Accumulation copper (Cu) in the Halimione portulacoides (L.) Aellen and Suaeda prostrata subsp. prostrata pall. taxa, spreading in Ayvalık saltern (Balıkesir-Turkey)

Yıl 2020, Cilt: 22 Sayı: 1, 172 - 180, 10.01.2020

Güngör Ay Murat Kılıç Fatma Koçbaş Fatma Mungan Kılıç

https://doi.org/10.25092/baunfbed.679597

Öz

The aim of this present study was to compare the level of copper (Cu) in the soils and different organs (root, stem, leaves) of Halimione portulacoides (L.) Aellen and Suaeda prostrata subsp. prostrata Pall. taxa which are widespread distribution in every locality of from Ayvalık saltern in Balıkesir. Each month samples were collected from determined seven stations, from soil dam surrounding saltern. Analyses were done by using Perkin Elmer Analyst 700 Flame Atomic Absorption Spectrophotometer (FAAS) device. The level of Cu in H. portulacoides (0.003-0.925 ppm) and S. prostrata subsp. prostrata (0.004-0.896 ppm) was observed to be quite different. Levels of copper in the soils were below the limits of the Turkey soil pollution control regulations standard (TSP, 24609). The levels of Cu were found in the soil in H. portulacoides was 0.862-1.111 ppm, S. prostrata subsp. prostrata 0.858-1.111 ppm.

Anahtar Kelimeler

Ayvalık saltern, copper, halophytic plant, pollution

Proje Numarası

We wish to thank Scientific Investigation Project to Coordinate of Celal Bayar University (Project No. FEF 2009-035) for financial support.

Ayvalık tuzlasında yayılış gösteren Halimione portulacoides (l.) ve Suaeda prostrata subsp. prostrata pall. taksonlarında bakır (Cu) birikimi (Balıkesir-Türkiye)

Öz

Çalışmamızın amacı Balıkesir ilinde bulunan Ayvalık tuzlasının her lokalitesinde yayılış gösteren ve yoğun olarak bulunan Halimione portulacoides (L.) Aellen ve Suaeda prostrata subsp. prostrata Pall. taksonlarının topraklarında ve farklı organlarında (kök, gövde ve yaprak) bakır (Cu) seviyesini karşılaştırmaktır. Her ay tuzlayı çevreleyen toprak set üzerinde belirlenen yedi istasyondan örnekler alınmıştır. Analizler Perkin Elmer Analyst 700 model alevli atomik absorbsiyon Spektrofotometresi (FAAS) cihazı ile yapıldı. Cu seviyesi H. portulacoides (0.003-0.925 ppm) ve S. prostrata subsp. prostrata (0.004-0.896 ppm) oldukça farklı olduğu gözlemlenmiştir. Topraktaki Cu değerleri; H. portulacoides’de 862-1.111 ppm, S. prostrata subsp. prostrata’da ise 0.858-1.111 ppm olarak bulunmuş olup, Türkiye toprak kirliliği kontrol yönetmeliği değerlerinin altında çıkmıştır.

Anahtar Kelimeler

Ayvalık tuzlası, bakır, halofitik bitki, kirlilik

Proje Numarası

We wish to thank Scientific Investigation Project to Coordinate of Celal Bayar University (Project No. FEF 2009-035) for financial support.

Kaynakça

• Merlini, M., Some Considerations on Heavy Metals in the Marine Hydrosphere and Biosphere, Thallasia Jugoslavica, 16(2-4), 367-376, (1980).
• Engel, D. W., Sunda, W., Fowler B. A., Factors affecting trace metal uptake and toxicity to estuarine organisms. I. Environmental Parameters, Biological Monitoring of Marine Pollutants, 127-144, (1981).
• Zengin, F. K., Munzuroğlu, Ö., Fasulye Fidelerinin (Phaseolus vulgaris L. Strike) klorofil ve karotenoid miktarı üzerine bazı ağır metallerin (Ni+2, Co+2, Cr+3, Zn+2) etkileri, Fırat Üniversitesi Fen ve Mühendislik Bilimleri Dergisi, 17, 164-172, (2005).
• Seaward, M. R. D., Richardson D. H. S., Atmospheric sources of metal pollution an effects on vegatation. In:SHAW A.J. editors. Heavy metaltolerance in plants. 75-92, (1989).
• Nedelkoska, T. V., Doran, P. M., Characteristics of heavy metal uptake by plant species with potential for phytoremediation and phytomining, Mineral Engineering, 13, 549-561, (2000).
• Öztürk, M., Türkan, İ., Heavy metal accumulation by plants alongside the motor roads. Plants as biomonitors, 640-650, (1993).
• Nuhoğlu, Y., Malkoç, E., Gürses, A., Canpolat, N., Removal of Cu (II) from aqueous solution by Ulothrix zonata. Bioresource Technology, 85, 3, 331-333, (2002).
• Motto, H. L., Danies, R. P., Motto C. K., Lead in soils and plants; its relationship so traffic volume and proximity so highways, Environmental Science & Technology, 4, 231-237, (1970).
• Zengin, F. K., Munzuroğlu, Ö., Fasulye Fidelerinin (Phaseolus vulgaris L.) Kök, Gövde ve Yaprak Büyümesi Üzerine Kurşun (Pb++) ve Bakır (Cu++)’ın Etkileri. Gazi Üniversitesi Fen Bilimleri Dergisi, 17, 1-10, (2004).
• Phalsson, A. M. B., Toxicity of heavy metals (Zn, Cu, Cd, Pb) to vascular plants. Water, Air, & Soil Pollution, 47, 287-319, (1989).
• Reboreda, R., Caçador, I., Copper, zinc and lead speciation in salt marsh sediments colonised by Halimione portulacoides and Spartina maritima. Science Direct, Chemosphere. 69, 1655-1661, (2007).
• Válega, M., Lillebø, A. I., Caçador, I., Pereira, M. E., Duarte, A. C., Pardal, M. A., Mercury in salt marshes ecosystems: Halimione portulacoides as biomonitor. Science Direct, Chemosphere, 72, 1224-1229, (2008).
• Almedia, R. M. C., Dias, C. A., Mucha, P. A., Bordalo, A. A., Vasconcelos, S. D. T. M., Study of the influence of different organic pollutants on Cu accumulation by Halimione portulacoides, Estuarine, Coastal and Shelf Science, 627-632, (2009).
• Kılıç, M., Ay, G., Koçbaş, F., Mungan, F., Karabaş, M., Dikicioğlu, R., Kardaş, T., Ayvalık Tuzlasında Halimione portulacoides (L.) Aellen Bitkisi Kullanılarak Nikel Düzeyinin Belirlenmesi, Anadolu Doğa Bilimleri Dergisi, 2, 2, 16-23, (2011).
• UNEP. Sampling of selected marine organisms and sample preparation for trace metal analysis, Reference Methods for Marine Pollution Studies, 7, 2, 15, (1984).
• Chang, C. C., Vander Mallie, R. J., Garvey, J. S., A radioimmunoassay for human metallothionein. Toxicology and Applied Pharmacology, 55, 94-102, (1980).
• Sossé, B. A., Genet, P., Dunand-Vinit, F., Toussaint, L. M., Epron, D., Badot, P.M., Effect of copper on growth in cucumber plants (Cucumis sativus) and its relationships with carbonhydrate accumulation and changes in ion contents, Plant Science, 166, 1213-1218, (2004).
• Tam, N. F. Y., Liu, W. K., Wong, M. H., Wong, Y. S., Heavy metal pollution in roadside urban parks and gardens in Hong Kong, The Science of The Total Environment, 59, 325-328, (1987).
• Caselles, J., Levels of lead and other metals in Citrus alongside a motor road. Water, Air & Soil Pollution, 105,(3-4), 593-602, (1998).
• Bu-Olayan, A. H., Thomas, B. V., Biomonitoring Studies on The Lead Levels in Mesquite (Prosopis juliflora (Sw.) DC.) in The Arid Ecosystem of Kuwait. Kuwait Journal of Science & Engineering, 29,1, 65-73, (2002).
• Çelik, A., Kartal, A. A., Akdoğan, A., Kaska, Y., Determining the heavy metal pollution in Denizli (Turkey) by using Robinio pseudo-acacia L. Environmental International, 31,1, 105-112, (2004).
• Novotny, V., Chesters, G., Handbook of nonpoint pollution, sources and management, Van Nostrand-Reinhold Publishers: New York, (1981).
• Ndiokwere, C. L., A study of heavy metal pollution from motor vehicle emissions and its effect on roadside soil, vegetation and crop in Nigeria, Environmental Pollution Series B, Chemical and Physical, 7, 1, 35-42, (1984).
• Ho, Y. B., Tai, K. M., Elevated Levels of Lead and Other Metals in RoadsideSoil and Grass and Their Use to Monitor Aerial Metal Depositions in Hong Kong, Environmental Pollution, 49, 1, 37-51, (1988).