Greenhouse Gas Mitigation from Waste Materials Recycling Steven B. Young

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Greenhouse Gas Mitigation from Waste g Materials Recycling Steven B. Young

Question Carbon credits have not been realised from recycling projects. Why?

Literature Recycling avoids processes Previous work done on of mining, drilling, mineral municipal waste, metals, construction materials, processing, smelting and plastics refining GHG emissions benefits are quantified (USEPA 1998, 2006) Based on life cycle assessment (ISO 14040:2006) Future opportunities for increasing recycling are tremendous (UNEP 2011) USA (Weitzet t al 2002) Canada (ICF 2005, Mohareb 2008) China (Zhao 2009) CDM method exists UNFCCC Clean Development Mechanism. AMS III.AJ.: Recovery and recycling of materials from solid wastes

Methods International standards Life cycle assessment GHGquantification of projects ISO 14064 2:2006 Project quantification ISO 14040:2006 ISO 14044:2006 Life Cycle Assessment

Data set Four Enhanced Recycling projects Government of Canada Action Plan 2000 on Climate Change Five year (2001 2006) 2006) $3.4 million Minerals and Metals Program Projectsselectedfor selected activities and available data Measurement ISO 14064 Part 2 Baseline vs. project on lifecycle basis Low, medium, high hscenarios to 2010 Emissions factors from GoC (ICF 2005) GHG savings for recycling, reuse, etc. Also provided Measurement and reporting plans to serve as basis for expanded or replicated enhance recycling

Project 1: Construction waste recycling Let s Climb Another Molehill ll Recycling Council of Ontario Greater Toronto area Focused at on site WMAPs resulting in waste diversion activities Waste Management Action Plans Data, issues, barriers and opportunities to applying New residential progressive 3Rs on site construction Photo credit: Molehill report, RCO

15 sites sampled in total Wood Framing Component reuse Gypsum recycling Photo credit: Molehill report, RCO Concrete recycling: major demolition Pearson International Airport, Toronto, ON

Molehill overview of materials No. of case study sites (S): 15 CR& D activities: Construction (7 S), Renovation (4 S) and Demolition (4 S) Total CR& D waste generated = 222,837 tonnes Landfilling Recycle Waste to energy Reduce Reuse 3 tonnes 9,457 tonnes 3 tonnes 2 tonnes 213,372 tonnes -Wood - Gypsum -Wood -Mixed -Concrete - Asphalt - Concrete -Steel - Plastic - Steel - Wood -Trash -Wood -Clay brick - Copper - Asphalt -Plastic - Vinyl windows - Glass and OCC

Project 2: Adding residential scrap metal to municipal recycling programs Ottawa Valley Waste Recovery Centre Small metal items collected with traditional recyclables lbl Sort at MRF, sell to dealer 19,040 kg of metal Operates today and expanded in scope appears economically viable Photo credit: OVWRC

Project 3. Cost effective ways of recycling scrap metal from Northern communities ii Rankin Inlet Churchillhill Thompson Gillam Selkirk Photo credits: North Central Development

Scrap metal recovery from Northern communities ii Churchill, MB Gillam, MB Gillam, MB Photo credits: North Central Development Churchill, MB Rankin Inlet, NU Rankin Inlet, NU

Northern: transportation routes Rankin Inlet, NU (498 km) Via Kivalliq Marine Churchill, MB Churchill, MB (547 km) Via HBR/Omni Trax Thompson, MB Thompson, MB (770 km) Rightway Recyclers; Gardewine Selkirk, MB Mandak Metal Processors, Scrap Broker Gillam, MB (1072 km) Gardewine Selkirk, MB Mandak Metal Processors, Scrap Broker

E1 Production of metal products Northern scope of analysis E2 Use of metal products E3 Scrap pre-processing processing at sites E4 Sorting scrap metal E7 Transport E5 Recycling ferrous metal E6 Recycling nonferrous metal Legend controlled related affected not relevant

Quantification: (emission i factors x activity ii levels) l Emissions factors as GHG savings ICF (2005) report for NRCan

Project 4: Electronics waste recycling Quebec CFER Network Demonstrating a comprehensive treatment andrecycling of E waste: Cathode Ray Tube (CRT) Glass Plastic ferrous nonferrous metals other materials Photo : CFER

Electronics recycling: emissions factors UsedICFreport factors Complexities E.g.: g:computerreuse reuse GHG savings Recycling factor 1.61 t CO 2 e/t of computer (ICF) Reuse factor of 59 t CO 2 e/t of computer (from USA source) A significant contributor 4249 of the 4578 t CO 2 e in Low scenario (93%) What values to use? What confidence is needed?

Results Project 1: Project 2: Project 3: Project 4: Construction Residential scrap Northern Electronics wastes metal recovery recycling Waste collected 222,837 t across 15 sites 19 t for 3,927 households in 2,004 t at five remote sites in 294 t obsolete computers and eight months (6.06 kg/house/ northern Canada electronics (25,470 pieces) year) Baseline Landfill of Landfill via Dumping in open Landfill and activity construction waste residential stream sites hazardous disposal Project Reuse: 213,372 t Recycling: 15 t Recycle: 1,964 t Reuse: 72 t activity ferrous, 4 t nonferrous metals ferrous. Transport 84 t, non ferrous ferrous, 40 t non Recycling: ferrous Recycle: 9,457 t 500 1000 km metals 57 t, GHG reduction (t CO2e) 0.21 0.36 t per tonne recovered. Total: 222,000 t 2.0 t per tonne urban scrap metal collection. Total: 38 t 1.2 t per tonne metal collected. Total: 2,000 t plastics/glass 60 t 15 t per tonne reused or recycled. Total: 4,600 t

Discussion Additionality Whyhave have carbon credits have not projects 1, 3 and 4 Magnitude been realised Full scale is indeed small Construction waste >100,000 t from recycling projects? Over 15 sites vs. CDM typically 25,000 200,000 t Scale up, aggregation challenging Conclusions Ownership GHG benefits to recycling Carbon offsets may be wrong mechanism Economic additionality i was likely l in Location remote to baseline Projects (urban) reuse & recycling activity recycling Baselines distant, primary material production, large (capped) facilities Regulatory additionality (?) Full reference: Young, S. B. (2011). Greenhouse Gas Mitigation from Waste Materials Recycling. Greenhouse Gas Strategies in a Changing Climate Conference. AWMA. November 16 17, 2011. San Francisco, CA.

Acknowledgements Thanks to L. Bushi, project proponents, companies, NGO managers, and Nt Natural lresources Canada who provided d data dt and guidance. Supported by GOC contract NRCan 05 01003. AWMA 2011: GHG Strategies Conference Abstract #31: Lessons Learned from GHG Measurement and Reporting of Technologies with ISO 14064: Part 2 Abstract #32: Greenhouse Gas Mitigation from Waste Materials Recycling

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