hazardous waste determination

The Hazardous Waste Determination Under the Generator Improvements Rule

The Hazardous Waste Determination Under the Generator Improvements Rule

A generator of hazardous waste must conduct a hazardous waste determination for all solid waste it generates.  This requirement is codified in federal regulations at 40 CFR 262.11.  A solid waste is defined and explained at 40 CFR 261.2, but for the purposes of this article you may think of a solid waste as any discarded solid, liquid, semi-solid, or containerized gas; pretty much anything you throw away.

The Generator Improvements Rule went into effect on May 30, 2017 in the federal regulations of the U.S. Environmental Protection Agency (USEPA) and in those states that lack an authorized hazardous waste program.  Since that date, states with an authorized hazardous waste program have the option of adopting all of the 60+ changes to the generator regulations or only those that are more stringent than existing regulations.

Since all of the revisions made by the Generator Improvements Rule to the regulations of the hazardous waste determination are more stringent than existing regulations, every state must either adopt these revisions or create its own that are even more stringent.  This article will address the hazardous waste determination as revised by the Generator Improvements Rule found at 40 CFR 262.11 of the USEPA regulations.

View a side-by-side comparison of the old regulations of the hazardous waste determination and the new regulations after the Generator Improvements Rule

Introduction:Hazardous Waste Determination 40 CFR 262.11

A person who generates a solid waste must make an accurate determination as to whether it is a hazardous waste.  This determination must be made using the steps specified in §262.11.

  • A “person” as that term is used by USEPA – and is defined at §260.10 – includes an individual, a business, or branch of government.  This means that every hazardous waste generator – no matter its status – must complete the hazardous waste determination.
  • The determination is the sole responsibility of the generator of the waste.  Though it may be made by someone else: broker, consultant, transporter or TSDF, in the end it is the generator who will be held responsible for making an accurate determination.

Generators are, and always have been, ultimately responsible for making accurate hazardous waste determinations. (November 28, 2018; 81 FR 85750)

And…

A generator’s failure to properly analyze, label, and accumulate waste does not exempt the waste from regulation. (RO 11424).

  • The Generator Improvements Rule codified the requirement that a generator make an “accurate” determination.  In other words, you must get it right.
  • While the regulations prior to the Generator Improvements Rule required the generator to conduct the hazardous waste determination using a specified “method”, the revised regulations require the generator to follow specified “steps”.  This change to one word puts a stronger emphasis on the generator responsibility to follow through precisely as required by USEPA to conduct the hazardous waste determination.

Q:  I’m a very small quantity generator of hazardous waste or VSQG (known as a conditionally exempt small quantity generator or CESQG prior to the Generator Improvements Rule).  I don’t have to complete the hazardous waste determination, right?

A:  Wrong.  One of the conditions for exemption of a VSQG found at §262.14(a)(2) is that it “…complies with §262.11(a) through (d).”  This takes the VSQG all the way through the hazardous waste determination but stops short of paragraphs (e), (f), & (g) which are explained below.

Not sure of your hazardous waste generator status?  Take this short survey

“Accurate”?

The addition of the word accurate to §262.11, though a small change, has a significant impact and is worth further explanation.

  • From Merriam-Webster:

Definition of accurate
1 : free from error especially as the result of care
an accurate diagnosis
2 : conforming exactly to truth or to a standard : EXACT
providing accurate color
3 : able to give an accurate result
an accurate gauge
4 : going to, reaching, or hitting the intended target : not missing the target
an accurate shot/kick

  • The revised text indicates an accurate hazardous waste determination must be made, “in order to ensure wastes are properly managed according to applicable RCRA regulations.”  In other words, the purpose of an accurate determination is to make certain the waste (hazardous or non-hazardous) is managed in compliance with the regulations.
  • The use of “accurate” in §262.11 and its absence elsewhere in the regulations is not meant to imply that other compliance activities can be inaccurate.
  • The inclusion of the language, “in order to ensure wastes are properly managed according to applicable RCRA regulations.” allows for the over-management of a waste.  In other words, a generator may choose to manage their non-hazardous waste as a hazardous waste in order to ensure, beyond a doubt, proper and protective management of the waste.

“Steps”?

A hazardous waste determination must be made at the point of generation and continue throughout its management.  It must be made by the generator using the following steps in this sequence:

  1. Determine the point of generation for the solid waste.
  2. Determine if the solid waste is excluded from regulation at §261.4.
  3. If not excluded, determine if it is a listed hazardous waste per §261, subpart D.
  4. Then, determine if it is a characteristic hazardous waste per §261, subpart C.
  5. Maintain a record of the hazardous waste determination.
  6. Identify all applicable hazardous codes prior to shipping the waste off-site.
  • Notice that this is the hazardous waste determination and not a solid waste determination.  In fact, the regulations at §262.11 don’t explicitely direct a hazardous waste generator to identify the generation of a solid waste.  However, the opening language of the regulation reads:  “A person who generates a solid waste, as defined in 40 CFR 261.2…”  So, it is necessary to identify the generation of a solid waste before you can determine the presence of a hazardous waste.  Also, as noted below, the hazardous waste determination must begin at the point of generation, which is the moment a material is discarded and becomes a solid waste.

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/

When must the hazardous waste determination be made?

Though a long-standing policy and position of the USEPA that a hazardous waste determination be made at the point of generation, the Generator Improvements Rule codified this language at §262.11(a).

  • Hazardous waste determination must be made at the point of generation before any dilution, mixing, or other alteration that may change the waste.  Point of generation includes both the time and place the waste was first generated (81 FR 85750).
  • It is critical, therefore, that the generator determine the exact point of generation of the waste.  Any dilution, mixing, or alteration of the waste after this point may be regulated as treatment.
  • The determination must continue throughout the cradle-to-grave management of the waste.  That requires the generator to know the qualities of its waste, the conditions it will face during management, and to anticipate the changes it may undergo.  For example, a solution of a non-hazardous waste may – over time – separate into two or more phases, one of which may display a characteristic of a hazardous waste.

Excluded from regulation? Really?

USEPA regulations include many exclusions from regulation.  §262.11(b) now mandates that the generator determine if any of them apply to its waste.  If the generator can meet the conditions of one of these exclusions the solid waste may not be a hazardous waste or – even better – it may not be a solid waste at all and remain a material.  If any of these exclusions apply – and the generator chooses to utilize it – the hazardous waste determination will end right there.

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But what if the solid waste is not excluded at 40 CFR 261.4?

If not excluded at §261.4, the generator must then use their knowledge of the waste to determine if it is a listed hazardous waste.  At §262.11(c) the new regulations of the Generator Improvements Rule mandate that solely generator knowledge be used to identify a listed hazardous waste.  It also identified what is acceptable to use as knowledge.

  • The four (4) types of listed hazardous waste regulated by USEPA are identified at §261, subpart D.
  • Acceptable knowledge for completing this step of the hazardous waste determination may include:
    • Waste origin
    • Waste composition
    • The process producing the waste
    • Feedstock
    • Other reliable and relevant information
  • If it has an authorized hazardous waste program, your state may identify and regulate listed hazardous waste in addition to those of the USEPA.
  • The determination of a listed hazardous waste is based solely on generator knowledge.  It does not require the testing of a representative sample.
  • If listed, a generator may submit a de-listing petition to USEPA or its state per §260.20 & §260.22 to demonstrate the waste is not a hazardous waste.

That takes care of listed hazardous waste.  What about characteristic hazardous waste?

The generator must also determine if the waste exhibits one or more hazardous characteristics using either generator knowledge, testing of a representative sample if knowledge is inadequate, or a combination of both.  This represents a change from the original regulations at §262.11(c) which required the use of either testing or knowledge to determine the characteristic, but not both.  These regulations are now found at §262.11(d) and divided into two paragraphs:  (1) for the use of knowledge and (2) for the testing of a representative sample.

  • The four (4) types of characteristic hazardous waste regulated by USEPA are identified at §261, subpart C.
  • The determination of hazardous waste characteristics is required whether or not the waste was earlier (at §262.11(c)) identified as a listed hazardous waste.
  • The determination of a characteristic hazardous waste must first be made using knowledge of the waste.  If that knowledge is inadequate to make an accurate determination the generator must then test a representative sample.  However, if knowledge is adequate to make an accurate determination the testing of a representative sample is not required.
  • For the purposes of this step of the determination, acceptable knowledge may include:
    • Process knowledge (e.g., information about chemical feedstocks and other inputs to the production process).
    • Knowledge of products, by-products, and intermediates produced by the manufacturing process.
    • Chemical or physical characterization of wastes.
    • Information on the chemical and physical properties of the chemicals used or produced by the process or otherwise contained in the waste.
    • Testing that shows the properties of the waste.
    • Other reliable and relevant information about the properties of the waste or its constituents.
  • Test a representative sample of a wasteTesting of a representative sample of the waste by other than an approved method (found at §261, subpart C) or an equivalent test method approved by USEPA per §260.21, may be done and considered as generator knowledge.  However, such unapproved tests do not, by themselves, provide definitive results.
  • When available knowledge is inadequate to accurately determine if a waste displays the characteristic of a hazardous waste, the generator must do the following:
    • Obtain a representative sample of the waste as that term is defined at §260.10.
    • Test the sample according to the applicable methods of §261, subpart C or an equivalent method approved by USEPA per §260.21.
  • The results of a test properly performed per the requirements of §261, subpart C (but not §260.21) are definitive for the purposes of determining a hazardous waste characteristic.

What if the determination reveals a hazardous waste?

If the waste is determined to be hazardous the generator must refer to the specified parts of Title 40 for other possible exclusions or restrictions specific to the waste.

  • The specified parts are as follows:
    • 261 – Identification and listing of hazardous waste
    • 264 – Standards for owners and operators of treatment, storage, and disposal facilities
    • 265 – Interim standards for owners and operators of treatment, storage, and disposal facilities
    • 266 – Standards for the management of specific hazardous waste and specific types of hazardous waste management facilities

      Read: What’s the difference between Parts 264 and 265 of Title 40?

    • 267 – Standards for owners and operators of hazardous waste facilities operating under a standardized permit
    • 268 – Land disposal restrictions
    • 273 – Standards for universal waste management
  • But, where’s the used oil?  A material meeting the definition of used oil is subject to regulation at §279 and not those for a hazardous waste generator.  The generator of a used oil is not subject to the hazardous waste determination.  (RO 14054)
  • This paragraph of these regulations is unchanged from its form before the Generator Improvements Rule, though its citation has changed (it used to be at §262.11(d)).

Recordkeeping:

Created entirely new by the Generator Improvements Rule, this paragraph at §262.11(f) details the applicability of and requirements for maintaining records of the hazardous waste determination.  A small or large quantity generator must maintain records supporting its hazardous waste determinations, including records that identify whether a solid waste is a hazardous waste.

  • Prior to the Generator Improvements Rule the requirement for maintaining records of a hazardous waste determination was located at §262.40(c).  It was moved to §262.11 to highlight the importance of the recordkeeping requirement to the hazardous waste determination.  A reference to §262.11(f) remains at §262.40(c).
  • Though proposed, the Generator Improvements Rule did not finalize a requirement for generators to maintain records of their non-hazardous waste determination; though it is recommended as a best management practice.  So, if an accurate hazardous waste determination results in the determination of a non-hazardous waste, the generator is not required to maintain a record of that determination.  However, some states may be more stringent than federal regulations and may therefore require a generator to maintain records of a non-hazardous waste determination.

Q:  Does an inspector have the authority to ask for a hazardous waste determination be performed – or a record of one be provided – for a non-hazardous waste?

A:  Yes.  “When situations warrant, inspectors have the authority to ask that a hazardous waste determination be performed by the generator in the absence of any documentation and the attributes of the waste suggest a potential problem.”  (81 FR 85754)

  • Records of a hazardous waste determination must be maintained for at least three (3) years from the date the waste was last sent to on-site or off-site treatment, storage, or disposal.  Of course, record retention is extended automatically during an enforcement action or as requested by USEPA.
  • The records must comprise the generator’s knowledge of the waste and support the generator’s determination of the waste as either a listed or characteristic hazardous waste.
  • The records must include, but are not limited to, the following types of information:
    • The results of any tests, sampling, waste analyses, or other determinations made for the hazardous waste determination.
    • Records documenting the tests, sampling, and analytical methods used to demonstrate the validity and relevance of such tests.
    • Records consulted in order to determine the process by which the waste was generated, the composition of the waste, and the properties of the waste.
    • Records which explain the knowledge basis for the generator’s determination of a hazardous waste characteristic.

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Hazardous waste codes:

Also new thanks to the Generator Improvements Rule, §262.11(g) requires the generator (small and large quantity generator only) to identify all USEPA hazardous waste codes (aka: hazardous waste numbers) applicable to the waste.

  • Of course, this step need only be taken if the waste is determined to be a hazardous waste since only a hazardous waste has hazardous waste codes.
  • The generator must identify all applicable hazardous waste codes prior to offering the hazardous waste for off-site transportation.  It is not necessary to identify waste codes at the point of generation.  However, SQGs and LQGs may have waste management practices in place and choose to identify the RCRA waste codes sooner than prior to off-site shipment.
  • Federal hazardous waste codes are identified in subpart C and D of part 261.
  • A state may have waste codes in addition to those of the USEPA.  In that case state regulations will require their identification as well.
  • As part of the pre-transport requirements of §262.32, a small quantity generator and large quantity generator must mark its containers with all applicable hazardous waste codes prior to offering for off-site transportation.  Read: Marking of a Hazardous Waste Container for Off-Site Transportation.
  • The very small quantity generator is not required to identify the hazardous waste codes applicable to its hazardous waste.

Done!

Remember, the hazardous waste determination is only the first step of your responsibilities as a hazardous waste generator.  After you have completed the hazardous waste determination you must count your hazardous waste generation and determine your hazardous waste generator status (both of these regulations were also changed by the Generator Improvements Rule, but that’s an article for a later date).

Daniels Training Services, Inc.

815.821.1550

Info@DanielsTraining.com

https://www.danielstraining.com/

Comparison of Changes to the Hazardous Waste Determination Regulations Made by the Generator Improvements Rule

In another article I review in detail the federal USEPA regulations of 40 CFR 262.11 and its requirements to conduct a hazardous waste determination as those regulations were changed by the Generator Improvements Rule.  Read:  The Hazardous Waste Determination Under the Generator Improvements Rule.

While the in-depth analysis of that article will assist you in understanding and complying with this very important regulation, it may also be of assistance to you to see – side-by-side – the applicable regulations before and after the changes of the Generator Improvements Rule.  That is the purpose of this article.

262.11 Hazardous Waste Determination and Record keeping
New - 262.11Old - 262.11
A person who generates a solid waste, as defined in 40 CFR 261.2, must make an accurate determination as to whether that waste is a hazardous waste in order to ensure wastes are properly managed according to applicable RCRA regulations. A hazardous waste determination is made using the following steps:A person who generates a solid waste, as defined in 40 CFR 261.2, must determine if that waste is a hazardous waste using the following method:
(a) The hazardous waste determination for each solid waste must be made at the point of waste generation, before any dilution, mixing, or other alteration of the waste occurs, and at any time in the course of its management that it has, or may have, changed its properties as a result of exposure to the environment or other factors that may change the properties of the waste such that the RCRA classification of the waste may change.
(b) A person must determine whether the solid waste is excluded from regulation under 40 CFR 261.4.(a) He should first determine if the solid waste is excluded from regulation under 40 CFR 261.4.
(c) If the waste is not excluded under 40 CFR 261.4, the person must then use knowledge of the waste to determine whether the waste meets any of the listing descriptions under sub part D of 40 CFR part 261. Acceptable knowledge that may be used in making an accurate determination as to whether the waste is listed may include waste origin, composition, the process producing the waste, feed stock, and other reliable and relevant information. If the waste is listed, the person may file a delisting petition under 40 CFR 260.20 and 260.22 to demonstrate to the Administrator that the waste from this particular site or operation is not a hazardous waste.(b) He must then determine if the waste is listed as a hazardous waste in sub part D of 40 CFR part 261
(d) The person then must also determine whether the waste exhibits one or more hazardous characteristics as identified in sub part C of 40 CFR part 261 by following the procedures in the paragraph (d)(1) or (2) of this section or a combination of both.

(1) The person must apply knowledge of the hazard characteristic of the waste in light of the material or the processes used to generate the waste. acceptable knowledge may include process knowledge (e.g., information about chemical feed stocks and other inputs to the production process); knowledge of products, by-products, and intermediates produced by the manufacturing process; chemical or physical characterization of wastes; information on the chemical and physical properties of the chemical used o produced by the process or otherwise contained waste; testing that illustrates the properties of the waste; or other reliable or relevant information about the properties of the waste or its constituents. A test other than a test method set forth in sub part C of 40 CFR part 261, or an equivalent test method approved by the Administrator under 40 CFR 260.21, may be used as part of a person's knowledge to determine whether a solid waste exhibits a characteristic of a hazardous waste. However, such tests do not, by themselves, provide definitive results. Persons testing their waste must obtain a representative sample of the waste for the testing, as defined at 40 CFR 260.10.

(2) When available knowledge is inadequate to make an accurate determination, the person must test the waste according to the applicable methods set forth in sub part C of 40 CFR part 261 or according to an equivalent method approved by the Administrator under 40 CFR 260.21 and in accordance with the following:

(i) Persons testing their waste must obtain a representative sample of the waste for testing, as defined in 40 CFR 260.10.

(ii) where a test method is specific in sub part C of 40 CFR part 261, the results of the regulatory test, when poperly performed, are definitive for determining the regulatory status of the waste.
(c) For purposes of compliance with 40 CF part 268, or if the waste is not listed in sub part D of 40 CFR part 261, the generator must then determine whether the waste is identified in sub part C of 40 CFR part 261 by either:

(1) Testing the waste according to the methods set forth in subpart C of 40 CFR part 261, or according to an equivalent method appoved by the Administrator under 40 CFR 260.21; or

(2) Applying knowledge of the hazard characteristics of the waste in light of the materials or the processes used.
(e) If the waste is determined to be hazardous, the generator must refer to parts 261, 264, 265, 266, 267, 268, and 273 of this chapter for other possible exclusions or restrictions pertaining to the management of the specific waste. (d) If the waste is determined to be hazardous, the generator must refer to parts 261, 264, 265, 266, 267, 268, and 273 of this chapter for other possible exclusions or restrictions pertaining to the management of the specific waste.
(f) Record keeping for small and large quantity generators. A small or large quantity generator must maintain records supporting its hazardous waste determinations, including records that identify whether a solid waste is a hazardous waste, as defined by 40 CFR 261.3. Records must be maintained for at least three years from the date that the waste was last sent to on-site or off-site treatment, storage, or disposal. These records must comprise the generators's knowledge of the waste and support the generator's determination, as described at paragraphs (c) and (d) of this section. The records must include, but are not limited to, the following types of information: the results of any test, sampling, waste analyses, or other determinations made in accordance with this section, records documenting the tests, sampling, and analytical methods used to demonstrate the validity and relevance of such tests; records consulted in order to determine the process by which the waste was generated, the composition of the waste, and properties of the waste; and records which explain the knowledge basis for the generator's determination, as described at paragraph (d)(1) of this section. The periods of record retention referred to in this section are extended automatically during the course of any unresolved enforcement action regarding the regulated activity or as requested by the Administrator.
(g) Identifying hazardous waste numbers for small and large quantity generatos. If the waste is determined to be hazardous, small quantity generators and large quantity generators must identify all aplicable EPA hazardous waste numbers (EPA hazardous waste codes) in sub part C and D of part 261 of this chapter prior to shipping the waste off site, the generator also must mark its containers with all applicable EPA hazardous waste numbers (EPA hazardous waste codes) according to §262.32.

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

Daniels Training Services, Inc.

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Q&A: Hazardous Waste Determination for Lab Waste

A question from a former customer of mine on June 14, 2016:

Hello again Dan,

I’m sorry to bother you with another question but I’m having trouble deciphering this information.  I’m looking to do some lab tests.  I was first reviewing the SDS for the reagents involved and two include hazardous waste disposal.

The  Peroxydisulfuric Acid, Dipotassium Salt in the Metals Prep set Reagent B  and potassium cyanide in Lead TNT Reagent Vial.  (Safety Data Sheets were attached to the email)

Could you please explain disposal considerations for both of these (how they must be disposed of and why).  Is there any quantity guidelines (like you told me about As)?

Once again I greatly appreciate your help!

I replied a few days later on June 16th:

I will try to answer your questions and provide the answers you need.

  • The Safety Data Sheet (SDS) is authorized and required to be used by OSHA, the Occupational Health and Safety Administration.  While its information can be useful, it is not authorized by the USEPA.  Specifically, sections 1 through 11 and 16 of the SDS are authorized and required by OSHA.  Sections 12 through 15 – including section 13 Disposal Considerations  – is not authorized or required by OSHA.  Information in these unauthorized sections of the SDS is provided voluntarily the manufacturer and may not be relied upon for compliance.
  • The generator of a waste must determine if a waste is hazardous and then manage it properly from “cradle-to-grave.”
  • Based on the information on the SDS for the product Metals Prep Set Reagent B it is 100% Potassium persulfate and an oxidizer.  If it retains the characteristic of an oxidizer at its point of generation as a waste, i.e. when you discard it, then it will be a hazardous waste for the characteristic of Ignitability (D001).
  • Based on the information on the SDS for the product Lead TNT Reagent Vial it contains 60-70% potassium cyanide which is a p-listed material.  It may be a p-listed hazardous waste if it is disposed of unused.  If it is used then the P-code will not apply.  It is also possible – but unlikely – that it could also be a hazardous waste for the characteristic of Reactivity (D003) if it emits cyanide gas at toxic levels.

Summary:

While the SDS can be a good source of information, it is not the final word on the determination of whether or not a waste is hazardous.  It is important to note that the SDS describes an unused product and may not be an accurate description of that product when it becomes a waste.
The responsibility for the hazardous waste determination is solely the generator’s.
I hope this helps.
Please don’t hesitate to contact me with any questions or if you require HazMat Employee Training or Hazardous Waste Personnel Training.
That seemed to settle it!

Proper Disposal of a Hazardous Material: Is it a Hazardous Waste?

On February 2, 2015 an EHS Professional who had attended one of my Training Seminars contacted me with a question:

Dan, I attended your HazMat Employee & Hazardous Waste Training class last <<MONTH>> in <<CITY, STATE>>. I am hoping that you could help me out by advising me what to do with a 4 oz bottle of lacto phenol cotton blue stain that we just discovered hidden in a drawer in our laboratory.

According to SDS, it is approx. 80% phenol which is hazardous.
My question to you is how would you recommend handling this? I know we are allowed to keep small amounts on site. Would you safely package it up and store on site or would you go ahead and pay the cost of disposing it immediately?
Last year we went through the lab to clean out expired chemicals and did hire a company to dispose of all hazardous material but missed this bottle of stain.

I would greatly appreciate your advice.

My response on February 9, 2014:

I apologize for my delay in responding. I’ve been super busy the past few weeks.

To answer your question you have a few options, I have outlined some of them below along with some suggestions.

  • I would not be in any rush to call it a waste – and therefore a hazardous waste – too quickly. As the generator you have some discretion in deciding when it is a waste (i.e. when it is discarded) as long as it does not appear to be abandoned. As such, you could continue to keep it on the lab shelf with some plans in the near future to use it.
  • Is it possible to use it? If you can find some way to use it as a product in a legitimate manner, then it would not be discarded and would not be a waste. Perhaps your lab personnel could use it in some form of experiment that consumes the material leaving nothing but a RCRA Empty container which can then go in the trash.
  • If it becomes a waste, as the generator you have the option to treat a waste to make it non-hazardous. This can be done if the waste is hazardous due to a characteristic (D001, D002, D003, or D004-D043) but not if it is a listed hazardous waste (F-codes, K-codes, P-codes, U-codes). It sounds like what you have is a characteristic hazardous waste (D001 for Ignitability). You could therefore, mix it with a large amount of non-ignitable waste and make it non-hazardous. Or you could solidify it with absorbants and dispose of it as a non-hazardous waste.
  • If you are a CESQG and it is not a listed hazardous waste (see above) you could add it to your Used Oil and still manage it as a Used Oil.

In sum, you have a lot of options for the management of this material that does not require off-site transportation as a hazardous waste. Though of course that remains an option.

I hope this helps. Please don’t hesitate to contact me with any other questions.

Dan

EHS Professional replied:

Excellent information!  Thank you very much!

Daniels Training Services815.821.1550Info@DanielsTraining.com

https://www.danielstraining.com/

Royal Farms Store in Dover, DE Issued RCRA Violation for not Conducting a Hazardous Waste Determination

The Bullet:

A Dover, DE store in the Royal Farms chain was issued a violation by the Delaware Department of Natural Resources and Environmental Control for a simple – but common – violation of the State’s hazardous waste regulations.

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

International and Domestic

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Who:

Royal Farms Store #139 of the Royal Farms chain of retail stores.

Delaware Department of Natural Resources and Environmental Control (DNREC).  DNREC Contact: William DavisDelaware Department of Natural Resources and Environmental Control

What:

As a generator of a solid waste, the store failed in its responsibility under both Federal and State regulations to conduct, and document, a hazardous waste determination.

Where:
Royal Farms Store #139
6 West Lebanon Road
Dover, DE 19901
When:

Date Discovered: 05/02/2014

Enforcement Action Served Date: 07/22/2014

Date Corrected: 08/21/2014

Why:

A person that discards any material generates a solid waste.  Unless that person is exempt from regulation under the Resource Conservation and Recovery Act (RCRA) – and this store clearly is not – they must conduct a hazardous waste determination.  This determination must be documented (no format is specified) and a record kept for at least three years from the last date the waste was shipped off-site for treatment, disposal, or recycling.

How:

The state of Delaware – like most other states – has an authorized hazardous waste program which requires it to enforce the RCRA regulations within its borders.  A state that does not enforce its regulations stands to loose its authorization to manage its own hazardous waste program.

Conclusion:

A person can be forgiven of thinking that the hazardous waste regulations of RCRA apply only to large industries, utilities, landfills, and the like.  It can be surprising to learn that a local retail store is subject to the same regulations.  First and foremost among the RCRA regulations is to conduct a hazardous waste determination.  From that, a solid waste generator can determine what status of hazardous waste generator they are, and what regulations apply to the cradle-to-grave management of their hazardous waste.Heavy industry

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Don’t wait for a Notice of Violation from your state to learn you are subject to the regulations.  Contact me and I can assist you with the hazardous waste determination and any training you may require as well.

Company in Baltimore Settles With USEPA Regarding Alleged RCRA Violations. Pays $39,400 Penalty.

The Bullet:

The owner/operator of a manufacturing facility in Baltimore, MD agreed to a settlement with the USEPA over its alleged violations of Federal regulations based on the Resource Conservation and Recovery Act (RCRA).  As part of settlement the company agreed to come into full compliance with state and Federal regulations and to pay a penalty of $39,400.

Who:

Simpson Strong-Tie Company, Inc. manufactures epoxy-based products, grout and cement products, and fiberglass molds.

USEPA contact:  Donna Heron 215-814-5113 / heron.donna@epa.govLogo for US Environmental Protection Agency

What:

The alleged violations involve containers of spent acetone and spent dibasic ester managed as hazardous waste and include:

  • Failure to make a hazardous waste determination.
  • Failure to keep hazardous waste containers closed except when adding or removing waste.
  • Failure to label and date hazardous waste containers
  • Failure to provide proper EPA identification numbers on hazardous waste manifests.

As part of this settlement, the company has neither admitted nor denied liability for the alleged violations, but has certified its compliance with applicable RCRA regulations.

Where:

The company operates a manufacturing plant located at 3100 Falls Cliff Rd., Baltimore, Md.

When:

Initial USEPA inspection of facility in April of 2012.

USEPA news release of settlement dated June 10, 2014.

Why:

RCRA is designed to protect public health and the environment, and avoid costly cleanups, by requiring the safe, environmentally sound storage and disposal of hazardous waste. By complying with regulatory requirements for managing hazardous waste, the company will significantly reduce the possibility of accidents that could contaminate soil and groundwater.

How:

Though Maryland has an authorized hazardous waste program administered by the Maryland Department of the Environment, in this case the USEPA was the lead Agency in settling this issue with the company.Maryland Department of Environment

Conclusion:

How expensive is training?  How much time will it take?  Will it be a big hassle?  My answer to these questions, and others like it, is that my training is much less expensive and time-consuming than a single violation of the Federal or State hazardous waste regulations.  If you’re a Large Quantity Generator of hazardous waste you must provide annual training for all of your Facility Personnel who are exposed to hazardous waste.  Confused?  Don’t be.  Contact me for a free RCRA Training consultation.

Contact me with any questions you may have about the transportation of hazardous materials

 

Daniels Training Services

815.821.1550

Info@DanielsTraining.com

https://www.danielstraining.com/

State Certified Labs for the Hazardous Waste Determination

Conducting a hazardous waste determination is a requirement for all persons that generate a solid waste, learn more:  The Hazardous Waste Determination.  The determination may be based on either or both of the following methods:  Process Knowledge or Analysis.  The regulations of the USEPA do not indicate which of these methods is preferred, however, many states with an authorized hazardous waste program will specify that they prefer (aka:  require) the hazardous waste determination to rely on the analysis of a representative sample of the waste whenever that is possible.  Some states will require that the lab used to conduct the analysis be a state approved or state certified lab in order for the results to be acceptable while others have no such requirement.

It is your responsibility as a generator of any waste, particularly a hazardous waste, to ensure the lab you use to determine the hazardous waste characteristics of your waste (eg. Ignitable, Corrosive, Reactive, or Toxic) complies with the following:

The following is an attempt to tabulate the lab certification or approval requirements of the 50 states and provide a link to each state’s list of approve labs, if applicable.  This list will be updated as the requirements of each state become known to me.  Please don’t hesitate to contact me with information about your state if you wish to see it added to this list.

And finally, this information is correct to the best of my ability and knowledge.  I make no guarantee of its correctness or completeness.  Be sure to check with the requirements of your state to ensure compliance. (more…)

Documentation of the Hazardous Waste Determination

In earlier articles I wrote of the regulatory requirement for a facility that generates any solid waste to conduct a hazardous waste determination:  The Hazardous Waste Determination and the basis for making the hazardous waste determination.  To summarize both articles, a generator of a solid waste must determine if the waste is a hazardous waste and if any applicable exemptions or exclusions exist.  This determination may be based on the analysis of a representative sample of the waste by an approved lab and test method (analysis-based), or it may be based on the generator’s  knowledge of the raw materials and processes involved (knowledge-based).  Either way, the generator must document not only the results of the determination (ie. hazardous or non-hazardous) but also the basis for that determination.  The purpose of this article is to make known the USEPA requirements for maintaining records of the hazardous waste determination. (more…)

Waste Characterization and Generator Status: What You Need to Know. Wednesday September 25, 2013, 10 – 11 a.m., EST

Hosted by Ohio EPA’s Office of Compliance Assistance and Pollution Prevention (OCAPP). This free 1-hour webinar will discuss the basics of how to determine if a waste meets the definition of hazardous waste, how to properly characterize those wastes, and how to count them in determining your company’s generator status.  Examples of common hazardous wastes, excluded wastes, universal wastes, and waste evaluation methods and tips will be explained.  The practical impacts of proper waste characterization, accounting, and waste reduction practices will also be discussed. Presenter:  Dan Sowry, OCAPP, Environmental Specialist, Central District Office, Columbus, OH.

Webinar seats are limited, click here to register.

After this free webinar on September 25th, come to my full day training seminar in Columbus, OH on September 26th.  There is a fee, but in 8 hours you’ll learn more about the hazardous waste determination, how to manage hazardous waste and how to transport hazardous materials.

The Hazardous Waste Determination for a Waste that Changes from Non-Hazardous to Hazardous

A generator of any solid waste is required to complete a hazardous waste determination according to the procedure at 40 CFR 262.11.  This determination is typically made at the point of generation, ie., at the moment the solid waste is first generated.  However, a generator’s responsibility to complete the hazardous waste determination may continue beyond the initial point of generation if the solid waste may later undergo a chemical or physical change. (more…)