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    Contents

    What is LCA? Why LCA?

    The ISO 14040 framework

    Goal and scope definition

    Inventory analysis

    Impact assessment

    Interpretation

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    What is LCA? (1)

    Officially:Life Cycle Assessment

    Here confined to:quantitative environmental Life Cycle Assessment of products

    environmental

    Life Cycle

    Assessment

    quantitative

    products

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    44

    What is LCA? (2)

    At least three different meanings: LCA as a field of study

    LCA as a technique

    LCA as a specific study

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    55

    What is LCA? (3)

    Basically: tool for decision-support computational aspects

    which data

    which models

    which formulas procedural aspects

    who to involve

    how to report

    how to use

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    66

    What is LCA? (4)

    ISO-standardised procedure (ISO 14040, created in1997-2000; revised in 2006)

    Structured framework: four phases

    Rules, requirements and considerations specified

    Specific data and calculation steps not specified Much attention for transparency in reporting

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    ISO 14040 framework (1)

    - Product development

    and improvement

    - Strategic planning

    - Public policy making

    - Market ing

    - Other

    Goal

    and scope

    definition

    Inventory

    analysis

    Impact

    assessment

    Interpretation

    Direct applications:

    Life cycle assessment framework

    Source: ISO 14040

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    ISO 14040 framework (2)

    ISO: Compilation and evaluation of the inputs, outputsand the potential environmental impacts of a productsystem throughout its life cycle

    International Standard ISO 14040

    complementary International Standards ISO 14041,14042, 14043

    no Technical Report to 14040, but Technical Reports to14041 and 14042

    14044 merges the revised 14040-14043 (2006)

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    99

    Why LCA? (1)

    Why a product-oriented information tool? Increased attention for product policy

    several national policy plans

    EUs Integrated Product Policy

    UNEPs International Declaration on Cleaner Production etc.

    Influence consumption and production patterns

    clean(er) production

    ecolabel product stewardship

    etc.

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    1010

    Why LCA? (2)

    Why an integrated information tool? Prevent problem shifting

    to other life cycle stages

    to other substances

    to other environmental problems to other countries

    to the future

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    1111

    Why LCA? (3)

    Why a method? To structure the large amount of complex data

    To facilitate comparisons across product alternatives

    To enable benchmarking

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    Why LCA? (4)

    Why complex data?

    etc

    2 mg0 mgmercury content

    540 g30 gmass

    5000 hr1000 hrlife span

    18 W60 Wpower consumption

    Fluorescent lampIncandescent lampProduct property

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    1313

    ISO 14040 framework (3)

    - Product development

    and improvement

    - Strategic planning

    - Public policy making

    - Market ing

    - Other

    Goal

    and scope

    definition

    Inventory

    analysis

    Impact

    assessment

    Interpretation

    Direct applications:

    Life cycle assessment framework

    Source: ISO 14040

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    1414

    Phase 1: Goal and scope definition (1)

    Phase of life cycle assessment in which the aim of thestudy, and in relation to that, the breadth and depth ofthe study is established

    goal definition

    scope definition

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    Phase 1: Goal and scope definition (2)

    Goal definition: intended application product development and improvement

    strategic planning

    public decision making marketing

    other

    reasons for carrying out the study

    intended audience

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    Phase 1: Goal and scope definition (4)

    Functional unit: comparison on the basis of an equivalent function

    example: 1000 liters of milk packed in glass bottles orpacked in carton, instead of 1 glass bottle versus 1 carton

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    1818

    Phase 1: Goal and scope definition (5)

    Critical review and other procedural aspects

    critical review to ensure the consistency, scientific validity,transparency of the report, etc.

    internal review, external review, review by interested

    parties procedural embedding of LCA: LCA as a (participatory)

    process

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    2020

    Phase 2: Inventory analysis (2)

    Central position for unit process

    smallest portion of a product system for which data arecollected

    Typical examples:

    electricity production by coal combustion PVC production

    use of a passenger car

    recycling of aluminum scrap

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    2121

    Phase 2: Inventory analysis (3)

    Data collection for unit processes:

    flows of intermediate products or waste for treatment

    elementary flows from or to the environment

    electricity production

    electricitycoal

    generator fly ash

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    Phase 2: Inventory analysis (4)

    Combination of unitprocesses into aproduct system

    Graphical

    representation in aflow diagramelectricity production

    electricity

    coal generator

    fly ash

    coal mining

    equipment

    generator production

    steel

    fly ash treatment

    gypsum

    system boundary

    reference flow

    product system

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    2323

    Phase 2: Inventory analysis (5)

    Source: http://www.fibersource.com/f-tutor/LCA-Page.htm

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    Phase 2: Inventory analysis (6)

    Calculation procedures

    relate process data to the functional unit (matrix algebra)

    allocation of multiple processes (multiple outputs, multipleinputs, re-use and recycling)

    aggregation over all unit processes in the inventory table

    electricity productionwith cogeneration

    of heat (CHP)

    electricitycoal

    generator fly ash

    heat

    Ph 2 I l i (7)

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    Phase 2: Inventory analysis (7)

    Inventory table

    etc

    22000 kg37000 kgCrude oil from earth

    20 g3 gCopper to water

    80 kg1000 kgSO2 to air

    50000 kg800000 kgCO2 to air

    Fluorescent lampIncandescent lampElementary flow

    Ph 3 I t t (1)

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    2626

    Phase 3: Impact assessment (1)

    Assessment of the importance of the potentialenvironmental effects with the aid of the results of theinventory analysis

    Steps:

    selection and definition of impact categories, indicatorsand models

    classification

    characterisation

    normalisation aggregation and/or weighing

    Ph 3 I t t (2)

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    Phase 3: Impact assessment (2)

    Life cycle inventory results

    LCI results assigned to

    impact category

    Category indicator

    Category endpoint(s)

    - forest- vegetation

    - etc.

    Characterisation model

    Environmental relevance

    Impact

    category

    Proton release(H+aq)

    Acidifying emissions(NOx, SO2, etc.

    assigned to acidification)

    Acidification

    Cd, CO2, NOx, SO2, etc.(kg/functional unit)

    Example

    Phase 3 Impactassessment (3)

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    Phase 3: Impact assessment (3)

    Example of a category indicator

    Global Warming:

    Global Warming Potential (GWP): measure for Global Warmingin terms of radiative forcing of a mass-unit

    Example calculation:

    5 kg CO2 (GWP = 1)

    +

    3 kg CH4 (GWP = 21)

    =

    1 x 5 + 21 x 3 kg CO2 - equivalents (= 68 kg CO2 equivalents)

    Phase 3: Impactassessment (4)

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    Phase 3: Impact assessment (4)

    Characterisation:

    Simple conversion and aggregation of GHGs:

    subs

    subssubscatcat esultInventoryRCharFactesultIndicatorR ,

    CO2, CH4

    climate change

    GWP (1 and 21) 5 and 3 kg

    68 kg CO2-eq

    infrared radiative forcing

    IPCC climate model

    Phase 3: Impactassessment (5)

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    Phase 3: Impact assessment (5)

    Impact categories, characterisation methods andcharacterisation models: some baseline examples

    impact category category indicator characterisation model characterisationfactor

    equivalencyunit

    abiotic depletion ultimate reserve irtannual use

    Guinee & Heijungs 95 ADP kg Sb

    climate change infrared radiativeforcing

    IPCC model GWP kg CO2

    stratosphericozone depletion

    strat. ozonebreakdown

    WMO model ODP kg CFC-11

    human toxicity PDI/ADI Multimedia model, e.g.EUSES, CalTox

    HTP kg 14-DCB

    ecotoxicity(aquatic,terrestrial etc.)

    PEC/PNEC Multimedia model, e.g.EUSES, CalTox

    AETP, TETP, etc. kg 14-DCB

    photo-oxidantformation

    trop. ozoneformation

    UNECE Trajectory model POCP kg C2H4

    acidification deposition/ac.critical

    load

    RAINS AP kg SO2

    ... ... ... ...

    Phase 3: Impactassessment (8)

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    Phase 3: Impact assessment (8)

    etc

    0.3 kg antinomy-eq0.8 kg antinomy-eqDepletion of resources

    21 kg SO2-eq45 kg SO2-eqAcidification

    440 kg DCB-eq320 kg DCB-eqEcotoxicity

    40000 kg CO2-eq120000 kg CO2-eqClimate change

    Fluorescent lampIncandescent lampImpact category

    Phase 3: Impactassessment (7)

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    Phase 3: Impact assessment (7)

    Impact category results still difficult to understand:

    difference in units

    difference in scale

    Normalisation step to relate the results to a reference

    value e.g., total world impacts in 2002

    result often referred to as the normalised environmentalprofile

    Phase 3: Impactassessment (8)

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    Phase 3: Impact assessment (8)

    etc

    910-13 yr2410-12 yrDepletion of resources

    4.210-11 yr910-11 yrAcidification

    2.210-10 yr1.610-10 yrEcotoxicity

    410-12 yr1.210-11 yrClimate change

    Fluorescent lampIncandescent lampImpact category

    Phase 3: Impact assessment (9)

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    Phase 3: Impact assessment (9)

    Even after normalisation no clear answer

    aggregation of (normalized) impact category results into asingle index

    subjective weighting factors needed

    Phase 3: Impactassessment (10)

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    Phase 3: Impact assessment (10)

    Example of a weighted environmental index

    1.410-10 yr8.510-10 yrWeighted index

    Fluorescent lampIncandescent lampWeighed index

    Phase 4: Interpretation (1)

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    Phase 4: Interpretation (1)

    Conclusions, recommendations, analysis, all related togoal and scope of the research

    among others based on data quality and sensitivityanalysis

    also: critical review by independent experts

    Phase 4: Interpretation (2)

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    Phase 4: Interpretation (2)

    Example of a contribution analysis

    40000 kg CO2-eq120000 kg CO2-eqTotal climate change

    15%5%Other

    10%2%Waste disposal

    15%5%Copper production

    60%88%Electricity production

    Fluorescent lampIncandescent lampProcess

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