Fróðskaparrit - 01.01.2005, Side 103

Fróðskaparrit - 01.01.2005, Side 103
MERKINGARROYNDIR VIÐ FØROYSKUM TOSKI 1952-1965 101 tion (a result of the migration pattern) of predators and preys is affecting the struc- ture and trophic importance of food webs (Steingrund and Gaard, 2005). In fisher- ies management, the migration pattern of commercial fish stocks is often used as a guideline when defining management ar- eas and management units, for example in the Baltic sea (Bagge and Steffensen, 1989). When protecting local fish popula- tions by defining areas closed for fishing (temporarily or permanently), it is crucial to have sufficient information about the migration pattern of the fish populations in question. There are several closed areas in Faroese waters (ICES, 2004). During its life the cod normally occu- pies several different areas and habitats. The larvae normally drift with the current from the spawning area to the nursery area for fry or juvenile fish. The juvenile fish migrate to the feeding grounds of adult fish when they are large enough. When sexually mature the adult cod migrate to the spawning area in spring and return to the feeding area after spawning. Some Canadian cod stocks occupy an overwin- tering area after the feeding season in summer/autumn and the spawning season m spring (Chouinard and Swain, 2005). Some populations of cod may not occupy a]l these three (or four) different areas, smce the nursery area sometimes is the more or less the same as the feeding area, as is the case in e.g. the Barents Sea (Ot- tersen and Sundby, 2005). The feeding area may also be more or less the same as the spawning area (e.g. close to the spawning area “Norðhavið” on the Faroe Plateau, unpubl.). Some cod stocks occu- py the same area regardless of individual size or season, e.g. on the Faroe Bank (unpubl.). The migration pattern of cod may not be constant versus time. Nursery areas may change as observed in the North Sea where the German Bight gradually lost its importance as nursery area for juvenile cod (age 1) from 1971-2002 (Blanchard et al., 2005). Spawning areas may also change as observed for West Greenland offshore cod (Wieland and Storr-Paulsen, 2005) and Arcto-Norwegian cod (Ottersen and Sundby, 2005). Feeding areas may also change as observed for West Green- land offshore cod in 1989-1991 that moved to East Greenland waters (Wieland and Storr-Paulsen, 2005). On a broad scale, the migration pattern seems to be more robust for north-east Atlantic cod stocks compared to the north-west Atlantic (Ro- bichaud and Rose, 2004). On a broad scale, the migration pat- tern of cod groups may be grouped into four: sedentary, accurate homers, inac- curate homers and dispersers (Robichaud and Rose, 2004). Sedentary groups had lower biomass than the others confirming that migration/dispersal begets abundance (Robichaud and Rose, 2004). The authors also hypothesised that the migration pat- tern was dependent on hydrographic con- ditions (“oceanographic regimes”). In the north-east Atlantic the environment is characterised by predictable oceano- graphic conditions leading to fairly stable migration patterns whereas the opposite is the case in the north-west Atlantic. Cod on
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