Ecochemistry Laboratory, Institute for Applied Ecology, University of Canberra, Canberra, ACT 2601, Australia.
Ecotoxicology. 2017 Apr;26(3):415-434. doi: 10.1007/s10646-017-1774-7. Epub 2017 Mar 22.
Metal uptake and induced toxic effects on Hyridella australis were investigated by establishing 28 day exposure-dose-response relationships (EDR) of transplanted H. australis at four sites along a sediment metal contamination gradient in the mine affected Molonglo River, NSW. Laboratory exposure of this organism to the same sediments, collected from in situ sites, was run concurrently. Metal concentrations in whole organisms, individual tissues and sub-cellular tissue fractions were measured as organism metal dose. Total antioxidant capacity (TAOC), lipid peroxidation (MDA) and lysosomal membrane destabilisation (LMS) were measured as biological responses. H. australis accumulated significantly higher tissue zinc concentrations compared to the other metals. In situ organisms at the mine affected sites accumulated more metals than organisms in laboratory microcosms. Accumulated zinc, cadmium and the total metal concentrations in whole organism tissues reflected exposure-dose relationships. Sub-cellular analysis showed that most of the accumulated metals, both in the field and laboratory exposed organisms, were detoxified over 28 days exposure. Clear exposure and dose dependent responses of decreased TAOC and measurable increases in MDA and LMS with increased metal exposure and dose were evident in H. australis caged in the river. In contrast, a dose-response relationship was only evident for cadmium in laboratory exposed organisms. Organisms caged at mine affected sites showed stronger EDR relationships than those exposed in laboratory microcosms as they were exposed to additional sources of dissolved zinc and cadmium. Exposure in laboratory microcosms underestimated metal uptake and effects, thus assessment of metal contaminated sediments should be undertaken "in situ".
采用建立金属污染物沿莫朗格罗河沉积物污染梯度的四个采样点的 28 天暴露剂量-反应关系(EDR),研究了金属在澳大利亚扁蜉蝣中的摄取及其诱导的毒性效应。同时,还进行了从原位采集的同种沉积物对该生物进行的实验室暴露实验。将生物体内的金属浓度作为金属剂量来测量整体生物、个体组织和亚细胞组织部分的金属浓度。总抗氧化能力(TAOC)、脂质过氧化(MDA)和溶酶体膜不稳定(LMS)作为生物响应进行测量。与其他金属相比,澳大利亚扁蜉蝣组织中积累的锌浓度明显更高。矿区受影响地点的原位生物比实验室微宇宙中的生物积累了更多的金属。在实验室和现场暴露的生物组织中,积累的锌、镉和总金属浓度反映了暴露剂量关系。亚细胞分析表明,在 28 天暴露期间,大多数在野外和实验室暴露的生物中积累的金属都被解毒。在河流中笼养的澳大利亚扁蜉蝣中,随着金属暴露和剂量的增加,TAOC 明显降低,MDA 和 LMS 可测量增加,表明存在明显的暴露和剂量依赖性反应。相比之下,只有在实验室暴露的生物中才观察到镉的剂量反应关系。在矿区受影响地点暴露的生物比在实验室微宇宙中暴露的生物表现出更强的 EDR 关系,因为它们接触到了额外的溶解锌和镉来源。在实验室微宇宙中的暴露低估了金属的摄取和效应,因此对金属污染沉积物的评估应该在“原位”进行。