McCarthy Ian D, Fuiman Lee A
The University of Texas at Austin, Marine Science Institute, Port Aransas, TX 78373, USA.
Aquat Toxicol. 2008 Jul 30;88(4):220-9. doi: 10.1016/j.aquatox.2008.05.001. Epub 2008 May 13.
Contaminant exposure can affect development, growth, and behaviour of fish larvae, but its effect on rates of protein synthesis and protein degradation are not known. The aim of the present study was to examine the effects of a single pulsed dose aqueous exposure to environmentally realistic levels of two contaminants, atrazine (0, 40 and 80 microgl(-1)) and malathion (0, 1 and 10 microgl(-1)), on growth and protein synthesis in red drum (Sciaenops ocellatus) larvae. Growth was assessed in terms of increase in length, weight, and protein content over an 8-day period following exposure. Rates of protein synthesis were measured by the flooding dose technique 2, 4, and 8 days after initial exposure to each contaminant by bathing larvae in seawater containing L-[2,6-(3)H] phenylalanine. Exposure to atrazine had no effect on larval growth in length, but caused marginally significant declines in growth in weight (P=0.05) and protein content (P=0.06). However, protein synthesis rates were significantly higher for atrazine-exposed larvae on days 4 (P=0.04) and 8 (P=0.01), suggesting an increase in rates of protein degradation. On day 8, the efficiency with which synthesised proteins contributed to growth was significantly lower (P=0.04) in atrazine-exposed larvae. In contrast, malathion had no significant effects on growth in length or protein content, but there were significant decreases in growth in weight over 8 days. The only other significant effect of malathion was an increase in protein synthesis on day 2 for treated larvae relative to controls. Previous work [Alvarez, M.C., Fuiman, L.A., 2005. Environmental levels of atrazine and its degradation products impair survival skills and growth of red drum larvae. Aquat. Toxicol. 74, 229-241] reported hyperactivity and increased metabolic rate in larval red drum exposed to atrazine, indicating a clear energetic cost. Our results further emphasise the energetic cost of atrazine exposure through elevated rates of protein synthesis and degradation resulting in reduced protein retention efficiency and lower growth rates. Overall, we conclude that exposure to atrazine from surface water run-off can increase the energy requirements and the larval phase duration in red drum larvae, possibly resulting in reduced survival and recruitment in cohorts exposed to atrazine.
污染物暴露会影响鱼类幼体的发育、生长和行为,但其对蛋白质合成速率和蛋白质降解速率的影响尚不清楚。本研究的目的是检测单次脉冲剂量水暴露于环境现实水平的两种污染物——阿特拉津(0、40和80微克/升)和马拉硫磷(0、1和10微克/升)对红鼓鱼(眼斑拟石首鱼)幼体生长和蛋白质合成的影响。在暴露后的8天内,根据体长、体重和蛋白质含量的增加来评估生长情况。在初次暴露于每种污染物后的第2、4和8天,通过将幼体置于含有L-[2,6-(3)H]苯丙氨酸的海水中,采用饱和剂量技术测量蛋白质合成速率。暴露于阿特拉津对幼体体长生长没有影响,但导致体重(P = 0.05)和蛋白质含量(P = 0.06)略有显著下降。然而,在第4天(P = 0.04)和第8天(P = 0.01),暴露于阿特拉津的幼体蛋白质合成速率显著更高,这表明蛋白质降解速率增加。在第8天,暴露于阿特拉津的幼体中合成蛋白质对生长的贡献效率显著更低(P = 0.04)。相比之下,马拉硫磷对体长生长或蛋白质含量没有显著影响,但在8天内体重增长显著下降。马拉硫磷的唯一其他显著影响是,与对照组相比,处理后的幼体在第2天蛋白质合成增加。先前的研究[阿尔瓦雷斯, M.C., 富伊曼, L.A., 2005. 环境水平的阿特拉津及其降解产物损害红鼓鱼幼体的生存技能和生长。水生毒理学。74, 229 - 241]报道,暴露于阿特拉津的红鼓鱼幼体活动亢进且代谢率增加,这表明存在明显的能量消耗。我们的结果进一步强调了通过提高蛋白质合成和降解速率来暴露于阿特拉津的能量消耗,这导致蛋白质保留效率降低和生长速率下降。总体而言,我们得出结论,地表水径流中的阿特拉津暴露会增加红鼓鱼幼体的能量需求和幼体阶段持续时间,可能导致暴露于阿特拉津的群体中存活率和补充率降低。