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砷化镓的体外溶解度和体内毒性。

In vitro solubility and in vivo toxicity of gallium arsenide.

作者信息

Webb D R, Sipes I G, Carter D E

出版信息

Toxicol Appl Pharmacol. 1984 Oct;76(1):96-104. doi: 10.1016/0041-008x(84)90032-2.

DOI:10.1016/0041-008x(84)90032-2
PMID:6484996
Abstract

The in vitro solubilities of gallium arsenide (GaAs) and its metal oxides were arsenic(III) oxide greater than GaAs much greater than gallium(III) oxide. GaAs dissolution was also dependent upon the type and concentration of buffer anion. The amount of arsenic dissolved in 12 hr by various aqueous media was 0.2 M phosphate buffer greater than or equal to 0.1 M phosphate buffer greater than Krebs-Hensleit buffer greater than distilled H2O greater than HCl-KCl buffer. GaAs was apparently soluble under in vivo conditions. Blood arsenic concentrations in rats 14 days after intratracheal instillation of 10, 30, or 100 mg/kg GaAs were 5.5, 14.3, and 53.6 micrograms/ml, respectively; gallium was not detected at any doses. An increase in lung wet weight at 14 days was dose dependent with these organs retaining 17 to 42% of the dose as gallium or arsenic. Excretion of gallium and arsenic was limited to the feces. Urinary porphyrin concentrations and body weight, monitored as indices of toxicity, were significantly altered over the 14-day study. The analysis of porphyrins revealed that uroporphyrin replaced coproporphyrin as the primary urinary metabolite. Rats receiving 10, 100, or 1000 mg/kg GaAs po exhibited similar signs of toxicity. Blood arsenic concentrations at 14 days were 3.5, 6.8, and 17.6 micrograms/ml, respectively. Porphyria was increased, and body weight was decreased at 1000 mg/kg GaAs. These values were equivalent to those obtained with an intratracheal dose of 10 to 30 mg/kg GaAs. Our results showed that pulmonary and po exposure to GaAs resulted in systemic arsenic intoxication. The finding that urinary uroporphyrin concentrations were greater than coproporphyrin concentrations may serve as a sensitive indicator for GaAs exposure.

摘要

砷化镓(GaAs)及其金属氧化物的体外溶解度为:三氧化二砷大于GaAs,且远大于三氧化二镓。GaAs的溶解还取决于缓冲阴离子的类型和浓度。在12小时内,不同水性介质溶解的砷量为:0.2M磷酸盐缓冲液≥0.1M磷酸盐缓冲液>克雷布斯-亨斯莱特缓冲液>蒸馏水>盐酸-氯化钾缓冲液。GaAs在体内条件下显然是可溶的。大鼠经气管内滴注10、30或100mg/kg GaAs 14天后,血液中的砷浓度分别为5.5、14.3和53.6微克/毫升;在任何剂量下均未检测到镓。14天时肺湿重增加呈剂量依赖性,这些器官中保留了17%至42%的剂量作为镓或砷。镓和砷的排泄仅限于粪便。作为毒性指标监测的尿卟啉浓度和体重在14天的研究中发生了显著变化。卟啉分析表明,尿卟啉取代粪卟啉成为主要的尿代谢产物。经口给予10、100或1000mg/kg GaAs的大鼠表现出相似的毒性迹象。14天时血液中的砷浓度分别为3.5、6.8和17.6微克/毫升。在1000mg/kg GaAs剂量下,卟啉症增加,体重下降。这些数值与经气管内给予10至30mg/kg GaAs所获得的数值相当。我们的结果表明,肺部和经口接触GaAs会导致全身性砷中毒。尿中尿卟啉浓度大于粪卟啉浓度这一发现可能是GaAs接触的敏感指标。

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