南京林业大学学报(自然科学版) ›› 2010, Vol. 34 ›› Issue (06): 38-42.doi: 10.3969/j.jssn.1000-2006.2010.06.009

• 研究论文 • 上一篇    下一篇

次生栎林与火炬松人工林的土壤微生物量氮动态

吴春林1,2,陶忠芳1,3,王国兵1*,阮宏华1   

  1. 1.南京林业大学森林资源与环境学院,江苏南京210037;2.南京林业大学下蜀林场,江苏句容212411;3.安徽省林业调查规划院,安徽合肥230001
  • 出版日期:2010-12-27 发布日期:2010-12-27
  • 基金资助:
    收稿日期:2010-05-24修回日期:2010-10-08基金项目:国家林业局林业公益性行业科研专项项目(200804006,200704005/wb02);国家自然科学基金项目(30370256)作者简介:吴春 林(1963—),工程师。*王国兵(通信作者),讲师。Email: wangguobing81@yahoo.com.cn。引文格式:吴春林,陶忠芳,王国兵,等. 次生栎林与火炬松人工林的土壤微生物量氮动 态

The study on soil microbial biomass N in secondary oak forest and pine plantation

WU Chunlin1,2, TAO Zhongfang1,3, WANG Guobing1*, RUAN Honghua1   

  1. 1.College of Forest Resources and Environment, Nanjing Forestry University, Nanjing 210037, China; 2.The Xiashu Forest Farm of Nanjing Forestry University, Jurong 212411, China; 3.Forest Inventory and Planning Institute of Anhui Province, Hefei 230001, China
  • Online:2010-12-27 Published:2010-12-27

摘要: 为了阐明土壤微生物量氮(SMBN)对土壤中氮的植物有效性及氮循环的影响,从2006年4月到2007年4月对下蜀林场次生栎林和火炬松人工林中的SMBN进行了初步研究。结果表 明:(1)次生栎林与火炬松人工林SMBN均具有明显的季节动态变化,且变化规律基本一致,均表现为SMBN夏季最高,冬季最低,春秋两季居中;(2)自然情况下次生栎林SMBN显著大 于火炬松人工林的(p<0.01),而在凋落物去除后二者之间差异消失;(3)相关分析表明,SMBN和土壤微生物量碳(SMBC)在不同林分中均表现出显著正相关关系(p<0.05),但是与土壤 总氮、土壤湿度、凋落物输入量之间均无显著相关关系。总之,SMBN的季节变化主要受土壤微生物量季节变化的影响,其调控机理可能与土壤中碳、氮元素的供应及植物生长状况 有关,但凋落物的性质对SMBN含量具有显著的影响。

Abstract: In order to clarify the effects of soil microbial biomass N on soil N availability of plants and N cycling, SMBN, SMBC, soil N, litterfall input, and other factors were determined in a secondary oak forest and pine plantation in Xiashu experimental sites in Jiangsu province from April 2006 to April 2007, the results are as follows: (1)There are obvious seasonal dynamics of SMBN both in secondary oak forest and pine plantation, and the variation is consistent, which shows the highest microbial biomass N in summer, lowest in winter, spring and autumn are middle; (2)In the condition of the undisturbed natural state(control treatment), SMBN in oak forest is significantly larger than in pine plantation (p<0.01), but the difference between the two forest types disappear after the litterfall is removed(litterfall excluding treatment); (3)The correlation analysis shows that soil microbial biomass N is significantly and positively correlated to SMBC both in secondary oak forest and pine plantation (p<0.05), but not to soil nitrogen, soil moisture or litterfall input. Our results show that the obviously seasonal changes of SMBN mainly controlled by the seasonal changes of soil microbial biomass, which may be influenced by the soil C, N availability and the competition between soil microbial biomass and plant growth with the deeper reasons, but the properties of litterfall had a significant impact on the SMBN.

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