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Santiago/Chile 14 November 2014
Global Waste Management Perspectives and Extended Producer Responsibility Santiago/Chile 14 November 2014 Hermann Koller ISWA Managing Director
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Contents Global situation and approaches in waste management Organisation and financing in waste management Extended Producer Responsibility Challenges and possible solutions for Chile
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1. Global situation and approaches in waste management
Global Waste Market The global waste market of MSW (Municipal Solid Waste), including collection and recycling, is estimated to € 310 billion per year, which equals the GDP of Denmark. And the sizeable informal sector is not included in this number. The generation of waste amounts to 4 billion tonnes per year total, of which 1,9 billion tonnes household World wide in the waste management sector the number of employees is app. 40 million people – half informal
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1. Global situation and approaches in waste management
The amount of waste generated worldwide in one year is enough to bury the entire area of Munich under 130 metres of waste Notes: Area 31,000 ha Density of waste100kg/m³
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What do we do with the waste on a global scale?
1. Global situation and approaches in waste management What do we do with the waste on a global scale? 70 % landfilled or open dumps 10 % incinerated 20 % recycled → This produces circa 1 billion tonnes of CO2 equivalents rising to 3 billion tonnes in 2030 mainly from landfills.
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Consequences Loss of resources Emissions
1. Global situation and approaches in waste management Consequences Loss of resources Emissions Missed employment opportunities Destruction of natural resources Public and urban health risks, epidemics Illegal trade Ocean litter
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1. Global situation and approaches in waste management
What we want to see
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And what we do not want to see
1. Global situation and approaches in waste management And what we do not want to see
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1. Global situation and approaches in waste management
Shares of landfills, energy recovery and recycling in different countries Sources: (1) Eurostat Analysis by M. Bauer and N.J. Themelis 5/25/09, (2) World Waste Survey, Veolia and Cyclope 9/06
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Financing Options - Overview
2. Organisation and financing in waste management Financing Options - Overview Tax system For any waste type For special purposes (e.g. landfill tax for contaminated site remediation) Fee system In general (e.g. certain fee and charges for residual waste per container, per household, per square metre living space, …) For specific purposes (e.g. bulky waste, integrated disposal fee for refrigerators, fluorescent tubes, packaging, …) Deposit System For certain waste types (e.g. refillable glass or plastic bottles) Full cost system (all services covered) For certain waste types (e.g. Producer responsibility driven systems for packaging, electric/electronic waste) Additional Cost system For certain waste types (stakeholders share costs involved for packaging waste) 12
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Different waste types are financed by different means
2. Organisation and financing in waste management Different waste types are financed by different means Residual waste Bio waste Hazardous waste Bulky waste Non packaging Paper Metals Packaging waste Electrical and electronic equipment Cars Batteries System operator Communities Dual System Waste fees/taxes (fee per household, per emptying, per bin, …) Financing Method Fees on weight or unit Lebensministerium – wie Sich BMU nennt - als Aufsichtsbehörde: Ziele der EU Richtllinie Hat volkswirtschaftliche Sinnhaftigkeit und Effizienz im Gesetz verankert Wirtschaft: Geringe Kosten und Rechtssicherheit Aber auch: bequeme Sammlung, weil IG-Verpackungen. -> Zielkonflikt Konsumenten: Einfache, bequeme Sammelsysteme Kostengünstig (Müllgebühr + Lizenzentgelte) -> Zielkonflikt wie oben Kommunen: Restmüllentlastung – Machtverlust als Nachfrager Kooperationsmodell und Schnittstellen zu den Sammelsystemen Entsorgungswirtschaft: Erfolgreiche Auftragnehmerschaft im Wettbewerb, Planungs- und Investitionssicherheit Systembetreiber: Erforderliche Gestaltungsfreiheit, Effizienz und Wettbewerbsfähigkeit Nicht erwähnt: Politik, Medien, Wissenschaft/Forschung, Umweltgruppen Investoren Obliged companies (Extended producer responsibility) Financed by Consumers/Citizens
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Main Cost Factors Collection targets (set by law)
2. Organisation and financing in waste management Main Cost Factors Collection targets (set by law) Actual collection quantities Kind and performance of collection system Prices for collection, sorting, and recycling services Prices for treatment services (recovery, landfill) Revenues from recycled materials Cost allocation principles (full/incremental cost) Other legal requirements (e.g. communication and monitoring requirements)
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Landfill cost versus Landfill rates in European countries
2. Organisation and financing in waste management Landfill cost versus Landfill rates in European countries 15
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2. Organisation and financing in waste management
Costs for waste managements vary according to the services provided and standard of waste management Serbia €30/person/annum, 5% recycling rate, no energy recovery Hungary €60/person/annum, 15% recycling rate + energy recovery Belgium €185/person/annum, 75% recycling rate + energy recovery
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What are the costs of bad waste management ? Here are some…….
2. Organisation and financing in waste management What are the costs of bad waste management ? Here are some……. Health – epidemics, malaria, dengue fever, typhoid, cholera, respiratory diseases, black soot emissions, dioxin emissions, poisoning Environment - pollution of water tables, air quality, C02 emissions, HFC emissions, greater resource extraction Economic – damages to tourism, urban quality (house prices), business investment Social – waste scavengers, child labour, crime, urban degradation
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The European focus is on waste minimisation and resource management
2. Organisation and financing in waste management The European focus is on waste minimisation and resource management Landfill directive No untreated waste on landfills Recycling or recovery of any waste type Only inert waste after treatment allowed for landfilling Producer responsibility Organisational change through producer pays principle Producers are responsible for products when they become waste and have to fulfil the goals set by law Costs of waste management measures have to be taken by producers
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What is Extended Producer Responsibility?
Product Life Cycle Design/construction Producer Responsibility Production Distribution Extended Producer Responsibility Utilisation End-of-life Reuse Waste treatment Recycling Source: ei:ee
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Extended Producer Responsibility (EPR) as a suitable and proven tool
Applied in EU waste politics to specific waste types: Packaging and Packaging Waste Batteries and Accumulators End of life Vehicles, tires Waste Electronic and Electrical Equipment WEEE EPR aims to recover and recycle resources and reduce landfilling volumes Establishment of national compliance systems to manage recovery and recycling and collect industry fees Producer committment to recycling and compliance costs leads to improved design and construction Recyclability is becoming a product quality criteria
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EPR – Different approaches in Europe
3. Extended Producer Responsibility EPR – Different approaches in Europe Source: Spasova, B., Lund University 2014, EXPRA
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Guidance for successful EPR schemes
4. Challenges and possible solutions for Chile Guidance for successful EPR schemes Definition, scope and objectives should be clarified Responsibilities should be shared and clearly defined along the whole supply chain Ensuring fair competition, with sufficient control and equal rules for all Independent clearing house, especially in case of competing Producer Recovery Organisations (PROs) In line with the polluter pays principle, the design and implementation of an EPR should make sure that the full costs related to the end of life of products are covered Transparency is required on performances and costs
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Key success factors for efficient waste management
4. Challenges and possible solutions for Chile Key success factors for efficient waste management Appropriate Legislative framework including clear responsibilities for all stakeholders Schedule and goals for implementation Capacity building to raise expertise Waste management planning Business friendly frameworks to encourage investments Efficient measures for financing, e.g. EPR, fees Awareness rising to motivate consumers Monitoring
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An international perspective on EPR legislation in Chile
Seminario AMUSA: “REP tarea de todos” Santiago de Chile, November 14, 2014
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Content Overview of Extended Producer Responsibility
Law project to promote recycling: El proyecto de ley de fomento al reciclaje Comments on the legislation Some lessons learned Next steps?
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Extended Producer Responsibility (EPR)
Extended Producer Responsibility (EPR) is, according to OECD (2001), an environmental policy approach in which a producer's responsibility, physical and/or financial, for a product is extended to the post- consumer stage of a product's life cycle. A wide range of EPR models have been implemented globally.
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Core recommendations of the OECD
Chile is a member of the OECD since May 2010 OECD recommends the implementation of EPR, leading to: Increased collection and recycling rates Reduction of public spending on waste management Reduction in overall waste management costs Design for environment (DfE) innovations Realities of informal waste collection and treatment in developing countries must be considered in EPR design OECD workshop on EPR, Tokyo, June 2014
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? ? ? ? Overview of EPR landscape worldwide V Proposed/Expected
EPR or Product Stewardship in Place Zimbabwe Zambia Yemen Vietnam Venezuela Vanuatu Uzbekistan Uruguay United Kingdom U.A.E. Ukraine Uganda Turkmenistan Turkey Tunisia Togo Thailand Tanzania Tajikistan Syria Switz. Sweden Swaziland Suriname Sudan Sri Lanka Spain South Africa Somalia Solomon Islands Slovenia Slovakia Sierra Leone Senegal Saudi Arabia Rwanda Russia Romania Qatar Portugal Poland Philippines Peru Paraguay New Guinea Papua Panama Pakistan Oman Norway Nigeria Niger Nicaragua New Zealand Netherlands Nepal Namibia Mozambique Morocco Mongolia Moldova Mexico Mauritania Malta Mali Malaysia Malawi Madagascar Macedonia Lux. Lithuania Libya Liberia Lesotho Lebanon Latvia Laos Kyrgyzstan Kuwait S. Korea Taiwan N. Korea Kenya Kazakhstan Jordan Japan Jamaica Italy Israel Ireland Iraq Iran Indonesia India Iceland Hungary Honduras Haiti Guyana Guinea-Bissau Guinea Guatemala Greenland Greece Ghana Germany Georgia Gambia Gabon French Guiana France Finland Fiji Ethiopia Estonia Eritrea Equatorial Guinea El Salvador Egypt Ecuador East Timor Dominican Republic Dijbouti Denmark Czech Rep. Cyprus Cuba d’Ivoire Cote Costa Rica Congo Dem. Rep. Colombia China Chile Chad Republic African Central Cape Verde Cameroon Cambodia Burundi Burma Burkina Faso Bulgaria Brunei Brazil Botswana Bolivia Bhutan Benin Belize Bel. Belarus Bangladesh Bahamas Azerbaijan Austria Armenia Argentina Angola Algeria Albania Afghanistan Western Sahara Bosnia & Herz. Serbia Montenegro Croatia Alaska Texas Utah Montana California Arizona Idaho Nevada Oregon Iowa Colorado Kansas Wyoming New Missouri Minnesota Nebraska Oklahoma Dakota South Washington Arkansas North Louisiana Hawaii Illinois Ohio Florida Alabama Wisconsin Virginia Indiana Michigan Mississippi Kentucky Tennessee Pennsylvania Carolina West New Jersey Maine York VT MD NH CT Delaware Massachusetts RI United States Canada Territory Yukon Territories Northwest Nunavut Columbia British Alberta Saskatchewan Manitoba Ontario Quebec Brunswick Scotia Nova Edward Island Prince Newfoundland & Labrador Australia Singapore ? ? ? ? V
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Law project to promote recycling: El proyecto de ley de fomento al reciclaje
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Legislative procedure and status
The Government of Chile has introduced legislation containing extended producer responsibility policies which are consistent with OECD recommendations. An EPR framework law project was signed in August 2013. The reworked legislation under the new government (now called “Ley de Fomento al Reciclaje”) was submitted to the Chilean House of Representatives on August 5, 2014 under the simple urgency rule. Once the legislative process of the EPR-law has concluded, drafting of regulations will be required to give effect to the law.
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Supreme decrees to follow
A regulation shall establish the procedure for working out the supreme decrees to establish products subject to EPR, targets and other associated obligations for each priority product This will include: a) A general economic and social impact analysis b) Consultation with an extended operating committee created by the Ministry c) A public consultation phase, which shall include the opinion of the Advisory Council of the Ministry of the Environment Supreme decrees will be subject to the approval the Council of Ministers for Sustainability
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Objectives and scope of the Law
Make value recovery from waste a priority in Chile’s waste management strategy Introduce EPR as an economic mechanism to increase the recycling rate of packaging and products for at least 9 categories of goods set by the Ministry of Environment (article 9): Packaging Lubricating oils Tires WEEE/light bulbs Batteries Vehicles Newspapers and magazines Expired medicines Pesticides
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Central rules of the new legislation
This law places the obligation for product responsibility on the first company to put a priority product on the market (“producer” as per art. 3) The “Ley de fomento al reciclaje” will: Create cradle-to-grave responsibility: The waste producer is responsible for the handling of the waste, from its creation to its recovery and/or disposal. Put in place the principle of “the polluter pays”: The producer of waste is responsible for the costs associated with its handling. Obligate every producer and importer supplying the market in Chile to declare the quantities/tonnages of obligated materials and finance their recycling process – either on its own or through a collective management system.
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Industry responsibilities
Register the quantity of obligated products supplied into Chile in national database Organize and finance the collection of priority products waste in all the national territory individually (self-compliance) through an authorised collective management system Deliver their waste to a manager authorised to process it unless the producer handles the waste itself Solid household or comparable waste shall be delivered to an authorised manager The penalties for infringements of the law range from significant fines (up to 10 times the waste management costs) to temporary prohibition of sale of the priority product
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Industry responsibilities
The Ministry of the Environment may also require through supreme decrees: Labelling Information to distributors or marketers, managers and consumers, including an itemisation of waste management costs on the receipt or invoice. These costs shall be maintained throughout the entire marketing chain. Design and implementation of strategies for communication and raising awareness Design and implementation of waste preventive measures Separate collection at source and selective waste collection
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Role of municipalities
The legislation states municipalities may be allowed to sign agreements with collective management systems and provide enough area for the installation and/or operation of storage sites. Producers can contract directly with operators to provide recycling services Municipalities can help producers meet their legal obligations by: Helping to identify the most effective recycling solutions for their communities Incorporating new recycling services within their existing and future waste management contract Facilitating the implementation of new recycling services and facilities Educating and encouraging their citizens to sort recyclables from waste
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Comments on the legislation
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General remarks Chile should be commended for its proposal on EPR
Chile‘s approach to formulating a general framework EPR law followed by product specific regulations reflects international best practices It recognizes the need to involve the informal recycling sector It introduces other supporting mechanisms that will make EPR more effective and efficient The list of “priority products” noted in the legislation would make Chile one of the leading EPR jurisdictions in the world Agreeing on general framework for EPR is not easy. Working out product specific regulation through decrees is even more difficult
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Key planning data needed for all stakeholders
Robust data on quantities and waste characteristics of priority products Understanding of Chilean recycling preferences and behaviors Effectiveness of alternative recycling collection approaches under Chilean conditions Key recycling program operating data Participation rates Material capture rates Material recovery rates Capital & operating costs Market demand and prices for recovered materials
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Data needed to prepare for:
Basis for setting targets Timeframe to cover entire national market and to reach targets Scope of priority products to be included Municipal and industrial & commercial waste? Product size restrictions (WEEE, packaging, tires, pesticides)? Business exemptions/de-minimis provisions “taking into account their status as small or medium-sized enterprises” Other specific requirements on producers (labelling, itemizing costs on invoices, communications, waste prevention) Waste management characteristics of the used priority products
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Keys lessons learned
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Key lessons learned You cannot simply copy and paste a collective management model from another country Need a solid Chilean fact base to ensure that the requirements of the regulations which follow the legislation are achievable Training and motivating citizens to properly sort priority products for separate collection is the key to success Most successful national programs build a common recycling “brand” Ensure that the regulations and collective system financing schemes encourage recycling program effectiveness and efficiency Regional programs provide economies of scale Test many different program elements to learn what works best in Chile
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What could be the next steps?
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Use these results to help define the best way of recycling in Chile
Next Steps? Develop mechanisms for cooperation between producers & municipalities Test different household collection techniques within AMUSA: Use of different containers for collecting recyclables door-to-door Increase the frequency of recycling collection Compare door-to-door collection with drop off points Collect recyclables from multi-family buildings Segregation of glass from other materials Audit the waste and the recycling streams Test recycling away-from-home: schools, offices, retail, public spaces Support these efforts with a strong promotion & education campaign Use these results to help define the best way of recycling in Chile
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Contact information Derek Stephenson Director Global Solutions Im Zollhafen 2-4 50768 Cologne, Germany Phone: Mobile:
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¡Muchas Gracias!
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