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Sea
Otters in the
Sanctuary
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A
large proportion (72 percent) of the California
population of sea otters (Enhydra lutris nereis) is
found within the boundaries of the Monterey Bay
National Marine Sanctuary. Small populations of
otters also exist at San Nicolas and San Miguel
Islands off Southern California. For the past ten
years, the mainland range has been well-established
between Año Nuevo Island at the north end
and Purisima Point at the south. Through the years,
individual otters have occasionally been seen as
far north as Bodega Bay. Within just the last year,
otters also for several months occupied Cojo Bay to
the south of the established range, in a group
often numbering over 100 animals.
In 1911, otters were
protected under the International Fur Seal Treaty
from fur hunting. Additional protection was
afforded via the federal Endangered Species Act
(ESA), under which the species has been listed as
"threatened" since 1977, and by the Marine Mammal
Protection Act, where otters are listed as
"depleted." With these protections, the population
has slowly grown in size and range. However, the
population remains small relative to historic
levels, and is vulnerable to impacts from oil
spills, point- and non-point water pollution,
accidental capture in some types of fishing gear,
and other human-related activities. Despite the
ease with which sea otters can be observed and
studied, the individual and collective role each
real or potential impact can play remains difficult
to isolate and quantify.
Reversing what had been a
generally slow but positive growth trend, the
California otter population began an apparent
decline in 1994 that persists in 1998. (See Figure
1.)
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Sea
Otter Survey Data
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Spring
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Fall
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Year
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Total
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Pups
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Total
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Pups
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PPI
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SPR%
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FAL%
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%Dead
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1982
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1346
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222
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1338
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144
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292
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-
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-
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7.4
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1983
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1275
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122
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1226
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164
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214
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-5.3
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-8.4
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9.2
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1984
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1304
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123
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-
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-
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-
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2.3
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-
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10.1
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1985
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1360
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236
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1221
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155
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306
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4.3
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-
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5.1
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1986
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1570
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225
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1204
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113
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285
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15.4
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-1.4
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5.1
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1987
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1650
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220
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1369
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108
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267
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5.1
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13.7
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5.6
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1988
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1724
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219
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-
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-
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-
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4.5
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-
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5.0
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1989
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1856
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285
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1599
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115
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337
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7.7
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-
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5.1
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1990
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1678
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214
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1636
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120
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281
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-9.6
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2.3
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5.7
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1991
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1941
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241
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1661
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138
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309
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15.7
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1.5
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3.9
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1992
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2101
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291
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1715
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134
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344
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8.2
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3.3
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4.9
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1993
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2239
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217
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1805
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143
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288
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6.6
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5.2
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5.5
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1994
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2359
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283
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1845
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115
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343
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5.4
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2.2
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5.3
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1995
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2377
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282
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2190
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137
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331
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0.8
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18.7
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6.6
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1996
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2278
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315
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2019
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161
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385
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-4.2
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-7.8
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7.9
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1997
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2229
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310
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2205
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197
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376
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-2.2
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-0.7
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6.8
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1998
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2114
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159
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1937
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211
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250
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-5.2
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-12.2
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9.3
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(PPI Pup Production Index; SPR%C %
Change Total Otters, Spring; FALL%C %
Change Total Otters, Fall; %DEAD % Dead as
Percent of Spring Count)
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Survey
counts can fluctuate from year to year without
providing proof that the population is actually
declining. However, there has been an overall
decline of 11 percent between the Spring 1995 and
Spring 1998 counts, a downward trend that has
persisted for three years and appears real. If this
rate of decline continues, the California sea otter
population may qualify for an "endangered" listing
under the ESA as early as the year 2000.
Hand in hand with the
decreased numbers from the surveys, and supporting
the sense that the decline is indeed real, has been
an increase in the number of dead otters recovered
each year since around 1991 (shown in Figure 1 as a
proportion of total otters counted the previous
spring).
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Sea
Otter Research and Conservation
Program
In a cooperative
project headed by the Marine Wildlife
Veterinary Care and Research Center in
Santa Cruz and the Wildlife Health Center
at the University of California at Davis,
with assistance from the U.S. Geological
Survey Biological Resources Division and
the Monterey Bay Aquarium, thirty otters
were captured from Monterey, Moss Landing,
and Santa Cruz as part of an ongoing
effort to assess the health status of the
southern sea otter
population.
During a short holding period, project
participants tagged the animals for
identification purposes, and collected
blood to monitor baseline hematological
parameters and to test for the prevalence
of Brucella, Leptospira, canine distemper,
calicivirus, and Coccidioides immitis in
free-ranging and rehabilitated southern
sea otters.
Plans are
underway by this same group to study
behavior and causes of mortality in
juvenile southern sea otters, to examine
contaminant levels in sea otters and
coastal invertebrate species, to monitor
accidental drownings of sea otters that
become entrapped in gear used for coastal
fin-fish fisheries and gillnet fisheries
in Monterey Bay, and to reinitiate field
studies on basic behavioral and
demographic parameters, all in an effort
to understand and mitigate the causes of
the current southern sea otter population
decline better.
On another note:
at least three boat-strike deaths occurred
in Elkhorn Slough in 1998, including an
otter successfully raised and reintroduced
through the Aquarium's rehabilitation
program. Another boat-strike victim,
rescued from Monterey harbor, required
orthopedic surgery to repair a broken
ankle, but was eventually returned to the
wild.
Andrew B.
Johnson
Monterey Bay Aquarium,
Sea Otter Research and Conservation
Program
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Sources of mortality among
otters range from the natural to the unexpected.
The unexpected finding of the past few years, from
studies by the National Wildlife Health Center, has
been that infectious disease accounts for 40
percent of the sea otter deaths, a level five times
higher than that typically seen in wild,
free-ranging populations of other animals known to
or studied by the Center. These diseases are
encountered by otters in food or water; there is no
known incidence of these diseases being
communicable to other otters, other marine animals,
or humans.
Some of these diseases may
have been present in the otter population for
decades but gone undetected until recently, when
more exacting post-mortem examinations were made.
In others cases, the presence of some diseases are
apparent on even a gross examination of the dead
otter, and changes in infection rates indicate a
change within the otter environment or with an
otter's physiological and immunological ability to
ward off the infection.
Increased susceptibility
to disease can be caused by the presence of
environmental contaminants. Sea otters are exposed
to various environmental contaminants through
point- and non-point sources and through the
nearshore food web, which includes many species of
filter-feeding shellfish that concentrate
contaminants before they are eaten by otters,
seabirds, or humans. Our understanding of the role
played by these contaminants is still astoundingly
incomplete.
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Endangered
Species Snapshot:
Sanctuary Salmon and Steelhead
Populations
- Warm ocean
temperatures associated with El
Niño harmed southern Coho salmon
populations. Adults arriving in the
fall and early winter, when the
temperatures were highest, were most
affected; because of the warm
temperatures early females produced
eggs with no nucleus. Even in
March-April (with cooler water), where
80-90 percent fertility is common,
fertility was in the 60-70 percent
range.
- Very high
winter and spring river flows destroyed
both Coho food (aquatic insects) and
their nests. The good news: in the
summer the tremendous flows continued,
so populations were in better shape, in
that regard, than they've been in past
drought years.
- Angling
regulations changed significantly in
1998. The San Lorenzo River is now the
only river where one can catch and keep
steelhead; all others are "catch and
release." In that river one can keep
hatchery fish only. The Carmel River
was opened for "catch and release" of
steelhead in winter 1998 for the first
time in ten years.
- Sea lions'
fondness for salmon continued to create
conflicts between sea lions and
fishers. However, this year saw an
increased cooperative effort between
conservation groups, fishers, and
scientists to address this
issue.
- The
California Department of Fish and Game
allotted significant funds in 1998 to
watershed restoration. (These include,
by county: Marin - $40,881; San
Francisco - $0; San Mateo - $136,684;
Santa Cruz - $241,188; Monterey -
$117,271; San Luis Obispo - $65,000.*)
It also completed a draft restoration
plan for Coho salmon in Santa Cruz and
San Mateo Counties.
* These figures
represent funds allocated by the end of
the calendar year; additional 1998 funds
will be distributed in 1999.
Jenny Carless
Editor
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Our
knowledge of the role played by nearshore fisheries
is also still incomplete. Resource users -
particularly those in commercial sea urchin and
abalone shellfisheries - are watching closely to
see how recent sea otter survey and mortality
information affects sea otter population recovery
and management decisions, and potentially, the
livelihood and survival of key fisheries. Likewise,
concerns over possible sea otter entrapment in fish
and shellfish traps have grown over the past year,
as has renewed awareness of possible continued
entanglement in coastal gill nets. A clearer
understanding of the impact of fisheries on sea
otters, and of otters on fisheries, is critical to
guiding future conservation management decisions.
Other California coastal resource uses, such as oil
extraction and transport, local kelp harvest
activities, and human recreational activities, also
contribute to possible impacts on otters and their
habitat.
Sea otters serve as an
"indicator" species of ecosystem change, and
perhaps more telling, an indication of how well we
can use our collective creative intelligence to
resolve issues of sea otter and nearshore ecosystem
recovery, protection, and future management. The
Sanctuary provides not only critical habitat to 70
percent of the population of this species, it will
serve a catalytic role in addressing issues related
to its health, recovery, and management.
Ellen Faurot-Daniels
Energy, Ocean Resources, and Technical Services
Div.,
California Coastal Commission
Examples
of Endangered and Threatened Species of the
Monterey Bay National Marine
Sanctuary
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The
Sanctuary is home to many endangered and
threatened species. The Sanctuary's
legislation works in concert with the
Endangered Species Act (ESA) and other
laws to protect the marine
environment.
A species is
listed as "endangered" if it is in danger
of extinction throughout all or a
significant portion of its range, or
"threatened" if it is likely to become
endangered in the foreseeable future. The
chart below highlights some of the listed
species found in the Sanctuary.
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Organism
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Federal Status
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State Status
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Cetaceans
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Blue whale (Balaenoptera
musculus)
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Endangered
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None
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Humpback whale (Megaptera
novaeangliae)
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Endangered
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None
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Fin whale (Balaenoptera
physalus)
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Endangered
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None
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Sperm whale (Physeter
macrocephalus)
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Endangered
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None
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Right whale (Eubalaena
glacialis)
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Endangered
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None
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Sei whale (Balaenoptera
borealis)
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Endangered
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None
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Pinnipeds
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Guadalupe fur seal (Arctocephalus
townsendi)
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Threatened
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Threatened
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Steller sea lion (Eumetopias
jubatus)
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Threatened
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None
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Birds
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California Brown Pelican (Pelecanus
occidentalis)
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Endangered
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Endangered
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California Least Tern (Sterna
antillarum browni)
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Endangered
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Endangered
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California Snowy Plover (Charadrius
alexandrinus nivosus)
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Species of Special
Concern
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Threatened
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Marbled Murrelet (Brachyramphus
marmoratus)
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Threatened
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Endangered
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Fissiped
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Southern sea otter (Enhydra
lutris)
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Endangered
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None
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Turtles
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Green sea turtle (Chelonia
mydas)
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Threatened
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None
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Leatherback sea turtle (Dermochelys
coriacea)
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Endangered
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None
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Pacific ridley sea turtle
(Lepidochelys olivacea)
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Threatened
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None
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Loggerhead sea turtle (Caretta
caretta)
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Threatened
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None
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Anadromous Fishes
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Chinook salmon (Oncorhynchus
tshawytscha) - spring
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Canidatae for Endangered
Listing
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Threatened
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Chinook salmon (Oncorhynchus
tshawytscha) - winter
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Endangered
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Endangered
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Coho salmon (Oncorhynchus
kisutch) - Central CA
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Threatened
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Endangered
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Steelhead trout (Oncorhynchus
mykiss)
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Threatened
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None
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Source: California Dept. of Fish and
Game; US Fish and Wildlife Service
Compiled by Kip Evans, Monterey Bayt
National Marine Sanctuary
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Right
Whale Sighting
One of the
world's most endangered baleen whales, the
right whale, was sighted off the Big Sur
coast in early 1998. For marine scientists
and whale biologists, this particular
event was extraordinary not only because
of the rarity of such sightings, but
because it was a unique observation of two
different types of baleen whales
interacting.
Sanctuary
Superintendent Bill Douros and NOAA pilot
Matt Pickett looked down from their plane
during aerial surveys and saw a large
black whale being chased by several gray
whales. Douros estimates that there were
twelve gray whales in an area of about a
quarter square mile near the right whale,
although only two were obviously
interacting with the right
whale.
The fifty-foot
right whales were hunted to the brink of
extinction near the turn of the century.
They are very rare along the California
coast.
Nineteenth
century whaling records show that right
whales were once abundant along all major
continents in the temperate waters of the
northern and southern hemispheres,
although their numbers may have been much
lower along the Central Coast. In the
eastern North Pacific, they could once be
seen from central Baja California to the
Bering Sea in Alaska. Today, such
sightings are few and very scattered.
During the past fifteen years, only four
verified sightings have been recorded in
the eastern North Pacific, yet now three
of these were within the boundaries of the
Sanctuary.
Some experts
estimate that as few as fifty to 100 right
whales are left in the eastern North
Pacific. (Please see Spring 1998
newsletter for further details on this
sighting and on right whales.)
Kip Evans
Monterey Bay National marine
Sanctuary
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