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Evaluating main factors controlling aluminum solubility in acid forest soils, southern and southwestern China

机译:评估控制铝在中国南方和西南地区酸性森林土壤中溶解度的主要因素

摘要

The mechanism controlling Al solubility in Chinese acidic forest soils is not clearly understood. This is the main limitation to the ability to generate adequate dose-response prediction models of the ecological effect of acid rain. To evaluate the relative significance of possible processes, soils and soil solutions from five forest catchments, located in southern and southwestern China, were collected and analyzed for chemical parameters. Monitoring showed that inorganic Al (Al-i) was the dominant fraction in most soil solutions; organic Al (Al-o) was usually less than 10% of total monomeric Al (Al-a). Aluminum fractions varied significantly between and within the different sites, though appearing to follow a similar pattern. Over the entire pH range of 3.6-5.6, the pAl (i.e. -log of the Al3+ activity) closely correlated with solution pH, following regression slopes of 1.28 and 2.00 for upper and lower soil horizons, respectively. The variations in Al3+ activity could not be explained satisfactorily using mineral dissolution equilibria. Partial least square (PLS) regression showed that soil acidity (quality) and ionic strength (intensity) of the solution were the main explanatory variables for the variation in the concentration of All fractions. Aluminum in upper horizons originated from both organic and inorganic solid Al pools, while aqueous Al in lower horizons was dominantly of inorganic origin. Aluminum solubility was strongly influenced by cation exchange, especially in the upper horizon. In the upper horizon, ionic strength (I) had a greater influence on Al solubility due to cation exchange reaction. In the lower horizon, dissolution of inorganic Al pools by the elevated H+ concentrations was the main Al release mechanism. So Al activity was more dependent on H+ (or pH) in the lower horizon. (c) 2006 Elsevier Ltd. All rights reserved.
机译:目前尚不清楚控制铝在中国酸性森林土壤中溶解度的机制。这是产生足够的酸雨生态效应剂量反应预测模型的能力的主要限制。为了评估可能过程的相对重要性,收集了中国南部和西南部五个森林集水区的土壤和土壤溶液,并对其化学参数进行了分析。监测表明,在大多数土壤溶液中,无机铝(Al-i)是主要成分。有机铝(Al-o)通常少于总单体铝(Al-a)的10%。铝含量在不同部位之间和之内变化很大,尽管看起来遵循相似的模式。在3.6-5.6的整个pH范围内,pAl(即Al3 +活性的对数)与溶液pH密切相关,分别对应于上层和下层土壤层的1.28和2.00回归斜率。使用矿物溶解平衡无法令人满意地解释Al3 +活性的变化。偏最小二乘(PLS)回归表明,溶液的土壤酸度(质量)和离子强度(强度)是所有馏分浓度变化的主要解释变量。上层铝是有机和无机固体铝的来源,而下层铝水主要是无机的。铝的溶解度受到阳离子交换的强烈影响,尤其是在上部地平线上。在较高的视野中,由于阳离子交换反应,离子强度(I)对Al的溶解度影响更大。在较低的视野中,通过增加的H +浓度来溶解无机Al池是Al释放的主要机理。因此,Al的活性在较低水平时更依赖于H +(或pH)。 (c)2006 Elsevier Ltd.保留所有权利。

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