PL EN


Preferencje help
Widoczny [Schowaj] Abstrakt
Liczba wyników
Powiadomienia systemowe
  • Sesja wygasła!
  • Sesja wygasła!
Tytuł artykułu

Przydatność Anodonta anatina (L.) jako organizmu wskaźnikowego odzwierciedlającego poziomy metali ciężkich (Cu, Zn, Pb, Co, Cd, Hg) w wodzie i osadach dennych

Autorzy
Treść / Zawartość
Identyfikatory
Warianty tytułu
EN
Use of Anodonta anatina (L.) as indicatory organism reflecting levels of heavy metals (Cu, Zn, Pb, Co, Cd, Hg) in water and bottom sediments
Języki publikacji
PL
Abstrakty
PL
Celem niniejszego artykułu było stwierdzenie, w jakim stopniu tkanki miękkie i muszle Anodonta anatina (L.) (szczeżuja pospolita) odzwierciedlają zmiany poziomów Cu, Zn, Pb, Co, Cd i Hg w wodzie powierzchniowej i osadach dennych (frakcja poniżej 0,20 mm) ujścia Odry. Materiał do badań laboratoryjnych został pobrany w latach 1999 i 2000 z obszaru ujścia Odry (19 stanowisk) oraz z jeziora Miedwie (jedno stanowisko). Na każdym stanowisku oznaczano koncentracje metali w wodzie powierzchniowej, osadach dennych (frakcja poniżej 0,20 mm) oraz w tkankach miękkich (całe ciało) i muszlach Anodonta anatina. Analizowano 20 próbek tkanek miękkich i 12 próbek muszli Anodonta anatina oraz po 20 próbek wody powierzchniowej i osadów dennych. Na każdym stanowisku analizowano próbki Anodonta anatina obejmujące co najmniej kilkanaście okazów o różnych rozmiarach (tzw. próbki uśrednione). Oznaczenia Cu, Zn, Pb, Co, Cd dokonano techniką ICP-AES, a Hg oznaczono techniką CV-AES. Przy zastosowaniu Anodonta anatina, jako organizmu wskaźnikowego, rejestruje się zmiany poziomów stężeń metali ciężkich w wodzie powierzchniowej na podstawie analizy tkanek miękkich i muszli (Cu i Zn), analizy muszli (Pb i Hg) oraz analizy tkanek (Hg). Z sześciu badanych metali nie kontroluje się tylko zmian Co. Z kolei zmiany koncentracji metali w osadach można kontrolować, wykorzystując tkanki miękkie i muszle (Zn i Hg), tylko tkanki (Cu, Pb i Cd) i tylko muszle (Co).
EN
The aim of the present article was the determination to what extent soft tissues and shells of the Anodonta anatina (Anodonta cygnea piscinalis NILSSON 1823; Anodonta piscinalis NILSSON 1823) reflect the changes Cu, Zn, Pb, Co, Cd and Hg in superficial water and bottom sediments (fraction below 0.20 mm) of the Odra River estuary. The material for laboratory investigations was taken in years 1999 and 2000 of the Odra River estuary (19 research points) and from Lake Miedwie (one research point). The concentrations of metals were marked at every research point in superficial water, bottom sediments and in soft tissues (whole body) and shells of the Anodonta anatina. 20 samples of soft tissues, 12 samples of the shells of the Anodonta anatina and 20 the samples of superficial water and bottom sediments were analysed. Samples of the Anodonta anatina (averaged samples) were analysed at every research point consisting more than ten specimens of various sizes. Quantitative determination Cu, Zn, Pb, Co, Cd was executed with the technique ICP-AES and Hg was marked with the technique CV-AES. The changes of the levels of the concentrations of heavy metals in superficial water were correlated with the results of the analysis of soft tissues and shells (Cu and Zn), the analysis of shells (Pb and Hg) and the analysis of soft tissues (Hg). Only changes of the Co did not show appropriate correlation. The soft tissues and shells (Zn and Hg), only soft tissues (Cu, Pb and Co) and only shells (Co) can reflect the changes of concentration of metals in bottom sediments.
Rocznik
Strony
259--277
Opis fizyczny
Bibliogr. 56 poz.
Twórcy
Bibliografia
  • [1] Kovács M., Biological indicators in environmental protection, Akademiai Kiadó, Budapest 1992,208.
  • [2] Manning W.J., Feder W.A., Biomonitoring air pollutants with plants, Applied Science Publ. Ltd., London 1980,142.
  • [3] Markert B. (eds.), Plants as Biomonitors - Indicators for Heavy Metals in the Terrestrial Environment, VCH-Verlaggesellschaft mbh, Weinheim-New York 1993, pp. 644.
  • [4] Spelleberg F.J., Monitoring Ecological Change, Cambridge Univ. Press, Cambridge-New York-Port Chester-Melbourne-Sydney 1991, pp. 334.
  • [5] Jurkiewicz-Karnkowska E., Accumulation of zinc and copper in molluscs from the Zegrzyński Reservoir and the Narew River, Ekol. Pol. 1989,37(3-4), 347-357.
  • [6] Jurkiewicz-Karnkowska E., Occurrence of mol1uscs in the littoral zone of the Zegrzyński Reservoir and in the pre-mouth and mouth zones of supplying rivers, Ekol. Pol. 1989, 37, 319-336.
  • [7] Jurkiewicz-Karnkowska E., Mięczaki a metale ciężkie w środowiskach słodkowodnych i lądowych, Molluscs and heavy metall in freshwater and terrestrial environments, Wiad. Ekolog. 1994, XL(3), 127-140.
  • [8] Jurkiewicz-Karnkowska E., Możliwości wykorzystania wybranych gatunków mięczaków w bioindykacji skażenia metalami ciężkimi wód Zbiornika Zegrzyńskiego. Application possibiliti es of selected mollusc species in bioindication of heavy metal contamination in the Zegrzyński Reservoir, Chem. Inż. Ekol. 1999,6(5-6).
  • [9] Jurkiewicz-Karnkowska E., Krolak E., Heavy metal concentrations in molluscs from the Zegrzynski Reservoir and the rivers supplying it, Pol. Arch. Hydrobiol. 1996, 43(3), 335-346.
  • [10] Jurkiewicz-Karnkowska E., Królak E., Zróżnicowanie międzygatunkowe koncentracji metali ciężkich (Cu, Zn, Mn, Fe, Pb i Cd) w mięczakach ze Zbiornika Zegrzyńskiego. Interspecific differentiation of heavy metal concentrations (Cu, Zn, Mn, Fe, Pb and Cd) in molluscs from the Zegrzyński Reservoir, Chem. Inż. Ekol. 1999,6(5-6),485-490.
  • [11] Piotrowski S., Geochemia wybranych elementów ekosystemu jeziora Dąbie. Maszynopis (praca doktorska), Arch. ING UWr, Wrocław 1994.
  • [12] Piotrowski S., Heavy metal contents in shel1s of Lymnaea peregra (O.F. Müll.) and Lymnaea stagnalis (L.) from a fish pond in the area of Kłęby near Nowogard, Quaternary Studies in Poland 1999, Special issue, 281-288.
  • [13] Piotrowski S., Accumulation of heavy metal s (Cu, Zn, Pb, Co, Cd, Hg) in fresh water molluscs shel1s compared to their concentrations in water and bottom sediments using the example of Roztoka Odrzańska (The Odra River Estuary), III Conference on Trace Metals, Efects on Organisms and Environment, Sopot 2000, 39-41.
  • [14] Piotrowski S., Wpływ toksyczności metali ciężkich w osadach dennych estuarium Odry i wybranych jezior Pomorza Zachodniego na organizmy bentoniczne. Heavy metal toxicity to benthic organisms in bottom sediments of River Odra Estuary and selected Western Pomeranian lakes, Zeszyty Naukowe Politechniki Śląskiej 2003, Seria Górnictwo, 256, 185-192.
  • [15] Piotrowski S., Use of fresh water molluscs as indicators of water environment contamination with heavy metals (Cu, Zn, Pb, Co, Cd, Hg), [in:] Valorisation of the environment in the areas exposed to long term industrial and mining activites, 2-4 June 2004, Wisła-Ustroń 2004, 24.
  • [16] Piotrowski S., Zależność koncentracji metali ciężkich i węgla organicznego od wielkości muszli mięczaków słodkowodnych: Lymnaea peregra (Müller, 1774), Lymnaea stagnalis (L.) i Dreissena polymorpha (Pallas, 1771), Przeg. Geolog. 2006, 54, 6, 501-508.
  • [17] Włosik-Bieńczak E., Mięczaki (MOLLUSCA) strumienia Junikowskiego w Poznaniu i glinianek w jego dolinie, XIII Krajowe Seminarium Malakologiczne nt. Wykorzystanie badań malakologicznych w ekologii i ochronie środowiska, Świnoujście 1997, 81-98.
  • [18] Bouquegnean J.M., Noël-Lambot F., Disteche A, Fate of heavy metals in experimental aquatic food chains. Uptake and release of Hg and Cd by some marine organisms, Role of metallothioneins, Inter. Counc. Explor. Sea 1979, Ser. E, 58,1-9.
  • [19] Burrows G., Whitton B.A, Heavy metals in water, sediments and invertebrates from a metal contaminated river free of organic pol1ution, Hydrobiologia 1993, 106, 263-273.
  • [20] Dmowski K., Karolewski M.A, Cumulation of zinc, cadmium and lead in invertebrates and in some vertebrates according to the degree of an area contamination, Ekol. Pol. 1979,27,333-349.
  • [21] Laskowski R., Maryański M., Heavy metals in epigeic fauna: trophic level and physiological hypothesis, Bull. Environ. Contain. Toxicol. 1993,50,232-240.
  • [22] Klerks P.L., Fraleigh P.C., Lawniczak J.E., Effects of the exotic zebra mussels (oreissena polymorpha) on metal cycling in Lake Erie, Can. J. Fish. Aquat. Sci. 1997,54(7), 1630-1638.
  • [23] Puente X., Villares R., Carral E., Carballeira A., Nacreous shell of Mytilus galloprovincialis as a biomonitor of heavy metal pollution in Galiza (NW Spain), Sci. Total Environ. 1996, 183,205-211.
  • [24] Theede H., Andersson J., Lehnberg W., Cadmium in Mytilus edulis from Germany coastal waters, Meeresforschung 1979, 27,147-155.
  • [25] Jenner H.A., Hemelraad l, Marquenie J.M., Noppert F., Cadmium kinetics in freshwater clams (Unionidae) under field and laboratory conditions, Sci. Total Environ. 1991, 108,205-214.
  • [26] Hickey C.W., Roper O.S., Buckland S.J., Metal concentrations of resident and transplanted freshwater mussels Hyridella menziesi (Unionacea: Hyriidae) and sediments in the Waikato River, New Zealand, Sci. Total Environ. 1995, 175(3),163-177.
  • [27] Malley D.F., Chang P.S.S., Hesslein R.H., Whole lake addition of cadmium-109: radiotracer accumulation in the mussel population in the first season, Sci. Total Environ. 1989, 87/88, 397-417.
  • [28] Manly R., George W.O., The occurence of some heavy metals in populations of the freshwater mussel Anodonta anatina (L.) from the river Thames, Environ. Pollut. 1977,14, 139-154.
  • [29] Salanki J., Van-Balogh K., Uptake and release of mercury and cadmium in various organs of mussels (Anodonta cygnea L.), Symposia Biologica Hungarica 1985, 29, 325-340.
  • [30] Van-Balogh K., Heavy metal pollution from a point source demonstrated by mussel (Unio pictorum L.) at Lake Balaton, Hungary, Bull. Environ. Contam. Toxicol. 1988,41,910-914.
  • [31] Bertine K.K., Goldberg E.D., Trace elements in clams, mussels and shrimp, Umnol. Oceanogr. 1972, 17,877-884.
  • [32] Bolognani Fantin A.M., Benedetti L., Bolognani L., Ottaviani E., The effects of lead pollution on the freshwater gastropod Viviparus viviparus L.: biochemical and histochemical features, Malacologia 1982, 22(1-2), 19-21.
  • [33] Imlay M.1., Use of shells of freshwater mussels in monitoring heavy metals and environmental stresses: A review, Malacol. Rev.1982, 15, 1-14.
  • [34] Bias R., Karbe L., Bioaccumulation and partitioning of cadmium within the freshwater mussel Dreissena polymorpha Pallas, Int. Rev. Gesamten Hydrobiol. 1985, 70, 113-125.
  • [35] Carell B., Folberg S., Grundelius E., Henrikson L., Can mussel shells reveal environmental history? Ambio 1987, 16, 2-10.
  • [36] Lingard S.M., Evars R.D., Bourgoin B.P., Method for the estimation of organic-bound and crystal-bound metal concentrations in bivalve shells, Bulletin of Environmental Contamination and Toxicology 1992, 48, 179-184.
  • [37] Pitts L.C., Wallace G.T., Lead deposition in the shell of the bivalve, Mya arenaria: an indicator of dissolved lead in seawater, Estuarine, Coastal, Shelf Sci. 1994, 39, 93-104.
  • [38] Elder J.F., Collins J.J., Freshwater molluscs as indicators of bioavailability and toxicity of metals in surface-water systems, Rev. Environ. Contam. Toxicol. 1991, 122,37-79.
  • [39] Hansten C., Heino M., Pynnonen K., Viability of glochidia of Anodonta anatina (Unionidae) exposed to selected metal s and chelating agents, Aqnat. Toxicol. 1996, 34(1), 1-12.
  • [40] Pynnonen K., Changes in acid-base status, gases and electrolytes in the hemolymph of freshwater unionids during continuous and intermittent exposure to acid water, Annales Zoologici Fennici 1995,32,355-363.
  • [41] Leatherland T.M., Burton J.D., The occurence of some trace metal s in coastal organisms with particular reference to the Solent region, J. Mar. Biol. Ass. UK 1974,54,457-468.
  • [42] Makela T.P., Oikari A.O.J., Pentaehlorophenol accumulation in the freshwater mussels Anodonta anatina and Pseudoanodonta complanata, and some physiological consequences of laboratory maintenance, Chemosphere 1995, 31 (7), 3651-3662.
  • [43] Segar D.A., Collins J.D., Riley J.P., The distributions of the major and some minor elements in marine animals, Part II, Molluscs, J. Mar. Biol. Ass. UK 1971, 51, 131-136.
  • [44] Streit B., Winter S., Cadmium uptake and compartmental time characteristics in the freshwater mussel Anodonta anatina, Chemosphere 1993,26(8), 1479-1490.
  • [45] Jamil A., Lajtha K., Radan S., Ruzsa G., Cristofor S., Postolache C., Mussels as bioindicators of trace metal pollution in the Danube Delta of Romania, Hydrobiologia 1999, 392(2), 143-158.
  • [46] Orme S., Kegley S., 2004, PAN Pesticides Database, Pesticide Action Network, North America (San Francisco, CA), Chemical Toxicity Studies on Aquatic Organisms. www.pesticideinfoorg/List_EcoChemSpecies.jsp?Taxa_Group='Moll uscs"
  • [47] Piotrowski S., Heavy metals in water and bottom sediments of the Odra river estuary and selected lakes of west Pomerania (north-west Poland), Limnolog. Rev. 2003,3, 181-188.
  • [48] Piotrowski S., Geochemical characteristic of bottom sediments in the Odra River estuary - Roztoka Odrzańska (north-west Poland), Geol. Quart. 2004, 48(I), 61-76.
  • [49] Van Hattum B., Timmermans K., Govers H.A., Abiotic and biotic factors influencing in situ trace metal levels in macroinvertebrates in freshwater ecosystems, Environ. Toxicol. Chem. 1991,10,175-292.
  • [50] Gundacker C., Tissue-specific heavy metal (Cd, Pb, Cu, Zn) deposition in a natural population of the zebra mussel Dreissena polymorpha PALLAS, Chemosphere 1999,38,3339-3356.
  • [51] Gundacker C., Comparison of heavy metal bioaccumulation in freshwater molluscs of urban river habitats in Vienna, Environ. Pollut. 2000, 110(I), 61-71.
  • [52] Kraak M.H.S., Toussaint M., Bleeker E.A.J., Lavy D., Metal regulation in two species of freshwater bivalves, [In: Dallinger R., Rainbow P. (eds.) - Ecotoxicology of Metals intnvertebrates (SETAC Special Publications), Lewis, Chelsea, MI 1993, 175-186.
  • [53] Huebner J.D., Pynnonen K.S., Viability of glochidia of two species of anodonta exposed to low pH and selected metals, Can. J. Zool. 1992,70(12),2348-2355.
  • [54] Forbes V.E., Response of Hydrobia ventrosa (Montagu) to environmental stress: effects of salinity fluctuations and cadmium exposure on growth, Funct. Ecol. 1991, 5, 642-648.
  • [55] Raj A.J.M., Hameed P.S., Effect of copper, cadmium and mercury on metabolism of the freshwater mussel Lamellidens marginalis (Lamarek), Jour. Environ. Biol. 1991, 12, 131-135.
  • [56] Willis M., A comparative survey of Aneylus fluviatilis (Müller) populations the Afon Crafnant, N. Wales, above and below an input of zinc from mine waste, Arch. Hydrobiol. 1983, 98, 198-214.
Typ dokumentu
Bibliografia
Identyfikator YADDA
bwmeta1.element.baztech-article-LOD7-0027-0063
JavaScript jest wyłączony w Twojej przeglądarce internetowej. Włącz go, a następnie odśwież stronę, aby móc w pełni z niej korzystać.