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Wood ash use in forestry - a review of the environmental impacts.

机译:林业中使用木灰-对环境影响的回顾。

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The use of wood fuel for energy production in the UK is set to increase in the near future as part of a government commitment to increase renewable sources by 10% by 2010. The ash generated as a by-product of combustion, whether for heat or power generation, has potential use as a fertilizer in forest systems. This review assesses the available information on factors affecting the quality of the ash and environmental implications arising from its application. The key determinants of wood ash chemistry are the tree species combusted, the nature of the burn process and the conditions at the application site. Wood ash from hardwood species produces higher levels of macronutrients in their ash than conifers, and the silica content is frequently lower. A furnace temperature between 500 and 900 degrees C is critical to the retention of nutrients, particularly potassium, and determines the concentrations of potentially toxic metals including aluminium in the ash. Fly ash, the lightest component that accumulates in the flue system, can contain high concentrations of cadmium, copper, chromium, lead and arsenic and this ash should not be used as fertilizer. The form of the ash at application is important, with loose ash releasing calcium, potassium and sodium more rapidly than granulated ash. Heavy metal, radionuclide and dioxin contamination of wood ash-based fertilizers is minimal and unlikely to affect ecosystem function. The effects of wood ash are primarily governed by application rate and soil type. The benefits are maximized at low rates, with possible toxicity from applications in excess of 10 t ha-1. For most forest sites, a single wood ash application per rotation could replace all the nutrients lost after whole-tree harvesting (excepting nitrogen). Long-lasting positive effects on tree growth have been observed on shallow peats, in which the humus is slowly mineralized in response to elevated pH and increased nutrient availability. In contrast, wood ash application to Podzols is only effective in enhancing tree growth when nitrogen availability is non-limiting. To date, published research of wood ash effects on trees growing in clays and loams is minimal. A lag time for positive tree responses to wood ash application is often observed, and may be the result of phosphorous limitation at higher soil pH. The greatest reported adverse ecological effects are to acidophilic ecosystems, particularly the constituent bryophyte, soil bacteria and ectomycorrhizal communities..
机译:作为政府承诺到2010年将可再生能源增加10%的一部分,英国将在不久的将来使用木燃料生产能源。灰烬是燃烧产生的副产物,无论是热能还是热能。发电,有可能在森林系统中用作肥料。这项评估评估了有关影响灰分质量的因素以及由灰分产生的环境影响的可用信息。决定木灰化学性质的关键因素是燃烧的树木种类,燃烧过程的性质以及施工现场的条件。与针叶树相比,来自硬木树种的木灰在其灰分中可产生更高水平的大量营养素,并且二氧化硅含量通常较低。 500到900摄氏度之间的炉温对于保留养分(尤其是钾)至关重要,它决定了烟灰中包括铝在内的潜在有毒金属的浓度。粉煤灰是烟道系统中积累的最轻的成分,它可能含有高浓度的镉,铜,铬,铅和砷,因此不应将其用作肥料。施用时的灰分形式很重要,散落的灰分比粒状灰分释放钙,钾和钠的速度更快。木灰基肥料对重金属,放射性核素和二恶英的污染极少,并且不太可能影响生态系统功能。木灰的影响主要取决于施用量和土壤类型。在低速率下最大程度地提高了效益,而施用量超过10 t ha-1可能会产生毒性。对于大多数森林地点,每轮使用一次木灰即可替代整棵树采伐后损失的所有养分(氮除外)。在浅层泥炭上已观察到对树木生长的持久积极影响,其中腐殖质因pH升高和养分利用率提高而缓慢矿化。相反,当氮的有效性不受限制时,将木灰施加到Podzols仅对增强树木生长有效。迄今为止,已发表的有关木灰对粘土和壤土中树木生长的影响的研究很少。经常观察到树木对木灰施用有积极反应的滞后时间,这可能是土壤pH值较高时磷限制的结果。所报告的最大的不利生态影响是对嗜酸生态系统,尤其是构成苔藓植物,土壤细菌和菌根菌群落。

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