Bundt M, Krauss M, Blaser P, Wilcke W
Swiss Federal Institute for Forest, Snow, and Landscape Research (WSL), Birmensdorf, Switzerland.
J Environ Qual. 2001 Jul-Aug;30(4):1296-304. doi: 10.2134/jeq2001.3041296x.
Before wood ash can be safely used as a fertilizer in forests, possible negative effects such as input of organic contaminants or remobilization of contaminants already stored in the soil must be investigated. The objective of this study was to examine the effects of wood ash application on concentrations, storage, and distribution of polycyclic aromatic hydrocarbons (PAHs) and polychlorinated biphenyls (PCBs) in a Swiss forest soil. In May 1998, we added 8 Mg wood ash ha(-1) to a forest soil. We determined 20 PAHs and 14 PCBs in the organic layer, in the bulk mineral soil, and in soil material taken from preferential flow paths and from the matrix before and after the wood ash application. In the control plots, the concentrations of PAHs in the organic layer indicated moderate pollution (sum of 20 PAHs: 0.8-1.6 mg kg(-1)), but sum of PCB concentrations was high (21-48 microLg kg(-1)). The wood ash had high concentrations of PAHs (sum of 20 PAHs: 16.8 mg kg(-1)), but low concentrations of PCBs (sum of 14 PCBs: 3.4 microg kg(-1)). The wood ash application increased the PAH concentrations in the organic horizons up to sixfold. In contrast, PCB concentrations did not change in the Oa horizon and decreased up to one third in the Oi and Oe horizons. The decrease was probably caused by the mobilization of stored PCBs because of the high pH of the wood ash. This probably results in a higher mobility of dissolved organic matter, acting as PCB carrier. In the mineral soil, the preferential flow paths of the A horizon contained more PAHs and PCBs (+20 +/- 15% and +43 +/- 60%, respectively) than the matrix. This was particularly true for higher molecular weight compounds (molecular weight > 200 g mol(-1)). Below 50 cm depth, concentrations of PAHs and PCBs were smaller in the preferential flow paths, suggesting that in deeper depths, processes acting as sinks dominated over inputs in the preferential flow paths.
在木灰能够安全地用作森林肥料之前,必须对其可能产生的负面影响进行调查,比如有机污染物的输入或土壤中已储存污染物的再迁移。本研究的目的是考察在瑞士森林土壤中施用木灰对多环芳烃(PAHs)和多氯联苯(PCBs)的浓度、储存及分布的影响。1998年5月,我们向森林土壤中添加了8 Mg·ha⁻¹的木灰。在施用木灰前后,我们测定了有机层、矿质土总体以及取自优先流路径和基质的土壤物质中的20种PAHs和14种PCBs。在对照样地中,有机层中PAHs的浓度显示为中度污染(20种PAHs的总和:0.8 - 1.6 mg·kg⁻¹),但PCBs浓度总和较高(21 - 48 μg·kg⁻¹)。木灰中PAHs浓度较高(20种PAHs的总和:16.8 mg·kg⁻¹),但PCBs浓度较低(14种PCBs的总和:3.4 μg·kg⁻¹)。施用木灰使有机层中的PAH浓度增加了高达六倍。相比之下,Oa层中的PCB浓度没有变化,而Oi层和Oe层中的PCB浓度降低了多达三分之一。这种降低可能是由于木灰的高pH值导致储存的PCBs发生了迁移。这可能导致作为PCB载体的溶解有机物具有更高的迁移性。在矿质土中,A层的优先流路径所含的PAHs和PCBs分别比基质多(分别为 +20 ± 15%和 +43 ± 60%)。对于分子量较高的化合物(分子量 > 200 g·mol⁻¹)尤其如此。在50 cm深度以下,优先流路径中的PAHs和PCBs浓度较小,这表明在更深的深度,作为汇的过程比优先流路径中的输入更为重要。