Regional spotlight: Extended Producer Responsibility (EPR) in China — what's different and why it matters

China generated 235 million tonnes of municipal solid waste in 2024, making it the world's largest waste-producing nation by absolute volume, yet its formal Extended Producer Responsibility framework covers only four product categories compared to the EU's 15-plus mandatory EPR schemes. This gap between waste generation scale and policy coverage defines both the challenge and the opportunity for sustainability professionals operating in or sourcing from China. Understanding how China's EPR system diverges from European and North American models is essential for multinational companies navigating compliance, for investors evaluating circular economy ventures, and for policymakers studying alternative implementation pathways.

Why It Matters

China's EPR landscape sits at the intersection of three forces that make it fundamentally different from Western counterparts. First, the sheer scale of production: China manufactures approximately 60% of the world's consumer electronics, 50% of global textile output, and 30% of global plastics production (UNEP, 2025). Any EPR policy applied to Chinese manufacturing has supply chain implications that radiate across every major consumer market.

Second, China's regulatory architecture is centralized in design but decentralized in execution. The State Council and the Ministry of Ecology and Environment (MEE) set national EPR frameworks, but provincial and municipal governments retain significant discretion over implementation timelines, collection targets, and enforcement intensity. This creates a patchwork of compliance environments within a single national jurisdiction, a dynamic unfamiliar to practitioners accustomed to the relatively uniform application of EPR directives across EU member states.

Third, China's informal waste sector, estimated at 3 to 5 million workers engaged in collection, sorting, and recycling of discarded materials, operates alongside formal EPR channels. The informal sector handles an estimated 30 to 40% of recyclable materials by weight (World Bank, 2024), creating both competition and complementarity with producer-funded take-back systems. Any EPR framework that ignores this reality risks displacing livelihoods without improving environmental outcomes.

Key Concepts

The Four-Category EPR Framework

China's current EPR system, formalized through the 2017 Extended Producer Responsibility Implementation Plan issued by the State Council, mandates producer responsibility for four product categories: electrical and electronic equipment (EEE), lead-acid batteries, packaging materials, and end-of-life vehicles. Each category operates under distinct regulatory instruments, collection mechanisms, and compliance targets.

For EEE, the Waste Electrical and Electronic Equipment (WEEE) Recycling Fund, established in 2012, requires manufacturers and importers to pay per-unit levies into a central fund that subsidizes licensed dismantling enterprises. The fund collected approximately RMB 5.2 billion ($720 million) in 2024 and disbursed subsidies to 109 licensed recyclers processing 87.6 million units of waste electronics (MEE, 2025). This fund-based model differs fundamentally from the EU's WEEE Directive, where producers are individually or collectively responsible for financing collection and recycling of their own branded products.

Fund-Based vs. Individual Producer Responsibility

The critical distinction between China's EPR model and EU or Canadian approaches lies in the degree of individual producer accountability. In the EU, producers join Producer Responsibility Organizations (PROs) that allocate costs based on the quantity and recyclability of products each company places on the market, creating direct financial incentives for design-for-recyclability. In China's fund-based system, all producers in a category pay a flat per-unit levy regardless of product design, material composition, or actual end-of-life recyclability. A television manufacturer using easily separable components pays the same levy as one using glued, mixed-material assemblies.

This flat-levy structure eliminates the eco-modulation incentive that drives design improvements in European EPR systems. The MEE acknowledged this limitation in its 2024 policy review and announced plans to pilot differentiated fee structures for electronics by 2027, with levy rates varying by product category, hazardous substance content, and recycled material usage (MEE, 2025).

Pilot Programs and Provincial Variation

Beyond the four mandated categories, China has launched EPR pilot programs in 15 provinces covering additional waste streams including textiles, express delivery packaging, and agricultural film. Shanghai's pilot for express delivery packaging EPR, launched in 2023, requires logistics companies including SF Express, ZTO Express, and JD Logistics to establish collection points at distribution centers and fund the recycling of cardboard and plastic packaging. In its first full year of operation, the Shanghai pilot achieved a 42% collection rate for e-commerce packaging, compared to a national average below 20% (Shanghai Municipal Bureau of Ecology and Environment, 2025).

Guangdong Province has taken a different approach, establishing a textile EPR pilot in the Pearl River Delta manufacturing cluster that targets pre-consumer textile waste from garment factories rather than post-consumer clothing. This producer-oriented approach reflects the reality that China's textile waste challenge is concentrated at the manufacturing stage: an estimated 26 million tonnes of textile waste are generated annually in Chinese factories, of which 15 million tonnes are pre-consumer offcuts and defective materials (China National Textile and Apparel Council, 2024).

What's Working

Electronics Recycling Infrastructure Scale

China's WEEE fund has successfully scaled formal electronics recycling infrastructure from 43 licensed facilities in 2012 to 109 in 2024, with combined annual processing capacity of 160 million units. Formal sector collection of waste electronics reached 87.6 million units in 2024, representing approximately 20% of estimated annual WEEE generation. While this rate lags behind the EU's 45% WEEE collection target, the absolute volume of formally processed electronics exceeds any single EU member state's throughput.

GEM Co., Ltd., China's largest electronics recycler, processed 5.2 million tonnes of e-waste, end-of-life vehicles, and batteries in 2024, recovering approximately 300,000 tonnes of copper, cobalt, nickel, and rare earth elements. GEM operates 16 recycling parks across China and has invested RMB 12 billion ($1.66 billion) in urban mining infrastructure since 2015, demonstrating that China's EPR-adjacent industrial policy can catalyze world-scale recycling enterprises (GEM Annual Report, 2024).

Lead-Acid Battery Collection

China's lead-acid battery EPR system achieves one of the highest collection rates of any EPR-covered product globally. The combination of intrinsic material value (lead prices averaged $2,150 per tonne in 2024), regulatory mandates requiring battery retailers to accept returns, and an extensive informal collection network produces an estimated collection rate of 95 to 98% by weight. The formal recycling sector, led by companies such as Camel Group and Tianneng Power International, operates smelting facilities that recover 97% of lead content from used batteries. This success, however, is driven primarily by commodity economics rather than EPR policy design: lead-acid batteries would be collected at high rates with or without EPR mandates due to their scrap value.

Express Packaging Pilot Results

The Shanghai express delivery packaging pilot demonstrates that targeted EPR interventions can achieve rapid results in China's logistics sector. JD Logistics deployed 120,000 reusable packaging containers across its Shanghai fulfillment network in 2024, each designed for a minimum of 50 use cycles. The company reported that reusable containers reduced packaging material consumption by 38% per shipment and lowered per-package logistics costs by RMB 0.8 ($0.11) after the fifth reuse cycle (JD Logistics Sustainability Report, 2025). SF Express implemented a parallel program using biodegradable mailer bags made from PLA (polylactic acid) sourced from Anhui BBCA Biochemical, achieving 100% compostability certification under China's GB/T 20197 standard.

What's Not Working

Informal Sector Displacement Without Integration

The expansion of formal EPR-funded recycling infrastructure has created friction with China's informal waste sector. Licensed recycling facilities receive government subsidies tied to documented processing volumes, giving them a cost advantage over informal operators who lack permits and cannot access fund disbursements. In Guangdong and Zhejiang provinces, informal WEEE collection rates declined by an estimated 15 to 20% between 2020 and 2024 as formal channels expanded, but this displacement has not been accompanied by worker transition programs or livelihood support (Tsinghua University Circular Economy Research Center, 2025).

The environmental consequences are mixed. Formal recyclers achieve higher material recovery rates and better control of hazardous substances, but informal operators often achieve higher overall collection rates due to their door-to-door service model and willingness to accept smaller quantities. A study by the Basel Convention Regional Centre for Asia and the Pacific found that cities with strong informal collection networks achieved 25 to 35% higher overall WEEE collection rates than cities relying exclusively on formal EPR channels.

Packaging EPR Enforcement Gaps

China's packaging EPR requirements remain largely voluntary outside pilot zones. The 2020 revision to the Law on the Prevention and Control of Environmental Pollution by Solid Waste included provisions for packaging reduction, but implementing regulations have been slow to materialize. E-commerce platforms including Alibaba, Pinduoduo, and Douyin's e-commerce division have established packaging reduction targets voluntarily, but compliance monitoring is minimal. A 2024 audit by the China Consumers Association found that 62% of sampled e-commerce shipments used excessive packaging (defined as void fill exceeding 30% of package volume), with compliance varying significantly across product categories and seller tiers.

Eco-Modulation Absence

The flat-levy structure of China's WEEE fund fails to incentivize design for recyclability. Products with modular, easily disassembled designs pay the same per-unit levy as products with glued batteries, mixed-material housings, and proprietary fasteners. Analysis by the China Household Electrical Appliances Association found that the average disassembly time for Chinese-manufactured smartphones increased by 18% between 2019 and 2024, moving in the opposite direction from circular design principles, partly because EPR fees create no financial differentiation based on recyclability.

Key Players

Established Companies

GEM Co., Ltd.: China's largest urban mining and recycling enterprise, processing 5.2 million tonnes annually across 16 recycling parks, with particular strength in battery materials and precious metals recovery.

Camel Group: Dominant player in lead-acid battery recycling with 95%+ recovery rates, operating six smelting facilities with combined annual processing capacity of 400,000 tonnes.

JD Logistics: Leading implementation of reusable packaging systems with 120,000 containers deployed in Shanghai, targeting 50% reduction in single-use packaging by 2028.

Startups and Innovators

Aihuishou (AHS Recycle): Online-to-offline platform for consumer electronics trade-in and recycling, processing over 30 million devices annually through 1,000+ collection points and partnerships with Apple, Samsung, and Xiaomi.

Feiniu Environmental Technology: Shenzhen-based startup developing AI-powered sorting systems for mixed WEEE streams, achieving 95% material identification accuracy at processing speeds of 120 items per minute.

Yiliu Environmental: Specializing in textile waste recycling in the Pearl River Delta, converting pre-consumer textile offcuts into recycled polyester staple fiber at a capacity of 80,000 tonnes per year.

Investors and Funders

Hillhouse Capital: Major investor in circular economy infrastructure including a $200 million investment in AHS Recycle's Series D round, reflecting confidence in China's consumer electronics recycling market growth.

China Green Development Fund: Government-backed fund supporting EPR infrastructure development with RMB 10 billion ($1.38 billion) in committed capital across waste management, recycling technology, and circular design ventures.

International Finance Corporation (IFC): Active in financing Chinese recycling enterprises, with $150 million in commitments to solid waste management projects across six provinces since 2022.

EPR Coverage and Performance Comparison

Metric	China	EU	United States
Product categories covered	4 mandatory + 15 pilots	15+ mandatory	State-level, varies (5-12)
WEEE collection rate	~20% formal	45% target (avg 39%)	~15-25% (state dependent)
Lead-acid battery collection	95-98%	99%	99%
Packaging EPR	Pilot phase	Mandatory (PPWD revision)	5 states enacted
Eco-modulation	Absent (piloting 2027)	Active in 18 member states	Limited
Informal sector role	30-40% of recycling	Minimal	Minimal
Annual WEEE fund revenue	$720M	Varies by PRO	N/A (no federal fund)

Action Checklist

• Map your product categories against China's four mandated EPR streams and 15 provincial pilot programs to identify current and upcoming compliance obligations
• Audit per-unit levy exposure for electronics, batteries, packaging, and vehicles sold into the Chinese market and model costs under anticipated eco-modulated fee structures
• Engage with provincial environmental bureaus in key manufacturing regions (Guangdong, Zhejiang, Jiangsu) to understand local EPR pilot timelines and requirements
• Evaluate partnership opportunities with licensed recyclers such as GEM or AHS Recycle to demonstrate supply chain circularity to Chinese regulators and global stakeholders
• Assess design-for-recyclability improvements now, ahead of China's planned eco-modulation pilot in 2027, to capture first-mover cost advantages
• Develop a stakeholder engagement strategy that accounts for informal waste sector dynamics, particularly for operations in cities where informal collection remains dominant
• Monitor the Shanghai express packaging EPR pilot outcomes as a leading indicator for national packaging EPR requirements likely to formalize by 2028

FAQ

Q: How does China's EPR fund model compare to EU Producer Responsibility Organizations? A: China's centralized fund model collects flat per-unit levies from all producers in a category and redistributes subsidies to licensed recyclers based on documented processing volumes. EU PROs typically allocate costs to individual producers based on the quantity and type of products placed on the market, with eco-modulated fees that reward design for recyclability. China's model is administratively simpler but lacks the individual producer accountability and design incentives built into EU systems. The MEE plans to pilot eco-modulated levies for electronics by 2027, which would move China's system closer to EU practice.

Q: What compliance risks do multinational companies face under China's EPR framework? A: The primary risks are: unexpected levy increases as China expands EPR coverage to new product categories (textiles and agricultural film are likely next); provincial pilot programs creating compliance requirements in specific regions before national mandates take effect; and reputational exposure from informal sector supply chain connections. Companies sourcing from or selling into China should maintain a regulatory monitoring function focused on MEE announcements and provincial environmental bureau directives.

Q: How should companies account for China's informal waste sector in their EPR strategy? A: Ignoring the informal sector creates both operational and reputational risks. Companies should: map informal collection channels in their key operating regions to understand actual end-of-life flows for their products; evaluate partnerships with organizations like AHS Recycle that bridge formal and informal channels; and support industry initiatives that integrate informal workers into formal recycling systems rather than displacing them. The World Bank's 2024 assessment recommends that EPR programs in developing economies explicitly incorporate informal sector transition plans.

Q: Is China likely to adopt mandatory packaging EPR nationally? A: Yes, based on current policy trajectory. The 2020 Solid Waste Law amendments established the legal foundation for packaging EPR, and the Shanghai pilot has generated positive data on collection rates and cost efficiency. The MEE's 14th Five-Year Plan for Solid Waste Management (2021 to 2025) identified packaging EPR as a priority policy instrument. National mandatory packaging EPR requirements are anticipated by 2028 to 2029, likely starting with e-commerce packaging and expanding to food and beverage packaging subsequently.

Sources

• United Nations Environment Programme. (2025). Global Waste Management Outlook: China Country Profile. Nairobi: UNEP.
• World Bank. (2024). What a Waste 3.0: Informal Sector Integration in Solid Waste Management. Washington, DC: World Bank Group.
• Ministry of Ecology and Environment, People's Republic of China. (2025). Annual Report on the Implementation of Extended Producer Responsibility for Electrical and Electronic Equipment. Beijing: MEE.
• Shanghai Municipal Bureau of Ecology and Environment. (2025). Express Delivery Packaging EPR Pilot Program: First-Year Performance Review. Shanghai: SMBEE.
• China National Textile and Apparel Council. (2024). Textile Industry Waste Generation and Recycling Report. Beijing: CNTAC.
• GEM Co., Ltd. (2024). Annual Report 2024: Urban Mining and Circular Economy Operations. Shenzhen: GEM Co.
• JD Logistics. (2025). Sustainability Report 2024: Packaging Innovation and Circular Supply Chain. Beijing: JD Logistics.
• Tsinghua University Circular Economy Research Center. (2025). Informal Sector Dynamics Under Expanding EPR Coverage: Evidence from Guangdong and Zhejiang. Beijing: Tsinghua University Press.