Pennsylvania State University - Greater Allegheny, 4000 University Drive, McKeesport, PA 15132, USA.
Aquat Toxicol. 2013 Sep 15;140-141:242-8. doi: 10.1016/j.aquatox.2013.06.009. Epub 2013 Jun 20.
Wood frogs (Rana sylvatica) were exposed to aluminum (Al; 10, 100, 500, 1000, or 2000 μgL(-1)) or copper (Cu; 1, 10, 50, 100, 200 μgL(-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 μgL(-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 μgL(-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 μgL(-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.
林蛙(Rana sylvatica)从幼虫期开始至变态完成(43-102 天)一直暴露在 pH 值为 4.70 的环境中,接触的物质有铝(Al;10、100、500、1000 或 2000μgL(-1)) 或铜(Cu;1、10、50、100、200μgL(-1))。在整个幼虫发育期内,对死亡率、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率进行了观察。仅观察到一个畸形病例,除最高 Cu 浓度(死亡率为 33%)外,所有浓度下的死亡率均≤10%。所有幸存的幼虫都成功完成了变态,但两种金属都对生长和发育产生了显著影响,其中 Cu 的影响最为明显。在最高 Al 浓度(2000μgL(-1))下,孵化后 20 天(DPH)幼虫体重显著降低(比对照组低 17%),达到后肢(HL)、前肢(FL)和尾部吸收(TR)阶段的时间显著延长(比对照组长 9-10 天)。暴露于三种最高浓度 Cu(50、100、200μgL(-1))的幼虫体重在 20 DPH 时降低了 30-34%。暴露于这些浓度还导致达到 HL、FL 和 TR 阶段的时间增加,最高浓度的幼虫达到这些阶段需要 21-29 天的时间。暴露于 10μgL(-1)Cu 的幼虫达到 FL 和 TR 发育阶段的时间也较长,与对照组相比,所有 Cu 浓度都增加了两天以上的尾部吸收时间。虽然 Al 唯一观察到的影响是在一个可能没有生态相关性的浓度下,但结果表明,在环境现实水平下,Cu 可能会产生重大的生物学影响,从而影响个体适应性和种群水平的过程。