A Revision of What Life Cycle Sustainability Assessment Should Entail: Towards Modeling the Net Impact on Human Well‐Being
In: Journal of Industrial Ecology, Band 21, Heft 6, S. 1464-1477
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In: Journal of Industrial Ecology, Band 21, Heft 6, S. 1464-1477
SSRN
In: Environmental science & policy, Band 57, S. 31-39
ISSN: 1462-9011
In: Environmental science & policy, Band 27, S. 68-80
ISSN: 1462-9011
In: Applied Energy, Band 145, S. 234–245
SSRN
In: Land use policy: the international journal covering all aspects of land use, Band 100, S. 104898
ISSN: 0264-8377
In: Berger , M , Sonderegger , T , Alvarenga , R , Bach , V , Cimprich , A , Dewulf , J , Frischknecht , R , Guinée , J , Helbig , C , Huppertz , T , Jolliet , O , Motoshita , M , Northey , S A , Rugani , B , Schrijvers , D , Schulze , R , Tikana , L & Valero , A 2018 , ' Harmonizing LCIA of mineral resource use - guidance from the UN Environment Life Cycle Initiative task force ' , Ecobalance 2018 , Tokyo , Japan , 9/10/18 - 12/10/18 .
The environmental impacts caused by mining and refining processes producing usable materials are considered in relatively well established impact categories (e.g., climate change, acidification, and eco-toxicity). However, the assessment of impacts of resource use as such is still controversial – even though a wide range of methods are available. Therefore, the task force primary mineral resources of the global guidance for LCIA indicators project (a central project of the Life Cycle Initiative hosted by UN Environment) works towards consensual guidance for assessing resource use in LCA. In a comprehensive literature review, 29 methods assessing impacts of resource use in LCA have been identified. Depending on the impact pathways described, these methods have been clustered into four categories: methods assessing depletion of stocks, methods assessing "future efforts" resulting from ore grade decline as an (assumed) consequence of current extraction, methods using thermodynamic accounting (exergy and emergy approaches), and methods assessing the supply risk of raw materials based on socio-economic aspects (like country concentration, political stability, barriers of trade, etc.). Within the four clusters of methods, key axioms and methodological choices, like the resource stocks used in depletion methods, the reference environment used in exergy methods, or the socioeconomic aspects considered in methods addressing supply risk are discussed. All methods are analyzed and compared by means of a comprehensive evaluation scheme comprising criteria like scientific robustness, documentation, applicability, and acceptance. Moreover, all methods are applied to analyze the life cycle inventory of an electric vehicle and to discuss the different findings resulting from methodological differences. Finally, relevant impact pathways leading to the agreed on area of protection "availability of resources for humans in the technosphere" are recommended and clear guidance for selecting methods depending on the question to be ...
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The EU Water Framework Directive aims to ensure restoration of Europe's water bodies to "good ecological status" by 2027. Many Member States will struggle to meet this target, with around half of EU river catchments currently reporting below standard water quality. Diffuse pollution from agriculture represents a major pressure, affecting over 90% of river basins. Accumulating evidence shows that recent improvements to agricultural practices are benefiting water quality but in many cases will be insufficient to achieve WFD objectives. There is growing support for land use change to help bridge the gap, with a particular focus on targeted tree planting to intercept and reduce the delivery of diffuse pollutants to water. This form of integrated catchment management offers multiple benefits to society but a significant cost to landowners and managers. New economic instruments, in combination with spatial targeting, need to be developed to ensure cost effective solutions – including tree planting for water benefits - are realised. Payments for Ecosystem Services (PES) are flexible, incentive-based mechanisms that could play an important role in promoting land use change to deliver water quality targets. The PESFOR-W COST Action will consolidate learning from existing woodlands for water PES schemes in Europe and help standardize approaches to evaluating the environmental effectiveness and cost-effectiveness of woodland measures. It will also create a European network through which PES schemes can be facilitated, extended and improved, for example by incorporating other ecosystem services linking with aims of the wider forests-carbon policy nexus.
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In: Valatin , G , Abildtrup , J , Accastello , C , Said Al-Tawaha , A R M , Andreucci , M-B , Atanasova , S , Avdibegović , M , Baksic , N , Banasik , K , Barquin , J , Barstad , J , Bastakova , V , Becirovic , D , Begueria , S , Bethers , U , Bihunova , M , Blagojevic , B , Bösch , M , Bournaris , T , Cao , Y , Carvalho-Santos , C , Chikalanov , A , A. Cunha e Sá , M , Czyżyk , K , Daly , H , Davies , H , Del Campo , A , de Groot , R , De Vreese , R , Dostál , T , El Mokaddem , A , Finér , L , Evans , R , Fiquepron , J , Frac , M , Futter , M , Garcia , S , Gatto , P , Geneletti , D , Gezik , V , Giupponi , C , González-Sanchís , M , Gordillo , F , Gorriz , E , Grigorova , Y , Heinsoo , K , Hochbichler , E , Högbom , L , Image , M , Jacobsen , J B , Japelj , A , Jelic , S , Junk , J , Juhasz , C , Kagalou , I , Kelly-Quinn , M , Klamerus-Iwan , A , Kluvankova , T , Koeck , R , Konovska , I , Krajter Ostoic , S , Krc , J , Lavnyy , V , Leonardi , A , Libiete , Z , Little , D , Lo Porto , A , Loukas , A , Lyubenova , M I , Maric , B , Martínez-López , J , Martinez , I , Maxim , A , Metslaid , M , Melvin , A , Costică , M , Mincev , I , Morkvenas , Z , Nevenic , R , Nisbet , T , O'hUallachain , D , Olschewski , R , Östberg , J , Oszust , K , Ovando , P , Paletto , A , Parpan , T , Pettenella , D , Pezdevšek Malovrh , Š , Planinšek , Š , Podlipná , R , Posavec , S , Potočki , K , Prokofieva , I , Quinteiro , P , Radocz , L , Ristic , R , Robert , N , Rugani , B , Sabanovic , J , Sarvasova , Z , Savoska , S , Schleppi , P , Schueler , G , Shannon , M , Silgram , M , Srdjevic , B , Stefan , G , Stijovic , A , Strange , N , Tattari , S , Teofilovski , A , Termansen , M , Thorsen , B J , Toth , A , Trebs , I , Tmušić , N , Vasiliades , L , Vedel , S E , Ventrubová , K , Vuletic , D , Winkel , G , Yao , R , Young , S , Yousefpour , R , Zahvoyska , L , Zhang , D , Zhou , J & Žižková , E 2017 , ' PESFOR-W : improving the design and environmental effectiveness of woodlands for water payments for ecosystem services ' , Research Ideas and Outcomes , vol. 3 , e13828 . https://doi.org/10.3897/rio.3.e13828
The EU Water Framework Directive aims to ensure restoration of Europe's water bodies to "good ecological status" by 2027. Many Member States will struggle to meet this target, with around half of EU river catchments currently reporting below standard water quality. Diffuse pollution from agriculture represents a major pressure, affecting over 90% of river basins. Accumulating evidence shows that recent improvements to agricultural practices are benefiting water quality but in many cases will be insufficient to achieve WFD objectives. There is growing support for land use change to help bridge the gap, with a particular focus on targeted tree planting to intercept and reduce the delivery of diffuse pollutants to water. This form of integrated catchment management offers multiple benefits to society but a significant cost to landowners and managers. New economic instruments, in combination with spatial targeting, need to be developed to ensure cost effective solutions – including tree planting for water benefits - are realised. Payments for Ecosystem Services (PES) are flexible, incentive-based mechanisms that could play an important role in promoting land use change to deliver water quality targets. The PESFOR-W COST Action will consolidate learning from existing woodlands for water PES schemes in Europe and help standardize approaches to evaluating the environmental effectiveness and cost-effectiveness of woodland measures. It will also create a European network through which PES schemes can be facilitated, extended and improved, for example by incorporating other ecosystem services linking with aims of the wider forests-carbon policy nexus. ; The EU Water Framework Directive aims to ensure restoration of Europe's water bodies to "good ecological status" by 2027. Many Member States will struggle to meet this target, with around half of EU river catchments currently reporting below standard water quality. Diffuse pollution from agriculture represents a major pressure, affecting over 90% of river basins. Accumulating evidence shows that recent improvements to agricultural practices are benefiting water quality but in many cases will be insufficient to achieve WFD objectives. There is growing support for land use change to help bridge the gap, with a particular focus on targeted tree planting to intercept and reduce the delivery of diffuse pollutants to water. This form of integrated catchment management offers multiple benefits to society but a significant cost to landowners and managers. New economic instruments, in combination with spatial targeting, need to be developed to ensure cost effective solutions – including tree planting for water benefits - are realised. Payments for Ecosystem Services (PES) are flexible, incentive-based mechanisms that could play an important role in promoting land use change to deliver water quality targets. The PESFOR-W COST Action will consolidate learning from existing woodlands for water PES schemes in Europe and help standardize approaches to evaluating the environmental effectiveness and cost-effectiveness of woodland measures. It will also create a European network through which PES schemes can be facilitated, extended and improved, for example by incorporating other ecosystem services linking with aims of the wider forests-carbon policy nexus.
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