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Seasonal Dynamics of Biomass and Copper Concentrations in Ectohumus of Forest Soils Impacted by Copper Industry in South-West Poland

机译:波兰西南铜业影响森林土壤植物植物植入植物和铜浓度的季节性动态

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Humus plays an important role in the functioning of forest ecosystems. It acts as a link between above- and below-ground ecosystem compartments. The fall and decomposition of organic matter return minerals and energy to the soil biota. The forest floor is the most dynamic part of soil organic matter (Yanai et al. 2003). Previous studies about nutrient release from forest litters, formed under various tree species, show significant differences in dynamics of nutrients. The release of nutrient elements during decomposition of forest floor is an important internal pathway in nutrient flux of forested ecosystems. Nutrients may be released from ectohumus horizons by leaching or mineralization (Regina, 2000). Nutrient release from decomposing litter affects the primary productivity of ecosystem, since these nutrients become available for plant uptake and are not lost in the ecosystem. The rate at which nutrients are released depends on several factors: the chemical composition of the forest litter, the structural nature of the nutrient in the litter matrix, the microbial demand for the nutrient, and the availability of exogenous substance sources for example from anthropogenic activity (Brown et al., 1999). Litter quality affects the rates of mass loss, but also the patterns and rates of nutrient immobilization or release. Forest litter highly contaminated with heavy metals may effect nutrient cycling throughout the whole ecosystem (Tyler, 1974). Many reports have shown that short-term or long-term exposure to toxic metals results in the reduction of microbial diversity and activity which is mainly observed in inhibiting litter decomposition and increase of undecomposed organic matter in humus layer (Berg et al., 1991). From the other hand, forest litter acts like a sink for contaminants, regulating the amount of heavy metals leaching to deeper soil layers (Medynska and Kaba?a, 2007 Laskowski et al. 1995). Dynamics of heavy metals in contaminated forest floor is exceptionally investigated, and in particular - on recently afforested soils, where the ectohumus layer has been already formed.
机译:腐殖质发挥森林生态系统的功能具有重要作用。它作为地上和地下的生态系统的隔室之间的联系。秋季和有机物质回报矿物质的分解和精力土壤生物。森林的地面是土壤有机质最活跃的部分(柳井等人,2003)。关于森林凋落物,在各种树种形成养分释放以前的研究,显示在营养成分的动态显著差异。营养元素的落叶层分解过程中的释放是在森林生态系统的营养通量的重要的内部通路。营养物质可以从ectohumus视野通过沥滤或矿化(伊利,2000)被释放。从垃圾分解养分释放影响的生态系统的初级生产力,因为这些营养物质成为供植物吸收,并在生态系统中不会丢失。在该营养物释放的速率取决于几个因素:凋落的化学组成,在垫料基质营养的结构性质,对于营养微生物的需求,以及外源性物质来源例如从人类活动的可用性(Brown等,1999)。垫料质量会影响质量损失率,而且图案和养分的固定或释放速率。森林凋落物与重金属高污染可以在整个生态系统(泰勒,1974年)的影响养分循环。许多报告显示,短期或长期暴露于其中抑制垃圾分解和未分解的有机物增加腐殖质层主要观察到微生物多样性和活性的降低有毒金属结果(Berg等人,1991) 。从另一方面,凋落作用就像用于污染物的水槽,调节重金属浸出到更深的土壤层(Medynska和卡巴?一,2007年郭先生等人,1995)的量。在被污染的森林地面的重金属动力学异常调查,尤其是 - 在最近绿化的土壤,这里的ectohumus层已经形成。

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