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Bathymetric distribution of macroinvertebrates in the Northeastern Levantine Sea and the Northeastern Aegean Sea based on bottom-trawl surveys Cover

Bathymetric distribution of macroinvertebrates in the Northeastern Levantine Sea and the Northeastern Aegean Sea based on bottom-trawl surveys

By: Onur Gönülal and  Cem Dalyan  
Open Access
|Dec 2017

Full Article

Introduction

The Mediterranean Sea is a peculiar basin regarding marine animal species composition. Many Indo-Pacific species with established populations in the Levantine Sea have passed via the Suez Canal and mixed with autochthonous species (Golani 2002; Galil, Zenetos 2002). Although the range of several species has expanded and reached the Northeastern Sea and the Sea of Marmara, the Turkish Levantine coast has been the most affected area. As a result of this phenomenon, the Eastern Mediterranean Sea is characterized by increasing faunal divergence (Golani, Ben-Tuvia 1995; Golani 2002). The introduction of alien species into the Eastern Mediterranean Sea is a dynamic and ongoing process and should be continuously monitored.

The Levantine Sea and the Northeastern Aegean Sea are two important areas of the Mediterranean Sea (Bianchi 2007). Most of the Aegean Sea has a narrow continental shelf and about 2000 small islands. This sea was considered as an area of low biological productivity (Kallianiotis et al. 2000). The southern Aegean Sea has unique topographic and bathymetric features with numerous islands, which is one of the main reasons of its zoogeographical distinction from the Northeastern Aegean Sea (Gertman et al. 2006).

Depth is generally the main gradient factor with respect to changes in the faunal composition of fauna, thus knowledge of the bathymetric distribution of benthic species is of great importance (Katsanevakis, Maravelias 2009).

There are no detailed studies on the bathymetric distribution of invertebrate species for any of the areas, i.e. the Northeastern Levantine Sea or the Northeastern Aegean Sea. Most studies conducted within this bathymetric zone have focused on fish species and stock assessments.

This study is intended to provide an overview of the bathymetric distribution and composition of invertebrate species occurring in the Northeastern Levantine Sea and the Northeastern Aegean Sea. This study is also the first comprehensive attempt to study the composition and distribution of invertebrates, ranging from shallow waters to the deepest zones of the East Mediterranean Sea.

Materials and methods

A total of 157 trawl hauls were carried out seasonally (from June to September 2014 as well as from January to April and from June to September 2015): 83 hauls (37 at a depth of 30-100 m; 24 at 100-200 m; 11 at 200-300 m; 11 at 300-410 m) in the Northeastern Aegean Sea and 74 hauls (36 at 30-100 m; 23 at 100-200 m; 9 at 200-300 m; 6 at 300-410 m) in the Northeastern Levantine Sea (Fig. 1). Samples were collected by commercial trawlers with 44 mm cod-end mesh size at depths of 30-410 m in both areas.The duration of each trawl ranged from 10 to 20 minutes and the average towing speed was about 2.5 knots, depending on the sea conditions.

Fieldwork included recording of the faunistic composition of the whole catch, sorted as fish (vertebrates) and invertebrates.

Macroinvertebrates in the collected samples were identified to the lowest possible taxonomic level by visual inspection on the desk. Next, all specimens of the identified species were counted to estimate diversity indices. The abundance of species was estimated for each depth range and each area. Percentages within bathymetric ranges and percentage occurrence in all samples were calculated for each invertebrate species. The similarity between areas was assessed using Bray-Curtis’ (1957) similarity index. The analysis was carried out using mean species abundance in depth stratum matrices in order to summarize information according to the sampling scheme (four depth strata: 30-100 m; 100-200 m; 200-300 m; 300-410 m) and to determine the relationship between species assemblages and distributions. Shannon-Weaver’s (1949) diversity index (H) was calculated to describe the community structure. Similarity percentage analysis (SIMPER) was also applied to determine the contribution of each invertebrate species to the similarity or dissimilarity in the community structure. Cluster analysis based on presence/absence data for the Northeastern Levantine Sea and the Northeastern Aegean Sea was performed to show the invertebrate assemblage composition. Data analysis was carried out using the PRIMER software (Clarke, Warwick 2001).

Figure 1

Sampling areas

Results

A total of 149 invertebrate species, including 6 pelagic ones, were collected from the Northeastern Levantine Sea and the Northeastern Aegean Sea (Table 1). Ninety five species were found in the Northeastern Aegean Sea and 100 species were found in the Northeastern Levantine Sea. Forty three species were common to the two studied areas.

Table 1

List of invertebrate species by depth zone

The Northeastern AegeanThe Northeastern Levantine
Phylum/SpeciesDepth Stratum (m)Phylum/SpeciesDepth Stratum (m)
30-100100-200200-300300-41030-100100-200200-300300-410
PORIFERA
Aplysina aerophoba (Nardo, 1833)xPorifera spp.xx
Porifera spp.xx
CNIDARIA
Alcyonium sp.xAlcyonium sp.xxx
Caryophyllia sp.xAlicia mirabilis Johnson, 1861xx
Pennatula phosphorea Linnaeus, 1758xx(1)Funiculina quadrangularis (Pallas, 1766)x
(2)Lytocarpiamyriophyllum (Linnaeus, 1758)xxx
Phyllorhiza punctata von Lendenfeld, 1884pelagic
Pennatula phosphorea Linnaeus, 1758xx
BRYOZOA
Bryozoa spp.xBryozoa spp.x
BRANCHIPODA
(3)Gryphus vitreus (Born, 1778)xxx
ANNELIDA
(4)Hermodice carunculata (Pallas, 1766)xHermodice carunculata (Pallas, 1766)xx
Pontobdella muricata (Linnaeus, 1758)x(5)Pontobdella muricata (Linnaeus, 1758)x
MOLLUSCA
Acanthocardia sp.xAbra sp.x
Aequipecten opercularis (Linnaeus, 1758)xAcanthocardia sp.x
Calyptraea chinensis (Linnaeus, 1758)xAporrhais pespelecani (Linnaeus, 1758)x
Diodora sp.xArgonauta argo Linnaeus, 1758pelagic
Cymbulia peronii Blainville, 1818pelagicBolinus brandaris (Linnaeus, 1758)xx
Eledone cirrhosa (Lamarck, 1798)xxx(6)Conomurex persicus (Swainson, 1821)xx
Euspira fusca (Blainville, 1825)xCypraeidae sp.x
Galeodeaechinophora (Linnaeus, 1758)x(7)Diodora ruppellii (G. B. Sowerby I, 1835)x
Illex coindetii (Vérany, 1839)xxxxEledone cirrhosa (Lamarck, 1798)xx
Loligo vulgaris Lamarck, 1798xxEnsis ensis (Linnaeus, 1758)x
Nudibranchia spp.xIllex coindetii (Vérany, 1839)xxxx
Octopus salutii Vérany, 1836xLoligo vulgaris Lamarck, 1798xxx
Octopus vulgaris Cuvier, 1797xxMuricidae sp.x
Pleurobranchus testudinarius Cantraine, 1835xxNaticarius stercusmuscarum (Gmelin, 1791)xx
Pseudamussium clavatum (Poli, 1795)xNudibranchia spp.xx
Rossia macrosoma (Delle Chiaje, 1830)xxxCallistoctopus macropus (Risso, 1826)x
Sepia elegans Blainville, 1827xxOctopus vulgaris Cuvier, 1797xxx
Sepia officinalis Linnaeus, 1758xxSemicassis granulata (Born, 1778)x
Sepia orbignyana Férussac [in d’Orbigny], 1826xxPleurobranchaea meckeli (Blainville, 1825)x
Solen marginatus Pulteney, 1799xPlocamopherus tilesii Bergh, 1877x
Todarodes sagittatus (Lamarck, 1798)xRondeletiola minor (Naef, 1912)xxxx
Rossia macrosoma (Delle Chiaje, 1830)xx
Sepia elegans Blainville, 1827xxx
Sepia officinalis Linnaeus, 1758xxx
Sepia orbignyana Férussac [in d’Orbigny], 1826xx
Tonna galea (Linnaeus, 1758)x
Tylodina perversa (Gmelin, 1791)x
ARTHROPODA
Aegeon lacazei (Gourret, 1887)xxxAegaeon cataphractusx
Alpheus sp.xAegeon lacazei (Gourret, 1887)xxx
Calappa granulata (Linnaeus, 1758)xAnapagurus spp.x
Chlorotocus crassicornis (A. Costa, 1871)x(8)Atergatis roseus (Rüppell, 1830)x
Galathea bolivari Zariquiey Álvarez, 1950xx(9)Carupa tenuipes Dana, 1852xx
Inachus communissimus Rizza, 1839x(10)Charybdis longicollis Leene, 1938xx
Inachus dorsettensis (Pennant, 1777)x(11)Clorida albolitura Ahyong & Naiyanetr, 2000xx
Latreillia elegans Roux, 1830xx(12)Erugosquilla massavensis (Kossmann, 1880)xx
Liocarcinus depurator (Linnaeus, 1758)xxEthusa mascarone (Herbst, 1785)xx
Macropodia linaresi Forest & Zariquiey-Álvarez, 1964xxGoneplax rhomboides (Linnaeus, 1758)x
Macropodia longirostris (Fabricius, 1775)xHomola barbata (Fabricius, 1793)xx
Macropodia rostrata (Linnaeus, 1761)xInachus communissimus Rizza, 1839xx
Maja squinado (Herbst, 1788)x(13)Ixa monodi Holthuis & Gottlieb, 1956xx
Medorippe lanata (Linnaeus, 1767)xxLatreillia elegans Roux, 1830xxx
Munida sp.xxxLiocarcinus depurator (Linnaeus, 1758)x
Nephrops norvegicus (Linnaeus, 1758)xMacropodia linaresi Forest & Zariquiey-Álvarez, 1964xx
Paguristes eremita (Linnaeus, 1767)xMacropodia longipes (A. Milne-Edwards & Bouvier, 1899)xx
Pagurus prideaux Leach, 1815xxMacropodia longirostris (Fabricius, 1775)xx
Pandalina brevirostris (Rathke, 1843)xMacropodia rostrata (Linnaeus, 1761)x
Pasiphaea sivado (Risso, 1816)xMacropodia tenuirostris (Leach, 1814)x
Parapenaeus longirostris (Lucas, 1846)xxxxMedorippe lanata (Linnaeus, 1767)xxx
Phrosina semilunata Risso, 1822pelagicMetapenaeus monoceros (Fabricius, 1798)xx
Pilumnus hirtellus (Linnaeus, 1761)xMonodaeus couchii (Couch, 1851)xx
Pilumnus minutus De Haan, 1835xMunida sp.x
Pisa armata (Latreille, 1803)xPagurus chevreuxi (Bouvier, 1896)x
Pisa nodipes Leach, 1815xPagurus prideaux Leach, 1815xx
Plesionika edwardsii (Brandt, 1851)xxxxParapenaeus longirostris (Lucas, 1846)xxxx
Plesionika martia (A. Milne-Edwards, 1883)xPasiphaea sivado (Risso, 1816)x
Polycheles typhlops Heller, 1862xxxPenaeus kerathurus (Forskål, 1775)x
Scalpellum scalpellum (Linnaeus, 1767)xx(14)Penaeus japonicus Spence Bate, 1888x
Solenocera membranacea (Risso, 1816)x(15)Penaeussemisulcatus De Haan, 1844xx
Squilla mantis (Linnaeus, 1758)xxPisa armata (Latreille, 1803)xx
Xantho poressa (Olivi, 1792)xPisa nodipes Leach, 1815x
Plesionika edwardsii (Brandt, 1851)xxxx
Pilumnus hirtellus (Linnaeus, 1761)x
Polycheles typhlops Heller, 1862x
Processa canaliculata Leach, 1815x
(16)Scalpellum scalpellum (Linnaeus, 1767)x
Sicyonia carinata (Brünnich, 1768)xx
(17)Sicyonia lancifer (Olivier, 1811)x
Solenocera membranacea (Risso, 1816)x
Spinolambrus macrochelos (Herbst, 1790)x
Squilla mantis (Linnaeus, 1758)x
Synalpheus africanus Crosnier & Forest, 1965x
(18)Thalamita poissonii (Audouin, 1826)x
ECHINODERMATA
Anseropodaplacenta (Pennant, 1777)xAntedon mediterranea (Lamarck, 1816)xxx
Antedon mediterranea (Lamarck, 1816)xxAstropecten irregularis (Pennant, 1777)xx
Astropecten aranciacus (Linnaeus, 1758)xAstropecten sp.xxx
Astropecten irregularis (Linnaeus, 1758)xBrissopsis lyrifera (Forbes, 1841)xx
Astropecten jonstoni (Delle Chiaje, 1827)xCentrostephanus longispinus (Philippi, 1845)x
Astropecten sp.xxxCidaris cidaris (Linnaeus, 1758)xx
Astropecten spinulosus (Philippi, 1837)xEchinaster sepositus (Retzius, 1783)x
Brissopsis lyrifera (Forbes, 1841)xEchinus melo Lamarck, 1816x
Centrostephanus longispinus (Philippi, 1845)x(19)Hymenodiscus coronata (Sars G.O., 1872)x
Cidaris cidaris (Linnaeus, 1758)xxxxLuidia sarsii Düben & Koren in Düben, 1845xx
Echinaster sepositus (Retzius, 1783)xxMarthasterias glacialis (Linnaeus, 1758)x
Echinus melo Lamarck, 1816xOphiothrix fragilis (Abildgaard in O.F. Müller, 1789)x
Genocidaris maculata A. Agassiz, 1869xParacentrotus lividus (Lamarck, 1816)x
Holothuria sp.x
Luidia ciliaris (Philippi, 1837)x
Luidia sarsii Düben & Koren in Düben, 1845xx
Marthasterias glacialis (Linnaeus, 1758)xx
Ophiacantha setosa (Bruzelius, 1805)x
Ophiactis kroeyeri Lütken, 1856x
Ophiothrix fragilis (Abildgaard in O.F. Müller, 1789)x
Ophiura ophiura (Linnaeus, 1758)xx
Parastichopus regalis (Cuvier, 1817)xxx
Peltaster placenta (Müller & Troschel, 1842)x
Ova canaliferus (Lamarck, 1816)x
Sphaerechinus granularis (Lamarck, 1816)xx
CHORDATA (SUBPHYLUM) TUNICATA
Aplidium sp.xAscidiidae spp.xx
Ascidiidae spp.xCiona intestinalis (Linnaeus, 1767)x
Ciona intestinalis (Linnaeus, 1767)xxxMolgula manhattensis (De Kay, 1843)x
Halocynthia papillosa (Linnaeus, 1767)xx(20)Pyrosoma atlanticum Péron, 1804pelagic
Polyclinella (cf) azemai Harant, 1930x
Phallusia mammillata (Cuvier, 1815)xx
Thalia democratica (Forskål, 1775)pelagic

While six species were reported for the first time from the Turkish Levantine coast [Funiculina quadrangularis (Pallas, 1766), Gryphus vitreus (Born, 1778), Hymenodiscus coronata (Sars G.O., 1872), Pontobdella muricata (Linnaeus, 1758), Lytocarpia myriophyllum (Linnaeus, 1758) and Scalpellum scalpellum (Linnaeus, 1767)], only one species – Hermodice carunculata (Pallas, 1766) – was reported for the first time from the Aegean Sea coast of Turkey. Twelve alien species were encountered in the Northeastern Levantine Sea and no alien species were found in the Northeastern Aegean Sea during the study period (Table 1).

Pyrosoma atlanticum was recorded for the first time on the Turkish coast (Fig. 2). Although the species had been considered absent in the Eastern Mediterranean (Furnestin 1979; Por, Dimentman 1989), it was recorded there during mesopelagic surveys (Godeaux 1990). Later, Galil & Goren (1994) caught three colonies of P. atlanticum below 1400 m in the Southern Levantine Sea. It was also collected in small numbers at The Northeast of Cyprus (Weikert, Godeaux 2008).

Figure 2

Pyrosoma atlanticum

In the Northeastern Aegean Sea, the Shannon-Weaver diversity index (H’) showed significant differences between the depth ranges, and its values ranged from 1.002 to 4.16. The index increased with depth between 30 and 200 m, and decreased at 410 m. In the Northeastern Levantine Sea, the highest index value was calculated for a depth ranging from 30 to 100 m and the minimum index value of 1.331 was determined for a depth of 200-300 m (Table 2).

Table 2

Result of SIMPER analysis

Depth (m)SNdJ′H′1-Lambda′
The Northeastern Aegean Sea
30-100465867.0610.70023.8680.8892
100-2006311740.7720.69594,160.9016
200-3003733464.4360.42742.2260.6325
300-4104666855.1090.18141.0020.238
The Northeastern Levantine Sea
30-100366735.3750.59013.0510.7643
100-2006427517.9550.39882.3930.559
200-3005675036.1640.22921.3310.3411
300-4104743365.4930.36512.0280.5724

SIMPER analysis was applied to compare the Northeastern Aegean Sea and the Northeastern Levantine Sea. The result revealed clear differences between the two surveyed areas except for the 300-410 m depth range (Fig. 3). The average similarity for this depth range is 52.12%. Parapenaeus longirostris contributed 47.17% to the total similarity, and was followed by Plesionika edwardsii and Illex coindetii with 15.34% and 11.02%, respectively. P. longirostris and I. coindetii are also the most contributing species to the total similarity at the other depth ranges (Table 3).

Figure 3

Cluster analysis based on presence/absence data from samples collected in the Northeastern Levantine Sea and the Northeastern Aegean Sea

Table 3

Results of the SIMPER routine analyzing the similarity between depth ranges for macroinvertebrate fauna

Group 30-100 mGroup 100-200 m
Average similarity: 14.14Average similarity: 35.67
SpeciesAv.AbundAv.SimContrib%SpeciesAv.AbundAv.SimContrib%
Parapenaeus longirostris12.677.150.19Parapenaeus longirostris28.817.3520.62
Illex coindetii3.11.5510.95Illex coindetii10.985.0514.16
Porifera sp2.671.5510.95Sepia officinalis8.84.2111.8
Echinaster sepositus3.051.268.94
Luidia sarsii10.896.32
Group 200-300 mGroup 300-410 m
Average similarity: 45.55Average similarity: 52.12
SpeciesAv.AbundAv.SimContrib%SpeciesAv.AbundAv.SimContrib%
Parapenaeus longirostris60.3719.3942.58Parapenaeus longirostris64.324.5947.17
Illex coindetii22.136.9915.35Plesionika edwardsii19.15815.34
Sepia elegans11.194.319.47Illex coindetii12.395.7411.02
Sepia officinalis13.644.229.26

Discussion

Alien species have become very important components of benthic communities in the Levantine basin. Most of the studies carried out in the area included only new records of alien species, whereas data on the abundance and biomass of alien species in this area are comparatively scarce. In addition, trawl surveys focused mainly on fish species distribution, neglecting invertebrate species in both areas, i.e. the Northeastern Levantine and the Northeastern Aegean Sea. Nevertheless, this study has determined the diversity and bathymetric distribution of invertebrate species in both areas.

Albayrak (2010) reported that alien species in Iskenderun Bay accounted for 14.3% of the total number of bivalve species and 7.7% of the total number of bivalve individuals between 2 m and 30 m depth. However, Mollusca is the richest group (Çınar et al. 2011) among alien species in the Mediterranean. Although Bakir et al. (2012) reported 286 mollusk species, including 78 alien species from the Iskenderun Bay between 0 m and 100 m depth, no alien mollusk species have been recorded from the Northeastern Levantine Sea in this study. Depth seems the only possible factor causing this differentiation.

Özcan et al. (2005) conducted research surveys along the coast of the Iskenderun Bay at depths ranging from 4 to 50 m. Twenty different brachyuran crab species were identified. In addition, alien species: Charybdis longicollis, Portunus pelagicus and Callinectes sapidus, were most numerous and most often caught in the area. According to Can et al. (2004), Metapenaeus stebbingi had the highest average catch rate (76.9%) in the catch composition of penaeid shrimps from the Iskenderun Bay. The catch ratios for other shrimp species were as follows: Penaeus semisulcatus (18.20%), Metapenaeus monoceros (2.30%), Merlicertus kerathurus (1.50%), and Metapenaeus japonicus (1.20%). In addition, all shrimp species, except for M. kerathurus, are alien.

A bottom trawl haul conducted in Iskenderun Bay at a depth of 30 m revealed that 92% of the total number of specimens and 89% of the total biomass belonged to Lessepsian species. Rhopilema nomadica (58%), Charybdis longicollis (17%), Penaeus semisulcatus (5%) and Equulites klunzingeri (4%) accounted for the prevailing part of the total biomass (84%) in the area and C. longicollis was the most abundant species in the catch (63% of all specimens) (Çınar et al. 2011).

So far, the Northeastern Levant basin has been thoroughly surveyed only by Gücü, Bingel (1994). In that study, 31 invertebrate species and 134 fish species were collected at depths ranging from 8 to 78 m, while fish species accounted for 72.1% of the total biomass. In addition, the biomass of alien species decreased from 65% to 11% at a depth of 55-78 m.

Çınar et al. (2011) reported the highest number of alien species (330) from the Levantine coast of Turkey and 224 of them were invertebrate species. We reported only 12 alien species in the Northeastern Levantine Sea. This result clearly shows that Lessepsian invertebrate species are much less common in deep waters.

Another study of the catch composition and biodiversity of Mersin Bay shows only 23 invertebrate species collected (Gökçe et al. 2016). Çiçek et al. (2014) conducted a bottom trawl fishery along the coasts of Karataş in the 2002-2003 fishing season, where 90 fish species and 20 invertebrate species (5 crustacean species and 5 species of cephalopods) were collected.

Trawl researches in the Turkish seas were mainly focused on demersal fish assemblages. JICA (1993) conducted surveys in territorial waters of Turkey as well as in international waters at a depth of 20-500 m. There were 24 and 20 invertebrate species observed in the Northern Aegean Sea and the South Aegean Sea, respectively. Soykan et al. (2016) conducted studies in Sigacik Bay (Central Aegean Sea) using a commercial trawler, in which a total of 28 invertebrate species, 10 cephalopods, 13 crustaceans, 4 echinoderms and one porifera were captured. Kallianiotis et al. (2000) reported 26 invertebrate species off Heraklion Bay between 50 and 1000 m.

We identified more invertebrate species than other studies for both areas, i.e. the Northeastern Aegean and Northeastern Levantine Sea. The differences in the results were due to the fact that our study was focused on invertebrates species.

The result of SIMPER showed clear differences in the invertebrate species composition between the Northeastern Aegean Sea and the Northeastern Levantine Sea (Fig. 3). The average similarity between the Northeastern Levantine Sea and the Northeastern Aegean Sea is 52.12% for a depth of 300-410 m. P. longirostris, P. edwardsii and I. coindetii contributed 73.5% to the total similarity at this depth range. Similarities of the other depth ranges are below 50%. Lessepsian species are mostly distributed in waters below 70 m due to low temperate (Galil, Zenetos 2002). Because the coast of the Levantine Sea is under the influence of Lessepsian migration, the similarity between the two surveyed areas is very low, especially below 200 m.

This study is the first attempt to determine the invertebrate distributions, ranging from shallow waters to the deepest zones of the Northeastern Levantine Sea and the Northeastern Aegean Sea. The results show the differences in the bathymetric distribution and composition of invertebrate species occurring in the Northeastern Levantine Sea and the Northeastern Aegean Sea.

New records for the Turkish Levantine coast

New records for the Turkish Levantine coast

New records for the Turkish Levantine coast

New records for the Turkish Aegean coast

New records for the Turkish Levantine coast

Alien species

Alien species

Alien species

Alien species

Alien species

Alien species

Alien species

Alien species

Alien species

Alien species

New records for the Turkish Levantine coast

Alien species

Alien species

New records for the Turkish Levantine coast

New records for the Turkish seas

DOI: https://doi.org/10.1515/ohs-2017-0040 | Journal eISSN: 1897-3191 | Journal ISSN: 1730-413X
Language: English
Page range: 405 - 413
Submitted on: Apr 28, 2017
Accepted on: Jul 10, 2017
Published on: Dec 12, 2017
Published by: University of Gdańsk
In partnership with: Paradigm Publishing Services
Publication frequency: 4 issues per year

© 2017 Onur Gönülal, Cem Dalyan, published by University of Gdańsk
This work is licensed under the Creative Commons Attribution-NonCommercial-NoDerivatives 4.0 License.