Great Lakes Environmental and Molecular Sciences Center, Department of Biological Sciences, Western Michigan University, Kalamazoo, MI 49008, USA.
Aquat Toxicol. 2011 Aug;104(3-4):243-53. doi: 10.1016/j.aquatox.2011.04.021. Epub 2011 May 6.
Six studies were performed regarding the effects of atrazine, the most frequently detected pesticide in fresh water in the US, on developing Xenopus laevis tadpoles exposed 5 days post-hatch through Nieuwkoop Faber Stage 62. The levels of atrazine tested included those potentially found in puddles, vernal ponds and runoff soon after application (200 and 400 μg/L) and a low level studied by a number of other investigators (25 μg/L). One study tested 0, 25 and 200 μg/L, another tested 0, 200 and 400 μg/L, while the remaining four studies tested 0 and 400 μg/L. During all exposures, mortality, growth, metamorphosis, sex ratio, fat body (a lipid storage organ) size and liver weights, both relative to body weight, were evaluated. In selected studies, feeding behavior was recorded, livers and fat bodies were histologically evaluated, liver glycogen and lipid content were determined by image analysis, and immunohistochemical detection of activated caspase-3 in hepatocytes was performed. The NOEC was 25 μg/L. None of these exposure levels changed sex ratios nor were intersex gonads noted, however, no definitive histological evaluation of the gonads was performed. Although a marginal increase in mortality at the 200 μg/L level was noted, this was not statistically significant. Nor was there an increase in mortality at 400 μg/L versus controls. At the 400 μg/L level, tadpoles were smaller than controls by 72 h of exposure and remained smaller throughout the entire exposure. Appetite was not decreased at any exposure level. Slowed metamorphosis was noted only at 400 μg/L in two of five studies. Livers were significantly smaller in the study that tested both 200 and 400 μg/L, yet no pathological changes or differences in glycogen or lipid stores were noted. However, livers from 400 μg/L exposed tadpoles had higher numbers of activated caspase-3 immunopositive cells suggesting increased rates of apoptosis. Fat body size decreased significantly after exposure to 200 and 400 μg/L although these organs still contained some lipid and lacked any pathology. Since this was noted across all studies, it was considered the most sensitive indicator of atrazine exposure measured. The changes noted in body and organ size at 200 and 400 μg/L atrazine indicated exposure throughout development compromised the tadpoles. Significant reductions in fat body size could potentially decrease their ability to survive the stresses of metamorphosis or reduce reproductive fitness as frogs rely on stored lipids for these processes.
六项研究探讨了在美国淡水中最常检测到的农药莠去津对孵化后 5 天的非洲爪蟾(Xenopus laevis)幼体的影响,此时幼体处于尼氏发育分期(Nieuwkoop Faber Stage)62 期。所测试的莠去津浓度包括在水坑、春塘和施药后不久的径流中可能发现的浓度(200 和 400μg/L)以及一些其他研究人员研究的低浓度(25μg/L)。一项研究测试了 0、25 和 200μg/L,另一项研究测试了 0、200 和 400μg/L,而其余四项研究则测试了 0 和 400μg/L。在所有暴露期间,评估了死亡率、生长、变态、性别比例、脂肪体(脂质储存器官)大小和肝脏重量,均相对于体重进行评估。在选定的研究中,记录了摄食行为,对肝脏和脂肪体进行了组织学评估,通过图像分析测定了肝糖原和脂质含量,并对肝细胞中活化的 caspase-3 进行了免疫组化检测。无作用浓度(NOEC)为 25μg/L。这些暴露水平均未改变性别比例,也未观察到间性性腺,但对性腺未进行明确的组织学评估。尽管在 200μg/L 水平观察到死亡率略有增加,但无统计学意义。在 400μg/L 水平与对照组相比,死亡率也没有增加。在 400μg/L 水平,暴露 72 小时后,幼体比对照组小,整个暴露过程中一直保持较小。在任何暴露水平下,食欲都没有下降。在五项研究中的两项研究中仅观察到在 400μg/L 时变态速度减慢。在同时测试了 200 和 400μg/L 的研究中,肝脏明显较小,但未观察到病理变化或糖原或脂质储存的差异。然而,暴露于 400μg/L 的幼体的肝脏中活化的 caspase-3 免疫阳性细胞数量增加,提示凋亡率增加。尽管这些器官仍含有一些脂质且缺乏任何病理变化,但脂肪体大小在暴露于 200 和 400μg/L 莠去津后显著减小。由于这在所有研究中均有观察到,因此被认为是测量莠去津暴露最敏感的指标。在 200 和 400μg/L 莠去津的身体和器官大小的变化表明,在整个发育过程中暴露会损害幼体。脂肪体大小的显著减小可能会降低它们在变态过程中应对压力的能力,或者降低作为青蛙在这些过程中依赖储存脂质的繁殖能力。