Ecotoxicology Program, Environmental Research Institute of the Supervising Scientist, GPO Box 461, Darwin, Northern Territory 0801, Australia.
Chemosphere. 2010 Apr;79(5):547-54. doi: 10.1016/j.chemosphere.2010.02.017. Epub 2010 Mar 9.
The effects of chronic uranium (U) exposure on larval Northern trout gudgeon, Mogurnda mogurnda, were assessed in two experiments using a newly-developed 28d survival and growth toxicity test. Significant effects were observed in both tests, but toxicity was markedly higher in Test 2 than Test 1. The LC50s for Tests 1 and 2 were 2090microgL(-1) and 1070microgL(-1), respectively. Larval growth IC10s for Tests 1 and 2 were 860microgL(-1) and 660microgL(-1) (dry weight), and 1160microgL(-1) and 850microgL(-1) (length), respectively. Uranium speciation modelling showed that a lower pH in Test 2 (mean of 6.0) compared to Test 1 (mean of 6.7) resulted in a greater proportion of free uranyl ion (UO(2)(2+)), the predominant bioavailable form of U. A higher dissolved organic carbon concentration (DOC) in Test 2 (4.2mgL(-1)) compared to Test 1 (2.1mgL(-1)) resulted in a higher proportion of U-DOC in Test 2, but this was insufficient to counter the effect of pH on the proportion of UO(2)(2+). The difference in U toxicity between the two tests could be explained by normalising for UO(2)(2+); the concentrations of UO(2)(2+) at the LC50s for Tests 1 and 2 were calculated to be 13.3 and 13.7microgL(-1), respectively. Finally, the results of this study, and comparisons with other studies suggest that U toxicity to M. mogurnda appears to be as much, if not more, a function of exposure water quality and feeding regime, as exposure duration.
采用一种新建立的 28d 生存和生长毒性试验,评估了慢性铀(U)暴露对北方圆口铜鱼幼鱼的影响。在两个试验中均观察到了显著的影响,但在试验 2 中毒性明显高于试验 1。试验 1 和试验 2 的 LC50 分别为 2090μg/L 和 1070μg/L。试验 1 和试验 2 的幼鱼生长 IC10 分别为 860μg/L 和 660μg/L(干重)以及 1160μg/L 和 850μg/L(体长)。铀形态建模表明,与试验 1(平均 pH 值为 6.7)相比,试验 2 (平均 pH 值为 6.0)的 pH 值较低,导致游离铀离子(UO22+)的比例更高,UO22+是 U 的主要生物可利用形式。与试验 1(DOC 浓度为 2.1mg/L)相比,试验 2 (DOC 浓度为 4.2mg/L)的溶解有机碳浓度(DOC)较高,导致试验 2 中 U-DOC 的比例较高,但这不足以抵消 pH 值对 UO22+比例的影响。由于 UO22+的比例,两个试验之间的 U 毒性差异可以得到解释;试验 1 和试验 2 的 LC50 时的 UO22+浓度分别计算为 13.3 和 13.7μg/L。最后,本研究的结果以及与其他研究的比较表明,U 对 M. mogurnda 的毒性与其暴露水质和摄食方式,而不是暴露时间,同样密切相关。