Fish and Shellfish Stocks: 2013
Information on the state of fish and shellfish stocks of commercial importance to the Scottish fleet, inclduing Total Allowable Catches (TACs) for each stock.
Brown Crab
Latin name : Cancer pagurus
Common names : Edible crab, Brown
Introduction
The brown crab fishery is economically a very important
fishery for Scotland with total landings in 2011 of around 11,900
tonnes and a value of £14.2 million. The fishery is long
established and landings, although variable, have increased
significantly over the last thirty years. Previously, most brown
crab was caught inshore in mixed species creel fisheries. From the
mid 1980s technological advances allowed the fishery to expand to
offshore areas to the west and north of Scotland, which nowadays
account for almost a third of total landings. Landings from the six
principal brown crab assessment units: the Hebrides, Sule, Papa,
South Minch, East Coast and Orkney, made up 85% of the total in
2011. The majority of crabs are landed in the third and fourth
quarters of the year and a large proportion are exported live to
markets in southern Europe.
Biology and life cycle
The brown crab is found all around the Scottish coast from
the shallow sub-littoral into offshore waters to depths exceeding
100 m. It inhabits rocky reefs, mixed coarse grounds and soft
sediments (muddy sand) particularly on the offshore grounds. Brown
crabs eat mainly benthic invertebrates, particularly bivalves,
small decapods and barnacles; although their capture in baited
traps indicates that they will also scavenge for food. In common
with other crustaceans, brown crab grow by casting (moulting) their
shell and then hardening a new larger shell. Growth rate varies
between areas, and animals will typically reach minimum landing
size, (140 mm carapace width
CW) at four to six years
old. Small animals may moult several times in a year, but at larger
sizes growth slows down and the inter-moult period can be as long
as four years. Female brown crabs in Scottish waters typically
mature between 130-150 mm
CW. During courtship the
mature female is guarded by a male. Mating takes place post moult
while the shell is still soft. Females produce up to three million
eggs. Fertilised eggs are carried under the female's "tail" for up
to nine months, over the winter, until they hatch. The larvae are
pelagic and drift with water movements until they settle to the
seabed as miniature adults (about 2.5 mm in size) in summer or
autumn depending on latitude and water temperature. Juvenile crabs
are more commonly found in shallow inshore waters.
Adult crabs, especially females, can undertake extensive seasonal migrations (100s km), behaviour thought to be associated with reproduction. Migration of adults and the dispersal of larvae will both influence how connected stocks are. The structure of brown crab populations around Scotland is poorly understood.
Landings (Tonnes) of Brown Crab into Scotland by Scottish Vessels, 1974 to 2010.
Management advice
The brown crab fishery is not subject to
EU
TAC regulations or
national quotas although there are
EU measures in place to
restrict the fishing effort (kW days) of all vessels > 15 m
(including creel boats) in
ICES
Subarea VI. In Scotland, vessels landing brown crabs are required
to hold a licence with a shellfish entitlement. Vessels without
this entitlement are only allowed to land limited amounts (25 crabs
per day). The main regulatory mechanism is a minimum landing size
of 140 mm
CW to the north of 56 oN
and 130 mm
CW to the south of 56 oN
(except for the Firth of Forth).
Assessment
Age determination is generally not possible for animals
which moult and application of age-structured assessment methods to
crustacean stocks is problematic. Length Cohort Analysis (
LCA) is the
method used for assessing brown crab stocks. It uses official
landings and length frequency data collected as part of the Marine
Scotland Science market sampling programme.
LCA results are
calculated in terms of yield-per-recruit and biomass-per-recruit
relative to changes in fishing mortality, providing a framework for
evaluation of management measures. Assuming a direct relationship
between fishing mortality and effort, generally, lower levels of
fishing effort will result in an increase in stock size and a
reduction in landings. A higher level of fishing effort will reduce
total stock biomass but landings may also fall, as animals are
caught before they have had time to grow to a size that would
contribute much weight to the yield (growth overfishing). In
between these lies
F
MAX, the fishing mortality rate that maximizes yield per
recruit. The changes that the
LCA predicts are
long term (equilibrium). The method does not provide any indication
of short-term stock dynamics or recruitment over-fishing.
Assessments are performed on a regional basis for males and females
separately.
State of the stocks
Results of assessments based on
LCAs for the
period 2006-2008 for nine of the twelve assessment units,
summarising estimates of fishing mortality in relation to the
reference point
F
MAX are shown on the map. There were insufficient
sampling data from the Mallaig, Ullapool and Papa areas to conduct
LCAs. Of the
assessed areas, the majority were growth overfished to some extent,
particularly male crabs. In the areas of major importance for brown
crab landings, fishing mortality was estimated to be significantly
above
F
MAX for both males and females in Clyde, South Minch and
South East whilst in the Hebrides and Sule, current fishing
mortality was approximately
F
MAX. In Shetland, Orkney, North Coast and East Coast,
the fishing mortality for females was close to
F
MAX while males were fished above
F
MAX. The stock assessment for brown crab in Scottish
waters will be updated in 2013.
Creel Fishery Assessment Areas and Scottish Brown Crab Landings (Tonnes) in 2010.
Management advice
Overall, assessments for the period 2006-2008 showed that
most brown crab assessment units in Scotland were fished close to
or above
F
MAX, which is above the optimum level to achieve the
maximum yield per recruit. In many of the assessment units, a
higher yield and biomass per recruit in the long term could
potentially be obtained by reducing the level of fishing mortality
(effort).
Creel Fishery Assessment Units And Estimated Fishing Mortality, 2006-2008.
Fishing mortality at or around
F
MAX.
Fishing mortality significantly above
F
MAX for either males or females
Fishing mortality significantly above
F
MAX for both males and females
Not assessed
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