National Institute of Water and Atmospheric Research, PO Box 11-111, Hamilton, New Zealand.
Aquat Toxicol. 2010 Sep 15;99(4):507-13. doi: 10.1016/j.aquatox.2010.07.004. Epub 2010 Jul 7.
The ability to recover from environmental perturbations is essential for the sustainability of ecological systems. Variation in the ability of individual organisms to recover from stressors influences overall resilience at higher levels of biological organisation. Such variation is likely to be genetically based. To investigate this hypothesis we examined the genetic basis of both resistance to and recovery from zinc, a common stormwater contaminant, in the New Zealand freshwater clam Sphaerium novaezelandiae. We undertook a 4-day toxicity test using zinc exposure concentrations ranging from 0.31 to 5.00 mg/L. These concentrations are consistent with levels recorded in urban streams during the first flush of storms. As our response measures we recorded mortality at the end of the 4-day period, as well as reburial rate (time to rebury in sediment) following the 4-day exposure ("exposure") and then again following a 24h period of recovery ("recovery"). Genotypic composition was determined using allozyme electrophoresis, focusing on the enzyme Pgm (phosphoglucomutase). Overall, a significant effect on mortality was observed, with an average value of 78.6% (+/-7.9) at 5.00 mg/L zinc, compared with only 3.8% (+/-3.8) mortality at 0.31 mg/L zinc. An inhibition concentration (IC(50)) of 1.16 mg/L was recorded, when considered regardless of genotypes. There was no significant genotype-specific differences in mortality. There was a significant difference in reburial rates across all genotypes at the end of the exposure period with an average reburial time of 83.0+/-3.6 min at 5.00 mg/L (22.8+/-2.9 min at 0.31 mg/L). There was a near-significant (p=0.058) difference in time taken to rebury when comparing between genotypes at the "exposure" stage for any concentration. Significant differences in reburial rates across all genotypes were also observed following 24h recovery. When individual genotypes were compared at this stage, genotype 33 reburied on average significantly faster (24.0+/-4.5 min) than other genotypes at the highest exposure concentration and was also significantly faster than genotype 44 at 1.25mg/L. Studies investigating the genetic basis to recovery from stressors at an individual level are limited. This study has shown that populations of organisms display genetically-based variation in their ability to recover from zinc exposure in the laboratory and that such variation is linked to a physiological trait (reburial). The potential effects on other life history traits (e.g. feeding), possible physiological trade-offs and the implications for such variation on ecosystem resilience requires further investigation.
从环境扰动中恢复的能力对于生态系统的可持续性至关重要。个体生物从胁迫中恢复的能力的变化会影响更高层次生物组织的整体恢复力。这种变化可能是基于遗传的。为了验证这一假说,我们研究了新西兰淡水蛤 Sphaerium novaezelandiae 对锌的抗逆性和恢复能力的遗传基础,锌是一种常见的雨水污染物。我们进行了为期 4 天的毒性测试,使用的锌暴露浓度范围为 0.31 至 5.00mg/L。这些浓度与城市溪流在风暴初期记录的水平一致。作为我们的反应措施,我们记录了 4 天暴露期结束时的死亡率,以及暴露期结束后重新掩埋率(重新掩埋到沉积物中的时间),然后再记录 24 小时恢复期后的重新掩埋率。基因型组成通过同工酶电泳确定,重点是酶 Pgm(磷酸葡萄糖变位酶)。总体而言,在 5.00mg/L 锌的情况下,死亡率观察到显著影响,平均为 78.6%(+/-7.9),而在 0.31mg/L 锌的情况下,死亡率仅为 3.8%(+/-3.8)。记录到的抑制浓度(IC(50))为 1.16mg/L,无论基因型如何,均考虑在内。在死亡率方面,没有发现基因型特异性差异。在暴露期结束时,所有基因型的重新掩埋率均存在显著差异,在 5.00mg/L 时的平均重新掩埋时间为 83.0+/-3.6 分钟(在 0.31mg/L 时为 22.8+/-2.9 分钟)。在任何浓度下,比较基因型时,暴露阶段的重新掩埋时间都存在接近显著的差异(p=0.058)。在 24 小时恢复期后,所有基因型的重新掩埋率也存在显著差异。在这个阶段比较单个基因型时,基因型 33 在最高暴露浓度下平均重新掩埋速度明显更快(24.0+/-4.5 分钟),并且在 1.25mg/L 时也明显快于基因型 44。研究个体水平应激恢复的遗传基础的研究有限。本研究表明,生物体种群在实验室中从锌暴露中恢复的能力存在基于遗传的差异,这种差异与生理特征(重新掩埋)有关。对其他生活史特征(如摄食)的潜在影响、可能的生理权衡以及这种差异对生态系统恢复力的影响需要进一步研究。