Rybak Michał, Kołodziejczyk Agata, Joniak Tomasz, Ratajczak Izabela, Gąbka Maciej
Department of Water Protection, Institute of Environmental Biology, Faculty of Biology, Adam Mickiewicz University, Poznań, Umultowska 89, 61-614 Poznań, Poland.
European Space Research and Technology Centre, Keplerlaan 1, PO Box 299, NL-2200 AG Noordwijk, Netherlands.
Ecotoxicol Environ Saf. 2017 Nov;145:359-366. doi: 10.1016/j.ecoenv.2017.07.056. Epub 2017 Jul 28.
The objective of this study was to examine the impact of aluminium on the perennial macroalgae Chara hispida L. and its bioaccumulation capacities. Aluminium (Al) was introduced into the environment in the form of polyaluminium chloride, an agent utilized in the restoration of waterbodies. Research was conducted in an experimental setting using mesocosms (volume 0.8m) placed in the littoral zone of a lake with C. hispida. Three doses of the coagulant were applied, each with a different volume: low - 6.1g Al m, medium - 12.2gm and high - 24.5g Al m. A significant acidification of environment was determined, which would imply the presence of toxic Al ions. It has been demonstrated that aluminium penetrates and accumulates in the cells of the charophyte. This caused damage to the thalli, which manifested itself in chloroses, necroses, flaking of the cortex cells and softening of the thallus, whose severity was proportionate to the dose of the coagulant. The first negative signs were observed after 24h. The study shows that C. hispida is a poor accumulator of aluminium (bioconcentration factor < 200), while bioaccumulation capacity was inhibited at the concentration of approx. 2.0mg Al g d.w. Accumulation in the thalli of the charophytes accounted for 58% of variation following removal of aluminium from the environment. The results of the experiment demonstrate a negative impact of aluminium on charophytes at concentrations used in aggressive restoration of lakes.
本研究的目的是考察铝对多年生大型藻类刚毛藻的影响及其生物累积能力。铝以聚合氯化铝的形式引入环境中,聚合氯化铝是一种用于水体修复的试剂。研究在实验环境中进行,使用放置在有刚毛藻的湖泊沿岸带的中型生态箱(体积0.8立方米)。施加了三种剂量的混凝剂,每种剂量的体积不同:低剂量 - 6.1克铝/立方米,中剂量 - 12.2克铝/立方米,高剂量 - 24.5克铝/立方米。确定环境出现了显著酸化,这意味着存在有毒的铝离子。已证明铝渗透并累积在轮藻细胞中。这对藻体造成了损害,表现为褪绿、坏死、皮层细胞剥落以及藻体软化,其严重程度与混凝剂剂量成正比。在24小时后观察到了最初的负面迹象。研究表明,刚毛藻是铝的低效累积者(生物浓缩系数<200),而在铝浓度约为2.0毫克铝/克干重时生物累积能力受到抑制。从环境中去除铝后,轮藻藻体中的累积占变异的58%。实验结果表明,在湖泊的高强度修复中使用的铝浓度对轮藻有负面影响。