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首页> 外文期刊>Aquatic Toxicology >Effects of chronic aluminum and copper exposure on growth and development of wood frog (Rana sylvatica) larvae
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Effects of chronic aluminum and copper exposure on growth and development of wood frog (Rana sylvatica) larvae

机译:长期铝和铜暴露对木蛙(Rana sylvatica)幼虫生长发育的影响

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Wood frogs (Rana sylvatica) were exposed to aluminum (Al; 10, 100, 500, 1000, or 2000 mu g L-1) or copper (Cu; 1, 10, 50, 100, 200 mu g L-1) at a pH of 4.70 from the beginning of the larval period through the completion of metamorphosis (range = 43-102 days). Observations on mortality, malformation, time to reach specific developmental stages, body mass at these stages, and metamorphic success were made throughout the larval developmental period. Only one case of malformation was observed and mortality was <= 10% at all concentrations except the highest Cu concentration where the rate was 33%. All larvae that survived the experiment successfully completed metamorphosis, but significant effects on growth and development occurred for both metals and these were most prominent for Cu. At the highest Al concentration (2000 mu g L-1), body mass of larvae was significantly lower (reduced by 17% compared to the control) at 20 days post hatching (DPH) and the time to reach the hind-limb (HL), front-limb (FL), and tail resorption (TR) stages was significantly increased (9-10 days longer than the control). Body mass of larvae exposed to the three highest concentrations of Cu (50, 100,200 mu g L-1) was reduced by 30-34% at 20 DPH. Exposure to these concentrations also resulted in increased time to reach the HL, FL, and TR stages with larvae in the highest concentration taking 21-29 days longer to reach these stages. Larvae exposed to 10 mu g L-1 Cu also took longer to reach the FL and TR stages of development, and exposure to all Cu concentrations increased tail resorption time by more than two days compared to the control. Although the only observed effects of Al were for a concentration that is probably not ecologically relevant, results demonstrate that environmentally-realistic levels of Cu may have significant biological effects that could influence individual fitness and population-level processes. (C) 2013 Elsevier B.V. All rights reserved.
机译:木蛙(Rana sylvatica)暴露于铝(Al; 10、100、500、1000或2000μg L-1)或铜(Cu; 1,10、50、100、200μgL-1)从幼虫期开始到变态完成的pH为4.70(范围= 43-102天)。在整个幼虫的发育阶段,观察死亡率,畸形,达到特定发育阶段的时间,这些阶段的体重以及变态成功的情况。仅观察到一个畸形病例,并且在所有浓度下死亡率均≤10%,但最高的Cu浓度除外,死亡率为33%。在实验中幸存的所有幼虫均成功完成了变态,但是两种金属均对生长和发育产生了显着影响,而对于铜而言,这些最显着。在最高的铝浓度(2000μg L-1)下,在孵化后(DPH)和到达后肢的时间(HL),幼虫的体重显着降低(与对照组相比降低了17%) ),前肢(FL)和尾巴吸收(TR)阶段显着增加(比对照组长9-10天)。在20 DPH下,暴露于三种最高浓度的Cu(50、100,200μgL-1)的幼虫的体重降低了30-34%。暴露于这些浓度还会导致到达HL,FL和TR阶段的时间增加,而幼虫处于最高浓度则需要更长的时间21-29天才能到达这些阶段。暴露于10μgL-1 Cu的幼虫也需要更长的时间才能到达FL和TR发育阶段,并且与对照相比,暴露于所有Cu浓度会使尾部吸收时间延长两天以上。尽管观察到的唯一影响是铝的浓度可能与生态无关,但结果表明,现实环境水平的铜可能具有重大的生物学效应,可能影响个体适应性和种群水平过程。 (C)2013 Elsevier B.V.保留所有权利。

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