单一汞同位素示踪大气与农田作物汞的交换过程

朱宗强, 王训, 王衡, LIN Che, 冯新斌. 单一汞同位素示踪大气与农田作物汞的交换过程[J]. 环境化学, 2018, 37(3): 419-427. doi: 10.7524/j.issn.0254-6108.2017080902
引用本文: 朱宗强, 王训, 王衡, LIN Che, 冯新斌. 单一汞同位素示踪大气与农田作物汞的交换过程[J]. 环境化学, 2018, 37(3): 419-427. doi: 10.7524/j.issn.0254-6108.2017080902
ZHU Zongqiang, WANG Xun, WANG Heng, LIN Che, FENG Xinbin. Mercury exchange process between crop foliage and atmosphere by using single mercury isotope[J]. Environmental Chemistry, 2018, 37(3): 419-427. doi: 10.7524/j.issn.0254-6108.2017080902
Citation: ZHU Zongqiang, WANG Xun, WANG Heng, LIN Che, FENG Xinbin. Mercury exchange process between crop foliage and atmosphere by using single mercury isotope[J]. Environmental Chemistry, 2018, 37(3): 419-427. doi: 10.7524/j.issn.0254-6108.2017080902

单一汞同位素示踪大气与农田作物汞的交换过程

  • 基金项目:

    国家科技部973项目(2013CB430002),国家自然科学基金重点项目(41430754)和环境地球化学国家重点实验室开放基金(SKLEG2017906)资助.

Mercury exchange process between crop foliage and atmosphere by using single mercury isotope

  • Fund Project: Supported by the National 973 Program of China (2013CB430002), Natural Science Foundation of China (41430754) and Opening Fund of the State Key Laboratory of Environmental Geochemistry (SKLEG2017906).
  • 摘要: 汞是引人注目的全球性污染物,植被叶片吸收是大气汞的主要去除途径之一.然而,当前对于大气-植被叶片汞通量交换过程及吸收后的汞在植被体内的归趋等认识尚有不明确之处.本文利用单一大气汞同位素标记技术,测定了大气汞浓度为0、2、5、10 ng·m-3时,C3植物水稻与C4植物玉米叶片汞交换通量的变化特征,并分析了标记的汞同位素在植被体中根-茎-叶的分布比例.结果表明:(1)水稻和玉米叶片汞的沉降通量与大气汞浓度呈显著正相关关系;(2)植物叶片汞的沉降通量有明显的昼夜变化,水稻和玉米的吸收通量白天均高于晚上;(3)玉米对大气汞的补偿点白天为0.63 ng·m-3,夜间为2.85 ng·m-3;水稻白天为1.24 ng·m-3,夜间为1.32 ng·m-3,水稻对大气汞的富集能力强于玉米,但二者的补偿点均显著低于国内大气汞浓度;(4)植被从大气吸收的汞主要集中在植物地上部,水稻叶片分布88.92%,茎中分布11.08%,而玉米叶片分布90.95%,茎中分布7.09%,根中分布1.96%.这些结果表明,农田系统的植被能富集大气中的汞,并主要贮存在叶片内部,向茎、根迁移量较少,是大气汞的重要汇.上述结论为进一步估算中国农田系统的大气汞汇与认识汞在大气-叶片-茎-根-土壤中循环提供了科学依据.
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  • [1] GUSTIN M S, BIESTER H, KIM C S. Investigation of the light-enhanced emission of mercury from naturally enriched substrates[J]. Atmospheric Environment, 2002, 36(20):3241-3254.
    [2] GUSTIN M S. Are mercury emissions from geologic sources significant? A status report[J]. Science of the Total Environment, 2003, 304(1-3):153-167.
    [3] GUSTIN M S, AMOS H M, HUANG J, et al. Measuring and modeling mercury in the atmosphere:A critical review[J]. Atmospheric Chemistry & Physics, 2015, 15(10):5697-5713.
    [4] AGNAN Y, LE D T, MOORE C W, et al. New constraints on terrestrial surface-atmosphere fluxes of gaseous elemental mercury using a global database[J]. Environmental Science & Technology, 2016, 50(2):507-524.
    [5] SCHULZE E D. Plant Life forms and their carbon, water and nutrient relations[M]. Berlin Heidelberg:Springer, 1982:615-676.
    [6] HANSON P J, LINDBERG S E, TABBERER T A, et al. Foliar exchange of mercury vapor:Evidence for a compensation point[J]. Water Air & Soil Pollution, 1995, 80(1-4):373-382.
    [7] FU X W, ZHU W, ZHANG H, et al. Depletion of atmospheric gaseous elemental mercury by plant uptake at Mt. Changbai, Northeast China[J]. Atmospheric Chemistry & Physics, 2016, 16(20):1-31.
    [8] MAO Y, LI Y, RICHARDS J, et al. Investigating uptake and translocation of mercury species by sawgrass (Cladium jamaicense) using a stable isotope tracer technique[J]. Environmental Science & Technology, 2013, 47(17):9678-9684.
    [9] CUI L W, FENG X B, LIN C J, et al. Accumulation and translocation of 198Hg in four crop species[J]. Environmental Toxicology & Chemistry, 2014, 33(2):334-340.
    [10] GREGER M, WANG Y, NEUSCHVTZ C. Absence of Hg transpiration by shoot after Hg uptake by roots of six terrestrial plant species[J]. Environmental Pollution, 2005, 134(2):201-208.
    [11] STRICKMAN R J, MITCHELL C P. Accumulation and translocation of methylmercury and inorganic mercury in Oryza sativa:An enriched isotope tracer study[J]. Science of the Total Environment, 2017, 574:1415-1423.
    [12] ASSAD M, PARELLE J, CAZAUX D, et al. Mercury uptake into poplar leaves[J]. Chemosphere, 2016, 146(3):1-7.
    [13] 颜紫云,冯新斌,LIN CHE-JEN,等.高效稳定的单一汞同位素大气发生系统[J]. 地球与环境, 2014,42(3):413-418.

    YAN Z Y, FENG X B, LIN C J, et al. The controlled atmospheric system that can produce efficientstable and single mercury isotope[J]. Earth and Environment, 2014, 42(3):413-418(in Chinese).

    [14] ECKLEY C S, GUSTIN M, LIN C J, et al. The influence of dynamic chamber design and operating parameters on calculated surface-to-air mercury fluxes[J]. Atmospheric Environment, 2010, 44(2):194-203.
    [15] SLEMR F, BRUNKE E G, EBINGHAUS R, et al. Worldwide trend of atmospheric mercury since 1995[J]. Atmospheric Chemistry & Physics, 2011, 11(1):4779-4787.
    [16] CHEN L G, LIU M, XU Z C, et al. Variation trends and influencing factors of total gaseous mercury inthe Pearl River Delta-A highly industrialised region in South China influenced by seasonal monsoons[J]. Atmospheric Environment, 2013, 77(7):757-766.
    [17] 付学吾,冯新斌,张辉.贵阳市大气气态总汞:Lumex RA-915AM与Tekran2537A的对比观测[J]. 生态学杂志,2011,30(5):939-943.

    FU X W, FENG X B, ZHANG H. atmospheric total gasous mercury concentration in Guiyang measurements intercomparison with Lumex RA-915AM and Tekran 2537A[J]. Chinese Journal of Ecology, 2011, 30(5):939-943(in Chinese).

    [18] RUTTER A P, SCHAUER J J, SHAFER M M, et al. Dry deposition of gaseous elemental mercury to plants and soils using mercury stable isotopes in a controlled environment[J]. Atmospheric Environment, 2011, 45(4):848-855.
    [19] HINTELMANN H, OGRINC N. Determination of stable mercury isotopes by ICP/MS and their application in environmental studies[M]. Washington DC:ACS Publications, 2002:321-338.
    [20] MILLHOLLEN A G, OBRIST D, GUSTIN M S. Mercury accumulation in grass and forb species as a function of atmospheric carbon dioxide concentrations and mercury exposures in air and soil[J]. Chemosphere, 2006, 65(5):889-897.
    [21] STAMENKOVIC J, GUSTIN M S, JOHNSON D W, et al. Atmospheric mercury exchange with a tallgrass prairie ecosystem housed in mesocosms[J]. Science of the Total Environment, 2008, 406(1-2):227-238.
    [22] POISSANT L, PILOTE M, YUMVIHOZE E, et al. Mercury concentrations and foliage/atmosphere fluxes in a maple forest ecosystem in Québec, Canada[J]. Journal of Geophysical Research-Atmospheres, 2008, 113:D10307.
    [23] STAMENKOVIC J, GUSTIN M S. Nonstomatal versus stomatal uptake of atmospheric mercury[J]. Environmental Science & Technology, 2009, 43(5):1367-1372.
    [24] LUO Y, DUAN L, DRISCOLL C T, et al. Foliage/atmosphere exchange of mercury in a subtropical coniferous forest in south China[J]. Journal of Geophysical Research-Biogeosciences, 2016, 121(7):2006-2016.
    [25] 赵曦,李娟,黄艺,等.珠三角某垃圾焚烧厂周边植物叶片汞含量空间格局及影响因素[J]. 生态毒理学报,2015,10(4):105-114.

    ZHAO X, LI J, HUANG Y, et al. Spatial pattern and influencing factors of mercury levels in leaves of plants surrounding a solid waste incinerator in the Pearl River Delta[J]. Asian Journal of Ecotoxicology, 2015, 10(4):105-114(in Chinese).

    [26] 牛振川,张晓山,陈进生,等.植被在大气汞收支中作用的研究进展与展望[J]. 生态毒理学报,2014,9(5):843-849.

    NIU Z C, ZHANG X S, CHEN J S, et al. The role of vegetation in atmospheric mercury budgets:Progresses and perspectives[J]. Asian Journal of Ecotoxicology, 2014, 9(5):843-849(in Chinese).

    [27] 刘婷,郑祥民,刘飞,等.上海市香樟树叶总汞含量时空分布及影响因素[J]. 环境化学,2017,36(3):486-495.

    LIU T, ZHENG X M, LIU F, et al. Seasonal and spatial distribution of mercury contents in camphora leaves and its influencing factors in Shanghai[J]. Environmental Chemistry, 2017, 36(3):486-495(in Chinese).

    [28] WANG X, BAO Z D, LIN C J, et al. Assessment of global mercury deposition through litterfall[J]. Environmental Science & Technology, 2016, 50(16):8548-8557.
    [29] OBRIST D, JOHNSON D W, LINDBERG S E, et al. Mercury distribution across 14 U.S. Forests. Part Ⅰ:Spatial patterns of concentrations in biomass, litter, and soils[J]. Environmental Science & Technology, 2011, 45(9):3974-3981.
    [30] DU S H, FANG S C. Uptake of elemental mercury vapor by C3, and C4, species[J]. Environmental & Experimental Botany, 1982, 22(4):437-443.
    [31] NIU Z C, ZHANG X, WANG Z, et al. Field controlled experiments of mercury accumulation in crops from air and soil[J]. Environmental Pollution, 2011, 159(10):2684-2689.
    [32] DU S H, FANG S C. Catalase activity of C3, and C4, species and its relationship to mercury vapor uptake[J]. Environmental & Experimental Botany, 1983, 23(4):347-353.
    [33] GRAYDON J A, ST LOUIS V L, LINDBERG S E, et al. Investigation of mercury exchange between forest canopy vegetation and the atmosphere using a new dynamic chamber[J]. Environmental Science & Technology, 2006, 40(15):4680-4688.
    [34] LAACOURI A, NATER E A, KOLKA R K. Distribution and uptake dynamics of mercury in leaves of common deciduous tree species in Minnesota, U.S.A.[J]. Environmental Science & Technology, 2013, 47(18):10462-10470.
    [35] ZHANG H H, POISSANT L, XU X, et al. Explorative and innovative dynamic flux bag method development and testing for mercury air-vegetation gas exchange fluxes[J]. Atmospheric Environment, 2005, 39(39):7481-7493.
    [36] 陈剑,王章玮,张晓山,等.开顶式气室原位研究水稻汞富集对大气汞浓度升高的响应[J]. 环境科学, 2015, 36(8):2997-3003.

    CHEN J, WANG Z W, ZHANG X S, et al. Open-top chamber for in situ research on response of mercury enrichment in rice to the rising gaseous elemental mercury in the atmosphere[J]. Environmental Science, 2015, 36(8):2997-3003(in Chinese).

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出版历程
  • 收稿日期:  2017-08-09
  • 刊出日期:  2018-03-15
朱宗强, 王训, 王衡, LIN Che, 冯新斌. 单一汞同位素示踪大气与农田作物汞的交换过程[J]. 环境化学, 2018, 37(3): 419-427. doi: 10.7524/j.issn.0254-6108.2017080902
引用本文: 朱宗强, 王训, 王衡, LIN Che, 冯新斌. 单一汞同位素示踪大气与农田作物汞的交换过程[J]. 环境化学, 2018, 37(3): 419-427. doi: 10.7524/j.issn.0254-6108.2017080902
ZHU Zongqiang, WANG Xun, WANG Heng, LIN Che, FENG Xinbin. Mercury exchange process between crop foliage and atmosphere by using single mercury isotope[J]. Environmental Chemistry, 2018, 37(3): 419-427. doi: 10.7524/j.issn.0254-6108.2017080902
Citation: ZHU Zongqiang, WANG Xun, WANG Heng, LIN Che, FENG Xinbin. Mercury exchange process between crop foliage and atmosphere by using single mercury isotope[J]. Environmental Chemistry, 2018, 37(3): 419-427. doi: 10.7524/j.issn.0254-6108.2017080902

单一汞同位素示踪大气与农田作物汞的交换过程

  • 1.  中国科学院地球化学研究所环境地球化学国家重点实验室, 贵阳, 550081;
  • 2.  中国科学院大学, 北京, 100049;
  • 3.  Lamar 大学土木工程学院, Beaumont Texas, USA
基金项目:

国家科技部973项目(2013CB430002),国家自然科学基金重点项目(41430754)和环境地球化学国家重点实验室开放基金(SKLEG2017906)资助.

摘要: 汞是引人注目的全球性污染物,植被叶片吸收是大气汞的主要去除途径之一.然而,当前对于大气-植被叶片汞通量交换过程及吸收后的汞在植被体内的归趋等认识尚有不明确之处.本文利用单一大气汞同位素标记技术,测定了大气汞浓度为0、2、5、10 ng·m-3时,C3植物水稻与C4植物玉米叶片汞交换通量的变化特征,并分析了标记的汞同位素在植被体中根-茎-叶的分布比例.结果表明:(1)水稻和玉米叶片汞的沉降通量与大气汞浓度呈显著正相关关系;(2)植物叶片汞的沉降通量有明显的昼夜变化,水稻和玉米的吸收通量白天均高于晚上;(3)玉米对大气汞的补偿点白天为0.63 ng·m-3,夜间为2.85 ng·m-3;水稻白天为1.24 ng·m-3,夜间为1.32 ng·m-3,水稻对大气汞的富集能力强于玉米,但二者的补偿点均显著低于国内大气汞浓度;(4)植被从大气吸收的汞主要集中在植物地上部,水稻叶片分布88.92%,茎中分布11.08%,而玉米叶片分布90.95%,茎中分布7.09%,根中分布1.96%.这些结果表明,农田系统的植被能富集大气中的汞,并主要贮存在叶片内部,向茎、根迁移量较少,是大气汞的重要汇.上述结论为进一步估算中国农田系统的大气汞汇与认识汞在大气-叶片-茎-根-土壤中循环提供了科学依据.

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