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Employees must inspect portable ladders before the first use on each shift and remove unsafe or damaged ladders from service. However, they can’t properly inspect a ladder if they can’t recognize a problem, so they need training.

Before OSHA published revisions in 2016, the regulation included a list of items to check when inspecting ladders. However, OSHA removed the list because the items might have included things that weren’t needed, and might have missed items that should be checked.

For example, after a tip-over, the list required looking for dents or bends in the side rails and rungs, checking hardware connections, and examining rivets. However, the list did not require checking the ladder footing, which might have been the problem. OSHA therefore adopted performance-based language, allowing employers to determine the scope of each inspection based on variables like the ladder type and work area.

Determine what to check

Pre-use inspections might include ensuring the footing is firm and stable, checking the spreader or locking devices, and looking for any missing or damaged components. If a ladder tips over, the inspection might focus on whether footing problems may have caused the tip-over and verifying that rungs are still firmly attached. Employers should tailor inspections for the situation.

OSHA doesn’t require documenting ladder inspections, but providing a checklist could serve as a reminder and help demonstrate to OSHA that you're requiring and enforcing ladder inspections. If an OSHA compliance officer visits your facility, he or she might ask employees when they perform ladder inspections and what they look for. If employees cannot answer those questions (or if the compliance officer sees a defective ladder in use), OSHA will likely issue a citation.

Stepstool inspections

OSHA regulates many stepstools as portable ladders. Not every device sold as a stepstool meets OSHA’s definition, but the regulation at 1910.23(b) applies to all ladders, including stepstools. According to 1910.21, a stepstool means “a self-supporting, portable ladder that has flat steps and side rails” and is no more than 32 inches in height.

For example, a simple platform or two-step stool without side rails would not be a “stepstool” under the standard. However, if employees use stepstools with side rails, they must perform pre-use inspections. Of course, inspecting other stools (even those not covered by OSHA) is a good idea.

As with other ladders, to properly conduct stepstool inspections, employees must know what to look for. Defects might include sharp edges, dents or bends, cracks, slippery treads, or damaged rivets. In addition, the rules for safely using ladders would apply when using stepstools. However, the regulation says, “a stepstool is designed so an employee can climb and stand on all of the steps and the top cap.” Unlike ladders, employees may stand on the top step of a stepstool.

Before employees start climbing a ladder or stool, make sure they know how to properly inspect it and how to safely use it. If OSHA asks employees how they perform inspections before use, they should be able to answer confidently. And of course, safely using equipment that was thoroughly inspected for defects can help prevent injuries.

Key to remember: Employees need training to properly inspect ladders for defects, preferably using checklist of items to document inspections.

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Most Recent Highlights In Environmental

2026-04-24T05:00:00Z

North Dakota establishes AST regulations

Effective date: April 1, 2026

This applies to: Owners and operators of aboveground storage tanks (ASTs) and liquid fuel storage tanks

Description of change: The Department of Environmental Quality adopted technical standards and corrective action requirements for ASTs. The department also approved amendments to the registration dates and fee categories of the Petroleum Tank Release Compensation Fund for liquid fuels storage tanks.

Related state info: Aboveground storage tanks (ASTs) state comparison — ASTs

2026-04-24T05:00:00Z

Ohio finalizes sewage sludge amendments

Effective date: March 1, 2026

This applies to: Facilities regulated by the sewage sludge program

Description of change: The Ohio Environmental Protection Agency finalized changes to the sewage sludge program through its 5-year review of the regulations. The approved amendments:

  • Add professional operator of record requirements for privately owned treatment works;
  • Increase and add isolation distances for facilities;
  • Prohibit beneficial use of biosolids within a vulnerable hydrogeological setting;
  • Remove dioxin monitoring requirements; and
  • Add requirements for beneficial user certification (including the application and examination process, recordkeeping requirements, and reasons for suspending or revoking a certification).
2026-04-24T05:00:00Z

New Mexico adopts Clean Transportation Fuel Program rules

Effective date: April 1, 2026

This applies to: Transportation fuel produced in, imported into, or dispensed for use in New Mexico

Description of change: The New Mexico Environment Department finalized regulations to implement the Clean Transportation Fuel Program (CTFP) to reduce the carbon intensity of transportation fuel (including gasoline and diesel). The program covers transportation fuel producers, importers, and dispensers.

The CTFP:

  • Establishes annual statewide carbon intensity standards that apply to transportation fuel (e.g., gasoline and diesel) produced, imported, and dispensed for use in New Mexico;
  • Allocates credits and calculates deficits for regulated entities based on the fuel’s carbon intensity; and
  • Sets up a marketplace for selling and purchasing credits to comply with the carbon intensity standards.

The first compliance period runs from April 1, 2026, to December 31, 2027. The first compliance period report is due by April 30, 2028. Annual compliance reports will be due by April 30 for the previous calendar year.

2026-04-24T05:00:00Z

Maine lists materials covered for packaging stewardship program

Effective date: March 3, 2026

This applies to: Entities subject to the Stewardship Program for Packaging Regulations

Description of change: The Maine Department of Environmental Protection’s amendments to the Stewardship Program for Packaging Regulations (06-096 C.M.R. Chapter 428) include:

  • Aligning the rules with changes made by An Act to Improve Recycling by Updating the Stewardship Program for Packaging (L.D. 1423), and
  • Adding Appendix A — The Packaging Material Types List to the Stewardship Program for Packaging Regulations.

L.D. 1423:

  • Excludes certain commercial, cosmetic, medical, environmental, dangerous, hazardous, and flammable product packaging from the program requirements;
  • Excludes packaging of products related to public health and water quality testing from the program requirements;
  • Requires the department to adopt a process for approving a producer payment system; and
  • Updates definitions for clarity.

Appendix A defines packaging material and designates the material types readily recyclable as applicable. It may also designate materials as compostable or reusable.

2026-04-24T05:00:00Z

California adopts permanent illegal disposal rules

Effective date: March 4, 2026

This applies to: Entities that handle, transfer, compost, transform, or dispose of solid waste

Description of change: CalRecycle made permanent the current illegal disposal emergency regulations, allowing enforcement agencies to take action against any person who illegally disposes of solid waste.

The rule also:

  • Adds the land application activities to the regulations, making the activities subject to the permitting tier structure and associated requirements (i.e., operator filing requirements, state minimum standards, recordkeeping, and enforcement agency inspection requirements); and
  • Amends sampling and recordkeeping for solid waste facilities, operations, and activities.
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Most Recent Highlights In Transportation

2026-04-24T05:00:00Z

West Virginia establishes fee schedule for UIC Program

Effective date: March 4, 2026

This applies to: Underground Injection Control (UIC) Program permittees

Description of change: This rule establishes the schedules of fees for carbon dioxide capture and sequestration authorized by the West Virginia Department of Environmental Protection’s (WVDEP’s) Division of Water and Waste Management.

EPA granted primacy to the WVDEP to implement the UIC Program for Class VI wells in February 2025.

2026-04-24T05:00:00Z

Colorado extends timeline to comply with GHG intensity targets

Effective date: April 14, 2026

This applies to: Small operators in the oil and gas sector

Description of change: The Colorado Air Quality Control Commission revised the intensity targets for reducing greenhouse gas (GHG) emissions for small oil and gas operators (those with less than 45 thousand barrels of oil equivalent (kBOE) production in 2025). The commission extended the first deadline to 2030 for small operators to meet applicable intensity requirements.

However, small operators must still submit the intensity plan for the 2027 targets, which is due by June 30, 2026.

Related state info: Clean air operating permits state comparison — Clean air operating permits

2026-04-24T05:00:00Z

Colorado finalizes state dredge and fill permit regulations

Effective date: March 30, 2026

This applies to: Projects that require preconstruction notification or compensatory mitigation

Description of change: The Colorado Water Quality Control Division finalized rules for implementing a state dredge and fill discharge authorization program established by HB24-1379. The program covers state waters that aren’t subject to federal dredge and fill permitting requirements under Section 404 of the Clean Water Act.

The division will continue issuing Temporary Authorizations until August 31, 2026. After that, applicants must apply for coverage under General Authorizations. The division already accepts applications for Individual Authorizations.

Related state info: Construction water permitting — Colorado

2026-04-24T05:00:00Z

New York adds wastewater cybersecurity rules

Effective date: March 26, 2026

This applies to: Wastewater treatment facilities

Description of change: The New York State Department of Environmental Conservation added cybersecurity regulations for wastewater treatment facilities. The rules:

  • Require all State Pollutant Discharge Elimination System (SPDES) permittees to report cybersecurity incidents,
  • Require publicly owned treatment works (POTWs) to establish, maintain, and implement an Emergency Response Plan and certify compliance with the provisions annually by March 28;
  • Establish baseline cybersecurity control requirements;
  • Add network monitoring and logging for certain POTWs with design flows of 10 million+ gallons per day; and
  • Require wastewater treatment plant operators to complete a minimum number of training hours within their existing required hours on cybersecurity to renew certification every 5 years.
2026-04-24T05:00:00Z

California permanently adopts EPA’s conditional exemption for airbag waste

Effective date: March 6, 2026

This applies to: Airbag waste handlers and transporters

Description of change: The California Department of Toxic Substances Control permanently adopted the Environmental Protection Agency’s (EPA’s) interim final rule that allows airbag waste handlers and transporters to meet less stringent hazardous waste requirements (e.g., not manifesting the waste) if they meet certain conditions. Once the airbag waste is received at a collection facility or designated facility for proper disposal, it must be managed as hazardous waste.

The scope of the rule applies to all airbag waste, including recalled airbag inflators.

Related state info: Hazardous waste generators — California

See More

Most Recent Highlights In Safety & Health

2026-04-24T05:00:00Z

New Jersey extends polystyrene foam exemption

Effective date: March 12, 2026

This applies to: Certain polystyrene foam food service products

Description of change: The New Jersey Department of Environmental Protection extended the exemption from the Single-Use Paper and Plastic Carryout Bags and Polystyrene Foam Food Service Products Rules for certain polystyrene foam products from May 4, 2026, to May 4, 2027. It applies to these polystyrene foam products:

  • Trays used for raw or butchered meat or fish that’s sold from a refrigerator or similar retail appliance;
  • Food products pre-packaged by the manufacturer in a polystyrene foam food service product;
  • Polystyrene foam food service products that are used for the health or safety of hospital, nursing home, or correctional facility patients or residents; and
  • Any other polystyrene foam food service product as determined needed by the department.
Effluent limitations: FAQs for direct dischargers of industrial wastewater
2026-04-16T05:00:00Z

Effluent limitations: FAQs for direct dischargers of industrial wastewater

Facilities across the country conduct industrial activities that generate wastewater containing pollutants and then release it directly into nearby surface waters, such as streams, rivers, or lakes. However, before any industrial wastewater can be discharged from a site, the facility must obtain a National Pollutant Discharge Elimination System (NPDES) permit.

The Environmental Protection Agency (EPA) uses effluent limitations as the primary method to regulate direct discharges of industrial wastewater into waters of the United States. These restrictions are incorporated into NPDES permits.

Meeting effluent limitations is the key to compliance with NPDES permits. But like other environmental regulations, these standards can get complex quickly without a solid foundation of understanding. We’ve compiled common FAQs to help you become fluent in effluent limitations.

What’s effluent?

There’s no specific statutory or regulatory definition of “effluent.” Thankfully, a 1997 document from EPA entitled Terms of Environment: Glossary, Abbreviations, and Acronyms, Revised December 1997 (EPA 175-B-97-001) provides clarity, defining effluent as “wastewater — treated or untreated — that flows out of a treatment plant, sewer, or industrial outfall.”

What’s the difference between effluent guidelines and limitations?

There are subtle but important distinctions between these two terms.

Effluent guidelines (also known as effluent limitations guidelines and standards or ELGs) are the national industrial wastewater discharge standards established by EPA for all facilities in an industrial category.

The federal agency develops effluent guidelines based on the performance of the best available technology that’s economically achievable for an industry. Notably, effluent guidelines are technology-based; they’re not based on risk or impacts to receiving waters (i.e., water quality-based).

Federal effluent guidelines (40 CFR Subchapter N) for direct dischargers of industrial wastewater are implemented through the NPDES permitting program.

Effluent limitations are any restrictions imposed “on quantities, discharge rates, and concentrations of pollutants” from industrial wastewater discharges (122.2). Simply put, effluent limitations are the specific numeric and non-numeric requirements developed for facilities to comply with the effluent guidelines. Unlike effluent guidelines, effluent limitations may be both technology- and water quality-based.

Most states issue NPDES permits, except for the District of Columbia, Massachusetts, New Hampshire, and New Mexico, where EPA serves as the permitting authority. The permit writer develops effluent limitations for NPDES permits and issues them to facilities. The permit may be general (covering multiple facilities with similar operations and discharges) or individual (customized with site-specific conditions).

What’s the bottom line? Effluent guidelines aren’t directly enforceable permit conditions, whereas effluent limitations are.

What are the types of effluent limitations?

Two categories of effluent limitations may appear in NPDES permits:

  • Technology-based effluent limitations (TBELs), and
  • Water quality-based effluent limitations (WQBELs).

TBELs are based on available treatment technologies and require facilities to meet a minimum level of treatment of pollutants in wastewater discharges.

WQBELs apply only when TBELs aren’t enough to achieve water quality standards. States develop total maximum daily loads (TMDLs). A TMDL is the maximum amount of a pollutant that can be discharged into a waterbody while still meeting the water quality standards. Specific portions of the TMDL are then allotted to permitted facilities (called wasteload allocation). Facilities can’t release more than their allocated amounts.

Any applicable wasteload allocations are incorporated into a facility’s NPDES permit.

Do facilities have to use specific control technologies?

Although EPA’s effluent guidelines are based on the use of a specific control technology, facilities aren’t required to install the same technology system. As long as they comply with the standards, facilities may implement other treatment technologies.

Key to remember: Understanding effluent limitations is key to complying with industrial wastewater discharge permits.

EPA proposes major changes to coal combustion residuals rules
2026-04-16T05:00:00Z

EPA proposes major changes to coal combustion residuals rules

The Environmental Protection Agency (EPA) published a proposed rule on April 13, 2026, to revise the existing regulations governing the disposal of coal combustion residuals (CCR) in landfills and surface impoundments as well as the beneficial use of CCR.

Who’s impacted?

The proposed rule affects coal-fired electric utilities and independent power producers subject to the CCR disposal and beneficial use regulations at 40 CFR Part 257.

What are the changes?

Significant changes the EPA proposes include:

  • Adding an option for facilities to certify the closure of legacy CCR surface impoundments by CCR removal that were closed before November 8, 2024, under regulatory oversight;
  • Expanding the eligibility criteria for facilities to defer CCR closure requirements until site-specific determinations are made for legacy surface impoundments that were closed before November 8, 2024, under regulatory oversight;
  • Exempting CCR dewatering structures (used to dewater CCR waste for the disposal of CCR elsewhere) from federal CCR regulations (Part 257);
  • Rescinding all CCR management unit (CCRMU) requirements or revising the existing CCRMU regulations;
  • Allowing permit authorities to make site-specific determinations regarding certain requirements during permitting for CCR units complying with federal CCR groundwater monitoring, corrective action, and closure requirements under a federal or an approved-state CCR permit; and
  • Revising the beneficial use requirements by:
    • Removing the environmental demonstration requirement for non-roadway use of more than 12,400 tons of unencapsulated CCR; and
    • Excluding these beneficial uses from federal CCR regulations (Part 257):
      • CCR used in cement manufacturing at cement kilns,
      • Flue gas desulfurization (FGD) gypsum used in agriculture, and
      • FGD gypsum used in wallboard.

Key to remember: EPA plans to make significant amendments to the coal combustion residuals requirements.

What to know about EPA’s proposed manifest sunset rule
2026-04-14T05:00:00Z

What to know about EPA’s proposed manifest sunset rule

The Environmental Protection Agency (EPA) is taking another major step toward modernizing hazardous waste tracking. The agency’s proposed “manifest sunset rule” would officially phase out paper hazardous waste manifests and require the exclusive use of the e-Manifest system. For employers, especially those generating or managing hazardous waste, it’s a fundamental shift in how waste shipments are documented, tracked, and audited.

Since 2018, EPA’s e-Manifest system has been available as a digital alternative to paper manifests. Over the years, the agency has added requirements pushing the industry toward adoption, including mandatory registration and electronic data submission. But despite those efforts, many companies have continued to rely on paper manifests, either out of habit, for convenience, or because parts of their waste chain weren’t ready to go digital. EPA even states in the proposed rule that fewer than 1 percent of all e-Manifest users have completely switched to digital manifests. The proposed sunset rule is designed to close that gap. Once finalized, it would set a firm deadline (24 months) after which paper manifests would no longer be allowed.

Why EPA wants to eliminate paper manifests

EPA’s reasoning is pretty straightforward. Paper manifests are slower, easier to lose, and more prone to errors. They rely on manual handling and delayed processing, which can create gaps in tracking and compliance. A fully electronic system, on the other hand, allows for real-time visibility, standardized data entry, and faster correction of mistakes. It also gives regulators a clearer, more immediate picture of what’s happening across the entire waste life cycle.

Addressing one of the biggest digital barriers: signatures

One overlooked part of the proposed rule is how EPA is trying to solve one of the biggest barriers to going fully digital, which is signatures in the field. Anyone who has dealt with manifests knows that the weak point is often the hand-off between the generator and the transporter, especially when drivers don’t have system access or reliable connectivity.

To address that, EPA is proposing new functionality that would allow users to sign manifests using quick response (QR) codes or even short message service (SMS). In practice, this could mean a driver scans a QR code or receives a text prompt and then completes the signature process directly on the phone. So, no login or full system access is needed. EPA is also exploring the ability to use SMS and QR-based tools to make updates to manifest data without needing full system permissions. That’s a big deal operationally because it removes one of the most common bottlenecks in needing a registered user at a specific site to make even minor corrections.

Operational challenges companies should expect

With that said, moving to a fully digital system still comes with potential issues. It requires coordination across your entire operation. Generators, transporters, and disposal facilities all have to be aligned and capable of using the system effectively. If one party in that chain struggles, it can create delays or compliance issues for everyone involved. There’s also an upfront investment to consider. Companies may need to upgrade internal systems, ensure reliable connectivity, and train employees in new work processes. For organizations with multiple sites or field operations, this can take some planning. But over time, many of those burdens are expected to decrease. Electronic signatures, reusable templates, and centralized recordkeeping can significantly reduce administrative work.

One of the biggest shifts employers will notice is the level of visibility. With paper manifests, there’s often a lag between shipment and final documentation. In a digital system, that lag disappears. Information becomes available almost immediately, and regulators have access to the same data. That means errors or discrepancies are easier to find and harder to ignore.

The good news is that companies don’t have to wait for the final rule to start preparing. Taking a close look at your current manifest process is a good first step. If paper is still a major part of your workflow, that’s a clear signal that changes are coming. Making sure your e-Manifest account is fully set up and that employees understand how to use it will go a long way in avoiding future disruptions.

Keys to remember: The EPA’s proposed Paper Manifest Sunset Rule would set a firm date to phase out paper hazardous waste manifests and require that all covered shipments be tracked through the agency’s electronic e‑Manifest system, through which the Agency says will improve hazardous waste tracking and transparency while reducing administrative burden and saving regulated entities roughly $28.5 million per year.

How incinerators are permitted: A look at the regulatory framework and EPA’s new streamlining proposal
2026-04-13T05:00:00Z

How incinerators are permitted: A look at the regulatory framework and EPA’s new streamlining proposal

Incinerators in the United States operate under a complex permitting framework designed to protect air quality, public health, and the environment. Under the Clean Air Act (CAA), facilities that burn waste must meet strict emission standards, maintain operating controls, and follow extensive monitoring and reporting rules. These requirements ensure that incineration, while a valuable tool for waste management, wildfire mitigation, and disaster recovery, remains safe and consistent with federal air quality objectives. Against this backdrop, the Environmental Protection Agency (EPA) recently proposed a rule to streamline permitting for specific types of incinerators used in wildfire prevention and disaster cleanup, a move that could reduce delays for state and local governments.

The regulatory basis for incinerator permitting

Most incinerators fall under Section 129 of the CAA, which mandates EPA to establish performance standards and emission guidelines for categories of solid waste combustion units. These standards govern pollutants such as particulate matter, carbon monoxide, sulfur dioxide, nitrogen oxides, lead, cadmium, mercury, hydrogen chloride, and dioxins/furans. Operators must also conduct emissions testing, maintain continuous monitoring equipment, track operational parameters, and submit regular compliance reports.

Permitting generally occurs through Title V operating permits, which consolidate all applicable air quality requirements into a single enforceable document. A Title V permit typically requires annual certifications, detailed recordkeeping, periodic emissions tests, and reporting of deviations. While the Title V program doesn't impose new standards, it ensures that incinerators comply with all existing federal and state air quality rules.

Different categories of incinerators, such as large municipal waste combustors (LMWC), small municipal waste combustors (SMWC), commercial and industrial solid waste incinerators (CISWI), and other solid waste incinerators (OSWI), have distinct requirements. These subcategories reflect variations in unit size, waste composition, and operational design, and each has its own subpart under EPA’s air quality regulations.

Air curtain incinerators: A special case

Air curtain incinerators (ACIs), which burn wood waste, yard debris, and clean lumber, occupy a niche segment of the permitting landscape. They use a mechanized “curtain” of air to increase combustion efficiency and reduce particulate emissions compared to open burning. However, their regulatory treatment has historically been inconsistent.

Because ACIs fit partly within several existing subparts, operators often face confusion about which monitoring, opacity limits, and reporting duties apply. Overlap across four regulatory categories can create delays, particularly during emergencies when ACIs are deployed to remove vegetative fuels that increase wildfire risk or to process debris after storms.

EPA’s emergent focus on streamlining

In March 2026, EPA announced a proposal to consolidate the regulatory requirements for ACIs used solely to burn wood-derived materials into a single subpart under Section 129 of the CAA. The proposal would also allow these ACIs to operate without a Title V permit unless located at a facility that otherwise requires one.

EPA stated that the change would “cut red tape” and provide clarity for state, local, and Tribal governments, allowing them to respond more effectively to natural disasters and conduct wildfire mitigation activities without unnecessary administrative delays. The agency emphasized that unprocessed debris contributes to poor air and water quality and poses safety risks, particularly in post disaster environments.

Context: Broader federal actions on disaster-related incineration

The proposal follows earlier federal steps to ease the temporary use of incinerators during emergencies. In 2025, EPA issued an interim final rule permitting CISWI units to burn nonhazardous disaster debris for up to 8 weeks without prior EPA approval, a provision intended to accelerate cleanup after hurricanes, wildfires, and floods. These units must still operate their pollution control equipment, and extensions beyond 8 weeks require EPA authorization.

Such measures reflect the increasing volume of debris associated with severe weather events and the need for rapid, environmentally sound disposal mechanisms. The current proposal for ACIs builds on these efforts by targeting the specific regulatory bottlenecks associated with vegetative and wood waste disposal.

Looking ahead

EPA’s streamlined permitting proposal doesn't alter emission standards but rather clarifies and simplifies administrative pathways. If finalized, it may make ACIs more accessible during periods of heightened wildfire risk and in the critical early stages of disaster recovery.

Key to remember: At its core, the permitting system for incinerators aims to balance environmental protection with operational flexibility. The new proposal underscores EPA’s recognition that, in emergency contexts, speed matters but so does environmental stewardship.

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Most Recent Highlights In Human Resources

EPA delays TSCA Section 8(a)(7) PFAS reporting timeline again
2026-04-13T05:00:00Z

EPA delays TSCA Section 8(a)(7) PFAS reporting timeline again

On April 13, 2026, the Environmental Protection Agency (EPA) published a final rule that further delays the submission period for the one-time report required of manufacturers on per- and polyfluoroalkyl substances (PFAS) by the PFAS Reporting and Recordkeeping Rule (PFAS Reporting Rule).

This final rule pushes the starting submission period to either 60 days after the effective date of a future final rule updating the PFAS Reporting Rule or January 31, 2027, whichever is earlier.

Who’s impacted?

Established under Toxic Substances Control Act (TSCA) Section 8(a)(7), the PFAS Reporting Rule (40 CFR Part 705) requires any business that manufactured (including imported) any PFAS or PFAS-containing article between 2011 and 2022 to report. Covered manufacturers and importers must submit information on:

  • Chemical identity, uses, and volumes made and processed;
  • Byproducts;
  • Environmental and health effects;
  • Worker exposure; and
  • Disposal.

What’s the new timeline?

The opening submission period was moved from April 13, 2026, to either 60 days after the effective date of a future final PFAS Reporting Rule or January 31, 2027, whichever is earlier.

Most manufacturers have 6 months to submit the report. Small manufacturers reporting only as importers of PFAS-containing articles have 1 year.

TSCA Section 8(a)(7) PFAS Reporting Rule submission period
Start dateEnd date
Most manufacturers60 days from effective date of final PFAS Reporting Rule or January 31, 2027 (whichever is earlier)6 months from start date or July 31, 2027 (whichever is earlier)
Small manufacturers reporting solely as PFAS article importers60 days from effective date of final PFAS Reporting Rule or January 31, 2027 (whichever is earlier)1 year from start date or January 31, 2028 (whichever is earlier)

Why the delay?

In November 2025, the agency proposed updates to the PFAS Reporting Rule. EPA has delayed the reporting period to give the agency time to issue a final rule (expected later this year).

Key to remember: EPA has delayed the starting submission deadline for the TSCA Section 8(a)(7) PFAS Reporting Rule from April 2026 to no later than January 2027.

EPA amends specific oil and gas emission standards
2026-04-10T05:00:00Z

EPA amends specific oil and gas emission standards

On April 9, 2026, the Environmental Protection Agency (EPA) published a final rule that makes technical changes to the emission standards established in March 2024 (2024 Final Rule) for crude oil and natural gas facilities. This rule (2026 Final Rule) amends the requirements for:

  • Temporary flaring of associated gas, and
  • Vent gas net heating value (NHV) monitoring provisions for flares and enclosed combustion devices (ECDs).

Who’s impacted?

The 2026 Final Rule affects new and existing oil and gas facilities. Specifically, it applies to the regulations for the Crude Oil and Natural Gas source category, including the:

  • New Source Performance Standards at 40 CFR 60 Subpart OOOOb, and
  • Emission guidelines at 60 Subpart OOOOc.

These emission standards are commonly referred to as OOOOb/c.

What are the changes?

The 2026 Final Rule implements technical changes to the temporary flaring and vent gas NHV monitoring requirements set by the 2024 Final Rule.

Temporary flaring

The rule extends the baseline time limit for temporary flaring of associated gas at well sites in certain situations (like conducting repairs or maintenance) from 24 to 72 hours. Owners and operators must stop temporary flaring as soon as the situation is resolved or the temporary flaring limit is reached (whichever happens first).

It also grants allowances beyond the 72-hour limit if exigent circumstances occur (such as severe weather that prevents safe access to a well site to address an emergency or maintenance issue) and there’s a need to extend duration for repairs, maintenance, or safety issues. Owners and operators must keep records of exigent circumstances and include the information in their annual reports.

NHV monitoring

For new and existing sources, the 2026 Final Rule exempts all flare types (unassisted and assisted) and ECDs from monitoring due to high NHV content, except when inert gases are added to the process streams or for other scenarios that decrease the NHV content of the inlet stream gas. In these cases, EPA requires NHV monitoring via continuous monitoring or the alternative performance test (sampling demonstration) option for all flares and ECDs.

Other significant changes include:

  • Replacing the general exemption from NHV monitoring for associated gas for any control device used at well site affected facilities with NHV monitoring requirements,
  • Granting operational pauses during weekends and holidays for the consecutive 14-day sampling demonstration requirements (limiting it to no more than 3 operating days from the previous sampling day), and
  • Permitting less than 1-hour sampling times for twice daily samples where low or intermittent flow makes it infeasible (as long as owners and operators report the sampling time used and the reason for the reduced time).

The 2026 Final Rule takes effect on June 8, 2026.

Key to remember: EPA’s technical changes to the emission standards for oil and gas facilities apply to temporary flaring provisions and vent gas NHV monitoring requirements.

EHS Monthly Round Up - March 2026

EHS Monthly Round Up - March 2026

In this March 2026 roundup video, we'll review the most impactful environmental health and safety news.

Hi everyone! Welcome to the monthly news roundup video, where we’ll review the most impactful environmental health and safety news. Let’s take a look at what happened over the past month.

OSHA released an updated Job Safety and Health poster. Employers can use either the revised version or the older one, but the poster must be displayed in a conspicuous place where workers can easily see it.

OSHA recently removed a link from its Data topic webpage that displayed a list of “high-penalty cases” at or over $40,000 since 2015. The agency says it discontinued and removed it in December. The data is frozen and archived elsewhere.

OSHA published two new resources as part of its newly launched Safety Champions Program. The fact sheet provides an overview of how the program works, eligibility criteria, and key benefits. The step-by-step guide helps businesses navigate the core elements of OSHA’s Recommended Practices for Safety and Health Programs.

Several forces are nudging OSHA to address a number of workplace hazards and high-hazard industries. This comes from other agencies, safety organizations, watchdogs, legislative proposals, and persistent injury/fatality data. Among the hazards are combustible dust; first aid; personal protective equipment; and workplace violence. How all this translates into new regulations, guidance, programmed inspections, or other initiatives remains to be seen.

Turning to environmental news, EPA issued a proposed rule to require waste handlers to use electronic manifests to track all RCRA hazardous waste shipments. Stakeholders have until May 4 to comment on the proposal.

On March 10, EPA finalized stronger emission limits for new and existing large municipal waste combustors and made other changes to related standards.

And finally, EPA temporarily extended coverage under the 2021 Multi-Sector General Permit for industrial stormwater discharges until the agency issues a new general permit. The permit expired February 28 and remains in effect for facilities previously covered. EPA won’t take enforcement action against new facilities for unpermitted stormwater discharges if the facilities meet specific conditions.

Thanks for tuning in to the monthly news roundup. We’ll see you next month!

EPA releases draft list of drinking water contaminants for possible regulation
2026-04-07T05:00:00Z

EPA releases draft list of drinking water contaminants for possible regulation

The Environmental Protection Agency (EPA) published the draft Sixth Contaminant Candidate List (CCL 6) for the next group of contaminants to be considered for regulation under the Safe Drinking Water Act (SDWA). The agency’s proposed list designates microplastics and pharmaceuticals as priority contaminant groups for the first time.

What’s on the list?

The proposed CCL 6 contains:

  • 4 chemical groups, including:
    • Microplastics,
    • Pharmaceuticals,
    • Per- and polyfluoroalkyl substances (PFAS), and
    • Disinfection byproducts.
  • 75 chemicals; and
  • 9 microbes.

EPA may regulate the listed contaminants in the future.

What does the CCL do?

The drinking water CCL is the first part of the process to regulate contaminants in public water systems. The list identifies unregulated contaminants known or anticipated to be present in drinking water that pose the greatest health risk. It helps EPA prioritize which contaminants to evaluate for potential regulation.

The SDWA requires EPA to make regulatory determinations (i.e., whether to develop rules for a contaminant) for at least five contaminants listed on the CCL every 5 years. When the agency determines a contaminant needs to be regulated, it begins the rulemaking process to develop a National Primary Drinking Water Regulation (NPDWR) for the contaminant. The NPDWRs apply to public water systems.

How can I participate?

EPA will receive public comments on the CCL 6 through June 5, 2026. You can send comments to EPA via regulations.gov or by mail. Make sure your submission includes the Docket ID No. EPA-HQ-OW-2022-0946.

Key to remember: The draft list of the next round of drinking water contaminants to be considered for regulation adds priority groups for microplastics and pharmaceuticals.

EPA delivers 2026–2027 renewable fuel volumes
2026-04-03T05:00:00Z

EPA delivers 2026–2027 renewable fuel volumes

On April 1, 2026, the Environmental Protection Agency (EPA) published the “Set 2” Rule, establishing the Renewable Fuel Standard (RFS) program’s 2026 and 2027 renewable fuel volumes and associated percentage standards for:

  • Cellulosic biofuel,
  • Biomass-based diesel (BBD),
  • Advanced biofuel, and
  • Total renewable fuel.

The final rule also implements other significant changes.

Who’s impacted?

The “Set 2” Rule affects:

  • Transportation fuel (i.e., gasoline and diesel) refiners, blenders, marketers, distributors, importers, and exporters; and
  • Renewable fuel producers and importers.

The volume and percentage requirements apply to obligated parties, which include transportation fuel refiners and importers.

What are the changes?

The final rule sets the renewable fuel volume requirements and associated percentage standards for 2026 and 2027. Volume requirements are measured in billion Renewable Identification Numbers (RINs). One RIN represents 1 gallon of ethanol-equivalent renewable fuel.

Renewable fuel categoryVolume requirements (in billion RINs)Percentage standards
2026202720262027
Cellulosic biofuel1.361.430.79%0.84%
BBD9.079.205.24%5.37%
Advanced biofuel11.1011.326.42%6.61%
Total renewable fuel26.8127.0215.50%15.78%

The “Set 2” Rule also:

  • Reallocates 70 percent of the exempted Renewable Volume Obligations (RVOs) for 2023–2025 to 2026 and 2027 (which are reflected in the above table’s volume requirements),
  • Partially waives the 2025 cellulosic biofuel volume requirement from 1.38 billion RINs to 1.21 billion RINs and adjusts the related percentage standard from 0.81 percent to 0.71 percent, and
  • Removes renewable electricity as a qualifying renewable fuel under the RFS program.

RFS program refresher

The RFS program requires transportation fuel sold in the United States to contain a minimum volume of renewable fuels. EPA sets the renewable fuel volume targets for each of the four renewable fuel categories.

To comply, obligated parties must:

  • Calculate their RVOs for each renewable fuel category, and
  • Obtain and retire enough RINs to meet their RVOs.

Regulations also apply to fuel blenders, marketers, and exporters.

Small refiners may petition EPA for a small refinery exemption (SRE), which allows refineries to produce gasoline and diesel without having to meet the RVOs required by the RFS program. EPA grants SREs annually, and they cover one specific compliance year.

Key to remember: EPA’s final “Set 2” rule establishes the renewable fuel volumes and percentage standards for 2026 and 2027 and drives other changes to the RFS program.

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Enforcement Policy for Respiratory Hazards Not Covered by OSHA Permissible Exposure Limits

Standard Number:1910.1200
OSH Act:Section 5(a)(1)

Nov 02, 2018

MEMORANDUM FOR:REGIONAL ADMINISTRATORS
FROM:KIMBERLY STILLE
Acting Director
Directorate of Enforcement Programs
SUBJECT:Enforcement Policy for Respiratory Hazards Not Covered by OSHA Permissible Exposure Limits

As you are aware, Section 5(a)(1) of the Occupational Safety and Health Act (OSH Act) is occasionally used to cite respiratory hazards from exposure to an air contaminant that is not covered by an OSHA permissible exposure limit (PEL). This memorandum serves to clarify existing Agency enforcement policy for developing these citations.

Specifically, Section 5(a)(1) of the OSH Act requires each employer to “furnish to each of his employees employment and a place of employment which are free from recognized hazards that are causing or are likely to cause death or serious physical harm.” As explained in the OSHA Field Operations Manual (FOM) (CPL 02-00-160), when enforcing this requirement, the Occupational Safety and Health Review Commission and court precedent have determined that the following elements must be established in order for OSHA to prove a violation of the general duty clause:

  1. The employer failed to keep the workplace free of a hazard to which employees of that employer were exposed;
  2. The hazard was recognized;
  3. The hazard was causing or was likely to cause death or serious physical harm; and
  4. here was a feasible and useful method to correct the hazard.

When applying these elements to respiratory hazards, it is important for Area Directors to ensure that 5(a)(1) citations are not based solely on evidence that a measured exposure exceeded a recommended occupational exposure limit (OEL), such as a Threshold Limit Value (TLV)1, or based on the fact that there is a documented exposure to a recognized carcinogen.2 Unless the case file evidence proves all four of the above elements, the Area Office should issue a hazard alert letter (HAL). The HAL should advise the employer that one or more employees at the establishment was being, or had been, exposed to a potentially serious respiratory hazard from a chemical that exceeded an OEL, and provide a series of recommended exposure control suggestions. For your information, attached is a sample HAL for a respiratory hazard.

However, if the evidence does provide sufficient proof of the four elements listed above, then the general duty clause should be cited, following the general guidance in the FOM, Chapter 4. We are providing the following additional guidance for developing evidence for each of these elements when specifically applied to respiratory hazards:

  1. a. The employer failed to keep the workplace free of a hazard to which employees of that employer were exposed - Evidence that documents this element includes personal air sampling results, written workplace observations, photographs, and witness statements noting how workers were exposed to the chemical, and descriptions of any implemented engineering, work practice, and administrative control measures, and personal protective equipment. The evidence should also substantiate that regular and continuing employee exposure to the chemical at the measured levels could reasonably occur. However, if the exposed employees were wearing appropriate respiratory protection with no deficiencies in the respirator program, then the likelihood that OSHA could establish a respiratory hazard covered by the general duty clause would be low.
  2. b. The hazard was recognized - OSHA can establish this element in one of two ways. (1) For employer recognition: Evidence may include employee complaints to management, illness and injury logs, consultant reports, a previous HAL, internal safety and health policies related to workplace operations involving the chemical that may refer to an OEL, or information from a manufacturer describing safety and health precautions for equipment or chemicals used in the workplace such as the chemical manufacturers’ safety data sheet (SDS). (2) For industry recognition: Evidence may include an industry or trade association’s guidance document, or an assessment from an industry expert describing the work practice or operation used at the establishment and explaining the particular health hazards and recommended control measures. Alternatively, a similar publication from a (non-OSHA) federal, state, or local government agency, or from a professional organization, may also provide good evidence. Some examples of government agencies include the National Institute for Occupational Safety and Health (NIOSH), the National Toxicology Program (NTP), and the U.S. Environmental Protection Agency (EPA). Examples of organizations include The Center for Construction Research and Training (CPWR, formerly The Center to Protect Workers’ Rights), the American Conference of Governmental Industrial Hygienists (ACGIH™), and the Occupational Alliance for Risk Science (OARS).
  3. c. The hazard was causing or was likely to cause death or serious physical harm - Although an illness or injury from the measured exposure need not have occurred yet, the strongest evidence is an employee illness/injury, hospitalization, fatality, or medical diagnosis related to workplace exposure. In the absence of this, the evidence must include more than just the fact that a measured exposure exceeded a TLV or REL, because these recommended limits may be much lower than the level at which a serious heath effect may be experienced. In most cases, proving this element will require an expert or industry-related peer reviewed study to document that serious physical harm could occur at the measured level with continuing employee exposure. Additionally, establishing serious physical harm for some respiratory hazards may be particularly difficult if the resulting illness, such as cancer, would require a substantial period of time to occur.
  4. d. There was a feasible and useful method to correct the hazard - Evidence may include the SDS describing work practices for safe handling, engineering controls, and personal protective equipment, or published industry and/or NIOSH studies (e.g., health hazard evaluations (HHEs)) involving similar chemical processes or operations. Proving that feasible abatement measures would eliminate or materially reduce workplace exposure to a level that no longer presents a serious health hazard will likely require expert testimony.

For technical assistance in developing the required evidence related to the above elements, OSHA compliance officers may coordinate with their Regional Office to contact the Directorate of Technical Support and Emergency Management’s (DTSEM) Salt Lake Technical Center (SLTC) at (801) 233-4900 and the Office of Occupational Medicine and Nursing (OOMN) at (202) 693-2323. For additional guidance for compliance officers, the Directorate of Training and Education’s (DTE) OSHA Training Institute (OTI) has developed a job aid on this subject, which also includes tips for writing chemical 5(a)(1) citations.

Please distribute this memorandum to all health compliance officers. If you have any questions on this, please contact the Office of Health Enforcement at (202) 693-2190.

Attachment

Endnote (1) - Per 29 CFR 1910.1200, Hazard Communication, chemical manufacturers must list ir product’s safety data sheet (SDS) all known exposure limits. Specifically, Section 8 of the SDS must include: “OSHA permissible exposure limit (PEL), American Conference of Governmental Industrial Hygienists (ACGIH) Threshold Limit Value (TLV), and any other exposure limit used or recommended by the chemical manufacturer, importer, or employer preparing the safety data sheet, where available.” [See Table D.1, 1910.1200 Appendix D]. For evaluating respiratory hazards of chemicals without a PEL, compliance officers may refer to applicable published OELs, which include, but are not limited to, the following:

  1. a. Recommended Exposure Limits (RELs) issued by the National Institute for Occupational Safety and Health (NIOSH);
  2. b. Threshold Limit Values™ (TLVs™) published by the American Conference of Governmental Industrial Hygienists (ACGIH™); and
  3. c. Workplace Environmental Exposure Levels™ (WEELs™) published by the Occupational Alliance for Risk Science (OARS), which is managed by Toxicology Excellence for Risk Assessment (TERA™).
  4. d. Other recommended exposure limits from chemical manufacturers or industry/trade associations, such as may be provided on SDSs or in industry guidance publications.
Endnote (2) - Per 29 CFR 1910.1200, Hazard Communication, chemical manufacturers must also list on their product’s SDS all known carcinogenic ingredients when greater than 0.1% of the product mixture. Specifically, Section 11 of the SDS must include all known toxicological information, including: “Whether the hazardous chemical is listed in the National Toxicology Program (NTP) Report on Carcinogens (latest edition) or has been found to be a potential carcinogen in the International Agency for Research on Cancer (IARC) Monographs (latest edition), or by OSHA.” [See Table D.1, 1910.1200 Appendix D].

Attachment - Sample Hazard Alert Letter for a Chemical with no PEL

[Date]

ABC Company [Address]

RE: Inspection Number XXXXXXX

Dear Company Owner:

An inspection of your workplace at [address], initiated on [date], disclosed conditions that are consistent with employee exposure to 1-bromopropane. 1-bromopropane (CAS: 106-94-5), as covered in this inspection, was used as a solvent in your vapor degreasing operations. Symptoms of exposure to 1-bromopropane (or 1BP) include irritation and damage to the nervous system. Neurological damage can appear as headaches, dizziness, loss of consciousness, slurred speech, confusion, difficulty walking, and/or loss of feeling in the arms and legs. Exposure to employees can occur by inhalation and absorption through skin contact. Studies have shown that health effects from exposure to this chemical may present within as little as two days, however most serious effects are more commonly associated with prolonged exposure.

Currently, Federal OSHA does not have a specific exposure standard for 1BP. However, OSHA and the National Institute for Occupational Safety and Health (NIOSH) jointly issued a hazard alert for occupational exposure to 1BP in 2013. ( See enclosed copy). In 2014, the American Conference of Governmental Industrial Hygienists (ACGIH™) adopted a Threshold Limit Value™ (TLV™) for 1-bromopropane of 0.1 parts per million (ppm), or 0.5 milligrams per cubic meter (0.5 mg/m3), as an 8-hour time-weighted average (TWA).

Monitoring Results: Measured employee exposures to 1-bromopropane were well above the AGCIH 8-hour TLV of 0.1 ppm as discussed in the below sampling results.

During the inspection at your facility, three employees were monitored to determine their exposure to 1BP. On [date], one employee spraying the interior of metal parts with different concentrations of 1BP solutions in the [spray area] was exposed to [xx] ppm of 1BP, as an 8-hr TWA. The employee conducting the spraying was sampled for [aaa] minutes, with zero exposure assumed for the remainder of the 480-minute shift. On [date], one employee manually coating the exterior of metal parts with various 1BP solutions in the [coating area] was exposed to [YY] ppm 1BP as an 8-hr TWA. The employee conducting the coating was sampled for [bbb] minutes, with zero exposure assumed for the remainder of the 480-minute shift. On [date], one employee operating the flush-and-blow system in close proximity to the degreaser was exposed to [ZZ] ppm 1BP as an 8-hr TWA. The flush-and-blow operator was sampled for [ccc] minutes, with zero exposure assumed for the remainder of the 480-minute shift. All three employees’ 8-hr TWAs for 1BP was significantly greater than the ACGIH TLV of 0.1 ppm.

We recommend that you voluntarily take the necessary steps to materially reduce or eliminate your employees’ exposures to the conditions listed above.

While the risk of health hazards associated with exposure to 1BP can be reduced or eliminated by implementing a single means of abatement, in most cases a variety of abatement methods will provide a more effective method of addressing these hazards. These include workplace analysis of jobs and tasks to assess hazards associated with those jobs and tasks and the steps to abate them: product substitutions; engineering, administrative, and work practice controls; accurate injury and illness recordkeeping; medical surveillance; medical management of occupational illnesses and injuries; education and training of employees; and management oversight.

We have examined available information on the hazards associated with the degreasing operation conducted at your facility. The evaluation suggests that one or more of the following additional methods of abatement should be implemented.

  1. 1. Engineering Controls.
    Engineering controls are the first line of defense in employee protection. Therefore, your company should provide appropriate engineering controls throughout the facility. Employees should be trained on the use of the engineering controls to ensure that occupational exposure to 1BP is maintained below levels that are hazardous to employees. The following engineering controls are recommended:
    • Engineering of the spray and coating areas so that employees are isolated from the operation where 1BP is applied to the interior or exterior of the metal parts. This could include a system that automatically coats the parts or by means of increasing the distance between the employees and the spray operation.
    • Installation of local exhaust ventilation systems where the employees conduct the operations to reduce the amount of exposure. For the spray area, a local ventilation should be located where the employee is spraying the interior of the parts, and for the coating area, a local hood ventilation system should be set up such that any vapors from the rags are collected before reaching the employee’s breathing zone. Additionally, ventilation should be considered around the degreasing tank in order to capture fugitive 1BP vapors escaping from the degreasing tank during the degreasing process.
  2. 2. Administrative and Work Practices Controls.
    The following work practices should be used to reduce occupational exposure to 1BP during degreasing operations:
    • Evaluation of employee body positioning during the various operations. By observing and evaluating the operator’s location during various points in the coating operations, it may be possible to prevent the operator from standing in an area where exposure to fugitive 1BP vapors is likely. This includes consideration for where the fans are located in relation to the employees, as well.
    • Revise the coating operation’s standard operating procedure to document how often the spray hood requires cleaning, how to effectively conduct the cleaning with less employee exposure, and how much solution is required on a rag to effectively coat the exterior of the parts.
    • Instituting a job rotation schedule for the spray area and activities around the degreaser. Other company employees should be trained on these operations so that employees could rotate in and out during the course of the day.
    • Ensuring appropriate preventative maintenance is conducted on the degreaser and still according to the manufacturer’s recommendations.
    • Conducting personal air monitoring on a regular basis to determine employee exposure levels to 1BP, ensuring that personal air samples are taken from the employee’s breathing zone. Breathing zone samples provide the best indication of the concentration of contaminants in the air the employee is actually breathing.
    • Ensuring employees immediately and thoroughly wash their skin with soap and flowing water if dermal contact with 1BP occurs.
    3. Personal Protective Equipment.
    To be effective, personal protective equipment must be individually selected, properly fitted and periodically refitted, conscientiously and properly worn, regularly maintained, and replaced as necessary. In addition, employers must:
    • Perform a revised workplace hazard assessment in accordance with 29 CFR 1910.132(d) to determine if hazards are present, or are likely to be present which necessitate the use of personal protective equipment (PPE), and identify and evaluate respiratory hazards as required by 29 CFR 1910.134(d)(1)(iii).
    • Establish, implement, and maintain a written respiratory protection program in accordance with 29 CFR 1910.134(c) in any workplace where respirators are necessary to protect employee health.
    • Provide and ensure that employees use appropriate respiratory protection where necessary to protect employee health.
    • Provide and ensure the use of the appropriate gloves (e.g., butyl, nitrile), goggles, and protective clothing when necessary to protect employees from workplace hazards (e.g., exposure to contaminated equipment, chemical containers).
    • Train employees on the limitations and proper use and maintenance of required PPE in accordance with 29 CFR 1910.132(f).
  3. 4. Training and Information.
    Employers must comply with the OSHA Hazard Communication standard, 29 CFR 1910.1200. In particular, employers must ensure that employees exposed to 1BP are trained in and have access to the following information:
    • The operations in their workplace where hazardous chemicals are present;
    • Safety data sheets (SDSs) for chemicals containing 1BP, which must include information about the signs and symptoms of exposure and the hazards of dermal contact with 1BP;
    • Any protective measures the employer is using to reduce employee exposures to 1BP;
    • Specific work practices employees can use to reduce exposure to 1BP;
    • Appropriate use of personal protective equipment;
    • Methods that may be used to detect the presence of the 1BP in the workplace, such as workplace monitoring.

You may voluntarily provide this Area Office with progress reports on your efforts to address these conditions. OSHA may return to your work site in one year to further examine employee exposures to 1BP.

Enclosed is the above-mentioned OSHA publication that may be of assistance to you in preventing work-related injuries and illnesses in your workplace. If you have any questions, please feel free to call [###].

Sincerely,

Area Director

Enclosure (OSHA/NIOSH Hazard Alert publication)

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