Congrès [avniR], 5-6 novembre 2014, Lille Biodiversity in LCA methods Some proposals to bridge the gap François Danic 1 , Benjamin Lévêque 2 , Stéphane Le Pochat 1 , Lénaïc Moniot 2 , Guillaume Neveux 2 , Jade Garcia 3 1. Evea 2. I Care Environnement 3. Score LCA Congrès [avniR] 2014, Lille
• Context and objectives • Definitions • Steps • Findings • Proposals for improvement • Conclusion 2 Congrès [avniR] 2014, Lille
• Context A study ordered by Score LCA : ‘’ How to use LCA flows, indicators, and methods for biodiversity impact assessment ?’’ A study carried out by Evea and I Care A study delivered in 2014 3 Congrès [avniR] 2014, Lille
• Objectives • Achieve a state of the art on LCA – biodiversity indicators and methods (LCA (flows, indicators, methods) and others) – ongoing research about the integration of biodiversity in LCA – the current level of consideration of biodiversity in LCA • Identify ways to take into account Biodiversity biodiversity in LCA methods Ecosystems • [Compare methods, indicators and flows used in LCA with regulatory requirements Habitats for industrial sites] Species 4 Congrès [avniR] 2014, Lille
• Definitions (scope of the study) Biodiversity [CBD, UN 1992] « Biological diversity means the variability among living organisms from all sources including, inter alia, terrestrial, marine and other aquatic ecosystems and the ecological complexes of which they are part : this includes diversity within species, between species and of ecosystems. » Ecosystem [CBD, UN 1992] « A dynamic complex of plant, animal and micro-organism communities and their non-living environment interacting as a functional unit. » Biodiversity can not be reduced to ecosystems. Ecosystems are only one of the dimensions of biodiversity. Biodiversity Ecosystems Species Biotope Habitats Biocenosis Ecosystems Ecological functions 5 Congrès [avniR] 2014, Lille
• Steps 1 Inventory of indicators of biodiversity 2 Analysis of indicators (potential for LCA) 3 LCA versus biodiversity studies : a case study 4 Recommandations for improvement 6 Congrès [avniR] 2014, Lille
• Inventory of indicators of biodiversity Typology of indicators LCA ― Endpoints ― Midpoints Ecosystem services ― Ecological functions ― Monetarized indicators Biodiversity ― Biodiversity status and trends ― Drivers of biodiversity loss ― Dependance on ecosystem services 7 Congrès [avniR] 2014, Lille
• Some identified indicators for biodiversity assessment Existing and developing Biodiversity indicators indicators in LCA • 3 midpoints related to biodiversity: land use, • 451 biodiversity indicators identified ecotoxicity, acidification / eutrophication – Biodiversity status and trends: 172 – Drivers of biodiversity loss : 264 • 2 endpoints related to biodiversity: Ecosystem – Dependence on ecosystem services: 15 Quality: characterization of the impacts on • Not limited to species and including all ecosystems by the PDF/PAF factors dimensions of biodiversity – Habitats, species, ecosystem services • A lot of research supporting the development • A lot of research supporting indicators of of the land use indicator ecosystem services – Ongoing development of indicators of ecological functions, at the origin of ecosystem services – First series of “ monetarized ” indicators by ecosystem service and biome • Some indicators trying to assess biodiversity in LCA methods exist, providing a limited vision of biodiversity issues • Richness and diversity of indicators existing in biodiversity studies 8 Congrès [avniR] 2014, Lille
• Synthesis on drivers of biodiversity loss taken into account by existing LCA methods Pressures on Consideration in LCA Sub-types of pressure biodiversity methods Land occupation Land transformation Habitat change Fragmentation Disturbances Protection of habitats and biodiversity Introduction of alien species Alien species Use of means of spread of alien species Water consumption Endangered species Overexploitation Participation in species diversity Participation in genetic diversity Sustainable use of natural resources Pollution of water bodies Soil pollution Pollutions Air pollution Acidification / Eutrophication Pollutants and wastes emissions [From Curran et al., 2011] Climate change GHG emissions • A limited number of sub-types of drivers is taken into account • « Habitat change » and « Pollutions » are the more detailed drivers in the LCA methods 9 Congrès [avniR] 2014, Lille
• LCA versus biodiversity studies : a case study 3 modes of electricity supply (kWh of coal, gas,and photovoltaic) LCA methods Biodiversity studies • • Analysis of biodiversity studies on: Modeling on the software Simapro7 by 3 methods – Impacts by drivers and sub-type of drivers of – Eco-indicator 99 biodiversity loss Methodology – Impacts on habitats, species and ecological – Impact 2002+ functions – ReCiPe – Geographically located case studies Transformation / Distribution Coal Coal Electricity mining transport production High Medium Low voltage elec. voltage elec. voltage elec. Ecoindicator 99 Illustrations ReCiPe Legend: Land occupation/transformation Ecotoxicity Acidification /eutrophication Climate change • LCA methods show interesting midpoints to assess biodiversity issues and a relevant hierarchy between technologies at the endpoint step • An important weight attributed to the PDF factor for Climate change in ReCiPe • Some issues are clearly missing compared with biodiversity studies (fragmentation, …) 10 Congrès [avniR] 2014, Lille
• Focus on methodological differences within LCA methodologies Study of Differentiation by Study of land climate change Number of « substances » type of impacted Aggregation factors Spatialization transformation applied to considered ecosystems ecosystems Ecotoxicity 196 Use of the PAF Eco-indicator 99 Acidif./ Yes No 9 No factor, not very No (unit: PDF*m²*yr) eutrophication specific Land use 142 Possible Ecotoxicity 2.589 Unavailability of with the IMPACT 2002 + Acidif./ Terrestrial / acidification/ No No 7 Impact (unit: PDF*m²*yr) eutrophication aquatic eutrophication World + factors Land use 88 version Ecotoxicity 26.752 Terrestrial/ ReCiPe Acidif./ Good accuracy of Yes Yes 20 fresh water / No (unit: species.yr) eutrophication factors marine water Land use 75 Legend: Strength Weakness 11 Congrès [avniR] 2014, Lille
• Proposal : 5 ways to improve the calculation of biodiversity in LCA methods Biodiversity Company Ecosystems 5 drivers of biodiversity Habitats loss Species Integration of 3 indicators of drivers of biodiversity loss 2 Flow spatialization 1 Improvement of existing Input flows 4 Mid- End- indicators and Linking impacts points points methods and ecosystems Output flows 5 Focus on the most critical impacts 12 Congrès [avniR] 2014, Lille
• Proposal : 5 ways and in-depth approaches Level of complexity Approach A Approach B Approach C Improvement of Improvement of land use Improvement of existing Improvement of the PDF 1 aggregation factors for PDF and land use change indicators and methods coefficient indicator indicators Definition of relevant scales for biodiversity study on Data acquisition on the 2 Flow spatialization Coupling GIS and LCA value chain and lifecycle different scales steps Integration of indicators of Integration of an indicator Integration of an indicator 3 / pressures on biodiversity by pressure by sub-type of pressure Linking impacts and Crossing impact and risk Modeling impacts on Modeling impacts on 4 ecosystems level for ecosystems species ecosystem services Focus on the most critical Prioritization of impacts in a Prioritization on the most 5 / impacts lifecycle step impactful lifecycle steps Approaches with higher or lower consideration of biodiversity and different horizons of implementation 13 Congrès [avniR] 2014, Lille
• Toward a progressive implementation of biodiversity complexity in LCA 1 2 3 4 5 Level of implementation Modeling impacts on Modeling services impacts on species Detailed 1 midpoint technical 3 1 midpoint by sub-type approach by pressure of pressure Data acquisition at different scales Prioritization Prioritization in a lifecycle on lifecycle Relevant Crossing step steps scales for impact x biodiversity study ecosystem risk Global 2 approach Improvement of PDF factor Extension of Improvement of existing Improvement of 1 land-use and land-use Coupling GIS aggregation work in LCA change indicators and LCA factors Short term Mid term Long term Time 1-3 years 3-6 years 6-9 years horizon 14 Congrès [avniR] 2014, Lille
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