Myth-busting Deposit return schemes & packaging reuse: separating hype from reality

Deposit return schemes (DRS) and packaging reuse systems are experiencing a surge of policy attention and startup activity across North America. Oregon became the first US state to implement a bottle deposit in 1971, yet more than fifty years later, fewer than a dozen states operate container deposit programs, and national legislation remains elusive. Meanwhile, a new generation of founders is building reuse and refill platforms that promise to eliminate single-use packaging entirely. The gap between the rhetoric surrounding these systems and their actual performance is significant, and closing it requires confronting several deeply embedded misconceptions.

Why It Matters

North America generates approximately 82 million metric tons of packaging waste annually, of which only 28 to 33% is recycled. Beverage containers, the primary target of deposit return schemes, represent roughly 15% of municipal solid waste by volume but a disproportionate share of litter. In US states without deposit programs, beverage container recycling rates average 24%. In states with deposits, rates average 63 to 84%, depending on deposit value and program design. This performance gap represents both an opportunity and a source of confusion about what DRS can and cannot accomplish.

The regulatory landscape is shifting rapidly. Canada has implemented or is expanding DRS programs in every province, with British Columbia and Alberta operating mature systems that achieve return rates above 80%. In the United States, Connecticut, Delaware, and several other states have passed or are considering new deposit legislation. At the federal level, the Break Free From Plastics Pollution Act has been reintroduced in multiple congressional sessions, though passage remains uncertain. Extended producer responsibility (EPR) laws enacted in Maine, Oregon, Colorado, and California create overlapping or complementary frameworks that founders must navigate.

For founders building in this space, understanding what actually drives collection rates, what reuse systems truly cost at scale, and where the genuine unit economics work is essential to raising capital, designing viable products, and avoiding the pitfalls that have consumed numerous well-funded predecessors.

Key Concepts

Deposit Return Schemes (DRS) charge consumers a refundable deposit at the point of sale for beverage containers. When consumers return containers to designated collection points (reverse vending machines, retail take-back, or depot locations), the deposit is refunded. The system creates a direct financial incentive for return, separating high-value recyclable materials from mixed waste streams and dramatically improving both collection rates and material quality.

Packaging Reuse Systems replace single-use containers with durable alternatives that are collected, washed, and redistributed. Models range from standardized container pools (as operated by IFCO and Tosca for commercial food distribution) to consumer-facing platforms where customers return reusable cups, takeout containers, or delivery packaging at designated drop-off locations or through reverse logistics networks.

Return Rate measures the percentage of containers sold that are returned through the system. It is the single most important performance metric for DRS, directly determining environmental impact, material recovery value, and system financial viability. Mature, well-designed programs achieve return rates of 85 to 95%, while poorly designed or newly launched programs may achieve only 50 to 70%.

Reuse Cycle Count measures how many times a reusable container completes a use-wash-redistribute cycle before being retired. Higher cycle counts spread the embodied carbon and cost of durable containers across more uses, improving both environmental and economic performance. Most reuse systems require containers to complete a minimum of 15 to 25 cycles to break even on carbon versus single-use alternatives.

Myths vs. Reality

Myth 1: Deposit return schemes are too expensive to implement and always raise consumer prices

Reality: The net cost of DRS to consumers is close to zero, because the deposit is refunded upon return. System operating costs, typically $0.01 to $0.03 per container, are funded through unredeemed deposits, material sales revenue, and producer fees. In British Columbia, where the Encorp Pacific system handles 1.3 billion containers annually, the net cost to producers averages CAD $0.02 per unit, a fraction of the marketing budgets attached to the same products. A 2024 analysis by the Container Recycling Institute found that US states with deposit programs spend an average of $0.015 per container on system operations, compared to $0.008 to $0.012 per container for curbside recycling collection of the same materials, but DRS achieves return rates 2 to 3 times higher and delivers significantly cleaner material streams commanding 40 to 60% higher commodity prices. The "too expensive" framing typically originates from beverage industry lobbying that conflates gross system costs with net costs after accounting for material revenues and unredeemed deposits.

Myth 2: Curbside recycling makes deposit return schemes redundant

Reality: Curbside recycling and deposit return schemes serve fundamentally different functions and achieve fundamentally different outcomes. Curbside systems are designed for broad material collection from households but suffer from contamination rates of 15 to 25%, which degrades material quality and limits end markets. DRS collects specific container types at high purity, with contamination rates typically below 2%. In Oregon, which operates both curbside recycling and one of the nation's most established bottle deposit programs, beverage container recycling rates through the deposit system consistently exceed 80%, while beverage containers placed in curbside bins are recovered at rates below 40%. The materials also follow different paths: DRS-collected PET bottles achieve food-grade recycled content certification at rates above 70%, while curbside-collected PET achieves food-grade certification at rates below 30% due to contamination. Michigan's deposit system, which charges $0.10 per container (the highest in the US), achieves return rates of 89%, demonstrating that deposit value directly correlates with participation.

Myth 3: Reuse systems always have a lower carbon footprint than single-use alternatives

Reality: The carbon math for reuse is highly conditional. A reusable container must complete enough cycles to offset its higher manufacturing footprint and the emissions associated with collection, washing, and redistribution logistics. A peer-reviewed lifecycle assessment published in the Journal of Cleaner Production (2024) found that reusable takeout containers in urban North American markets broke even on carbon at approximately 12 to 18 cycles for lightweight polypropylene systems and 25 to 40 cycles for stainless steel or glass alternatives. In practice, many consumer-facing reuse platforms struggle to achieve average cycle counts above 8 to 10 due to container loss, breakage, and consumer non-return. Loop, the high-profile reuse platform launched by TerraCycle in partnership with major CPG brands, paused its US direct-to-consumer operations in 2023 after reporting average cycle counts well below break-even thresholds and per-container logistics costs that exceeded the value of the packaging being replaced. The lesson for founders: reuse systems must be designed around logistics density and return rate economics first, with environmental claims validated by actual operational data rather than theoretical models.

Myth 4: Technology will solve collection and return logistics without behavior change

Reality: Reverse vending machines (RVMs), smart bins, and app-based tracking systems improve convenience but do not substitute for the fundamental behavioral incentive that drives return rates: the deposit value. Norway's Infinitum system, widely regarded as the global benchmark with a 97% return rate for PET bottles, succeeds because it combines a meaningful deposit (NOK 2 to 3, approximately $0.20 to $0.30 USD), ubiquitous RVM infrastructure (over 14,000 machines nationwide), and a cultural norm reinforced by decades of consistent operation. Technology-first approaches that minimize deposit values or rely on gamification rather than financial incentives consistently underperform. Alberta's Beverage Container Management Board tested reduced-deposit categories and found that every $0.05 reduction in deposit value correlated with a 12 to 15 percentage point decline in return rates. Founders building collection technology should treat the deposit incentive as the primary driver and technology as an enabler, not a replacement.

Myth 5: Deposit return schemes only work for beverage containers

Reality: While beverage containers represent the most common DRS application, the model has been successfully extended to other product categories. British Columbia's program covers all beverage containers plus milk containers and certain non-beverage containers. In the EU, deposit schemes are being expanded to include electronics batteries, with the revised EU Battery Regulation mandating collection and recycling targets that effectively require deposit-like incentive structures. Maine's EPR for packaging law creates a framework that could evolve toward deposit-type mechanisms for additional packaging categories. For founders, the DRS model of financial incentive, standardized collection, and high-purity material recovery is a design pattern applicable wherever return rates for specific material streams need to exceed what voluntary or curbside systems can deliver.

Key Players

Established Operators

TOMRA manufactures reverse vending machines deployed in over 80 markets globally, processing approximately 45 billion containers annually. Their technology platform includes automated sorting, digital deposit tracking, and data analytics for system operators.

Encorp Pacific operates British Columbia's deposit return system, handling 1.3 billion containers per year with a return rate consistently above 80%. Their model of producer-funded, independently operated collection infrastructure is widely studied as a template for new programs.

Infinitum manages Norway's deposit system, achieving a 97% PET bottle return rate through a combination of high deposit values, extensive RVM infrastructure, and decades of operational refinement.

Emerging Startups

Dispatch Goods operates a reusable takeout container service in San Francisco and the Bay Area, using standardized stainless steel containers collected through a network of return points and delivery driver pickups. Their model targets the high-density urban restaurant delivery market where logistics costs per container are minimized.

Muuse provides reusable cup and container systems for corporate campuses, universities, and food service operations, using RFID tracking to manage container inventory and measure return rates. Their B2B model avoids the consumer behavior challenges that have undermined direct-to-consumer reuse platforms.

Re:Dish operates in the New York City market with a reusable restaurant container system integrated directly into delivery app workflows, addressing the last-mile return logistics problem through partnerships with delivery platforms.

Action Checklist

• Evaluate the regulatory landscape in target markets for pending DRS legislation and EPR requirements
• For reuse ventures, validate unit economics at projected cycle counts using actual operational data, not theoretical models
• Design return incentives with deposit values sufficient to drive target return rates (minimum $0.10 for beverage containers based on US data)
• Prioritize logistics density over geographic coverage in early reuse system deployment
• Conduct or commission lifecycle assessments using ISO 14040/14044 methodology with real-world operational parameters
• Engage with producer responsibility organizations and existing DRS operators as potential distribution and collection partners
• Build data infrastructure to track container-level cycle counts, return rates, and loss rates from day one

FAQ

Q: What deposit value is needed to achieve return rates above 80%? A: US data consistently shows that deposit values of $0.10 or higher are necessary to achieve return rates above 80%. States with $0.05 deposits (such as Connecticut at $0.05 prior to its 2024 increase) typically achieve return rates of 50 to 60%. Michigan, with a $0.10 deposit, achieves 89%. International evidence from Norway ($0.20 to $0.30 equivalent) and Germany ($0.27 equivalent) confirms that higher deposits drive higher returns, with diminishing returns above approximately $0.25.

Q: How many reuse cycles does a container need to be environmentally preferable to single-use? A: For lightweight polypropylene containers in urban markets with efficient washing infrastructure, the break-even point is typically 12 to 18 cycles. For heavier materials (glass, stainless steel), the range is 25 to 40 cycles. These figures assume washing facilities operating on grid electricity with average North American carbon intensity. Systems powered by renewable energy or located in low-carbon grids can achieve break-even at lower cycle counts. The critical variable is the actual return rate: if 20% of containers are lost per cycle, the average cycle count is mathematically capped at approximately 5, making the system environmentally worse than single-use.

Q: What are the biggest risks for founders entering the packaging reuse space? A: The three primary risks are: (1) container loss rates exceeding financial and environmental break-even thresholds, which has undermined multiple well-funded ventures; (2) washing and reverse logistics costs that scale linearly rather than achieving the economies of scale projected in business plans; and (3) consumer behavior inertia, particularly the inconvenience of returning containers, which limits adoption in all but the most motivated customer segments. Founders should design for these risks explicitly, with business models that remain viable at conservative return rate assumptions (60 to 70%) rather than optimistic projections (90%+).

Q: Can DRS and EPR coexist in the same jurisdiction? A: Yes, and this is increasingly the norm. British Columbia, Oregon, and Maine all operate both DRS for beverage containers and broader EPR frameworks for packaging. The key design question is how costs and material flows are allocated between systems to avoid duplication and ensure that high-value materials captured by DRS are not double-counted in EPR recycling rate calculations. Founders and system designers should engage with both DRS and EPR program administrators early to understand how their products and services fit within overlapping regulatory frameworks.

Sources

• Container Recycling Institute. (2024). Bottle Bills and Curbside Recycling: A Comparative Analysis of Collection Costs and Performance. Culver City, CA: CRI.
• Encorp Pacific Canada. (2025). Annual Report 2024: British Columbia Deposit Return System Performance Data. Vancouver: Encorp Pacific.
• Infinitum. (2025). Annual Report 2024: Norwegian Deposit System Performance and Return Rate Data. Oslo: Infinitum AS.
• Coelho, P.M., Corona, B., & Worrell, E. (2024). "Reusable vs. Single-Use Packaging: A Lifecycle Assessment of Takeout Container Systems in North American Urban Markets." Journal of Cleaner Production, 442, 140892.
• Beverage Container Management Board, Alberta. (2024). Deposit Value and Return Rate Correlation: Program Data Analysis 2019-2024. Edmonton: BCMB.
• US EPA. (2025). Advancing Sustainable Materials Management: 2023 Fact Sheet. Washington, DC: United States Environmental Protection Agency.
• Reloop Platform. (2025). Global Deposit Return Systems: Comparative Performance Analysis. Brussels: Reloop.