Interpretation Response #06-0238 ([EnergySolutions] [Mr. James H. Portsmouth ])
Below is the interpretation response detail and a list of regulations sections applicable to this response.
Interpretation Response Details
Response Publish Date:
Company Name: EnergySolutions
Individual Name: Mr. James H. Portsmouth
Location State: WA Country: US
View the Interpretation Document
Response text:
Jan 17, 2007
Mr. James H. Portsmouth Reference No. 06-0238
EnergySolutions
345 Hills Street
Richiand, Washington 99354-5507
Dear Mr. Portsmouth:
This is in response to your October 17, 2006 letter regarding the requirements for transporting Class 7 (radioactive) material under the Hazardous Materials Regulations (HMR; 49 CFR Parts 17 1-180). Your questions are summarized and answered as follows:
Q1: The definition of LSA-II material in § 173.403 includes “other radioactive material in which the activity is distributed throughout and the average specific activity does not exceed 10-4 A2/g for solids and gases, and 10-5 A2/g for liquids.” What methods may be used to demonstrate that the activity of radioactive material is “distributed throughout” for the purpose of classifying a material as LSA-II? Is the guidance in NUREG-1608 for determining if the activity is “distributed throughout,” still applicable since it was published in 1998?
Al: The HMR do not specifically define the phrase “distributed throughout” as it applies to the definition of LSA-II or LSA-III material. Furthermore, the HMR do not specify qualitative or quantitative techniques to determine if radioactivity is “distributed throughout” a material. In July of 1998, the Department of Transportation and the Nuclear Regulatory Commission published a guidance document titled, “Categorizing and Transporting Low Specific Activity Materials and Surface Contaminated Objects;” NUREG-1608. The guidance in NUREG-l608 remains applicable for classifying material in accordance with the current regulations. The guidance in NUREG-1608 clarifies that the term “distributed throughout” may include non-homogeneous materials and states that both qualitative and quantitative methods may be used to determine if the activity of the radioactive material is considered to be distributed throughout. The guidance states that qualitative techniques may generally be used for LSA materials having radioactivity in quantities less than 1 A2 but for materials with radioactivity exceeding 1 A quantitative techniques are more appropriate. This determination can be made through reasoned argument, reference, calculation, or measurement. An acceptable method to quantitatively determine if a material’s radioactivity is “distributed throughout” is provided in NUREG-1608 as follows:
“For distributed throughout, the material can be divided into ten or more equal volumes. The volume of each portion should he no greater than 0. 1m³. The
specific activity of each volume should then be assessed (through me treatments, calculations, or process knowledge) and compared. Specific activity differences between any two volumes should not vary by more than a factor of 10.”
Q2: Because of the Department of Energy radioactive materials safety considerations for keeping worker exposure to radioactive materials As Low As Reasonably Achievable (ALARA), it is not always feasible to make extensive direct radiation or contamination measurements. When using the NUREG-1608 techniques, what are the DOT expectations for a shipper of LSA materials to document that they have in fact met the requirement of showing that the specific activity in the waste matrix does not vary by more than a factor of ten from one portion to another in the total volume of waste?
A2: It is the shipper’s responsibility to properly class and describe a hazardous material in accordance with the HMR. The recommended techniques in NUREG- 1603 for determining if radioactivity is “distributed throughout” a material are guidance only; the HMR do not require that these techniques be applied. Alternative methods 0 determining if radioactivity is “distributed throughout” a material may be acceptable for the purpose classing an LSA material, provided the determination is adequately justified.
The techniques described in NUREG-1608 provide a conceptual framework for determining whether the radioactivity is “distributed throughout” a given LSA material. In applying those techniques, the shipper may use any information available to estimate whether the criteria stated there are satisfied. In most cases it would not be expected that. the shipper physically divide up the material in 0.1 m³ (or smaller) volumes and measure the average specific activity in each. However, if the total activity of the material exceeds 1 A2 some quantitative analysis is expected.
Q3: How is “void space” in a waste matrix of LSA material considered in the above question? Must it be included in the quantitative calculation of radioactivity?
A4: Under the method described in Al, void space does not have to be included in the calculation of activity distribution for the purpose of determining if a material is LSA under the HMR.
I hope this information is helpful. If you have further questions, please do not hesitate to contact this office.
Sincerely,
John A. Gale
Chief, Standards Development
Office of Hazardous Materials Standards
173.403
Regulation Sections
Section | Subject |
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173.403 | Definitions |