4.1 A. Prag, policy guidance from OECD work

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EXTENDED PRODUCER RESPONSIBILITY Andrew Prag, OECD Environment Directorate 18 June 2014 Towards guidance for policy makers

Transcript of 4.1 A. Prag, policy guidance from OECD work

Page 1: 4.1 A. Prag, policy guidance from OECD work

EXTENDED PRODUCER RESPONSIBILITY

Andrew Prag, OECD Environment Directorate

18 June 2014

Towards guidance for policy makers

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• The changing context since 2001

• What are we learning from case studies

• Initial emerging areas for policy guidance

Outline

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Changing context for EPR since 2001

2014

Intrinsic value of waste

International trade of waste

Globalisation of value chains and producersUrgency of waste

accumulation in non-OECD countries

Internet sales and new market opportunities

2001

More countries developing EPR

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Case studies currently feeding into the OECD review

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Some lessons from case studies

Increasing recycling rates

Cost transfers

Better recycling technologies

Competition and trade concerns

Free-riding

Leakage Low data quality and transparency

If concerns are adequately addressed in EPR policies

Main challenges Main achievements

Better recyclability

Not reducing overall waste

Consumer awareness

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10 areas for guidance emerging

Governance Economic Emerging issues

OverallEPR instruments tailored to specific product and country context

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10 areas for guidance emerging

Governance

Clear roles and responsibilities

Early and full consultations

Adequate transparency level

Economic

Multi-level competition assessmentClear performance targets & full cost recoveryEncouraging “DfE” and waste prevention

Emerging issues

Integrating the informal waste sector

Anticipating impacts of changing waste value

Free riding and ownership in new market conditions

OverallEPR instruments tailored to specific product and country context

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2.5m

Competition concerns:A level playing field… or is it?

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Need for regular policy assessments of multi-layered competition concerns

Seeking a balance between competition and a stable, predictable investment framework

Competition concerns on three levels

Product market impact

Competition among

PROs

Impacts on collection,

sorting, treatment markets

Competition concerns

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• Understand the role of informal and/or illegal actors EPR design should seek to provide greater

incentive than local materials markets Build on existing informal networks where

possible Provide strong regulation to eliminate harmful

practices and to ensure non-valuable waste is captured

Integrating the informal waste sector

• A challenge for OECD and non-OECD countries

UK Ghana

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• Recyclability and waste prevention as separate objectives

• Key policy challenges :– Globalised production – can one country’s EPR

make a difference to global design?– Differentiated fees and individual producer

responsibility: can they be cost effective and efficient?

Policy design should consider how differential fees can help to target individual producer recycling costs

International (and national!) co-ordination of policy where possible to maximise influence on product design

Encouraging design for environment

Collective responsibility: uniform fees

Individual financial responsibility: fully differentiated fees

Partly differentiated / modulated fees

Increasing strength of design change incentive

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10 areas for guidance emerging

Governance

Clear roles and responsibilities

Early and full consultations

Adequate transparency level

Economic

Multi-level competition assessmentClear performance targets & full costs recoveryEncouraging “DfE” and waste prevention

Emerging issues

Integrating the informal waste sector

Anticipating impacts of changing waste value

Free riding and ownership in new market conditions

OverallEPR instruments tailored to specific product and country context

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Anticipating new market conditions

• Internet and other new market outlets: ensuring EPR definitions and enforcement can capture new actors

• Increasing value of waste: – Reassessing need for EPR when waste streams reach

positive value – Beyond average value: understanding heterogeneity

in the waste stream– Considering how to support new ownership

structures (leasing and services) Need for continuous evaluation of the

environmental and social value of EPR policies and periodically assess scheme boundaries