Institute for the Environment, Brunel University, Uxbridge, Middlesex UB8 3PH, United Kingdom.
Environ Toxicol Chem. 2010 Dec;29(12):2831-9. doi: 10.1002/etc.351. Epub 2010 Oct 23.
Two studies to examine the effect of waterborne clofibric acid (CA) on growth-rate and condition of rainbow trout were conducted using accepted regulatory tests (Organisation for Economic Co-operation and Development [OECD] 215). The first study (in 2005) showed significant reductions after 21 d of exposure (21-d growth lowest-observed-effect concentration [LOEC] = 0.1 µg/L, 21-d condition LOEC = 0.1 µg/L) that continued to 28 d. Growth rate was reduced by approximately 50% (from 5.27 to 2.67% per day), while the condition of the fish reduced in a concentration-dependant manner. Additionally, in a concentration-dependent manner, significant changes in relative liver size were observed, such that increasing concentrations of CA resulted in smaller livers after 28-d exposure. A no-observed-effect concentration (NOEC) was not achieved in the 2005 study. An expanded second study (in 2006) that included a robust bridge to the 2005 study, with four replicate tanks of eight individual fish per concentration, did not repeat the 2005 findings. In the 2006 study, no significant effect on growth rate, condition, or liver biometry was observed after 21 or 28 d (28-d growth NOEC = 10 µg/L, 28-d condition NOEC = 10 µg/L), contrary to the 2005 findings. We do not dismiss either of these findings and suggest both are relevant and stand for comparison. However, the larger 2006 study carries more statistical power and multiple-tank replication, so probably produced the more robust findings. Despite sufficient statistical power in each study, interpretation of these and similar studies should be conducted with caution, because much significance is placed on the role of limited numbers of individual and tank replicates and the influence of control animals.
进行了两项研究,以检验水传播的氯贝酸(CA)对虹鳟生长速度和健康状况的影响,采用的是公认的监管测试(经济合作与发展组织[OECD] 215)。第一项研究(2005 年)表明,在 21 天的暴露期后,生长速度显著降低(21 天生长最低观察到的效应浓度[LOEC]=0.1μg/L,21 天健康状况 LOEC=0.1μg/L),这种情况一直持续到 28 天。生长速度降低了约 50%(从每天 5.27%降至 2.67%),而鱼类的健康状况则呈浓度依赖性下降。此外,还观察到相对肝脏大小以浓度依赖的方式发生显著变化,即 CA 浓度增加导致 28 天暴露后肝脏变小。在 2005 年的研究中,没有达到无观察到效应浓度(NOEC)。一项扩展的第二项研究(2006 年),包括对 2005 年研究的稳健桥接,每个浓度有四个重复的 8 条鱼的水槽,没有重复 2005 年的发现。在 2006 年的研究中,在 21 天或 28 天后,没有观察到生长速度、健康状况或肝脏生物计量学的显著影响(28 天生长的 NOEC=10μg/L,28 天健康状况的 NOEC=10μg/L),与 2005 年的发现相反。我们并没有忽视这两个发现,认为它们都是相关的,可以进行比较。然而,规模更大的 2006 年研究具有更大的统计能力和多个水槽的重复,因此可能产生了更可靠的结果。尽管每个研究都有足够的统计能力,但对这些研究和类似研究的解释应该谨慎进行,因为大量的意义在于个体和水槽重复的数量有限,以及对照动物的影响。