Europaudvalget 2022-23 (2. samling)
EUU Alm.del
Offentligt
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Final Report
Fluoropolymer waste in Europe 2020
End-of-life
(EOL) analysis of fluoropolymer applications, products and associated waste streams
Elaborated for
July 2022
EUU, Alm.del - 2022-23 (2. samling) - Supplerende svar på spørgsmål 49: Spm. om, hvilke interessenter, virksomheder mv. ministeriet har været i dialog med i forbindelse med ønsket om at indføre et forbud imod anvendelsen af PFAS, til miljøministeren, kopi til udenrigsministeren
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Main objective and conclusion
Main objective
The report ‘Fluoropolymer
waste
in Europe 2020‘
was initiated to provide detailed
information about the end-of-life fate of fluoropolymer applications, products and
associated waste streams. The report has qualitative and quantitative character.
Conclusion
In 2020, around 40 kt of fluoropolymer materials were sold to EU
fluoropolymer product manufacturers. 23.5 kt of fluoropolymer waste were
collected, either in commingled waste streams or partly in source separated
waste fractions.
Almost 84% of all fluoropolymer applications were incinerated at the end of
their life in energy recovery (MSWI ~72%) or thermal destruction (metal
recycling ~12%) processes. 13% of the collected fluoropolymer waste was
landfilled and around 3% was recycled.
This report delivers an in-depth description on how and where fluoropolymer
containing products and corresponding wastes are generated and what happens to
the collected fractions at the end of their life. Quantities of fluoropolymer waste are
included as far as possible based on an end-of-life fluoropolymer (and relevant
fluoropolymer containing products) lifetime assessment model.
A correlation matrix between fluoropolymer applications and the penetration of
relevant waste streams (by mass in kt and %) was developed and the waste
treatment route (recycling, energy recovery and landfill) is shown.
Identification where fluoropolymer applications and products end up at the end
of their life including re-use of processing scrap and recycling of either pre- or
post-consumer fluoropolymer waste (either mechanical, e.g., conversion into
PTFE micro powders or chemical) in the EU.
Identification of major waste streams in which the fluoropolymer applications
and products end up incl. total volumes in kt as well as the penetration of
fluoropolymers (in kt and %) in the EU.
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End-of-life fluoropolymer production and processing equipment used for
different industrial segments, such as Chemical, Energy, Food & beverage,
Pharma and Semiconductor accounted for the major share of the total
fluoropolymer waste quantity collected (~13 kt).
The overall fluoropolymer penetration in all waste streams was less than
0.01% by weight. In comparison, plastics in total accounted for about 4.8% of
the total waste collection volume (excl. mineral fractions).
Chemical recycling of fluoropolymer waste offers the opportunity to produce
virgin-like fluoropolymer raw materials for the production of goods and
products without quality limitations. However, building robust supply chains for
large-scale and economical feasible recycling processes is one of the most
important issues to be addressed in the coming years.
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Conversio Market & Strategy GmbH
About Conversio
Conversio employees specialize in b2b research and consultancy and work in the field of plastics production, processing and waste management more
than 25 years. In 2018 Conversio conducted a fluoropolymer analysis focusing on potential recycling opportunities on behalf of the PlasticsEurope
Fluoropolymer project group.
In March 2022, Conversio was commissioned to conduct a new report with focus on the end-of-life scenario of fluoropolymer products and applications
by the industry association Pro-K.
Christoph Lindner
+49 (0) 6021 / 9219991
[email protected]
Hendrik Beylage
+49 (0) 6021 / 9219996
[email protected]
Julia Hein
+49 (0) 6021 / 9219997
[email protected]
Conversio Market & Strategy GmbH
Am Glockenturm 6
63814 Mainaschaff
Germany
+49 (0) 6021 1506 700
[email protected]
www.conversio-gmbh.com
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Agenda
Introduction and project frame
Management Summary
5
21
Fluoropolymer products & applications
Fluoropolymer waste
In-depth waste analysis
Circular economy approach
Appendix
27
33
44
55
60
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List of abbreviations
ABS
AFRA
ASR
B&C
C&I
CAPA
CCL
CPI
ELV
EOL
ETFE
EU
EV
FEP
FKM
FP
HVACR
kt
LCA
Acrylonitrile butadiene-styrene copolymer
Aircraft fleet recycling association
Auto shredder residue
Building & construction
Commercial & industrial
Centre for aviation
Copper cladded laminates
Chemical, process & industrial
End-of-life vehicle
End-of-life
Ethylene tetrafluoroethylene
abbreviated for EU27 + Norway, Switzerland, UK
Electric vehicle
Fluorinated ethylene propylene
Fluor-rubber/caoutchouc
Fluoropolymers
Heating, ventilation, air conditioning, refrigeration
kilo tonnes
Life cycle analysis
LCV
MSW
MSWI
PCB
PCTFE
PE-HD
PFA
PP
PS
PTFE
PV
PVC
PVDF
PVF
RDF
SLF
SRF
t
WEEE
Light commercial vehicle
Municipal solid waste
Municipal solid waste incineration
Printed circuit boards
Polychlorotrifluoro ethylene
High-density polyethylene
Perfluoroalkoxy
Polypropylene
Polystyrene
Polytetrafluorethylene
Photovoltaic
Polyvinyl chloride
Polyvinylidene fluoride
Polyvinyl fluoride
Refuse derived fuel
Shredder-light fraction
Solid recovered fuel
tonnes (metric)
Waste from electrical and electronic equipment
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Initial situation, frame and target
Fluoropolymers are high-tech polymers with fluorine atoms directly attached to their carbon backbone. They are plastics which are virtually chemically
inert, non-wetting, non-stick, and highly resistant to temperature, fire and weather. These polymers are used various applications and different industries,
e.g., transportation, chemical process industry, (consumer-)electronics, pharmaceutical industry.
Since the discovery of PTFE in 1938, fluoropolymers have become critical components in numerous technologies, industrial processes and everyday
applications. Their use is widespread what makes it a challenge to evaluate the full range of applications and shares (by weight) in associated waste
streams.
Compared to other plastics, fluoropolymers are usually used as part of other applications and represent around 0.1% of the total plastics processing
demand of the EU countries.
Nevertheless, these plastics, with their unique properties, are high-quality materials where other materials are either inferior or simply do not offer
adequate substitutes.
The data and information presented in this report reflect the willingness of the fluoropolymer industry to provide additional end-of-life information on
fluoropolymer applications and products in response to requests from EU legislators.
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Project frame
1
Regional focus
EU27+3 countries (abbreviated by the term “EU” in this report)
Analyzed types of fluoropolymers within this study
Non-melt processible fluoroplastics, such as PTFE, represent the main focus of the study*
Thermoplastics such as PVDF
Other ETFE
5%
PFA
3%
6%
PCTFE
2%
FEP
8%
Elastomers (vulcanized, rubbers) such as FKM
The distribution of FP types shown in the graph on the right is
unique for the EU market and differs with regard to individual
FP shares in other regions such as North America.
The share of FEP materials used for Local Area network (LAN)
cabling (fire resistance) for housing applications in the US is for
example significantly higher compared to the EU market.
PTFE
56%
Total 40 kt
of fluoropolymers
converted into
products by EU
converters
12%
PVDF
8%
FKM
* almost 90% of all fluoropolymer (and elastomer) processors process PTFE materials for the manufacturing of their products
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Project frame
2
Important applications and origin of fluoropolymers waste
Fluoropolymers provide specific physical and chemical characteristics for wide range of different processes, components and final product applications.
The widespread use of fluoropolymers in various applications and industry segments makes it a challenge to evaluate the full extent of fluoropolymer
waste origins and corresponding penetration of major waste streams.
This study will focus on six major industries where the use and waste generation of fluoropolymers is considered to be particularly significant.
Within each of the key sector, the specific uses (“applications / products”) of fluoropolymers will be identified. For each key
sector (based on the
corresponding relevant products and applications), this report shows the quantity of fluoropolymers put on the market, different lifetime scenarios and
end-of-life treatment of fluoropolymer waste.
The study will cover the following industry segments:
Automotive
Aerospace
Electronics & semiconductors
Chemicals (CPI)
Medical & pharma
Other (e.g., cookware)
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Project frame
3
Fluoropolymer products and applications in different industry segments
Automotive, Aerospace, Electronics and semiconductors
Major fluoropolymer applications and product illustrations I
Industry segment
Automotive
Major applications
Excl. vehicles >3.5 tonnes and other transport segments such as
trains and ships
Battery binder, e.g., PTFE and PVDF in EVs
Oxygen sensor parts (wire insulation, grommet and sleeve)
Seals & bearings; fuel and brake system components
Ventilation of electronic housings, gear boxes, lamp housings and
batteries using porous PTFE.
Large and small commercial and private aircrafts, aerospace
communication technology and associated aerospace periphery
Cable insulation (tape winding)
PTFE tubing for fuel system & hydraulics
Spring reinforced seals for hydraulic systems
Bearings
Electronic devices of any kind incl. semiconductor manufacturing,
communication technology, HVACR, consumer electronics
PCB (printed circuit boards), CCL (copper cladded laminates)
Associated products such as smartphones, tablets, notebooks
Cable insulation, containers, pumps and other (ultra-pure) liquid
handling equipment, e.g., in chip manufacturing plants
Seals, valves, tapes used in various HVACR applications
Fluoropolymer product illustrations
Aerospace
Electronics &
semiconductors
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Project frame
4
Fluoropolymer products and applications in different industry segments
Automotive, Aerospace, Electronics and semiconductors
Major fluoropolymer applications and product illustrations II
Industry segment
Chemicals (CPI)
Major applications
Industry segments chemical, process & industrial incl. petrochemical
and energy applications
Pipe liners (e.g., PTFE); lining of valves, pumps (e.g., PFA)
Bellows (flexible vessels), lining of distillation columns, containers
for storage and transportation
Hoses, seals, films etc. used for renewable energy applications
Gaskets, filters, membranes, flue gas coolers, etc.
Medical applications and equipment of any kind, pharmaceutical
processing equipment
Tubing (e.g., PTFE)
Components for syringes & diaphragms
Components and products for microinvasive surgery
Implants, stents
Fluoropolymer product illustrations
Medical & pharma
Other (e.g., cookware)
Coated consumer & professional cookware, coated sheer metal
applications such as building cladding, industrial food & beverage
processing equipment, lubricants, architectural and wearable textiles,
defence & military applications, renewables like PV and wind power
Coating of pans, pots and trays, sheet metal building cladding
Textiles (wearable) and coated (glass) fabrics (architectural)
Applications not listed in the other industry segments
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Project frame
5
Fluoropolymer waste in major waste streams
residential, electronics and automotive
Corresponding waste streams I
Waste stream
Residential household waste and
municipal waste generated by
commercial activities
Definition
Residential waste collected by or on behalf of municipalities (household
waste, excluding all waste fractions which are collected separately) as
well as municipal waste generated by commercial activities and other
sources, whose activities and waste are similar to those of households
(commerce, trade, small business, institutions and municipal services),
collected by or on behalf of municipalities
Waste from electrical and electronic equipment (commonly referred to
as WEEE) from households and commercial and industrial (professional
WEEE) activities; collected on behalf of municipalities, retailers and
private organizations
Plastic waste through dismantling of end-of-life vehicles (ELVs) and
plastic residual fractions as part of metal shredding processes in auto-
shredder residue respectively shredder-light-fraction
Fluoropolymer end-of-life applications
Other (e.g., cookware)
Electronics (usually smaller end-of-life
consumer electronics)
Electronic waste collection (WEEE)
Electronics & semiconductors
ELV incl. auto-shredder residue (ASR)
Automotive
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Project frame
6
Fluoropolymer waste in major waste streams
commercial and industrial
Corresponding waste streams II
Waste stream
Commercial & industrial
Various waste streams collected (mostly)
on behalf of private waste management
companies respectively dedicated waste
services for specific industries.
Description of relevant fluoropolymer waste
streams as far as possible (e.g., extraction
of fluoropolymer pipe liners from chemical
process equipment)
Definition
Commercial & industrial waste generated, collected, sorted, treated and
disposed of by private waste management companies, e.g., waste
services for chemical and pharmaceutical industries, energy sector
(power plants), food and beverage industry, building and construction
applications, medical applications, aerospace applications, car repair
shops, as well as all remainder products and applications not collected
in residential household waste and municipal waste generated by
commercial activities, WEEE and ELV waste streams
Fluoropolymer end-of-life applications
Automotive
Aerospace
Electronics & semiconductors
Chemicals (CPI)
Medical & pharma
Other (e.g., professional cookware)
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Project frame
7
Waste treatment
Recycling, Energy Recovery, Landfill
Waste treatment
Recycling
Definition
Physical material processing of fluoropolymers waste into regrind and recycled granules and compound materials
Recycling of pre- and post-consumer fluoropolymer waste. Thermoplastic fluoropolymer supply for recycling primarily from industrial
applications such as semiconductor process equipment or from chemical and pharmaceutical end-of-life applications.
As most fluoropolymers (and elastomers) are not melt-processable such as thermoplastics, the term recycling in this report includes mechanical
recycling and other recycling technologies such as regrind and sintering as well as chemical recycling.
Waste incineration for energy recovery purposes in MSWI plants (municipal solid waste incineration), SRF / RDF (solid recovered fuel / refuse
derived fuel) power plants or cement kilns (e.g., rotary kilns) and hazardous waste incineration plants (e.g., for hospital waste).
The average calorific value of some FP waste fractions such as PTFE is typically lower compared to other plastics such polyolefins. However,
the usually small shares of fluoropolymers within a mixed waste fractions send to MSWI plants have no significant effect on the overall waste-
to-energy performance.
Please note, that this report does not provide detailed information about average operative incineration temperature levels. A further analysis of
existing exhaust gas treatment systems is also not part of this report.
Waste treatment on a landfill sites for the disposal of waste fractions
The EU landfill directive defines the different categories of waste (municipal waste, hazardous waste, non-hazardous waste and inert waste)
and applies to all landfills, defined as waste disposal sites for the deposit of waste onto or into land.
Typically, fluoropolymer waste is chemically inert.
Incineration for heat /
electricity utilization
(Energy recovery)
Landfill
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Project frame
8
Target companies
End-of-life fluoropolymer applications and relevant players along the waste chain
Large shredder WEEE
facilities
dismantlers
Waste
management
companies
Metal recyclers
Industrial
service
companies
Hospitals
Aircraft
dismantlers
Municipal
Internal service
waste services / maintenance
Automotive
Aerospace
Electronics &
semiconductors
Chemicals (CPI)
Medical &
pharma
Other (e.g.,
cookware)
(✓)
(✓)
(✓)
(✓)
(✓)
(✓)
(✓)
(✓)
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Main objective, key questions and targets
1
The main objective of the project was to further determine and define the main applications and products, where fluoropolymers are used and to
understand what happens to those applications at the end of their life. A correlation matrix between fluoropolymer applications and the penetration of
relevant waste streams (by mass in kt and %) was developed and the waste treatment route (recycling, energy recovery and landfill) is shown.
This report delivers an in-depth description on how and where fluoropolymer containing products and corresponding wastes are generated and what
happens to the collected fractions at the end of their life. Quantities of fluoropolymer waste are included as far as possible based on an end-of-life
fluoropolymer (and relevant fluoropolymer containing products) lifetime assessment model. This report has qualitative and quantitative character.
The main scope of the report can be summarized as follows:
Identification where fluoropolymer applications and products end up at the end of their life including re-use of processing scrap and recycling of
either pre- or post-consumer fluoropolymer waste (either mechanical, e.g., conversion into PTFE micro powders or chemical) in the EU.
Identification of major waste streams in which the fluoropolymer applications and products end up incl. total volumes in kt as well as the penetration
of fluoropolymers (in kt and %) in the EU.
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Main objective, key questions and targets
2
The report has a semi-quantitative character with additional supplemental qualitative case studies for specific waste streams and applications providing
further information about the fate of fluoropolymer-relevant applications at their end-of-life.
This report provides…
information on where the fluoropolymer applications end up at the end of their life and in which waste streams,
data about the quantities of different waste streams with a model-based estimation about the expected fluoropolymer penetration,
a general overview for the treatment of relevant waste streams and where included end-of-life fluoropolymers applications end up or are co-
treated as part of commingled fractions (e.g., metal recycling, waste incineration, landfill, etc.),
information about collection and treatment opportunities of fluoropolymer associated products in terms of circularity,
additional knowledge on the treatment of pre-consumer fluoropolymer processing waste of fluoropolymer product manufacturers.
Analysis of end-of-life
fate of fluoropolymers within…
different applications
different products
corresponding waste streams
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Methodology and data model
1
Structure of the fluoropolymer flow analysis
Identification and assessment of pre-defined fluoropolymer applications and corresponding products within the applications Automotive, Aerospace,
Electronics & semiconductors, Chemicals (CPI), Medical & pharma and Other (e.g., cookware)
Description and assessment of the end-of-life fate of different fluoropolymer associated applications and products
Model calculation of corresponding waste streams and their treatment, including fluoropolymer shares
Data model approach
Identification of major fluoropolymer-relevant products and applications in different industry segments
End-of-life analysis of fluoropolymer products based on individual EOL scenarios, e.g., by average lifetimes of fluoropolymer products and
applications
Modeling of fluoropolymer waste collection data for the main industry segments and applications considering the dated back FP market volumes for
a calculation of the total EU fluoropolymer waste in 2020 incl. continuous plausibility checks
Identification of relevant waste streams and the different waste treatment routes (recycling, incineration, landfill)
Estimation of the fluoropolymer penetration and (co-)treatment routes within the different waste streams
Discussion of preliminary results with the Fluoropolymer project group and preparation of a final model calculation and reporting
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Methodology and data model
2
Multimethodological approach
Secondary research
Comprehensive analysis of information and data
from
external databases and secondary
research sources
Conversio own databases
Analysis of existing knowledge
including data
transfer, validation and reframing from previous
reports, e.g., EU Circular Economy 2020 report or
Post-consumer fluoropolymer report 2019
Incl. reports from environmental agencies, official
Incl. analysis of existing model calculations in with
statistics and databases, fluoropolymer
regard to individual lifetime and waste collection
manufacturer datasheets, academic journals,
scenario incl. validation and reframing of existing
information from associations, etc.
knowledge together with new insights.
Analysis of data from
different information
sources, elaboration of a
The project methodology is based on a
semi-quantitative,
data model, validation
multi-methodological approach.
and reporting
Primary research
Interviews
with quantitative and qualitative
questions in Europe with fluoropolymer
product manufacturers, waste generators,
waste management companies, shredder
facilities, WEEE dismantlers, etc.
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Generally, for application and industry segment shares, average
lifetimes and fluoropolymer waste collected in different waste
streams, information from
several information sources
has
been used such as data and information from official production
and waste statistics, Conversio own reports and databases,
interviews with industry experts along the fluoropolymer value
chain as well as further secondary research sources.
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Methodology and data model
3
Data model
Where a calculation on individual fluoropolymer EOL product scenarios was insufficient, a data extrapolation was performed, e.g., for the large number of different
commercial & industrial applications.
FP products & applications
LCA model for individual FP products
EOL analysis of major FP products in different
industry segments
FP waste analysis
Alignment of dated back FP market volumes, LCA
assumptions and interview results
Topic
Interviews with fluoropolymer product manufacturers
and harmonization with existing data and calculations
Result
FP put on the EU market in 2020
FP market volumes per industry segment and
application; estimation market shares by FP types
Lifetime model for FP applications
EOL FP data model by average lifetime in years incl.
dated back FP market volumes per application
EU FP waste in 2020
FP waste volumes per waste stream and industry
segment incl. waste treatment routes
Secondary research + Primary research + Plausibility checks
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Agenda
Introduction and project frame
Management Summary
5
21
Fluoropolymer products & applications
Fluoropolymer waste
In-depth waste analysis
Circular economy approach
Appendix
27
33
44
55
60
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Management Summary I
In 2020 about 40 kt of FP materials were sold to European FP product manufacturers. The
largest share accounted for PTFE materials (~56%) followed by PVDF (~12%), FKM (~8%) and
FEP (~8%).
By view of FP product manufacturers, tubes & pipes (~15%) followed by liners (~13%), coatings
(~12%) and Seals (~11%) were the most relevant FP applications.
The most relevant industry segments were Chemicals (~29% incl. Energy), Automotive (~31%)
and Others (~21% incl. coated metals, cookware, lubricants, textiles, Food & beverage etc.).
Fluoropolymer market by industry
segments & products / applications 2020
Shares based on quantity in kt
The data for FP materials used by manufacturers (i.e., FP materials sold) in the European
market was aligned with the report* by the Wood Group on behalf of PlasticsEurope in 2022.
Based on the Wood Group report, the quantity of FP materials sold in Europe declined by
around 23% from 52 kt in 2015 to 40 kt in 2020 due to lower import volumes, the pandemic
situation, raw material price increases and data model adaptions.
In total, about 49 kt of FP raw materials were produced in the EU in 2020, making the EU a net
exporter of FP raw materials (export surplus).
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* Update of market data for the socio-economic analysis (SEA) of the European fluoropolymer industry (Wood Group UK Limited; May 2022)
EUU, Alm.del - 2022-23 (2. samling) - Supplerende svar på spørgsmål 49: Spm. om, hvilke interessenter, virksomheder mv. ministeriet har været i dialog med i forbindelse med ønsket om at indføre et forbud imod anvendelsen af PFAS, til miljøministeren, kopi til udenrigsministeren
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Management Summary II
In 2020, around 23.5 kt of FP waste were collected* via different residential as well as commercial and industrial waste streams.
Applications with typically longer lifetimes accounted for the larges share of FP materials used. Accordingly, the backdated FP volumes which were, for example, used
in a passenger car or aircraft 20 years ago were significantly lower which results in a gap between FP manufacturing and waste quantities in the same year.
In total almost 60% of
the FP manufacturing
quantities in 2020 were
collected as FP waste
in the same year.
Additional reasons for a gap between FP manufacturing quantities and collected waste
are statistical gaps of reported end-of-life vehicle figures in Europe. According to the
Heinrich Böll
Foundation’s European Mobility Atlas 2021, around 12 million cars leave
European roads, but only about half of these are handled in authorised recycling facilities
respectively are recorded by official statistics.
In addition, the EU is a net exporter of many FP based products, incl. industrial
production and processing equipment, passenger cars, aircrafts or medical and pharma
applications. The export surplus resulted in lower quantities of FP products and
applications being put on the market compared to FP products and applications being
manufactured.
Compared to the 2017 figures, where about 22.9 kt of FP waste were generated and 19.7
kt were officially collected, the amount of FP waste collected in 2020 slightly increased.
For the calculation of FP waste collected in 2020, additional new insights and an
extended research scope (e.g., through maintenance measures of transport applications)
were taken into account.
Pre-consumer process losses of FP product manufacturers accounted for around 20% or
~8 kt in 2020.
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Fluoropolymer waste in Europe 2020
* Waste generation and waste collection often slightly differ. For example if an EU end-of-life aircraft or ship is dismantled in extra-EU countries.
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Management Summary III
The most relevant waste streams for the collection of end-of-life FP applications are commercial and industrial waste streams, which are usually collected by private
waste management or industrial service companies.
Only a small proportion of FP waste is collected in residential or private waste streams, such as mixed residential waste, which is often collected on behalf of
municipal waste collection services.
Commercial and industrial waste streams
mainly cover end-of-life FP production and
processing equipment from (petro-)chemical
and pharmaceutical companies, food &
beverage producers, the semiconductor
industry or the energy sector.
Significant volumes of FP waste are also
collected in electronic waste (WEEE) or ELV
waste.
Large shredder facilities often process ELV
wrecks and larger end-of-life appliances within
the same waste stream and lighter materials
such as plastics (incl. FP) are sorted out in a
shredder-light fraction.
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Management Summary IV
In total, about 23.5 kt of FP waste were collected in 2020, which is less than 0.01% of the total waste collection (615,000 kt).
In comparison, around 29,450 kt of plastics were collected in 2020 (<5% of the total waste collection excl. mineral fractions).
Almost 84% (or 20.4 kt) of the total FP waste collected in Europe in 2020 is either (co-)incinerated or thermally destructed.
Around 3.1 kt or slightly over 13% of the total FP waste collected were sent to landfill sites.
Slightly more than 0.8 kt were collected separately for recycling and a significant proportion of this was exported for recycling, e.g. to Asian countries.
Potential circular
economy approach
for FP waste
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Fluoropolymer waste in Europe 2020
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At a glance
In 2020, around 40 kt of fluoropolymer materials were sold to EU fluoropolymer product manufacturers.
23.5 kt of fluoropolymer waste were collected, either in commingled waste streams or partly in source separated waste fractions.
Almost 84% of all fluoropolymer applications were incinerated at the end of their life in energy recovery (MSWI ~72%) or thermal destruction (metal
recycling ~12%) processes. 13% of the collected fluoropolymer waste was landfilled and around 3% was recycled.
End-of-life fluoropolymer production and processing equipment used
for different industrial segments, such as Chemical, Energy, Food &
beverage, Pharma and Semiconductor accounted for the major share
of the total fluoropolymer waste quantity collected (~13 kt).
The overall fluoropolymer penetration in all waste streams
was less than 0.01% by weight. In comparison, plastics in total
accounted for about 4.8% of the total waste collection volume
(excl. mineral fractions).
Chemical recycling of fluoropolymer waste offers the opportunity to
produce virgin-like fluoropolymer raw materials for the production of
goods and products without quality limitations. However, building robust
supply chains for large-scale and economical feasible recycling processes is one of the most important issues to be addressed in the coming years.
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EUU, Alm.del - 2022-23 (2. samling) - Supplerende svar på spørgsmål 49: Spm. om, hvilke interessenter, virksomheder mv. ministeriet har været i dialog med i forbindelse med ønsket om at indføre et forbud imod anvendelsen af PFAS, til miljøministeren, kopi til udenrigsministeren
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Agenda
Introduction and project frame
Management Summary
5
21
Fluoropolymer products & applications
Fluoropolymer waste
In-depth waste analysis
Circular economy approach
Appendix
27
33
44
55
60
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EUU, Alm.del - 2022-23 (2. samling) - Supplerende svar på spørgsmål 49: Spm. om, hvilke interessenter, virksomheder mv. ministeriet har været i dialog med i forbindelse med ønsket om at indføre et forbud imod anvendelsen af PFAS, til miljøministeren, kopi til udenrigsministeren
2698345_0027.png
Converting of fluoropolymer materials in EU in 2020
by industry segments
Fluoropolymer market by industry segments 2020
Shares based on quantity in kt
Aerospace
2%
31%
Electronics &
semiconductors
10%
Chemicals (CPI)
29%
Total 40 kt
of fluoropolymers
converted into
products by EU
converters
7%
21%
Automotive
Medical & pharma
Other
Around 12 - 13 kt of FP materials were used for the production of automobiles
and associated spare parts. Modern cars use around 0.6 up to 0.8 kg of FP
materials to cope with the tighter emission regulations and the growing
importance of sensor, communication, safety and comfort systems.
In addition, EVs use PVDF electrode binders and separator coatings in their
battery systems improving the overall battery performance and long-term
reliability of the battery system.
The chemical industry together with the petrochemical and energy industry
(incl. renewables) accounted for almost 30% of all FP products and
applications manufactured in the EU. Relevant applications are for example
liners for pipes, pumps and vessels or FP gaskets, tubing, bellows, flue gas
treatment / cooling systems and various other products.
Medical applications, such as syringes, tubing, pipes, milled & drilled lab
equipment, diaphragms or microinvasive surgery applications, such as stents,
account for around 2 - 3 kt of FP materials used for manufacturing.
Electronics & semiconductors also include electronic devices such as
smartphones, tables and notebooks incl. the associated infrastructure for long
distance communication such as antennas.
Other applications account for around 7 - 8 kt of FP materials used in 2020,
incl. ~5 kt for coated metals incl. consumer cookware (>2 kt).
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2698345_0028.png
Converting of fluoropolymer materials in EU in 2020
by products & applications
Fluoropolymer market by products & applications 2020
Shares based on quantity in kt
Pumps Wire conduits & cables
Seals (O rings, gaskets)
Electrolysis cells / Batteries
5%
11%
Bearings
2%
4%
1%
Other
Hoses
9%
(incl. Fluoroelastomers)
8%
The split into different FP products & applications was based on survey results
with more than 20 different FP product manufacturers in the EU.
The three FP application and product categories Tubes & pipes (100% FP
materials), liners (e.g., for corrosion prevention of steel pipes) and seals (incl.
O rings and gaskets accounted for around 40% (or 15 - 16 kt) of the total FP
materials processed in the EU in 2020. Coatings for coils / sheet metal, pans,
pots, etc. account for about 5 kt.
The category textiles & fabrics includes wearable FP (membrane) materials for
outdoor clothing as well as protective clothing for professional tasks such as
firefighter coats. This category also includes glass coated fabrics used for
architectural and industrial applications.
The category Other includes, for example, other additives, compounding with
engineering polymers, as well as various other smaller applications such as
bellows, membranes, etc.
Tubes & pipes
15%
(100% plastic)
Total 40 kt
of fluoropolymers
converted into
products by EU
converters
3%
Lubricants & greases
12%
Coatings
13%
Liners
8%
6%
3%
Milled & drilled parts
Films & tapes
Textiles & fabrics
Lubricants & greases include dry FLP lubricants or FP additives for lubricants /
greases.
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Converting of fluoropolymer materials in EU in 2020
by FP types
Fluoropolymer market by polymer & elastomer types 2020
Shares based on quantity in kt
Other
ETFE
5%
PFA
3%
6%
PCTFE
2%
Around 50 - 60% of the EU 2020 FP market accounted for PTFE based
products & applications for different industry segments.
PTFE
56%
Total 40 kt
of fluoropolymers
converted into
products by EU
converters
8%
8%
FEP
12%
PVDF
PTFE is a not melt-processable thermoplastic resin with duroplast
characteristics and therefore not suitable for mechanical recycling processes,
which are usually used for thermoplastic materials such as for example
polyolefins. Fluoroelastomers, such as FKM, are also not suitable for
mechanical plastic recycling processes.
Chemical recycling provides an opportunity to recycle pre- and post-consumer
PTFE materials into a virgin material qualities.
Opened in 2015, a chemical pilot recycling plant located in Burgkirchen
(Germany) by 3M (former Dyneon) shows that the recycling of non-melt-
processable FP is possible. The existing plant is capable of recycling up to
500 t of FP materials per year.
In addition, pre- and post-consumer PTFE is for example thermo-mechanically
recycled into micro-powders.
FP materials, such as PVDF or PFA, are technically suitable for conventional
mechanical recycling processes.
29
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2698345_0030.png
Fluoropolymers quantities by industry segment in the EU in 2020
long lifetimes, export surplus and
export of used cars and electronics
12.5 kt
Export surplus of new cars
and associated
parts. In general low service requirements of FP
affiliated parts. Typical age of an ELV around 12
years + approx. 60 g of FP materials replaced
via maintenance.
Export surplus of used and
deregistered cars
to countries outside the EU.
0.8 kt
Automotive
Aerospace
Electronics &
semiconductors
FP products manufactured by EU companies are mainly used for
applications that have longer lifetimes and often for products that
have high export surplus rates.
Compared to other materials such as polyolefins or PET, which
are aften used in short-life (<1 year) packaging applications, FP
materials are predominantly used for technical applications.
Export surplus of new aircrafts
and associated parts. D-check maintenance of commercial
aircrafts in use every 12 years incl. exchange of (at least partly) FP fuel and hydraulic system parts.
4 kt
Usually
lifetimes of 10 - 20 years
for processing equipment. Lifetimes of consumer
electronics between 3 - 10 years.
Export surplus of used electronics
outside the EU.
Average
lifetimes
of liners and other affiliated FP products used for
chemical production processes between
10 - 20 years.
Range from
1 year, e.g., for high-purity applications and very aggressive
substances and demanding production environments
up to 50
years
for tubes and pipes used for less aggressive substances and
less demanding production environments.
Possibility to improve
recycling,
e.g., of liners previously used for corrosion prevention.
Chemicals (CPI)
11.5 kt
Medical & pharma
Other
2.8 kt
Lifetimes of ,e.g., PTFE coated pots and pans on average
4 - 5 years other transport applications 15 - 25 years,
architectural fabrics up to 20 years, processing equipment in
the food and beverage industry 5 - 15 years, etc.
40 kt of FP products & applications
manufactured in the EU in 2020
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Fluoropolymer waste in Europe 2020
8.4 kt
Average
lifetimes
of FP pharma processing
equipment of around
5 - 15 years.
Medical
FP applications range from short life single-
use products, e.g., sterile syringe filters up to
several decades for PTFE covered stents.
30
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2698345_0031.png
Fluoropolymers quantities 2015 vs. 2020
FP raw materials sold to the EU FP product manufacturers
export and import adjusted
Sector
Chemical & Power
Food & Pharma
Electronics
2020 FP quantity
sold in the EU in kt
10 - 12
2
3.5
2015 FP quantity
sold in the EU in kt
16.5
3
3.5
The data for the FP materials used by manufacturers (i.e., FP materials sold)
in the EU market was aligned with the Wood Group report “Update of market
data for the socio-economic analysis (SEA) of the European fluoropolymer
industry” on behalf of
PlasticsEurope in 2022.
Transport
Renewable energy
Cookware
Medical
Textiles & architecture
Other
Total
2022-07-19
15.5
0.5
2
0.5
1.5
3
40
Fluoropolymer waste in Europe 2020
18.5
0.5
3.5
1.5
3
2
52
The authors noted that the data presented in their latest report covers a high
market share (i.e., higher number of participants) and was not extrapolated
compared to 2015 data, which was extrapolated.
According to the report the major reasons for the decline from 52 kt of FP
materials sold in 2015 compared to 40 kt in 2020 were a result of lower import
quantities and the overall production drop in various industries due to the
pandemic situation. The increase of FP raw material prices was also stated as
a reason for the lower FP quantities in 2020.
The data used in this report was aligned to the data published on behalf of
PlasticsEurope, but slightly adapted to a different industry segmentation focus.
In total, about 49 kt of FP raw materials were produced in the EU in 2020,
making the EU a net exporter of FP raw materials (export surplus).
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Agenda
Introduction and project frame
Management Summary
5
21
Fluoropolymer products & applications
Fluoropolymer waste
In-depth waste analysis
Circular economy approach
Appendix
27
33
44
55
60
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2698345_0033.png
Fluoropolymers quantities by industry segment in kt
differences between FP products
manufactured and FP waste collected in the EU in 2020
FP quantities manufactured vs. FP waste collected
Automotive
Aerospace
Electronics &
semiconductors
12.5 kt
The differences between FP manufactured products & applications
and FP waste collected in different waste streams in the same years
is a result different measures:
0.8 kt
export-import balance of manufactured products,
LCA (average lifetimes) of different FP associated products
and applications,
dated-back FP volumes in total an per industry segment over
the last 30 years,
maintenance measures of FP associated products and
applications in use,
export-import balance of used products (e.g., cars exported for
second use outside the EU),
official waste statistics (i.e., waste collected)
often not a
100% coverage of all waste arisings (i.e., waste generated)
incl. statistical gaps, e.g., unknown whereabouts of ELVs, etc.,
4 kt
3.5 kt
0.3 kt
Chemicals (CPI)
11.5 kt
Medical & pharma
Other
2.8 kt
In total almost 60% of
the FP manufacturing
quantities in 2020 were
collected as FP waste
in the same year.
2.7 kt
9.4 kt
2.3 kt
5.3 kt
8.4 kt
continuous adjustments through additional information by
waste management companies, waste producers and existing
Conversio internal databases and reports.
40 kt of FP products & applications
manufactured in the EU in 2020
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Fluoropolymer waste in Europe 2020
23.5 kt of FP waste
collected in the EU in 2020
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2698345_0034.png
FP waste collection by industry segment in the EU in 2020
Collected FP waste by industry segment in the EU in 2020
Industry segment
Automotive
Collected FP waste
in kt
3.5
In total, around 23.5 kt of FP waste were collected in different industry
segments in the EU in 2020.
Aerospace
Electronics & semiconductors
Chemicals (CPI)
Medical & pharma
Other
0.3
2.7
9.4
2.3
5.3
In 2017 around 22.9 kt of FP waste were generated and 19.7 kt were officially
collected.
For the calculation of FP waste collected, additional new insights and an
extended research scope (e.g., through maintenance measures of transport
applications) were taken into account.
Statistical gaps between officially collected waste and waste generated still
exist and will be described in more detail in the individual case studies.
One example is the number of officially treated end-of-life vehicles:
According to the Heinrich Böll
Foundation’s European Mobility Atlas 2021,
around 12 million cars leave European roads due to total loss after an
accident, economic write-off, non-compliance with new safety or emissions
standards or a change in design preferences
but only around half of them
are handled in authorised recycling facilities respectively are recorded by
official statistics.
Total
23.5
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2698345_0035.png
Waste collection by waste stream in the EU in 2020
total, plastics, fluoropolymers
Collected FP waste by waste stream in the EU in 2020
FP relevant waste stream
Residential household waste and municipal waste
generated by commercial activities
Electronic waste collection (WEEE)
ELV incl. auto-shredder residue (ASR)
Commercial & industrial
(various streams; usually commingled)
Total
Other waste streams not further analysed / relevant
e.g., separate collection of LWP waste or separate collection
of commercial packaging waste
Total waste collected
in kt
148,500
5,000
10,000
400,000
563,500
Thereof plastics
in kt
10,300
1,170
1,190
4,700
17,360
Share
in %
6.9
23.4
11.9
1.2
3.1
Thereof FP
in kt
2.2
2.3
3.0
15.1
23.5
Share
in %
<0.01
0.05
0.03
<0.01
<0.01
51,500
12,090
23.5
<1 kt
<0.01
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Fluoropolymer waste in Europe 2020
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EUU, Alm.del - 2022-23 (2. samling) - Supplerende svar på spørgsmål 49: Spm. om, hvilke interessenter, virksomheder mv. ministeriet har været i dialog med i forbindelse med ønsket om at indføre et forbud imod anvendelsen af PFAS, til miljøministeren, kopi til udenrigsministeren
2698345_0036.png
Graphical illustration of FP waste collected by industry segment and waste stream
Total: 23.5 kt FP waste collected
Industry segment
Automotive
Aerospace
Electronics &
semiconductors
Chemicals (CPI)
Medical & pharma
Other
Waste stream*
Residential household
Electronic waste collection
waste and municipal waste
(WEEE)
generated by commercial
activities
ELV incl. auto-shredder
residue (ASR)
Commercial & industrial
*excl. ‘Other waste streams not further analysed / relevant’
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2698345_0037.png
Waste stream flow chart
collection, treatment and utilization
Collection
Collected
waste
Recovery
Not recovered /
untreated
Landfill
Treatment
Utilization
Mechanical
recycling
Dissolution/
Purification
Chemical
recycling
Recyclates
1)
Recovered
by recovering operations
Recycling
Household and household-like
waste streams
Mixed waste streams
Separately collected waste
streams
Commercial and industrial waste
streams
Mixed waste streams
Separately collected waste
streams
Energy
recovery
Monomers
used for polymerization
Other base chemicals
2)
used for processing and
polymerization
Alternative fuel
RDF / SRF
Incineration with
energy
recovery
3)
1) Including mixed plastics
2) Other base chemicals without polymerization can be utilized
as feedstock for other purposes or for energy recovery
3) Incineration with „Energy-from-waste (EfW)“
Energy
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2698345_0038.png
Circular economy illustration for fluoropolymers
Fluorspar / calcium fluoride (CaF2) is a limited resource. The
circularity of FP materials could offer a way to cope with the growing
market demand for FP materials and the tight supply situation
(import dependency) for relevant secondary raw materials.
Export of FP
products
FP conversion
Mechanical recycling of FP
Melt-processable FP such as
PVDF or PFA
Re-grind and processing of not
melt-processable FP materials
into powders etc.
Export of FP raw
materials
Import of FP raw
materials
FP production
Import of FP
products
FP consumption
FP
products
in use
renewable and fossil
Feedstock
(Pre-)sorting
Export of sorted (FP)
waste for recycling
2022-07-19
Fluoropolymer waste in Europe 2020
v
v
Chemical recycling of FP
3M recycling plant for not melt-
processable FP materials
Virgin-like raw material quality for
the manufacturing of new FP
products & applications
Export of
recycled FP
FP recycling
Import of sorted (FP)
waste for recycling
Import of collected
waste for sorting
Waste collection
Export of
collected waste
Landfill
Energy recovery
MSWI / RDF / SRF
38
EUU, Alm.del - 2022-23 (2. samling) - Supplerende svar på spørgsmål 49: Spm. om, hvilke interessenter, virksomheder mv. ministeriet har været i dialog med i forbindelse med ønsket om at indføre et forbud imod anvendelsen af PFAS, til miljøministeren, kopi til udenrigsministeren
2698345_0039.png
Treatment of FP waste by industry segment in the EU in 2020
Industry segment
Automotive
Aerospace
Electronics & semiconductors
Chemicals (CPI)
Medical & pharma
Other
Total
Collected FP
waste
in kt
3.5
0.3
2.7
9.4
2.3
5.3
23.5
Energy
recovery
in kt
2.50
0.24
2.15
7.10
2.00
2.90
16.89
Share
in %
71.4
80.0
79.6
75.5
87.0
54.7
71.9
Landfill
in kt
0.80
0.04
0.25
1.05
0.15
0.80
3.09
Share
in %
22.9
13.3
9.3
11.2
6.5
15.1
13
Metal
recycling
in kt
0.20
0.01
0.15
0.90
0.05
1.40
2.71
Share
in %
5.7
3.3
5.6
9.6
2.2
26.4
12
FP recycling
in kt
-
0.01
0.15
0.35
0.10
0.20
0.81
Share
in %
-
3.3
5.6
3.7
4.3
3.8
3.4
2022-07-19
Fluoropolymer waste in Europe 2020
39
EUU, Alm.del - 2022-23 (2. samling) - Supplerende svar på spørgsmål 49: Spm. om, hvilke interessenter, virksomheder mv. ministeriet har været i dialog med i forbindelse med ønsket om at indføre et forbud imod anvendelsen af PFAS, til miljøministeren, kopi til udenrigsministeren
2698345_0040.png
(Co-)treatment of FP waste and associated waste streams
FP relevant waste stream
Residential household waste
and municipal waste generated
by commercial activities
Electronic waste collection
(WEEE)
ELV incl. auto-shredder residue
(ASR)
Commercial & industrial
(various streams; usually
commingled)
Total
Other waste streams not further
analysed / relevant
2022-07-19
Collected FP
waste
in kt
Energy
recovery
in kt
Share
in %
Landfill
in kt
Share
in %
Metal
recycling
in kt
Share
in %
FP recycling
in kt
Share
in %
2.2
2.3
3.0
15.1
23.5
0.9
1.35
1.7
2.1
11.04
16.89
0.7
61.4
0.85
0.4
0.7
0.99
3.09
0.15
38.6
-
0.15
0.2
2.31
2.71
0.05
-
-
0.05
-
0.76
0.81
-
-
73.9
70.0
17.4
23.3
6.5
6.7
2.2
-
73.1
6.6
15.3
5.0
71.9
77.8
13.1
16.7
11.5
5.6
3.4
-
40
Fluoropolymer waste in Europe 2020
EUU, Alm.del - 2022-23 (2. samling) - Supplerende svar på spørgsmål 49: Spm. om, hvilke interessenter, virksomheder mv. ministeriet har været i dialog med i forbindelse med ønsket om at indføre et forbud imod anvendelsen af PFAS, til miljøministeren, kopi til udenrigsministeren
2698345_0041.png
FP waste treatment routes post-consumer FP waste and treatment in the EU in 2020
(Co-)treatment route of post-consumer FP waste in the EU in 2020
FP waste collected (post-consumer)
23.5 kt (100%)
Most FP are (co-)incinerated in MSWI plants or
dedicated hazardous waste incineration plants
which are for example treating different wastes
from chemical waste producers.
The total penetration of FP waste by mass is in
mixed or commingled waste streams typically very
low (<0.01%).
FP waste from commercial and industrial waste
producers with is either pre-sorted or results
directly from dismantling operations is also mainly
incinerated for energy recovery.
Some fractions of pre-sorted PF waste are send to
recycling, either to domestic recyclers or exported
for recycling in intra- and extra-EU countries.
Other recycling includes for example re-grinding
and sintering as well as chemical recycling of FP
materials.
41
Recovery processes
20.4 kt (86.9%)
Disposal
3.1 kt (13.1%)
Incineration / thermal destruction
19.6 kt (~83.5%)
Recycling
0.81 kt (3.4%)
Landfill
3.1 kt (13.1%)
Energy recovery MSWI / RDF / SRF
16.9 kt (~72%)
Metal recycling
2.7 kt (11.5%)
Other
recycling
>0.7 kt (<3%)
Thermoplast.
recycling
<0.1 kt (<0.5%)
2022-07-19
Fluoropolymer waste in Europe 2020
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2698345_0042.png
Pre-consumer processing losses during the manufacturing of FP products and applications
FP raw materials sold to EU FP product manufacturers
FP product manufacturing in the EU
The processing of FP materials such as the machining of PTFE rods and
cubes for the manufacturing of various milled and drilled parts results pre-
consumer FP processing losses.
Due to high costs of FP raw materials, the resulting FP processing losses like
shavings, off-cuts or samples are of high value for other companies.
In total, EU FP product manufactures have process losses of around 20%
which means that roughly 8 kt of FP process losses were generated in the EU
in 2020.
Pre-consumer FP
processing losses
during manufacturing
2022-07-19
Final FP products and
applications
Around 20 - 25% of the FP product manufacturers stated to have own internal
re-processing steps for their process losses. 30 - 35% stated to send their pre-
consumer FP waste to external material re-processing companies and 15%
exported their pre-consumer wastes to other companies inside the EU.
5 - 10% stated that their FP processing losses are exported outside the EU for
re-processing, e.g., to Asian countries. 5% confirmed that they do not know
what happens to their process losses. These companies usually (full-service)
contracts with waste management companies. 15% of all FP process losses
are not recycled and predominantly (co-)incinerated in MSWI plants or
dedicated hazardous waste incineration plants.
42
Fluoropolymer waste in Europe 2020
EUU, Alm.del - 2022-23 (2. samling) - Supplerende svar på spørgsmål 49: Spm. om, hvilke interessenter, virksomheder mv. ministeriet har været i dialog med i forbindelse med ønsket om at indføre et forbud imod anvendelsen af PFAS, til miljøministeren, kopi til udenrigsministeren
2698345_0043.png
Agenda
Introduction and project frame
Management Summary
5
21
Fluoropolymer products & applications
Fluoropolymer waste
In-depth waste analysis
Circular economy approach
Appendix
27
33
44
55
60
2022-07-19
Fluoropolymer waste in Europe 2020
43
EUU, Alm.del - 2022-23 (2. samling) - Supplerende svar på spørgsmål 49: Spm. om, hvilke interessenter, virksomheder mv. ministeriet har været i dialog med i forbindelse med ønsket om at indføre et forbud imod anvendelsen af PFAS, til miljøministeren, kopi til udenrigsministeren
2698345_0044.png
Case study ELV
1
Produced new vehicles and collected ELVs with the associated FP volumes
According to the European Mobility Atlas 2021 by Heinrich Böll Foundation
around 12 million cars leave European roads due to total loss after an
accident, economic write-off, non-compliance with new safety or emissions
standards or a change in design preferences. According the report only
around half of them are handled in authorised recycling facilities.
Using latest Eurostat data for 2019, around 6.9 million ELVs were statistically
covered for EU27 + 1.6 million from the UK.
For 2020, it was assumed that around 8.6 - 8.7 million ELVs were officially
collected in the EU27+3 countries which means that there are still statistical
gaps between the total number of ELV arisings and the number of ELVs
officially collected.
The FP share in ELVs (usually around 12 years old) is significantly lower
compared to modern cars. It was assumed that the average FP content
ranged between 0.35 - 0.4 kg per ELV which accounted for around 3 - 3.5 kt
of FP materials collected in total in the EU27+3 countries.
Additional 0.3 kt of FP materials were collected as part of end-of life vehicles
>3.5 tonnes, trucks and busses, motorcycles or construction and agricultural
(constr. & agricult.) vehicles.
Most of the collected ELVs undergo a dismantling process where valuable
parts (e.g., front and rear lights) or applications with safety issues such as
airbags and liquids are removed before the further treatment process.
2022-07-19
Fluoropolymer waste in Europe 2020
Fluoropolymers by average weight per new vehicle
Cars & LCV
Trucks & buses
Weight
0.7 kg
1.2 kg
EU27+3 production volume for new vehicles 2020
Number
13.7 million
0.30 million
Motorcycles
0.1 kg
Constr. & Agricult.
1 kg
0.95 million
0.3 million
EU27+3 associated FP volume used in new vehicles 2020
[estimated]
Total weight
9.6 kt
0.36 kt
0.10 kt
0.30 kt
Fluoropolymers by average weight per ELV
Cars & LCV
Trucks & buses
Weight
0.37 kg
0.8 kg
EU27+3 total number of collected ELVs 2020
Number
8.65 million [est.]
0.16 million
Motorcycles
0.1 kg
Constr. & Agricult.
0.7 kg
0.8 million
0.12 million
EU27+3 associated FP waste collected in ELVs 2020
[estimated]
Total weight
3.2 kt
0.128 kt
0.08 kt
0.08 kt
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EUU, Alm.del - 2022-23 (2. samling) - Supplerende svar på spørgsmål 49: Spm. om, hvilke interessenter, virksomheder mv. ministeriet har været i dialog med i forbindelse med ønsket om at indføre et forbud imod anvendelsen af PFAS, til miljøministeren, kopi til udenrigsministeren
2698345_0045.png
Case study ELV
2
Typical ELV processing route
ELVs generated
Waste management
Recovery processes
Official ELV treatment
Unofficial ELV
treatment / Export
Dismantling
ELV collection center
Reuse
Recycling
Thermoplastic
recycling
Other recycling
Shredding
Incineration processes
Metal recycling
Disposal
Landfill
Energy recovery
MSWI / RDF / SRF
After ELV collection by registered ELV collection centres, ELVs are
dismantled and valuable reusable parts or critical applications such as
airbags and liquids, are removed.
The stripped (and compacted) ELV wrack is then shredded. Shredding
facilities often shred ELV wracks together with large appliances. After
shredding post-processing and separation processes focus on the recovery
of metal fractions.
EOL FP parts are usually co-treated with metal fractions (metal recycling
and thermal destruction of FP materials) or incinerated in MSWI respectively
RDF / SRF incineration plants as part of a shredder-light fraction (SLF).
The post-processing of the SLF can differ. Most shredder facilities have
additional recovery steps for the recovery of metals. But only a few plants in
Europe focus on the recovery of plastic fractions such as PP or other
plastics. Small shares (<0.1%) of FP might end up in plastic fractions sorted
for recycling, but the major share (almost 80%) is going into incineration
processes and around 20% end up in landfills.
Lambda sensors are either dismantled separately (recycling of metal- or
ceramic-based catalytic converters with focus on the recovery of platin,
palladium and rhodium) or shredded together with part of the exhaust
system. The attached wire, incl. the FP insulation of Lambda sensors, is
often cut off and collected separately for cable recycling. The FP insulation
is removed and mainly incinerated with energy recovery.
45
2022-07-19
Fluoropolymer waste in Europe 2020
EUU, Alm.del - 2022-23 (2. samling) - Supplerende svar på spørgsmål 49: Spm. om, hvilke interessenter, virksomheder mv. ministeriet har været i dialog med i forbindelse med ønsket om at indføre et forbud imod anvendelsen af PFAS, til miljøministeren, kopi til udenrigsministeren
2698345_0046.png
Case study ELV
3
ELV treatment in Germany, France, Italy and UK
End-of-life vehicles collected and treated in selected European countries
Sources: Eurostat data 2019, individual ELV country reports by
environmental agencies or ELV systems 2019 and 2020, Circular
Economy of Plastics 2020 in EU27+3 (Conversio), own model
calculations
Number of ELVs collected
Total recycling & reuse rate
Total plastics quantity
Recycling rate of plastics
Incineration rate of plastics
Landfill / disposal rate of plastics
Thereof FP quantity
Incineration / thermal destruction rate of FP
Landfill / disposal rate of FP
2022-07-19
Fluoropolymer waste in Europe 2020
0.46 million
(export surplus of used cars)
1.6 million
87.1%
160 kt
41%
(based on figures by Ademe)
27%
32%
0.56 kt
>80%
<20%
1.1 million
84.2%
139 kt
10%
10%
80%
0.39 kt
>50%
<50%
1.6 million (est.)
85% (est.)
273 kt
15%
55%
30%
0.56 kt
>60%
<40%
46
86.9%
67 kt
25%
69%
6%
0.16 kt
>95%
<5%
EUU, Alm.del - 2022-23 (2. samling) - Supplerende svar på spørgsmål 49: Spm. om, hvilke interessenter, virksomheder mv. ministeriet har været i dialog med i forbindelse med ønsket om at indføre et forbud imod anvendelsen af PFAS, til miljøministeren, kopi til udenrigsministeren
2698345_0047.png
Case study Aerospace
Fluoropolymers by weight per average new aircraft
Average
Weight
120 kg
EU27+3 production volume for new aircrafts 2020
Number
566 (Airbus figures, 611 in 2021)
According the Centre for Aviation (CAPA) statistics, around 7,500 commercial aircrafts are in service
by Western and Central + Eastern European airlines.
In Europe, each year about 250 - 300 commercial aircrafts reach their end of service life. Thereof
approx. 180 - 220 aircrafts remain in Europe for further dismantling and recycling operations.
Commercial aircrafts are also exported to extra-EU countries for reuse. In addition, more than 300
aircrafts are stored in large open spaces either for reactivation or for spare parts supply.
The Aircraft Fleet Recycling Association (AFRA) estimated that around 15,000 aircrafts will retire in
the next two decades worldwide incl. around 2,000 - 3,000 aircrafts in Europe.
The French company Tarmac Aerosave has three sites where up to 280 aircrafts can be stored for
longer periods. Over the past years, the company has recycled over 300 aircrafts (75% of all Airbus
A340 aircrafts worldwide). Additional aircraft dismantlers and recyclers in Europe are, for instance,
ecocube (UK) with focus on aircraft EOL treatment (overall market share >40% in Europe and ~20%
worldwide), AELS with >75 aircrafts recycled since business start (Netherlands), Air Salvage
International (UK), Roth International (Germany / Czechia), Cronimet (Germany) and JAS Jet Aircraft
Services (Netherlands).
The focus of aircraft dismantlers and recyclers is to extract valuable and reusable parts as well as
recovery of metal fractions such as skeleton and cladding. Non-recyclable materials are mainly
incinerated for energy recovery operations. Only a small share of plastics, incl. a small share FP
materials, is landfilled, e.g., in the UK or in France.
2022-07-19
Fluoropolymer waste in Europe 2020
EU27+3 associated FP volume used in new aircrafts 2020
[est.]
Total weight
68 tonnes (excl. 10 - 15 kt sold in Boeing aircr.)
Fluoropolymers by average weight per end of life aircraft
Average
Weight
100 kg
EU27+3 total number of EOL aircrafts 2020
Number
200
EU27+3 associated FP waste collected in EOL aircrafts 2020
[est.]
Total weight
20 tonnes
47
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2698345_0048.png
Case study WEEE
1
WEEE management and protentional FP circularity approaches for end-of-life electronic & semiconductor production and processing equipment
In the most European countries WEEE management systems have been
successfully established for the collection, categorizing, dismantling and
treatment of WEEE.
Despite the success of these dedicated WEEE management systems which
provide high market coverage of the generated electronic waste in many
countries, there is still a lot of mismanagement of electronic waste even in
wealthy industrial countries. Illegal exports of electronic waste (often
categorized as ‘used electronics’) to countries with improper recycling
environments is one of the issues that should be addressed by EU
legislators in the coming years.
The domestic WEEE management in countries such as Germany, France,
Italy or the UK, is mostly safe if done properly. Most WEEE arising is
covered by dedicated WEEE streams. Additional volumes are collected, for
example, through residential waste streams and a small share through
mixed commercial and industrial waste streams. The major share of end-of-
life electronics which are not routed for recycling is going into waste
incineration.
There are some WEEE recovery operations established for obtaining
recyclable plastic fractions, incl. ABS, PE-HD, or PS. The recovery of FP
materials is more or less limited to the recycling of production and
processing equipment, e.g., FP piping for ultra-pure water / solvent supply.
Fluoropolymer waste in Europe 2020
48
The WEEE collection does not cover information about associated
production and processing equipment, e.g., FP materials used
semiconductor or chip manufacturing plants. These material streams are
usually collected as part of commercial and industrial waste streams either
on behalf of specialized service companies or larger waste management
companies.
A circularity approach for end-of-life FP materials should be directly
addressed with electronic & semiconductor manufacturers respectively
users of FP production and processing equipment. Closed-loop recycling
systems will only be functional, if chip manufacturers such as Semikron
(Germany), Diodes Incorporated (UK), GlobalFoundries (Germany),
Nexperia (Germany), STMicroelectronics (France and Italy), Analog
Devices (Ireland), TDK - Micronas (Germany), X-FAB (Germany), etc., will
be involved. The overall FP volumes that can be recovered from end-of-life
production and processing equipment will probably be relatively small, but
it’s one step closer towards the circularity of FP materials.
2022-07-19
EUU, Alm.del - 2022-23 (2. samling) - Supplerende svar på spørgsmål 49: Spm. om, hvilke interessenter, virksomheder mv. ministeriet har været i dialog med i forbindelse med ønsket om at indføre et forbud imod anvendelsen af PFAS, til miljøministeren, kopi til udenrigsministeren
2698345_0049.png
Case study WEEE
2
WEEE treatment in Germany, France, Italy and UK
End-of-life vehicles collected and treated in selected European countries
Sources: Eurostat data 2019, individual WEEE country reports by
environmental agencies and WEEE systems, Circular Economy of
Plastics 2020 in EU27+3 (Conversio), own model calculations
WEEE systems
Collection rate of WEEE systems
Total WEEE collected
Thereof plastics
Recycling rate of plastics
None, but Stiftung EAR
(central monitoring of WEEE)
Major two players are
Ecosystem and Ecologic
60 - 70%
855 kt
160 kt
59%
(based on figures by Ademe)
13 non-profit WEEE
collection systems
40 - 50%
365 kt
85 kt
23%
Around 25 - 30 WEEE
collection systems
40 - 60%
680 kt
135 kt
44%
n.a.
(60 - 70% collection rate)
1,030 kt
240 kt
28%
Incineration rate of plastics
Landfill / disposal rate of plastics
Thereof FP quantity
Incineration / thermal destruction rate of FP
Landfill / disposal rate of FP
2022-07-19
Fluoropolymer waste in Europe 2020
72%
<1%
0.47 kt
>99%
<1%
28%
13%
0.39 kt
>85%
<15%
46%
31%
0.17 kt
>70%
<30%
47%
9%
0.31 kt
>90%
<10%
49
EUU, Alm.del - 2022-23 (2. samling) - Supplerende svar på spørgsmål 49: Spm. om, hvilke interessenter, virksomheder mv. ministeriet har været i dialog med i forbindelse med ønsket om at indføre et forbud imod anvendelsen af PFAS, til miljøministeren, kopi til udenrigsministeren
2698345_0050.png
Case study industrial processes
Chemical, Energy, Food & beverage, Pharma, Semiconductor 1
The Chemical industry is using FP materials for many different applications,
mainly for corrosive substances or environment with higher temperature
levels.
After a certain period of time these FP applications need to be dismantled
and replaced to keep downtimes of production processes and risk of
malfunctions as low as possible.
Average lifetimes of liners and other affiliated FP products used for
chemical production processes range between 10 and 20 years. Lifetimes
can be as low as 1 year, e.g., for high-purity applications and very
aggressive substances and demanding production environments and can
go up to 50 years for (thicker) tubes and pipes used for less aggressive
substances in less demanding production environments.
For the replacement of FP applications used in production and processing
equipment different practices are common. Either internal maintenance
service departments (often contracted third-party companies on site) are
responsible or external (and specialized) service companies provide
services on request. A combination of both practices on one site is also
possible.
After dismantling end-of-life pipes, valves, pumps, tanks, etc., (incl. FP
liners) or PF tubes, pipes, hoses, seals, filters, etc., are collected as waste
and mainly separated on site for further waste treatment.
Fluoropolymer waste in Europe 2020
50
Steel pipes incl. FP liners are usually collected for metal recycling. Some
companies extract the FP content for further processing or to simply
increase the average recyclable metal content which is then sold to metal
recycling companies.
Most of the FP materials from chemical industry applications are usually
collected (separately) by private waste management companies for waste
incineration, either in MSWI or hazardous waste incineration plants. Smaller
FP quantities are also collected in commingled (mixed) waste fractions
which usually are also send to waste incineration processes.
Within the power industry segment, larger volumes of FP are, for example,
collected from flue gas lining and piping with an average lifetime/
replacement frequency of about 10 to 15 years, for instance, in coal-fired
power plants as well as in other processes where industrial flue gas coolers
are used. Hereby also larger volumes of pre-sorted
and ‘clean’ FP material
streams can be obtained, e.g., for chemical recycling processes.
2022-07-19
EUU, Alm.del - 2022-23 (2. samling) - Supplerende svar på spørgsmål 49: Spm. om, hvilke interessenter, virksomheder mv. ministeriet har været i dialog med i forbindelse med ønsket om at indføre et forbud imod anvendelsen af PFAS, til miljøministeren, kopi til udenrigsministeren
2698345_0051.png
Case study industrial processes
Chemical, Energy, Food & beverage, Pharma, Semiconductor 2
Europe is one of the largest chemical production location in the world.
Companies such as BASF, DuPont, Ineos, LyodellBasell, Air Liquide, Linde,
Evonik, Covestro, TotalEnergies, Bayer, etc., are only a couple of exemplary
users of FP production and processing equipment as well as possible
contributors to a potential FP circularity model.
In addition, a cooperation between waste service companies and larger
chemical parks with many different companies on site could also contribute
to substantial quantities of recyclable FP materials.
Concerns were raised, e.g., for materials that have previously been used to
produce drugs or specific production aids.
Besides all concerns, end-of-life industrial production and processing
equipment offers the best opportunity to collect significant volumes of
recyclable FP materials. The post-sorting of commingled waste streams to
obtain FP materials for recycling is not an option as the overall penetration
of FP is too small (often <0.01% by total mass). The industry should focus
on pre-sorted material streams such extracted FP pipe liners or FP tubing
and piping to create a robust circularity model for end-of-life FP waste.
Some users of FP production and processing equipment stated concerns
related to product safety issues that might occur for some of the FP material
Circular economy approaches for FP materials should be targeted for
equipment that has previously been used for hazardous substances such
Chemical, Energy, Pharma and Semiconductor production and processing
as aggressive chemical media, that might lead to health and safety issues.
equipment as these industry segments account for significant volumes of
Accordingly, companies often require third party waste management
FP waste collected.
companies or service providers to treat their end-of-life
EU27+3 Fluoropolymers utilized for different production and processing applications 2020
materials as safely as possible (i.e., hazardous
Chemical
Energy
Food & beverage
Pharma
Semiconductor
Total
waste incineration).
Another issue was raised by Pharmaceutical companies.
Due to patent and legal requirements these companies
could restrict the recycling opportunities of end-of-life FP
production and processing equipment.
Fluoropolymer waste in Europe 2020
FP quantity
9.5 kt
2.0 kt
1.2 kt
1.6 kt
1.7 kt
16.0 kt
EU 27+3 Fluoropolymer waste collected 2020
[estimated]
FP quantity
7.6 kt
1.8 kt
0.9 kt
1.2 kt
1.5 kt
13.0 kt
2022-07-19
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EUU, Alm.del - 2022-23 (2. samling) - Supplerende svar på spørgsmål 49: Spm. om, hvilke interessenter, virksomheder mv. ministeriet har været i dialog med i forbindelse med ønsket om at indføre et forbud imod anvendelsen af PFAS, til miljøministeren, kopi til udenrigsministeren
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Case study industrial processes
Chemical, Energy, Food & beverage, Pharma, Semiconductor 3
Commercial & industrial waste treatment in Germany, France, Italy and UK
Commercial & industrial (mixed) waste collected and treated in selected European countries
Sources: Individual country reports by environmental agencies,
Circular Economy of Plastics 2020 in EU27+3 (Conversio),
own model calculations
Waste separation
Total C&I mixed waste collected
Thereof plastics
Recycling rate of plastics
Incineration rate of plastics
Landfill / disposal rate of plastics
Thereof FP quantity
Incineration / thermal destruction rate of FP
Landfill / disposal rate of FP
2022-07-19
Fluoropolymer waste in Europe 2020
Extended source / on site
separation into different fractions
Limited source / on site
separation into different fractions
Limited (Central/South) to
extended (North) source / on site
separation into different fractions
Limited source / on site
separation into different fractions
54,000 kt
1,010 kt
26%
73%
1%
2.7 kt
>99%
<1%
55,000 kt
580 kt
7%
46%
47%
2.0 kt
>80%
<20%
48,000 kt
560 kt
10%
43%
47%
1.3 kt
>80%
<20%
21,000 kt
(different collection scope)
420 kt
(different collection scope)
8%
55%
37%
1.8 kt
>85%
<15%
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EUU, Alm.del - 2022-23 (2. samling) - Supplerende svar på spørgsmål 49: Spm. om, hvilke interessenter, virksomheder mv. ministeriet har været i dialog med i forbindelse med ønsket om at indføre et forbud imod anvendelsen af PFAS, til miljøministeren, kopi til udenrigsministeren
2698345_0053.png
Case study cookware
Metal-based consumer and professional cooking equipment such as pans,
pots and trays, is usually made of different metals incl. steel, aluminium and
copper and a coating.
Coatings of cookware usually focus on reducing the stickiness of bakery
and other food products as well as minimizing the risk of burning in. These
characteristics are, for example, beneficial for industrial sized food
processing equipment or regular pans and pots which can be found in
households.
The overall FP content which is used for a regular frying pans (i.e., often
referred to as Teflon coating) ranges between 6 - 12 g (on average 8 g).
Frying pans weigh between 0.5 and 3 kt (on average 0.8 - 1 kg),
accordingly the average FP mass per frying pan by weight is just below the
1% mark. According to different Eurostat product datasets, it can be
estimated that around 250 Mio. t of coated (consumer) pans, pots and trays
were put on the market in the EU in 2020.
In addition, recyclable pans or often disposed of in mixed residential waste
streams and, therefore, lost for any recycling approach (waste incineration
or landfill). Mixed recyclables collection such as the ‘Wertstofftonne’, where
different recyclable waste materials made from plastic or metal are
collected, offer the opportunity to reach significantly higher recycling shares
from end-of-life cookware via automated sorting facilities compared to
recyclables bring-in stations or dedicated metal scrap collectors.
Manufacturer take-back systems for old pans when buying new ones, are
also an opportunity to collect ‘clean’ fractions of end-of-life
cookware for
metal recycling.
The recovery of plastic fractions for recycling (e.g., handles) is not targeted
by most recycling companies. These materials are incinerated, landfilled or
thermally destructed (metal recycling furnace). There are also no
technologies available to recycle the FP content from coatings.
EU27+3 Fluoropolymers in new cookware 2020
FP quantity
2.3 kt
The total FP weight used for coated consumer and professional cookware
was estimated to approx. 2 - 2.5 kt in 2020 of which the largest share
accounted for consumer frying pans.
After use, coated end-of-life frying pans are collected in different waste
streams. Some countries have restrictions for the collection of coated pans
due to safety concerns related to waste treatment and recycling.
Fluoropolymer waste in Europe 2020
EU27+3 Fluoropolymer waste in EOL cookware 2020
[estimated]
FP quantity
2.1 kt
2022-07-19
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EUU, Alm.del - 2022-23 (2. samling) - Supplerende svar på spørgsmål 49: Spm. om, hvilke interessenter, virksomheder mv. ministeriet har været i dialog med i forbindelse med ønsket om at indføre et forbud imod anvendelsen af PFAS, til miljøministeren, kopi til udenrigsministeren
2698345_0054.png
Agenda
Introduction and project frame
Management Summary
5
21
Fluoropolymer products & applications
Fluoropolymer waste
In-depth waste analysis
Circular economy approach
Appendix
27
33
44
55
60
2022-07-19
Fluoropolymer waste in Europe 2020
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EUU, Alm.del - 2022-23 (2. samling) - Supplerende svar på spørgsmål 49: Spm. om, hvilke interessenter, virksomheder mv. ministeriet har været i dialog med i forbindelse med ønsket om at indføre et forbud imod anvendelsen af PFAS, til miljøministeren, kopi til udenrigsministeren
2698345_0055.png
Status quo
recycling of FP materials
The recycling of FP materials today is often limited to ‘clean’ pre-consumer
materials from FP manufacturers. Only small volumes of post-consumer FP
materials are recovered for recycling.
20 - 25% of all FP product manufacturers stated to have own internal re-
processing steps for their own process losses. 30 - 35% pass on their FP
pre-consumer waste to external material re-processing companies
(recyclers). 15% export their pre-consumer wastes to other companies
inside the EU (export for recycling intra-EU). 5 - 10% export their FP
processing losses to countries outside the EU, e.g., to Asian countries for
further processing (export for recycling extra-EU).
Recycling of post-consumer FP waste from commingled (mixed) waste
streams either from households and comparable sources or from
commercial and industrial end-users is not existent and will not be a
promising option for circularity of FP in the coming years. The overall share
of FP is too low to establish any sorting and recycling approach.
A common recycling process is to grind PTFE waste into a fine powder and
blend this powder with pure PTFE to be used either in compression
moulding or ram extrusion processes. Before grinding, PTFE waste is
usually heated to above its melting point to remove any organic
contaminants. Once ground, it is treated with acid to dissolve inorganics
after which it is washed and re-heated to vaporise any volatiles (i.e.,
recycling could be described as a sintering process).
Extract of existing FP recyclers in Europe
(excl. chemical recycling and trading / export of FP waste for recycling)
Krall Kunststoff-Recycling with focus on technical plastics waste such as PC
and PMMA but also PA, PEEK, PPSU, PSU, PVDF, PTFE, PEI
Heroflon (Daikin) with focus on PTFE waste
MCAM Symalit (Mitsubishi Chemical Holdings Corporation) with focus on
PVDF, ECTFE, ETFE, PFA, FEP, PEEK
The recycling of post-consumer FP waste is more or less limited to the
recovery and separation of ‘clean’ fractions, e.g., from commercial and
industrial production and processing equipment (around 13 kt in total).
The accessible quantity of post-consumer FP waste suitable for recycling is
significantly smaller. Only if all stakeholders along the FP value chain work
more closely together, progress can be made on the circularity of FPs.
Fluoropolymer waste in Europe 2020
Ambofluor with focus on PVDF, ETFE, ECTFE, FEP, MFA, PFA, PTFE
Prodotti (Fluormetal) with focus on PTFE
Shamrock Technologies with focus on PTFE
Mikro-Technik with focus on PTFE
United Polymer Mixers (UPM Kunststoffen) with focus on PTFE
55
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EUU, Alm.del - 2022-23 (2. samling) - Supplerende svar på spørgsmål 49: Spm. om, hvilke interessenter, virksomheder mv. ministeriet har været i dialog med i forbindelse med ønsket om at indføre et forbud imod anvendelsen af PFAS, til miljøministeren, kopi til udenrigsministeren
2698345_0056.png
Critical success factors for the circularity of FP
drivers & barriers
Drivers
High cost of raw materials / limitation of accessible raw materials
Existing chemical recycling plant with a capacity of 500 t p.a.
Cooperation only between few stakeholders necessary
Relatively ‘clean’ material streams if selected properly
Barriers
Various applications with overall small FP volumes
Limitation to selected and pre-sorted EOL material streams
Logistical efforts to collect sufficient volumes for recycling
Objections from the industry related to ‘product safety issues’
2022-07-19
Fluoropolymer waste in Europe 2020
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EUU, Alm.del - 2022-23 (2. samling) - Supplerende svar på spørgsmål 49: Spm. om, hvilke interessenter, virksomheder mv. ministeriet har været i dialog med i forbindelse med ønsket om at indføre et forbud imod anvendelsen af PFAS, til miljøministeren, kopi til udenrigsministeren
2698345_0057.png
In-depth circular economy approach for FP pipe liners
PTFE converting
(e.g., PTFE liners)
PTFE production
Possible EOL
management of
post-consumer
FP liners
Target PTFE
Chemical recycling
PTFE applications
in use
Collection,
processing and
pre-sorting of EOL
PTFE products
Non-target PTFE
Waste incineration
2022-07-19
Fluoropolymer waste in Europe 2020
Today, the recovery of post-consumer EOL fluoropolymer waste often relies on
(co-)incineration in waste incineration plants.
After production and converting of PFTE into products and applications, commercial
end-users such as large petrochemical companies (e.g., BASF or Bayer), usually send
their EOL products to MSWI plants, mainly via contracted service or waste
management companies.
The existing pilot plant by 3M (former Dyneon) in Gendorf/Germany is capable to
recycle 500 t of post-consumer PTFE, PFA or ETFE materials per year by cracking
fluoropolymers into monomers (chemical recycling). These monomers can be used to
produce new fluoropolymer raw materials. Besides 3M, InVerTec is also able to provide
turn-key chemical recycling plants for fluoropolymer end-of-life applications.
A circularity target could be the set-up of a closed material circle in the coming years.
Collected EOL FP products from commercial end-users
could be sent to ‘up-cycling
plants’ and the extracted monomers could be distributed back to PTFE raw material
producers.
In order to create more economic viable chemical recycling opportunities. A plant
should cover a processing capacity of about 2 kt/p.a.. If 5 of these plants are built in the
coming years, about 10 kt of post-consumer FP material could be recycled in the EU,
which would represent about 20 - 30% of the annual FP processing capacity.
Together with other companies, the manufacturer BAUM is currently working on a
closed-loop solution for the recovery of PTFE and other PF EOL products.
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EUU, Alm.del - 2022-23 (2. samling) - Supplerende svar på spørgsmål 49: Spm. om, hvilke interessenter, virksomheder mv. ministeriet har været i dialog med i forbindelse med ønsket om at indføre et forbud imod anvendelsen af PFAS, til miljøministeren, kopi til udenrigsministeren
2698345_0058.png
In-depth circular economy approach for FP coated cookware
The average use phase (i.e., lifetime) of coated cookware is highly
dependent on the frequency of use or disregard of the maximum approved
temperature respectively scratching of the coating, e.g. with metal
cookware. Small scratches and slight colour changes of FP based coatings
are often only aesthetical disadvantages and do not impact the mechanical/
chemical characteristics of the coating. Coated cookware should be
replaced, if proper functionality (i.e., reduced anti-stick characteristics) is
not given anymore.
Another option is applying a new FP based coating. Some manufacturers of
cookware and coatings (e.g., BAF, Olav and ITN) already offer a solution
where the used pans and pots can be sent in for renewal of the non-stick
coating. ITN offers its services for all metals and all cookware
manufacturers. The company removes the old coating (sandblasting) under
controlled conditions, incl. dust and particle extraction measures, and
applies new PTFE based coatings.
The renewal of anti-stick coatings is one way to extend the longevity of
coated cookware. The service life of FP-based coatings is estimated by
manufacturers to around 4 to 5 years on average. Applying a new FP based
coating would accordingly double the average lifetime and offer another
opportunity to reuse ‘old’ cookware with the characteristics of a new
product.
Fluoropolymer waste in Europe 2020
Raw material
suppliers
(metals, coatings etc.)
Recyclable scrap /
waste collection;
metal recyclers
Reuse of coated
cookware; renewal
of FP coatings
FP coated
cookware in use
(4 - 5 years)
FP coated
cookware
manufacturers
FP coating renewal;
reuse of coated
cookware
2022-07-19
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EUU, Alm.del - 2022-23 (2. samling) - Supplerende svar på spørgsmål 49: Spm. om, hvilke interessenter, virksomheder mv. ministeriet har været i dialog med i forbindelse med ønsket om at indføre et forbud imod anvendelsen af PFAS, til miljøministeren, kopi til udenrigsministeren
2698345_0059.png
Agenda
Introduction and project frame
Management Summary
5
21
Fluoropolymer products & applications
Fluoropolymer waste
In-depth waste analysis
Circular economy approach
Appendix
27
33
44
55
60
2022-07-19
Fluoropolymer waste in Europe 2020
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EUU, Alm.del - 2022-23 (2. samling) - Supplerende svar på spørgsmål 49: Spm. om, hvilke interessenter, virksomheder mv. ministeriet har været i dialog med i forbindelse med ønsket om at indføre et forbud imod anvendelsen af PFAS, til miljøministeren, kopi til udenrigsministeren
2698345_0060.png
Typical treatment route of mixed residential and commercial & industrial waste streams
FP waste collection and treatment route
Waste generation
Waste management
Export
Recovery processes
FP pre-consumer waste respectively reusable materials are often
sent to recyclers or are internally re-processed again. Intra and
extra-EU export of pre-consumer FP waste is also common.
Post-consumer waste incl. FP waste from commercial & industrial
end-users is primarily managed by private waste management
companies. Post-consumer FP waste from private households is
mainly managed by municipal waste management companies
and (co-)contracted private waste management companies.
The largest share of FP waste in commingled waste streams
such as mixed residential household waste, commercial and
industrial mixed waste or shredder light-fractions of ELV and
large appliances shredder facilities is not post-sorted for
recycling. Accordingly, almost all FP waste fractions are
(co-)incinerated in MSWI or hazardous waste incineration plants.
A smaller share of FP waste is incinerated in commingled
fractions in dedicated RDF or SRF plants, e.g., cement kilns.
Only pre-sorted
and ‘cleaner’ FP waste fractions from end-of-life
applications such as pipe liners or tubes and pipes are suitable
waste streams for recycling. Post-sorting of FP materials from
mixed waste streams is not feasible, neither technical nor
economical.
60
Recycling
Thermoplastic
recycling
Other recycling
Pre-consumer waste
Production and processing
waste, re-processable internal
FP offcuts, samples etc.
Inhouse
re-processing
Post-consumer waste
Commercial & industrial
ELV waste, Commercial &
industrial mixed waste, pre-
sorted FP waste fractions
Waste collection &
(pre-)sorting by
municipal and / or
private waste
management
organizations
Incineration processes
Metal recycling
Energy recovery
MSWI / RDF / SRF
Post-consumer waste
Household & comparable
Residential household waste,
municipal waste generated by
commercial activities, WEEE
Disposal
Landfill
2022-07-19
Fluoropolymer waste in Europe 2020