CanmetMINING, Natural Resources Canada, Ottawa, ON, Canada.
Ecotoxicol Environ Saf. 2015 May;115:300-8. doi: 10.1016/j.ecoenv.2014.12.024. Epub 2015 Feb 7.
Thallium has been shown to significantly increase in both water and aquatic biota after exposure to metal mine effluent, however, there is a lack of knowledge as to its fate and effect in the aquatic environment. The objectives of this project were to assess (1) fate of thallium by conducting speciation analysis and determining the influence of water quality on toxicity and (2) effects of thallium (I) and (III) on three aquatic species; the algae, Pseudokirchneriella subcapitata, the invertebrate Ceriodaphnia dubia and the vertebrate Pimephales promelas. Speciation analysis proved challenging with poor recovery of thallium (I), however analysis with solutions >125μg/L revealed that over a 7-d period, recovery of thallium (III) was less than 15%, suggesting that the majority of thallium (III) was converted to Thallium (I). It was only in fresh solutions where recovery of Thallium (III) was greater than 80%. The lowest IC25s generated during our effects assessment for both Thallium (I) and (III) were more than 10-fold greater than the highest concentration recorded in receiving environments (8μg/L) and more than 100-fold greater than the current guideline (0.8μg/L). To assess the influence of water quality on thallium toxicity, the concentrations of both potassium and calcium were reduced in dilution water. When potassium was reduced for both C. dubia and P. subcapitata tests, the lowest IC25 generated was 5-fold higher than the current guideline, but within the range of concentrations reported in receiving environments for both Thallium (I) and (III). When calcium was reduced in dilution water, toxicity only increased in the Tl (III) tests with C. dubia; the IC25 for Tl(III), similar to the exposures conducted with reduced potassium, was within the range of total thallium concentrations reported in the receiving environment. Without an accurate, repeatable method to assess thallium speciation at low concentrations it is not possible to draw any firm conclusions as to whether the IC25s for Tl (III) are relevant to concentrations present in receiving environments. Based on the results of our study we recommend that any test, to determine Thallium (III) toxicity, use fresh solutions, made daily, to get good recovery and accurate toxicity results. The results generated in our effects and exposure assessment would indicate that the current guideline of 0.8μg/L is protective. Special attention should be placed on the concentration of potassium in receiving environments when estimating thallium toxicity.
铊在暴露于金属矿山废水后,其在水中和水生生物体内的含量均显著增加,然而,人们对其在水生环境中的归宿和影响知之甚少。本项目的目的是评估:(1) 通过形态分析评估铊的归宿,并确定水质对毒性的影响;(2) 铊(I)和(III)对三种水生物种的影响,藻类 Pseudokirchneriella subcapitata、无脊椎动物 Ceriodaphnia dubia 和脊椎动物 Pimephales promelas。形态分析具有挑战性,铊(I)的回收率很差,但是,在浓度超过 125μg/L 的溶液中进行的分析表明,在 7 天的时间内,铊(III)的回收率低于 15%,这表明大部分铊(III)转化为铊(I)。只有在新鲜溶液中,铊(III)的回收率才大于 80%。在我们的影响评估中,铊(I)和(III)产生的最低 IC25 均比接收环境中记录的最高浓度(8μg/L)高出 10 倍以上,比现行指南(0.8μg/L)高出 100 倍以上。为了评估水质对铊毒性的影响,在稀释水中降低了钾和钙的浓度。当 C.dubia 和 P.subcapitata 的测试中降低了钾的浓度时,产生的最低 IC25 比现行指南高 5 倍,但在铊(I)和(III)的接收环境报告的浓度范围内。当在稀释水中降低钙的浓度时,只有在 C.dubia 的 Tl(III)测试中才会增加毒性;Tl(III)的 IC25 与降低钾时相似,处于接收环境中报告的总铊浓度范围内。由于没有一种准确、可重复的方法来评估低浓度下的铊形态,因此无法确定 Tl(III)的 IC25 是否与接收环境中的浓度有关。根据我们的研究结果,我们建议任何测试确定 Tl(III)毒性时,都应使用每天新鲜制备的溶液,以获得良好的回收率和准确的毒性结果。在我们的影响和暴露评估中产生的结果表明,现行的 0.8μg/L 指南是具有保护作用的。在估计铊毒性时,应特别注意接收环境中钾的浓度。