Chapter 3 - Corporate Perspective 3.5 Life Cycle Assessment Flashcards

1
Q

Which tests should be carried out as part of the evaluation?

A

Completeness check
Sensitivity check
Consistency check
Other checks

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2
Q

What is the difference between the ReCiPe method and the UBA method?

A

Damage-based method, i.e. **in contrast to **the UBA method, evaluation at midpoint and endpoint level

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3
Q

What does the Life Cycle Sustainability Assessment (LCSA) consist of?

A

LCSA = LCA + LCC + SLCA
LCA: Life Cycle Assessment (Ökobilanzierung)
LCC: Life Cyvle Costing (Lebenszykluskostenrechnung)
SLCA: Social Life Cycle Assessment

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4
Q

State the goal and scope of the social LCA:

A
  • Analysis of social and socio-economic impacts
  • Stakeholder engagement as part of the analysis itself, e.g., by providing information on impacts
  • Justification necessary if an impact category is omitted
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5
Q

List the disadvantages of the UBA method

A
  • No aggregation of environmental impacts possible
  • No calculation of the impact potential of the area, toxicity, noise & water consumption available (yet)
  • Applicability to other countries not possible/only possible to a limited extent
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6
Q

LCA VS Social LCA: Impact Assessment

A

LCA
* At least partially scientifically-based
* No site-specific impact assessment; definition of impact categories of site types, which depend on physical factors, such as population density or geographical conditions
* Analysis of positive effects is

SOCIAL LCA
* Subjective by nature
* Possibly site specific impact assessment; partial inclusion of ‘political characteristics, such as country, laws
* Analysis of positive and negative effects
* Application of performance reference points (e.g.,

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7
Q

LCA Life Cycle Inventory

A
  • Information on the physical properties of products as well as their production, use and disposal
  • Different data sources
  • Differences in data collection steps and methods
  • Differences in balance between quantitative, qualitative and semi-quantitative data
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8
Q
  • Fctional Unit: Example
A

e.g. 20 times a year 250 m2 lawn mowing over 10 years

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9
Q

Which environmental impacts have to be considered in the assessment?

A

Categories of the UBA (Umweltbundesamt / German Federal Environmental Protection Agency): * Raw materials consumption
* Greenhouse effect
* Ozone depletion
* Human toxicity
* Ecotoxicity
* Formation of photooxidants (summer smog) * Acidification
* Eutrophication (overfertilization)
* Land consumption
* Noise pollution

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10
Q

Reference Flow

A

The amount of a product that is needed to provide a service / function.

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11
Q

Midpoint categories

A
  • Ozone depletion
  • Human toxicity
  • Ionizing radiation
  • Photochemical oxidizer formation
  • Particle formation
  • Climate change
  • Terrestrial ecotoxicity
  • Terrestrial acidification
  • Agricultural land occupation
  • Urban land occupation
  • Natural land transformation
  • Marine ecotoxicity
  • Marine eutrophication
  • Fresh water eutrophication
  • Freshwater ecotoxicity
  • Consumption of fossil raw materials
  • Consumption of mineral raw materials
  • Water consumption
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12
Q

Life Cycle Assessment Steps

A
  1. Definition of the objective and the scope of the investigation
  2. Life cycle inventory
  3. Impact assessment
  4. Evaluation/ interpretation

Continuous: Direct application of the results

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13
Q

Life Cycle Assessment
Life Cycle Inventory – Comparability

A

Comparability
Challenge:
Incomparability, i.e., challenge to compare systems that generate products (functions) of different quality and quantity ( incomparable systems)
Target:
Comparison of systems that provide the same functionality
**
Approach: Expansion of System Boundaries**
– Ensuring the same functionality through the expansion of system boundaries
– Adjustment of system boundaries: Modelling the manufacturing of products / functions with the same quality and quantity within the different systems (Equivalent Processes)
a) Boundary Extension = Adding of equivalent processes
b) Positive Credits = Subtraction of equivalent processes

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14
Q

Life Cycle Assessment
Life Cycle Inventory – Allocation

A

Allocation
Challenge:
* Joint production, i.e. two or more products are produced in one process due to natural or technical reasons
* One process  several products: How to allocate the process-related emissions?
Target:
* Allocation of input- and output flows (environmental impacts) to different products
Approach:
* Guidance for allocation according to DIN EN ISO 14.040 ff.:
1. Avoidance of an allocation (system expansion, substitution,…)
2. Allocation due to physical terms (energy content, mass,…)
3. Allocation due to economic terms (product prices)

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15
Q

Life Cycle Assessment
Impact Assessment – Target and General Approach

A

Targets
* Assess the significance of potential environmental impacts using the results of the life cycle inventory.
* Provision of information for the evaluation phase of the life cycle assessment

Procedure
1.Selection of an evaluation procedure depending on the application (e.g. marketing / comparison with competitive products, internal decision making,…)
2.Linking lifecycle inventory data with specific impactcategories and impact indicators
3.Weighing up the various impactcategories against each other

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16
Q

Life Cycle Assessment
Goal & Scope Definition

A

Relevant Material Flows
Business-relevant material and energy flows
* Material and energy flows with (internalized) costs and prices
* Information available, e.g., price, quantity ≠ Environmentally-relevant material and energy flows
* Material and energy flows that have environmental impacts (but not necessarily costs), e.g. cause greenhouse effect, have toxicity etc.
* Example: quantity, composition/ingredients, infrastructure, material flows < 1 g

17
Q

LCA Goal and Scope Definition

A
  • Environmental impact analysis
  • Stakeholder involvement as part of the study’s review process
  • No justification required for omitting an impact category
18
Q

How is standardisation carried out according to the UBA method?

A

With the help of population averages, the values determined are set in relation to the total pollution in Germany

19
Q

Functional Unit

A
  • Quantifies the service / function / utility of a product
  • Product-specific benchmark for all input and output data and for all environmental effects
  • Allows to compare material- and energy flows of different products and processes
20
Q

Example “Mowing the lawn” Functional Unit/Reference Flow

A

Alternatives: Lawn-mowers: manual / electric / gasoline / robot
Functional Unit: e.g. 20 times a year 250 m2 lawn mowing over 10 years
Reference Flows:
1⁄2 hand mower, 3⁄4 electric mower, 1 gasoline mower (due to different lifetimes of the mowers).

21
Q

Endpoint categories Protected property

A
  • Damage to human health - Human health
  • Damage to ecosystem diversity - Ecosystem quality
  • Damage to resource availability - Resource availability