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FARKLI KURŞUN KONSANTRASYONLARININ Elodea canadensis Michx. ‘ İN KLOROFİL A VE KLOROFİL B MİKTARLARI ÜZERİNE ETKİLERİ

Year 2005, Volume: 7 Issue: 2, 12 - 18, 01.12.2005

Abstract

Araştırmada farklı kurşun konsantrasyonlarında klorofil a ve klorofil b miktarlarının değişimlerini tespit etmek amaçlanmıştır. Elodea canadensis gövde parçaları 0.1, 0.5, 1, 5, 10, 20, 50, ve 100 mg L-1kurşun konsantrasyonlarına 24, 48, 72, 120, 168 ve 216 saatlik peryotlarda tutulmuşlardır. Kontrol bitkilerinde ve 5,10,20, ve 100 mg L-1 kurşun konsantrasyonlarında klorofil a ve b miktarları 30-120 mg L1 , 0.1 ,0.5, ve 1 mg L-1 kurşun konsantrasyonlarında ise 20-70 mg L-1 ölçülmüştür. 168. saatten itibaren 50 ve 100 mgL-1 kurşun konsantrasyonlarına maruz bırakılan örneklerin yapraklarında senesens ile ilgili morfoılojik belirtiler ortaya çıkmıştır

References

  • [1] Raskin, I., Smith, R.D., Salt, D.E. “Phytoremediation of metals: using plants to remove pollutants from the environment”. Current Opinion in Biotechnology 8, 221-226.(1997).
  • [2] Lovett-Doust, L., Lovett-Doust. J., Biernacki, M. “American wildcelery, Vallisneria americana, as a biomonitor of organic contaminants in aquatic ecosystems.” Journal of Great Lakes Research 20, 333-354. (1994).
  • [3] Biernacki, M., Lovett-Doust, J., Lovett-Doust, L. “ Temporal biomonitoring usingwild celery, Vallisneria Americana”. Journal of Great Lakes Research 23, 97- 107.(1997).
  • [4] Lewis, M.A. “Use of freshwater plants for phytotoxicity testing: a review.” Environmental Pollution 87. 319-336.(1995).
  • [5] Salt, D.E., Smith, R.D., Raskin, I. “Phytoremediation”. Annual Review of Plant Physiology and Plant Molecular Biology 49, 643-668.(1998).
  • [6] Biernacki, M., Lovett-Doust, J. “Vallisneria americana (Hydro-genotypes)”. American Journal of Botany 84, 1743-1751.(1997).
  • [7] Everard, M., Denny, P. “Flux of lead in submerged plants and its relevance to a freshwater system.” Aquatic Botany 21, 181-193.(1985).
  • [8] Bowmer, K.H., Jacobs, S.W.L., Sainty, G.R. “Identification, biology and management of Elodea canadensis, Hydrocharitaceae”. Journal of Aquatic Plant Management 33, 13-19.(1995).
  • [9] Brown, B.T., Rattigan. B.M. “ Toxicity of soluble copper and other metal ions to Elodea Canadensis”. Environmental Pollution 20, 303 314.(1979).
  • [10] Vesk, P.A., Allaway, W.G. “Spatial variation of copper and lead 1 concentrations of water hyacinth plants in a wetland receiving urban run-off.” Aquatic Botany 59. 33 44. (1997).
  • [11] Akman, Y.,Ketenoğlu, O.,Evren, H., Kurt, L.,Düzenli, S. “Çevre Kirliliği. Çevre Biyolojisi” Palme Yayıncılık. 273 s. (2000).
  • [12] Kahkonen, M.A., Manninen, P.K.G. “The uptake of nickel and chromium from water by Elodea canadensis at different nickel and chromium exposure levels”. Chemosphere 36. 1381 - 1390. (1998).
  • [13] Kahkonen, M.A., Pantsar-Kallio, M., Manninen, P.K.G. “Analysing heavy metal concentrations in the different parts of Elodea canadensis and surface sediment with PCA in two boreal lakes in southern Finland”. Chemosphere 35, 2645-2656.(1997).
  • [14] Mal, K.T., Adorjan, P.,Corbett, A.L. “Effect of copper on growth of an aquatic macrophyte, Elodea canadensis”. Environmental pollution, 120,307-311. (2002).
  • [15] Lichtenthaler, H.K., Wellburn, A.R. “Determinations of total carotenoids and chlorophylls a and b of leaf extracts in different solvents”. Biochemical Society Transactions 11: 591 - 592. (1983).
  • [16] Temel, M., Yardımcı, C. H. “Büyükçekmece gölü ekosisteminde civa ve kurşun konsantrasyonları ve su kalitesi üzerine bir araştırma.”(Bildiri). Su Ürünleri Sempozyumu. 20-22 Eylül 2000. Sinop, 397-409.(2000).
  • [17] Temel, M. “ The Phytoplankton of Lake Büyükçekmece , Istanbul – TURKEY”, Pakistan Journal of Botany.Vol:34. No:1., p:81-92. Karachi-PAKİSTAN. (2002).
  • [18] Stoyanova, D.P., Tchakalova. E.S. “The effect of lead and copper on the photosynthetic apparatus in Elodea Canadensis”. Rich.Photosynthetica 28, 63 74.(1993).

The Effects of Various Concentrations of Lead to Chlorophyll A and Chlorophyll B of elodea canadensis michx

Year 2005, Volume: 7 Issue: 2, 12 - 18, 01.12.2005

Abstract

This study aims to determine the changes in quantities of chlorophyll a and chlorophyll b in various lead concentrations. The main parts of Elodea canadensis have been subjected to lead concentrations, such as 0.1, 0.5, 1, 5, 10, 20, 50 and 100 mg L-1, with periods of 24, 48, 72, 120, 168 and 216 hours. Chlorophyll a and b quantities were measured in control plants and lead concentrations of 5, 10, 20 and 100 mg L-1 as 30 – 120 mg L-1 and in lead concentrations of 0.1, 0.5 and 1 mg L-1 as 20-70 mg L-1. Some morphological indications related with senescence were observed on leaves of the samples that were exposed to 50 and 100 mg L-1 lead concentrations beginning from the 168th hour

References

  • [1] Raskin, I., Smith, R.D., Salt, D.E. “Phytoremediation of metals: using plants to remove pollutants from the environment”. Current Opinion in Biotechnology 8, 221-226.(1997).
  • [2] Lovett-Doust, L., Lovett-Doust. J., Biernacki, M. “American wildcelery, Vallisneria americana, as a biomonitor of organic contaminants in aquatic ecosystems.” Journal of Great Lakes Research 20, 333-354. (1994).
  • [3] Biernacki, M., Lovett-Doust, J., Lovett-Doust, L. “ Temporal biomonitoring usingwild celery, Vallisneria Americana”. Journal of Great Lakes Research 23, 97- 107.(1997).
  • [4] Lewis, M.A. “Use of freshwater plants for phytotoxicity testing: a review.” Environmental Pollution 87. 319-336.(1995).
  • [5] Salt, D.E., Smith, R.D., Raskin, I. “Phytoremediation”. Annual Review of Plant Physiology and Plant Molecular Biology 49, 643-668.(1998).
  • [6] Biernacki, M., Lovett-Doust, J. “Vallisneria americana (Hydro-genotypes)”. American Journal of Botany 84, 1743-1751.(1997).
  • [7] Everard, M., Denny, P. “Flux of lead in submerged plants and its relevance to a freshwater system.” Aquatic Botany 21, 181-193.(1985).
  • [8] Bowmer, K.H., Jacobs, S.W.L., Sainty, G.R. “Identification, biology and management of Elodea canadensis, Hydrocharitaceae”. Journal of Aquatic Plant Management 33, 13-19.(1995).
  • [9] Brown, B.T., Rattigan. B.M. “ Toxicity of soluble copper and other metal ions to Elodea Canadensis”. Environmental Pollution 20, 303 314.(1979).
  • [10] Vesk, P.A., Allaway, W.G. “Spatial variation of copper and lead 1 concentrations of water hyacinth plants in a wetland receiving urban run-off.” Aquatic Botany 59. 33 44. (1997).
  • [11] Akman, Y.,Ketenoğlu, O.,Evren, H., Kurt, L.,Düzenli, S. “Çevre Kirliliği. Çevre Biyolojisi” Palme Yayıncılık. 273 s. (2000).
  • [12] Kahkonen, M.A., Manninen, P.K.G. “The uptake of nickel and chromium from water by Elodea canadensis at different nickel and chromium exposure levels”. Chemosphere 36. 1381 - 1390. (1998).
  • [13] Kahkonen, M.A., Pantsar-Kallio, M., Manninen, P.K.G. “Analysing heavy metal concentrations in the different parts of Elodea canadensis and surface sediment with PCA in two boreal lakes in southern Finland”. Chemosphere 35, 2645-2656.(1997).
  • [14] Mal, K.T., Adorjan, P.,Corbett, A.L. “Effect of copper on growth of an aquatic macrophyte, Elodea canadensis”. Environmental pollution, 120,307-311. (2002).
  • [15] Lichtenthaler, H.K., Wellburn, A.R. “Determinations of total carotenoids and chlorophylls a and b of leaf extracts in different solvents”. Biochemical Society Transactions 11: 591 - 592. (1983).
  • [16] Temel, M., Yardımcı, C. H. “Büyükçekmece gölü ekosisteminde civa ve kurşun konsantrasyonları ve su kalitesi üzerine bir araştırma.”(Bildiri). Su Ürünleri Sempozyumu. 20-22 Eylül 2000. Sinop, 397-409.(2000).
  • [17] Temel, M. “ The Phytoplankton of Lake Büyükçekmece , Istanbul – TURKEY”, Pakistan Journal of Botany.Vol:34. No:1., p:81-92. Karachi-PAKİSTAN. (2002).
  • [18] Stoyanova, D.P., Tchakalova. E.S. “The effect of lead and copper on the photosynthetic apparatus in Elodea Canadensis”. Rich.Photosynthetica 28, 63 74.(1993).
There are 18 citations in total.

Details

Other ID JA22DM74UM
Journal Section Research Articles
Authors

Mustafa Temel This is me

Publication Date December 1, 2005
Submission Date December 1, 2005
Published in Issue Year 2005 Volume: 7 Issue: 2

Cite

APA Temel, M. (2005). FARKLI KURŞUN KONSANTRASYONLARININ Elodea canadensis Michx. ‘ İN KLOROFİL A VE KLOROFİL B MİKTARLARI ÜZERİNE ETKİLERİ. Balıkesir Üniversitesi Fen Bilimleri Enstitüsü Dergisi, 7(2), 12-18.
AMA Temel M. FARKLI KURŞUN KONSANTRASYONLARININ Elodea canadensis Michx. ‘ İN KLOROFİL A VE KLOROFİL B MİKTARLARI ÜZERİNE ETKİLERİ. BAUN Fen. Bil. Enst. Dergisi. December 2005;7(2):12-18.
Chicago Temel, Mustafa. “FARKLI KURŞUN KONSANTRASYONLARININ Elodea Canadensis Michx. ‘ İN KLOROFİL A VE KLOROFİL B MİKTARLARI ÜZERİNE ETKİLERİ”. Balıkesir Üniversitesi Fen Bilimleri Enstitüsü Dergisi 7, no. 2 (December 2005): 12-18.
EndNote Temel M (December 1, 2005) FARKLI KURŞUN KONSANTRASYONLARININ Elodea canadensis Michx. ‘ İN KLOROFİL A VE KLOROFİL B MİKTARLARI ÜZERİNE ETKİLERİ. Balıkesir Üniversitesi Fen Bilimleri Enstitüsü Dergisi 7 2 12–18.
IEEE M. Temel, “FARKLI KURŞUN KONSANTRASYONLARININ Elodea canadensis Michx. ‘ İN KLOROFİL A VE KLOROFİL B MİKTARLARI ÜZERİNE ETKİLERİ”, BAUN Fen. Bil. Enst. Dergisi, vol. 7, no. 2, pp. 12–18, 2005.
ISNAD Temel, Mustafa. “FARKLI KURŞUN KONSANTRASYONLARININ Elodea Canadensis Michx. ‘ İN KLOROFİL A VE KLOROFİL B MİKTARLARI ÜZERİNE ETKİLERİ”. Balıkesir Üniversitesi Fen Bilimleri Enstitüsü Dergisi 7/2 (December 2005), 12-18.
JAMA Temel M. FARKLI KURŞUN KONSANTRASYONLARININ Elodea canadensis Michx. ‘ İN KLOROFİL A VE KLOROFİL B MİKTARLARI ÜZERİNE ETKİLERİ. BAUN Fen. Bil. Enst. Dergisi. 2005;7:12–18.
MLA Temel, Mustafa. “FARKLI KURŞUN KONSANTRASYONLARININ Elodea Canadensis Michx. ‘ İN KLOROFİL A VE KLOROFİL B MİKTARLARI ÜZERİNE ETKİLERİ”. Balıkesir Üniversitesi Fen Bilimleri Enstitüsü Dergisi, vol. 7, no. 2, 2005, pp. 12-18.
Vancouver Temel M. FARKLI KURŞUN KONSANTRASYONLARININ Elodea canadensis Michx. ‘ İN KLOROFİL A VE KLOROFİL B MİKTARLARI ÜZERİNE ETKİLERİ. BAUN Fen. Bil. Enst. Dergisi. 2005;7(2):12-8.