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AN IN SITU TOXICITY IDENTIFICATION EVALUATION METHOD PART Ⅱ: FIELD VALIDATION

机译:一种原位毒性鉴定方法,第二部分:现场验证

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When sediments are found to be toxic usually there is a mixture of chemicals present. Often it is important to establish which chemicals contribute to the toxicity. Establishing causality can be difficult and often requires fractionation with subsequent toxicity testing. The sample collection and manipulation process can alter chemical bioavailability and toxicity. An in situ toxicity identification evaluation (iTIE) chamber is described that was placed in sediments and fractionated pore-water chemicals into nonpolar chemicals, metals, and ammonia-type groups. This method was field tested and compared to the laboratory-based, U.S. Environmental Protection Agency (U.S. EPA) toxicity identification evaluation (TIE) method. Field studies were performed at three sites contaminated primarily with polycyclic aromatic hydrocarbons (PAHs) (Little Scioto River, OH, USA), polychlorinated bi-phenyls (PCBs) (Dicks Creek, OH, USA), and chlorobenzenes (Sebasticook River, ME, USA). Both the iTIE and the U.S. EPA TIE methods used Daphnia magna in 24-h exposures. Although the iTIE and TIE were conducted on sediments from the same location, there was significantly more toxicity observed in the iTIE testing. The dominant chemical classes were separated by the iTIE method and revealed which fractions contributed to toxicity. The loss of toxicity in the TIE approach did not allow for subsequent fractionation and stressor identification. Advantages of the iTIE over the TIE method were greater sensitivity and ability to detect causative toxic chemical fractions; lack of sediment collection and subsequent manipulation; and, thus, reduction in potential artifacts, more realistic exposure with slow, continual pore-water renewal in situ, ability to evaluate pore waters in sandy or rocky substrates where pore waters are difficult to collect, and a quicker phase Ⅰevaluation. Limitations of the iTIE method as compared to the TIE methods were extensive pretest assembly process, fewer phase Ⅰ fractionation possibilities, and restriction to shallow waters. The results of these studies suggest that the iTIE method provides a more accurate and sensitive evaluation of pore water toxicity than the laboratory TIE method.
机译:当发现沉积物有毒时,通常会存在多种化学物质的混合物。通常重要的是确定哪些化学物质会引起毒性。建立因果关系可能很困难,并且经常需要进行分级,随后进行毒性测试。样品的收集和处理过程可以改变化学生物利用度和毒性。描述了一个原位毒性鉴定评估(iTIE)室,该室放置在沉积物中,并将孔隙水化学物质分为非极性化学物质,金属和氨类。该方法经过现场测试,并与基于实验室的美国环境保护署(U.S. EPA)毒性鉴定评估(TIE)方法进行了比较。在三个主要被多环芳烃(PAHs)(美国俄亥俄州Little Scioto River),多氯联苯(PCBs)(美国俄亥俄州Dicks Creek)和氯苯(美国密苏里州塞巴斯蒂克库克河)污染的地点进行了实地研究。美国)。 iTIE和美国EPA TIE方法都在24小时暴露中使用了水蚤(Daphnia magna)。尽管iTIE和TIE在同一位置的沉积物上进行,但在iTIE测试中观察到的毒性明显更高。主要化学类别通过iTIE方法进行了分离,并揭示了哪些部分造成了毒性。 TIE方法中毒性的损失不允许进行后续分级分离和应激源鉴定。与TIE方法相比,iTIE的优势在于灵敏度更高,并且能够检测出有毒化学成分。缺乏沉淀物收集和后续处理;因此,减少了潜在的人为因素,通过缓慢,连续的原位更新孔隙水实现了更真实的曝光,能够评估难以收集孔隙水的沙质或岩石质基质中的孔隙水,并且能够更快地进行Ⅰ期评估。与TIE方法相比,iTIE方法的局限性在于广泛的预测试组装过程,较少的Ⅰ相分馏可能性以及对浅水的限制。这些研究的结果表明,与实验室TIE方法相比,iTIE方法可提供对孔水毒性的更准确和敏感的评估。

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