Centre for Environmental Sustainability, School of the Environment, University Technology Sydney, Broadway, NSW 2007, Australia.
Ecochemistry Laboratory, Institute for Applied Ecology, University of Canberra, Canberra, ACT 2601, Australia.
Ecotoxicol Environ Saf. 2014 Aug;106:126-35. doi: 10.1016/j.ecoenv.2014.03.004. Epub 2014 May 16.
In the environment, arsenic (As) exists in a number of chemical species, and arsenite (As(III)) and arsenate (As(V)) dominate in freshwater systems. Toxicity of As species to aquatic organisms is complicated by their interaction with chemicals in water such as phosphate that can influence the bioavailability and uptake of As(V). In the present study, the toxicities of As(III), As(V) and dimethylarsinic acid (DMA) to three freshwater organisms representing three phylogenetic groups: a phytoplankton (Chlorella sp. strain CE-35), a floating macrophyte (Lemna disperma) and a cladoceran grazer (Ceriodaphnia cf. dubia), were determined using acute and growth inhibition bioassays (EC₅₀) at a range of total phosphate (TP) concentrations in OECD medium. The EC₅₀ values of As(III), As(V) and DMA were 27 ± 10, 1.15 ± 0.04 and 19 ± 3 mg L(-1) for Chlorella sp. CE-35; 0.57 ± 0.16, 2.3 ± 0.2 and 56 ± 15 mg L(-1) for L. disperma, and 1.58 ± 0.05, 1.72 ± 0.01 and 5.9 ± 0.1 mg L(-1) for C. cf. dubia, respectively. The results showed that As(III) was more toxic than As(V) to L. disperma; however, As(V) was more toxic than As(III) to Chlorella sp. CE-35. The toxicities of As(III) and As(V) to C. cf. dubia were statistically similar (p>0.05). DMA was less toxic than iAs species to L. disperma and C. cf. dubia, but more toxic than As(III) to Chlorella sp. CE-35. The toxicity of As(V) to Chlorella sp. CE-35 and L. disperma decreased with increasing TP concentrations in the growth medium. Phosphate concentrations did not influence the toxicity of As(III) to either organism. Chlorella sp. CE-35 showed the ability to reduce As(V) to As(III), indicating a substantial influence of phytoplankton on As biogeochemistry in freshwater aquatic systems.
在环境中,砷(As)以多种化学形态存在,亚砷酸盐(As(III))和砷酸盐(As(V))在淡水系统中占主导地位。砷物种对水生生物的毒性因与水中化学物质(如磷酸盐)的相互作用而变得复杂,这些化学物质会影响 As(V)的生物有效性和摄取。在本研究中,使用急性和生长抑制生物测定法(EC₅₀),在 OECD 培养基中总磷酸盐(TP)浓度范围内,确定了三种代表三个系统发育群的淡水生物(一种浮游植物(绿球藻 sp. 株 CE-35)、一种漂浮的大型植物(浮萍)和一种桡足类食草动物(水蚤))对 As(III)、As(V)和二甲砷酸(DMA)的毒性。对于绿球藻 sp. CE-35,As(III)、As(V)和 DMA 的 EC₅₀ 值分别为 27 ± 10、1.15 ± 0.04 和 19 ± 3 mg L(-1);对于浮萍,0.57 ± 0.16、2.3 ± 0.2 和 56 ± 15 mg L(-1);对于水蚤,1.58 ± 0.05、1.72 ± 0.01 和 5.9 ± 0.1 mg L(-1)。结果表明,对于浮萍,As(III)比 As(V)毒性更强;然而,对于绿球藻 sp. CE-35,As(V)比 As(III)毒性更强。对于水蚤,As(III)和 As(V)的毒性在统计学上没有显著差异(p>0.05)。与 iAs 物种相比,DMA 对浮萍和水蚤的毒性较低,但对绿球藻 sp. CE-35 的毒性较高。随着生长培养基中 TP 浓度的增加,As(V)对绿球藻 sp. CE-35 和浮萍的毒性降低。磷酸盐浓度对这两种生物的 As(III)毒性没有影响。绿球藻 sp. CE-35 表现出将 As(V)还原为 As(III)的能力,这表明浮游植物对淡水水生系统中 As 生物地球化学的影响很大。