铬在寡毛纲动物中的毒代动力学

Toxicokinetics of Chromium in (Oligochaeta).

作者信息

Santos Fátima C F, Verweij Rudo A, van Gestel Cornelis A M, Amorim Mónica J B

机构信息

Department of Biology & CESAM, University of Aveiro, 3810-193 Aveiro, Portugal.

Department of Ecological Science, Faculty of Science, Vrije Universiteit Amsterdam, De Boelelaan 1085, 1081 HV Amsterdam, The Netherlands.

出版信息

Toxics. 2022 Feb 9;10(2):82. doi: 10.3390/toxics10020082.

Abstract

Chromium is naturally occurring, but emission from anthropogenic sources can lead to increased soil concentrations. Information on its toxicokinetics is essential in order to understand the time needed to reach toxicity and the mechanisms of uptake/elimination. In this study the toxicokinetics of Cr(III) was evaluated using the soil standard species . The animals were exposed to 180 mg Cr/kg dry soil, a sublethal concentration, in LUFA 2.2 natural soil. OECD guideline 317 was followed, with a 14-day uptake phase in spiked soil followed by a 14-day elimination in clean soil. Exposure to Cr led to fast uptake and elimination, with = 0.012 kg/kg/day and = 0.57 day. The bioaccumulation factor was 0.022, and DT for elimination was 1.2 days. The concentration of Cr reached an internal equilibrium in the animals after 10 days. Transfer to clean soil allowed body Cr concentrations to return to background levels after approximately 7 days. seemed able to efficiently regulate internal Cr concentrations by actively eliminating Cr (an essential element). Although and deviated from the values reported in other studies for other soil invertebrates, the bioaccumulation factors were similar. These findings show the importance of toxicokinetic studies in evaluating toxicity based on internal metal concentrations that can more accurately represent the bioavailable concentration.

摘要

铬是天然存在的,但人为源排放会导致土壤中铬浓度升高。了解其毒代动力学信息对于理解达到毒性所需的时间以及吸收/消除机制至关重要。在本研究中,使用土壤标准物种评估了Cr(III)的毒代动力学。将动物暴露于LUFA 2.2天然土壤中180 mg Cr/kg干土的亚致死浓度下。遵循经合组织准则317,在加标土壤中进行14天的吸收阶段,然后在清洁土壤中进行14天的消除阶段。暴露于铬导致快速吸收和消除,吸收速率常数为0.012 kg/kg/天,消除半衰期为0.57天。生物累积因子为0.022,消除的DT为1.2天。10天后动物体内的铬浓度达到内部平衡。转移到清洁土壤后,大约7天后体内铬浓度恢复到背景水平。(某种生物)似乎能够通过主动消除铬(一种必需元素)来有效调节体内铬浓度。尽管吸收速率常数和消除半衰期与其他研究中报道的其他土壤无脊椎动物的值有所偏差,但生物累积因子相似。这些发现表明毒代动力学研究在基于能够更准确代表生物可利用浓度的内部金属浓度评估毒性方面的重要性。

https://cdn.ncbi.nlm.nih.gov/pmc/blobs/b139/8876269/21e765d0fbda/toxics-10-00082-g001.jpg

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