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Industrial stormwater compliance can feel complex for facilities balancing operations, employees, and shifting permit requirements. Many questions center on the federal general permit, pollution prevention plan expectations, monitoring, and what to do in everyday situations where stormwater risks arise. The following sections summarize core topics and practical concerns.

What is the current status of the federal 2021 Multi-Sector General Permit (MSGP)?

EPA issued the current MSGP in 2021, and it remains in effect beyond its February 28, 2026 expiration until EPA finalizes the proposed 2026 MSGP. Because the proposed 2026 permit is still under review, the 2021 MSGP continues to govern covered facilities.

Why has the proposed 2026 MSGP not taken effect?

EPA released the proposed 2026 MSGP in December 2024. Public comments, including an extended comment period ending May 19, 2025, must be reviewed before finalizing the permit. Since the existing MSGP remains valid until replaced, the 2021 permit stays in force while EPA completes its process.

What is a Stormwater Pollution Prevention Plan (SWPPP)?

A SWPPP outlines how a facility prevents pollutants from reaching stormwater. It identifies pollutant sources, control measures, inspection routines, monitoring steps, and staff training. A SWPPP must be written before submitting a Notice of Intent (NOI) for permit coverage and updated when operations or stormwater risks change.

What are the requirements for authorized state stormwater permits?

Most states issue their own industrial stormwater permits modeled on the federal MSGP. These permits typically require:

  • Preparation and maintenance of a SWPPP;
  • Inspections and monitoring (such as benchmark, effluent, or visual monitoring);
  • Corrective actions when control measures fail; and
  • Reporting through state online systems.

States may add requirements based on local conditions. When EPA updates the MSGP, states often revise their permits to align with new federal standards.

Who needs coverage under the MSGP?

Industrial facilities that discharge stormwater to waters of the United States generally need permit coverage unless they qualify for a no‑exposure exclusion. The federal MSGP applies in areas where EPA, not the state, holds National Pollutant Discharge Elimination System (NPDES) authority.

How does a facility obtain coverage?

To obtain coverage, a facility must:

  • Prepare and implement a SWPPP;
  • Put pollution controls in place, such as good housekeeping and spill prevention;
  • Identify sector specific requirements based on the permit; and
  • Submit a Notice of Intent through EPA’s online system.

The proposed 2026 MSGP includes updated forms and appendices, but current requirements remain based on the 2021 version until a new permit is published.

What monitoring is required?

Under the 2021 MSGP, required monitoring may include:

  • Quarterly visual assessments,
  • Benchmark monitoring in designated years, and
  • Effluent limitations monitoring for specific regulated discharges.

The proposed 2026 MSGP would expand per- and polyfluoroalkyl substances (PFAS) sampling, increase benchmark monitoring frequency, and add requirements for impaired waters. These changes remain pending.

What happens if benchmark thresholds are exceeded?

A benchmark exceedance requires the facility to investigate causes, improve control measures, and document actions in the SWPPP. The proposed 2026 MSGP would formalize additional implementation measures and reporting steps, but these wouldn’t apply until the new permit takes effect.

What about common real world compliance scenarios?

Industrial stormwater issues often arise from everyday activities. Consider these examples:

Employees’ vehicles leaking oil in parking lots

Leaks from employee vehicles can contaminate stormwater. While the MSGP does not regulate personal vehicles directly, the facility is responsible for any pollutants that enter stormwater from its property. Good housekeeping practices include absorbent stations, spill kits, drip pans, and designated parking areas with routine inspection.

Nonroutine outdoor maintenance

Temporary outdoor activities such as conducting maintenance, unloading equipment, or staging materials, can introduce pollutants. The SWPPP should address nonroutine tasks by requiring temporary controls like tarps, containment pads, or scheduling activities during dry weather. Documentation of these activities is also part of good recordkeeping.

Outdoor waste storage or scrap piles

These materials should be covered or sheltered, kept away from storm drains, and inspected frequently. If runoff contacts industrial materials, the discharge becomes regulated and must be managed under the permit.

These scenarios reinforce the need for strong housekeeping practices, staff training, and prompt corrective actions.

What documentation must facilities keep?

Facilities must maintain monitoring records, inspection logs, SWPPP updates, and corrective action reports. EPA may request these documents at any time. Appendices in the proposed 2026 MSGP preview updated forms, but the 2021 requirements remain in place for now.

What should facilities do while waiting for the 2026 MSGP?

Facilities should continue full compliance with the 2021 MSGP, track regulatory updates, and prepare for more frequent monitoring and PFAS sampling likely included in the 2026 permit. Reviewing proposed changes now helps facilities plan needed SWPPP updates in advance.

Key to remember: Industrial facilities covered under the 2021 MSGP or a state equivalent must continue following that permit until EPA issues a new federal MSGP. Staying informed, maintaining strong housekeeping, and keeping SWPPP documentation current remain the most effective strategies for compliance.

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Most Recent Highlights In Environmental

Hazardous waste manifests: Hybrid vs. fully electronic
2026-04-28T05:00:00Z

Hazardous waste manifests: Hybrid vs. fully electronic

More industries are embracing the exclusive use of electronic platforms. For example, digital payments are replacing cash, news sites are going fully online, and cloud storage is eclipsing external computer storage. And, based on recent proposed rulemaking, hazardous waste manifests may join the list.

The Environmental Protection Agency (EPA) proposed the Paper Manifest Sunset Rule in March 2026, planning to shift to electronic-only manifests for tracking hazardous waste that’s regulated by the Resource Conservation and Recovery Act (RCRA).

If the proposed rule is finalized, regulated entities will have to track all hazardous waste shipments electronically. Specifically, generators, transporters, and receiving facilities could only use hybrid or fully electronic manifests on the Hazardous Waste Electronic Manifest System (e-Manifest).

So, what are the differences between hybrid and fully electronic manifests? Let’s compare the distinctions and explore some of the benefits that electronic manifests can offer.

What’s a hybrid manifest?

EPA initially established the hybrid manifest for generators that couldn’t fully participate in electronic manifests when the e-Manifest launched in 2018. The hybrid manifest combines paper and electronic manifests, allowing generators that aren’t registered in e-Manifest or don’t have an EPA identification (ID) number to sign printed copies of electronic manifests.

Here’s the general hybrid manifest process:

  • The first transporter initiates an electronic manifest in e-Manifest. A hard copy of the electronic manifest is printed out, and the generator and initial transporter sign the paper copy.
  • The generator keeps a signed paper copy on-site. The transporter keeps a signed paper copy with the shipment until it’s delivered to the receiving facility.
  • From that point forward, the initial transporter and all subsequent waste handlers track the shipment in e-Manifest (using electronic signatures and electronic transmissions).
  • The manifest is complete when the receiving facility or exporter electronically signs it on e-Manifest.

What’s a fully electronic manifest?

The fully electronic manifest is tracked completely online. All handlers — generators, transporters, and receiving facilities or exporters — must have an EPA ID number and be registered in e-Manifest to use the fully electronic manifest.

The entire process is conducted on e-Manifest:

  • The manifest is created electronically in e-Manifest.
  • All handlers electronically sign the manifest in e-Manifest.
  • The manifest is complete when the receiving facility or exporter electronically signs it on e-Manifest.

What benefits do electronic manifests offer?

Regardless of whether EPA’s rule is finalized as is, electronic manifests offer hazardous waste handlers a range of benefits. Consider the following potential perks.

Compliance with existing regulations

Many handlers are already required to embrace electronic manifesting. In July 2024, EPA finalized the e-Manifest Third Rule, which requires:

  • Large quantity generators and small quantity generators to register for e-Manifest,
  • Exporters to submit manifests and continuation sheets to e-Manifest (and pay the associated fees), and
  • Waste handlers to submit manifest-related reports and data corrections to e-Manifest.

Streamlined recordkeeping for generators

Hazardous waste handlers using e-Manifest automatically meet the recordkeeping requirements to maintain records of manifests (paper or electronic) since the manifests are retained electronically in the system.

This eliminates the need to keep hard copies. It also provides a centralized place where handlers can access these documents at any time.

However, the provision doesn’t apply to generators using hybrid manifests; they must keep the initial paper copies of the electronic manifest for 3 years.

Reduced costs

Embracing electronic manifesting removes the costs associated with printing paper manifests from EPA-approved sources.

Keep in mind, there’s an unavoidable cost for receiving facilities and exporters. These entities have to pay user fees for each manifest they submit to e-Manifest.

Proactive preparation

EPA’s proposed Paper Manifest Sunset Rule would prohibit the use of paper manifests 2 years after the publication of a final rule. Hazardous waste handlers who transition to using only electronic manifests now will be better prepared to comply with future regulations. It gives businesses time to coordinate resources and address any unexpected issues.

Key to remember: Do you know the differences between hybrid and fully electronic hazardous waste manifests? The distinctions could be the difference between compliance and noncompliance.

EPA publishes first round of expiring TSCA CBI claims
2026-04-27T05:00:00Z

EPA publishes first round of expiring TSCA CBI claims

The Environmental Protection Agency (EPA) published the first list of expiring Confidential Business Information (CBI) claims for information submitted under the Toxic Substances Control Act (TSCA). The list covers CBI claims that expire from June 22, 2026, to July 31, 2026.

What are expiring CBI claims?

The Frank R. Lautenberg Chemical Safety for the 21st Century Act (which became law in June 2016) set an automatic 10-year expiration for most CBI claims made under TSCA. The first round of claims submitted since the act took effect will expire in June 2026.

EPA allows businesses to request extensions of CBI protection for up to another 10 years.

How do I know if my CBI claims are expiring?

EPA will notify businesses of expiring CBI claims directly through the Central Data Exchange (CDX), the agency's electronic reporting platform.

The agency will also release public lists of upcoming expiring CBI claims monthly on the “CBI Claim Expiration” webpage. EPA encourages businesses to review the lists to verify whether any of their claims are included.

How do I request an extension of expiring CBI claims?

Businesses seeking to extend a CBI claim beyond its expiration date must submit an extension request at least 30 days before the claim expires using the newly launched TSCA Section 14(e) CBI Claim Extension Request application in EPA’s CDX.

Here’s the general process:

  • EPA notifies the business of an expiring CBI claim directly through CDX and via the public lists on the “CBI Claim Expiration” webpage.
  • The business submits a request for extension through EPA’s CDX at least 30 days before the CBI claim expires. Requests must comply with the substantiation requirements at 40 CFR 703.5(a) and (b).
  • EPA reviews the submission and either grants or denies the request.

What are the possible outcomes?

If EPA approves the extension request, the information in the CBI claim will remain protected for up to another 10 years.

If EPA denies the extension request, the agency can publicize the information in the claim 30 days after notifying the submitter in CDX. Additionally, if a business doesn’t submit an extension request at least 30 days before the expiration date, EPA may publicize the information without notifying the submitter.

Key to remember: EPA published the first round of expiring CBI claims for information submitted under TSCA. Businesses must submit extension requests to keep the information protected.

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.

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Most Recent Highlights In Transportation

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.
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

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Most Recent Highlights In Safety & Health

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

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.

See More

Most Recent Highlights In Human Resources

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

What to know about the EPA’s proposed manifest sunset rule

The U.S. 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, convenience, or because parts of their waste chain weren’t ready to go digital. EPA even states in the proposed rule that less than one percent of all e-manifest users have completely switched to digital manifest. 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, then completes the signature process directly from their phone. So, no login or full system access 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, which can take some planning. But over time, many of those burdens are expected to decrease. Electronic signatures, reusable templates, and centralized record-keeping 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, in 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.

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!

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§571.305a Standard No. 305a; electric-powered vehicles: Electric powertrain integrity; mandatory applicability begins on September 1, 2027.

S1. Scope. This standard specifies requirements for protection from harmful electric shock, fire, explosion, and gas venting during normal vehicle operation and during and after a crash.

S2. Purpose. The purpose of this standard is to reduce deaths and injuries during normal vehicle operations and during and after a crash that occur because of electrolyte leakage, intrusion of electric energy storage/conversion devices into the occupant compartment, electric shock, fire, explosion, and gas venting, including deaths and injuries due to driver error.

S3. Application. (a) This standard applies to passenger cars, multipurpose passenger vehicles, trucks, and buses that use electrical propulsion components with working voltages greater than 60 volts direct current (VDC) or 30 volts alternating current (VAC), and whose speed attainable over a distance of 1.6 km on a paved level surface is more than 40 km/h.

(b) Mandatory applicability begins September 1, 2027, for vehicles with a gross vehicle weight rating of 4,536 kilograms (kg) or less and September 1, 2028, for vehicles with a gross vehicle weight rating over 4,536 kg. Small-volume manufacturers, final-stage manufacturers, and alterers are provided an additional year to comply with the requirements beyond the dates identified in this paragraph (b).

S4. Definitions.

Active driving possible mode

means the vehicle mode when application of pressure to the accelerator pedal (or activation of an equivalent control) or release of the brake system causes the electric power train to move the vehicle.

Automatic disconnect

means a device that when triggered, conductively separates a high voltage source from the electric power train or the rest of the electric power train.

Breakout harness

means connector wires that are connected for testing purposes to the REESS on the traction side of the automatic disconnect.

Capacitor

means a device used to store electrical energy, consisting of one or more pairs of conductors separated by an insulator: x-capacitors are connected between electrical mains or neutral and y-capacitors are connected between a main to ground.

Charge connector

is a conductive device that, by insertion into a vehicle charge inlet, establishes an electrical connection of the vehicle to an external electric power supply for the purpose of transferring energy.

Chassis dynamometer

means a mechanical device that uses one or more fixed roller assemblies to simulate different road conditions within a controlled environment and is used for a wide variety of vehicle testing.

Connector

means a device providing mechanical connection and disconnection of high voltage electrical conductors to a suitable mating component, including its housing.

n C Rate

means the constant current of the REESS, which takes 1/n hours to charge or discharge the REESS between 0 and 100 percent state of charge.

Direct contact

is the contact of any person or persons with high voltage live parts.

Electric energy storage device

means a high voltage source that stores energy for vehicle propulsion. This includes, but is not limited to, a high voltage battery or battery pack, rechargeable energy storage device, and capacitor module.

Electric energy storage/conversion device

means a high voltage source that stores or converts energy for vehicle propulsion. This includes, but is not limited to, a high voltage battery or battery pack, fuel cell stack, rechargeable energy storage device, and capacitor module.

Electric energy storage/conversion system

means an assembly of electrical components that stores or converts electrical energy for vehicle propulsion. This includes, but is not limited to, high voltage batteries or battery packs, fuel cell stacks, rechargeable energy storage systems, capacitor modules, inverters, interconnects, and venting systems.

Electric power train

means an assembly of electrically connected components which includes, but is not limited to, electric energy storage/conversion systems and propulsion systems.

Electrical chassis

means conductive parts of the vehicle whose electrical potential is taken as reference and which are:

(1) Conductively linked together, and

(2) Not high voltage sources during normal vehicle operation.

Electrical isolation

of a high voltage source in the vehicle means the electrical resistance between the high voltage source and any of the vehicle's electrical chassis divided by the working voltage of the high voltage source.

Electrical protection barrier

is the part providing protection against direct contact with high voltage live parts from any direction of access.

Electrolyte leakage

means the escape of liquid electrolyte from the REESS.

Exposed conductive part

is a conductive part that can be touched under the provisions of the IPXXB protection degree and that is not normally energized, but that can become electrically energized under isolation fault conditions. This includes parts under a cover if the cover can be removed without using tools.

External charging mode

means the vehicle mode when the REESS is charging with external electric power supply connected through the charge connector to the vehicle charge inlet.

External electric power supply

is a power supply external to the vehicle that provides electric power to charge the electric energy storage device in the vehicle through the charge connector.

Fuel cell system

is a system containing the fuel cell stack(s), air processing system, fuel flow control system, exhaust system, thermal management system, and water management system.

High voltage live part

means a live part of a high voltage source.

High voltage source

means any electric component which is contained in the electric power train or conductively connected to the electric power train and has a working voltage greater than 30 VAC or 60 VDC.

Indirect contact

is the contact of any person or persons with exposed conductive parts.

Live part

is a conductive part of the vehicle that is electrically energized under normal vehicle operation.

Luggage compartment

is the space in the vehicle for luggage accommodation, separated from the passenger compartment by the front or rear bulkhead and bounded by a roof, hood or trunk lid, floor, and side walls, as well as by electrical protection barriers provided for protecting the occupants from direct contact with high voltage live parts.

Normal vehicle operation

includes operating modes and conditions that can reasonably be encountered during typical operation of the vehicle, such as driving, parking, and standing in traffic, as well as charging using chargers that are compatible with the specific charging ports installed on the vehicle. It does not include conditions where the vehicle is damaged, either by a crash or road debris, subjected to fire or water submersion, or in a state where service and/or maintenance is needed or being performed.

Parking mode

is the vehicle mode in which the vehicle power is turned off, the vehicle propulsion system and ancillary equipment such as the radio are not operational, and the vehicle is stationary.

Passenger compartment

is the space for occupant accommodation that is bounded by the roof, floor, side walls, doors, outside glazing, front bulkhead and rear bulkhead or rear gate, as well as electrical protection barriers provided for protecting the occupants from direct contact with high voltage live parts.

Propulsion system

means an assembly of electric or electro-mechanical components or circuits that propel the vehicle using the energy that is supplied by a high voltage source. This includes, but is not limited to, electric motors, inverters/converters, and electronic controllers.

Protection degree IPXXB

is protection from contact with high voltage live parts. It is tested by probing electrical protection barriers with the jointed test finger probe, IPXXB, in figure 7b to this standard.

Protection degree IPXXD

is protection from contact with high voltage live parts. It is tested by probing electrical protection barriers with the test wire probe, IPXXD, in figure 7a to this standard.

Rechargeable Electrical Energy Storage System (REESS)

means the rechargeable electric energy storage system that provides electric energy for electrical propulsion.

Rupture

means an opening through the casing of the REESS that would permit the IPXXB test probe to penetrate and contact live parts.

Service disconnect

is the device for deactivation of an electrical circuit when conducting checks and services of the vehicle electrical propulsion system.

State of charge (SOC)

means the available electrical charge in a REESS expressed as a percentage of the normal operating capacity specified by the vehicle manufacturer.

Thermal event

means the condition when the temperature within the REESS is significantly higher than the maximum operating temperature.

Thermal runaway

means an uncontrolled increase of cell temperature caused by exothermic reactions inside the cell.

Thermal propagation

means the sequential occurrence of thermal runaway within a REESS triggered by thermal runaway of a cell in the REESS.

VAC

means volts of alternating current (AC) expressed using the root mean square value.

VDC

means volts of direct current (DC).

Vehicle charge inlet

is the device on the electric vehicle into which the charge connector is inserted for the purpose of transferring energy and exchanging information from an external electric power supply.

Venting

means the release of excessive internal pressure from cell or battery in a manner intended by design to preclude rupture or explosion.

Working voltage

means the highest root mean square voltage of the voltage source, which may occur across its terminals or between its terminals and any conductive parts in open circuit conditions or under normal operating conditions.

S5. General requirements.

S5.1 Vehicles of GVWR of 4,536 kilograms (kg) or less (light vehicles). Each vehicle with a GVWR of 4,536 kg or less shall meet the requirements set forth in S6 (normal vehicle operation safety), S8 (post-crash safety), S11 (vehicle controls managing REESS safe operations), S13 (warning in the case of thermal event in REESS), and S14 (water exposure safety) of this standard.

S5.2 Vehicles with a GVWR greater than 4,536 kg other than school buses (heavy vehicles other than school buses). Each heavy vehicle with a GVWR greater than 4,536 kg, other than school buses, shall meet the requirements set forth in S6 (normal vehicle operation safety), S11 (vehicle controls managing REESS safe operations), S13 (warning in the case of thermal event in REESS), and S14 (water exposure safety) of this standard.

S5.3 School buses with a GVWR greater than 4,536 kg. Each school bus with a GVWR greater than 4,536 kg shall meet the requirements set forth in S6 (normal vehicle operation safety), S8 (post-crash safety), S11 (vehicle controls managing REESS safe operations), S13 (warning in the case of thermal event in REESS), and S14 (water exposure safety) of this standard.

S6. Normal vehicle operation safety. Each vehicle to which this standard applies must meet the requirements in S6.1 to S6.6 of this standard, when tested according to the relevant provisions in S7 of this standard.

S6.1 Protection against direct contact.

S6.1.1 Marking. The symbol shown in figure 6 to this standard shall be present on or near electric energy storage devices. The symbol in figure 6 shall also be visible on electrical protection barriers which, when removed, expose live parts of high voltage sources. The symbol shall be yellow and the bordering and the arrow shall be black.

S6.1.1.1 The marking is not required for electrical protection barriers that cannot be physically accessed, opened, or removed without the use of tools. Markings are not required for electrical connectors or the vehicle charge inlet.

S6.1.2 High voltage cables. Cables for high voltage sources which are not located within electrical protection barriers shall be identified by having an outer covering with the color orange.

S6.1.3 Service disconnect. For a service disconnect which can be opened, disassembled, or removed without tools, protection degree IPXXB shall be provided when tested under procedures specified in S7.3.1 of this standard using the IPXXB test probe shown in figures 7a and 7b to this standard.

S6.1.4 Protection degree of high voltage live parts. (a) Protection degree IPXXD shall be provided for high voltage live parts inside the passenger or luggage compartment when tested according to the procedures specified in S7.3.1 of this standard using the IPXXD test probe shown in figure 7a to this standard.

(b) Protection degree IPXXB shall be provided for high voltage live parts in areas other than the passenger or luggage compartment when tested according to the procedures specified in S7.3.1 of this standard using the IPXXB test probe shown in figures 7a and 7b to this standard. High voltage live parts that are not energized except during charging of the REESS are excluded from protection degree IPXXB if they are located on the vehicle roof such that the wrap around distance from the instep of the vehicle, or the lowest step (if multiple steps are present) of the vehicle, to the high voltage source is at least 3 meters.

S6.1.5 Connectors. All connectors shall provide direct contact protection by:

(a) Meeting the requirements specified in S6.1.4 when the connector is connected to its corresponding mating component; and,

(b) If a connector can be separated from its mating component without the use of a tool, meeting at least one of the following conditions from S6.1.5(b)(1), (2), or (3):

(1) The connector meets the requirements of S6.1.4 when separated from its mating component;

(2) The voltage of the live parts becomes less than or equal to 60 VDC or 30 VAC within one second after the connector is separated from its mating component; or

(3) The connector requires at least two distinct actions to separate from its mating component and there are other components that must be removed in order to separate the connector from its mating component and these other components cannot be removed without the use of tools.

S6.1.6 Vehicle charge inlet. Direct contact protection for a vehicle charge inlet shall be provided by meeting the requirements specified in S6.1.4 when the charge connector is connected to the vehicle inlet and by meeting at least one of the requirements of S6.1.6(a) or (b).

(a) The vehicle charge inlet meets the requirements of S6.1.4 when the charge connector is not connected to it; or

(b) The voltage of the high voltage live parts becomes equal to or less than 60 VDC or equal to or less than 30 VAC within 1 second after the charge connector is separated from the vehicle charge inlet.

S6.2 Protection against indirect contact.

S6.2.1 The resistance between all exposed conductive parts of electrical protection barriers and the electrical chassis shall be less than 0.1 ohms when tested according to the procedures specified in S7.3.2 of this standard.

S6.2.2 The resistance between any two simultaneously reachable exposed conductive parts of the electrical protection barriers that are less than 2.5 meters from each other shall be less than 0.2 ohms when tested according to the procedures specified in S7.3.2 of this standard.

S6.3 Electrical isolation.

S6.3.1 Electrical isolation of AC and DC high voltage sources. The electrical isolation of a high voltage source, determined in accordance with the procedure specified in S7.2 of this standard, must be greater than or equal to one of the following:

(a) 500 ohms/volt for an AC high voltage source;

(b) 100 ohms/volt for an AC high voltage source if it is conductively connected to a DC high voltage source, but only if the AC high voltage source meets the requirements for protection against direct contact in S6.1.4 and the protection from indirect contact in S6.2; or

(c) 100 ohms/volt for a DC high voltage source.

S6.3.2 Exclusion of high voltage sources from electrical isolation requirements. A high voltage source that is conductively connected to an electric component which is conductively connected to the electrical chassis and has a working voltage less than or equal to 60 VDC, including a pulsating DC voltage source without a change in polarity, is not required to meet the electrical isolation requirements in S6.3.1 if the voltage between the high voltage source and the electrical chassis is less than or equal to 30 VAC or 60 VDC.

S6.3.3 Electrical isolation of high voltage sources for charging the electric energy storage device. For the vehicle charge inlet intended to be conductively connected to the AC external electric power supply, the electric isolation between the electrical chassis and the high voltage sources that are conductively connected to the vehicle charge inlet during charging of the electric energy storage device shall be greater than or equal to 500 ohms/volt when the charge connector is disconnected. The electrical isolation is measured at the high voltage live parts of the vehicle charge inlet and determined in accordance with the procedure specified in S7.2 of this standard. During the measurement, the electric energy storage device may be disconnected.

S6.4 Electrical isolation monitoring. DC high voltage sources of vehicles with a fuel cell system shall be monitored by an electrical isolation monitoring system that displays a warning for loss of isolation when tested according to S7.4 of this standard. The system must monitor its own readiness and the visual warning display must be provided to the driver. For a vehicle with automated driving systems and without manually operated driving controls, the visual warning must be provided to all the front row occupants.

S6.5 Electric shock protection during charging. For motor vehicles with an electric energy storage device that can be charged through a conductive connection with a grounded external electric power supply, a device to enable conductive connection of the electrical chassis to the earth ground shall be provided. This device shall enable connection to the earth ground before exterior voltage is applied to the vehicle and retain the connection until after the exterior voltage is removed from the vehicle.

S6.6 Mitigating driver error.

S6.6.1 Indicator of active driving possible mode. At least a momentary indication shall be given to the driver each time the vehicle is first placed in active driving possible mode after manual activation of the propulsion system. This requirement does not apply under conditions where an internal combustion engine directly or indirectly provides the vehicle's propulsion power when the vehicle is first placed in the active driving possible mode after manual activation of the propulsion system.

S6.6.2 Indicator of active driving possible mode when leaving the vehicle. When leaving the vehicle, the driver shall be informed by an auditory or visual signal if the vehicle is still in the active driving possible mode.

S6.6.3 Prevent drive-away. If the on-board electric energy storage device can be externally charged, vehicle movement of more than 150 mm by its own propulsion system shall not be possible as long as the charge connector of the external electric power supply is physically connected to the vehicle charge inlet in a manner that would permit charging of the electric energy storage device.

S7. Electrical safety test procedures for normal vehicle operation safety. The following provisions specify the test procedures associated with the requirements of S6 of this standard.

S7.1 Voltage measurements. For the purpose of determining the voltage level of the high voltage source, voltage is measured as shown in figure 1 to this standard using a voltmeter that has an internal resistance of at least 10 MΩ. All post-crash voltage measurements for determining electrical isolation of high voltage sources specified in S8.2(a) of this standard are made at least 10 seconds after impact. All post-crash voltage measurements for determining the voltage levels specified in S8.2(b) of this standard and the energy in capacitors specified in S8.2(d) of this standard are made between 10 to 60 seconds after impact.

S7.1.1 For a high voltage source that has an automatic disconnect that is physically contained within itself, the voltage measurement after the test is made from the side of the automatic disconnect connected to the electric power train or to the rest of the electric power train if the high voltage source is a component contained in the power train. For a high voltage source that has an automatic disconnect that is not physically contained within itself, the voltage measurement after the test is made from both the high voltage source side of the automatic disconnect and from the side of the automatic disconnect connected to the electric power train or to the rest of the electric power train if the high voltage source is a component contained in the power train.

S7.1.2 Voltage Vb is measured across the two terminals of the voltage source. Before a vehicle crash test, Vb is equal to or greater than the working voltage as specified by the vehicle manufacturer.

S7.1.3 Voltage V1 is measured between the negative side of the high voltage source and the electrical chassis as shown in figure 2 to this standard. Voltage V2 is measured between the positive side of the high voltage source and the electrical chassis as shown in figure 3 to this standard.

S7.2 Test method for determining electrical isolation. Measure the voltages V1, V2, and Vb as shown in figure 1 to this standard in accordance with S7.1.

S7.2.1 If V1 is greater than or equal to V2, insert a known resistance (Ro) between the negative side of the high voltage source and the electrical chassis. With the Ro installed, measure the voltage (V1') as shown in figure 4 to this standard between the negative side of the high voltage source and the electrical chassis. Calculate the electrical isolation resistance (Ri) according to the formula shown. Divide Ri (in ohms) by the working voltage of the high voltage source (in volts) to obtain the electrical isolation (in ohms/volt).

S7.2.2 If V2 is greater than V1, insert a known resistance (Ro) between the positive side of the high voltage source and the electrical chassis. With the Ro installed, measure the voltage (V2') as shown in figure 5 to this standard between the positive side of the high voltage source and the electrical chassis. Calculate the electrical isolation resistance (Ri) according to the formula shown. Divide Ri (in ohms) by the working voltage of the high voltage source (in volts) to obtain the electrical isolation (in ohms/volt).

S7.3 Test methods for evaluating physical barrier protection.

S7.3.1 Test method to evaluate protection from direct contact with high voltage sources. (a) Any parts surrounding the high voltage components are opened, disassembled, or removed without the use of tools.

(b) The selected access probe is inserted into any gaps or openings of the electrical protection barrier with a test force between 9 Newton to 11 Newton with the IPXXB probe or 1 Newton to 2 Newton with the IPXXD probe. If the probe partly or fully penetrates into the electrical protection barrier, it is placed in every possible position to evaluate contact with high voltage live parts. If partial or full penetration into the electrical protection barrier occurs with the IPXXB probe, the IPXXB probe shall be placed as follows: starting from the straight position, both joints of the test finger are rotated progressively through an angle of up to 90 degrees with respect to the axis of the adjoining section of the test finger and are placed in every possible position.

(c) A low voltage supply (of not less than 40 V and not more than 50 V) in series with a suitable lamp may be connected between the access probe and any high voltage live parts inside the electrical protection barrier to indicate whether high voltage live parts were contacted.

(d) A mirror or fiberscope may be used to inspect whether the access probe touches high voltage live parts inside the electrical protection barrier.

(e) Protection degree IPXXD or IPXXB is verified when the following conditions are met:

(1) The access probe does not touch high voltage live parts. The IPXXB access probe may be manipulated as specified in S7.3.1(b) for evaluating contact with high voltage live parts. The methods specified in S7.3.1(c) or S7.3.1(d) may be used to aid the evaluation. If method S7.3.1(c) is used for verifying protection degree IPXXB or IPXXD, the lamp shall not light up.

(2) The stop face of the access probe does not fully penetrate into the electrical protection barrier.

S7.3.2 Test method to evaluate protection against indirect contact with high voltage sources. Any parts surrounding the high voltage components are opened, disassembled, or removed without the use of tools. At the option of the manufacturer, protection against indirect contact with high voltage sources shall be determined using the test method in S7.3.2(a) or (b).

(a) Test method using a resistance tester. The resistance tester is connected to the measuring points (the electrical chassis and any exposed conductive part of electrical protection barriers or any two simultaneously reachable exposed conductive parts of electrical protection barriers that are less than 2.5 meters from each other), and the resistance is measured using a resistance tester that can supply current levels of at least 0.2 Amperes with a resolution of 0.01 ohms or less. The resistance between two exposed conductive parts of electrical protection barriers that are less than 2.5 meters from each other may be calculated using the separately measured resistances of the relevant parts of the electric path.

(b) Test method using a DC power supply, voltmeter, and ammeter. (1) Connect the DC power supply, voltmeter, and ammeter to the measuring points (the electrical chassis and any exposed conductive part or any two simultaneously reachable exposed conductive parts that are less than 2.5 meters from each other) as shown in figure 8 to this standard.

(2) Adjust the voltage of the DC power supply so that the current flow becomes more than 0.2 Amperes.

(3) Measure the current I and the voltage V shown in figure 8 to this standard.

(4) Calculate the resistance R according to the formula, R = V/I.

(5) The resistance between two simultaneously reachable exposed conductive parts of electrical protection barriers that are less than 2.5 meters from each other may be calculated using the separately measured resistances of the relevant parts of the electric path.

S7.3.3 Test method to determine voltage between exposed conductive parts of electrical protection barriers and the electrical chassis and between exposed conductive parts of electrical protection barriers. (a) Any parts surrounding the high voltage components are opened, disassembled, or removed without the use of tools.

(b) Connect the voltmeter to the measuring points (exposed conductive part of an electrical protection barrier and the electrical chassis or any two simultaneously reachable exposed conductive parts of electrical protection barriers that are less than 2.5 meters from each other).

(c) Measure the voltage.

(d) The voltage between two simultaneously reachable exposed conductive parts of electrical protection barriers that are less than 2.5 meters from each other may be calculated using the separately measured voltages between the relevant electrical protection barriers and the electrical chassis.

S7.4 Test method for evaluating on-board electrical isolation monitoring system. Prior to any impact test, the requirements of S6.4 of this standard for the on-board electrical isolation monitoring system shall be tested using the following procedure.

(a) The electric energy storage device is at the state of charge specified in S7.1.

(b) The switch or device that provides power from the electric energy storage/conversion system to the propulsion system is in the activated position or the ready-to-drive position.

(c) Determine the isolation resistance, Ri, of the high voltage source with the electrical isolation monitoring system using the procedure outlined in S7.2.

(d) Insert a resistor with resistance Ro equal to or greater than 1/(1/(95 times the working voltage of the high voltage source)−1/Ri) and less than 1/(1/(100 times the working voltage of the high voltage source)−1/Ri) between the positive terminal of the high voltage source and the electrical chassis.

(e) The electrical isolation monitoring system indicator shall provide a visual warning to the driver. For a vehicle with automated driving systems and without manually operated driving controls, the visual warning must be provided to all the front row occupants.

S7.5 Test method for determining post-crash energy in capacitors. (a) Prior to the crash tests, the vehicle manufacturer must identify the capacitors, type of capacitors (x-capacitors and y-capacitors) and their respective capacitance (Cx and Cy 1 and Cy 2 ) in the electric power train for which the low energy compliance option for post-crash electrical safety in S8.2(d) of this standard is applied.

(b) Voltages Vb, V1, and V2 are measured across the capacitors in accordance with S7.1.

(c) The total energy in a x-capacitor is equal to 0.5 × Cx × Vb 2 .

(d) The total energy in the y-capacitor Cy 1 is equal to 0.5 × Cy 1 × V1 2 and the total energy in the y-capacitor Cy 2 is equal to 0.5 × Cy 2 × V2 2 .

S8. Post-crash safety. Each vehicle with a GVWR of 4,536 kg or less to which this standard applies must meet the requirements in S8.1, S8.2, S8.3, and S8.4 when tested according to S9 of this standard under the conditions of S10 of this standard. Each school bus with a GVWR greater than 4,536 kg to which this standard applies must meet the requirements in S8.1, S8.2, S8.3, and S8.4 when tested according to S9.5 of this standard under the conditions of S10.

S8.1 Fire safety. Starting from the time of impact and continuing until one hour after the completion of the sequence of tests specified in S9 of this standard, there shall be no evidence of fire or explosion in any part of the vehicle. The assessment of fire or explosion is verified by visual inspection without disassembly of the REESS or vehicle.

S8.2 Electrical safety. After each test specified in S9 of this standard, each high voltage source in a vehicle must meet one of the following electrical safety requirements: electrical isolation requirements of S8.2(a), the voltage level requirements of S8.2 (b), or the physical barrier protection requirements of S8.2(c); or the high voltage capacitors in the electric power train must meet the low-energy requirements of S8.2(d).

(a) The electrical isolation of the high voltage source, determined in accordance with the procedure specified in S7.2 of this standard, must be greater than or equal to one of the following:

(1) 500 ohms/volt for an AC high voltage source;

(2) 100 ohms/volt for an AC high voltage source if it is conductively connected to a DC high voltage source, but only if the AC high voltage source meets the physical barrier protection requirements specified in S8.2(c)(1) and (2); or

(3) 100 ohms/volt for a DC high voltage source.

(b) The voltages V1, V2, and Vb of the high voltage source, measured according to the procedure specified in S7.1 of this standard, must be less than or equal to 30 VAC for AC components or 60 VDC for DC components.

(c) Protection against electric shock by direct and indirect contact (physical barrier protection) shall be demonstrated by meeting the following three conditions:

(1) The high voltage source (AC or DC) meets the protection degree IPXXB when tested according to the procedure specified in S7.3.1 of this standard using the IPXXB test probe shown in figures 7a and 7b to this standard;

(2) The resistance between exposed conductive parts of the electrical protection barrier of the high voltage source and the electrical chassis is less than 0.1 ohms when tested according to the procedures specified in S7.3.2 of this standard. In addition, the resistance between an exposed conductive part of the electrical protection barrier of the high voltage source and any other simultaneously reachable exposed conductive parts of electrical protection barriers within 2.5 meters of it must be less than 0.2 ohms when tested using the test procedures specified in S7.3.2 of this standard; and

(3) The voltage between exposed conductive parts of the electrical protection barrier of the high voltage source and the electrical chassis is less than or equal to 30 VAC or 60 VDC as measured in accordance with S7.3.3 of this standard. In addition, the voltage between an exposed conductive part of the electrical protection barrier of the high voltage source and any other simultaneously reachable exposed conductive parts of electrical protection barriers within 2.5 meters of it must be less than or equal to 30 VAC or 60 VDC as measured in accordance with S7.3.3 of this standard.

(d) The total energy of unidirectional single impulse currents from capacitors shall be less than 0.2 Joules when determined in accordance with the procedure specified in S7.5 of this standard.

S8.3 Electric energy storage/conversion device retention. During and after each test specified in S9 of this standard:

(a) Electric energy storage/conversion devices shall remain attached to the vehicle by at least one component anchorage, bracket, or any structure that transfers loads from the device to the vehicle structure, and

(b) Electric energy storage/conversion devices located outside the occupant compartment shall not enter the occupant compartment.

S8.4 Electrolyte leakage from electric energy storage devices. Not more than 5.0 liters of electrolyte shall leak from electric energy storage devices, and no visible trace of electrolyte shall leak into the passenger compartment. Leakage is measured from the time of the impact until 30 minutes thereafter, and throughout any static rollover after a barrier impact test, specified in S9 of this standard.

S9. Crash test specifications. A test vehicle with a GVWR less than or equal to 4,536 kg, under the conditions of S10 of this standard, is subject to any one single barrier crash test of S9.1, S9.2, or S9.3, followed by the static rollover test of S9.4. A school bus with a GVWR greater than 4,536 kg, under the conditions of S10, is subject to the contoured barrier crash test of S9.5. A particular vehicle need not meet further test requirements after having been subjected to a single barrier crash/static rollover test sequence.

S9.1 Frontal barrier crash. The test vehicle, with test dummies in accordance with S6.1 of §571.301, traveling longitudinally forward at any speed up to and including 48 km/h, impacts a fixed collision barrier that is perpendicular to the line of travel of the vehicle, or at an angle up to 30 degrees in either direction from the perpendicular to the line of travel of the vehicle.

S9.2 Rear moving barrier impact. The test vehicle, with test dummies in accordance with S6.1 of §571.301, is impacted from the rear by a barrier that conforms to S7.3(b) of §571.301 and that is moving at any speed between 79 and 81 km/h.

S9.3 Side moving deformable barrier impact. The test vehicle, with the appropriate 49 CFR part 572 test dummies specified in §571.214 at positions required for testing by S7.1.1, S7.2.1, or S7.2.2 of Standard 214 (§571.214), is impacted laterally on either side by a moving deformable barrier moving at any speed between 52.0 km/h and 54.0 km/h.

S9.4 Post-impact test static rollover. After each crash test specified in S9.1, S9.2, and S9.3, without any alteration of the vehicle, the vehicle is rotated on its longitudinal axis to each successive increment of 90 degrees under the test conditions of S10.3 of this standard.

S9.5 Moving contoured barrier crash. The test vehicle, under the conditions of S10.1 and S10.2 of this standard, is impacted at any point and at any angle by the moving contoured barrier assembly, specified in S7.5 and S7.6 in §571.301, traveling longitudinally forward at any speed up to and including 48 km/h.

S10. Crash test conditions.

S10.1 State of charge. The electric energy storage device(s) shall be at the state of charge specified in either S10.1(a), (b), or (c):

(a) At the maximum state of charge in accordance with the vehicle manufacturer's recommended charging procedures, as stated in the vehicle owner's manual or on a label that is permanently affixed to the vehicle; or

(b) If the manufacturer has made no recommendation for charging procedures in the owner's manual or on a label permanently affixed to the vehicle, at a state of charge of not less than 95 percent of the maximum capacity of the electric energy storage device(s); or

(c) If the electric energy storage device(s) is/are rechargeable only by an energy source on the vehicle, at any state of charge within the normal operating voltage defined by the vehicle manufacturer.

S10.2 Vehicle conditions. The switch or device that provides power from the electric energy storage/conversion system to the propulsion system is in the activated position or the ready-to-drive position. Bypass any devices or systems that do not allow the propulsion system to be energized at the time of impact when the vehicle ignition is on and the vehicle is in neutral.

S10.2.1 The parking brake is disengaged and the vehicle drive system is in the neutral position. In a test conducted under S9.3 of this standard, the parking brake is set.

S10.2.2 Tires are inflated to the manufacturer's specifications.

S10.2.3 The vehicle, including test devices and instrumentation, is loaded as follows:

(a) A passenger car is loaded to its unloaded vehicle weight plus its rated cargo and luggage capacity weight, secured in the luggage compartment, plus the necessary test dummies as specified in S9 of this standard, restrained only by means that are installed in the vehicle for protection at its seating position.

(b) A multipurpose passenger vehicle, truck, or bus, with a GVWR of 4,536 kg (10,000 lb) or less, is loaded to its unloaded vehicle weight plus the necessary dummies, as specified in S9 of this standard, plus 136 kg or its rated GVWR, whichever is less, secured in the load carrying area and distributed as nearly as possible in proportion to its GVWR. For the purpose of this standard, unloaded vehicle weight does not include the weight of work-performing accessories. Each dummy is restrained only by means that are installed in the vehicle for protection at its seating position.

(c) A school bus with a GVWR greater than 4,536 kg is loaded to its unloaded vehicle weight, plus 54 kg of unsecured mass at each designated seating position.

S10.3 Static rollover test conditions. The vehicle is rotated about its longitudinal axis, with the axis kept horizontal, to each successive increment of 90°, 180°, and 270° at a uniform rate, with 90° of rotation taking place in any time interval from 1 to 3 minutes. After reaching each 90° increment the vehicle is held in that position for 5 minutes.

S10.4 Rear moving barrier impact test conditions. The conditions of S7.3(b) and S7.6 of §571.301 apply to the conducting of the rear moving deformable barrier impact test specified in S9.2 of this standard.

S10.5 Side moving deformable barrier impact test conditions. The conditions of S8.9, S8.10, and S8.11 of §571.214 apply to the conduct of the side moving deformable barrier impact test specified in S9.3 of this standard.

S11. Vehicle controls managing REESS safe operations. Each vehicle to which the standard applies shall meet the requirements in S11.1, when tested according to S12 of this standard and the requirements in S11.2.

S11.1 When tested in accordance with the overcharge test in S12.1, the over-discharge test in S12.2, the overcurrent test in S12.3, the high-temperature test in S12.4, and the short circuit test in accordance with S12.5 of this standard, each vehicle shall meet the following:

(a) During the test, there shall be no evidence of electrolyte leakage, rupture, venting, fire, or explosion of the REESS as verified by visual inspection without disassembly of the vehicle.

(b) The isolation resistance of the high voltage sources measured after the test shall not be less than 100 ohms/volt when determined in accordance with S7.2 of this standard.

S11.2 In the event of operational failure of the vehicle controls that manage safe operation of the REESS, the vehicle must provide a visual warning while in active driving possible mode. The warning system shall monitor its own readiness and the visual warning must be provided to the driver. For a vehicle with automated driving systems and without manually operated driving controls, the visual warning must be provided to all the front row occupants.

S12. Test methods for evaluating vehicle controls managing REESS safe operations.

S12.1 Overcharge test. The overcharge test is conducted at ambient temperatures between 10 °C and 30 °C, with the vehicle REESS initially set between 90 to 95 percent SOC. The following steps are conducted to evaluate the vehicle's overcharge protection controls:

(a) A breakout harness is connected to the traction side of the REESS. The manufacturer must specify an appropriate location(s) and attachment point(s) to connect the breakout harness.

(b) Temperature probes are connected to the REESS outer casing to monitor changes in REESS temperature. Temperature measurements may also be obtained through communication with the REESS control module.

(c) The external charge/discharge equipment, with maximum voltage and current set at least 10 percent higher than the REESS voltage and current limits, is connected to the breakout harness.

(d) The vehicle switch or device that provides power to the vehicle controls that manage REESS operations is set to the activated position.

(e) The REESS is charged with the external charge/discharge equipment with the maximum charge current specified by the manufacturer. If the manufacturer does not specify an appropriate charge current, then a charge rate of 1/3 C is used.

(f) Charging is continued until one of the following occurs:

(1) The overcharge protection control terminates the charge current;

(2) The REESS temperature is 10 °C above the manufacturer-specified maximum operating temperature of the REESS; or

(3) 12 hours have passed since the start of charging the vehicle.

(g) After the charge current is terminated, if charge and discharge are permitted by the vehicle controls, a standard cycle is performed in accordance with S12.6.

(h) After the completion of the standard cycle, or if the standard cycle was not performed, after charging is terminated, the vehicle is observed for 1 hour for evidence of electrolyte leakage, rupture, venting, fire, or explosion of the REESS.

(i) At the conclusion of the test, electrical isolation of the REESS is determined in accordance with S7.2 of this standard.

S12.2 Over-discharge test. The over-discharge test is conducted at ambient temperatures between 10 °C and 30 °C, with the vehicle REESS initially set between 10 and 15 percent SOC. For a vehicle with on-board energy conversion systems such as an internal combustion engine or a fuel cell, the fuel supply is set to the minimum level where active driving possible mode is permitted. The following steps are conducted to evaluate the vehicle's over-discharge protection controls:

(a) A breakout harness is connected to the traction side of the REESS. The manufacturer must specify an appropriate location(s) and attachment point(s) to connect the breakout harness.

(b) Temperature probes are connected to the REESS outer casing to monitor changes in REESS temperature. Temperature measurements may also be obtained through communication with the REESS control module.

(c) The external charge/discharge equipment, with maximum voltage and current set at least 10 percent higher than the REESS voltage and current limits, is connected to the breakout harness.

(d) The vehicle switch or device that provides power from the REESS to the electric power train is set to the activated position or the active driving possible mode.

(e) The REESS is discharged with the external charge/discharge equipment with the maximum discharge rate under normal operating conditions specified by the manufacturer. If the manufacturer does not specify an appropriate discharge rate, a power load of 1kW is used.

(f) Discharging is continued until one of the following occurs:

(1) The over-discharge protection control terminates the discharge current;

(2) The temperature gradient of the REESS is less than 4°C through 2 hours from the start of discharge; or

(3) The vehicle is discharged to 25 percent of its working voltage level.

(g) After the discharge current is terminated, a standard cycle is performed in accordance with S12.6, if charge and discharge are permitted by the vehicle controls.

(h) After the completion of the standard cycle, or if the standard cycle was not performed, after discharging is terminated, the vehicle is observed for 1 hour for evidence of electrolyte leakage, rupture, venting, fire, or explosion of the REESS.

(i) At the conclusion of the test, electrical isolation of the REESS is determined in accordance with S7.2 of this standard.

S12.3 Overcurrent test. The overcurrent test is only conducted on vehicles that have the capability of charging by DC external electricity supply. The test is conducted at ambient temperatures between 10 °C and 30 °C, with the vehicle REESS initially set between 40 to 50 percent SOC. The following steps are conducted to evaluate the vehicle's over-current protection controls:

(a) A breakout harness is connected to the traction side of the REESS. The manufacturer must specify an appropriate location(s) and attachment point(s) to connect the breakout harness.

(b) Temperature probes are connected to the REESS outer casing to monitor changes in REESS temperature. Temperature measurements may also be obtained through communication with the REESS control module.

(c) The external charge/discharge equipment, with maximum voltage and current set at least 10 percent higher than the REESS voltage and current limits, is connected to the breakout harness.

(d) The vehicle switch or device that provides power to the vehicle controls that manage REESS operations is set to the activated position.

(e) The REESS is charged with the external charge/discharge equipment with the maximum charge current specified by the manufacturer. If the manufacturer does not specify an appropriate charge current, then a charge rate of 1/3 C is used.

(f) After charging is initiated, the overcurrent specified by the manufacturer is supplied over the course of 5 seconds from the maximum charge current level to the over-current level. If the vehicle manufacturer does not supply an overcurrent level, a 10 Ampere over-current is supplied over 5 seconds. If charging is not terminated, the over-current supply is increased in steps of 10 Amperes.

(g) Charging at the over-current level is continued until one of the following occurs:

(1) The over-current protection control terminates the charge current; or

(2) The temperature gradient of the REESS is less than 4 °C through 2 hours from the first overcurrent input.

(h) After the charge current is terminated, if charge and discharge are permitted by the vehicle controls, a standard cycle is performed in accordance with S12.6.

(i) After the completion of the standard cycle or if the standard cycle was not performed, after charging is terminated, the vehicle is observed for 1 hour for evidence of electrolyte leakage, rupture, venting, fire, or explosion of the REESS.

(j) At the conclusion of the test, electrical isolation of the REESS is determined in accordance with S7.2 of this standard.

S12.4 Over-temperature test. The overtemperature test is conducted at ambient temperatures between 10 °C and 30 °C on a chassis-dynamometer with the vehicle REESS initially set between 90 to 95 percent SOC. For a vehicle with on-board energy conversion systems such as an internal combustion engine or a fuel cell, the fuel supply is set to allow operation for about one hour of driving. The following steps are conducted to evaluate the vehicle's high temperature protection controls:

(a) The cooling system of the REESS is disabled using manufacturer supplied information. For an REESS that will not operate if the cooling system is disabled, the cooling operation is significantly reduced. If manufacturer does not supply information to disable or significantly reduce the cooling system, methods such as crimping the liquid cooling hose, removing refrigerant fluid, or blocking cabin air intakes for air cooled REESS are applied.

(b) Temperature probes are connected to the REESS outer casing to monitor changes in REESS temperature. Temperature measurements may also be obtained through communication with the REESS control module.

(c) The vehicle is installed on a chassis dynamometer and the vehicle switch or device that provides power from the REESS to the electric power train is set to the activated position or the active driving possible mode.

(d) The vehicle is driven on the dynamometer using an appropriate vehicle manufacturer supplied drive profile and charging information for discharge and charge of the REESS to raise the REESS temperature to its upper boundary safe operating temperature within one hour. If an appropriate manufacturer-supplied drive profile is not available, the vehicle is repeatedly accelerated to 80 mph and then decelerated to 15 mph within 40 seconds. If the manufacturer does not supply a charge profile, then a charge rate greater than 1/3 C current is used.

(e) The discharge/charge procedure on the chassis-dynamometer is continued until one of the following occurs:

(1) The vehicle terminates the discharge/charge cycle;

(2) The temperature gradient of the REESS is less than 4 °C through 2 hours from the start of the discharge/charge cycle; or

(3) Three (3) hours have passed since the start of discharge/charge cycles.

(f) After the discharge and charge procedure is terminated, if charge and discharge are permitted by the vehicle controls, a standard cycle is performed in accordance with S12.6.

(g) After the completion of the standard cycle, or if the standard cycle is not performed, after the discharge and charge procedure is terminated, the vehicle is observed for 1 hour for evidence of electrolyte leakage, rupture, venting, fire, or explosion of the REESS.

(h) At the conclusion of the test, electrical isolation of the REESS is determined in accordance with S7.2 of this standard.

S12.5 External short circuit test. The short circuit test is conducted at ambient conditions with the vehicle REESS initially set between 90 to 95 percent SOC. The following steps are conducted to evaluate the vehicle's external short circuit protection controls:

(a) A breakout harness is connected to the REESS. The manufacturer must specify an appropriate location(s) and attachment point(s) to connect the breakout harness.

(b) Temperature probes are connected to the REESS outer casing to monitor changes in REESS temperature. Temperature measurements may also be obtained through communication with the REESS control module.

(c) The vehicle switch or device that provides power to the vehicle controls that manage REESS operations is set to the activated position.

(d) The short circuit contactor (with the contactors in open position) is connected to the breakout harnesses. The total resistance of the equipment to create the external short circuit (short circuit contactor and breakout harnesses) is verified to be between 2 to 5 milliohms.

(e) The short circuit contactor is closed to initiate the short circuit.

(f) The short circuit condition is continued until one of the following occurs:

(1) Short circuit current is terminated; or

(2) The temperature gradient of the REESS is less than 4 °C through 2 hours from the start of initiating the short circuit condition.

(g) After the short circuit current is terminated, if charge and discharge are permitted by the vehicle controls, a standard cycle is performed in accordance with S12.6.

(h) After the completion of the standard cycle, or if the standard cycle was not performed, after short circuit current is terminated, the vehicle is observed for 1 hour for evidence of electrolyte leakage, rupture, venting, fire, or explosion of the REESS.

(i) At the conclusion of the test, electrical isolation of the REESS is determined in accordance with S7.2 of this standard.

S12.6 Standard cycle. The standard cycle is conducted at ambient temperatures between 10 °C and 30 °C and starts with a standard discharge followed by a standard charge. The discharge and charge procedures would follow manufacturer supplied information. The charge procedure is initiated 15 minutes after discharge is terminated.

(a) If the manufacturer does not provide a discharge procedure, the vehicle is discharged with 1C current until discharge is terminated by vehicle controls.

(b) If the manufacturer does not provide a charge procedure, the vehicle is charged with 1/3 C current until terminated by vehicle controls.

S13. Warning in the case of thermal event in REESS. The vehicle shall provide a warning to the driver in the case of a thermal event in the REESS when the vehicle is in active driving possible mode. The thermal event warning system must monitor its own readiness. The warning shall activate within three minutes of the onset of the thermal event. The warning shall consist of auditory and visual signals that remain active for at least 5 minutes. For a vehicle with automated driving systems and without manually operated driving controls, the visual warning must be provided to all the front row occupants.

S14. Water exposure safety. Each vehicle to which the standard applies shall maintain electrical isolation as specified in S6.3.1 and S6.3.2 of this standard at these times:

(a) Just after exposure to water in each of the two tests specified below and with the vehicle still wet; and

(b) After a minimum of 24 hours after completing each of the tests specified in S14.1 and S14.2.

S14.1 Vehicle washing test. The vehicle is sprayed from any direction with a stream of freshwater from a standard test nozzle shown in figure 9 to this standard that has a nozzle internal diameter of 6.3 millimeters, delivery rate of 11.9 to 13.2 liters/minute, and water pressure at the nozzle between 30 kPa to 35 kPa.

(a) During the washing, the distance from the nozzle to the vehicle surface is 3.0 to 3.2 meters. The distance of the nozzle from the vehicle surface may be reduced, if necessary, to ensure the surface is wet when spraying upwards. The washing test duration per square meter of the vehicle surface area is 60 to 75 seconds, with a minimum total test duration of 3 minutes.

(b) The vehicle external surface, including the vehicle sides, front, rear, top, and bottom is exposed to the water stream. Border lines on the vehicle such glass seals, outline of opening parts (doors, windows, vehicle inlet cover), outline of front grille, and seals of vehicle lamps are exposed to the water stream from any direction.

(c) At the conclusion of the normal washing test, with the vehicle still wet, electrical isolation is determined in accordance with S7.2 of this standard.

S14.2 Driving through standing water test. The vehicle is driven through a wade pool of at least 10 centimeters but not more than 15 centimeters depth of freshwater for a distance of 500 meters at a minimum speed of 12 mph (20 km/h) but not more than 15 mph (24 km/h).

(a) If the wade pool is less than 500 m in length, then the vehicle shall be driven through it several times for a total distance of 500 m. The total time, including the period outside of the wade pool, shall be less than 10 minutes.

(b) At the conclusion of the standing water test, with the vehicle still wet, electrical isolation is determined in accordance with S7.2 of this standard.

Figures to FMVSS No. 305a



Figure 1. Voltage Measurements of the High Voltage Source



Figure 2. Measurement for V1 Voltage Between the Negative Side of the High Voltage Source and the Electrical Chassis



Figure 3. Measurement for V2 Voltage Between the Positive Side of the High Voltage Source and the Electrical Chassis



Figure 4. Measurement for V1' Voltage Across Resistor Between Negative Side of the High Voltage Source and Electrical Chassis



Figure 5. Measurement for V2' Voltage Across Resistor Between Positive Side of the High Voltage Source and Electrical Chassis



Figure 6. Marking of High Voltage Sources



Figure 7a. Access Probes for the Tests of Direct Contact Protection. Access Probe IPXXB (Top) and Access Probe IPXXD (Bottom)



Figure 7b. Jointed Test Finger IPXXB



Figure 8. Connection To Determine Resistance Between Exposed Conductive Parts of Electrical Protection Barrier and Electrical Chassis



Figure 9. Standard Nozzle for IPX5 Water Exposure Test

[89 FR 104352, Dec. 20, 2024; 90 FR 9609, Feb. 14, 2025]

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