Joachim Sandrine, Roussel Hélène, Bonzom Jean-Marc, Thybaud Eric, Mebane Christopher A, Van den Brink Paul, Gauthier Laury
In Vitro and In Vivo Unit, INERIS, Parc Technologique ALATA, Verneuil-en-Halatte, France.
Laboratoire ECOLAB, UMR 5245, Paul Sabatier University, Toulouse, France.
Environ Toxicol Chem. 2017 Oct;36(10):2698-2714. doi: 10.1002/etc.3822. Epub 2017 May 30.
A lotic mesocosm study was carried out in 20-m-long channels, under continuous, environmentally realistic concentrations of copper (Cu) in low, medium, and high exposures (nominally 0, 5, 25, and 75 μg L ; average effective concentrations <0.5, 4, 20, and 57 μg L respectively) for 18 mo. Total abundance, taxa richness, and community structure of zooplankton, macroinvertebrates, and emerging insects were severely affected at Cu treatment levels of 25 and 75 μg L . Some taxa were sensitive to Cu, including gastropods such as Lymnaea spp. and Physa sp., crustaceans such as Chydorus sphaericus, Gammarus pulex, and Asellus aquaticus, rotifers such as Mytilina sp. and Trichocerca sp., leeches such as Erpobdella sp., and the emergence of dipteran insects such as Chironomini. Other taxa appeared to be tolerant or favored by indirect effects, as in Chironimidae larvae, the emergence of Orthocladiinae, and the zooplankter Vorticella sp., which increased in the 25 and 75 μg L treatments. After approximately 8 mo of Cu exposure, the macroinvertebrate community in the high treatment was decimated to the point that few organisms could be detected, with moderate effects in the medium treatment, and very slight effects in the low-Cu treatment. Subsequently, most taxa in the high-Cu exposure began a gradual and partial recovery. By the end of the study at 18 mo, macroinvertebrate taxa richness was similar to control richness, although overall abundances remained lower than controls. After 18 mo of copper exposure, a no-observed-effect concentration at the community level for consumers was set at 5 μg L (4 μg L as average effective concentration), and a lowest-observed-effect concentration at 25 μg L (20 μg L as average effective concentration). Environ Toxicol Chem 2017;36:2698-2714. © 2017 SETAC.
在20米长的渠道中进行了流水中型生态系统研究,在低、中、高暴露水平(名义浓度分别为0、5、25和75微克/升;平均有效浓度分别<0.5、4、20和57微克/升)下,持续保持环境现实浓度的铜(Cu),实验为期18个月。在铜处理水平为25和75微克/升时,浮游动物、大型无脊椎动物和羽化昆虫的总丰度、分类单元丰富度和群落结构受到严重影响。一些分类单元对铜敏感,包括椎实螺属(Lymnaea spp.)和膀胱螺属(Physa sp.)等腹足纲动物,球形盘肠溞(Chydorus sphaericus)、河蚬(Gammarus pulex)和水生等足虫(Asellus aquaticus)等甲壳纲动物,米氏轮虫(Mytilina sp.)和三肢轮虫(Trichocerca sp.)等轮虫,蛭蚓属(Erpobdella sp.)等水蛭,以及摇蚊科(Chironomini)等双翅目昆虫的羽化。其他分类单元似乎具有耐受性或受到间接影响的青睐,如摇蚊科幼虫、直突摇蚊亚科(Orthocladiinae)的羽化,以及钟形虫属(Vorticella sp.)浮游动物,它们在25和75微克/升处理中数量增加。在大约8个月的铜暴露后,高处理组中的大型无脊椎动物群落几乎灭绝,以至于几乎检测不到生物,中处理组有中度影响,低铜处理组影响非常轻微。随后,高铜暴露组中的大多数分类单元开始逐渐部分恢复。到18个月研究结束时,大型无脊椎动物分类单元丰富度与对照组相似,尽管总体丰度仍低于对照组。在18个月的铜暴露后,消费者群落水平的未观察到影响浓度设定为5微克/升(平均有效浓度为4微克/升),最低观察到影响浓度为25微克/升(平均有效浓度为20微克/升)。《环境毒理学与化学》2017年;36:2698 - 2714。© 2017 SETAC。