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Productivity
Cycles in the Monterey Bay Pelagic
Ecosystem and La Niña - Boom or
Bust?
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Within
the past three years, Monterey Bay has experienced
two acute and distinctly different climatic events
that have had far-reaching impacts on seasonal
productivity within the offshore ecosystem. The
1997-98 El Niño event was the strongest
recorded this century and caused profound declines
in nutrient upwelling, phytoplankton growth,
zooplankton productivity, and seabird and marine
mammal abundance and reproduction (see Ecosystem
Observations 1998, page 17).
This year La Niña
conditions have prevailed in the Northeast Pacific.
La Niña events have, in many ways, the
opposite effects of El Niños. Typically, La
Niñas are characterized by colder than
normal ocean temperatures occurring along most of
the West Coast of North America. This cold water is
the result of intense wind-driven upwelling along
the coast (the northwest winds during the spring of
1999 were some of the strongest and most persistent
on record!). The La Niña event has provided
us once again with a unique opportunity to gain
insights into the ecology of the pelagic ecosystems
during acute climatic events.
Upwelling
and Phytoplankton Productivity
Strong northwest
winds during the spring of 1999 resulted in
extremely high levels of upwelling. Upwelling
indices were up to two standard deviations above
normal for the central California region. AVHRR
(Advanced Very High Resolution Radiometers)
satellite imagery from this period revealed
numerous, long filaments of cold nutrient-rich
water extending far offshore from headlands
associated with coastal upwelling centers including
Points Arena, Reyes, Año Nuevo, Sur, and
Conception. Nutrient input associated with this
intense upwelling resulted in a broad band of high
phytoplankton productivity that extended up to 100
km offshore of Monterey Bay. Upwelling-favorable
winds dramatically diminished in July and were
largely absent throughout late summer and fall. In
response, phytoplankton levels in Monterey Bay
decreased markedly, and by late summer values were
around the long-term mean for this time of
year.
Monterey
Bay Zooplankton Abundance
1997-99
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Figure
1: Mean seasonal monthly zooplankton
abundance (integrated backscatter, 200kHz)
within Monterey Bay from
1997-1999.
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Patterns of primary productivity within the central
California region during 1998 were distinctly
different to those described above. Upwelling and
phytoplankton levels were anomalously low during
the spring and early summer of 1998 when the
pelagic ecosystem was still heavily under the
influence of El Niño conditions. By July
1998 upwelling-favorable winds returned to central
California and upwelling indices remained well
above the long-term mean late into the
fall.
Zooplankton
Abundance
High levels of primary productivity in the spring
of 1999 translated to high zooplankton abundance in
early- and mid-summer. This followed the typical
seasonal pattern of summer peaks in zooplankton
biomass following spring peaks in phytoplankton
productivity. Zooplankton levels during the summer
of 1999 were the highest recorded during the past
three years, and they remained high throughout the
fall (Figure 1). In comparison, zooplankton levels
were distinctly lower in the summer of 1998 but
increased following the resurgence of upwelling in
the late summer and fall.
Krill
Abundance and Species
Composition
High primary productivity levels in the spring of
1999 resulted in high levels of larval production
and recruitment to krill populations within the
central California region. In addition, krill --
particularly larvae and juveniles—were broadly
distributed offshore, due in all likelihood to
offshore water flow caused by strong levels of
upwelling. Numerous surface swarms of large
reproductive adults were observed within Monterey
Bay on several occasions in April and May 1999,
indicating ongoing spawning activity. These swarms
were targeted by a number of predators including
fish, seabirds, and even opportunistic gray whales
en route to their feeding grounds in Alaska! This
was in stark contrast to conditions in the spring
of 1998, when krill abundance was conspicuously
lower. Krill levels declined noticeably with the
cessation of coastal upwelling in July 1999,
however it is unclear whether this was due to
declines in total abundance, dispersal to deeper
water, or a combination of both.

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Figure
2: Thysanoessa spinifera, a relatively
large krill found in cooler coastal waters
from Alaska to California. (©Baldo
Marinovic)
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A major shift in the species composition of the
krill community in Monterey Bay also occurred
between 1998 and 1999. Euphausia pacifica typically
dominates the krill community year round in
Monterey Bay; however, in the early part of 1998
the southern species Nyctiphanes simplex comprised
a substantial portion of the community and the cool
temperate Thysanoessa spinifera (Figure 2) was
virtually absent. By late 1998, with the onset of
coastal upwelling, the species composition
gradually shifted back to a more typical mix of E.
pacifica and T. spinifera. This pattern continued
into 1999, with high levels of recruitment for T.
spinifera observed both in the spring and
fall.
What
have we learned?
Both the 1997-98
El Niño and the current La Niña
events have provided us with unique insights into
ecological processes within the Monterey Bay
pelagic ecosystem. Productivity at multiple levels
demonstrated predictable responses to both these
events, declining dramatically in 1997-98 and
reaching high levels in late 1998 and 1999. There
were, however, unexpected patterns observed during
both events as well. In 1998 the return of
upwelling late in the season resulted in dense
krill aggregations within Monterey Bay that
attracted record numbers of whales. In contrast,
the fall of 1999 was characterized by relatively
low levels of coastal upwelling. As a result, krill
aggregations were more diffuse and foraging whales
more scarce. One implication of these findings is
that it appears that episodic periods of upwelling
that persist into the fall are necessary to
maintain dense aggregations of krill within
Monterey Bay, even during years when overall (and
especially springtime) productivity is high. These
findings highlight the value of acute climatic
events in providing insights into ecological
processes as well as the importance of maintaining
ongoing ecosystem monitoring within the pelagic
waters of the Sanctuary.
Baldo Marinovic1,
Donald A. Croll1, Francisco
Chavez2,
and Scott R. Benson3
1 University of
California Santa Cruz
2 Monterey Bay Aquarium Research Institute
3 Moss Landing Marine Laboratories

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Contrasting
Effects of La Niña and El
Niño on Recruitment of Juvenile
Rockfishes
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Understanding
how and why populations and communities change over
time is one of the greatest challenges to marine
ecologists and fisheries biologists alike. Such
knowledge is critical to distinguishing population
responses to natural environmental fluctuations
from those caused by human impacts. Critical to
this goal is recognizing how life history traits
influence how populations respond to environmental
variation. This is made very clear by observing how
populations responded to the recent dramatic
environmental changes experienced between the El
Niño of 1998 followed abruptly by the La
Niña of 1999.
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Figure
1: Changes in recruitment of
young-of-year rockfish between El
Niño and La Niña years.
"Kelp complex" rockfish include kelp,
gopher, and black and yellow rockfish.
"Mid-water aggregating" rockfish include
olive, yellowtail, and black rockfish.
Error bars represent one standard
error.
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One of the most important
life history traits of most marine organisms is the
great distance that young can be dispersed from the
adults that produce them. Because the eggs and
larvae of most reef fishes and invertebrates
(barnacles, mussels, crabs, sea urchins, and the
like) are carried great distances by water
currents, reproduction by a population of adults
has little direct bearing on how many young will
replenish that population that year. Instead, local
populations are reliant on the delivery of young
that are produced by adults elsewhere. This
delivery of young to a population can vary markedly
from year to year, greatly influencing the number
of juveniles and, eventually, adults in a
population. Ecologists refer to this replenishment
of populations by young from the plankton as
"recruitment" and know now that it is critical to
understanding year-to-year variation in population
size.
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Figure
2: Changes in recruitment of young-of-year
kelp, gopher, and black and yellow
rockfish to experimental kelp plots
between La Niña and El Niño
years.
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Surveys of rockfish recruitment during the El
Niño conditions of 1998 and the La
Niña of 1999 demonstrate the dramatic
effects of such large-scale punctuated events on
reef fish populations and communities. We surveyed
rockfish recruitment visually by counting young
(< 8 cm long) rockfish in kelp beds along the
coast of Monterey during the summers of 1998 and
1999. We also created plots of giant kelp plants
and monitored recruitment to these controlled
habitats from one year to the next. During El
Niño conditions, shallow dwelling rockfishes
such as gopher, kelp, and black and yellow rockfish
recruited in great numbers (Figure 1). At the same
time, recruitment of juvenile blue, black, olive,
yellowtail, and boccacio rockfish was poor.
However, the pattern was completely reversed the
following year under La Niña conditions
(Figure 1). The marked change in recruitment of the
kelp-associated species to kelp plots indicates
that such changes are not based on changes in the
amount of kelp (Figure 2). In fact, there was much
more kelp during La Niña conditions. These
observations indicate not only how these climatic
events contribute to year-to-year changes in
replenishment of reef fish populations, but also
how species respond very differently to such
events.
Similar patterns have been
reported for other areas along the central coast by
biologists with the California Department of Fish
and Game and the National Marine Fisheries Service.
Such observations, along with data on distribution
of rockfish larvae, suggest that differences in
patterns of larval dispersal and timing of
spawning, coupled with differences in the timing
and strength of coastal upwelling, may be
responsible for the strong differences in how
species respond to such climatic events. Such
implications highlight the importance of
relationships between life histories and
oceanographic features in understanding the
dynamics of reef fish populations and
communities.
--Mark Carr and
Arnold Ammann
Department of Ecology and Evolutionary
Biology,
University of California Santa Cruz
Long-Term
Variations of the Northeast
Pacific
The Monterey Bay National Marine
Sanctuary is located on the eastern edge
of the northeast Pacific (NEP), a region
that experiences large variations of the
atmosphere and ocean that can strongly
affect environmental conditions in the
Sanctuary. These NEP variations are part
of atmosphere-ocean fluctuations that
occur throughout the entire north Pacific.
Often, these fluctuations can be traced
back to disturbances that occurred in
southern and eastern Asia, the tropical
Pacific, or even more remote regions. The
best known of these long-term variations
are the normal seasonal changes in winds,
sea surface temperatures (SSTs),
precipitation, runoff, and other physical
factors. Seasonal variations in the NEP
are part of the worldwide seasonal cycle,
a cycle that is especially pronounced in
southern and eastern Asia and in the
western tropical Pacific.
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Figure
1: Sea surface temperature (SST)
anomalies for the Pacific Ocean,
1991-1997. Positive (shaded)
values indicate SSTs that are
warmer than average; negative
values indicate the opposite. The
average is for the 29-year
period, 1968-1996. Contour
interval is 0.2 degrees
C.
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These seasonal variations can vary
themselves, leading to what are called
climate anomalies, the best known of which
are El Niño and La Niña
events. The most recent of these are the
1997–1998 El Niño and the 1999
La Niña. Such events occur
primarily in the tropical Pacific but have
global impacts. During these events, a
number of environmental factors in the NEP
deviate from their seasonal norms. For
example, during El Niño events,
SSTs tend to be anomalously warm in a
broad swath extending along the coast of
western North America, from the Aleutians
to Baja California, while SSTs in the
central North Pacific are unusually cool.
A reverse pattern of SST anomalies tends
to occur during La Niña events.
El Niño and La Niña
events tend to last about a year and recur
about every two to seven years.
Ecologically important climate variations
also occur on much longer time scales. In
particular, the east Asian—North
Pacific region undergoes variations that
last on the order of ten to twenty years.
These variations, often referred to as
Pacific decadal oscillations, can have
major impacts on oceanic and atmospheric
conditions and, thereby, large impacts on
marine and terrestrial organisms. Figure 1
shows the average SST anomalies in 1991 --
1997, during the phase of one of these
decadal oscillations in which SSTs in the
NEP and much of the tropical Pacific are
unusually warm, while the central North
Pacific is unusually cool. This is similar
to the SST anomaly patterns seen during El
Niño events. During the opposite
phase, the SST anomalies tend to be the
reverse of those in Figure 1, and similar
to those during La Niña events.
There are strong links between decadal
variations and El Niño and La
Niña events, with a large number of
El Niño events occurring during the
phase of decadal events shown in Figure 1,
and a large number of La Niña
events during the opposite phase.
Scientists are studying these links and
the mechanisms by which a variety of
climate anomalies affect the NEP,
especially coastal regions such as the
Sanctuary.
There are similarities in the response
of coastal marine ecosystems to El
Niño and longer-term warming
because the anomalous physical conditions
associated with these phenomena are
similar (e.g., warmer SSTs, deeper mixed
layer, shifts in ocean currents). While
many of the unusual biological events in
1998 may be due to the 1997—1998 El
Niño, many others are related to
longer-term climate change trends,
compounded by El Niño's effects. An
improved ability to understand and predict
physical conditions and local
environmental responses to climate change
will increase our ability to anticipate
and mitigate changes to marine populations
in the Sanctuary.
--Tom Murphree
Naval Postgraduate School
--Frank Schwing
Pacific Fisheries Environmental
Laboratory
SWFSC/NMFS/NOAA
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