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TOXIC EFFECTS OF POLYCHLORINATED BIPHENYL BIOACCUMULATION IN SEA URCHINS EXPOSED TO CONTAMINATED SEDIMENTS

机译:多氯联苯生物累积在污染的底泥中对海胆的毒性作用

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The uptake patterns and toxicity of polychlorinated biphenyl (PCB) congeners in the white sea urchin, Lytechinuspictus, on exposure to contaminated sediments were investigated. First-order modeling of uptake of the 10 most abundant PCB congeners or domains (containing more than one coeluting congener) by L. pictus indicated that a 35-d exposure was insufficient to reach steady state. Bioaccumulation of PCBs in sea urchins exhibited substantial difference between field and amended sediments, suggesting that caution must be exercised in sample preparation. Some evidence was observed of dependence of measured biota-sediment accumulation factors (BSAFs) on K_(ow), indicating that equilibrium partitioning of PCBs may not always be achieved between biota lipid, sediment organic carbon, and water. Survival of L. pictus was unaffected by exposure to field and amended sediments with PCB concentrations varying more than three orders of magnitude. The growth measures (diameter, wt, and gonad wt) were significantly reduced in L. pictus exposed to San Diego Bay ([SDB]; San Diego, CA, USA) sediment, whereas they were relatively unaffected after exposure to amended sediments (with much higher PCB concentrations than SDB sediment) prepared from a New Bedford Harbor (MA, USA) sediment. The toxic effects as measured by the growth rates in L. pictus were likely attributable to polycyclic aromatic hydrocarbons (PAHs), which were elevated in SDB sediment (7.3 μg/g), rather than PCBs.
机译:研究了白海胆(Lytechinuspictus)中多氯联苯(PCB)同源物在暴露于受污染沉积物中的吸收方式和毒性。一氧化碳对L. pictus吸收10个最丰富的PCB同类物或域(包含一个以上共洗脱的同类物)的一级建模表明,暴露35天不足以达到稳态。海胆中PCBs的生物富集表现出田间沉积物和修正沉积物之间的实质性差异,这表明在样品制备中必须谨慎行事。观察到一些证据表明所测量的生物沉积物累积因子(BSAFs)依赖于K_(ow),这表明在生物脂类,沉积有机碳和水之间不一定总是实现PCB的平衡分配。暴露于野外和修正的PCB浓度变化超过三个数量级的沉积物不会影响L. pictus的存活。暴露于圣地亚哥湾(SDB);美国加利福尼亚州圣地亚哥的L. pictus的生长指标(直径,重量和性腺重量)显着降低,而暴露于经修正的沉积物(有比从新贝德福德港(美国马萨诸塞州)沉积物中制备的SDB沉积物高得多的PCB浓度。用苦瓜的生长速率来衡量的毒性作用可能归因于多环芳烃(PAH),其在SDB沉积物中(7.3μg/ g)升高,而不是PCBs。

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