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Development of a conceptual framework to take the dissipation of non-energetic abiotic resources into account within Life Cycle Assessment (LCA)

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Science Arts & Métiers (SAM)

is an open access repository that collects the work of Arts et Métiers Institute of Technology researchers and makes it freely available over the web where possible.

This is an author-deposited version published in: https://sam.ensam.eu

Handle ID: .http://hdl.handle.net/10985/17022

To cite this version :

Alexandre CHARPENTIER-PONCELET, Philippe LOUBET, Bertrand LARATTE, Guido

SONNEMANN - Development of a conceptual framework to take the dissipation of non-energetic abiotic resources into account within Life Cycle Assessment (LCA) - 2019

Any correspondence concerning this service should be sent to the repository Administrator : archiveouverte@ensam.eu

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Development of a conceptual framework to take the

dissipation of non-energetic abiotic resources into

account within Life Cycle Assessment (LCA)

Alexandre Charpentier Poncelet, Philippe Loubet,

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CONTENT

Context

Research question & Method

Dissipation approach

Overview

Key considerations

Methodological developments

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CONTEXT

• Recent developments for the Natural Resources Area of Protection (AoP) in Life Cycle Assessment (LCA) (eg. Dewulf et al. (2015); Sonderegger et al. (2017))

• Existing methods for abiotic resource use have been discussed and criticized by many in recent years (eg. Swart, Alvarenga, & Dewulf (2015); Drielsma et al. (2016); Sonderegger et al. (2017))

Safeguard subject for non-energetic abiotic resources has been defined as “the potential to make use of the

value that mineral resources, as embedded in a natural or anthropogenic stock, can hold for humans in the technosphere” (Berger et al., 2018)

• Damage to the safeguard subject happens when abiotic resources are dispersed in a way which make them unavailable for future use or when they are rendered inaccessible in technosphere through different

mechanisms

• Dissipation approach is a promising way forward to account for this damage, and should be investigated further (Zampori & Sala (2017); Berger et al. (2018))

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RESEARCH QUESTION & METHOD

Research question: In light of most actual knowledge, what has to be considered in a conceptual framework to account for abiotic resource dissipation in LCA?

Method:

State of the art for Natural Resources AoP

Conceptual framework

• Define abiotic resource use and Natural resource AoP

• Identify perspective for abiotic resources based on Dewulf et al. (2015)

• Critique existing methods

• Identify relevant guidance for method development • Identify research needs for dissipation approach

• Take position on methodological choices • Define key words and concepts

• Build conceptual framework

• Identify data collection needs / cross-sectoral complementary research

Meta-analysis of critical reviews Guidance

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DISSIPATION APPROACH - OVERVIEW

Extraction, smelting, refining Primary resource Primary resource, in technosphere Product Resource, in technosphere Secondary resource Secondary resource, in technosphere Production Recycling (smelting, refining) Ultimate reserve Reserve base Economic reserve Resource, raw Managed waste Resource, in managed stocks Environment Technosphere Collecting/s orting Legend Stock Process Impact Dissipative flow

Well-managed waste flow Flows towards production

Use

Currently unrecyclable Currently recyclable

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DISSIPATION APPROACH - OVERVIEW

Extraction, smelting, refining Primary resource Primary resource, in technosphere Product Resource, in technosphere Secondary resource Secondary resource, in technosphere Production Recycling (smelting, refining) Ultimate reserve Reserve base Economic reserve Resource, raw Managed waste Resource, in managed stocks Environment Technosphere Collecting/s orting Legend Stock Process Impact Dissipative flow

Well-managed waste flow Flows towards production

Use Currently unrecyclable Currently recyclable

Eg.: CML

(ADP)

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DISSIPATION APPROACH - OVERVIEW

Extraction, smelting, refining Primary resource Primary resource, in technosphere Anthropogenic reserve Product Resource, in technosphere Secondary resource Secondary resource, in technosphere Production Recycling (smelting, refining) Ultimate reserve Reserve base Economic reserve Resource, raw Managed waste Resource, in managed stocks Landfill mining Environment Technosphere Collecting/s orting Legend Stock Process Impact Dissipative flow

Well-managed waste flow Flows towards production

Use Currently unrecyclable Currently recyclable

Credit for

recycled

resources

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DISSIPATION APPROACH - OVERVIEW

Extraction, smelting, refining Primary resource Primary resource, in technosphere Anthropogenic reserve Product Resource, in technosphere Secondary resource Secondary resource, in technosphere Production In-use dissipated Recycling (smelting, refining) Ultimate reserve Reserve base Economic reserve Resource, raw Managed waste Resource, in managed stocks Landfill mining Environment Technosphere Collecting/s orting Legend Stock Process Impact Dissipative flow

Well-managed waste flow Flows towards production

Use

Poorly managed waste Poorly managed

waste emissions, Process

unmanaged waste

Currently unrecyclable

emissions Currently recyclable

Dissipativ

e flows to

environm

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DISSIPATION APPROACH - OVERVIEW

Extraction, smelting, refining Primary resource Primary resource, in technosphere Anthropogenic reserve Product Resource, in technosphere Secondary resource Secondary resource, in technosphere Production In-use dissipated Recycling (smelting, refining) Ultimate reserve Reserve base Economic reserve Resource, raw Managed waste Resource, in managed stocks Landfill mining Environment Technosphere Collecting/s orting Legend Stock Process Impact Dissipative flow

Well-managed waste flow Flows towards production

Use

Poorly managed waste Poorly managed

waste emissions, Process

unmanaged waste Tailings Currently unrecyclable emissions Δq Δq Δq Currently recyclable Poorly managed waste residues Losses in sorting, Unrecyclable

Dissipative flows also inside technosphere

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DISSIPATION APPROACH – KEY CONSIDERATIONS

Dissipation (permanent loss of mass and/or quality) over the whole life cycle

• Dissipation based on use type/design (eg. Lost by Design, Ciacci et al. (2015))

• Dissipation in environmental compartments

• Dissipation in techsnosphere (loss of quality, dissipated in managed waste, etc.)

Time

Timeframe (how long?)

• Resource occupation/borrowing uses (see eg. Frischknecht, 2016)

• Dissipation patterns over time. Resource-level (global)?, product-level? sector-level?

Geographical scale

• Recycling rates

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DISSIPATION APPROACH – KEY CONSIDERATIONS

Dissipation (permanent loss of mass and/or quality) over the whole life cycle

• Dissipation based on use type/design (eg. Lost by Design, Ciacci et al. (2015))

• Dissipation in environmental compartments

• Dissipation in other material flows

• Dissipation in managed waste

Time

Timeframe (how long?)

• Resource occupation/borrowing uses (see eg. Frischknecht, 2016)

• Dissipation patterns over time. Resource-level (global)?, product-level? sector-level?

Geographical scale

• Recycling rates

• Product lifetimes variations

Dynamic MFA data

Information depends on MFA scope

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Product system

DISSIPATION APPROACH – METHODOLOGICAL DEVELOPMENTS

Two possible ways forward to integrate dissipation data in the conceptual framework

Environment Technosphere Primary non-energetic abiotic resources Dissipation to environment Dissipation as quality loss, contaminant in other material flows or human managed waste Option 1 Secondary non-energetic abiotic resources (input from other PSS) Extraction /refining Fabrication EoL Output to other product/service system F C1 C2 E2 E1 D2 D1 A B Use C3 D3 D4 D E3 E4 Dissipation in human managed waste (tailings) Dissipation as quality loss or human managed waste  Dissipation as determined

with key considerations integrated in LCI

 Balanced input-output

flows per process (ideally)

 Characterization factors (CFs) convert LCI dissipation in impact assessment Dynamic MFA data Example : C1 – C2 = D2 + E2

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DISSIPATION APPROACH – METHODOLOGICAL DEVELOPMENTS

Two possible ways forward to integrate dissipation data in the conceptual framework

Product system Environment Technosphere Primary non-energetic abiotic resources Dissipation to environment Dissipation as quality loss, contaminant in other material flows or human managed waste Option 2 Secondary non-energetic abiotic resources (input from other PSS) Extraction /refining Fabrication EoL Output to other product/service system A B Use Dissipation in human managed waste (tailings) Dissipation as quality loss or human managed waste Dynamic MFA data  Dissipation as determined

with key considerations is integrated in CFs

 Balanced input-output

flows per process unchecked

 Characterization factors

(CFs) convert actual LCI data in impact assessment Caculate dissipation ratios D E2 E1 D2 D4 E3 E4 D1 D3 F C1 C2 C3

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CONCLUSIONS

• More definite parameters have been selected to ameliorate abiotic resource use considerations in LCA using a dissipation approach

• Dynamic MFA can serve as a basis to calculate dissipation pattern over time

• 2 possible paths forward to implement dissipation in a conceptual framework have been presented

FUTURE WORKS

• Chose resource-centric perimeter for data collection (product-level, sector-level or global) and geographical granularization for different parameters

• Determine how to integrate quality considerations

• Make methodological decision between integrating data in LCI or LCIA (CFs) or mix of both

• Determine whether reserve size and/or dissipation curve is appropriate for the selected timeframe to include in CF calculations in order to account for availability (or loss of availability)

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REFERENCES

Berger, M., Sonderegger, T., de Alvarenga, R., Bach, V., Cimprich, A.,

Frischknecht, R., … others. (2018). Harmonizing the LCIA of mineral resource

use. EcoBalance 2018-13th Biennial International Conference on EcoBalance,

(October).

Ciacci, L., Reck, B. K., Nassar, N. T., & Graedel, T. E. (2015). Lost by Design.

Environmental Science and Technology, 49(16), 9443–9451.

https://doi.org/10.1021/es505515z

Dewulf, J., Benini, L., Mancini, L., Sala, S., Blengini, G. A., Ardente, F., …

Pennington, D. (2015). Rethinking the area of protection “natural resources”

in life cycle assessment. Environmental Science and Technology, 49(9), 5310–

5317. https://doi.org/10.1021/acs.est.5b00734

Drielsma, J., Russell-Vaccari, A. J., Drnek, T., Brady, T., Weihed, P., Mistry, M.,

& Si b (20 6) i

l

i lif

l i

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Acknowledgements

Co-financing : Agence de l’Environnement et de la Maîtrise

de l’Energie (ADEME) and French geological survey (BRGM)

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