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Large Marine Ecosystems and coastal water archetypes implemented in LCIA methods for marine eutrophication and metals ecotoxicity

机译:大型海洋生态系统和沿海水原型采用LCIa方法实施海洋富营养化和金属生态毒性

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摘要

The marine eutrophication (MEu) and marine ecotoxicity (MEc) indicators in Life Cycle Impact Assessment (LCIA) respectively express the eutrophying impact of nitrogen (N) and the toxic impact of metals emissions to the marine environment. Characterisation Factors (CF) are calculated to translate the emissions into impact potentials. For consistency in the characterisation modelling across impact categories, the same modelling framework was applied including Fate Factors of N or metals (FF), habitat Exposure Factor (XF) in MEu or Bioavailability Factor of metals (BF) in MEc, and Factors for the Effect on biota (EF). In both impact categories there is a need for spatial differentiation according to the receiving ecosystems, and the parameterisation of the characterisation models requires the adoption of suitable spatial units out of the global receiving coastal marine ecosystem. The Large Marine Ecosystems (LME) biogeographical classification system identifies 64 spatial units of coastal marine waters and it was adopted for both MEu and MEc. The applicability of 13 alternative zonation systems was compared before choosing the LME classification. The hydraulic residence time (RT) of the receiving LMEs expressing the system’s flushing through local hydrodynamics is required for the parameterisation of the FF term to estimate the loss of N or metals from the LME through advection. The RT was found in literature for 36% of the LMEs, whereas 4 archetypes were built for the remaining, for which no data was found (47%) or to settle high variability of found sources (17%). The 4 archetypes were defined by the exposure to currents and regional marine circulation, depth and profile of the continental shelf, and stratification. Archetype 1 (high dynamics and exposure) with estimated RT=3 months, Archetype 2 (medium dynamics and exposure) with RT=2 yr, Archetype 3 (low dynamics) with RT=25 yr, and Archetype 4 (very low dynamics, embayed, often stratified) with RT=90 yr. It is assumed that the system dynamics is determining the RT of both N and metals in the photic zone in each LME. The LME classification system was chosen for its data availability, modelling feasibility, and adequacy of size and number of spatial units considering the needs of LCIA. The application of the archetypical RTs was useful for the parameterisation of the fate models. The spatial differentiation of the resulting CFs was found essential to increase the discriminatory power of the models.
机译:生命周期影响评估(LCIA)中的海洋富营养化(MEu)和海洋生态毒性(MEc)指标分别表示氮(N)的富营养化影响和金属排放对海洋环境的毒性影响。计算特征因子(CF)可以将排放物转化为潜在影响。为了使影响类别之间的特征建模保持一致,应用了相同的建模框架,包括氮或金属的命运因子(FF),MEu中的栖息地暴露因子(XF)或MEc中的金属生物利用因子(BF),以及影响因子。对生物区系(EF)的影响。在这两种影响类别中,都需要根据接收生态系统进行空间区分,并且表征模型的参数化要求从全球接收沿海海洋生态系统中采用合适的空间单位。大型海洋生态系统(LME)生物地理分类系统可识别沿海海洋水域的64个空间单位,MEu和MEc均采用了该系统。在选择LME分类之前,比较了13种替代分区系统的适用性。为了表示FF项的参数化,需要估计通过对流从LME中损失的N或金属,接收LME的液压停留时间(RT)表示系统通过局部流体动力学进行冲洗。在文献中发现了36​​%的LME的RT,而其余的则建立了4种原型,没有找到任何数据(47%)或解决了所发现来源的高变异性(17%)。通过暴露于洋流和区域海洋环流,大陆架的深度和剖面以及分层来定义这四个原型。原型1(高动态和暴露),估计RT = 3个月,原型2(中等动态和暴露),RT = 2年,原型3(低动力学),RT = 25年,原型4(低动态,被困,通常分层),RT = 90年。假定系统动力学决定了每个LME中光区中N和金属的RT。选择LME分类系统是因为其数据可用性,建模可行性以及考虑LCIA需求的空间单元的大小和数量的适当性。原型RT的应用对于命运模型的参数化非常有用。发现所得CF的空间差异对于增加模型的鉴别能力至关重要。

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