U.S. Government/Industry Collaboration for Sustainable Endof-Life Vehicle Recycling Ed Daniels, Director Energy Systems Division SAE Government/Industry Meeting Washington D.C. April 15, 2007 Outline of Today’s Presentation Overview of ELV Recycling Today--- Typically more than 75% of automotive materials (primarily metals) are profitably recycled, the balance is commonly referred to as “automotive” shredder residue Overview of ELV Regulations/Directives--- Europe, Japan, China have adopted versions of ELV recycle directives, North America has not Overview of the U.S. ELV CRADA Team government/industry partnership--- a research partnership focused on development and demonstration of technology to support enhanced sustainable recycling of automotive materials Conclusions--- The changing automotive material mix over the past fifteen years and evolutionary technology trends relative to automobile architecture for improved safety and environmental performance will increase the recycling technical challenge 2 Overview of ELV Recycling Today About 35 million vehicles enter the recycle infrastructure each year: – ~13 million; N. America – ~11 million; Western Europe – ~5 million; Japan – balance; others Under current and expected future market conditions for scrap metal; it is difficult to anticipate that subsidies would be required to sustain the current level of automotive materials recycle 4 3.5 Billions of Vehicles Typically more than 75% of automotive materials (primarily metals) are profitably recycled, the balance is commonly referred to as “automotive” shredder residue and is typically landfilled 3 2.5 2 1.5 Industrialized Nations World 1 0.5 0 1996 2050 3 ELV Recycling is a Market Driven Success Today Supported by a Comprehensive Infrastructure - 75% of automotive materials are recycled - the other 25% is commonly called “automotive” shredder residue - ~ 4-5 million tons of shredder residue in N. America; 15 million tons worldwide N. America---•More than 12000 dismantlers •About 20000 remanufacturers •About 200 shredders 4 ELV Recycle Concerns Lead to Regulations and Directives Response to increasing public expectations relative to environmental stewardship and an expectation of producer responsibility ELV, Electronics, Appliances European Union promulgated the “E.U. ELV Directive” in 2000 Japan’s “Automobile Recycling Law” was promulgated in 2002 China “Statute 307- ELV Standard” was issued in 2001 5 ELV regulations in China Current automotive fleet in China; ~30 million ELV about 1.5 million per year Dismantling/materials recovery/ “remanufacturing” conducted by individuals Under Statute 307, only 367 dismantling enterprises are to be authorized (minimum capacity of 500 vehicles per year) Vehicle owners must sell ELV to an authorized dismantler Vehicles become ELV according to a mileage schedule (e.g. passenger vehicle; 500,000 km) 6 European Union ELV Directives---Goals Goals of the EU Directives – Ultimate goal: Less than 5% of ELV to landfill by January 2015 • 95% re-use and recovery (includes 10% waste to energy) • 85% re-use and recycle – By 2006: EU Target of 85% re-use and recovery – Member states may have lower targets, but not lower than • 75% re-use and recovery (includes 5% waste to energy) • 70% re-use and recycle – Last owner of the ELV should not pay for disposal (if costs are negative) – OEMs or Importers are expected to be responsible for “most” of the cost of meeting the goals – Recyclers (dismantlers) will be licensed to ensure compliance with de-pollution (fluids removal, battery removal) requirements 7 European Union ELV Directives---Issues Clearly focused on avoided landfill and certification of recyclers rather than lifecycle Member states have ultimate responsibility for implementation and policing (Not all member states have developed implementation plans) How do you verify that you are in compliance? (requires extensive data collection on inputs and outputs at each stage, production, dismantling, shredding) – OEM’s are supplying materials data – Some (not all) dismantlers and shredders are creating data bases to account for materials inputs and outputs (Some recyclers argue that materials are being diverted to those who do not incur the costs of tracking inputs and outputs, less than 20% accountability in France) Some recyclers argue that reporting costs associated with the Directives to date are diverting ELV from Europe to North Africa, Eastern Europe, China: Exports of “Used” Vehicles from Western Europe has increased to more than 30% of ELV. Numerous technology options being offered (primarily energy recovery); still discussions about what constitutes recycling vs recovery---which creates uncertainty for post-shred technology investment Recyclers (and OEMS) are asking for some reconsideration of the Directives---which is within the framework of the current directives 8 Strategic R&D Partnership for Sustainable Endof-Life Vehicle (ELV) Recycling---An Alternative to Directives ELV CRADA Partners (US ELV CRADA Team) – Argonne National Laboratory/ U.S. Dept. of Energy – American Chemistry Council—Plastics Division – USCAR’s Vehicle Recycling Partnership (DaimlerChrysler, Ford, GM) Organizing Theme – To achieve greater fuel-efficiency and safety, today’s cars incorporate an increasing share of innovative lightweighting materials. While these materials greatly enhance efficiency during vehicle use, they can present special challenges to recycling. Essential Question – Is there a business case for increased automotive materials recycling? Partnership Goals – Enable market-based optimum recycling of automotive materials – Ensure materials that are beneficial over the life cycle are not arbitrarily precluded from the design slate due to recycle limitations 9 Current R&D Portfolio Evolved from Roadmap Roadmap Issued May 25, 2001 – Information – Technology – Markets Albany Research Center The Aluminum Association American Plastics Council Argonne National Laboratory Automotive Parts Rebuilders Assoc. DaimlerChrysler Corp. Department of Natural Resources, Canada Ford Motor Co. General Motors Corp. Institute of Scrap Recycling Industries Massachusetts Institute of Technology Oak Ridge National Laboratory Rochester Institute of Technology Steel Recycling Institute Sandia National Laboratory US DOE 10 Current R&D Portfolio of the Team Evolved from a Stakeholder Workshop Report The recyclability of ELVs is presently limited and several technical and economic barriers need to be overcome to increase recovery and recycling – Lack of commercially proven technology to cost-effectively separate, identify and sort materials – Lack of profitable post-use markets – Collection infrastructure exists Development of technology to recycle today’s materials will provide the basis for recycling of future materials Initial focus should be on post-shred technology Industry-wide collaboration is needed Worldwide technology needs to be tracked and information disseminated to users 11 Why and Why Not Shredder Residue as a Source Material? Complex mixture of waste resulting from the shredding of cars, other durables, and scrap metal to recover metals for recycling---difficult separation and/or conversion Metals Ironoxides Polymers Only 200 shredders---opportunity for volumes of material that could be of commercial interest in comparison to more than 20000 dismantlers PU Foam Oils & Dirt Other fines 10 9 8 7 6 5 4 3 2 1 O th er 0 Po ly pr o Po p y le ly et n e hy le ne EP D AB M S, PC H IP S N yl on s Po P ly e s VC te r TP million pounds 12 What are the Recycle Options? – Mechanical recycling --- separation and recovery of materials for re-use in original and/or other materials applications – Feedstock and Chemical Recycling---Conversion of organic materials such as polymers to fuels and chemicals (e.g. pyrolysis, gasification, glycolysis) – Energy Recovery--Conversion of organic materials such as polymers to heat for energy recovery Life-cycle analyses are being conducted to ensure that any option is environmentally beneficial--A number of technology options (U.S. and Europe) are being benchmarked 13 Argonne’s Mechanical Separation Pilot-plant Provides a Focal Point Physical separation produces material concentrates from bulk shredder residue – Foam – Ferrous and Non-ferrous – Polymer Concentrate Plastics recovery process is a 6stage wet (froth flotation) system for recovery of plastics from the polymer concentrate – Polyolefins – ABS – Nylons – Other Physical Separation Pilot-Plant Plastics Recovery Facility 14 Mold Trials Confirm the Technical Feasibility of Re-use of Recovered Polyolefins (50-50 PP/PE) Steering column cover Battery tray Knee bolster Spare tire base plate 15 Changing World Technologies---Thermochemical conversion The Changing World Technologies (CWT) two-stage thermodepolymerization process converts industrial waste to oils, gases, and solids CWT’s first commercial facility based on this technology was commissioned in April 2003 and converts 200 ton/day of offal from a ConAgra Foods turkey slaughterhouse into oil 16 Changing World Technologies , cont. CWT’s thermo-depolymerization process is potentially applicable to a significant fraction of shredder residue A proof-of-concept bench scale test confirmed the technical feasibility of their process CWT’s Bench Scale Unit A controlled 2000 lb test run is scheduled to be completed during the 2nd quarter of FY07 – Analysis will be completed in 2007 – Validation of the mass and energy balances – Confirmation of process economics CWT’s Pilot Plant Unit 17 Accomplishments to Date Developed a modular LCA for evaluation of alternative “post-shred” recycle technologies Designed, built and installed 1/10 scale mechanical separation and froth flotation pilot-plant at Argonne (confirmation of process technology and supply of control samples to other technology developers) Confirmed the technical feasibility of recovering and reusing polyolefins from shredder residue (research is ongoing to recovery additional plastics) Changing World Technologies confirmed the technical feasibility of converting shredder residue to liquid hydrocarbon fuels Troy Polymers confirmed the technical feasibility of converting polyurethane foam from shredder residue to polyol initiators Process economics appear favorable, but need confirmation; currently preparing engineering designs to evaluate process economics 18 Conclusions Implementation of the EU ELV Directives is raising a number of issues that need to be resolved---difficult to gauge success at this time; regulatory constraints can limit market options Almost any recycling process option (with adequate controls) is likely to be environmentally preferable to landfilling A number of technology approaches have been demonstrated to be technically feasible for increasing the recycle rate of automotive materials – Mechanical recycling – Conversion of the organic materials to alternate fuels – Energy recovery 19 The changing automotive material mix over the past fifteen years and evolutionary technology trends relative to automobile architecture for improved safety and environmental performance increase the recycling technical challenge A joint U.S. government-industry CRADA was established in 2003 to lead the development of improved recovery and recycling methods for current and future ELVs The vision leading to this effort is one of sustainability and reduced environmental impact over the lifecycle of the automobile Ultimately, any new technology developed in response to these changes must have minimal risk-• Proven cost-effective at full-scale • Proven markets for products • Regulatory barriers removed/transactions costs minimized 20 Questions? Visit the U.S. ELV CRADA TEAM Website (www.es.anl.gov/Energy_systems/CRADA_Team_Link/Index.html.) This research is funded by the U.S. Department of Energy Office of FreedomCAR and Vehicle Technologies and our CRADA partners: the Vehicle Recycling Partnership of USCAR and the Plastics Division of the American Chemistry Council. The submitted manuscript has been authored by a contractor of the U.S. Government under contract No. W-31-109ENG-38. Accordingly, The U.S. Government retains a nonexclusive, royalty-free license to publish or reproduce the published form of this contribution, or allow others to do so, for U.S. Government purposes. 21