Heijerick D G, De Schamphelaere K A C, Janssen C R
Ghent University, Laboratory of Environmental Toxicology and Aquatic Ecology, J. Plateaustraat 22, B-9000 Ghent, Belgium.
Comp Biochem Physiol C Toxicol Pharmacol. 2002 Sep;133(1-2):207-18. doi: 10.1016/s1532-0456(02)00077-7.
Biotic ligand models have been developed for various metals (e.g. Cu, Ag, Zn) and different aquatic species. These models incorporate the effect of physico-chemical water characteristics (major cations, pH, dissolved organic carbon) on the bioavailability and toxicity of the metal. In this study, the individual effects of calcium, magnesium, potassium, sodium and pH on zinc toxicity to the green alga Pseudokirchneriella subcapitata (formerly and better known as Selenastrum capricornutum and Raphidocelis subcapitata) were investigated. Stability constants for binding to algal cells (K(BL)) were derived for those cations affecting zinc toxicity, using the mathematical approach proposed by De Schamphelaere and Janssen [Environ. Sci. Technol. 63, (2002) 48-54]. Potassium proved to be the only cation tested that did not alter zinc toxicity to algae significantly. Log (K(BL)) values for Ca, Mg and Na, derived at pH 7.5, were 3.2, 3.9 and 2.8, respectively. Toxicity tests performed at different pH values (5.5-8.0) indicated that competition between H(+) and Zn(2+) reduces zinc toxicity. However, the observed relationship between (H(+)) and the 72h-EbC(50) [expressed as microM (Zn(2+))] is not linear and suggests that pH affects the physiology of the biotic ligand. Although, in general, our findings seem to suggest that zinc toxicity to algae can be modelled as a function of key water characteristics, the results also demonstrate that the part of the conventional BLM-hypothesis-i.e. that the binding characteristics of the biotic ligand are independent of the test medium characteristics-is not valid for algae. The observed pH-dependent change of stability constants should therefore be further investigated and incorporated in future BL-modelling efforts with algae.
生物配体模型已针对各种金属(如铜、银、锌)和不同的水生物种开发出来。这些模型纳入了物理化学水质特征(主要阳离子、pH值、溶解有机碳)对金属生物有效性和毒性的影响。在本研究中,研究了钙、镁、钾、钠和pH值对锌对绿藻小新月菱形藻(以前更熟知的名称为羊角月牙藻和近头状针杆藻)毒性的单独影响。利用De Schamphelaere和Janssen [《环境科学与技术》63,(2002) 48 - 54]提出的数学方法,得出了影响锌毒性的那些阳离子与藻类细胞结合的稳定常数(K(BL))。结果证明,钾是所测试的唯一一种对锌对藻类的毒性没有显著影响的阳离子。在pH值为7.5时得出的钙、镁和钠的Log (K(BL))值分别为3.2、3.9和2.8。在不同pH值(5.5 - 8.0)下进行的毒性试验表明,H(+)和Zn(2+)之间的竞争降低了锌的毒性。然而,观察到的(H(+))与72小时半数效应浓度(以 microM (Zn(2+))表示)之间的关系并非线性,这表明pH值会影响生物配体的生理机能。虽然总体而言,我们的研究结果似乎表明锌对藻类的毒性可以作为关键水质特征的函数进行建模,但结果也表明,传统生物配体模型假设的一部分——即生物配体的结合特性与测试介质特征无关——对藻类并不成立。因此,应进一步研究观察到的稳定性常数随pH值的变化,并将其纳入未来针对藻类的生物配体建模工作中。