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The fate and effects of Triclosan in the lower Hudson River estuary.

机译:三氯生在哈德逊河下游河口的命运和影响。

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This study examined the dispersal, fate and ecological effects of Triclosan in the lower Hudson River estuary. Four major concerns regarding this compound were assessed; (1) the overall accumulation and degradation of Triclosan within estuarine sediments; (2) the correlation between Triclosan with carbon (organic and inorganic); (3) the factors determining the overall distribution and concentration of Triclosan throughout the estuary; and (4) the potential toxicological effects of Triclosan on estuarine micro-organisms.;Triclosan concentrations in sediments from the lower Hudson River estuary ranged from 2-88 ng/g. The vertical profile of Triclosan in a one-meter sediment vibracore (dated using Cesium-137) indicated that Triclosan has been preserved in sediments dating back to the mid 1960's, when it was first released. In addition, there is limited evidence of a negative correlation between the concentrations of Triclosan and organic carbon with no evidence of a correlation between inorganic carbon and Triclosan. This lack of correlation between Triclosan and carbon may reflect the relative uniform organic and inorganic carbon concentrations measured in the sediment cores collected throughout the estuary, and variations in Triclosan's input function via CSOs and treated wastewater discharges.;The average water column concentration of Triclosan for the lower Hudson River estuary is 3+/-2 ng/1 and is consistent with a dilution of average wastewater concentrations with freshwater and seawater. The empirically derived partitioning coefficient (using average sediment concentrations of 26+/-11 ng/g) for Triclosan the kd ∼ 104, which is similar to theoretical and laboratory estimates of the kd. Photodegradation and biological uptake should be evaluated on a site by site basis.;This study demonstrates that the current concentration aqueous and particulate bound Triclosan do not pose a risk to natural communities in the lower estuary. However, chlorophyll a concentrations in algal communities were significantly reduced by 20--30% when phytoplankton were exposed to 20 and 200 ng/g concentrations of aqueous Triclosan for 12--24 h (p 0.05). Additionally the estimated effective concentration (EC50 ) for laboratory bacteria exposed to aqueous Triclosan for less than 1 hour is 13 ng/l. There was no effect, however, from acutely exposing bacteria to particulate-bound Triclosan (15--34 ng/g).
机译:这项研究研究了三氯生在哈得逊河下游河口的扩散,命运和生态影响。评估了与该化合物有关的四个主要问题; (1)河口沉积物中三氯生的总体积累和降解; (2)三氯生与碳(有机和无机)之间的关系; (3)决定三氯生在河口整体分布和浓度的因素; (4)三氯生对河口微生物的潜在毒理作用。哈德逊河下游河口沉积物中三氯生的浓度范围为2-88 ng / g。三氯生在一个一米长的沉积物颤振岩中(使用铯137测年)的垂直剖面表明,三氯生在最早释放到1960年代中期的沉积物中得到了保存。另外,仅有有限的证据表明三氯生和有机碳的浓度之间存在负相关,而没有证据表明无机碳和三氯生之间存在相关性。三氯生与碳之间缺乏相关性可能反映了在整个河口收集的沉积物中测得的相对均匀的有机碳和无机碳浓度,以及三氯生通过CSO和处理后的废水排放的输入功能的变化。哈德逊河下游河口为3 +/- 2 ng / 1,这与淡水和海水对平均废水浓度的稀释是一致的。根据经验得出的三氯生kd〜104的分配系数(使用平均沉积物浓度为26 +/- 11 ng / g)与kd的理论和实验室估计相似。光降解和生物摄取应逐个地点进行评估。这项研究表明,目前水和微粒结合三氯生的浓度不会对河口下游的自然群落构成威胁。但是,当浮游植物暴露于20和200 ng / g浓度的三氯生水溶液中12--24小时时,藻类群落中的叶绿素a浓度显着降低了20--30%(p <0.05)。另外,暴露于三氯生水溶液中少于1小时的实验室细菌的估计有效浓度(EC50)为13 ng / l。但是,将细菌急性暴露于结合颗粒的三氯生(15--34 ng / g)并没有影响。

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