Chapter 3 - Corporate Perspective 3.5 Life Cycle Assessment Flashcards
Which tests should be carried out as part of the evaluation?
Completeness check
Sensitivity check
Consistency check
Other checks
What is the difference between the ReCiPe method and the UBA method?
Damage-based method, i.e. **in contrast to **the UBA method, evaluation at midpoint and endpoint level
What does the Life Cycle Sustainability Assessment (LCSA) consist of?
LCSA = LCA + LCC + SLCA
LCA: Life Cycle Assessment (Ökobilanzierung)
LCC: Life Cyvle Costing (Lebenszykluskostenrechnung)
SLCA: Social Life Cycle Assessment
State the goal and scope of the social LCA:
- 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
List the disadvantages of the UBA method
- 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
LCA VS Social LCA: Impact Assessment
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.,
LCA Life Cycle Inventory
- 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
- Fctional Unit: Example
e.g. 20 times a year 250 m2 lawn mowing over 10 years
Which environmental impacts have to be considered in the assessment?
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
Reference Flow
The amount of a product that is needed to provide a service / function.
Midpoint categories
- 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
Life Cycle Assessment Steps
- Definition of the objective and the scope of the investigation
- Life cycle inventory
- Impact assessment
- Evaluation/ interpretation
Continuous: Direct application of the results
Life Cycle Assessment
Life Cycle Inventory – Comparability
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
Life Cycle Assessment
Life Cycle Inventory – Allocation
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)
Life Cycle Assessment
Impact Assessment – Target and General Approach
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