solid waste

Q&A: Are discarded sodium-sulfur batteries eligible for a RCRA exclusion if the sodium is reclaimed for use?

A question on June 24, 2020:

Daniel,

I’ve come across some of your training online – quite informative – and was wondering if I could run a RCRA question past you. I have a client with some sodium-sulfur batteries that are no longer needed for their intended purpose. There are very few recyclers globally who can handle sodium-sulfur batteries and this is mainly due to the presence of sodium which is reactive and when thermally treated is detrimental to the refractory liner in the furnace.

We are exploring an option where we would reclaim the sodium from the cell, which can be used in, or to make, other products. In this case, would the company extracting the sodium require a TSDF permit? Based on the following logic, I would argue they are not a TSDF because the reclaimed sodium is not a hazardous waste. They would, however, be considered a waste generator with respect to the remainder of the battery:

  • In order for a waste to be a hazardous waste, it must first be considered a solid waste (40 CFR 261.3).
  • Sodium is a by-product of the chemical reaction in a sodium-sulfur battery – it is not present when produced at 0% SOC and is generated through chemical reaction when charging the battery and is consumed when discharging the battery. The process is not fully reversible so there is always some residual sodium present. For this scenario, where the sodium is desired to be extracted, it is more advantageous for the battery to not be discharged to 0% SOC.
  • According to 40 CFR 261.2, Table 1, by-products exhibiting a characteristic of hazardous waste (sodium is reactive – D003) are not considered solid wastes when reclaimed. Per US EPA interpretations (which I have seen leveraged in your training) an analogy to this situation is a thermometer being reclaimed for its mercury. Because mercury is a Commercial Chemical Product, per 40 CFR 261.2, Table 1, it is not solid waste and therefore cannot be a hazardous waste.
  • The act of extracting the sodium now makes the remainder of the cell waste and the generator (the entity who extracted the sodium) would need to classify it for its hazardous properties. Assuming it is hazardous, the generator would likely take advantage of the universal waste option for management and disposal.

If you have time and are willing, I would appreciate your feedback on the above.

Stay safe and well,

My reply seeking more information that same day:

Thank you for contacting me. Please see below.

  • Q1: Is the battery a solid waste?
  • Q2: If it is a solid waste, is it a hazardous waste?
  • After that is determined, we can proceed to Table 1:
    • Q3: What category of hazardous waste is it? (left-hand column of Table 1).
    • Q4: What type of recycling are you practicing? (top row of Table 1).

Please clarify my understanding on the first two bullet points.

Note: an image of 40 CFR 261.2 – Table 1 is included below:

RCRA Table of Solid Waste Exclusions

40 CFR 261.2 – Table 1

Read: Categories of Waste to Consider When Determining a RCRA Recycling Exclusion From Solid Waste

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Back with more information:

Daniel,

Where I find the RCRA rules difficult is that there are two situations not one. There is the sodium and then there is the remainder of the battery. The questions do not allow this differentiation.

  • Q1: Is the battery a solid waste?
    • A1: Yes, because the battery will be recycled by reclamation.
  • Q2: If it is a solid waste, is it a hazardous waste?
    • A2: Yes, sodium possesses a hazardous characteristic – reactivity (D003)
  • After that is determined, we can proceed to Table 1:
    • Q3: What category of hazardous waste is it? (left-hand column of Table 1).
      • A3: The battery would be considered spent, the sodium would be considered a by product.
    • Q4: What type of recycling are you practicing? (top row of Table 1).
      • A4: Reclamation. The battery will be smelted to recover metals for use in making products. The sodium will be reclaimed in its current form and used to make other products.
My reply:

Please see below.

  • I agree that the battery is a solid waste. This is because it is being discarded. Recycling is a form of discarding.
  • The presence of sodium does not by itself make the battery a reactive hazardous waste. The battery – not the sodium – when spent would have to display the characteristic of Reactivity (D003). Let’s presume it is a D003 Reactive hazardous waste.
  • Table 1 contains some of the exclusions from regulation as a solid waste for materials that are recycled.
  • It may be that the battery is considered to be a spent secondary material. However, the sodium is not a waste that is a by-product. It is part of the battery.
  • If reclaiming, the reclaimed materials may be excluded from regulation as a solid waste and therefore cannot be a hazardous waste. This would mean the process of reclamation would not require a RCRA permit.
  • Any waste generated during reclamation would have to be managed by the generator of the waste, that is, the person conducting the reclamation.

Please contact me with any other questions.

Later that same day with two more questions:

Thanks for your assessment. I would like to discuss further if you are open to it. My two follow-up questions:

  1. Given the scenario below would the entity reclaiming the sodium be considered a TSDF? Since it is not a hazardous waste I would assume not.
  2. While I follow your point, an intact sodium-sulfur battery does not demonstrate the characteristic because the cells are hermetically sealed. There is no possibility of water intrusion and thus no reactivity concern. The battery will be intact when it first becomes solid waste (abandon or recycled) but at some point in the process will demonstrate the characteristic because the cells will be breached. So when does the hazardous characteristic need to be demonstrated to be considered hazardous waste? I would argue that most intact industrial batteries do not demonstrate a characteristic hazardous waste when intact, yet nearly all are managed as universal waste (which inherently implies it demonstrates a hazardous characteristic).
I had more answers:

Please see below.

  • If the battery is excluded from regulation as a solid waste then its recycling by reclamation would not require a RCRA permit.
  • You’re correct that the hazardous waste determination is made at the point of generation for the entire battery. If the battery contains a reactive element (sodium) it would likely be a D003 Reactive hazardous waste.

I am available all day (06.25.20) to discuss. Can we schedule a time?

Contact me with any questions you may have about the generation, identification, management, and disposal of hazardous waste

Daniels Training Services, Inc.

815.821.1550

Info@DanielsTraining.com

https://www.danielstraining.com/

Some more discussion took place over the phone (no transcripts available) but then another email on July 5th:

Daniel,

I hope you enjoyed the Independence Day holiday. I had a follow-up question on the definition of a commercial chemical product (CCP). RO 14012 states “For purposes of Section 261.2, CCP means all types of unused commercial products, whether chemicals or not.” The mercury thermometer example refers to new, off-spec thermometers. In my case, I have a used battery from which we will reclaim the sodium (which recall is produced through a chemical reaction during battery charging).

Through RO 14012, I found reference to an EPA memo which provides checklist to assist in evaluating whether CCPs are hazardous waste under the RCRA. In that memo, they state: “In the RCRA hazardous waste management regulations the term commercial chemical product generally refers to materials that would, under usual circumstances, be considered products and not wastes…”. It doesn’t specifically state ‘unused’ but rather “product”. I would argue that the reclaimed sodium from a used battery is useable product, which is also consistent with the definition of reclamation in 40 CFR 261.1(d).

I’ll submit this to state regulators but was curious of your opinion.

My reply July 06, 2020:

Please see below.

  • You are correct – and something I should have mentioned – that for the purposes of the recycling exclusions at 40 CFR 261.2 a commercial chemical product must be unused. The batteries you are considering are used and therefore are not eligible for inclusion with CCP as defined at 40 CFR 261.2.
  • Also, from McCoy Guidance: “Although Table 1 in 261.2(c) specifies ‘commercial chemical products listed in 40 CFR 261.33,’ EPA interprets the term to also include those products that are not listed in 261.33, but exhibit one or more characteristics of hazardous waste. [April 11, 1985; 50 FR 14219, RO 11713, 11726, 13356, 13490, 14883] So, a battery could be a CCP per 40 CFR 261.2 but only if unused.
  • I believe the USEPA memo you refer to confirms the requirement the CCP be unused, “…would…be considered products and not wastes…” If it does not state unused here, it clearly does elsewhere.
  • I don’t believe the status of the sodium in the battery or how it is recycled is any longer an issue. If the battery is not CCP per 40 CFR 261.2, it is not subject to the exclusion no matter how it is recycled.

Please contact me with any other questions.

If you like this article, please share it using any of the social media platforms identified at the bottom of this article.

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No further communication after that – at least not yet.

It’s clear to see that knowledgeable persons can disagree about the exclusions from regulation in RCRA. In this situation I think the questioner did not fully understand that the hazardous waste determination – and thus any exclusions from regulation – begin at the point of generation. Subsequent treatment of a waste does not affect it’s eligibility for exclusions from regulation. But, perhaps, I wasn’t understanding his situation properly. It takes knowledge and careful research of the regulations to make a hazardous waste determination.

Q&A: Is Specification Packaging Required for the Transport of a Non-Hazardous Waste?

Q&A: Is Specification Packaging Required for the Transport of a Non-Hazardous Waste?

A unique situation.  One where I assist a company provide a service to its customers who wish to purchase packaging for the transport of their waste or other hazardous materials.  I’m the guy the supplier contacts when they are unsure of the needs of their customers.  Sometimes, as in this case, I provide additional consulting services to the supplier’s customer.  It all started on December 13, 2016…

Hi Daniel

Our customer has a 55 gallon drum filled with crushed #10 paint cans. He said it is not considered hazardous, but has the same question if it were. He wants to know if there is a limit to the amount he can ship in a 55 gallon drum, other than the rating in kg listed on the drum.

The drum he is looking at is rated UN 1A2/x430/s.

I am guessing you might have more questions!

Thanks!

My reply that same day to the supplier (my customer) and the person with the question (the supplier’s customer):

If the material to be shipped is not a hazardous material (crushed paint cans with no free liquids are not a hazardous material), then none of the Hazardous Material Regulations of the USDOT apply.  This includes the need for DOT specification packaging.

Therefore, since this is not a hazardous material – unless I’m missing something – the gross mass in kilograms for the package (430 kg in this case) doesn’t apply.  There is no limit to the weight of the packaging or the weight of the material in the packaging.
Additional information:
  • If this was a solid hazardous material, then specification packaging would be required and there would be two weight limits to take into account:
    • The manufacturers rated gross mass in kg for the entire package.  This is marked on the packaging as part of the DOT specification or UN Standard.
    • The maximum net mass of hazmat in the package (hazmat alone not the weight of the packaging), which for a steel drum is 400 kg or 882 lbs.
    • 882 lbs is the upper weight limit for a solid in a non-bulk packaging.  Read more:  What is a Bulk Packaging?

I hope this helps.

Please don’t hesitate to contact me with any other questions.

Contact me with any questions you may have about the generation, identification, management, and disposal of hazardous waste

Daniels Training Services

815.821.1550

Info@DanielsTraining.com

https://www.danielstraining.com/

The customer of the supplier had some questions just for me on 12.14.16:

Dan,

Thank you for clarifying things. So in my case, we are transporting crushed empty paint cans in 55 gallon drums. Since no liquids or hazmat remaining in the paint cans it is considered solid waste, and therefore the DOT requirements do not apply.

The two questions I have are below. I have a 55 gal drum that is designed for liquids. The UN number for the drum is (in 2 lines):
UN 1A2/Y1.5/150
16/USA/M4453

1. Can we use this drum (designed for liquids) to transfer our crushed solid waste?
2. And if so, how do I determine what the weight capacity/limit is for this particular drum to ship our solids in?   Unlike the markings for a 55 gal drum designed for solids, which specify a max weight, it the 55 gal drums for liquids does not specify a weight.

Thank you for your help!

Contact me with any questions you may have about the transportation of hazardous materials by air, highway, vessel, or rail

International and Domestic

Daniels Training Services

815.821.1550

Info@DanielsTraining.com

https://www.danielstraining.com/

We’d spoken on the phone about this as well but my answer that day was in the following email:

I will do my best to answer your questions and provide guidance.  Please see below:

  • For a waste to be hazardous per the regulations of the USEPA – and a state with an authorized hazardous waste program – it must either be listed or display a characteristic.
  • The empty, crushed, steel paint cans as you describe (even if a small amount of liquid is present) should not meet the USEPA definition of a hazardous waste.  Though it remains a solid waste and therefore subject to state regulation.
  • If recycled as scrap metal the paint cans are excluded from regulation as a solid waste.
  • The classification of a hazardous material per USDOT regulations is distinct from how USEPA determines a hazardous waste.  It is possible that a solid waste may be a USDOT hazardous material (e.g. asbestos).
  • Based on the information provided, it does not appear that the empty, crushed, steel paint cans are a hazardous material per USDOT regulations.
  • Answer to question #1:  Yes.  Since the empty, crushed steel paint cans are not a hazardous material subject to USDOT regulations, specification packaging is not required.  Any sturdy, leak-proof packaging that will contain the paint cans and is acceptable to the transporter will suffice.  Since it is not required by regulation, using specification packaging in this case may be viewed as an unnecessary expense.  Recycling as scrap metal may provide more cost savings.
  • Answer to question #2:  See answer to question #1.  The use of a specification packaging for the transport of solids when the packaging is rated for liquids is acceptable under certain conditions.  It is not applicable here.  I can assist you with this determination if you have other specific examples.
I hope this helps.
I answer a lot of questions for a lot of people.  Sometimes people pay me for my time.  Other times I offer free guidance to anyone with a question.  If you have a question about the management of waste or the transportation of hazardous materials, don’t hesitate to contact me!  Questions are free and normally my answers are as well.  If you have a question that you are unable to find an answer to, give me a try!

Daniels Training Services

815.821.1550

Info@DanielsTraining.com

https://www.danielstraining.com/

The New Definition of “Contained” From the 2015 Definition of Solid Waste Final Rule

The New Definition of “Contained” From the 2015 Definition of Solid Waste Final Rule

In the January 13, 2015 Federal Register the USEPA announced its Final Rule for the Definition of Solid Waste (2015 DSW) which revised – and is supposed to correct deficiencies in – the 2008 Definition of Solid Waste Final Rule (2008 DSW).  Though announced, the 2015 DSW does not become effective until July 13, 2015 and then only at the Federal level and in states without an authorized hazardous waste program.

A full summary of the 2015 DSW can be found at the USEPA Website for its DSW Rulemakings.  The purpose of this article is to explain one small – but important – part of the 2015 DSW:  The codified definition of “contained”. (more…)

Categories of Waste to Consider When Determining a RCRA Recycling Exclusion From Solid Waste

The definition of a solid waste at 40 CFR 261.2(a)(1) includes any discarded material that is not excluded from regulation by:

  • The conditional exclusions for certain solid waste at §261.4(a).
  • A variance granted under §260.30 and §260.31.
  • A non-waste determination under §260.30 and §260.34

Unless you can find an exclusion from regulation, everything you “throw away” (ie. discard) is a solid waste.  So, what then does it mean to “discard” something?

Pursuant to 40 CFR 261.2(a)(2)(i), a discarded material is anything that is:

If you generate a solid waste – and you know that you do – it may be excluded from regulation if it is recycled in a manner prescribed by USEPA regulation.  Table 1 of 40 CFR 261.2 identifies five categories of solid wastes (two categories – Sludges and By-Products – are further subdivided into two sub-categories each, making a total of seven entries in Table 1) and identifies their regulatory status (solid waste or no solid waste) based on how they are recycled.  Not included in Table 1, but essential to its complete understanding is a Co-Product, which is referenced in the explanation of a By-Product.

(more…)

The Identification of Solid Waste in Texas

TCEQ training for hazardous waste personnel

TCEQ regulates hazardous and non-hazardous waste from both industrial and non-industrial facilities.

Though very similar to those of the USEPA, as a state with an authorized hazardous waste program under RCRA, Texas waste regulations – created and enforced by the Texas Commission on Environmental Quality (TCEQ) – have their own state-specific nuances.  For a person in Texas subject to these regulations, slight differences between state and Federal regulations can make a big difference.  This article will look at one aspect of the waste regulations of the TCEQ in Texas:  What is, and isn’t, a Solid Waste. (more…)

40 CFR 261.4(b)(12) The RCRA Exclusion from Hazardous Waste for Used Chlorofluorocarbons

MassDEP Enforces the Massachusetts Landfill Ban With 98 Notices of Non-Compliance in the Past Year

Even those states without authorized hazardous waste programs under RCRA (Iowa, Alaska, & Puerto Rico) are responsible for the management of non-hazardous solid waste within their state.  While regulations for hazardous waste find their authority in Subtitle C of the Resource Conservation and Recovery Act, non-hazardous wastes are addressed in Subtitle D of RCRA.  It’s in Subtitle D that the USEPA delegates the management of non-hazardous waste to each state.  I have found that the states take a myriad of approaches to the management of non-hazardous waste and in this article we will read of how Massachusetts is enforcing its ban from landfill disposal for certain recyclable materials. (more…)

Company to Pay More Than $93,000 Over Claims of Illegal Dumping of Construction Waste at Methuen Site

BOSTON — A waste hauling firm based in Essex will pay more than $93,000 to settle claims that it illegally dumped multiple loads of construction and demolition waste at an unpermitted site in Methuen, Attorney General Martha Coakley announced today.

According to the complaint, entered Wednesday along with the consent judgment in Suffolk Superior Court, Dynamic Waste Systems, Inc. violated the state’s solid waste disposal laws by dumping more than 115 loads of construction and demolition waste, including concrete, brick, and stone, at the site over a period of 70 days.

“We will vigorously pursue those who fail to follow the Commonwealth’s solid waste laws and regulatory requirements,” AG Coakley said. “This settlement sends a strong message that haulers who improperly dispose of waste will be forced to clean up illegal dumping grounds.”

According to the complaint, Thomas Battye, the owner of the Methuen site, never applied for or received an assignment to operate a solid waste facility from the Methuen Board of Health or a solid waste management facility permit from the Massachusetts Department of Environmental Protection (MassDEP).

“Illegal dumping of solid waste undermines the protection of the Commonwealth’s natural resources, and it won’t be tolerated,” said MassDEP Commissioner Kenneth Kimmell. “Disposal of materials must be done at properly approved or permitted facilities without exception.”

The consent judgment requires that Dynamic Waste Systems pay a total of $90,000 into a special fund established by the Commonwealth to help with the cost of site evaluation and subsequent cleanup work at the Battye site. Under the judgment, Dynamic will also pay a $3,750 civil penalty.

Battye is the subject of a separate, pending action brought by the Commonwealth related to solid waste violations at the Methuen site. The AG’s Office is also pursuing claims against additional waste haulers and demolition contractors who dumped or contracted for solid waste disposal at the Battye site.

Assistant Attorney General Matthew Ireland of AG Coakley’s Environmental Protection Division handled the case, with assistance from MassDEP Environmental Analysts Mark Fairbrother, John MacAuley and Karen Goldensmith, and MassDEP attorneys Jeanne Argento and Colleen McConnell, all from MassDEP’s Northeast Regional Office.

Even though the waste in question was not a hazardous waste, the potential remains for significant fines if the state’s regulations are violated.  The regulations of both the USEPA and MassDEP identify a solid waste as any discarded material that is not excluded from regulation (eg. due to recycling).  Some solid waste may also be a hazardous waste if they are either identified as a listed hazardous waste and/or exhibit a characteristic of a hazardous waste (ignitability, corrosivity, reactivity, or toxicity).  If not listed nor characteristic, or an exclusion applies, then the waste remains a non-hazardous solid waste.

Conducting a hazardous waste determination for all of your solid waste is one of your primary responsibilities.  If only a solid waste, you must still comply with the regulations of your State and the USEPA under Subtitle D of the Resource Conservation and Recovery Act (RCRA).

Please don’t hesitate to contact me with any questions about the management of solid waste, hazardous waste, used oil, or universal waste in Massachusetts or anywhere in the US.

EP Fines Ohio Company $12,000 for Illegal Open Burning in Lycoming County

Company Ignored Agency Warning and Repeated Violation

WILLIAMSPORT — The Department of Environmental Protection today announced that it has fined Welded Construction LP of Perrysburg, Ohio, $12,000 for illegally burning wood mats on two occasions in August at its facility in Wolf Township, Lycoming County.

“We told company officials that the open burning of wood waste is a violation of Pennsylvania’s Solid Waste Management Act during our first complaint investigation,” DEP North-central Regional Director Marcus Kohl said. “Yet just eight days later, DEP inspectors caught the company doing the exact same thing.”

Kohl added that it is the responsibility of out-of-state companies to become familiar with Pennsylvania’s environmental laws and regulations to avoid enforcement action, including fines, which may be taken by the department when violations are documented.

“These mats should have been beneficially reused, or taken to a permitted landfill for proper disposal,” Kohl said.

A follow-up inspection conducted by the department in early September confirmed that all violations had been corrected.

The mats – made from hardwood timbers bound together by metal bolts and pins –are used to prevent destruction of land during the movement of heavy equipment in areas of soft ground, wetlands or streams.

You may think that open burning would be a violation of a state’s air regulations, and not its solid waste regulations, as is indicated here.  In fact, the open burning of waste, both hazardous and non-hazardous, was one of the original goals of the Resource Conservation and Recovery Act (RCRA) passed in 1976, codified as Federal regulations of the USEPA beginning in 1980, and adopted or incorporated into state regulations by most states (all but Iowa, Alaska, and Puerto Rico) throughout the 1980s.  Read more about it here:  The History of the Resource Conservation and Recovery Act.

Contact me to schedule training that will ensure compliance with the regulations of the USEPA and your state.

For more information, visit www.dep.state.pa.us or call 570-327-3653.

What is a Sludge? The US EPA Definition

Like the term “solid waste”, “sludge” when used by the EPA can be confusing.  It can be found in 40 CFR 261.2 as part of EPA’s description of what wastes may and may not be a solid waste (more on that below) .  The reason for this confusion is that the EPA definition of a sludge differs from the common English definition:

EPA definition of sludge from 40 CFR 260.10:  Sludge means any solid, semi-solid, or liquid waste generated from a municipal, commercial, or industrial wastewater treatment plant, water supply treatment plant, or air pollution control facility exclusive of the treated effluent from a wastewater treatment plant.

Whereas the standard English definition:  Thick, soft, wet mud or a similar viscous mixture of liquid and solid components, esp. the product of an industrial or refining process.

(more…)