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格氏栲天然林与人工林土壤异养呼吸特性及动态
引用本文:杨玉盛,陈光水,谢锦升,王小国,牛志鹏,韩永刚,张有利. 格氏栲天然林与人工林土壤异养呼吸特性及动态[J]. 土壤学报, 2006, 43(1): 53-61
作者姓名:杨玉盛  陈光水  谢锦升  王小国  牛志鹏  韩永刚  张有利
作者单位:1. 福建师范大学地理科学学院,亚热带资源与环境省重点实验室,福州,350007
2. 福建农林大学林学院,福州,350002
基金项目:高等学校优秀青年教师教学科研奖励计划;福建省基础性研究计划;教育部科学技术研究项目
摘    要:通过用静态碱吸收法对中亚热带福建三明格氏栲自然保护区内的格氏栲天然林和33年生的格氏栲人工林及杉木人工林的土壤异养呼吸进行为期2年的定位研究。结果表明,三种森林枯枝落叶层呼吸和无根土壤呼吸速率季节变化均呈单峰曲线,最大峰值出现在5月至6月,最小值出现在12月至1月。格氏栲天然林、格氏栲人工林和杉木人工林枯枝落叶层呼吸速率平均值分别为CO2 79.88、44.37和21.02mgm^-2h^-1,无根土壤呼吸速率平均值分别为CO2 217.4、85.85和94.04mg m^-2h^-1。2002年枯枝落叶层呼吸速率和无根土壤呼吸速率主要受土壤温度影响,但在极端干旱的2003年则主要受土壤湿度的影响。双因素关系模型(R=ae^bTW^c)拟合结果优于仅考虑土壤温度或土壤湿度的单因素关系模型,土壤温度和土壤湿度共同解释不同年份枯枝落叶层呼吸和无根土壤呼吸速率季节变化的82%~85%和85%~92%。不同森林枯枝落叶层呼吸对土壤温度和湿度的敏感性均高于无根土壤呼吸的。格氏栲天然林、格氏栲人工林和杉木人工林枯枝落叶层呼吸年通量分别为C3.76、2.63和1.23t hm^-2a^-1,无根土壤呼吸年通量则分别为C3.44、2.79和1.49t hm^-2a^-1。不同森林土壤异养呼吸通量的差异主要与枯落物数量和质量、土壤有机质数量和质量的差异有关。杉木林枯枝落叶层呼吸对干旱敏感性高于格氏栲(天然林和人工林)的,而人工林(杉木和格氏栲)的土壤有机C对干旱敏感性则要高于格氏栲天然林。

关 键 词:天然林  人工林  土壤异养呼吸  土壤温度  土壤湿度
收稿时间:2004-12-17
修稿时间:2004-12-172005-04-12

SOIL HETEROTROPHIC RESPIRATION IN NATIVE CASTANOPSIS KAWAKAMII FOREST AND MONOCULTURE CASTANOPSIS KAWAKAMII PLANTATIONS IN SUBTROPICAL CHINA
Yang Yusheng,Chen Guangshui,Xie Jinsheng,Wang Xiaoguo,Niu Zhipeng,Han Yonggang and Zhang Youli. SOIL HETEROTROPHIC RESPIRATION IN NATIVE CASTANOPSIS KAWAKAMII FOREST AND MONOCULTURE CASTANOPSIS KAWAKAMII PLANTATIONS IN SUBTROPICAL CHINA[J]. Acta Pedologica Sinica, 2006, 43(1): 53-61
Authors:Yang Yusheng  Chen Guangshui  Xie Jinsheng  Wang Xiaoguo  Niu Zhipeng  Han Yonggang  Zhang Youli
Affiliation:1 Key Laboratory of Subtropical Resources and Environments of Fujian Province, College of Geography Sciences, Fujian Normal University, Fuzhou 350007, China;2 College of Forestry, Fujian Agricuture and Forestry University, Fuzhou 350002, China
Abstract:Soil heterotrophic respiration(HR)was investigated in one tract of native Castanopsis kawakamii forest(NF), a 33-year-old Castanopsis kawakamii plantation(CK)and a Cunninghamia lanceolata(Chinese fir,CF)plantation of the same age in Sanming,Fujian Province,China.Soil CO2 efflux was measured in situ in a 2-year period with the alkali sorption technique.Respirations of root-free soils(RRF)and litter layer(RL)were measured separately by trenching and removing litter, respectively.Both RRF and RL in the three forests showed a similar seasonal pattern with o ne single peak occurring during May or June and a valley during December or January.RL averaged CO2 79188,44137 and 21102 mg m-2 h-1,and RRF averaged CO2 21714,85185 and 94104 mg m-2 h-1 in NF,CK and CF,respectively.The model R=aebTWc (R stands for soil CO2 efflux, T for soil temperature and W for soil water content at 0~10 cm soil depth,and a,b,c for the constants)indicated that soil temperature and soil water content together could explain 82%~85% and 85%~92% of RL and RRF,respectively,with soil temperature being the dominating factor affecting soil respiration rate in 2002 and soil humidity in a dry year of 2003.RL was more sensitive to variation in soil temperature and humidity than RRF.Annual RL averaged C 3176,2163 and 1123 t hm-2 a-1, and annual RRF averaged C 3144,2179 and 1149 t hm-2 a-1,respectively,in the NF,CK,and CF.Differences in soil heterotrophic respiration between forests were associated with differences in quantity and quality of organic inputs,biomass and activity of roots,and content and components of soil organic carbon.RL in CF showed higher sensitivity to drought than in CK and NF,and the sensitivity of soil organic C to drought was higher in the plantations(CK and CF)than in the native forest (NF).
Keywords:Native forest   Plantation forest   Soil heterotrophic respiration   Soil temperature   Soil humidity
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