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本文引用的文献

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Exposure pathways and health effects associated with chemical and radiological toxicity of natural uranium: a review.
Rev Environ Health. 2005 Jul-Sep;20(3):177-93. doi: 10.1515/reveh.2005.20.3.177.
2
Tumor necrosis factor-alpha-independent downregulation of hepatic cholesterol 7alpha-hydroxylase gene in mice treated with lead nitrate.硝酸铅处理的小鼠肝脏胆固醇7α-羟化酶基因的肿瘤坏死因子-α非依赖性下调
Toxicol Sci. 2005 Oct;87(2):537-42. doi: 10.1093/toxsci/kfi267. Epub 2005 Jul 27.
3
The quantitative analysis of uranium isotopes in the urine of the civilian population of eastern Afghanistan after Operation Enduring Freedom.持久自由行动后阿富汗东部平民尿液中铀同位素的定量分析。
Mil Med. 2005 Apr;170(4):277-84. doi: 10.7205/milmed.170.4.277.
4
Effect of depleted uranium weapons used in the Balkan war on the incidence of cervical intraepithelial neoplasia (CIN) and invasive cancer of the cervix in Greece.
Clin Exp Obstet Gynecol. 2005;32(1):58-60.
5
The effect of stress on the temporal and regional distribution of uranium in rat brain after acute uranyl acetate exposure.急性醋酸铀酰暴露后应激对大鼠脑内铀的时间和区域分布的影响。
J Toxicol Environ Health A. 2005 Jan 22;68(2):99-111. doi: 10.1080/15287390590885910.
6
Effects of short-term and long-term depleted uranium exposure on open-field behavior and brain lipid oxidation in rats.短期和长期接触贫铀对大鼠旷场行为及脑脂质氧化的影响。
Neurotoxicol Teratol. 2005 Jan-Feb;27(1):135-44. doi: 10.1016/j.ntt.2004.09.001.
7
Micronuclei occurrence in population exposed to depleted uranium and control human group in correlation with sex, age and smoking habit.
Med Arh. 2004;58(6):335-8.
8
The number of malignant neoplasm in Sarajevo region during the period 1998-2002.1998年至2002年期间萨拉热窝地区恶性肿瘤的数量。
Med Arh. 2004;58(5):275-8.
9
Uranium contents and (235)U/(238)U atom ratios in soil and earthworms in western Kosovo after the 1999 war.1999年战争后科索沃西部土壤和蚯蚓中的铀含量及(235)U/(238)U原子比
Sci Total Environ. 2005 Jan 20;337(1-3):109-18. doi: 10.1016/j.scitotenv.2004.07.001.
10
Heat shock proteins and acquired resistance to uranium nephrotoxicity.热休克蛋白与铀肾毒性的获得性抗性
Toxicology. 2005 Jan 5;206(1):59-73. doi: 10.1016/j.tox.2004.07.007.

贫铀作为一种环境风险因素的演变:来自其他金属的教训。

The evolution of depleted uranium as an environmental risk factor: lessons from other metals.

作者信息

Briner Wayne E

机构信息

Department of Psychology, University of Nebraska at Kearney, Kearney, NE 68849, USA.

出版信息

Int J Environ Res Public Health. 2006 Jun;3(2):129-35. doi: 10.3390/ijerph2006030016.

DOI:10.3390/ijerph2006030016
PMID:16823086
原文链接:https://pmc.ncbi.nlm.nih.gov/articles/PMC3807504/
Abstract

Depleted uranium (DU) is used in both civilian and military applications. Civilian uses are primarily limited to ballast and counterweights in ships and aircraft with limited risk of environmental release. The very nature of the military use of DU releases DU into the environment. DU released into the environment from military use takes the form of large fragments that are chemically unchanged and dust in the form of oxides. DU dust is nearly insoluble, respirable and shows little mobility in the soil. Exposure to DU occurs primarily from inhalation of dust and possible hand to mouth activity. Toxicity of DU is believed to be primarily chemical in nature with radiological activity being a lesser problem. DU has been shown to have a variety of behavioral and neurological effects in experimental animals. DU has been used the Balkans, Afghanistan, and both Iraq wars and there is a high probability of its use in future conflicts. Further, other nations are developing DU weaponry; some of these nations may use DU with a greater radiological risk than those currently in use. The toxicity of DU has been studied mostly as an issue of the health of military personnel. However, many tons of DU have been left in the former theater of war and indigenous populations continue to be exposed to DU, primarily in the form of dust. Little epidemiological data exists concerning the impact of DU on these groups. It may be possible to extrapolate what the effects of DU may be on indigenous groups by examining the data on similar metals. DU has many similarities to lead in its route of exposure, chemistry, metabolic fate, target organs, and effect of experimental animals. Studies should be conducted on indigenous groups using lead as a model when ascertaining if DU has an adverse effect.

摘要

贫铀(DU)用于民用和军事领域。民用主要限于船舶和飞机的压载物及配重,环境释放风险有限。贫铀的军事用途本身会将其释放到环境中。军事用途释放到环境中的贫铀呈化学性质未变的大碎片形式以及氧化物形式的粉尘。贫铀粉尘几乎不溶、可吸入且在土壤中流动性很小。接触贫铀主要通过吸入粉尘以及可能的手口接触活动。贫铀的毒性据信主要是化学性质的,放射性活性问题较小。贫铀已在巴尔干地区、阿富汗以及两次伊拉克战争中使用,未来冲突中很有可能继续使用。此外,其他国家正在研发贫铀武器;其中一些国家使用贫铀时可能比目前使用的国家面临更大的放射性风险。贫铀毒性大多作为军事人员健康问题进行研究。然而,大量贫铀留在了以前的战区,当地居民继续接触贫铀,主要是粉尘形式。关于贫铀对这些群体影响的流行病学数据很少。通过研究类似金属的数据,有可能推断贫铀对当地群体可能产生的影响。贫铀在接触途径、化学性质、代谢归宿、靶器官以及对实验动物的影响等方面与铅有许多相似之处。在确定贫铀是否有不良影响时,应以铅为模型对当地群体进行研究。