What is EPR?

What is EPR?

According to the Organisation for Economic Cooperation and Development (OECD), Extended Producer Responsibility (EPR) is an environmental policy approach in which a producer’s responsibility for a product is extended to the post-consumer stage of a product’s life cycle. Its defining feature is the shift of financial and operational responsibility for end-of-life management away from municipalities and taxpayers and onto producers.

By moving responsibility upstream, EPR can, in principle, create incentives for producers to integrate environmental considerations into product and packaging design.

EPR has a long history

Its roots go back to producer-funded deposit return systems for beverage containers in the 1970s, which are widely recognised as the first practical application of EPR. In the 1990s, countries began adopting EPR policies for packaging, and in the 2000s, the EU implemented directives requiring EPR for Waste Electrical and Electronic Equipment (WEEE), batteries, accumulators, and vehicles, while also encouraging adoption for packaging. By 2011, the largest global EPR schemes covered:

  • electronics (35%)
  • packaging (17%)
  • vehicles (12%)
  • tyres (18%)

More recently, the EU’s 2019 Single-Use Plastics Directive has prompted further expansion of EPR to plastics-heavy products, including construction materials, textiles, electronics, fishing gear, and vehicles, many of which are commonly found in litter surveys.

How EPR has evolved and extended

While the OECD’s definition of EPR is widely regarded as a solid foundation, it’s important to note that EPR has evolved, and so have expectations. Historically, EPR schemes have been effective at mobilising resources for waste management, but they did not always create strong incentives for better product design or waste prevention.

Recognising this, Europe’s Circular Economy Act reframes EPR as more than a narrow waste-management tool: it positions EPR as a key enabler of circularity by ensuring the financing and infrastructure needed so that other circular-economy strategies, such as reuse, recycled content, eco-design, and improved material recovery, can be effectively implemented.

Since the first programmes were launched in Germany in 1991 and France in 1992, EPR has expanded globally and helped professionalise waste and resource management through the development of skilled Producer Responsibility Organisations (PROs). These institutions now operate robust data systems, technical capacity, and large-scale collection and recycling networks. They are well placed to support broader circular economy measures; however, it remains essential that EPR itself stays a distinct policy instrument and that other policy tools like reuse and recycled content targets be established through separate policy frameworks to maintain ambition, clarity, and accountability. When these policies fall under the umbrella of producer-run organisations, there is a risk that targets are weakened to maintain the status quo. Because PROs represent business interests, they cannot self-regulate their way into transformative change.

EPR’s unique value is its financing functionality; the stable, predictable funding stream that underpins all circular-economy performance. Positioned correctly, EPR functions as a resource-management instrument that supports closed loops, strengthens material sovereignty, and reduces environmental impacts, while other policy instruments set the ambition needed to deliver full circularity.

How EPR can be implemented

Like many public policy tools, EPR can be designed and implemented in different ways across jurisdictions, with differing scopes (financial and/or operational), governance models, and supporting policy instruments, each reflecting the specific objectives of governments, producers, and other stakeholders.

About Reloop’s EPR Toolbox

The EPR Toolbox is designed to support governments, regulators and producers in building and implementing EPR schemes that are fair, transparent and effective. It sets out the core components of strong EPR design while drawing on lessons from mature schemes to help emerging programmes avoid common pitfalls.

Because each jurisdiction has its own approach to cost allocation, institutional structure, and level of government involvement, the toolbox is deliberately adaptable and relevant for Europe, the U.S., Asia, Australia, and beyond.

Because effective EPR depends both on strong regulation and on well-designed delivery systems, the toolbox separates its core components into two categories, Operational and Policy.

This distinction helps clarify where public authorities must set direction and oversight, and where producers and PROs are responsible for implementation.

Back
to top