what are processing alternatives and market opportunities for mixed plastic fractions? l.tange...
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What are processing alternatives and market opportunities for mixed plastic
fractions?
L.Tange (Eurobrom DSBG) D.Drohmann (GLCC)
Representing European Flame Retardant Association (EFRA)
Presentation to workshop Where are “WEEE”going?October 2004 Antwerp
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EFRA Aims and Objectives
• EFRA is a Sector Group within CEFIC which:– represents all the major manufacturers of FRs– covers all flame retardant chemistries– promotes the safe use of FRs to achieve fire
safety– recognises the perceived environmental
issues and encourages debate on a scientific basis
• FR Industry sponsors studies into key issues– Tests in support of EU Risk Assessments– Life Cycle Assessments– Consumer exposure– End of Life studies, incineration and recycling– Monitoring of certain FRs in the environment
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EFRA Members 2004
Full Members
Akzo Nobel, Albemarle, Bayer, Borax, Budenheim, Ciba, Clariant, DSBG/Eurobrom, DSM, Ferro, Great Lakes, Italmatch, Joseph Storey, Nabaltec, Rhodia
Associate Members
Noveon, Tegewa, Schill & Seilacher
Observers Plastics Europe, CIA, FRCA, FRCJ, GTFI
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Operation and Cooperation Between FR Industry Groups
Representing the unified Flame Retardants industry in Europe - The ‘One Stop Shop’ for the outside world
Funding research and international coordination of product related issues
Dealing with product related issues in Europe
European Br FR Industry Panel
Phosphorus
GroupMinerals
Group
PefrcPhosphate
Ester Flame Retardants Consortium
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PLASTIC WASTE FROM E & E EQUIPMENT Plastic content waste in total E & E (West Europe, 2000)
Total waste (all materials): 4,395,000 tonnes
Source: TN SOFRES Consulting
82.3% : other waste :• ferrous metals• non-ferrous metals• wood• glass• elastomers• concrete• oil• optic fibres• ...
Plastic waste : 17.7%
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PLASTIC WASTE FROM E & E EQUIPMENT
Total plastic consumption compared with total plastic waste, by sub-sector(Western Europe, 2000)
Plastic consumption in 2000:1,483,000 tonnes
Source: TN SOFRES Consulting, based on data provided by plastic and product manufacturers
Plastic waste generated in 2000:777,000 tonnes
Automatic dispensers:
1%
E & E tools:1%
Medical equipment:
0.5%
Toys: 0.5%
Lighting equipment:
0%
Monitoringand control
instruments:0%
Large household appliances:
41%
IT & Telecommunications:
34%
Consumerequipment:14%
Small household
appliances:9%
Automaticdispensers:
1%
E & E tools:1%
Others: 0%
Large household appliances:32.5%
Consumer equipment:14.5%
Small householdappliances:
10%
IT & Telecommunications: 40%• Telecommunications: 5%• Office equipment: 6%• Data processing: 29%
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Variety of Flame Retardantsuse of FRs, worldwide, of total tonnage (1.2 mill/tons/y)
source SRI Consulting http://www.sriconsulting.com
In many cases, several different types of flame retardants are combined to achieve optimal material performance
and product safety (synergy)
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Use of flame retarded plastics in E&E equipment – 2000 data
Non Flame Retarded
Plastics - 70%
(1,030,000 tonnes)
Flame Retarded
Plastics - 30%
(450,000 tonnes)
Source: TN SOFRES Consulting for APME
Plastics with non -halogenated
flame retardants – 59%
(264,000 tonnes)
Plastics with halogenated
flame retardants – 41%
(186,000 tonnes)All E&E plastics
FR E&E plastics
Non Flame Retarded
Plastics - 70%
(1,030,000 tonnes)
Flame Retarded
Plastics - 30%
(450,000 tonnes)
Source: TN SOFRES Consulting for APME
Plastics with non -halogenated
flame retardants – 59%
(264,000 tonnes)
Plastics with halogenated
flame retardants – 41%
(186,000 tonnes)All E&E plastics
FR E&E plastics
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EU Directives: Restrictions on Marketing & Use
• Directive 2003/11/EC amending for the 24th time Council Directive 76/769/EEC relating to restrictions on the marketing and use of certain dangerous substances and preparations
• PentaBDE and OctaBDE may not be placed on the market or used as a substance or as a constituent of substances or of preparations in concentrations higher than 0.1% by mass.
• Articles may not be placed on the market if they, or FR-parts thereof, contain these substances in concentrations higher than 0.1% by mass.
• Ban to be effective from 15.08.2004
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EU Directives: RoHS - 2002/95/EC
• The European Commission launched a Stakeholder Consultation in May 2004 to evaluate exemption for DecaBDE
– 90 inputs from stakeholders (not only for DecaBDE but also for other applications included in the consultation)
– 20th July: first evaluation of the European Commission & Member States on input
– August / September: proposal from Commission– 22 October: “vote” by Member States
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WEEE EU Directive consequences for FRs
•As a minimum, plastics containing brominated flame
retardants, printed circuit boards (greater than 10 cm2),
and other components have to be removed from any
separately collected WEEE.
•WEEE plastics containing BFRs need to be separately
treated like: e.q. directly in a smelter or via co-
combustion into incineration or cement kilns
•Within the WEEE directive there are NO restrictions
related to other FRs
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Process-installation Definition: Energy Recovery/material recycling or disposal
Cost Euro/ ton
Issues
Mechanical recycling Material recycling ? Sorting, quality, economics, end market
Feedstock recycling (FS) Material recycling /Energy Rec 150-400 Economics, reliability new technique
FS: Dehalogenation Material recycling ? Economics, new technique
FS: Haloclean Material recycling ? Pilot scale
Solvolyse process Material recycling High
Super Critical Water Oxidation
Material recycling High Economics, pilot scale
Metal smelter Energy recovery with material recycling (metals)
Low? Definition of energy recovery/ type of smelter
Cement kiln-fuel replacement
Energy recovery or after EU hearing material recycling as option
Low? Corrosion / energy recovery
Plastics with BFR’s as additive
Energy recovery or after EU hearing material recycling as option
Low? Definition of energy recovery?
House hold waste incinerators co-combustion
Energy recovery 50-130 Political acceptance, max 3% WEEE plastics
Landfill Disposal 50-130 Politically not accepted
Available technical solutions for WEEE Plastics
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Mechanical Recycling and Separation
On the ladder of Lansing the most preferred solution is re-use in same applicationThe issues are mostly related to the quality of aged plastics, variety of and changes in additive contents, and economy of scale
• Mechanical recycling requires separation• Evolution of separation techniques & equipment is
crucial• Existing methods for sorting are ;density difference
(wet floating system), dry (windsifting), tribo-electric, heated drum method and jigging system
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Mechanical Recycling
• FR plastics recycling is happening (including for closed loop) resulting in valuable types of recyclate (e.g. Ricoh and Fuji Xerox)
• Examples of mechanical recycling are possible once the plastics can be seperated:– Polyamides (PA6) using Exolit OP 1312 (tested by
Clariant)– HIPS with DecaBDE (tested by GFA-EBFRIP)– HIPS with EBP and EBTBP (tested by Albemarle)– PC/ABS containing PFRs (BPADP is tested by
Albemarle)– ABS with BEOs (tested by Technopolymer Japan)
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FRs and Mechanical Recycling
• Main conclusion of all these extrusion and injection molding test: Majority of the mechanical properties were maintained during 3 or 5 recycle steps and also full filling the German chemical banning ordinance
• These plastics can be recycled for same applications due to maintenance of physical properties of polymer and flame retardant
• Recyclate maintains flame retardancy to levels in excess of UL tests V-0 and 5VB
• Main issue is historical plastics containing Penta- and OctaBDE plus PBBs which needs to be sorted out. Also for these old plastics the issue of dioxin/furans related to the German chemical banning ordinance can be difficult to meet
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Management of E&E plastic waste(current trends and possible options)
Beside Mechanical Recycling:• Metal smelters (mainly PWBoards)• Incineration co-combustion: Tamara and Norway study• Landfill• Cement kilns – fuel replacementNew possible options• Feedstock recycling : Haloclean etc• Dehalogination with blast furnaces• Creosolv, solvolysis, super critical CO2 extraction• Smelter (copper and precious) as reducing agent as
during the Umicore trial with 250 ton WEEE plastic
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Metal smelter recycling in Europe
Plants Recycling capacity
(per year)
Boliden, Norway 35,000 tons of E E scrap(25% plastic)
Umicore, Belgium Could treat >10.000 tons per year (mainly PWB’s)
Norddeutsche Affinerie AG, Germany
Treats 10.000 tons of PWB plus an other 15000 tons of E&E plastics and more is possible in the future
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Energy & Material Recovery by Co-combustion of WEEE and MSW by APME-FZK-EBFRIP
J. Vehlow, B. Bergfeldt, H. Hunsinger, K. Jay, H. SeifertForschungszentrum Karlsruhe
Institut für Technische Chemie / Bereich Thermische Abfallbehandlung
3 4O
O O
Br
Cl
Br
BrBr Cl
ClCl
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German Pilot Plant FZK Tamara Co-combustion trials together with APM E
• A pilot plant as copy of a modern MSW incinerator
• Trial in cooperation with APME and FZK
• Capacity 250 kg/h containing 50 kg WEEE plastics
• Bromine content up to 10 g/kg MSW
• After combustion the HBr is transferred into the flue gas
• The HBr is absorbed in a scrubber with water or NaOH
• Samples were collected & tested by Bromine producers
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rotary drum 450 °C
Br recovery
gas / oil (containing Br)
HBr/Br2
gas (process energy)
oil (chemical industry)
coke
Cu
no
ble
met
als
Cu smelter
rotary drum 350 °C
feed
Haloclean Process
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Future Trends for thermal processes
Main criteria:1. Political acceptance2. Economical solution (eco-efficiency)3. “Zero” emission (eco-efficiency)4. Outlet for the produced products!!By these criteria it is most likely that feed stock recyling will
become a favourite solution but only if the economics improve
Metal smelters and “clean” processes like Haloclean are able to play an important role !
For metal smelters a “full scale trial” has run with positive results
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Overall conclusion (1)
• Flame retardants are needed in a world with plastics.
• If plastics with FR’s are produced we need to deal
with these products during their whole life cycle
including all End of Life options
• For new plastics with FR’s produced today
mechanical recycling can be an option
• Historical WEEE plastics do have several issues for
direct mechanical recycling.
• Today thermal processes do have the advantage of
large scale of economy plus are able to handle the
different FRs
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Overall conclusions (2)
• Energy recovery and feedstock recycling can play an
important role in a waste management
• Up to to 3 % plastics from WEEE can be mixed and
co-fired with Municipal Solid Waste Incineration without
increasing PBDD/F formation
• Smelters are able to use large amount of plastics as
reducing agent. Depending of the definition of recycling
it can be part of this quota or could count as energy
recovery