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Giresun İlindeki Bazı Ortaokulların Hava Kalitesinin Ağır Metaller Yönünden Değerlendirilmesi

Yıl 2024, Cilt: 14 Sayı: 2, 802 - 815, 18.06.2024
https://doi.org/10.31466/kfbd.1437174

Öz

Bu çalışmada, Giresun’daki bazı ortaokulların bahçesinden toplanan karayosunlarında ağır metal analizleri gerçekleştirilerek, okulların ağır metal kirliliği yönünden hava kalitesinin değerlendirilmesi amaçlanmaktadır. Karayosunlarında gerçek manada kök, gövde, yaprak bulunmamakta ve yapraksı yapılarında da kütikula ve epidermis tabakası olmadığından, havadaki ağır metalleri bünyelerinde biriktirebilmektedirler, bundan dolayı çok iyi biyoindikatör bitkilerdir. Ağır metaller, çocuklar üzerinde de olumsuz etkilere neden olduklarından, çocukların önemli vakitlerini geçirdikleri okulların hava kalitesi bu açıdan önemlidir. Bu çalışmada; Giresun’daki dört ortaokul il merkezinde ve bir beldede olmak üzere beş ortaokuldan toplam onaltı karayosunu numunesi ve dört karayosunu numunesi de kontrol bölgesi olarak kulakkaya yaylasından toplandı. Toplanan karayosunu numunelerindeki ağır metaller Inductively Coupled Plasma-Mass Spectrometer (ICP-MS) cihazında analizler neticesinde belirlendi. Okul bahçelerinden toplanan karayosunlarının analizleri neticesinde ortalamaları; Al, V, Cr, Mn, Fe, Co, Ni, Cu, Zn ve Pb’un konsantrasyon değerleri sırasıyla 8214.67, 38.72, 16.76, 320.96, 10470.31, 4.65, 10.10, 33.69, 94.39 ve 23.80 olarak belirlendi. Kontrol bölgesinden toplanan karayosunlarının ortalama konsantrasyonları ise 3345.90, 11.00, 6.77, 2102. 2017.86, 1.39, 5.26, 7.91, 37.22 ve 3.17 olarak belirlendi. Analizler sonucunda, kontrol bölgesinden toplanan karayosunlarının ağır metal miktarlarının hepsi okul bahçelerinden toplanan numunelerin ağır metal miktarlarından az olduğu görülmüştür. Bu çalışma sonucunda; Okullarımızı, mümkün olduğunca insan kaynaklı kirlilikten uzak noktalara yapılması gerektiği bir kez daha ortaya konulmaktadır.

Destekleyen Kurum

Bu çalışma Giresun Üniversitesi Bilimsel Araştırma Projeleri Koordinasyon Birimi tarafından FEN-BAP-C-230123-10 nolu proje kapsamında desteklenmiştir

Kaynakça

  • Akdur, R. (2009). Hava Kirliliği ve Çözümler. Halk Sağlığı ile İlgili Güncel Sorunlar ve Yaklaşımlar” Ankara Tabipler Odası, Ankara, 151.
  • U.S. Government. Control of emissions of hazrdous air pollutants from mobile sources; final rule. Federal register 40, CFR parts 80 and 86. US Government Printing Office, Washington, DC; 2001.
  • Markert, B.A., Breure, A.M., Zechmeister, H.G. Bioindicators&Biomonitors, Principles, Concepts and Applications. London, 334; 2003.
  • Çobanoğlu, G. (2015). The use of lichens for biomonitoring of atmospheric pollution. Sigma Journal of Engineering and Natural Sciences, 33(4), 591-613.
  • Uyar, G., Oren, M. and Đnce, M., 2007. Atmospheric Heavy Metal Deposition in Duzce Province by Using Mosses as Biomonitors. Fresenius Environmental Bulletin, 16, 145-153.
  • Koz. B., Cevik, U., Ozdemir, T., Duran, C., Kaya, S., Gundogdu, A., Celik, N., 2008. Analysis of Mosses along Sarp-Samsun Highway in Turkey. Journal of Hazardous Materials, 153, 1-2, 646-654.Rühling, Å., & Steinnes, E. (Eds.). (1998). Atmospheric heavy metal deposition in Europe 1995-1996. Nordic Council of Ministers.
  • Wolterbeek, B., 2002. Biomonitoring of trace element air pollution: principles, possibilities and perspectives. Environmental Pollution, 120 (1); 11–21.
  • Zechmeister, H.G., Hohenwallner, D., Riss, A., Hanus-Illnar, A., 2005. Estimation of element deposition derived from roadtraffic sources by using mosses. Environmental Pollution, 138; 238-249.
  • Smith, A. J. E. The moss flora of Britain and Ireland. Edinburgh: Cambridge University Press; 2004.
  • Frey,W., Frahm, J. P., Fischer, E., Lobin,W. Die Moosund Farnpfanzen Europas. Stuttgart: G. Fischer; 1985.
  • Pedrotti, C. C. Flora Dei Muschi D’İtalia. Rome: Antonia Delfino Editore; 2001.
  • Turkmen.M., Dura, N., 2016. Assessment of heavy metal concentrations in fish from south western black sea. Indian Journal of Geo-Marine Science, 45(11); 1552-1559.
  • Thorpe A., Harrison, R.M., 2008. Sources and properties of non-exhoust particulate matter from road traffic: a review, Science of the Total Environment, 400; 270-282.
  • Westerlund, K.G., Johansson, C. Emissions of metals and particulate matter due to wear of brake linings in Stockholm. In: Brebbia, C.A., Martin-Duque, J.F.(Eds), Air Pollution X. WIT Press, Southampton, pp793-802; 2002.
  • Communities of the European Commission, 2002. Commission Regulation (EC) 221/2002 of 6 February 2002 amending regulation (EC) No.466/2002 setting maximum levels for certain contaminants in foodstuffs. Official journal of the European Communities. Brussels, 6 February 2002; 2008.
  • Hulskotte, J.H.J., Denier van der Gon, H.A.C., Visschedijk, A.J.H., Schaap, M., 2007. Brake wear from vehicles as an important source of diffuse copper pollution. Water Science & Technology, 56; 223-231.
  • Garg, B.D., Cadle, S.H., Mulawa, P.A., Groblicki, P.J., Laroo, C. and Parr, G.A., 2000. Brake wear particulate matter emissions. Environmental Science Technology, 34; 4463-4469.
  • IARC., 1993. IARC Monographs on the Evaluation of Carcinogenic Risks to Humans, Vol. 58, Lyon, France. http://www.ekonomihaber7.com (8.Mart.2018)
  • Agency for Toxic Substances and Disease Registry (ATSDR). Division of Toxicology, Clifton Road, NE, Atlanta, GA, available at: http://www.atsdr.cdc.gov/toxprofiles/.
  • Mukherjee, B., Patra, B., Mahapatra, S., Banerjee, P., Tiwari, A., Chatterjee, M., 2004. Vanadium-An elementof atypical biological significance. Toxicology Letters, 150; 135-143.
  • World Health Organization. Environmental Health Criteria 58- Chromium. Geneva: WHO; 1988a. World Health Organization. Environmental Health Criteria-Mangenese. Geneva: WHO; 1980b World Health Organization. Environmental Health Criteria- Cadmium. Geneva: WHO; 1992 World Health Organization. Environmental Health Criteria- Nickel. Geneva: WHO; 1991a
  • World Health Organization. Environmental Health Criteria- Zinc. Geneva: WHO; 2001a
  • Ozaki, H., Watanabe, I., Kuno, K., 2004. Investigation of the heavy metal sources in relation to automobiles. Water, Air&Soil Pollution, 157; 209-223.
  • Herpin, U., Berlekamp, J., Markert,B., Wolterbeek, B., Grodzinska, K., Sievers, U., Lieth, H., Weckert, V., 1996. The distribution of heavy metals in a transect of the three states Netherlands, Germany and Poland determined with the aid of moss monitoring. Science of the Total Environment, 187; 185-198.
  • Vanderpoorten, A., Goffinet, B. Introduction to bryophytes. New York: Cambridge University Press; 2009.

Evaluation of Air Quality of Some Middle Schools in Gı̇resun Province in Terms of Heavy Metals

Yıl 2024, Cilt: 14 Sayı: 2, 802 - 815, 18.06.2024
https://doi.org/10.31466/kfbd.1437174

Öz

This study aims to evaluate the air quality of schools in terms of heavy metal pollution by performing heavy metal analyzes on mosses collected from the gardens of some secondary schools in Giresun. Since mosses do not have any real roots, stems or leaves, and since they do not have a cuticle or epidermis layer in their leafy structures, they can accumulate heavy metals in the air, therefore they are very good bioindicator plants. Since heavy metals also cause negative effects on children, the air quality of schools where children spend significant time is important in this respect. In this study; A total of sixteen moss samples were collected from five secondary schools, four in the city center and one in a town in Giresun, and four moss samples were collected from Kulakkaya plateau as a control region. Heavy metals in the collected moss samples were determined as a result of analysis on the Inductively Coupled Plasma-Mass Spectrometer (ICP-MS) device. As a result of the analysis of mosses collected from school gardens, the averages are; The concentration values of Al, V, Cr, Mn, Fe, Co, Ni, Cu, Zn and Pb were determined as 8214.67, 38.72, 16.76, 320.96, 10470.31, 4.65, 10.10, 33.69, 94.39 and 23.80, respectively. The average concentrations of mosses collected from the control region were determined as 3345.90, 11.00, 6.77, 2102. 2017.86, 1.39, 5.26, 7.91, 37.22 and 3.17. As a result of the analysis, it was seen that the heavy metal amounts of the mosses collected from the control area were less than the heavy metal amounts of the samples collected from the school gardens. As a result of this study; It is once again demonstrated that our schools should be built in locations as far away from human-induced pollution as possible.

Kaynakça

  • Akdur, R. (2009). Hava Kirliliği ve Çözümler. Halk Sağlığı ile İlgili Güncel Sorunlar ve Yaklaşımlar” Ankara Tabipler Odası, Ankara, 151.
  • U.S. Government. Control of emissions of hazrdous air pollutants from mobile sources; final rule. Federal register 40, CFR parts 80 and 86. US Government Printing Office, Washington, DC; 2001.
  • Markert, B.A., Breure, A.M., Zechmeister, H.G. Bioindicators&Biomonitors, Principles, Concepts and Applications. London, 334; 2003.
  • Çobanoğlu, G. (2015). The use of lichens for biomonitoring of atmospheric pollution. Sigma Journal of Engineering and Natural Sciences, 33(4), 591-613.
  • Uyar, G., Oren, M. and Đnce, M., 2007. Atmospheric Heavy Metal Deposition in Duzce Province by Using Mosses as Biomonitors. Fresenius Environmental Bulletin, 16, 145-153.
  • Koz. B., Cevik, U., Ozdemir, T., Duran, C., Kaya, S., Gundogdu, A., Celik, N., 2008. Analysis of Mosses along Sarp-Samsun Highway in Turkey. Journal of Hazardous Materials, 153, 1-2, 646-654.Rühling, Å., & Steinnes, E. (Eds.). (1998). Atmospheric heavy metal deposition in Europe 1995-1996. Nordic Council of Ministers.
  • Wolterbeek, B., 2002. Biomonitoring of trace element air pollution: principles, possibilities and perspectives. Environmental Pollution, 120 (1); 11–21.
  • Zechmeister, H.G., Hohenwallner, D., Riss, A., Hanus-Illnar, A., 2005. Estimation of element deposition derived from roadtraffic sources by using mosses. Environmental Pollution, 138; 238-249.
  • Smith, A. J. E. The moss flora of Britain and Ireland. Edinburgh: Cambridge University Press; 2004.
  • Frey,W., Frahm, J. P., Fischer, E., Lobin,W. Die Moosund Farnpfanzen Europas. Stuttgart: G. Fischer; 1985.
  • Pedrotti, C. C. Flora Dei Muschi D’İtalia. Rome: Antonia Delfino Editore; 2001.
  • Turkmen.M., Dura, N., 2016. Assessment of heavy metal concentrations in fish from south western black sea. Indian Journal of Geo-Marine Science, 45(11); 1552-1559.
  • Thorpe A., Harrison, R.M., 2008. Sources and properties of non-exhoust particulate matter from road traffic: a review, Science of the Total Environment, 400; 270-282.
  • Westerlund, K.G., Johansson, C. Emissions of metals and particulate matter due to wear of brake linings in Stockholm. In: Brebbia, C.A., Martin-Duque, J.F.(Eds), Air Pollution X. WIT Press, Southampton, pp793-802; 2002.
  • Communities of the European Commission, 2002. Commission Regulation (EC) 221/2002 of 6 February 2002 amending regulation (EC) No.466/2002 setting maximum levels for certain contaminants in foodstuffs. Official journal of the European Communities. Brussels, 6 February 2002; 2008.
  • Hulskotte, J.H.J., Denier van der Gon, H.A.C., Visschedijk, A.J.H., Schaap, M., 2007. Brake wear from vehicles as an important source of diffuse copper pollution. Water Science & Technology, 56; 223-231.
  • Garg, B.D., Cadle, S.H., Mulawa, P.A., Groblicki, P.J., Laroo, C. and Parr, G.A., 2000. Brake wear particulate matter emissions. Environmental Science Technology, 34; 4463-4469.
  • IARC., 1993. IARC Monographs on the Evaluation of Carcinogenic Risks to Humans, Vol. 58, Lyon, France. http://www.ekonomihaber7.com (8.Mart.2018)
  • Agency for Toxic Substances and Disease Registry (ATSDR). Division of Toxicology, Clifton Road, NE, Atlanta, GA, available at: http://www.atsdr.cdc.gov/toxprofiles/.
  • Mukherjee, B., Patra, B., Mahapatra, S., Banerjee, P., Tiwari, A., Chatterjee, M., 2004. Vanadium-An elementof atypical biological significance. Toxicology Letters, 150; 135-143.
  • World Health Organization. Environmental Health Criteria 58- Chromium. Geneva: WHO; 1988a. World Health Organization. Environmental Health Criteria-Mangenese. Geneva: WHO; 1980b World Health Organization. Environmental Health Criteria- Cadmium. Geneva: WHO; 1992 World Health Organization. Environmental Health Criteria- Nickel. Geneva: WHO; 1991a
  • World Health Organization. Environmental Health Criteria- Zinc. Geneva: WHO; 2001a
  • Ozaki, H., Watanabe, I., Kuno, K., 2004. Investigation of the heavy metal sources in relation to automobiles. Water, Air&Soil Pollution, 157; 209-223.
  • Herpin, U., Berlekamp, J., Markert,B., Wolterbeek, B., Grodzinska, K., Sievers, U., Lieth, H., Weckert, V., 1996. The distribution of heavy metals in a transect of the three states Netherlands, Germany and Poland determined with the aid of moss monitoring. Science of the Total Environment, 187; 185-198.
  • Vanderpoorten, A., Goffinet, B. Introduction to bryophytes. New York: Cambridge University Press; 2009.
Toplam 25 adet kaynakça vardır.

Ayrıntılar

Birincil Dil Türkçe
Konular Yapısal Biyoloji
Bölüm Makaleler
Yazarlar

Hasan Demir 0009-0001-0273-6578

Bahadır Koz 0000-0003-3264-0144

Yayımlanma Tarihi 18 Haziran 2024
Gönderilme Tarihi 14 Şubat 2024
Kabul Tarihi 9 Mayıs 2024
Yayımlandığı Sayı Yıl 2024 Cilt: 14 Sayı: 2

Kaynak Göster

APA Demir, H., & Koz, B. (2024). Giresun İlindeki Bazı Ortaokulların Hava Kalitesinin Ağır Metaller Yönünden Değerlendirilmesi. Karadeniz Fen Bilimleri Dergisi, 14(2), 802-815. https://doi.org/10.31466/kfbd.1437174