Abstract

Demersal fish fauna of the Sea of Marmara, Turkey was determined by bottom trawl surveys between March 2017-December 2018 at 34 stations with the monthly samplings. During the study, a total of 61 teleost and 12 cartilaginous fish species belonging to 42 families were sampled. The target, bycatch and discard rates of CPUE were determined as 13.40%, 69.64% and 16.95%, respectively. In total, 53.9% of the CPUE was stemmed from Trachurus trachurus. Mustelus mustelus, Raja clavata, Merluccius merluccius and Merlangius merlangius had the highest CPUE with a mean of 77.63, 71.86, 71.72 and 72.68 kg/km2, respectively. The highest biodiversity was observed in the southwestern part of the Marmara Sea. With increasing depth, the species number of the teleost fish decreased, whereas the species number of the cartilaginous fish increased. The mean CPUE values of the economical demersal fish species were lower in comparison to those reported from other regions in Turkey. Evidence suggests fish stocks with shallower distribution is under heavier threat against fishing pressure. Since commercial trawling is banned in the Sea of Marmara, beam trawl fishery can be considered as the major threat to demersal fish stocks in the region.

Highlights

  • Studying demersal fish composition, biomass and variations over spatial and temporal scales is a basic tool for fisheries management authorities

  • We investigated demersal fish stocks in the sea of Marmara

  • A total of 61 teleost and 12 cartilaginous fish species belonging to 42 families were sampled

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Summary

Introduction

Biomass and variations over spatial and temporal scales is a basic tool for fisheries management authorities. The damaging impacts of demersal trawls on demersal communities and habitats have been studied by many researchers (Auster and Langton, 1999; Bergman and van Santbrink, 2000; Hinz et al, 2009) Since deep water trawling is a common fishing method, well established scientific knowledge has been obtained from the seas of Turkey (Zengin et al, 2004; Knudsen et al, 2010; Ceylan et al, 2013; Yemişken et al, 2014; Keskin et al, 2014; Çiçek et al, 2014; Yıldız and Karakulak, 2017; Dalyan, 2020). Within the scope of this study, CPUE, species richness and spatial and temporal variations in fish compositons were determined

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