首页> 外文期刊>Environmental toxicology and chemistry >EFFECT OF THE INPUT PATHWAY ON THE DISTRIBUTION OF 1,2,3,4,7-PENTACHLORODIBENZO-p-DIOXIN IN AN AQUATIC MESOCOSM
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EFFECT OF THE INPUT PATHWAY ON THE DISTRIBUTION OF 1,2,3,4,7-PENTACHLORODIBENZO-p-DIOXIN IN AN AQUATIC MESOCOSM

机译:输入途径对水生介体中1,2,3,4,7-五氯二苯并二氮杂-p-二恶英分布的影响

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The effect of the input pathway on the distribution of 1,2,3,4,7-pentachlorodibenzo-p-dioxin (P_5CDD) in small-pond mesocosms was determined by introducing ~(14)C-labeled dioxin (468 μg) into the water sorbed to sediment particles and by a surface sprayover in a water-miscible organic solvent. Rates of clearance from the water column were rapid and unrelated to the input method in either case, with pseudo-first-order half-lives (t_(1/2)) of 0.38 ± 0.19 d (r~2 = 0.81) and 0.57 ± 0.08 d (r~2 = 0.98) for the particle-sorbed and sprayover applications, respectively, over the first 24 h after input. However, redistribution pathways were strongly influenced by the route of entry of P_5CDD into the ecosystem. Ponds receiving a sprayover of P_5CDD showed higher concentrations of the dioxin in surface microlayers with larger amounts also collected in air above these ponds. Concentrations of P_5CDD in the bottom sediments of these ponds were significantly lower (0.6 ng/g dry weight) compared to concentrations in sediments of ponds receiving a sediment slurry input (1.2 ng/g dry weight). Evaluation of the results using several fugacity-based aquatic-fate models indicated that when P_5CDD entered the aquatic ecosystem in the sorbed state, sedimentation dominated its redistribution. However, with a sprayover input, film-to-water transfer, partitioning and deposition to bottom sediment, volatilization, and photolytic degradation in surface microlayers were important processes affecting the fate of P_5CDD in the mesocosm.
机译:通过将〜(14)C标记的二恶英(468μg)引入到小池体中来确定输入途径对1,2,3,4,7-五氯二苯并-p-二恶英(P_5CDD)分布的影响通过与水混溶的有机溶剂中的表面喷射吸附到沉淀颗粒的水。两种情况下,从水柱中清除的速度都很快,并且与输入方法无关,伪一阶半衰期(t_(1/2))为0.38±0.19 d(r〜2 = 0.81)和0.57在输入后的最初24小时内,对于颗粒吸附和喷涂应用分别为±0.08 d(r〜2 = 0.98)。但是,再分布途径受到P_5CDD进入生态系统的途径的强烈影响。接受P_5CDD喷洒的池塘在表面微层中显示出较高的二恶英浓度,在这些池塘上方的空气中也收集到大量的二恶英。与接受沉积物泥浆输入的池塘(1.2 ng / g干重)相比,这些池塘底部沉积物中的P_5CDD浓度要低得多(0.6 ng / g干重)。使用几种基于逸度的水生命运模型对结果进行的评估表明,当P_5CDD以吸附状态进入水生生态系统时,沉积物决定了其再分配。但是,通过喷洒输入,膜到水的转移,分配和沉积到底部沉积物,挥发和表面微层中的光解降解是影响中膜P_5CDD命运的重要过程。

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