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Transcript of Heijungs_1
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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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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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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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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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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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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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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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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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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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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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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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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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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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