欢迎访问中国科学院大学学报,今天是
生物学

自然丰度法与同位素稀释法测定植物固氮能力的比较

  • 李润富 ,
  • 牛海山 ,
  • 孔倩 ,
  • 刘强
展开
  • 中国科学院大学资源与环境学院, 北京 101408

收稿日期: 2020-10-26

  修回日期: 2021-01-28

  网络出版日期: 2021-01-28

基金资助

中国科学院战略性先导科技专项(XDA20050103)资助

Comparison of natural 15N abundance technique and 15N dilution technique in the determination of plant nitrogen fixation

  • LI Runfu ,
  • NIU Haishan ,
  • KONG Qian ,
  • LIU Qiang
Expand
  • College of Resources and Environment, University of Chinese Academy of Sciences, Beijing 101408, China

Received date: 2020-10-26

  Revised date: 2021-01-28

  Online published: 2021-01-28

摘要

生物固氮是生态系统有效氮的重要来源,目前存在多种测定和计算方法。以青藏高原高寒草原豆科植物团垫黄芪(Astragalus arnoldii)为对象,对比自然丰度法和同位素稀释法的差异,探讨4种计算方法、4种参考植物和2个取样时间对团垫黄芪生物固氮百分率(% Ndfa)评估的影响。结果表明:参考植物的δ15N在自然生长状态下与7月份相比,8月份均显著降低(P<0.05);施加(15NH42SO4后,4种参考植物紫花针茅(Stipa purpurea)、高山嵩草(Kobresia pygmaea)、矮火绒草(Leontopodium nanum)和青藏苔草(Carex moorcroftii)24h取样的测定值高于30d后取样的测定值(P<0.05)。无论标记与否,团垫黄芪的15N丰度在2个采样时间都无明显差异,采用原子百分超和原子百分差这2种计算方法得到的% Ndfa也没有显著差异。除矮火绒草外,以其他3种植物以及4种植物的平均值作为参考时,采用自然丰度法计算的% Ndfa都显著高于同位素稀释法(P<0.05)。取样时间不同自然丰度法的测定结果差异显著(F=89.906,P<0.01),标记后取样时长对同位素稀释法影响显著(F=496.712,P<0.01)。

本文引用格式

李润富 , 牛海山 , 孔倩 , 刘强 . 自然丰度法与同位素稀释法测定植物固氮能力的比较[J]. 中国科学院大学学报, 2022 , 39(1) : 34 -42 . DOI: 10.7523/j.ucas.2021.0008

Abstract

Biological nitrogen fixation (BNF) is an important source of nitrogen in ecosystem, therefore, several experimental techniques and calculating methods have been developed to quantify the contribution of BNF to plants and vegetations. In this study, percentage of plant N derived from N2-fixation (%Ndfa) was evaluated for a leguminous species, Astragalus arnoldii, in an alpine steppe in Qinghai-Tibet Plateau in order to compare two dominant in situ experimental techniques with different calculating approaches, reference plants, and sampling times. The δ15N values of four reference plants, i.e., Stipa purpurea, Kobresia pygmaea, Leontopodium nanum, and Carex moorcroftii, were significantly lower in late August than in late July (P<0.05). However, they were significantly higher in later August, 30 days after application of (15NH4)2SO4 to soil, than late July which was 24h after labeling (P<0.05). In either site with or without (15NH4)2SO4 application, δ15N of A. arnoldii did not differ in the two sampling times. Besides,%Ndfa of A. arnoldii did not differ between calculation based on 15N excess relative to atmospheric N2 and that relative to unlabeled plants. Nevertheless,%Ndfa measured by natural abundance technique was significantly higher than that by isotope dilution technique (P<0.05) except for L. nanum as the reference species. The sampling time had a significant effect on estimated%Ndfa values in both the naturalabundance technique (F=89.906, P<0.01), and isotope dilution technique (F=496.712, P<0.01).

参考文献

[1] Vicente E J, Dean D R. Keeping the nitrogen-fixation dream alive[J]. Proceedings of the National Academy of Sciences of the United States of America, 2017, 114(12):3009-3011.
[2] 何道文, 孙辉, 黄雪菊. 利用N-15自然丰度法研究固氮植物生物固氮量[J]. 干旱地区农业研究, 2004, 22(1):132-137.
[3] 陈朝勋, 席琳乔, 姚拓, 等. 生物固氮测定方法研究进展[J]. 草原与草坪, 2005, 25(2):24-26.
[4] Hong J T, Ma X X, Zhang X K, et al. Nitrogen uptake pattern of herbaceous plants:coping strategies in altered neighbor species[J]. Biology and Fertility of Soils, 2017, 53(7):729-735.
[5] Xu X L, Ouyang H, Cao G M, et al. Dominant plant species shift their nitrogen uptake patterns in response to nutrient enrichment caused by a fungal fairy in an alpine meadow[J]. Plant and Soil, 2011, 341(1/2):495-504.
[6] Schleuss P M, Heitkamp F, Sun Y, et al. Nitrogen uptake in an alpine Kobresia pasture on the Tibetan Plateau:localization by 15N labeling and implications for a vulnerable ecosystem[J]. Ecosystems, 2015, 18(6):946-957.
[7] Carranca C, de Varennes A, Rolston D E. Biological nitrogen fixation estimated by 15N dilution, natural 15N abundance, and N difference techniques in a subterranean clover-grass sward under Mediterranean conditions[J]. European Journal of Agronomy, 1999, 10(2):81-89.
[8] Lonati M, Probo M, Gorlier A, et al. Nitrogen fixation assessment in a legume-dominant alpine community:comparison of different reference species using the 15N isotope dilution technique[J]. Alpine Botany, 2015, 125(1):51-58.
[9] Yang B J, Qiao N, Xu X L, et al. Symbiotic nitrogen fixation by legumes in two Chinese grasslands estimated with the 15N dilution technique[J]. Nutrient Cycling in Agroecosystems, 2011, 91(1):91-98.
[10] McAuliffe C, Chamblee D S, Uribe-Arango H, et al. Influence of inorganic nitrogen on nitrogen fixation by legumes as revealed by N15[J]. Agronomy Journal, 1958, 50(6):334-337.
[11] Arnone Ⅲ J A. Symbiotic N2 fixation in a high Alpine grassland:effects of four growing seasons of elevated CO2[J]. Functional Ecology, 1999, 13(3):383-387.
[12] Che R X, Deng Y C, Wang F, et al. Autotrophic and symbiotic diazotrophs dominate nitrogen-fixing communities in Tibetan grassland soils[J]. Science of the Total Environment, 2018, 639:997-1006.
[13] Jacot K A, Lüscher A, Nösberger J, et al. The relative contribution of symbiotic N2 fixation and other nitrogen sources to grassland ecosystems along an altitudinal gradient in the Alps[J]. Plant and Soil, 2000, 225(1/2):201-211.
[14] 代冬雪. 西藏高寒草原豆科与非豆科优势植物群落生物固氮功能比较研究[D]. 北京:中国科学院大学, 2015.
[15] Yang K, He J, Tang W J, et al. On downward shortwave and longwave radiations over high altitude regions:observation and modeling in the Tibetan Plateau[J]. Agricultural and Forest Meteorology, 2010, 150(1):38-46.
[16] Ledgard S F, Simpson J R, Freney J R, et al. Field evaluation of 15N techniques for estimating nitrogen fixation in legume-grass associations[J]. Australian Journal of Agricultural Research, 1985, 36(2):247.
[17] Rennie R J, Dubetz S. Nitrogen-15-determined nitrogen fixation in field-grown chickpea, lentil, fababean, and field pea[J]. Agronomy Journal, 1986, 78(4):654-660.
[18] Sun Y, Schleuss P M, Pausch J, et al. Nitrogen pools and cycles in Tibetan Kobresia pastures depending on grazing[J]. Biology and Fertility of Soils, 2018, 54(5):569-581.
[19] Ti C P, Pan J J, Xia Y Q, et al. A nitrogen budget of mainland China with spatial and temporal variation[J]. Biogeochemistry, 2012, 108(1/2/3):381-394.
[20] Bowman W D, Schardt J C, Schmidt S K. Symbiotic N2-fixation in alpine tundra:ecosystem input and variation in fixation rates among communities[J]. Oecologia, 1996, 108(2):345-350.
[21] Jacot K A, Lüscher A, Nösberger J, et al. Symbiotic N2 fixation of various legume species along an altitudinal gradient in the Swiss Alps[J]. Soil Biology and Biochemistry, 2000, 32(8/9):1043-1052.
[22] Boddey R M, Urquiaga S, Neves M C P, et al. Quantification of the contribution of N2 fixation to field-grown grain legumes:a strategy for the practical application of the 15N isotope dilution technique[J]. Soil Biology and Biochemistry, 1990, 22(5):649-655.
[23] 罗绪强, 张桂玲, 杨鸿雁, 等. 喀斯特山地不同退化植被下烟管荚蒾氮同位素组成的季节变化[J]. 科学技术与工程, 2020, 20(11):4243-4249.
[24] 苏波, 韩兴国, 黄建辉. 15N自然丰度法在生态系统氮素循环研究中的应用[J]. 生态学报, 1999, 19(3):408-416.
[25] Chalk P M, Ladha J K. Estimation of legume symbiotic dependence:an evaluation of techniques based on 15N dilution[J]. Soil Biology and Biochemistry, 1999, 31(14):1901-1917.
[26] Yang L J, Zhang L L, Geisseler D, et al. Available C and N affect the utilization of glycine by soil microorganisms[J]. Geoderma, 2016, 283:32-38.
[27] Hossain S A, Waring S A, Strong W M, et al. Estimates of nitrogen fixations by legumes in alternate cropping systems at Warra, Queensland, using enriched-15N dilution and natural 15N abundance techniques[J]. Australian Journal of Agricultural Research, 1995, 46(3):493-505.
[28] Burchill W, James E K, Li D, et al. Comparisons of biological nitrogen fixation in association with white clover (Trifolium repens L.) under four fertiliser nitrogen inputs as measured using two 15N techniques[J]. Plant and Soil, 2014, 385(1/2):287-302.
[29] Høgh-Jensen H, Schjoerring J K. Measurement of biological dinitrogen fixation in grassland:comparison of the enriched 15N dilution and the natural 15N abundance methods at different nitrogen application rates and defoliation frequencies[J]. Plant and Soil, 1994, 166(2):153-163.
文章导航

/