Disposal of Radioactive Material by Release Into Sanitary Sewer Systems; Withdrawal of Advance Notice of Proposed Rulemaking, 68350-68368 [05-22432]
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68350
Proposed Rules
Federal Register
Vol. 70, No. 217
Thursday, November 10, 2005
This section of the FEDERAL REGISTER
contains notices to the public of the proposed
issuance of rules and regulations. The
purpose of these notices is to give interested
persons an opportunity to participate in the
rule making prior to the adoption of the final
rules.
NUCLEAR REGULATORY
COMMISSION
10 CFR Part 20
[RIN 3150–AE90]
Disposal of Radioactive Material by
Release Into Sanitary Sewer Systems;
Withdrawal of Advance Notice of
Proposed Rulemaking
Nuclear Regulatory
Commission.
ACTION: Advance notice of proposed
rulemaking: Withdrawal.
AGENCY:
SUMMARY: The Nuclear Regulatory
Commission (NRC) is withdrawing an
advance notice of proposed rulemaking
(ANPR) that presented possible changes
to the regulations governing the release
of radionuclides from licensed nuclear
facilities into sanitary sewer systems.
Changes were proposed to account for
the potential for radionuclide
concentration during some types of
wastewater treatment processes. NRC is
withdrawing this advance notice of
proposed rulemaking because it has
determined that there are no widespread
public health and safety concerns due to
potential radiation exposures associated
with the handling, beneficial use, and
disposal of sewage sludge containing
radioactive materials. This notice of
withdrawal acknowledges public
comments sent in response to the
ANPR.
FOR FURTHER INFORMATION CONTACT: A.
Christianne Ridge, Office of Nuclear
Material Safety and Safeguards, U.S.
Nuclear Regulatory Commission,
Washington, DC 20555–0001, telephone
(301) 415–5673, e-mail acr1@nrc.gov.
SUPPLEMENTARY INFORMATION: On
February 25, 1994 (59 FR 9146), NRC
published an ANPR to seek information
to determine whether an amendment to
its regulations governing the release of
radionuclides from licensed nuclear
facilities into sanitary sewer systems
was needed. NRC was considering
revising the approach to limiting these
releases because of the potential effects
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of newly-developed sewage treatment
technologies on radionuclide
reconcentration during wastewater
treatment. The Commission requested
advice and recommendations on several
proposals and asked related questions
regarding whether and in what way the
regulations governing the release of
radionuclides from licensed nuclear
facilities into sanitary sewer systems
should be changed. NRC received
seventy-four comment letters in
response to the ANPR. The comment
period expired on May 26, 1994.
Because there were concerns raised
on the broader issue of long-term effects
of releases of radioactive materials into
sanitary sewer systems, action on the
ANPR was deferred until studies were
conducted regarding potential
radioactive contamination in sewage
sludge. Since that time, NRC
participated in the Interagency Steering
Committee of Radiation Standards
(ISCORS) and co-chaired, with the
Environmental Protection Agency
(EPA), the Sewage Sludge
Subcommittee to facilitate a systematic
and thorough study of the potential
concerns related to radionuclides in
sewage sludge and to obtain data to
support a technical basis for a regulatory
decision.
Regulatory Framework Relevant to the
Release of Radioactive Material Into
Sanitary Sewers
NRC regulations governing the release
of licensed material into sanitary sewer
systems can be found in 10 CFR
20.2003. This regulation was published
in the Federal Register (56 FR 23360;
May 21, 1991) as part of an overall
revision of NRC standards for protection
against radiation. Licensees were
required to implement this regulation by
January 1, 1993. As part of the 1991
revision of 10 CFR Part 20 regulations,
NRC removed the broad provision that
allowed the release of non-biological
insoluble materials into sanitary sewers
because of the potential for this material
to reconcentrate in sewers, publicly
owned treatment works (POTWs), and
sewage sludge. The current NRC
regulations require that any licensed
material discharged into a sanitary
sewer system must be readily soluble in
water or be readily dispersible
biological material. In addition, the
concentration limits for radionuclides
released into a sanitary sewer system,
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listed in Table 3 of the Appendix B to
Part 20, were reduced by a factor of 10
as part of an overall reduction in
effluent release limits. In addition to the
limits in 10 CFR 20.2003, NRC
recommends that licensees should
maintain doses as low as is reasonably
achievable (ALARA) by setting goals for
effluent concentrations and quantities to
be only a modest fraction (10 to 20
percent) of their allowable limits, as
described in NRC Regulatory Guide
8.37, ‘‘ALARA Levels for Effluents from
Materials Facilities,’’ dated July 1993.
NRC also conducts periodic inspections
to ensure that licensees are in
compliance with NRC regulations.
Surveys, Studies, and Reports Relevant
to the Release of Radioactive Material
Into Sanitary Sewers
In May 1992, NRC issued the results
of a scoping study in NUREG/CR–5814,
‘‘Evaluation of Exposure Pathways to
Man from Disposal of Radioactive
Materials into Sanitary Sewer Systems,’’
which evaluated the potential
radiological doses to POTW workers
and members of the public from
exposure to radionuclides in sewage
sludge. The first part of the analysis
estimated the potential doses to workers
for five cases in which radioactive
materials were detected at POTWs
(Tonawanda, NY; Grand Island, NY;
Royersford, PA; Oak Ridge, TN; and
Washington, DC). Doses from the case
studies were estimated to range from
less than 10 microsieverts per year (µSv/
yr) (1 millirem per year (mrem/yr)) to
930 µSv/yr (93 mrem/yr) for members of
the public, using a deterministic
scenario analysis and the reported
radionuclide concentrations and/or
discharges. The second part of the study
estimated the maximum radiation
exposures to POTW workers and others
who could be affected by low levels of
man-made radioactivity in wastewater.
The quantities of radionuclides released
into the sewer systems were assumed to
be the maximum allowed under NRC
regulations at the time. Estimates of the
hypothetical, maximum exposures to
workers ranged from zero to a dose
roughly equal to the dose individuals
receive from natural background
radiation.
In May 1994, the U.S. General
Accounting Office (GAO, now U.S.
Government Accountability Office)
issued a report, GAO/RCED–94–133,
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‘‘Nuclear Regulation: Action Needed to
Control Radioactive Contamination at
Sewage Treatment Plants’’, that
described nine cases where
contamination was found in sewage
sludge or ash or in wastewater
collection systems. GAO concluded that
the full extent of contamination
nationwide was unknown. GAO also
concluded that the ‘‘problem of
radioactive contamination of sludge and
ash in the reported cases was the result,
in large part, of NRC’s regulation, which
was incorrectly based on the
assumption that radioactive materials
would flow through treatment systems
and not concentrate.’’ In June 1994, a
joint U.S. House of Representatives and
Senate hearing (June 21, 1994; S. Hrg.
103–1034) was held to officially release
and address questions raised in the
GAO report. At the hearing, NRC and
EPA agreed to cooperate to develop
guidance for POTWs and to collect more
data on the concentration of radioactive
materials in samples of sewage sludge
and ash from POTWs nationwide.
Between 1994 and 1997, Federal,
State, and industry studies were
conducted to assess reconcentration of
radioactive materials that are released
into sanitary sewer systems. In
December 1994, NRC published
NUREG/CR–6289, ‘‘Reconcentration of
Radioactive Material Released into
Sanitary Sewers in Accordance with 10
CFR Part 20.’’ A review of the literature
demonstrated that some radioactive
materials discharged into sanitary sewer
systems reconcentrate in sewage sludge.
However, the report concluded that the
available data were not sufficient to
assess the adequacy of the requirements
in 10 CFR 20.2003 in preventing
occurrences of radionuclide
reconcentration in sewage sludge at
levels which present significant risk to
the public; nor is the available data
sufficient to suggest strategies for
changing the requirements.
In 1996, the Association of
Metropolitan Sewerage Agencies
(AMSA) conducted a limited survey of
reconcentration of radioactivity in
sewage sludge and ash samples from
some of its member POTWs. Samples
were obtained from 55 wastewater
treatment plants in 17 States. The most
significant sources of radioactivity were
potassium and radium isotopes, which
are Naturally Occurring Radioactive
Materials (NORM). In December 1997,
the Washington State Department of
Health issued a report WDOH/320–013,
‘‘The Presence of Radionuclides in
Sewage Sludge and Their Effect on
Human Health,’’ that was based on
sludge samples taken at six POTWs in
the State. The report concluded that that
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there was no indication that radioactive
material in sewage sludge in the State of
Washington poses a health risk.
The Interagency Steering Committee
on Radiation Standards (ISCORS) was
formed in 1995, to address
inconsistencies, gaps, and overlaps in
current radiation protection standards.
In 1996, the Sewage Sludge
Subcommittee of ISCORS was formed to
coordinate efforts to address the
recommendations in the 1994 GAO
Report. Between 1998 and 2000, the
EPA and NRC (through the ISCORS)
jointly conducted a voluntary survey of
POTW sewage sludge and ash to help
assess the potential need for NRC and/
or EPA regulatory decisions. Sludge and
ash samples were analyzed from 313
POTWs, some of which had greater
potential to receive releases of
radionuclides from NRC and Agreement
State licensees, and some of which were
located in areas of the country with
higher concentrations of NORM. In
November 2003, the results of the
survey were published in a final report,
NUREG–1775, ‘‘ISCORS Assessment of
Radioactivity in Sewage Sludge:
Radiological Survey Results and
Analysis.’’ No widespread or
nationwide public health concern was
identified by the survey and no
excessive concentrations of radioactivity
were observed in sludge or ash. The
results indicated that the majority of
samples with elevated radioactivity had
elevated concentrations of NORM, such
as radium, and did not have elevated
concentrations of radionuclides from
manmade sources.
In February, 2005, the Sewage Sludge
Subcommittee published a report,
NUREG–1783, ‘‘ISCORS Assessment of
Radioactivity in Sewage Sludge:
Modeling to Assess Radiation Doses.’’
This report contains dose modeling
results for seven different sewage sludge
management scenarios for POTW
workers and members of the public.
Results of the dose models and survey
results indicated that there is no
widespread concern to public health
and safety from potential radiation
exposures associated with the handling,
beneficial use, and disposal of sewage
sludge containing radioactive materials,
including NORM.
In February, 2005, the Sewage Sludge
Subcommittee also published a report,
‘‘ISCORS Assessment of Radioactivity in
Sewage Sludge: Recommendations on
Management of Radioactive Materials in
Sewage Sludge and Ash at Publicly
Owned Treatment Works;’’ (EPA 832–
R–03–002B; ISCORS Technical Report
2004–04). This report provides guidance
to: (1) Alert POTW operators, as well as
State and Federal regulators, to the
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possibility that radioactive materials
may concentrate in sewage sludge and
incinerator ash; (2) inform POTW
operators how to determine whether
there are elevated levels of radioactive
materials in the POTW’s sludge or ash;
and (3) assist POTW operators in
identifying actions for reducing
potential radiation exposure from
sewage and ash.
Reasons for Withdrawing the ANPR
The results of the survey and dose
modeling work conducted by the
ISCORS Sewage Sludge Subcommittee
regarding radioactive materials in
sewage sludge and ash provide a
technical basis for withdrawing the
ANPR. The survey demonstrated that
the most significant levels of radioactive
materials in POTWs are attributable to
NORM. The dose modeling work
indicated that, in general, the doses
from licensed materials in sewage
sludge present a sufficiently low health
and safety risk to POTW workers and to
the public under the current regulatory
structure. Therefore, it is not necessary
to modify the current restrictions
regarding the release of radioactive
materials into sanitary sewers (10 CFR
20.2003) as discussed in the ANPR. In
addition, public comments indicated
that several of the options discussed in
the ANPR would be costly to implement
and may not be consistent with efforts
to maintain doses ALARA. For these
reasons, NRC is withdrawing the ANPR.
Public Comments on the Potential
Changes to 10 CFR Part 20
In the ANPR, NRC invited comment
on the following aspects of the
regulation of release of radionuclides
into sanitary sewers: The form of
materials suitable for disposal, the
limits on the total radioactivity of
materials that can be released by a
licensee into sanitary sewers in a year,
also called the ‘‘total quantity limit,’’ the
types of limits applied, and the
exemption for medical patient excreta.
The following is a summary of those
comments and NRC responses.
(1) Form of Material for Disposal
The May 21, 1991, final rule (10 CFR
20.2003) allows soluble and readily
dispersible biological material to be
released but prohibits the release of any
non-biological insoluble material.
Because NRC recognized that new
technologies for wastewater treatment,
such as ion-exchange and some types of
biological treatment, can reconcentrate
radionuclides, NRC invited comments
regarding whether and how regulations
should account for the effects of
different wastewater treatment
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technologies on radionuclide
reconcentration. NRC also invited
comments regarding the potential
impacts that additional restrictions on
the form of materials allowable for
release into sanitary sewers would have
on licensee operations. Public
comments regarding the adequacy of the
current restrictions also were received.
Comment: Nine commenters,
including representatives of the New
York State Energy Office, New York
State Department of Environmental
Conservation, AMSA, and the
Department of Energy (DOE), expressed
the view that the regulations should be
reevaluated because of new sewage
treatment technologies or should
account for the effects of new
technologies used to treat sewage or
sewage sludge. One commenter
suggested that NRC limits should
account for a variety of POTW-specific
factors, including sludge handling
processes, and sludge disposal methods,
and restrictions on the POTW’s treated
water discharge. Another commenter
suggested NRC should take new sewage
treatment technologies into account
only if the results of NUREG/CR–6289,
which was incomplete at the time the
comment was made, indicated that new
sewage treatment technologies had the
potential to cause significant
reconcentration of radionuclides in
sewage sludge. Two commenters
recommended NRC develop technologyspecific reconcentration factors to help
POTW operators to design appropriate
pretreatment plans. A representative of
DOE suggested NRC should expect that
advances in the sewage treatment
process would result in increasing
concentration of radionuclides in
sewage sludge. Two commenters
recommended NRC regulations account
for synergistic health effects of radiation
and pollutants in wastewater, and one
suggested NRC evaluate the synergistic
effects of radiation and the chlorine and
fluoride used in drinking water
treatment.
Response: NRC acknowledges the
commenters’ support for regulations
that would account for the
reconcentration of radionuclides by
wastewater treatment processes.
However, the regulations will not be
changed because the ANPR is being
withdrawn for the reasons previously
explained.
Comment: Four commenters
expressed the view that NRC regulations
should not take sewage treatment
technologies into account. Reasons
included uncertainty that new
technologies will be implemented and a
lack of information about the effects of
the new technologies on radionuclide
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reconcentration. A representative of the
State of Illinois Department of Nuclear
Safety suggested NRC should keep
informed of technological
developments, but should not
implement additional restrictions
without significant evidence that the
current restrictions are not adequate.
Two commenters suggested that, rather
than revising § 20.2003 to account for
new treatment technologies, NRC
should consider placing additional
restrictions on individual licensees to
provide the necessary protection to the
receiving POTWs in unusual cases
where the number of licensees, size of
the sewage treatment plant or nature of
the technology used at the treatment
plant may cause doses above 100 mrem/
yr. One commenter stated that it is
unnecessary for NRC regulations to
account for sewage sludge treatment
technologies because local POTWs have
the authority and mandate to account
for these technologies by developing
industrial water discharge permits
pursuant to 40 CFR 403.5(c)(1).
Response: NRC acknowledges the
commenters’ opposition to the proposed
rule change, which supports NRC’s
decision to withdraw the ANPR. With
respect to the comment that POTWs
have the authority and mandate to
impose limits on radioactive materials
released into sanitary sewers, NRC notes
that, as described in Section 4.7 of the
ISCORS recommendations on
management of radioactive materials in
sewage sludge and ash (EPA 832–R–03–
002B), POTWs may not have the same
authority to regulate radioactive
material as they do to regulate other
materials released into sanitary sewers.
Comment: Eight commenters
expressed the view that NRC regulations
should account for the fact that several
licensees may discharge to the same
POTW, and, of those, five expressed the
view that the regulations should also
take the capacity of the POTW into
account. Five commenters stated that
restrictions on the release of
nonradioactive pollutants established
under EPA’s National Pollutant
Discharge Elimination System (NPDES)
account for the capacity of the receiving
POTW, the wastewater treatment
systems used, and the number of
industrial users discharging to a POTW,
and suggested any new regulations
governing the release of radioactive
materials into sanitary sewers should
take these factors into account. A
representative of DOE expressed the
view that changes to the regulations to
account for multiple dischargers should
be considered but may not be necessary
because sanitary systems serving
multiple licensees would probably be
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large systems in which the licensees’
effluent would be diluted by many other
inputs to the sewer system. One
commenter suggested that, if limits on
the total amount of radioactivity
individual POTWs could receive were
developed, any cases in which the
limits are being exceeded by licensees
that were already discharging sewage
into the sewer system before the limits
were developed should be handled on a
case-by-case basis.
Response: NRC acknowledges the
commenters’ support for regulations
that would account for the capacity of
individual POTWs and the number of
licensees discharging to a single POTW.
However, the proposed change will not
be implemented for the reasons
previously explained.
Comment: Twenty-seven commenters
were opposed to additional restrictions
on the forms of material suitable for
release into sanitary sewers. Twenty-one
stated that the potential for significant
reconcentration of radionuclides during
wastewater treatment probably had been
addressed by the May 21, 1991 changes
to Part 20 (56 FR 23360) that restricted
the forms of materials that could be
released into sanitary sewers and
lowered concentration limits. Another
commenter expressed the view that it
was unclear whether contamination
described in the case studies discussed
in the ANPR occurred because of
violations of the existing regulations,
and also that it would be inappropriate
for NRC to respond to individual
violations of regulatory requirements by
making changes to the regulations for all
licensees. Representatives of six
licensees indicated that additional
restrictions on the forms of material
appropriate for disposal would impose
a significant burden on their operations.
Commenters listed the costs of building
new storage facilities, analyzing samples
of waste to determine whether insoluble
radionuclides were present, and
establishing new collection, handling,
and disposal procedures as well as
retraining of personnel as expenses that
would be incurred if additional
restrictions were imposed. In addition,
three commenters expressed the
concern that further restricting the
forms of material appropriate for
disposal in a sanitary sewer would not
be consistent with NRC’s policy that
doses should be maintained ALARA
because the additional waste handling
that would be required would cause
doses to workers that would not be
justified based on the minimal dose to
members of the public or POTW
workers that might be avoided.
Response: NRC acknowledges the
commenters’ remarks, which support
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the withdrawal of the ANPR. However,
the NRC staff notes the need to analyze
samples of waste to determine if the
waste contains insoluble radionuclides
should not impose an additional burden
because the restriction on releasing
insoluble, non-biological wastes was
already in place when the comment was
made.
Comment: Twenty-three commenters
encouraged NRC to continue to allow
release of readily soluble wastes that
met the quantity and concentration
release criteria in 10 CFR Part 20.
Twenty-one of those commenters
indicated that they were unaware of any
significant problems caused by the
disposal of soluble radioactive material
in sewer systems. Three commenters
stated that they were not aware of any
mechanisms that would reconcentrate
the wastes typical of biomedical
research in sewage sludge, and two of
these stated that the activity levels were
sufficiently low that reconcentration,
even if it did occur, would not cause a
significant dose.
Response: NRC acknowledges the
commenters’ support for the
continuation of the current regulations
which allow certain concentration and
quantities of readily soluble radioactive
material into sanitary sewers.
Comment: Two commenters suggested
that NRC should change the regulation
to re-establish disposal of dispersible
non-biological materials. One
commenter suggested disposal of nonbiological dispersible materials should
be allowed for materials that have halflives of less than 100 days or are below
the concentrations listed in 10 CFR Part
20 Appendix C.
Response: NRC acknowledges the
commenters’ suggestion that release of
non-biological dispersible material into
sanitary sewers be allowed. NRC
understands that reconcentration of a
radionuclide in sewage sludge can be
limited by its half life. However, NRC
has chosen not to change the regulation
governing the release of radioactive
material into sanitary sewers for the
reasons previously explained.
Comment: Six commenters, including
a representative of DOE, noted that the
chemical form of materials released into
the sewer can change, and that materials
that are soluble when released may
precipitate or sorb to solid particles in
the sewer or treatment plant. A
representative of the New York State
Department of Environmental
Conservation suggested NRC study not
only the effect of new technologies on
radionuclide solubilities, but also how
the solubility of radioactive materials
change in sanitary sewers. A
representative of DOE noted that
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precipitation and sorption could cause
risks to individuals who work in
POTWs, work in close contact with
sewers, or who incinerate or use
wastewater treatment sludge. In
addition, the commenter remarked that,
while it appeared to be reasonable to
limit sewer releases to soluble and
dispersible biological materials, NRC
should realize that licensees could
release insoluble or nondispersible
materials to sewer systems
inadvertently. One commenter
expressed the view that NRC regulations
should account not only for the form of
material when released, but the form it
was likely to take after being discharged.
Three commenters expressed the view
that, because the form of a material
discharged is likely to change when it
reaches the sewer or POTW, the
modification to 10 CFR 20 that
eliminated disposal for non-biological
‘‘readily-dispersible’’ materials may not
have removed the chance that
radionuclides could reconcentrate in
wastewater treatment sludge. Two
commenters remarked that
reconcentration of radionuclides
probably would continue, in part
because POTWs are designed to remove
dissolved contaminants from
wastewater. However, both commenters
expressed the opinion that
reconcentration is not necessarily a
problem if the dose any individual is
expected to receive from exposure to
sewers, sewage, or sludge is low.
Response: NRC understands that
materials that are released into the
sewer in a soluble form can precipitate
or sorb to solid materials in sewers or
POTWs, as discussed in NUREG/CR–
6289. Most of the commenters’ concerns
about the potential risk to POTW
workers are addressed in the ISCORS
dose modeling report (NUREG–1783), as
previously explained. Although the
ISCORS dose analysis (NUREG–1783)
does not include an analysis of doses to
workers that come into contact with
sewers, those doses are expected to be
limited because of the limited amount of
time a worker would spend in close
contact with a sewer and because of the
relatively low doses predicted for most
scenarios that involve contact with
sewage sludge.
NRC acknowledges the concern that
licensees may inadvertently dispose of
insoluble non-biological material. NRC
also acknowledges the suggestion that
the regulations should account for
changes in the form of materials that are
likely to occur in sewers and POTWs
and the concern about the efficacy of the
1991 revisions. For the reasons
previously explained, NRC has decided
not to change the regulations governing
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the release of radioactive material into
sanitary sewers. However, NRC staff
notes that, in addition to restrictions on
form, NRC also has imposed annual
limits in 10 CFR 20.2003(a)(4) on the
total amount of radioactivity that can be
released into sanitary sewers to limit the
potential for reconcentration of
radioactive material in sanitary sewers,
sewage sludge, and sludge ash.
Comment: Five commenters
supported additional restrictions on the
form of materials that can be released
into sanitary sewers. One commenter
expressed the view that the practice,
used by some medical research
laboratories, of releasing pureed tissue
samples to the sanitary sewer was
distasteful. Another commenter
expressed the opinion that NRC should
impose any requirement that would
minimize the amount of radioactivity in
the environment.
Response: NRC acknowledges the
commenters’ support for additional
restrictions on the forms of material
suitable for release into sanitary sewers
but is not changing the regulations
because it believes the current approach
is sufficiently protective, as previously
explained.
Comment: Three commenters
requested clarification regarding the
distinction between soluble and readily
dispersible materials. One requested
that an information notice be produced
to address materials used in the biotech
industry. Another commenter expressed
the concern that it would be difficult to
demonstrate compliance with the
restriction that only soluble and readilydispersible biological materials be
released into sanitary sewers if colloids
that flow through filters and resins are
classified as non-biological dispersible
material. The commenter proposed an
operational procedure to distinguish
between soluble and readily dispersible
materials. A representative of the New
York State Department of
Environmental Conservation noted that
traces of insoluble radioactive material
could be released into sewers with
soluble materials, and requested that
NRC establish a lower limit of detection
for insoluble material.
Response: NRC acknowledges the
commenters’ request for additional
guidance on how licensees should
demonstrate the solubility of radioactive
material released to sanitary sewers.
Although NRC does not have plans to
provide additional guidance on this
issue, the staff notes that, as discussed
in NRC Information Notice 94–007,
licensees are free to develop alternative
methods of demonstrating the solubility
of materials they wish to release into
sanitary sewers and to submit these
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procedures to NRC for evaluation on a
case-by-case basis.
(2) Total Quantity of Material
In the May 21, 1991 final rule, NRC
did not change the total quantity limits,
which allow a licensee to release 185
gigabecquerel (GBq) (5 curies (Ci)) of
H-3, 37 GBq (1 Ci) of C-14, and 37 GBq
(1Ci) of all other radioactive materials
combined into sanitary sewers each
year. The use of total quantity limits has
been a long-standing requirement and
was originally included in the rule (10
CFR 20.2003(a)(4)) to address concerns
regarding the possibility for
reconcentration of radionuclides. In the
ANPR, NRC invited comments about the
alternative approach of limiting the
annual release of each radionuclide
individually. NRC also invited
comments about the current total
quantity limits and the potential
impacts that additional restrictions on
the annual releases into sanitary sewers
would have on licensees.
Prior to publishing the ANPR, NRC
received a petition for rulemaking to
amend 10 CFR 20.303 (superseded by
§ 20.2003) and § 20.305 (superseded by
§ 20.2004) from the Northeast Ohio
Regional Sewer District (PRM–20–22). A
notice of receipt of the petition was
published in the Federal Register (58
FR 54071; October 20, 1993). The
petitioner requested that NRC amend its
regulations to require that all licensees
provide at least 24 hours advance notice
to the appropriate POTW before
releasing radioactive material to the
sanitary sewer system. The petitioner
also requested that NRC exempt
materials that enter the sanitary waste
stream from the requirements regarding
Commission approval for incineration
under NRC’s current regulations. NRC
solicited comments on the petition in
the ANPR. The denial of the petition
was noticed in the Federal Register on
January 27, 2005 (70 FR 3898).
Comment: Six comments received in
response to the ANPR supported annual
total quantity limits. Two commenters,
including a representative of DOE,
suggested total quantity limits should be
retained because they help prevent
reconcentration of radionuclides in
sewage sludge and two supported the
total quantity limits because they are
easy for licensees and regulators to
understand and implement. Two
commenters, including the
representative of DOE, suggested it may
be worthwhile for NRC to evaluate
whether the regulation could be
optimized by changing the annual
release limits for some radionuclides. A
representative of the Illinois Department
of Nuclear Safety expressed the opinion
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that the relatively low doses calculated
for the case studies described in the
ANPR and predicted for other scenarios
in NUREG/CR–5814 indicated that
reconcentration of radionuclides in
sewage sludge could be addressed on a
case-by-case basis rather than by
changing the total quantity limits in
§ 20.2003.
Response: NRC acknowledges support
for the current approach of using annual
limits on the total quantity of
radioactive material that can be released
into sanitary sewers by a licensee. In
accord with the commenters’
suggestion, NRC performed a study to
evaluate the reconcentration of various
radiounuclides in POTWs, the results of
which are discussed in NUREG/CR–
6289.
Comment: A representative of the City
of Oak Ridge made positive and
negative statements about NRC annual
total quantity limits. The commenter
stated that both concentration and total
quantity limits were necessary to ensure
protection of workers and to ensure that
traditional methods of sludge disposal
remain acceptable. However, the
commenter also expressed the view that
the current values of the total quantity
limits are too high and stated that
disposal of 37 GBq (1 Ci) of Co-60
annually to the Oak Ridge POTW would
result in unacceptably high
concentrations of Co-60 in the POTW’s
sludge, especially if the material was
released during a relatively short time
period. The commenter also expressed
the opinion that the total quantity limits
are inappropriate for low specific
activity radionuclides because of the
large mass of the radionuclide that
could be discharged. As an example, the
commenter stated that release of 37 GBq
(1 Ci) of U-238 to the city’s POTW in a
year would result in a mass
concentration of uranium of more than
0.05 percent in the POTW’s sludge,
making the sludge licensable source
material. In addition to these comments,
the commenter suggested that, because
the mean retention time of sludge at a
POTW typically is one month or less, a
monthly discharge limit would be more
appropriate than an annual limit.
Response: NRC acknowledges the
commenter’s concern about the release
of Co-60 to a POTW and the suggestion
that quantity limits should be
implemented on a monthly, rather than
an annual, basis. The staff notes that the
1991 revision to 10 CFR Part 20 that
eliminated the discharge of insoluble
non-dispersible radioactive material
into sanitary sewers was implemented
to reduce the possibility of significant
contamination of sewage sludge with
insoluble radionuclides, such as Co-60.
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NRC has decided not to change the
regulations governing sewer release of
radioactive material for the reasons
previously explained. NRC
acknowledges the commenter’s concern
about the applicability of the total
quantity limit to low specific activity
radionuclides. However, NRC does not
agree that the accumulation of large
masses of low-specific activity
radionuclides in POTWs is likely to be
problematic. In addition POTWs have
some authority to impose limits on the
release of material into sanitary sewers
when the purpose of the limits is not
radiation protection, as discussed in
Section 4.7 of the ISCORS
recommendations on management of
radioactive materials in sewage sludge
and ash (EPA 832–R–03–002B).
Comment: Twenty-three commenters
described concerns about the current
approach of limiting the total amount of
radioactivity a licensee may release into
a sanitary sewer system. Nineteen
commenters expressed the opinion that
it is not appropriate to apply the same
total quantity limit to large and small
facilities that discharge different
amounts of sewage and therefore dilute
radioactive materials to different
extents. Another commenter stated that
NRC should not attempt to impose total
quantity limits on large facilities.
Seventeen commenters expressed the
view that NRC should consider relaxing
the total quantity limits because of the
new restriction on the form of material
and lower release concentration limits
implemented in the 1991 revision to 10
CFR Part 20. The commenters expressed
the opinion that adherence to the new
form and concentration limits may
eliminate the need for total quantity
limits. Three commenters suggested
that, instead of limiting the total
quantity of radioactivity a licensee
could dispose of into a sewer, NRC
should focus on the radionuclides and
chemical forms of radionuclides that
reconcentrate in POTWs to a significant
extent. One commenter expressed the
concern that a person could dispose of
37 GBq (1 Ci) of Cs-137 within a month
while remaining in compliance with the
current concentration and total quantity
limits. Another commenter suggested
concentration limits are sufficient and
are superior to total quantity limits
because concentration limits account for
the total volume of water a licensee
releases to the sanitary sewer system.
The commenter noted that, although the
nominal purpose of the total quantity
limits is to eliminate reconcentration,
the total quantity limits do not appear
to prevent reconcentration, as evidenced
by the case studies described in the
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ANPR. The commenter suggested
reconcentration could be avoided by
reducing the allowable concentrations
of those radionuclides that have shown
a tendency to reconcentrate in sewage
sludge.
Response: NRC acknowledges the
comment about the application of the
same total quantity limit to large and
small facilities, but believes that the
system is appropriate. Because the total
quantity limit is designed to reduce the
potential for reconcentration of
radionuclides at POTWs, an appropriate
total quantity limit is more dependent
on the volume of sewage received by a
POTW than it is on the volume of a
licensee’s effluent.
NRC acknowledges the comment that
total quantity limits should be relaxed
or eliminated, but does not agree that
the limits on form and concentration
eliminate the need for annual quantity
limits. As discussed in NUREG/CR–
6289, the form of radionuclides can
change upon entering a sewer or POTW
because of sorption and precipitation.
NRC also acknowledges the concern that
total quantity limits did not prevent the
cases of contamination discussed in the
ANPR. NRC believes that limiting both
the form and total quantity of material
released into sanitary sewers is the best
way to limit the potential for significant
reconcentration of radionuclides
released by licensees into sanitary
sewers.
NRC acknowledges the commenters’
suggestion that, instead of imposing
total quantity limits, it should focus on
those radionuclides that have been
shown to reconcentrate in sewers or
sewage sludge. NRC also acknowledges
the commenter’s concern about the
discharge of Cs-137 but believes the
current approach to be sufficiently
protective for the reasons previously
explained.
Comment: One commenter expressed
the view that additional limitations on
the release of H-3 and C-14 into sanitary
sewers would not produce any public
health benefit because any dose an
individual received from sewerdisposed H-3 and C-14 would be
negligible in comparison to the dose the
individual would receive from
naturally-produced H-3 and C-14.
Response: NRC acknowledges the
commenter’s view that additional
restrictions on the quantities of H-3 and
C-14 are unnecessary. The comment
supports the withdrawal of the ANPR
and the current total quantity limits
which allow the annual release of 185
GBq (5 Ci) of H-3 and 37 GBq (1 Ci) of
C-14 in addition to the release of 37 GBq
(1 Ci) of all other radionuclides
combined.
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Comment: Eight licensees expressed
the view that additional restrictions on
the total quantity of radioactive material
that could be released into sanitary
sewers annually would have a severe
negative impact on their facilities’
operations. Representatives of a
biomedical company, a university, and
the National Institutes of Health (NIH)
noted that a reduction in the total
quantity limits would impose a
significant financial burden on
organizations involved in biotechnical
research, development, or medical
practice, especially if the limits were
reduced to a point that liquid wastes
would need to be solidified and
disposed of as low level waste (LLW).
The representative of NIH estimated that
solidification and disposal of liquid
wastes as LLW would cost NIH 2.8
million dollars annually, as of 1994.
Two commenters remarked that
companies would bear the additional
expense of acquiring or building storage
facilities or acquiring treatment
technologies to remove radioactivity
from liquid waste streams. One
commenter noted that LLW disposal of
many of the materials currently released
into sanitary sewer systems would be a
particularly unnecessary expense and
inefficient use of LLW landfill space
because, in many cases, the material
would decay to negligible quantities
before it reached the LLW landfill.
Five commenters associated with
medical research facilities or companies
that produce radiopharmaceuticals
suggested additional restrictions on the
total quantity of radioactive material
that could be released into sanitary
sewers annually could harm public
health and safety by causing companies
to limit biomedical research and
development efforts. One of these
commenters stated that the amount of
radioactivity released into sanitary
sewers in association with medical
research was insignificant as compared
to the amount of radioactivity released
to sewers in patient excreta and
concluded that release of radioactive
materials associated with biomedical
research should be allowed as long as
the exemption for patient excreta is
continued. Two commenters expressed
the opinion that additional restrictions
on the total quantity of radioactivity a
licensee could release into sanitary
sewers annually would not be
consistent with efforts to maintain doses
ALARA because workers would be
exposed to radioactive material while
processing liquid waste to make it
suitable for LLW disposal.
A representative of a company that
offers health physics services stated
that, for most of its clients who want to
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68355
release radioactive material into sanitary
sewers, the most limiting factor is the
annual total quantity limits. A
representative of the University of
California expressed concern that the
numerical limits in 10 CFR 20.2003
would be lowered, although the
university typically releases only 11.1
Gbq (0.2 Ci) of radioactivity into
sanitary sewers each year.
Response: NRC acknowledges the
commenter’s concerns about the
potential impacts of additional
restrictions on the total quantity of
radioactive material that a licensee can
release to sewers annually. As
previously explained, the additional
restrictions discussed in the ANPR will
not be implemented.
Comment: A representative of AMSA
stated that, although the organization
understands that lowering total quantity
limits could impose financial burdens
on licensees, additional restrictions are
appropriate if they are needed to
prevent contamination of sewage
sludge.
Response: NRC acknowledges the
commenter’s statement, but has decided
not to change the total quantity limits
because it believes the current approach
is sufficiently protective for the reasons
previously explained.
Comment: Twenty-one letters
received in response to the ANPR
included comments on the Northeast
Ohio Regional Sewer District’s request
for NRC to amend its regulations to
require that all licensees provide at least
24 hours advance notice to the
appropriate POTW before releasing
radioactive material into a sanitary
sewer system. Six of the twenty-one
commenters supported a requirement
for licensees to provide the sewage
treatment plant with some type of
reporting on the radioactive materials
released into the sanitary sewer system.
These commenters supported a wide
range of reporting requirements,
including the petitioner’s request for a
24-hour advance notification before
licensees release radioactive material,
monthly or annual discharge reports,
reports of releases that could be a threat
to the POTW workers or the
environment, or notification of large
accidental releases. One commenter
suggested licensees should analyze
effluent samples and include the results
in discharge reports. A representative of
AMSA stated that advance notice of
releases is necessary so that POTW
operators can ensure worker health and
safety and make appropriate decisions
about sludge disposal and reuse.
Fifteen of the twenty-one commenters
did not support such a requirement for
licensees to provide at least 24-hour
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advance notice to the appropriate
sewage treatment plant before releasing
radioactive material into a sanitary
sewer system. Several commenters said
that a 24-hour advance notification
would result in an unnecessary
regulatory burden without providing
additional protection against radiation
or dose reduction. These commenters
expressed the view that the existing
regulations for discharges of licensed
material maintain doses at or below the
existing dose limits for members of the
public and if licensees meet the ALARA
goals, the 24-hour advance notification
would be unnecessary. Several
commenters noted that such notification
would be impractical because most
releases are continuous and involve
very small quantities of radioactive
material. For example, discharges from
hospitals and medical facilities would
change daily depending on the number
of patients treated and types of
treatment used.
Several commenters also noted that
there could be large cost implications
and regulatory burdens associated with
such notification. In addition,
commenters were concerned that data
about releases of radioactive material
could be misinterpreted if release
reports were received and interpreted by
sewage treatment plant personnel rather
than radiation safety specialists. Several
commenters stated that such an NRC
requirement for licensees to provide a
24-hour advance notification was
unnecessary because local
municipalities have authority over their
local sewer district, already have
requirements to follow the Clean Water
Act, and may establish a pretreatment
program for wastewater acceptance. One
commenter noted that the usefulness of
a 24-hour advance notification should
be assessed after the new limits for
sewer discharges are in place.
Response: NRC has determined that a
requirement for advance notification of
each release of radioactive material to a
sanitary sewer would impose an
unnecessary regulatory burden on
licensees without a commensurate
health and safety benefit. Additional
reasons for the denial of the petition are
discussed in the Federal Register notice
published on January 27, 2005 (70 FR
3898).
Comment: Six comment letters
received in response to the ANPR
included comments on the Northeast
Ohio Regional Sewer District’s request
that NRC exempt materials that enter
the sanitary waste stream from the
requirement for NRC approval prior to
treatment or disposal of licensed
material by incineration. Four
commenters supported such an
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amendment because, given the
radioisotopes and activities involved,
the pathways for human exposure from
radioactive wastes seem no more or less
significant if the wastes are dispersed
into water or air. These commenters
suggested that, if release into a sanitary
sewer system is to be considered
disposal, the limits should be set so that
no further regulation of the radioactive
material is needed after release. One
commenter did not support such an
amendment and expressed the view that
it would only serve to provide an openended system for radioactive material to
pass into the environment and to the
public without limitation or
characterization.
Response: NRC approval to
incinerating waste is required to ensure
that NRC may evaluate the potential
impact to the public health and safety
and the environment on a case-by-case
and site-specific basis. Hazards
associated with incineration of sewage
sludge will depend on the specific
characteristic of the sludge and the
radionuclides that may be present.
Additional reasons for the denial of the
petition are discussed in the Federal
Register notice published on January 27,
2005 (70 FR 3898).
(3) Type of Limits
The present approach to limiting
releases of radioactive material into
sanitary sewers is to specify limits on
both the monthly average concentration
of each radionuclide in a licensee’s
sewage and the total quantity of
radioactive matter that a licensee can
release annually. Table 3, Appendix B,
of 10 CFR Part 20 lists the allowable
monthly average concentration of each
radionuclide in a licensee’s release to
sewers. Allowable concentrations are
based upon a calculated dose of 5 mSv/
yr (500 mrem/yr) due to ingestion of 2
liters per day of a licensee’s effluent into
the sanitary sewer.
In the ANPR, NRC invited comments
on this regulatory approach.
Specifically, NRC invited comment as to
whether it should continue to base
concentration limits on the assumption
that an individual would drink 2 liters
of the effluent from a licensee’s facility
each day, and whether exposure at other
locations, such as at a POTW, should be
considered in developing release limits.
In addition, NRC invited comments
about how other exposure scenarios,
such as exposure to radionuclides in
contaminated sludge, should be
accounted for. NRC also invited
comments as to whether it should
establish limits in terms of dose instead
of limits on the quantity and
concentrations of radioactive material
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discharged. Included with the responses
to these inquiries were several
comments about monitoring,
enforcement actions, and regulatory
authority to set limits on releases of
radioactive material into sanitary sewers
that have been addressed with the
General Comments.
Comment: Twenty-three commenters
supported the current modeling
approach of assuming that an individual
ingests 2 liters of water taken from the
licensee’s outfall to the sewer system
each day. Nineteen of these
commenters, representing hospitals,
biomedical laboratories, and
universities, noted that this assumption
is conservative and easy for licensees to
understand. A representative of DOE
noted that the approach appears to be
bounding, and has been ‘‘largely
successful as a regulatory measure’’. The
commenter also expressed the view that,
because this type of consumption is not
expected to be chronic, it is appropriate
to base concentration limits on a
calculated annual dose of 500 mrem
instead of 100 mrem. One commenter
did not specifically address the
assumption that an individual would
drink 2 liters of a licensee’s discharge
each day, but did support the use of a
licensee’s sewer outfall as an
appropriate exposure location. Two
commenters expressed the view that the
modeling assumption was appropriate
because individuals, including children,
could drink or otherwise be exposed to
water directly downstream of a sewer
outfall. Another commenter that
supported the current assumption
expressed the view that modeling
exposure at a licensee’s outfall to a
sewer system is consistent with
modeling exposure at a licensee’s fence
line, as is done in other NRC
assessments, and that considering a
downstream location would be
inconsistent with modeling exposure to
the maximally exposed individual.
Response: NRC acknowledges support
for the current modeling assumption.
The staff notes that several commenters
appeared to believe that the
concentration limits were based on the
assumption that an individual would
consume 2 liters of sewage from a
POTW outfall, rather than 2 liters of a
licensee’s effluent into the sewer
system, each day. Staff notes that the
assumption that an individual would
consume a licensee’s effluent is more
conservative than the assumption that
an individual would consume POTW
effluent because the concentration of
radionuclides in POTW effluent will
have been diluted with effluent from all
of the other residential and industrial
dischargers to the POTW.
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Comment: Three commenters
expressed concern that the
concentration limits are based on an
annual dose of 5 mSv (500 mrem) and
stated that the concentration limits
should be based on an annual dose of
no more than 1 mSv (100 mrem), in
accord with the 10 CFR 20.1301 limit on
doses to members of the general public
from licensed activities. One commenter
expressed the view that the 1 mSv (100
mrem) annual public dose limit should
be lowered. Two commenters expressed
the view that the dose from ingesting a
licensee’s effluent should be included in
the 1 mSv (100 mrem) TEDE annual
public dose limit rather than being
calculated separately and excluded from
the 10 CFR 20.1301 limit. Another
expressed the view that, if any activity
were to be permitted to be discharged
into sanitary sewers, the limiting dose
for exposure to sewage sludge should be
no greater than the dose limit for low
level radioactive waste.
Response: NRC acknowledges the
commenters’ concern about the
hypothetical dose used as the basis for
the concentration limits. As discussed
in the ANPR, the NRC staff believes the
concentration limits based on an annual
dose of 5 mSv (500 mrem) are
reasonable because it is unlikely that an
individual would have access to and
would consume water at the point at
which a licensee discharges water into
the sanitary sewer and because dilution
from additional discharges into the
sewer is likely to reduce the expected
dose to well below the 1 mSv (100
mrem) annual dose limit.
NRC also acknowledges the
commenters’ suggestion that the dose
from consuming effluent released into
the sanitary sewer be included in the
TEDE from other licensee operations.
However, in the case of sewer discharge,
the point of exposure is expected to be
remote from the licensee’s facility.
Because individuals that could be
exposed to a facility’s effluent are
different individuals than those that live
closest to the facility, it would be
unrealistic to include the dose from
exposure to a licensed facility’s effluent
in the total dose from all of the facility’s
activities. The staff notes that comments
regarding the appropriate value of the
annual dose limit for members of the
public from licensed activities specified
in 10 CFR 20.1301 are beyond the scope
of this rulemaking.
Comment: Ten commenters did not
support the use of the current modeling
approach of assuming that an individual
ingests 2 liters of water taken from a
licensee’s sewer outfall each day.
Almost all of these commenters
expressed the view that the assumption
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is unrealistic. One commenter expressed
the view that, while the assumption that
an individual ingests 2 liters of water
taken from a licensee’s sewer outfall
each day is a reasonably conservative
basis for concentration limits, the
assumption may not be a basis for total
quantity limits because it would overemphasize the potential impact of shortlived radionuclides.
Response: NRC acknowledges the
commenters’ opposition to the current
modeling approach. However, it will be
retained because the ANPR is being
withdrawn for the reasons previously
explained. With respect to the comment
about the basis for total quantity limits,
the staff notes that the assumption that
an individual would consume a
licensee’s effluent is used as the basis of
the concentration limits but is not used
as the basis of the total quantity limits.
Comment: Ten commenters suggested
alternate locations that NRC should
consider when developing restrictions
on the release radioactive materials into
sanitary sewer systems. Of these, five
suggested NRC consider the dose to a
person ingesting water once it has
reached or is leaving a POTW rather
than at the licensee’s sewer outfall.
Three commenters suggested NRC
consider locations downstream of a
POTW that would be likely to be
locations from which a municipality
would extract drinking water, while one
suggested doses in the nearest
residential area should be considered.
Another commenter suggested realistic
models would incorporate a factor of at
least one million between the point of
discharge and a receptor locations, and
suggested that, if NRC used a more
realistic dose model, it would become
clear that additional release restrictions
are unnecessary. One commenter
suggested that, in considering potential
doses to members of the public, NRC
should consider that sludge could be
sent to a landfill, applied to agricultural
land, or made into compost for sale to
the public.
Five commenters, including
representatives of POTWs and DOE,
recommended NRC consider doses to
sanitation workers and two commenters
suggested NRC consider doses to
workers that come into contact with
sewage collection systems as well as
POTW workers. One commenter noted
the importance of matching exposure
locations to appropriate pathways and
suggested external radiation by gamma
emitters may be an important pathway
for POTW workers, whereas ingestion of
beta emitters would be expected to be
more important at a downstream
drinking water source. Five commenters
suggested NRC consider that the careful
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68357
treatment given to sewage and sludge
because of the other hazards it presents
should limit doses to sanitary system
workers. One commenter added that
NRC regulations also should prevent
contamination of sewers, POTWs,
receiving waters, and sludge and ash
disposal sites. Another commenter
suggested NRC consider potential
exposures to all POTW residuals,
including sludge, screenings, grit, and
ash. The commenter also pointed out
that sewer pipes may leak and suggested
NRC consider the potential for
groundwater contamination.
Response: The alternate locations that
the commenters suggested should be
considered in dose models will not be
used as a basis for a revision to the
regulations because the ANPR is being
withdrawn for the reasons previously
explained. However, the NRC staff notes
that several of the modeling scenarios
suggested by the commenters, including
sludge handling by POTW workers,
sludge incineration, and exposure to
land-applied sewage sludge, were
considered in the ISCORS dose
modeling project (NUREG–1783).
Comment: Six commenters, including
representatives of POTWs and the New
York State Department of
Environmental Conservation, suggested
that, in addition to protecting the
general public and sanitation workers,
NRC regulations should ensure that
POTWs can continue to use traditional
forms of use or disposal of biosolids
(sewage sludge). One commenter noted
that events that have not resulted in
significant worker exposure have
prevented POTWs from using or
disposing of sewage sludge.
Response: Additional restrictions on
the release of radioactive material into
sanitary sewers will not be implemented
for the reasons previously discussed.
Section 7.2 of the ISCORS
recommendations on management of
radioactive materials in sewage sludge
and ash (EPA 832–R–03–002B) provides
guidance to assist POTW operators in
reducing sources of radiation entering
their treatment facilities.
Comment: Four commenters made
suggestions about ways to account for
complex exposure scenarios, such as
exposure to contaminated sewage
sludge. One commenter suggested that a
variety of scenarios should be evaluated
and that the scenario resulting in the
highest dose should be used to establish
limits on releases of radionuclides to
sewers. Another commenter expressed
the opinion that dose models should
reflect limitations on access that are
imposed to protect individuals from
other health risks associated with
sewage and sewage sludge. One
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commenter suggested no model could
adequately represent complex exposure
scenarios because dose modeling was
not sufficiently well developed.
Response: The approaches the
commenters suggested will not be used
as a basis for new restrictions on the
release of radioactive material into
sanitary sewers because the ANPR is
being withdrawn for the reasons
previously explained. NRC staff
acknowledge the commenter’s statement
about the capabilities of dose modeling.
Comment: Of the fourteen
commenters that addressed dose limits,
seven supported implementation of
dose limits. One commenter expressed
the view that dose limits are preferable
to limits on concentration and quantity
alone because dose limits are easier to
relate to risk. The commenter suggested
the assumptions used to evaluate
compliance with dose limits should be
realistic. The commenter also suggested
the use of a tiered approach, in which
simple bounding assumptions are first
used to evaluate compliance, and more
complex models and more site-specific
data are used only if the simple
bounding model does not demonstrate
compliance. Another commenter
suggested that, if the appropriate models
were developed, releases into sanitary
sewers should be controlled under the
requirements of 10 CFR 20.1302 and
ALARA guidelines just as other facility
effluents are. The commenter also noted
that the potential doses calculated in
NUREG/CR-5814 indicate that the
current regulations governing the
release of radionuclides into sanitary
sewers are more restrictive than other
NRC dose limits on facility effluents.
Two commenters expressed the view
that dose limits should be adopted only
if the current limits were found not to
be protective of the public or POTW
workers. Four commenters agreed with
the proposal in the ANPR that, if dose
limits were adopted, NRC should
publish a regulatory guide that included
concentration and total quantity
guidelines to facilitate compliance. One
commenter asked if licensees would
have a choice of complying with the
dose limit or with the concentration and
quantity guidelines published in a
Regulatory Guide. Two commenters
advocated dose limits, but expressed the
view that the dose limits should be
based on measured radionuclide
concentrations from samples taken from
sewer outfalls and intakes or on
readings from dosimeters placed at
POTWs rather than on concentrations
calculated based on assumptions about
releases to and dilution in sanitary
sewers.
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Response: NRC acknowledges the
commenters’ support for sewer release
restrictions to be expressed as limits on
dose rather than activity. NRC also
acknowledges the commenters’
suggestion that compliance with dose
limits be made based on sample
measurements. However, these options
will not be implemented because the
ANPR is being withdrawn for the
reasons previously explained. No
response is required to the commenter’s
question about compliance with dose
limits because the ANPR is being
withdrawn.
Comment: Of the fourteen
commenters that addressed dose limits,
six commenters opposed dose limits,
and a representative of the New York
State Department of Environmental
Conservation noted potential problems
with implementing dose limits but
suggested NRC study the option. Almost
all of the commenters that opposed dose
limits commented on the uncertainty of
assumptions about exposure pathways
and the relative complexity of
implementing dose limits as compared
to concentration and quantity limits.
Three commenters predicted dose limits
would require more regulatory oversight
because NRC would need to review each
licensee’s dose model. One commenter
expressed the concern that dose limits
could make it necessary for licensees to
require prior approval for releases of
radioactive material into sanitary
sewers. One commenter supported the
current limits but suggested that, if dose
limits were adopted, the dose limit
should be 500 mrem/yr, realistic
modeling assumptions should be made,
and the modeling assumptions to be
used in compliance calculations should
be clearly defined. Another commenter
advocated the use of limits expressed in
‘‘verifiable units of measure’’ rather than
limits expressed as dose and expressed
doubts about the capabilities of
computer models used to calculate dose.
Another commenter stated NRC should
not limit the dose a patient could
receive from a prescribed medical
procedure.
Response: NRC acknowledges the
commenters’ opposition to dose limits,
which will not be implemented because
the ANPR is being withdrawn.
With respect to the commenter’s
concern that NRC should not limit the
dose a patient could receive due to a
medical procedure prescribed by his
physician, the NRC staff notes the scope
of the ANPR was limited to potential
doses due to exposure to radioactive
material in sewage or sludge. In general,
NRC regulates the uses of radionuclides
in medicine as necessary to provide for
the radiation safety of workers and the
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general public and does not intrude into
medical judgments affecting patients.
Additional detail on this topic can be
found in NRC’s Final Policy Statement
on the Medical Use of Byproduct
Material, which was published in the
Federal Register on August 3, 2000 (70
FR 3898).
Comment: Two commenters
expressed concern that NRC would
consider setting any non-zero dose limit
for POTW workers. Both commenters
expressed the view that any dose
received by a POTW worker because of
exposure to radionuclides released into
sanitary sewers by licensees would not
be ALARA if the only reason such
releases were allowed was to provide an
inexpensive method of waste disposal to
NRC licensees.
Response: NRC acknowledges the
commenters’ concern about sanitary
system worker doses but disagrees with
the view that only a dose of zero could
be ALARA. The staff notes that the
ISCORS dose modeling report (NUREG–
1783) concludes that POTW worker
doses typically are very low and are
dominated by exposure to NORM.
Additional restrictions on the release of
radioactive material into sanitary sewers
will not be implemented for the reasons
previously discussed.
Comment: Three commenters
expressed views on the appropriate time
period over which releases should be
averaged. A representative of a
municipality suggested monthly
averages should not be used because the
practice encourages the use of dilution
as a means of meeting the regulations.
A representative of AMSA suggested
daily averages should be used because
POTW workers could be exposed to
sewage and sludge on a daily basis. In
contrast, a representative of a public
utility district supported the use of
weekly or monthly averages.
Response: NRC acknowledges the
commenters’ suggestions about
appropriate time periods over which
releases should be averaged. NRC
believes monthly averages are
appropriate because the effects of small
quantities of radioactivity released
during a month are not expected to
depend on the time period over which
the radioactive material is discharged.
Monthly limits will be retained because
the ANPR is being withdrawn for the
reasons previously explained.
Comment: Ten commenters supported
the development of annual release
limits for individual radionuclides or
groups of radionuclides. Eight
commenters suggested limits for
individual radionuclides should be
based on the results of dose models.
Specific factors that commenters
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suggested should be included in a dose
model included a radionuclide’s
specific activity, half-life, and solubility,
and factors affecting the radionuclide’s
fate and transport in sewers, wastewater
treatment process, and the environment.
Two commenters recommended NRC
consider imposing different discharge
limits for those radionuclides and
chemical forms that reconcentrate in
POTWs to a significant extent and those
that do not. Another commenter
suggested NRC set limits for individual
radionuclides based on whether they
pose a risk primarily due to internal or
external exposure and specifically
suggested pathway modeling should
include exposure to radionuclides that
volatilize from sewage at a POTW,
exposure to raw river water, and
ingestion of treated river water. Another
commenter suggested NRC consider the
fate of radionuclides in engineered
wetlands that are used by some POTWs
as a final treatment step. One
commenter predicted annual release
limits for individual radionuclides
would provide more flexibility to
licensees and eliminate the need for
special licensing exceptions to the
current total quantity limits. A
representative of DOE predicted that
only a very few radionuclides would
require reduced quantity limits even if
the limits were conservative to bound
variations in sewage plant designs and
operating characteristics and to account
for potential improvements in waste
water treatment technology.
Four commenters suggested that
annual release limits should be based on
radionuclide half-life. A representative
of the Texas Department of Health
predicted it may be difficult for
licensees to keep track of the quantity of
each radionuclide released and
suggested NRC impose one quantity
limit for short-lived radionuclides that
would be unlikely to reconcentrate in
sewage sludge and a lower limit for
long-lived radionuclides that have a
greater potential to reconcentrate in
sewage sludge.
A representative of the New York
State Department of Environmental
Conservation noted that it may not be
appropriate to use Annual Limit of
Intake (ALI) values as a basis for annual
release limits for individual
radionuclides, as suggested in the
ANPR, because the ingestion pathway
may not be the most significant
exposure pathway and because the
chemical form of a radionuclide may be
significantly different when it is
released from a POTW than it was when
it was originally discharged to the
sewer. One commenter suggested both
the total quantity of all radionuclides as
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well as quantities of individual
radionuclides released should be
limited, and that quantity limits for
individual radionuclides should be
based on fractions, rather than
multiples, of ALI values. The
commenter also suggested annual limits
should assure the lowest possible rather
than the lowest ‘‘reasonably achievable’’
exposure of members of the public to
radionuclides.
Response: NRC acknowledges the
commenters’ support for the
development of annual release limits for
individual radionuclides or groups of
radiounuclides. However, the proposed
change will not be made because the
ANPR is being withdrawn for the
reasons previously explained.
Comment: Five commenters opposed
the development of annual release
limits for individual radionuclides. Two
commenters suggested the low
calculated doses received in the case
studies discussed in the ANPR indicate
the current regulations are adequate.
Two commenters suggested that, if NRC
were to change the annual quantity
limits, it should focus on Co-60, Sr-90,
Cs-137, Ir-192, and Am-241, because
these radionuclides were identified in
NUREG/CR–5814 as having the
potential to result in a significant dose,
based on the pre-1991 release limits. A
representative of the State of Illinois
Department of Nuclear Safety
recommended NRC change the total
quantity limits only if the releases of Co60, Sr-90, Cs-137, Ir-192, and Am-241
that were determined to be potentially
problematic in NUREG/CR–5814 would
still be permitted, given the restrictions
on form and lower concentration limits
introduced in the 1991 revision to 10
CFR part 20.
Another commenter noted that,
although limiting the quantities of
radionuclides released would not
necessarily be difficult, the need to
analyze batches of wastewater to
determine the quantities of individual
radionuclides being released would be a
significant burden as compared to the
current method the company uses,
which is to base releases on DOT
shipping papers that identify the most
limiting radionuclide in a batch.
However, the commenter also noted that
using limits based on multiples of ALI
would be ‘‘on the right track’’ and
would be similar to methods used in
Europe.
One commenter expressed the view
that the biokinetics of individual
radionuclides could not be modeled
well enough to provide a basis for limits
on the quantity, concentration, or form
in which a radionuclide could be
discharged, especially because the
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models would not include the
synergistic effects of radiation and other
pollutants. The commenter also
expressed the view that the exempt
quantities published in 10 CFR Part 30
represented quantities ‘‘below
regulatory concern’’ (BRC) and
suggested it would be inappropriate to
use multiples of the exempt quantity
values as annual quantity limits.
Response: NRC acknowledges the
commenters’ opposition to annual
release limits for individual
radionuclides, which supports
withdrawal of the ANPR.
(4) Exemption of Patient Excreta
The fourth topic on which NRC
invited comment was the exemption of
patient excreta from the regulations
governing releases of radioactive
material into sanitary sewers. NRC
received fifty-two letters that addressed
the exemption for patient excreta.
Comment: Forty-four commenters,
including a representative of AMSA,
recommended the exemption for patient
excreta be continued and suggested it
required no additional evaluation.
Thirty-three of the commenters stated
the exemption is necessary to maintain
doses ALARA. Several commenters
predicted that the radiological risks to
health care workers, in the case of
hospitalized patients, or family
members, in the case of patients
released from the hospital, associated
with managing excreta would be far
greater than any risk that the excreta
would pose to POTW workers or
members of the general public once
released to the sewer system. Several
commenters noted the possibility that
excreta could be spilled or inadequately
shielded, especially in the case of
patients that had been released from the
hospital. One commenter expressed
concern about radioactive materials
volatilizing from containers of urine.
Another commenter noted that children
or pregnant women could be subject to
increased risk from excreta stored in the
home if the exemption were withdrawn.
Seven commenters noted that, in
addition to the radiological risks,
collection and storage of patient excreta
also could pose biological hazards.
Twenty-seven of the commenters that
supported the exemption noted the
short half life of most
radiopharmaceuticals, and most of these
commenters hypothesized that the risk
that radiopharmaceuticals could pose to
sanitary system workers or members of
the general public would be limited by
their short half lives. Representatives of
two hospitals indicated that
approximately 90 percent of the
radioactivity used at their hospitals was
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in the form of Tc-99m, which has a half
life of 6 hours, and that most of the
remaining radionuclides used have a
half-life on the order of a few days.
Twenty commenters noted the soluble
or dispersible nature of patient excreta
and five commenters suggested the
dilution of patient excreta that occurs in
the sewer system affords ample
protection to the public and to the
environment.
Four commenters remarked that, if
NRC believes the regulation is adequate,
as stated in the ANPR, there should not
be a need to modify the exemption for
patient excreta. Two commenters
predicted restrictions on the release of
patient excreta into sanitary sewers
would not provide a significant benefit
to public health and eleven commenters
suggested the current exemption creates
no environmental or public health
hazard. One commenter remarked that
none of the six case studies presented in
the ANPR indicated that patient excreta
released into sanitary sewers had caused
a significant dose to any individual. A
representative of a large health care
organization noted that no complaints
had been made about the sewage from
any of the organization’s hospitals,
although the hospitals’ effluents were
tested by sanitary system staff routinely.
Another hospital representative
expressed the opinion that hospitals
should not be required to monitor
patient excreta because the practice
causes undue anxiety in the patients,
creates additional burdens for nursing
staff, and is unnecessary because survey
readings generally are low.
Response: NRC acknowledges the
commenters’ support for the exemption
for patient excreta, which supports the
withdrawal of the ANPR.
Comment: Fourteen commenters
stated that elimination of the exemption
would impose significant burdens on
their facilities’ operations. Commenters
expressed concern about the costs of
building holding tanks for excreta,
building separate plumbing systems,
retraining workers, and employing
additional workers to manage patient
excreta. One commenter remarked that
facilities would also incur the cost of
hiring professionals to assess their
current waste management practices
and to recommend changes that would
be needed to comply with new
regulations. Three commenters
remarked that medical facilities may
also incur the costs of increased NRC
licensing fees and inspections. Several
commenters suggested any net health
benefits associated with eliminating the
exemption could not justify the costs of
controlling the excreta, particularly for
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patients being treated on an out-patient
basis.
Seven commenters predicted the costs
of compliance with restrictions on
release of patient excreta into sanitary
sewers would cause a significant
increase in health care costs for patients.
Three commenters predicted that health
care costs would increase both because
of the increased infrastructure and labor
required to manage patient excreta and
because patients’ hospital stays would
be extended so that their excreta could
be managed by hospital staff. A
physician and member of the NRC’s
Advisory Committee on the Medical
Uses of Isotopes (ACMUI) estimated that
the national increase in health care costs
would be approximately 4.5 billion
dollars for patients undergoing
therapeutic procedures and 62 billion
dollars for patients undergoing
diagnostic procedures, as of 1994. The
American College of Nuclear Physicians
and the Society of Nuclear Medicine
jointly estimated that elimination of the
exemption would cause an increase in
health care costs of 5.9 billion dollars
annually.
One commenter expressed the
concern that medical facilities may stop
offering nuclear medicine services to
avoid the legal consequences that could
result if patients did not comply with
restrictions on the release of excreta to
sewer systems. Five commenters
predicted that it would be difficult to
compel patients being treated on an outpatient basis to store their excreta for
decay or return it to a licensed facility.
One commenter expressed the concern
that strict controls over patients could
infringe upon a patient’s constitutional
rights.
Several commenters expressed the
concern that elimination of the
exemption would impact patient care.
Four commenters expressed the opinion
that, if the exemption were eliminated,
the costs or logistical difficulties
associated with managing patient
excreta would cause many facilities to
discontinue offering nuclear medicine
services and could cause the end of
nuclear medicine in the United States.
Three commenters expressed the
concern that elimination of the
exemption for patient excreta would
limit patient access to diagnostic and
therapeutic nuclear medicine services
and five commenters expressed the view
that inaccessibility of nuclear medicine
services would be far more detrimental
to public health than any adverse health
effects that could be averted by
eliminating the exemption for patient
excreta. One commenter noted that
many facilities already have eliminated
some clinical procedures because of the
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lack of access to low level radioactive
waste disposal facilities. Two
commenters expressed the concern that
eliminating the exemption for patient
excreta would diminish the quality of
care that patients received if facilities
limited patient doses to comply with
restrictions on the radioactivity of
patient excreta released into sanitary
sewers. One commenter expressed the
concern that patients may decline
beneficial medical procedures because
of an objection to collecting or having
someone else collect their excreta. One
commenter noted that patient wellbeing would be compromised if patients
needed to remain in the hospital so that
their excreta could be managed because
it would prolong the time away from
their families and jobs. Another
commenter suggested the current
exemption for patient excreta should be
maintained until the impact on health
care could be assessed.
Response: NRC acknowledges the
commenters’ concerns about the
potential costs, legal implications, and
impacts on patient care that may be
caused by removing the exemption for
patient excreta. The exemption will be
maintained because the ANPR is being
withdrawn for the reasons previously
explained.
Comment: Three commenters
suggested the effects of the exemption
should be studied to determine if the
exemption should be eliminated or
modified. A representative of DOE
recommended NRC maintain the
exemption for the excreta of patients
undergoing diagnostic procedures, but
consider placing restrictions on the
excreta of patients undergoing
therapeutic procedures because they
typically receive higher doses of
radiopharmaceuticals. Another
commenter remarked that it would be
inconsistent of NRC to impose strict
restrictions on the release of excreta by
hospitalized patients if the excreta of
patients being treated on an out-patient
basis contributed more radioactivity to
sanitary sewer systems. A representative
of an association of POTWs in
Minnesota stated that the organization is
prepared to rely on NRC judgement
about the appropriateness of the
exemption once NRC has evaluated the
amounts and types of radioactive
materials released into sanitary sewers
through patient excreta, but expressed
concern that the ANPR indicated that
the effects of the exemption had not
been studied and would not be included
in planned modeling efforts. The
commenter also expressed the opinion
that the safety of the exemption should
be evaluated irrespective of the origin of
the waste in medical uses. A
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representative of the New York State
Department of Environmental
Conservation suggested that a range of
possibilities, including retaining the
exemption, eliminating the exemption,
and modifying the exemption, should be
evaluated in an Environmental Impact
Statement (EIS). The commenter stated
an EIS would provide a ‘‘long-needed’’
record of the rationale for the decision
to exempt patient excreta from the
sewer release restrictions and the
expected impacts of the exemption on
the environment and public health.
Response: NRC acknowledges the
suggested modifications to the
exemption of patient excreta and the
suggestion that an EIS should be
performed. However, those suggestions
will not be implemented because the
ANPR is being withdrawn for the
reasons previously explained.
Comment: Two commenters suggested
releases of radioactive materials into
sanitary sewers should be regulated
uniformly, irrespective of the origin of
the wastes. One of the commenters
questioned why the ANPR specifically
stated that doses from patient excreta
were expected to be ‘‘far below the
NRC’s dose limit’’ when this description
was equally appropriate for the
discharges from other licensees.
Another commenter remarked that,
although it may be difficult for medical
institutions to meet restrictions on the
release of patient excreta, the releases
should be regulated because they have
been shown to contaminate sewage
sludge. Another commenter provided
measurements of I–131 in sewage and
sludge in one municipality’s POTW and
expressed the concern that I–131 could
be a source of radiation exposure to
sanitary system workers. The
commenter also expressed the concern
that, although it has a short half life, Tc99m could cause significant radiation
doses to workers exposed to sewage
collection systems directly downstream
of hospitals. In addition, the commenter
expressed the concern that, because I–
131 is very soluble, most of the I–131
that entered a POTW would be
discharged in the treated effluent and
that the POTW’s effluent may, therefore,
exceed NRC limits on the allowable
releases of radioactivity to unrestricted
areas. The commenter also expressed
concern that many municipalities are
not aware that releases of patient excreta
are exempt from NRC restrictions and
can be a significant source of
radioactivity in wastewater.
Response: NRC acknowledges the
commenters’ suggestion that the release
of radioactive material should be
regulated uniformly irrespective of its
origin. However, NRC believes the
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exemption for patient excreta is
appropriate because of the potential
biological and radiological hazards
associated with alternate methods of
managing patient excreta. Additional
limitations on the release of patient
excreta into sanitary sewers are not
being imposed for the reasons
previously discussed. NRC appreciates
the commenter’s concern that
municipalities may be unaware of the
potential for patient excreta to
contribute to the radioactivity of
wastewater and sewage sludge. Section
3.2 of the ISCORS recommendations on
managing radioactive material in sewage
sludge and ash (EPA 832–R–03–002B)
alerts POTW operators that a significant
amount of the radioactivity discharged
to POTWs that serve medical facilities
can be discharged in the form of patient
excreta.
Comment: Two commenters suggested
the exemption for patient excreta should
be eliminated to minimize the release of
man-made radioactivity to the
environment. One commenter expressed
concern about NRC’s policy on allowing
patients who had received nuclear
medicine treatments to leave the
hospital (described in NRC Information
Notice 94–009). The commenter also
expressed concern about specific
incidents in which, the commenter
believed, patients had not been warned
that high residual radioactivity would
result from the medical procedures they
had undergone or had been told that
releasing excreta to a septic system
would not cause adverse health effects.
The commenter remarked that, although
the radionuclides used in nuclear
medicine procedures may be shortlived, each contribution of radioactivity
to wastewater increased the potential
dose to a member of the public. Another
commenter noted that the contribution
of radiopharmaceuticals to the
radioactivity of wastewater increases as
the number of procedures performed
increases. The commenter also
remarked that, if the half-lives of
radioisotopes used in medical
procedures typically are short, as NRC
stated in the ANPR, the burden of
storing the excreta until the
radioactivity decays to background
levels should not be large.
Response: NRC acknowledges the
commenters’ concerns about the
potential effects of the release of patient
excreta into sanitary sewers. However,
NRC believes the current regulations are
protective and has decided to retain the
exemption and withdraw the ANPR for
the reasons previously explained. The
staff notes that comments about the
regulations governing the release of
nuclear medicine patients from the
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68361
hospital are beyond the scope of this
rulemaking.
Comment: One commenter suggested
patient ‘‘vomitus’’ should be included
in the exemption for the release of
patient excreta into sanitary sewers
explicitly. Two additional commenters
mentioned sweat, saliva, blood, tears,
and nasal fluids, but did not make any
specific suggestions about how those
fluids should be addressed in NRC
regulations.
Response: The suggested change to
the wording of the exemption will not
be made because the ANPR is being
withdrawn. However, NRC staff note
that, in practice, the term ‘‘patient
excreta’’ typically is understood to
include situations when patients vomit.
Comment: A representative of a
company that manufactures equipment
that removes radionuclides from
hospital waste noted German law
requires that radioactive materials be
removed from hospital effluent before it
is released into sanitary sewers.
Response: NRC appreciates the
information provided by the
commenter. However, the exemption for
patient excreta will be retained because
the ANPR is being withdrawn for the
reasons previously explained.
Comment: Three commenters asked
questions about the regulatory
implications of potential modifications
to the exemption of patient excreta from
sewer release restrictions. Two
commenters asked whether patients
would be required to store their excreta
at home until it decayed to background
levels of radioactivity or if they would
be required to return it to the medical
facility at which they were treated. Two
commenters asked whether the homes
of nuclear medicine patients would
need to be monitored to ensure that
proper waste disposal procedures had
been followed. One commenter asked if
the elimination of the exemption would
result in changes to 10 CFR 35.75. The
commenter also asked whether
restrictions would apply to all patients
treated with radiopharmaceuticals,
irrespective of the dose they had
received. The commenter also asked
how a licensee would calculate the
radioactivity released by each patient
and whether records of the releases
would need to be maintained by the
licensee.
Response: NRC acknowledges the
many questions on this issue, but is not
responding to them because the ANPR
is being withdrawn.
Comment: One commenter suggested
NRC should exempt the excreta of
animals used in biomedical research
from the restrictions governing the
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release of radioactive material into
sanitary sewers.
Response: NRC notes that this
comment is beyond the scope of this
rulemaking.
(5) General Comments
In addition to comments on the topics
discussed in the ANPR, NRC received a
number of comments on other aspects of
the release of radioactive material into
sanitary sewers. These comments are
addressed in this section.
Comment: Sixteen commenters
expressed the opinion that the current
regulations governing the release of
radioactive materials into sanitary
sewers are adequate and should not be
changed. To support this view,
commenters remarked that the number
of incidents of contamination is small
compared to the number of POTWs
receiving radioactive materials and that
the doses received in those instances are
believed to be low. Commenters also
suggested the regulations should not be
changed in response to a small number
of cases of contamination, especially if
some of those cases involved violations
of the applicable regulations. One
commenter noted that modeling results
described in NUREG/CR–5814 indicate
that releases of radionuclides used in
biomedical research are expected to
result in doses below the ALARA
guidelines in NRC Regulatory Guide
8.37. A representative of the Texas
Department of Health suggested the
regulations should not be changed
unless modeling results demonstrated
that exposures other than ingestion
could cause an annual dose greater than
5 mSv (500 mrem). Two commenters
suggested the risk of adverse health
effects associated with exposure to
radioactive material released into
sanitary sewers should be evaluated in
comparison to the health risks
associated with exposure to hazardous
chemical and biological materials in
sewage and sludge. One commenter
suggested the current limits are
appropriate because the quantities and
concentrations of radionuclides at
affected POTWs appear to be within 10
CFR part 30 limits for general licensees.
Response: NRC acknowledges the
commenters’ support for the current
regulations, which supports withdrawal
of the ANPR.
Comment: Nine commenters,
including a representative of DOE,
suggested the changes made to 10 CFR
part 20 in 1991 may have significantly
reduced the potential for
reconcentration of radionuclides in
POTWs, and that resources should not
be expended to address a problem that
may have already been solved. Of these,
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five commenters noted that the ANPR
did not include any information about
contamination problems that had
occurred since the modification of 10
CFR part 20 and two commenters noted
that most of the contaminants in the
case studies presented in the ANPR
were insoluble non-biological materials
and would not meet current release
criteria. Several commenters
recommended NRC evaluate the effects
of the lower discharge concentration
limits and prohibition against
discharging insoluble, non-biological
materials into sanitary sewers before
making additional changes to 10 CFR
part 20. One commenter expressed the
opposite view and stated that the NRC
should not assume that the changes
made to 10 CFR part 20 in 1991 would
eliminate contamination of POTWs with
licensed radioactive materials.
Response: NRC acknowledges the
commenters’ recommendation that it
study the effect of the changes made to
10 CFR part 20 in 1991 on the amount
of radioactive material at POTWs. The
NRC staff notes that the ISCORS sewage
sludge survey and dose modeling work
were performed several years after the
January 1, 1993, deadline for licensees
to meet the revised requirements and
should reflect the effects of the 1991
revision of the regulation.
Comment: Five commenters
expressed the view that additional
restrictions on the release of radioactive
materials into sanitary sewers would not
be consistent with efforts to keep doses
ALARA. Several of the commenters
predicted that doses to workers that
were required to collect or prepare
waste for disposal would be far greater
than the collective dose that could be
averted by more restrictive sewer release
limits.
Response: NRC acknowledges the
commenters’ opposition to additional
restrictions on the release of radioactive
materials into sanitary sewers, which
supports the withdrawal of the ANPR.
Comment: Four commenters stated
that any additional restrictions on the
release of radioactive material into
sanitary sewers would have a significant
negative impact on the facilities they
represented. One commenter expressed
the view that banning the release of
radioactive material into sewers would
impose a large financial burden on all
biological research facilities and
estimated that, as of 1994, alternative
disposal methods would cost his
company $150,000 to $300,000
annually. A representative of a nuclear
laundry stated that additional
restrictions on the release of radioactive
material into sanitary sewers could have
a serious detrimental effect on his
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company and its customers in nuclear
laundries could no longer operate.
Another commenter suggested new
restrictions should be implemented
gradually by adding new restrictions
during license renewals.
One commenter expressed concern
that additional restrictions on the
release of radioactive material to sewers
would encumber facilities that perform
medical research, and requested that
educational and medical research
institutions be exempted from the
regulations because the long-lived
radionuclides that had been detected in
the cases described in the ANPR
typically are not used by medical
research facilities. The commenter also
requested that, if medical research
facilities were not exempted, more
explicit guidance about the implications
of the regulations on specific practices
used in medical research facilities be
provided by NRC. Another commenter
proposed that the regulation should
explicitly permit disposal of medical
diagnostic products in aqueous mixtures
that contain less than 370 kBq (10
microcuries) of radioactivity and which
are composed of isotopes with half-lives
less than 61 days.
Response: NRC acknowledges the
commenters’ information about the
burdens that could be caused by
additional restrictions on the release of
patient excreta into sanitary sewers,
which supports the withdrawal of the
ANPR. The staff notes that requests for
exemptions of certain classes of
facilities or types of waste are beyond
the scope of this rulemaking. NRC
acknowledges that guidance written
specifically for medical research
facilities would be helpful to some
licensees, but does not have plans or
resources to develop such guidance.
Comment: A representative of DOE
expressed the view that the current
rules are protective of public heath and
safety and the environment, and noted
that, if the provision for release of
radioactive materials into sanitary
sewers was not available, risks to the
public would result from other waste
management options. As an example,
the commenter predicted elimination of
the release of radioactive material into
sewers would cause an increase in
traffic accidents because of the need to
transport more waste to LLW disposal
facilities. However, the commenter also
recommended NRC increase inspections
of licensees’ releases into sanitary
sewers and perform additional analyses
of potential doses to members of the
public and sanitary system workers to
ensure that adequate safety provisions
are in place to preclude accidental
discharge of large quantities of
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radioactive material. The commenter
also recommended NRC contact AMSA
and industry trade groups to obtain
additional information about variations
and trends in wastewater treatment
technologies, practices, and regulations.
Response: NRC acknowledges the
commenter’s remarks regarding the risks
that could result from additional
restrictions on the release of radioactive
material into sanitary sewers, which
support the withdrawal of the ANPR. In
accord with the commenter’s
suggestions, NRC participated in the
ISCORS sewage sludge survey (NUREG–
1775) and dose modeling report
(NUREG–1783), the results of which
provide a technical basis for
withdrawing the ANPR. The staff
acknowledges the suggestion regarding
NRC inspection activities but notes the
topic is beyond the scope of this
rulemaking.
Comment: A representative of NIH
stated that, although NIH is a large
facility conducting both biomedical
research and medical diagnosis and
treatment, and its usage of some
isotopes fluctuates considerably, NIH
has been able to manage its radioactive
liquid wastes in compliance with NRC
regulations. The commenter also stated
that NIH uses large, centrally-located
tanks to hold short-lived radionuclides
for decay, and that NIH has been
granted an exception to the total
quantity limits that allows it to
discharge a total of 296 GBq (8 Ci)
annually.
Response: NRC acknowledges the
commenter’s information regarding the
adequacy of the current regulations
governing the release of radioactive
material into sanitary sewers.
Comment: A commenter who was a
member of ACMUI as well as a
physician and professor of Radiological
Sciences at the University of California,
Los Angeles, expressed several concerns
regarding the possible changes
described in the ANPR. The commenter
expressed the opinion that NRC
resources would be better spent
changing other parts of 10 CFR part 20
than by making the changes proposed in
the ANPR. The commenter also stated
that Agreement States had been
reluctant to adopt the changes made to
10 CFR part 20 in 1991 because of
unspecified problems with the revised
rule. The commenter expressed concern
that user fees were used to support a
National Council on Radiation
Protection study of the number of
various types of nuclear medicine
procedures performed annually as of
1989. The commenter also expressed
concern that any change in NRC
regulations governing the release of
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radioactive materials into sewers would
later be changed by an EPA rule, and
that NRC licensees would, in effect, pay
for a rule twice by paying both NRC user
fees and paying taxes to support EPA.
The commenter asked why the NRC
had published the ANPR and expressed
concern that NRC wasted licensees’ time
by asking for data regarding various
nuclear medicine procedures. The
commenter stated that the data had been
given to NRC in 1990 and asked why
NRC did not use these data to derive
concentrations of various radionuclides
in sanitary sewage. The commenter also
suggested NRC could request data
regarding concentrations of radioactive
materials in wastewater and sewage
sludge from POTWs in Agreement
States. In addition, the commenter
suggested NRC review any proposed
changes related to medical uses of
isotopes with the ACMUI and expressed
an unfavorable opinion about NRC’s
program to regulate medical uses of
radionuclides.
Response: NRC acknowledges the
commenter’s statements about the 1991
revision to 10 CFR part 20 but notes that
other parts of the regulation are beyond
the scope of this rulemaking. A response
to the commenter’s displeasure at
paying licensing fees to support this
rulemaking is not needed because the
ANPR is being withdrawn. The same
applies to the commenter’s concern that
EPA would impact a change in NRC’s
regulations. Because the ANPR is being
withdrawn, that concern is no longer
applicable to this issue.
NRC published the ANPR to invite
comments and recommendations from
interested parties on potential changes
in the regulations governing the release
of radioactive materials into sanitary
sewers. In response to the commenter’s
concern about the time licensees may
have spent responding to the ANPR,
NRC notes that the ANPR invited
comment but did not require a response.
In addition, NRC notes that the ANPR
invited comment on a variety of issues
and was not limited to a request for
information to support the derivation of
concentrations of radionuclides in
sewage.
NRC acknowledges the commenter’s
suggestion that potential changes to the
rule be discussed with the ACMUI, and
the commenter’s statements about
NRC’s program to regulate medical uses
of radionuclides.
Comment: Three commenters
expressed the view that cases of
contamination at POTWs demonstrate
that the current regulations governing
the release of radioactive material into
sanitary sewers is inadequate. All three
commenters expressed the concern that
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the regulations did not adequately
protect the health and safety of POTW
workers. In addition, a representative of
AMSA expressed the concern that the
current regulations could jeopardize the
ability of POTWs to fulfill their
environmental objectives. The
commenter also expressed concern
about NRC’s involvement with existing
cases of contamination and urged NRC
to take a more active role in protecting
POTWs from contamination with
radionuclides.
Each of the three commenters
expressed the opinion that the current
regulations also fail to protect POTWs
from the legal and financial
consequences of contamination of
POTWs and POTW biosolids with
radionuclides. Two commenters noted
that the public ultimately bears the costs
associated with contamination of
POTWs and one estimated that billions
of dollars of public funds could be
required to dispose of contaminated
sludge and decontaminate POTWs. A
representative of the City of Oak Ridge
outlined the history of contamination of
the Oak Ridge POTW with Co-60, Cs137, uranium isotopes, and I-131 from
1984 to 1994. The commenter noted
that, as of 1994, disposal of wastewater
treatment sludge cost the City of Oak
Ridge approximately $100,000 per year,
primarily because of radioactive
contamination. The commenter stated
that, because of this expense, the city is
in the process of implementing its own
limits to control releases of radioactive
materials into the sanitary sewers and
provided a reference that describes the
approach that has been taken to control
radioactive materials through the
municipality’s industrial pretreatment
program.
A representative of the Northeast
Ohio Regional Sewer District noted that,
although no significant health or safety
problems had been found to result from
the contamination at the district’s
Southerly Facility, the district has had
to manage difficult regulatory issues and
concerns from the public and from
workers that had cost the district, as of
1994, $1.5 million to resolve. The
commenter remarked that the sanitary
district had over one hundred thousand
cubic meters (4 million cubic feet) of
Co-60 contaminated ash at its Southerly
Facility and had recently discovered
contamination at another one of its
POTWs. The commenter expressed the
view that the District’s problems were
attributable to inadequate regulations or
ineffective enforcement by NRC and
suggested that major revisions to both
10 CFR part 20 and to NRC’s
enforcement program were overdue.
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Response: NRC acknowledges the
commenters’ concerns about cases of
contamination and protection of POTW
workers. However, NRC believes that
the restrictions on the forms of material
suitable for release and lower
concentration limits established in the
1991 revision to 10 CFR part 20 have
reduced the potential for significant
contamination of POTWs or sewage
sludge with radionuclides. Although
additional restrictions on the release of
radioactive material into sanitary sewers
will not be implemented, Section 7.2 of
the ISCORS recommendations on
management of radioactive materials in
sewage sludge and ash (EPA 832–R–03–
002B) provides guidance to assist POTW
operators in reducing sources of
radiation entering their treatment
facilities. Comments about NRC’s
enforcement program are beyond the
scope of this rulemaking.
NRC acknowledges the information
provided by the City of Oak Ridge
regarding the POTW’s industrial
pretreatment program. Information
about the program is summarized in
Appendix F of the ISCORS
recommendations on management of
radioactive materials in sewage sludge
and ash (EPA 832–R–03–002B).
Comment: A representative of a
sanitary district stated that, contrary to
the position taken by NRC in the ANPR,
many cases of contamination of POTWs
are the result of relatively basic
wastewater treatment technologies. In
addition, the commenter expressed the
view that NRC’s emphasis on the
concept of ‘‘reconcentration’’ as the
cause of contamination problems is
misleading and noted that, at one POTW
in the district, it appeared that particles
of Co-60 were removed from the sewage
through settling, as other solids are
removed, rather than through
reconcentration of dissolved cobalt or
agglomeration of fine particles. The
commenter expressed the view that the
new restrictions on the forms of
materials suitable for release into
sanitary sewers may prevent many
problems with insoluble materials such
as Co-60 if the regulations are properly
enforced.
Response: NRC acknowledges the
commenter’s concern that the term
‘‘reconcentration’’ was used in the
ANPR to describe all processes by
which the concentration of
radionuclides in sewage sludge or ash
could be increased on volumetric basis.
NRC understands that radioactive
materials may be concentrated by
common wastewater treatment
processes, as discussed in NUREG/CR–
6289.
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Comment: Seven commenters
expressed the view that discharges of
radioactive materials into sanitary
sewers should be regulated locally. Two
commenters suggested that, because
relatively few cases of contamination
had been observed, it appeared that the
cases could be resolved without NRC
involvement. One commenter expressed
the view that local control would be
easiest to implement if the problematic
discharges involved other hazardous,
nonradioactive materials.
Five commenters, including a
representative of AMSA, expressed the
opinion that POTWs should have the
legal authority to establish local limits
for the release of radioactive material
into sanitary sewers. Three of the
commenters expressed the concern that,
although municipalities are held
responsible for the disposal or beneficial
use of POTW sludge, the municipalities
have no control over the radioactivity of
materials discharged to the sewer
system that affect sludge quality. One
commenter expressed the concern that
the existing regulatory framework is
inadequate because NRC maintains that
the party in possession of the
radioactive material is responsible for
remediation, offers no assistance to
POTWs that have been contaminated by
a licensee’s effluent, and states that the
AEA indicates that its regulations
preempt more restrictive local
regulations. The commenter expressed
concern that NRC has indicated that this
position would not change even if NRC
had proof that material was illegally
discharged by a licensee and that a
POTW’s only recourse to recover
remediation costs is to take legal action
against the discharger. One of the
commenters suggested NRC should
either assume responsibility for
disposing of radioactive sludge
generated in POTWs as a result of
‘‘errant discharge’’ from NRC licensees
or allow POTWs to regulate the
discharge of radioactive materials into
sewer systems. The other commenter
suggested that, in cases in which the
reuse or disposal of sludge is restricted
because of its radiological
contamination, NRC should cooperate
with EPA to help affected POTWs
establish local discharge limits to
protect the traditional method of
disposal or reuse of the biosolids.
Another commenter stated that it was
not necessary, feasible, or appropriate
for NRC to develop new regulations that
would limit the disposal of radioactive
material into sanitary sewers because
POTWs already had the legal authority
and mandate to establish and enforce
appropriate pretreatment standards that
would prevent contamination of POTWs
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or sewage sludge, pursuant to the Clean
Water Act (33 U.S.C. 1317(b) and (d)
and 1319) and EPA Clean Water Act
Standards (40 CFR Part 403).
Response: NRC acknowledges the
commenters’ concern about the power
that local authorities have to regulate
the release of radioactive material to
their POTWs. The U.S. Supreme Court
has held that, for certain activities
covered by the AEA, Federal authority
preempts other regulatory authorities
whose purpose is radiation protection. It
is difficult to predict whether unusual
cost to the POTW caused by radioactive
effluent discharges would be a sufficient
reason to impose more restrictive
discharge limits than those permitted
under Federal law because there are no
Federal cases in which the specific facts
corresponded to the scenarios faced by
local POTW authorities. More
information on this issue is presented in
Chapter 4 and Section 7.2 of the ISCORS
recommendations on management of
radioactive materials in sewage sludge
and ash (EPA 832–R–03–002B).
Comments regarding NRC’s
responsibility for the disposal of
contaminated sludge are beyond the
scope of this rulemaking. As discussed
in Chapter 7 of the ISCORS
recommendations (EPA 832–R–03–
002B), in individual cases of
contamination, legal counsel should be
consulted to determine if dischargers
may be liable for portions of
remediation costs.
Comment: One commenter
recommended NRC exempt POTWs
from any regulations that would apply
to material released into their systems
because the potential benefits of
regulating POTWs would not justify the
costs.
Response: This suggestion is beyond
the scope of this rulemaking.
Comment: Five commenters,
including a representative of AMSA,
expressed the view that POTWs should
be able to apply the same type of
pretreatment standards to radionuclides
in licensees’ effluent that are applied to
toxic materials discharged into sewer
systems by industrial dischargers as part
of EPA’s NPDES program. Commenters
noted that local limits can account for
the number of licensees discharging to
a single POTW, the total flow into a
POTW, and the effects of various
treatment process on radionuclide
reconcentration. Three commenters
noted that, in general, local restrictions
on discharges of pollutants to POTWs
are established by determining an
allowable load of a pollutant to a POTW
that will not create a violation of the
POTW’s effluent limit and not interfere
with disposal or reuse of the POTW’s
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biosolids, and then allocating that limit
among industrial facilities that
discharge effluent to the POTW. Two
commenters expressed the view that the
same process should be used to develop
individual limits for each radionuclide,
taking into account each radionuclide’s
specific activity, half-life, and solubility.
One commenter noted that this
procedure cannot be followed with
radioactive materials because no
‘‘acceptable’’ levels of radionuclides in
sludge have been established. Another
commenter recommended NRC
coordinate any future regulations
affecting sanitary sewer discharges with
EPA requirements for Clean Water Act
discharges, including Categorical
Standards, NPDES permits, and
regulations pertaining to sewage
sludges.
Two commenters suggested that,
because setting limits for radioactive
materials will be new to many POTWs,
NRC should provide guidance on
establishing local limits on the release
of radioactive materials into sanitary
sewers. A representative of AMSA
suggested a number of topics that the
recommended guidance should address
and recommended NRC consider two
EPA resources used to develop limits on
industrial discharges to POTWs.
Response: This comment includes
detailed recommendations about the
creation of a program in which the
release of radionuclides into sanitary
sewers would be regulated by local,
rather than Federal, authorities, and is
beyond the scope of this rulemaking.
Although guidelines for the
development of local limits under such
a program have not been developed,
many of the topics the commenters
requested be included in such guidance
are included in the ISCORS
recommendations on management of
radioactive materials in sewage sludge
and ash (EPA 832–R–03–002B), as is
information about local pretreatment
programs established in Albuquerque,
NM, St. Louis, MO, and Oak Ridge, TN.
Comment: One commenter was
concerned that system-specific
discharge limits could be difficult to
implement if, as is done in the NPDES
process, discharge limits are based on
the ‘‘waste assimilative capacity’’ of the
receiving waterway, which, the
commenter stated, could be difficult to
determine. The commenter also
expressed concern that licensees would
need to obtain prior approval for sewer
discharges, and that regulatory agencies
would need to keep track of separate
discharge allotments for each licensee
and any changes to each POTW’s
treatment processes. The commenter
noted that an alternative to establishing
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system-specific discharge limits would
be to set activity limits so low that
regulatory limits or ALARA goals for
public doses would be met, irrespective
of the wastewater treatment process
used, the capacity of the receiving
POTW, or the number of dischargers
discharging to the POTW. The
commenter noted that this approach
would not require as much regulatory
oversight and suggested these
approaches should be evaluated in an
EIS.
Response: NRC acknowledges the
commenter’s concerns about the
difficulties involved with implementing
system-specific discharge limits. An EIS
that evaluates the alternatives will not
be developed because the ANPR is being
withdrawn for the reasons previously
discussed.
Comment: One commenter asked for
clarification as to how the revised rule
would relate to NRC decommissioning
standards and various EPA rules and
suggested NRC hold public hearings on
the issue.
Response: NRC is not responding to
the request for clarification on the
relationship between the proposed rule
and EPA or NRC standards because the
ANPR is being withdrawn.
Comment: Ten commenters expressed
the view that any change to the
regulations governing the release of
radioactive materials into sanitary
sewers should have a solid technical
basis. Three commenters recommended
NRC delay decisions about the need for
modifications to the regulation until
NUREG/CR–6289, which was
incomplete at the time, was made
available to licensees. Two commenters
expressed concern that the ANPR was
offered without a significant risk
assessment. Six commenters
recommended that any proposed change
in the regulation should be based on a
realistic assessment of either the
collective dose or the risks to members
of the public and POTW workers that
the new regulations would avert. Two
commenters expressed the concern that
changes to the regulations would be
made for reasons other than technical
reasons, including regulatory
convenience, a perception of public
opinion, or political pressure.
A representative of the New York
State Department of Labor remarked that
some of the regulatory changes
proposed in the ANPR would be
complex for both licensees and
regulatory agencies to implement and,
therefore, should not be undertaken
without a without a firm technical basis.
The commenter expressed the view that,
except for the exemption of patient
excreta, all of the options discussed in
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the ANPR required more analysis before
NRC would have sufficient information
on which to base a decision. The
commenter expressed the opinion that
frequent changes in the same regulation
are especially burdensome for licensees
and urged NRC to perform the necessary
analyses before changing the rule again.
Representatives of the New York State
Energy Office and New York State
Department of Environmental
Conservation encouraged NRC to
develop an EIS to evaluate the options
discussed in the ANPR. The
representative of the New York State
Department of Environmental
Conservation remarked that the current
regulations, including the revisions
made in 1991, had never undergone a
full environmental review.
Two commenters expressed the
concern that the current limits on the
discharge of radioactive material to
sewers do not reflect the hazards
radioactive materials could pose in a
POTW or after release to the
environment. The commenters
recommended NRC initiate a study that
would include a POTW hazard
identification and assessment, exposure
and toxicity assessments, and a risk
characterization. The two commenters
also recommended NRC study the fate
and transport of radionuclides in
sewers, POTWs, and the environment. A
representative of the City of Oak Ridge
provided a reference that discussed the
fate and transport of radionuclides in
the municipality’s POTW. A
representative of AMSA recommended
NRC cooperate with EPA, POTWs, and
affected industries to assess the
exposure and contamination pathways
of radionuclides, and the impact of
radioactive materials on wastewater
treatment processes.
Response: NRC acknowledges the
commenters’ view that the 1991 revision
to the regulations governing the release
of radioactive materials into sanitary
sewers should have been based upon
detailed risk analyses. As discussed
previously, NRC cooperated with
representatives of EPA and POTWs in
developing the ISCORS survey and dose
modeling project to assess the
radioactive contamination in POTWs
and pathways for exposure of POTW
workers and members of the general
public to radionuclides released into
sanitary sewers. The results of these
analyses served as the technical basis
for the withdrawal of the ANPR. An EIS
for the rulemaking will not be
performed because the ANPR is being
withdrawn for the reasons previously
discussed.
Comment: Three commenters,
including a representative of AMSA,
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recommended NRC study the extent of
the use of sewer discharges and
contamination of POTWs around the
country. The representative of AMSA
suggested that, because NRC had
acknowledged that it did not know how
many POTWs in the country were
contaminated with radionuclides and
because it would be inappropriate to
develop national standards based on
contamination in a few isolated cases,
NRC should establish a task force
composed of NRC and EPA staff as well
as representatives of POTWs and
licensees to study the nature and extent
of radioactive contamination of POTWs
nationally. Three commenters
recommended NRC determine which
licensees release radioactive material
into sanitary sewers and two of these
commenters recommended NRC make
the information available in a national
database. Of these commenters, one
suggested the database should be similar
to the EPA’s Toxic Release Inventory
and the other suggested the database
should include information about the
mass of each radionuclide discharged
per year by each licensee, the volume of
the licensee’s discharge, and the
licensee’s POTW service area. A
representative of one utility district
expressed concern that, as of 1994, the
NRC had not been able to provide a list
of the licensees discharging into the
district’s sewer system and that the
district had, therefore, been unable to
initiate an appropriate monitoring
program.
Response: NRC acknowledges the
commenters’ request for a national
database, but notes that a database that
contains information about releases of
radioactive material into sanitary sewers
by licensees is not being developed. As
discussed in Section 5.1 of the ISCORS
recommendations on management of
radioactive materials in sewage sludge
and ash (EPA 832–R–03–002B), POTW
operators are encouraged to contact the
applicable NRC Regional Office,
appropriate State Radiation Safety
Office, and any nearby DOE facilities if
they have questions about the sewer
releases of facilities in the POTW’s
service area that use radioactive
materials.
Comment: One commenter requested
that, because NRC had just begun to
study the fate of radionuclides in
POTWs and because NRC did not know
which of its licensees discharged
materials into sanitary sewers, a
moratorium be imposed on the disposal
of radioactive material into sanitary
sewers until NRC had the information
necessary to help POTWs develop
protective limits.
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Response: NRC notes that this
comment is beyond the scope of this
rulemaking.
Comment: One commenter expressed
concern that the assumptions used in 10
CFR part 20 ignored exposures to
children, fetuses, elderly, people with
existing body burdens of radioactive
material, and individuals in other
sensitive groups. The commenter
expressed concern that the risk of birth
defects from ionizing radiation had been
limited to only two generations in NRC
analyses and stated that the greatest
number of birth defects will be seen in
generations beyond the next two. The
commenter also expressed the view that
NRC should consider non-cancer and
nonfatal cancer health effects in risk
calculations and expressed concern that
these effects were not considered in the
promulgation of 10 CFR part 20.
Response: The commenter’s remarks
about NRC’s development of standards
for the protection against radiation are
beyond the scope of this rulemaking.
Comment: Three commenters
recommended NRC perform a cost/
benefit analysis of alternatives to the
release of radioactive materials into
sanitary sewers before proceeding with
a rulemaking and two of those
commenters expressed the view that the
proposed changes could not be justified
by either a risk analysis or cost/benefit
analysis. One commenter urged NRC to
apply the backfit provisions that apply
to power reactors to a broader scope of
rulemaking decisions, and expressed the
view that the alternatives suggested in
the ANPR could not be justified in a
backfit analysis.
Response: NRC is not performing a
cost/benefit analysis or risk analysis
because the ANPR is being withdrawn
for the reasons previously discussed.
The staff note that the commenter’s
opinions about NRC’s backfit provisions
are beyond the scope of this rulemaking.
Comment: One commenter expressed
the concern that limits based on overlysimplified dose models could be overlyrestrictive and could cause unintended
harm to the public by limiting beneficial
uses of radioactive materials. The
commenter suggested NRC consider the
‘‘total societal impact’’ of its release
limits, and expressed the view that NRC
and other regulatory agencies typically
perform inadequate assessments of the
financial impacts of their rules. The
commenter added that NRC should not
avoid this responsibility by claiming
that the AEA does not give it the
responsibility to evaluate the total
societal impact of its rules, because
evaluation of cost, benefit, and total
societal impact is inherently included in
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Sfmt 4702
the concept of maintaining doses
ALARA.
Response: NRC acknowledges the
commenter’s concern about the
adequacy of financial impact analyses
performed by NRC and other regulatory
agencies. NRC staff agree that, as
defined in 10 CFR 20.1003, the term
‘‘ALARA’’ indicates consideration of
societal and socioeconomic impacts.
Comment: Five commenters
expressed the opinion that, in general,
any changes to the regulations should
allow less radioactive material to be
released into sanitary sewers. Reasons
for this position included new
information about the adverse effects of
chronic exposure to low levels of
ionizing radiation, information about
the synergistic effects of radiation and
chemical pollutants, and concern about
the cumulative effects of multiple
sources of radiation on public health
and the environment. Two commenters
suggested that all radioactive waste
should be isolated in secure storage or
disposal facilities. Another commenter
stated that NRC should not allow
environmental build-up of multiple
sources of radiation even if each,
individually, could be dismissed as
being minimal. One commenter stated
that his organization had commented on
the revision of 10 CFR part 20
repeatedly and that it remains
concerned that the allowable
concentrations of many radionuclides in
air and water increase.
Response: The ANPR is being
withdrawn for the reasons previously
explained. Comments about the basis for
NRC’s standards for the protection
against radiation are beyond the scope
of this rulemaking.
Comment: Four commenters
expressed the opinion that the potential
burden that additional restrictions on
the release of radioactive material into
sanitary sewers would impose on
licensees is secondary to the primary
goal of protecting public health and
safety and should be given little weight
in the evaluation of whether additional
restrictions should be established. Two
commenters expressed concern that, in
the ANPR, NRC made several inquiries
about the impacts of new restrictions on
licensees without expressing a similar
interest in the potential impacts of the
release of radioactive material into
sanitary sewers on other parties. One of
the commenters expressed the view that
the concern for licensees may be
misplaced because it is municipalities,
and not licensees, that ultimately bear
the costs of disposal of contaminated
sludge and POTW decontamination.
The commenter also remarked that it
appeared to be more appropriate for
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licensees, rather than the public, to bear
the expense of the disposal of
radioactive materials used by licensees.
The other commenter suggested NRC
should have solicited comments
regarding the potential impact of the
regulations on public health, healthcare
costs, contamination of agricultural
land, restriction of land uses, and
environmental degradation. Two
commenters stated that it would be
inappropriate for NRC to allow any risk
to members of the public to lessen
economic or regulatory burden on
licensees. Another commenter noted
that, in cases in which contamination of
a POTW has been discovered, licensees
must recognize that safety of the
community is more important than the
desire for a licensee to use its current
disposal options.
Response: NRC acknowledges the
commenters’ concerns regarding the
specific requests for comment in the
ANPR. With regard to the consideration
given to the potential effects of changes
in the regulation on public health and
the environment as compared to
potential burdens on licensees, the NRC
staff notes that a significant effort was
made to study the potential effects of
the release of radioactive material into
sanitary sewers on the public and
POTW workers in conjunction with the
ISCORS reports that were described
previously. Comments about the basis
for NRC’s standards for the protection
against radiation are beyond the scope
of this rulemaking.
Comment: Six commenters suggested
that detection of radionuclides at a few
POTWs is an insufficient reason to
impose additional restrictions on the
release of radioactive material to
sanitary sewers. These commenters
stated that radioactivity can be
measured at very low levels that are not
expected to cause a significant adverse
health effect for any individual. One
commenter stated that lowering release
limits to values that are significantly
lower than limits needed to protect the
public makes it more difficult for
licensees to assure compliance of
medical research and clinical staff with
radiation safety procedures and
undermines the public’s confidence in
realistic exposure or activity standards.
Another commenter recommended NRC
acknowledge that the risks caused by
radioactivity in sewage sludge are small
compared to the risks associated with
the extra handling and transportation of
waste that would occur if releases of
radioactive material to sanitary sewers
were eliminated.
One commenter also suggested that,
because radioactivity can exist in sewer
systems and POTWs without causing a
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15:31 Nov 09, 2005
Jkt 208001
significant dose to any individual, and
because there are beneficial uses of
radioactive materials, that it might be
better to attempt to build public
acceptance of the current practices than
it would be to lower release limits or
eliminate sewer discharge. Another
commenter suggested incidents of
contamination should be handled in a
consistent, routine way without undue
alarm. A representative of DOE
predicted that any discovery of
radioactive contamination of sewage
pipes or sewage treatment plants is
likely to result in regulatory concern,
even if the possible doses are tiny,
because it may take time to determine
whether the contamination poses a
threat to public health and safety.
Response: NRC acknowledges the
commenters’ opinions, which support
the withdrawal of the ANPR. The staff
acknowledges the commenters’
recommendations about proper
treatment of cases of contamination, but
notes they are beyond the scope of this
rulemaking.
Comment: Three commenters
addressed the potential for accidental
releases of radioactive material into
sanitary sewers. One commenter
hypothesized that the case studies
presented in the ANPR may have been
the result of abnormal events and
expressed the opinion that no amount of
regulation, planning or notification can
prevent inadvertent releases that result
from system failures or other errors.
Another commenter suggested NRC
should realize that, irrespective of its
regulations, an individual is likely to
find a way to defeat ‘‘reasonable
safeguards.’’ Another commenter
expressed concern that the modeling
results described in the ANPR did not
account for the potential for accidental
releases in excess of the 10 CFR part 20
limits and suggested the reported
calculated doses may be underestimates.
Response: NRC acknowledges the
commenters’ statements about the
possibility of accidental releases. NRC
staff note that its inspections are
designed to ensure licensees’ operations
are conducted safely and in accordance
with good practices and license
conditions. With respect to the
commenter’s concern that the dose
modeling results discussed in the ANPR
do not include the effects of accidental
releases, NRC staff note that the doses
estimated in NUREG/CR–1548 did not
include the potential effects of
accidental releases; however, the doses
reported in the ISCORS dose modeling
report (NUREG–1783) were based on
observed levels of radioactivity
measured in conjunction with the
ISCORS sewage sludge survey (NUREG–
PO 00000
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Fmt 4702
Sfmt 4702
68367
1775) and, therefore, reflect any
accidental releases that may have been
made to the 313 POTWs surveyed.
Comment: Seven commenters
addressed LLW disposal. Four
commenters noted that additional
restrictions on the release of radioactive
materials to sewers would increase the
amount of low level radioactive waste
that would need to be disposed of in
some other way. Two commenters
recommended NRC evaluate the options
proposed in the ANPR in the context of
the risks associated with the disposal of
low level nuclear waste and the limited
capacity of LLW disposal facilities. Two
commenters noted that many licensees
had, as of 1994, very limited or no
access to LLW disposal facilities and
one of the commenters noted that
licensees without access to a LLW
disposal facility would need to store
waste on site indefinitely. Three
commenters noted that additional
restrictions on the release of radioactive
materials into sanitary sewers would be
especially burdensome because the
facilities they represented lacked access
to LLW disposal sites. One commenter
stated that sewer disposal is the primary
way that many medical research and
biotechnology laboratories minimize
generation of LLW.
One commenter expressed the
concern that the use of sanitary sewer
disposal of radioactive material would
increase because of the high cost and
limited availability of LLW disposal.
The commenter noted that the release of
radioactive material into sanitary sewers
itself can lead to the creation of large
volumes of LLW by contaminating
sludge. Another commenter opposed the
implication that sanitary sewer
disposals would be used as a means of
relief from the relative inaccessibility of
LLW disposal and noted that most types
of LLW do not meet the requirements
for release into sanitary sewers.
Response: NRC acknowledges the
commenters’ concerns regarding the
impact that the proposed changes would
have because of some licensees’ lack of
access to LLW disposal facilities. These
comments support the withdrawal of
the ANPR.
NRC also acknowledges the
commenter’s concern that limitations on
LLW disposal could lead to an increase
in the release of radioactive material to
sanitary sewers. The NRC staff notes
that the results of the ISCORS sewage
sludge survey (NUREG/CR–1775) do not
indicate that the frequency of POTW
contamination incidents has increased
since the commenters’ remarks were
made in 1994.
Comment: Five commenters
expressed the opinion that licensees
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Federal Register / Vol. 70, No. 217 / Thursday, November 10, 2005 / Proposed Rules
should bear all costs associated with
waste disposal. One commenter
suggested NRC’s descriptions of case
studies should include a description of
the financial costs associated with the
contamination and should indicate the
party paying the remediation costs. Two
commenters stated that NRC licensees
should bear the costs of data collection,
data reporting, and worker training
needed to implement any new NRC
studies or regulations needed to protect
POTWs from contamination. Two
commenters expressed the view that
licensees should pay to have monitoring
equipment installed at POTWs.
Response: NRC acknowledges the
commenter’s suggestion that NRC’s
descriptions of case studies should
include information about the economic
aspects of the contamination and notes
that some information about
remediation costs is provided in Section
1.2 of the ISCORS recommendations on
management of radioactive materials in
sewage sludge and ash (EPA 832–R–03–
002B). Comments regarding the costs
associated with implementation of new
sewer release restrictions are moot
because the ANPR is being withdrawn.
Comment: Six commenters expressed
opinions about NRC enforcement
actions. A representative of DOE stated
that it was unclear whether one or more
of the incidents described in the ANPR
involved violations of the regulations,
and suggested enhanced inspections,
and not additional rulemaking, would
be the most appropriate way to
eliminate contamination of POTWs.
Three commenters suggested NRC or
POTWs should verify licensee’s
reported discharges into sanitary sewers
and one commenter suggested
compliance with NRC regulations
should be demonstrated at the licensee’s
outfall into the sanitary sewer system so
that POTWs would not be impacted and
would not need to implement special
controls. Two representatives of POTWs
noted that POTWs routinely sample the
effluent of major industrial users as part
of their industrial pretreatment
programs. Another commenter
suggested NRC should assist POTWs
with monitoring of licensee’s effluents
and enforcement of the discharge limits.
Response: NRC notes that suggestions
about inspection and enforcement
activities are beyond the scope of this
rulemaking.
Comment: Six commenters made
specific suggestions about monitoring.
Two commenters suggested licensees’
outfalls and potable water intakes
should be monitored, and three
commenters suggested monitoring also
should occur at POTWs. One of the
commenters that advocated monitoring
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15:31 Nov 09, 2005
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at POTWs expressed the view that
monitoring would limit uncertainty in
model results and would facilitate the
study of the effects of influent
radionuclide form and quantity on
POTW worker doses. The commenter
also suggested licensees should be
encouraged to provide dosimetry and
elementary radiation safety training to
POTW workers. One commenter
expressed the opinion that
radionuclides in licensees’ effluents
should be monitored to record the
highest concentrations discharged and
facilitate a regulator’s ability to link
discharges with their sources. Three
commenters suggested the radioactivity
of sewage sludge should be monitored.
One commenter expressed concern
about the radioactivity of an engineered
wetland used to treat wastewater in his
town.
Response: Recommendations
regarding locations for monitoring a
licensee’s effluent are beyond the scope
of the proposed rulemaking.
Comment: A representative of the
New York State Department of
Environmental Conservation
recommended that the Notice of
Proposed Rulemaking for any change to
the regulation governing the release of
radioactive material into sanitary sewers
notice, for public comment, the
compatibility category NRC intends to
apply to each provision so that
Agreement States and other interested
parties can participate in decisions
about compatibility requirements. The
commenter stated that, as of 1994,
Agreement States were required to
develop regulations that were
compatible with the revised 10 CFR part
20 without NRC having determined
compatibility requirements and stated
that this type of situation must not
recur.
Response: NRC acknowledges the
commenter’s recommendation that
intended compatibility categories be
included in Notices of Proposed
Rulemaking. Compatibility categories
for the options discussed in the ANPR
are moot because the ANPR is being
withdrawn.
Comment: One commenter expressed
a number of concerns about the case
studies described in the ANPR.
Concerns raised by the commenter
included specific exposure pathways
that may not have been included in the
dose analyses, the appropriateness of
NRC’s comparison of doses with
background radiation, and the concern
that calculated doses to individuals
could have been higher if the sludge to
which they were exposed included
radiation from multiple sources. The
commenter expressed the view that
PO 00000
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Fmt 4702
Sfmt 4702
radioactivity in the environment may
increase because of human activity, and
that it would be inappropriate to
consider manmade contributions of
radioactivity to the environment in the
calculation of ‘‘background’’ radiation,
or to allow releases because they would
be minimal in comparison to
background radiation. The commenter
also remarked that the cases of
contamination that had occurred in
Washington, DC, and Cleveland, OH,
indicated the potential for
contamination to be significant to large
populations. In addition, the commenter
asked specific questions about the
assumptions used to calculate the doses
resulting from the case studies
discussed in the ANPR and what
sources of radiation NRC included in its
calculation of ‘‘background radiation.’’
Response: The commenter’s concerns
about the doses calculated in the case
studies are no longer applicable because
more recent studies served as the
technical basis for the withdrawal of the
ANPR. NRC acknowledges the
commenter’s concern regarding
contamination at POTWs. The
commenter’s specific questions about
the modeling assumptions used to
calculate doses for the case studies
discussed in the ANPR are addressed in
NUREG/CR–1548. NRC notes that its
definition of ‘‘background radiation,’’
provided in 10 CFR 20.1003, excludes
contributions of radioactivity from
source, byproduct, or special nuclear
materials regulated by NRC.
For the reasons cited in this document,
NRC withdraws this ANPR.
Dated at Rockville, Maryland, this 11th day
of October, 2005.
For the Nuclear Regulatory Commission.
Luis A. Reyes,
Executive Director for Operations.
[FR Doc. 05–22432 Filed 11–9–05; 8:45 am]
BILLING CODE 7590–01–P
SMALL BUSINESS ADMINISTRATION
13 CFR Part 121
RIN 3245–AF28
Small Business Size Standards;
Security Guards and Patrol Services
U.S. Small Business
Administration.
ACTION: Proposed rule.
AGENCY:
SUMMARY: The U.S. Small Business
Administration (SBA) proposes to
increase the size standard for the
Security Guards and Patrol Services
Industry (North American Industry
Classification System (NAICS) 561612)
E:\FR\FM\10NOP1.SGM
10NOP1
Agencies
[Federal Register Volume 70, Number 217 (Thursday, November 10, 2005)]
[Proposed Rules]
[Pages 68350-68368]
From the Federal Register Online via the Government Printing Office [www.gpo.gov]
[FR Doc No: 05-22432]
========================================================================
Proposed Rules
Federal Register
________________________________________________________________________
This section of the FEDERAL REGISTER contains notices to the public of
the proposed issuance of rules and regulations. The purpose of these
notices is to give interested persons an opportunity to participate in
the rule making prior to the adoption of the final rules.
========================================================================
Federal Register / Vol. 70, No. 217 / Thursday, November 10, 2005 /
Proposed Rules
[[Page 68350]]
NUCLEAR REGULATORY COMMISSION
10 CFR Part 20
[RIN 3150-AE90]
Disposal of Radioactive Material by Release Into Sanitary Sewer
Systems; Withdrawal of Advance Notice of Proposed Rulemaking
AGENCY: Nuclear Regulatory Commission.
ACTION: Advance notice of proposed rulemaking: Withdrawal.
-----------------------------------------------------------------------
SUMMARY: The Nuclear Regulatory Commission (NRC) is withdrawing an
advance notice of proposed rulemaking (ANPR) that presented possible
changes to the regulations governing the release of radionuclides from
licensed nuclear facilities into sanitary sewer systems. Changes were
proposed to account for the potential for radionuclide concentration
during some types of wastewater treatment processes. NRC is withdrawing
this advance notice of proposed rulemaking because it has determined
that there are no widespread public health and safety concerns due to
potential radiation exposures associated with the handling, beneficial
use, and disposal of sewage sludge containing radioactive materials.
This notice of withdrawal acknowledges public comments sent in response
to the ANPR.
FOR FURTHER INFORMATION CONTACT: A. Christianne Ridge, Office of
Nuclear Material Safety and Safeguards, U.S. Nuclear Regulatory
Commission, Washington, DC 20555-0001, telephone (301) 415-5673, e-mail
acr1@nrc.gov.
SUPPLEMENTARY INFORMATION: On February 25, 1994 (59 FR 9146), NRC
published an ANPR to seek information to determine whether an amendment
to its regulations governing the release of radionuclides from licensed
nuclear facilities into sanitary sewer systems was needed. NRC was
considering revising the approach to limiting these releases because of
the potential effects of newly-developed sewage treatment technologies
on radionuclide reconcentration during wastewater treatment. The
Commission requested advice and recommendations on several proposals
and asked related questions regarding whether and in what way the
regulations governing the release of radionuclides from licensed
nuclear facilities into sanitary sewer systems should be changed. NRC
received seventy-four comment letters in response to the ANPR. The
comment period expired on May 26, 1994.
Because there were concerns raised on the broader issue of long-
term effects of releases of radioactive materials into sanitary sewer
systems, action on the ANPR was deferred until studies were conducted
regarding potential radioactive contamination in sewage sludge. Since
that time, NRC participated in the Interagency Steering Committee of
Radiation Standards (ISCORS) and co-chaired, with the Environmental
Protection Agency (EPA), the Sewage Sludge Subcommittee to facilitate a
systematic and thorough study of the potential concerns related to
radionuclides in sewage sludge and to obtain data to support a
technical basis for a regulatory decision.
Regulatory Framework Relevant to the Release of Radioactive Material
Into Sanitary Sewers
NRC regulations governing the release of licensed material into
sanitary sewer systems can be found in 10 CFR 20.2003. This regulation
was published in the Federal Register (56 FR 23360; May 21, 1991) as
part of an overall revision of NRC standards for protection against
radiation. Licensees were required to implement this regulation by
January 1, 1993. As part of the 1991 revision of 10 CFR Part 20
regulations, NRC removed the broad provision that allowed the release
of non-biological insoluble materials into sanitary sewers because of
the potential for this material to reconcentrate in sewers, publicly
owned treatment works (POTWs), and sewage sludge. The current NRC
regulations require that any licensed material discharged into a
sanitary sewer system must be readily soluble in water or be readily
dispersible biological material. In addition, the concentration limits
for radionuclides released into a sanitary sewer system, listed in
Table 3 of the Appendix B to Part 20, were reduced by a factor of 10 as
part of an overall reduction in effluent release limits. In addition to
the limits in 10 CFR 20.2003, NRC recommends that licensees should
maintain doses as low as is reasonably achievable (ALARA) by setting
goals for effluent concentrations and quantities to be only a modest
fraction (10 to 20 percent) of their allowable limits, as described in
NRC Regulatory Guide 8.37, ``ALARA Levels for Effluents from Materials
Facilities,'' dated July 1993. NRC also conducts periodic inspections
to ensure that licensees are in compliance with NRC regulations.
Surveys, Studies, and Reports Relevant to the Release of Radioactive
Material Into Sanitary Sewers
In May 1992, NRC issued the results of a scoping study in NUREG/CR-
5814, ``Evaluation of Exposure Pathways to Man from Disposal of
Radioactive Materials into Sanitary Sewer Systems,'' which evaluated
the potential radiological doses to POTW workers and members of the
public from exposure to radionuclides in sewage sludge. The first part
of the analysis estimated the potential doses to workers for five cases
in which radioactive materials were detected at POTWs (Tonawanda, NY;
Grand Island, NY; Royersford, PA; Oak Ridge, TN; and Washington, DC).
Doses from the case studies were estimated to range from less than 10
microsieverts per year ([mu]Sv/yr) (1 millirem per year (mrem/yr)) to
930 [mu]Sv/yr (93 mrem/yr) for members of the public, using a
deterministic scenario analysis and the reported radionuclide
concentrations and/or discharges. The second part of the study
estimated the maximum radiation exposures to POTW workers and others
who could be affected by low levels of man-made radioactivity in
wastewater. The quantities of radionuclides released into the sewer
systems were assumed to be the maximum allowed under NRC regulations at
the time. Estimates of the hypothetical, maximum exposures to workers
ranged from zero to a dose roughly equal to the dose individuals
receive from natural background radiation.
In May 1994, the U.S. General Accounting Office (GAO, now U.S.
Government Accountability Office) issued a report, GAO/RCED-94-133,
[[Page 68351]]
``Nuclear Regulation: Action Needed to Control Radioactive
Contamination at Sewage Treatment Plants'', that described nine cases
where contamination was found in sewage sludge or ash or in wastewater
collection systems. GAO concluded that the full extent of contamination
nationwide was unknown. GAO also concluded that the ``problem of
radioactive contamination of sludge and ash in the reported cases was
the result, in large part, of NRC's regulation, which was incorrectly
based on the assumption that radioactive materials would flow through
treatment systems and not concentrate.'' In June 1994, a joint U.S.
House of Representatives and Senate hearing (June 21, 1994; S. Hrg.
103-1034) was held to officially release and address questions raised
in the GAO report. At the hearing, NRC and EPA agreed to cooperate to
develop guidance for POTWs and to collect more data on the
concentration of radioactive materials in samples of sewage sludge and
ash from POTWs nationwide.
Between 1994 and 1997, Federal, State, and industry studies were
conducted to assess reconcentration of radioactive materials that are
released into sanitary sewer systems. In December 1994, NRC published
NUREG/CR-6289, ``Reconcentration of Radioactive Material Released into
Sanitary Sewers in Accordance with 10 CFR Part 20.'' A review of the
literature demonstrated that some radioactive materials discharged into
sanitary sewer systems reconcentrate in sewage sludge. However, the
report concluded that the available data were not sufficient to assess
the adequacy of the requirements in 10 CFR 20.2003 in preventing
occurrences of radionuclide reconcentration in sewage sludge at levels
which present significant risk to the public; nor is the available data
sufficient to suggest strategies for changing the requirements.
In 1996, the Association of Metropolitan Sewerage Agencies (AMSA)
conducted a limited survey of reconcentration of radioactivity in
sewage sludge and ash samples from some of its member POTWs. Samples
were obtained from 55 wastewater treatment plants in 17 States. The
most significant sources of radioactivity were potassium and radium
isotopes, which are Naturally Occurring Radioactive Materials (NORM).
In December 1997, the Washington State Department of Health issued a
report WDOH/320-013, ``The Presence of Radionuclides in Sewage Sludge
and Their Effect on Human Health,'' that was based on sludge samples
taken at six POTWs in the State. The report concluded that that there
was no indication that radioactive material in sewage sludge in the
State of Washington poses a health risk.
The Interagency Steering Committee on Radiation Standards (ISCORS)
was formed in 1995, to address inconsistencies, gaps, and overlaps in
current radiation protection standards. In 1996, the Sewage Sludge
Subcommittee of ISCORS was formed to coordinate efforts to address the
recommendations in the 1994 GAO Report. Between 1998 and 2000, the EPA
and NRC (through the ISCORS) jointly conducted a voluntary survey of
POTW sewage sludge and ash to help assess the potential need for NRC
and/or EPA regulatory decisions. Sludge and ash samples were analyzed
from 313 POTWs, some of which had greater potential to receive releases
of radionuclides from NRC and Agreement State licensees, and some of
which were located in areas of the country with higher concentrations
of NORM. In November 2003, the results of the survey were published in
a final report, NUREG-1775, ``ISCORS Assessment of Radioactivity in
Sewage Sludge: Radiological Survey Results and Analysis.'' No
widespread or nationwide public health concern was identified by the
survey and no excessive concentrations of radioactivity were observed
in sludge or ash. The results indicated that the majority of samples
with elevated radioactivity had elevated concentrations of NORM, such
as radium, and did not have elevated concentrations of radionuclides
from manmade sources.
In February, 2005, the Sewage Sludge Subcommittee published a
report, NUREG-1783, ``ISCORS Assessment of Radioactivity in Sewage
Sludge: Modeling to Assess Radiation Doses.'' This report contains dose
modeling results for seven different sewage sludge management scenarios
for POTW workers and members of the public. Results of the dose models
and survey results indicated that there is no widespread concern to
public health and safety from potential radiation exposures associated
with the handling, beneficial use, and disposal of sewage sludge
containing radioactive materials, including NORM.
In February, 2005, the Sewage Sludge Subcommittee also published a
report, ``ISCORS Assessment of Radioactivity in Sewage Sludge:
Recommendations on Management of Radioactive Materials in Sewage Sludge
and Ash at Publicly Owned Treatment Works;'' (EPA 832-R-03-002B; ISCORS
Technical Report 2004-04). This report provides guidance to: (1) Alert
POTW operators, as well as State and Federal regulators, to the
possibility that radioactive materials may concentrate in sewage sludge
and incinerator ash; (2) inform POTW operators how to determine whether
there are elevated levels of radioactive materials in the POTW's sludge
or ash; and (3) assist POTW operators in identifying actions for
reducing potential radiation exposure from sewage and ash.
Reasons for Withdrawing the ANPR
The results of the survey and dose modeling work conducted by the
ISCORS Sewage Sludge Subcommittee regarding radioactive materials in
sewage sludge and ash provide a technical basis for withdrawing the
ANPR. The survey demonstrated that the most significant levels of
radioactive materials in POTWs are attributable to NORM. The dose
modeling work indicated that, in general, the doses from licensed
materials in sewage sludge present a sufficiently low health and safety
risk to POTW workers and to the public under the current regulatory
structure. Therefore, it is not necessary to modify the current
restrictions regarding the release of radioactive materials into
sanitary sewers (10 CFR 20.2003) as discussed in the ANPR. In addition,
public comments indicated that several of the options discussed in the
ANPR would be costly to implement and may not be consistent with
efforts to maintain doses ALARA. For these reasons, NRC is withdrawing
the ANPR.
Public Comments on the Potential Changes to 10 CFR Part 20
In the ANPR, NRC invited comment on the following aspects of the
regulation of release of radionuclides into sanitary sewers: The form
of materials suitable for disposal, the limits on the total
radioactivity of materials that can be released by a licensee into
sanitary sewers in a year, also called the ``total quantity limit,''
the types of limits applied, and the exemption for medical patient
excreta. The following is a summary of those comments and NRC
responses.
(1) Form of Material for Disposal
The May 21, 1991, final rule (10 CFR 20.2003) allows soluble and
readily dispersible biological material to be released but prohibits
the release of any non-biological insoluble material. Because NRC
recognized that new technologies for wastewater treatment, such as ion-
exchange and some types of biological treatment, can reconcentrate
radionuclides, NRC invited comments regarding whether and how
regulations should account for the effects of different wastewater
treatment
[[Page 68352]]
technologies on radionuclide reconcentration. NRC also invited comments
regarding the potential impacts that additional restrictions on the
form of materials allowable for release into sanitary sewers would have
on licensee operations. Public comments regarding the adequacy of the
current restrictions also were received.
Comment: Nine commenters, including representatives of the New York
State Energy Office, New York State Department of Environmental
Conservation, AMSA, and the Department of Energy (DOE), expressed the
view that the regulations should be reevaluated because of new sewage
treatment technologies or should account for the effects of new
technologies used to treat sewage or sewage sludge. One commenter
suggested that NRC limits should account for a variety of POTW-specific
factors, including sludge handling processes, and sludge disposal
methods, and restrictions on the POTW's treated water discharge.
Another commenter suggested NRC should take new sewage treatment
technologies into account only if the results of NUREG/CR-6289, which
was incomplete at the time the comment was made, indicated that new
sewage treatment technologies had the potential to cause significant
reconcentration of radionuclides in sewage sludge. Two commenters
recommended NRC develop technology-specific reconcentration factors to
help POTW operators to design appropriate pretreatment plans. A
representative of DOE suggested NRC should expect that advances in the
sewage treatment process would result in increasing concentration of
radionuclides in sewage sludge. Two commenters recommended NRC
regulations account for synergistic health effects of radiation and
pollutants in wastewater, and one suggested NRC evaluate the
synergistic effects of radiation and the chlorine and fluoride used in
drinking water treatment.
Response: NRC acknowledges the commenters' support for regulations
that would account for the reconcentration of radionuclides by
wastewater treatment processes. However, the regulations will not be
changed because the ANPR is being withdrawn for the reasons previously
explained.
Comment: Four commenters expressed the view that NRC regulations
should not take sewage treatment technologies into account. Reasons
included uncertainty that new technologies will be implemented and a
lack of information about the effects of the new technologies on
radionuclide reconcentration. A representative of the State of Illinois
Department of Nuclear Safety suggested NRC should keep informed of
technological developments, but should not implement additional
restrictions without significant evidence that the current restrictions
are not adequate. Two commenters suggested that, rather than revising
Sec. 20.2003 to account for new treatment technologies, NRC should
consider placing additional restrictions on individual licensees to
provide the necessary protection to the receiving POTWs in unusual
cases where the number of licensees, size of the sewage treatment plant
or nature of the technology used at the treatment plant may cause doses
above 100 mrem/yr. One commenter stated that it is unnecessary for NRC
regulations to account for sewage sludge treatment technologies because
local POTWs have the authority and mandate to account for these
technologies by developing industrial water discharge permits pursuant
to 40 CFR 403.5(c)(1).
Response: NRC acknowledges the commenters' opposition to the
proposed rule change, which supports NRC's decision to withdraw the
ANPR. With respect to the comment that POTWs have the authority and
mandate to impose limits on radioactive materials released into
sanitary sewers, NRC notes that, as described in Section 4.7 of the
ISCORS recommendations on management of radioactive materials in sewage
sludge and ash (EPA 832-R-03-002B), POTWs may not have the same
authority to regulate radioactive material as they do to regulate other
materials released into sanitary sewers.
Comment: Eight commenters expressed the view that NRC regulations
should account for the fact that several licensees may discharge to the
same POTW, and, of those, five expressed the view that the regulations
should also take the capacity of the POTW into account. Five commenters
stated that restrictions on the release of nonradioactive pollutants
established under EPA's National Pollutant Discharge Elimination System
(NPDES) account for the capacity of the receiving POTW, the wastewater
treatment systems used, and the number of industrial users discharging
to a POTW, and suggested any new regulations governing the release of
radioactive materials into sanitary sewers should take these factors
into account. A representative of DOE expressed the view that changes
to the regulations to account for multiple dischargers should be
considered but may not be necessary because sanitary systems serving
multiple licensees would probably be large systems in which the
licensees' effluent would be diluted by many other inputs to the sewer
system. One commenter suggested that, if limits on the total amount of
radioactivity individual POTWs could receive were developed, any cases
in which the limits are being exceeded by licensees that were already
discharging sewage into the sewer system before the limits were
developed should be handled on a case-by-case basis.
Response: NRC acknowledges the commenters' support for regulations
that would account for the capacity of individual POTWs and the number
of licensees discharging to a single POTW. However, the proposed change
will not be implemented for the reasons previously explained.
Comment: Twenty-seven commenters were opposed to additional
restrictions on the forms of material suitable for release into
sanitary sewers. Twenty-one stated that the potential for significant
reconcentration of radionuclides during wastewater treatment probably
had been addressed by the May 21, 1991 changes to Part 20 (56 FR 23360)
that restricted the forms of materials that could be released into
sanitary sewers and lowered concentration limits. Another commenter
expressed the view that it was unclear whether contamination described
in the case studies discussed in the ANPR occurred because of
violations of the existing regulations, and also that it would be
inappropriate for NRC to respond to individual violations of regulatory
requirements by making changes to the regulations for all licensees.
Representatives of six licensees indicated that additional restrictions
on the forms of material appropriate for disposal would impose a
significant burden on their operations. Commenters listed the costs of
building new storage facilities, analyzing samples of waste to
determine whether insoluble radionuclides were present, and
establishing new collection, handling, and disposal procedures as well
as retraining of personnel as expenses that would be incurred if
additional restrictions were imposed. In addition, three commenters
expressed the concern that further restricting the forms of material
appropriate for disposal in a sanitary sewer would not be consistent
with NRC's policy that doses should be maintained ALARA because the
additional waste handling that would be required would cause doses to
workers that would not be justified based on the minimal dose to
members of the public or POTW workers that might be avoided.
Response: NRC acknowledges the commenters' remarks, which support
[[Page 68353]]
the withdrawal of the ANPR. However, the NRC staff notes the need to
analyze samples of waste to determine if the waste contains insoluble
radionuclides should not impose an additional burden because the
restriction on releasing insoluble, non-biological wastes was already
in place when the comment was made.
Comment: Twenty-three commenters encouraged NRC to continue to
allow release of readily soluble wastes that met the quantity and
concentration release criteria in 10 CFR Part 20. Twenty-one of those
commenters indicated that they were unaware of any significant problems
caused by the disposal of soluble radioactive material in sewer
systems. Three commenters stated that they were not aware of any
mechanisms that would reconcentrate the wastes typical of biomedical
research in sewage sludge, and two of these stated that the activity
levels were sufficiently low that reconcentration, even if it did
occur, would not cause a significant dose.
Response: NRC acknowledges the commenters' support for the
continuation of the current regulations which allow certain
concentration and quantities of readily soluble radioactive material
into sanitary sewers.
Comment: Two commenters suggested that NRC should change the
regulation to re-establish disposal of dispersible non-biological
materials. One commenter suggested disposal of non-biological
dispersible materials should be allowed for materials that have half-
lives of less than 100 days or are below the concentrations listed in
10 CFR Part 20 Appendix C.
Response: NRC acknowledges the commenters' suggestion that release
of non-biological dispersible material into sanitary sewers be allowed.
NRC understands that reconcentration of a radionuclide in sewage sludge
can be limited by its half life. However, NRC has chosen not to change
the regulation governing the release of radioactive material into
sanitary sewers for the reasons previously explained.
Comment: Six commenters, including a representative of DOE, noted
that the chemical form of materials released into the sewer can change,
and that materials that are soluble when released may precipitate or
sorb to solid particles in the sewer or treatment plant. A
representative of the New York State Department of Environmental
Conservation suggested NRC study not only the effect of new
technologies on radionuclide solubilities, but also how the solubility
of radioactive materials change in sanitary sewers. A representative of
DOE noted that precipitation and sorption could cause risks to
individuals who work in POTWs, work in close contact with sewers, or
who incinerate or use wastewater treatment sludge. In addition, the
commenter remarked that, while it appeared to be reasonable to limit
sewer releases to soluble and dispersible biological materials, NRC
should realize that licensees could release insoluble or nondispersible
materials to sewer systems inadvertently. One commenter expressed the
view that NRC regulations should account not only for the form of
material when released, but the form it was likely to take after being
discharged.
Three commenters expressed the view that, because the form of a
material discharged is likely to change when it reaches the sewer or
POTW, the modification to 10 CFR 20 that eliminated disposal for non-
biological ``readily-dispersible'' materials may not have removed the
chance that radionuclides could reconcentrate in wastewater treatment
sludge. Two commenters remarked that reconcentration of radionuclides
probably would continue, in part because POTWs are designed to remove
dissolved contaminants from wastewater. However, both commenters
expressed the opinion that reconcentration is not necessarily a problem
if the dose any individual is expected to receive from exposure to
sewers, sewage, or sludge is low.
Response: NRC understands that materials that are released into the
sewer in a soluble form can precipitate or sorb to solid materials in
sewers or POTWs, as discussed in NUREG/CR-6289. Most of the commenters'
concerns about the potential risk to POTW workers are addressed in the
ISCORS dose modeling report (NUREG-1783), as previously explained.
Although the ISCORS dose analysis (NUREG-1783) does not include an
analysis of doses to workers that come into contact with sewers, those
doses are expected to be limited because of the limited amount of time
a worker would spend in close contact with a sewer and because of the
relatively low doses predicted for most scenarios that involve contact
with sewage sludge.
NRC acknowledges the concern that licensees may inadvertently
dispose of insoluble non-biological material. NRC also acknowledges the
suggestion that the regulations should account for changes in the form
of materials that are likely to occur in sewers and POTWs and the
concern about the efficacy of the 1991 revisions. For the reasons
previously explained, NRC has decided not to change the regulations
governing the release of radioactive material into sanitary sewers.
However, NRC staff notes that, in addition to restrictions on form, NRC
also has imposed annual limits in 10 CFR 20.2003(a)(4) on the total
amount of radioactivity that can be released into sanitary sewers to
limit the potential for reconcentration of radioactive material in
sanitary sewers, sewage sludge, and sludge ash.
Comment: Five commenters supported additional restrictions on the
form of materials that can be released into sanitary sewers. One
commenter expressed the view that the practice, used by some medical
research laboratories, of releasing pureed tissue samples to the
sanitary sewer was distasteful. Another commenter expressed the opinion
that NRC should impose any requirement that would minimize the amount
of radioactivity in the environment.
Response: NRC acknowledges the commenters' support for additional
restrictions on the forms of material suitable for release into
sanitary sewers but is not changing the regulations because it believes
the current approach is sufficiently protective, as previously
explained.
Comment: Three commenters requested clarification regarding the
distinction between soluble and readily dispersible materials. One
requested that an information notice be produced to address materials
used in the biotech industry. Another commenter expressed the concern
that it would be difficult to demonstrate compliance with the
restriction that only soluble and readily-dispersible biological
materials be released into sanitary sewers if colloids that flow
through filters and resins are classified as non-biological dispersible
material. The commenter proposed an operational procedure to
distinguish between soluble and readily dispersible materials. A
representative of the New York State Department of Environmental
Conservation noted that traces of insoluble radioactive material could
be released into sewers with soluble materials, and requested that NRC
establish a lower limit of detection for insoluble material.
Response: NRC acknowledges the commenters' request for additional
guidance on how licensees should demonstrate the solubility of
radioactive material released to sanitary sewers. Although NRC does not
have plans to provide additional guidance on this issue, the staff
notes that, as discussed in NRC Information Notice 94-007, licensees
are free to develop alternative methods of demonstrating the solubility
of materials they wish to release into sanitary sewers and to submit
these
[[Page 68354]]
procedures to NRC for evaluation on a case-by-case basis.
(2) Total Quantity of Material
In the May 21, 1991 final rule, NRC did not change the total
quantity limits, which allow a licensee to release 185 gigabecquerel
(GBq) (5 curies (Ci)) of H-3, 37 GBq (1 Ci) of C-14, and 37 GBq (1Ci)
of all other radioactive materials combined into sanitary sewers each
year. The use of total quantity limits has been a long-standing
requirement and was originally included in the rule (10 CFR
20.2003(a)(4)) to address concerns regarding the possibility for
reconcentration of radionuclides. In the ANPR, NRC invited comments
about the alternative approach of limiting the annual release of each
radionuclide individually. NRC also invited comments about the current
total quantity limits and the potential impacts that additional
restrictions on the annual releases into sanitary sewers would have on
licensees.
Prior to publishing the ANPR, NRC received a petition for
rulemaking to amend 10 CFR 20.303 (superseded by Sec. 20.2003) and
Sec. 20.305 (superseded by Sec. 20.2004) from the Northeast Ohio
Regional Sewer District (PRM-20-22). A notice of receipt of the
petition was published in the Federal Register (58 FR 54071; October
20, 1993). The petitioner requested that NRC amend its regulations to
require that all licensees provide at least 24 hours advance notice to
the appropriate POTW before releasing radioactive material to the
sanitary sewer system. The petitioner also requested that NRC exempt
materials that enter the sanitary waste stream from the requirements
regarding Commission approval for incineration under NRC's current
regulations. NRC solicited comments on the petition in the ANPR. The
denial of the petition was noticed in the Federal Register on January
27, 2005 (70 FR 3898).
Comment: Six comments received in response to the ANPR supported
annual total quantity limits. Two commenters, including a
representative of DOE, suggested total quantity limits should be
retained because they help prevent reconcentration of radionuclides in
sewage sludge and two supported the total quantity limits because they
are easy for licensees and regulators to understand and implement. Two
commenters, including the representative of DOE, suggested it may be
worthwhile for NRC to evaluate whether the regulation could be
optimized by changing the annual release limits for some radionuclides.
A representative of the Illinois Department of Nuclear Safety expressed
the opinion that the relatively low doses calculated for the case
studies described in the ANPR and predicted for other scenarios in
NUREG/CR-5814 indicated that reconcentration of radionuclides in sewage
sludge could be addressed on a case-by-case basis rather than by
changing the total quantity limits in Sec. 20.2003.
Response: NRC acknowledges support for the current approach of
using annual limits on the total quantity of radioactive material that
can be released into sanitary sewers by a licensee. In accord with the
commenters' suggestion, NRC performed a study to evaluate the
reconcentration of various radiounuclides in POTWs, the results of
which are discussed in NUREG/CR-6289.
Comment: A representative of the City of Oak Ridge made positive
and negative statements about NRC annual total quantity limits. The
commenter stated that both concentration and total quantity limits were
necessary to ensure protection of workers and to ensure that
traditional methods of sludge disposal remain acceptable. However, the
commenter also expressed the view that the current values of the total
quantity limits are too high and stated that disposal of 37 GBq (1 Ci)
of Co-60 annually to the Oak Ridge POTW would result in unacceptably
high concentrations of Co-60 in the POTW's sludge, especially if the
material was released during a relatively short time period. The
commenter also expressed the opinion that the total quantity limits are
inappropriate for low specific activity radionuclides because of the
large mass of the radionuclide that could be discharged. As an example,
the commenter stated that release of 37 GBq (1 Ci) of U-238 to the
city's POTW in a year would result in a mass concentration of uranium
of more than 0.05 percent in the POTW's sludge, making the sludge
licensable source material. In addition to these comments, the
commenter suggested that, because the mean retention time of sludge at
a POTW typically is one month or less, a monthly discharge limit would
be more appropriate than an annual limit.
Response: NRC acknowledges the commenter's concern about the
release of Co-60 to a POTW and the suggestion that quantity limits
should be implemented on a monthly, rather than an annual, basis. The
staff notes that the 1991 revision to 10 CFR Part 20 that eliminated
the discharge of insoluble non-dispersible radioactive material into
sanitary sewers was implemented to reduce the possibility of
significant contamination of sewage sludge with insoluble
radionuclides, such as Co-60. NRC has decided not to change the
regulations governing sewer release of radioactive material for the
reasons previously explained. NRC acknowledges the commenter's concern
about the applicability of the total quantity limit to low specific
activity radionuclides. However, NRC does not agree that the
accumulation of large masses of low-specific activity radionuclides in
POTWs is likely to be problematic. In addition POTWs have some
authority to impose limits on the release of material into sanitary
sewers when the purpose of the limits is not radiation protection, as
discussed in Section 4.7 of the ISCORS recommendations on management of
radioactive materials in sewage sludge and ash (EPA 832-R-03-002B).
Comment: Twenty-three commenters described concerns about the
current approach of limiting the total amount of radioactivity a
licensee may release into a sanitary sewer system. Nineteen commenters
expressed the opinion that it is not appropriate to apply the same
total quantity limit to large and small facilities that discharge
different amounts of sewage and therefore dilute radioactive materials
to different extents. Another commenter stated that NRC should not
attempt to impose total quantity limits on large facilities. Seventeen
commenters expressed the view that NRC should consider relaxing the
total quantity limits because of the new restriction on the form of
material and lower release concentration limits implemented in the 1991
revision to 10 CFR Part 20. The commenters expressed the opinion that
adherence to the new form and concentration limits may eliminate the
need for total quantity limits. Three commenters suggested that,
instead of limiting the total quantity of radioactivity a licensee
could dispose of into a sewer, NRC should focus on the radionuclides
and chemical forms of radionuclides that reconcentrate in POTWs to a
significant extent. One commenter expressed the concern that a person
could dispose of 37 GBq (1 Ci) of Cs-137 within a month while remaining
in compliance with the current concentration and total quantity limits.
Another commenter suggested concentration limits are sufficient and are
superior to total quantity limits because concentration limits account
for the total volume of water a licensee releases to the sanitary sewer
system. The commenter noted that, although the nominal purpose of the
total quantity limits is to eliminate reconcentration, the total
quantity limits do not appear to prevent reconcentration, as evidenced
by the case studies described in the
[[Page 68355]]
ANPR. The commenter suggested reconcentration could be avoided by
reducing the allowable concentrations of those radionuclides that have
shown a tendency to reconcentrate in sewage sludge.
Response: NRC acknowledges the comment about the application of the
same total quantity limit to large and small facilities, but believes
that the system is appropriate. Because the total quantity limit is
designed to reduce the potential for reconcentration of radionuclides
at POTWs, an appropriate total quantity limit is more dependent on the
volume of sewage received by a POTW than it is on the volume of a
licensee's effluent.
NRC acknowledges the comment that total quantity limits should be
relaxed or eliminated, but does not agree that the limits on form and
concentration eliminate the need for annual quantity limits. As
discussed in NUREG/CR-6289, the form of radionuclides can change upon
entering a sewer or POTW because of sorption and precipitation. NRC
also acknowledges the concern that total quantity limits did not
prevent the cases of contamination discussed in the ANPR. NRC believes
that limiting both the form and total quantity of material released
into sanitary sewers is the best way to limit the potential for
significant reconcentration of radionuclides released by licensees into
sanitary sewers.
NRC acknowledges the commenters' suggestion that, instead of
imposing total quantity limits, it should focus on those radionuclides
that have been shown to reconcentrate in sewers or sewage sludge. NRC
also acknowledges the commenter's concern about the discharge of Cs-137
but believes the current approach to be sufficiently protective for the
reasons previously explained.
Comment: One commenter expressed the view that additional
limitations on the release of H-3 and C-14 into sanitary sewers would
not produce any public health benefit because any dose an individual
received from sewer-disposed H-3 and C-14 would be negligible in
comparison to the dose the individual would receive from naturally-
produced H-3 and C-14.
Response: NRC acknowledges the commenter's view that additional
restrictions on the quantities of H-3 and C-14 are unnecessary. The
comment supports the withdrawal of the ANPR and the current total
quantity limits which allow the annual release of 185 GBq (5 Ci) of H-3
and 37 GBq (1 Ci) of C-14 in addition to the release of 37 GBq (1 Ci)
of all other radionuclides combined.
Comment: Eight licensees expressed the view that additional
restrictions on the total quantity of radioactive material that could
be released into sanitary sewers annually would have a severe negative
impact on their facilities' operations. Representatives of a biomedical
company, a university, and the National Institutes of Health (NIH)
noted that a reduction in the total quantity limits would impose a
significant financial burden on organizations involved in biotechnical
research, development, or medical practice, especially if the limits
were reduced to a point that liquid wastes would need to be solidified
and disposed of as low level waste (LLW). The representative of NIH
estimated that solidification and disposal of liquid wastes as LLW
would cost NIH 2.8 million dollars annually, as of 1994. Two commenters
remarked that companies would bear the additional expense of acquiring
or building storage facilities or acquiring treatment technologies to
remove radioactivity from liquid waste streams. One commenter noted
that LLW disposal of many of the materials currently released into
sanitary sewer systems would be a particularly unnecessary expense and
inefficient use of LLW landfill space because, in many cases, the
material would decay to negligible quantities before it reached the LLW
landfill.
Five commenters associated with medical research facilities or
companies that produce radiopharmaceuticals suggested additional
restrictions on the total quantity of radioactive material that could
be released into sanitary sewers annually could harm public health and
safety by causing companies to limit biomedical research and
development efforts. One of these commenters stated that the amount of
radioactivity released into sanitary sewers in association with medical
research was insignificant as compared to the amount of radioactivity
released to sewers in patient excreta and concluded that release of
radioactive materials associated with biomedical research should be
allowed as long as the exemption for patient excreta is continued. Two
commenters expressed the opinion that additional restrictions on the
total quantity of radioactivity a licensee could release into sanitary
sewers annually would not be consistent with efforts to maintain doses
ALARA because workers would be exposed to radioactive material while
processing liquid waste to make it suitable for LLW disposal.
A representative of a company that offers health physics services
stated that, for most of its clients who want to release radioactive
material into sanitary sewers, the most limiting factor is the annual
total quantity limits. A representative of the University of California
expressed concern that the numerical limits in 10 CFR 20.2003 would be
lowered, although the university typically releases only 11.1 Gbq (0.2
Ci) of radioactivity into sanitary sewers each year.
Response: NRC acknowledges the commenter's concerns about the
potential impacts of additional restrictions on the total quantity of
radioactive material that a licensee can release to sewers annually. As
previously explained, the additional restrictions discussed in the ANPR
will not be implemented.
Comment: A representative of AMSA stated that, although the
organization understands that lowering total quantity limits could
impose financial burdens on licensees, additional restrictions are
appropriate if they are needed to prevent contamination of sewage
sludge.
Response: NRC acknowledges the commenter's statement, but has
decided not to change the total quantity limits because it believes the
current approach is sufficiently protective for the reasons previously
explained.
Comment: Twenty-one letters received in response to the ANPR
included comments on the Northeast Ohio Regional Sewer District's
request for NRC to amend its regulations to require that all licensees
provide at least 24 hours advance notice to the appropriate POTW before
releasing radioactive material into a sanitary sewer system. Six of the
twenty-one commenters supported a requirement for licensees to provide
the sewage treatment plant with some type of reporting on the
radioactive materials released into the sanitary sewer system. These
commenters supported a wide range of reporting requirements, including
the petitioner's request for a 24-hour advance notification before
licensees release radioactive material, monthly or annual discharge
reports, reports of releases that could be a threat to the POTW workers
or the environment, or notification of large accidental releases. One
commenter suggested licensees should analyze effluent samples and
include the results in discharge reports. A representative of AMSA
stated that advance notice of releases is necessary so that POTW
operators can ensure worker health and safety and make appropriate
decisions about sludge disposal and reuse.
Fifteen of the twenty-one commenters did not support such a
requirement for licensees to provide at least 24-hour
[[Page 68356]]
advance notice to the appropriate sewage treatment plant before
releasing radioactive material into a sanitary sewer system. Several
commenters said that a 24-hour advance notification would result in an
unnecessary regulatory burden without providing additional protection
against radiation or dose reduction. These commenters expressed the
view that the existing regulations for discharges of licensed material
maintain doses at or below the existing dose limits for members of the
public and if licensees meet the ALARA goals, the 24-hour advance
notification would be unnecessary. Several commenters noted that such
notification would be impractical because most releases are continuous
and involve very small quantities of radioactive material. For example,
discharges from hospitals and medical facilities would change daily
depending on the number of patients treated and types of treatment
used.
Several commenters also noted that there could be large cost
implications and regulatory burdens associated with such notification.
In addition, commenters were concerned that data about releases of
radioactive material could be misinterpreted if release reports were
received and interpreted by sewage treatment plant personnel rather
than radiation safety specialists. Several commenters stated that such
an NRC requirement for licensees to provide a 24-hour advance
notification was unnecessary because local municipalities have
authority over their local sewer district, already have requirements to
follow the Clean Water Act, and may establish a pretreatment program
for wastewater acceptance. One commenter noted that the usefulness of a
24-hour advance notification should be assessed after the new limits
for sewer discharges are in place.
Response: NRC has determined that a requirement for advance
notification of each release of radioactive material to a sanitary
sewer would impose an unnecessary regulatory burden on licensees
without a commensurate health and safety benefit. Additional reasons
for the denial of the petition are discussed in the Federal Register
notice published on January 27, 2005 (70 FR 3898).
Comment: Six comment letters received in response to the ANPR
included comments on the Northeast Ohio Regional Sewer District's
request that NRC exempt materials that enter the sanitary waste stream
from the requirement for NRC approval prior to treatment or disposal of
licensed material by incineration. Four commenters supported such an
amendment because, given the radioisotopes and activities involved, the
pathways for human exposure from radioactive wastes seem no more or
less significant if the wastes are dispersed into water or air. These
commenters suggested that, if release into a sanitary sewer system is
to be considered disposal, the limits should be set so that no further
regulation of the radioactive material is needed after release. One
commenter did not support such an amendment and expressed the view that
it would only serve to provide an open-ended system for radioactive
material to pass into the environment and to the public without
limitation or characterization.
Response: NRC approval to incinerating waste is required to ensure
that NRC may evaluate the potential impact to the public health and
safety and the environment on a case-by-case and site-specific basis.
Hazards associated with incineration of sewage sludge will depend on
the specific characteristic of the sludge and the radionuclides that
may be present. Additional reasons for the denial of the petition are
discussed in the Federal Register notice published on January 27, 2005
(70 FR 3898).
(3) Type of Limits
The present approach to limiting releases of radioactive material
into sanitary sewers is to specify limits on both the monthly average
concentration of each radionuclide in a licensee's sewage and the total
quantity of radioactive matter that a licensee can release annually.
Table 3, Appendix B, of 10 CFR Part 20 lists the allowable monthly
average concentration of each radionuclide in a licensee's release to
sewers. Allowable concentrations are based upon a calculated dose of 5
mSv/yr (500 mrem/yr) due to ingestion of 2 liters per day of a
licensee's effluent into the sanitary sewer.
In the ANPR, NRC invited comments on this regulatory approach.
Specifically, NRC invited comment as to whether it should continue to
base concentration limits on the assumption that an individual would
drink 2 liters of the effluent from a licensee's facility each day, and
whether exposure at other locations, such as at a POTW, should be
considered in developing release limits. In addition, NRC invited
comments about how other exposure scenarios, such as exposure to
radionuclides in contaminated sludge, should be accounted for. NRC also
invited comments as to whether it should establish limits in terms of
dose instead of limits on the quantity and concentrations of
radioactive material discharged. Included with the responses to these
inquiries were several comments about monitoring, enforcement actions,
and regulatory authority to set limits on releases of radioactive
material into sanitary sewers that have been addressed with the General
Comments.
Comment: Twenty-three commenters supported the current modeling
approach of assuming that an individual ingests 2 liters of water taken
from the licensee's outfall to the sewer system each day. Nineteen of
these commenters, representing hospitals, biomedical laboratories, and
universities, noted that this assumption is conservative and easy for
licensees to understand. A representative of DOE noted that the
approach appears to be bounding, and has been ``largely successful as a
regulatory measure''. The commenter also expressed the view that,
because this type of consumption is not expected to be chronic, it is
appropriate to base concentration limits on a calculated annual dose of
500 mrem instead of 100 mrem. One commenter did not specifically
address the assumption that an individual would drink 2 liters of a
licensee's discharge each day, but did support the use of a licensee's
sewer outfall as an appropriate exposure location. Two commenters
expressed the view that the modeling assumption was appropriate because
individuals, including children, could drink or otherwise be exposed to
water directly downstream of a sewer outfall. Another commenter that
supported the current assumption expressed the view that modeling
exposure at a licensee's outfall to a sewer system is consistent with
modeling exposure at a licensee's fence line, as is done in other NRC
assessments, and that considering a downstream location would be
inconsistent with modeling exposure to the maximally exposed
individual.
Response: NRC acknowledges support for the current modeling
assumption. The staff notes that several commenters appeared to believe
that the concentration limits were based on the assumption that an
individual would consume 2 liters of sewage from a POTW outfall, rather
than 2 liters of a licensee's effluent into the sewer system, each day.
Staff notes that the assumption that an individual would consume a
licensee's effluent is more conservative than the assumption that an
individual would consume POTW effluent because the concentration of
radionuclides in POTW effluent will have been diluted with effluent
from all of the other residential and industrial dischargers to the
POTW.
[[Page 68357]]
Comment: Three commenters expressed concern that the concentration
limits are based on an annual dose of 5 mSv (500 mrem) and stated that
the concentration limits should be based on an annual dose of no more
than 1 mSv (100 mrem), in accord with the 10 CFR 20.1301 limit on doses
to members of the general public from licensed activities. One
commenter expressed the view that the 1 mSv (100 mrem) annual public
dose limit should be lowered. Two commenters expressed the view that
the dose from ingesting a licensee's effluent should be included in the
1 mSv (100 mrem) TEDE annual public dose limit rather than being
calculated separately and excluded from the 10 CFR 20.1301 limit.
Another expressed the view that, if any activity were to be permitted
to be discharged into sanitary sewers, the limiting dose for exposure
to sewage sludge should be no greater than the dose limit for low level
radioactive waste.
Response: NRC acknowledges the commenters' concern about the
hypothetical dose used as the basis for the concentration limits. As
discussed in the ANPR, the NRC staff believes the concentration limits
based on an annual dose of 5 mSv (500 mrem) are reasonable because it
is unlikely that an individual would have access to and would consume
water at the point at which a licensee discharges water into the
sanitary sewer and because dilution from additional discharges into the
sewer is likely to reduce the expected dose to well below the 1 mSv
(100 mrem) annual dose limit.
NRC also acknowledges the commenters' suggestion that the dose from
consuming effluent released into the sanitary sewer be included in the
TEDE from other licensee operations. However, in the case of sewer
discharge, the point of exposure is expected to be remote from the
licensee's facility. Because individuals that could be exposed to a
facility's effluent are different individuals than those that live
closest to the facility, it would be unrealistic to include the dose
from exposure to a licensed facility's effluent in the total dose from
all of the facility's activities. The staff notes that comments
regarding the appropriate value of the annual dose limit for members of
the public from licensed activities specified in 10 CFR 20.1301 are
beyond the scope of this rulemaking.
Comment: Ten commenters did not support the use of the current
modeling approach of assuming that an individual ingests 2 liters of
water taken from a licensee's sewer outfall each day. Almost all of
these commenters expressed the view that the assumption is unrealistic.
One commenter expressed the view that, while the assumption that an
individual ingests 2 liters of water taken from a licensee's sewer
outfall each day is a reasonably conservative basis for concentration
limits, the assumption may not be a basis for total quantity limits
because it would over-emphasize the potential impact of short-lived
radionuclides.
Response: NRC acknowledges the commenters' opposition to the
current modeling approach. However, it will be retained because the
ANPR is being withdrawn for the reasons previously explained. With
respect to the comment about the basis for total quantity limits, the
staff notes that the assumption that an individual would consume a
licensee's effluent is used as the basis of the concentration limits
but is not used as the basis of the total quantity limits.
Comment: Ten commenters suggested alternate locations that NRC
should consider when developing restrictions on the release radioactive
materials into sanitary sewer systems. Of these, five suggested NRC
consider the dose to a person ingesting water once it has reached or is
leaving a POTW rather than at the licensee's sewer outfall. Three
commenters suggested NRC consider locations downstream of a POTW that
would be likely to be locations from which a municipality would extract
drinking water, while one suggested doses in the nearest residential
area should be considered. Another commenter suggested realistic models
would incorporate a factor of at least one million between the point of
discharge and a receptor locations, and suggested that, if NRC used a
more realistic dose model, it would become clear that additional
release restrictions are unnecessary. One commenter suggested that, in
considering potential doses to members of the public, NRC should
consider that sludge could be sent to a landfill, applied to
agricultural land, or made into compost for sale to the public.
Five commenters, including representatives of POTWs and DOE,
recommended NRC consider doses to sanitation workers and two commenters
suggested NRC consider doses to workers that come into contact with
sewage collection systems as well as POTW workers. One commenter noted
the importance of matching exposure locations to appropriate pathways
and suggested external radiation by gamma emitters may be an important
pathway for POTW workers, whereas ingestion of beta emitters would be
expected to be more important at a downstream drinking water source.
Five commenters suggested NRC consider that the careful treatment given
to sewage and sludge because of the other hazards it presents should
limit doses to sanitary system workers. One commenter added that NRC
regulations also should prevent contamination of sewers, POTWs,
receiving waters, and sludge and ash disposal sites. Another commenter
suggested NRC consider potential exposures to all POTW residuals,
including sludge, screenings, grit, and ash. The commenter also pointed
out that sewer pipes may leak and suggested NRC consider the potential
for groundwater contamination.
Response: The alternate locations that the commenters suggested
should be considered in dose models will not be used as a basis for a
revision to the regulations because the ANPR is being withdrawn for the
reasons previously explained. However, the NRC staff notes that several
of the modeling scenarios suggested by the commenters, including sludge
handling by POTW workers, sludge incineration, and exposure to land-
applied sewage sludge, were considered in the ISCORS dose modeling
project (NUREG-1783).
Comment: Six commenters, including representatives of POTWs and the
New York State Department of Environmental Conservation, suggested
that, in addition to protecting the general public and sanitation
workers, NRC regulations should ensure that POTWs can continue to use
traditional forms of use or disposal of biosolids (sewage sludge). One
commenter noted that events that have not resulted in significant
worker exposure have prevented POTWs from using or disposing of sewage
sludge.
Response: Additional restrictions on the release of radioactive
material into sanitary sewers will not be implemented for the reasons
previously discussed. Section 7.2 of the ISCORS recommendations on
management of radioactive materials in sewage sludge and ash (EPA 832-
R-03-002B) provides guidance to assist POTW operators in reducing
sources of radiation entering their treatment facilities.
Comment: Four commenters made suggestions about ways to account for
complex exposure scenarios, such as exposure to contaminated sewage
sludge. One commenter suggested that a variety of scenarios should be
evaluated and that the scenario resulting in the highest dose should be
used to establish limits on releases of radionuclides to sewers.
Another commenter expressed the opinion that dose models should reflect
limitations on access that are imposed to protect individuals from
other health risks associated with sewage and sewage sludge. One
[[Page 68358]]
commenter suggested no model could adequately represent complex
exposure scenarios because dose modeling was not sufficiently well
developed.
Response: The approaches the commenters suggested will not be used
as a basis for new restrictions on the release of radioactive material
into sanitary sewers because the ANPR is being withdrawn for the
reasons previously explained. NRC staff acknowledge the commenter's
statement about the capabilities of dose modeling.
Comment: Of the fourteen commenters that addressed dose limits,
seven supported implementation of dose limits. One commenter expressed
the view that dose limits are preferable to limits on concentration and
quantity alone because dose limits are easier to relate to risk. The
commenter suggested the assumptions used to evaluate compliance with
dose limits should be realistic. The commenter also suggested the use
of a tiered approach, in which simple bounding assumptions are first
used to evaluate compliance, and more complex models and more site-
specific data are used only if the simple bounding model does not
demonstrate compliance. Another commenter suggested that, if the
appropriate models were developed, releases into sanitary sewers should
be controlled under the requirements of 10 CFR 20.1302 and ALARA
guidelines just as other facility effluents are. The commenter also
noted that the potential doses calculated in NUREG/CR-5814 indicate
that the current regulations governing the release of radionuclides
into sanitary sewers are more restrictive than other NRC dose limits on
facility effluents. Two commenters expressed the view that dose limits
should be adopted only if the current limits were found not to be
protective of the public or POTW workers. Four commenters agreed with
the proposal in the ANPR that, if dose limits were adopted, NRC should
publish a regulatory guide that included concentration and total
quantity guidelines to facilitate compliance. One commenter asked if
licensees would have a choice of complying with the dose limit or with
the concentration and quantity guidelines published in a Regulatory
Guide. Two commenters advocated dose limits, but expressed the view
that the dose limits should be based on measured radionuclide
concentrations from samples taken from sewer outfalls and intakes or on
readings from dosimeters placed at POTWs rather than on concentrations
calculated based on assumptions about releases to and dilution in
sanitary sewers.
Response: NRC acknowledges the commenters' support for sewer
release restrictions to be expressed as limits on dose rather than
activity. NRC also acknowledges the commenters' suggestion that
compliance with dose limits be made based on sample measurements.
However, these options will not be implemented because the ANPR is
being withdrawn for the reasons previously explained. No response is
required to the commenter's question about compliance with dose limits
because the ANPR is being withdrawn.
Comment: Of the fourteen commenters that addressed dose limits, six
commenters opposed dose limits, and a representative of the New York
State Department of Environmental Conservation noted potential problems
with implementing dose limits but suggested NRC study the option.
Almost all of the commenters that opposed dose limits commented on the
uncertainty of assumptions about exposure pathways and the relative
complexity of implementing dose limits as compared to concentration and
quantity limits. Three commenters predicted dose limits would require
more regulatory oversight because NRC would need to review each
licensee's dose model. One commenter expressed the concern that dose
limits could make it necessary for licensees to require prior approval
for releases of radioactive material into sanitary sewers. One
commenter supported the current limits but suggested that, if dose
limits were adopted, the dose limit should be 500 mrem/yr, realistic
modeling assumptions should be made, and the modeling assumptions to be
used in compliance calculations should be clearly defined. Another
commenter advocated the use of limits expressed in ``verifiable units
of measure'' rather than limits expressed as dose and expressed doubts
about the capabilities of computer models used to calculate dose.
Another commenter stated NRC should not limit the dose a patient could
receive from a prescribed medical procedure.
Response: NRC acknowledges the commenters' opposition to dose
limits, which will not be implemented because the ANPR is being
withdrawn.
With respect to the commenter's concern that NRC should not limit
the dose a patient could receive due to a medical procedure prescribed
by his physician, the NRC staff notes the scope of the ANPR was limited
to potential doses due to exposure to radioactive material in sewage or
sludge. In general, NRC regulates the uses of radionuclides in medicine
as necessary to provide for the radiation safety of