Age structure and diel activity of pouting on the Poole Bay artificial reef

Predominantly (86·6%) juvenile ( 0·3 m s−1, the pouting congregated close to the reef units, remained low in the water column and maintained position. At current speeds <0·1 m s−1, the schools were more dispersed, further away from reef units and higher in the water column. This tidally-related behaviour is thought to be related to energy conservation during the daylight hours, when the pouting utilize the lee of reef units during strong tidal currents. Between 15 and 30 min after dusk the majority of pouting left the artificial reef, and returned 45–60 min before dawn. A brief mark-recapture programme, using 0- to 1-group pouting, confirmed that a proportion of the pouting tagged were present on the artificial reef up to 5 days after marking, suggesting that the site was being used to some extent as a home reef. The nocturnal foraging pattern may be related to the availability of prey species.

[1]  H. Wennhage,et al.  Diel movements of juvenile plaice Pleuronectes platessa in relation to predators, competitors, food availability and abiotic factors on a microtidal nursery ground , 1998 .

[2]  I. D. Tuck,et al.  Patch exploitation by small gadoids: evidence for an asymmetric tidal effect , 1996 .

[3]  C. Glass,et al.  Differences in diet and behaviour of sympatric saithe and pollack in a Scottish sea loch , 1994 .

[4]  C. Glass,et al.  A comparison of the movements of two species of gadoid in the vicinity of an underwater reef , 1994 .

[5]  A. Temming,et al.  Daily activity, feeding and rations in gobies and brown shrimp in the northern Wadden Sea , 1994 .

[6]  C. Glass,et al.  Diurnal patterns in the spatial relationships between saithe, Pollachius virens, schooling in the wild , 1993 .

[7]  K. Hostens,et al.  Growth, feeding, production and consumption in 0-group bib (Trisopterus luscus L.) and whiting (Merlangius merlangus L.) in a shallow coastal area of the south-west Netherlands , 1993 .

[8]  W. Seaman,et al.  1 – Artificial Habitat Practices in Aquatic Systems , 1991 .

[9]  A. Jensen,et al.  Fishery Enhancement Reef Building Exercise , 1990 .

[10]  P. Henderson,et al.  On the structure of the inshore fish community of England and Wales , 1989, Journal of the Marine Biological Association of the United Kingdom.

[11]  D. Kelley Food of bass in U.K. waters , 1987, Journal of the Marine Biological Association of the United Kingdom.

[12]  J. Robin,et al.  Preliminary Observations on the Feeding Activity of Fishes during Tidal and Diel Cycles in the Loire Estuary: The Bib Trisopterus luscus L. 1758 , 1986 .

[13]  M. W. Hardisty,et al.  Seasonal Changes in Movements, Abundance, Size Composition and Diversity of the Fish Fauna of the Severn Estuary , 1986, Journal of the Marine Biological Association of the United Kingdom.

[14]  I. Potter,et al.  Abundance, movements and size of gadoids (Teleostei) in the Severn Estuary , 1984, Journal of the Marine Biological Association of the United Kingdom.

[15]  J. J. Otero,et al.  Contribution of infauna and mussel-raft epifauna to demersal fish diets , 1984 .

[16]  R. Rosenberg,et al.  Food selection and consumption of the shrimp Crangon crangon in some shallow marine areas in western Sweden , 1984 .

[17]  M. Armstrong The predator-prey relationships of Irish Sea poor-cod (Trisopterus minutus L.), pouting (Trisopterus luscus L.) and cod (Gadus morhua L.) , 1982 .

[18]  W. V. D. Broek Dietary habits of fish populations in the lower Medway Estuary , 1978 .

[19]  P. Ehrlich,et al.  The behavior of heterotypic resting schools of juvenile grunts (Pomadasyidae) , 1977 .

[20]  E. Naylor,et al.  Emergence rhythms and tidal migrations in the brown shrimp Crangon crangon (L.) , 1975, Journal of the Marine Biological Association of the United Kingdom.

[21]  E. Hobson Predatory behavior of some shore fishes in the Gulf of California , 1968 .