Ocean Dumping; De-Designation of Ocean Dredged Material Disposal Site and Designation of New Site Near Coos Bay, OR, 27396-27405 [06-4286]
Download as PDF
27396
*
*
Federal Register / Vol. 71, No. 91 / Thursday, May 11, 2006 / Rules and Regulations
*
*
*
[FR Doc. 06–4395 Filed 5–10–06; 8:45 am]
BILLING CODE 6560–50–P
ENVIRONMENTAL PROTECTION
AGENCY
40 CFR Part 228
[FRL–8167–7]
Ocean Dumping; De-Designation of
Ocean Dredged Material Disposal Site
and Designation of New Site Near
Coos Bay, OR
Environmental Protection
Agency (EPA).
ACTION: Final rule.
AGENCY:
SUMMARY: EPA is finalizing its proposal
to de-designate an existing ocean
dredged material disposal site and
designate a new ocean dredged material
disposal site located offshore of Coos
Bay, Oregon. EPA’s proposed rule was
published March 31, 2000. The new site
is needed for long-term use by
authorized Coos Bay navigation projects
and may be available for use by persons
meeting the criteria for ocean disposal
of dredged material. The de-designation
of the existing site allows for its
incorporation into the newly designated
site. This will allow EPA to manage the
entire new site to avoid adverse
mounding conditions and will ensure
site capacity is sufficient for total
volumes of dredged material. The newly
designated site is necessary for current
and future dredged material ocean
disposal needs and will be subject to
ongoing monitoring and management to
ensure continued protection of the
marine environment so as to mitigate
adverse impacts on the environment to
the greatest extent practicable.
DATES: This final rule will be effective
on June 12, 2006.
ADDRESSES: EPA has established a
docket for this final action under Docket
ID No. EPA–R10–OW–2006–0409. All
documents in the docket are listed on
the www.regulations.gov Web site. The
documents are also available for
inspection at the Region 10 Library,
10th Floor, 1200 Sixth Avenue, Seattle,
Washington 98101. For access to the
documents at the Region 10 Library,
contact the Region 10 Library Reference
Desk at (206) 553–1289, between 9 a.m.
to 11:30 a.m. and 1 p.m. to 4 p.m.,
Monday through Friday, excluding legal
holidays, for an appointment or contact
John Malek, U.S. EPA, Region 10, 1200
Sixth Avenue, Mail Stop ETPA–083, email: malek.john@epa.gov, phone
number (206) 553–1286.
John
Malek, Ocean Dumping Coordinator,
U.S. Environmental Protection Agency,
Region 10 (ETPA–083), 1200 Sixth
Avenue, Seattle, WA 98101–1128,
telephone (206) 553–1286, e-mail:
malek.john@epa.gov.
FOR FURTHER INFORMATION CONTACT:
SUPPLEMENTARY INFORMATION:
1. Potentially Affected Persons
Persons potentially affected by this
action include those who seek or might
seek permits or approval by EPA to
dispose of dredged material into ocean
waters pursuant to the Marine
Protection, Research, and Sanctuaries
Act, as amended, 33 U.S.C. 1401 to
1414, (‘‘MPRSA’’). EPA’s action would
be relevant to persons, including
organizations and government bodies
seeking to dispose of dredged material
in ocean waters offshore of Coos Bay,
Oregon. Currently, the U.S. Army Corps
of Engineers (Corps) and other persons
with permits to use designated sites at
Coos Bay would be most impacted by
this final action. Potentially affected
categories and persons include:
Category
Examples of potentially regulated persons
Federal Government ...........................................
Industry and General Public ...............................
State, local and tribal governments ....................
U.S. Army Corps of Engineers Civil Works Projects, 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.
This table is not intended to be
exhaustive, but rather provides a guide
for readers regarding persons likely to
be affected by this action. For any
questions regarding the applicability of
this action to a particular person, please
refer to the section of this action titled
FOR FURTHER INFORMATION CONTACT.
2. Background
cchase on PROD1PC60 with RULES
a. History of Disposal Site Designations
Off of Coos Bay, OR
Pursuant to the MPRSA, the
Administrator of EPA, as delegated to
the Regional Administrator, designated
three disposal sites (Site E, original Site
F and Site H) off of Coos Bay, Oregon
in 1986. The original Site F began to
experience mounding that rendered it
unable to accept the total volume of
dredged material generated on an
annual basis. In 1989, with EPA
approval, the size of the original Site F
was roughly doubled by the Corps
exercising its Section 103 authority to
select disposal sites under the MPRSA.
In 1995, EPA approved a second Corps
VerDate Aug<31>2005
16:19 May 10, 2006
Jkt 208001
expansion of the original Site F. On
March 31, 2000, EPA published in the
Federal Register its proposal to dedesignate the original Site F and
designate a new Site F that consisted of
the 103 configured Site F and the
original Site F (65 FR 17240). A fortyfive day public comment period, which
closed on May 14, 2000, was provided.
EPA did not receive comments from the
public on the proposed rule. The
coordinates of the proposed Site F
(North American Datum 1983; NAD 83)
were:
43°22′58″ N, 124°19′32″ W
43°21′50″ N, 124°20′29″ W
43°22′52″ N, 124°23′28″ W
43°23′59″ N, 124°22′31″ W
The proposed site was rectangular with
an east-west side length dimension of
14,500 feet and a north-south side
length dimension of 8,000 feet. Figure 1
is a diagram of the site EPA proposed
in 2000.
Subsequent to EPA’s proposed
designation, the North Jetty at Coos Bay
failed in December 2002, due in part to
PO 00000
Frm 00012
Fmt 4700
Sfmt 4700
undermining. The Corps then examined
the potential for augmenting transport of
disposed material into the eddy created
by the North Jetty itself. With EPA
concurrence, the Corps began making
selected disposals in the southeastern
corner of the 103 Site F nearest the jetty.
Monitoring indicated that some material
was captured by the eddy and
augmented the substrate that the jetty
rests upon. This experience and the
lessons learned during the designations
of ocean dredged material disposal sites
near the Mouth of the Columbia River
in 2005, as well as increased public
awareness of, and attention to, coastal
erosion processes and opportunities to
manage dredged material more
beneficially led EPA to review its
proposed site designation near Coos
Bay. The result of this review is a minor
change to the configuration of new Site
F toward the North Jetty at the north
side of the mouth of Coos Bay. This
reconfiguration could potentially benefit
the stabilization of the North Jetty and
keep material in the littoral zone. This
E:\FR\FM\11MYR1.SGM
11MYR1
Federal Register / Vol. 71, No. 91 / Thursday, May 11, 2006 / Rules and Regulations
reconfiguration is expected to allow
dredged material disposed in shallower
portions of the new Site F to naturally
disperse into the littoral zone without
creation of mounding conditions that
would contribute to adverse impacts to
navigation, including adverse wave
conditions.
cchase on PROD1PC60 with RULES
b. Location and Configuration of New
Site F
Figure 2 is a diagram of the new Site
F as EPA is finalizing the site in today’s
rule. It also shows the other designated
sites (E and H), the de-designated Site
F, the 103 configured Site F and the
proposed Site F. The shoremost side of
the site has been extended
approximately 600 feet as compared to
the site when proposed and the
southeastern corner has been located
closer to the North Jetty at the mouth of
Coos Bay. This has resulted in an
VerDate Aug<31>2005
16:19 May 10, 2006
Jkt 208001
overall increase to the site footprint of
399.8 acres bringing the total area of
new Site F to 3,075.2 acres. This
configuration will allow EPA to ensure
that disposal of dredged material into
the site will be managed to retain more
of the material in the active littoral drift
area to augment shoreline building
processes. The relocation of the corner
of the site closer to the jetty will allow
dredged material to be more effectively
placed to continue augmentation toward
the nearshore and toward the North
Jetty at the mouth of Coos Bay. This
change, while minor, expands sediment
management opportunities that are
beneficial to the coastal environment in
Coos Bay. The coordinates for the new
Site F near Coos Bay (NAD 83) as
finalized today are:
43°22′54.8887″ N, 124°19′28.9905″ W
43°21′32.8735″ N, 124°20′37.7373″ W
PO 00000
Frm 00013
Fmt 4700
Sfmt 4700
27397
43°22′51.4004″ N, 124°23′32.4318″ W
43°23′58.4014″ N, 124°22′35.4308″ W
The new Site F is expected to
accommodate the approximately 1.38
million cubic yards (mcy) of material
dredged annually from the Coos Bay
estuary by the Corps to maintain the
existing Federal navigation channel.
The nearshore boundary of the new site
is within two thousand feet of the
shoreline. Sediments disposed near this
boundary are considered to be in the
active transport zone and are expected
to disperse rapidly both onshore and
alongshore. Limited onshore transport is
expected because of the nature of
prevailing currents and wave transport
in the vicinity. Predicted material
transport at the new site is southward in
the summer months and northward
during the remainder of the year.
BILLING CODE 6560–5–P
E:\FR\FM\11MYR1.SGM
11MYR1
VerDate Aug<31>2005
Federal Register / Vol. 71, No. 91 / Thursday, May 11, 2006 / Rules and Regulations
16:19 May 10, 2006
Jkt 208001
PO 00000
Frm 00014
Fmt 4700
Sfmt 4725
E:\FR\FM\11MYR1.SGM
11MYR1
ER11MY06.004
cchase on PROD1PC60 with RULES
27398
cchase on PROD1PC60 with RULES
BILLING CODE 6560–50–C
c. Management and Monitoring of New
Site F
The newly designated Site F will
receive sediments dredged by the Corps
to maintain the federally authorized
navigation project at Coos Bay, Oregon
VerDate Aug<31>2005
16:19 May 10, 2006
Jkt 208001
and will be available to current
permittees and for use by others after
obtaining the appropriate permits and
approvals. Existing permits issued
pursuant to subchapter H of Title 40 of
the CFR will not need to be modified to
use new Site F. The new Site F is
designated with restrictions with which
PO 00000
Frm 00015
Fmt 4700
Sfmt 4700
27399
all persons must comply. All persons
using the site are required to follow the
final Site Management and Monitoring
Plan (SMMP) which is effective as of the
effective date of this action. The SMMP
generally addresses managing new Site
F to minimize and avoid mounding and
to ensure that dredged materials
E:\FR\FM\11MYR1.SGM
11MYR1
ER11MY06.005
Federal Register / Vol. 71, No. 91 / Thursday, May 11, 2006 / Rules and Regulations
27400
Federal Register / Vol. 71, No. 91 / Thursday, May 11, 2006 / Rules and Regulations
disposed at the site are suitable for
ocean disposal. The SMMP includes
management and monitoring
requirements for all of the designated
sites near Coos Bay and addresses the
timing of disposal into new Site F to
minimize interference with commercial
crabbing in the nearshore zone. Among
other things, the SMMP sets out
monitoring and management
requirements to ensure that dredged
material disposed at the site is suitable
for disposal and will not lead to
unacceptable impacts to human health
or the environment during the dredging
process, during transportation to the
designated sites, during disposal or once
disposed or at the disposal sites.
cchase on PROD1PC60 with RULES
d. MPRSA
EPA finds that today’s final action
satisfies the site designation criteria of
the MPRSA and the regulatory criteria
of 40 CFR part 228. The assessment of
the statutory criteria and general and
specific regulatory criteria presented in
the proposed rule has been examined in
response to the slight reconfiguration of
the new Site F. Moving the corner of the
new Site F to the southeast and closer
to the North Jetty based on EPA’s
increased understanding of coastal
erosion issues will allow EPA to manage
disposal at the new Site to retain
material in the active littoral zone to
augment shoreline building processes.
This meets the statutory and regulatory
criteria to use an appropriate location
based on considerations affecting the
public interest and to locate the site to
minimize interference with other
activities in the marine environment.
New data collected since the proposed
rule has been included in the discussion
of the general and specific site
designation criteria.
General Criteria (40 CFR 228.5)
1. Sites must be selected to minimize
interference with other activities in the
marine environment, particularly
avoiding areas of existing fisheries or
shellfisheries, and regions of heavy
commercial or recreational navigation
(40 CFR 228.5(a)).
EPA’s assessment of information
available at the time of the proposed
rule demonstrated that new Site F as
proposed would cause only minimal
interference with fisheries and
shellfisheries and with navigation
notwithstanding the location of the site
in the Coos Bay navigation channel.
This assessment has not changed with
the minor reconfiguration of the site
toward the North Jetty. Most of new Site
F has been used over the past decade for
dredged material disposal pursuant to
section 103 authority exercised by the
VerDate Aug<31>2005
16:19 May 10, 2006
Jkt 208001
Corps with EPA concurrence and
mariners in this area are accustomed to
the site use. In addition, based on a
conservation recommendation from the
National Marine Fisheries Service
(NMFS) resulting from an EPA
consultation on essential fish habitat,
EPA will impose use restrictions at the
site to minimize the use of the site
before June 1 of any year to essential
work and will encourage staggering of
disposal events when juvenile coho and
Chinook salmon are holding in
nearshore habitats.
2. Sites must be situated such that
temporary perturbations to water quality
or other environmental conditions
during initial mixing caused by disposal
operations would be reduced to normal
ambient levels or undetectable
contaminant concentrations or effects
before reaching any beach, shoreline,
marine sanctuary, or known
geographically limited fishery or
shellfishery (40 CFR 228.5(b)).
EPA’s analysis at the time of the
proposed rule concluded that the new
Site F would satisfy this criterion. EPA’s
understanding of the nearshore
processes near the North Jetty indicates
that this criterion will continue to be
met with the reconfiguration of new Site
F as finalized today. Although EPA
expects some material disposed at new
Site F to reach the base of the North
Jetty, normal ambient levels and
undetectable contaminant
concentrations or effects would be
expected before any material reached
any beach, shoreline, marine sanctuary
or known geographically limited fishery
or shellfishery because of the existing
high currents and wave energy.
3. If site designation studies show that
any interim disposal sites do not meet
the site selection criteria, use of such
sites shall be terminated as soon as any
alternate site can be designated (40 CFR
228.5(c)).
There are no interim disposal sites
near Coos Bay as defined under the
Ocean Dumping regulations. This
criterion is not applicable to today’s
action de-designating existing Site F and
designating new Site F.
4. The sizes of disposal sites will be
limited in order to localize for
identification and control any
immediate adverse impacts, and to
permit the implementation of effective
monitoring and surveillance to prevent
adverse long-range impacts. Size,
configuration, and location are to be
determined as part of the disposal site
evaluation (40 CFR 228.5(d)).
EPA sized the proposed site to meet
this criterion. The site, as finalized in
today’s action, continues to meet this
criterion. The total area of new Site F is
PO 00000
Frm 00016
Fmt 4700
Sfmt 4700
approximately 3,075.2 acres or 3.63
nm2. The site tends to be moderately
dispersive in the nearshore area and
tends to be less dispersive in other parts
of the site. The overall stability of the
site is a significant part of the
justification for the size of the site. The
original Site F experienced significant
mounding and lead to the selection of
the larger site designated today. Data
collected by the Corps through
bathymetric monitoring shows the
spread and movement of material
placed at original Site F and suggests
that material from the original Site F did
eventually disperse over the footprint of
the 103-selected site. This data also
indicates that effective monitoring and
surveillance of the site has been
performed for many years. The SMMP
describes the plan for management and
monitoring of the site.
5. EPA will, wherever feasible,
designate ocean dumping sites beyond
the edge of the continental shelf and
other such sites where historical
disposal has occurred (40 CFR 228.5(e)).
EPA’s evaluation at the time of the
proposed rule concluded that long
distances and travel times between the
dredging locations near Coos Bay and
the continental shelf posed significant
environmental, operational, safety and
environmental concerns, including risk
of encounter with endangered species
and increased air emissions. This
conclusion is unchanged and new Site
F, finalized by today’s rule, is consistent
with this criterion.
Specific Criteria (40 CFR 228.6)
1. Geographical Position, Depth of
Water, Bottom Topography and Distance
From Coast (40 CFR 228.6(a)(1))
Based on the data available at the time
EPA proposed the designation of Site F
and data available from bathymetric
surveys conducted by the Corps, EPA
has concluded that the geographical
position, depth of water, bottom
topography and distance from the coast
of new Site F will avoid adverse effects
to the marine environment. Near the
North Jetty, the new site will allow for
the placement of material that is
expected to contribute material to the
littoral zone and may help decrease
erosion of the jetty. Throughout most of
the shallow portions of the new site the
area is dispersive. Based on EPA’s
understanding of currents at the site and
their influence on the movement of
material in the area this means there is
a high likelihood that material will be
transported to the adjacent seafloor. The
site is located and sized to allow for
long-term disposal without creation of
adverse mounding conditions.
E:\FR\FM\11MYR1.SGM
11MYR1
Federal Register / Vol. 71, No. 91 / Thursday, May 11, 2006 / Rules and Regulations
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))
New Site F is not located in breeding,
spawning, nursery or feeding areas for
adult or juvenile phases of living
resources. The site is, or may be, a
passage area for living resources during
adult or juvenile phases. The National
Marine Fisheries Service (NMFS),
during consultations with EPA in 2005
and 2006 for endangered species and for
essential fish habitat, requested that
disposal at new Site F be restricted to
stagger disposal events at the new site,
particularly in the nearshore zone, to
avoid continuous disposal while
juveniles, including salmon and
groundfish species, are outmigrating or
holding in nearshore environments.
EPA agreed to include staggered
disposal in its final SMMP. This will
benefit the juveniles of concern to
NMFS and will also minimize any
potential short-term localized effects to
marine organisms in the immediate
vicinity of disposal events by
minimizing the creation of mounds at
the site.
3. Location in Relation to Beaches and
Other Amenity Areas (40 CFR
228.6(a)(3))
EPA’s proposed rule concluded that
the proposed site met this criterion and
EPA’s conclusion is not changed today
notwithstanding the minor
reconfiguration of the site toward the
North Jetty. The site, although located in
the navigation channel and close to the
North Jetty is located to avoid adverse
impacts to beaches and other amenity
areas.
cchase on PROD1PC60 with RULES
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 228.6(a)(4))
The new Site F is being designated
today for the disposal of dredged
material. Disposal of other types of
material will not be allowed at this site
or at any of the ocean dredged material
disposal sites at Coos Bay. Dredged
material to be disposed at the new Site
F will be predominantly sand and finegrained material. Data collected
subsequent to EPA’s proposed rule
included seventeen sediment samples
collected from along the length of the
federal navigation channel in Coos Bay,
Isthmus Slough, and Charleston
Channel in 2004 (Coos Bay Sediment
Quality Evaluation Report, March 2005).
These samples were subjected to
physical and chemical analyses, which
VerDate Aug<31>2005
16:19 May 10, 2006
Jkt 208001
included analyses for metals, total
organic carbon, pesticides,
polychlorinated biphenyls (PCBs),
phenols, phthalates, miscellaneous
extractables, polynuclear aromatic
hydrocarbons (PAHs) and total and pore
water organotin (TBT).
The physical analyses resulted in
mean values of 1.6% gravel (0%–10.0%
range), 69.6% sand (4.0%–98.8% range),
and 28.8% silt/clay (1.2%–96.0% range)
with 4.5% volatile solids (0.2%–16.7%
range). The chemical analyses indicated
low levels of chemicals in some of the
samples. The results were compared
with results from previous Corps
sampling efforts in 1980, 1986, 1987,
1989, 1993, 1994, 1995, and 1998. All
the data are consistent in showing that
material below river mile (RM) 12 of the
Coos Bay channel is typically sand,
while material above RM 12 is typically
silt. With only a few exceptions (where
adjacent sources are obvious) the sand
matrix is considered low risk for
contamination. The silty areas of the
estuary and river typically contain low
levels of contaminants-of-concern that
have remained unchanged for many
years or appear to be improving slightly
(i.e. concentrations are dropping).
Materials to be disposed of at the site
must be suitable for ocean disposal.
With respect to proposed methods of
releasing material at the new site,
material will be released just below the
surface from dredges while the dredges
are under power and slowly transit the
site. This method of release is expected
to minimize mounding at the site and to
minimize impacts to the benthic
community.
5. Feasibility of Surveillance and
Monitoring (40 CFR 228.6(a)(5))
Monitoring and surveillance at new
Site F is expected to be feasible. The site
is accessible for bathymetric and sidescan sonar surveys. Most of the site has
been successfully monitored by the
Corps during the Corps’s use of the 103
site. It is also expected to be feasible to
monitor and survey the minor addition
made to the site through the
reconfiguration toward the North Jetty.
The Corps has monitored the base of the
jetty on a routine basis and during
emergency repairs made in 2002 after a
failure of the jetty. The final SMMP
requires monitoring and surveillance of
the new site. At a minimum, annual
bathymetric surveys will be conducted
at new Site F and more frequent surveys
will be required in areas of the site that
receive dredged material. Off-site beach
monitoring will also be required.
Routine monitoring will concentrate on
determining how to ensure the
distribution of material in the nearshore
PO 00000
Frm 00017
Fmt 4700
Sfmt 4700
27401
portions of the site to augment littoral
processes and in the deeper portions of
the site to avoid or minimize mounding.
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))
At the time EPA proposed the
designation of the new site, EPA
understood the dispersal patterns along
the Oregon coast to generally flow
parallel to the bathymetric contours of
the bottom. Local wave and current
strength and direction are impacted by
the variability of the local winds,
especially in shallower water. During
summer months which make up the
normal dredge and disposal season,
material transport trends southward.
The trend at other times of the year is
north and northwest for currents and
material transport. Re-suspension and
transport of material disposed at the site
would be expected to be at a maximum
during winter months when winter
storms occur and when no active
disposal is taking place at the site.
Throughout the year, material disposed
in the nearshore and shallower portions
of new Site F are expected to be
redistributed by existing littoral
processes.
Mounding at originally designated
Site F led the Corps to exercise its
authorities pursuant to Section 103 of
the MPRSA to select a significant
expansion of the site and to use
modeling techniques to model
placement of material within the site to
avoid excessive mounding. The
originally designated Site F was
generally not used for disposal after
1989. However, it was thought that
material at that location was eroding
toward the 103 selected Site F. For this
reason, the original Site F, although
proposed for de-designation as a standalone site, was to be incorporated into
the new Site F. The movement of
material was considered to be most
dispersive in the shallower zones of the
103 site but material disposed in the
deeper and less dynamic portions of the
site are redistributed across the site.
Eventually, the redistribution is
expected to move the material disposed
at the site to the north and east.
Subsequent to publication of the
proposed Rule in 2000, the Corps
continued to conduct annual
bathymetric surveys at the 103 Site F
and to share the data collected with EPA
to assess capacity at the site for the
coming year’s anticipated dredging.
This data tended to show that the
mound at the 1986-designated Site F
was slowly eroding to its present
E:\FR\FM\11MYR1.SGM
11MYR1
27402
Federal Register / Vol. 71, No. 91 / Thursday, May 11, 2006 / Rules and Regulations
cchase on PROD1PC60 with RULES
average at below minus 60 feet mean
lower low water (MLLW). This indicates
a minimum of 10 feet of material having
eroded out of 1986-designated Site F.
Dredged material was placed at various
locations within the 103 Site F and
monitored. Computer modeling of
disposal operations was used to
determine short-term and long-term
sediment fate to design disposal units or
cells. Bathymetric surveys during and
following disposals were conducted.
Initial work was focused on confirming
accuracy of the models. Bathymetric
changes measured by the monitoring
compared well with the changes
predicted by the model. For example,
the model predicted a 2.9 foot change
and monitoring measured the actual
change at 3.0 feet. The model was used
to predict disposal results in the
nearshore area (i.e., along the innermost
edge of the 103 Site F) and field
monitoring was conducted to verify the
modeled predictions. Placement height
was managed to a maximum of 3 feet
during initial disposal into 180 separate
cells each sized as a 200 foot by 500 foot
cell.
These bathymetric surveys show that
the shallow water portion of the site has
accumulated about 1 foot of material on
the bottom, with small areas of
accumulation of up to 5 feet. In the
deeper portion of the 103 site, disposals
were conducted to dispose of up to 24
feet of material at specific locations.
Bathymetric monitoring indicates these
thicker disposals had eroded down to 19
feet of accumulated material on the
bottom. The surveys further show that
this accumulated material is dispersing
in a northeasterly direction.
7. Existence and Effects of Current and
Previous Discharges and Dumping in
the Area (Including Cumulative Effects)
(40 CFR 228.6(a)(7))
Annually, approximately 1.3 million
cubic yards (mcy) of material has been
disposed of at the Coos Bay designated
sites, Sites E, F and H, from dredging
undertaken by the Corps to maintain the
navigation channel. The Coos Bay sites
were used consistently prior to their
designations in 1986. Sites E and F were
not used after the late eighties because
of mounding concerns. As discussed
above, the mounds at those sites have
been eroding over time. Originally
designated Site F was recently used by
the Corps for the disposal of dredged
material to maintain safe navigation in
the navigation channel. This site, which
is de-designated by today’s rule as a
stand-alone site, is incorporated into the
footprint of the new Site F. EPA’s
evaluation of data and modeling results
indicates that past disposal operations
VerDate Aug<31>2005
16:19 May 10, 2006
Jkt 208001
at these sites and current operations
have not resulted in unacceptable
environmental degradation. Adverse
effects are not expected to result from
the minor reconfiguration of the site
toward the North Jetty. EPA expects that
portion of the site to benefit the
nearshore environment.
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 site is not expected to interfere
with shipping, fishing, recreation or
other legitimate uses of the ocean.
Commercial crabbing, which was
referenced in EPA’s proposed rule as an
activity occurring in the nearshore, is
not expected to be impacted by the
minor reconfiguration of new Site F.
Disposals at the new site will be
managed through the SMMP to
minimize interference with other
legitimate uses of the ocean through
careful timing and staggering of
disposals in the nearshore portion of the
new site.
9. The Existing Water Quality and
Ecology of the Sites as Determined by
Available Data or Trend Assessment of
Baseline Surveys (40 CFR 228.6(a)(9))
At the time of EPA’s proposed rule in
2000, EPA had not identified any
adverse water quality impacts from
ocean disposal of dredged material at
originally designated Site F or at 103
selected Site F. In 2004, the Corps
released a report titled ‘‘Comparison of
SPI Data and STFATE Simulation
Results at Coos Bay, OR ODMDS Site
‘F’,’’ which provided some verification
of numerical models used to predict the
behavior of disposed material on water
quality and ecology of the site. The
samples, i.e. sediment profile images,
indicated some important
characteristics about the native
sediments and dredged sediments
disposed of at the site. Native sediment
in the shallow and intermediate water
portions of the site did not show a layer
of fine grained material at the sedimentwater interface. This absence indicates
that burrowing infauna were absent or
extremely limited in the area. This
finding was not unexpected because the
intermediate/shallow water locations
within the site are heavily dominated by
wave-current action which forces
repeated and routine resuspension of
sediment. The report found that ‘‘the
effects on initial disposal on benthic
marine life in these areas are likely
minimal.’’ By contrast, the deeper
portion of the site did indicate the
PO 00000
Frm 00018
Fmt 4700
Sfmt 4700
presence of benthic infaunal activity. In
addition to the sediment profile imaging
(SPI), a plan-view video was also
produced. Crabs, shrimp, and flatfish
were all seen on the video; however, no
inferences were made as to population.
Biological activity and reworking of the
surface sediments by natural forces was
indicated in the imaging but it was not
possible to penetrate the sandy substrate
to measure the full thickness of the
deposited material at the site.
10. Potentiality for the Development or
Recruitment of Nuisance Species in the
Disposal Site (40 CFR 228.6(a)(10))
In its proposed rule, EPA stated that
nuisance species had not been observed
at the existing Coos Bay sites in over ten
years of monitoring and that EPA did
not expect there to be a significant
potential for the development or
recruitment of nuisance species in the
proposed site. That statement was based
in part on the lack of organic material
disposed at the site. Subsequent to
EPA’s proposed rule, however,
circumstances at designated Site H have
caused that site to be closed at present
and the potential for organic material to
be disposed of at new Site F has
increased. Organic material is generally
found above RM 12 in the Coos Bay
Channel and is likelier than material
below RM12 to be more attractive to
nuisance species. While there is the
potential for the development or
recruitment of nuisance species where
dredged material from above RM12
might be disposed of at the new Site F,
this potential remains low. The SMMP
will provide for monitoring of the new
site to help ensure that nuisance species
are not recruited to and do not develop
at the new site.
11. Existence at or in Close Proximity to
the Site of Any Significant Natural or
Cultural Feature of Historical
Importance (40 CFR 228.6(a)(11))
EPA stated in its proposed rule that
no cultural features of historical
importance had been identified at or
near the proposed site. This continues
to be the case. The new Site F is located
over 7 statute miles southwest of the
Oregon Dunes National Recreation Area,
a significant natural feature, but is not
considered to be in close proximity to
that feature. The new site is located
approximately 3 statute miles northeast
of three Oregon state parks: Shore Acres
State Park, Cape Arago State Park and
Sunset Bay State Park. The new site is
not considered to be in proximity to
these areas. The national historic
landmark, located near Cape Arago State
Park, over 4 statute miles south of the
new site, is not within the proximity of
E:\FR\FM\11MYR1.SGM
11MYR1
Federal Register / Vol. 71, No. 91 / Thursday, May 11, 2006 / Rules and Regulations
the site. Impacts to significant natural or
cultural features have not been
identified.
e. National Environmental Policy Act
(NEPA); Magnuson-Stevens Act (MSA);
Coastal Zone Management Act (CZMA);
Endangered Species Act (ESA)
1. NEPA
Section 102 of the National
Environmental Policy Act of 1969, 42
U.S.C. 4321, et seq., (NEPA) 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. NEPA does not apply to
EPA designations of ocean disposal sites
under the MPRSA as EPA has made
clear in EPA’s ‘‘Notice of Policy and
Procedures for Voluntary Preparation of
NEPA Documents,’’ 63 FR 58045
(October 29, 1998). EPA did voluntarily
cooperate with the U.S. Army Corps of
Engineers (Corps) as a cooperating
agency on the Feasibility Report on
Navigation Improvements with
Environmental Impact Statement (EIS)
prepared in 1994. As discussed in the
proposed rule, 63 FR 17240 (March 31,
2000), the EIS provided documentation
to support the final designation of the
proposed Site F. EPA did not see a need
to supplement the EIS to address the
minor reconfiguration of the new Site F
which is finalized in today’s
designation.
cchase on PROD1PC60 with RULES
2. MSA
In the fall of 2005, EPA consulted
with the National Marine Fisheries
Service (NMFS) concerning essential
fish habitat. EPA prepared an essential
fish habitat (EFH) assessment pursuant
to section 305(b) of the MagnusonStevens Act, as amended (MSA), 16
U.S.C. 1855(b). NMFS reviewed EPA’s
action and issued six non-binding
conservation recommendations. EPA
accepted three of the recommendations.
The three accepted by EPA included:
Using the best relevant analytical
methods in sampling and analysis plans
included in the final SMMP; limiting
site use before June 1 and staggering
disposal events during nearshore
holding and outmigration of juvenile
salmon; and provisions to provide the
results of bathymetric monitoring to
NMFS. EPA incorporated these
recommendations into the final SMMP.
EPA did not accept the remaining
three recommendations. These
recommendations asked EPA to develop
and implement studies to collect
information to better inform agencies on
species presence and use in the disposal
VerDate Aug<31>2005
16:19 May 10, 2006
Jkt 208001
area, in areas that might be designated
in the future, and for all existing ocean
disposal sites in Oregon. EPA did not
accept these recommendations because
EPA did not find that the collection of
information as recommended by NMFS
constituted measures for ‘‘avoiding,
mitigating, or offsetting the impact’’ of
the Federal action on essential fish
habitat.
3. CZMA
EPA consulted with the state of
Oregon on coastal zone management
issues. EPA prepared a consistency
determination for the Oregon Ocean and
Coastal Management Program (OCMP)
to address consistency determinations
required by the Coastal Zone
Management Act, 16 U.S.C. 1446. The
Oregon Department of Land
Conservation and Development (DLCD)
reviewed the consistency determination
and concurred with EPA that the action
is consistent with the OCMP to the
maximum extent practicable basing its
findings on the certification EPA
provided.
4. ESA
EPA also consulted with NMFS and
the U.S. Fish and Wildlife Service on its
action to de-designate existing Site F
and to designate new Site F finding that
the action would not be likely to
adversely affect aquatic or wildlife
species listed as endangered pursuant to
the Endangered Species Act, 16 U.S.C.
1531 to 1544, (ESA), or the critical
habitat of such species. EPA found that
site designation does not have a direct
impact on any of the identified ESA
species but also found that indirect
impacts had to be considered. These
indirect impacts included a short-term
increase in suspended solids and
turbidity in the water column when
dredged material was disposed at the
new site and an accumulation of
material on the ocean floor when
material was disposed at the site. EPA
concluded that while its action may
affect ESA-listed species, the action
would not be likely to adversely affect
ESA-listed species.
The U.S. Fish and Wildlife Service
concurred with EPA’s conclusion based
on its finding that ‘‘abundant suitable
foraging habitat throughout the area’’ for
birds of concern would be available
during disposal activities, i.e. site use,
and that minor behavioral changes, such
as foraging in areas other than the
designated site, would be temporary.
NMFS concurred with EPA’s findings
for ESA-listed marine mammals, sea
turtles, and southern Oregon/northern
California coho salmon, finding that the
new site was not designated as critical
PO 00000
Frm 00019
Fmt 4700
Sfmt 4700
27403
habitat for any of those species. NMFS
did not agree with EPA’s conclusions
for Oregon Coast coho salmon and
requested additional consultation.
Subsequent to that request, NMFS
announced that it was withdrawing its
proposal to list Oregon Coast coho
salmon as endangered. The ESA
consultation concluded with the
withdrawal of the NMFS proposal to list
Oregon Coast coho salmon and NMFS
addressed Oregon Coast coho salmon in
the EFH consultation.
3. Response to Comment
No public comments on the proposed
designation were received; however, a
letter from the Oregon Department of
Environmental Quality (ODEQ) pointed
out the need for improved coordination
procedures between the EPA, the Corps,
ODEQ’s central office and ODEQ’s Coos
Bay field office for dredging projects in
the vicinity of Coos Bay. EPA generally
supports improved coordination
between federal and state agencies.
Coordination will be a priority for EPA
at the new site to ensure that disposal
activities by the Corps and by local port
authorities are aware of site restrictions
and are adhering to the SMMP.
4. Statutory and Executive Order
Reviews
This rule finalizes the de-designation
of an existing ocean dredged material
disposal site, existing Site F, and
designates a new ocean dredged
material disposal site, new Site F. This
rule complies with applicable executive
orders and statutory provisions as
follows:
a. Executive Order 12866
Under Executive Order 12866 (58 FR
51735, October 4, 1993), the Agency
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: (1) 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; (2) create
a serious inconsistency or otherwise
interfere with an action taken or
planned by another agency; (3)
materially alter the budgetary impact of
entitlements, grants, user fees, or loan
programs, or the rights and obligations
of recipients thereof; or (4) raise novel
legal or policy issues arising out of legal
mandates, the President’s priorities, or
E:\FR\FM\11MYR1.SGM
11MYR1
27404
Federal Register / Vol. 71, No. 91 / Thursday, May 11, 2006 / Rules and Regulations
the principles set forth in the Executive
Order. It has been determined that this
final action, which simultaneously dedesignates an existing ocean dredged
material disposal site and designates a
new site, Site F, is not a significant
regulatory action under Executive Order
12866 and is therefore not subject to
OMB review.
cchase on PROD1PC60 with RULES
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., because this
final action does not establish or modify
any information or recordkeeping
requirements for the regulated
community.
Burden means the total time, effort, or
financial resources expended by persons
to generate, maintain, retain, or disclose
or provide information to or for a
Federal agency. This includes the time
needed to review instructions; develop,
acquire, install, and utilize technology
and systems for the purposes of
collecting, validating, and verifying
information, processing and
maintaining information, and disclosing
and providing information; adjust the
existing ways to comply with any
previously applicable instructions and
requirements; train personnel to be able
to respond to a collection of
information; search data sources;
complete and review the collection of
information; and transmit or otherwise
disclose the information.
An agency may not conduct or
sponsor, and a person is not required to
respond to a collection of information
unless it displays a currently valid OMB
control number. The OMB control
numbers for EPA’s regulations in 40
CFR are listed in 40 CFR part 9.
c. Regulatory Flexibility
The Regulatory Flexibility Act (RFA),
as amended by the Small Business
Regulatory Enforcement Fairness Act
(SBREFA), 5 U.S.C. 601, et seq.,
generally requires federal agencies to
prepare a final regulatory flexibility
analysis whenever the agency
promulgates a final 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. Small entities include small
businesses, small organizations, and
small governmental jurisdictions. For
purposes of assessing the impacts of
today’s rule on small entities, small
entity is defined as: (1) A small business
defined by the Small Business
VerDate Aug<31>2005
16:19 May 10, 2006
Jkt 208001
Administration’s Size Regulations at 13
CFR 121.201; (2) a small governmental
jurisdiction that is a government of a
city, county, town, school district or
special district with a population of less
than 50,000; and (3) a small
organization that is any not-for-profit
enterprise which is independently
owned and operated and is not
dominant in its field. EPA has
determined that this action will not
have a significant economic impact on
small entities because the final action
regulates the location of sites to be used
for the disposal of dredged materials in
ocean waters. After considering the
economic impacts of today’s final action
on small entities, I certify that this
action will not have a significant impact
on a substantial number of small entities
directly regulated by this action.
d. Unfunded Mandates Reform Act
Title II of the Unfunded Mandates
Reform Act (UMRA) of 1995 (Pub. L.
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 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
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 why the 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, enabling
officials of 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
PO 00000
Frm 00020
Fmt 4700
Sfmt 4700
small governments on compliance with
the regulatory requirements. Today’s
action contains no Federal mandates
(under the regulatory provisions of Title
II of the UMRA) for State, local or tribal
governments or the private sector. It
imposes no new enforceable duty on
any State, local or tribal governments or
the private sector. Similarly, EPA has
also determined that this action
contains no regulatory requirements that
might significantly or uniquely affect
small government entities. Thus, today’s
action is not subject to the requirements
of sections 202 and 203 of the UMRA.
e. 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 action 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 action
will be effective June 12, 2006.
f. Executive Order 13132: Federalism
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’’ are 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
various levels of government.’’ This
action 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 various levels of
government, as specified in Executive
Order 13132. This action addresses the
designation and de-designation of sites
near the mouth of Coos Bay, Oregon.
Thus, Executive Order 13132 does not
apply to this action.
E:\FR\FM\11MYR1.SGM
11MYR1
Federal Register / Vol. 71, No. 91 / Thursday, May 11, 2006 / Rules and Regulations
g. Executive Order 13175: Consultation
and Coordination With Indian Tribal
Governments
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 action does not have
tribal implications, as specified in
Executive Order 13175. Thus, Executive
Order 13175 does not apply to this
action.
h. Executive Order 13045: Protection of
Children From Environmental Health
and Safety Risks
Executive Order 13045 applies to any
rule that: (1) Is determined to be
‘‘economically significant’’ as defined
under Executive Order 12866, and (2)
concerns an environmental health or
safety risk that EPA has reason to
believe may have a disproportionate
effect on children. If the regulatory
action meets both criteria, the Agency
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 the
Agency. This action is not subject to
Executive Order 13045 because it is not
economically significant as defined in
Executive Order 12866 and because the
Agency does not have reason to believe
the environmental health or safety risks
addressed by this action present a
disproportionate risk to children. The
action concerns the designation and dedesignation of ocean disposal sites and
would only have the effect of providing
designated locations to use for ocean
disposal of dredged material pursuant to
section 102(c) of the MPRSA.
cchase on PROD1PC60 with RULES
i. Executive Order 13211: Actions That
Significantly Affect Energy Supply,
Distribution, or Use
This action 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’’ as
defined under Executive Order 12866.
j. National Technology Transfer and
Advancement Act
Section 12(d) of the National
Technology Transfer and Advancement
Act of 1995 (‘‘NTTAA’’), Public Law
104–113, section 12(d) (15 U.S.C. 272)
directs EPA to use voluntary consensus
standards in its regulatory activities
VerDate Aug<31>2005
16:19 May 10, 2006
Jkt 208001
unless to do 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 to
Congress, through the OMB,
explanations when the Agency decides
not to use available and applicable
voluntary consensus standards.
Although EPA stated that the proposed
action did not directly involve technical
standards, the proposed action and
today’s final action include
environmental monitoring and
measurement as described in EPA’s
SMMP. EPA will not require the use of
specific, prescribed analytic methods for
monitoring and managing the
designated sites. Rather, the Agency
plans to allow the use of any method,
whether it constitutes a voluntary
consensus standard or not, that meets
the monitoring and measurement
criteria discussed in the final SMMP.
k. Executive Order 12898: Federal
Actions To Address Environmental
Justice in Minority Populations and Low
Income Populations
To the greatest extent practicable and
permitted by law, and consistent with
the principles set forth in the report on
the National Performance Review, each
Federal agency must make achieving
environmental justice part of its mission
by identifying and addressing, as
appropriate, disproportionately high
and adverse human health and
environmental effects of its programs,
policies, and activities on minority
populations and low-income
populations in the United States and its
territories and possessions, the District
of Columbia, the Commonwealth of
Puerto Rico, and the Commonwealth of
the Mariana Islands. Because this action
addresses ocean disposal site
designations (away from inhabited land
areas), no significant adverse human
health or environmental effects are
anticipated. The action is not subject to
Executive Order 12898 because there are
no anticipated significant adverse
human health or environmental effects.
List of Subjects in 40 CFR Part 228
Environmental protection, Water
pollution control.
Authority: This action is issued under the
authority of section 102 of the Marine
Protection, Research, and Sanctuaries Act, as
amended, 33 U.S.C. 1401, 1411, 1412.
PO 00000
Frm 00021
Fmt 4700
Sfmt 4700
27405
Dated: April 28, 2006.
L. Michael Bogert,
Regional Administrator, Region 10.
For the reasons set out in the
preamble, Chapter I of title 40 is
amended as set forth below:
I
PART 228—[AMENDED]
1. The authority citation for part 228
continues to read as follows:
I
Authority: 33 U.S.C. 1412 and 1418.
2. Section 228.15 is amended by
revising paragraphs (n)(4)(i), (ii), (iii),
(iv), (v), and (vi) to read as follows:
I
§ 228.15 Dumping sites designated on a
final basis.
*
*
*
*
*
(n) * * *
(4) * * *
(i) Location: 43°22′54.8887″ N,
124°19′28.9905″ W; 43°21′32.8735″ N,
124°20′37.7373″ W; 43°22′51.4004″ N,
124°23′32.4318″ W; 43°23′58.4014″ N,
124°22′35.4308″ W (NAD 83).
(ii) Size: 4.45 kilometers long and 2.45
kilometers wide.
(iii) Depth: Ranges from 6 to 51
meters.
(iv) Primary Use: Dredged material
determined to be suitable for ocean
disposal.
(v) Period of Use: Continuing Use.
(vi) Restriction: Disposal shall be
limited to dredged material determined
to be suitable for unconfined disposal;
Disposal shall be managed by the
restrictions and requirements contained
in the currently-approved Site
Management and Monitoring Plan
(SMMP); Monitoring, as specified in the
SMMP, is required.
*
*
*
*
*
[FR Doc. 06–4286 Filed 5–10–06; 8:45 am]
BILLING CODE 6560–50–P
ENVIRONMENTAL PROTECTION
AGENCY
40 CFR Part 271
[EPA–R04–RCRA–2006–0429; FRL–8168–4]
Tennessee: Final Authorization of
State Hazardous Waste Management
Program Revisions
Environmental Protection
Agency (EPA).
ACTION: Immediate final rule.
AGENCY:
SUMMARY: Tennessee has applied to EPA
for final authorization of the changes to
its hazardous waste program under the
Resource Conservation and Recovery
Act (RCRA). EPA proposes to grant
Final authorization to Tennessee. In the
E:\FR\FM\11MYR1.SGM
11MYR1
Agencies
[Federal Register Volume 71, Number 91 (Thursday, May 11, 2006)]
[Rules and Regulations]
[Pages 27396-27405]
From the Federal Register Online via the Government Printing Office [www.gpo.gov]
[FR Doc No: 06-4286]
-----------------------------------------------------------------------
ENVIRONMENTAL PROTECTION AGENCY
40 CFR Part 228
[FRL-8167-7]
Ocean Dumping; De-Designation of Ocean Dredged Material Disposal
Site and Designation of New Site Near Coos Bay, OR
AGENCY: Environmental Protection Agency (EPA).
ACTION: Final rule.
-----------------------------------------------------------------------
SUMMARY: EPA is finalizing its proposal to de-designate an existing
ocean dredged material disposal site and designate a new ocean dredged
material disposal site located offshore of Coos Bay, Oregon. EPA's
proposed rule was published March 31, 2000. The new site is needed for
long-term use by authorized Coos Bay navigation projects and may be
available for use by persons meeting the criteria for ocean disposal of
dredged material. The de-designation of the existing site allows for
its incorporation into the newly designated site. This will allow EPA
to manage the entire new site to avoid adverse mounding conditions and
will ensure site capacity is sufficient for total volumes of dredged
material. The newly designated site is necessary for current and future
dredged material ocean disposal needs and will be subject to ongoing
monitoring and management to ensure continued protection of the marine
environment so as to mitigate adverse impacts on the environment to the
greatest extent practicable.
DATES: This final rule will be effective on June 12, 2006.
ADDRESSES: EPA has established a docket for this final action under
Docket ID No. EPA-R10-OW-2006-0409. All documents in the docket are
listed on the www.regulations.gov Web site. The documents are also
available for inspection at the Region 10 Library, 10th Floor, 1200
Sixth Avenue, Seattle, Washington 98101. For access to the documents at
the Region 10 Library, contact the Region 10 Library Reference Desk at
(206) 553-1289, between 9 a.m. to 11:30 a.m. and 1 p.m. to 4 p.m.,
Monday through Friday, excluding legal holidays, for an appointment or
contact John Malek, U.S. EPA, Region 10, 1200 Sixth Avenue, Mail Stop
ETPA-083, e-mail: malek.john@epa.gov, phone number (206) 553-1286.
FOR FURTHER INFORMATION CONTACT: John Malek, Ocean Dumping Coordinator,
U.S. Environmental Protection Agency, Region 10 (ETPA-083), 1200 Sixth
Avenue, Seattle, WA 98101-1128, telephone (206) 553-1286, e-mail:
malek.john@epa.gov.
SUPPLEMENTARY INFORMATION:
1. Potentially Affected Persons
Persons potentially affected by this action include those who seek
or might seek permits or approval by EPA to dispose of dredged material
into ocean waters pursuant to the Marine Protection, Research, and
Sanctuaries Act, as amended, 33 U.S.C. 1401 to 1414, (``MPRSA''). EPA's
action would be relevant to persons, including organizations and
government bodies seeking to dispose of dredged material in ocean
waters offshore of Coos Bay, Oregon. Currently, the U.S. Army Corps of
Engineers (Corps) and other persons with permits to use designated
sites at Coos Bay would be most impacted by this final action.
Potentially affected categories and persons include:
------------------------------------------------------------------------
Category Examples of potentially regulated persons
------------------------------------------------------------------------
Federal Government........... U.S. Army Corps of Engineers Civil Works
Projects, 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 owning and/or responsible for
governments. 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 persons likely to be affected by this
action. For any questions regarding the applicability of this action to
a particular person, please refer to the section of this action titled
FOR FURTHER INFORMATION CONTACT.
2. Background
a. History of Disposal Site Designations Off of Coos Bay, OR
Pursuant to the MPRSA, the Administrator of EPA, as delegated to
the Regional Administrator, designated three disposal sites (Site E,
original Site F and Site H) off of Coos Bay, Oregon in 1986. The
original Site F began to experience mounding that rendered it unable to
accept the total volume of dredged material generated on an annual
basis. In 1989, with EPA approval, the size of the original Site F was
roughly doubled by the Corps exercising its Section 103 authority to
select disposal sites under the MPRSA. In 1995, EPA approved a second
Corps expansion of the original Site F. On March 31, 2000, EPA
published in the Federal Register its proposal to de-designate the
original Site F and designate a new Site F that consisted of the 103
configured Site F and the original Site F (65 FR 17240). A forty-five
day public comment period, which closed on May 14, 2000, was provided.
EPA did not receive comments from the public on the proposed rule. The
coordinates of the proposed Site F (North American Datum 1983; NAD 83)
were:
43[deg]22'58'' N, 124[deg]19'32'' W
43[deg]21'50'' N, 124[deg]20'29'' W
43[deg]22'52'' N, 124[deg]23'28'' W
43[deg]23'59'' N, 124[deg]22'31'' W
The proposed site was rectangular with an east-west side length
dimension of 14,500 feet and a north-south side length dimension of
8,000 feet. Figure 1 is a diagram of the site EPA proposed in 2000.
Subsequent to EPA's proposed designation, the North Jetty at Coos
Bay failed in December 2002, due in part to undermining. The Corps then
examined the potential for augmenting transport of disposed material
into the eddy created by the North Jetty itself. With EPA concurrence,
the Corps began making selected disposals in the southeastern corner of
the 103 Site F nearest the jetty. Monitoring indicated that some
material was captured by the eddy and augmented the substrate that the
jetty rests upon. This experience and the lessons learned during the
designations of ocean dredged material disposal sites near the Mouth of
the Columbia River in 2005, as well as increased public awareness of,
and attention to, coastal erosion processes and opportunities to manage
dredged material more beneficially led EPA to review its proposed site
designation near Coos Bay. The result of this review is a minor change
to the configuration of new Site F toward the North Jetty at the north
side of the mouth of Coos Bay. This reconfiguration could potentially
benefit the stabilization of the North Jetty and keep material in the
littoral zone. This
[[Page 27397]]
reconfiguration is expected to allow dredged material disposed in
shallower portions of the new Site F to naturally disperse into the
littoral zone without creation of mounding conditions that would
contribute to adverse impacts to navigation, including adverse wave
conditions.
b. Location and Configuration of New Site F
Figure 2 is a diagram of the new Site F as EPA is finalizing the
site in today's rule. It also shows the other designated sites (E and
H), the de-designated Site F, the 103 configured Site F and the
proposed Site F. The shoremost side of the site has been extended
approximately 600 feet as compared to the site when proposed and the
southeastern corner has been located closer to the North Jetty at the
mouth of Coos Bay. This has resulted in an overall increase to the site
footprint of 399.8 acres bringing the total area of new Site F to
3,075.2 acres. This configuration will allow EPA to ensure that
disposal of dredged material into the site will be managed to retain
more of the material in the active littoral drift area to augment
shoreline building processes. The relocation of the corner of the site
closer to the jetty will allow dredged material to be more effectively
placed to continue augmentation toward the nearshore and toward the
North Jetty at the mouth of Coos Bay. This change, while minor, expands
sediment management opportunities that are beneficial to the coastal
environment in Coos Bay. The coordinates for the new Site F near Coos
Bay (NAD 83) as finalized today are:
43[deg]22'54.8887'' N, 124[deg]19'28.9905'' W
43[deg]21'32.8735'' N, 124[deg]20'37.7373'' W
43[deg]22'51.4004'' N, 124[deg]23'32.4318'' W
43[deg]23'58.4014'' N, 124[deg]22'35.4308'' W
The new Site F is expected to accommodate the approximately 1.38
million cubic yards (mcy) of material dredged annually from the Coos
Bay estuary by the Corps to maintain the existing Federal navigation
channel. The nearshore boundary of the new site is within two thousand
feet of the shoreline. Sediments disposed near this boundary are
considered to be in the active transport zone and are expected to
disperse rapidly both onshore and alongshore. Limited onshore transport
is expected because of the nature of prevailing currents and wave
transport in the vicinity. Predicted material transport at the new site
is southward in the summer months and northward during the remainder of
the year.
BILLING CODE 6560-5-P
[[Page 27398]]
[GRAPHIC] [TIFF OMITTED] TR11MY06.004
[[Page 27399]]
[GRAPHIC] [TIFF OMITTED] TR11MY06.005
BILLING CODE 6560-50-C
c. Management and Monitoring of New Site F
The newly designated Site F will receive sediments dredged by the
Corps to maintain the federally authorized navigation project at Coos
Bay, Oregon and will be available to current permittees and for use by
others after obtaining the appropriate permits and approvals. Existing
permits issued pursuant to subchapter H of Title 40 of the CFR will not
need to be modified to use new Site F. The new Site F is designated
with restrictions with which all persons must comply. All persons using
the site are required to follow the final Site Management and
Monitoring Plan (SMMP) which is effective as of the effective date of
this action. The SMMP generally addresses managing new Site F to
minimize and avoid mounding and to ensure that dredged materials
[[Page 27400]]
disposed at the site are suitable for ocean disposal. The SMMP includes
management and monitoring requirements for all of the designated sites
near Coos Bay and addresses the timing of disposal into new Site F to
minimize interference with commercial crabbing in the nearshore zone.
Among other things, the SMMP sets out monitoring and management
requirements to ensure that dredged material disposed at the site is
suitable for disposal and will not lead to unacceptable impacts to
human health or the environment during the dredging process, during
transportation to the designated sites, during disposal or once
disposed or at the disposal sites.
d. MPRSA
EPA finds that today's final action satisfies the site designation
criteria of the MPRSA and the regulatory criteria of 40 CFR part 228.
The assessment of the statutory criteria and general and specific
regulatory criteria presented in the proposed rule has been examined in
response to the slight reconfiguration of the new Site F. Moving the
corner of the new Site F to the southeast and closer to the North Jetty
based on EPA's increased understanding of coastal erosion issues will
allow EPA to manage disposal at the new Site to retain material in the
active littoral zone to augment shoreline building processes. This
meets the statutory and regulatory criteria to use an appropriate
location based on considerations affecting the public interest and to
locate the site to minimize interference with other activities in the
marine environment. New data collected since the proposed rule has been
included in the discussion of the general and specific site designation
criteria.
General Criteria (40 CFR 228.5)
1. Sites must be selected to minimize interference with other
activities in the marine environment, particularly avoiding areas of
existing fisheries or shellfisheries, and regions of heavy commercial
or recreational navigation (40 CFR 228.5(a)).
EPA's assessment of information available at the time of the
proposed rule demonstrated that new Site F as proposed would cause only
minimal interference with fisheries and shellfisheries and with
navigation notwithstanding the location of the site in the Coos Bay
navigation channel. This assessment has not changed with the minor
reconfiguration of the site toward the North Jetty. Most of new Site F
has been used over the past decade for dredged material disposal
pursuant to section 103 authority exercised by the Corps with EPA
concurrence and mariners in this area are accustomed to the site use.
In addition, based on a conservation recommendation from the National
Marine Fisheries Service (NMFS) resulting from an EPA consultation on
essential fish habitat, EPA will impose use restrictions at the site to
minimize the use of the site before June 1 of any year to essential
work and will encourage staggering of disposal events when juvenile
coho and Chinook salmon are holding in nearshore habitats.
2. Sites must be situated such that temporary perturbations to
water quality or other environmental conditions during initial mixing
caused by disposal operations would be reduced to normal ambient levels
or undetectable contaminant concentrations or effects before reaching
any beach, shoreline, marine sanctuary, or known geographically limited
fishery or shellfishery (40 CFR 228.5(b)).
EPA's analysis at the time of the proposed rule concluded that the
new Site F would satisfy this criterion. EPA's understanding of the
nearshore processes near the North Jetty indicates that this criterion
will continue to be met with the reconfiguration of new Site F as
finalized today. Although EPA expects some material disposed at new
Site F to reach the base of the North Jetty, normal ambient levels and
undetectable contaminant concentrations or effects would be expected
before any material reached any beach, shoreline, marine sanctuary or
known geographically limited fishery or shellfishery because of the
existing high currents and wave energy.
3. If site designation studies show that any interim disposal sites
do not meet the site selection criteria, use of such sites shall be
terminated as soon as any alternate site can be designated (40 CFR
228.5(c)).
There are no interim disposal sites near Coos Bay as defined under
the Ocean Dumping regulations. This criterion is not applicable to
today's action de-designating existing Site F and designating new Site
F.
4. The sizes of disposal sites will be limited in order to localize
for identification and control any immediate adverse impacts, and to
permit the implementation of effective monitoring and surveillance to
prevent adverse long-range impacts. Size, configuration, and location
are to be determined as part of the disposal site evaluation (40 CFR
228.5(d)).
EPA sized the proposed site to meet this criterion. The site, as
finalized in today's action, continues to meet this criterion. The
total area of new Site F is approximately 3,075.2 acres or 3.63 nm\2\.
The site tends to be moderately dispersive in the nearshore area and
tends to be less dispersive in other parts of the site. The overall
stability of the site is a significant part of the justification for
the size of the site. The original Site F experienced significant
mounding and lead to the selection of the larger site designated today.
Data collected by the Corps through bathymetric monitoring shows the
spread and movement of material placed at original Site F and suggests
that material from the original Site F did eventually disperse over the
footprint of the 103-selected site. This data also indicates that
effective monitoring and surveillance of the site has been performed
for many years. The SMMP describes the plan for management and
monitoring of the site.
5. EPA will, wherever feasible, designate ocean dumping sites
beyond the edge of the continental shelf and other such sites where
historical disposal has occurred (40 CFR 228.5(e)).
EPA's evaluation at the time of the proposed rule concluded that
long distances and travel times between the dredging locations near
Coos Bay and the continental shelf posed significant environmental,
operational, safety and environmental concerns, including risk of
encounter with endangered species and increased air emissions. This
conclusion is unchanged and new Site F, finalized by today's rule, is
consistent with this criterion.
Specific Criteria (40 CFR 228.6)
1. Geographical Position, Depth of Water, Bottom Topography and
Distance From Coast (40 CFR 228.6(a)(1))
Based on the data available at the time EPA proposed the
designation of Site F and data available from bathymetric surveys
conducted by the Corps, EPA has concluded that the geographical
position, depth of water, bottom topography and distance from the coast
of new Site F will avoid adverse effects to the marine environment.
Near the North Jetty, the new site will allow for the placement of
material that is expected to contribute material to the littoral zone
and may help decrease erosion of the jetty. Throughout most of the
shallow portions of the new site the area is dispersive. Based on EPA's
understanding of currents at the site and their influence on the
movement of material in the area this means there is a high likelihood
that material will be transported to the adjacent seafloor. The site is
located and sized to allow for long-term disposal without creation of
adverse mounding conditions.
[[Page 27401]]
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))
New Site F is not located in breeding, spawning, nursery or feeding
areas for adult or juvenile phases of living resources. The site is, or
may be, a passage area for living resources during adult or juvenile
phases. The National Marine Fisheries Service (NMFS), during
consultations with EPA in 2005 and 2006 for endangered species and for
essential fish habitat, requested that disposal at new Site F be
restricted to stagger disposal events at the new site, particularly in
the nearshore zone, to avoid continuous disposal while juveniles,
including salmon and groundfish species, are outmigrating or holding in
nearshore environments. EPA agreed to include staggered disposal in its
final SMMP. This will benefit the juveniles of concern to NMFS and will
also minimize any potential short-term localized effects to marine
organisms in the immediate vicinity of disposal events by minimizing
the creation of mounds at the site.
3. Location in Relation to Beaches and Other Amenity Areas (40 CFR
228.6(a)(3))
EPA's proposed rule concluded that the proposed site met this
criterion and EPA's conclusion is not changed today notwithstanding the
minor reconfiguration of the site toward the North Jetty. The site,
although located in the navigation channel and close to the North Jetty
is located to avoid adverse impacts to beaches and other amenity areas.
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 228.6(a)(4))
The new Site F is being designated today for the disposal of
dredged material. Disposal of other types of material will not be
allowed at this site or at any of the ocean dredged material disposal
sites at Coos Bay. Dredged material to be disposed at the new Site F
will be predominantly sand and fine-grained material. Data collected
subsequent to EPA's proposed rule included seventeen sediment samples
collected from along the length of the federal navigation channel in
Coos Bay, Isthmus Slough, and Charleston Channel in 2004 (Coos Bay
Sediment Quality Evaluation Report, March 2005). These samples were
subjected to physical and chemical analyses, which included analyses
for metals, total organic carbon, pesticides, polychlorinated biphenyls
(PCBs), phenols, phthalates, miscellaneous extractables, polynuclear
aromatic hydrocarbons (PAHs) and total and pore water organotin (TBT).
The physical analyses resulted in mean values of 1.6% gravel (0%-
10.0% range), 69.6% sand (4.0%-98.8% range), and 28.8% silt/clay (1.2%-
96.0% range) with 4.5% volatile solids (0.2%-16.7% range). The chemical
analyses indicated low levels of chemicals in some of the samples. The
results were compared with results from previous Corps sampling efforts
in 1980, 1986, 1987, 1989, 1993, 1994, 1995, and 1998. All the data are
consistent in showing that material below river mile (RM) 12 of the
Coos Bay channel is typically sand, while material above RM 12 is
typically silt. With only a few exceptions (where adjacent sources are
obvious) the sand matrix is considered low risk for contamination. The
silty areas of the estuary and river typically contain low levels of
contaminants-of-concern that have remained unchanged for many years or
appear to be improving slightly (i.e. concentrations are dropping).
Materials to be disposed of at the site must be suitable for ocean
disposal.
With respect to proposed methods of releasing material at the new
site, material will be released just below the surface from dredges
while the dredges are under power and slowly transit the site. This
method of release is expected to minimize mounding at the site and to
minimize impacts to the benthic community.
5. Feasibility of Surveillance and Monitoring (40 CFR 228.6(a)(5))
Monitoring and surveillance at new Site F is expected to be
feasible. The site is accessible for bathymetric and side-scan sonar
surveys. Most of the site has been successfully monitored by the Corps
during the Corps's use of the 103 site. It is also expected to be
feasible to monitor and survey the minor addition made to the site
through the reconfiguration toward the North Jetty. The Corps has
monitored the base of the jetty on a routine basis and during emergency
repairs made in 2002 after a failure of the jetty. The final SMMP
requires monitoring and surveillance of the new site. At a minimum,
annual bathymetric surveys will be conducted at new Site F and more
frequent surveys will be required in areas of the site that receive
dredged material. Off-site beach monitoring will also be required.
Routine monitoring will concentrate on determining how to ensure the
distribution of material in the nearshore portions of the site to
augment littoral processes and in the deeper portions of the site to
avoid or minimize mounding.
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))
At the time EPA proposed the designation of the new site, EPA
understood the dispersal patterns along the Oregon coast to generally
flow parallel to the bathymetric contours of the bottom. Local wave and
current strength and direction are impacted by the variability of the
local winds, especially in shallower water. During summer months which
make up the normal dredge and disposal season, material transport
trends southward. The trend at other times of the year is north and
northwest for currents and material transport. Re-suspension and
transport of material disposed at the site would be expected to be at a
maximum during winter months when winter storms occur and when no
active disposal is taking place at the site. Throughout the year,
material disposed in the nearshore and shallower portions of new Site F
are expected to be redistributed by existing littoral processes.
Mounding at originally designated Site F led the Corps to exercise
its authorities pursuant to Section 103 of the MPRSA to select a
significant expansion of the site and to use modeling techniques to
model placement of material within the site to avoid excessive
mounding. The originally designated Site F was generally not used for
disposal after 1989. However, it was thought that material at that
location was eroding toward the 103 selected Site F. For this reason,
the original Site F, although proposed for de-designation as a stand-
alone site, was to be incorporated into the new Site F. The movement of
material was considered to be most dispersive in the shallower zones of
the 103 site but material disposed in the deeper and less dynamic
portions of the site are redistributed across the site. Eventually, the
redistribution is expected to move the material disposed at the site to
the north and east.
Subsequent to publication of the proposed Rule in 2000, the Corps
continued to conduct annual bathymetric surveys at the 103 Site F and
to share the data collected with EPA to assess capacity at the site for
the coming year's anticipated dredging. This data tended to show that
the mound at the 1986-designated Site F was slowly eroding to its
present
[[Page 27402]]
average at below minus 60 feet mean lower low water (MLLW). This
indicates a minimum of 10 feet of material having eroded out of 1986-
designated Site F. Dredged material was placed at various locations
within the 103 Site F and monitored. Computer modeling of disposal
operations was used to determine short-term and long-term sediment fate
to design disposal units or cells. Bathymetric surveys during and
following disposals were conducted. Initial work was focused on
confirming accuracy of the models. Bathymetric changes measured by the
monitoring compared well with the changes predicted by the model. For
example, the model predicted a 2.9 foot change and monitoring measured
the actual change at 3.0 feet. The model was used to predict disposal
results in the nearshore area (i.e., along the innermost edge of the
103 Site F) and field monitoring was conducted to verify the modeled
predictions. Placement height was managed to a maximum of 3 feet during
initial disposal into 180 separate cells each sized as a 200 foot by
500 foot cell.
These bathymetric surveys show that the shallow water portion of
the site has accumulated about 1 foot of material on the bottom, with
small areas of accumulation of up to 5 feet. In the deeper portion of
the 103 site, disposals were conducted to dispose of up to 24 feet of
material at specific locations. Bathymetric monitoring indicates these
thicker disposals had eroded down to 19 feet of accumulated material on
the bottom. The surveys further show that this accumulated material is
dispersing in a northeasterly direction.
7. Existence and Effects of Current and Previous Discharges and Dumping
in the Area (Including Cumulative Effects) (40 CFR 228.6(a)(7))
Annually, approximately 1.3 million cubic yards (mcy) of material
has been disposed of at the Coos Bay designated sites, Sites E, F and
H, from dredging undertaken by the Corps to maintain the navigation
channel. The Coos Bay sites were used consistently prior to their
designations in 1986. Sites E and F were not used after the late
eighties because of mounding concerns. As discussed above, the mounds
at those sites have been eroding over time. Originally designated Site
F was recently used by the Corps for the disposal of dredged material
to maintain safe navigation in the navigation channel. This site, which
is de-designated by today's rule as a stand-alone site, is incorporated
into the footprint of the new Site F. EPA's evaluation of data and
modeling results indicates that past disposal operations at these sites
and current operations have not resulted in unacceptable environmental
degradation. Adverse effects are not expected to result from the minor
reconfiguration of the site toward the North Jetty. EPA expects that
portion of the site to benefit the nearshore environment.
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 site is not expected to interfere with shipping, fishing,
recreation or other legitimate uses of the ocean. Commercial crabbing,
which was referenced in EPA's proposed rule as an activity occurring in
the nearshore, is not expected to be impacted by the minor
reconfiguration of new Site F. Disposals at the new site will be
managed through the SMMP to minimize interference with other legitimate
uses of the ocean through careful timing and staggering of disposals in
the nearshore portion of the new site.
9. The Existing Water Quality and Ecology of the Sites as Determined by
Available Data or Trend Assessment of Baseline Surveys (40 CFR
228.6(a)(9))
At the time of EPA's proposed rule in 2000, EPA had not identified
any adverse water quality impacts from ocean disposal of dredged
material at originally designated Site F or at 103 selected Site F. In
2004, the Corps released a report titled ``Comparison of SPI Data and
STFATE Simulation Results at Coos Bay, OR ODMDS Site `F','' which
provided some verification of numerical models used to predict the
behavior of disposed material on water quality and ecology of the site.
The samples, i.e. sediment profile images, indicated some important
characteristics about the native sediments and dredged sediments
disposed of at the site. Native sediment in the shallow and
intermediate water portions of the site did not show a layer of fine
grained material at the sediment-water interface. This absence
indicates that burrowing infauna were absent or extremely limited in
the area. This finding was not unexpected because the intermediate/
shallow water locations within the site are heavily dominated by wave-
current action which forces repeated and routine resuspension of
sediment. The report found that ``the effects on initial disposal on
benthic marine life in these areas are likely minimal.'' By contrast,
the deeper portion of the site did indicate the presence of benthic
infaunal activity. In addition to the sediment profile imaging (SPI), a
plan-view video was also produced. Crabs, shrimp, and flatfish were all
seen on the video; however, no inferences were made as to population.
Biological activity and reworking of the surface sediments by natural
forces was indicated in the imaging but it was not possible to
penetrate the sandy substrate to measure the full thickness of the
deposited material at the site.
10. Potentiality for the Development or Recruitment of Nuisance Species
in the Disposal Site (40 CFR 228.6(a)(10))
In its proposed rule, EPA stated that nuisance species had not been
observed at the existing Coos Bay sites in over ten years of monitoring
and that EPA did not expect there to be a significant potential for the
development or recruitment of nuisance species in the proposed site.
That statement was based in part on the lack of organic material
disposed at the site. Subsequent to EPA's proposed rule, however,
circumstances at designated Site H have caused that site to be closed
at present and the potential for organic material to be disposed of at
new Site F has increased. Organic material is generally found above RM
12 in the Coos Bay Channel and is likelier than material below RM12 to
be more attractive to nuisance species. While there is the potential
for the development or recruitment of nuisance species where dredged
material from above RM12 might be disposed of at the new Site F, this
potential remains low. The SMMP will provide for monitoring of the new
site to help ensure that nuisance species are not recruited to and do
not develop at the new site.
11. Existence at or in Close Proximity to the Site of Any Significant
Natural or Cultural Feature of Historical Importance (40 CFR
228.6(a)(11))
EPA stated in its proposed rule that no cultural features of
historical importance had been identified at or near the proposed site.
This continues to be the case. The new Site F is located over 7 statute
miles southwest of the Oregon Dunes National Recreation Area, a
significant natural feature, but is not considered to be in close
proximity to that feature. The new site is located approximately 3
statute miles northeast of three Oregon state parks: Shore Acres State
Park, Cape Arago State Park and Sunset Bay State Park. The new site is
not considered to be in proximity to these areas. The national historic
landmark, located near Cape Arago State Park, over 4 statute miles
south of the new site, is not within the proximity of
[[Page 27403]]
the site. Impacts to significant natural or cultural features have not
been identified.
e. National Environmental Policy Act (NEPA); Magnuson-Stevens Act
(MSA); Coastal Zone Management Act (CZMA); Endangered Species Act (ESA)
1. NEPA
Section 102 of the National Environmental Policy Act of 1969, 42
U.S.C. 4321, et seq., (NEPA) 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. NEPA does not apply to EPA designations of ocean
disposal sites under the MPRSA as EPA has made clear in EPA's ``Notice
of Policy and Procedures for Voluntary Preparation of NEPA Documents,''
63 FR 58045 (October 29, 1998). EPA did voluntarily cooperate with the
U.S. Army Corps of Engineers (Corps) as a cooperating agency on the
Feasibility Report on Navigation Improvements with Environmental Impact
Statement (EIS) prepared in 1994. As discussed in the proposed rule, 63
FR 17240 (March 31, 2000), the EIS provided documentation to support
the final designation of the proposed Site F. EPA did not see a need to
supplement the EIS to address the minor reconfiguration of the new Site
F which is finalized in today's designation.
2. MSA
In the fall of 2005, EPA consulted with the National Marine
Fisheries Service (NMFS) concerning essential fish habitat. EPA
prepared an essential fish habitat (EFH) assessment pursuant to section
305(b) of the Magnuson-Stevens Act, as amended (MSA), 16 U.S.C.
1855(b). NMFS reviewed EPA's action and issued six non-binding
conservation recommendations. EPA accepted three of the
recommendations. The three accepted by EPA included: Using the best
relevant analytical methods in sampling and analysis plans included in
the final SMMP; limiting site use before June 1 and staggering disposal
events during nearshore holding and outmigration of juvenile salmon;
and provisions to provide the results of bathymetric monitoring to
NMFS. EPA incorporated these recommendations into the final SMMP.
EPA did not accept the remaining three recommendations. These
recommendations asked EPA to develop and implement studies to collect
information to better inform agencies on species presence and use in
the disposal area, in areas that might be designated in the future, and
for all existing ocean disposal sites in Oregon. EPA did not accept
these recommendations because EPA did not find that the collection of
information as recommended by NMFS constituted measures for ``avoiding,
mitigating, or offsetting the impact'' of the Federal action on
essential fish habitat.
3. CZMA
EPA consulted with the state of Oregon on coastal zone management
issues. EPA prepared a consistency determination for the Oregon Ocean
and Coastal Management Program (OCMP) to address consistency
determinations required by the Coastal Zone Management Act, 16 U.S.C.
1446. The Oregon Department of Land Conservation and Development (DLCD)
reviewed the consistency determination and concurred with EPA that the
action is consistent with the OCMP to the maximum extent practicable
basing its findings on the certification EPA provided.
4. ESA
EPA also consulted with NMFS and the U.S. Fish and Wildlife Service
on its action to de-designate existing Site F and to designate new Site
F finding that the action would not be likely to adversely affect
aquatic or wildlife species listed as endangered pursuant to the
Endangered Species Act, 16 U.S.C. 1531 to 1544, (ESA), or the critical
habitat of such species. EPA found that site designation does not have
a direct impact on any of the identified ESA species but also found
that indirect impacts had to be considered. These indirect impacts
included a short-term increase in suspended solids and turbidity in the
water column when dredged material was disposed at the new site and an
accumulation of material on the ocean floor when material was disposed
at the site. EPA concluded that while its action may affect ESA-listed
species, the action would not be likely to adversely affect ESA-listed
species.
The U.S. Fish and Wildlife Service concurred with EPA's conclusion
based on its finding that ``abundant suitable foraging habitat
throughout the area'' for birds of concern would be available during
disposal activities, i.e. site use, and that minor behavioral changes,
such as foraging in areas other than the designated site, would be
temporary. NMFS concurred with EPA's findings for ESA-listed marine
mammals, sea turtles, and southern Oregon/northern California coho
salmon, finding that the new site was not designated as critical
habitat for any of those species. NMFS did not agree with EPA's
conclusions for Oregon Coast coho salmon and requested additional
consultation. Subsequent to that request, NMFS announced that it was
withdrawing its proposal to list Oregon Coast coho salmon as
endangered. The ESA consultation concluded with the withdrawal of the
NMFS proposal to list Oregon Coast coho salmon and NMFS addressed
Oregon Coast coho salmon in the EFH consultation.
3. Response to Comment
No public comments on the proposed designation were received;
however, a letter from the Oregon Department of Environmental Quality
(ODEQ) pointed out the need for improved coordination procedures
between the EPA, the Corps, ODEQ's central office and ODEQ's Coos Bay
field office for dredging projects in the vicinity of Coos Bay. EPA
generally supports improved coordination between federal and state
agencies. Coordination will be a priority for EPA at the new site to
ensure that disposal activities by the Corps and by local port
authorities are aware of site restrictions and are adhering to the
SMMP.
4. Statutory and Executive Order Reviews
This rule finalizes the de-designation of an existing ocean dredged
material disposal site, existing Site F, and designates a new ocean
dredged material disposal site, new Site F. This rule complies with
applicable executive orders and statutory provisions as follows:
a. Executive Order 12866
Under Executive Order 12866 (58 FR 51735, October 4, 1993), the
Agency 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: (1) 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; (2) create a serious
inconsistency or otherwise interfere with an action taken or planned by
another agency; (3) materially alter the budgetary impact of
entitlements, grants, user fees, or loan programs, or the rights and
obligations of recipients thereof; or (4) raise novel legal or policy
issues arising out of legal mandates, the President's priorities, or
[[Page 27404]]
the principles set forth in the Executive Order. It has been determined
that this final action, which simultaneously de-designates an existing
ocean dredged material disposal site and designates a new site, Site F,
is not a significant regulatory action under Executive Order 12866 and
is therefore not subject to OMB review.
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.,
because this final action does not establish or modify any information
or recordkeeping requirements for the regulated community.
Burden means the total time, effort, or financial resources
expended by persons to generate, maintain, retain, or disclose or
provide information to or for a Federal agency. This includes the time
needed to review instructions; develop, acquire, install, and utilize
technology and systems for the purposes of collecting, validating, and
verifying information, processing and maintaining information, and
disclosing and providing information; adjust the existing ways to
comply with any previously applicable instructions and requirements;
train personnel to be able to respond to a collection of information;
search data sources; complete and review the collection of information;
and transmit or otherwise disclose the information.
An agency may not conduct or sponsor, and a person is not required
to respond to a collection of information unless it displays a
currently valid OMB control number. The OMB control numbers for EPA's
regulations in 40 CFR are listed in 40 CFR part 9.
c. Regulatory Flexibility
The Regulatory Flexibility Act (RFA), as amended by the Small
Business Regulatory Enforcement Fairness Act (SBREFA), 5 U.S.C. 601, et
seq., generally requires federal agencies to prepare a final regulatory
flexibility analysis whenever the agency promulgates a final 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. Small entities include small
businesses, small organizations, and small governmental jurisdictions.
For purposes of assessing the impacts of today's rule on small
entities, small entity is defined as: (1) A small business defined by
the Small Business Administration's Size Regulations at 13 CFR 121.201;
(2) a small governmental jurisdiction that is a government of a city,
county, town, school district or special district with a population of
less than 50,000; and (3) a small organization that is any not-for-
profit enterprise which is independently owned and operated and is not
dominant in its field. EPA has determined that this action will not
have a significant economic impact on small entities because the final
action regulates the location of sites to be used for the disposal of
dredged materials in ocean waters. After considering the economic
impacts of today's final action on small entities, I certify that this
action will not have a significant impact on a substantial number of
small entities directly regulated by this action.
d. Unfunded Mandates Reform Act
Title II of the Unfunded Mandates Reform Act (UMRA) of 1995 (Pub.
L. 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
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 why the
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, enabling
officials of 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. Today's action contains no Federal mandates (under the
regulatory provisions of Title II of the UMRA) for State, local or
tribal governments or the private sector. It imposes no new enforceable
duty on any State, local or tribal governments or the private sector.
Similarly, EPA has also determined that this action contains no
regulatory requirements that might significantly or uniquely affect
small government entities. Thus, today's action is not subject to the
requirements of sections 202 and 203 of the UMRA.
e. 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
action 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 action will be effective June 12, 2006.
f. Executive Order 13132: Federalism
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'' are 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 various levels of government.'' This action 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 various levels of government, as specified in
Executive Order 13132. This action addresses the designation and de-
designation of sites near the mouth of Coos Bay, Oregon. Thus,
Executive Order 13132 does not apply to this action.
[[Page 27405]]
g. Executive Order 13175: Consultation and Coordination With Indian
Tribal Governments
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 action does not have
tribal implications, as specified in Executive Order 13175. Thus,
Executive Order 13175 does not apply to this action.
h. Executive Order 13045: Protection of Children From Environmental
Health and Safety Risks
Executive Order 13045 applies to any rule that: (1) Is determined
to be ``economically significant'' as defined under Executive Order
12866, and (2) concerns an environmental health or safety risk that EPA
has reason to believe may have a disproportionate effect on children.
If the regulatory action meets both criteria, the Agency 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 the Agency. This action is not subject to Executive Order 13045
because it is not economically significant as defined in Executive
Order 12866 and because the Agency does not have reason to believe the
environmental health or safety risks addressed by this action present a
disproportionate risk to children. The action concerns the designation
and de-designation of ocean disposal sites and would only have the
effect of providing designated locations to use for ocean disposal of
dredged material pursuant to section 102(c) of the MPRSA.
i. Executive Order 13211: Actions That Significantly Affect Energy
Supply, Distribution, or Use
This action 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'' as defined under Executive Order
12866.
j. National Technology Transfer and Advancement Act
Section 12(d) of the National Technology Transfer and Advancement
Act of 1995 (``NTTAA''), Public Law 104-113, section 12(d) (15 U.S.C.
272) directs EPA to use voluntary consensus standards in its regulatory
activities unless to do 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 to
Congress, through the OMB, explanations when the Agency decides not to
use available and applicable voluntary consensus standards. Although
EPA stated that the proposed action did not directly involve technical
standards, the proposed action and today's final action include
environmental monitoring and measurement as described in EPA's SMMP.
EPA will not require the use of specific, prescribed analytic methods
for monitoring and managing the designated sites. Rather, the Agency
plans to allow the use of any method, whether it constitutes a
voluntary consensus standard or not, that meets the monitoring and
measurement criteria discussed in the final SMMP.
k. Executive Order 12898: Federal Actions To Address Environmental
Justice in Minority Populations and Low Income Populations
To the greatest extent practicable and permitted by law, and
consistent with the principles set forth in the report on the National
Performance Review, each Federal agency must make achieving
environmental justice part of its mission by identifying and
addressing, as appropriate, disproportionately high and adverse human
health and environmental effects of its programs, policies, and
activities on minority populations and low-income populations in the
United States and its territories and possessions, the District of
Columbia, the Commonwealth of Puerto Rico, and the Commonwealth of the
Mariana Islands. Because this action addresses ocean disposal site
designations (away from inhabited land areas), no significant adverse
human health or environmental effects are anticipated. The action is
not subject to Executive Order 12898 because there are no anticipated
significant adverse human health or environmental effects.
List of Subjects in 40 CFR Part 228
Environmental protection, Water pollution control.
Authority: This action is issued under the authority of section
102 of the Marine Protection, Research, and Sanctuaries Act, as
amended, 33 U.S.C. 1401, 1411, 1412.
Dated: April 28, 2006.
L. Michael Bogert,
Regional Administrator, Region 10.
0
For the reasons set out in the preamble, Chapter I of title 40 is
amended as set forth below:
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 revising paragraphs (n)(4)(i), (ii),
(iii), (iv), (v), and (vi) to read as follows:
Sec. 228.15 Dumping sites designated on a final basis.
* * * * *
(n) * * *
(4) * * *
(i) Location: 43[deg]22'54.8887'' N, 124[deg]19'28.9905'' W;
43[deg]21'32.8735'' N, 124[deg]20'37.7373'' W; 43[deg]22'51.4004'' N,
124[deg]23'32.4318'' W; 43[deg]23'58.4014'' N, 124[deg]22'35.4308'' W
(NAD 83).
(ii) Size: 4.45 kilometers long and 2.45 kilometers wide.
(iii) Depth: Ranges from 6 to 51 meters.
(iv) Primary Use: Dredged material determined to be suitable for
ocean disposal.
(v) Period of Use: Continuing Use.
(vi) Restriction: Disposal shall be limited to dredged material
determined to be suitable for unconfined disposal; Disposal shall be
managed by the restrictions and requirements contained in the
currently-approved Site Management and Monitoring Plan (SMMP);
Monitoring, as specified in the SMMP, is required.
* * * * *
[FR Doc. 06-4286 Filed 5-10-06; 8:45 am]
BILLING CODE 6560-50-P