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The IUCN/SSC Shark Specialist Group

Shark News 12: November 1998

Commercial Landings of Sharks in South-Western England
Philip Vas and Teresa Thorpe
Commercial fisheries can have a significant impact upon the status of elasmobranch populations (Anon. 1997). Consequently it is important that any fisheries which land such species, either as a directed catch or as by-catch be strictly regulated. To regulate such fisheries, it is important to have not only the biological data on which to build a management plan, but also to maintain accurate species-specific records of landings for monitoring purposes (NMFS 1997). Unfortunately, in many parts of the world, this information is all too frequently lacking.

The north-east Atlantic, FAO Fishery Area 27, contributes roughly one-tenth of the world's total elasmobranch landings. One of the major elasmobranch fishing countries in this region is the United Kingdom, with average annual elasmobranch landings in excess of 25,000 tonnes/year, of which 67% are sharks (Bonfil 1994). The principal shark species taken in the UK are the spurdog Squalus acanthias, lesser spotted dogfish Scyliorhinus canicula and the bull huss Scyliorhinus stellaris. A number of other species are known to be taken, but official figures currently fail to differentiate between them, reporting them collectively under the heading of "dogfish". Furthermore, these figures do not include details of by-catches or discards and thus the true landings are likely to be somewhat higher.

In 1995 and 1996, recreational 'tag and release' shark fishing tournaments were held in the Cornish city of Penzance in the far west of England. During these tournaments, it was possible to conduct some observations on elasmobranch landings at the nearby fishing port of Newlyn, one of the most important and oldest ports in the UK. From these initial observations, it was evident that a wide range of elasmobranch species were taken and that different species were susceptible to different gears. These preliminary observations formed the basis for a more detailed and thorough survey of the fisheries at Newlyn conducted between 1997 and 1998.

The Port of Newlyn and its Fisheries

Newlyn is situated one mile west of Penzance and around seven miles east of Lands End. Consequently, it is the most western of the major ports in southern England and has ready access to both coastal and deeper, offshore waters of the Celtic Sea and Bay of Biscay.

The port is home to a large fleet of vessels ranging from 8 to 20 m in length and between 11 and 40 GRT in weight. The smaller vessels primarily work inshore grounds, usually either trawling or crabbing, with some occasionally fishing using longlines. These vessels operate on a daily basis, returning to port to land catches at night.

The larger vessels are either gill netters which target hake Merluccius merluccius and monkfish Lophius piscatorius, orbeam trawlers targeting a wide variety of flatfish and shellfish. One or two of the larger vessels occasionally fish using demersal longlines set for conger eels Conger conger. These larger vessels operate further offshore on extended trips of five to seven days, occasionally as far out as the Bay of Biscay. During the summer months, several of the vessels specifically switch to driftnets in order to work the profitable tuna grounds in the Bay of Biscay, with trips lasting around 15 days.

The port of Newlyn is also important in that it is a major fish market, receiving landings by road from as far afield as Newquay, Padstow and many of the smaller Cornish fishing villages for sale. Thus, observations of landings made here are truly representative of those for the whole south-west of England.

Detailed Shark Landings

All of the fisheries were observed to land sharks at one time or another during the study period. Those that landed sharks as a by-catch were considered to be 'incidental fisheries', while those targeting sharks were considered 'directed fisheries'.

A total of 11 different species of shark were recorded during both the preliminary observations and study period. Spurdog and catsharks (Scyliorhinus spp.) were the most abundant of all sharks taken and were present in landings throughout the year. Spurdog were usually taken in association with gill nets or bottom-set longlines and were considered a targeted species by some vessels. In contrast, the catsharks were taken closer inshore, usually by trawlers, and were considered a by-catch. Few catsharks were sold on the market for human consumption, with the majority (90% of those observed) being sold for bait to commercial crab fishermen. As the landings of spurdog and catshark are recorded by the Ministry of Agriculture, Food and Fisheries in the UK, little else will be said of their landings at this point.

Of the remaining species, blue shark Prionace glauca, tope Galeorhinus galeus and porbeagle Lamna nasus were the most abundant. Three species were represented by single specimens in the catches: two from tuna vessels, the bigeye thresher Alopias superciliosus and the kitefin shark Dalatias licha, while the starry smoothhound Mustelus asterias was taken in a gill net. One species, the sixgill shark Hexanchus griseus, was found to be surprisingly abundant in the landings, appearing regularly in gill net catches during the late summer and autumn.

Inshore Shark Landings



Blue Sharks

Of the larger sharks, the blue shark was the most commonly landed species, being taken on a variety of gears. Some were taken on bottom set longlines with some individuals taking the baits on the way down, others while the gear was set in 40- 50 m of water. A small proportion were caught in gill nets, set close to the bottom in 50-70 m of water. In both instances, these sharks were considered a by-catch.

The greatest proportion of blue shark (excluding tuna catches) were taken on lines set specifically for the sharks. Off the Cornish coast, it is common practice for fishermen to set lines attached to the dahns on the ends of thenets. These lines support 5-8 hooks, each baited with squid, and are designed to catch the blue sharks which are locally abundant between May and October. The blue sharks, although targeted with these hooks, do not form the principal catch of the fishery (which is the hake, taken in the nets), but are regarded by the fishermen as a bonus catch. Thus the sharks represent an 'accessory catch' to the net fishery. A total of 796 blue sharks were observed, 86% of which were females. Males ranged in length from 72 to 214 cm TL while females were from 88 to 251 cm TL. The average size of male sharks was always less than that of females.

Landings of sharks were made as early as June and, rather surprisingly, as late as December when a group of very small females 88-130 cm TL were caught. No blue sharks were caught in November, during a period of bad weather which restricted fishing. Sixty-seven percent of all blue sharks caught were taken in July and August 1997.

Porbeagle Sharks

Porbeagle sharks were landed on a regular basis, with all being landed as a by-catch from gill nets. None were taken on longlines. A total of 31 porbeagles were observed although a number of others were landed when no observer was at the market. Males and females occurred in roughly equal proportions (15 males, 16 females), though again males were slightly smaller (71-210cm TL) than females (101-244cm TL).

No evidence of seasonal abundance was apparent in the landings, with roughly equal numbers being taken in all months. Unlike the blue sharks which are gutted at sea and fetch a low price at the market ($0.50\lb), the porbeagles were highly prized, landed ungutted and sold for a much higher price (up to $2-3/lb) at auction. Many were exported to France after sale.

Tope Sharks

A total of 59 tope were landed during the study. All were taken in gill nets set in at least 60 m of water and were landed in an ungutted condition. While examining boxes in the market, several tope were found mixed in with spurdogs and so were not readily visible. Whether they had been recorded separately by the skippers or Ministry of Agriculture, Food and Fisheries (MAFF) officers is not known. The observers themselves may have missed some individuals as several landings of spurdog could not be checked. Consequently, it is likely that the figures for tope are an underestimate of those actually caught.

Of the tope observed, 59% were males ranging in length from 44 to 148 cm TL, while the females ranged from 81 to 157 cm TL, with an overall larger average size. There was a noticeable seasonal change in the sex ratio of the landings, with males becoming more abundant than females later in the year.

Six-gill Sharks

This species was rarely landed as it has no effective market value. Consequently, those taken as a by-catch in gill nets were usually discarded at sea. However, once the fishermen knew that the observers were interested, records were kept of numbers caught. During the study, a total of 123 records were provided. Of those that were returned to market (primarily for the observers interest), all were females ranging length from 78 to 161 cm TL. Catches of this species were more common in the western approaches and there was some suggestion of localised abundance, with skippers catching either isolated specimens or large hauls (up to 60 sharks).

Offshore Tuna Landings

During the months of July and August each year, up to five of the larger vessels (18 m in length), changed from gill nets to drift nets and prosecuted the tuna fishery in the Bay of Biscay (40-51°N, 10-15°W). Fishing for 8-10 days with nets of 2.5 km, these vessels took large by-catches of sharks, primarily blue shark. As these sharks were not the targeted species and took up valuable space in the hold, many were discarded. An on-board observer programme in 1995 indicated a discard rate for blue sharks in this fishery of 37% (Tregenza 1995).

A total of 588 blue sharks were landed from five tuna trips observed. Individual catches ranged from 96 to 180 sharks with the number varying depending on the quality of the tuna fishing. Generally more sharks were landed when tuna were scarce. Males ranged in length from 115 to 253 cm TL and accounted for 46% of the landings but were generally smaller than the females (105-222 cm TL). There was a slight variation in sex ratio of the catches between vessels, attributed to geographical differences in fishing locality.

Two other species of shark were regularly (i.e in more than one trip) taken as a by-catch, the porbeagle and shortfin mako Isurus oxyrinchus. Unlike the blue sharks, because of their high market value, 100% of these species were retained. In 1997, three makos were observed (two males and one female, 117-172 cm TL). Higher numbers are known to have occurred in previous years. For porbeagle shark, a total of 12 specimens were observed (seven males 88-217cm TL, five females 102-212 cm TL).

From these data it is clear that the blue shark represents the principal elasmobranch by-catch from this fishery. However, the British vessels represent only a relatively small proportion of the effort expended in the tuna fishery. Larger numbers of Spanish and French vessels also prosecute this fishery, previous studies indicating total by-catches of blue sharks in excess of 82,000 sharks in 1993.

The study has extended our knowledge of the regional biology of various shark species and has also thrown up several new problems. For example, why do commercial fisheries catch male blue sharks while recreational fisheries in the same waters do not? It has also shown that blue sharks may remain longer in British coastal waters than was thought. Previous studies suggested few if any sharks, remained as late as October. And finally, the study has shown that the six-gill shark is comparatively abundant and the area may provide an opportunity for an extended study of this species.

This study has demonstrated the relative susceptibility of sharks to fisheries in the NE Atlantic and given some indications of which areas need consideration. It is clear that drift net fisheries produce the highest mortality upon shark populations in this region. Monitoring of these fisheries will continue through 1998-1999, but additional studies will focus on technical methods of reducing the by-catch from such fisheries.

References

Anon. 1997. An Overview of the impacts on the biological status of sharks. Discussion Paper Pursuant to CITES Resolution CONF. 9.17.

Bonfil, R. 1994. Overview of world elasmobranch fisheries. FAO Fisheries Technical Paper 341.

National Marine Fisheries Service 1997. Managing the Nation's Bycatch: Priorities, Programs and actions for the National Marine Fisheries Service. US Dept of Commerce, Washington DC, March 20, 1997.

Tregenza, N. 1995. Cetacean bycatch in the UK tuna driftnet fishery in 1995. Contract Report to the Ministry of Agriculture, Fisheries and Food. P639.2/ 11,95. Science & Environment Section. House of Commons Library.

A more detailed account of this study is in preparation: Commercial and recreational landings of sharks in SW England, Aquatic Conservation.

Philip Vas, c/o 15 Woodlands Ave,
Peel Green, Eccles,
Manchester, M30 7GN, UK
Email: 106370.1164@compuserve.com