the circular footprint formula (cff) and its practical application · 2020. 12. 3. · process run...
TRANSCRIPT
1 Copyright (c) (2020) European Commission – All rights reserved
Project officers:
Alicia BOYANO-LARRIBA, Lionel THELLIER European Commission, DG ENV
10 November 2020
The Circular Footprint Formula (CFF) and its practical application Training; Environmental Footprint (EF) transition phase
Trainer:
Marc-Andree WOLF maki Consulting GmbH
Quality assurance:
Kirana (CHOMKHAMSRI) WOLF maki Consulting GmbH
Hannes PARTL Sphera Solutions GmbH
2
1. This training is directed primarily for Product Environmental Footprint
Category Rules / Organisation Environmental Footprint Sector Rules
(PEFCR/OEFSR) development and EF-compliant data set
development, both under the latest, transition phase PEF/OEF Method
(„Suggestions for updating the Product Environmental Footprint (PEF)
method”)
2. It is also supporting the implementation of PEF/OEF studies under
transition phase PEFCRs/OEFSRs, developed under those rules
3. Note for PEF/OEF studies or data sets that relate to preceding versions
of the PEF/OEF guide or are to be implemented under
PEFCRs/OEFSRs developed during the pilot phase, that the CFF rules
slightly differ in some aspects
Scope of training
4
Why the Circular Footprint Formula?
Recycling and energy recovery, as well as using secondary materials and energy leads to questions in EF work on how to account for benefits and burdens of these processes. For reproducibility and fairness, guidance is needed:
• Where is the boundary between the first and the second product system?
• How should benefits and burdens of generating and of using recycled material be shared between the first and the second product system?
• As generated secondary materials and energy carriers avoid primary materials and energy carriers being produced: how to select the specific primary material and/or energy that is avoided?
• How to handle downcycling, i.e. differences in quality between secondary material or energy and the primary material or energy?
• How to avoid double counting or gaps of benefits and burdens?
5
Overview
6
Circular Footprint Formula (CFF)
Life Cycle Inventory
(LCI) of primary material LCI associated to
secondary material input
LCI of the material recycling (or
part/product reuse) process minus
the credit for avoided primary material
LCI of the energy recovery process minus
the credit for avoided primary energy LCI of the disposal
of remaining waste
+
+
=
7
Primary
production
Manufacturing
Primary
material
Recycled
material
Ev
Qp
Recycling
process
From secondary materials and energy input and output ...
Notes: Energy and consumables input, transport, storage and other activities are always included in the model, but graphic
focuses on core steps. Waste/ashes/slag… from recycling and incineration are to be modelled to go to landfill (not shown).
Emissions
Resources
Recycling
process
Incineration
landfill
Erecycling
Ed
EER
Recycled
material
Secondary
energy
Qout
https://www.maxpixel.net/lep-elektrichestvo-Energy-Industry-Electricity-4237504
8
Primary
production
Manufacturing
Recycling
process
Incineration
landfill
Primary
material
Recycled
material
Ev
Erecycling
Primary
production
Ev*
Ed
EER
Energy
production
Primary
production
Avoided
primary
production
(“credit”)
Qp
Recycling
process
Recycled
material
Secondary
energy
Qout
... to connection with subsequent and preceding life cycles via crediting and debiting ...
Primary debit
for used
secondary
materials (as
recycled
content)
Emissions
Resources
9
Primary
production
Manufacturing Use
Recycling
process
Incineration
Landfilling
Primary
material
Recycled
material
Ev
ErecyclingEoL
Primary
production
E*v 1-R1
R1
R2
R3
1-R2-R3 ED
EER
Prim. energy
production
Primary
production
Recycling
process
Recycled
material
Secondary
energy
QSout
1-A
(1-A)
(1-B)
Avoided
primary
production
(“credit”)
Primary debit
for used
secondary
materials (as
recycled
content)
... to abstraction and formularisation.
Emissions
Resources
Qsin
Erecycled
Qp =1
A
Ev
10
The components of the CFF
11
End-of-life: recycling and avoided primary production; includes composting etc.
Use
Recycling
process
ErecyclingEoL
Primary
production
E*v
R2 Recycled
material
QSout
(1-A)
Avoided
primary
production
(“credit”)
Life Cycle Inventory (LCI) of the material
recycling (or part/product reuse) process
minus the credit for avoided primary material
QP=1
12
Point of substitution
• Necessary to be determined for the material part of the formula, i.e.
what exactly is Ev and E*v (and to which point the recycling at EoL is to
be modelled)
• Point of substitution = point in the value chain where the secondary
material substitutes primary material(s)
• Not always straightforward, e.g.:
• glass cullet vs. melted glass
• steel scrap vs. secondary steel slab
• downcycled mixed polymers vs. fence/park bench (“open loop”)
https://www.pexels.com/photo/factory-glass-machinery-melting-131820/
Use
Recycling
process
ErecyclingEoL
Primary
production
E*v
R2 Recycled
material
QSout
(1-A)
QP=1
Point of substitution
13
CFF: Factor “A”
» The factor A allocates burdens and benefits from recycling and primary material production
between the two connected life cycles
In CFF: A = 0.2, 0.5, or 0.8 . “A” is representing the market situation:
o A = 0.2: more high quality secondary material demanded than produced (e.g. many metals, glass, …);
indicator: market price is close to / same as primary
o A = 0.8: the opposite is the case (e.g. textiles, …); indicator: market price is very low compared to
primary
o A = 0.5: market situation is more balanced or unknown
A = 1 A = 0
14
• Quality ratios QSin/QP and QSout/QP shall be determined at the point of substitution per application or material and be based on:
1. Economic aspects: i.e. price ratio of secondary compared to
primary materials at the point of substitution. In case the price of
secondary materials is higher than that of the primary ones, the
quality ratios shall be set equal to 1.
2. When economic aspects are less relevant than physical aspects,
the latter may be used.
• Accounts for quality of both ingoing and outgoing recycled materials
o If Ev=E*v, the two quality ratios are needed: QSin/QP associated to the
recycled content, and QSout/QP associated to recycling at EoL -> to capture
downcycling
o If Ev≠E*v, recycling to a different product (“open-loop recycling”), one quality
ratio is needed: QSin/QP associated to the recycled content. QSout/QP is
integrated in E*v (via defining the equivalent functional unit) .
• For packaging default values are provided in Annex C
CFF: Quality ratios QSin/QP and QSout/QP
15
Primary
production
Manufacturing
Primary
material
Recycled
material
Ev
1-R1
R1 Primary
production
Qp =1
Recycling
process
1-A
Primary debit
for used
secondary
materials (as
recycled
content)
Qsin
Erecycled
LCI of primary material LCI associated to
secondary material input
Recycled content – the credit-debit balance among connected life cycles
A
Ev
16
Use Incineration
R3 EER
Prim. energy
production Secondary
energy
(1-B)
Avoided
primary
production
(“credit”)
LCI of the energy recovery process burdens
minus the credit for avoided primary energy
End-of-life: waste-to-energy and avoided primary production (plus analogous debit for secondary energy use)
! “To avoid double-counting between the current and the
subsequent system in case of energy recovery, the
subsequent system shall model its own energy use as
primary energy.” Secondary
energy
Primary
energy
production
17
CFF: Factor “B”
• The factor B is used as an allocation factor between connected life
cycles for EoL energy recovery processes and generated secondary
energy
• B is equal to 0 as default, i.e. 100% of generated, externally used
energy is credited at the producer and debited at the user of the
secondary energy
• This also applies to waste fuels (e.g. of used rubber in cement kilns,
but requires correct identification of point of substitution)
18
Use
Landfilling
1-R2-R3 ED
LCI of the disposal
of remaining waste
End-of-life: landfilling (includes other EoL treatment without product output)
Note that remaining waste after energy recovery is to be modelled as landfilled, in addition (unless used, e.g.
as ash for cement making); EF waste-to-energy data sets consider this generally already.
19
Circular Footprint Formula (CFF)
Life Cycle Inventory
(LCI) of primary material LCI associated to
secondary material input
LCI of the material recycling (or
part/product reuse) process minus
the credit for avoided primary material
LCI of the energy recovery process minus
the credit for avoided primary energy LCI of the disposal
of remaining waste
+
+
=
! Also used secondary
energy / waste materials to
be modelled as replaced
primary energy (mix)!
20
List of variables and parameters of the CFF
A Allocation factor of burdens and benefits (jointly: “credits”) between supplier and user of recycled materials.
B Allocation factor of energy recovery processes. It applies both to burdens and benefits.
QSin Quality of the ingoing secondary material, i.e. the quality of the recycled material at the point of substitution.
QSout Quality of the outgoing secondary material, i.e. the quality of the recycled material at the point of substitution.
QP Quality of the primary material, i.e. quality of the virgin material.
R1 Proportion of material in the input to the production that has been recycled from a previous system.
R2 Proportion of the material in the product that will be recycled (or reused) in a subsequent system. R2 shall therefore take into
account the inefficiencies in the collection and recycling (or reuse) processes. R2 shall be measured at the output of the recycling
plant.
R3 Proportion of the material in the product that is used for energy recovery at EoL.
Erecycled Specific emissions and resources consumed (per functional unit) arising from the recycling process of the recycled (reused)
material, including collection, sorting and transportation process.
ErecyclingEoL Specific emissions and resources consumed (per functional unit) arising from the recycling process at EoL, including collection,
sorting and transportation process.
Ev Specific emissions and resources consumed (per functional unit) arising from the acquisition and pre-processing of virgin
material.
E*v Specific emissions and resources consumed (per functional unit) arising from the acquisition and pre-processing of virgin
material assumed to be substituted by recyclable materials.
EER Specific emissions and resources consumed (per functional unit) arising from the energy recovery process (e.g. incineration with
energy recovery, landfill with energy recovery, etc.).
ESE,heat and ESE,elec Specific emissions and resources consumed (per functional unit) that would have arisen from the specific substituted energy
source, heat and electricity respectively.
ED Specific emissions and resources consumed (per functional unit) arising from disposal of waste material at the EoL of the
analysed product, without energy recovery or other usable product output.
XER,heat and XER,elec The efficiency of the energy recovery process for both heat and electricity.
LHV Lower heating value of the material in the product that is used for energy recovery.
21
Determining the values of the CFF variables and parameters
22
CFF: Recycled content „R1“
The PEFCR shall prescribe the list of R1 values.
Situation Option Most relevant process Other process
Situation 1:
Process run by the company using the
PEFCR
Option 1 Specific R1 value
Option 2 Specific R1 value Default (application-
specific) R1 value
Situation 2:
Process not run by the company but with
access to (company)-specific information
Option 1 Supply-chain specific R1 value
Option 2 Default (application-specific) R1 value
Situation 3:
Process not run by the company and without
access to specific information
Option 1 Default (application-specific) R1 value
• Default values are given in Annex C of the PEF method document: Current version Annex C:
https://eplca.jrc.ec.europa.eu/permalink/Annex_C_V2.1_May2020.xlsx (check
https://eplca.jrc.ec.europa.eu/LCDN/developerEF.xhtml for updates)
• For PEF studies on product groups and organisations for which a PEFCR is not available, and for common
requirements on traceability and evidence needed, please see PEF method document p. 69 f
23
CFF: Recycling output rate „R2“
• The PEFCR shall list the default R2 values (i.e. as provided in Annex C of the
PEF method) to be used when no company-specific values are available
• In case no company-specific R2 values are available, the Technical Secretariat
of PEFCR selects and fixes either:
• R2 shall be equal to 0
• Technical Secretariat generates new statistics to assign a new R2 value for
use in PEF studies; to be approved by the Commission
For PEF studies:
• Evaluate the recyclability of the material, provide evidence (see p. 72 of PEF method), use company-specific values if available
• If no company-specific values are available and the criteria for the evaluation of recyclability are fulfilled, application-specific R2 values from Annex C shall be used
• If an R2 value is not available for a specific country, then the European average shall be used;
• If an R2 value is not available for a specific application, the R2 values of the material shall be used (e.g. materials’ average);
• In case no R2 values are available, R2 shall be set equal to 0 or new statistics may be generated in order to assign an R2 value in the specific situation.
24
Default values for CFF parameters Annex C
• Factor A (for sharing recycling burdens and benefits among connected
life cycles); either “0.2”, “0.5” or “0.8”
• Factor B (for sharing energy recovery burdens and benefits among
connected life cycles); always “0”
• QSin, QSout - downcycling factors for secondary materials
• Recycled content R1
• Recycling rate R2
• Shares of landfilling and of waste incineration per country and for EU28
25
Example PET blister packaging as part of a PEF study on a packaged product
26
Primary
production
Manufacturing Use
Recycling
process
Incineration
Landfilling
Primary
material
Recycled
material
Ev
ErecyclingEoL
Primary
production
E*v 1-R1
R1
R2
R3
1-R2-R3 Ed
EER
Energy
production
Primary
production
Recycling
process
Recycled
material
Secondary
energy
QSout
1-A
(1-A)
(1-B)
QSin
EER
Erecycled
QP =1
Example PET blister packaging, 20 g
Ev 0.0442 kg CO2-eq (per 20 g PET)
Erecycled 0.0133 kg CO2-eq (per 20 g PET)
QSin 1 (SSP high qual. recycled PET pellets)
QP 1
A 0.5
R1 0.2 (company specific; default = 0)
𝟏 − 𝑹𝟏 𝑬𝒗 + 𝑹𝟏 𝒙 (𝑨𝑬𝒓𝒆𝒄𝒚𝒄𝒍𝒆𝒅 + 𝟏 − 𝑨 𝑬𝒗𝑸
𝑺𝒊𝒏
𝑸𝑷
) = 0.0411 kg CO2-eq
A
Ev
+
+
=
27
Primary
production
Manufacturing Use
Recycling
process
Incineration
Landfilling
Primary
material
Recycled
material
Ev
ErecyclingEoL
Primary
production
E*v 1-R1
R1
R2
R3
1-R2-R3 Ed
EER
Energy
production
Primary
production
Recycling
process
Recycled
material
Secondary
energy
QSout
1-A
(1-A)
(1-B)
QSin
EER
Erecycled
QP =1
Example PET blister packaging, 20 g
E*v 0.0442 kg CO2-eq (per 20 g PET)
ErecyclingEoL 0.0133 kg CO2-eq (per 20 g PET)
QSout 1 (SSP recycled PET pellets)
QP 1
A 0.5
R2 0.4 (company specific, default = 0)
𝟏 − 𝑨 𝑹𝟐 x (ErecyclingEoL- E*v𝑸
S𝒐𝒖𝒕
𝑸P
) = − 0.00618 kg CO2−eq
Use
+
+
=
28
Primary
production
Manufacturing Use
Recycling
process
Incineration
Landfilling
Primary
material
Recycled
material
Ev
ErecyclingEoL
Primary
production
E*v 1-R1
R1
R2
R3
1-R2-R3 Ed
EER
Prim. energy
production
Primary
production
Recycling
process
Recycled
material
Secondary
energy
QSout
1-A
(1-A)
(1-B)
QSin
Erecycled
QP =1
Example PET blister packaging, 20 g
EER plus credits 0.0279 kg CO2-eq (per 20 g PET)
B 0
R3 0.27
(1-B) R3 x (EER - LHV x XER,heat x ESE,heat – LHV x XER,elec x ESE,elec) = 0.00753 kg CO2-eq
+
+
=
No use of secondary energy in
PET blister packaging
production step, hence no debit
on secondary energy.
29
Primary
production
Manufacturing Use
Recycling
process
Incineration
Landfilling
Primary
material
Recycled
material
Ev
ErecyclingEoL
Primary
production
E*v 1-R1
R1
R2
R3
1-R2-R3 ED
EER
Energy
production
Primary
production
Recycling
process
Recycled
material
Secondary
energy
QSout
1-A
(1-A)
QSin
Erecycled
QP =1
Example PET blister packaging, 20 g
ED 0.000680 kg CO2-eq (per 20 g PET)
R2 0.4 (company specific, default = 0)
R3 0.27
(1-B) R3 x) = 0 kg CO2eq
(1 - R2 - R3) x ED = 0.000224 kg CO2-eq
+
+
=
30
Example PET blister packaging, 20 g
0.0411 kg CO2-eq (jointly with primary PET)
- 0.00618
kg CO2-eq
0.00753
kg CO2-eq
0.000224
kg CO2-eq
= 0.0411 – 0.00618 + 0.00753 + 0.000224 = 0.0427 kg CO2-eq per 1 PET blister packaging from CFF calculation
A
Ev
! The PEF study shall report all parameters and variable values used, the source and – if not default – provide evidence.
31
Special cases
32
How to apply the CFF to intermediate products
• Intermediate products --> cradle-to-gate PEF studies (e.g. metal sheets, flexible packaging, paper)
• The PEFCR shall prescribe…
• the use of the CFF
• to exclude the end-of-life by setting R2, R3 and ED to 0
• application- or material-specific A-values for the product, and
• to use and report results with two types of A values for the product in scope:
o Setting A = 1 in the PEF profile calculation
o Setting A = default value as listed in PEFCR to be used when creating EF
compliant datasets
33
Example: metal sheets, as intermediate product
Metal sheets (steel) for building (from pilot phase):
A = 1 / 0.2; R1 = 0.54; R2 = 0; R3 = 0, QSin/QP = 1; QSout/QP = 1
Setting A = 1 in the PEF profile calculation:
» 0.46Ev + 0.54(Erecycled) + 0
Setting A = default value (“0.2”) as listed in PEFCR to be used for additional technical information and for creating EF-compliant data sets:
» 0.46Ev + 0.54(0.2Erecycled – 0.8Ev) + 0
𝟏 − 𝑹𝟏 𝑬𝒗 + 𝑹𝟏 𝒙 𝑨𝑬𝒓𝒆𝒄𝒚𝒄𝒍𝒆𝒅 + 𝟏 − 𝑨 𝑬𝒗
𝑸𝑺𝒊𝒏
𝑸𝑷
+ 𝟏 − 𝑨 𝑹𝟐 x (ErecyclingEoL- E*v
𝑸𝑺𝒐𝒖𝒕
𝑸𝑷
)
Material part of CFF (i.e. energy and landfill part still to be added):
34
How to deal with specific aspects
• Recovery of bottom ashes or slag from incineration
• Landfill with energy recovery
• Municipal solid waste
• Compost and anaerobic digestion/ sewage treatment
• Waste materials used as fuel on input side
• Modelling complex products
• Extended product lifetime
• Reuse and refurbishment
• Reuse (e.g. of packaging)
For details, please see PEF method document, p. 74 ff
37
Exercise – wood-aluminium window frame
38
Exercise/ Case study
Product characteristics
• Wood-aluminium window with 165 mm frame depth, insulating glass 4mm flat glass in
outer sash. Dimensions 1.23 x 1.48 m, weight 76.5 kg
• Lifetime 60 years
• Maintenance measures: gaskets replacement every 10 years, painting every 15 years,
washing as needed
• Product standard EN 13163:2015 - Thermal insulation products for building
• Market: Denmark
! For this training, we will focus on aluminium and wood frame, only.
! Impacts will be calculated for Climate change (GWP), only.
39
Exercise/ Case study - Material composition
43.09 kg
25.42 kg
5.66 kg
0.91 kg
0.90 kg
0.49 kg
0.49 kg
76.5 kg Total
Materials/parts
40
Template to note down parameters and calculation
=
=
= A
Ev
=
=
Mass= ;R1 = ; R2 = ; R3 = A = ; B = 0; Qsin/Qp = ; Qsout/Qp =
Climate change [kg CO2 eq] of …EV,EV*= ; Erecycled= ; ErecyclingEoL= ; EER= ; Ed=
41
4.4.8 End of life modelling
Materials for exercise
Users of the PEF method shall report all the parameters used. Default values for some parameters (A,
R1, R2, R3 and Qs/Qp for packaging) are available in Annex C (see following sections for further details):
users of the PEF method shall refer to the version of Annex C they are using. Annex C is available at
http://eplca.jrc.ec.europa.eu/LCDN/developerEF.xhtml.
If a default value for R1 and R2 is not included in Annex C, users of the PEF method may provide
new values to the Commission. Such values shall be part of a study that has been reviewed by an
external independent third party reviewer. The Commission will take the decision if the new values are
acceptable and can be implemented in an updated version of Annex C.
Chapter 4 and Annex C
PEF Method, i.e. Suggestions for updating the Product Environmental Footprint (PEF) method *
* Zampori, L. and Pant, R., Suggestions for updating the Product Environmental Footprint (PEF) method, EUR 29682 EN, Publications
Office of the European Union, Luxembourg, 2019, ISBN 978-92-76- 00654-1, doi:10.2760/424613, JRC115959.
42
Circular Footprint Formula (CFF)
Life Cycle Inventory
(LCI) of primary material LCI associated to
secondary material input
LCI of the material recycling (or
part/product reuse) process minus
the credit for avoided primary material
LCI of the energy recovery process minus
the credit for avoided primary energy LCI of the disposal
of remaining waste
+
+
=
This environmental impact of incineration and credits
for recovered energy is available as combined EF
secondary data set, per material (analogous as ED is a
combined data set) – no need to manually calculate,
usually
43
R1 R2 (Europe, post-consumer) A
Materials for exercise
! The company sources aluminium input with 20% recycled content R1 = 0.2
44
Materials for exercise
45
R3 = (1-R2)*incineration share R3 = (1-0.9)*0.97= 0.097
Materials for exercise
Aluminium EoL fate of un-recycled share:
46
Materials for exercise
Wood info on A, R1, R2, Qsin, Qsout:
• No recycled wood in wooden window fame profile (R1 = 0)
• No recycling at EoL, due to organic coating and fungicide treatment (R2 = 0)
• Hence, no need for factor A, i.e. all formula parts with parameter “A” are = 0
• Hence, also Qsin and Qsout are not required, for our example
47
Source: “Screening of EU and national policies, legislation and trends for EoL wooden doors and windows,
2018”
1-R2-R3 (landfilling) R3 (waste incineration) R2 (recycling)
Materials for exercise
Wood EoL routes
48
Environmental footprint secondary data sets* to be used:
Dataset name UUID EV and EV*: Climate change impact
[kg CO2 eq.]
per 1 kg product/service
EU28+ Aluminium ingot mix DD93261C-D6DA-44EC-
A842-78B4A42C2884
8.3
Landfill of inert (aluminium) 3F7D5E8A-A112-4585-
9E2F-DC8B667D66DC
0.027
Recycling of aluminium into
aluminium scrap - from post-
consumer **
C4F3BFDE-C15F-4F7F-
8D35-BED6241704DB
0.55
Waste incineration of non-ferro
metals, aluminium, more than 50µm
FCA45061-A4D6-4665-
B583-8EC95C407FB5
0.12 ***
Material for exercise (Aluminium)
* Access to data sets via data nodes of data providers (https://eplca.jrc.ec.europa.eu/LCDN/contactListEF.xhtml), or distributed integrated in
major LCA Software tools. Note use restrictions outside PEF/OEF studies under established PEFCRs/OEFSRs.
** The data set name is misleading: This is melting of scrap into secondary aluminium slabs, while this includes some losses, as the data
set is not for clean scrap, so somewhat overestimates the impact.
*** The metal is not oxidised/burned, i.e. does not generate any energy output that could be credited; recovery from Aluminium from
slag/ash not done in practice, hence no credit neither
49
Environmental footprint secondary data sets* to be used:
Material for exercise
Dataset name UUID EV and EV*: Climate change impact
[kg CO2 eq]
per 1 kg product/service
Sawn wood, softwood 4BDF9A29-2AE8-49F4-
A92A-CDF7B668EBBE
0.011
DK Waste incineration of
processed wood
A52AF3C9-08B7-48AB-
9309-74DA8356245D
- 0.97 **
Landfill of processed wood 0907B969-C8A5-4317-84B3-
04AD0A04447E
1.8 **
* Access to data sets via data nodes of data providers (https://eplca.jrc.ec.europa.eu/LCDN/contactListEF.xhtml), or distributed integrated in
major LCA Software tools. Note use restrictions outside PEF/OEF studies under established PEFCRs/OEFSRs.
** Including the credit (grid mix) for exported/used electricity and heat from energy recovery / landfill gas
50
Excercise: results 20 Minutes remaining 19 18 17 16 15 14 13 12 11 10 9 8 7 6 5 4 3 2 1 0
51
Aluminium (recycled content, EoL route shares)
= 0.9
= 0.097
= 1-0.9-0.097
= 0.003 A
Ev
! The PEF study shall report all parameter and variable values used, the source and – if not default – provide evidence.
= 1-0.2 = 0.8
= 0.2
R1 = 0.2, R2 = 0.9, R3 = 0.097
52
= 0.9*5.66
= 5.09 [kg]
= 0.097*5.66
= 0.55 [kg]
= 0.003*5.66 = 0.017 [kg] A
Ev
! The PEF study shall report all parameter and variable values used, the source and – if not default – provide evidence.
= (1-0.2)*5.66 = 4.53 [kg]
Aluminium (mass recycled content, EoL routes)
= 0.2*5.66 = 1.13 [kg]
Aluminium mass = 5.66 [kg]
53
= (1-0.2)*0.9
*5.66*(0.55-
8.3*1)= - 31.56 [kg CO2 eq]
= (1-0)*0.097
*5.66*(0.12-0-0)
= 0.066 [kg CO2 eq]
= (1-0.9-0.097)*5.66*0.027 = 0.00046
[kg CO2 eq]
A
Ev
= (1-0.2)*5.66*8.3 [kg CO2 eq]
= 37.60 [kg CO2 eq]
A = 0.2, Qsin/Qp = 1, Qsout/Qp = 1, B = 0
= 37.60 + 7.63 – 31.56 + 0.066 + 0.00046 = 13.74 [kg CO2-eq] per 1 window frame (contribution Aluminium part)
Aluminium (GWP recycled content, EoL routes)
Note: disassembly, sorting, transport etc. not considered here for simplicity
= 0.2*5.66*((0.2*0.55) + (1-0.2)*8.3*1) [kg CO2 eq]
= 1.13*(0.11+6.64) = 7.63 [kg CO2 eq]
= 𝑹𝟏 𝒙 𝑨𝑬𝒓𝒆𝒄𝒚𝒄𝒍𝒆𝒅 + 𝟏 − 𝑨 𝑬𝒗
𝑸𝑺𝒊𝒏
𝑸𝑷
= 𝟏 − 𝑹𝟏 𝑬𝒗
= 𝟏 − 𝑨 𝑹𝟐 x (ErecyclingEoL- E*v
𝑸𝑺𝒐𝒖𝒕
𝑸𝑷
)
= 𝟏 − 𝑩 𝑹𝟑 x (EER – LHV x XER,heat x ESE,heat
– LHV x XER,elec x ESE,elec)
= 𝟏 − 𝑹𝟐 − 𝑹𝟑 x ED
54
Wood (recycled content, EoL route shares)
= 0
= 0.75
= 0.25 A
Ev
! The PEF study shall report all parameters and variable values used, the source and – if not default – provide evidence.
= 1-0 = 1
= 0
55
Wood (mass material input, EoL routes)
= 0 [kg]
= 19.06 [kg]
= 6.36 [kg] A
Ev
! The PEF study shall report all parameters and variable values used, the source and – if not default – provide evidence.
= 25.42 [kg]
= 0 [kg]
Wood mass = 25.42 [kg]
56
Wood (GWP material input, EoL routes)
= (1-0.5)*0*…
= 0 [kg CO2 eq]
= (1-0)*19.06*(-
0.97) = - 18.49
[kg CO2 eq]
= (1-0-0.75)*25.42*1.8 = 11.44 [kg CO2 eq] A
Ev
= 25.42*0.011
= 0.280 [kg CO2 eq]
= 0.280 +0 + 0 – 18.49 + 11.44 = - 6.77 [kg CO2-eq] 1 window frame (contribution wood part)
total (Aluminium and wood parts): 13.74 - 6.77 = 6.97 [kg CO2-eq]
A=0.5, B=0
Notes: Energy credit for used landfill gas included in landfilling dataset. Disassembly, sorting, transport etc. not
considered here for simplicity.
= 𝑹𝟏 𝒙 𝑨𝑬𝒓𝒆𝒄𝒚𝒄𝒍𝒆𝒅 + 𝟏 − 𝑨 𝑬𝒗
𝑸𝑺𝒊𝒏
𝑸𝑷
= 𝟏 − 𝑹𝟏 𝑬𝒗
= 0*… = 0 [kg CO2 eq]
= 𝟏 − 𝑨 𝑹𝟐 x (ErecyclingEoL- E*v
𝑸𝑺𝒐𝒖𝒕
𝑸𝑷
)
= 𝟏 − 𝑩 𝑹𝟑 x (EER – LHV x XER,heat x ESE,heat
– LHV x XER,elec x ESE,elec)
= 𝟏 − 𝑹𝟐 − 𝑹𝟑 x ED
There was an error in the original exercise calculations
(0.11 instead of 0.011), which is now corrected here and in
the following steps). Please accept our apologies.
57
Aspects not covered in the training exercise
The following aspects and elements have not been explicit part of the exercise – please
refer to slides 6 to 35 for guidance:
1. Open loop recycling (e.g. of wood to particle board)
2. Landfill gas recovery (e.g. from wood in landfill; included in EF secondary datasets)
3. Use of secondary energy or waste materials as energy input (e.g. waste wood or waste tires for
industrial heat production)
4. Use of material/application combinations that are not (yet) part of Annex C
5. Identifying the point of substitution
6. Direct replacement of primary material or after mixing with secondary material
7. Extended product lifetime, Reuse and refurbishment, Reuse (e.g. of packaging)
8. Claiming / not claiming pre-consumer scrap input as recycled content
9. CFF for intermediate products
58
CFF in software models
PEF/OEF studies are assumed to be implemented using software support:
1. Specific EF software with a pre-configured model of the product system, e.g. implementing a
PEFCR. Usually the formula will be integrated and the user exclusively needs to confirm or
correct the parameters (A, R1, R2,…) for each material, or add them, in case any new materials
are used (as far as eligible within a PEFCR)
2. Generic LCA software with CFF processes or models provided by the developers or to be
developed by the user, with specifics depending on the software. The parameters are to be
compiled by the user (or taken from the PEFCR, if existing).
61
Link Collection
» Further reading about the EF transition phase
» EF Wiki
» Training calendar, access also to webinar and training recordings and slides
» PEF method
» OEF method
» Description of governance bodies
» Existing PEFCRs/OEFSRs, e-learning tools, and technical reports
» Rules for EF compliant data sets
» Email address technical helpdesk: [email protected]
» Email address EF Team at DG ENV: [email protected]
62
Thank you for your interest and time!
The contents of this training have been produced under service contract
07.0203/2017/SI2.762537/SER/ENV.B.1 with the European Commission.
The slides’ content has been approved by the Commission and represents the view of the
Commission, while opinions expressed during the webinar are those of the contractors only
and do not necessarily represent the EU’s official position.
Source: Marc-A. Wolf; freely usable under CC license