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Life cycle assessment of biomass production from drained wetlands areas for composite briquettes fabrication

机译:废水湿地区生物质生产的生物质生物量评估综合压块制造

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The area of wetlands after peat mining in Belarus is about 190,000 hectares and once peat harvesting has ceased it is impossible to grow any cultural plants for some years. One of the perspective directions is rewetting wetlands after peat extraction that stimulate vegetation of natural grass, like reed, rush and others which are growing in natural conditions. The grass biomass may be used for energy purpose, in particular for composite briquettes fabrication, which contents in 50 % from grass and 50 % from peat. The LCA method based on the standards series ISO 14040 was used for evaluation of environmental impact of growing and production of composite briquettes from wetland biomass. The goal of LCA was comparison two scenarios of biomass production for composite briquettes. Product system B (PSB) based on biomass harvesting with simultaneous shredding and product system A (PSA) based on biomass mowing, raking for drying and bailing. The basic LCA impact categories were: climate change, acidification, photo oxidant formation, eco toxicity and human toxicity. The product system A (mowing and baling biomass) achieved better results in 3 categories out of 5, and especially eco toxicity and human toxicity. And if for climate change the indicator results for both systems were close, for acidification, eco toxicity and human toxicity PSB systems impact was significantly higher to compare to PSA. It may be explained by peat using for biomass drying in product system B. The contents of SO2 and Hg in the peat in several times higher to compare to diesel and gas, while PCB and GCB are contained only in the peat.
机译:白俄罗斯泥炭开采后的湿地面积约为190,000公顷,一旦泥炭收获停止,不可能长期种植任何文化植物。其中一个透视方向在泥炭萃取后重新润湿湿地,以刺激自然草的植被,如芦苇,匆忙等在自然条件下生长。草生物质可用于能量用途,特别是用于复合煤层的制造,其含量从草的50%和50%来自泥炭。基于标准系列ISO 14040的LCA方法用于评估来自湿地生物量的复合煤层的生长和生产的环境影响。 LCA的目标是对复合煤层的两种生物质生产情景进行比较。基于生物量收获的产品系统B(PSB)与基于生物量割草的同时粉碎和产品系统A(PSA),耙干燥和保释。基本LCA影响类别是:气候变化,酸化,光氧化剂形成,生态毒性和人类毒性。产品系统A(割割和BALING生物量)在5分中达到了3个类别,特别是生态毒性和人类毒性。如果气候变化,两种系统的指标结果接近,对于酸化,Eco毒性和人类毒性PSB系统的影响明显高于比较PSA。它可以通过泥炭使用产品系统B中的生物质干燥来解释。泥炭中SO2和Hg的含量高出几倍以比较柴油和气体,而PCB和GCB仅在泥炭中含有。

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