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PLATE II: Karaburun, zmir 1. Sigmoilinita costata (Schlumberger). External view, 1A, 80.00 m. 2. Euthymonacha polita (Chapman). External view, 1C, 100.00 m. 3. Euthymonacha polita (Chapman). Detailed view of shell, Karaburun, 1C, 100.00 m, zmir. 4. Euthymonacha polita (Chapman). Detailed view of aperture and last chambers, 1C,100.00 m. 5. Peneroplis pertusus (Forskal). External view, 1A, 80.00 m. 6. Peneroplis pertusus (Forskal). External view, 1A, 80.00 m. 7. Peneroplis pertusus (Forskal). Unusual specimen, external view, 1A, 80.00 m. 8. Peneroplis planatus (Fichtel and Moll). External view, 1A, 90.00 m. 9. Peneroplis planatus (Fichtel and Moll). External view, 1A, 100.00 m. 10. Peneroplis planatus (Fichtel and Moll). External view, 1A, 100.00 m. 11. Peneroplis planatus (Fichtel and Moll). Unusual specimen, external view, 2B, 80.00 m. 12. Peneroplis planatus (Fichtel and Moll). Unusual specimen, external view, 2B, 80.00 m. 13. Peneroplis planatus (Fichtel and Moll). External view, 2B, 80.00 m. 14. Peneroplis planatus (Fichtel and Moll). Unusual specimen, external view, 2B, 80.00 m. 15. Peneroplis planatus (Fichtel and Moll). Unusual specimen, external view, 2B, 80.00 m. 16. Rosalina bradyi Cushman. External view, spiral side, 1A, 80.00 m. 17. Rosalina bradyi Cushman. External view, spiral side, 1A, 80.00 m.  

PLATE II: Karaburun, zmir 1. Sigmoilinita costata (Schlumberger). External view, 1A, 80.00 m. 2. Euthymonacha polita (Chapman). External view, 1C, 100.00 m. 3. Euthymonacha polita (Chapman). Detailed view of shell, Karaburun, 1C, 100.00 m, zmir. 4. Euthymonacha polita (Chapman). Detailed view of aperture and last chambers, 1C,100.00 m. 5. Peneroplis pertusus (Forskal). External view, 1A, 80.00 m. 6. Peneroplis pertusus (Forskal). External view, 1A, 80.00 m. 7. Peneroplis pertusus (Forskal). Unusual specimen, external view, 1A, 80.00 m. 8. Peneroplis planatus (Fichtel and Moll). External view, 1A, 90.00 m. 9. Peneroplis planatus (Fichtel and Moll). External view, 1A, 100.00 m. 10. Peneroplis planatus (Fichtel and Moll). External view, 1A, 100.00 m. 11. Peneroplis planatus (Fichtel and Moll). Unusual specimen, external view, 2B, 80.00 m. 12. Peneroplis planatus (Fichtel and Moll). Unusual specimen, external view, 2B, 80.00 m. 13. Peneroplis planatus (Fichtel and Moll). External view, 2B, 80.00 m. 14. Peneroplis planatus (Fichtel and Moll). Unusual specimen, external view, 2B, 80.00 m. 15. Peneroplis planatus (Fichtel and Moll). Unusual specimen, external view, 2B, 80.00 m. 16. Rosalina bradyi Cushman. External view, spiral side, 1A, 80.00 m. 17. Rosalina bradyi Cushman. External view, spiral side, 1A, 80.00 m.  

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The aim of this study is to investigate the meifaunal assemblages of the north coasts of Karaburun Peninsula and figure out the effects of mercury mine and other elements on these assemblages. Two mercury mines are found on the north of the peninsula, " Karareis " located on the northwest of Tuzla Cove and " Kalecik " on the southeast of Karaburun....

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... Methods of detecting marine pollution over time are the subjects of active research with an increasing global awareness about environmental problems. Numerous studies dealing with the relationship between foraminifera and pollution have considered trace metal as a significant variable acting on ecosystem with a notable influence on foraminiferal distribution (Barut et al. 2011;Barut et al. 2013;Bergin et al. 2006;Burone et al. 2006;Donnici et al. 2012;du Châtelet et al. 2011;Yalçın et al. 2008). ...
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The benthic foraminiferal community is an excellent bio-indicator of pollution in coastal and marginal marine settings. Their abundance, diversity and its relationship with environmental parameters, viz. grain size, organic carbon (Corg) and trace metals concentration, from the surface sediment layer of the southwestern shelf of the Bay of Bengal, have been used to understand the marine pollution in this study. A total of 32 surface sediment samples were collected at various water depths.The samples were analysed for grain size distribution, organic matter (OM), foraminiferal and trace metals studies. Statistical analyses such as correlation matrix, PCA (Principal Component Analysis) and cluster analysis show that the foraminiferal species composition is significantly influenced by the organic carbon (Corg), Co, Pb, Zn, Cr, and Ni concentrations. The dominance of stress-tolerant species, viz. Ammonia beccarii, Ammonia tepida, Nonion faba, Bulimina marginata, Bolivina robusta, Elphidium craticulatum and Elphidium advenum, as well as less species diversity, demonstrates the elevated Corg and trace metal pollution in the marine environment.
... In this assemblage, another noteworthy feature is abundance of benthic foraminifera especially Peneroplis tests displaying extreme morphological disorders. The recent sediments consist of light gray sands in the other studied areas, and a small number of partly colored or colorless benthic foraminifera are observed in the upper levels (Meriç et al., 2012a,b;Barut et al., 2013;Yümün et al., 2016). Ammonia compacta Hofker, A. parkinsoniana (d'Orbigny), Challengerella bradyi Billman, Hottinger and Oesterle, Elphidium complanatum (d'Orbigny) and E. crispum (Linn e) are the dominant species in this assemblage. ...
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In coastal parts of the study areas, heavy metals containing ground water flows along the faults and fractures and reaches at sea. In these contaminated waters, morphologically abnormal individuals of the affected meiofauna (benthic foraminifera, ostracod, mollusc) can be found. Three cores were taken from the seafloor in the four separate stations that are located in NW of Ayvalık village, around Alibey and Maden islands, and one core of each three core groups was studied in order to investigate the aforementioned morphological affects on the recent meiofauna, which have been inhibited in those contaminated waters. Lead, manganese, hematite and limonite deposits with small reserves were present in Alibey, Maden and Küçük (Small) Maden islands. Morphological changes and coloring were observed in tests of large number of Peneroplis, Lobatula, Ammonia and Elphidium samples collected from these areas. This observation vindicates impact of heavy metals onto the foraminifera assemblages. Heavy metals and other chemical and radioactive elements found in the surrounding country side have been naturally transported into the adjacent sea water during the past and present. The aim of this study is to figure out the effects of the chemical and radioactive elements, which were carried from the land on the meiofaunal (benthic foraminifera, ostracod and mollusc) assemblages.
... In this assemblage, another noteworthy feature is abundance of benthic foraminifera especially Peneroplis tests displaying extreme morphological disorders. The recent sediments consist of light gray sands in the other studied areas, and a small number of partly colored or colorless benthic foraminifera are observed in the upper levels (Meriç et al., 2012a,b;Barut et al., 2013;Yümün et al., 2016). Ammonia compacta Hofker, A. parkinsoniana (d'Orbigny), Challengerella bradyi Billman, Hottinger and Oesterle, Elphidium complanatum (d'Orbigny) and E. crispum (Linn e) are the dominant species in this assemblage. ...
... A total of 67 benthic foraminiferal species were documented in the Gulf of Izmir (western Turkey, eastern Aegean Sea) by Bergin et al. (2006) (2). The benthic foraminiferal diversity of Gulf of Izmir was also studied by Meriç et al. (2012a) and Barut et al. (2013). A very detailed investigation in the Gulf of Kalloni (Lesvos Island, Greece) (15) has been carried out by Debenay et al. (2005) who documented the presence of 147 benthic foraminiferal species. ...
... ; 2 Çeşme-Ilica Bay: Avşar and Meriç (2001), Bergin et al. (2006), Meriç et al. (2012a) and Barut et al. (2013); 3 Gokceada Island: Avşar and Ergin (2001), Avşar (2002), Meriç et al. (2001aMeriç et al. ( , 2004b, Yalçın et al. (2008) and Bassler-Veit et al. (2013); 4 Bozcaada Island: Avşar and Ergin (2001), Meriç et al. (2001aMeriç et al. ( , 2004b, Avşar (2002) and Yalçın et al. (2008); 5 Canakkale: Avşar and Ergin (2001), Avşar (2002) and Meriç et al. (2004b); 6 Gulf of Saros: Meriç et al. (2002bMeriç et al. ( , 2004a; 7 the Gulf of Edremit (Meriç et al. 2003(Meriç et al. , 2004b and Bassler-Veit et al. (2013); 8 central Crete: Drinia et al. (2004); 9 Kallithea Bay: Rasmussen (2005); 10 Saros Gulf: Meriç (1996), Meriç et al. (2001bMeriç et al. ( , 2004bMeriç et al. ( , 2005Meriç et al. ( , 2008b, Bassler-Veit et al. (2013); 11 near the island of Bozcaada: Meriç (1996), Meriç et al. (2001bMeriç et al. ( , 2004bMeriç et al. ( , 2005Meriç et al. ( , 2008b and Yalçın et al. (2008); 12 the Edremit Gulf: Meriç (1996) and Meriç et al. (2001bMeriç et al. ( , 2004bMeriç et al. ( , 2005Meriç et al. ( , 2008b; 13 Gökova Gulf: Meriç (1996) and Meriç et al. (2001bMeriç et al. ( , 2004bMeriç et al. ( , 2005Meriç et al. ( , 2008b; 14 Korthi and Kastro gulfs (Andros Island) Triantaphyllou et al. (2005Triantaphyllou et al. ( , 2009Triantaphyllou et al. ( , 2012 and Koukousioura et al. (2011); 15 Gulf of Kalloni (Lesvos Island, Greece): Debenay et al. (2005); 16 eastern Mitilini: by Yalçın et al. (2008); 17 Pamucak Cove: (Meriç et al. 2008c(Meriç et al. , 2009a(Meriç et al. , 2010a Meriç et al. (2004bMeriç et al. ( , 2012c; 38 Gulf of Kusadasi: Meriç et al. (2004b); 39 Gulluk Bay: Meriç et al. (2004b); 40 Gulf of Datca: Meriç et al. (2004b); 41 Marmaris Bay: Meriç et al. (2004b); 42 Illica Bay: Meriç et al. (2012b, c, d); 43 Camalti saltpan: Meriç et al. (2010b) Acknowledgments The research for this paper was partially made possible by the financial support from the PRIN 2010-2011 Ministero dell'Istruzione, dell'Università e della Ricerca (MIUR) (protocollo 2010RMTLYR). MAK thanks A.E. Aksu (Memorial University of Newfoundland) and the Captain and crew of the R/V "Piri Reis" for the opportunity to collect samples in Saros Bay. ...
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