Widianarko B, Kuntoro F X, Van Gestel C A, Van Straalen N M
Faculty of Agricultural Technology, Soegijapranata Catholic University, Semarang, Indonesia.
Environ Toxicol Chem. 2001 Apr;20(4):763-8.
Levels of toxic substances released into the environment are often highly variable and fluctuate over time. The present study deals with a simple type of time-variable exposure, diluted pulse. We determined toxicokinetic parameters of zinc in guppy fish (Poecilia reticulata) and evaluated the applicability of a toxicokinetics-based survival model developed earlier. In the toxicokinetics experiment, zinc was rapidly taken up and released again; the half-life in fish was only 1.5 d. In the toxicity experiments with diluted-pulse exposure, survival leveled off to a baseline level, which in accordance with the model is explained by the dilution of zinc. The model fitted reasonably well for the lower initial concentrations but tended to overestimate survival rates at the higher concentrations. Toxicokinetic parameters estimated from changes in survival were close to values estimated from measured zinc concentrations in water. Elimination rates during pulse exposure varied from 0.434 to 0.488 d(-1) and corresponded very well to the elimination rate during constant exposure (0.463 d(-1)). Ultimate LC50 values were estimated as 6.40 and 9.10 mg/L. These results suggest that toxicity experiments with a simple, time-varying exposure can be used as an alternative to conventional, constant-exposure experiments. Toxicokinetic parameters and toxicological endpoints can still be estimated in static bioassays with decreasing exposure if the concentration in the medium is measured. At the same time, diluted-pulse experiments may simulate exposure from discharges in the field better than constant-exposure experiments.
释放到环境中的有毒物质水平通常变化很大,且会随时间波动。本研究涉及一种简单的随时间变化的暴露类型,即稀释脉冲。我们测定了孔雀鱼(Poecilia reticulata)体内锌的毒代动力学参数,并评估了先前开发的基于毒代动力学的生存模型的适用性。在毒代动力学实验中,锌被迅速吸收并再次释放;鱼体内的半衰期仅为1.5天。在稀释脉冲暴露的毒性实验中,存活率趋于稳定在基线水平,根据模型,这是由锌的稀释来解释的。该模型对较低初始浓度拟合得较好,但在较高浓度时往往高估存活率。根据存活率变化估算的毒代动力学参数与根据水中测得的锌浓度估算的值接近。脉冲暴露期间的消除率在0.434至0.488 d⁻¹之间,与持续暴露期间的消除率(0.463 d⁻¹)非常吻合。最终LC50值估计为6.40和9.10 mg/L。这些结果表明,简单的随时间变化的暴露毒性实验可作为传统持续暴露实验的替代方法。如果测量介质中的浓度,在暴露量降低的静态生物测定中仍可估算毒代动力学参数和毒理学终点。同时,稀释脉冲实验可能比持续暴露实验更好地模拟现场排放的暴露情况。