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北部湾沉积物中放射性核素的分布特征与控制因素

林武辉 冯禹 余克服 蓝文陆 莫珍妮 宁秋云 冯亮亮 何贤文

林武辉,冯禹,余克服,等. 北部湾沉积物中放射性核素的分布特征与控制因素[J]. 海洋学报,2020,42(2):143–154,doi:10.3969/j.issn.0253−4193.2020.02.015
引用本文: 林武辉,冯禹,余克服,等. 北部湾沉积物中放射性核素的分布特征与控制因素[J]. 海洋学报,2020,42(2):143–154,doi:10.3969/j.issn.0253− 4193.2020.02.015
Lin Wuhui,Feng Yu,Yu Kefu, et al. Characteristics of radionuclides in sediments collected from the Beibu Gulf and influence factors[J]. Haiyang Xuebao,2020, 42(2):143–154,doi:10.3969/j.issn.0253−4193.2020.02.015
Citation: Lin Wuhui,Feng Yu,Yu Kefu, et al. Characteristics of radionuclides in sediments collected from the Beibu Gulf and influence factors[J]. Haiyang Xuebao,2020, 42(2):143–154,doi:10.3969/j.issn.0253−4193.2020.02.015

北部湾沉积物中放射性核素的分布特征与控制因素

doi: 10.3969/j.issn.0253-4193.2020.02.015
基金项目: 国家自然科学基金(91428203,41906043);广西“珊瑚礁资源与环境”八桂学者项目(2014BGXZGX03);广西自然科学基金(2017GXNSFBA198096,2019GXNSFAA185006);国家海洋局海洋−大气化学与全球变化重点实验室开放基金(GCMAC1606)。
详细信息
    作者简介:

    林武辉(1987—),男,福建省泉州市人,博士,主要研究海洋过程的同位素示踪、海洋放射性监测与评价。E-mail:linwuhui8@163.com

    通讯作者:

    余克服(1969—),男,湖北省公安县人,教授,博士,主要从事南海珊瑚礁地质、生态与环境研究。E-mail:kefuyu@scsio.ac.cn

  • 中图分类号: X55;X591

Characteristics of radionuclides in sediments collected from the Beibu Gulf and influence factors

  • 摘要: 北部湾是我国大西南地区重要的海上通道,也是我国重要的渔场之一。本研究利用高纯锗γ谱仪系统分析北部湾表层和柱状沉积物中4种最主要的天然放射性核素(238U、226Ra、228Ra、40K)含量和分布特征。结果显示,北部湾沉积物中放射性核素含量低于我国大部分海域的结果,高于珊瑚礁区的极低放射性水平的结果。北部湾沉积物中4种核素都存在“蝴蝶”状空间分布特征,该特征主要源于沉积物粒径的非线性调控,且与沉积物总有机碳浓度存在正相关。此外,利用Mn和210Pb所指示的氧化还原状态和物理/生物扰动过程也可以对柱状沉积物中氧化还原敏感型核素(比如,238U)分布产生一定的影响。本文从232Th/238U、40K/238U、226Ra/238U活度比值角度,发现北部湾沉积物具有典型的陆源沉积物特征,且显著不同于南海珊瑚礁区中生源沉积物特征。本研究有利于掌握滨海核电发展背景下的北部湾海洋环境中放射性核素水平,揭示核素的“蝴蝶”状分布特征和控制因素,探索基于放射性核素的地球化学新指标在海洋沉积过程中的应用。
  • 图  1  采样站位

    环流(冬季和夏季)图参考自文献 [18]

    Fig.  1  Sampling stations

    The distribution of summer and winter circulation in the figure refers to reference[18]

    图  2  北部湾表层沉积物中放射性核素238U(a)、226Ra(b)、228Ra(c)、40K(d)比活度的“蝴蝶”状分布特征

    Fig.  2  “Butterfly pattern” of specific activities of 238U(a), 226Ra(b), 228Ra(c), and 40K(d) in surface marine sediments collected from the Beibu Gulf

    图  3  涠洲岛(WZ)与三娘湾(SN)沉积物柱状样中放射性核素238U(a)、226Ra(b)、228Ra(c)、40K(d)比活度剖面图

    图中虚线和点线分别代表涠洲岛和三娘湾的柱样中核素比活度平均值

    Fig.  3  Vertical profiles of specific activities of 238U(a), 226Ra(b), 228Ra(c), and 40K(d) in sediment cores from the stations of WZ and SN

    The average value was indicated by the dashed line and dotted line for WZ and SN, respectively

    图  4  北部湾表层沉积物的粒径(a)和TOC含量(b)的空间分布特征

    Fig.  4  Spatial distribution of grain size (a) and organic carbon (b) in surface sediments of the Beibu Gulf

    图  5  北部湾沉积物中232Th和238U(a)、40K和238U(b)的关系

    虚线为数据线性回归后的结果

    Fig.  5  Relationship of 232Th vs.238U(a) and 40K vs.238U(b) in marine sediments collected from the Beibu Gulf

    Linear regression of 232Th vs.238U(a) and 40K vs.238U(b) is indicated by the dashed lines

    图  6  北部湾表层沉积物中238U比活度与TOC、粒径的关系

    虚线为数据线性和非线性回归后的结果

    Fig.  6  Relationship of 238U specific activity, TOC, and grain size in surface sediments from the Beibu Gulf

    The linear and nonlinear regression were indicated by the dashed lines

    图  7  涠洲岛(WZ)与三娘湾(SN)沉积物柱状样中放射性核素238U(a)和210Pb(b)比活度剖面图,以及WZ柱样中铀(238U)和锰(Mn)两种氧化还原敏感型元素的垂直分布图(c)

    Fig.  7  Vertical profiles of activities of 238U (a) and 210Pb (b) in sediment cores from the stations of WZ and SN. Vertical profile of redox sensitive element of 238U and Mn in WZ sediment core (c)

    图  8  北部湾和我国其他海域沉积物中226Ra和238U比活度关系,k代表226Ra/238U活度比值,所有数据来自表1和本研究

    Fig.  8  Relationship between 226Ra and 238U in surface marine sediments from the Beibu Gulf and other China seas. k is denoted as activity ratio of 226Ra to 238U. All data was obtained from Table 1 and this study

    表  1  不同海域的表层沉积物中238U、226Ra、228Ra、40K含量(单位:Bq/kg)

    Tab.  1  Activities of 238U、226Ra、228Ra、40K in surface sediments from distinct sea regions (unit: Bq/kg)

    地区238U226Ra228Ra40K参考文献
    范围平均值范围平均值范围平均值范围平均值
    大连湾26.4~47.034.911.2~25.319.3669~807746[24]
    莱州湾54.4±11.728.6±4.3057.9±9.70542±21.0[25]
    胶州湾32.4~56.239.2±8.8020.6~44.126.5±3.3035.7~53.340.3±4.80607~732688±58.0[26]
    长江口14.1~62.332.8±10.613.7~52.324.3±7.426.1~71.940.9±9.4392~898628±135[27]
    厦门海域11.5~65.140.227.5~4032.449.9~94.369.3510~1096692[28]
    大亚湾36.6~64.149.2±3.915.6~29.720.9±0.740.3~52.747.2±1.9360~482432±19[29]
    黄茅海—广海湾66.5~98.877.432.0~48.736.649.7~64.858.1505~644571[30]
    阳江海域75.2~102.082.4±5.232.6~38.635.5±2.040.9~70.657.1±3.1580~660621±29[31]
    白龙半岛12.0~87.048.3±20.210.3~51.832.4±9.4013.2~72.946.1±13.469.6~514355±125[32]
    南海东北部21.2~59.035.4±3.025.9~32.427.7±1.322.6~65.244.9±5.9273~686538±52[34]
    海南岛东部6.0~33.221.7±6.412.6~25.519.0±1.0[33]
    南沙海域19.9~70.214.1~14711.0~80.0155~868[35]
    中国土壤7.30~44938.5±21.12.80~53337.6±23.410.3~184454.6±51.3ND~1548584±183[36]
    南海珊瑚礁22.1~38.229.0±5.091.47~9.393.34±2.510.51~14.45.08±4.912.15~15424.4±49.1[20]
    北部湾5.07~43.224.7±11.64.33~42.222.2±10.77.76~88.834.4±18.70.16~588253±192本文
      注:"—"代表没有数据。
    下载: 导出CSV

    表  2  不同海域表层沉积物的辐射环境质量评价

    Tab.  2  Assessment of environmental radiation quality for sediments from other sea regions

    地点Raeq /Bq·kg−1HexHinD/nGy·h−1参考文献
    胶州湾1370.370.4465.5[26]
    莱州湾1530.410.4970.9[25]
    上海长江口1310.350.4262.3[27]
    大亚湾1220.330.3956.3[29]
    黄茅海−广海湾1640.440.5476.0[30]
    白龙半岛1210.330.4155.7[32]
    中国土壤1610.430.5474.9[36]
    南海珊瑚礁12.50.030.045.63[20]
    北部湾90.90.250.3141.7本研究
    国际推荐值3701.001.0084.0[2]
      注:"—"代表没有数据。
    下载: 导出CSV
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  • 收稿日期:  2019-04-25
  • 修回日期:  2019-07-03
  • 网络出版日期:  2020-11-18
  • 刊出日期:  2020-02-25

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