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CONTROLLED RELEASE EXPERIMENTS WITH NONYLPHENOL IN AQUATIC MICROCOSMS

机译:壬基酚在水生微生物中的受控释放实验

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A method of controlled release of technical nonylphenol (tNP) was developed to simulate realistic exposure in ecotox-icological studies on aquatic organisms. The direct addition of tNP from an aqueous stock solution into 50 ml of water led to a concentration decrease of 80 to 90% weight/volume (w/v) from nominal values within 48 h. The inclusion of tNP in semipermeable low-density polyethylene (LDPE) lay-flat tubing (controlled-release devices [CRDs]) of different length allowed a continuous release into pure water at a rate of about 30 μg/cm~2/d. Using CRDs in aquaria containing 15 L of 63-μm-filtered lake water, eight different concentrations with maxima between 38.1 and 326.7 μg/L were maintained for 11 d. During a second experiment in 15-L aquaria, five replicates of three concentrations were maintained using CRDs of the same length. Concentrations after 38 d varied between 0.1 and 6.7, 26.1 and 41.9, and 49.9 and 76.0 μg/L. In aquatic microcosms containing 230 L of lake water, a natural plankton community, 50 L of sediment, and macrophytes, seven different tNP concentrations (maxima 11-120.1 μg/L) were maintained over 45 d using CRDs of different length. They were replaced after 14 and 25 d because release of tNP was slower than predicted from laboratory experiments. Concentrations in the top 1-cm sediment layer were on average 19 times higher during the dosing period than concentrations in the water at the same time. In the sediments, different levels of applications led to concentrations that differed less distinctly than in the water. This method is suitable for exposing aquatic organisms continuously to constant, ecologically relevant concentrations of NP and represents an improvement over previous dosing methods in which exposure varied.
机译:开发了一种控制性释放壬基酚(tNP)的方法,以模拟对水生生物进行生态毒理学研究时的实际暴露。将tNP从水溶液中直接添加到50 ml水中导致浓度在48小时内从标称值降低80%至90%重量/体积(w / v)。在不同长度的半渗透性低密度聚乙烯(LDPE)扁平管(控释装置[CRD])中包含tNP可以以约30μg/ cm〜2 / d的速率连续释放到纯水中。在包含15升63微米过滤湖水的水族箱中使用CRD,可将8种不同浓度的最大浓度保持在38.1至326.7微克/升之间,持续11天。在15升水族箱的第二个实验中,使用相同长度的CRD保持了三个浓度的五个重复。 38 d后的浓度在0.1和6.7、26.1和41.9以及49.9和76.0μg/ L之间变化。在包含230 L湖泊水,天然浮游生物群落,50 L沉积物和大型植物的水生微观世界中,使用不同长度的CRD在45 d内保持了7种不同的tNP浓度(最大11-120.1μg/ L)。由于tNP的释放比实验室实验预测的慢,因此在14和25天后将它们替换。在投配期间,顶部1厘米沉积物层中的浓度平均比同时水中的浓度高19倍。在沉积物中,不同的施用水平导致其浓度的差异不如在水中。该方法适用于将水生生物连续暴露于恒定的,与生态相关的NP浓度,并且比以前的暴露量有所变化的给药方法有所改进。

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