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酸性森林土壤中Ali/(Ca+Mg)摩尔比值的分布特征及影响因素
引用本文:郭景恒,张晓山,蒋春来,赵大为,涂志江,向仁军,罗家海.酸性森林土壤中Ali/(Ca+Mg)摩尔比值的分布特征及影响因素[J].应用生态学报,2006,17(7):1207-1212.
作者姓名:郭景恒  张晓山  蒋春来  赵大为  涂志江  向仁军  罗家海
作者单位:1. 中国科学院生态环境研究中心,北京,100085
2. 重庆环境科学研究院,重庆,400020
3. 贵州省环境科学设计研究院,贵阳,550002
4. 湖南环境保护科学研究院,长沙,410004
5. 广州市环境保护科学研究所,广州,510620
基金项目:国家自然科学基金;科技部科研项目;中国-挪威合作项目
摘    要:研究了西南和华南酸性森林土壤中Ali/(Ca+Mg)摩尔比值的分布特征与影响因素,用主成分分析(PCA)和偏最小二乘法(PLS)回归综合评价各种影响因素及其相对重要性. 2000~2002年连续3年的监测结果表明,大多数土壤水中该摩尔比值都小于临界值1.0,说明土壤铝释放还未对植被造成显著伤害.偏最小二乘法(PLS)回归显示,土壤铝饱和度(AlS)是影响A层土壤水中Ali/(Ca+Mg)摩尔比值的首要因素;土壤铝饱和度愈高,土壤水中Ali/(Ca+Mg)摩尔比值愈高.5个流域中,尽管流溪河流域酸沉降量偏低,但由于土壤铝饱和度较高,A层土壤水中Ali/(Ca+Mg)摩尔比值高于其他流域.土壤水中无机铝(Ali)浓度是影响深层(B1、B2、BC层)土壤水中Ali/(Ca+Mg)摩尔比值的主导因素;土壤水中无机铝浓度愈高,Ali/(Ca+Mg)摩尔比值愈高.各流域内摩尔比值沿土壤深度的变化与无机铝浓度的变化基本一致.可以认为,土壤铝饱和度是影响土壤水中Ali/(Ca+Mg)摩尔比值区域性差异的主要因素,土壤水中无机铝浓度是影响Ali/(Ca+Mg)摩尔比值纵向差异的主要因素.

关 键 词:Ali/(Ca  Mg)摩尔比值  酸性森林土壤  酸沉降
文章编号:1001-9332(2006)07-1207-06
收稿时间:2005-07-08
修稿时间:2006-05-05

Distribution characters and affecting factors of Ali/(Ca+Mg) molar ratio in acid forest soils
GUO Jingheng,ZHANG Xiaoshan,JIANG Chunlai,ZHAO Dawei,TU Zhijiang,XIANG Renjun,LUO Jiahai.Distribution characters and affecting factors of Ali/(Ca+Mg) molar ratio in acid forest soils[J].Chinese Journal of Applied Ecology,2006,17(7):1207-1212.
Authors:GUO Jingheng  ZHANG Xiaoshan  JIANG Chunlai  ZHAO Dawei  TU Zhijiang  XIANG Renjun  LUO Jiahai
Institution:1Research Center for Eco-Environmental Sciences, Chinese Academy of Sciences, Beijing 100085, China; 2 Chongqing Academy of Environmental Sciences and Monitoring, Chongqing 400020, China; 3 Guizhou Academy of Environmental Protection Sciences, Guiyang 550002, China; 4Hunan Academy of Environmental Protection Sciences, Changsha 410004, China; 5 Guangzhou Research Institute of Environmental Protection Sciences, Guangzhou 510620, China
Abstract:By using principle component analysis(PCA) and partial least square(PLS) regression,this paper studied the distribution characters and their affecting factors of Al_i/(Ca+Mg) molar ratio in acid forest soils in southern and southwestern China.The monitoring data from 2000 to 2002 showed that in most cases,the Al_i/(Ca+Mg) molar ratio in soil moisture was lower than assumed critical value 1.0,indicating that significant aluminum toxicity to vegetation was not occurred in the study regions.PLS regression suggested that soil aluminum saturation(AlS) was the dominant factor affecting the Al_i/(Ca+Mg) molar ratio in soil A horizon.Higher AlS led to a higher Al_i/(Ca+Mg) molar ratio in soil moisture.Despite of its lower acid deposition,Liuxihe basin had a higher Al_i/(Ca+Mg) molar ratio in soil A horizon than other catchments,mainly due to its higher AIS.In deeper soil horizons(B_1,B_2 and BC),the inorganic aluminum(Al_i) in soil moisture was the main factor affecting Al_i/(Ca+Mg) molar ratio.Higher inorganic aluminum concentration resulted in higher Al_i/(Ca+Mg) molar ratio.In each of study catchments,the vertical distribution of Al_i/(Ca+Mg) molar ratio was basically identical with the distribution of inorganic aluminum(Al_i) through soil profile.It was concluded that soil aluminum saturation was the main factor controlling the regional variation of Al_i/(Ca+Mg) molar ratio in soil moisture,and the vertical distribution of soil Al_i/(Ca+Mg) molar ratio in each site was mainly due to the vertical change of inorganic aluminum in soil moisture.
Keywords:Al_i/(Ca+Mg) molar ratio  Acid forest soil  Acid deposition  
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