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我国非铀矿山222Rn和220Rn水平初步调查研究
引用本文:尚兵,崔宏星,武云云,张庆召,苏旭.我国非铀矿山222Rn和220Rn水平初步调查研究[J].中华放射医学与防护杂志,2008,28(6):559-565.
作者姓名:尚兵  崔宏星  武云云  张庆召  苏旭
作者单位:中国疾病预防控制中心辐射防护与核安全医学所 北京,100088
基金项目:科技部社会公益研究项目 
摘    要:目的 测量非铀矿山222Rn、220Rn水平,了解我国矿山氡超标比率和矿工受照剂量。方法 根据典型抽样方法选择12个省17类44座矿山,采用LD-P分辨型探测器测量222Rn、220Rn累积浓度。结果 222Rn、220Rn浓度呈对数正态分布,金属矿(25座,147处)222Rn浓度算数均值(AM)和几何均值(GM)分别为(1211±2359)和(311±5.5) Bq m3;220Rn浓度AM和GM分别为(269±700)和(71±4.4) Bq m3。非金属矿(18座,118处)222Rn浓度AM和GM分别为(98±207)和(55±2.5) Bq m3;220Rn浓度AM和GM分别为(60±76)和(38±2.4) Bq m3。测量地下矿井40处,其中6处222Rn浓度均值超过1000 Bq m3 (工作场所氡浓度限值),占抽样率15.0%;约有7%测点222Rn超过浓度3700 Bq m3 (我国铀矿冶氡浓度限值),个别测点超过10 000 Bq m3。井下和地面工作区室内222Rn平衡因子分别为0.33±0.15和0.47±0.18。220Rn平衡因子的波动范围较大,为0.001~0.032。地下矿山矿工的年均受照剂量约为8.15mSv。结论 我国金属矿山特别是有色金属矿井下222Rn浓度偏高的问题依然严重,值得关注和进行跟踪研究。

关 键 词:非铀矿山  累积浓度  平衡因子  剂量
收稿时间:2008/7/31 0:00:00

A preliminary investigation of 222Rn and 220Rn levels in non-uranium mines in China
SHANG Bing,CUI Hong-xing,WU Yun-yun.A preliminary investigation of 222Rn and 220Rn levels in non-uranium mines in China[J].Chinese Journal of Radiological Medicine and Protection,2008,28(6):559-565.
Authors:SHANG Bing  CUI Hong-xing  WU Yun-yun
Institution:National Institute for Radiological Protection, Chinese Center for Disease Control and Prevention, 100088 Beijing, China;National Institute for Radiological Protection, Chinese Center for Disease Control and Prevention, 100088 Beijing, China;National Institute for Radiological Protection, Chinese Center for Disease Control and Prevention, 100088 Beijing, China;National Institute for Radiological Protection, Chinese Center for Disease Control and Prevention, 100088 Beijing, China;National Institute for Radiological Protection, Chinese Center for Disease Control and Prevention, 100088 Beijing, China
Abstract:Objective To measure levels of 222Rn and 220Rn in typical non-uranium mines, China, and to estimate dose from the occupational radon exposure in the miners.Methods Using typical sampling scheme, 44 mines were selected in 12 provinces, which can be classified into 4 categories and 17 types of mines. The radon-thoron discriminative detectors were used to measure 222Rn and 220Rn concentrations in mines.Result The concentration of 222Rn or 220Rn was log-normally distributed. The arithmetic mean (AM) concentration and geometric mean (GM) concentration of 222Rn and 220Rn in 25 metal mines (n=147) were estimated to be (1211±2359) Bq m3 (AM) and (311±5.5) Bq m3 (GM), and (269±700) Bq m3 (AM) and (71±4.4)Bq m3 (GM), respectively. The mean concentrations of 222Rn and 220Rn in 18 non-metal mines (n=118) were (98±207) Bq m3 (AM) and(55±2.5) Bq m3 (GM), and (60±76) Bq m3 (AM) and (38 ± 2.4)Bq m3(GM), respectively. In total, we measured 222Rn concentration in 44 underground mines,6 of them, accounted for 15%, with the mean radon concentration exceeding 1000 Bqm-3 (limit of workplace in China). Approximately 7% of radon concentration in mines measured were higher than 3700Bq m3 (current limit in uranium mine in China), some points even exceeded 10?000 Bq m3. Based on this typical measurements, the equilibrium factor for 222Rn was estimated to be 0.33±0.15 in underground mines and 0.47±0.18 in nearby houses. Equilibrium factor for 220Rn ranged from 0.001 to 0.032. Using the data obtained in this typical survey, the average annual effective dose of underground miners exposed to radon and thoron was estimated to be 8.15 mSv/a.Conclusions High levels of 222Rn exists in metal mines, such as copper, tin, lead and zinc, gold, and aluminum mines among others. More study and administrative measures are needed to address the radiation protection of workers occupationally exposed to high radon in mines.
Keywords:222Ra  220Rn
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