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首页> 外文期刊>risk analysis >Urinary Excretion of Chromium Following Ingestion of Chromite‐Ore Processing Residues in Humans: Implications for Biomonitoring
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Urinary Excretion of Chromium Following Ingestion of Chromite‐Ore Processing Residues in Humans: Implications for Biomonitoring

机译:人体摄入铬铁矿加工残留物后尿液中铬的排泄:对生物监测的影响

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Biomonitoring programs for urinary chromium (Cr) typically attempt to evaluate occupational exposure via the inhalation route. This study investigated whether Cr can be detected in the urine of people following the ingestion of soils that contain relatively high concentrations of chromium in chromite ore processing residue (COPR). To evaluate the reasonableness of using urinary monitoring to assess environmental exposure, six volunteers ingested 400 mg of soil/day (low‐dose group), two others ingested 2.0 g of soil/day (high‐dose group) for 3 consecutive days, and one person ingested a placebo on each of 3 days. The soil and COPR mixture contained concentrations of total chromium (Cr) and hexavalent chromium Cr(VI) of 103 ± 20 and 9.3 ± 3.8 mg/kg, respectively. Therefore, the low‐dose group ingested 41 μg Cr/day including 3.7 μg Cr(VI)and the high‐dose group ingested 206 μg Cr/day including 18.6 μg Cr(VI) on each of 3 consecutive days. All urine samples were collected and analyzed individually for total Cr on the day prior to dosing, during the 3 days of dosing, and up to the first void 48 h after the last dose. No significant increases in urinary Cr excretion were found when background excretion data were compared with data following each of the 3 days of dosing or in daily mean urine concentrations of the high‐ vs the low‐dose groups. It appears that Cr present in a soil and COPR mixture at Cr doses up to 200 μg/day is not sufficiently bioavailable for biomonitoring of urine to be informative. These results are consistent with previously published findings suggesting that incidental exposure to dusts and soils containing comparable levels of Cr will not result in increased concentrati
机译:尿铬 (Cr) 的生物监测计划通常尝试通过吸入途径评估职业暴露。本研究调查了摄入铬铁矿加工残渣 (COPR) 中铬浓度相对较高的土壤后,是否可以在人们的尿液中检测到 Cr。为了评估使用尿液监测来评估环境暴露的合理性,六名志愿者连续 3 天摄入 400 毫克土壤(低剂量组),另外两名志愿者连续 3 天摄入 2.0 克土壤/天(高剂量组),1 人每天摄入安慰剂3 天。土壤和COPR混合物的总铬(Cr)和六价铬[Cr(VI)]浓度分别为103±20和9.3±3.8 mg/kg。因此,低剂量组连续3天每天摄入41 μg Cr [包括3.7 μg Cr(VI)],高剂量组每天摄入206 μg Cr [包括 18.6 μg Cr(VI)]。在给药前一天、给药后 3 天内以及最后一次给药后 48 小时,收集所有尿液样本并单独分析总 Cr。当将背景排泄数据与给药 3 天后的数据或高剂量组与低剂量组的每日平均尿液浓度进行比较时,未发现尿 Cr 排泄显着增加。似乎土壤中存在的Cr和COPR混合物中Cr剂量高达200μg/天,其生物利用度不足以对尿液进行生物监测,无法提供信息。这些结果与先前发表的研究结果一致,表明偶然暴露于含有相当水平的Cr的灰尘和土壤不会导致浓度增加

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