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草业学报 ›› 2010, Vol. 19 ›› Issue (1): 67-74.

• 研究论文 • 上一篇    下一篇

东祁连山高寒草地返青期不同草地型土壤氮的分布特征

杨成德1,陈秀蓉1,龙瑞军2*,满元荣1,张俊忠1   

  1. 1.甘肃农业大学草业学院 草业生态系统教育部重点实验室 中-美草地畜牧业可持续发展研究中心,
    甘肃 兰州 730070;
    2.兰州大学草地农业科技学院,甘肃 兰州 730020
  • 收稿日期:2009-02-11 出版日期:2010-01-25 发布日期:2010-02-20
  • 作者简介:杨成德(1975-),男,甘肃武都人,副教授,博士。E-mail: yangcd@gsau.edu.cn,ycd3003@163.com
  • 基金资助:
    甘肃省自然科学基金(096RJZA003)和退化草原植被恢复与碳固定之间的研究(052456CHA-GS-Y-4)资助

Distribution characteristics of soil nitrogen during the greening period of forageunder different alpine grasslands in the eastern Qilian Mountain

YANG Cheng-de1, CHEN Xiu-rong1, LONG Rui-jun2, MAN Yuan-rong1, ZHANG Jun-zhong1   

  1. 1.College of Pratacultural Science, Gansu Agricultural University;
    Key Laboratory of Grassland
    Ecosystem, Ministry of Education;
    Sino-U.S. Center for Grazingland Ecosystem
    Sustainability, Lanzhou 730070, China;
    2.College of Pastoral Agriculture
    Science and Technology, Lanzhou University, Lanzhou 730020, China
  • Received:2009-02-11 Online:2010-01-25 Published:2010-02-20

摘要: 本试验在东祁连山选择代表性的7种高寒草地型为研究对象,在返青期对其土壤微生物量氮、全氮、K2SO4浸提氮、碱解氮、氮密度及其相关性进行了研究。结果表明,土壤全氮、碱解氮和氮密度分别介于4.2~7.9 g/kg、104.1~234.0 mg/kg和0.38~0.61 kg/m2。2005和2006年土壤K2SO4浸提氮分别介于3.4~11.4和1.8~13.9 mg/kg,占土壤微生物量氮的3.93%~11.62%和3.88%~15.37%。微生物量氮在2005和2006年分别介于49.0~143.0 mg/kg和35.9~171.7 mg/kg;与K2SO4浸提碳在灌丛草地呈显著正相关(P<0.05),在草本草地呈极显著正相关(P<0.01);与K2SO4浸提氮在杜鹃灌丛和高山柳灌丛呈极显著正相关(P<0.01),在金露梅灌丛和草本草地呈显著正相关(P<0.05)。除嵩草草地外,微生物量氮与微生物量碳和微生物量磷呈极显著正相关(P<0.01)。2005年K2SO4浸提氮和微生物量氮对土壤全氮贡献率分别为0.07%~0.16%和1.16%~1.93%。在东祁连山高寒草地,草地型间土壤全氮、碱解氮、K2SO4浸提氮及微生物量氮有明显差异,且草地型决定了微生物量氮的数量和生态分布,植物群落是影响微生物量氮数量和生态分布及其与土壤K2SO4浸提碳、氮相关性的关键因素之一;微生物量碳、氮、磷间的相关性由土壤微生物本身或其群落结构决定。

Abstract: Seven different alpine grassland types [Rhododendrons brushland (DJ), Salix cupularis brushland (GL), Potentilla fruticosa brushland (JL), Polygonum viviparum grassland (ZY), Grass steppe (HC), Swamp grassland (ZZ) and Kobresia grassland (SC)] in the eastern Qilian Mountains of the Qinghai-Tibetan Plateau, west China, were investigated for their soil nitrogen [Including microbial biomass nitrogen (MBN), soil total nitrogen, K2SO4-extractable nitrogen, alkali-hydrolysable nitrogen and nitrogen density] and their co-relationships. Soil total nitrogen, alkali-hydrolysable nitrogen, and nitrogen density varied from 4.2 to 7.9 g/kg, 104.1 to 234.0 mg/kg, and 0.38 to 0.61 kg/m2, respectively. In 2005 and 2006, K2SO4-extractable nitrogen ranged from 3.4 to 11.4 mg/kg and 1.8 to 13.9 mg/kg, respectively. The contribution of K2SO4-extractable nitrogen to MBN varied from 3.93% to 11.62% in 2005 and 3.88% to 15.37% in 2006. MBN ranged from 49.0 to 143.0 mg/kg in 2005 and 35.9 to 171.7 mg/kg in 2006. MBN showed a significant positive correlation at P<0.05 with K2SO4-extractable carbon under brushland and a significant positive correlation at P<0.01 with K2SO4-extractable carbon under grassland. It also showed a significant positive correlation at P<0.01 with K2SO4-extractable nitrogen under DJ and GL, and a significant positive correlation at P<0.05 with K2SO4-extractable nitrogen under JL, ZY, HC, ZZ and SC. With the exception of SC, MBN showed a significant positive correlation at P<0.01 with MBC or MBP. The contribution of K2SO4-extractable nitrogen or MBN to soil total nitrogen varied from 0.07% to 0.16% and 1.16% to 1.93% respectively in 2005. In the eastern Qilian Mountains of the Qinghai-Tibetan Plateau, the values of total nitrogen, K2SO4-extractable nitrogen, and alkali-hydrolysable nitrogen were differed between the different types of grassland. Furthermore, the type of grassland was the deciding factor for quantity and ecological distribution of soil MBN and plant communities, and was the important factor influencing their quantity and ecological distribution, and the co-relationship between MBN and K2SO4-extractable nitrogen or K2SO4-extractable carbon. The co-relationship between MBN and MBC or MBP was decided by soil microorganism communities or their community structure.

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