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应用生态学报 ›› 2012, Vol. 23 ›› Issue (09): 2404-2410.

• 研究报告 • 上一篇    下一篇

闽江河口湿地枯落物分解及主要影响因子

张林海1,3,曾从盛1,2,3**,张文娟1,王天鹅1,仝川1,2,3   

  1. (1福建师范大学地理科学学院, 福州 350007; 2湿润亚热带生态地理过程省部共建教育部重点实验室, 福州 350007; 3福建师范大学亚热带湿地研究中心, 福州 350007)
  • 出版日期:2012-09-18 发布日期:2012-09-18

Litter decomposition and its main affecting factors in tidal marshes of Minjiang Riverestuary, East China.

ZHANG Lin-hai1,3, ZENG Cong-sheng1,2,3, ZHANG Wen-juan1, WANG Tian-e1, TONG Chuan1,2,3   

  1. (1College of Geographical Sciences, Fujian Normal University, Fuzhou 350007, China; 2Ministry of Education Key Laboratory of Humid Subtropical Ecogeographical Process, Fuzhou 350007, China; 3Research Centre of Wetlands in Subtropical Regions, Fujian Normal University, Fuzhou 350007, China)
  • Online:2012-09-18 Published:2012-09-18

摘要: 以闽江河口湿地挺水植物本地种芦苇和入侵种互花米草的花和叶枯落物为研究对象,采用分解袋法分析其分解过程及主要影响因素.结果表明: 立枯分解(0~90 d)是2种湿地盐沼植物重要的分解阶段,芦苇和互花米草的花和叶质量损失率分别为(15.0±3.5)%、(13.3±1.1)%和(31.9±1.1)%、(20.8±1.4)%.倒伏分解阶段(91~210 d),芦苇和互花米草的花和叶质量损失率分别为(69.5±0.6)%、(71.5±2.5)%和(76.8±1.9)%、(67.5±2.1)%.在立枯分解阶段,2种挺水植物枯落物的分解速率与C/N呈正相关,与N/P呈负相关,分解过程受到P的限制程度较大.倒伏分解阶段,枯落物C/N、C/P和N/P的影响降低,而大气温湿度、土壤水分、酸碱度、盐度和沉积物特性等的影响加大.不同分解阶段枯落物分解影响因子的差异主要与其所处的微域环境和潮汐因素有关.

Abstract: By using litterbag method, this paper studied the decomposition of the leaf and flower litters of two emergent macrophytes, native species Phragmites australis and invasive species Spartina alterniflora, and related affecting factors in the Minjiang River estuary of East China. In the decomposition process of the litters, the decay of standing litter (0-90 days) was an important period, and the loss rate of the flower and leaf litters dry mass of P. australis and S. alterniflora was 15.0±3.5% and 13.3±1.1%, and 31.9±1.1% and 20.8±1.4%, respectively. During lodging decay period (91-210 days), the loss rate of the flower and leaf litters dry mass of P. australis and S. alterniflora was 69.5±0.6% and 71.5±2.5%, and 76.8±1.9% and 67.5±2.1%, respectively. In standing decay period, the decomposition rate of the two plants litters was positively correlated with the litters C/N but negatively correlated to the litters N/P, and the litters P was an important factor limiting the litters decay. In lodging decay period,  the effects of the litters C/N, C/P, and N/P decreased, while the
environment factors (climate, soil moisture, soil acidity and salinity, and sediment properties) acted more important roles. The differences in the factors affecting the decay of the litters in different decomposition periods were mainly related to the micro-environment and tidal process for the two plant communities.