Kumsal Sedimanlarının Mikroplastik İçeriklerinin ve Sediman Tanelerinin Karakterizasyonu: Muğla Kıyılarından (GB Türkiye) Örnek Çalışma

Yıl 2023, Cilt: 14 Sayı: 1, 123 - 134, 23.03.2023

Murat Gul Ceren Küçükuysal Ahmed Masud

https://doi.org/10.24012/dumf.1212109

Öz

Günlük hayatta önemli bir yere sahip olan plastikler, fiziksel bozunmaya uğradıklarında kolaylıkla taşınarak göllere, akarsulara, denizlere, dağlara ve topraklara ulaşmakta ve kirletici olarak tüm doğal ekosistemlere zarar vermektedirler. Mikroplastiklerin özellikle kıyı alanlarında birikimini etkileyen en önemli unsurlardan ilki jeolojik süreçlerden olan karasal ve denizel sedimanların taşınımları ikincisi ise antropojenik etmenlerdir. Muğla kıyı sedimanlarında biriken mikroplastik miktarını belirlemek amacıyla Palamutbükü, Datça, Marmaris ve Akyaka sahil kumlarından alınan örnekler tane boyu bakımından karakterize edilmiş; düşük yoğunluklu mikroplastik ayırma yöntemleri kullanılmıştır. Plastik içeriği sırasıyla; Palamutbükü örneğinde 11 adet meso-makro plastik, 56 adet mikroplastik / 50 g, Datça örneğinde 13 adet meso-makro plastik, 33 adet mikroplastik / 50 g, Marmaris örneğinde 13 adet meso-makro plastik, 143 adet mikroplastik / 50 g, ve Akyaka örneğinde 4 adet meso-makro plastik, 59 adet mikroplastik / 50 g olarak belirlenmiştir. Orta kum boyunda, incelenen örnekler içinde en küçük ortalama tane boyutuna sahip Akyaka sahili örneği meso-makroplastik içeriği en düşük olandır. İnce çakıl ortalama tane boyuyla en kaba ortalama tane boyuna ve en yüksek çakıl yüzdesine sahip Datça örneği ise mikroplastik sayısı en düşük örnektir. Lif ve parça formunda plastik parçalarında Fourier Dönüşümlü Kızıl Ötesi Spektrometresi analizi gerçekleştirilmiştir. Mikroplastiklerin bileşimlerinde selülöz, polietilen ve polipropilen olduğu belirlenmiştir.

Anahtar Kelimeler

Mikroplastik, Kıyı Sedimanı, Tane Boyu, FTIR, Muğla

Characterization of Microplastic Contents and Sediment Grains of Beach Sediments: A Case Study from Muğla Coasts (SW Turkey)

Öz

Plastics, which have an important place in daily life, are easily transported when they are physically degraded, reach lakes, streams, seas, mountains, and soils and damage all natural ecosystems as pollutants. The first of the most important factors affecting the accumulation of microplastics, especially in coastal areas, is the transport of terrestrial and marine sediments through geological processes, and the second is anthropogenic factors. To determine the amount of microplastic accumulated in Muğla coastal sediments, samples taken from Palamutbükü, Datça, Marmaris and Akyaka beach sands were characterized in terms of grain size and low-density microplastic separation methods were used. Plastic contents were determined: 11 meso-macro plastics, 56 microplastics / 50 g in Palamutbükü sample, 13 meso-macro plastics, 33 microplastics / 50 g in Datça sample, 13 meso-macro plastics, 143 microplastics / 50 g in Marmaris sample, and 4 meso-macro plastics and 59 microplastics / 50 g in Akyaka sample, respectively. Akyaka sample of medium sand size, which has the smallest average grain size among the studied samples, has the lowest meso-macroplastic content. Datça sample, which has the coarsest average grain size with the average grain size of fine gravel and the highest percentage of gravel, is the sample with the lowest microplastic content. Fourier Transform Infrared Spectrometer analysis was performed on microplastics of fiber and fragment forms. It is determined that the compositions of microplastics are cellulose, polyethylene and polypropylene.

Anahtar Kelimeler

Microplastic, Coastal Sediment, Grain size, FTIR, Muğla

Kaynakça

• [1] European Commission, Directorate-General for Research and Innovation, “Environmental and health risks of microplastic pollution,” Publications Office of the European Union, Available: https://data.europa.eu/doi/10.2777/65378, 2019.
• [2] P. L. Corcoran, T. Norris, T. Ceccanese, M.J. Walzak, P. A. Helm, and C. H. Marvin, “Hidden plastics of Lake Ontario, Canada and their potential preservation in the sediment record,” Environmental Pollution, vol. 204, pp. 17-25, 2015.
• [3] S. Magni, L. Nigro, C. D. Torre, and A. Binelli, “Characterization of plastics and their ecotoxicological effects in the Lambro River (N. Italy),” Journal of Hazardous Materials, vol. 412, 125204, 2021.
• [4] D. Materić, R. Holzinger, and H. Niemann, “Nanoplastics and ultrafine microplastic in the Dutch Wadden Sea – The hidden plastics debris?” Science of The Total Environment, vol. 846, pp. 157371, 2022.
• [5] Y. Huo, F. A. Dijkstra, M. Possell, and B. Singh. “Chapter One - Plastics in soil environments: All things considered” Advances in Agronomy, vol. 175, pp. 1- 132, 2022.
• [6] N. F. A. Biber, A. Foggo, and R. C. Thompson, “Characterising the deterioration of different plastics in air and seawater,” Marine Pollution Bulletin, vol. 141, pp. 595-602, 2019.
• [7] V. Hidalgo-Ruz, L. Gutow, R. C. Thompson, and M. Thiel, “Microplastics in the marine environment: A review of the methods used for identification and quantification” Environmental Science and Technology, vol. 46, pp. 3060–3075, 2012.
• [8] A. Lusher, “Microplastics in the Marine Environment: Distribution, Interactions and Effects” in Marine Anthropogenic Litter. Springer, Cham. pp. 245-307, 2015.
• [9] R. C. Thompson, “Microplastics in the Marine Environment: Sources, Consequences and Solutions,” in Marine Anthropogenic Litter, Springer Open, pp. 185-200, 2015.
• [10] C. Alomar, F. Estarellas, S. Deudero, “Microplastics in the Mediterranean Sea: Deposition in coastal shallow sediments, spatial variation and preferential grain size,” Marine Environmental Research, vol. 115, pp. 1-10, 2016.
• [11] L. G. A. Barboza, A. D. Vethaak, B. R. B. O. Lavorante, A. K. Lundebye, and L. Guilhermino, “Marine microplastic debris: An emerging issue for food security, food safety and human health,” Marine Pollution Bulletin, vol. 133, pp. 336–348, 2018.
• [12] M. Eriksen, L. C. M. Lebreton, H. S. Carson, M. Thiel, C. J. Moore, J. C. Borerro, F. Galgani, P. G. Ryan, and J. Reisser, “Plastic pollution in the world's oceans: more than 5 trillion plastic pieces weighing over 250,000 tons afloat at sea,” PLoS One, vol. 9(12), e111913, 2014.
• [13] T. S. Galloway, “Micro- and Nano-plastics and Human Health,” in Marine Anthropogenic Litter. Springer, Cham., 2015, pp. 343-366.
• [14] A. A. Koelmans, E. Besseling, and W. J. Shim, “Nanoplastics in the Aquatic Environment. Critical Review” in Marine Anthropogenic Litter. Springer, Cham. pp. 325-340, 2015.
• [15] G. Suaria, C. G. Avio, A. Mineo, G. L. Lattin, M. G. Magaldi, G. Belmonte, C. J. Moore, F. Regoli, and S. Aliani, “The Mediterranean plastic soup: synthetic polymers in Mediterranean surface waters,” Scientific Reports, vol. 6, 37551, 2016.
• [16] M. A. Browne, “Sources and Pathways of Microplastics to Habitats,” in Marine Anthropogenic Litter. Springer, Cham. pp. 229-244, 2015.
• [17] M. R. Gregory, “Plastic ‘scrubbers’ in hand cleansers: a further (and minor) source for marine pollution identified,” Marine Pollution Bulletin, vol. 32, no.12, pp. 867-871, 1996.
• [18] L.S. Fendall, and M. A. Sewell, “Contributing to Marine Pollution by Washing Your Face: Microplastics in Facial Cleansers,” Marine Pollution Bulletin, vol. 58, pp. 1225-1228, 2009.
• [19] M. A. Browne, T. Galloway, and R. Thompson, “Microplastic—An Emerging Contaminant of Potential Concern?” Integrated Environmental Assessment and Management, vol. 3, no. 4, pp. 559-561, 2007.
• [20] O. Güven, K. Gökdağ, B. Jovanoviç, and A. E. Kıdeyş, “Microplastic litter composition of the Turkish territorial waters of the Mediterranean Sea, and its occurrence in the gastrointestinal tract of fish” Environmental Pollution, vol. 223, pp. 286-294, 2017.
• [21] S. Rist, B. C. Almroth, N. B. Hartmann, and T. M. Karlsson, “A critical perspective on early communications concerning human health aspects of microplastics,” Science of the Total Environment, vol. 626, pp. 720–726, 2018.
• [22] S. Gündoğdu, and C. Çevik, “Micro- and mesoplastics in Northeast Levantine coast of Turkey: The preliminary results from surface samples” Marine Pollution Bulletin, vol. 118, pp. 341–347, 2017.
• [23] A. Cincinelli, T. Martellini, C. Guerranti, C. Scopetani, D. Chelazzi, and T. Giarrizzo, “A potpourri of microplastics in the sea surface and water column of the Mediterranean Sea,” Trends in Analytical Chemistry, vol. 110, pp. 321-326, 2019.
• [24] E. Constantino, I. Martins, J. M. Salazar Sierra, and F. Bessa, “Abundance and composition of floating marine macro litter on the eastern sector of the Mediterranean Sea,” Marine Pollution Bulletin, vol. 138, pp. 260–265, 2019.
• [25] U. Aytan, A. Valente, Y. Şentürk, R. Usta, F. B. Esensoy Şahin, R. E. Mazlum, and E. Ağırbaş, “First evaluation of neustonic microplastics in Black Sea waters,” Marine Environmental Research, vol. 119, pp. 22-30, 2016.
• [26] Y. Terzi, K. Gedik, A. R. Eryaşar, R. Ç. Öztürk, and A. Şahin, “Microplastic contamination and characteristics spatially vary in the southern Black Sea beach sediment and sea surface water,” Marine Pollution Bulletin, vol. 174, 113228, 2022.
• [27] S. Tunçer, O. B. Artüz, M. Demirkol, and M. L. Artüz, “First report of occurrence, distribution, and composition of microplastics in surface waters of the Sea of Marmara, Turkey,” Marine Pollution Bulletin, vol. 135, pp. 283–289, 2018.
• [28] S. Vardar, T. T. Onay, B. Demirel, and A. E. Kideys, “Evaluation of microplastics removal efficiency at a wastewater treatment plant discharging to the sea of Marmara,” Environmental Pollution, vol. 289, 117862, 2021.
• [29] K. Gedik, A. R. Eryaşar, and A. M. Gözler, “The microplastic pattern of wild-caught Mediterranean mussels from the Marmara Sea,” Marine Pollution Bulletin, vol. 175, 113331, 2022.
• [30] ÇŞB, “Denizlerde Bütünleşik Kirlilik İzleme İşi 2014-2016 Akdeniz Özet Raporu” Çevre ve Şehircilik Bakanlığı – Çevresel Etki Değerlendirmesi, İzin ve Denetim Genel Müdürlüğü, 2017, pp. 68.
• [31] E. Kılıç, and N. Yücel, “Microplastic occurrence in the gastrointestinal tract and gill of bioindicator fish species in the northeastern Mediterranean” Marine Pollution Bulletin, vol. 177, 113556, 2022.
• [32] A. E. Kıdeyş, “ODTÜ - Deniz Bilimleri Enstitüsünde deniz atıkları/mikroplastik araştırmaları ve ilköğretime yönelik “Denizimi Tanıyorum Koruyorum Eğitimi. 5. Plaj Mavi Bayrak Temsilcisi Eğitimi Programi”, Antalya, 6-7 Nisan 2017.
• [33] M. Yabanlı, A. Yozukmaz, İ. Şener, and Ö. T. Ölmez, “Microplastic pollution at the intersection of the Aegean and Mediterranean Seas: A study of the Datça Peninsula (Turkey),” Marine Pollution Bulletin, vol. 145, pp. 47–55, 2019.
• [34] A. Yozukmaz, “Investigation of microplastics in edible wild mussels from İzmir Bay (Aegean Sea, Western Turkey): A risk assessment for the consumers,” Marine Pollution Bulletin, vol. 171, 112733, 2021.
• [35] A. Masud, “Microplastic Contents and Sediment Classification of Selected Sites in Bodrum and Güllük Beaches (Muğla, SW Turkey),” M.S. thesis, Graduate School of Natural and Applied Sciences, Muğla Sıtkı Koçman University, Muğla, 2022.
• [36] http://yerbilimleri.mta.gov.tr/anasayfa.aspx (erişim tarihi: 19/03/2020)
• [37] N. Konak, N. Akdeniz, and E. M. Öztürk, “Geology of the south of Menderes Massif” in Guide Book for the Field Excursion along Western Anatolia, for the IGCP Project No. 5: Correlation of Variscan and pre-Variscan events of the Alpine-Mediterranean mountain belt. Maden Tetkik ve Arama Enstitüsü, pp. 42-53, 1987.
• [38] A. Okay, “Geology of the Menderes Massif and the Lycian Nappes south of Denizli, western Taurides,” Bulletin of the Mineral Research and Exploration, vol. 109, pp. 37-51, 1989.
• [39] O. Ö. Dora, N. Kun, and O. Candan, “Metamorphic history and geotectonic evolution of the Menderes Massif”. In Proc. International Earth Sciences Congress on Aegean Regions, 1990, vol.2, pp. 102-115.
• [40] S. Özer, H. Sözbilir, I. Özkar, V. Toker, and B. Sarı, “Stratigraphy of Upper Cretaceous–Palaeogene sequences in the southern and eastern Menderes Massif (western Turkey),” International Journal of Earth Sciences, vol. 89, pp. 852–866, 2001.
• [41] E. Bozkurt, “Granitoid rocks of the southern Menderes Masif (southwestern Turkey): field evidence for Tertiary magmatism in an extensional shear zone,” International Journal of Earth Sciences, vol. 93, pp. 52–71, 2004.
• [42] Ş. Ersoy, “Batı Toros (Likya) Napları'nın yapısal öğelerinin ve evrimin analizi,” Jeoloji Mühendisliği Dergisi vol. 37, 5-16, 1990.
• [43] Ş. Ersoy, “Datça (Muğla) yarımadasının stratigrafisi ve Tektoniği,” Türkiye Jeoloji Bülteni, vol. 34, pp. 1-14, 1991.
• [44] N. Görür, A. M. C. Şengör, M. Sakınç, O. Tüysüz, R. Akkök, E. Yiğitbaş, F. Y. Oktay, A. Barka, N. Sarıca, B. Ecevitoğlu, E. Demirbağ, Ş. Ersoy, O. Algan, C. Güneysu, and A. Aykol, “Rift formation in the Gökova Region, Southwest Anatolia: implications for the opening of the Aegean Sea” Geological Magazine, vol. 132, no. 6, pp. 637-650, 1995.
• [45] A. S. Collins, and A. H. F. Robertson, “Lycian melange, southwestern Turkey: an emplaced Late Cretaceous accretionary complex,” Geology, vol. 25, pp. 255-258, 1997.
• [46] A. S. Collins, and A. H. F. Robertson, “Processes of Late Cretaceous to Late Miocene episodic thrust-sheet translations in the Lycian Taurides, SW Turkey,” Journal of the Geological Society of London, vol. 155, pp. 759–772, 1998.
• [47] A. S. Collins, and A. H. F. Robertson, “Evolution of the Lycian Allochthon, western Turkey, as a north-facing Late Palaeozoic to Mesozoic rift and passive continental margin,” Geological Journal, vol. 34, pp. 107–138, 1999.
• [48] A. H. F. Robertson, “Mesozoic Tertiary tectonic-sedimentary evolution of a south Tethyan oceanic basin and its margins in southern Turkey” in Tectonics and Magmatism in Turkey and the Surrounding Area. Geological Society, London, Special Publications, vol 173, pp. 43-82, 2000.
• [49] K. Dirik, A. Türkmenoğlu, N. Tuna, and M. Dirican, “Datça Yarımadası’nın Neotektoniği, Jeomorfolojisi ve Bunların Eski Medeniyetlerin Yerleşimi ve Gelişimi Üzerindeki Etkisi” ODTÜ AFP-00-07-03-13 Kod Nolu Proje, 2003.
• [50] M. Gül, Ö. Yılmaz, and Ö. Zeybek, “Morphology and Textural Characteristics of Coastal Sediments of the NE of the Gökova Graben (SW Turkey)”, Journal of Coastal Conservation, vol. 23, pp.417-434, 2019.
• [51] K. Dirik, “Neotectonic characteristic and Seismicity of the Reşadiye Peninsula and Surrounding Area, southwest Anatolia,” Türkiye Jeoloji Bülteni, vol. 50 no. 3, pp. 130-149, 2007.
• [52] T. Ercan, E. Günay, H. Baş, and B. Can, “Datça Yarımadasındaki Kuvaterner yaşlı volkanik kayaçların petrolojisi ve kökensel yorumu,” MTA Dergisi, vol. 97/98, pp. 45-56, 1984.
• [53] G. Gençalioğlu- Kuşcu, and G. Uslular, “Geochemical characterization of mid-distal Nisyros tephra on Datça peninsula (southwestern Anatolia),” Journal of Volcanology and Geothermal Research, vol. 354, pp. 13-28, 2018.
• [54] R. L. Folk, “The petrology of sedimentary rocks,” Hemphill Publishing Co., Austin, 1974, pp. 182.
• [55] A. Besley, M. G. Vijver, P. Behrens, and T. Bosker, “A standardized method for sampling and extraction methods for quantifying microplastics in beach sand,” Marine Pollution Bulletin, vol. 114, pp. 77–83, 2017.
• [56] D. Yang, H. Shi, L. Li, J. Li, K. Jabeen, and P. Kolandhasamy, “Microplastic pollution in table salts from China,” Environmental Science and Technology, vol. 49, pp. 13622-13627, 2015.
• [57] G. Canché-Escamilla, D. E. Pacheco-Catalán, and S. B. Andrade-Canto, “Modification of properties of rayon fibre by graft copolymerization with acrylic monomers,” Journal of Materials Science, vol. 41, pp. 7296–7301, 2006.
• [58] E. Andreassen, “Infrared and Raman spectroscopy of polypropylene,” in Polypropylene: An A-Z Reference Chapter: Infrared and Raman spectroscopy of polypropylene. Kluwer Publishers, 1999.
• [59] P. Garside, and P. Wyeth, “Identification of Cellulosic Fibres by FTIR Spectroscopy- Thread and Single Fibre Analysis by Attenuated Total Reflectance,” Studies in Conservation, vol. 48, no. 4, pp. 269-275, 2003.
• [60] B. Manoj, and P. Narayanan, “Study of Changes to the Organic Functional Groups of a High Volatile Bituminous Coal during Organic Acid Treatment Process by FTIR Spectroscopy,” Journal of Minerals and Materials Characterization and Engineering, vol. 1, pp. 39-43, 2013.
• [61] M. Yuan, Y. Zhang, W. Guo, S. Chen, Y. Qiu, , and P. Zhang, A rapid staged protocol for efficient recovery of microplastics from soil and sediment matrices based on hydrophobic separation. Marine Pollution Bulletin, vol. 182, 113978, 2022. https://doi.org/10.1016/J. MARPOLBUL.2022.113978.
• [62] V.T.K. Khuyen, D.V. Le, H.A. Le, A.R. Fischer, and C. Dornack, “Assessing Microplastic Prevalence and Dispersion from Saigon Urban Canals via Can Gio Mangrove Reserve to East Sea by Raman Scattering Microscopy,” Microplastics, vol. 1, pp. 536-553, 2022. https://doi.org/10.3390/microplastics1030038
• [63] C. Li, Q. Cui, M. Zhang, R.D. Vogt, and X. Lu, “A commonly available and easily assembled device for extraction of bio/non-degradable microplastics from soil by flotation in NaBr solution,” Science of the Total Environment, vol. 759, 143482, 2021. https://doi.org/10.1016/ J.SCITOTENV.2020.143482.
• [64] I. Nabi, A.U.R. Bacha, and L. Zhang, “A review on microplastics separation techniques from environmental media,” Journal of Cleaner Production, vol. 337, 130458, 2022.