The University of Queensland, National Research Centre for Environmental Toxicology, Brisbane, Australia; Cooperative Research Centre for Contamination Assessment and Remediation of the Environment, Callaghan, NSW 2308, Australia.
Cooperative Research Centre for Contamination Assessment and Remediation of the Environment, Callaghan, NSW 2308, Australia; Global Centre for Environmental Remediation, The University of Newcastle, Callaghan, NSW 2308, Australia.
Chemosphere. 2016 Mar;147:444-50. doi: 10.1016/j.chemosphere.2015.12.091. Epub 2016 Jan 15.
Recent decades have seen a growing popularity of in vitro bioaccessibility being utilised as a screening tool in human health risk assessment. However the existing bioaccessibility studies only focus on single contaminant. Considering human are likely to ingest multi-contaminants, these contaminants could interact within human gastrointestinal tract which may lead to an increase or decrease in bioaccessibility. In this study, seven different types of soil were spiked with arsenic (As) or cadmium (Cd) and aged for one year. The effects of soil properties on the bioaccessibility were examined. Moreover, the interaction between As and Cd in simulated human digestive system was studied by mixing As-spiked soil with Cd-spiked soil of the same type during bioaccessibility test. Results shows the bioaccessibility of As ranged from 40 ± 2.8 to 95 ± 1.3% in the gastric phase and 16 ± 2.0 to 96 ± 0.8% in the intestinal phase whilst a significant difference was observed between Cd gastric bioaccessibility (72 ± 4.3 to 99 ± 0.8%) and intestinal bioaccessibility (6.2 ± 0.3 to 45 ± 2.7%). Organic carbon, iron oxide and aluminium oxide were key parameters influencing the bioaccessibility of As (gastric and intestinal phases) and Cd (intestinal phase). No interactions between As and Cd during bioaccessibility test were observed in any soils, which indicates As and Cd may age independently and did not interact while being solubilised during bioaccessibility test. Thus additive effect may be proposed when estimating the bioaccessibility of mixtures of independently-aged As and Cd in soils.
近几十年来,越来越多的人将体外生物可给性用作人类健康风险评估的筛选工具。然而,现有的生物可给性研究仅关注单一污染物。考虑到人类可能会摄入多种污染物,这些污染物在人体胃肠道内可能相互作用,从而导致生物可给性增加或减少。在本研究中,七种不同类型的土壤分别用砷(As)或镉(Cd)进行污染,并陈化一年。研究了土壤性质对生物可给性的影响。此外,通过在生物可给性测试过程中混合砷污染土壤和相同类型的镉污染土壤,研究了模拟人体消化系统中砷和镉之间的相互作用。结果表明,在胃阶段,As 的生物可给性范围为 40±2.8%至 95±1.3%,在肠阶段为 16±2.0%至 96±0.8%;而 Cd 在胃阶段的生物可给性(72±4.3%至 99±0.8%)和肠阶段的生物可给性(6.2±0.3%至 45±2.7%)之间存在显著差异。有机碳、氧化铁和氧化铝是影响 As(胃和肠阶段)和 Cd(肠阶段)生物可给性的关键参数。在任何土壤中都没有观察到生物可给性测试过程中 As 和 Cd 之间的相互作用,这表明 As 和 Cd 可能在陈化过程中独立老化且不相互作用,也不相互作用。因此,在估计土壤中独立老化的 As 和 Cd 混合物的生物可给性时,可以提出加和效应。