Uptake and distribution of a copper, iron and zinc mixture in gill, liver and plasma of a freshwater teleost, Tilapia sparrmanii

• Published in: Water S. A. Vol. 27; no. 1; pp. 99 - 108
• Main Authors: Wepener, V., Van Vuren, J.H.J., Du Preez, H.H.
• Format: Journal Article
• Language: English
• Published: Pretoria Water Research Commission (WRC) 01.01.2001; Water Research Commision
• Subjects: Agnatha. Pisces; Animal, plant and microbial ecology; Applied ecology; Biological and medical sciences; Ecotoxicology, biological effects of pollution; Effects of pollution and side effects of pesticides on vertebrates; Fundamental and applied biological sciences. Psychology; South Africa, Olifants R; Tilapia sparrmanii; Plasma; Gill; Digestive system; Liver; Experimental study; Heavy metal; Freshwater environment; Pollutant; Vertebrata; Absorption; Pisces; Content; Water pollution; Kinetics; Localization; Teleostei; Osteichthyes
• ISSN: 0378-4738

Since polluted environments contain mixtures of different contaminants, the aim of this study was to investigate the time-integrated uptake of individual metals by a freshwater teleost, Tilapia sparrmanii following exposure to a metal mixture containing Cu, Fe and Zn. The metal concentrations used during the bioassays were chosen to represent ecologically relevant concentrations as found in the Olifants River, Kruger National Park, South Africa. The concentrations used in the bioassay were 0.16 mg·ℓ-1, 4.3 mg·ℓ-1 and 1.003 mg·ℓ-1 for Cu, Fe and Zn respectively. Gill, plasma and liver were sampled at 0, 2, 4, 6, 12, 24, 24, 48, 72, 96 h and four weeks. Gill tissue is the initial site of accumulation of water-borne metals. Although the fish were exposed to a metal mixture, the interactions between metals and the external gill surface, as well as the subsequent uptake rate, were associated with the particular chemical properties of individual metals. The tendency of the individual metals in the metal mixture to bind to the external gill surface via ionic bonds, and to gill cytosolic compounds via covalent bonds, was Cu > Fe > Zn. The ensuing uptake rates into the extracellular compartment (blood) and intracellular compartment (liver tissue) were Zn > Fe > Cu. The toxic effects of Cu and Fe were, therefore, primarily exerted on the gill surface and in the gill cytosol, whereas the toxic action of Zn was primarily limited to the internal organs.