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饮用水中的铬:来源、代谢和癌症风险。

Chromium in drinking water: sources, metabolism, and cancer risks.

机构信息

Department of Pathology and Laboratory Medicine, Brown University, 70 Ship Street, Providence, RI 02912, United States.

出版信息

Chem Res Toxicol. 2011 Oct 17;24(10):1617-29. doi: 10.1021/tx200251t. Epub 2011 Jul 28.

Abstract

Drinking water supplies in many geographic areas contain chromium in the +3 and +6 oxidation states. Public health concerns are centered on the presence of hexavalent Cr that is classified as a known human carcinogen via inhalation. Cr(VI) has high environmental mobility and can originate from anthropogenic and natural sources. Acidic environments with high organic content promote the reduction of Cr(VI) to nontoxic Cr(III). The opposite process of Cr(VI) formation from Cr(III) also occurs, particularly in the presence of common minerals containing Mn(IV) oxides. Limited epidemiological evidence for Cr(VI) ingestion is suggestive of elevated risks for stomach cancers. Exposure of animals to Cr(VI) in drinking water induced tumors in the alimentary tract, with linear and supralinear responses in the mouse small intestine. Chromate, the predominant form of Cr(VI) at neutral pH, is taken up by all cells through sulfate channels and is activated nonenzymatically by ubiquitously present ascorbate and small thiols. The most abundant form of DNA damage induced by Cr(VI) is Cr-DNA adducts, which cause mutations and chromosomal breaks. Emerging evidence points to two-way interactions between DNA damage and epigenetic changes that collectively determine the spectrum of genomic rearrangements and profiles of gene expression in tumors. Extensive formation of DNA adducts, clear positivity in genotoxicity assays with high predictive values for carcinogenicity, the shape of tumor-dose responses in mice, and a biological signature of mutagenic carcinogens (multispecies, multisite, and trans-sex tumorigenic potency) strongly support the importance of the DNA-reactive mutagenic mechanisms in carcinogenic effects of Cr(VI). Bioavailability results and kinetic considerations suggest that 10-20% of ingested low-dose Cr(VI) escapes human gastric inactivation. The directly mutagenic mode of action and the incompleteness of gastric detoxification argue against a threshold in low-dose extrapolation of cancer risk for ingested Cr(VI).

摘要

许多地理区域的饮用水供应中都含有三价和六价铬。公众健康关注的焦点是存在六价铬,六价铬通过吸入被归类为已知的人类致癌物。Cr(VI) 具有很高的环境迁移性,可能来自人为和自然来源。高有机物含量的酸性环境促进 Cr(VI)还原为无毒的 Cr(III)。Cr(III) 形成 Cr(VI)的相反过程也会发生,特别是在存在含有 Mn(IV)氧化物的常见矿物质的情况下。有限的流行病学证据表明,摄入 Cr(VI)与胃癌风险升高有关。动物暴露于饮用水中的 Cr(VI)会在消化道中诱导肿瘤,在小鼠小肠中呈线性和超线性反应。在中性 pH 下,铬酸盐是 Cr(VI)的主要形式,通过硫酸盐通道被所有细胞吸收,并被普遍存在的抗坏血酸和小硫醇非酶激活。Cr(VI)诱导的 DNA 损伤的主要形式是 Cr-DNA 加合物,它会导致突变和染色体断裂。新出现的证据表明,DNA 损伤和表观遗传变化之间存在双向相互作用,共同决定肿瘤基因组重排的谱和基因表达的谱。大量形成 DNA 加合物、高预测致癌性的遗传毒性检测中的阳性结果、小鼠肿瘤剂量反应的形状以及致突变致癌物的生物学特征(多物种、多部位和跨性别致癌潜能)强烈支持 DNA 反应性致突变机制在 Cr(VI)致癌作用中的重要性。生物利用度结果和动力学考虑表明,摄入低剂量 Cr(VI)的 10-20%逃避了人体胃的失活。直接致突变作用模式和胃解毒的不完全性表明,在摄入 Cr(VI)的低剂量外推癌症风险方面不存在阈值。

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