Establishment of Marine Reserves and a Marine Conservation Area Within the Channel Islands National Marine Sanctuary, 29208-29235 [E7-10096]
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Federal Register / Vol. 72, No. 100 / Thursday, May 24, 2007 / Rules and Regulations
DEPARTMENT OF COMMERCE
National Oceanic and Atmospheric
Administration
15 CFR Part 922
50 CFR Part 660
[Docket No. 0612242956–7123–01]
RIN 0648–AT18
Establishment of Marine Reserves and
a Marine Conservation Area Within the
Channel Islands National Marine
Sanctuary
National Marine Sanctuary
Program (NMSP), National Ocean
Service (NOS) and National Marine
Fisheries Service (NOAA Fisheries),
National Oceanic and Atmospheric
Administration (NOAA), Department of
Commerce (DOC).
ACTION: Final rule.
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AGENCY:
SUMMARY: On August 11, 2006 NOAA
issued a notice of proposed rulemaking
to establish a network of marine zones
within the state and federal waters of
the Channel Islands National Marine
Sanctuary (CINMS or Sanctuary). State
waters in the Sanctuary extend from the
shoreline of the islands to
approximately 3 nautical miles from
shore. Federal waters of the Sanctuary
extend from the offshore extent of state
waters to the Sanctuary’s outer
boundary. In this final rule, NOAA is
issuing final regulations for the federalwaters portion of the Sanctuary. NOAA
has decided to defer a final decision and
seeking additional comment on the
state-waters portion of the Sanctuary
pending action by the State of California
to extend the boundaries of several
existing state-waters zones to the three
mile state-federal-waters boundary.
Marine zones are discrete areas that
have special regulations differing from
the regulations that apply throughout or
above the Sanctuary as a whole. The
purpose of these zones within the
federal waters of the Sanctuary is to
further the protection of Sanctuary
biodiversity and complement an
existing network established by the
State of California in October 2002, and
implemented in April 2003, under its
authorities. Two types of zones are
being established by this action: Marine
reserves and marine conservation areas.
All extractive activities (e.g., removal of
any Sanctuary resource) and injury to
Sanctuary resources are prohibited in all
marine reserves. Commercial and
recreational lobster fishing and
recreational fishing for pelagic species
are allowed within the marine
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conservation area, while all other
extraction and injury are prohibited.
This action establishes approximately
110.5 square nautical miles of marine
reserves and 1.7 square nautical miles of
marine conservation area in the federal
waters of the Sanctuary. As part of this
action, NOAA is also modifying the
terms of designation for the Sanctuary,
which were originally published on
October 2, 1980 (45 FR 65198), to allow
for the regulation of extractive activities,
including fishing, in marine reserves
and marine conservation areas, and a
slight modification to the outer
boundary of the CINMS.
DATES: Pursuant to section 304(b) of the
National Marine Sanctuaries Act
(NMSA), 16 U.S.C. 1434(b), the revised
terms of designation and this final rule
shall take effect and become final after
the close of a review period of 45 days
of continuous session of Congress,
beginning on the day on which this
document is published in the Federal
Register. Announcement of the effective
date of this final rule will be published
in the Federal Register at a later date.
Public comments on the state-waters
portion of this rulemaking must be
received by July 23, 2007.
ADDRESSES: Copies of the final
environmental impact statement,
regulatory impact review, and final
regulatory flexibility analyses may be
obtained from NOAA’s Channel Islands
National Marine Sanctuary Web site at
https://channelislands.noaa.gov/ or by
writing to Sean Hastings, Resource
Protection Coordinator, Channel Islands
National Marine Sanctuary, 113 Harbor
Way, Suite 150, Santa Barbara, CA
93109; e-mail: Sean.Hastings@noaa.gov.
You may submit comments on the
state-waters portion of this rulemaking
by any of the following methods:
• E-mail:
CINMSReserves.FEIS@noaa.gov. Include
in the subject line the following
document identifier: Marine reserves in
CINMS.
• Federal e-Rulemaking Portal: https://
www.regulations.gov. Follow the
instructions for submitting comments.
• Mail: Sean Hastings, Channel
Islands National Marine Sanctuary, 113
Harbor Way, Suite 150, Santa Barbara,
CA 93109.
FOR FURTHER INFORMATION CONTACT:
Sean Hastings, (805) 884–1472; e-mail:
Sean.Hastings@noaa.gov.
SUPPLEMENTARY INFORMATION:
I. Background
A. Channel Islands National Marine
Sanctuary
The CINMS area is approximately
1,113 square nautical miles adjacent to
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the following islands and offshore rocks:
San Miguel Island, Santa Cruz Island,
Santa Rosa Island, Anacapa Island,
Santa Barbara Island, Richardson Rock,
and Castle Rock (collectively the
Channel Islands), extending seaward to
a distance of approximately 6 nautical
miles. NOAA designated the CINMS in
1980 to protect the area’s rich and
diverse range of marine life and
habitats, unique and productive
oceanographic processes and
ecosystems, and culturally significant
resources (see 45 FR 65198). The
Sanctuary was designated pursuant to
NOAA’s authority under the National
Marine Sanctuaries Act (NMSA; 16
U.S.C. 1431 et seq.). There are
significant human uses in the Sanctuary
as well, including commercial and
recreational fishing, marine wildlife
viewing, boating and other recreational
activities, research and monitoring
activities, numerous educational
activities, and maritime shipping.
The waters surrounding California’s
Channel Islands represent a globally
unique and diverse assemblage of
habitats and species. This region is a
subset of the larger ecosystem of the
Southern California Bight, an area
bounded by Point Conception in the
north and Punta Banda, Mexico in the
south. In the area between Santa Barbara
Island in the south and San Miguel
Island in the northwest, the colder
waters of the Oregonian oceanic
province in the north converge and mix
with the warmer waters of the
Californian oceanic province. Each of
these two provinces has unique oceanic
conditions and species assemblages,
which in turn are parts of distinct
biogeographic regions. The mixing of
these two provinces in the vicinity of
the Channel Islands creates a transition
zone within the island chain. Upwelling
and ocean currents in the area create a
nutrient rich environment that supports
high species and habitat diversity.
In the Southern California Bight,
marine resources have declined under
pressure from a variety of factors,
including commercial and recreational
fishing, changes in oceanographic
˜
conditions associated with El Nino and
other large-scale oceanographic cycles,
introduction of disease, and increased
levels of pollutants. The urbanization of
southern California has significantly
increased the number of people visiting
the coastal zone. The burgeoning coastal
population has greatly increased the
influx of human, industrial, and
agricultural wastes to California coastal
waters. Population growth has also
increased human demands on the
ocean, including commercial and
recreational fishing, wildlife viewing
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and other activities. New technologies
have increased the yield of sport and
commercial fisheries. Many former
natural refuges for targeted species, such
as submarine canyons, submerged
pinnacles, deep waters, and waters
distant from harbors, can now be
accessed due to advancements in fishing
technology and increased fishing effort.
The significant changes in ecological
conditions resulting from the array of
human activities in the Channel Islands
region are just beginning to be
understood. For example, many kelp
beds have converted to urchin barrens,
where urchins and coralline algae have
replaced kelp as the dominant feature.
Deep canyon and rock areas that were
formerly rich rockfishing grounds have
significantly reduced populations of
larger rockfish such as cowcod and
bocaccio.
In the Southern California Bight,
commercial and recreational fisheries
target more than 100 fish species and
more than 20 invertebrate species.
Targeted species have exhibited high
variability in landings from year to year
(e.g., squid) and in several cases have
declined to the point that the fishery has
had to be shut down (e.g., abalone).
Many targeted species are considered
overfished and one previously targeted
species (white abalone) is listed as
endangered. Excessive bycatch has
caused declines of some non-targeted
species. The removal of species that
play key ecological roles, such as
predatory fish, has altered ecosystem
structure. Some types of fishing gear
have caused temporary or permanent
damage to marine habitats. The
combination of direct take, bycatch,
indirect effects, and habitat damage and
destruction has contributed to a
negative transformation of the marine
environment around the Channel
Islands.
B. Marine Zoning
For over twenty years, NOAA has
used marine zoning as a tool in specific
national marine sanctuaries to address a
wide array of resource protection and
user conflict issues. Marine zones are
discrete areas within or above a national
marine sanctuary that have special
regulations that differ from the
regulations that apply throughout or
above the sanctuary as a whole. For
example, marine zones are used to
regulate the use of motorized personal
watercraft in the Monterey Bay National
Marine Sanctuary. Marine zones,
including areas where all extraction is
prohibited, have also been established
in the Florida Keys National Marine
Sanctuary to provide for varying levels
of resource protection.
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NOAA has used zoning within the
CINMS since its original designation in
1980. For example, the CINMS
regulations prohibit:
1. Cargo vessels from coming within
1 nautical mile of any island in the
CINMS;
2. disturbance of marine mammals or
seabirds by flying aircraft below 1,000
feet within 1 nautical mile of any island
within the CINMS; and
3. construction upon or drilling into
the seabed within 2 nautical miles of
any island in the CINMS.
In addition to NOAA, other federal
and state agencies have also established
marine zones wholly or partially within
the Sanctuary (e.g., California
Department of Fish and Game, National
Park Service). In 1978, commercial and
recreational fishing was prohibited by
the State of California in one small
marine protected area of the Channel
Islands, the Anacapa Island Ecological
Reserve. The International Maritime
Organization has designated a voluntary
vessel traffic separation scheme to guide
large vessel traffic running through the
Santa Barbara Channel. The National
Park Service (NPS) has established
several zoned areas within the Channel
Islands National Park for different
public uses, principally to protect
seabird colonies and marine mammal
haul outs. More recently, the NPS is
instituting a new zoning approach to
managing park lands, coasts, and
adjacent waters.
Due to historic lows in the stocks of
certain rockfish (e.g., cowcod and
bocaccio), in 2001 the Pacific Fishery
Management Council (PFMC) took
emergency action and established large
bottom closures to rebuild these stocks.
NOAA implemented the Cowcod
Conservation Area regulations on
January 1, 2001 (66 FR 2338) and the
Rockfish Conservation Area emergency
regulations on September 13, 2002 (67
FR 57973). The Cowcod Conservation
Area and the California Rockfish
Conservation Area partially overlay
Sanctuary waters. Finally, in 2002, the
California Fish and Game Commission
(FGC) authorized the establishment of
marine reserves and marine
conservation areas within the state
waters of the Sanctuary that prohibit or
limit the take of living, geological or
cultural marine resources.
C. Marine Reserves
The number of documented
successful examples of no-take marine
reserves is growing, providing
substantial evidence that rapid increases
in biomass, biodiversity, abundance and
size of organisms usually result from
their designation. Increased
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biodiversity, abundance, and habitat
quality within closed areas generally
improve the resiliency and ability of
marine ecosystems to adapt to ongoing
human-caused or natural disturbance,
such as climate shifts, major storm
damage, and pollution.
The designation of marine reserves
can also reinforce traditional fish
management approaches to substantially
reduce overall fishery impacts to the
ecosystem. Traditional management,
like controls on fishery catch and effort,
may fail due to factors such as stock
assessment errors, inadequate
institutional frameworks, and
uncertainty. Marine reserves can help to
rebuild depleted populations, reduce
bycatch and discards, and reduce
known and as-yet-unknown ecosystem
effects of fishing. In addition, marine
reserves offer scientists and resource
managers a controlled opportunity to
study the influence of change on marine
ecosystems in the absence of direct
human disturbance.
D. Channel Islands Marine Reserves
Process, Community Phase 1999–2001
The NMSA requires NOAA to
periodically review the management
plan and regulations for each national
marine sanctuary and to revise them, as
necessary, to fulfill the purposes and
policies of the NMSA (16 U.S.C.
1434(e)). NOAA began the process to
review the CINMS management plan
and regulations in 1999. Through the
scoping process, many members of the
public voiced concern over the state of
biodiversity in the CINMS and called for
fully protected (i.e., no-take) zones to be
established.
In 1998, the Commission received a
recommendation from a local
recreational fishing group to create
marine reserves around the northern
Channel Islands as a response to
declining fish populations. In response
to concerns about changes in the
ecosystem and comments raised to the
Commission and during the CINMS
management plan scoping process,
NOAA and the California Department of
Fish and Game (CDFG) developed a
Federal-state partnership to consider the
establishment of marine reserves in the
Sanctuary.
Since the marine reserves process is
inherently complex, and is a standalone action that is programmatically
independent of and severable from the
more general suite of actions
contemplated in the management plan
review process, NOAA decided to
separate the process to consider marine
reserves from the larger CINMS
management plan review process. The
draft management plan and DEIS for the
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management plan review were released
for public comment on May 19, 2006 (71
FR 29148). NOAA also published a
proposed rule to implement the
management plan on May 19, 2006 (71
FR 29096). Please see https://
channelislands.noaa.gov for more
information.
The CINMS Advisory Council, a
federal advisory board of local
community representatives and federal,
state and local government agency
representatives, created a multistakeholder Marine Reserves Working
Group (MRWG) to seek agreement on a
recommendation regarding the potential
establishment of marine reserves within
the Sanctuary. The CINMS Advisory
Council also designated a Science
Advisory Panel of recognized experts
and a NOAA-led Socio-economic Team
to support the MRWG in its
deliberations.
Extensive scientific, social, and
economic data were collected in support
of the marine reserves assessment
process. From July 1999 to May 2001,
the MRWG met monthly to receive,
weigh, and integrate advice from
technical advisors and the public. The
MRWG reached consensus on a set of
ground rules, a mission statement, a
problem statement, a list of species of
interest, and a comprehensive suite of
implementation recommendations. The
MRWG found that in order to protect,
maintain, restore, and enhance living
marine resources, it is necessary to
develop new management strategies that
encompass an ecosystem perspective
and promote collaboration between
competing interests. A set of goals were
also agreed upon by the MRWG:
1. To protect representative and
unique marine habitats, ecological
processes, and populations of interest.
2. To maintain long-term
socioeconomic viability while
minimizing short-term socioeconomic
losses to all users and dependent
parties.
3. To achieve sustainable fisheries by
integrating marine reserves into
fisheries management.
4. To maintain areas for visitor,
spiritual, and recreational opportunities
which include cultural and ecological
features and their associated values.
5. To foster stewardship of the marine
environment by providing educational
opportunities to increase awareness and
encourage responsible use of resources.
The MRWG developed over 40
different designs for potential marine
reserves and evaluated the ecological
value and potential economic impact of
each design. To do so, members of the
MRWG contributed their own expertise
to modify designs or generate
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alternatives and utilized a geospatial
tool, known as the Channel Islands
Spatial Support and Analysis Tool (CISSAT). CI-SSAT provided opportunities
for visualization, manipulation, and
analysis of data for the purpose of
designing marine reserves.
After months of deliberation, a
consensus design could not be reached
and the MRWG selected two designs to
represent the diverse views of the group.
These designs depict the best effort that
each MRWG representative could
propose. Ultimately, the CINMS
Advisory Council provided the MRWG’s
two designs, as well as all of the
supporting information developed
during the process, including
background scientific and economic
information, to NOAA and the CDFG for
consideration and action.
Based on this information and
additional internal agency analysis,
NOAA and the CDFG crafted a draft
reserve network and sent it to the
CINMS Advisory Council and the
former MRWG, Science Panel and
Socio-Economic Team members seeking
further input. The draft reserve network
was also published in local papers and
on the CINMS Web site to solicit input
from the general public. Several
meetings were held with constituent
groups, including the CINMS Advisory
Council’s Conservation Working Group,
Fishing Working Group and Ports and
Harbors Working Group, to discuss the
draft network. Following this period of
input, the CDFG and NOAA prepared a
recommendation for establishing a
network of marine reserves and marine
conservation areas. The
recommendation proposed a network of
marine reserves and marine
conservation areas in the same general
locations as the MRWG Composite Map.
The composite map was forwarded to
the CINMS Advisory Council and
represented two versions of a reserve
and conservation area network, one
version from consumptive interests and
the other from non-consumptive
interests. These two versions were
overlaid on one map, and depicted a
number of areas that the constituent
groups agreed upon. This
recommendation became the basis for
the preferred alternative in the State’s
California Environmental Quality Act
(CEQA) environmental review process.
E. Establishment of State Reserves in the
CINMS, 2001 to 2003
Due to the fact that the proposed
network spanned both state and federal
waters, NOAA and the CDFG
determined the implementation of the
recommendation would need to be
divided into a state phase and a federal
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phase. State waters extend from the
shore to a distance of three nautical
miles. Federal waters extend beyond the
limit of state waters to the extent of the
exclusive economic zone, with the outer
boundary of the CINMS at a distance of
approximately six nautical miles from
shore. The state phase was to be
considered by the Commission under its
authorities.
The CDFG completed an
environmental review under the
requirements of CEQA resulting in the
publication of an environmental
document. The draft environmental
document (ED) was released for public
comment on May 30, 2002. Comments
were accepted for an extended period
until September 1, 2002. The
Commission and CDFG received 2,492
letters, e-mails and oral comments. Of
this total, 2,445 were form letters that
made identical comments.
The Commission certified the final ED
on October 23, 2002. At this same
meeting, the Commission approved the
CDFG’s preferred alternative. The CDFG
published final regulations for its action
in January 2003. As part of its
implementation, the FGC acknowledged
the need for NOAA to complete the
network by extending the marine zones
into the deeper and federal waters of the
CINMS.
F. Federal Marine Reserves Process,
2003–2007
Following the publication of the
CDFG’s final regulations in 2003,
NOAA’s NMSP initiated the federal
marine reserves process, and hosted
scoping meetings with the general
public, the CINMS Advisory Council,
and PFMC. In 2004, the NMSP released
a preliminary environmental document
with a range of alternatives for public
review. In 2005, the NMSP consulted
with local, state, and federal agencies
and the PFMC on possible amendments
to the CINMS designation document
pursuant to section 303(b)(2) of the
NMSA (16 U.S.C. 1433(b)(2)). In
addition, in 2005 the NMSP provided
the PFMC with the opportunity to
prepare draft NMSA fishing regulations
pursuant to section 304(a)(5) of the
NMSA (16 U.S.C. 1434(a)(5)) for the
potential establishment of marine
reserves and marine conservation areas.
In its response to NOAA’s letter
regarding draft NMSA fishing
regulations, the PFMC stated its support
for NOAA’s goals and objectives for
marine zones in the CINMS but
recommended that NOAA issue fishing
regulations under the MagnusonStevens Fishery Conservation and
Management Act (MSA) and the
relevant authorities of the states of
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California, Oregon, and Washington
rather than under the NMSA. To that
end, and in accordance with advice
from the NOAA Administrator in his
October 19, 2005 letter to the PFMC, the
PFMC recommended the Channel
Islands marine zones in federal waters
be designated as Essential Fish Habitat
and Habitat Areas of Particular Concern
with corresponding management
measures to prohibit the use of bottom
contact gear under Amendment 19 of
the Groundfish Fishery Management
Plan. To complete the process of
addressing closure of the remaining
aspect of the marine zones (i.e., in the
water column) the PFMC stated its
intent to pursue those closures through
other fishery management plan
authorities and complementary state
laws.
NOAA reviewed the PFMC’s
recommendations and determined that
they did not have the specificity or
record to support the use of the MSA or
state laws to establish limited take or
no-take zones in the water column and
thereby did not fulfill NOAA’s goals and
objectives for these marine zones in the
CINMS. However, Amendment 19 to the
Groundfish Fishery Management Plan
implemented, in part, the proposed
marine zones by prohibiting all bottom
contact gear in the proposed zones.
Accordingly, the NMSA regulations
issued in this rule prohibit the take of
resources from the zones not prohibited
by the Amendment 19 regulations.
Thus, along with the regulations
implementing Amendment 19, the
NMSA regulations establish
comprehensive limited-take and no-take
zones in the CINMS in a manner that
fulfills NOAA’s goals and objectives for
these marine zones in the CINMS.
As stated in the summary, the
purpose of these zones is to further the
protection of Sanctuary biodiversity and
complement an existing network
established by the State of California in
October 2002, and implemented in
April, 2003, under its authorities. The
goals of the zones are:
• To ensure the long-term protection
of Sanctuary resources by restoring and
enhancing the abundance, density,
population age structure, and diversity
of the natural biological communities.
• To protect, restore, and maintain
functional and intact portions of natural
habitats (including deeper water
habitats), populations, and ecological
processes in the Sanctuary.
• To provide, for research and
education, undisturbed reference areas
that include the full spectrum of
habitats within the CINMS where local
populations exhibit a more natural
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abundance, density, diversity, and age
structure.
• To set aside, for intrinsic and
heritage value, representative habitats
and natural biological communities.
• To complement the protection of
CINMS resources and habitats afforded
by the State of California’s marine
reserves and marine conservation areas.
• To create models of and incentives
for ways to conserve and manage the
resources of CINMS.
On August 11, 2006 NOAA issued a
notice of proposed rulemaking (71 FR
46134) to prohibit the take of resources
from the zones not prohibited by the
Amendment 19 regulations. NOAA
subsequently issued a correction to this
notice on October 5, 2006 (71 FR 58767)
to correct certain figures presented on
the size of the Sanctuary.
Between August and October of 2006,
NOAA received public comments and
held two hearings on the proposed rule.
Over 30,000 individuals submitted
written comments and/or presented oral
testimony on NOAA’s proposal. 99% of
these individuals supported the
establishment of marine zones in some
form, particularly Alternatives 1A and 2
as described in NOAA’s DEIS. During
the public comment period, the State of
California also submitted comments on
NOAA’s proposal. In its October 2006
letter, the CDFG stated that it could only
support Alternative 1C as described in
NOAA’s draft environmental impact
statement (DEIS). Under Alternative 1C,
NOAA would establish marine reserves
only in federal waters. NOAA’s
preferred alternative in the DEIS,
identified as Alternative 1A, would
have established marine zones in both
federal and state waters with federal
regulations overlaying the entire
network (i.e., from the outer boundary
of the federal waters reserves to the
shore of the Channel Islands). As
indicated in the DEIS, Alternative 1C
would leave gaps in protection between
the offshore extent of some of the state
waters marine zones established by the
State of California in 2003 and the
marine zones proposed by NOAA (refer
to figure 1 for an illustration of these
gaps).
On March 16, 2007, the California
Coastal Commission (Coastal
Commission) held a public meeting on
NOAA’s proposal pursuant to its
authorities under section 307 of the
Coastal Zone Management Act (16
U.S.C. 1456). See https://
www.coastal.ca.gov/meetings/mtg-mm73.html for more information about this
meeting. At that meeting, the Coastal
Commission passed a motion as follows:
‘‘In the event NOAA elects not to
implement Alternative 1a, NOAA will
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implement Alternative 1c, with the
following additional provisions: Until
such time as the Resources Agency and
the Fish and Game Commission
designate the areas in between the
existing State-designated MPAs and the
3 mile limit (i.e., the ‘‘gaps’’ between the
existing state MPAs and the federal
MPAs depicted in Alternative 1c [and
shown on Exhibit 9]), or the Fish and
Game Commission/DFG and NOAA
enter into an interagency agreement that
establishes MPA protection for these
‘‘gap’’ areas, NOAA will expand
Alternative 1c to include in its MPA
designation these ‘‘gaps’’ between the
outer boundaries of the existing state
MPAs and the state-federal waters
boundary (3nm from shore).’’ At this
meeting, the CDFG representative also
stated that the FGC could close these
gaps in protection using state laws by
August 2007.
Based on the record, including
comments received during the public
comment period and the record of the
Coastal Commission, NOAA has
determined that there is sufficient
information and rationale to establish
marine zones in the federal waters of the
Sanctuary (i.e., implement NOAA’s
Alternative 1C). With regard to state
waters of the Sanctuary, NOAA has
decided to defer action on establishing
marine zones until the FGC has had an
opportunity to close those gaps in a
manner consistent with the Coastal
Commission’s motion and the CDFG
representative’s statement. The State of
California has already begun this
process by placing it on the agenda for
a decision at the August 2007 meeting
of the FGC. Also, the CDFG has begun
preparing the necessary documentation
to support the FGC’s decision. NOAA is,
therefore, leaving the record open with
regard to a decision to establish marine
zones in state waters of the Sanctuary,
and will be accepting additional public
comment on this specific issue.
NOAA will make a final decision with
regard to its action in state waters in
fall, 2007. If the FGC is able to take
sufficient action before this time, NOAA
proposes to take no further action under
the NMSA. If the FGC is not able to take
sufficient action before this time, NOAA
would finalize regulations under the
NMSA that would effectively close the
gaps associated with alternative 1C by
extending federal protections into state
waters to meet the boundaries of the
marine zones established by the FGC in
2003. In either case, NOAA will provide
public notice of this action through
issuance of a Federal Register document
at the appropriate time.
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II. Summary of Final Environmental
Impact Statement and Record of
Decision
NOAA prepared a draft
environmental impact statement (DEIS)
for the proposed rule to establish marine
reserves and marine conservation areas
within the Sanctuary (71 FR 46220;
August 11, 2006). The DEIS was
prepared in accordance with the NMSA
and National Environmental Policy Act
of 1969 (NEPA) requirements. The DEIS
was distributed for public comments in
early August 2006. The public comment
period, which closed on October 10,
2006, yielded many comments on
NOAA’s proposed action and
suggestions for improving the DEIS.
NOAA has prepared a final
environmental impact statement (FEIS)
to address these comments and make
appropriate changes to its
environmental analysis. The FEIS
contains a statement of the purpose and
need for the project, description of
proposed alternatives including the no
action alternative, description of the
affected environment, and evaluation
and comparison of environmental
consequences including cumulative
impacts. The preferred alternative
incorporates the network of marine
reserves and marine conservation areas
originally identified for the federal
phase in the Commission’s CEQA
document.
NOAA’s record of decision for this
action, prepared pursuant to 40 CFR
1505.2, is set forth below:
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Record of Decision
Introduction
Designated in 1980, the Channel
Islands National Marine Sanctuary
(CINMS or Sanctuary) consists of an
area of approximately 1,113 square
nautical miles (nmi2) off the southern
coast of California. The Sanctuary
boundary begins at the mean high water
line and extends seaward to a distance
of approximately six nautical miles
(nmi) from the following islands and
offshore rocks: San Miguel Island, Santa
Cruz Island, Santa Rosa Island, Anacapa
Island, Santa Barbara Island, Richardson
Rock, and Castle Rock (collectively the
Islands). Located offshore from Santa
Barbara and Ventura counties, the
Sanctuary supports a rich and diverse
range of marine life and habitats, unique
and productive oceanographic processes
and ecosystems, and culturally
significant resources. More than 27
species of cetaceans (whales and
dolphins) use the Sanctuary during at
least part of the year. There are also 5
species of pinnipeds (seals and sea
lions) that occur in the area. More than
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60 species of birds feed in the sanctuary
and more than 23 species of sharks
occur here. In addition, a wealth of
Chumash Native American artifacts as
well as the remains of over 100 historic
shipwrecks line the ocean floor of the
Sanctuary.
The primary objective of the CINMS
is to protect Sanctuary resources. In
meeting this objective, NOAA is
establishing federal marine zones in the
CINMS to further the protection of
Sanctuary biodiversity, and to
complement the existing network of
marine zones established by the State of
California in October 2002 (and
implemented under its authorities in
April 2003). The regulations
implementing this action add nine new
federal marine zones to the Sanctuary
(eight no-take marine reserves and one
limited-take marine conservation area).
These zones total 110.5 nmi2 as
marine reserves and 1.7 nmi2 as marine
conservation areas. The area of the total
network, including the existing state
marine zones, is 214.1 nmi2. All
extractive activities (e.g., removal of any
sanctuary resource) and injury to
Sanctuary resources are prohibited in
marine reserves. Lobster harvest and
recreational fishing for pelagic finfish
(with hook and line only) are allowed
within the marine conservation area,
while all other extraction or injury to
Sanctuary resources is prohibited.
NOAA has prepared this record of
decision (ROD) in accordance with
regulations published by the Council on
Environmental Quality (40 CFR 1505.2)
implementing the National
Environmental Policy Act (NEPA).
Decision
NOAA is issuing new regulations for
the CINMS. These new regulations
prohibit take of all Sanctuary resources
in marine reserves and limit take of all
Sanctuary resources in a marine
conservation area.
Alternatives Considered
In its final environmental impact
statement, NOAA considered three
alternatives for this action: A no action
(or status quo) alternative, Alternative 1,
and Alternative 2.1
No Action Alternative
The no action alternative would have
maintained the status quo in the
Sanctuary (i.e., no new marine zones
would be designated). Under this
alternative, the NMSP would not have
1 In addition, NOAA and the State of California
considered and analyzed dozens of other spatial
designs. See section 3 of the FEIS for more
information about the process used to develop the
range of alternatives.
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taken any new regulatory action under
the NMSA. Existing Sanctuary
regulations (e.g., no discharge) would
continue to apply throughout the
CINMS. Existing state marine reserves
and marine conservation areas and
existing state and federal management
of commercial and recreational
activities, including fishing, would
remain in place.
Alternative 1
Under Alternative 1, the NMSP will
establish a series of marine zones. The
spatial extent of the overall marine
zoning network alternative was
developed by the CDFG and NMSP in
2001, based on the extensive work of the
MRWG and its advisory panels, and is
the original proposed project in the
CDFG (2002). The portions of the
marine zones within state waters were
established by the FGC and CDFG in
2003.
Alternative 1 contained three subalternatives: 1A, 1B, and 1C. In
Alternative 1A, the boundaries of the
marine zones (and their corresponding
NMSA regulations) completely overlay
the existing state marine zones and
terminate at the mean high water line of
the northern Channel Islands. In
Alternative 1B, the boundaries of the
marine zones (and their corresponding
NMSA regulations) abut the existing
state marine zone boundaries, thereby
including a small portion of state
waters. In Alternative 1C, the
boundaries of the proposed marine
zones terminate at the boundary
between state and federal waters (3 nmi
from shore), thereby including no state
waters. Alternative 1C was NOAA’s
preferred alternative.
Alternative 2
Alternative 2 is based on a larger
network of marine reserves developed
during the MRWG process with slight
modifications to conform to the
boundaries of the existing state marine
reserves and conservation areas.
Alternative 2 is the largest of the
alternatives proposed, thereby
increasing protection of various habitats
and species of interest, as compared to
Alternative 1A. When compared to the
no-action alternative, Alternative 2 adds
11 new marine reserves and one new
marine conservation area. Alternative 2
has a total of 276.9 nmi 2 as marine
reserves and 12.1 nmi 2 as marine
conservation areas for a total of 289.0
nmi 2. Alternative 2 would have had the
same regulations as Alternative 1.
Environmentally Preferred Alternative
All alternatives, aside from the no
action alternative, would result in
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environmental benefits in the form of
protection of sensitive marine habitats
and species. Alternative 2 is the largest
of the alternatives proposed and
includes a network of existing state
marine zones and new federal zones,
and would increase protection of
various habitats and species of interest,
as compared to the sub-alternatives
under Alternative 1. Therefore, this
alternative is considered to be the
environmentally preferred. It was not
selected because Alternative 1 better
met NOAA’s purpose and need.
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Mitigation Measures
Because the action would not result in
any environmental harm, there are no
specific mitigation measures needed to
avoid, minimize, or compensate for
environmental harm.
Decision Making Process
Collectively referred to as the
‘‘Channel Islands marine reserves
process,’’ the consideration of marine
zones within the CINMS occurred in
three distinct phases: (1) A communitybased phase; (2) a State of California
(State) regulatory phase; and (3) a
federal regulatory phase. These three
phases are described in detail in the
Final Environmental Impact Statement
for this action (see ADDRESSES).
In summary, the alternatives
described evolved as a result of the
Channel Islands marine reserves
process. Comprehensive marine zoning
network options were originally
developed by NOAA and the CDFG
following a comprehensive stakeholder
process conducted from 1999 through
2002. In 2002, the FGC supported
establishment of state marine zones in
the state waters of the Sanctuary (0–3
nmi) 2.
Following the publication of the
State’s final regulations in 2003, NOAA
hosted scoping meetings to consider the
extension of the State’s zones into
deeper waters of the Sanctuary. In 2004,
NOAA released a preliminary
environmental document with a range
of alternatives for public review. NOAA
then consulted with local, state, and
federal agencies and the Pacific Fishery
Management Council (PFMC) on
possible amendments to the CINMS
designation document pursuant to
section 303(b)(2) of the National Marine
Sanctuaries Act (NMSA) (16 U.S.C.
1433(b)(2)). In addition, in 2005 NOAA
provided the PFMC with the
opportunity to prepare draft NMSA
2 Refer to the Environmental Impact Report
prepared by the State of California for its 2002
action. This document is available for download on
NOAA’s CINMS Web site at https://
channelislands.noaa.gov/marineres/main.html.
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fishing regulations pursuant to section
304(a)(5) of the NMSA (16 U.S.C.
1434(a)(5)) for the potential
establishment of marine reserves and
marine conservation areas.
The PFMC response to NOAA’s letter
regarding draft fishing regulations stated
its support for NOAA’s goals and
objectives for marine zones in the
CINMS, but recommended that, rather
than utilizing the NMSA, NOAA issue
fishing regulations under the MagnusonSteven Fishery Conservation and
Management Act (MSA) and the
relevant authorities of the states of
California, Oregon, and Washington. To
that end, and in accordance with advice
from the NOAA Administrator in his
October 19, 2005 letter to the PFMC, the
PFMC recommended the northern
Channel Islands federal marine zones be
designated as Essential Fish Habitat
(EFH) and Habitat Areas of Particular
Concern (HAPC) under Amendment 19
of the Groundfish Fishery Management
Plan (FMP). The water column in the
marine zones would be closed under
other fishery management plan
authorities and complementary state
laws.
NOAA reviewed the PFMC’s
recommendations and determined that
PFMC did not have the specificity or
record to support the use of the MSA or
state laws to establish limited take or
no-take zones in the water column and
thereby did not fulfill NOAA’s goals and
objectives for these marine zones in the
CINMS. Amendment 19 to the
Groundfish FMP implemented, in part,
the proposed marine zones by
prohibiting all bottom contact gear in
those proposed zones. Accordingly,
NOAA’s NMSA regulations prohibit the
take of resources from the zones not
prohibited by the Amendment 19
regulations. Thus, along with the
regulations implementing Amendment
19, the NMSA regulations establish
comprehensive marine reserves and a
marine conservation area in the federal
waters part of the CINMS in a manner
that fulfills NOAA’s goals and objectives
for the marine zones in the CINMS.
In August 2006, NOAA published
proposed regulations for this action and
released the related draft environmental
impact statement (DEIS) for public
review and comment. Between August
and October of 2006, NOAA received
public comment and held two hearings
on the proposed rule and DEIS. Over
30,000 individuals submitted written
comments and/or presented oral
testimony on NOAA’s proposal.
Approximately 99% of these
individuals supported the establishment
of Alternative 1A or Alternative 2.
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29213
During the public comment period,
the State of California also submitted
comments on NOAA’s proposal. In its
October 2006 letter, the CDFG stated
that it could only support Alternative
1C (NMSA regulations in federal waters
only) as described in the DEIS. In
subsequent consultations with State
representatives and in a letter from the
Secretary of Resources dated January 2,
2007, the State reiterated that it could
only support Alternative 1C at this time.
Under Alternative 1C, NOAA would
establish marine reserves and a marine
conservation area only in federal waters.
NOAA’s preferred alternative, identified
as Alternative 1A in the DEIS, would
have established marine zones in both
federal and state waters with federal
regulations overlaying the entire
network (i.e., from the outer boundary
of the federal waters reserves to the
mean high water line of the Channel
Islands). As indicated in the DEIS,
Alternative 1C leaves small gaps in
protection between the offshore extent
of some of the state waters marine zones
established by the State of California in
2003 and the federal waters marine
zones proposed by NOAA.
On March 16, 2007, the Coastal
Commission held a public meeting on
NOAA’s consistency determination with
California’s Coastal Zone Management
Plan under section 307 of the Coastal
Zone Management Act (see https://
www.coastal.ca.gov/meetings/mtg-mm73.html). At that meeting, the Coastal
Commission passed a motion as follows:
In the event NOAA elects not to implement
Alternative 1a, NOAA will implement
Alternative 1c, with the following additional
provisions: Until such time as the Resources
Agency and the Fish and Game Commission
designate the areas in between the existing
State-designated MPAs and the 3 mile limit
(i.e., the ‘‘gaps’’ between the existing state
MPAs and the federal MPAs depicted in
Alternative 1c [and shown on Exhibit 9]), or
the Fish and Game Commission/DFG and
NOAA enter into an interagency agreement
that establishes MPA protection for these
‘‘gap’’ areas, NOAA will expand Alternative
1c to include in its MPA designation these
‘‘gaps’’ between the outer boundaries of the
existing state MPAs and the State-federal
waters boundary (3nm from shore).
At this meeting, the CDFG
representative also stated that the FGC
could close these gaps in protection
using state laws by August 2007.
Based on the record, including
comments received during the public
comment period and the record of the
Coastal Commission, NOAA determined
that at this time there is sufficient
information and rationale to establish
marine zones in the federal waters of the
Sanctuary (i.e., implement NOAA’s
alternative 1C). This Record of Decision
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supports that determination and
represents NOAA’s final decision to
implement the regulations in the federal
waters of the Sanctuary associated with
Alternative 1C.
With regard to state waters of the
Sanctuary, NOAA has decided to defer
action on establishing federal marine
zones until the FGC has had an
opportunity to close the gaps between
the federal marine zones and the state
marine zones in a manner consistent
with the Coastal Commission’s
resolution and the CDFG
representative’s statement.3 The State of
California has already begun this
process by placing it on the agenda for
a decision at the August 2007 meeting
of the FGC. Also, the CDFG has begun
preparing the necessary documentation
to support the FGC’s decision. If the
FGC is able to take sufficient action in
a timely manner, NOAA would take no
further action under the NMSA. If the
FGC is not able to take sufficient action
in a timely manner, NOAA would issue
regulations under the NMSA that would
effectively close the gaps associated
with Alternative 1C by extending
federal protections into state waters to
meet the boundaries of the marine zones
established by the FGC in 2003. In that
instance, a second record of decision for
that subsequent action would be issued
to finalize such action.
Conclusion
The new regulations identified above
apply to all users of the Sanctuary.
Based on socioeconomic information
gathered by NOAA and identified in the
FEIS, the socioeconomic impacts of
these regulations can be characterized
as:
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• Having a small impact on existing
consumptive activities (commercial fishing
and consumptive recreational activities).
• Beneficial to non-consumptive
recreational users. These increased benefits
take the form of increases in diversity and
abundance of wildlife for viewing and
photography opportunities. Benefits may also
be derived from the decrease in the density
of users or in the reduction in conflicts with
consumptive users.
• Beneficial to management, research, and
education because relatively undisturbed
areas (i.e., reference areas) will be available
for comparison with areas outside the marine
zones; and
• Beneficial for intrinsic and heritage
purposes.
NOAA expects, therefore, that this
rule will have no significant
socioeconomic impacts and that the
3 Closing the gaps would also be consistent with
the public record supporting the 2002 decision of
the California Fish and Game Commission to
establish marine zones in the Sanctuary.
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implementation of marine zones in the
CINMS will have beneficial ecological
impacts on marine communities and
habitats.
III. Revised Designation Document
Section 304(a)(4) of the NMSA
requires that the terms of designation
include the geographic area included
within the Sanctuary; the characteristics
of the area that give it conservation,
recreational, ecological, historical,
research, educational, or aesthetic value;
and the types of activities subject to
regulation by the Secretary to protect
these characteristics. Section 304(a)(4)
also specifies that the terms of
designation may be modified only by
the same procedures by which the
original designation was made. To
implement this action, the CINMS
Designation Document, originally
published in the Federal Register on
October 2, 1980 (45 FR 65198), is
modified to read as follows (new text in
bold and deleted text in brackets and
italics):
Preamble
Under the authority of the Marine
Protection, Research and Sanctuaries
Act of 1972, Pub. L. 92–532, (the Act)
the waters surrounding the northern
Channel Islands and Santa Barbara
Island are hereby designated a Marine
Sanctuary for the purposes of preserving
and protecting this unique and fragile
ecological community.
Article 1. Effect of Designation
Within the area designated as the
Channel Islands National Marine
Sanctuary (the Sanctuary), described in
Article 2, the Act authorizes the
promulgation of such regulations as are
reasonable and necessary to protect the
values of the Sanctuary. Article 4 of this
Designation lists those activities which
may require regulation but the listing of
any activity does not by itself prohibit
or restrict it. Restrictions or prohibitions
may be accomplished only through
regulation, and additional activities may
be regulated only by amending Article
4.
Article 2. Description of the Area
The Sanctuary consists of an area of
the waters off the coast of California, of
approximately [1252.5] 1,128 square
nautical miles (nmi) adjacent to the
northern Channel Islands and Santa
Barbara Island seaward to a distance of
approximately 6 nmi. The precise
boundaries are defined by regulation.
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Article 3. Characteristics of the Area
That Give It Particular Value
The Sanctuary is located in an area of
upwelling and in a transition zone
between the cold waters of the
California Current and the warmer
Southern California Countercurrent.
Consequently, the Sanctuary contains
an exceptionally rich and diverse biota,
including 30 species of marine
mammals and several endangered
species of marine mammals and sea
birds. The Sanctuary will provide
recreational experiences and scientific
research opportunities and generally
will have special value as an ecological,
recreational, and esthetic resource.
Article 4. Scope of Regulation
Section 1. Activities Subject to
Regulation
In order to protect the distinctive
values of the Sanctuary, the following
activities may be regulated within the
Sanctuary to the extent necessary to
ensure the protection and preservation
of its marine features and the ecological,
recreational, and esthetic value of the
area:
a. Hydrocarbon operations.
b. Discharging or depositing any
substance.
c. Dredging or alteration of, or
construction on, the seabed.
d. Navigation of vessels except fishing
vessels or vessels [travelling] traveling
within a Vessel Traffic Separation
Scheme or Port Access Route designated
by the Coast Guard outside of 1 nmi
from any island.
e. Disturbing marine mammals or
birds by overflights below 1000 feet.
f. Removing or otherwise deliberately
harming cultural or historical resources.
g. Within a marine reserve, marine
park, or marine conservation area,
harvesting, removing, taking, injuring,
destroying, possessing, collecting,
moving, or causing the loss of any
Sanctuary resource, including living or
dead organisms or historical resources,
or attempting any of these activities.
h. Within a marine reserve, marine
park, or marine conservation area,
possessing fishing gear.
Section 2. Consistency With
International Law
The regulations governing the
activities listed in Section 1 of this
article will apply to foreign flag vessels
and persons not citizens of the United
States only to the extent consistent with
recognized principles of international
law including treaties and international
agreements to which the United States
is signatory.
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Section 3. Emergency Regulations
Section 2. Defense Activities
Where essential to prevent immediate,
serious and irreversible damage to the
ecosystem of the area, activities other
than those listed in Section 1 may be
regulated within the limits of the Act on
an emergency basis for an interim
period not to exceed 120 days, during
which an appropriate amendment of
this article would be proposed in
accordance with the procedures
specified in Article 6.
The regulation of those activities
listed in Article 4 shall not prohibit any
activity conducted by the Department of
Defense that is essential for national
defense or because of emergency. Such
activities shall be consistent with the
regulations to the maximum extent
practicable.
Article 5. Relation to Other Regulatory
Programs
Section 1. Fishing
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The regulation of fishing is not
authorized under Article 4, except
within portions of the Sanctuary
designated as marine reserves, marine
parks, or marine conservation areas
established pursuant to the goals and
objectives of the Sanctuary and within
the scope of the State of California’s
Final Environmental Document ‘‘Marine
Protected Areas in NOAA’s Channel
Islands National Marine Sanctuary’’
(California Department of Fish and
Game, October 2002), certified by the
California Fish and Game Commission.
However, fishing vessels may be
regulated with respect to discharges in
accordance with Article 4, Section 1,
paragraph (b) and aircraft conducting
kelp bed surveys below 1000 feet can be
regulated in accordance with Article 4,
Section 1, paragraph (e). All regulatory
programs pertaining to fishing,
including particularly regulations
promulgated under the California Fish
and Game Code and Fishery
Management Plans promulgated under
the Fishery Conservation and
Management Act of 1976, 16 U.S.C.
1801 et seq., shall remain in effect. All
permits, licenses and other
authorizations issued pursuant thereto
shall be valid within the Sanctuary
unless authorizing any activity
prohibited by any regulation
implementing Article 4. Fishing as used
in this article and in Article 4 includes
kelp harvesting.
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Jkt 211001
Section 3. Other Programs
All applicable regulatory programs
shall remain in effect and all permits,
licenses and other authorizations issued
pursuant thereto shall be valid within
the Sanctuary unless authorizing any
activity prohibited by any regulation
implementing Article 4. The Sanctuary
regulations shall set forth any necessary
certification procedures.
Article 6. Alterations to This
Designation
This Designation can be altered only
in accordance with the same procedures
by which it has been made, including
public hearings, consultation with
interested federal and state agencies and
the Pacific Regional Fishery
Management Council, and approval by
the President of the United States.
IV. Summary of Regulations
These final regulations implement
NOAA’s preferred alternative by
establishing marine reserves and a
marine conservation area within the
federal waters of CINMS. The
regulations define two new terms
(pelagic finfish and stowed and not
available for immediate use), prohibit
all extractive activities and injury to
Sanctuary resources within the marine
reserves, and prohibit all extractive
activities and injury to Sanctuary
resources within the marine
conservation area except recreational
fishing for pelagic finfish and
commercial and recreational lobster
fishing (Anacapa Island Marine
Conservation Area). These regulations
also add two new appendices that list
the boundary coordinates for the marine
reserves and marine conservation area.
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29215
These regulations modify subpart G of
the National Marine Sanctuary Program
Regulations (15 CFR part 922), the
regulations for the Channel Islands
National Marine Sanctuary.
A. Establishment of Marine Reserves
and Marine Conservation Areas
These regulations establish under the
NMSA eight marine reserves and one
marine conservation area within the
CINMS. Refer to figure 1 for a map
depicting the locations of the marine
reserves and marine conservation area.
The marine reserves are distributed
throughout the CINMS and extend
slightly beyond the current boundaries
of the CINMS in four locations,
increasing the geographic area of the
Sanctuary by about 15 square nautical
miles. This action increases the overall
size of the Sanctuary from
approximately 1,113 square nautical
miles to approximately 1,128 square
nautical miles, an approximately 15
square nautical mile increase. This
small amount added allows the
boundary of four of the marine reserves
to be defined by straight lines projecting
outside the current CINMS boundary,
allowing for better enforcement of the
marine reserves. The boundaries of the
marine reserves and marine
conservation area are consistent with
the marine reserves and marine
conservation areas established by the
Commission in 2002 in state watersessentially extending most of them into
federal waters of the Sanctuary. NOAA
is changing the number identifying the
total area of the CINMS from
approximately 1,252.5 square nautical
miles to approximately 1,128 square
nautical miles. This change is based on
North American Datum of 1983 (NAD
83) and adjusts for technical corrections
using updated technologies. The legal
description of the CINMS is updated to
reflect this change. This update does not
constitute a change in the geographic
area of the Sanctuary (other than the
approximately 15 square nautical miles
referred to above) but rather an
improvement in the estimate of its size.
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Under these final regulations, NOAA
establishes two marine reserves in the
area around San Miguel Island, one
around Santa Rosa Island, two around
Santa Cruz Island, two around Anacapa
Island, and one around Santa Barbara
Island. The marine conservation area is
established off of Anacapa Island.
The total area designated marine
reserves under these final regulations is
110.5 square nautical miles. The marine
conservation area encompasses an
additional 1.7 square nautical miles.
Based on the record, including
comments received during the public
comment period and the record of the
Coastal Commission, NOAA has
determined that there is sufficient
information and rationale to establish
marine zones in the federal waters of the
Sanctuary (i.e., implement NOAA’s
Alternative 1C). With regard to state
waters of the Sanctuary, NOAA has
decided to defer action on establishing
marine zones until the FGC has had an
opportunity to close those gaps in a
manner consistent with the Coastal
Commission’s motion and the CDFG
representative’s statement. The State of
California has already begun this
process by placing it on the agenda for
a decision at the August 2007 meeting
of the FGC. Also, the CDFG has begun
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Jkt 211001
preparing the necessary documentation
to support the FGC’s decision. NOAA is,
therefore, leaving the record open with
regard to a decision to establish marine
zones in state waters of the Sanctuary,
and is requesting additional public
comment on this specific issue.
B. Activities Prohibited Within the
Marine Reserves
Under the final regulations, NOAA
prohibits any harvesting, removing,
taking, injuring, destroying, collecting,
moving, or causing the loss of any
Sanctuary resource, including living or
dead organisms or historical resources,
or attempting to do so, within any of the
marine reserves. The term ‘‘sanctuary
resource’’ is broadly defined in the
NMSP regulations at 15 CFR 922.3 and
means any living or non-living resource
that contributes to the conservation,
recreational, ecological, historical,
scientific, educational, or aesthetic
value of the Sanctuary. For the CINMS,
the term ‘‘Sanctuary resource’’ includes,
for example, the seafloor and all animals
and plants of the Sanctuary. It also
includes historical resources (which,
pursuant to 15 CFR 922.3, include
cultural and archeological resources),
such as shipwrecks and Native
American remains. In addition, to
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enhance compliance and aid in
enforcement, these final regulations also
prohibit possessing fishing gear and
Sanctuary resources inside a marine
reserve, except in certain circumstances.
These final regulations allow possession
of legally harvested fish stowed on a
vessel at anchor in or transiting through
a marine reserve and also allow the
possession of stowed fishing gear,
provided the gear is not available for
immediate use.
These final regulations prohibit only
those extractive activities within marine
reserves that are not prohibited by 50
CFR part 660, the NOAA regulations
that govern ‘‘Fisheries off West Coast
States’’ (MSA regulations). Therefore, if
an extractive activity is prohibited by
MSA regulations, it is not prohibited by
these final NMSA regulations.
Conversely, all extractive activities not
prohibited by MSA regulations are
prohibited by these final NMSA
regulations within marine reserves. In
the future, if NOAA were to amend the
MSA regulations to prohibit additional
extractive activities within marine
reserves, these NMSA regulations would
correspondingly narrow in scope. If, for
MSA purposes, NOAA were to amend
the MSA regulations to allow additional
extractive activities, these NMSA
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regulations would correspondingly
expand in scope to ensure all forms of
extraction are prohibited within marine
reserves. In either case, the MSA
rulemaking making such change would
provide the public with notice of the
corresponding change in applicability of
the NMSA regulation.
Regardless of the specific regulatory
mechanism, the intended result of this
final rule is for all extractive activities
to be prohibited within the marine
reserves.
C. Activities Prohibited Within the
Marine Conservation Areas
These final regulations prohibit the
same activities within the marine
conservation area as within the marine
reserves except that commercial and
recreational lobster fishing and
recreational fishing for pelagic finfish
are allowed in the marine conservation
area at Anacapa Island. Commercial
fishing for pelagic finfish is prohibited
within the marine conservation area.
Like the final regulations for marine
reserves, the final regulations for the
marine conservation area only prohibit
activities that are not prohibited by
applicable MSA regulations codified at
50 CFR part 660. Any changes to the
applicable MSA regulations would
result in a corresponding change in the
applicability of the NMSA regulations,
as discussed above.
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D. Enforcement
The final regulations will be enforced
by NOAA and other authorized agencies
(e.g., the California Department of Fish
and Game, United States Coast Guard,
and National Park Service) in a
coordinated and comprehensive way.
Enforcement actions for an infraction
will be prosecuted under the
appropriate statutes or regulations
governing that infraction. The result is
that enforcement actions may be taken
under State of California authorities, the
NMSA, the MSA, or other relevant legal
authority.
E. Permitting
The NMSP regulations, including the
regulations for the CINMS, allow NOAA
to issue permits to conduct activities
that would otherwise be prohibited by
the regulations. Most permits are issued
by the Superintendent of the CINMS.
Requirements for filing permit
applications are specified in NMSP
regulations and the Office of
Management and Budget-approved
application guidelines (OMB control
number 0648–0141). Criteria for
reviewing permit applications are
contained in the CINMS and NMSP
regulations at 15 CFR 922.77 and
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922.48, respectively. In general, permits
may be issued for activities related to
scientific research, education, and
management. Permits may also be
issued for activities associated with the
salvage and recovery efforts for a recent
air or marine casualty. (Emergency
activities would not require a permit.)
Nationwide, NOAA issues
approximately 200 national marine
sanctuary permits each year. Of this
amount, two or three are for activities
within the CINMS. The majority of
permits issued for activities within the
CINMS are for activities related to
scientific research. NOAA expects this
trend to continue with the final
regulations. Although there may be an
increase in the number of permits
requested for activities within the
CINMS, NOAA does not expect this
increase to appreciably raise the average
number of permits issued nationwide.
Therefore, NOAA has determined that
these final regulations do not necessitate
a modification to its information
collection approval by the Office of
Management and Budget under the
Paperwork Reduction Act.
V. Summary of Comments and
Responses
This section contains NOAA’s
responses to the substantive comments
received on the proposed rule and DEIS.
NOAA has summarized the comments
according to the content of the
statement or question put forward in the
letters, e-mails, and written and oral
testimony at the public hearings on this
action. Many commenters submitted
similar enough questions or statements
that they could be addressed by one
response. NOAA also made several
changes in the FEIS in response to the
public comments, e.g., updating the
socioeconomic and ecological impact
analyses. Several technical or editorial
comments on the DEIS and proposed
rule were taken under consideration by
NOAA and, where appropriate, applied
to the FEIS and this final rule. These
comments are not, however, included in
the substantive list below.
NOAA’s FEIS contains these
comments and responses, but also
includes a table listing the names of the
individuals that submitted comments on
the DEIS and proposed rule and an
index indicating which comments were
submitted by each person and NOAA’s
response to those particular comments.
1. Comment: Collectively, the
following five reasons were identified
by commenters in support of NOAA’s
Alternative 2:
• It provides the greatest amount of
ecosystem protection, habitat
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representation, and opportunities for
species recovery/restoration.
• It best recognizes the intrinsic
values associated with biodiversity and
ecosystem-based protection.
• It contains zones of sufficient size,
space, and connectivity to maximize
larval production and recruitment.
• It best fulfills the mandates of the
National Marine Sanctuaries Act
(NMSA) and the goals of the proposed
network.
• It best achieves recommendations
in the 2004 report from the Pew Oceans
Commission and U.S. Ocean
Commission.
Response: Alternative 2 would
provide the greatest amount of
ecosystem protection as it is the largest
spatial alternative. However, Alternative
1 (and its sub-alternatives) provides not
only a robust level of ecosystem
protection, habitat representation, and
opportunity for species recovery and
restoration, but is consistent with the
existing network established by the
State of California (State) in state waters
of the Sanctuary and aligned with the
offshore marine zones envisioned by the
State’s preferred alternative in its CEQA
document. Also, Alternative 1 (and its
three subalternatives) is consistent with
the benthic habitat protections adopted
by the PFMC and NOAA Fisheries
through the EFH conservation areas
established by NOAA under MSA
regulations (see NOAA’s final rule at 71
FR 27408; May 11, 2006). Further,
implementation of Alternative 1 would
fulfill the mandates of the NMSA,
achieve the goals of the CINMS zoning
network, and meet several of the
recommendations put forward by the
Pew Oceans and U.S. Ocean
Commissions.
Designation of Alternative 2 under the
envisioned regulatory structure may
require additional administrative
actions that may delay implementation.
This regulatory structure, which uses a
combination of the MSA and NMSA,
may require that the current EFH
designation in the Sanctuary, which
corresponds to the zone boundaries
under Alternative 1, be re-designated to
incorporate the larger zone boundaries
proposed under Alternative 2.
Alternative 1 is the most prudent course
of action for the marine zoning network
in the Sanctuary.
2. Comment: Approximately 30,000
commenters supported NOAA’s
preferred alternative in the DEIS
(Alternative 1A) as the most efficient
and coherent zone network for
protecting Channel Islands wildlife.
Response: In the DEIS, the three subalternatives analyzed under Alternative
1 (1A, 1B, and 1C) provide different
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boundary configurations for the marine
zoning network based on the extent of
federal regulatory overlap in state
waters. During the public comment
period, the CDFG submitted a letter to
NOAA stating that Alternative 1C was
the only acceptable alternative. In a
January 2, 2007 letter to NOAA, the
Secretary of the California Resources
Agency reiterated this position again
stating that Alternative 1C was the only
alternative acceptable to the State of
California and that overlap by federal
regulations in state waters was never
contemplated by the State.
The NMSA allows the Governor of a
state for which the NMSP is making
changes to a sanctuary’s terms of
designation to review and reject those
changes with regard to state waters.
Because implementation of Alternative
1A requires a change to the CINMS
terms of designation (to allow regulation
of fishing and other resource extraction
in State, as well as Federal, waters),
NOAA conducted a thorough reevaluation of Alternatives 1A and 1C,
given the Secretary of Resources’
opposition to all NOAA alternatives but
1C.
As identified in the DEIS, Alternative
1C leaves small gaps between some of
the state designated marine reserves and
the proposed federal marine reserves
(see section 3.2.4 of the FEIS). The
January 2, 2007 letter also stated that the
CDFG and the FGC would as soon as
possible initiate the process to close the
gaps associated with Alternative 1C by
bringing the boundaries of a number of
the existing state marine zones up to the
State-Federal jurisdictional line; that
process has commenced. NOAA’s
analysis identifies that, if these gaps are
closed, the differences among the three
sub-alternatives are distinguished by
management considerations, not
ecological and socioeconomic impacts.
As such, because the CDFG and the FGC
are closing the gaps associated with
Alternative 1C, the net ecological
benefits and socioeconomic impacts
between Alternatives 1A (NOAA’s
original preferred alternative) and 1C
(the State of California’s recommended
alternative) will be the same. NOAA has
determined, therefore, that Alternative
1C will accomplish the goals of the
zoning network while respecting the
position of the State. If NOAA
implements Alternative 1C and the State
does not act to close the gaps in a timely
manner, NOAA envisions closing the
gaps via NMSA regulations.
Furthermore, NOAA and the State
strongly support a close, collaborative
working relationship to implement the
CINMS zoning network and will sign a
formal agreement to ensure that
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management of the network (e.g.,
enforcement, education and outreach,
and monitoring) is implemented in a
collaborative, efficient, and effective
manner.
3. Comment: Several commenters
support the no action alternative
because they believe existing
regulations are sufficient to meet the
goals of NOAA’s action.
Response: NOAA has determined
existing regulations are not sufficient to
meet the goals of this action. The State
of California has reached the same
conclusion in adopting the state waters
portions of the network and is asking
NOAA for prompt action in the federal
waters zones. NOAA’s analysis
discusses the relationship of the action
with other existing management regimes
in the region (see sections 3.1 and 5.1.2
of the FEIS) and the effectiveness they
have on achieving NOAA’s goals for this
action.
Marine zones and sound fishery
management are complementary
components of a comprehensive effort
to sustain marine habitats and fisheries.
Marine zones are considered one of
many tools available to ocean managers
and are not the only tool used in the
project area for this action. However,
certain ecosystem functions cannot be
protected as well by other management
measures. For example, size, season,
and bag limits do not prevent bycatch of
non-target species or undersized
individuals nor do they fully provide for
natural predator and prey interactions.
Traditional single species-based
management measures alone have not
been sufficient to protect groundfish
and other populations in the CINMS
region and other parts of the world.
Incidental impacts of various fishing
practices may also have unintended
effects that would not occur in a marine
zone, particularly in a no-take reserve.
This includes both direct impacts to the
environment (e.g., habitat damage from
trawling) and indirect ecosystem
impacts (e.g., removing all large, old fish
and altering the species size
composition). Marine zones of the type
proposed here by their nature provide
relatively undisturbed habitats and act
as ‘‘natural hatcheries’’, which leads to
benefits in total production and export
of young.
NOAA’s action is intended to address
a suite of ecological goals, including
providing special protection of habitats
and species for their intrinsic values.
Marine zones of the type proposed here
provide insurance for management
uncertainty by providing areas where
species can interact in a relatively
undisturbed ecosystem. Furthermore,
NOAA’s action under the NMSA does
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not duplicate existing NOAA
regulations promulgated under the
MSA. The regulations being issued
under this action have been carefully
crafted in such a way so that the
regulations being issued here under the
NMSA are subject to NOAA’s
regulations under the MSA. This applies
to the current regime and any future
changes, so that if NOAA were to amend
the MSA regulations, the applicability
of the NMSA regulations would expand
or contract automatically to ensure
complete protection with no
duplication. See the final regulations for
how this is achieved.
The specific integration of marine
zones into fisheries management,
including reductions in overall fleet
capacity, total allowable catch, and
allocation between user groups is more
appropriately dealt with through the
PFMC and FGC processes, which is
used to establish these limits.
4. Comment: Several commenters
support the no action alternative
because they believe that any additional
zones can and should be designated by
the PFMC via the MSA and the State of
California via State statutes.
Response: In May 2005, NOAA
presented the PFMC, per section
304(a)(5) of the NMSA, with the
opportunity to prepare draft NMSA
fishing regulations to meet the goals of
the CINMS marine zones. Section
304(a)(5) requires that the relevant
Fishery Management Council be given
the opportunity to prepare draft fishing
regulations within the Exclusive
Economic Zone (EEZ) portion of the
given sanctuary. The EEZ portion of the
CINMS is from 3 to 6 nmi offshore the
northern Channel Islands. The PFMC
responded and recommended that
fishing regulations for the CINMS
marine zones in federal waters be
implemented through the existing
authorities of the MSA and the states of
California, Oregon, and Washington.
Based on its review of the existing
factual and scientific evidence, NOAA
determined that there was a credible
basis for regulations prohibiting the use
of bottom-contact gear in the CINMS
marine zones under the MSA. With
respect to fishing throughout the
remainder of the water column,
however, NOAA determined that there
was an insufficient factual and scientific
basis to support pursuit of this aspect of
the PFMC’s proposal under the MSA.
NOAA determined that the PFMC’s
recommendations did not have the
specificity or record to support the use
of the MSA or state laws to establish
limited take or no-take zones in the
water column and thereby did not fulfill
the goals and objectives of the CINMS.
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Further, MSA regulations cannot legally
address other extractive activities that
could be addressed under the NMSA,
such as certain scientific research
activities. In response, the PFMC
changed its recommendation under
Amendment 19 to the Pacific Coast
Groundfish Management Plan (see next
paragraph) to close the existing and
proposed CINMS marine zones to only
bottom-contact gear.
In 2006, the PFMC submitted and
NOAA approved Amendment 19 to the
Pacific Coast Groundfish Fishery
Management Plan, which, among other
things, identified and described EFH
within the CINMS for groundfish
species and designated the existing and
proposed CINMS marine zones as
Habitat Areas of Particular Concern
(HAPC). Amendment 19 also prohibited
the use of bottom-contact gear in the
CINMS HAPCs.
The final NMSA regulations for this
marine zones action prohibit those
extractive activities within the marine
zones that are not prohibited by 50 CFR
part 660, the NOAA regulations that
govern ‘‘Fisheries off West Coast
States,’’ which includes the Amendment
19 regulations. Therefore, if an
extractive activity is prohibited by those
MSA regulations, it is not prohibited by
the NMSA regulations. Conversely, all
extractive activities not prohibited by
those MSA regulations in the marine
reserves are prohibited by these NMSA
regulations. In the future, if NOAA were
to amend the MSA regulations to
prohibit additional extractive activities
in the marine zones, notice and
opportunity for public comment would
be provided regarding those activities
no longer being prohibited by
regulations under the NMSA. Likewise,
if NOAA were to amend the MSA
regulations to allow currently
prohibited extractive activities in the
marine zones, notice and opportunity
for public comment would be provided
regarding those additional activities
being prohibited under these NMSA
regulations.
5. Comment: Ecosystem-based
management should be favored over
traditional fisheries management in this
action, because it is more effective at
meeting NOAA’s purpose and need.
Response: This action to complete the
CINMS marine zoning network is a form
of ecosystem-based management that is
being applied to meet NOAA’s
responsibility to protect Sanctuary
resources. Sanctuary resources are
defined at 15 CFR 922.3 as follows:
‘‘Sanctuary resource means any living or
non-living resource of a National Marine
Sanctuary that contributes to the
conservation, recreational, ecological,
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historical, research, educational, or aesthetic
value of the Sanctuary, including, but not
limited to, the substratum of the area of the
Sanctuary, other submerged features and the
surrounding seabed, carbonate rock, corals
and other bottom formations, coralline algae
and other marine plants and algae, marine
invertebrates, brineseep biota,
phytoplankton, zooplankton, fish, seabirds,
sea turtles and other marine reptiles, marine
mammals and historical resources.’’
6. Comment: Limit the proposed
designation document changes and
regulations to prohibit non-fishing
activities and fishing in the water
column only.
Response: Under the NMSA, when a
national marine sanctuary is designated,
NOAA must specify the new sanctuary’s
‘‘terms of designation.’’ The terms of
designation include the boundaries of
the sanctuary, the characteristics that
give it value, and ‘‘the types of activities
that will be subject to regulation’’ by
NOAA. Terms of designation may only
be modified by following the same
procedures by which the sanctuary was
designated. The types of activities
subject to regulation are usually
expressed in fairly general terms. This is
necessary to allow NOAA to make
appropriate modifications to the
regulations in the future, e.g., to allow
for adaptive management. However,
even minor changes must be made
through a full public process, including
an opportunity for the public to review
the change and provide comment before
it is finalized. Furthermore, NOAA must
prepare all legally required analysis for
such regulatory changes, including
appropriate environmental and
economic impact analyses (under the
National Environmental Policy Act and
Regulatory Flexibility Act).
The designation document
amendment has been carefully crafted
and comments were solicited from
NOAA Fisheries, other relevant resource
management agencies, and the PFMC. It
is also crafted to be consistent with the
deliberations made throughout this
process, including the community and
state phases (see the Executive
Summary of NOAA’s FEIS for a
summary of the process). As indicated
above, the scope of authority defined in
designation documents for all national
marine sanctuaries is typically general,
and the implementing regulations are
more specific. NOAA believes this
provides sufficient parameters to its
authority while allowing flexibility to
manage the network adaptively in the
future in response to biological,
ecological, and economic indicators of
the network’s effectiveness. Any
proposed regulatory adjustment to the
current network would undergo
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rigorous environmental review,
analysis, and public input.
As indicated above, in contrast to the
general scope of the terms of
designation, sanctuary regulations are
often very specific and are developed to
implement the terms of designation by
defining the human activities that are
prohibited or otherwise restricted. The
final regulations for this NOAA action
prohibit those extractive activities
within marine reserves that are not
prohibited by 50 CFR part 660, the
NOAA regulations that govern
‘‘Fisheries off West Coast States’’ (MSA
regulations). Therefore, if an extractive
activity is prohibited by MSA
regulations, it is not prohibited by these
final NMSA regulations. Conversely, all
extractive activities not prohibited by
MSA regulations are prohibited by these
final NMSA regulations within marine
reserves.
Furthermore, NOAA has determined
that limiting the scope of the regulations
and terms of designation to prohibiting
activities only within the water column
would leave unacceptable gaps in the
cover of the regulations. Certain
activities, such as scientific research,
would not be covered by other
regulations (either State or MSA
regulations) thus preventing total
closure of the zones. Given this, NOAA
has determined that limiting the scope
of the regulations and terms of
designation would not meet its purpose
and need for this action.
7. Comment: The geographic scope of
the proposed authority to regulate
fishing under the NMSA, as described
in the DEIS, is too broad.
Response: The designation document
amendment has been carefully crafted
and comments solicited from NOAA
Fisheries, other relevant resource
management agencies, and the PFMC. It
is also crafted to be consistent with the
deliberations made throughout this
process, including the community and
state phases (see the Executive
Summary of NOAA’s FEIS for a
summary of the process). The scope of
authority defined in designation
documents for all national marine
sanctuaries is typically general, and the
implementing regulations are more
specific. NOAA believes this provides
sufficient parameters to its authority
while allowing flexibility to manage the
network adaptively in the future in
response to biological, ecological, and
economic indicators of the network’s
effectiveness. Any proposed regulatory
adjustment to the current network
would undergo rigorous environmental
review, analysis, and public input.
8. Comment: CINMS lacks a fisheries
manager position, expert fisheries
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advisory bodies, an extensive
stakeholder input process, and overall
adequate organization for fisheries
management, which will complicate
existing fisheries management
coordination.
Response: The CINMS marine zoning
process has required close coordination
among staff from the PFMC, NOAA
Fisheries, CDFG, FGC and NMSP, and
the constituents involved in the
respective public policy forums. See
Appendix D of the FEIS for a meeting
history among these organizations
during the CINMS marine zoning
process.
In addition, the CINMS Advisory
Council has provided, and will continue
to provide, a robust, open, and
transparent community based public
forum to provide advice to NOAA on
resource protection, education, and
research issues, including fishing issues
within the Sanctuary. The Advisory
Council has representatives from all
major sectors that utilize the CINMS,
including commercial and recreational
fishermen and the region’s primary
fisheries regulators, NOAA Fisheries
and the CDFG. In addition, the Advisory
Council’s recreational fishing working
group has representatives from local,
regional, and national fishing
organizations, including United Anglers
of Southern California and the
Recreational Fishing Alliance. The
commercial fishing working group
includes representatives from the Santa
Barbara and Ventura fishing
communities and fishing organizations
such as the Sea Urchin Harvesters
Association.
9. Comment: Commenter requests
funding for collaborative research
involving the fishing community.
Response: NOAA continues to
support and fund the Channel Islands
Collaborative Marine Research Program
(CMRP), managed by the Channel
Islands Marine Sanctuary Foundation,
which involves the commercial and
recreational fishing communities. To
date the CMRP has funded close to
$200,000 in research projects involving
commercial and recreational fishermen
and the scientific community. If future
CINMS budgets are stable, funding for
this program would continue.
10. Comment: NMSA fishery
regulations need to be enforceable,
clearly understood by the public, and
meet the goals and objectives of the
PFMC and NOAA.
Response: NOAA has utilized and
continues to seek guidance on
enforcement of NMSA regulations
provided by the PFMC Enforcement
Sub-committee, CDFG wardens,
National Park Service (NPS) Park
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Rangers, the NOAA Office of Law
Enforcement, and U.S. Coast Guard
(USCG) officials. These enforcement
experts have provided extensive input
on the regulations, and this input is
reflected in the final rule. Further, this
NOAA action is intended to achieve
goals established for the CINMS marine
zones under the NMSA, not specific
PFMC fishery goals.
11. Comment: The various agencies
are under-funded and there are not
enough staff members to monitor and
enforce the existing or proposed project.
Response: NOAA believes that
adequate resources exist to manage,
monitor, and report on the CINMS
marine zones. The Channel Islands
region benefits from the resources and
coordinated efforts of multiple state and
federal agencies and institutions.
Through formal and informal
agreements, the CDFG, NOAA, the
USCG, and the NPS will continue to
work collaboratively to monitor,
enforce, and manage the marine reserves
network.
In addition to research by these
agencies, other research organizations
and institutions (e.g., University of
California, California State Universities,
and California Sea Grant Extension
Program) have provided research,
monitoring and evaluation programs
and opportunities. Existing monitoring
projects will continue to provide data
on changes in the abundance of various
species in the region (see https://
www.dfg.ca.gov/mrd/channel_islands/
monitoring.html).
Interagency coordination will result
in more efficient use of NOAA and State
resources. CDFG enforcement staff
cooperates with other public agencies
through existing agreements and there
are several enforcement agreements and
funding mechanisms among the CDFG,
the NPS NOAA, and the USCG.
12. Comment: Commenter believes
there is currently not enough research
for NOAA to choose Alternatives 1 or 2
and therefore supports the no action
alternative.
Response: NOAA’s analysis contained
in the proposed rule, DEIS and FEIS
presents detailed information on the
projected biological and socioeconomic
impacts of its alternatives for this action
and believes this adequately supports
the final action.
13. Comment: Commenter requests
installation of artificial reefs and rigs-toreefs programs to create replacement
fishing opportunities to mitigate the loss
of fishing grounds.
Response: Under NOAA’s action,
fishing would continue to be allowed in
81% of the Sanctuary (over 800 square
nmi), subject to existing state and
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federal fishery regulations. NOAA
expects displacement impacts resulting
from its action will be minimal (see
section 5.1 of the FEIS). NOAA does not
believe there will be any significant loss
of fishing grounds and, therefore, no
need to develop any mitigation
measures at this time. The CINMS social
science program calls for monitoring
displacement of fishing effort to
determine if any mitigation efforts are
warranted. Should displacement
impacts prove to be significant in the
future, NOAA and the State have the
ability to take appropriate action under
their respective authorities.
14. Comment: The action will
displace fishing effort and increase
impacts in other areas.
Response: Displacement from
NOAA’s action is expected to be
minimal and less than significant (see
section 5.1 of the FEIS). Ongoing
monitoring, research, and evaluation
after implementation will provide
additional information on this issue.
Should displacement impacts prove to
be significant in the future, NOAA and
the State have the ability to take
appropriate action under their
respective authorities.
15. Comment: There is no dedicated
source of funding at CINMS for
education and outreach programs that
explain fishery management measures,
marine zoning, and marine access
programs.
Response: A significant amount of
funding from the CINMS budget is
dedicated to extensive education and
outreach efforts on the CINMS marine
zones. Since 2000, the CINMS education
and outreach program has been helping
the public understand what and where
the state marine reserves and marine
conservation areas are within the
Sanctuary, why they were established,
and what we can learn from them (see
the Public Awareness and
Understanding action plan in section III
of the CINMS draft management plan at
https://www.cinms.nos.noaa.gov/
manplan/overview.html). The CINMS
also works closely with CDFG to match
funding for marine zoning education
and outreach. Education and outreach
on regional fishery management
measures is addressed by NOAA
Fisheries, the PFMC, and the CDFG.
16. Comment: NOAA should consider
more stringent restrictions for
commercial lobster fishing and more
lenient restrictions for recreational
lobster fishing.
Response: Lobster fishing is regulated
by the FGC. The existing marine zoning
network adopted by the State of
California includes two marine
conservation areas (Anacapa Island
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MCA and Painted Cave MCA) that
permit recreational lobster harvest.
Commercial lobster fishing is allowed in
the Anacapa MCA, but not in the
Painted Cave MCA.
17. Comment: The FEIS should
discuss the effectiveness of other agency
management actions.
Response: NOAA’s DEIS included a
detailed discussion the relationship of
NOAA’s preferred action with other
existing management regimes in the
region (see, e.g., sections 2.2 and
3.1.2.1). The effectiveness of these
regulatory regimes in achieving NOAA’s
goals for this action is also discussed.
These sections are included in the FEIS.
18. Comment: The Channel Islands
National Marine Sanctuary (CINMS)
Advisory Council (SAC) should be
reformed to better address fisheries
issues. Specifically, the SAC lacks any
members with expertise in fisheries
economics, anthropology, geography,
etc.
Response: The SAC has
representatives from the CDFG and
NOAA Fisheries. Representatives from
these two entities, in addition to the
representatives from commercial and
recreational fishing interests and their
associated community-based fishing
working groups, provide NOAA with
significant insight into fisheries issues.
In addition, NOAA Fisheries and the
CDFG representatives also serve as a
conduit to the PFMC and FGC,
respectively, which brings NOAA
additional perspective on fisheries
issues. Moreover, the vast majority of
issues faced by the CINMS and its SAC
are not related to fisheries and,
therefore, require a broad and diverse
SAC membership.
19. Comment: The ‘‘effective date’’
provision in the proposed regulation is
unclear, burdensome, and inconsistent
with the model language previously
presented to the PFMC by NOAA for
inclusion under the NMSA 304(a)(5)
process, and therefore should not be
used.
Response: The effective date clause
has been omitted from the final rule.
20. Comment: Do not remove the
Marine Reserve Working Group’s
(MRWG) sustainable fisheries goal of
integrating marine reserves with
existing fisheries management.
Response: The goals for NOAA’s
action are based on the NMSA. NOAA’s
goals for this action do attempt to
address the goals put forward by the
MRWG where appropriate.
21. Comment: The CINMS should be
an ‘‘experimental station’’ for holistic
management.
Response: NOAA manages the
National Marine Sanctuary System on
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the principles of ecosystem-based
management. This ‘‘holistic’’ approach
attempts to incorporate all functions of
the marine environment into the
decision-making process at all
sanctuaries, including the CINMS.
22. Comment: NOAA should expand
its assessment of the action’s economic
impacts to better account for nonmonetary benefits.
Response: NOAA believes the
analysis of the passive (non-use) value
of the marine zones is sufficient to
inform its decision making on this
action (see Section 5.2.6 of the FEIS for
an evaluation of the passive values
associated with NOAA’s action).
23. Comment: Marine reserves are
superior to marine conservation areas in
meeting NOAA’s purpose and need and
are more consistent with the MRWG’s
recommendations.
Response: See section 3.1.2.2 of the
FEIS for a discussion of the differences
between marine reserves and marine
conservation areas.
24. Comment: Many commenters state
NOAA should implement the offshore
waters of the CINMS marine zone
network as the final phase of the CINMS
marine reserves process that began in
1999.
Response: See section 2.0 of the FEIS
for a description of the purpose of this
action, which identifies complementing
the existing state network as one of the
goals.
25. Comment: NOAA should consider
fishing as an important cultural resource
and protect it as such.
Response: NOAA has carefully
evaluated the impacts of the action on
fishing communities and has
determined the impacts to be minimal.
See section 5.2 of the FEIS.
26. Comment: Commenter is
concerned about the impacts of bottom
trawl and long line fishing, bycatch,
harvest of bait fish, pesticides and
pollution in the ocean, and impacts to
kelp and coastal ecosystems.
Response: Marine zones provide
reference sites in which to gauge the
impacts of many of the commenters’
concerns relative to fished areas.
27. Comment: Commenter
recommends increasing the number of
regional field game wardens and their
wages, increasing fines, and making
sure catch limits are enforced.
Response: NOAA recognizes the
critical role enforcement officials play
in management of the marine zoning
network. This recommendation,
however, is outside the scope of
NOAA’s immediate action.
28. Comment: NMSA fishing
regulations and designation document
amendments for the CINMS marine
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zones should automatically expire
(‘‘sunset’’) at the time MSA regulations
are promulgated.
Response: NOAA has determined that
provision a sunset date is not
appropriate because it would not
provide NOAA with the flexibility to
adaptively manage and respond to
unforeseen circumstances.
29. Comment: The proposed closures
don’t greatly affect commercial
fishermen, but the previous closures
have been devastating.
Response: NOAA’s analysis takes
existing fishery closures into account
and acknowledges their socioeconomic
and biological impacts. For this
particular CINMS action, NOAA’s
analysis has determined that the
socioeconomic impacts of new closures
in the federal waters of the network will
be minimal (see section 5.2 of the FEIS
for more details).
30. Comment: If sea urchin fishermen
were offered money for their urchin
permits, they might move on to a
different career, but they can’t transfer
or sell their permits.
Response: The issue of permit
transferability is beyond the scope of
this action and would be handled by the
CDFG and FGC, who both issue and
manage these types of permits.
31. Comment: Pollution has a huge
impact on water conditions and the
resources in southern California.
Response: Marine resources in the
Southern California Bight, such as kelp
forest ecosystems, have declined under
pressure from a variety of factors,
including commercial and recreational
fishing, changes in oceanographic
˜
conditions associated with El Nino and
other large-scale oceanographic cycles,
introduction of disease, and increased
levels of pollutants. Marine reserves
offer scientists and resource managers a
controlled opportunity to study the
influence of change (e.g., pollution) on
marine ecosystems in the absence of
direct human disturbance (e.g., fishing
pressure).
32. Comment: The regional seal
population negatively impacts the
regional halibut population.
Response: The management of seals
and halibut as individual species falls
under the purview of NOAA Fisheries
and the PFMC and is outside the scope
of this rule.
33. Comment: The DEIS was not
distributed to the United Anglers of
Southern California.
Response: NOAA records indicate the
President of United Anglers of Southern
California was sent a copy of the DEIS
on Aug. 11, 2006, and was notified
electronically via e-mail of the
availability of the document on the
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CINMS Web site or by requesting a copy
from the CINMS.
34. Comment: NOAA’s aerial
monitoring program data does not
account for existing regulations (such as
the Rockfish Conservation Area)
displacing fishing vessels. NOAA has,
therefore, erroneously concluded that
there is little fishing activity in the
proposed zones.
Response: NOAA’s aerial monitoring
program, which has been collecting data
since prior to the establishment of the
Rockfish Conservation Area, confirms
that there is little fishing activity in the
geographic area associated with NOAA’s
action. See section 5.2.6.4 of the FEIS
for NOAA’s analysis of this issue.
35. Comment: There are too many
marine reserves and not enough marine
conservation areas in NOAA’s proposed
action.
Response: Marine conservation areas
will not achieve the purpose and goals
of the action as well as marine reserves.
However, NOAA has decided to
establish one marine conservation area
off of Anacapa Island to ensure
consistency with the State of
California’s marine zone network,
which also established a marine
conservation area in that location. See
sections 3.1.2.2 and 5.1.1.1 of the FEIS
for more discussion on the ecological
value of marine reserves compared to
marine conservation areas.
36. Comment: NOAA should
implement marine parks where pelagic
fishing is allowed, especially in the
Footprint area.
Response: Allowing the take of
pelagic species does not fully meet the
goals of NOAA’s action. See section
3.1.2.2 of the FEIS for a discussion on
the impacts of limited take.
37. Comment: NOAA’s action will
negatively impact uses prioritized in the
Local Coastal Plan, such as commercial
fishing, tourism, and residential sectors,
and therefore the commenter supports
the no action alternative.
Response: NOAA supports healthy
fisheries, economies, and harbors and
believes the zoning network is likely to
support Sanctuary-dependent and
coastal dependent uses. The proposed
marine zones are expected to promote
visitation and may assist, over the long
term, in the sustainability of local
fisheries.
On March 16, 2007, the Coastal
Commission held a public meeting on
NOAA’s proposal pursuant to its
authorities under section 307 of the
Coastal Zone Management Act (16
U.S.C. § 1456). At that meeting, the
Coastal Commission issued a
conditional concurrence for the
consistency determination by NOAA on
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the grounds that, if modified as
described in the Commission’s
conditional concurrence below, the
project would be fully consistent, and
thus consistent to the maximum extent
practicable, with the policies of Chapter
3 of the Coastal Act. The conditional
concurrence is: ‘‘In the event NOAA
elects not to implement Alternative 1a,
NOAA will implement Alternative 1c,
with the following additional
provisions: until such time as the
Resources Agency and the Fish and
Game Commission designate the areas
in between the existing State-designated
MPAs and the 3 mile limit (i.e., the
‘‘gaps’’ between the existing state MPAs
and the federal MPAs depicted in
Alternative 1c), or the Fish and Game
Commission/DFG and NOAA enter into
an interagency agreement that
establishes MPA protection for these
‘‘gap’’ areas, NOAA will expand
Alternative 1c to include in its MPA
designation these ‘‘gaps’’ between the
outer boundaries of the existing state
MPAs and the State-federal waters
boundary (3nm from shore).’’ NOAA is,
therefore, leaving the record open with
regard to a decision to establish marine
zones in state waters of the Sanctuary,
and is requesting additional public
comment on this specific issue.
38. Comment: NOAA should not
reject the zone options put forward by
local fishermen.
Response: NOAA conducted a
preliminary analysis on all of the
fishermen options and determined that
they did not adequately or completely
protect a full range of habitats and
populations in the Sanctuary and thus
do not satisfy the purpose and goals of
NOAA’s action. For more, see section
3.2.5 of the FEIS.
39. Comment: Incorporate into the
FEIS all of the PFMC Science and
Statistical Committee’s (SSC) critique of
the CINMS marine zoning process and
Sanctuary documentation.
Response: The input from the SSC has
been addressed in NOAA’s analysis in
the FEIS. The SSC’s input can be found
at https://pcouncil.org/
40. Comment: Include a verbatim
copy of the original designation
document in the FEIS and proposed rule
so the public can compare the proposed
amendments.
Response: The original designation
document, in its entirety, and the
amendments being made by this action
are included in this preamble to the
final rule.
41. Comment: NOAA’s environmental
review process is not a robust stakeholder process like the PFMC process,
because CDFG and the PFMC are not
represented.
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Response: The CDFG, PFMC, and
NOAA Fisheries have been integral
partners in the process to date. CDFG
and NOAA Fisheries, which both have
membership on the PFMC, also hold
seats on the CINMS SAC.
42. Comment: Include discussions
and consultations with the State of
California, other agencies within NOAA,
and the other agencies within the
government in the public record.
Response: All official correspondence
related to this action and all comment
letters NOAA has received on this
action are available on the CINMS Web
site at https://www.cinms.nos.noaa.gov/
marineres/main.html.
43. Comment: Include in the FEIS the
journal article written by NOAA
employee Mark Helvey that critiques the
community-based phase of the CINMS
marine zoning project.
Response: NOAA has determined this
article is not integral to the decision
making process for this action and
should not, therefore, be included in the
FEIS.
44. Comment: Recreational fishermen
have a relatively minimal impact on the
resources and should not be excluded
from the CINMS marine zones.
Response: NOAA has determined that
any take of marine resources within the
marine reserves would compromise the
goals for this action. Limited take is
allowed in the Anacapa Marine
Conservation areas Area in order to be
consistent with the State’s action, which
in turn determined that the overall
benefits of limited take status in the
marine conservation areas (areas off
Anacapa Island and Santa Cruz Island,
the latter area totally in state waters)
might be studied in comparison to the
overall benefits of no-take status in
marine reserves. Fishing is allowed
throughout the rest of the Sanctuary,
subject to other existing federal and
state restrictions where applicable.
45. Comment: Restrict sea lion
populations in the CINMS region
because they may be contributing to the
demise of fishing.
Response: Sea lions are protected
under the Marine Mammal Protection
Act, which is administered by NOAA
Fisheries.
46. Comment: The decline in many
species, like abalone, is due to natural
cycles and the reintroduction of sea
otters, not over-fishing or excessive take
by sport divers.
Response: Abalone decline has been
linked to a combination of human and
natural caused influences. For more see
Karpov et al. 2000 and Moore et al.
2002. Karpov, K. A., P. L. Haaker, I. K.
Taniguchi, and L. Rogers-Bennett. 2000.
Serial depletion and the collapse of the
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California abalone (/Haliotis/ spp.)
fishery. /In/ Workshop on rebuilding
abalone stocks in British Columbia, A.
Campbell, ed. Can. Spec. Publ. Fish.
Aquat. Sci. 130: 11–24. Moore, J.D., C.
A. Finley, T. T. Robbins, and C. S.
Friedman. 2002. Withering syndrome
and restoration of southern California
abalone populations. CalCOFI Report.
43: 112–117.
47. Comment: The Gull Island and
Footprint closures will greatly affect
harpoon sword fishermen, who have
limited access to these two areas due to
weather, fishing seasons, and migration
patterns of the fish.
Response: While any impact may
seem significant for those who
experience it, NOAA’s economic
analysis has determined that the
socioeconomic impact to fisheries from
NOAA’s action will be minimal.
48. Comment: How will enforcement
work with a harpooned fish that swims
into a closed area?
Response: Each situation is evaluated
on a case by case basis to determine
whether an enforcement response is
warranted, and if so, the appropriate
course of action.
49. Comment: Commenter
acknowledges the usefulness of creating
an MPA for scientific study purposes,
but believes there is no urgent need to
do so in CINMS.
Response: For more on the need for
this action, see section 2.0 of the FEIS.
50. The Pacific Fishery Management
Council process is a fair, public and
scientifically based process to deal with
conservation and/or fishery
management questions.
Response: NOAA recognizes and
supports the PFMC’s role in addressing
fishery management issues.
51. Comment: The proposed closures
will affect the supply of seafood locally
and nationally.
Response: On page 25 of Leeworthy,
Wiley, and Stone (2005), the potential
impacts on supply and prices of various
seafoods are assessed for potential
losses as measured by consumer surplus
(i.e., losses to consumers from
restrictions in supply of commercial
seafood). Per this analysis, none of the
alternatives considered would change
the amount of supply enough to have
any effects on prices and thus, no loss
in consumer surplus. Leeworthy,
Vernon R., Peter C. Wiley and Edward
A. Stone, 2005. Socioeconomic Impact
Analysis of Marine Reserves for the
Channel Islands National Marine
Sanctuary. U.S. Department of
Commerce, National Oceanic and
Atmospheric Administration, National
Ocean Service, Special Projects, Silver
Spring, Maryland, May 2005.
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52. Comment: If an area is closed to
commercial fishing it should also be
closed to recreational fishing because
recreational fishing has an impact on
the resource too.
Response: All fishing (both
commercial and recreational) in the
marine reserves is prohibited. See
Response 44 for information about the
Anacapa Marine Conservation Area.
53. Comment: The simultaneous rule
changes to both the CINMS management
plan and designation document indicate
that the NMSP intended to create the
marine zones well in advance of it
having the authority to do so, indicating
the process has been designed simply to
justify the preconceived conclusion.
Response: This action and the CINMS
management plan review process are
distinct processes with separate and
distinct rules and amendments to the
CINMS designation document. With
regard to the designation document
changes and regulations for this action,
NOAA has followed the processes to
prepare NMSA regulations for fishing
(and other activities) and to amend the
CINMS designation document in
compliance with the requirements of the
NMSA. A history of the NMSA process
for preparing fishing regulations and
amending the Sanctuary’s designation
document for this action can be found
on the CINMS Web site at https://
channelislands.noaa.gov/marineres/
main.html.
54. Comment: NOAA fails to provide
scientific support for the need to impose
the severe restrictions on recreational
fishing.
Response: The need for NOAA’s
action is detailed in general in section
2.0 and specifically as it pertains to
recreational fishing in section 5.1.1.1 of
the FEIS.
55. Comment: NOAA fails to
adequately address the proposals of the
Pacific Fishery Management Council
with regard to management under the
Magnuson-Stevens Act.
Response: The PFMC’s proposal that
was submitted through formal
consultation did not fulfill the purpose
and goals of this action (see, for
example, section 3.1.2.1 of the FEIS for
more details on this process). See also,
for example, the responses to #4 and
#17 above.
56. Comment: NOAA fails to consider
the economic impacts on recreational
fishing beyond the charter sector.
Response: In addition to the charter
sector, NOAA’s economic impact
analysis on recreational fishing
included evaluation of impacts to
private boat fishing and consumptive
diving (see section 5.2.3 of the FEIS).
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57. Comment: The DEIS justifies a
preconceived outcome, rather than
providing the analysis of a full range of
options as required by the National
Environmental Policy Act.
Response: The range of alternatives
and analysis of them is sufficient under
the requirements of NEPA (see section
3.1 of the FEIS).
58. Comment: NOAA fails to properly
follow the requirements of the NMSA in
preparing regulations for fishing and
modifying the CINMS terms of
designation.
Response: NOAA has followed the
processes to prepare NMSA regulations
for fishing and to amend the CINMS
designation document in compliance
with the requirements of the NMSA. A
history of the NMSA process for
preparing fishing regulations and
amending the Sanctuary’s designation
document for this action can be found
on the CINMS Web site at https://
channelislands.noaa.gov/marineres/
main.html. See also, for example,
memorandum for the record from Daniel
J. Basta, Director, National Marine
Sanctuary Program, re: Reiteration of
Rational for the Decision to Issue
Fishing Regulations for the Channel
Islands National Marine Sanctuary
under the National Marine Sanctuaries
Act.
59. Comment: Acknowledge in the
FEIS and final rule that fishing
regulations are being developed by the
PFMC that relate to this action.
Response: See section 3.1.2.1 of the
FEIS for a description of the correlation
between the PFMC’s actions and this
action. See also the response to #17
above.
60. Comment: Does quantifying the
difference between the biological
benefits of marine reserves versus the
biological benefits of limited take
marine conservation areas advance the
process of evaluating the cost benefit
analysis of the project under the NEPA?
Response: NOAA has determined that
marine reserves provide greater
biological benefit than marine
conservation areas. In addition,
prohibition of all take is necessary to
achieve the goals for this action. (See
Response 44 regarding the one marine
conservation area.) With regard to
economic evaluation, NOAA’s analysis
has determined that the potential
impacts are expected to be minimal.
61. Comment: Ecological response in
areas that are not currently fished or
lightly fished will likely be less than
that response predicted for protection of
more heavily fished areas in state
reserves.
Response: Final outcomes of the
marine zones will be subject to a variety
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of ecological and economic responses
that are challenging to predict. As
discussed, NOAA will monitor the
impact of the reserves to determine the
actual responses.
62. Comment: Conduct an analysis of
alternatives for the scale of no-take
reserves that could mitigate mandatory
stock rebuilding timelines and examine
alternatives to the size of CINMS
reserves that would mitigate the size of
the California Rockfish Conservation
zone in the Sanctuary as an explicit
trade off in stock rebuilding tactics.
Response: As stated in the FEIS, the
purpose of NOAA’s proposed action is
to further the protection of CINMS
biodiversity and to complement the
existing network of marine zones
established by the State. This action is
not being proposed as a stock rebuilding
measure.
The scale of marine zones in the
Sanctuary is expected to primarily affect
local populations of fish, rather than
stocks that range along the entire west
coast. Marine reserves that incorporate
locations where overfished groundfish
can be found may protect a portion of
the population from fishing mortality as
well as protect habitats from
disturbance by fishing and other gear.
NOAA’s action also addresses
ecological goals that do not relate to
fisheries management. The NOAA
Fisheries and State groundfish closures
are directed at rebuilding specific
species of groundfish, not at a wide
range of other species. In addition, the
groundfish closures are based on annual
assessments and could be removed if
assessments improve.
63. Comment: Assess stock rebuilding
goals and an adaptive management
approach to the MPAs in the event of an
oceanographic regime change that
results in more stable recruitment of
depleted fisheries.
Response: One of the benefits of
complete no-take zones is that they
provide research and reference areas.
Monitoring of the CINMS zones is
expected to provide information on a
wide variety of ecosystem parameters
(including oceanographic effects) and
the effectiveness of closing these areas
on Sanctuary biodiversity and habitat
protection. In addition, as stated above,
this action is to further the protection of
biodiversity of the CINMS and to
complement the existing network of
marine zones established by the State
and is not being proposed as a stock
rebuilding measure. Any changes to
groundfish conservation measures
would require action by the
implementing authorities, the PFMC
and NOAA Fisheries.
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64. Comment: Consider habitats that
are important to overfished groundfish,
including shelf and slope habitats
outside the CINMS boundary as a trade
off in relaxing regulations in the Cow
Cod Conservation zone.
Response: NOAA’s action was
developed through analysis of network
design based on ecological criteria
within the boundaries of the CINMS.
Further, NOAA’s action is to further the
protection of biodiversity and to
complement the existing network of
marine zones established by the State
and is not being done as a stock
rebuilding measure for an individual
species of fish. Any changes to the Cow
Cod Conservation zone would require
action by the implementing authorities,
the Pacific Fishery Management Council
and NOAA Fisheries.
65. Comment: NOAA should not take
on any more administrative capacity
until it develops performance criteria
for synthesizing and managing marine
reserves monitoring data.
Response: CDFG and NOAA have a
State/Federal partnership to monitor the
biological and socioeconomic changes
occurring inside and outside of the
CINMS marine zoning network. NOAA
works with a multitude of partners,
such as the National Park Service and
UCSB, to analyze data from a variety of
research projects. The Sanctuary
Advisory Council’s Research Activities
Panel (RAP) reviews research priorities
and activities related to the marine
zones and assists NOAA and the CDFG
with determining the effectiveness of
the zoning network. Performance
criteria are included in the monitoring
plans (see https://www.dfg.ca.gov/mrd/
channel_islands/monitoring.html).
66. Comment: The Species of Interest
list in the DEIS states that species at the
edge of their range are excluded from
the list. However, eight species on the
list, including Pacific ocean perch, dark
blotch rockfish, widow rockfish, black
rockfish, canary rockfish, yelloweye
rockfish, Pacific cod and Pacific herring,
have never been caught at the Channel
Islands.
Response: The CINMS occurs at a
biogeographic boundary between the
colder water Oregonian province to the
north and the warmer water Californian
province to the south. The western
portion of the Sanctuary typically lies in
the colder waters of the Oregonian
Province. San Miguel Island, with its
influence of Oregonian province waters,
may offer suitable habitat for species
that are more common in central and
northern California. For instance,
yelloweye rockfish and widow rockfish,
which are common between Alaska and
northern California, have been
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documented to occasionally occur at
San Miguel Island (Love et al. 2002).
67. Comment: A discrepancy exists
between the fishing regulations reported
in Appendix F of the DEIS and the notes
regarding the status of fishing for certain
species in Appendix G. For example,
Appendix G lists pink, red and white
abalone as fished species, while
Appendix F states that abalone may not
be taken.
Response: Footnote 1 in Appendix G
intends to identify species that have
either been historically fished and/or
currently fished in the CINMS. The
language has been clarified to highlight
that species denoted with the footnote
could indicate either a historical or
current fishery.
68. Comment: The Sanctuary is only
providing 1.7 square miles for pelagic
fishing, while prohibiting fishing in
approximately 130 square miles.
Response: Under NOAA’s action,
pelagic fishing would continue to be
allowed in 81% of the Sanctuary (over
800 square nmi), subject to existing state
and federal fishery regulations.
69. Comment: When reserves network
experiments are designed to sustain
fisheries, the monitoring programs must
be designed to measure the species they
are designed to manage. The commenter
provides several specific
recommendations for such a monitoring
program.
Response: Although NOAA’s action is
not being implemented to sustain
fisheries, the zone monitoring program
for the CINMS network is guided by the
CDFG’s Channel Islands Marine
Protected Area Monitoring Plan and the
Channel Islands Deep Water Monitoring
Plan Development Workshop Report.
The monitoring programs involve a
variety of partners collecting data on
species, communities and habitats that
occur in the Sanctuary. Performance of
the zone network will be based on
analysis of trends in biological
parameters, such as abundance, mean
size and reproductive potential of
various species. Performance may be
determined by either examining
biological parameters at an individual
site before and after the designation of
the zone or comparing biological
parameters at sites inside and outside of
the zones.
A multitude of partners work with
NOAA and CDFG conducting
monitoring activities and collecting
information on a variety of species and
habitats. The data collected on a
comprehensive suite of species
inhabiting the Sanctuary allows for an
assessment of zone effectiveness on both
targeted and non-targeted species as
well as community-level changes as a
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result of prohibited activities. NOAA
and the CDFG plan a major review of
the monitoring program’s results in
spring of 2008. For more information on
the monitoring program, go to https://
www.dfg.ca.gov/mrd/channel_islands/
monitoring.html.
70. Comment: There is no scientific
validity of identifying the transition
zone as a unique region between the
Californian and Oregonian bioregions
and therefore the recommendations on
the number and spacing of individual
zones and total size of the preferred
alternative is flawed.
Response: The transition zone was
identified as a unique region by the
Science Advisory Panel during the
MRWG process. The zone is delineated
by steep persistent isotherms from
satellite sea surface temperature images.
It is a region with its own dynamics
relative to the Oregonian and
Californian subregions within CINMS.
Unique species interactions occur in the
transition zone because of mixing of two
groups of species from the adjoining
bioregions.
Marine reserves in the transition zone
provide several ecological benefits.
First, they may function as replicate
sites that provide insurance that a single
catastrophic event would most likely
not impact all zones at the same time.
Second, establishment of marine
reserves in the transition zone enhances
three of the criteria that contribute to
biodiversity conservation: habitat
representation, habitat replication, and
connectivity between individual
reserves that contribute to meeting the
action goals (as discussed in Section 3.3
of the FEIS). Finally, protection of
habitats and species in the transition
zone is also valuable to scientists
because it allows them to utilize the
unique species’ interactions to study
marine evolution and ecology.
71. Comment: The DEIS describes
Sanctuary resources as in decline,
which is flawed and inaccurate.
Response: Section 4 of the FEIS,
Affected Environment, has been
´
updated vis-a-vis the DEIS to include a
discussion of the current status and
trends of those species that were
historically in decline and are now
showing some signs of recovery. For
example, giant kelp distribution and
productivity in California has increased
˜
since the 1998 El Nino event,
potentially as a result of a decadal shift
in climatic conditions, although not to
historical levels preceding the 1980s.
However, a general declining trend in
the density and abundance of kelp
canopy over the past 40 years has been
documented in the scientific literature,
particularly in southern California. The
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decline has been attributed to a variety
of both natural and human caused
disturbances. Natural disturbances
include a corresponding warming trend
in sea surface temperatures and the
˜
frequency of severe El Nino events.
Human caused disturbances include
increased turbidity, siltation, pollution
and commercial and recreational fishing
activities that remove animals such as
California sheephead and California
spiny lobster that affect species grazing
on kelp.
Over the past few years,
oceanographic conditions have been
characterized by relatively cool summer
sea temperatures and winters with
relatively few large swell events. Such
conditions are generally favorable for
kelp resulting in stronger recruitment
and an increase in canopy area of some
beds in southern California. It is
unknown if the increase in kelp
productivity over the last few years will
be sustained given the inherent interannual variability of the oceanographic
environment. Furthermore, the effect of
oceanographic conditions on kelp
productivity is not uniform across all
kelp beds. Certain beds in the Sanctuary
that historically had an abundance of
kelp remain mostly devoid of kelp and
are dominated by echinoderms when
studied during summer 2006. In these
locations, kelp did not respond to a
change in oceanographic conditions,
indicating that other factors drive
productivity.
Some marine mammal populations,
such as gray whales and humpback
whales, appear to have increased due to
additional protection under the Marine
Mammal Protection Act. Also refer to
section 2.2 of the FEIS, Need for Action,
for further details on the need for this
action.
72. Comment: Many highly migratory
and epipelagic species that traverse
through the Sanctuary receive no benefit
from site specific MPAs.
Response: Highly migratory and
pelagic species may receive benefits
from marine reserves even if they spend
more time outside than inside marine
reserves. Highly migratory and pelagic
species fulfill an ecosystem role within
marine reserves as predators on and
forage for other species. Such species
may benefit from fully protected zones
if their prey is concentrated in a given
area or if the zones include breeding,
aggregating or resting grounds.
Scientific research suggests that pelagic
species gather in certain spots (usually
banks or ridges), particularly during
critical life cycle stages. Establishment
of marine reserves in these areas is
crucial, as the number and size of
pelagic animals in the food web dictates
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what other organisms thrive or decline.
In other words, direct pressure on
pelagic species causes indirect pressure
on other species present in the
ecosystem.
73. Comment: The DEIS has not
addressed the ecosystem benefits of
existing fishery management to achieve
the Sanctuary’s biodiversity goals.
Response: Section 2.2 (Need for
Action) of the DEIS and FEIS generally
discusses the ecosystem impacts of
existing fishery management measures,
while section 5.1 addresses this issue in
more detail.
74. Comment: Deepwater sponges and
corals should be included as species of
interest.
Response: NOAA recognizes that
there are other important species, such
as deepwater sponges and corals, that
are not included in the Species of
Interest list. This section of the DEIS
was written in 2000, preceding the
discovery of these deepwater species
sponges and corals. As such, there
remains the possibility of other species
and communities yet to be discovered.
75. Comment: NOAA should use the
best available substrate information to
update Figure 11.
Response: NOAA has updated the
substrate information using United
States Geological Survey (USGS) high
resolution data to refine description of
each individual marine zone where data
is available. The USGS data could not
be used to re-analyze the percentage of
each habitat type included in each
alternative because it is not available for
the entire Sanctuary. Currently, 20% of
the Sanctuary has been mapped with
high resolution technology.
76. Comment: There is a lack of
information on marine zone benefits in
temperate waters. Based on data from
tropical reef ecosystems, marine
reserves may only benefit a small group
of west coast nearshore resident species.
Response: Over the last five years,
many peer-reviewed research articles
have highlighted the effects of marine
reserves on temperate marine
ecosystems. A meta-analysis of
temperate water marine reserves shows
that many species tend to benefit from
the establishment of marine reserves as
measured by biomass, density and size
of individuals as well as diversity of
communities within their bounds. See
Section 5.1.1 of the FEIS for a
discussion of marine reserve benefits in
temperate marine ecosystems.
77. Comment: The FEIS should
address the benefits of the proposed
marine reserves to southern sea otter
recovery.
Response: There are no formal studies
on the benefits of marine reserves to
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southern sea otter recovery. Sea otter
sightings in the zones are rare at this
time. However, marine reserves are
generally expected to increase the
biomass of apex species within their
bounds and could potentially benefit
sea otters by increasing the populations
of their prey, such as abalone, urchins,
clams, and crabs.
78. Comment: Provide a detailed
discussion of habitat patch replication
for Alternative 1A.
Response: A discussion on habitat
patch replication of Alternative 1 has
been added to Section 3.3 in the FEIS.
79. Comment: Provide an analysis and
discussion that describes the actual
distances between protected habitats
within an MPA for each alternative
rather than the average distance.
Response: A discussion on
connectivity has been added to Section
3.3, specifically, by providing a figure
and discussion on the distances
between individual marine zones for
each alternative.
80. Comment: Provide more detailed
information on the number and
distances between patches of rocky
substrate included in the MPA network.
Response: The discussion on
connectivity has been updated to
include distances between patches of
rocky substrate.
81. Comment: Include Alternative 2 in
the analysis of management
considerations and in the table
summarizing the alternatives’
management considerations.
Response: As stated in the DEIS, the
same management considerations for
Alternative 1A apply to Alternative 2. A
column has been added to Table 52 of
the FEIS.
82. Comment: In Section 5.1 of the
DEIS, NOAA claims adverse ecological
impacts are ‘‘unlikely.’’ If adverse
ecological impacts are defined as
declines in abundance, then this term
should be redefined.
Response: NOAA considers ‘‘adverse
impacts’’ as those impacts that are
counter to the goals identified for this
action, such as ensuring the long-term
protection of Sanctuary resources by
restoring and enhancing the abundance,
density, population age structure, and
diversity of the natural biological
communities. NOAA recognizes that
declines in abundance of certain species
are an expected outcome of zone
designation, but does not consider this
in all cases to be an adverse ecological
impact. For example, certain
commercially targeted species may
increase in abundance (e.g., spiny
lobsters) due to reduced fishing pressure
while their prey items decrease (e.g.,
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purple urchin) because of an increase in
lobster predation.
83. Comment: Language in Section 5.1
indicates that relatively little fishing
activity occurs in the proposed marine
zones. The statement does not account
for the fact that other regulations
currently restrict fishing in these areas.
The discussion should clarify this point
by adding ‘‘currently’’ before ‘‘relatively
little activity.’’
Response: This recommendation has
been added to the FEIS.
84. Comment: Provide references for
assertions regarding the ecological
impacts of the no-action alternative
made in section 5.1.2 of the DEIS.
Response: Section 5.1.2 provides
references regarding current and future
anthropogenic stresses on California’s
coastal environment.
85. Comment: Add a reference for the
recommended distances between
marine zones.
Response: References for
recommended distances between
marine zones have been added.
86. Comment: The statement in the
DEIS (section 5.1.6) that the spot prawn
trawling prohibition is a response to
declining catch and bycatch of bocaccio
is incomplete and needs clarification.
The trawl closure for spot prawns was
implemented primarily due to concerns
of potential damage to high relief habitat
from roller gear and from overall levels
of bycatch, particularly finfishes,
relative to spot prawn catch.
Response: As the commenter states,
the trawl closure for spot prawns was
implemented primarily due to concerns
of potential damage to high relief habitat
from roller gear and from overall levels
of bycatch, particularly finfishes,
relative to spot prawn catch. The FEIS
has been revised accordingly (see page
102 of the FEIS).
87. Comment: It is illogical to include
potential impacts from the existing
Channel Islands state marine zones as
this impact should have already
occurred.
Response: Under NEPA guidelines
NOAA is required to consider
cumulative impacts which include the
impacts of the state MPAs in the
analysis. Please see Table 25 of the
FEIS, (Commercial Fishing and Kelp—
Summary of Impacts by Alternative Step
1 Analysis), which clearly distinguishes
the cumulative impact of the ‘‘Total
New Proposal.’’
88. Comment: The kelp fishery should
not be included in the analysis, since no
kelp beds occur in the proposed MPAs.
Response: NOAA agrees there is no
impact to kelp harvesting in the federal
water marine zones (see Table 26 of the
FEIS, which indicates the ex-vessel
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value of kelp at 0% in the additional
state and federal water areas). However,
under its NEPA guidelines (NOAA
Administrative Order 216–6), NOAA is
required to consider cumulative
impacts, which include the impacts to
kelp harvesting in the existing state
marine zones (Table 26 indicates the exvessel value for these areas is 5.48%).
89. Comment: Table 26 and Table 31
are confusing because the column
headers say ‘‘value’’ but what the tables
depict is actually ‘‘impact’’ to the
fisheries. It would help to add another
column just before the last one that lists
the total value of each fishery.
Response: Ex vessel value is what the
fishermen receive as revenue for their
catch and only represents one category
or portion of the total impact, i.e., the
impact to fishermen. Other categories
include income, employment, etc. To
use the word ‘‘impact’’ in the table
would be misleading, because the tables
contain ‘‘maximum potential loss’’, i.e.,
all ex vessel value associated with the
alternative, which is not expected as the
final impact, as one would expect
fishers to engage in mitigating behavior.
The total value of each fishery is
provided in Table 18 of the FEIS.
90. Comment: If $24,233,406 is used
as the total value of all fisheries (Table
24, Column 2), and $3,012,974 is the
total potential impact (Table 26 bottom
of next to last column), then the percent
total impact should be 12.43, and not
12.50 as listed at the bottom of the last
column in Table 26. For Table 31, a
similar problem occurs.
Response: The commenter’s
calculations are incorrect because they
used the total baseline kelp and
commercial fishing as the numerator,
not the total of species for which the
analysts have spatial data.
91. Comment: In 2003 to 2005, the
landings for the port of Santa Barbara
for the nearshore, shelf, and slope
rockfish fisheries should not be
considered as having ‘‘steep’’ declines.
Shelf rockfish landings actually
increased during this period.
Response: The commenter’s estimate
of what is sustainable for rockfish, and
therefore the baseline for assessing
socioeconomic impact, is still most
likely an overstatement given the
generally strong downward trend of the
entire species group.
92. Comment: There isn’t much
fishing pressure in the proposed reserve
areas, thus the economic impact of
reserve establishment will be minimal.
Response: NOAA’s analysis shows
that the fishing activity in the marine
zones is indeed minimal.
93. Comment: Further closures,
particularly in the Smugglers’ Cove/
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Yellow Banks area, would result in
economic harm to the sportfishing
industry.
Response: There are no marine zones
proposed for the Smugglers’ Cove/
Yellow Banks area. Furthermore, the
economic analysis associated with this
action predicts the overall impacts to
the sportfishing industry will be
minimal. See section 5.2.3 of the FEIS.
94. Comment: The data used in
NOAA’s economic analysis are dated
and there are additional sources now
available that should be used to update
the document.
Response: The estimates from
Leeworthy, Wiley, and Stone (2005) are
based on the best available information.
Adding one or two years of recent data
does not necessarily provide a better
estimate. In statistics, this would be
recognized as an ‘‘outlier’’ influencing
the estimate of the mean.
More recent trends show that for some
species the 2000–2003 averages are
better measures of what could be
sustainable than the 1996–1999 average
used in prior analyses. Economic
impacts were updated based on these
new assessments of what is sustainable
and can be found in Leeworthy, Wiley,
and Stone (2005).
Although some of the information is
several years old, it is the only spatially
distributed data available. The
distributions represent a historical
average of areas fished over four to five
year time periods and were provided by
fishermen. For a more detailed
socioeconomic impact analysis, see
Leeworthy, Wiley, and Stone (2005).
95. Comment: The socioeconomic
analysis underestimates the impacts of
the preferred alternative to commercial
fishing.
Response: It can be expected that
there will be short-term losses to the
commercial fisheries from Alternative 1.
However, overall the impacts are small
and the net cost or benefits to
commercial fisheries are likely to be
negligible. See also response #29 above.
96. Comment: Please clarify how the
‘‘Baseline person days of recreation
activity’’ were determined and reevaluate these statistics. Discrepancies
between the ratio of private and charter
boat dives, and consumptive vs. nonconsumptive divers seem inaccurate.
Commenter questions whether trips in
Santa Barbara are less expensive than in
Los Angeles.
Response: Baseline person-days of
recreation activity were determined by a
survey of all charter and party boat
operations active in the CINMS. Private
boat fishing and consumptive diving
data were compiled from a variety of
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sources (see Leeworthy, Wiley and
Stone, 2005, Appendix B).
The data does not show discrepancies
or relative price differences among
geographic areas.
97. Comment: Clarify the meaning of
‘‘employment’’ in private boat diving.
Response: Employment related to
private boat fishing and diving occurs
through the expenditures paid by those
engaged in the activity. This includes
fuel, food, beverages, lodging,
transportation, launch fees, etc. For each
industry, there is an assumed ratio of
sales and employment. Additionally,
there is a multiplier effect, which
accounts for additional employment of
businesses supplying these businesses.
For a complete explanation, see
Leeworthy, Wiley, and Stone (2005).
98. Comment: The kayaking statistics
seem inaccurate. Commenter claims that
last year, for example, there were 7,000
kayaking days at Scorpion Anchorage,
Santa Cruz Island.
Response: The kayaking statistics only
include that activity associated with
charter/party operations. The analysis
does not include non-consumptive
activity undertaken with private
household boats. No institution
estimates this activity. A project
currently underway in the
Socioeconomic Research & Monitoring
Program for the CINMS is tracking the
amount of this activity.
99. Comment: Make the tables easier
to understand, and if appropriate
presented as figures instead. If the
numbers are estimates, add confidence
intervals. If differences are significant,
that should be noted with the level of
significance. Clarify the time period and
area in which the data was gathered.
Response: Figures would not provide
the level of detail required to provide all
of the necessary information. None of
the estimates were derived through a
stochastic process and therefore
confidence intervals are not calculable.
The time period is stated clearly in the
text.
100. Comment: Commenter states that
the negative perception toward Channel
Islands MPAs by recreational fishermen
has resulted in diminished recreational
fishing effort and, consequently, lower
revenues for businesses that serve
recreational fishing interests in Santa
Barbara and Ventura Counties.
Response: Scientifically credible and
verifiable data regarding the statements
made was not provided by the
commenter and NOAA is not aware of
any such data.
101. Comment: Add an expenditure
that represents guiding fees for
kayaking, e.g., a day kayaking trip is
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approximately $180.00 (including boat
fee).
Response: Kayaking fees are included
in the analysis. See page 31 of
Leeworthy, Wiley, and Stone (2005) for
all recreation expenditure information.
102. Comment: Add data from the
National Economics Project, National
Park Service, and Chris LaFranchi.
Response: The commenter did not
provide NOAA with sufficient
information to provide a response.
103. Comment: The impacts shown
are partially an artifact of the proposed
zoned areas being temporarily closed by
fisheries management measures.
Recommend noting that current EFH
rules may change.
Response: In the Step 2 analysis in the
FEIS, other regulations are discussed
and how they might impact the
estimates presented in the Step 1
analysis, which includes ‘‘maximum
potential loss’’.
104. Comment: To protect the
fisheries dependent infrastructure of
Ventura Harbor, integrate into the
NOAA action goals for sustainable
fisheries, maintenance of long-term
socioeconomic viability, and
minimization of short-term
socioeconomic loses to all uses and
dependent parties.
Response: The goals for NOAA’s
action are guided by the NMSA and are
clearly stated in section 2.0 of the FEIS
as well as earlier in this preamble to the
final rule.
105. Comment: Regulatory agencies
should promote collaboration between
competing interests to accomplish
mutual fisheries goals.
Response: The SAC/MRWG process
and State/Federal partnership and
coordination with the PFMC have
promoted collaboration between all
interested parties. NOAA’s goals for this
action are not fisheries-specific.
106. Comment: Multiplier effects for
the local community and the state
economy must be factored into
socioeconomic data for a fisheries
management plan to be effective.
Response: NOAA’s socioeconomic
analysis includes indirect impacts to
fisheries-related support services and
businesses (multiplier effects). This
methodology is detailed in Leeworthy,
Wiley, and Stone (2005) on pages 13–16
for commercial fishing and 28–29 for
the recreation industry. The analysis
utilized multipliers created specifically
for the commercial fishing industry. The
multipliers were obtained from the
Fishery Economic Assessment Model
(FEAM). The FEAM was developed
under contract to the PFMC, and is
based on input-output models detailing
inter-industry relationships. The FEAM
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was designed for regional economic
analysis and processing of the
commercial fishery landings taking
place within the county where the port
is located.
107. Comment: Ex-Vessel value
reported in Table 19 of the DEIS
suggests that current regulations have
effectively reduced the number of
commercial fishing operators and show
lower catch volumes. These trends
translate into less fish harvested in the
region. The percentage of vessels
reporting catch from CINMS has
declined from 79% in 2000 to an
average of 47% in subsequent years.
Response: Table 19 shows a decline in
vessels reporting catch from CINMS
from 79 percent in 2000 down to 34
percent in 2002, followed by an increase
between 2002 and 2003.
108. Comment: Commenter indicates
there is a decrease of 86% in the
cumulative ex-vessel value for the
Ventura Harbor when comparing the
study area totals for ex-vessel value by
port in Table 17 (Commercial Fishing:
Study Area Totals Ex Vessel Value by
Port) to Table 27 (Commercial Fishing—
Alternative 1 Study Area Totals, Ex
Vessel Value by Port)
Response: The two tables are not
showing the same estimate. Table 17
shows the study area total, while Table
27 shows the total in Alternative 1. The
estimate in Table 17 did not ‘‘decrease’’
to the estimate in Table 27.
109. Comment: Ventura County has
the highest economic dependency on
activities in the CINMS, relative to all
counties in the study area, as shown in
Table 11 (Local/Regional Economic
Dependence on CINMS Baseline
Personal Income).
Response: While any impact may
seem significant for those who
experience it, the table also shows that
the baseline personal income associated
with all activities in CINMS for Ventura
County is less than one quarter of one
percent of personal income for the
county.
110. Comment: Ensure that nonconsumptive activities are sustainable
in the CINMS by balancing and
promoting collaboration between
competing interests.
Response: NOAA believes that the
CINMS Advisory Council provides an
ideal forum for ‘‘competing’’ interests to
discuss their respective issues regarding
use of the Sanctuary and to provide
input and advice on such matters to the
CINMS superintendent.
111. Comment: Provide the sources of
data for analysis of charter/party and
private boating impacts.
Response: The source of the
information is Leeworthy, Wiley, and
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Stone (2005) and is cited at the
beginning of sections 4.3.1 and 5.2 of
the FEIS. In Leeworthy, Wiley, and
Stone (2005), Appendix C documents all
data used in the assessment for the
recreation industry. A cumulative
analysis of impacts, including the state
areas of closure, is provided.
112. Comment: The socioeconomic
analysis fails to adequately address
displacement and impacts on
recreational access, ignores the
cumulative impact of existing state and
federal closures, and projects unverified
supply benefits.
Response: In the Step 2 analysis in the
FEIS, the potential short- and long-term
impacts to a fisherman’s ability to
relocate fishing activity to areas outside
marine zones is noted in qualitative
terms using an ecological-economic
model. It is not possible to estimate the
net outcomes of how the ecological and
economic processes will play out. For
example, replenishment effects from the
closed areas could offset the impacts of
displacement or vice versa. The
possibility of long-term losses to the
recreational fishing industry by
restricted access is acknowledged.
Several ecological and socioeconomic
monitoring efforts are underway, while
others are planned. Monitoring will
help determine what actual outcomes
will occur, and the major stakeholders
were involved in developing the priority
monitoring items.
113. Comment: Please update Table
11 (Local/Regional Economic
Dependence on CINMS: Baseline
Personal Income) and Table 12 (Local/
Regional Economic Dependence on
CINMS—Baseline Employment) and the
text explanations to reflect
socioeconomic impacts to all direct and
indirect incomes related to commercial
and recreational fishing.
Response: The estimates in Tables 11
and 12 do reflect socioeconomic
impacts to all direct, indirect, and
induced incomes related to commercial
and recreational fishing. This
methodology is detailed in Leeworthy,
Wiley and Stone (2005) on pages 13–16
for commercial fishing and 28–29 for
the recreation industry.
114. Comment: Include Leeworthy,
Wiley, and Stone (2005) as an appendix
to the Final EIS.
Response: Leeworthy, Wiley, and
Stone (2005) includes the sources of all
the economic data used in determining
the economic impacts. This report is
available at https://
channelislands.noaa.gov/marineres/
main.html. As such, to avoid bulk, it
was not added to the FEIS as an
appendix.
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115. Comment: The references and
data that analyze the value and
employment associated with ‘‘Total
Consumptive Activities’’ (Table 1.3 and
1.4) ignore the additional value of
businesses and services dedicated to
supporting commercial and recreational
fishing; recommend that the FEIS
include the value of these businesses
and support services in order to assess
overall economic impact.
Response: The additional businesses
and services dedicated to supporting
commercial and recreational fishing are
included in the estimates in Leeworthy,
Wiley and Stone (2005) on Tables 1.3
and 1.4 through the multiplier process.
This methodology is detailed on pages
13–16 for commercial fishing and 28–29
for the recreation industry.
116. Comment: The potential impact
on ports and the potential economic
costs of the percentage reductions in
catch landings should be included.
Response: Throughout the analyses
the percentage impacts on ex vessel
value of the catch is presented. Ex
vessel value of the catch is just pounds
of catch times the price per pound and
reflects both effects on supply and
demand. There is no added value of
listing percentage of pounds of catch
separately.
117. Comment: The overall potential
reductions in annual income and full
and part time employment should
include the values as percentages of the
regional and local commercial fishing
industries as well as the overall regional
economy.
Response: The suggested percentages
are in Table 25 of the FEIS.
118. Comment: Tables 27, 28, 29, 32,
33, and 34 (Commercial Fishing Impact)
do not include the values of support
services and businesses associated with
commercial and recreational fishing.
Response: The impacts on ex value of
the commercial fisheries are shown in
Tables 27 and 32. The impacts on
support services and businesses
associated with commercial fisheries are
included in Tables 33 and 34. Table 35
includes multiplier impacts for income
and employment for recreational fishing
as noted in footnotes 3 and 4 of Table
35.
119. Comment: Provide additional
details on the socioeconomic,
education, and outreach options that
minimize or mitigate potential increased
social costs and lawsuits, and increased
costs of enforcement.
Response: The State of California and
NOAA have developed ecological and
socioeconomic monitoring plans to
gauge the effects of the marine zones. In
addition, the agencies have developed
interpretive enforcement education
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materials (e.g., brochures, signage) with
affected stakeholders to better inform
users of the marine zones. Effective
communication of monitoring results
through education and outreach and the
application of interpretive enforcement
tools may defray or avoid these social
costs.
120. Comment: Partnering with the
Sanctuary to manage the zoning
network is very important.
Response: During the community
phase and establishment of state marine
zones, NOAA has relied on partners
such as State of California, National
Park Service, and U.S. Coast Guard, to
implement the zone network. See the
response to comment #2 for more
information on this issue.
121. Comment: The CDFG supports
Alternative 1C. It will work with FGC to
fill any spatial gaps between the existing
zones and the federal water zones.
Response: NOAA acknowledges the
CDFG’s position on the alternatives
analyzed in the DEIS. See the response
to comment #2 for more information on
this issue.
122. Comment: The CDFG supports
the proposed CINMS designation
document amendments.
Response: NOAA acknowledges the
CDFG’s support for the proposed
changes to the CINMS designation
document.
123. Comment: NOAA’s action may
reduce conflicts between seabirds and
fisheries, thus complementing NOAA’s
Office of Spill Prevention and Response
seabird restoration efforts.
Response: Although this outcome is
not a direct intent of this action, NOAA
supports the Office of Spill Prevention
and Response’s seabird restoration
efforts. Seabirds may become entangled
or hooked on fishing gear and their
feeding and breeding behaviors
disrupted by fishing activity, such as
fishing at night with bright lights.
124. Comment: Consultation with the
State of California is required under
Section 106 of the National Historic
Preservation Act.
Response: NOAA has complied with
all required consultations, including the
National Historic Preservation Act.
125. Comment: A number of
commenters expressed general support
for marine reserves, marine
conservation in general, and expanding
the CINMS.
Response: NOAA acknowledges these
comments.
126. Comment: The NOAA document
should define short-term losses to both
recreational and commercial fisheries,
why losses will be short-term, and how
the temporal nature of the impacts will
be measured.
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Response: As described in section
5.2.2.2 of the FEIS, short-term losses are
defined as impacts over the next 1–5
years and long-term impacts are defined
as 5–20 years. NOAA expects the
projected maximum potential economic
impacts to be primarily short-term
because NOAA expects the affected
community will be able to adapt to the
new regulatory environment.
NOAA’s socioeconomic monitoring
plan calls for monitoring value of
commercial fisheries catch (both inside
and outside the CINMS and in state
waters). Monitoring State-wide trends
helps to separate out effects that have
nothing to do with the CINMS marine
reserves.
For the recreational fisheries, NOAA
plans to monitor the following: (1)
Spatial use patterns and intensity of use
(total number of person-days of use); (2)
charter/party boats using CDFG
logbooks for Charter Passenger Fishing
Vessels (CPFV); (3) private boats using
the new California recreational fishing
statistics data; (4) socioeconomic
profiles of fishermen, including
expenditure profiles; (5) net value or
consumer’s surplus; and (6) knowledge,
attitudes and perceptions of
management strategies and regulations.
For more information, see the
Socioeconomic Monitoring Plan at
https://www.cinms.nos.noaa.gov/
marineres/main.html.
127. Comment: The expected
socioeconomic impacts to the
recreational and commercial fisheries
and fishermen’s income should be
compared to that sector’s total income
by county and not to the total county
income and regional data.
Response: The FEIS details how value
of catch by each species/species group
and the total across all species/species
group are impacted as a percent of all
commercial fishing catch from the
CINMS. This is also done by port and
the percentages present how the percent
of the total ports value of catch is
impacted by each alternative. See
appendix tables in Leeworthy, Wiley
and Stone (2005) for more information
on the impacts by port and by county
with the percents being the percents of
the totals for each county.
For the recreation industry, greater
detail is provided in Leeworthy, Wiley
and Stone (2005) on the total impacts by
county and percents of the total CINMS
recreation impacted from the total
CINMS recreation in the county.
128. Comment: As the focus of the
action is Santa Barbara Channel, data
relevant to this area, not the State as a
whole, should be used. A statement is
made that ‘‘almost 20 percent of those
who use California’s coastal areas for
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recreation are interstate or international
visitors * * *’’ Does this figure also
apply to the more geographically
limited Channel Islands area? Another
statement is made that as numbers of
people increase (referring to coastal
population growth), so do the number of
CINMS users. Are there any data to
support this statement? Does the
increase in CINMS use parallel the rates
of increase elsewhere?
Response: Recognizing there is a
paucity of data specific to the CINMS or
the specific local surrounding area of
Santa Barbara, Ventura, and Los Angeles
counties, NOAA used the best available
data to estimate the amount of activity
in the CINMS.
There were two sources of time series
data for assessing trends: NOAA
Fisheries’ Marine Fishing Statistics
Survey (MRFSS), which has now been
replaced with the California
Recreational Fishing Statistics Program,
and the U.S. Fish and Wildlife Service’s
National Survey of Hunting, Fishing and
Wildlife Associated Recreation. Both
estimate use for Southern California.
Leeworthy, Wiley, and Stone (2005)
summarize trends from these two
sources (page 27) and the trends from
the two sources were not consistent.
From 1993–1999, MRFSS shows a
downward trend, while from 1991–1996
(survey is done every five years) it
shows an upward trend. From 1999–
2002, MRFSS shows an upward trend.
A 1997 California Resources Agency
report estimated that for all coastal areas
20 percent of recreation is done by out
of State visitors. A Santa Barbara County
Conference & Visitors Bureau and Film
Commission report included an estimate
that 20 percent of the visitors to Santa
Barbara County were foreign visitors.
There are not any surveys of the visitors
to the CINMS to know if the same
would hold true for recreational users of
the CINMS. The statement that ‘‘as
coastal population grows, so will
number of CINMS users’’ is an
extrapolation from an assessment of
national trends for ocean and coastal
(marine) recreation from the National
Survey on Recreation and the
Environment (NSRE) 2000. Year 2000
data were analyzed for demographic
factors related to participation in marine
recreation activities and equations used
to forecast future participation for years
2005 and 2010. Generally, national
participation rates (the percent of the
U.S. population doing an activity) are
projected to decline. However, the total
number of participants is projected to
increase because the population growth
more than compensates for the lower
participation rates. The statement
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presumes these same trends may hold
for California or the CINMS.
129. Comment: There is no
quantitative evidence to show that nonconsumptive activities will increase in
the new zones, especially because all of
the non-consumptive use occurs
nearshore.
Response: The establishment of the
new marine zones is expected to result
in benefits to nonconsumptive
recreational users. While there is no
data currently available to directly
estimate the magnitude of these
benefits, NOAA conducted a benefits
transfer/policy analysis simulation to
quantify potential benefits. In addition,
a two year study is now underway to
help quantify these benefits. Nonconsumptive uses in the proposed new
zones are a relatively small percentage
of the total non-consumptive uses that
are concentrated in the nearshore waters
of the Sanctuary. See section 5.2.5 of the
FEIS for further discussion.
130. Comment: It is not clear how
closures will affect the marine zones or
how they will benefit the intent of those
closures. The DEIS indicates that the
proposed action would supplement the
closures by ‘‘establishing temporally
permanent zones,’’ but no details are
given and the statement is confusing.
Response: The action partially
supplements the existing fishery
closures, such as the Cowcod
Conservation Area. The designation of
marine reserves in or near areas
protected by fishery closures adds
another layer of protection, further
ensuring that no fishing will occur on
targeted species in the fishery closures
and the adjacent areas protected by the
marine reserves. Protection of the water
column and all biophysical
characteristics of marine reserves likely
will enhance the recovery of targeted
species protected by fishery closures by
eliminating bycatch and further
protection of habitats. Synergistic effects
may result from protection by marine
reserves of species and ecological
processes consistent and adjacent to
fishery closures.
131. Comment: Alternative 2 may
cause negative financial impacts to
coastal communities, recreational and
commercial boating, and specifically,
the ability of a local agency to repay
existing state loans that are used for the
construction and improvement of small
craft harbors.
Response: The state marine zones
have been in place for over three years
and there is no evidence that the ability
of local agencies to repay small harbor
construction and improvement loans
has been exacerbated due to impacts on
recreational and commercial boating
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from the state zones. Furthermore, there
is a marginal increase in the estimated
‘‘maximum potential impact’’ to
recreational and commercial boating
with the extension of marine zones from
the existing state marine zones into
deeper waters of the Sanctuary with
either Alternative 1 or 2.
132. Comment: The DEIS should
specifically address Environmental
Justice. The Council on Environmental
Quality requires this inclusion, and the
counties under consideration differ in
income and social structure.
Response: See Section 6.7 of the FEIS
for a discussion on Environmental
Justice and all other required
consultations.
133. Comment: The commercial
fishing sector developed five
alternatives that have lower economic
impacts to both recreational and
commercial fishermen than the
preferred alternative, because a balance
of marine conservation areas and marine
reserves was used instead of marine
reserves only.
Response: Marine conservation areas,
where certain fishing activity and
impacts to habitat and species still
occurs, would not achieve the purpose
and goals of the proposed project as
well as marine reserves. However,
NOAA has decided to establish one
marine conservation area off of Anacapa
Island to ensure consistency with the
State of California’s marine zone
network, which also established a
marine conservation area in that
location. See section 3.1.2.2 of the FEIS.
Also, see response #44 for the reason the
one marine conservation area is
included.
reserves, these activities would no
longer be prohibited under 15 CFR
922.73; or because 50 CFR part 660 is
being amended to allow the use of
bottom contact gear, that activity would
be prohibited under 15 CFR 922.73).
In paragraph (b)(3) of § 922.73, the
exception to the prohibition on
possessing Sanctuary resources has been
broadened somewhat to ensure fish that
were harvested in the marine
conservation area are allowed to be in
a person’s possession regardless of the
status of the person’s vessel.
In paragraph (a)(1), (a)(3), (b)(1), and
(b)(3), the phrase ‘‘any living or dead
organism, historical resource, or other
Sanctuary resource’’ has been replaced
with ‘‘any Sanctuary resource, including
living or dead organisms or historical
resources’’ in each place it appears to
clarify the application of the regulation
to all Sanctuary resources.
The reference to the Painted Cave
Marine Conservation Area in paragraph
(b) of § 922.73 been removed. The
Painted Cave Marine Conservation Area
is completely within state waters of the
Sanctuary, and is therefore (as discussed
in the preamble) not subject to this
rulemaking.
The coordinates for the marine
reserves and marine conservation area
in appendices B and C, respectively,
have been modified so that only federal
waters are included in this final rule. As
discussed in the preamble, should
NOAA decide to extend these marine
reserves and marine conservation area
into state waters of the Sanctuary,
another final rulemaking action will
further modify these coordinates as
appropriate.
VI. Changes From Proposed Rule
NOAA made changes to the proposed
rule issued on August 11, 2006 to
respond to public comments. The
changes are as follows:
In paragraphs (a) and (b) of § 922.73,
the reference to the effective date of the
final rule has been removed. The
purpose of this provision was to ensure
that changes made to NOAA’s MSA
regulations after the effective date of the
final NMSA regulations would not affect
the applicability of the NMSA
regulations without public notice.
NOAA has decided (1) to insert a
reference to these NMSA regulations in
NOAA’s MSA regulations at 50 CFR part
660 as part of this final rulemaking, and
(2) in future notices proposing to amend
50 CFR part 660, to advise the public
and seek comment on any consequences
as it relates to the regulations at 15 CFR
922.73 (e.g., that because 50 CFR part
660 is being amended to prohibit fishing
in the water column of the marine
VII. Miscellaneous Rulemaking
Requirements
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A. National Marine Sanctuaries Act
Section 304 of the NMSA (16 U.S.C.
1434) requires the Secretary of
Commerce in designating a sanctuary to
submit Sanctuary designation
documents to the United States
Congress (Committee on Resources of
the House of Representatives and the
Committee on Commerce, Science, and
Transportation of the Senate) and
Governor of each state in which any part
of the Sanctuary would be located. The
designation documents are to be
submitted on the same date the notice
is published and must include the
proposed terms of the designation, the
proposed regulations, a draft
environmental impact statement, and a
draft management plan. The terms of
designation may only be modified by
the same procedures by which the
original designation is made. In
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accordance with Section 304, the
appropriate documents have been
submitted to the specified Congressional
Committees and the Governor of
California.
B. National Environmental Policy Act
In accordance with Section 304(a)(2)
of the NMSA (16 U.S.C. 1434(a)(2)), and
the provisions of NEPA (42 U.S.C.
4321–4370(a)), an FEIS has been
prepared for the proposed action.
Copies of the FEIS are available upon
request to NOAA at the address listed in
the ADDRESSES section. The FEIS notice
of availability was published on April
20, 2007 (72 FR 19928). The 30-day
period for the FEIS ended on May 21,
2007.
C. Executive Order 12866: Regulatory
Impact
This rule has been determined to be
not significant within the meaning of
Executive Order 12866.
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D. Executive Order 13132: Federalism
The Assistant Secretary for
Intergovernmental and Legislative
Affairs, Department of Commerce, has
consulted with appropriate elected
officials in the State of California, as
appropriate. Since 1999, NOAA has
partnered with and supported the State
in this effort. During the federal phase,
NOAA has continually briefed the
Secretary of Resources and the Director
of the California Department of Fish and
Game. NOAA also held numerous
consultations with all California
resource management agencies as
required under section 303(b)(2) of the
NMSA.
E. Regulatory Flexibility Act
In accordance with the requirements
of section 604(a) of the Regulatory
Flexibility Act (5 U.S.C. 604(a)), NOAA
has prepared a final regulatory
flexibility analysis (FRFA) describing
the impact of the proposed action on
small businesses. Section 604(a)
requires that each FRFA contain:
1. A succinct statement of the need
for, and objectives of, the rule;
2. A summary of the significant issues
raised by the public comments in
response to the initial regulatory
flexibility analysis, a summary of the
assessment of the agency of such issues,
and a statement of any changes made in
the proposed rule as a result of such
comments;
3. A description of and an estimate of
the number of small entities to which
the rule will apply or an explanation of
why no such estimate is available;
4. A description of the projected
reporting, recordkeeping and other
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compliance requirements of the rule,
including an estimate of the classes of
small entities which will be subject to
the requirement and the type of
professional skills necessary for
preparation of the report or record; and
5. A description of the steps the
agency has taken to minimize the
significant economic impact on small
entities consistent with the stated
objectives of applicable statutes,
including a statement of the factual,
policy, and legal reasons for selecting
the alternative adopted in the final rule
and why each one of the other
significant alternatives to the rule
considered by the agency which affect
the impact on small entities was
rejected. The FRFA is available upon
request to NOAA at the address listed in
the ADDRESSES section above. A
summary of the FRFA follows.
Summary of the Final Regulatory
Flexibility Act Analysis
1. Statement of need. A statement of
why action by NOAA is being
considered and the objectives of, and
legal basis for, this final rule is
contained in the preamble section of
this final rule and is not repeated here.
2. Summary of public comments.
Section V. in the preamble of this final
rule contains a summary of all of the
comments submitted to NOAA and
NOAA’s responses thereto. Some
comments about the economic impact of
the proposed action were submitted.
Refer, for example, to comment numbers
86 through 133 for summaries of these
comments and NOAA’s responses
thereto.
3. Number of small entities affected.
The Small Business Administration has
established thresholds on the
designation of businesses as ‘‘small
entities’’. A fish-harvesting business is
considered a ‘‘small’’ business if it has
annual receipts not in excess of $3.5
million (13 CFR 121.201). Sports and
recreation businesses and scenic and
sightseeing transportation businesses
are considered ‘‘small’’ businesses if
they have annual receipts not in excess
of $6 million (13 CFR 121.201).
According to these limits, each of the
businesses listed below are considered
small entities. (All analyses are based on
the most recently updated and best
available information.)
a. Number of commercial fishing
operations. In 2003, there were 441
commercial fishing operations that
reported catches from the CINMS. Total
commercial fishing revenue from the
CINMS was $17.3 million in 2003.
b. Number of consumptive
recreational operations. In 1999, there
were 18 recreational fishing charter/
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party boats operating in the CINMS. In
1999, there were 10 consumptive diving
charter/party boats operating in the
CINMS. Total reported 1999 gross
revenue from these consumptive
recreational activities was $8.8 million.
Total costs for 1999 were reported at
$8.4 million. After all costs were paid,
the consumptive recreational activities
resulted in $420,000 in profit.
c. Number of non-consumptive
recreational operations. In 1999, there
were 8 whale watching operations, 7
non-consumptive diving operations, 4
operations that offered kayaking or
island sightseeing activities, and 8
sailing operations, within the CINMS.
Total reported 1999 gross revenue from
these non-consumptive recreational
activities was $2.6 million. Total costs
for 1999 were reported at $2.5 million.
After all costs were paid, the nonconsumptive recreational activities
resulted in $82,000 in profit.
4. There are no new reporting,
recordkeeping, or other compliance
requirements.
5. Two alternatives plus a no-action
alternative were considered. The no
action (status quo) alternative would not
establish marine reserves and marine
conservation areas in the Sanctuary.
Therefore there is no economic impact.
Alternative 1C, the proposed
alternative, including both the existing
state network and proposed extensions,
would include approximately 110.5
square nautical miles of marine reserves
and 1.7 square nautical miles of marine
conservation areas for a total of 214.1
square nautical miles of the CINMS
when combined with the existing state
zones. The new proposed federal areas
of Alternative 1C potentially impact
0.51% (approximately $124,000) of ex
vessel value of commercial catch in the
CINMS. The total maximum potential
loss to the income of commercial fishing
businesses is 0.61% ($440,000) and to
the employment of commercial fishing
businesses is 0.66% (13 jobs). For
consumptive recreation in the CINMS,
the estimated maximum potential loss
associated with alternative 1 is $935,000
(3.5%) in annual income and about 42
full and part-time jobs (3.7%) in the
local county economies. For nonconsumptive recreation in the CINMS,
the estimated range of potential
increases in income generated in the
local county economies associated with
alternative 1 is between $337 and about
$380,000. The estimated range of
potential increases in employment in
the local county economies is between
0.02 and 19 full- and part-time jobs.
Alternative 1C was chosen as NOAA’s
preferred alternative because it best
accomplished the purpose and need of
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furthering the protection of Sanctuary
biodiversity while complementing the
existing State-designated network.
Alternatives 1A and 1B were rejected
because they involved the establishment
of federal marine reserves and marine
conservation areas in state waters of the
Sanctuary; which was opposed by the
State of California.
Alternative 2, including both the
existing state network and proposed
extensions, would encompass
approximately 275.8 square nautical
miles of marine reserves and 12.1 square
nautical miles of marine conservation
areas for a total of 287.8 square nautical
miles of the CINMS. Alternative 2 is
larger than alternative 1, and proposes
some different reserve areas not
proposed in alternative 1. The new
proposed federal areas of alternative 2
potentially impact 0.82%
(approximately $197,000) of ex vessel
value of commercial catch in the
CINMS. The total maximum potential
loss to the income of commercial fishing
businesses is 0.91% ($650,000) and to
the employment of commercial fishing
businesses is 0.97% (19 jobs). For
consumptive recreation in the CINMS,
the estimated maximum potential loss
associated with alternative 2 is
$1,300,000 (5.0%) in annual income and
about 59 full and part-time jobs (5.2%)
in the local county economies. For nonconsumptive recreation in the CINMS,
the estimated range of potential
increases in income generated in the
local county economies associated with
alternative 2 is between $748 and about
$841,000. The estimated range of
potential increases in employment in
the local county economies is between
0.04 and 44 full- and part-time jobs.
Please refer to comment/response #1 for
the reasons alternative 2 was rejected.
F. Paperwork Reduction Act
This rule contains a collection-ofinformation requirement subject to the
Paperwork Reduction Act (PRA) which
has been approved by OMB under
control number 0648–0141. The public
reporting burden for national marine
sanctuary permits is estimated to
average 1 hour per response, including
the time for reviewing instructions,
searching existing data sources,
gathering and maintaining the data
needed, and completing and reviewing
the collection of information. This rule
would not modify the average annual
number of respondents or the reporting
burden for this information
requirement, so a modification to this
approval is not necessary. Send
comments regarding this burden
estimate, or any other aspect of this data
collection, including suggestions for
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reducing the burden, to NOAA (see
and by e-mail to
David_Rostker@omb.eop.gov, or fax to
(202) 395–7285.
Notwithstanding any other provision
of the law, no person is required to
respond to, nor shall any person be
subject to a penalty for failure to comply
with, a collection of information subject
to the requirements of the PRA, unless
that collection of information displays a
currently valid OMB Control Number.
San Miguel Island, Santa Cruz Island,
Santa Rosa Island, Anacapa Island,
Santa Barbara Island, Richardson Rock,
and Castle Rock (collectively the
Islands) extending seaward to a distance
of approximately six nmi. The boundary
coordinates are listed in appendix A to
this subpart.
I 3. Redesignate §§ 922.71 and 922.72
as §§ 922.72 and 922.74, respectively.
I 4. Add § 922.71 to subpart G of part
922 to read as follows:
G. Unfunded Mandates Reform Act of
1995
This final rule contains no federal
mandates (under the regulatory
provisions of Title II of the Unfunded
Mandates Reform Act of 1995 (UMRA))
for State, local, and tribal governments
or the private sector. Thus, this rule is
not subject to the requirements of
section 202 and 205 of UMRA.
§ 922.71
ADDRESSES)
List of Subjects
15 CFR Part 922
Administrative practice and
procedure, Coastal zone, Education,
Environmental protection, Marine
resources, Natural resources, Penalties,
Recreation and recreation areas,
Reporting and recordkeeping
requirements, Research.
50 CFR Part 660
Administrative practice and
procedure, American Samoa, Fisheries,
Fishing, Guam, Hawaiian Natives,
Indians, Northern Mariana Islands,
Reporting and recordkeeping
requirements.
Dated: May 18, 2007
John H. Dunnigan,
Assistant Administrator for Ocean Services
and Coastal Zone Management.
Dated: May 17, 2007.
William T. Hogarth,
Assistant Administrator for Fisheries.
For the reasons stated in the preamble,
15 CFR chapter IX and 50 CFR chapter
VI are amended as follows:
I
15 CFR CHAPTER IX
PART 922—[AMENDED]
1. The authority for part 922
continues to read as follows:
I
Authority: 16 U.S.C. 1431 et seq.
I
2. Revise § 922.70 to read as follows:
§ 922.70
Boundary.
The Channel Islands National Marine
Sanctuary (Sanctuary) consists of an
area of the waters off the coast of
California of approximately 1,128
square nautical miles (nmi) adjacent to
the following islands and offshore rocks:
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Definitions.
In addition to those definitions found
at § 922.3, the following definitions
apply to this subpart:
Pelagic finfish are defined as:
northern anchovy (Engraulis mordax),
barracudas (Sphyraena spp.), billfishes
(family Istiophoridae), dolphinfish
(Coryphaena hippurus), Pacific herring
(Clupea pallasi), jack mackerel
(Trachurus symmetricus), Pacific
mackerel (Scomber japonicus), salmon
(Oncorhynchus spp.), Pacific sardine
(Sardinops sagax), blue shark (Prionace
glauca), salmon shark (Lamna ditropis),
shortfin mako shark (Isurus oxyrinchus),
thresher sharks (Alopias spp.),
swordfish (Xiphias gladius), tunas
(family Scombridae), and yellowtail
(Seriola lalandi).
Stowed and not available for
immediate use means not readily
accessible for immediate use, e.g., by
being securely covered and lashed to a
deck or bulkhead, tied down, unbaited,
unloaded, or partially disassembled
(such as spear shafts being kept separate
from spear guns).
I 5. Add § 922.73 to subpart G to read
as follows:
§ 922.73 Marine reserves and marine
conservation area.
(a) Marine reserves. Unless prohibited
by 50 CFR part 660 (Fisheries off West
Coast States), the following activities are
prohibited and thus unlawful for any
person to conduct or cause to be
conducted within a marine reserve
described in Appendix B to this subpart:
(1) Harvesting, removing, taking,
injuring, destroying, collecting, moving,
or causing the loss of any Sanctuary
resource, including living or dead
organisms or historical resources, or
attempting any of these activities.
(2) Possessing fishing gear on board a
vessel unless such gear is stowed and
not available for immediate use.
(3) Possessing any Sanctuary resource,
including living or dead organisms or
historical resources, except legally
harvested fish on board a vessel at
anchor or in transit.
(b) Marine conservation area. Unless
prohibited by 50 CFR part 660 (Fisheries
E:\FR\FM\24MYR2.SGM
24MYR2
Federal Register / Vol. 72, No. 100 / Thursday, May 24, 2007 / Rules and Regulations
off West Coast States), the following
activities are prohibited and thus
unlawful for any person to conduct or
cause to be conducted within the
marine conservation area described in
Appendix C to this subpart:
(1) Harvesting, removing, taking,
injuring, destroying, collecting, moving,
or causing the loss of any Sanctuary
resource, including living or dead
organisms or historical resources, or
attempting any of these activities,
except:
(i) Recreational fishing for pelagic
finfish; or
(ii) Commercial and recreational
fishing for lobster.
(2) Possessing fishing gear on board a
vessel, except legal fishing gear used to
fish for lobster or pelagic finfish, unless
such gear is stowed and not available for
immediate use.
(3) Possessing any Sanctuary resource,
including living or dead organisms or
historical resources, except legally
harvested fish.
I 6. In § 922.74, as redesignated, revise
paragraph (a) introductory text to read
as follows:
§ 922.74
Permit procedures and criteria.
(a) Any person in possession of a
valid permit issued by the Director in
accordance with this section and
§ 922.48 may conduct any activity
within the Sanctuary prohibited under
§§ 922.72 or 922.73 if such activity is
either:
*
*
*
*
*
I 7. Revise Appendix A to subpart G to
read as follows:
Appendix A to Subpart G of Part 922—
Channel Islands National Marine
Sanctuary Boundary Coordinates
[Coordinates listed in this Appendix are
unprojected (Geographic) and based on the
North American Datum of 1983.]
rmajette on PROD1PC67 with RULES2
Point
Latitude (N)
Longitude (W)
1 ............
2 ............
3 ............
4 ............
5 ............
6 ............
7 ............
8 ............
9 ............
10 ..........
11 ..........
12 ..........
13 ..........
14 ..........
15 ..........
16 ..........
17 ..........
18 ..........
19 ..........
20 ..........
33.94138
33.96776
34.02607
34.07339
34.10185
34.11523
34.11611
34.11434
34.11712
34.11664
34.13389
34.13825
34.14784
34.15086
34.15450
34.15450
34.15142
34.13411
34.14635
34.15988
¥119.27422
¥119.25010
¥119.23642
¥119.25686
¥119.29178
¥119.33040
¥119.39120
¥119.40212
¥119.42896
¥119.44844
¥119.48081
¥119.49198
¥119.51194
¥119.54670
¥119.54670
¥119.59170
¥119.61254
¥119.66024
¥119.69780
¥119.76688
VerDate Aug<31>2005
14:53 May 23, 2007
Jkt 211001
Point
21
22
23
24
25
26
27
28
29
30
31
32
33
34
35
36
37
38
39
40
41
42
43
44
45
46
47
48
49
50
51
52
53
54
55
56
57
58
59
60
61
62
63
64
65
66
67
68
69
70
71
72
73
74
75
76
77
78
79
80
81
82
83
84
85
86
87
88
89
90
91
92
93
94
PO 00000
..........
..........
..........
..........
..........
..........
..........
..........
..........
..........
..........
..........
..........
..........
..........
..........
..........
..........
..........
..........
..........
..........
..........
..........
..........
..........
..........
..........
..........
..........
..........
..........
..........
..........
..........
..........
..........
..........
..........
..........
..........
..........
..........
..........
..........
..........
..........
..........
..........
..........
..........
..........
..........
..........
..........
..........
..........
..........
..........
..........
..........
..........
..........
..........
..........
..........
..........
..........
..........
..........
..........
..........
..........
..........
Frm 00027
29233
Latitude (N)
Longitude (W)
Point
Latitude (N)
Longitude (W)
34.15906
34.15928
34.16213
34.16962
34.17266
34.17588
34.17682
34.17258
34.13535
34.13698
34.12994
34.12481
34.12519
34.11008
34.11128
34.13632
34.15341
34.16408
34.17704
34.20492
34.20492
34.20707
34.20520
34.19254
34.20540
34.20486
34.18182
34.10208
34.08151
34.05848
34.01940
34.01349
33.98698
33.95039
33.92694
33.92501
33.91403
33.91712
33.90956
33.88976
33.84444
33.83146
33.81763
33.81003
33.79425
33.79379
33.79983
33.81076
33.81450
33.84125
33.84865
33.86993
33.86195
33.86195
33.86110
33.86351
33.85995
33.86233
33.87330
33.88594
33.88688
33.88809
33.89414
33.90064
33.90198
33.90198
33.90584
33.90424
33.90219
33.90131
33.90398
33.90635
33.91304
33.91829
¥119.77800
¥119.79327
¥119.80347
¥119.83643
¥119.85240
¥119.88903
¥119.93357
¥119.95830
¥120.01964
¥120.04206
¥120.08582
¥120.11104
¥120.16076
¥120.21190
¥120.22707
¥120.25292
¥120.28627
¥120.29310
¥120.30670
¥120.30670
¥120.38830
¥120.41801
¥120.42859
¥120.46041
¥120.50728
¥120.53987
¥120.60041
¥120.64208
¥120.63894
¥120.62862
¥120.58567
¥120.57464
¥120.56582
¥120.53282
¥120.46132
¥120.42170
¥120.37585
¥120.32506
¥120.30857
¥120.29540
¥120.25482
¥120.22927
¥120.20284
¥120.18731
¥120.13422
¥120.10207
¥120.06995
¥120.04351
¥120.03158
¥119.96508
¥119.92316
¥119.88330
¥119.88330
¥119.80000
¥119.79017
¥119.77130
¥119.74390
¥119.68783
¥119.65504
¥119.62617
¥119.59423
¥119.58278
¥119.54861
¥119.51936
¥119.51609
¥119.43311
¥119.43311
¥119.42422
¥119.40730
¥119.38373
¥119.36333
¥119.35345
¥119.33280
¥119.32206
95 ..........
96 ..........
97 ..........
98 ..........
99 ..........
100 ........
101 ........
102 ........
103 ........
104 ........
105 ........
106 ........
107 ........
108 ........
109 ........
110 ........
111 ........
112 ........
113 ........
33.48250
33.44235
33.40555
33.39059
33.36804
33.36375
33.36241
33.36320
33.36320
33.47500
33.48414
33.52444
33.53834
33.58616
33.59018
33.58516
33.58011
33.54367
33.51161
¥119.16874
¥119.16797
¥119.14878
¥119.13283
¥119.08891
¥119.06803
¥119.04812
¥119.03670
¥118.90879
¥118.90879
¥118.90712
¥118.91492
¥118.92271
¥118.99540
¥119.02374
¥119.06745
¥119.08521
¥119.14460
¥119.16367
Fmt 4701
Sfmt 4700
8. Add Appendix B to subpart G to
read as follows:
I
Appendix B to Subpart G of Part 922—
Marine Reserve Boundaries
[Coordinates listed in this Appendix are
unprojected (Geographic) and based on the
North American Datum of 1983.]
B.1. Richardson Rock (San Miguel Island)
Marine Reserve
The Richardson Rock Marine Reserve
(Richardson Rock) boundary is defined by
the 3 nmi State boundary, the coordinates
provided in Table B–1, and the following
textual description.
The Richardson Rock boundary extends
from Point 1 to Point 2 along a straight line.
It then extends from Point 2 to Point 3 along
a straight line. The boundary then extends
along a straight line from Point 3 to the 3 nmi
State boundary established under the
Submerged Lands Act (3 nmi State boundary)
where a line defined by connecting Point 3
and Point 4 with a straight line intersects the
3 nmi State boundary. The boundary then
extends northwestward and then eastward
along the 3 nmi State boundary until it
intersects the line defined by connecting
Point 5 and Point 6 with a straight line. At
that intersection, the boundary extends from
the 3 nmi SLA boundary to Point 6 along a
straight line.
TABLE B–1.—RICHARDSON ROCK
(SAN MIGUEL ISLAND) MARINE RESERVE
Point
1
2
3
4
5
6
................
................
................
................
................
................
Latitude
34.17333
34.17333
34.12900
34.03685
34.03685
34.17333
°N
°N
°N
°N
°N
°N
Longitude
120.60483
120.47000
120.47000
120.52120
120.60483
120.60483
°W
°W
°W
°W
°W
°W
B.2. Harris Point (San Miguel Island) Marine
Reserve
The Harris Point Marine Reserve (Harris
Point) boundary is defined by the 3 nmi State
E:\FR\FM\24MYR2.SGM
24MYR2
29234
Federal Register / Vol. 72, No. 100 / Thursday, May 24, 2007 / Rules and Regulations
boundary, the coordinates provided in Table
B–2, and the following textual description.
The Harris Point boundary extends from
Point 1 to Point 2 along a straight line. It then
extends along a straight line from Point 2 to
the 3 nmi State boundary where a line
defined by connecting Point 2 and Point 3
with a straight line intersects the 3 nmi State
boundary. The boundary then follows the 3
nmi State boundary northwestward until it
intersects the line defined by connecting
Point 4 and Point 5 with a straight line. At
that intersection, the boundary extends from
the 3 nmi State boundary to Point 5 along a
straight line.
Point 4 and Point 5 with a straight line. At
that intersection, the boundary extends from
the 3 nmi State boundary to Point 5 along a
straight line.
TABLE B–2.—HARRIS POINT (SAN
MIGUEL ISLAND) MARINE RESERVE
B.5. Scorpion (Santa Cruz Island) Marine
Reserve
The Scorpion Marine Reserve (Scorpion)
boundary is defined by the 3 nmi State
boundary, the coordinates provided in Table
B–5, and the following textual description.
The Scorpion boundary extends from Point
1 to Point 2 along a straight line. It then
extends along a straight line from Point 2 to
the 3 nmi State boundary where a line
defined by connecting Point 2 and Point 3
with a straight line intersects the 3 nmi State
boundary. The boundary then follows the 3
nmi State boundary westward until it
intersects the line defined by connecting
Point 4 and Point 5 with a straight line. At
that intersection, the boundary extends from
the 3 nmi State boundary to Point 5 along a
straight line.
Point
1
2
3
4
5
................
................
................
................
................
Latitude
34.20492
34.20492
34.10260
34.15200
34.20492
°N
°N
°N
°N
°N
Longitude
120.38830
120.30670
120.30670
120.38830
120.38830
°W
°W
°W
°W
°W
B.3. South Point (Santa Rosa Island) Marine
Reserve
The South Point Marine Reserve (South
Point) boundary is defined by the 3 nmi State
boundary, the coordinates provided in Table
B–3, and the following textual description.
The South Point boundary extends from
Point 1 to Point 2 along a straight line. It then
extends along a straight line from Point 2 to
the 3 nmi State boundary where a line
defined by connecting Point 2 and Point 3
with a straight line intersects the 3 nmi State
boundary. The boundary follows the 3 nmi
State boundary southeastward until it
intersects the line defined by connecting
Point 4 and Point 5 along a straight line. At
that intersection, the boundary extends from
the 3 nmi State boundary to Point 5 along a
straight line.
TABLE B–3.—SOUTH POINT (SANTA
ROSA ISLAND) MARINE RESERVE
Point
rmajette on PROD1PC67 with RULES2
1
2
3
4
5
................
................
................
................
................
Latitude
33.84000
33.84000
33.86110
33.84700
33.84000
°N
°N
°N
°N
°N
Longitude
120.10830
120.16670
120.16670
120.10830
120.10830
°W
°W
°W
°W
°W
B.4. Gull Island (Santa Cruz Island) Marine
Reserve
The Gull Island Marine Reserve (Gull
Island) boundary is defined by the 3 nmi
State boundary, the coordinates provided in
Table B–4, and the following textual
description.
The Gull Island boundary extends from
Point 1 to Point 2 along a straight line. It then
extends along a straight line from Point 2 to
the 3 nmi State boundary where a line
defined by connecting Point 2 and Point 3
with a straight line intersects the 3 nmi State
boundary. The boundary then follows the 3
nmi State boundary westward until it
intersects the line defined by connecting
VerDate Aug<31>2005
14:53 May 23, 2007
Jkt 211001
TABLE B–4.—GULL ISLAND (SANTA
CRUZ ISLAND) MARINE RESERVE
Point
1
2
3
4
5
................
................
................
................
................
Latitude
33.86195
33.86195
33.92690
33.90700
33.86195
°N
°N
°N
°N
°N
Longitude
119.80000
119.88330
119.88330
119.80000
119.80000
°W
°W
°W
°W
°W
TABLE B–5.—SCORPION (SANTA CRUZ
ISLAND) MARINE RESERVE
Point
1
2
3
4
5
................
................
................
................
................
Latitude
34.15450
34.15450
34.10140
34.10060
34.15450
°N
°N
°N
°N
°N
119.59170
119.54670
119.54670
119.59170
119.59170
°W
°W
°W
°W
°W
TABLE B–6.—FOOTPRINT MARINE
RESERVE
Point
Latitude
Longitude
1 ................
2 ................
3 ................
33.90198 °N
33.90198 °N
33.96120 °N
119.43311 °W
119.51609 °W
119.51609 °W
Frm 00028
Fmt 4701
Point
Latitude
Longitude
4 ................
5 ................
33.95710 °N
33.90198 °N
119.43311 °W
119.43311 °W
B.7. Anacapa Island Marine Reserve
The Anacapa Island Marine Reserve
(Anacapa Island) boundary is defined by the
3 nmi State boundary, the coordinates
provided in Table B–7, and the following
textual description.
The Anacapa Island boundary extends
from Point 1 to Point 2 along a straight line.
It then extends to the 3 nmi State boundary
where a line defined by connecting Point 2
and Pont 3 with a straight line intersects the
3 nmi State boundary. The boundary follows
the 3 nmi State boundary westward until it
intersects the line defined by connecting
Point 4 and Point 5 with a straight line. At
that intersection, the boundary extends from
the 3 nmi State boundary to Point 5 along a
straight line.
TABLE B–7.—ANACAPA ISLAND
MARINE RESERVE
Point
1
2
3
4
5
................
................
................
................
................
Latitude
34.08330
34.08330
34.06450
34.06210
34.08330
°N
°N
°N
°N
°N
Longitude
119.41000
119.35670
119.35670
119.41000
119.41000
°W
°W
°W
°W
°W
Longitude
B.6. Footprint Marine Reserve
The Footprint Marine Reserve (Footprint)
boundary is defined by the 3 nmi State
boundary, the coordinates provided in Table
B–6, and the following textual description.
The Footprint boundary extends from
Point 1 to Point 2 along a straight line. It then
extends along a straight line from Point 2 to
the 3 nmi State boundary where a line
defined by connecting Point 2 and Point 3
with a straight line intersects the 3 nmi State
boundary. The boundary follows the 3 nmi
State boundary northeastward and then
southeastward until it intersects the line
defined by connecting Point 4 and Point 5
along a straight line. At that intersection, the
boundary extends from the 3 nmi State
boundary to Point 5 along a straight line.
PO 00000
TABLE B–6.—FOOTPRINT MARINE
RESERVE—Continued
Sfmt 4700
B.8. Santa Barbara Island Marine Reserve
The Santa Barbara Island Marine Reserve
(Santa Barbara) boundary is defined by the 3
nmi State boundary, the coordinates
provided in Table B–8, and the following
textual description.
The Santa Barbara boundary extends from
Point 1 to Point 2 along a straight line. It then
extends along a straight line from Point 2 to
the 3 nmi State boundary where a line
defined by connecting Point 2 and Point 3
with a straight line intersects the 3 nmi State
boundary. The boundary follows the 3 nmi
State boundary northeastward until it
intersects the line defined by connecting
Point 4 and Point 5 with a straight line. At
that intersection, the boundary extends from
the 3 nmi State boundary to Point 5 along a
straight line. The boundary then extends
from Point 5 to Point 6 along a straight line.
TABLE B–8.—SANTA BARBARA ISLAND
MARINE RESERVE
Point
1
2
3
4
5
6
................
................
................
................
................
................
E:\FR\FM\24MYR2.SGM
24MYR2
Latitude
33.36320
33.36320
33.41680
33.47500
33.47500
33.36320
°N
°N
°N
°N
°N
°N
Longitude
118.90879
119.03670
119.03670
118.97080
118.90879
118.90879
°W
°W
°W
°W
°W
°W
Federal Register / Vol. 72, No. 100 / Thursday, May 24, 2007 / Rules and Regulations
Appendix C to Subpart G of Part 9222—
Marine Conservation Area Boundary
rmajette on PROD1PC67 with RULES2
C.1. Anacapa Island Marine Conservation
Area
The Anacapa Island Marine Conservation
Area (AIMCA) boundary is defined by the 3
nmi State boundary, the coordinates
provided in Table C–1, and the following
textual description.
The AIMCA boundary extends from Point
1 to Point 2 along a straight line. It then
extends to the 3 nmi State boundary where
a line defined by connecting Point 2 and
Point 3 with a straight line intersects the 3
nmi State boundary. The boundary follows
the 3 nmi State boundary westward until it
intersects the line defined by connecting
Point 4 and Point 5 with a straight line. At
that intersection, the boundary extends from
the 3 nmi State boundary to Point 5 along a
straight line.
VerDate Aug<31>2005
14:53 May 23, 2007
Jkt 211001
§ 660.2
TABLE C–1.—ANACAPA ISLAND
MARINE CONSERVATION AREA
Point
1
2
3
4
5
................
................
................
................
................
Latitude
34.08330
34.08330
34.06210
34.06300
34.08330
°N
°N
°N
°N
°N
Longitude
119.44500
119.41000
119.41000
119.44500
119.44500
50 CFR CHAPTER VI
PART 660—[AMENDED]
10. The authority for part 660
continues to read as follows:
I
Authority: 16 U.S.C. 1801 et seq.
°W
°W
°W
°W
°W
Relation to other laws.
(a) NMFS recognizes that any state
law pertaining to vessels registered
under the laws of that state while
operating in the fisheries regulated
under this part, and that is consistent
with this part and the FMPs
implemented by this part, shall
continue in effect with respect to fishing
activities regulated under this part.
(b) Fishing activities addressed by this
Part may also be subject to regulation
under 15 CFR part 922, subpart G, if
conducted in the Channel Islands
National Marine Sanctuary
[FR Doc. E7–10096 Filed 5–23–07; 8:45 am]
BILLING CODE 3510–NK–P
I
11. Revise § 660.2 to read as follows:
PO 00000
Frm 00029
Fmt 4701
Sfmt 4700
29235
E:\FR\FM\24MYR2.SGM
24MYR2
Agencies
[Federal Register Volume 72, Number 100 (Thursday, May 24, 2007)]
[Rules and Regulations]
[Pages 29208-29235]
From the Federal Register Online via the Government Printing Office [www.gpo.gov]
[FR Doc No: E7-10096]
[[Page 29207]]
-----------------------------------------------------------------------
Part II
Department of Commerce
-----------------------------------------------------------------------
National Oceanic and Atmospheric Administration
-----------------------------------------------------------------------
15 CFR Part 922
50 CFR Part 660
Establishment of Marine Reserves and a Marine Conservation Area Within
the Channel Islands National Marine Sanctuary; Final Rule
Federal Register / Vol. 72, No. 100 / Thursday, May 24, 2007 / Rules
and Regulations
[[Page 29208]]
-----------------------------------------------------------------------
DEPARTMENT OF COMMERCE
National Oceanic and Atmospheric Administration
15 CFR Part 922
50 CFR Part 660
[Docket No. 0612242956-7123-01]
RIN 0648-AT18
Establishment of Marine Reserves and a Marine Conservation Area
Within the Channel Islands National Marine Sanctuary
AGENCY: National Marine Sanctuary Program (NMSP), National Ocean
Service (NOS) and National Marine Fisheries Service (NOAA Fisheries),
National Oceanic and Atmospheric Administration (NOAA), Department of
Commerce (DOC).
ACTION: Final rule.
-----------------------------------------------------------------------
SUMMARY: On August 11, 2006 NOAA issued a notice of proposed rulemaking
to establish a network of marine zones within the state and federal
waters of the Channel Islands National Marine Sanctuary (CINMS or
Sanctuary). State waters in the Sanctuary extend from the shoreline of
the islands to approximately 3 nautical miles from shore. Federal
waters of the Sanctuary extend from the offshore extent of state waters
to the Sanctuary's outer boundary. In this final rule, NOAA is issuing
final regulations for the federal-waters portion of the Sanctuary. NOAA
has decided to defer a final decision and seeking additional comment on
the state-waters portion of the Sanctuary pending action by the State
of California to extend the boundaries of several existing state-waters
zones to the three mile state-federal-waters boundary.
Marine zones are discrete areas that have special regulations
differing from the regulations that apply throughout or above the
Sanctuary as a whole. The purpose of these zones within the federal
waters of the Sanctuary is to further the protection of Sanctuary
biodiversity and complement an existing network established by the
State of California in October 2002, and implemented in April 2003,
under its authorities. Two types of zones are being established by this
action: Marine reserves and marine conservation areas. All extractive
activities (e.g., removal of any Sanctuary resource) and injury to
Sanctuary resources are prohibited in all marine reserves. Commercial
and recreational lobster fishing and recreational fishing for pelagic
species are allowed within the marine conservation area, while all
other extraction and injury are prohibited. This action establishes
approximately 110.5 square nautical miles of marine reserves and 1.7
square nautical miles of marine conservation area in the federal waters
of the Sanctuary. As part of this action, NOAA is also modifying the
terms of designation for the Sanctuary, which were originally published
on October 2, 1980 (45 FR 65198), to allow for the regulation of
extractive activities, including fishing, in marine reserves and marine
conservation areas, and a slight modification to the outer boundary of
the CINMS.
DATES: Pursuant to section 304(b) of the National Marine Sanctuaries
Act (NMSA), 16 U.S.C. 1434(b), the revised terms of designation and
this final rule shall take effect and become final after the close of a
review period of 45 days of continuous session of Congress, beginning
on the day on which this document is published in the Federal Register.
Announcement of the effective date of this final rule will be published
in the Federal Register at a later date.
Public comments on the state-waters portion of this rulemaking must
be received by July 23, 2007.
ADDRESSES: Copies of the final environmental impact statement,
regulatory impact review, and final regulatory flexibility analyses may
be obtained from NOAA's Channel Islands National Marine Sanctuary Web
site at https://channelislands.noaa.gov/ or by writing to Sean Hastings,
Resource Protection Coordinator, Channel Islands National Marine
Sanctuary, 113 Harbor Way, Suite 150, Santa Barbara, CA 93109; e-mail:
Sean.Hastings@noaa.gov.
You may submit comments on the state-waters portion of this
rulemaking by any of the following methods:
E-mail: CINMSReserves.FEIS@noaa.gov. Include in the
subject line the following document identifier: Marine reserves in
CINMS.
Federal e-Rulemaking Portal: https://www.regulations.gov.
Follow the instructions for submitting comments.
Mail: Sean Hastings, Channel Islands National Marine
Sanctuary, 113 Harbor Way, Suite 150, Santa Barbara, CA 93109.
FOR FURTHER INFORMATION CONTACT: Sean Hastings, (805) 884-1472; e-mail:
Sean.Hastings@noaa.gov.
SUPPLEMENTARY INFORMATION:
I. Background
A. Channel Islands National Marine Sanctuary
The CINMS area is approximately 1,113 square nautical miles
adjacent to the following islands and offshore rocks: San Miguel
Island, Santa Cruz Island, Santa Rosa Island, Anacapa Island, Santa
Barbara Island, Richardson Rock, and Castle Rock (collectively the
Channel Islands), extending seaward to a distance of approximately 6
nautical miles. NOAA designated the CINMS in 1980 to protect the area's
rich and diverse range of marine life and habitats, unique and
productive oceanographic processes and ecosystems, and culturally
significant resources (see 45 FR 65198). The Sanctuary was designated
pursuant to NOAA's authority under the National Marine Sanctuaries Act
(NMSA; 16 U.S.C. 1431 et seq.). There are significant human uses in the
Sanctuary as well, including commercial and recreational fishing,
marine wildlife viewing, boating and other recreational activities,
research and monitoring activities, numerous educational activities,
and maritime shipping.
The waters surrounding California's Channel Islands represent a
globally unique and diverse assemblage of habitats and species. This
region is a subset of the larger ecosystem of the Southern California
Bight, an area bounded by Point Conception in the north and Punta
Banda, Mexico in the south. In the area between Santa Barbara Island in
the south and San Miguel Island in the northwest, the colder waters of
the Oregonian oceanic province in the north converge and mix with the
warmer waters of the Californian oceanic province. Each of these two
provinces has unique oceanic conditions and species assemblages, which
in turn are parts of distinct biogeographic regions. The mixing of
these two provinces in the vicinity of the Channel Islands creates a
transition zone within the island chain. Upwelling and ocean currents
in the area create a nutrient rich environment that supports high
species and habitat diversity.
In the Southern California Bight, marine resources have declined
under pressure from a variety of factors, including commercial and
recreational fishing, changes in oceanographic conditions associated
with El Ni[ntilde]o and other large-scale oceanographic cycles,
introduction of disease, and increased levels of pollutants. The
urbanization of southern California has significantly increased the
number of people visiting the coastal zone. The burgeoning coastal
population has greatly increased the influx of human, industrial, and
agricultural wastes to California coastal waters. Population growth has
also increased human demands on the ocean, including commercial and
recreational fishing, wildlife viewing
[[Page 29209]]
and other activities. New technologies have increased the yield of
sport and commercial fisheries. Many former natural refuges for
targeted species, such as submarine canyons, submerged pinnacles, deep
waters, and waters distant from harbors, can now be accessed due to
advancements in fishing technology and increased fishing effort.
The significant changes in ecological conditions resulting from the
array of human activities in the Channel Islands region are just
beginning to be understood. For example, many kelp beds have converted
to urchin barrens, where urchins and coralline algae have replaced kelp
as the dominant feature. Deep canyon and rock areas that were formerly
rich rockfishing grounds have significantly reduced populations of
larger rockfish such as cowcod and bocaccio.
In the Southern California Bight, commercial and recreational
fisheries target more than 100 fish species and more than 20
invertebrate species. Targeted species have exhibited high variability
in landings from year to year (e.g., squid) and in several cases have
declined to the point that the fishery has had to be shut down (e.g.,
abalone). Many targeted species are considered overfished and one
previously targeted species (white abalone) is listed as endangered.
Excessive bycatch has caused declines of some non-targeted species. The
removal of species that play key ecological roles, such as predatory
fish, has altered ecosystem structure. Some types of fishing gear have
caused temporary or permanent damage to marine habitats. The
combination of direct take, bycatch, indirect effects, and habitat
damage and destruction has contributed to a negative transformation of
the marine environment around the Channel Islands.
B. Marine Zoning
For over twenty years, NOAA has used marine zoning as a tool in
specific national marine sanctuaries to address a wide array of
resource protection and user conflict issues. Marine zones are discrete
areas within or above a national marine sanctuary that have special
regulations that differ from the regulations that apply throughout or
above the sanctuary as a whole. For example, marine zones are used to
regulate the use of motorized personal watercraft in the Monterey Bay
National Marine Sanctuary. Marine zones, including areas where all
extraction is prohibited, have also been established in the Florida
Keys National Marine Sanctuary to provide for varying levels of
resource protection.
NOAA has used zoning within the CINMS since its original
designation in 1980. For example, the CINMS regulations prohibit:
1. Cargo vessels from coming within 1 nautical mile of any island
in the CINMS;
2. disturbance of marine mammals or seabirds by flying aircraft
below 1,000 feet within 1 nautical mile of any island within the CINMS;
and
3. construction upon or drilling into the seabed within 2 nautical
miles of any island in the CINMS.
In addition to NOAA, other federal and state agencies have also
established marine zones wholly or partially within the Sanctuary
(e.g., California Department of Fish and Game, National Park Service).
In 1978, commercial and recreational fishing was prohibited by the
State of California in one small marine protected area of the Channel
Islands, the Anacapa Island Ecological Reserve. The International
Maritime Organization has designated a voluntary vessel traffic
separation scheme to guide large vessel traffic running through the
Santa Barbara Channel. The National Park Service (NPS) has established
several zoned areas within the Channel Islands National Park for
different public uses, principally to protect seabird colonies and
marine mammal haul outs. More recently, the NPS is instituting a new
zoning approach to managing park lands, coasts, and adjacent waters.
Due to historic lows in the stocks of certain rockfish (e.g.,
cowcod and bocaccio), in 2001 the Pacific Fishery Management Council
(PFMC) took emergency action and established large bottom closures to
rebuild these stocks. NOAA implemented the Cowcod Conservation Area
regulations on January 1, 2001 (66 FR 2338) and the Rockfish
Conservation Area emergency regulations on September 13, 2002 (67 FR
57973). The Cowcod Conservation Area and the California Rockfish
Conservation Area partially overlay Sanctuary waters. Finally, in 2002,
the California Fish and Game Commission (FGC) authorized the
establishment of marine reserves and marine conservation areas within
the state waters of the Sanctuary that prohibit or limit the take of
living, geological or cultural marine resources.
C. Marine Reserves
The number of documented successful examples of no-take marine
reserves is growing, providing substantial evidence that rapid
increases in biomass, biodiversity, abundance and size of organisms
usually result from their designation. Increased biodiversity,
abundance, and habitat quality within closed areas generally improve
the resiliency and ability of marine ecosystems to adapt to ongoing
human-caused or natural disturbance, such as climate shifts, major
storm damage, and pollution.
The designation of marine reserves can also reinforce traditional
fish management approaches to substantially reduce overall fishery
impacts to the ecosystem. Traditional management, like controls on
fishery catch and effort, may fail due to factors such as stock
assessment errors, inadequate institutional frameworks, and
uncertainty. Marine reserves can help to rebuild depleted populations,
reduce bycatch and discards, and reduce known and as-yet-unknown
ecosystem effects of fishing. In addition, marine reserves offer
scientists and resource managers a controlled opportunity to study the
influence of change on marine ecosystems in the absence of direct human
disturbance.
D. Channel Islands Marine Reserves Process, Community Phase 1999-2001
The NMSA requires NOAA to periodically review the management plan
and regulations for each national marine sanctuary and to revise them,
as necessary, to fulfill the purposes and policies of the NMSA (16
U.S.C. 1434(e)). NOAA began the process to review the CINMS management
plan and regulations in 1999. Through the scoping process, many members
of the public voiced concern over the state of biodiversity in the
CINMS and called for fully protected (i.e., no-take) zones to be
established.
In 1998, the Commission received a recommendation from a local
recreational fishing group to create marine reserves around the
northern Channel Islands as a response to declining fish populations.
In response to concerns about changes in the ecosystem and comments
raised to the Commission and during the CINMS management plan scoping
process, NOAA and the California Department of Fish and Game (CDFG)
developed a Federal-state partnership to consider the establishment of
marine reserves in the Sanctuary.
Since the marine reserves process is inherently complex, and is a
stand-alone action that is programmatically independent of and
severable from the more general suite of actions contemplated in the
management plan review process, NOAA decided to separate the process to
consider marine reserves from the larger CINMS management plan review
process. The draft management plan and DEIS for the
[[Page 29210]]
management plan review were released for public comment on May 19, 2006
(71 FR 29148). NOAA also published a proposed rule to implement the
management plan on May 19, 2006 (71 FR 29096). Please see https://
channelislands.noaa.gov for more information.
The CINMS Advisory Council, a federal advisory board of local
community representatives and federal, state and local government
agency representatives, created a multi-stakeholder Marine Reserves
Working Group (MRWG) to seek agreement on a recommendation regarding
the potential establishment of marine reserves within the Sanctuary.
The CINMS Advisory Council also designated a Science Advisory Panel of
recognized experts and a NOAA-led Socio-economic Team to support the
MRWG in its deliberations.
Extensive scientific, social, and economic data were collected in
support of the marine reserves assessment process. From July 1999 to
May 2001, the MRWG met monthly to receive, weigh, and integrate advice
from technical advisors and the public. The MRWG reached consensus on a
set of ground rules, a mission statement, a problem statement, a list
of species of interest, and a comprehensive suite of implementation
recommendations. The MRWG found that in order to protect, maintain,
restore, and enhance living marine resources, it is necessary to
develop new management strategies that encompass an ecosystem
perspective and promote collaboration between competing interests. A
set of goals were also agreed upon by the MRWG:
1. To protect representative and unique marine habitats, ecological
processes, and populations of interest.
2. To maintain long-term socioeconomic viability while minimizing
short-term socioeconomic losses to all users and dependent parties.
3. To achieve sustainable fisheries by integrating marine reserves
into fisheries management.
4. To maintain areas for visitor, spiritual, and recreational
opportunities which include cultural and ecological features and their
associated values.
5. To foster stewardship of the marine environment by providing
educational opportunities to increase awareness and encourage
responsible use of resources.
The MRWG developed over 40 different designs for potential marine
reserves and evaluated the ecological value and potential economic
impact of each design. To do so, members of the MRWG contributed their
own expertise to modify designs or generate alternatives and utilized a
geospatial tool, known as the Channel Islands Spatial Support and
Analysis Tool (CI-SSAT). CI-SSAT provided opportunities for
visualization, manipulation, and analysis of data for the purpose of
designing marine reserves.
After months of deliberation, a consensus design could not be
reached and the MRWG selected two designs to represent the diverse
views of the group. These designs depict the best effort that each MRWG
representative could propose. Ultimately, the CINMS Advisory Council
provided the MRWG's two designs, as well as all of the supporting
information developed during the process, including background
scientific and economic information, to NOAA and the CDFG for
consideration and action.
Based on this information and additional internal agency analysis,
NOAA and the CDFG crafted a draft reserve network and sent it to the
CINMS Advisory Council and the former MRWG, Science Panel and Socio-
Economic Team members seeking further input. The draft reserve network
was also published in local papers and on the CINMS Web site to solicit
input from the general public. Several meetings were held with
constituent groups, including the CINMS Advisory Council's Conservation
Working Group, Fishing Working Group and Ports and Harbors Working
Group, to discuss the draft network. Following this period of input,
the CDFG and NOAA prepared a recommendation for establishing a network
of marine reserves and marine conservation areas. The recommendation
proposed a network of marine reserves and marine conservation areas in
the same general locations as the MRWG Composite Map. The composite map
was forwarded to the CINMS Advisory Council and represented two
versions of a reserve and conservation area network, one version from
consumptive interests and the other from non-consumptive interests.
These two versions were overlaid on one map, and depicted a number of
areas that the constituent groups agreed upon. This recommendation
became the basis for the preferred alternative in the State's
California Environmental Quality Act (CEQA) environmental review
process.
E. Establishment of State Reserves in the CINMS, 2001 to 2003
Due to the fact that the proposed network spanned both state and
federal waters, NOAA and the CDFG determined the implementation of the
recommendation would need to be divided into a state phase and a
federal phase. State waters extend from the shore to a distance of
three nautical miles. Federal waters extend beyond the limit of state
waters to the extent of the exclusive economic zone, with the outer
boundary of the CINMS at a distance of approximately six nautical miles
from shore. The state phase was to be considered by the Commission
under its authorities.
The CDFG completed an environmental review under the requirements
of CEQA resulting in the publication of an environmental document. The
draft environmental document (ED) was released for public comment on
May 30, 2002. Comments were accepted for an extended period until
September 1, 2002. The Commission and CDFG received 2,492 letters, e-
mails and oral comments. Of this total, 2,445 were form letters that
made identical comments.
The Commission certified the final ED on October 23, 2002. At this
same meeting, the Commission approved the CDFG's preferred alternative.
The CDFG published final regulations for its action in January 2003. As
part of its implementation, the FGC acknowledged the need for NOAA to
complete the network by extending the marine zones into the deeper and
federal waters of the CINMS.
F. Federal Marine Reserves Process, 2003-2007
Following the publication of the CDFG's final regulations in 2003,
NOAA's NMSP initiated the federal marine reserves process, and hosted
scoping meetings with the general public, the CINMS Advisory Council,
and PFMC. In 2004, the NMSP released a preliminary environmental
document with a range of alternatives for public review. In 2005, the
NMSP consulted with local, state, and federal agencies and the PFMC on
possible amendments to the CINMS designation document pursuant to
section 303(b)(2) of the NMSA (16 U.S.C. 1433(b)(2)). In addition, in
2005 the NMSP provided the PFMC with the opportunity to prepare draft
NMSA fishing regulations pursuant to section 304(a)(5) of the NMSA (16
U.S.C. 1434(a)(5)) for the potential establishment of marine reserves
and marine conservation areas.
In its response to NOAA's letter regarding draft NMSA fishing
regulations, the PFMC stated its support for NOAA's goals and
objectives for marine zones in the CINMS but recommended that NOAA
issue fishing regulations under the Magnuson-Stevens Fishery
Conservation and Management Act (MSA) and the relevant authorities of
the states of
[[Page 29211]]
California, Oregon, and Washington rather than under the NMSA. To that
end, and in accordance with advice from the NOAA Administrator in his
October 19, 2005 letter to the PFMC, the PFMC recommended the Channel
Islands marine zones in federal waters be designated as Essential Fish
Habitat and Habitat Areas of Particular Concern with corresponding
management measures to prohibit the use of bottom contact gear under
Amendment 19 of the Groundfish Fishery Management Plan. To complete the
process of addressing closure of the remaining aspect of the marine
zones (i.e., in the water column) the PFMC stated its intent to pursue
those closures through other fishery management plan authorities and
complementary state laws.
NOAA reviewed the PFMC's recommendations and determined that they
did not have the specificity or record to support the use of the MSA or
state laws to establish limited take or no-take zones in the water
column and thereby did not fulfill NOAA's goals and objectives for
these marine zones in the CINMS. However, Amendment 19 to the
Groundfish Fishery Management Plan implemented, in part, the proposed
marine zones by prohibiting all bottom contact gear in the proposed
zones. Accordingly, the NMSA regulations issued in this rule prohibit
the take of resources from the zones not prohibited by the Amendment 19
regulations. Thus, along with the regulations implementing Amendment
19, the NMSA regulations establish comprehensive limited-take and no-
take zones in the CINMS in a manner that fulfills NOAA's goals and
objectives for these marine zones in the CINMS.
As stated in the summary, the purpose of these zones is to further
the protection of Sanctuary biodiversity and complement an existing
network established by the State of California in October 2002, and
implemented in April, 2003, under its authorities. The goals of the
zones are:
To ensure the long-term protection of Sanctuary resources
by restoring and enhancing the abundance, density, population age
structure, and diversity of the natural biological communities.
To protect, restore, and maintain functional and intact
portions of natural habitats (including deeper water habitats),
populations, and ecological processes in the Sanctuary.
To provide, for research and education, undisturbed
reference areas that include the full spectrum of habitats within the
CINMS where local populations exhibit a more natural abundance,
density, diversity, and age structure.
To set aside, for intrinsic and heritage value,
representative habitats and natural biological communities.
To complement the protection of CINMS resources and
habitats afforded by the State of California's marine reserves and
marine conservation areas.
To create models of and incentives for ways to conserve
and manage the resources of CINMS.
On August 11, 2006 NOAA issued a notice of proposed rulemaking (71
FR 46134) to prohibit the take of resources from the zones not
prohibited by the Amendment 19 regulations. NOAA subsequently issued a
correction to this notice on October 5, 2006 (71 FR 58767) to correct
certain figures presented on the size of the Sanctuary.
Between August and October of 2006, NOAA received public comments
and held two hearings on the proposed rule. Over 30,000 individuals
submitted written comments and/or presented oral testimony on NOAA's
proposal. 99% of these individuals supported the establishment of
marine zones in some form, particularly Alternatives 1A and 2 as
described in NOAA's DEIS. During the public comment period, the State
of California also submitted comments on NOAA's proposal. In its
October 2006 letter, the CDFG stated that it could only support
Alternative 1C as described in NOAA's draft environmental impact
statement (DEIS). Under Alternative 1C, NOAA would establish marine
reserves only in federal waters. NOAA's preferred alternative in the
DEIS, identified as Alternative 1A, would have established marine zones
in both federal and state waters with federal regulations overlaying
the entire network (i.e., from the outer boundary of the federal waters
reserves to the shore of the Channel Islands). As indicated in the
DEIS, Alternative 1C would leave gaps in protection between the
offshore extent of some of the state waters marine zones established by
the State of California in 2003 and the marine zones proposed by NOAA
(refer to figure 1 for an illustration of these gaps).
On March 16, 2007, the California Coastal Commission (Coastal
Commission) held a public meeting on NOAA's proposal pursuant to its
authorities under section 307 of the Coastal Zone Management Act (16
U.S.C. 1456). See https://www.coastal.ca.gov/meetings/mtg-mm7-3.html for
more information about this meeting. At that meeting, the Coastal
Commission passed a motion as follows: ``In the event NOAA elects not
to implement Alternative 1a, NOAA will implement Alternative 1c, with
the following additional provisions: Until such time as the Resources
Agency and the Fish and Game Commission designate the areas in between
the existing State-designated MPAs and the 3 mile limit (i.e., the
``gaps'' between the existing state MPAs and the federal MPAs depicted
in Alternative 1c [and shown on Exhibit 9]), or the Fish and Game
Commission/DFG and NOAA enter into an interagency agreement that
establishes MPA protection for these ``gap'' areas, NOAA will expand
Alternative 1c to include in its MPA designation these ``gaps'' between
the outer boundaries of the existing state MPAs and the state-federal
waters boundary (3nm from shore).'' At this meeting, the CDFG
representative also stated that the FGC could close these gaps in
protection using state laws by August 2007.
Based on the record, including comments received during the public
comment period and the record of the Coastal Commission, NOAA has
determined that there is sufficient information and rationale to
establish marine zones in the federal waters of the Sanctuary (i.e.,
implement NOAA's Alternative 1C). With regard to state waters of the
Sanctuary, NOAA has decided to defer action on establishing marine
zones until the FGC has had an opportunity to close those gaps in a
manner consistent with the Coastal Commission's motion and the CDFG
representative's statement. The State of California has already begun
this process by placing it on the agenda for a decision at the August
2007 meeting of the FGC. Also, the CDFG has begun preparing the
necessary documentation to support the FGC's decision. NOAA is,
therefore, leaving the record open with regard to a decision to
establish marine zones in state waters of the Sanctuary, and will be
accepting additional public comment on this specific issue.
NOAA will make a final decision with regard to its action in state
waters in fall, 2007. If the FGC is able to take sufficient action
before this time, NOAA proposes to take no further action under the
NMSA. If the FGC is not able to take sufficient action before this
time, NOAA would finalize regulations under the NMSA that would
effectively close the gaps associated with alternative 1C by extending
federal protections into state waters to meet the boundaries of the
marine zones established by the FGC in 2003. In either case, NOAA will
provide public notice of this action through issuance of a Federal
Register document at the appropriate time.
[[Page 29212]]
II. Summary of Final Environmental Impact Statement and Record of
Decision
NOAA prepared a draft environmental impact statement (DEIS) for the
proposed rule to establish marine reserves and marine conservation
areas within the Sanctuary (71 FR 46220; August 11, 2006). The DEIS was
prepared in accordance with the NMSA and National Environmental Policy
Act of 1969 (NEPA) requirements. The DEIS was distributed for public
comments in early August 2006. The public comment period, which closed
on October 10, 2006, yielded many comments on NOAA's proposed action
and suggestions for improving the DEIS. NOAA has prepared a final
environmental impact statement (FEIS) to address these comments and
make appropriate changes to its environmental analysis. The FEIS
contains a statement of the purpose and need for the project,
description of proposed alternatives including the no action
alternative, description of the affected environment, and evaluation
and comparison of environmental consequences including cumulative
impacts. The preferred alternative incorporates the network of marine
reserves and marine conservation areas originally identified for the
federal phase in the Commission's CEQA document.
NOAA's record of decision for this action, prepared pursuant to 40
CFR 1505.2, is set forth below:
Record of Decision
Introduction
Designated in 1980, the Channel Islands National Marine Sanctuary
(CINMS or Sanctuary) consists of an area of approximately 1,113 square
nautical miles (nmi2) off the southern coast of California. The
Sanctuary boundary begins at the mean high water line and extends
seaward to a distance of approximately six nautical miles (nmi) from
the following islands and offshore rocks: San Miguel Island, Santa Cruz
Island, Santa Rosa Island, Anacapa Island, Santa Barbara Island,
Richardson Rock, and Castle Rock (collectively the Islands). Located
offshore from Santa Barbara and Ventura counties, the Sanctuary
supports a rich and diverse range of marine life and habitats, unique
and productive oceanographic processes and ecosystems, and culturally
significant resources. More than 27 species of cetaceans (whales and
dolphins) use the Sanctuary during at least part of the year. There are
also 5 species of pinnipeds (seals and sea lions) that occur in the
area. More than 60 species of birds feed in the sanctuary and more than
23 species of sharks occur here. In addition, a wealth of Chumash
Native American artifacts as well as the remains of over 100 historic
shipwrecks line the ocean floor of the Sanctuary.
The primary objective of the CINMS is to protect Sanctuary
resources. In meeting this objective, NOAA is establishing federal
marine zones in the CINMS to further the protection of Sanctuary
biodiversity, and to complement the existing network of marine zones
established by the State of California in October 2002 (and implemented
under its authorities in April 2003). The regulations implementing this
action add nine new federal marine zones to the Sanctuary (eight no-
take marine reserves and one limited-take marine conservation area).
These zones total 110.5 nmi2 as marine reserves and 1.7
nmi2 as marine conservation areas. The area of the total
network, including the existing state marine zones, is 214.1
nmi2. All extractive activities (e.g., removal of any
sanctuary resource) and injury to Sanctuary resources are prohibited in
marine reserves. Lobster harvest and recreational fishing for pelagic
finfish (with hook and line only) are allowed within the marine
conservation area, while all other extraction or injury to Sanctuary
resources is prohibited.
NOAA has prepared this record of decision (ROD) in accordance with
regulations published by the Council on Environmental Quality (40 CFR
1505.2) implementing the National Environmental Policy Act (NEPA).
Decision
NOAA is issuing new regulations for the CINMS. These new
regulations prohibit take of all Sanctuary resources in marine reserves
and limit take of all Sanctuary resources in a marine conservation
area.
Alternatives Considered
In its final environmental impact statement, NOAA considered three
alternatives for this action: A no action (or status quo) alternative,
Alternative 1, and Alternative 2.\1\
---------------------------------------------------------------------------
\1\ In addition, NOAA and the State of California considered and
analyzed dozens of other spatial designs. See section 3 of the FEIS
for more information about the process used to develop the range of
alternatives.
---------------------------------------------------------------------------
No Action Alternative
The no action alternative would have maintained the status quo in
the Sanctuary (i.e., no new marine zones would be designated). Under
this alternative, the NMSP would not have taken any new regulatory
action under the NMSA. Existing Sanctuary regulations (e.g., no
discharge) would continue to apply throughout the CINMS. Existing state
marine reserves and marine conservation areas and existing state and
federal management of commercial and recreational activities, including
fishing, would remain in place.
Alternative 1
Under Alternative 1, the NMSP will establish a series of marine
zones. The spatial extent of the overall marine zoning network
alternative was developed by the CDFG and NMSP in 2001, based on the
extensive work of the MRWG and its advisory panels, and is the original
proposed project in the CDFG (2002). The portions of the marine zones
within state waters were established by the FGC and CDFG in 2003.
Alternative 1 contained three sub-alternatives: 1A, 1B, and 1C. In
Alternative 1A, the boundaries of the marine zones (and their
corresponding NMSA regulations) completely overlay the existing state
marine zones and terminate at the mean high water line of the northern
Channel Islands. In Alternative 1B, the boundaries of the marine zones
(and their corresponding NMSA regulations) abut the existing state
marine zone boundaries, thereby including a small portion of state
waters. In Alternative 1C, the boundaries of the proposed marine zones
terminate at the boundary between state and federal waters (3 nmi from
shore), thereby including no state waters. Alternative 1C was NOAA's
preferred alternative.
Alternative 2
Alternative 2 is based on a larger network of marine reserves
developed during the MRWG process with slight modifications to conform
to the boundaries of the existing state marine reserves and
conservation areas. Alternative 2 is the largest of the alternatives
proposed, thereby increasing protection of various habitats and species
of interest, as compared to Alternative 1A. When compared to the no-
action alternative, Alternative 2 adds 11 new marine reserves and one
new marine conservation area. Alternative 2 has a total of 276.9 nmi
\2\ as marine reserves and 12.1 nmi \2\ as marine conservation areas
for a total of 289.0 nmi 2. Alternative 2 would have had the
same regulations as Alternative 1.
Environmentally Preferred Alternative
All alternatives, aside from the no action alternative, would
result in
[[Page 29213]]
environmental benefits in the form of protection of sensitive marine
habitats and species. Alternative 2 is the largest of the alternatives
proposed and includes a network of existing state marine zones and new
federal zones, and would increase protection of various habitats and
species of interest, as compared to the sub-alternatives under
Alternative 1. Therefore, this alternative is considered to be the
environmentally preferred. It was not selected because Alternative 1
better met NOAA's purpose and need.
Mitigation Measures
Because the action would not result in any environmental harm,
there are no specific mitigation measures needed to avoid, minimize, or
compensate for environmental harm.
Decision Making Process
Collectively referred to as the ``Channel Islands marine reserves
process,'' the consideration of marine zones within the CINMS occurred
in three distinct phases: (1) A community-based phase; (2) a State of
California (State) regulatory phase; and (3) a federal regulatory
phase. These three phases are described in detail in the Final
Environmental Impact Statement for this action (see ADDRESSES).
In summary, the alternatives described evolved as a result of the
Channel Islands marine reserves process. Comprehensive marine zoning
network options were originally developed by NOAA and the CDFG
following a comprehensive stakeholder process conducted from 1999
through 2002. In 2002, the FGC supported establishment of state marine
zones in the state waters of the Sanctuary (0-3 nmi) \2\.
---------------------------------------------------------------------------
\2\ Refer to the Environmental Impact Report prepared by the
State of California for its 2002 action. This document is available
for download on NOAA's CINMS Web site at https://
channelislands.noaa.gov/marineres/main.html.
---------------------------------------------------------------------------
Following the publication of the State's final regulations in 2003,
NOAA hosted scoping meetings to consider the extension of the State's
zones into deeper waters of the Sanctuary. In 2004, NOAA released a
preliminary environmental document with a range of alternatives for
public review. NOAA then consulted with local, state, and federal
agencies and the Pacific Fishery Management Council (PFMC) on possible
amendments to the CINMS designation document pursuant to section
303(b)(2) of the National Marine Sanctuaries Act (NMSA) (16 U.S.C.
1433(b)(2)). In addition, in 2005 NOAA provided the PFMC with the
opportunity to prepare draft NMSA fishing regulations pursuant to
section 304(a)(5) of the NMSA (16 U.S.C. 1434(a)(5)) for the potential
establishment of marine reserves and marine conservation areas.
The PFMC response to NOAA's letter regarding draft fishing
regulations stated its support for NOAA's goals and objectives for
marine zones in the CINMS, but recommended that, rather than utilizing
the NMSA, NOAA issue fishing regulations under the Magnuson-Steven
Fishery Conservation and Management Act (MSA) and the relevant
authorities of the states of California, Oregon, and Washington. To
that end, and in accordance with advice from the NOAA Administrator in
his October 19, 2005 letter to the PFMC, the PFMC recommended the
northern Channel Islands federal marine zones be designated as
Essential Fish Habitat (EFH) and Habitat Areas of Particular Concern
(HAPC) under Amendment 19 of the Groundfish Fishery Management Plan
(FMP). The water column in the marine zones would be closed under other
fishery management plan authorities and complementary state laws.
NOAA reviewed the PFMC's recommendations and determined that PFMC
did not have the specificity or record to support the use of the MSA or
state laws to establish limited take or no-take zones in the water
column and thereby did not fulfill NOAA's goals and objectives for
these marine zones in the CINMS. Amendment 19 to the Groundfish FMP
implemented, in part, the proposed marine zones by prohibiting all
bottom contact gear in those proposed zones. Accordingly, NOAA's NMSA
regulations prohibit the take of resources from the zones not
prohibited by the Amendment 19 regulations. Thus, along with the
regulations implementing Amendment 19, the NMSA regulations establish
comprehensive marine reserves and a marine conservation area in the
federal waters part of the CINMS in a manner that fulfills NOAA's goals
and objectives for the marine zones in the CINMS.
In August 2006, NOAA published proposed regulations for this action
and released the related draft environmental impact statement (DEIS)
for public review and comment. Between August and October of 2006, NOAA
received public comment and held two hearings on the proposed rule and
DEIS. Over 30,000 individuals submitted written comments and/or
presented oral testimony on NOAA's proposal. Approximately 99% of these
individuals supported the establishment of Alternative 1A or
Alternative 2.
During the public comment period, the State of California also
submitted comments on NOAA's proposal. In its October 2006 letter, the
CDFG stated that it could only support Alternative 1C (NMSA regulations
in federal waters only) as described in the DEIS. In subsequent
consultations with State representatives and in a letter from the
Secretary of Resources dated January 2, 2007, the State reiterated that
it could only support Alternative 1C at this time. Under Alternative
1C, NOAA would establish marine reserves and a marine conservation area
only in federal waters. NOAA's preferred alternative, identified as
Alternative 1A in the DEIS, would have established marine zones in both
federal and state waters with federal regulations overlaying the entire
network (i.e., from the outer boundary of the federal waters reserves
to the mean high water line of the Channel Islands). As indicated in
the DEIS, Alternative 1C leaves small gaps in protection between the
offshore extent of some of the state waters marine zones established by
the State of California in 2003 and the federal waters marine zones
proposed by NOAA.
On March 16, 2007, the Coastal Commission held a public meeting on
NOAA's consistency determination with California's Coastal Zone
Management Plan under section 307 of the Coastal Zone Management Act
(see https://www.coastal.ca.gov/meetings/mtg-mm7-3.html). At that
meeting, the Coastal Commission passed a motion as follows:
In the event NOAA elects not to implement Alternative 1a, NOAA
will implement Alternative 1c, with the following additional
provisions: Until such time as the Resources Agency and the Fish and
Game Commission designate the areas in between the existing State-
designated MPAs and the 3 mile limit (i.e., the ``gaps'' between the
existing state MPAs and the federal MPAs depicted in Alternative 1c
[and shown on Exhibit 9]), or the Fish and Game Commission/DFG and
NOAA enter into an interagency agreement that establishes MPA
protection for these ``gap'' areas, NOAA will expand Alternative 1c
to include in its MPA designation these ``gaps'' between the outer
boundaries of the existing state MPAs and the State-federal waters
boundary (3nm from shore).
At this meeting, the CDFG representative also stated that the FGC
could close these gaps in protection using state laws by August 2007.
Based on the record, including comments received during the public
comment period and the record of the Coastal Commission, NOAA
determined that at this time there is sufficient information and
rationale to establish marine zones in the federal waters of the
Sanctuary (i.e., implement NOAA's alternative 1C). This Record of
Decision
[[Page 29214]]
supports that determination and represents NOAA's final decision to
implement the regulations in the federal waters of the Sanctuary
associated with Alternative 1C.
With regard to state waters of the Sanctuary, NOAA has decided to
defer action on establishing federal marine zones until the FGC has had
an opportunity to close the gaps between the federal marine zones and
the state marine zones in a manner consistent with the Coastal
Commission's resolution and the CDFG representative's statement.\3\ The
State of California has already begun this process by placing it on the
agenda for a decision at the August 2007 meeting of the FGC. Also, the
CDFG has begun preparing the necessary documentation to support the
FGC's decision. If the FGC is able to take sufficient action in a
timely manner, NOAA would take no further action under the NMSA. If the
FGC is not able to take sufficient action in a timely manner, NOAA
would issue regulations under the NMSA that would effectively close the
gaps associated with Alternative 1C by extending federal protections
into state waters to meet the boundaries of the marine zones
established by the FGC in 2003. In that instance, a second record of
decision for that subsequent action would be issued to finalize such
action.
---------------------------------------------------------------------------
\3\ Closing the gaps would also be consistent with the public
record supporting the 2002 decision of the California Fish and Game
Commission to establish marine zones in the Sanctuary.
---------------------------------------------------------------------------
Conclusion
The new regulations identified above apply to all users of the
Sanctuary. Based on socioeconomic information gathered by NOAA and
identified in the FEIS, the socioeconomic impacts of these regulations
can be characterized as:
Having a small impact on existing consumptive
activities (commercial fishing and consumptive recreational
activities).
Beneficial to non-consumptive recreational users. These
increased benefits take the form of increases in diversity and
abundance of wildlife for viewing and photography opportunities.
Benefits may also be derived from the decrease in the density of
users or in the reduction in conflicts with consumptive users.
Beneficial to management, research, and education
because relatively undisturbed areas (i.e., reference areas) will be
available for comparison with areas outside the marine zones; and
Beneficial for intrinsic and heritage purposes.
NOAA expects, therefore, that this rule will have no significant
socioeconomic impacts and that the implementation of marine zones in
the CINMS will have beneficial ecological impacts on marine communities
and habitats.
III. Revised Designation Document
Section 304(a)(4) of the NMSA requires that the terms of
designation include the geographic area included within the Sanctuary;
the characteristics of the area that give it conservation,
recreational, ecological, historical, research, educational, or
aesthetic value; and the types of activities subject to regulation by
the Secretary to protect these characteristics. Section 304(a)(4) also
specifies that the terms of designation may be modified only by the
same procedures by which the original designation was made. To
implement this action, the CINMS Designation Document, originally
published in the Federal Register on October 2, 1980 (45 FR 65198), is
modified to read as follows (new text in bold and deleted text in
brackets and italics):
Preamble
Under the authority of the Marine Protection, Research and
Sanctuaries Act of 1972, Pub. L. 92-532, (the Act) the waters
surrounding the northern Channel Islands and Santa Barbara Island are
hereby designated a Marine Sanctuary for the purposes of preserving and
protecting this unique and fragile ecological community.
Article 1. Effect of Designation
Within the area designated as the Channel Islands National Marine
Sanctuary (the Sanctuary), described in Article 2, the Act authorizes
the promulgation of such regulations as are reasonable and necessary to
protect the values of the Sanctuary. Article 4 of this Designation
lists those activities which may require regulation but the listing of
any activity does not by itself prohibit or restrict it. Restrictions
or prohibitions may be accomplished only through regulation, and
additional activities may be regulated only by amending Article 4.
Article 2. Description of the Area
The Sanctuary consists of an area of the waters off the coast of
California, of approximately [1252.5] 1,128 square nautical miles (nmi)
adjacent to the northern Channel Islands and Santa Barbara Island
seaward to a distance of approximately 6 nmi. The precise boundaries
are defined by regulation.
Article 3. Characteristics of the Area That Give It Particular Value
The Sanctuary is located in an area of upwelling and in a
transition zone between the cold waters of the California Current and
the warmer Southern California Countercurrent. Consequently, the
Sanctuary contains an exceptionally rich and diverse biota, including
30 species of marine mammals and several endangered species of marine
mammals and sea birds. The Sanctuary will provide recreational
experiences and scientific research opportunities and generally will
have special value as an ecological, recreational, and esthetic
resource.
Article 4. Scope of Regulation
Section 1. Activities Subject to Regulation
In order to protect the distinctive values of the Sanctuary, the
following activities may be regulated within the Sanctuary to the
extent necessary to ensure the protection and preservation of its
marine features and the ecological, recreational, and esthetic value of
the area:
a. Hydrocarbon operations.
b. Discharging or depositing any substance.
c. Dredging or alteration of, or construction on, the seabed.
d. Navigation of vessels except fishing vessels or vessels
[travelling] traveling within a Vessel Traffic Separation Scheme or
Port Access Route designated by the Coast Guard outside of 1 nmi from
any island.
e. Disturbing marine mammals or birds by overflights below 1000
feet.
f. Removing or otherwise deliberately harming cultural or
historical resources.
g. Within a marine reserve, marine park, or marine conservation
area, harvesting, removing, taking, injuring, destroying, possessing,
collecting, moving, or causing the loss of any Sanctuary resource,
including living or dead organisms or historical resources, or
attempting any of these activities.
h. Within a marine reserve, marine park, or marine conservation
area, possessing fishing gear.
Section 2. Consistency With International Law
The regulations governing the activities listed in Section 1 of
this article will apply to foreign flag vessels and persons not
citizens of the United States only to the extent consistent with
recognized principles of international law including treaties and
international agreements to which the United States is signatory.
[[Page 29215]]
Section 3. Emergency Regulations
Where essential to prevent immediate, serious and irreversible
damage to the ecosystem of the area, activities other than those listed
in Section 1 may be regulated within the limits of the Act on an
emergency basis for an interim period not to exceed 120 days, during
which an appropriate amendment of this article would be proposed in
accordance with the procedures specified in Article 6.
Article 5. Relation to Other Regulatory Programs
Section 1. Fishing
The regulation of fishing is not authorized under Article 4, except
within portions of the Sanctuary designated as marine reserves, marine
parks, or marine conservation areas established pursuant to the goals
and objectives of the Sanctuary and within the scope of the State of
California's Final Environmental Document ``Marine Protected Areas in
NOAA's Channel Islands National Marine Sanctuary'' (California
Department of Fish and Game, October 2002), certified by the California
Fish and Game Commission. However, fishing vessels may be regulated
with respect to discharges in accordance with Article 4, Section 1,
paragraph (b) and aircraft conducting kelp bed surveys below 1000 feet
can be regulated in accordance with Article 4, Section 1, paragraph
(e). All regulatory programs pertaining to fishing, including
particularly regulations promulgated under the California Fish and Game
Code and Fishery Management Plans promulgated under the Fishery
Conservation and Management Act of 1976, 16 U.S.C. 1801 et seq., shall
remain in effect. All permits, licenses and other authorizations issued
pursuant thereto shall be valid within the Sanctuary unless authorizing
any activity prohibited by any regulation implementing Article 4.
Fishing as used in this article and in Article 4 includes kelp
harvesting.
Section 2. Defense Activities
The regulation of those activities listed in Article 4 shall not
prohibit any activity conducted by the Department of Defense that is
essential for national defense or because of emergency. Such activities
shall be consistent with the regulations to the maximum extent
practicable.
Section 3. Other Programs
All applicable regulatory programs shall remain in effect and all
permits, licenses and other authorizations issued pursuant thereto
shall be valid within the Sanctuary unless authorizing any activity
prohibited by any regulation implementing Article 4. The Sanctuary
regulations shall set forth any necessary certification procedures.
Article 6. Alterations to This Designation
This Designation can be altered only in accordance with the same
procedures by which it has been made, including public hearings,
consultation with interested federal and state agencies and the Pacific
Regional Fishery Management Council, and approval by the President of
the United States.
IV. Summary of Regulations
These final regulations implement NOAA's preferred alternative by
establishing marine reserves and a marine conservation area within the
federal waters of CINMS. The regulations define two new terms (pelagic
finfish and stowed and not available for immediate use), prohibit all
extractive activities and injury to Sanctuary resources within the
marine reserves, and prohibit all extractive activities and injury to
Sanctuary resources within the marine conservation area except
recreational fishing for pelagic finfish and commercial and
recreational lobster fishing (Anacapa Island Marine Conservation Area).
These regulations also add two new appendices that list the boundary
coordinates for the marine reserves and marine conservation area. These
regulations modify subpart G of the National Marine Sanctuary Program
Regulations (15 CFR part 922), the regulations for the Channel Islands
National Marine Sanctuary.
A. Establishment of Marine Reserves and Marine Conservation Areas
These regulations establish under the NMSA eight marine reserves
and one marine conservation area within the CINMS. Refer to figure 1
for a map depicting the locations of the marine reserves and marine
conservation area. The marine reserves are distributed throughout the
CINMS and extend slightly beyond the current boundaries of the CINMS in
four locations, increasing the geographic area of the Sanctuary by
about 15 square nautical miles. This action increases the overall size
of the Sanctuary from approximately 1,113 square nautical miles to
approximately 1,128 square nautical miles, an approximately 15 square
nautical mile increase. This small amount added allows the boundary of
four of the marine reserves to be defined by straight lines projecting
outside the current CINMS boundary, allowing for better enforcement of
the marine reserves. The boundaries of the marine reserves and marine
conservation area are consistent with the marine reserves and marine
conservation areas established by the Commission in 2002 in state
waters-essentially extending most of them into federal waters of the
Sanctuary. NOAA is changing the number identifying the total area of
the CINMS from approximately 1,252.5 square nautical miles to
approximately 1,128 square nautical miles. This change is based on
North American Datum of 1983 (NAD 83) and adjusts for technical
corrections using updated technologies. The legal description of the
CINMS is updated to reflect this change. This update does not
constitute a change in the geographic area of the Sanctuary (other than
the approximately 15 square nautical miles referred to above) but
rather an improvement in the estimate of its size.
[[Page 29216]]
[GRAPHIC] [TIFF OMITTED] TR24MY07.002
Under these final regulations, NOAA establishes two marine reserves
in the area around San Miguel Island, one around Santa Rosa Island, two
around Santa Cruz Island, two around Anacapa Island, and one around
Santa Barbara Island. The marine conservation area is established off
of Anacapa Island.
The total area designated marine reserves under these final
regulations is 110.5 square nautical miles. The marine conservation
area encompasses an additional 1.7 square nautical miles.
Based on the record, including comments received during the public
comment period and the record of the Coastal Commission, NOAA has
determined that there is sufficient information and rationale to
establish marine zones in the federal waters of the Sanctuary (i.e.,
implement NOAA's Alternative 1C). With regard to state waters of the
Sanctuary, NOAA has decided to defer action on establishing marine
zones until the FGC has had an opportunity to close those gaps in a
manner consistent with the Coastal Commission's motion and the CDFG
representative's statement. The State of California has already begun
this process by placing it on the agenda for a decision at the August
2007 meeting of the FGC. Also, the CDFG has begun preparing the
necessary documentation to support the FGC's decision. NOAA is,
therefore, leaving the record open with regard to a decision to
establish marine zones in state waters of the Sanctuary, and is
requesting additional public comment on this specific issue.
B. Activities Prohibited Within the Marine Reserves
Under the final regulations, NOAA prohibits any harvesting,
removing, taking, injuring, destroying, collecting, moving, or causing
the loss of any Sanctuary resource, including living or dead organisms
or historical resources, or attempting to do so, within any of the
marine reserves. The term ``sanctuary resource'' is broadly defined in
the NMSP regulations at 15 CFR 922.3 and means any living or non-living
resource that contributes to the conservation, recreational,
ecological, historical, scientific, educational, or aesthetic value of
the Sanctuary. For the CINMS, the term ``Sanctuary resource'' includes,
for example, the seafloor and all animals and plants of the Sanctuary.
It also includes historical resources (which, pursuant to 15 CFR 922.3,
include cultural and archeological resources), such as shipwrecks and
Native American remains. In addition, to enhance compliance and aid in
enforcement, these final regulations also prohibit possessing fishing
gear and Sanctuary resources inside a marine reserve, except in certain
circumstances. These final regulations allow possession of legally
harvested fish stowed on a vessel at anchor in or transiting through a
marine reserve and also allow the possession of stowed fishing gear,
provided the gear is not available for immediate use.
These final regulations prohibit only those extractive activities
within marine reserves that are not prohibited by 50 CFR part 660, the
NOAA regulations that govern ``Fisheries off West Coast States'' (MSA
regulations). Therefore, if an extractive activity is prohibited by MSA
regulations, it is not prohibited by these final NMSA regulations.
Conversely, all extractive activities not prohibited by MSA regulations
are prohibited by these final NMSA regulations within marine reserves.
In the future, if NOAA were to amend the MSA regulations to prohibit
additional extractive activities within marine reserves, these NMSA
regulations would correspondingly narrow in scope. If, for MSA
purposes, NOAA were to amend the MSA regulations to allow additional
extractive activities, these NMSA
[[Page 29217]]
regulations would correspondingly expand in scope to ensure all forms
of extraction are prohibited within marine reserves. In either case,
the MSA rulemaking making such change would provide the public with
notice of the corresponding change in applicability of the NMSA
regulation.
Regardless of the specific regulatory mechanism, the intended
result of this final rule is for all extractive activities to be
prohibited within the marine reserves.
C. Activities Prohibited Within the Marine Conservation Areas
These final regulations prohibit the same activities within the
marine conservation area as within the marine reserves except that
commercial and recreational lobster fishing and recreational fishing
for pelagic finfish are allowed in the marine conservation area at
Anacapa Island. Commercial fishing for pelagic finfish is prohibited
within the marine conservation area.
Like the final regulations for marine reserves, the final
regulations for the marine conservation area only prohibit activities
that are not prohibited by applicable MSA regulations codified at 50
CFR part 660. Any changes to the applicable MSA regulations would
result in a corresponding change in the applicability of the NMSA
regulations, as discussed above.
D. Enforcement
The final regulations will be enforced by NOAA and other authorized
agencies (e.g., the California Department of Fish and Game, United
States Coast Guard, and National Park Service) in a coordinated and
comprehensive way. Enforcement actions for an infraction will be
prosecuted under the appropriate statutes or regulations governing that
infraction. The result is that enforcement actions may be taken under
State of California authorities, the NMSA, the MSA, or other relevant
legal authority.
E. Permitting
The NMSP regulations, including the regulations for the CINMS,
allow NOAA to issue permits to conduct activities that would otherwise
be prohibited by the regulations. Most permits are issued by the
Superintendent of the CINMS. Requirements for filing permit
applications are specified in NMSP regulations and the Office of
Management and Budget-approved application guidelines (OMB control
number 0648-0141). Criteria for reviewing permit applications are
contained in the CINMS and NMSP regulations at 15 CFR 922.77 and
922.48, respectively. In general, permits may be issued for activities
related to scientific research, education, and management. Permits may
also be issued for activities associated with the salvage and recovery
efforts for a recent air or marine casualty. (Emergency activities
would not require a permit.)
Nationwide, NOAA issues approximately 200 national marine sanctuary
permits each year. Of this amount, two or three are for activities
within the CINMS. The majority of permits issued for activities within
the CINMS are for activities related to scientific research. NOAA
expects this