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Norway lobster - West of Scotland (North Minch, South Minch, Clyde)
Marine Resource  Fact Sheet
ICES Advice 2012
Norway lobster - West of Scotland (North Minch, South Minch, Clyde)
Fact Sheet Citation  
Nephrops in Division VIa
Owned byInternational Council for the Exploration of the Sea (ICES) – More
Related observationsLocate in inventorydisplay tree map
 
Species:
FAO Names: en - Norway lobster, fr - Langoustine, es - Cigala
Geographic extent of Norway lobster - West of Scotland (North Minch, South Minch, Clyde)
Main Descriptors
Considered a single stock: Yes        Spatial Scale: Sub-Regional
Management unit: Yes        Reference year: 2012
 
 
Biological State and Trend
State & Trend Descriptors
PartnerFIRMS
Exploitation rateUndefinedUncertain/Not assessed
Abundance levelUndefinedUncertain/Not assessed
Habitat and Biology
Depth zone: Shelf (50 m - 200 m).   Vertical distribution: Demersal/Benthic.  


Nephrops is limited to a muddy habitat and requires sediment with a silt and clay content of between 10% and 100% to excavate its burrows. This means that the distribution of suitable sediment defines the species distribution. Adult Nephrops only undertake very small-scale movements (a few 100 m), but larval transfer may occur between separate mud patches in some areas. Catches typically consist of a smaller proportion of females than males, due to the lower burrow emergence (resulting in lower catchability) of females during the egg bearing. It is likely that maximum stock size and fishery potential is constrained by the available space since the species competes for space and there are upper limits on density.

Environmental influence on the stock

Temperature and hydrographic factors are critical to recruitment success in Nephrops, particularly during the larval phase. Different environmental factors such as sediment type and hydrography result in very different population structure, productivity, and vulnerability to fishing.

Effects of the fisheries on the ecosystem

There is a bycatch of other species in the Nephrops fisheries in Division VIa. This bycatch reflects the species associated with muddy sediments. Estimates of discards of whiting and haddock are high in Division VIa. Bycatches of cod are low and the Scottish Conservation Credits Scheme is in place to minimize cod catches. The use of creels for Nephrops fishing has increased in inshore areas in the Division VIa FUs. Discards and bycatch in the creel fisheries are considered to be low. The high mud content and soft nature of Nephrops grounds means that trawling readily marks the seabed, with trawl marks remaining visible for some time. Burrowing fauna can be seen re-emerging from freshly trawled grounds, implying that there is some resilience to trawling.
Geographical Distribution
Jurisdictional distribution: Shared between nations

Water Area Overview
Spatial Scale: Sub-Regional


Ecoregion: Celtic Sea.
Geo References
Resource Structure
Considered a single stock: Yes
Assessment
 
Scientific Advice

A summary of the advice per area can be found in Table 5.4.33.1.

To protect the Nephrops stocks in this management area, management should be implemented at the functional unit level.

There is no information available on the trends in the stock or exploitation status for the rectangles outside the FUs (‘other rectangles’) for which ICES provides advice. ICES advises that the catches in the other rectangles should not increase.
Overall Assessment Results
Figure 5.4.33.1 Nephrops Functional Units in Subarea IV and Division VIIa.
Assessment Model

Scientific basis


The assessment and advice for Nephrops stocks in Division VIa is primarily based on abundance estimates from underwater TV (UWTV) surveys together with fishery landings data and estimates of quantities of discards. Additional indicators of changes in stocks are derived from trends in length compositions and sex ratio in the catches.

Catch options tables for 2013 are derived for a range of FMSY and other options by applying the appropriate harvest ratios to the population numbers estimate from the most recent UWTV survey. This assumes that population numbers remain stable in the interim year. Landings are derived from the resultant total catch numbers after multiplying by the recent average of proportion retained and the mean weight in the landings.

Uncertainties in assessment and forecast

There is a gap of 18 months between the survey and the start of the year for which the assessment is used to set management levels. It is assumed that the stock is in equilibrium during this period (i.e. recruitment and growth balance mortality) although this is rarely the case. The effect of this on the accuracy of the catch forecast has not been investigated. The calculations of MSY proxies are all based on yield-per-recruit analyses from a length-based age-structured population model. These analyses utilize average length–frequency data taken over a 3-year period and therefore assume that the stock is in equilibrium. However, it is unlikely that the Nephrops stocks to which the approach has been applied are actually in equilibrium due to variable recruitment. MSY proxy estimates may vary in time due to changes in selection pattern.
Management
Management unit: Yes

Management Advice


Table 5.4.33.1 Nephrops in Subarea VIa. Summary of ICES advice by functional unit plus other rectangles.
Year Predicted landings corresponding to ICES advice

Agreed

TAC 1)

ICES

landings

 

North Minch

(FU11)

South

Minch

(FU12)

Firth of Clyde

(FU13)

Sound of Jura

(FU13)

Other

rectangles

Total advice    
1992           ~11.4 12.0 10.8
1993           ~11.3 12.0 11.3
1994           11.3 12.6 11.1
1995           11.3 12.6 12.8
1996           11.3 12.6 11.2
1997           11.3 12.6 11.2
1998           11.3 12.6 11.2
1999           11.3 12.6 11.5
2000           11.3 12.6 11.0
2001           11.3 11.34 10.9
2002           11.3 11.34 10.5
2003           11.3 11.34 10.8
2004           11.3 11.3 10.4
2005           11.3 12.7 10.5
2006           -2) 17.7 13.7
2007 3.2 7.2 3.765   0.8 15.0 19.9 16.3
2008 3.2 7.2 3.765   0.8 15.0 19.9 15.2
2009 < 4.1 < 5.0 < 5.7   < 0.3 3) 18.4 12.7
2010 < 1.0 < 4.1 < 3.9   <0.25 3) 16.1 12.2
2011 < 3.1 < 4.0 < 4.1 < 0.5 < 0.25 3) 13.7 12.8
2012 < 3.2 < 5.5 < 4.2 < 0.9 4) 3) 14.1  
2013 < 4.2 < 5.8 < 5.6 < 0.8 4) 3)    

Weights in thousand tonnes.

1) Subarea VI and EC waters of Division Vb.

2) Effort should not be increased.

3) ICES advises that stocks should be managed by functional unit.

4) ICES advises that the catches in the other rectangles should not increase.
Source of information
 

The above excerpts are from the first two pages of the ICES advice, the supporting information to this advice can be read in full at the following reference:
ICES. Nephrops in Division VIa. Report of the ICES Advisory Committee, 2012. ICES Advice, June 2012. Click to openhttp://www.ices.dk/committe/acom/comwork/report/2012/2012/Neph-Via.pdf
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