The
Sanctuary is mandated to approach resource protection from a broad, ecosystem
based perspective. This requires consideration of a complex array of habitats,
species, and interconnected processes and their relationship to human
activities. Krill are a critical component of the marine ecosystem and
fundamental to the trophic structure of the marine life within the Sanctuary.
The two principal species of krill that exist within the MBNMS and throughout
the California current are Euphausia pacifica and Thysanoessa spinifera.
These species are preyed upon by almost all commercially important species
within Sanctuary waters including salmon, rockfish, squid, sardine, mackerel
and flatfish. Blue whales, humpbacks, and numerous seabirds including
sooty shearwaters, marbled murrelets, and common murres are dependent
on krill as forage. Reliable regional estimates of biomass and prey requirements
do not exist. However, it has been estimated that krill makes up between
15 and 60 percent of the diet of commercially significant fish in ecosystems
with comparable trophic structures. More...
Working
Group Participants: |
~Working
Group Contact~ |
Name |
Affiliation |
Email |
Phone |
Huff McGonigal |
MBNMS |
huff.mcgonigal@noaa.gov |
831-647-4254 |
~Sanctuary
Advisory Council Members (SAC) & Other
Stakeholders ~ |
Name |
Affiliation |
Natasha
Yankoffski |
Save
Our Shores |
|
|
Baldo
Marinovic |
UC
Santa Cruz |
|
|
Steve
Ralston |
National
Marine Fisheries Service |
|
|
Bill
Sydeman |
Point
Reyes Bird Observatory |
|
|
Mike
Osmond |
World
Wildlife Fund |
|
|
Don
Croll |
UC
Santa Cruz |
|
|
~MBNMS
Staff ~ |
Name |
Affiliation |
Email |
Phone |
Jennifer
Parkin |
MBNMS |
jennifer.parkin@noaa.gov |
831-647-4204 |
Working
Group Timeline: |
Start:
January, 2003 |
Date |
Time |
Location |
Documents |
January
16 |
2-5pm |
|
Meeting
1 Agenda (pdf 116K) |
TBA |
|
|
|
Complete:
March, 2003 |
Issue
Summary: Ecological
Role:
The Sanctuary is mandated to approach resource protection from a broad,
ecosystem based perspective. This requires consideration of a complex
array of habitats, species, and interconnected processes and their relationship
to human activities. Krill are a critical component of the marine ecosystem
and fundamental to the trophic structure of the marine life within the
Sanctuary. The two principal species of krill that exist within the MBNMS
and throughout the California current are Euphausia pacifica and Thysanoessa
spinifera. These species are preyed upon by almost all commercially important
species within Sanctuary waters including salmon, rockfish, squid, sardine,
mackerel and flatfish. Blue whales, humpbacks, and numerous seabirds including
sooty shearwaters, marbled murrelets, and common murres are dependent
on krill as forage. Reliable regional estimates of biomass and prey requirements
do not exist. However, it has been estimated that krill makes up between
15 and 60 percent of the diet of commercially significant fish in ecosystems
with comparable trophic structures.
Krill are currently
not harvested within the Sanctuary, however the potential exists for this
fishery to develop in the future due to an increasing need for aquaculture
feed. A krill fishery could not only severely impact the integrity of
the marine ecosystem but could adversely affect commercial and recreational
fisheries of all kinds as most target species are directly or indirectly
dependent on the resource. To address this issue, MBNMS will explore the
potential for the future harvest of krill, outline the current regulatory
framework, and recommend permanent restrictions in the Sanctuary.
Current
State and Federal Management:
California is the first state to ban fishing for krill in state waters.
The bill was introduced by Assemblywoman Virginia Strom-Martin, and was
aimed at "protecting the marine food web by stopping any krill fishery
before it could be started in the state." The Strom-Martin bill was
requested by the Pacific Coast Federation of Fishermen's Associations
(PCFFA) and conservation groups after a krill fishery was established
last year off British Columbia. A commercial harvest of krill off the
Canadian east coast has been implicated in the poor recovery of cod in
the region; the BC krill fishery is the first off the Pacific coast. PCFFA
and others were concerned that "fishing for this essential link in
the food chain would prevent the recovery of highly valuable and threatened
commercial fish." This bill prohibits the taking or landing of krill
of the genus Thysanoessa or the genus Euphausia for commercial purposes
until January 1, 2011. The bill would further provide that after January
1, 2011, this commercial taking or landing is prohibited unless permitted
under regulations adopted by the commission. There has been no federal
action considered prohibiting or limiting krill fishing in federal waters
by the regional councils, NMFS, or Congress.
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Description
of Potential Fishery in MBNMS:
There are a number of problems associated with the krill industry. Krill
have extremely powerful digestive enzymes that tend to spoil the catch
by breaking down the krill's body tissue soon after death. Krill shells
are also rich in fluoride so they have to be removed before the meat is
fit for human consumption. These processing problems all add to the cost
of production so that fisheries have failed to grow as fast as some had
initially predicted. Of the global catch, 43% is used for aquaculture
feed, 45% is for sport fishing bait, and 12% is for human consumption.
The only significant market for krill on the west coast exists in Oregon
and Washington were salmon farms use krill meat to give farm raised fish
their pinkish color. Most of the supply comes from the British Columbia
fishery. However, the federal waters in the sanctuary may soon be open
to fish farming, outside the reach of state governments. NMFS is currently
soliciting comments on their proposed Code of Conduct for Offshore Aquaculture,
which could place net pens in areas of the Sanctuary. This code was generated
pursuant to the Department of Commerce’s stated goal of a five hundred
percent increase in the nation’s aquaculture by the year 2025. These
net pen raised fish will likely demand krill as feed stock. This may further
increase the likelihood of a krill fishery developing within Sanctuary
waters.
A krill fishery within
the MBNMS would correspond to peak krill abundance and aggregation which
occurs in summer and early fall. Any trawling vessel could participate
and as other fisheries are closed down there will be an increasing number
of vessels searching for viable alternatives. However, there are several
key limitations that would serve to effectively exclude most local fishermen
from any emerging krill fishery. Perhaps most significantly the Strom-Martin
bill not only prohibits the taking of krill from state waters but it also
makes landing krill in any state port illegal. Therefore, a krill fishery
on the central coast would most likely consist of either large out of
state trawlers or an unlikely partnership between local vessels and out
of state motherships or net pen aquaculture facilities. Whoever the primary
participants may be, the biggest obstacle for a fishery within the MBNMS
would be the krill’s dispersion and aggregation patterns. While
harvestable krill swarms are to some extent spatially and temporally predictable,
a significant percentage of these aggregations occur within state waters.
The Antarctic Example:
Estimates of krill abundance, based on the amount of krill
freed up by the removal of the baleen whales from the Southern Ocean,
suggested a sustainable krill harvest of around 150 million tons a year,
1.5 times greater than the total number of fish and shellfish harvested
annually from the world's oceans. Commercial krill fishing began in the
early 1970s and has continued unabated ever since. The current catch is
a little under 300,000 tons a year which although down from the peak years
of the early 1980s, is still by far the largest catch in Antarctic waters.
Krill are caught by large freezer trawlers and processed on board into
products for human consumption, domestic animals (cattle, poultry, pigs
and mink) and farmed fish. Currently only six nations are actively involved
in the fishery: South Korea, Chile, Poland, Japan, Russia and the Ukraine,
with the last three accounting for 96 percent of the catch.
The prospect of a free-for-all fishery for Antarctic krill led to the
signing of a unique fishing treaty in 1981. This is the Convention on
the Conservation of Antarctic Marine Living Resources (CCAMLR), designed
to protect the Antarctic ecosystem from the consequences of a rapidly
expanding krill fishery. CCAMLR set a limit of 1.5 million tons on the
catch of krill in the South Atlantic (where almost all of the krill has
been caught recently) and a limit of 390,000 tons for the Indian Ocean.
These limits are much higher than the current catch levels but this is
a reflection of the huge size of the resource and of the pre-emptive approach
to management that CCAMLR was designed to take. Market demand has been
the limiting factor since the fishery began and catch has remained at
a fraction of what are considered highly precautionary limits.
While the overall
take of Antarctic krill is relatively low compared to its abundance, concerns
have been raised over fishing’s regional effects. CCAMLR has instituted
an ecosystem monitoring program to detect and record significant changes
in critical components of the ecosystem. It has been assumed that it is
possible to assess the effects of fishing on krill availability through
some index of predator performance. Predator data has therefore been incorporated
into the management scheme. Accordingly, a system to regularly record
selected life history parameters of key seabird and seal populations has
been in place since 1986. Despite calculations of krill yield that take
into account krill and predator requirements, CCAMLR has been aware of
the potential for local competition between predators and the krill fishery.
On a global or regional scale fishing mortality might remain within the
limits set by management and so provide sufficient escapement for predator
needs. However, on a local level mortality may be much greater and escapement
too low to support predators with restricted foraging ranges, or may cause
a shift in the behavior and distribution of more widely ranging species.
This concern is exacerbated by the timing of the krill fishery during
months where many species of breeding bird and seal predators are dependent
on the resource.
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Issues
of Concern for MBNMS:
The oceanographic and bathymetric features of the MBNMS makes it uniquely
susceptible to the adverse effects of krill fishing. The Monterey submarine
canyon provides krill with a distinctive habitat that contributes to their
abundance and degree of aggregation. This makes the waters within the
Sanctuary a critical feeding ground for countless forms of wildlife. These
include predators like the blue whale, dense concentrations of seabirds,
and commercially important fish species such as salmon and rockfish. The
canyon habitat provides opportunity for high nighttime surface feeding
due to its location downstream from an upwelling center, a refuge from
daytime predation as krill can migrate to depths in excess of 100m in
the canyon, and reduced swimming energy output during daytime schooling
at depth due to reduced canyon slope currents.
As the fishery would
correspond to the times of peak blue whale abundance it could be expected
that the fishery could interfere with both the feeding behavior of the
whales, the whale watching industry, and tourism in general. Bycatch is
also a concern in that even though krill swarms are densely aggregated,
a very fine mesh net is used which would indiscriminately catch larger
predators. A krill fishery could adversely impact commercial and recreational
fisheries of all kinds as all target species are directly or indirectly
dependent on the resource. Particularly susceptible are recovering rockfish
populations which would not only compete with a fishery for forage but
would also be caught as bycatch.
Strategies
to be Pursued in the Work Group:
The goal of the this working group is to identify and pursue strategies
that result in a permanent ban on harvesting krill anywhere within the
Sanctuary. The initial phase will focus on formulating an ecological report
that includes a species-specific list of organisms dependent on krill
within the MBNMS and an assessment of the potential for fishing within
the MBNMS and its ecological and economic impacts. The next phase would
involve approaching NMFS and CDFG with this information, with the objective
of having these agencies enact a permanent ban on krill harvesting. If
these agencies do not agree to establish such a prohibition, then the
Sanctuary would request their endorsement of a Sanctuary enacted ban.
Statutory
and Regulatory Context for Prohibiting Krill Harvesting:
The original Designation Document and Final EIS for the
MBNMS state that existing fisheries are not being regulated as part of
the initial MBNMS regime. However, the Final EIS also states that if regulatory
exemptions for fishing threatens Sanctuary resources, NOAA could undertake
rule changes consistent with Federal procedures. This would involve the
MBNMS consulting with CDFG, PFMC, and NMFS to determine an appropriate
course of action. The National Marine Sanctuary Program recognizes that
the primary regulatory authority over fisheries management resides with
these agencies, and as an initial step will encourage these agencies to
take the necessary measures. However, their associated management strategies
have generally been species specific approaches that are not always adequate
to safeguard marine ecosystems. The National Marine Sanctuary Act focuses
on protection of the ecosystem as a whole, a field in which the Sanctuary
Program has 30 years experience. Pursuing the restriction of krill harvesting
is therefore a legitimate means for the Sanctuary to both meet its mandate,
and a valuable opportunity to provide its ecosystem based perspective
to fisheries management.
Citations:
Nicol, S. & Endo, Y. Krill Fisheries: Development, Management
and Ecosystem Implications. Aquat. Living Resour. 12 (2) (1999) 105-120.
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