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使用流式细胞术开发多物种藻类生物测定法。

Development of multispecies algal bioassays using flow cytometry.

作者信息

Franklin Natasha M, Stauber Jennifer L, Lim Richard P

机构信息

Centre for Advanced Analytical Chemistry, CSIRO Energy Technology, Private Mail Bag 7, Bangor, New South Wales 2234, Australia.

出版信息

Environ Toxicol Chem. 2004 Jun;23(6):1452-62. doi: 10.1897/03-250.

Abstract

Multispecies algal bioassays, suitable for assessing copper toxicity, were developed with three marine (Micromonas pusilla, Phaeodactylum tricornutum, and Heterocapsa niei) and three freshwater (Microcystis aeruginosa, Pseudokirchneriella subcapitata, and Trachelomonas sp.) microalgae. Flow cytometry was used to separate and count algal signals based on pigment fluorescence and cell size. Species were mixed together on the basis of equivalent surface areas to avoid the confounding effect on toxicity of increased biomass for metal binding. Under control conditions (no added copper), M. pusilla growth was inhibited in the presence of the other marine microalgae compared to single-species tests, while the opposite was true (i.e., growth stimulation) for M. aeruginosa and P. subcapitata in freshwater mixtures. Competition for nutrients, including CO2, and algal exudate production may account for these effects. Interactions between microalgal species also had a significant effect on copper toxicity to some species. In freshwater multispecies bioassays, the toxicity of copper to Trachelomonas sp. was greater in the presence of other species, with copper concentrations required to inhibit growth (cell division) rate by 50% (72-h [IC50]) decreasing from 9.8 to 2.8 microg Cu/L in single- and multispecies bioassays, respectively. In contrast, in marine multispecies bioassays, copper toxicity to the marine diatom P. tricornutum was reduced compared to single-species bioassays, with an increase in the 72-h IC50 value from 13 to 24 microg Cu/L. This reduction in copper toxicity was not explained by differences in the copper complexing capacity in solution (as a result of exudate production) because labile copper, measured by anodic stripping voltammetry, was similar for P. tricornutum alone and in the mixture. These results demonstrate that single-species bioassays may over- or underestimate metal toxicity in natural waters.

摘要

利用三种海洋微藻(微小原甲藻、三角褐指藻和尼氏异帽藻)和三种淡水微藻(铜绿微囊藻、斜生栅藻和囊裸藻属)开发了适用于评估铜毒性的多物种藻类生物测定法。流式细胞术用于根据色素荧光和细胞大小分离并计数藻类信号。基于等效表面积将物种混合在一起,以避免增加的生物量对金属结合毒性产生混淆效应。在对照条件下(不添加铜),与单物种试验相比,在存在其他海洋微藻的情况下,微小原甲藻的生长受到抑制,而在淡水混合物中,铜绿微囊藻和斜生栅藻则相反(即生长受到刺激)。对包括二氧化碳在内的营养物质的竞争以及藻类分泌物的产生可能是造成这些影响的原因。微藻物种之间的相互作用对某些物种的铜毒性也有显著影响。在淡水多物种生物测定中,在存在其他物种的情况下,铜对囊裸藻属的毒性更大,单物种和多物种生物测定中抑制生长(细胞分裂)率50%所需的铜浓度(72小时[半数抑制浓度])分别从9.8微克铜/升降至2.8微克铜/升。相比之下,在海洋多物种生物测定中,与单物种生物测定相比,铜对海洋硅藻三角褐指藻的毒性降低,72小时半数抑制浓度值从13微克铜/升增加到24微克铜/升。铜毒性的降低不能用溶液中铜络合能力的差异(由于分泌物的产生)来解释,因为通过阳极溶出伏安法测量的活性铜,对于单独的三角褐指藻和混合物中的三角褐指藻来说是相似的。这些结果表明,单物种生物测定可能高估或低估天然水体中的金属毒性。

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