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Spatially Explicit Characterization of Acidifying and Eutrophying Air Pollution in Life-Cycle Assessment

机译:生命周期评估中酸化和富营养化空气污染的空间显式表征

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Simple models are often used to assess the potential im- pact of acidifying and eLrtrophying substances released dur- ing the life cycle of products. As fate, background depositions. and ecosystem sensitivity are not included in these models, environmentallife-cycle assessment of prod- ucts(LCA) may produce incorrect results for these impact categories. This paper outlines the spatially explicit regional air pollution information and simulation model (RAINS- LCA), which was developed for the calculation of aciditica- tion ar)d terrestrial eLrtrophication potentials of ammonia (NH3) and nitrogen oxide (NOx) air emissions and acidi- ticationpotentials for sulfur dioxide (SOV air emissions for Europe and a number of European regions. taking fate. background depositions and effects Into account.Two impact definition~are ex- plored in the calculations: l) the marginal change in the hazard index of all ecosys- tems in Europe and 2) the marginal change in the hazard index of ecosystems in Europe where the critical load is actu- ally exceeded. The indusion of fate.. back- ground depositioQs,and ecosystem sensitivity results in a different ranking of substances compared to simplermodej outcomes. In the context of acidification, emissions of nitrogen compounds are re- garded as about a factor 2 less important. relative to sulfur compounds. Further- more, using RAINS-LCA as opposed to simpler models, it was found that region- specific differences in terrestrial eutrophi- cation and acidification potentials range up to 1.5 and 3.5 orders of magnitude, respectively. By means of scenario analysis, it was also shown that "only above critical .load" terrestrial eutrophication and acidi- fication potentials for the years 1995 and 20 10 differ up to 0.6 order and I order of magnitude, respectively. These results im- ply that it is important to use region-spe- cific and time-specificac.idifi~qtion and terrestrial eutrophication potentials, if it is expected that life-cyde emissions of acidi- fying and eutrophying air pollutants are predominantly situated in a few (Euro- pean) regions and within a specific year: Further improvements in RAINS-LCA may be established by induding source- receptor matrices of the Northern Hemisphere instead of Europe and using the probability of species occurrence as" a basis for the effect assessment
机译:通常使用简单的模型来评估在产品生命周期内释放出的酸化和电腐蚀物质的潜在影响。作为命运,背景沉积。这些模型不包括生态系统敏感性和生态系统敏感性,因此产品的环境生命周期评估可能会对这些影响类别产生不正确的结果。本文概述了空间明确的区域空气污染信息和模拟模型(RAINS-LCA),该模型用于计算氨(NH3)和氮氧化物(NOx)的空气排放和酸化的酸化和陆地水化电位-二氧化硫的潜在潜力(欧洲和许多欧洲地区的SOV空气排放。要考虑到命运,背景沉积和影响。计算中要考虑两个影响定义:l)危险指数的边际变化。欧洲的所有生态系统和2)实际上超出了临界负荷的欧洲生态系统的危害指数的边际变化。与简单的结果相比,命运..背景沉积物的产生以及生态系统的敏感性导致了不同的物质等级。在酸化的情况下,氮化合物的排放被认为不那么重要约2倍。相对于硫化合物。此外,与简单模型相比,使用RAINS-LCA发现,陆地富营养化和酸化电位的区域特定差异分别高达1.5和3.5个数量级。通过情景分析,还显示出1995年和20 10年“仅在临界负荷以上”的陆地富营养化和酸化潜力分别相差0.6个和1个数量级。这些结果表明,如果预期酸化和富营养化的空气污染物的生命周期排放主要位于以下地区,则必须使用针对特定地区和特定时间的酸化和陆地富营养化潜力,这一点很重要。几个(欧洲)地区并在特定年份内:可以通过引入北半球而非欧洲的源-受体矩阵并将物种发生的可能性作为“影响的基础”来建立RAINS-LCA的进一步改进评定

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