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February 26 – March 1, 2012 ♦ Phoenix, Arizona


Treatability Variance for Containerized Liquids in Mixed Debris Waste –
                            Abstract # 12101


  Catherine Alstatt, Director of Regulatory Interface and Integration
                        Wastren Advantage Inc.
                    TRU Waste Processing Center
                            Oak Ridge, TN
                                                               Session # 69
Transuranic Waste
        Processing Center
•   The TWPC’s mission is to process Transuranic
    (TRU) waste generated from the DOE Oak Ridge
    National Laboratory (ORNL), including debris,
    soils, and tank waste.
•   Waste includes both Contact Handled (CH) waste
    (<2 millisieverts) and Remote Handled (RH)
    waste.
•   Currently, processing CH and RH debris and some
    soils.
•   Low level (LL) and Low Level Mixed (LLM) wastes
    are generated from the processing activities and
    from the TRU waste.

TWPC Mission
• Acceptable Knowledge (AK) prepared for the waste
  characterizes the waste as mixed waste, meaning it
  is both radioactive and regulated under the
  Resource Conservation and Recovery Act (RCRA).
• The waste is generally characterized as containing
  several F listed and D characteristic codes.
• The AK also indicates that a number of the debris
  waste packages contain small amounts of
  containerized liquids.
• The documentation indicates liquid wastes
  generated in routine lab operations were typically
  collected for potential recovery of valuable isotopes.

Acceptable Knowledge
• However, during activities associated with
  decontamination and decommissioning (D&D), some
  containers with small amounts of liquids were placed
  into the waste containers with debris waste.




Acceptable Knowledge
• Many of these containers now hold from 2.5 milliliters
  (ml) to 237 ml of liquid; a few contain larger volumes.
• At least some of these containers were likely empty at
  the time of generation, but documentation of this
  condition is lacking.




Containerized Liquids
Since WIPP compliant Acceptable Knowledge (AK) is
developed on a waste stream basis, rather than an
individual container basis, and includes every potential
RCRA hazardous constituent within the waste stream,
it is insufficient for the purpose of characterizing
individual containers of liquid.




Containerized Liquids
• Debris waste is defined in 40 CFR 268.2(g) [1] as
  “solid material exceeding a 60 mm particle size that
  is intended for disposal and that is: a manufactured
  object; or plant or animal matter; or natural geologic
  material.”

• The definition further states that intact containers of
  hazardous waste that are not ruptured and that
  retain at least 75% of their original volume are not
  debris



Debris Waste
• The prescribed treatment is removal of intact
  containers from the debris waste, and treatment of
  their contents to meet specific Land Disposal
  Restrictions (LDR) standards.

• This is true for containers with incidental amounts of
  liquids, even if the liquid is less than 50% of the total
  waste volume.




Debris Waste
At the TWPC, the standard treatment for debris mixed LLW is
macroencapsulation in accordance with 40 CFR 268.45
standards. For characteristic waste codes there is no need to
treat for underlying hazardous constituents (UHCs).

The LDR treatment standard for containerized liquids with the
assigned listed waste codes are numerical standards.

The standard for most of the characteristic codes is also a
numerical standard with treatment to meet any UHCs.

A few such as D001(ignitable) and D002 (corrosive) must be
deactivated, followed by treatment to meet any UHCs.



Land Disposal Restrictions
The EPA has interpreted that a treatment variance
may be granted when treatment to meet the LDR
standard is feasible, but is nevertheless “not
appropriate.”

Agency rules require alternative standards approved
through the variance result in substantial treatment of
hazardous constituents in the waste so that threats
posed by its land disposal are minimized.



Treatment Variance Requirements
In response to a “Petition for Site Specific Variance
      from Treatment Standards at Sandia National
     Laboratories” dated April 16, 2004 [4], the New
    Mexico Environment Department (NMED) found
    that because the wastes contain radioactive
 materials they are physically different than those
 that were analyzed to develop the LDR treatment
                       standard.
              The NMED further found that
   “treatment and verification of treatment by the
       usual methods would not be protective of
                       workers”.

Basis for Treatability Variance
The existing RCRA LDR treatment standard for liquid
 wastes relevant to this petition is inappropriate due to
 the radioactive nature of the waste.

 The increased radiation exposure resulting from the
 required extra waste handling operations - including
 sampling, analysis, and transportation - is
 inconsistent with EPA guidelines related to
 minimization of risk to workers.



Treatability Variance Applicability
Under the proposed treatment variance containers
with small amounts of free liquids will be treated with a
specialty blend provided by NoChar®.
The NoChar® product is a polymer blend that is
designed to solidify a wide range of organics/aqueous
solutions with one step processing.




Proposed Treatment Process
Process creates a solid polymeric matrix, which
would immobilize RCRA characteristic metals
and reduce any possible leaching if metals are
present.
Additionally, the incorporation into a solid matrix
of any ignitable solvents, if present, would
eliminate the ignitable liquid phase form, in
favor of a deactivated solid form.
The treated liquids would then be placed back
into the debris waste stream to be treated by
macroencapsulation.
Proposed Treatment Process
Current Treatment Process Flow
TWPC Treatment Variance Process Flow




Proposed Treatment Process
In summary, after each individual liquid-bearing container
is treated with the NoChar® process, it is returned to the
debris waste stream and the entire debris package is
macroencapsulated using a process that meets the
specifications found in 40 CFR 268, Land Disposal
Restrictions.
The unique properties of NoChar® provide a combination
of acid-base neutralization, immobilization of potential
RCRA metals, and incorporation/deactivation of liquid
organic wastes.
The NoChar® Process, followed by final
macroencapsulation meets and exceeds the RCRA 3004
(m) standard regarding minimization of threats to human
health and the environment.
Proposed Treatability Variance Approach
The proposed variance meets the intent of the
Treatment Variance guidelines in that the constituents
of concern are substantially treated and the threat to
human health and the environment is minimized by
safe disposal of the treatment residuals.
Additionally, consistent with the guidelines, risks to
workers and the environment associated with extra
handling and transportation of radioactive material are
reduced.
Finally, significant amounts of secondary mixed waste,
that would otherwise be generated, would be
eliminated if the variance was approved.

Conclusion
The proposed variance method, with its redundant
protective features of an initial neutralization,
immobilization, and deactivation, combined with a final
macroencapsulation, is the best technology available
to achieve substantial treatment of these wastes while
minimizing radiological exposures from handling
operations.




Conclusion

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Wastren presentation

  • 1. February 26 – March 1, 2012 ♦ Phoenix, Arizona Treatability Variance for Containerized Liquids in Mixed Debris Waste – Abstract # 12101 Catherine Alstatt, Director of Regulatory Interface and Integration Wastren Advantage Inc. TRU Waste Processing Center Oak Ridge, TN Session # 69
  • 2. Transuranic Waste Processing Center
  • 3. The TWPC’s mission is to process Transuranic (TRU) waste generated from the DOE Oak Ridge National Laboratory (ORNL), including debris, soils, and tank waste. • Waste includes both Contact Handled (CH) waste (<2 millisieverts) and Remote Handled (RH) waste. • Currently, processing CH and RH debris and some soils. • Low level (LL) and Low Level Mixed (LLM) wastes are generated from the processing activities and from the TRU waste. TWPC Mission
  • 4. • Acceptable Knowledge (AK) prepared for the waste characterizes the waste as mixed waste, meaning it is both radioactive and regulated under the Resource Conservation and Recovery Act (RCRA). • The waste is generally characterized as containing several F listed and D characteristic codes. • The AK also indicates that a number of the debris waste packages contain small amounts of containerized liquids. • The documentation indicates liquid wastes generated in routine lab operations were typically collected for potential recovery of valuable isotopes. Acceptable Knowledge
  • 5. • However, during activities associated with decontamination and decommissioning (D&D), some containers with small amounts of liquids were placed into the waste containers with debris waste. Acceptable Knowledge
  • 6. • Many of these containers now hold from 2.5 milliliters (ml) to 237 ml of liquid; a few contain larger volumes. • At least some of these containers were likely empty at the time of generation, but documentation of this condition is lacking. Containerized Liquids
  • 7. Since WIPP compliant Acceptable Knowledge (AK) is developed on a waste stream basis, rather than an individual container basis, and includes every potential RCRA hazardous constituent within the waste stream, it is insufficient for the purpose of characterizing individual containers of liquid. Containerized Liquids
  • 8. • Debris waste is defined in 40 CFR 268.2(g) [1] as “solid material exceeding a 60 mm particle size that is intended for disposal and that is: a manufactured object; or plant or animal matter; or natural geologic material.” • The definition further states that intact containers of hazardous waste that are not ruptured and that retain at least 75% of their original volume are not debris Debris Waste
  • 9. • The prescribed treatment is removal of intact containers from the debris waste, and treatment of their contents to meet specific Land Disposal Restrictions (LDR) standards. • This is true for containers with incidental amounts of liquids, even if the liquid is less than 50% of the total waste volume. Debris Waste
  • 10. At the TWPC, the standard treatment for debris mixed LLW is macroencapsulation in accordance with 40 CFR 268.45 standards. For characteristic waste codes there is no need to treat for underlying hazardous constituents (UHCs). The LDR treatment standard for containerized liquids with the assigned listed waste codes are numerical standards. The standard for most of the characteristic codes is also a numerical standard with treatment to meet any UHCs. A few such as D001(ignitable) and D002 (corrosive) must be deactivated, followed by treatment to meet any UHCs. Land Disposal Restrictions
  • 11. The EPA has interpreted that a treatment variance may be granted when treatment to meet the LDR standard is feasible, but is nevertheless “not appropriate.” Agency rules require alternative standards approved through the variance result in substantial treatment of hazardous constituents in the waste so that threats posed by its land disposal are minimized. Treatment Variance Requirements
  • 12. In response to a “Petition for Site Specific Variance from Treatment Standards at Sandia National Laboratories” dated April 16, 2004 [4], the New Mexico Environment Department (NMED) found that because the wastes contain radioactive materials they are physically different than those that were analyzed to develop the LDR treatment standard. The NMED further found that “treatment and verification of treatment by the usual methods would not be protective of workers”. Basis for Treatability Variance
  • 13. The existing RCRA LDR treatment standard for liquid wastes relevant to this petition is inappropriate due to the radioactive nature of the waste. The increased radiation exposure resulting from the required extra waste handling operations - including sampling, analysis, and transportation - is inconsistent with EPA guidelines related to minimization of risk to workers. Treatability Variance Applicability
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  • 22. Under the proposed treatment variance containers with small amounts of free liquids will be treated with a specialty blend provided by NoChar®. The NoChar® product is a polymer blend that is designed to solidify a wide range of organics/aqueous solutions with one step processing. Proposed Treatment Process
  • 23.
  • 24. Process creates a solid polymeric matrix, which would immobilize RCRA characteristic metals and reduce any possible leaching if metals are present. Additionally, the incorporation into a solid matrix of any ignitable solvents, if present, would eliminate the ignitable liquid phase form, in favor of a deactivated solid form. The treated liquids would then be placed back into the debris waste stream to be treated by macroencapsulation. Proposed Treatment Process
  • 26. TWPC Treatment Variance Process Flow Proposed Treatment Process
  • 27. In summary, after each individual liquid-bearing container is treated with the NoChar® process, it is returned to the debris waste stream and the entire debris package is macroencapsulated using a process that meets the specifications found in 40 CFR 268, Land Disposal Restrictions. The unique properties of NoChar® provide a combination of acid-base neutralization, immobilization of potential RCRA metals, and incorporation/deactivation of liquid organic wastes. The NoChar® Process, followed by final macroencapsulation meets and exceeds the RCRA 3004 (m) standard regarding minimization of threats to human health and the environment. Proposed Treatability Variance Approach
  • 28. The proposed variance meets the intent of the Treatment Variance guidelines in that the constituents of concern are substantially treated and the threat to human health and the environment is minimized by safe disposal of the treatment residuals. Additionally, consistent with the guidelines, risks to workers and the environment associated with extra handling and transportation of radioactive material are reduced. Finally, significant amounts of secondary mixed waste, that would otherwise be generated, would be eliminated if the variance was approved. Conclusion
  • 29. The proposed variance method, with its redundant protective features of an initial neutralization, immobilization, and deactivation, combined with a final macroencapsulation, is the best technology available to achieve substantial treatment of these wastes while minimizing radiological exposures from handling operations. Conclusion