771 Regulatory Action’ is:
(i) A significant regulatory action as
defined in section 3(f) of E.O. 12866 that
has been finalized and that imposes
total costs greater than zero. . . .’’).
n. Congressional Review Act
The Congressional Review Act, 5
U.S.C. 801 et seq., as added by the Small
Business Regulatory Enforcement
Fairness Act of 1996, generally provides
that before a rule may take effect, the
agency promulgating the rule must
submit a rule report, which includes a
copy of the rule, to each House of the
Congress and to the Comptroller General
of the United States. EPA will submit a
report containing this rule and other
required information to the U.S. Senate,
the U.S. House of Representatives, and
the Comptroller General of the United
States prior to publication of the rule in
the Federal Register. A ‘‘major rule’’
cannot take effect until 60 days after it
is published in the Federal Register.
This action is not a major rule as
defined by 5 U.S.C. 804(2). This rule
will be effective 30 days after date of
publication.
List of Subjects in 40 CFR Part 228
Environmental protection, Water
pollution control.
Dated: May 15, 2018.
Alexandra Dapolito Dunn
Regional Administrator, EPA Region 1.
For the reasons stated in the
preamble, title 40, Chapter I, of the Code
of Federal Regulations is to be amended
as set forth below.
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PART 228—CRITERIA FOR THE
MANAGEMENT OF DISPOSAL SITES
FOR OCEAN DUMPING
1. The authority citation for part 228
continues to read as follows:
■
Authority: 33 U.S.C. 1412 and 1418.
2. Amend § 228.15 by revising
paragraphs (b)(2)(i), (ii), (iii), and (vi) to
read as follows:
■
§ 228.15 Dumping sites designated on a
final basis.
*
*
*
*
*
(b) * * *
(2) * * *
(i) Location: Two overlapping circles:
Center of existing MBDS: 42°25.1′ N,
70°35.0′ W, 1 nautical mile radius;
Center of temporary expansion:
42°26.417′ N, 70°35.373′ W, 0.75
nautical mile radius (NAD 1983).
(ii) Size: 4.60 sq. nautical miles.
(iii) Depth: Range from 70 to 91
meters.
*
*
*
*
*
(vi) Restriction: Disposal shall be
limited to dredged material which meets
the requirements of the MPRSA and its
accompanying regulations. Disposaland-capping is prohibited at the MBDS
until its efficacy can be effectively
demonstrated. The temporary expansion
of the MBDS shall be used solely for the
disposal of suitable dredged material
generated during the Boston Harbor
Deep Draft Navigation Project using the
berm-building method devised and
tested by the U.S. Army Corps of
Engineers. The temporary expansion
will automatically close upon
completion of the Boston Harbor Deep
Draft Navigation Project.
*
*
*
*
*
[FR Doc. 2018–11322 Filed 5–25–18; 8:45 am]
BILLING CODE 6560–50–P
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Agencies
[Federal Register Volume 83, Number 103 (Tuesday, May 29, 2018)]
[Rules and Regulations]
[Pages 24408-24414]
From the Federal Register Online via the Government Publishing Office [www.gpo.gov]
[FR Doc No: 2018-11322]
-----------------------------------------------------------------------
ENVIRONMENTAL PROTECTION AGENCY
40 CFR Part 228
[EPA-R01-OW-2017-0528; FRL-9978-51--Region 1]
Ocean Disposal; Temporary Modification of an Ocean Dredged
Material Disposal Site in Massachusetts Bay
AGENCY: Environmental Protection Agency (EPA).
ACTION: Final rule.
-----------------------------------------------------------------------
SUMMARY: The Environmental Protection Agency (EPA) is approving a
temporary modification of the boundaries of the Massachusetts Bay
Dredged Material Disposal Site (MBDS) pursuant to the Marine
Protection, Research, and Sanctuaries Act (MPRSA), as amended. The
purpose of this temporary site modification is to allow for the
environmental restoration of a particular area adjacent to the MBDS
(Potential Restoration Area) by temporarily expanding the boundaries of
the existing MBDS. The temporary expansion is a circular area that
contains the Potential Restoration Area, which includes most of the
historic Industrial Waste Site (IWS). Decades ago, the IWS was used for
the disposal of barrels containing industrial, chemical and low-level
radioactive waste, as well as for the disposal of munitions, ordnance,
construction equipment, and contaminated dredged material. The
modification of the disposal site boundary will enable the U.S. Army
Corps of Engineers (USACE) to place suitable dredged material generated
from the Boston Harbor Deep Draft Navigation Project at the Potential
Restoration Area in order to cover the barrels and other wastes
disposed there in the past. This is expected to improve environmental
conditions at the site. The Deep Draft Navigation Project includes
improvement dredging of the main ship channel, which will generate
approximately 11 million cubic yards (cy) of dredged material. The
existing MBDS will continue to be used for disposal of other dredging
projects, as usual. The expansion area will permanently close upon
completion of the Boston Harbor Deep Draft Navigation Project, while
the existing MBDS will remain open for the disposal of other suitable
dredged material. Like the MBDS, however, the expansion area will be
subject to ongoing monitoring and management to monitor the recovery of
the area and to ensure continued protection of the marine environment.
DATES: The effective date of this rule is June 28, 2018.
ADDRESSES: The EPA has established a docket for this action under
Docket ID No. EPA-R01-OW-2017-0528. All documents in the docket are
listed on the https://www.regulations.gov website or on the EPA Region
1 MBDS web page at https://www.epa.gov/ocean-dumping/massachusetts-bay-industrial-waste-site-restoration-project. Although listed in
[[Page 24409]]
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, is not placed on the
internet and will be publicly available only in hard copy form.
Publicly available docket materials are available electronically
through https://www.regulations.gov. They are also available in hard
copy during normal business hours at the EPA Region 1 Library, 5 Post
Office Square Boston, MA 02109.
The supporting document for this site modification is the Final
Environmental Assessment on the Proposed Expansion of the Massachusetts
Bay Ocean Dredged Material Disposal Site and Finding of No Significant
Impact, May 2018, which was prepared by EPA.
FOR FURTHER INFORMATION CONTACT: Alicia Grimaldi, U.S. Environmental
Protection Agency, Region 1, 5 Post Office Square, Suite 100, Mail
Code: OEP 6-1, Boston, MA 02109; telephone--(617) 918-1806; fax--(617)
918-0806; email [email protected]
SUPPLEMENTARY INFORMATION:
I. Potentially Affected Persons
The expansion of the MBDS is a temporary modification made in order
to improve environmental conditions at the Potential Restoration Area
by allowing suitable dredged material from the USACE Boston Harbor
improvement project to be placed over wastes dumped in the past at the
historic IWS. The USACE are persons potentially affected by this
action, as they are responsible for the Boston Harbor Deep Draft
Navigation Project and the disposal of dredged material into ocean
waters under MPRSA. The existing MBDS will continue to be used for the
disposal of dredged material from other projects that is suitable for
ocean disposal pursuant to the MPRSA. This action will also impact
those fishermen who utilize the historic IWS for fishing, despite
posted warnings, by helping to reduce the risk of potential injury
resulting from the inadvertent retrieval of wastes from the IWS in
their nets. There have been documented instances of fishermen trawling
up barrels in the IWS area and this action will lower the risk of that
occurring in the future.
II. Background
a. History of Disposal Sites in Massachusetts Bay
The IWS is a disposal site in Massachusetts Bay approximately 20
nautical miles (nmi) east of Boston that was used in the past for
disposal of a variety of wastes that would not be permitted for
disposal today. The IWS is a circular site with its center at
42[deg]25.7' N, 70[deg]35.0' W and a radius of 1 nmi. It is believed
that disposal of derelict vessels, construction debris, commercial
waste, and dredged material at the area may have begun in the early
1900s. There are records dating back to the 1940s documenting the
disposal of radioactive, chemical and hospital waste, ordnance,
munitions, etc. Use of the IWS was discontinued in 1977 and the site
was officially de-designated in 1990 (55 FR 3688, February 2, 1990).
From 1977 through 1993, there was an Interim Massachusetts Bay Disposal
Site for dredged material disposal with a center 1 nmi east of the IWS
at 42[deg]25.7' N, 70[deg]34.0' W and a radius of 1 nmi. In 1993, the
existing MBDS was designated by EPA with a center at 42[deg]25.1' N,
70[deg]35.0' W and a radius of 1 nmi, an area of 3.14 nmi\2\, and depth
ranges from 82 to 92 meters (m). The MBDS overlaps the southern portion
of the IWS, but avoids the known densest concentration of barrels, also
known as the barrel field. The MBDS is used solely for the disposal of
dredged material, primarily from Boston Harbor, but also from smaller
harbors and navigation channels north and south of Boston.
The USACE will begin the Boston Harbor improvement dredging project
in 2018. The project is expected to generate approximately 11 million
cy of suitable dredged material consisting primarily of Boston blue
clay and glacial till. EPA and USACE are proposing to use this dredged
material beneficially by covering the area in and around the historic
IWS barrel field to a depth of one to two meters. This will be
accomplished utilizing a method of disposal developed and tested by the
USACE, which is designed to prevent direct impact of sediment onto
waste containers. This method of disposal is intended to reduce the
risk of breaking barrels and resuspending potentially contaminated
seafloor sediment.
Before any entity can dispose of dredged material at the MBDS, EPA
and the USACE must evaluate the project according to the ocean dumping
regulatory criteria (40 CFR 227) and determine whether to authorize the
disposal. Under Section 103 of the MPRSA, disposal projects are
authorized by the USACE and EPA independently evaluates proposed
disposal projects and has the right to restrict and/or reject the
disposal of dredged material if it determines that the environmental
protection requirements under the MPRSA have not been met. This
modification to the MBDS site boundaries does not constitute an
approval by EPA or USACE for open-water disposal of dredged material
from any specific project. Thus, although the plan is that suitable
material from the USACE's Boston Harbor improvement project would be
placed at the temporary expansion area, any material proposed for
disposal will have to go through project-specific review and approval.
b. Location and Configuration of the Modified Ocean Dredged Material
Disposal Site
This Final Rule temporarily modifies the MBDS by expanding it to
include the Potential Restoration Area, which encompasses the IWS
barrel field. The expansion will be temporary, opening upon the
effective date of the Final Rule and closing upon completion of the
Boston Harbor Deep Draft Navigation Project. The temporarily expanded
site will consist of two partially overlapping circles:
Center 1--42[deg]25.1' N, 70[deg]35.0' W, 1 nautical mile
radius (existing MBDS)
Center 2--42[deg]26.417' N, 70[deg]35.373' W, 0.75 nautical
mile radius (temporary expansion)
The area of the temporarily modified MBDS is 4.60 nmi\2\ and the
western edge is approximately 19 nmi east of Boston. Water depths at
the modified site range from 70 to 91 m. Like the existing MBDS, the
modified MBDS will not overlap, and is not expected to impact, the
Stellwagen Bank National Marine Sanctuary (SBNMS).
c. Response to Comments
On September 22, 2017, EPA published a Proposed Rule proposing to
temporarily modify the MBDS with a supporting Draft Environmental
Assessment and opened a public comment period under Docket ID EPA-R01-
OW-2017-0528. The comment period ended on October 23, 2017. EPA
received eleven comments on the Proposed Rule and Draft Environmental
Assessment. The comments received are listed below:
Support of the temporary expansion of the MBDS (6
commenters);
Boundaries of the temporary expansion of the MBDS overlap
with the Neptune Deepwater Port (1 commenter);
Importance of proceeding with disposal carefully to
prevent breakage of barrels (4 commenters);
Barrels may no longer exist on the seafloor (1 commenter);
Sewage sludge should not be disposed in the ocean or used
for capping (1 commenter);
[[Page 24410]]
There is no evidence of contamination at the IWS (1
commenter);
Disposing material further out into the ocean is a cheaper
solution (1 commenter);
Other disposal sites were not considered (1 commenter);
The temporary expansion of the MBDS will eliminate
fishable bottom (2 commenters);
How to stay informed on the status of the project (2
commenters);
Disposal could impact the health of the ecosystem (1
commenter);
Typographic errors in Draft EA (1 commenter);
Modification of the MBDS will change the size of the SBNMS
(1 commenter);
The Potential Restoration Area will increase with
additional dredged material (1 commenter);
The removal of barrels from the IWS was not considered as
an alternative (2 commenters);
Ensure that the disposal of dredged material and the
temporary expansion is monitored (2 commenters);
The Massachusetts Department of Marine Fisheries (MDMF)
would like to consult on disposal time-of-year restrictions to minimize
impact to cod spawning (1 commenter); and
MDMF would like the USACE and EPA to continue
participating in a working group exploring other opportunities for
beneficial use of dredged material (1 commenter).
The responses to these comments can be found in the Final
Environmental Assessment on the Proposed Expansion of the Massachusetts
Bay Ocean Dredged Material Disposal Site and Finding of No Significant
Impact, which is available on Regulations.gov and the EPA Region 1 MBDS
web page: https://www.epa.gov/ocean-dumping/massachusetts-bay-industrial-waste-site-restoration-project.
d. Management and Monitoring of the Site
There will be two distinct areas of the modified MBDS: The existing
MBDS and the temporary expansion. The existing MBDS will continue to be
utilized as a dredged material disposal site for those projects
generating dredged material suitable for open-water disposal under the
MPRSA. The temporary expansion will be used solely for the disposal of
suitable dredged material generated from the Boston Harbor improvement
dredging project. Management of both the existing MBDS and the
temporary expansion will abide by the Site Management and Monitoring
Plan (SMMP) for the MBDS. The SMMP includes management and monitoring
requirements to ensure that the any dredged material placed at the
sites is suitable for ocean disposal and that the adverse impacts of
disposal, if any, are addressed to the maximum extent practicable. The
SMMP for the MBDS includes restrictions on disposal vessel speeds,
requirements for the presence of a marine mammal observer for each
disposal event, and other guidelines to minimize any potential
conflicts with threatened or endangered species and other uses or
activities in this area.
e. MPRSA Criteria
EPA has assessed the temporary modification to the MBDS according
to the criteria of the MPRSA, with particular emphasis on the general
and specific regulatory criteria of 40 CFR 228.5 and 228.6, to
determine whether the site modification satisfies those criteria. The
Final Environmental Assessment of the Proposed Expansion of the
Massachusetts Bay Ocean Dredged Material Disposal Site and Finding of
No Significant Impact provides an extensive evaluation of the site
selection criteria and other related factors considered for the
modification of the MBDS, and a summary is included below.
General Criteria (40 CFR 228.5)
(a) The dumping of materials into the ocean will be permitted only
at sites or in areas selected to minimize the interference of disposal
activities with other activities in the marine environment,
particularly avoiding areas of existing fisheries or shellfisheries,
and regions of heavy commercial or recreational navigation.
Since its designation in 1993, disposal at the MBDS has not
interfered with other activities in the marine environment. It is
anticipated that this also will be the case for the temporarily
modified MBDS. The IWS has been closed by the National Oceanic and
Atmospheric Administration's (NOAA) National Marine Fisheries Service
(NMFS) since 1980 to the harvesting of surf clams and ocean quahogs.
There is also a warning from NOAA and the Food and Drug Administration
(FDA) on all nautical charts against harvesting fish and shellfish in
the area. The expanded MBDS area has low recreational boater density
and does not overlap with the shipping lanes into and out of Boston
Harbor.
(b) Locations and boundaries of disposal sites will be so chosen
that temporary perturbations in water quality or other environmental
conditions during initial mixing caused by disposal operations anywhere
within the site can be expected to be reduced to normal ambient
seawater levels or to undetectable contaminant concentrations or
effects before reaching any beach, shoreline, marine sanctuary, or
known geographically limited fishery or shellfishery.
The modified MBDS will be used only for dredged material suitable
for ocean disposal under the MPRSA. USACE also models disposal projects
to evaluate their potential to violate water quality standards. The
nearest shoreline to the modified MBDS is approximately eight nmi to
the north. The prevailing current is not expected to transport dredged
material to surrounding beaches or shores. Temporary changes caused by
the physical movement of sediment through the water column will be
reduced to ambient conditions before reaching any environmentally
sensitive area. The SBNMS is immediately east of the site, but a steep
bathymetric rise between the two features provides containment of
dredged material in the deeper area known as Stellwagen Basin. There
are no known geographically-limited fisheries or shellfisheries in the
project area.
(d) The sizes of ocean disposal sites will be limited in order to
localize for identification and control any immediate adverse impacts
and permit the implementation of effective monitoring and surveillance
programs to prevent adverse long-range impacts. The size,
configuration, and location of any disposal site will be determined as
a part of the disposal site evaluation or designation study.
The size and configuration of the temporarily modified MBDS is
specifically designed to allow for the IWS barrel field to be covered
by suitable dredged material generated during the USACE Boston Harbor
improvement project. The MBDS area has been monitored under the USACE
Disposal Area Monitoring System (DAMOS) program since the late 1970s.
Monitoring will continue at the temporarily expanded MBDS to prevent
adverse long-range impacts.
(e) EPA will, wherever feasible, designate ocean dumping sites
beyond the edge of the continental shelf and other such sites that have
been historically used.
The continental shelf is over 220 nmi east of Boston. Therefore,
transporting material to, and performing long-term monitoring at, a
site located off the continental shelf is not economically or
operationally feasible. Moreover, taking material somewhere off the
continental shelf will not help to isolate the wastes previously placed
at the IWS. The
[[Page 24411]]
project area has been used for ocean disposal since at least the early
1900s.
Specific Criteria (40 CFR 228.6(a))
(1) Geographical position, depth of water, bottom topography and
distance from coast.
The temporarily expanded MBDS is located in an area of
Massachusetts Bay known as Stellwagen Basin and is approximately eight
nmi from the nearest coastline in Gloucester, MA. The depth of the
temporarily expanded site ranges from 70-91 m. The seafloor in the area
is primarily flat and consists primarily of silt and clay. There are
two large glacial knolls included within the boundaries of the
temporary expansion, both roughly 20 m high. These knolls are not
included in the Potential Restoration Area and, therefore, no disposal
will take place on them. There is a smaller glacial knoll,
approximately six m high, included within the boundaries of the
Potential Restoration Area. The USACE is drafting a project design that
will ensure that this feature will be avoided by disposal operations.
(2) Location in relation to breeding, spawning, nursery, feeding,
or passage areas of living resources in adult or juvenile phases.
The MBDS area contains Essential Fish Habitat (EFH) for various
fish species, and certain species of whale and sea turtle listed as
either threatened or endangered under the Endangered Species Act (ESA)
have been sighted in the vicinity of the MBDS. Furthermore, the
entirety of Massachusetts Bay and most of the larger Gulf of Maine are
designated as critical foraging habitat for the North Atlantic Right
Whale by NMFS. At the same time, NMFS has determined that dredged
material disposal at the MBDS would not impact any of these species and
restrictions are in place to ensure their safety, including vessel
speed limitations and the requirement that marine mammal observers
accompany the USACE on vessels during disposal operations. Furthermore,
any risk of contaminants entering the food web is expected to be
minimized by the covering of the IWS barrel field.
(3) Location in relation to beaches and other amenity areas.
The closest beach to the temporarily expanded MBDS is 10 nmi away.
The SBNMS is just east of the MBDS. Past dredged material disposal has
not impacted the SBNMS and no impact to the SBNMS is expected with the
temporary expansion of the MBDS.
(4) Types and quantities of wastes proposed to be disposed of, and
proposed methods of release, including methods of packing the waste, if
any.
The MBDS is only to be used for the disposal of dredged material
that is suitable for ocean disposal under the MPRSA. The temporary
expansion of the MBDS will only be used for suitable dredged material
generated during the USACE Boston Harbor improvement project. Disposal
within the temporary expansion will utilize a berm-building technique
devised by the USACE in order to minimize the risk of barrel breakage
or resuspension of potentially contaminated seafloor sediment.
(5) Feasibility of surveillance and monitoring.
The MBDS is monitored through the DAMOS program under the guidance
of the SMMP. Disposal is also monitored through the National Dredging
Quality Management Program to confirm accurate placement of dredged
material. The area of temporary expansion will be included in the
monitoring of the MBDS under the DAMOS program from the time of first
disposal for as long as MBDS monitoring continues.
(6) Dispersal, horizontal transport and vertical mixing
characteristics of the area, including prevailing current direction and
velocity, if any.
Current velocities range from 0-30 cm/s in the MBDS area. Currents
are influenced by tides in a rotational manner, but net water movement
is to the southeast. Regional dredged material is primarily made up of
fine sand, silt, and clay. Dredged material generated during the USACE
Boston Harbor improvement project is primarily Boston blue clay, which
is cohesive and, therefore, settles rapidly. Minimal horizontal mixing
or vertical stratification of dredged material occurs, resulting in low
suspended sediment concentrations. Previous modeling of initial
disposal indicates no adverse impacts in the water column or violations
of water quality criteria. Previous studies have demonstrated the
relative immobility of dredged material at the MBDS. Storms with the
potential to cause sediment resuspension at the MBDS are rare in
Massachusetts Bay.
(7) Existence and effects of current and previous discharges and
dumping in the area (including cumulative effects).
Beginning in the early 1900s, the historic IWS was used for the
disposal of industrial, chemical, medical, low-level radioactive, and
other hazardous wastes, in addition to contaminated dredged material,
construction debris, derelict vessels, etc. An Interim MBDS was
designated in 1977 for the disposal of dredged material and it was
closed in 1993, when the existing MBDS was designated following all the
requirements of the MPRSA and National Environmental Policy Act (NEPA).
Studies and monitoring of the area have shown no significant impacts on
water quality, sediment quality, or marine resources. More information
regarding the effects of disposal in the area can be found in the Final
Environmental Assessment on the Proposed Expansion of the Massachusetts
Bay Ocean Dredged Material Disposal Site and Finding of No Significant
Impact. The berm-building disposal technique designed by USACE is
intended to limit the resuspension of potentially contaminated seafloor
sediment or hazardous materials in the area. Furthermore, placing
suitable dredged material generated during the USACE Boston Harbor
improvement project on top of potentially contaminated materials dumped
at the IWS in the past will isolate these potential contaminants under
a protective layer of suitable sediments, consisting primarily of clay.
(8) Interference with shipping, fishing, recreation, mineral
extraction, desalination, fish and shellfish culture, areas of special
scientific importance and other legitimate uses of the ocean.
Extensive shipping, fishing, recreational, and scientific research
activities take place in Massachusetts Bay throughout the year. Dredged
material disposal operations at the MBDS have not interfered with these
activities and temporarily expanding the MBDS is not expected to
interfere with these activities either. Due to the hazardous nature of
material historically disposed in the IWS, a warning to fishermen
against fishing and shellfishing in the area is already included on all
nautical charts, and the area is closed for the harvesting of ocean
quahogs and surf clams. Therefore, disposal operations in the area are
not expected to interfere with any existing fishing activity. To the
extent that fishermen ignore the warnings regarding the IWS, the
proposed action will not create any greater interference because, as
stated above, both fishing and dredged material disposal activities
have long been carried out in the area of the MBDS without
interference. Moreover, once the IWS barrel field is covered, the area
should be safer for any fishermen who drag their nets through that
area.
(9) The existing water quality and ecology of the site as
determined by available data or by trend assessment or baseline
surveys.
Monitoring at the disposal area has taken place since the late
1970s under the DAMOS program. Surveys at the MBDS have detected no
significant differences in water quality or biological
[[Page 24412]]
characteristics in the disposal site and adjacent reference areas. A
Baseline Seafloor Assessment Survey for the Proposed Expansion of the
Massachusetts Bay Disposal Site was completed by the USACE in
anticipation of this project and is available on the USACE DAMOS
webpage at https://www.nae.usace.army.mil/Missions/Disposal-Area-Monitoring-System-DAMOS/.
(10) Potentiality for the development or recruitment of nuisance
species in the disposal site.
There are no known components of dredged material or consequences
of its disposal that would attract or result in the recruitment or
development of nuisance species at the expanded MBDS. Nuisance species
have not been detected in any survey of the area.
(11) Existence at or in close proximity to the site of any
significant natural or cultural features of historical importance.
There are two known shipwrecks within the boundaries of the
existing MBDS: a Coast Guard vessel and a 55-foot fishing boat. Both
were intentionally sunk in 1981 and are not considered to be
historically significant. Additional shipwrecks have been revealed in
the general area during subsequent surveys, although there are no
identified shipwrecks within the Potential Restoration Area. Disposal
operations have avoided and will continue to avoid any shipwrecks in
the project area by implementing a fifty-meter buffer around known
shipwrecks within which no disposal will occur.
III. Environmental Statutory Review
a. National Environmental Policy Act (NEPA)
Section 102 of the National Environmental Policy Act of 1969, as
amended (NEPA), 42 U.S.C. 4321 to 4370f, requires federal agencies to
prepare an Environmental Impact Statement (EIS) for major federal
actions significantly affecting the quality of the human environment.
When a federal agency evaluates an action that it plans to take and
finds that it will not significantly affect the environment, it may
issue an Environmental Assessment and a Finding of No Significant
Impact (i.e., an ``EA/FONSI'').
NEPA does not apply to EPA designations of ocean disposal sites
under the MPRSA because EPA's actions under the MPRSA are exempt from
the procedural requirements of NEPA through the functional equivalence
doctrine. Nevertheless, as a matter of policy, EPA undertakes a NEPA
review for certain of its regulatory actions, including the designation
of dredged material disposal sites under Section 102 of the MPRSA. The
EPA's ``Notice of Policy and Procedures for Voluntary Preparation of
NEPA Documents'' (Voluntary NEPA Policy), 63 FR 58045 (October 29,
1998), sets out both the policy and procedures the EPA uses when
preparing such environmental review documents.
The EPA's primary voluntary NEPA document addressing the temporary
expansion of the MBDS is the Final Environmental Assessment on the
Proposed Expansion of the Massachusetts Bay Ocean Dredged Material
Disposal Site and Finding of No Significant Impact (Final EA), prepared
by EPA in cooperation with USACE. Anyone desiring a copy of the Final
EA may obtain one using the methods provided above in the Docket
section. The Draft Environmental Assessment on the Expansion of the
Massachusetts Bay Ocean Dredged Material Disposal Site (ODMDS) (Draft
EA) was released for public review concurrently with the Proposed Rule.
The Final EA, which is part of the Docket for this action, provides the
environmental review for the temporary modification of the MBDS.
Information from the Final EA is used in the above discussion of the
ocean dumping criteria.
b. Magnuson-Stevens Fishery Conservation & Management Act (MSA)
EPA integrated the EFH assessment into the Draft EA, pursuant to
Section 305(b), 16 U.S.C. 1855(b)(2), of the Magnuson-Stevens Act, as
amended (MSA), 16 U.S.C. 1801-1891d, and submitted that assessment to
NMFS on September 28, 2017. NMFS responded via letter with a
recommendation to avoid disposal on the glacial knoll that is within
the boundaries of the Potential Restoration Area. EPA and USACE have
adopted this recommendation and will avoid the disposal of any dredged
material on this feature. This recommendation has also been
incorporated into the Final EA.
c. Coastal Zone Management Act (CZMA)
EPA determined that the modification of the MBDS is consistent to
the maximum extent practicable with the enforceable policies of the
Massachusetts coastal management program, and a letter was submitted to
the Massachusetts Office of Coastal Zone Management (MCZM) on September
28, 2017. MCZM submitted a letter of concurrence to EPA on November 30,
2017.
d. Endangered Species Act (ESA)
The Endangered Species Act, as amended (ESA), 16 U.S.C. 1531 to
1544, requires federal agencies to consult with NMFS and the U.S. Fish
and Wildlife Service (FWS) to ensure that any action authorized,
funded, or carried out by the federal agency is not likely to
jeopardize the continued existence of any endangered species or
threatened species or result in the destruction or adverse modification
of any critical habitat. The EPA incorporated an assessment of the
potential effects of temporarily modifying the MBDS on aquatic and
wildlife species, including any species listed under the ESA, into the
Draft EA, and EPA has submitted that assessment to NMFS and FWS. EPA
concluded that this action is not likely to adversely affect any
threatened or endangered species, nor would it adversely modify any
designated critical habitat. EPA submitted a letter to NMFS on October
30, 2017, that stated that the re-initiation of consultation was not
necessary for this action. NMFS submitted a letter of concurrence to
EPA on November 21, 2017. EPA sent a letter to FWS on September 22,
2017, and confirmed that no consultation was necessary.
e. National Historic Preservation Act (NHPA)
The National Historic Preservation Act, as amended (NHPA), 16
U.S.C. 470 to 470a-2, requires federal agencies to take into account
the effect of their actions on districts, sites, buildings, structures,
or objects, included in, or eligible for inclusion in, the National
Register of Historical Places. EPA submitted a letter to the
Massachusetts State Historic Preservation Office (SHPO) on September
28, 2017, outlining the plan to avoid the historic shipwrecks in the
area during disposal operations. The Massachusetts SHPO provided a
letter of concurrence with the avoidance plan to EPA on October 19,
2017.
IV. Statutory and Executive Order Reviews
This rulemaking proposes the modification of an ODMDS pursuant to
Section 102 of the MPRSA. This action complies with applicable
Executive Orders and statutory provisions as follows:
[[Page 24413]]
a. Executive Order 12866: Regulatory Planning and Review; Executive
Order 13563: Improving Regulation and Regulatory Review
This action is not a ``significant regulatory action'' under the
terms of Executive Order 12866 (58 FR 51735, October 3, 1993) and is,
therefore, not subject to review under Executive Orders 12866 and 13563
(76 FR 3821, January 21, 2011).
b. Paperwork Reduction Act
This action does not impose an information collection burden under
the provisions of the Paperwork Reduction Act, 44 U.S.C. 3501 et seq.
This temporary site modification does not require persons to obtain,
maintain, retain, report, or publicly disclose information to or for a
federal agency.
c. Regulatory Flexibility Act
The Regulatory Flexibility Act (RFA) generally requires federal
agencies to prepare a regulatory flexibility analysis of any rule
subject to notice and comment rulemaking requirements under the
Administrative Procedure Act or any other statute unless the agency
certifies that the rule will not have a significant economic impact on
a substantial number of small entities (businesses, organizations, or
jurisdictions). EPA has determined that this action will not have a
significant economic impact on small entities.
d. Unfunded Mandates Reform Act
This action contains no federal mandates under the provisions of
Title II of the Unfunded Mandates Reform Act (UMRA) of 1995, 2 U.S.C.
1531 to 1538, for state, local, or tribal governments or the private
sector. This action imposes no new enforceable duty on any state, local
or tribal governments or the private sector. Therefore, this action is
not subject to the requirements of sections 202 or 205 of the UMRA.
This action is also not subject to the requirements of section 203 of
the UMRA because it contains no regulatory requirements that might
significantly or uniquely affect small government entities. Those
entities are already subject to existing permitting requirements for
the disposal of dredged material in ocean waters.
e. Executive Order 13132: Federalism
This action does not have federalism implications. It does not have
substantial direct effects on the states, on the relationship between
the national government and the states, or on the distribution of power
and responsibilities among various levels of government, as specified
in Executive Order 13132. Thus, Executive Order 13132 does not apply to
this action. In the spirit of Executive Order 13132, and consistent
with EPA policy to promote communications between the EPA and state and
local governments, EPA has coordinated with, and specifically solicited
comments from, state and local officials with regard to this action.
f. Executive Order 13175: Consultation and Coordination With Indian
Tribal Governments
This action does not have tribal implications, as specified in
Executive Order 13175. The modification of the MBDS will not have a
direct effect on Indian tribes, on the relationship between the federal
government and Indian tribes, or on the distribution of power and
responsibilities between the federal government and Indian tribes.
Thus, Executive Order 13175 does not apply to this action.
g. Executive Order 13045: Protection of Children From Environmental
Health & Safety Risks
This action is not subject to Executive Order 13045 because it is
not economically significant as defined in Executive Order 12866 and
because the EPA does not believe the environmental health or safety
risks addressed by this action present a disproportionate risk to
children.
h. Executive Order 13211: Actions That Significantly Affect Energy
Supply, Distribution, or Use
This action is not subject to Executive Order 13211 (66 FR 28355)
because it is not a ``significant regulatory action'' as defined under
Executive Order 12866.
i. National Technology Transfer and Advancement Act
This rulemaking does not involve technical standards and,
therefore, the National Technology Transfer and Advancement Act does
not apply.
j. Executive Order 12898: Federal Actions To Address Environmental
Justice in Minority Populations and Low-Income Populations
Executive Order 12898 (59 FR 7629) establishes federal executive
policy on environmental justice. Its main provision directs federal
agencies, to the greatest extent practicable and permitted by law, to
make environmental justice part of their mission by identifying and
addressing, as appropriate, disproportionately high and adverse human
health or environmental effects of their programs, policies, and
activities on minority populations and low-income populations in the
United States. The EPA determined that this action will not have
disproportionately high and adverse human health or environmental
effects on minority or low-income populations. This action is expected
to be protective of human health because it will enable the wastes
already within the Potential Restoration Area to be isolated under a
protective layer of sediment. This should help prevent any accidental
recovery of barrels by fishermen and prevent contaminants from the
historic disposal from entering the food web. The EPA has assessed the
overall protectiveness of modifying the MBDS against the criteria
established pursuant to the MPRSA to ensure that any adverse impact to
the environment will be mitigated to the greatest extent practicable.
No adverse impacts are expected. The action is, instead, expected to
improve environmental conditions in Massachusetts Bay by enabling
contaminated material dumped at the IWS in the past to be covered with
suitable dredged material in order to isolate the former from the
environment.
k. Executive Order 13158: Marine Protected Areas
Executive Order 13158 (65 FR 34909, May 31, 2000) requires EPA to
``expeditiously propose new science-based regulations, as necessary, to
ensure appropriate levels of protection for the marine environment.''
EPA may take action to enhance or expand protection of existing marine
protected areas and to establish or recommend, as appropriate, new
marine protected areas. The purpose of the Executive Order is to
protect the significant natural and cultural resources with the marine
environment, which includes, ``those areas of coastal and ocean waters,
the Great Lakes and their connecting waters, and submerged lands
thereunder, over which the United States exercises jurisdiction,
consistent with international law.''
EPA anticipates that this action will afford additional protection
to the waters of Massachusetts Bay and organisms that inhabit them. By
covering the barrel field and surrounding seafloor sediment of the
historic IWS, potential contaminants should be prevented from entering
the water column or food web in Massachusetts Bay. This should provide,
if anything, greater protection for the natural resources of the SBNMS,
which is in the vicinity of the temporarily expanded MBDS.
[[Page 24414]]
l. Executive Order 13547: Stewardship of the Ocean, Our Coasts, and the
Great Lakes
Section 6(a)(i) of Executive Order 13547, (75 FR 43023, July 19,
2010) requires, among other things, EPA and certain other agencies `` .
. . to the fullest extent consistent with applicable law [to] . . .
take such action as necessary to implement the policy set forth in
section 2 of this order and the stewardship principles and national
priority objectives as set forth in the Final Recommendations and
subsequent guidance from the Council.'' The policies in section 2 of
Executive Order 13547 include, among other things, the following: `` .
. . it is the policy of the United States to: (i) Protect, maintain,
and restore the health and biological diversity of ocean, coastal, and
Great Lakes ecosystems and resources; [and] (ii) improve the resiliency
of ocean, coastal, and Great Lakes ecosystems, communities, and
economies. . . .'' As with Executive Order 13158 (Marine Protected
Areas), the overall purpose of the Executive Order is to promote
protection of ocean and coastal environmental resources.
EPA anticipates that this action will afford additional protection
to the waters of Massachusetts Bay and organisms that inhabit them. By
covering the barrel field and surrounding seafloor sediment of the
historic IWS, potential contaminants should be prevented from entering
the water column or food web in Massachusetts Bay.
m. Executive Order 13771 Reducing Regulation and Controlling Regulatory
Costs
This action would not be a ``significant regulatory action'' under
the terms of Executive Order 12866 (58 FR 51735, October 3, 1993) and
is, therefore, not subject to review under Executive Order 13771. See
OMB, ``Guidance Implementing Executive Order 13771, Titled ``Reducing
Regulation and Controlling Regulatory Costs'' (M-17-21) (April 5,
2017), p. 3 (``An `E.O. 13771 Regulatory Action' is: (i) A significant
regulatory action as defined in section 3(f) of E.O. 12866 that has
been finalized and that imposes total costs greater than zero. . .
.'').
n. Congressional Review Act
The Congressional Review Act, 5 U.S.C. 801 et seq., as added by the
Small Business Regulatory Enforcement Fairness Act of 1996, generally
provides that before a rule may take effect, the agency promulgating
the rule must submit a rule report, which includes a copy of the rule,
to each House of the Congress and to the Comptroller General of the
United States. EPA will submit a report containing this rule and other
required information to the U.S. Senate, the U.S. House of
Representatives, and the Comptroller General of the United States prior
to publication of the rule in the Federal Register. A ``major rule''
cannot take effect until 60 days after it is published in the Federal
Register. This action is not a major rule as defined by 5 U.S.C.
804(2). This rule will be effective 30 days after date of publication.
List of Subjects in 40 CFR Part 228
Environmental protection, Water pollution control.
Dated: May 15, 2018.
Alexandra Dapolito Dunn
Regional Administrator, EPA Region 1.
For the reasons stated in the preamble, title 40, Chapter I, of the
Code of Federal Regulations is to be amended as set forth below.
PART 228--CRITERIA FOR THE MANAGEMENT OF DISPOSAL SITES FOR OCEAN
DUMPING
0
1. The authority citation for part 228 continues to read as follows:
Authority: 33 U.S.C. 1412 and 1418.
0
2. Amend Sec. 228.15 by revising paragraphs (b)(2)(i), (ii), (iii),
and (vi) to read as follows:
Sec. 228.15 Dumping sites designated on a final basis.
* * * * *
(b) * * *
(2) * * *
(i) Location: Two overlapping circles: Center of existing MBDS:
42[deg]25.1' N, 70[deg]35.0' W, 1 nautical mile radius; Center of
temporary expansion: 42[deg]26.417' N, 70[deg]35.373' W, 0.75 nautical
mile radius (NAD 1983).
(ii) Size: 4.60 sq. nautical miles.
(iii) Depth: Range from 70 to 91 meters.
* * * * *
(vi) Restriction: Disposal shall be limited to dredged material
which meets the requirements of the MPRSA and its accompanying
regulations. Disposal-and-capping is prohibited at the MBDS until its
efficacy can be effectively demonstrated. The temporary expansion of
the MBDS shall be used solely for the disposal of suitable dredged
material generated during the Boston Harbor Deep Draft Navigation
Project using the berm-building method devised and tested by the U.S.
Army Corps of Engineers. The temporary expansion will automatically
close upon completion of the Boston Harbor Deep Draft Navigation
Project.
* * * * *
[FR Doc. 2018-11322 Filed 5-25-18; 8:45 am]
BILLING CODE 6560-50-P