Ocean Dumping; Site Designation, 55770-55774 [05-19063]
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55770
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[FR Doc. 05–19058 Filed 9–22–05; 8:45 am]
BILLING CODE 6560–50–S
ENVIRONMENTAL PROTECTION
AGENCY
40 CFR Part 228
[FRL–7973–8]
Ocean Dumping; Site Designation
Environmental Protection
Agency (EPA).
ACTION: Final rule.
AGENCY:
SUMMARY: EPA today designates a new
Ocean Dredged Material Disposal Site
(ODMDS) in the Atlantic Ocean offshore
Port Royal, South Carolina, as an EPAapproved ocean dumping site for the
disposal of suitable dredged material.
This action is necessary to provide an
acceptable ocean disposal site for
consideration as an option for dredged
material disposal projects in the greater
Port Royal, South Carolina, vicinity.
This site designation is for an indefinite
period of time, but the site is subject to
continuing monitoring to insure that
unacceptable adverse environmental
impacts do not occur.
DATES: This rule is effective on October
24, 2005.
ADDRESSES: The file supporting this
designation is available for public
inspection at the following location:
EPA Region 4, Sam Nunn Atlanta
Federal Center, 61 Forsyth Street, SW.,
Atlanta, Georgia 30303.
FOR FURTHER INFORMATION CONTACT: Gary
W. Collins, (404) 562–9395.
SUPPLEMENTARY INFORMATION:
A. Background
Section 102(c) of the Marine
Protection, Research, and Sanctuaries
Act (MPRSA) of 1972, as amended, 33
U.S.C. 1401 et seq., gives the
Administrator of EPA the authority to
designate sites where ocean disposal
may be permitted. On October 1, 1986,
the Administrator delegated the
authority to designate ocean disposal
sites to the Regional Administrator of
the Region in which the sites are
located. This designation is being made
pursuant to that authority.
The EPA Ocean Dumping Regulations
promulgated under MPRSA (40 CFR
Chapter I, Subchapter H, § 228.4) state
that ocean dumping sites will be
designated by promulgation in this part
228. This site designation is being
published as final rulemaking in
accordance with § 228.4(e) of the Ocean
Dumping Regulations, which permits
the designation of ocean disposal sites
for dredged material.
B. Regulated Entities
Entities potentially affected by this
action are persons, organizations, or
government bodies seeking to dispose of
dredged material into ocean waters
offshore Port Royal, South Carolina,
under the MPRSA and its implementing
regulations. This final rule is expected
to be primarily of relevance to parties
seeking permits from the U.S. Army
Corps of Engineers (COE) to transport
dredged material for the purpose of
disposal into ocean waters and to the
COE itself for its own dredged material
disposal projects. Potentially regulated
categories and entities that may seek to
use the proposed dredged material
disposal site may include:
Category
Examples of potentially regulated entities
Federal Government .................................................................................
U.S. Army Corps of Engineers Civil Works Projects, U.S. Marine
Corps, and Other Federal Agencies.
Port Authorities, Marinas and Harbors, Shipyards, and Marine Repair
Facilities, Berth Owners.
Governments owning and/or responsible for ports, harbors, and/or
berths, Government agencies requiring disposal of dredged material
associated with public works projects.
Industry and General Public .....................................................................
State, local and tribal governments ..........................................................
This table is not intended to be
exhaustive, but rather provides a guide
for readers regarding entities likely to be
affected by this action. To determine
whether your organization is affected by
this action, you should carefully
consider whether your organization is
subject to the requirement to obtain an
MPRSA permit in accordance with
Section 103 of the MPRSA and the
applicable regulations at 40 CFR Parts
220 and 225, and whether you wish to
use the site subject to today’s action.
EPA notes that nothing in this final rule
alters the jurisdiction or authority of
EPA or the types of entities regulated
under the MPRSA. Questions regarding
the applicability of this final rule to a
particular entity should be directed to
the contact person listed in the
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preceding FOR FURTHER INFORMATION
section.
CONTACT
C. EIS Development
Section 102(2)(C) of the National
Environmental Policy Act (NEPA) of
1969, as amended, 42 U.S.C. 4321 et
seq., requires that Federal agencies
prepare an Environmental Impact
Statement (EIS) on proposals for
legislation and other major federal
actions significantly affecting the
quality of the human environment. The
object of NEPA is to build into the
agency decision making process careful
consideration of all environmental
aspects of proposed actions. While
NEPA does not apply to EPA activities
of this type, EPA has voluntarily
committed to prepare NEPA documents
in connection with ocean disposal site
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designations. (See 63 FR 58045 [October
29, 1998], ‘‘Notice of Policy and
Procedures for Voluntary Preparation of
National Environmental Policy Act
(NEPA) Documents.’’)
EPA, in cooperation with the
Charleston District COE, has prepared a
Final EIS (FEIS) entitled ‘‘Final
Environmental Impact Statement for the
Port Royal Ocean Dredged Material
Disposal Site Designation.’’ On June 25,
2004, the Notice of Availability of the
FEIS for public review and comment
was published in the Federal Register
(69 FR 35597 [June 25, 2004]). Anyone
desiring a copy of the EIS may obtain
one from the address given above. The
public comment period on the FEIS
closed on July 26, 2004.
EPA received one comment letter on
the FEIS from the South Carolina
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Department of Health and
Environmental Control. This letter states
the Department’s findings that the
proposed ODMDS would be consistent
with the State’s Coastal Zone
Management Program.
Pursuant to an Office of Water policy
memorandum dated October 23, 1989,
EPA has evaluated the proposed site
designation for consistency with the
State of South Carolina’s (the State)
approved coastal management program.
EPA has determined that the
designation of the proposed site is
consistent to the maximum extent
practicable with the State coastal
management program, and submitted
this determination to the State for
review in accordance with EPA policy.
As stated above, the State agrees with
this determination.
The action discussed in the FEIS is
the permanent designation for
continuing use of an ODMDS near Port
Royal, South Carolina. The purpose of
this action is to provide an
environmentally acceptable option for
the continued ocean disposal of dredged
material. The need for the permanent
designation of a Port Royal ODMDS is
based on a demonstrated COE need for
ocean disposal of maintenance dredged
material from the Federal navigation
projects in the greater Port Royal Sound
area. However, every disposal activity
by the COE is evaluated on a case-bycase basis to determine the need for
ocean disposal for that particular case.
The need for ocean disposal for other
projects, and the suitability of the
material for ocean disposal, will be
determined on a case-by-case basis as
part of the COE’s process of issuing
permits for ocean disposal for private/
federal actions and a public review
process for its own actions.
For the Port Royal ODMDS, the COE
and EPA would evaluate all federal
dredged material disposal projects
pursuant to the EPA criteria given in the
Ocean Dumping Regulations (40 CFR
220–229) and the COE regulations (33
CFR 209.120 and 335–338). The COE
issues MPRSA permits to private
applicants for the transport of dredged
material intended for ocean disposal
after compliance with regulations has
been determined. EPA has the right to
disapprove any ocean disposal project
if, in its judgment, the MPRSA
environmental criteria [Section 102(a)]
or conditions of designation [Section
102(c)] are not met.
The FEIS discusses the need for this
site designation and examines ocean
and non-ocean disposal site alternatives
to the proposed action. Specific
alternatives considered were the two
interim ocean sites, sites off the
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continental shelf, land disposal sites,
and sites that might be used for shore
protection.
D. Site Designation
On February 24, 2005, EPA proposed
designation of an ODMDS for
continuing disposal of dredged material
from the Port Royal Sound area. The
period on this proposal closed on April
11, 2005. One e-mail letter of comment
was received opposing not only the
designation of this site, but all ocean
disposal in principle. In response to this
letter, EPA reiterates its support of
beneficial uses of dredged material,
when appropriate, and that this action
is in accordance with MPRSA and the
EPA Ocean Dumping Regulations
promulgated under MPRSA. In addition,
any project which proposes to dispose
of dredged material within this site
must evaluate the material to determine
its suitability for ocean disposal. Only
dredged material which has been shown
to meet the ocean dumping criteria
would be permitted to be placed in this
site.
The site is located approximately 7
nautical miles offshore Bay Point Island,
South Carolina. The proposed ODMDS
occupies an area of about 1.0 square
nautical miles (nmi2). Water depths
within the area average 36 feet (ft.). The
coordinates of the New Port Royal site
proposed for final designation are as
follows:
Latitude
32°05.00′
32°05.00′
32°04.00′
32°04.00′
Longitude
80°36.47′ W
80°35.30′ W
80°35.30′ W
80°36.47′ W
N
N
N
N
E. Regulatory Requirements
Pursuant to the Ocean Dumping
Regulations, 40 CFR 228.5, five general
criteria are used in the selection and
approval for continuing use of ocean
disposal sites. Sites are selected so as to
minimize interference with other
marine activities, to prevent any
temporary perturbations associated with
the disposal from causing impacts
outside the disposal site, and to permit
effective monitoring to detect any
adverse impacts at an early stage. Where
feasible, locations off the Continental
Shelf and other sites that have been
historically used are to be chosen. In
this case, locations off the Continental
Shelf are not feasible and no
environmental benefit would be
obtained by selecting such a site.
Historical use of this site has not
resulted in substantial adverse effects to
living resources of the ocean or to other
uses of the marine environment. If, at
any time, disposal operations at a site
cause unacceptable adverse impacts,
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further use of the site can be restricted
or terminated by EPA. The site conforms
to the five general criteria.
In addition to these general criteria in
§ 228.5, §228.6 lists the 11 specific
criteria used in evaluating a disposal
site to assure that the general criteria are
met. Application of these 11 criteria
constitutes an environmental
assessment of the impact of disposal at
the site. The characteristics of the site
are reviewed below in terms of these 11
criteria (the EIS may be consulted for
additional information).
1. Geographical Position, Depth of
Water, Bottom Topography, and
Distance From Coast (40 CFR
228.6(a)(1))
The boundary of the site is given
above. The northern boundary of the
site is located about 7 nmi offshore of
Bay Point Island, South Carolina. The
site is approximatelty 1.0 nmi2 in area.
The bottom topography is relatively flat
and featureless, with water depths
averaging 36 ft.
2. Location In Relation to Breeding,
Spawning, Nursery, Feeding, or Passage
Areas of Living Resources in Adult or
Juvenile Phases (40 CFR 228.6(a)(2))
Many of the area’s species spend their
adult lives in the offshore region, but are
estuary-dependent because their
juvenile stages use a low salinity
estuarine nursery region. Specific
migration routes are not known to occur
within the site. The site is not known to
include any major breeding or spawning
area. Due to the motility of finfish, it is
unlikely that disposal activities will
have any significant impact on any of
the species found in the area. In a letter
dated October 23, 2003, the Habitat
Conservation Division of National
Marine Fisheries Service concurred
with our assessment that this
designation would not have a
substantial individual or cumulative
adverse impact on essential fish habitat,
or fishery resources.
3. Location in Relation to Beaches and
Other Amenity Areas (40 CFR
228.6(a)(3))
The site is located approximately 7
nmi from the coast. Considering the
previous disposal activities of the
existing ODMDS (designated by the COE
under Section 103 authority), dredged
material disposal at the site is not
expected to have an effect on the
recreational uses of these beaches.
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4. Types and Quantities of Wastes
Proposed To Be Disposed of, and
Proposed Methods of Release, Including
Methods of Packing the Waste, If Any
(40 CFR 228(a)(4))
The types of materials to be disposed
of within this site are dredged materials
as described in type and quantity by
Section 2 of the FEIS. Between the years
1992 and 2003, approximately 200,000
cubic yards (annual average) have been
ocean disposed within this area,
typically once every two years. To date,
the material from the Federal navigation
project has been excluded from testing.
Future disposal, which would be by
hopper dredge or dump scow, should
not change significantly by either
volume or frequency. All disposals shall
be in accordance with the approved Site
Management and Monitoring Plan
(SMMP) developed for this site (FEIS,
Appendix B).
5. Feasibility of Surveillance and
Monitoring (40 CFR 228.6(a)(5))
Due to the relative proximity of the
site to shore and its depth, surveillance
will not be difficult. The SMMP for the
Port Royal ODMDS has been developed
and was included as an appendix in the
FEIS. This SMMP establishes a
sequence of monitoring surveys to be
undertaken to determine any impacts
resulting from disposal activities. The
SMMP may be reviewed and revised by
EPA. A copy of the SMMP may be
obtained at the address given above.
6. Dispersal, Horizontal Transport and
Vertical Mixing Characteristics of the
Area Including Prevailing Current
Direction and Velocity, If Any (40 CFR
228.6(a)(6))
A detailed current study, along with
fate modelling of dredged material, was
not deemed necessary because almost
all of the material historically placed in
the ocean has been sand. Therefore, a
site-specific current study was not
conducted within the site. Transport of
disposed material should not present
any adverse impacts. In summary,
littoral drift is reported to be
predominantly southwestward, while
nearshore surface currents are derived
primarily from wind stress, and are
subject to extreme variability.
7. Existence and Effects of Current and
Previous Discharges and Dumping in
the Area (Including Cumulative Effects)
(40 CFR 228.6(a)(7))
This site, as well as past interim sites
nearby, has been used to dispose of the
material from the Port Royal Sound area
since 1956. Subsequent monitoring of
these disposals and the long-term effects
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show that no adverse impacts have, or
are likely to occur to the area.
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 (40 CFR 228.6(a)(8))
The location of the ODMDS was
selected to avoid interference with
commercial shipping. It is not
anticipated that the site would interfere
with any recreational activity. In
addition, mineral extraction, fish and
shellfish culture, and desalination
activities do not occur in the area.
9. The Existing Water Quality and
Ecology of the Site as Determined by
Available Data or by Trend Assessment
or Baseline Surveys (40 CFR 228.6(a)(9))
Appropriate water quality and
ecological assessments have been
performed at the site. The most
abundant benthic invertebrates found
within the site were the annelid
Polygrodius sp., the bivalve Ervilia
concentrica, the polychaete Prionospio
cristata, annelids in the class
Oligochaeta, and the bivalve Crassinella
lunulata. These five taxa accounted for
more than 40 percent of total number of
individuals collected. More detailed
information concerning the water
quality and ecology at the ODMDS is
presented in the FEIS. A copy of the
FEIS may be obtained at any of the
addresses given above.
10. Potentiality for the Development or
Recruitment of Nuisance Species in the
Disposal Site (40 CFR 228.6(a)(10))
The disposal of dredged materials
should not attract or promote the
development of nuisance species. No
nuisance species have been reported to
occur at previously utilized disposal
sites in the vicinity.
11. Existence at or in Close Proximity to
the Site of Any Significant Natural or
Cultural Features of Historical
Importance (40 CFR 228.6(a)(11))
There are no known such natural or
cultural features of historical
importance. As stated in the FEIS, this
action has fully complied with both the
Archaeological and Historic
Preservation Act and the National
Historic Preservation Act, as amended.
F. Site Management
Site management of the Port Royal
ODMDS is the responsibility of EPA, in
cooperation with the COE. The COE
issues permits to private applicants for
ocean disposal; however, EPA/Region 4
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assumes overall responsibility for site
management.
The SMMP for the Port Royal ODMDS
was developed as a part of the process
of completing the EIS. This plan
provides procedures for both site
management and for the monitoring of
effects of disposal activities. This SMMP
is intended to be flexible and may be
reviewed and revised by the EPA.
G. Proposed Action
The EIS concludes that the site may
be appropriately designated for use. The
site is compatible with the 11 specific
and five general criteria used for site
evaluation.
The designation of the Port Royal site
as an EPA-approved ODMDS is being
published as final rulemaking. Overall
management of this site is the
responsibility of the Regional
Administrator of EPA/Region 4.
It should be emphasized that, if an
ODMDS is designated, such a site
designation does not constitute EPA’s
approval of actual disposal of material
at sea. Before ocean disposal of dredged
material at the site may commence, the
COE must evaluate a permit application
according to EPA’s Ocean Dumping
Criteria. EPA has the right to disapprove
the actual disposal, if it determines that
environmental concerns under MPRSA
have not been met.
The Port Royal ODMDS is not
restricted to disposal use by federal
projects; private applicants may also
dispose suitable dredged material at the
ODMDS once relevant regulations have
been satisfied. This site is restricted,
however, to suitable dredged material
from the greater Port Royal, South
Carolina, vicinity.
H. Regulatory Assessments
1. Executive Order 12866
Under Executive Order 12866, EPA
must determine whether the regulatory
action is ‘‘significant’’ and therefore
subject to OMB review and the
requirements of the Executive Order.
The Order defines ‘‘significant
regulatory action’’ as one that is likely
to result in a rule that may:
(a) Have an annual effect on the
economy of $100 million or more or
adversely affect in a material way the
economy, a sector of the economy,
productivity, competition, jobs, the
environment, public health or safety, or
State, local, or tribal governments or
communities;
(b) Create a serious inconsistency or
otherwise interfere with an action taken
or planned by another agency;
(c) Materially alter the budgetary
impact of entitlements, grants, user fees,
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or loan programs or the rights and
obligations of recipients thereof; or
(d) Raise novel legal or policy issues
arising out of legal mandates, the
President’s priorities, or the principles
set forth in the Executive Order.
EPA has determined that this action is
not a ‘‘significant regulatory action’’
under the terms of Executive Order
12866 and is therefore not subject to
OMB review.
2. Paperwork Reduction Act
This rule would not impose an
information collection burden under the
provisions of the Paperwork Reduction
Act of 1995 (44 U.S.C. 3501, et seq.)
because it would not require persons to
obtain, maintain, retain, report, or
publicly disclose information to or for a
Federal agency.
3. Regulatory Flexibility Act
Under the Regulatory Flexibility Act,
EPA is required to perform a Regulatory
Flexibility Analysis for all rules that
may have a significant impact on a
substantial number of small entities.
EPA has determined that this action will
not have a significant impact on small
entities since the designation will only
have the effect of providing an
environmentally acceptable disposal
option for dredged material on a
continued basis. Consequently, by
publication of this Rule, the Regional
Administrator certifies that this action
will not have a significant impact on a
substantial number of small entities and
therefore does not necessitate
preparation of a Regulatory Flexibility
Analysis.
4. Unfunded Mandates Reform Act
Title II of the Unfunded Mandates
Reform Act (UMRA), Public Law 104–4,
establishes requirements for Federal
agencies to assess the effects of their
regulatory actions on State, local, and
tribal governments and the private
sector. Under section 202 of the UMRA,
EPA generally must prepare a written
statement, including a cost-benefit
analysis, for proposed and final rules
with Federal Mandates that may result
in expenditures to State, local, and
tribal governments, in the aggregate, or
to the private sector, of $100 million or
more in any one year. Before
promulgating an EPA rule for which a
written statement is needed, section 205
of the UMRA generally requires EPA to
identify and consider a reasonable
number of regulatory alternatives and
adopt the least costly, most costeffective or least burdensome alternative
that achieves the objectives of the rule.
The provisions of section 205 do not
apply when they are inconsistent with
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applicable law. Moreover, section 205
allows EPA to adopt an alternative other
than the least costly, most cost-effective
or least burdensome alternative, if the
Administrator publishes with the final
rule an explanation of why that
alternative was not adopted. Before EPA
establishes any regulatory requirements
that may significantly or uniquely affect
small governments, including tribal
governments, it must have developed
under section 203 of the UMRA a small
government agency plan. The plan must
provide for notifying potentially
affected small governments to have
meaningful and timely input in the
development of EPA regulatory
proposals with significant Federal
intergovernmental mandates, and
informing, educating, and advising
small governments on compliance with
the regulatory requirements.
EPA has determined that this action
contains no Federal mandates (under
the regulatory provisions of Title II of
the UMRA) for State, local and tribal
governments or the private sector. It
imposes no new enforceable duty on
any State, local or tribal governments or
the private sector. Thus, the
requirements of section 202 and section
205 of the UMRA do not apply to this
proposed rule. Similarly, EPA has also
determined that this action contains no
regulatory requirements that might
significantly or uniquely affect small
government entities. Thus, the
requirements of section 203 of the
UMRA do not apply to this final rule.
5. Executive Order 13132
Executive Order 13132, entitled
‘‘Federalism’’ (64 FR 43255, August 10,
1999), requires EPA to develop an
accountable process to ensure
‘‘meaningful and timely input by State
and local officials in the development of
regulatory policies that have federalism
implications.’’ ‘‘Policies that have
federalism implications’’ is defined in
the Executive Order to include
regulations that 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 the
various levels of government.’’
This final rule does not have
federalism implications. It will 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 the various
levels of government, as specified in
Executive Order 13132. As described
elsewhere in this preamble, today’s
action would only have the effect of
providing a continual use of an ocean
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55773
disposal site pursuant to section 102(c)
of MPRSA. Thus, Executive Order
13132 does not apply to this final rule.
Although section 6 of Executive Order
13132 does not apply, EPA did consult
with State officials in developing this
action and no concerns were raised.
6. Executive Order 13175
Executive Order 13175, entitled
‘‘Consultation and Coordination with
Indian Tribal Governments’’ (65 FR
67249, November 9, 2000), requires EPA
to develop an accountable process to
ensure ‘‘meaningful and timely input by
tribal officials in the development of
regulatory policies that have tribal
implications.’’ This final rule does not
have tribal implications, as specified in
Executive Order 13175. As described
elsewhere in this preamble, today’s
action 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 final rule.
7. Executive Order 13045
Executive Order 13045, entitled
‘‘Protection of Children from
Environmental Health Risks and Safety
Risks’’ (62 FR 19885, April 23, 1997)
applies to any rule that: (a) Is
determined to be ‘‘economically
significant’’ as defined under Executive
Order 12866 and (b) 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 final 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 action 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 final rule is not subject to
Executive Order 13211, Actions
Concerning Regulations That
Significantly Affect Energy Supply,
Distribution, or Use (66 FR 28355 (May
22, 2001)) because it is not a significant
regulatory action under Executive Order
12866.
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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
NTTAA directs EPA to provide
Congress, through OMB, explanations
when the Agency decides not to use
available and applicable voluntary
consensus standards. This final rule
does not involve technical standards.
Therefore, EPA did not consider the use
of any voluntary consensus standards.
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).
Accordingly, the requirements of
Executive Order 12898 do not apply.
List of Subjects in 40 CFR Part 228
Environmental protection, Water
pollution control.
Dated: September 14, 2005.
J.I. Palmer, Jr.,
Regional Administrator for Region 4.
In consideration of the foregoing,
Subchapter H of Chapter I of Title 40 is
amended as follows:
I
PART 228—[AMENDED]
1. The authority citation for part 228
continues to read as follows:
I
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 final 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.
Authority: 33 U.S.C. 1412 and 1418.
2. Section 228.15 is amended by
adding (h)(23) to read as follows:
I
§ 228.15 Dumping sites designated on a
final basis.
VerDate Aug<31>2005
14:48 Sep 22, 2005
Jkt 205001
SUMMARY: The Environmental Protection
Agency (‘‘EPA’’ or the ‘‘Agency’’) New
England (Region 1) announces the
deletion of the Nutmeg Valley Road Site
(‘‘Site’’) from the National Priorities List
(‘‘NPL’’). The NPL constitutes appendix
B of 40 part 300 which is the National
Oil and Hazardous Substances Pollution
Contingency Plan (‘‘NCP’’), which EPA
promulgated pursuant to section 105 of
the Comprehensive Environmental
Response, Compensation and Liability
Act (‘‘CERCLA’’) of 1980, as amended.
EPA and the Connecticut Department of
Environmental Protection (‘‘CT DEP’’)
have determined that the Site poses no
significant threat to public health or the
environment and, therefore, no further
remedial measures pursuant to CERCLA
are appropriate.
EFFECTIVE DATE:
September 23, 2005.
FOR FURTHER INFORMATION CONTACT:
Karen Lumino, Remedial Project
Manager, at 617–918–1348, or,
lumino.karen@epa.gov.
ENVIRONMENTAL PROTECTION
AGENCY
The site to
be deleted from the NPL is:
Nutmeg Valley Road Site, Wolcott,
New Haven County, Connecticut.
A Notice of Intent to Delete for this
Site was published in the Federal
Register on August 5, 2005 (70 FR
45334). The closing date for comments
on the Notice of Intent to Delete was
September 6, 2005. No comments were
received therefore, EPA has not
prepared a Responsiveness Summary.
EPA identifies sites that appear to
present a significant risk to public
health, welfare, or the environment and
it maintains the NPL as the list of those
sites. Any site deleted from the NPL
remains eligible for fund-financed
remedial actions in the unlikely event
that conditions at the site warrant such
action. Section 300.425(e)(3) of the NCP
states that fund-financed actions may be
taken at sites deleted from the NPL.
Deletion of a site from the NPL does not
affect responsible party liability or
impede agency efforts to recover costs
associated with response efforts.
40 CFR Part 300
List of Subjects in 40 CFR Part 300
[FRL–7973–9]
Environmental protection, Air
pollution control, Chemicals, Hazardous
substances, Hazardous waste,
Intergovernmental relations, Penalties,
Reporting and recordkeeping
requirements, Superfund, Water
pollution control, Water supply.
*
*
*
*
*
(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′ 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.
*
*
*
*
*
[FR Doc. 05–19063 9–22–05; 8:45 am]
BILLING CODE 6560–50–P
11. The 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,
Notice of Deletion of the
Nutmeg Valley Road Site from the
National Priorities List.
ACTION:
National Oil and Hazardous
Substances Pollution Contingency
Plan; National Priorities List
AGENCY:
Environmental Protection
Agency.
PO 00000
Frm 00070
Fmt 4700
Sfmt 4700
SUPPLEMENTARY INFORMATION:
E:\FR\FM\23SER1.SGM
23SER1
Agencies
[Federal Register Volume 70, Number 184 (Friday, September 23, 2005)]
[Rules and Regulations]
[Pages 55770-55774]
From the Federal Register Online via the Government Printing Office [www.gpo.gov]
[FR Doc No: 05-19063]
-----------------------------------------------------------------------
ENVIRONMENTAL PROTECTION AGENCY
40 CFR Part 228
[FRL-7973-8]
Ocean Dumping; Site Designation
AGENCY: Environmental Protection Agency (EPA).
ACTION: Final rule.
-----------------------------------------------------------------------
SUMMARY: EPA today designates a new Ocean Dredged Material Disposal
Site (ODMDS) in the Atlantic Ocean offshore Port Royal, South Carolina,
as an EPA-approved ocean dumping site for the disposal of suitable
dredged material. This action is necessary to provide an acceptable
ocean disposal site for consideration as an option for dredged material
disposal projects in the greater Port Royal, South Carolina, vicinity.
This site designation is for an indefinite period of time, but the site
is subject to continuing monitoring to insure that unacceptable adverse
environmental impacts do not occur.
DATES: This rule is effective on October 24, 2005.
ADDRESSES: The file supporting this designation is available for public
inspection at the following location: EPA Region 4, Sam Nunn Atlanta
Federal Center, 61 Forsyth Street, SW., Atlanta, Georgia 30303.
FOR FURTHER INFORMATION CONTACT: Gary W. Collins, (404) 562-9395.
SUPPLEMENTARY INFORMATION:
A. Background
Section 102(c) of the Marine Protection, Research, and Sanctuaries
Act (MPRSA) of 1972, as amended, 33 U.S.C. 1401 et seq., gives the
Administrator of EPA the authority to designate sites where ocean
disposal may be permitted. On October 1, 1986, the Administrator
delegated the authority to designate ocean disposal sites to the
Regional Administrator of the Region in which the sites are located.
This designation is being made pursuant to that authority.
The EPA Ocean Dumping Regulations promulgated under MPRSA (40 CFR
Chapter I, Subchapter H, Sec. 228.4) state that ocean dumping sites
will be designated by promulgation in this part 228. This site
designation is being published as final rulemaking in accordance with
Sec. 228.4(e) of the Ocean Dumping Regulations, which permits the
designation of ocean disposal sites for dredged material.
B. Regulated Entities
Entities potentially affected by this action are persons,
organizations, or government bodies seeking to dispose of dredged
material into ocean waters offshore Port Royal, South Carolina, under
the MPRSA and its implementing regulations. This final rule is expected
to be primarily of relevance to parties seeking permits from the U.S.
Army Corps of Engineers (COE) to transport dredged material for the
purpose of disposal into ocean waters and to the COE itself for its own
dredged material disposal projects. Potentially regulated categories
and entities that may seek to use the proposed dredged material
disposal site may include:
------------------------------------------------------------------------
Examples of potentially
Category regulated entities
------------------------------------------------------------------------
Federal Government..................... U.S. Army Corps of Engineers
Civil Works Projects, U.S.
Marine Corps, and Other
Federal Agencies.
Industry and General Public............ Port Authorities, Marinas and
Harbors, Shipyards, and Marine
Repair Facilities, Berth
Owners.
State, local and tribal governments.... Governments owning and/or
responsible for ports,
harbors, and/or berths,
Government agencies requiring
disposal of dredged material
associated with public works
projects.
------------------------------------------------------------------------
This table is not intended to be exhaustive, but rather provides a
guide for readers regarding entities likely to be affected by this
action. To determine whether your organization is affected by this
action, you should carefully consider whether your organization is
subject to the requirement to obtain an MPRSA permit in accordance with
Section 103 of the MPRSA and the applicable regulations at 40 CFR Parts
220 and 225, and whether you wish to use the site subject to today's
action. EPA notes that nothing in this final rule alters the
jurisdiction or authority of EPA or the types of entities regulated
under the MPRSA. Questions regarding the applicability of this final
rule to a particular entity should be directed to the contact person
listed in the preceding FOR FURTHER INFORMATION CONTACT section.
C. EIS Development
Section 102(2)(C) of the National Environmental Policy Act (NEPA)
of 1969, as amended, 42 U.S.C. 4321 et seq., requires that Federal
agencies prepare an Environmental Impact Statement (EIS) on proposals
for legislation and other major federal actions significantly affecting
the quality of the human environment. The object of NEPA is to build
into the agency decision making process careful consideration of all
environmental aspects of proposed actions. While NEPA does not apply to
EPA activities of this type, EPA has voluntarily committed to prepare
NEPA documents in connection with ocean disposal site designations.
(See 63 FR 58045 [October 29, 1998], ``Notice of Policy and Procedures
for Voluntary Preparation of National Environmental Policy Act (NEPA)
Documents.'')
EPA, in cooperation with the Charleston District COE, has prepared
a Final EIS (FEIS) entitled ``Final Environmental Impact Statement for
the Port Royal Ocean Dredged Material Disposal Site Designation.'' On
June 25, 2004, the Notice of Availability of the FEIS for public review
and comment was published in the Federal Register (69 FR 35597 [June
25, 2004]). Anyone desiring a copy of the EIS may obtain one from the
address given above. The public comment period on the FEIS closed on
July 26, 2004.
EPA received one comment letter on the FEIS from the South Carolina
[[Page 55771]]
Department of Health and Environmental Control. This letter states the
Department's findings that the proposed ODMDS would be consistent with
the State's Coastal Zone Management Program.
Pursuant to an Office of Water policy memorandum dated October 23,
1989, EPA has evaluated the proposed site designation for consistency
with the State of South Carolina's (the State) approved coastal
management program. EPA has determined that the designation of the
proposed site is consistent to the maximum extent practicable with the
State coastal management program, and submitted this determination to
the State for review in accordance with EPA policy. As stated above,
the State agrees with this determination.
The action discussed in the FEIS is the permanent designation for
continuing use of an ODMDS near Port Royal, South Carolina. The purpose
of this action is to provide an environmentally acceptable option for
the continued ocean disposal of dredged material. The need for the
permanent designation of a Port Royal ODMDS is based on a demonstrated
COE need for ocean disposal of maintenance dredged material from the
Federal navigation projects in the greater Port Royal Sound area.
However, every disposal activity by the COE is evaluated on a case-by-
case basis to determine the need for ocean disposal for that particular
case. The need for ocean disposal for other projects, and the
suitability of the material for ocean disposal, will be determined on a
case-by-case basis as part of the COE's process of issuing permits for
ocean disposal for private/federal actions and a public review process
for its own actions.
For the Port Royal ODMDS, the COE and EPA would evaluate all
federal dredged material disposal projects pursuant to the EPA criteria
given in the Ocean Dumping Regulations (40 CFR 220-229) and the COE
regulations (33 CFR 209.120 and 335-338). The COE issues MPRSA permits
to private applicants for the transport of dredged material intended
for ocean disposal after compliance with regulations has been
determined. EPA has the right to disapprove any ocean disposal project
if, in its judgment, the MPRSA environmental criteria [Section 102(a)]
or conditions of designation [Section 102(c)] are not met.
The FEIS discusses the need for this site designation and examines
ocean and non-ocean disposal site alternatives to the proposed action.
Specific alternatives considered were the two interim ocean sites,
sites off the continental shelf, land disposal sites, and sites that
might be used for shore protection.
D. Site Designation
On February 24, 2005, EPA proposed designation of an ODMDS for
continuing disposal of dredged material from the Port Royal Sound area.
The period on this proposal closed on April 11, 2005. One e-mail letter
of comment was received opposing not only the designation of this site,
but all ocean disposal in principle. In response to this letter, EPA
reiterates its support of beneficial uses of dredged material, when
appropriate, and that this action is in accordance with MPRSA and the
EPA Ocean Dumping Regulations promulgated under MPRSA. In addition, any
project which proposes to dispose of dredged material within this site
must evaluate the material to determine its suitability for ocean
disposal. Only dredged material which has been shown to meet the ocean
dumping criteria would be permitted to be placed in this site.
The site is located approximately 7 nautical miles offshore Bay
Point Island, South Carolina. The proposed ODMDS occupies an area of
about 1.0 square nautical miles (nmi2). Water depths within
the area average 36 feet (ft.). The coordinates of the New Port Royal
site proposed for final designation are as follows:
Latitude Longitude
32[deg]05.00' N 80[deg]36.47' W
32[deg]05.00' N 80[deg]35.30' W
32[deg]04.00' N 80[deg]35.30' W
32[deg]04.00' N 80[deg]36.47' W
E. Regulatory Requirements
Pursuant to the Ocean Dumping Regulations, 40 CFR 228.5, five
general criteria are used in the selection and approval for continuing
use of ocean disposal sites. Sites are selected so as to minimize
interference with other marine activities, to prevent any temporary
perturbations associated with the disposal from causing impacts outside
the disposal site, and to permit effective monitoring to detect any
adverse impacts at an early stage. Where feasible, locations off the
Continental Shelf and other sites that have been historically used are
to be chosen. In this case, locations off the Continental Shelf are not
feasible and no environmental benefit would be obtained by selecting
such a site. Historical use of this site has not resulted in
substantial adverse effects to living resources of the ocean or to
other uses of the marine environment. If, at any time, disposal
operations at a site cause unacceptable adverse impacts, further use of
the site can be restricted or terminated by EPA. The site conforms to
the five general criteria.
In addition to these general criteria in Sec. 228.5, Sec. 228.6
lists the 11 specific criteria used in evaluating a disposal site to
assure that the general criteria are met. Application of these 11
criteria constitutes an environmental assessment of the impact of
disposal at the site. The characteristics of the site are reviewed
below in terms of these 11 criteria (the EIS may be consulted for
additional information).
1. Geographical Position, Depth of Water, Bottom Topography, and
Distance From Coast (40 CFR 228.6(a)(1))
The boundary of the site is given above. The northern boundary of
the site is located about 7 nmi offshore of Bay Point Island, South
Carolina. The site is approximatelty 1.0 nmi\2\ in area. The bottom
topography is relatively flat and featureless, with water depths
averaging 36 ft.
2. Location In Relation to Breeding, Spawning, Nursery, Feeding, or
Passage Areas of Living Resources in Adult or Juvenile Phases (40 CFR
228.6(a)(2))
Many of the area's species spend their adult lives in the offshore
region, but are estuary-dependent because their juvenile stages use a
low salinity estuarine nursery region. Specific migration routes are
not known to occur within the site. The site is not known to include
any major breeding or spawning area. Due to the motility of finfish, it
is unlikely that disposal activities will have any significant impact
on any of the species found in the area. In a letter dated October 23,
2003, the Habitat Conservation Division of National Marine Fisheries
Service concurred with our assessment that this designation would not
have a substantial individual or cumulative adverse impact on essential
fish habitat, or fishery resources.
3. Location in Relation to Beaches and Other Amenity Areas (40 CFR
228.6(a)(3))
The site is located approximately 7 nmi from the coast. Considering
the previous disposal activities of the existing ODMDS (designated by
the COE under Section 103 authority), dredged material disposal at the
site is not expected to have an effect on the recreational uses of
these beaches.
[[Page 55772]]
4. Types and Quantities of Wastes Proposed To Be Disposed of, and
Proposed Methods of Release, Including Methods of Packing the Waste, If
Any (40 CFR 228(a)(4))
The types of materials to be disposed of within this site are
dredged materials as described in type and quantity by Section 2 of the
FEIS. Between the years 1992 and 2003, approximately 200,000 cubic
yards (annual average) have been ocean disposed within this area,
typically once every two years. To date, the material from the Federal
navigation project has been excluded from testing. Future disposal,
which would be by hopper dredge or dump scow, should not change
significantly by either volume or frequency. All disposals shall be in
accordance with the approved Site Management and Monitoring Plan (SMMP)
developed for this site (FEIS, Appendix B).
5. Feasibility of Surveillance and Monitoring (40 CFR 228.6(a)(5))
Due to the relative proximity of the site to shore and its depth,
surveillance will not be difficult. The SMMP for the Port Royal ODMDS
has been developed and was included as an appendix in the FEIS. This
SMMP establishes a sequence of monitoring surveys to be undertaken to
determine any impacts resulting from disposal activities. The SMMP may
be reviewed and revised by EPA. A copy of the SMMP may be obtained at
the address given above.
6. Dispersal, Horizontal Transport and Vertical Mixing Characteristics
of the Area Including Prevailing Current Direction and Velocity, If Any
(40 CFR 228.6(a)(6))
A detailed current study, along with fate modelling of dredged
material, was not deemed necessary because almost all of the material
historically placed in the ocean has been sand. Therefore, a site-
specific current study was not conducted within the site. Transport of
disposed material should not present any adverse impacts. In summary,
littoral drift is reported to be predominantly southwestward, while
nearshore surface currents are derived primarily from wind stress, and
are subject to extreme variability.
7. Existence and Effects of Current and Previous Discharges and Dumping
in the Area (Including Cumulative Effects) (40 CFR 228.6(a)(7))
This site, as well as past interim sites nearby, has been used to
dispose of the material from the Port Royal Sound area since 1956.
Subsequent monitoring of these disposals and the long-term effects show
that no adverse impacts have, or are likely to occur to the area.
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 (40 CFR 228.6(a)(8))
The location of the ODMDS was selected to avoid interference with
commercial shipping. It is not anticipated that the site would
interfere with any recreational activity. In addition, mineral
extraction, fish and shellfish culture, and desalination activities do
not occur in the area.
9. The Existing Water Quality and Ecology of the Site as Determined by
Available Data or by Trend Assessment or Baseline Surveys (40 CFR
228.6(a)(9))
Appropriate water quality and ecological assessments have been
performed at the site. The most abundant benthic invertebrates found
within the site were the annelid Polygrodius sp., the bivalve Ervilia
concentrica, the polychaete Prionospio cristata, annelids in the class
Oligochaeta, and the bivalve Crassinella lunulata. These five taxa
accounted for more than 40 percent of total number of individuals
collected. More detailed information concerning the water quality and
ecology at the ODMDS is presented in the FEIS. A copy of the FEIS may
be obtained at any of the addresses given above.
10. Potentiality for the Development or Recruitment of Nuisance Species
in the Disposal Site (40 CFR 228.6(a)(10))
The disposal of dredged materials should not attract or promote the
development of nuisance species. No nuisance species have been reported
to occur at previously utilized disposal sites in the vicinity.
11. Existence at or in Close Proximity to the Site of Any Significant
Natural or Cultural Features of Historical Importance (40 CFR
228.6(a)(11))
There are no known such natural or cultural features of historical
importance. As stated in the FEIS, this action has fully complied with
both the Archaeological and Historic Preservation Act and the National
Historic Preservation Act, as amended.
F. Site Management
Site management of the Port Royal ODMDS is the responsibility of
EPA, in cooperation with the COE. The COE issues permits to private
applicants for ocean disposal; however, EPA/Region 4 assumes overall
responsibility for site management.
The SMMP for the Port Royal ODMDS was developed as a part of the
process of completing the EIS. This plan provides procedures for both
site management and for the monitoring of effects of disposal
activities. This SMMP is intended to be flexible and may be reviewed
and revised by the EPA.
G. Proposed Action
The EIS concludes that the site may be appropriately designated for
use. The site is compatible with the 11 specific and five general
criteria used for site evaluation.
The designation of the Port Royal site as an EPA-approved ODMDS is
being published as final rulemaking. Overall management of this site is
the responsibility of the Regional Administrator of EPA/Region 4.
It should be emphasized that, if an ODMDS is designated, such a
site designation does not constitute EPA's approval of actual disposal
of material at sea. Before ocean disposal of dredged material at the
site may commence, the COE must evaluate a permit application according
to EPA's Ocean Dumping Criteria. EPA has the right to disapprove the
actual disposal, if it determines that environmental concerns under
MPRSA have not been met.
The Port Royal ODMDS is not restricted to disposal use by federal
projects; private applicants may also dispose suitable dredged material
at the ODMDS once relevant regulations have been satisfied. This site
is restricted, however, to suitable dredged material from the greater
Port Royal, South Carolina, vicinity.
H. Regulatory Assessments
1. Executive Order 12866
Under Executive Order 12866, EPA must determine whether the
regulatory action is ``significant'' and therefore subject to OMB
review and the requirements of the Executive Order. The Order defines
``significant regulatory action'' as one that is likely to result in a
rule that may:
(a) Have an annual effect on the economy of $100 million or more or
adversely affect in a material way the economy, a sector of the
economy, productivity, competition, jobs, the environment, public
health or safety, or State, local, or tribal governments or
communities;
(b) Create a serious inconsistency or otherwise interfere with an
action taken or planned by another agency;
(c) Materially alter the budgetary impact of entitlements, grants,
user fees,
[[Page 55773]]
or loan programs or the rights and obligations of recipients thereof;
or
(d) Raise novel legal or policy issues arising out of legal
mandates, the President's priorities, or the principles set forth in
the Executive Order.
EPA has determined that this action is not a ``significant
regulatory action'' under the terms of Executive Order 12866 and is
therefore not subject to OMB review.
2. Paperwork Reduction Act
This rule would not impose an information collection burden under
the provisions of the Paperwork Reduction Act of 1995 (44 U.S.C. 3501,
et seq.) because it would not require persons to obtain, maintain,
retain, report, or publicly disclose information to or for a Federal
agency.
3. Regulatory Flexibility Act
Under the Regulatory Flexibility Act, EPA is required to perform a
Regulatory Flexibility Analysis for all rules that may have a
significant impact on a substantial number of small entities. EPA has
determined that this action will not have a significant impact on small
entities since the designation will only have the effect of providing
an environmentally acceptable disposal option for dredged material on a
continued basis. Consequently, by publication of this Rule, the
Regional Administrator certifies that this action will not have a
significant impact on a substantial number of small entities and
therefore does not necessitate preparation of a Regulatory Flexibility
Analysis.
4. Unfunded Mandates Reform Act
Title II of the Unfunded Mandates Reform Act (UMRA), Public Law
104-4, establishes requirements for Federal agencies to assess the
effects of their regulatory actions on State, local, and tribal
governments and the private sector. Under section 202 of the UMRA, EPA
generally must prepare a written statement, including a cost-benefit
analysis, for proposed and final rules with Federal Mandates that may
result in expenditures to State, local, and tribal governments, in the
aggregate, or to the private sector, of $100 million or more in any one
year. Before promulgating an EPA rule for which a written statement is
needed, section 205 of the UMRA generally requires EPA to identify and
consider a reasonable number of regulatory alternatives and adopt the
least costly, most cost-effective or least burdensome alternative that
achieves the objectives of the rule. The provisions of section 205 do
not apply when they are inconsistent with applicable law. Moreover,
section 205 allows EPA to adopt an alternative other than the least
costly, most cost-effective or least burdensome alternative, if the
Administrator publishes with the final rule an explanation of why that
alternative was not adopted. Before EPA establishes any regulatory
requirements that may significantly or uniquely affect small
governments, including tribal governments, it must have developed under
section 203 of the UMRA a small government agency plan. The plan must
provide for notifying potentially affected small governments to have
meaningful and timely input in the development of EPA regulatory
proposals with significant Federal intergovernmental mandates, and
informing, educating, and advising small governments on compliance with
the regulatory requirements.
EPA has determined that this action contains no Federal mandates
(under the regulatory provisions of Title II of the UMRA) for State,
local and tribal governments or the private sector. It imposes no new
enforceable duty on any State, local or tribal governments or the
private sector. Thus, the requirements of section 202 and section 205
of the UMRA do not apply to this proposed rule. Similarly, EPA has also
determined that this action contains no regulatory requirements that
might significantly or uniquely affect small government entities. Thus,
the requirements of section 203 of the UMRA do not apply to this final
rule.
5. Executive Order 13132
Executive Order 13132, entitled ``Federalism'' (64 FR 43255, August
10, 1999), requires EPA to develop an accountable process to ensure
``meaningful and timely input by State and local officials in the
development of regulatory policies that have federalism implications.''
``Policies that have federalism implications'' is defined in the
Executive Order to include regulations that 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 the various levels of government.''
This final rule does not have federalism implications. It will 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 the various levels of government,
as specified in Executive Order 13132. As described elsewhere in this
preamble, today's action would only have the effect of providing a
continual use of an ocean disposal site pursuant to section 102(c) of
MPRSA. Thus, Executive Order 13132 does not apply to this final rule.
Although section 6 of Executive Order 13132 does not apply, EPA did
consult with State officials in developing this action and no concerns
were raised.
6. Executive Order 13175
Executive Order 13175, entitled ``Consultation and Coordination
with Indian Tribal Governments'' (65 FR 67249, November 9, 2000),
requires EPA to develop an accountable process to ensure ``meaningful
and timely input by tribal officials in the development of regulatory
policies that have tribal implications.'' This final rule does not have
tribal implications, as specified in Executive Order 13175. As
described elsewhere in this preamble, today's action 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 final rule.
7. Executive Order 13045
Executive Order 13045, entitled ``Protection of Children from
Environmental Health Risks and Safety Risks'' (62 FR 19885, April 23,
1997) applies to any rule that: (a) Is determined to be ``economically
significant'' as defined under Executive Order 12866 and (b) 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 final 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 action 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 final rule is not subject to Executive Order 13211, Actions
Concerning Regulations That Significantly Affect Energy Supply,
Distribution, or Use (66 FR 28355 (May 22, 2001)) because it is not a
significant regulatory action under Executive Order 12866.
[[Page 55774]]
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 NTTAA directs EPA to provide
Congress, through OMB, explanations when the Agency decides not to use
available and applicable voluntary consensus standards. This final 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 final 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.
11. The 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).
Accordingly, the requirements of Executive Order 12898 do not
apply.
List of Subjects in 40 CFR Part 228
Environmental protection, Water pollution control.
Dated: September 14, 2005.
J.I. Palmer, Jr.,
Regional Administrator for Region 4.
0
In consideration of the foregoing, Subchapter H of Chapter I of Title
40 is amended as follows:
PART 228--[AMENDED]
0
1. The authority citation for part 228 continues to read as follows:
Authority: 33 U.S.C. 1412 and 1418.
0
2. Section 228.15 is amended by adding (h)(23) to read as follows:
Sec. 228.15 Dumping sites designated on a final basis.
* * * * *
(h) * * *
(23) Port Royal, SC; Ocean Dredged Material Disposal Site.
(i) Location (NAD83): 32[deg]05.00' N., 80[deg]36.47' W.;
32[deg]05.00' N., 80[deg]35.30' W.; 32[deg]04.00' N., 80[deg]35.30' W.;
32[deg]04.00' N., 80[deg]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.
* * * * *
[FR Doc. 05-19063 9-22-05; 8:45 am]
BILLING CODE 6560-50-P