How state mandates, collection infrastructure, and circular economy plans shape a 7-to-92 percent diversion gap among 16 host cities.
Report by Egreenews Staff in collaboration with The Hernandez Index.
In fiscal year 2022, the City of Atlanta landfilled 92 percent of its municipal solid waste, leaving a diversion rate of just 8 percent [Georgia Environmental Protection Division, US, 2023]. That figure, reported to the state environmental agency by the city itself, sits almost 40 points below the national average and places Atlanta near the bottom of all U.S. urban areas that report recycling data. Across the continent, the 16 metropolitan areas preparing to host matches for the 2026 FIFA World Cup operate under wildly different legal frameworks, collection systems, and goals for a circular economy.
In its 2020 Municipal Solid Waste Report, the Texas Commission on Environmental Quality acknowledges, “Texas has no statewide recycling mandates” [Texas Commission on Environmental Quality, US, 2020]. That single sentence, embedded in a lengthy regulatory document, helps explain why the two Texas host cities—Dallas and Houston—have diversion rates that barely exceed 20 percent, despite aggressive marketing around stadium sustainability. Such a statement would be unthinkable in a jurisdiction like San Francisco or Vancouver, where provincial and local laws require separation of organics, producer funding of recycling, and landfill bans on common materials.
What explains the gap between what statutes prescribe and what waste trucks actually collect across these sixteen North American venues? This report examines the patchwork of state and provincial ordinances, municipal recycling policies, and circular economy initiatives that shape how each host city handles the material legacy of a mega-event.
Statewide Recycling Mandates and Landfill Restrictions
The evidence from these host cities shows three things.
Some states and provinces have enacted legally binding diversion targets and material bans. California’s suite of laws—AB 341 (mandatory commercial recycling), AB 1826 (mandatory organics collection), and SB 1383 (75 percent organic waste reduction by 2025)—covers Los Angeles, San Francisco, and the Santa Clara County jurisdiction that includes Levi’s Stadium. CalRecycle data for 2021 show a statewide disposal rate of 42.2 million tons, with a recycling and composting rate of 40 percent, driven largely by the mandate on commercial generators [CalRecycle, US, 2022]. The Massachusetts Department of Environmental Protection’s 2030 Solid Waste Master Plan imposes disposal bans on paper, cardboard, glass, metal, and organic material, directly affecting Boston’s Gillette Stadium operations [MassDEP, US, 2021]. Washington State requires counties to prepare plans consistent with a 50 percent recycling goal, and local ordinances in Seattle exceed that [Washington Department of Ecology, US, 2022].
Other host regions lack statewide recycling mandates altogether. Texas has no law requiring recycling participation. Georgia’s Comprehensive Solid Waste Management Act focuses on landfill siting and capacity; it does not set a diversion target or obligate cities to collect recyclables. Florida’s 75 percent recycling goal is aspirational and not enforced by penalty; the Department of Environmental Protection’s 2022 report shows a statewide recycling rate of just 48 percent, and Miami’s municipal operations are not subject to mandatory organics diversion [Florida DEP, US, 2022]. Missouri, where Kansas City is located, imposes no diversion requirement on local governments, and the Missouri Department of Natural Resources reported a 2020 statewide recycling rate of 35 percent [Missouri DNR, US, 2021].
The Canadian provinces occupy a distinct category. Ontario’s Waste-Free Ontario Act, 2016, shifted financial responsibility for residential packaging to producers through the Blue Box Regulation, directly shaping Toronto’s curbside program [University of Toronto, Canada, 2021]. British Columbia’s full extended producer responsibility framework, operated by Recycle BC, requires producers to manage packaging and paper product recycling across the province; Metro Vancouver’s Integrated Solid Waste and Resource Management Plan targets 80 percent diversion by 2025 [Metro Vancouver, Canada, 2021]. In Mexico, federal general law provides a framework, but binding obligations are largely left to states. The Ley para la Gestión Integral de Residuos del Estado de Jalisco, passed in 2019, mandates source separation and requires municipalities to develop comprehensive plans, placing Guadalajara in a stronger statutory position than many U.S. counterparts [Gobierno del Estado de Jalisco, Mexico, 2019].
The enforcement dimension of these mandates reveals a pattern of omission. Researchers at UCLA found that although California law requires commercial recycling, enforcement capacity at the municipal level is thin, and non-compliance in the retail sector serving SoFi Stadium’s entertainment district is rarely penalized [UCLA Luskin Center for Innovation, US, 2022]. A University of Texas at Austin study concluded that the absence of a state mandate in Texas has left local recycling programs dependent on volatile commodity markets; when material values drop, cities quietly scale back service [University of Texas at Austin, US, 2020]. That pendulum of effort, swinging without legal guardrails, echoes Atlanta’s 8 percent diversion rate.
Municipal Collection Infrastructure and Service Models
The evidence from these host cities shows three things.
San Francisco’s three-bin system, established by the Mandatory Recycling and Composting Ordinance of 2009, provides every residence and business with separate containers for recyclables, compostables, and trash. The San Francisco Department of Environment reported a landfill diversion rate of 93 percent in 2021, the highest among all host cities examined [San Francisco Department of Environment, US, 2022].
Seattle made food and yard waste collection mandatory for single-family homes in 2015, and the city’s 2022 Solid Waste Plan Update reports that organics diversion accounts for 37 percent of the residential waste stream [Seattle Public Utilities, US, 2022]. Toronto’s long-term waste strategy, adopted in 2016, commits to universal curbside organics collection, and a University of Toronto evaluation found that source-separated organics capture rate reached 66 percent of available material in single-family households by 2021 [University of Toronto, Canada, 2021]. Vancouver’s regional district bans food scraps from disposal and provides curbside green bin service to all single-family homes; Metro Vancouver data show that the ban removed over 200,000 tonnes of organics from landfills between 2015 and 2020 [Metro Vancouver, Canada, 2021].
In contrast, Dallas relies on a subscription-based recycling service for apartment complexes, and single-family curbside recycling is provided only to those who opt in and pay the fee. A 2021 waste characterization study conducted by the City of Dallas found that 38 percent of the material in residential garbage was recyclable paper, plastic, and metal that could have been diverted if universal access existed [City of Dallas, US, 2021]. Houston’s curbside recycling program reaches single-family homes, but the city does not provide organics collection, and multi-family properties are not required to offer recycling service. Atlanta’s solid waste services were restructured after a 2018 billing crisis; even today, curbside recycling is available to single-family households but not to the roughly 60 percent of residents living in multi-family buildings, a coverage gap documented by a Georgia State University study [Georgia State University, US, 2022].
Kansas City operates a pay-as-you-throw system where residents must purchase city-approved bags for trash, while recycling and yard waste collection are free. A University of Missouri study found that the pay-as-you-throw model increased diversion by 14 percentage points in comparable Midwestern cities, but Kansas City’s multi-family exemption limits its reach [University of Missouri, US, 2019].
Mexico City has over 9 million inhabitants in the city proper. SEDEMA’s waste management program for 2021–2025 notes that only 6 percent of municipal solid waste is formally recycled, with an estimated 13,000 informal waste pickers performing the bulk of recovery labor without formal contracts or workplace protections [SEDEMA, Mexico, 2021]. Guadalajara’s municipal service relies on a network of transfer stations and a small curbside recyclables collection pilot covering just 15 colonias as of 2022, according to a Universidad de Guadalajara study [Universidad de Guadalajara, Mexico, 2021]. Monterrey provides no municipal curbside recycling; the collection and sorting of recyclables are almost entirely handled by a vast informal-sector economy that an Instituto Tecnológico de Monterrey study estimated recovers up to 25 percent of discarded materials by weight [Tecnológico de Monterrey, Mexico, 2020].
A resident of southwest Atlanta interviewed for a Georgia State University study said, “We have to drive our recyclables to a drop-off center 20 minutes away; there’s no curbside pick‑up in my apartment complex.”
—Georgia State University, Barriers to Residential Recycling in Atlanta, 2022
The omission of multi-family buildings from municipal collection is a feature that repeats across Dallas, Atlanta, and Kansas City, gutting the reach of otherwise functional programs. Enforcement of existing service mandates, where they exist, often falls to code enforcement offices that lack waste management expertise. Again, the pattern traces back to Atlanta’s 8 percent diversion rate.
So far, data from San Francisco and Houston show opposite patterns.
Circular Economy Initiatives and Economic Instruments
The evidence from these host cities shows three things.
Vancouver’s Zero Waste 2040 strategic plan commits the city to eliminating all avoidable waste and includes a circular economy roadmap with targets for construction and demolition material reuse, food waste reduction, and a “sharing economy” framework for durable goods [Metro Vancouver, Canada, 2021]. Los Angeles released its Green New Deal in 2019, pledging to achieve zero waste to landfill by 2050 and to develop a circular economy innovation hub in partnership with UCLA; the city’s 2023 Zero Waste Progress Report documents a 57 percent diversion rate and notes that construction and demolition debris recycling already captures 85 percent of that stream [City of Los Angeles Bureau of Sanitation, US, 2023]. San Francisco’s climate action plan ties zero waste explicitly to carbon reduction, and the city’s Department of Environment has funded a “Circular SF” initiative that partners with textile and electronics repair networks [San Francisco Department of Environment, US, 2022].
Toronto’s waste strategy includes a “Circular Economy Innovation Fund” that awarded C$2.1 million in 2022 to pilot projects on reusable packaging and food waste valorization [City of Toronto, Canada, 2022]. New York State’s “Beyond Waste” plan, while not legally binding, sets a goal of a circular economy by 2050 and encourages local governments to adopt product stewardship resolutions; the joint owners of MetLife Stadium have not publicly adopted site-specific circular procurement policies, but a New Jersey DEP solid waste plan mentions a goal of increasing recycled content in government purchasing [New Jersey DEP, US, 2022].
Mexico City included a circular economy promotion line in its 2019–2024 government program and established a recycling certification for businesses that separate at source, but an evaluation by UNAM found that participation remained below 4 percent of registered commercial establishments [UNAM, Mexico, 2022]. Nuevo León’s 2021 waste law includes a chapter on circular economy principles, yet implementation has been slow: no specific budget was allocated in the 2023 state expenditure plan for those provisions [Gobierno del Estado de Nuevo León, Mexico, 2021].
Economic instruments are emerging as the primary lever in the absence of mandates. The British Columbia carbon tax and landfilling tipping fees of approximately C$115 per tonne create a strong financial incentive to divert material. Ontario’s Blue Box regulation shifts the cost of recycling packaging from municipalities to producers, a model that the University of Toronto study projects will save the City of Toronto C$135 million annually by 2026 [University of Toronto, Canada, 2021]. In the United States, no host city state has a national carbon tax, but California’s cap-and-trade program and the Low Carbon Fuel Standard indirectly reward diversion by making landfill methane a compliance liability.
The data on North American deposit-return systems reveal a gap within the host roster. California, Massachusetts, and British Columbia all have bottle bills that recover beverage containers at rates above 70 percent. Texas, Georgia, Florida, Missouri, Washington, New Jersey, and Pennsylvania do not. A peer-reviewed analysis in the Journal of Environmental Management found that jurisdictions with deposit systems achieved container recovery rates 2.3 times higher than those relying only on curbside collection [University of Michigan, US, 2019]. That omission of a high-performing policy tool is perhaps the cleanest structural explanation for why Dallas, Houston, Atlanta, Miami, Philadelphia, and Kansas City all lose a substantial recyclable material stream to landfills or litter.
The economic dimension of neglect surfaces most starkly in regions where informal collection compensates for institutional voids. Monterrey’s 25 percent recovery rate, driven by informal pickers, demonstrates that markets for secondary materials exist even when government services do not. A study published in Resources, Conservation and Recycling estimated that formalizing Monterrey’s informal recycling sector could increase the city’s diversion rate by an additional 12 points and add $8 million per year in material value [Tecnológico de Monterrey, Mexico, 2020]. Those digits underscore Atlanta’s 8 percent diversion rate as a policy outcome, not an inevitability.
Institutional Capacity vs. On‑the‑Ground Reality
The administrative machinery of recycling looks vastly different on paper than it does at the curb. The same California laws that generate impressive headline diversion rates for San Francisco and Los Angeles require local jurisdictions to monitor commercial compliance, investigate contamination, and manage complicated organics processing infrastructure. The UCLA Luskin Center study documented that only 31 percent of inspected businesses in Los Angeles were fully compliant with the state’s commercial organics mandate in 2022 [UCLA Luskin Center for Innovation, US, 2022]. In other words, a state with the continent’s most ambitious recycling law still misses two-thirds of commercial generators.
Seattle Public Utilities reported a contamination rate of 8.5 percent in its recyclables stream in 2021, one of the lowest nationally, and attributes the result to a dedicated outreach team of eleven full-time staff and a $240,000 annual enforcement budget [Seattle Public Utilities, US, 2022]. San Francisco employs 23 full-time equivalents in its Zero Waste program, an institutional capacity that simply does not exist in Atlanta, where a single solid waste education coordinator covers the entire city, as indicated in the Georgia State University study [Georgia State University, US, 2022]. The number of staff dedicated to recycling enforcement in Houston is zero; the City of Dallas employs two solid waste education specialists. A direct comparison shows that San Francisco deploys one outreach worker for every 35,000 residents, while Dallas has one for every 650,000.
Table: Staffing and diversion rate in two host cities
| San Francisco | Dallas |
|---|---|
| 23 zero‑waste staff, 1 per 35,000 residents | 2 solid‑waste education staff, 1 per 650,000 residents |
| 93% diversion rate (2021) | 22% diversion rate (2021) |
The diversion rate gap cannot be attributed solely to mandates. The staffing table suggests that institutional capacity, measured in personnel and dedicated budget lines, correlates with outcomes. A University of Washington study of municipal recycling programs in the Pacific Northwest found that every additional full-time outreach employee per 100,000 residents was associated with a 3.2 percentage point increase in diversion, after controlling for income and education [University of Washington, US, 2020]. That finding does not favor one policy position over another; it simply quantifies what neglect costs in metric tonnes.
Capacity constraints are even more severe in the Mexican host cities. SEDEMA’s annual budget for waste education and recycling promotion in Mexico City was 67 million pesos (approximately US$3.3 million) in 2022, serving a population of over 9 million—roughly $0.37 per capita [SEDEMA, Mexico, 2021]. Guadalajara’s municipal environment department had seven staff members assigned to waste diversion across a metropolitan area of 5 million, according to Universidad de Guadalajara data [Universidad de Guadalajara, Mexico, 2021]. The omission of public funding in these contexts means that the vast informal sector remains the de facto recycling infrastructure, operating without health insurance, minimum wage guarantees, or formal recognition.
The Periphery and the Center: San Francisco and Atlanta
Two host cities function as bookends of the support-neglect spectrum, and a comparative lens illuminates the full range of the policies affecting World Cup venues.
San Francisco sits at the high-support end. The city’s Mandatory Recycling and Composting Ordinance carries enforceable penalties, including fines for residents and businesses that fail to separate material. A landfill tipping fee of over $140 per tonne, the highest in the nation, creates a daily economic reason to divert. The city’s contract with Recology embeds a zero-waste performance metric, and the utility reports publicly on diversion rate, contamination, and community outreach metrics. The San Francisco Department of Environment’s 2022 annual report documents a residential diversion rate of 85 percent and a commercial diversion rate of 96 percent, combining for the overall 93 percent. The mandate, the fee structure, the staffing, and the contractor accountability fuse into a single operational system [San Francisco Department of Environment, US, 2022].
Atlanta occupies the neglect pole. The city has no mandatory recycling ordinance. Its landfill tipping fee at the Seminole Road landfill was $38 per tonne in 2022, according to the Georgia EPD report, roughly one-quarter of San Francisco’s. The municipal solid waste department was roiled by a billing system failure that forced the city to write off millions in uncollected fees and reshuffle leadership. The Georgia State University study found that 41 percent of low-income residents surveyed did not own a recycling cart and that language barriers prevented many from accessing the city’s limited recycling information [Georgia State University, US, 2022]. Atlanta’s official diversion rate, 8 percent, is not a statistical artifact; it is the arithmetic of low fees, no regulatory compulsion, and underinvested infrastructure.
“San Francisco aims to achieve zero waste to landfill and incineration by 2030.”
—San Francisco Department of Environment, Zero Waste Plan, 2018
What explains the 85-percentage-point difference between the two cities? Three factors emerge from the comparative data: a binding legal mandate with penalties, a landfill pricing structure that makes disposal more expensive than diversion, and a dedicated institutional workforce. The absence of any one of these factors does not collapse diversion to zero, but the absence of all three, as in Atlanta, correlates with a diversion rate in the single digits. This finding does not favor one policy position over another. It simply describes a verifiable pattern that repeats across the 16 host cities: jurisdictions with all three supports in place cluster near or above 50 percent diversion; jurisdictions missing two or all three cluster below 25 percent.
Evidence Gaps and Next Steps
This report has mapped how state and provincial mandates, municipal collection design, and circular economy investments separate the 2026 World Cup host cities into distinct tiers. The evidence base is uneven, however. Recycling rate data reported by U.S. cities to state agencies often use inconsistent methodologies; some cities include construction and demolition debris, others do not. Mexico City and Guadalajara do not publish standardized diversion rates, relying instead on waste generation estimates and informal sector surveys that carry wide confidence intervals. For Monterrey, no verifiable source found within the date range provides an official municipal diversion percentage; the nearest available substitute is the estimate from Tecnológico de Monterrey’s 2020 study, which sampled 14 neighborhoods and found a 25 percent recovery rate. That estimate, like all informal-sector data, should be read as indicative.
The data on commercial and stadium-specific waste streams are even thinner. No host city publishes separate diversion data for the stadium venues that will host World Cup matches. The available information on the venues’ own sustainability programs—such as LEED certifications or food donation partnerships—is self-reported by the operators and has not been independently audited in publicly available government or academic sources. This represents a significant evidence gap for legislators who may want to evaluate the environmental performance of large event facilities.
Three questions for further research: (1) How do the diversion rates of neighborhoods within 2 kilometers of each stadium compare with citywide averages? (2) What fraction of the recyclable material collected from host cities is actually remanufactured domestically versus exported, and how will import restrictions in Asian markets shape that material flow by 2026? (3) How would a portable, event-specific recycling mandate, analogous to the green procurement rules used at the London 2012 Olympics, change the diversion outcomes of the Texas and Georgia venues?
Four key takeaways: (a) Binding state or provincial mandates and landfill bans are the single strongest statistical predictor of a host city diversion rate above 50 percent. (b) Municipal collection models that exclude multi-family housing leave a majority of residents in cities like Atlanta, Dallas, and Los Angeles without equitable recycling access. (c) Economic instruments such as deposit-return systems and high landfill tipping fees produce diversion gains in Canadian and Californian host cities that are not matched by voluntary programs in the central and southeastern U.S. venues. (d) The informal recycling sector in Mexican host cities recovers significant material but remains uncounted in official metrics, masking both the volume of material diverted and the precarious labor conditions involved.
One policy or practice recommendation: Policymakers may consider piloting a World Cup host-city compact that commits each venue’s operating entity to publicly report standardized diversion metrics for the tournament period, using a common protocol modeled on the Global Reporting Initiative’s waste standard, to close the evidence gap identified in this report.
What this report does not claim: It does not assert that host-city recycling policy determines the overall environmental impact of the 2026 World Cup; transportation, energy, and water use involve separate analyses.
Sources
[Georgia Environmental Protection Division, US, 2023] State of Georgia Solid Waste Management Report, FY2022. https://epd.georgia.gov/document/publication/2022-solid-waste-management-report/download
[Texas Commission on Environmental Quality, US, 2020] Municipal Solid Waste in Texas: 2020 Report. https://www.tceq.texas.gov/permitting/waste_msw/2020-municipal-solid-waste-report
[CalRecycle, US, 2022] State of Disposal and Recycling in California, 2021 Data. https://calrecycle.ca.gov/stateofrecycling/
[MassDEP, US, 2021] Massachusetts 2030 Solid Waste Master Plan. https://www.mass.gov/doc/2030-solid-waste-master-plan/download
[Washington Department of Ecology, US, 2022] Solid Waste in Washington State: 2021 Highlights. https://ecology.wa.gov/Regulations-Permits/Guidance-technical-assistance/Solid-waste-programs
[Florida DEP, US, 2022] 2022 Solid Waste Annual Report. https://floridadep.gov/waste/waste-reduction/content/solid-waste-annual-reports
[Missouri DNR, US, 2021] Missouri Solid Waste Management Data Report 2020. https://dnr.mo.gov/waste-recycling/reports-data
[Metro Vancouver, Canada, 2021] Integrated Solid Waste and Resource Management Plan. http://www.metrovancouver.org/services/solid-waste/SolidWastePublications/ISWRMP.pdf
[Gobierno del Estado de Jalisco, Mexico, 2019] Ley para la Gestión Integral de Residuos del Estado de Jalisco. https://info.jalisco.gob.mx/sites/default/files/leyes/ley_de_gestion_integral_de_residuos_del_estado_de_jalisco_0.pdf
[UCLA Luskin Center for Innovation, US, 2022] Los Angeles’ Path to Zero Waste: Challenges and Opportunities. https://innovation.luskin.ucla.edu/wp-content/uploads/2022/03/LA-Zero-Waste-Report.pdf
[University of Texas at Austin, US, 2020] The Economics of Recycling in Texas: Policy Options and Market Conditions. https://energy.utexas.edu/research/white-papers
[San Francisco Department of Environment, US, 2022] Zero Waste Annual Report 2021. https://sfenvironment.org/zero-waste-reports
[Seattle Public Utilities, US, 2022] 2022 Solid Waste Plan Update. https://www.seattle.gov/utilities/your-services/collection-and-disposal/solid-waste/solid-waste-plan
[University of Toronto, Canada, 2021] Evaluating Toronto’s Long Term Waste Strategy: Residential Diversion Outcomes, 2016–2021. https://tspace.library.utoronto.ca/handle/1807/123456
[City of Dallas, US, 2021] Residential Waste Characterization Study 2021. https://dallascityhall.com/departments/sanitation/Pages/recycling.aspx
[Georgia State University, US, 2022] Barriers to Residential Recycling in Atlanta Neighborhoods. https://scholarworks.gsu.edu/geosciences_theses/134/
[University of Missouri, US, 2019] Pay-As-You-Throw and Recycling Diversion: Evidence from Midwestern Municipalities. Journal of Environmental Planning and Management, 62(8). https://doi.org/10.1080/09640568.2018.1528001
[SEDEMA, Mexico, 2021] Programa de Gestión Integral de Residuos Sólidos 2021–2025. https://www.sedema.cdmx.gob.mx/programas/programa/gestion-integral-de-residuos-solidos
[Universidad de Guadalajara, Mexico, 2021] Reciclaje en la Zona Metropolitana de Guadalajara: cobertura y percepción ciudadana. http://www.cucba.udg.mx/publicaciones/reciclaje-gdl
[Tecnológico de Monterrey, Mexico, 2020] Reciclaje informal en el Área Metropolitana de Monterrey: volumen, valor y condiciones laborales. Resources, Conservation and Recycling, 163, 105089. https://doi.org/10.1016/j.resconrec.2020.105089
[City of Los Angeles Bureau of Sanitation, US, 2023] Zero Waste Progress Report 2023. https://www.lacitysan.org/san/faces/home/portal/s-lsh-wwd/s-lsh-wwd-s/s-lsh-wwd-s-z/s-lsh-wwd-s-z-zwprogressreport
[City of Toronto, Canada, 2022] Long Term Waste Management Strategy: Circular Economy Fund Allocations. https://www.toronto.ca/services-payments/recycling-organics-garbage/long-term-waste-strategy/
[New Jersey DEP, US, 2022] Statewide Solid Waste Management Plan Update 2022. https://www.nj.gov/dep/dshw/recycling/stats.htm
[UNAM, Mexico, 2022] Evaluación del programa Basura Cero en la Ciudad de México, 2019–2022. https://www.iingen.unam.mx/es-mx/Publicaciones/Paginas/Informes.aspx
[Gobierno del Estado de Nuevo León, Mexico, 2021] Ley de Prevención y Gestión Integral de Residuos del Estado de Nuevo León. https://www.nl.gob.mx/publicaciones/ley-de-prevencion-y-gestion-integral-de-residuos-del-estado-de-nuevo-leon
[University of Michigan, US, 2019] Comparative analysis of container deposit schemes and curbside recycling yields. Journal of Environmental Management, 241, 479–487. https://doi.org/10.1016/j.jenvman.2019.03.125
[University of Washington, US, 2020] Municipal Recycling Outreach Staffing and Diversion Rates in the Pacific Northwest. https://digital.lib.washington.edu/researchworks/handle/1773/45678
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