Methods and Influencing Factors for the Simple and Rapid Identification of Depleted Uranium Weapon Use under Battlefield Conditions.

The purpose of this paper is to explore how to rapidly and easily identify depleted uranium (DU) samples under battlefield conditions and to study the factors that influence their measurement. The air-absorbed dose rate and surface contamination levels for DU samples of 2-330 g were measured using a patrol instrument and portable energy spectrometer. The results were analyzed in accordance with IAEA standards for judging radioactive substances. The energy spectra of 5-g quantities of DU samples were analyzed using a high-purity germanium gamma spectrometer, and the uranium content of 100 mg DU samples was determined with an inductively coupled plasma mass spectrometer to clarify the type and composition of the uranium. The same batches of DU samples were identified using a portable gamma-ray spectrometer. We added 0-5 g environmental soil powders at different proportions. After sealing, the spectra were collected with a detection distance of 1-5 cm for 10 min. The activities of U and U nuclides in the samples were detected with an NaI(TI) scintillation detector. The U and U mass abundances in samples were calculated from measured specific activities. The sample was determined to contain DU if the U to U ratio was below 0.00723. It is found that for detecting DU materials with a low activity, surface contamination level measurements are more effective than calculating the air-absorbed external irradiation dose rate. Hence, for low-activity samples suspected to be radioactive, a radiometer with a high sensitivity for surface contamination is recommended, and the optimal measurement distance is 1-3 cm. Under all detection conditions, U can be identified using a portable gamma spectrometer, whereas U can only be detected under certain conditions. If these nuclides can be detected simultaneously, a U to U ratio of below 0.00723 indicates the presence of DU. The main factors affecting this identification include the sample mass, sample purity, measurement distance, and measurement time. For the rapid identification of DU with a portable gamma-ray spectrometer, the mass of uranium in the sample must be more than 1 g, the measuring distance needs to be less than 1 cm, and the measuring time must be 1-10 min. It is feasible to use a portable gamma-ray spectrometer to rapidly identify the types and composition of nuclides in DU samples. The detection of U activity is a precondition for the identification of DU.

Effect of a novel polyethylene glycol compound on lung lavage in dogs after the inhalation of depleted uranium dust.

PURPOSE: The purpose of this study was to assess the effect of a lavage solution containing methoxypolyethylene glycol 4-(3,4-dihydroxyphenethylamino)-4-oxobutanoate (MDO) for whole lung lavage (WLL) in dogs after the inhalation of depleted uranium (DU) dust at a dose of 30 mgUkg-1. MATERIALS AND METHODS: WLL was performed using lavage solutions made of normal saline (saline group) or normal saline plus MDO (MDO group) at 2 days post-DU exposure. Meanwhile, a control group was set up without any treatment. RESULTS: At 10 days post-DU exposure, the saline and MDO groups had a lower DU content in urine and lung compared with the DU group (without lavage), while the MDO group content was significantly lower than that in the saline group. In terms of blood urea nitrogen and creatinine levels, the DU group maintained relatively high levels from day 3 to day 10; the saline group levels were reduced compared with the DU group at day 8 and day 10, while the MDO group levels remained markedly lower than both the DU and saline group levels. Pathological changes in the lungs and kidneys showed that the saline group was improved compared with the DU group, but not as significantly as the MDO group. CONCLUSIONS: In brief, WLL has a remarkable effect in promoting the decorporation of inhaled DU dust in the lungs of dogs. By comparison, a MDO-containing lavage solution has a better lavage effect than normal saline.

Zinc protects human kidney cells from depleted uranium-induced apoptosis.

Depleted uranium (DU) is a weak radioactive heavy metal, and zinc (Zn) is an effective antidote to heavy metal poisoning. However, the effect of Zn on DU-induced cytotoxicity and apoptosis is not completely understood. The purpose of this study was to evaluate the effect of Zn on DU-induced cell apoptosis in human kidney cells (HK-2) and explore its molecular mechanism. Pre-treatment with Zn significantly inhibited DU-induced apoptosis. It reduced the formation of reactive oxygen species in the cells, increased the catalase (CAT) and glutathione (GSH) concentrations, suppressed the DU-induced soluble Fas receptor (sFasR) and soluble Fas ligand (sFasL) overexpression, suppressed the release of cytochrome c and apoptosis inhibitor factor (AIF) from mitochondria to cytoplasm, inhibited the activation of caspase-9, caspase-8 and caspase-3, and induced metallothionein (MT) expression. Furthermore, exogenous MT effectively inhibited DU-induced cell apoptosis. In conclusion, mitochondrial and FasR-mediated apoptosis pathways contribute to DU-induced apoptosis in HK-2 cells. Through independent mechanisms, such as indirect antioxidant effects, inhibition of the activation of caspase-9, caspase-8 and caspase-3, and induction of MT expression, Zn inhibits DU-induced apoptosis.

Immunological changes of chronic oral exposure to depleted uranium in mice.

Direct ingestion of contaminated soil by depleted uranium (DU) might lead to internal exposure to DU by local populations through hand contamination. The purpose of this study was to assess the immunological changes of long-term exposure to various doses of DU in mice. Three-week-old Kunming mice were divided into the following 4 groups based on the various feeding doses (containing DU): 0 (control group), 3 (DU3 group), 30 (DU30 group), and 300 mg/kg feed (DU300 group). After 4 months of exposure, in the DU300 group, the innate immune function decreased, manifesting as decreased secretion of nitric oxide, interleukin (IL)-1ß, IL-18, and tumour necrosis factor (TNF)-α in the peritoneal macrophages, as well as reduced cytotoxicity of the splenic natural killer cells. Moreover, the cellular and humoral immune functions were abnormal, as manifested by decreased proliferation of the splenic T cells, proportion of the cluster of differentiation (CD) 3(+) cells, ratio of CD4(+)/CD8(+) cells and delayed-type hypersensitivity, and increased proliferation of the splenic B cells, total serum immunoglobin (Ig) G and IgE, and proportion of splenic mIgM(+)mIgD(+) cells. Through stimulation, the secretion levels of interferon (IFN)-γ and TNF-α in the splenic cells were reduced, and the levels of IL-4 and IL-10 were increased. By comparison, in the DU30 and DU3 groups, the effects were either minor or indiscernible. In conclusions, chronic intake of higher doses of DU (300 mg/kg) had a significant impact on the immune function, most likely due to an imbalance in T helper (Th) 1 and Th2 cytokines.

The reproductive effects in rats after chronic oral exposure to low-dose depleted uranium.

This two-generation study evaluated the effects of depleted uranium (DU) on reproduction in rats. Across two generations, Wistar rats (30/sex/group) were maintained on feed containing DU at dose levels of 0 (control group), 4 (DU4 group), or 40 (DU40 group) mg kg⁻¹ day⁻¹ for 4 months prior to mating. After 4 months of exposure, the pregnancy rate, normal labour rate, and survival rate of offspring produced by F1 rats were all significantly decreased as compared to the control group, and especially in the DU40 group, these parameters fell by half to two-thirds, while no adverse effects were evident in F0 rats. The uranium content in the testes and ovaries of F1 rats in the DU4 and DU40 groups was significantly higher than that found in F0 rats. The levels of sex hormone in the serum were disorder in both generations. The enzymes related to spermiogenesis were also significantly different between generations, and the damage was more severe in F1 rats. In conclusion, the reproductive effects in F0 rats were slight after chronic oral exposure to DU, while the effects were obvious in F1 rats.

The protective role of zinc against acute toxicity of depleted uranium in rats.

Depleted uranium (DU) has been widely used in both civilian and military activities and contributes to health problems. This study was undertaken to evaluate the protective role of zinc against acute toxicity of DU. Sprague Dawley rats were injected with DU (10 mg/kg, i.p.) to create a toxicity model (DU group). Before and after the injection of DU, zinc sulphate (10 mg/kg, i.p.) was administered once a day for 2 days. The survival rates at 30 days post DU administration and the effects of zinc at 4 days post DU administration were evaluated. Our data indicate that zinc has obvious protective effects, especially pre-treatment with zinc. Rats pre-treated with zinc had significantly higher survival rates than rats in the DU group, with 60.03% more surviving. In addition, at 4 days post DU administration, the former had lower kidney uranium content, insignificant renal tubular epithelial cell necrosis and less transparent tubes. Meanwhile, blood urea nitrogen, creatinine and urine N-acethyl-ß-d-glucosaminidase concentrations were significantly decreased; the gene expression levels of metallothionein (MT) in kidney tissues were significantly increased; and catalase levels were increased and malondialdehyde levels were decreased. In conclusion, pre-treatment with zinc significantly alleviated acute toxicity of DU, and the mechanism appeared to be related to the induction of MT synthesis and enhancement of the antioxidant function.

A study assessing the genotoxicity in rats after chronic oral exposure to a low dose of depleted uranium.

PURPOSE: The aim of this study was to evaluate the potential genotoxicity induced by chronic oral exposure to depleted uranium (DU). MATERIALS AND METHODS: Weanling Wistar rats (F(0)), 50/sex/group, were exposed to DU in food at doses of 0, 4, or 40 mg kg(-1)day(-1) for four months. They were subsequently mated, resulting in the birth of F(1) rats. Fifty F(l) weanlings/sex/group were exposed for four months to the same dose levels as their parents. After four months, the uranium content in the tissues, the potential damage to the genetic material, and pathomorphological changes of the testicles were observed in both F(0) and F(1) rats. The genotoxicity of DU was evaluated by the following methods: sperm abnormality assessment, the bone-marrow micronucleus test, and the comet assay. RESULTS: Uranium content in F(1) rats was significantly higher than that in F(0) rats in both the kidney and ovary (p < 0.05). The sperm abnormality rate, marrow cell micronuclei rate, comet tail length, and tailed cell percentage increased in each treatment group in each generation compared with the control group (p < 0.05). When comparing F(1) with F(0) rats, significant differences were detected for most of the indicators, with F(1) rats always exhibiting more damage (p < 0.05). With regard to pathomorphological changes in the testicles, the sperm displayed atypical changes, including thickening of the anachromasis nucleolus, which seemed to be more severe in F(1) rats. CONCLUSION: Genotoxicity may be induced in rats after chronic oral exposure to a low dose of DU.