孙智超,哈日巴拉,格日勒满达呼,等.巴彦乌拉铀矿周围饮用井水中总放射性水平调查[J].中华放射医学与防护杂志,2022,42(7):527-530.Sun Zhichao,Haribala,Gerilemandahu,et al.Survey of total radioactivity in drinking well water around Bayanwula uranium mine[J].Chin J Radiol Med Prot,2022,42(7):527-530
巴彦乌拉铀矿周围饮用井水中总放射性水平调查
Survey of total radioactivity in drinking well water around Bayanwula uranium mine
投稿时间:2022-03-29  
DOI:10.3760/cma.j.cn112271-20220329-00129
中文关键词:  巴彦乌拉铀矿  饮用井水  总放射性  枯水期  丰水期
英文关键词:Bayanwula uranium mine  Drinking well water  Total α and β radioactivity  Dry season  Wet season
基金项目:国家自然科学基金项目(11865011);内蒙古自治区自然科学基金项目(2019MS08073);内蒙古自治区自然科学基金项目(2020MS08207)
作者单位E-mail
孙智超 内蒙古自治区综合疾病预防控制中心 内蒙古自治区医疗卫生放射卫生学重点实验室, 呼和浩特 010031  
哈日巴拉 内蒙古自治区综合疾病预防控制中心 内蒙古自治区医疗卫生放射卫生学重点实验室, 呼和浩特 010031 baihrbl@163.com 
格日勒满达呼 内蒙古自治区综合疾病预防控制中心 内蒙古自治区医疗卫生放射卫生学重点实验室, 呼和浩特 010031  
张帅 内蒙古自治区综合疾病预防控制中心 内蒙古自治区医疗卫生放射卫生学重点实验室, 呼和浩特 010031  
何文明 内蒙古自治区环境监测总站鄂尔多斯分站, 鄂尔多斯 017000  
包玉龙 内蒙古自治区综合疾病预防控制中心 内蒙古自治区医疗卫生放射卫生学重点实验室, 呼和浩特 010031  
许潇 内蒙古自治区综合疾病预防控制中心 内蒙古自治区医疗卫生放射卫生学重点实验室, 呼和浩特 010031  
王成国 内蒙古自治区综合疾病预防控制中心 内蒙古自治区医疗卫生放射卫生学重点实验室, 呼和浩特 010031  
刘祥 呼和浩特市疾病预防控制中心, 呼和浩特 010010  
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中文摘要:
      目的 调查巴彦乌拉铀矿周围饮用井水中总放射性水平。方法 采集2020年巴彦乌拉铀矿周围枯水期和丰水期饮用井水174份,以及居民家中经过滤后的饮用井水5份。分析枯水期和丰水期总α和总β放射性水平是否存在差异,总放射性水平与距离铀矿中心不同位置的关系,并对居民家中过滤后的饮用井水进行放射性水平调查。采用低本底α、β放射性测量仪测量分析其放射性水平。结果 巴彦乌拉铀矿周围饮用井水中,枯水期总α范围为0.024~ 2.468 Bq/L, 平均为(0.605±0.507)Bq/L,总β变化范围为0.125~1.395 Bq/L,平均为(0.420±0.235)Bq/L。丰水期总α变化范围为0.049~2.988 Bq/L,平均为(0.825±0.605)Bq/L,总β变化范围为0.059~1.623 Bq/L,平均为(0.506±0.265)Bq/L。距离铀矿中心位置水样的总放射性水平均值关系为10 km>30 km>20 km。结论 巴彦乌拉铀矿周围饮用井水中的放射性活度偏高,丰水期水样中总α、总β放射性水平均大于枯水期,放射性水平较未开采前未见升高。
英文摘要:
      Objective To investigate the total radioactivity in drinking well water around the Bayanwula uranium mine. Methods Totally 174 samples of drinking well water and 5 samples of filtered well water from residential houses were collected during dry and wet seasons in 2020 around the Bayanwula uranium mine. Total α and total β radioactivity in dry season and wet season were analyzed for detrmining whether there were differences between them and the relation between total radioactivity with different locations away from the uranium center. The radioactivity in filtered drinking well water used in residential houses was also investigated. Radioactivity were measured and analyzed using low background alpha and beta radioactivity meters, and the data were analysed using SPSS analytical statistical method. Results In the drinking well water around Bayanwula uranium mine, the activity concentrations of total α and β measured in dry season were 0.024-2.468 Bq/L with a mean of (0.605±0.507) Bq/L and 0.125-1.395 Bq/L with a mean of (0.420±0.235) Bq/L, respectively. The values measured in wet season were 0.049-2.988 Bq/L with a mean of (0.825±0.605) Bq/L for total α and 0.059-1.623 Bq/L with a mean of (0.506±0.265) Bq/L for total β, respectively. The average value of total radioactivity in water samples was lower within 10, 30 and 20 km of the uranium mine in the descending order. Conclusions The radioactivity in well water around the Bayanwula uranium mine is high, with the total α and β in samples greater in wet season than in the dry season and without elevated levels as compared to the pre-mining background.
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