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Based on the study of solid cancer incidence in survivors of the atomic bomb disaster (atomic bomb survivors) from 1958 to 1998, the Radiation Effects Research Foundation (RERF) performed an additional 11-year follow-up (1999—2009) to further investigate the 50-year solid cancer incidence of atomic bomb survivors from 1958 to 2009. Considering influencing factors such as gender, smoking, drinking, body mass index, and medical exposure, we updated the radiation risk estimate for solid cancer and found a new problem of the relationship between gender-specific dose response, exposure age and cancer incidence during the study, which provides guidance for future research.
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Objective To explore the applicable conditions for using urine plutonium monitoring data to assess personal internal doses,in order to provide references for the occupational health management and the urine plutonium monitoring in nuclear sector.Methods Using some plutonium mixtures from DOE nuclear facilities,as an example,the urine plutonium levels were estimated through simulation calculation at 1 mSv effective dose arising from either acute or chronic inhalation of plutonium compounds,respectively.The results were compared with the typical detection limit of radiochemical separation and α-spectrometry.The feasibility of urine plutonium monitoring for dose assessment of internal radiation exposure was discussed.Results Only for type M plutonium compunds,1 mSv detection limit can be achieved using radiochemical separation and α-spectrometry within 10 d after inhalation.Conclusions Before the monitoring plan of urine plutonium is made,detection limits of monitoring method should be considered.Internal dose could be accessed using workplace air monitoring and working hours when necessary.
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Objective To explore the applicable conditions for using urine uranium monitoring data to assess personal internal doses with a view to providing references for the occupational health management and the urine uranium monitoring in nuclear industry sector.Methods The urine uranium levels were calculated, through simulation calculation set at 1 mSv effective dose arising from either acute or chronic ingestion of uranium compounds.The results were compared with the monitoring values of workers without occupational exposure history.The feasibility of urine uranium monitoring for dose assessment of internal radiation exposure was discussed.Results For special monitoring of acute ingestion, liquid fluorimetry can meet monitoring requirements of Type F uranium compound, Type M low enriched uranium and Type S naturally occurring uranium.For routine monitoring, only Type F low enriched uranium and Type M naturally occurring uranium can be detected at shorter monitoring intervals, But it was not suitable for Type S uranium compounds.Conclusions Background levels and detection limits should be considered when urine uranium is measured for the purpose of assessment or control of exposure to uranium and the interpretation of the results.
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Objective Derived air concentration of Type F uranium compounds are calculated respectively in order to provide reference for the management and evaluation of occupational hazard factors in workplace.Methods The air concentrations in the workplace of Type F uranium compounds were derived respectively through numerical simulationn,from individual dose limits,acute poisoning and chronic chemical damage threshold.Results Under normal operation conditions,the concentration of 5 μg /m3 for Type F uranium compounds in air of workplace can meet the requirements of radiation and chemical hazard control.Open inhalation of 1.1 mg/m3 is acceptable in a short time.Conclusions It is feasible to establish a permissible concentration limit in workplace for Type F uranium compounds.
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Objective To evaluate the difference of PC values based on GBZ 97-2002 and on GBZ 97-2009 for lung cancer cases in Chinese uranium miners.Methods Using 19 lung cancer data ascertained in the past epidemiological study,PC values were calculated according to GBZ 97-2002 and GBZ 97-2009.Results In the 19 lung cancer cases,those cases that could not be judged as radiogenic cancers based on GBZ 97-2002,but may be judged as radiogenic cancers with GBZ 97-2009.The probability was enlarged by 1.1 times at least.The major reason was that the used value was the upper limit of 95％ in GBZ 2009 but the median in 2002.Conclusions Compared to GBZ 97-2002,the criteria value of PC in GBZ 97-2009 drops obviously.
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Objective To explore the effects of accumulated 60CD,γ-ray irradiation on small molecular metabolites in rats urine.Methods Ten healthy male SD rats were irradiated by 60Co γ-rays in 5 days and the accumulated doses were 0,0.2,0.4,0.6,0.8,1.0 Gy,respectively.The metabolites in urine of different groups were measured with 1 H-NMR combined with principal components analysis (PCA) and partial least square discriminate analysis (PLS-DA). Results The metabolites in rat urine were obviously changed after irradiation. Compared with control group,the amount of acetoacetate decreased after irradiation(t =29.7 -30.7,P ＜ 0.05 ),but its relative level was stable when the dose increased ( P ＞ 0.05 ).Meanwhile,the relative level of hippuric acid increased ( t =4.4 - 21.6,P ＜ 0.05 ) especially when the accumulated dose was higher than 1 Gy (t =21.6,P＜0.05). The relative level of proline,taurine and trimethylamine-N-oxide increased after irradiation with the same trend( t =3.5 - 13.4,4.7 - 11.5,2.9- 12.7,P＜0.05). Conclusions The acetoacetate,hippuric acid,proline,taurine,and trimethylamine-N-oxide may be applicable for biomarkers of accumulative irradiation on rat.