Table of Contents

1. Key Highlights:
2. Introduction
3. Why California’s Choice of a Single PRO Is Significant
4. Who Is Landbell USA and What Will It Do as the PRO?
5. Defining the “Producer” and the Scope of Covered Products
6. Financing the Program: Eco‑Modulated Fees and the Economics of Compliance
7. Operational Elements: Collection, Sorting, Reuse, Repair and Recycling
8. Immediate Compliance Steps for Producers: What to Do Before July 1, 2026
9. How California’s Model Compares With New York, Washington and the EU
10. Practical Implications for Brands, Retailers and Importers
11. Technology, Infrastructure and the Recycling Market: Capacity Gaps and Investment Needs
12. Opportunities for the Secondhand, Repair and Local Economies
13. Risks and Unintended Consequences to Watch
14. Consumer Behavior and Local Government Roles
15. Looking Ahead: Timelines, Enforcement and the Path to Convergence
16. Case Studies and Real‑World Examples
17. Strategic Choices for Producers: Redesign, Collaborate or Pay?
18. How to Prepare a Compliance Roadmap: A Practical Checklist
19. Conclusion
20. FAQ

Key Highlights:

• CalRecycle selected Landbell USA on February 27, 2026 to operate California’s textile extended producer responsibility (EPR) program under SB 707; producers must register with the PRO by July 1, 2026.
• The PRO will design statewide, “free and convenient” collection, manage sorting, reuse, repair and recycling pathways, and set eco-modulated fees based on product design characteristics that affect end‑of‑life outcomes.
• California’s move reflects accelerating global adoption of textile EPR: New York and Washington pursue state-level frameworks and the European Union requires Member States to implement textile and footwear EPR by 2027–2028, with several countries already operating schemes.

Introduction

California’s appointment of Landbell USA as the official Producer Responsibility Organization (PRO) for textiles under the Responsible Textile Recovery Act marks a turning point for how apparel, footwear and other textile products will be managed at end of life in the United States. That administrative choice triggers concrete obligations for companies that manufacture, import or sell covered textile items into the state: registration deadlines, new fees tied to product design, transparency and data reporting obligations, and participation in a statewide collection and recovery system. The decision is not an isolated regulatory curiosity. It occurs amid parallel legislative and policy activity in New York, recurring proposals in Washington State, and a clear mandate from the European Union requiring national textile EPR programs. Producers operating in—or selling into—multiple jurisdictions now face a patchwork of rules that will shape product design, supply chains and the business economics of textiles for years to come.

This article explains what Landbell USA’s selection means, breaks down the practical steps producers must take, compares California’s approach to other U.S. and European initiatives, and analyzes operational, legal and commercial implications. It also outlines short‑term actions companies should prioritize to limit compliance risk and to position products and business models advantageously under eco‑modulated fee systems.

Why California’s Choice of a Single PRO Is Significant

California’s Responsible Textile Recovery Act tasked CalRecycle with selecting a PRO to develop and operate the state’s textile EPR program. On February 27, 2026 CalRecycle designated Landbell USA to fulfill that role. The selection matters for three reasons.

First, it creates a centralized operational and administrative interface for regulated producers. Producers will not be able to rely on fragmented municipal programs alone; they must engage with a state‑level system that sets standards, collects fees, and reports performance metrics.

Second, the PRO model shifts costs from municipalities and taxpayers to producers. Rather than municipal budgets funding collection and disposal, producers will finance collection networks, reuse and recycling operations, and program administration through membership and eco‑modulated fees.

Third, the appointment accelerates implementation: statutory milestones now have concrete deadlines. Producers must register by July 1, 2026; the PRO must complete a needs assessment by March 1, 2027 and craft program plans and budgetary recommendations that will determine fee structures. Those timelines compress the window for companies to audit portfolios, forecast costs, and redesign products to reduce fees.

The selection also sets a practical precedent for how U.S. states may implement textile EPR—favoring a single designated PRO model rather than multiple competing organizations. That structure can deliver coordinated nationwide infrastructure investments and data uniformity, but it concentrates operational responsibility and gives the PRO substantial influence over service design and pricing.

Who Is Landbell USA and What Will It Do as the PRO?

Landbell USA is part of the Landbell Group, a multinational provider of EPR and product stewardship services with a footprint across multiple continents. The group operates PROs and compliance schemes in jurisdictions that include Austria, Germany, the Netherlands, the U.K., Italy, Spain, Canada (Ontario), Brazil, India and others. Its international experience spans packaging, electronics, batteries and—importantly—textiles.

As California’s PRO, Landbell USA has several specific responsibilities under SB 707:

• Register producers and maintain an auditable producer registry.
• Design and implement a statewide collection infrastructure that offers “free and convenient” options for consumers across urban, suburban and rural communities.
• Develop logistics and material‑handling protocols for collecting, sorting, repairing, reusing and recycling textiles, and minimize disposal.
• Propose and administer eco‑modulated fees: initial membership fees plus ongoing charges computed from producer sales volumes and product lifecycle characteristics that affect recyclability and durability.
• Track performance metrics, file annual reports with CalRecycle, and provide data that allow public oversight of compliance and program outcomes.
• Carry out stakeholder engagement, education and public outreach campaigns to encourage proper disposal and participation in collection programs.

The PRO’s operational remit is broad: it will make key determinations about collection modalities, partnerships with municipal governments, contracts with recyclers and sorters, and the degree to which the program prioritizes reuse or advanced recycling technologies. Landbell’s global relationships with collectors, sorters, and recyclers could help bootstrap California’s infrastructure, while its experience with eco‑modulation in other EPR programs will inform how fees are structured and enforced.

Defining the “Producer” and the Scope of Covered Products

SB 707 uses a hierarchy to identify which entities are responsible under the law. The primary “producer” is the manufacturer that owns or licenses the brand or trademark under which the covered product is sold or distributed in California. If no such entity is present, the statutory responsibility shifts down a defined chain: to the brand owner, then the exclusive licensee, then the importer into California, and finally the first person to sell or distribute the product in the state.

This hierarchical approach targets the economic actor best able to influence product design, labeling and upstream decisions. It also ensures California can hold someone in the supply chain accountable even when the original manufacturer is abroad or a product is sold under different distribution arrangements.

The statute’s definition of “covered products” is broad. It explicitly includes apparel, footwear, handbags, fabric window coverings, and even items such as napkins that have textile content. There are limited exclusions—certain personal protective equipment (PPE), reusable absorbent hygiene products, and single‑use paper towels or napkins may be carved out—but the net is wide enough to capture a sizeable portion of what brands, retailers and importers move into the California market.

Producers must therefore review product portfolios to determine whether specific SKUs fall under the program, and then establish mechanisms to capture sales volumes in California for fee calculations and data reporting. For multi‑channel sellers and direct‑to‑consumer e‑commerce businesses, this will require accurate geolocation of sales and returns, plus supply‑chain visibility to identify which entity is the regulated “producer.”

Financing the Program: Eco‑Modulated Fees and the Economics of Compliance

A central feature of California’s textile EPR program is the eco‑modulated fee structure. Fees will be charged to producers based on two broad factors: sales volume and environmental characteristics of the product that affect its end‑of‑life impact. Eco‑modulation is an incentive tool: products that are more durable, easier to repair, or more recyclable will attract lower fees than products with mixed fibers, significant contamination, or design features that impede recycling.

How eco‑modulation typically operates:

• Baseline fee per unit or per kilogram is established to cover average system costs.
• Product scores are calculated using objective criteria—fiber composition, mono‑ vs. mixed‑material construction, presence of non‑textile attachments, repairability ratings, ease of disassembly, and labeling that facilitates sorting.
• Fees are adjusted (modulated) up or down based on the product score. A high recyclability score reduces the fee; a low score increases it.

Eco‑modulation shifts economic incentives upstream. Manufacturers and designers who invest in mono‑material constructions, robust stitching, standard labeling for material recovery, and modular attachments that can be removed for recycling can expect reduced fees. Conversely, products with glued seams, mixed synthetic blends, and heavy non‑textile reinforcement will be costly to process and therefore attract higher fees.

Financial flows under SB 707 require producers to pay initial membership fees to the PRO and then ongoing charges determined by the PRO’s budget and the eco‑modulation formula. The PRO will use these funds to finance collection networks, sorting and processing facilities, administrative costs and outreach programs. CalRecycle will review and oversee the PRO’s activities through reporting and public workshops.

Producers should model several cost scenarios now: conservative, moderate and aggressive eco‑modulation assumptions. That modeling will inform product reengineering decisions, pricing strategies, and the potential need to pass costs to consumers. Smaller brands with low margins will need to evaluate whether to absorb fees, increase prices, or change product design to lower fees.

Operational Elements: Collection, Sorting, Reuse, Repair and Recycling

California’s statute requires the PRO to ensure “free and convenient” textile collection statewide. What that looks like in practice will depend on the needs assessment Landbell USA must conduct by March 1, 2027, but several established collection models provide useful reference points.

Common collection modalities include:

• Retailer and brand take‑back points: many large retailers offer drop‑off boxes or in‑store collection events. Extending and standardizing these programs provides predictable collection volumes.
• Municipal drop‑off hubs: partnership with cities and counties to co‑locate textile collection at existing recycling centers capitalizes on municipal infrastructure.
• Curbside collection pilots: some regions have piloted curbside textile pickup, often targeting bulky or high‑volume items, though curbside programs require specialized logistics and may be reserved for denser urban areas where economies of scale exist.
• Third‑party collectors and charities: donation networks and nonprofit organizations already operate extensive collection systems; integrating these actors into the PRO infrastructure can preserve existing reuse channels while improving data capture and verification.

Once collected, textiles must be sorted. Sorting differentiates reuse‑ready items from those suitable for mechanical or chemical recycling, and identifies materials requiring disposal. Successful sorting relies on trained staff, semi‑automated systems, and clear labeling to improve material classification. Investments in sorting capacity will be critical to divert materials from landfill and to feed recycling streams efficiently.

Processing pathways include:

• Reuse/resale: garments suitable for rewear can be sold in resale markets domestically or exported to destination markets, though careful oversight is required to avoid unintended social or environmental consequences of large export flows.
• Repair: repair networks—either independent repair shops or brand-operated repair services—extend product life and reduce material throughput.
• Mechanical recycling: shredding fibers and respinning into lower-grade textiles for insulation, stuffing, or industrial applications. Mechanical recycling is well‑established for certain materials but often results in downcycled products.
• Chemical recycling: fiber-to-fiber technologies that depolymerize synthetic or blended fibers into monomers or oligomers that can be reconstituted into new fibers. Chemical recycling offers closed-loop potential for difficult-to-recycle blends but is capital- and energy-intensive.
• Emerging technologies: enzymatic treatments, solvent-based separation, and other advanced processes aim to increase recovery yields for blended textiles.

A realistic program will combine multiple pathways. Reuse operations and repair deliver high circularity per item but capture only a portion of collected textiles. Mechanical and chemical recycling fill the remainder of the processing funnel. The PRO must balance investments across these routes, create market demand for recycled content, and ensure that downstream processors have predictable feedstock and quality.

Immediate Compliance Steps for Producers: What to Do Before July 1, 2026

The July 1, 2026 registration deadline is imminent relative to corporate planning cycles. Producers selling into California should prioritize the following actions immediately:

1. Determine whether you are a “producer” under the statute. Review corporate structure, brand ownership, licensing arrangements and import responsibilities to identify which legal entity must register.
2. Map product portfolios against the statutory definition of covered products. Identify SKUs that clearly fall under SB 707 and those that may be excluded. Pay special attention to non‑apparel textile items such as home textiles, fabric window coverings, rugs, and certain household disposables.
3. Establish systems to capture and report California sales data. Fee calculations will use sales volume in the state; producers must be able to attribute sales with geographic precision—this is particularly important for omnichannel retailers and cross‑border e‑commerce sales.
4. Catalogue product design attributes relevant to eco‑modulation. Create a material and design inventory for each SKU: fiber content by percentage, presence of mixed materials, fasteners and embellishments, repairability features, labels and wash tags, and potential for recycling.
5. Engage with Landbell USA and monitor the PRO’s public workshops. The first public informational workshop held by CalRecycle on April 7, 2026 will provide early signals on the needs assessment and the PRO’s process. Early engagement allows producers to influence program design and to anticipate fee structures.
6. Assess supply‑chain implications. If the regulated producer is a brand owner but manufacturing is outsourced overseas, coordinate with suppliers to collect material composition data and to redesign for recyclability where feasible.
7. Model financial impacts and product redesign scenarios. Quantify the potential fee exposure across product lines and evaluate whether design changes or pricing adjustments are required.
8. Prepare communications and consumer‑facing plans. Collection programs require consumer participation. Producers should prepare messaging and digital resources to inform customers about take‑back points, repair services, and proper disposal options.

Large brands may already have take‑back or circularity programs in place; such programs should be audited for alignment with the PRO’s requirements and for data capture compatibility. Small and mid‑sized producers should consider joining producer trade associations or representative organizations that can help manage administrative burdens.

How California’s Model Compares With New York, Washington and the EU

California’s PRO selection fits within a broader mosaic of textile policy activity in the U.S. and Europe. Comparing frameworks illuminates where harmonization may occur and where divergent approaches will impose additional compliance costs.

New York: The state introduced S3217A in January 2025 and carried it into the 2026 session. Its proposal would create an EPR framework covering apparel and textile articles, requiring producers to finance and operate statewide collection and authorizing penalties for noncompliance. A notable feature in New York’s discussion is a proposed phase‑in of a ban on textile disposal at solid waste facilities. A strict disposal ban would raise the compliance bar: producers would need to ensure sufficient recovery and recycling capacity to prevent landfill disposal, or alternatively invest in local processing capacity.

Washington State: HB 1420 introduced in January 2025 proposed a statewide textile EPR program; as of mid‑March 2026 the bill remained in committee and had not advanced to the governor. Washington has considered textile EPR before, and renewed attention in subsequent sessions is likely. The recurring proposals indicate that textile EPR will remain on the legislative agenda across U.S. states.

European Union: The EU has set binding timelines. Member States must transpose targeted revisions to waste legislation by June 17, 2027, and must establish EPR schemes for textiles and footwear by April 17, 2028. Several Member States already operate or have launched textile EPR systems:

• France: National scheme in place since 2008. Its early adoption provides a long‑running case study of integrating collection, sorting, and reuse channels.
• Netherlands: Launched its program in 2023, offering a more recent model of how national schemes can be designed to align with modern recycling technologies and circularity targets.
• Spain: Published a draft decree for public comment in 2025 and has continued to refine implementation details internally.

United Kingdom: The UK has not yet introduced a national textile EPR regime but policy signals in its Circular Economy Growth Plan and WRAP’s January 2026 “Blueprint for a UK Textiles EPR scheme” show strong interest. WRAP’s blueprint outlines recommendations for designing a UK program to stimulate circularity and green jobs.

Comparative implications:

• Timing and scope: EU deadlines force national implementation by mid‑ to late‑2027/2028, creating a dense timeline for European producers. U.S. states are moving at different paces; California’s program may become a de facto model for other states.
• Fee design: EU systems vary by country but often employ eco‑modulation; harmonization of scoring criteria could reduce compliance costs for multinational producers, but divergent national choices will create complexity.
• Enforcement: The severity of penalties and monitoring regimes will differ. Producers operating across jurisdictions must track regulatory variations and maintain robust compliance systems.

Companies with multinational footprints should expect growing pressure to harmonize data collection and product scoring systems across markets to avoid redundant audits and inconsistent fee assessments.

Practical Implications for Brands, Retailers and Importers

The introduction of textile EPR programs transforms several aspects of commercial operations.

Product design and sourcing: Eco‑modulated fees create a direct economic incentive to redesign products for durability, repairability and recyclability. Brands will increasingly prioritize mono‑material constructions, standardized fiber labeling and detachable components that simplify recycling.

Pricing and margins: Fees tied to sales volumes and product characteristics affect gross margins. Larger firms may be better positioned to absorb fees or negotiate supply‑chain efficiencies. Smaller firms face the dual challenge of limited margins and administrative costs; representative organizations may provide aggregation services to spread administrative burdens.

Supply chain transparency: Regulatory scrutiny demands accurate material composition data and traceable supplier attestations. Brands must require material disclosure and certification across supply chains, implement SKU‑level labeling systems, and maintain records for audits.

Logistics and inventory management: Collection systems and repair programs require reverse logistics. Companies that already operate take‑back programs will need to integrate with the PRO’s network and may be eligible for fee reductions if they demonstrate operational performance.

Resale and repair partnerships: Brands that build robust resale or repair services can extend product life and reduce fee exposure. Collaboration with third‑party resale platforms, independent repair networks, and community repair cafes will become a strategic consideration.

Data and reporting: Producers must implement systems to record California sales, track returned items entering the collection system, and submit performance data to the PRO. Investments in IT and compliance teams will be necessary.

Legal exposure: Misclassification of the regulated producer or failure to register can create penalties and reputational risk. Licensing arrangements must be scrutinized to determine which entity is the legally responsible actor.

Companies that act early—mapping exposure, engaging with Landbell USA, and redesigning vulnerable products—will limit surprise costs and can shape program rules in ways that reduce administrative friction.

Technology, Infrastructure and the Recycling Market: Capacity Gaps and Investment Needs

Achieving the goals set by California’s program requires substantial infrastructure. Sorting capacity, mechanical and chemical recycling facilities, repair networks, and quality control systems must scale to handle increased collection volumes.

Key infrastructure considerations:

• Sorting centers: High‑quality sorting improves feedstock quality for reuse and recycling. Investments in semi‑automated sorting lines and worker training will improve yields and reduce contamination.
• Recycling facilities: Capacity for both mechanical and chemical recycling is limited in many regions. Chemical recycling shows promise for mixed or synthetic textiles, but plants are expensive and require stable feedstock contracts.
• Market for recycled fibers: Recycled materials must be absorbed into manufacturing supply chains. Clear standards for recycled content, certification systems, and incentives for brands to use recycled fibers will ensure demand for processed textiles.
• Localized processing: Transport costs and emissions argue for regional processing hubs. California’s geographic size and dispersed population pose logistical challenges; rural collection must be paired with transport solutions that maintain economic viability.
• Export controls and markets: Where domestic recycling capacity is lacking, export of collected textiles to processing facilities abroad introduces regulatory and ethical complexities. Program design must consider traceability and environmental integrity of export flows.

Private capital can spur necessary investments. The PRO’s budget and long‑term contracts with processors influence bankability. Governments and public agencies can support infrastructure development through incentives, grants and permitting assistance. Producers may form consortia to finance recycling plants or pay premium fees that fund capacity expansions.

Opportunities for the Secondhand, Repair and Local Economies

Textile EPR programs deliberately emphasize reuse and repair as higher‑value recovery routes. That emphasis creates tangible opportunities.

Resale markets: Secondhand sales absorb reuse‑ready garments and can extend life cycles significantly. Successful resale businesses—from brick‑and‑mortar thrift stores to online marketplaces—benefit from increased feedstock made available through standardized collection.

Repair economy: Repair services become commercially viable when supported by steady volume and consumer awareness campaigns. Brands can integrate repair into service offerings—either in‑house or through partnerships—creating new revenue streams while reducing materials churn.

Green jobs: Sorting, repair, resale operations and recycling facilities generate local employment. Policy designers increasingly cite the potential for skilled jobs in circular economies as a social benefit of EPR programs.

Community organizations: Nonprofits and charitable groups can continue to play important roles, especially in collecting resale‑worthy items and providing repair skills training. The PRO must integrate community actors without displacing them and ensure that value flows back to local economies.

For entrepreneurs, the regulatory shift lowers barriers to entry in markets where feedstock uncertainty previously constrained investment. For established operators, scaling sorting and resale operations to meet PRO demands will be a priority.

Risks and Unintended Consequences to Watch

Well‑designed EPR programs can drive circularity, but policymakers and industry must be alert to pitfalls.

Export of waste: Increased collection without domestic processing capacity can lead to higher volumes of textile exports for disposal or low‑value reuse overseas. Programs must include controls, transparency and quality standards to avoid exporting environmental harm.

Downcycling dominance: Mechanical recycling often produces lower‑value materials. If markets for those downcycled materials do not exist, recycled output may still end up as low‑value products or waste. Creating demand for recycled fibers is as important as collecting them.

Administrative burdens on small producers: Smaller brands may lack resources to comply with registration, reporting and fee payment, creating competitive distortion. Representative organizations and fee aggregation models can mitigate inequities.

Perverse design incentives: If eco‑modulation criteria are not carefully crafted, producers might game scoring rules or prioritize low‑cost compliance measures that do not genuinely improve circularity. Transparent, evidence‑based scoring methodologies and periodic review will reduce gaming.

Social impacts: Large donations or resale supply floods can depress local secondhand markets in destination countries. Coordination with international partners and limits on low‑value exports can mitigate negative social impacts.

Enforcement complexity: Ensuring compliance, auditing data and enforcing penalties requires robust administrative capacity. CalRecycle and the PRO must allocate sufficient resources to monitoring and enforcement.

Policymakers and producers should track these risks, adapt program rules, and invest in complementary policies—like domestic processing incentives and market development for recycled fibers—to prevent unintended outcomes.

Consumer Behavior and Local Government Roles

Successful EPR systems depend on consumer participation. The PRO must pair collection infrastructure with clear communications so consumers know what to return and where.

Consumer engagement strategies include:

• Clear, simple messaging on accepted items and drop‑off locations.
• Incentives for participation—vouchers, discounts or loyalty benefits tied to take‑back programs.
• Labeling improvements that help consumers identify recyclable products.
• Partnerships with retailers to promote in‑store collection and repair services.

Local governments remain essential partners. Municipalities can host collection hubs, collaborate on outreach, and coordinate on contamination reduction. Integrating municipal recycling programs with the PRO’s system can preserve municipal investments and ensure residents have access to free and convenient collection.

Coordination also matters for illegal dumping and littering responses. Education campaigns and accessible drop‑off options reduce the likelihood that textiles enter mixed waste streams or are discarded improperly.

Looking Ahead: Timelines, Enforcement and the Path to Convergence

Key dates set by SB 707 and the PRO selection define near‑term milestones:

• February 27, 2026: CalRecycle selects Landbell USA as the PRO.
• April 7, 2026: CalRecycle public informational workshop on the needs assessment.
• July 1, 2026: Producer registration deadline with the PRO.
• March 1, 2027: PRO must complete a needs assessment, informing program design and budget.
• Subsequent years: PRO proposes fee schedules, rollouts of collection networks, and reporting frameworks; CalRecycle monitors and enforces compliance.

On the global stage, the EU requires Member States to adopt textile and footwear EPR schemes by April 17, 2028, with transposition of waste framework revisions by June 17, 2027. National programs in France, the Netherlands and Spain provide models of varied maturity.

For producers that sell in multiple markets, the coming years will require building harmonized internal systems: SKU‑level material data, sales localization, repair and take‑back integration, and investment in product redesign. While jurisdictional differences will persist, there is an emerging opportunity for cross‑border standards on eco‑modulation criteria, labeling and reporting that reduce compliance duplication.

Enforcement will be critical. CalRecycle and the PRO’s reporting requirements create audit trails. Producers should assume that regulators will require verifiable evidence of registration, fee payments, product attributes and participation in collection networks. Transparency and proactive engagement will reduce enforcement risk.

Case Studies and Real‑World Examples

Several existing corporate and national efforts illustrate how producers and jurisdictions can operationalize textile recovery.

Retailer take‑back pilots: Large retailers have operated voluntary take‑back programs for years. Brands such as H&M and Levi’s have offered collection points and resale or recycling initiatives. Those programs provide operational lessons: importance of clear labeling, need for consumer incentives, and challenges in processing mixed fibers.

France’s long‑running system: France’s national EPR for textiles, operating since 2008, offers a mature example of integrating collection, sorting and reuse. French experience shows the value of standardized collection containers, partnerships with charity networks, and incentives for reuse. It also highlights challenges in managing export flows and maintaining domestic processing capacity.

Chemical recycling demonstrations: Chemical recycling plants in Europe and Asia have piloted fiber recovery from synthetic blends. Although commercial scaling remains limited in some places, these demonstrations show technical feasibility and the need for steady feedstock to reach economic viability.

Community repair networks: Cities with active repair cultures—supported by nonprofit repair cafes and maker spaces—have shown how repair can become widely adopted when supported by training, public events and convenient services. Repair partnerships can materially reduce the number of garments entering recycling streams.

These examples suggest that a multi‑pronged approach—combining reuse, repair, mechanical and chemical recycling—works best in practice.

Strategic Choices for Producers: Redesign, Collaborate or Pay?

Producers face three strategic options, which are not mutually exclusive:

1. Redesign products to lower eco‑modulated fees. This requires investment in materials science and supply‑chain changes, but reduces long‑term fee exposure and can enhance brand sustainability credentials.
2. Collaborate through representative organizations or consortia to manage administrative burdens, fund shared recycling infrastructure, and negotiate favorable program terms.
3. Accept fees as a cost of doing business and focus on pricing strategies. Large producers with diversified portfolios may find this path viable, especially if compliance costs are predictable and can be passed through to consumers.

Each path has tradeoffs. Redesign can yield product differentiation and resilience to future regulation. Collaboration spreads costs and administrative burdens for smaller players. Fee absorption may be simplest in the short term but risks margin erosion and reputational criticism if environmental goals are not substantively pursued.

How to Prepare a Compliance Roadmap: A Practical Checklist

Producers should create a compliance roadmap with concrete milestones. A suggested checklist:

• Legal identification: Confirm which entity is the regulated producer under SB 707.
• Product inventory: List all SKUs, classify covered items, and collect material and construction data.
• Sales localization: Implement systems to track sales volumes in California and other jurisdictions with EPR rules.
• Registration: Register with Landbell USA by July 1, 2026.
• Data systems: Build or upgrade IT systems for reporting, tracking returned volumes and maintaining auditable records.
• Design audit: Prioritize high‑volume SKUs for redesign to improve recyclability and repairability.
• Partnerships: Identify potential partners for collection, repair, resale and recycling.
• Financial modeling: Project fee exposure under multiple eco‑modulation scenarios.
• Consumer communications: Prepare messaging and operational plans for collection and resale programs.
• Monitoring and governance: Assign internal ownership and governance for EPR compliance, including board‑level oversight for material changes in business strategy.

This roadmap is a starting point; the specifics will vary by company size, product mix and market exposure.

Conclusion

The selection of Landbell USA as California’s textile PRO operationalizes a major shift in regulatory responsibility for textile waste—from municipal governments and consumers to producers. The consequences are wide: fees tied to product design will influence what is made and how, service networks for collection and reuse will grow, and market signals will push producers toward designs that facilitate repair and recycling. For producers, the immediate task is clear: determine legal responsibility, register by July 1, 2026, and prepare for fee structures and reporting obligations that will shape business decisions for years. For policymakers and stakeholders, the challenge is to design programs that scale processing infrastructure, prevent unintended export of low‑value waste, and incentivize genuine circularity rather than superficial compliance.

The broader trajectory is unmistakable: textile EPR is becoming an established element of waste and materials policy worldwide. Companies that adapt quickly by aligning design, supply chain transparency, reverse logistics and consumer engagement will reduce compliance costs and gain advantage in a market where sustainability increasingly informs purchasing decisions and regulatory mandates.

FAQ

Q: Who must register with Landbell USA in California? A: The statute establishes a hierarchy. Primary responsibility lies with the manufacturer who owns or licenses the brand under which the covered product is sold in California. If no such entity is present, responsibility falls to the brand owner, exclusive licensee, the importer into California, or the first person to sell or distribute the product in the state. Entities should review contractual arrangements and supply‑chain relationships to identify the regulated producer and register by July 1, 2026.

Q: What products are covered by the textile EPR program? A: Covered products include a broad range of textile articles: apparel, footwear, handbags, fabric window coverings, and certain household textile items such as napkins with textile content. There are limited exclusions—certain PPE, reusable absorbent hygiene products, and single‑use paper towel/napkin products may be excluded. Producers should classify SKUs carefully to determine coverage.

Q: What are eco‑modulated fees and how will they be applied? A: Eco‑modulated fees adjust producer charges based on product design characteristics that affect environmental outcomes—durability, repairability, recyclability and material composition. Producers pay fees based on sales volume in California multiplied by an eco‑modulation factor. The PRO will propose specific scoring criteria and fee schedules as part of program budgeting.

Q: When must producers register and what happens after registration? A: Producers must complete registration with Landbell USA by July 1, 2026. Post‑registration, producers will be subject to fee assessments, reporting obligations, and will need to participate in statewide collection programs. The PRO will conduct a needs assessment (due March 1, 2027) that informs final budget and fee structures.

Q: Will consumers pay any fees directly? A: The program requires producers to finance collection and recovery; the legislation does not prescribe direct consumer fees. Producers may choose to pass on some costs to consumers through pricing adjustments, but the regulatory model places payment obligations on producers.

Q: How will “free and convenient” collection be ensured across California? A: The PRO must design a network that provides free and convenient collection options statewide. This can include retailer take‑back sites, municipal drop‑off hubs, third‑party collection partners, and potentially curbside pilots in dense areas. The needs assessment will identify geographic gaps and guide infrastructure investments.

Q: How will the PRO ensure transparency and accountability? A: The PRO must maintain a registry of producers, collect and report performance metrics, and file annual reports with CalRecycle. Data must be auditable to enable oversight. CalRecycle will also hold public workshops and has regulatory authority to monitor compliance.

Q: What are the penalties for noncompliance? A: California’s statute authorizes enforcement mechanisms administered by CalRecycle. While SB 707 requires the PRO to provide auditable data and registration records, specific penalties—including fines or administrative sanctions—depend on regulatory implementation and enforcement decisions. Producers should assume there will be consequences for nonregistration and nonpayment.

Q: How does California’s approach compare with what's happening in the EU? A: The EU requires Member States to adopt textile and footwear EPR schemes by April 17, 2028, with transposition of revised waste rules by June 17, 2027. Several EU countries have existing programs (France since 2008; Netherlands launched in 2023; Spain progressing). California’s model, centered on a single PRO with eco‑modulated fees and statewide collection, mirrors elements of European systems but may vary in specific scoring criteria, enforcement and timelines.

Q: What should small and mid‑sized producers do if they can’t afford large administrative costs? A: Small producers should explore representative organizations or producer consortia that can aggregate administrative functions, negotiate fee schedules, and manage reporting. Early engagement with trade associations and the PRO can clarify options and potential fee reductions or exemptions.

Q: Will existing voluntary take‑back programs count toward compliance? A: Existing take‑back programs may be integrated into the statewide collection network, but producers will need to ensure those programs meet the PRO’s standards for data collection, traceability and accessibility. The PRO will determine how voluntary programs are credited against obligations.

Q: Will there be opportunities for funding or support to build recycling infrastructure? A: The PRO’s budget and fee structure will fund program operations, and producers may invest directly in recycling capacity. Public incentives or grants could supplement private investment; producers and recyclers should monitor federal, state and local funding programs that support circular infrastructure.

Q: How will eco‑modulation be verified? A: Verification will require producers to supply material composition data, product design documentation and possibly third‑party certifications. The PRO will define the verification regime and auditors may review producer submissions to confirm scoring.

Q: How can producers influence program design? A: Producers should engage with Landbell USA and participate in CalRecycle workshops (such as the informational session on April 7, 2026). Early and constructive engagement can shape needs assessments, scoring criteria and collection design.

Q: Does the selection of Landbell USA mean only large international PROs can operate? A: Landbell USA’s selection reflects its capacity and international experience. Future program phases and complementary initiatives could involve multiple partners—local collectors, nonprofits, municipal agencies and private recyclers. The selection of a national PRO does not preclude collaboration with regional actors.

Q: Will this program reduce textile waste and increase circularity? A: The program’s design—emphasizing collection, eco‑modulation and reuse/recycling pathways—intends to reduce disposal and increase circularity. Outcomes will depend on effective implementation, sufficient processing capacity, demand for recycled materials, and consumer participation. Continuous monitoring and program adjustments will be necessary to achieve long‑term circularity goals.