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溶解有机物调节大型溞对芘的吸收、生物转化和消除速率。

Dissolved organic matter modulating the uptake, biotransformation, and elimination rates of pyrene in Daphnia magna.

机构信息

Department of Environmental Toxicology, Eawag, Swiss Federal Institute of Aquatic Science and Technology, Ueberlandstrasse 133, 8600 Duebendorf, Switzerland.

出版信息

Environ Toxicol Chem. 2010 Dec;29(12):2783-91. doi: 10.1002/etc.335. Epub 2010 Oct 1.

Abstract

In the current study, the toxicokinetics of pyrene in Daphnia magna was determined in detail, and the role of dissolved organic matter (DOM) in these processes was investigated. Uptake, biotransformation, parent compound and metabolite elimination rates (k(u), k(m), k(ep), k(em)), depuration rates, bioconcentration factors (BCFs), and biological half-lives were studied in one natural humic water, in two waters made from DOM isolates, and in DOM-free artificial fresh water. The daphnids were exposed to pyrene for 24 h and depurated for another 24 h. To analyze the data, the two-compartment model was used to obtain toxicokinetic parameters, and the depuration data were analyzed by linear regression. Extensive biotransformation of pyrene resulted in high metabolite concentration in the organisms (83% of total radioactivity) after 24 h exposure. Depuration of the parent compound seemed to be biphasic: at first, depuration was rapid, but after 4 to 10 h in uncontaminated water, the disappearance rate came close to zero. After a 24-h depuration time, 7.8% of the pyrene accumulated remained in the organism. Overall, the elimination of parent compound was faster than the elimination of metabolites, which might imply inefficient excretion of water-soluble biotransformation products from daphnids. The effect of DOM on accumulation of pyrene was seen in a decreased uptake rate, indicating lower bioavailability of the compound in waters that contain high-aromaticity DOM. In the same waters, DOM significantly accelerated pyrene biotransformation and overall elimination. Altogether, DOM appears to be able to affect toxicokinetics through mechanisms that are connected to interaction with the contaminant but also directly through interaction with biotransformation systems.

摘要

在当前的研究中,详细测定了二氯二苯并对二恶英在大型溞中的毒代动力学,研究了溶解有机物(DOM)在这些过程中的作用。在一种天然腐殖水中、两种源自 DOM 分离物的水中以及无 DOM 的人工淡水,研究了摄取、生物转化、母体化合物和代谢物消除率(k(u)、k(m)、k(ep)、k(em))、净化率、生物浓缩系数(BCF)和生物半衰期。大型溞暴露于二氯二苯并对二恶英 24 h,然后再净化 24 h。为分析数据,采用双室模型获得毒代动力学参数,并通过线性回归分析净化数据。二氯二苯并对二恶英的大量生物转化导致暴露 24 h 后生物体内的代谢物浓度很高(总放射性的 83%)。母体化合物的净化似乎呈两相:最初,净化速度很快,但在未受污染的水中 4 至 10 h 后,消失速度接近零。24 h 净化后,积累的二氯二苯并对二恶英中有 7.8%仍留在生物体内。总体而言,母体化合物的消除速度快于代谢物的消除速度,这可能意味着大型溞从水中排出水溶性生物转化产物的效率较低。DOM 对二氯二苯并对二恶英积累的影响表现在摄取率降低,表明在含有高芳香度 DOM 的水中,化合物的生物利用率较低。在相同的水中,DOM 显著加速了二氯二苯并对二恶英的生物转化和整体消除。总的来说,DOM 似乎能够通过与污染物相互作用的机制以及直接通过与生物转化系统相互作用的机制来影响毒代动力学。

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