Drinking Water Contaminant Candidate List 4-Final, 81099-81114 [2016-27667]
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Federal Register / Vol. 81, No. 222 / Thursday, November 17, 2016 / Notices
Center, Environmental Protection
Agency, Mail Code 28221T, 1200
Pennsylvania Ave. NW., Washington,
DC 20460; and (2) OMB via email to
oira_submission@omb.eop.gov. Address
comments to OMB Desk Officer for EPA.
EPA’s policy is that all comments
received will be included in the public
docket without change, including any
personal information provided, unless
the comment includes profanity, threats,
information claimed to be Confidential
Business Information (CBI), or other
information whose disclosure is
restricted by statute.
FOR FURTHER INFORMATION CONTACT:
Patrick Yellin, Monitoring, Assistance,
and Media Programs Division, Office of
Compliance, Mail Code 2227A,
Environmental Protection Agency, 1200
Pennsylvania Ave. NW., Washington,
DC 20460; telephone number: (202)
564–2970; fax number: (202) 564–0050;
email address: yellin.patrick@epa.gov.
SUPPLEMENTARY INFORMATION:
Supporting documents which explain in
detail the information that the EPA will
be collecting are available in the public
docket for this ICR. The docket can be
viewed online at www.regulations.gov
or in person at the EPA Docket Center,
WJC West, Room 3334, 1301
Constitution Ave. NW., Washington,
DC. The telephone number for the
Docket Center is 202–566–1744. For
additional information about EPA’s
public docket, visit: https://
www.epa.gov/dockets.
Abstract: Owners and operators of
affected facilities are required to comply
with reporting and record keeping
requirements for the General Provisions
(40 CFR part 60, subpart A), as well as
for the specific requirements at 40 CFR
part 60, subpart SSS. This includes
submitting initial notification reports,
performance tests and periodic reports
and results, and maintaining records of
the occurrence and duration of any
startup, shutdown, or malfunction in
the operation of an affected facility, or
any period during which the monitoring
system is inoperative. These reports are
used by EPA to determine compliance
with these standards.
Form Numbers: None.
Respondents/affected entities:
Magnetic tape coating facilities
constructed or modified after January
22, 1986.
Respondent’s obligation to respond:
Mandatory (40 CFR part 60, subpart
SSS).
Estimated number of respondents: 6
(total).
Frequency of response: Initially,
quarterly and semiannually.
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Total estimated burden: 2,030 hours
(per year). Burden is defined at 5 CFR
1320.3(b).
Total estimated cost: $295,000 (per
year), includes which $86,400 in
annualized capital/startup and
operation & maintenance costs.
Changes in the Estimates: There is an
adjustment increase in the respondent
labor hours as currently identified in the
OMB Inventory of Approved Burdens.
This increase is not due to any program
changes. Instead, the change in labor
hour and cost estimates occurred
because of a change in assumption. This
ICR assumes all existing sources will
have to re-familiarize with the
regulatory requirements each year.
Courtney Kerwin,
Director, Regulatory Support Division.
[FR Doc. 2016–27576 Filed 11–16–16; 8:45 am]
BILLING CODE 6560–50–P
ENVIRONMENTAL PROTECTION
AGENCY
[EPA–HQ–OW–2012–0217; FRL–9955–27–
OW]
Drinking Water Contaminant Candidate
List 4—Final
Environmental Protection
Agency (EPA).
ACTION: Notice.
AGENCY:
The U.S. Environmental
Protection Agency (EPA) is publishing a
final list of contaminants that are
currently not subject to any proposed or
promulgated national primary drinking
water regulation. These contaminants
are known or anticipated to occur in
public water systems and may require
regulation under the Safe Drinking
Water Act (SDWA). This list is the
Fourth Contaminant Candidate List
(CCL 4) published by EPA since the
SDWA amendments of 1996. This Final
CCL 4 includes 97 chemicals or
chemical groups and 12 microbial
contaminants.
FOR FURTHER INFORMATION CONTACT: For
information on chemical contaminants
contact Meredith Russell, Office of
Ground Water and Drinking Water,
Standards and Risk Management
Division, at (202) 564–0814 or email
russell.meredith@epa.gov. For
information on microbial contaminants
contact Hannah Holsinger, Office of
Ground Water and Drinking Water,
Standards and Risk Management
Division, at (202) 564–0403 or email
holsinger.hannah@epa.gov. For general
information contact the EPA Safe
Drinking Water Hotline at (800) 426–
4791. The Safe Drinking Water Hotline
SUMMARY:
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81099
is open Monday through Friday,
excluding legal holidays, from 10 a.m.
to 4 p.m. eastern time.
Abbreviations and Acronyms
CASRN—Chemical Abstract Services
Registry Number
CCL—Contaminant Candidate List
CCL 1—EPA’s First Contaminant Candidate
List
CCL 2—EPA’s Second Contaminant
Candidate List
CCL 3—EPA’s Third Contaminant Candidate
List
CCL 4—EPA’s Fourth Contaminant
Candidate List
CFR—Code of Federal Regulations
CIS—Contaminant Information Sheet
DWC—Drinking Water Committee
EPA—United States Environmental
Protection Agency
ESA—Ethanesulfonic acid
FR—Federal Register
HPC—Heterotrophic Plate Count
HRL—Health Reference Level
MCL—Maximum Contaminant Level
MCLG—Maximum Contaminant Level Goal
MRL— Minimum Reporting Level
NAWQA—National Water-Quality
Assessment
NDEA—N-Nitrosodiethylamine
NDMA—N-nitrosodimethylamine
NDPA—N-Nitroso-di-n-propylamine
NDPhA—N-Nitrosodiphenylamine
NDWAC—National Drinking Water Advisory
Council
NIRS—National Inorganics and
Radionuclides Survey
NRC—National Academy of Science’s
National Research Council
NPDWR—National Primary Drinking Water
Regulation
NPYR—N-nitrosopyrrolidine
PCCL 4—Preliminary Contaminant Candidate
List 4
PFOA—Perfluorooctanoic Acid
PFOS—Perfluorooctane Sulfonic Acid
PWS—Public Water System
RD—Regulatory Determination
RD 1—Regulatory Determination 1
RD 2—Regulatory Determination 2
RD 3—Regulatory Determination 3
SAB—Science Advisory Board
SDWA—Safe Drinking Water Act
SS—Screening Survey
TRI—Toxics Release Inventory
UCMR 1—First Unregulated Contaminant
Monitoring Rule
UCMR 2—Second Unregulated Contaminant
Monitoring Rule
UCMR 3—Third Unregulated Contaminant
Monitoring Rule
USGS—United States Geological Survey
WBDO—Waterborne Disease Outbreaks
SUPPLEMENTARY INFORMATION:
Table of Contents
I. General Information
A. Does this action apply to me?
B. How can I get copies of this document
and other related information?
1. Docket
2. Electronic Access
C. What is the purpose of this action?
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D. Statutory Requirements for CCL,
Regulatory Determination and
Unregulated Contaminant Monitoring
1. Interrelationship of the CCL, Regulatory
Determination and Unregulated
Contaminant Monitoring
2. Contaminant Candidate List
3. Unregulated Contaminant Monitoring
4. Regulatory Determinations
E. Where can I find information on
previous CCLs and Regulatory
Determinations?
1. Summary of Previous CCLs and
Regulatory Determinations
2. Summary of the CCL 3
3. Summary of the Regulatory
Determination 3
II. What is on EPA’s Drinking Water
Contaminant Candidate List 4?
The Final CCL 4 and a Cross-Walk of
Contaminants Between the CCL 4,
Regulatory Determination 3, and UCMRs
III. Summary of the Approach Used To
Identify and Evaluate Candidates for the
Draft CCL 4
A. Carry Forward of CCL 3 Contaminants
B. Summary and Evaluation of CCL 4
nominated contaminants
1. CCL 4 Nominations Summary
2. How Nominated Contaminants Were
Evaluated for the Draft CCL 4
C. Evaluation of Previous Negative
Regulatory Determinations
IV. What comments did EPA receive on the
Draft CCL 4 and how did the Agency
respond?
A. Recommendations From the EPA
Science Advisory Board
B. Public Comments
1. General Comments on CCL 4
2. Chemical Contaminants
a. Contaminants With Release Data
b. Cyanotoxins
c. Perfluorinated Compounds (PFOA and
PFOS)
d. Pesticides
e. Manganese
f. Nonylphenol
3. Microbial Contaminants
a. Overall Process Comments
b. Pathogens for Inclusion
c. Pathogens for Exclusion
V. Data Needs for CCL 4 Contaminants
Categorization of Contaminants
A. Health Effects
B. Occurrence
C. Analytical Methods
VI. Next Steps and Future Contaminant
Candidate Lists
VII. References
I. General Information
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A. Does this action apply to me?
The Final CCL 4 will not impose any
requirements on anyone. Instead, this
action notifies interested parties of the
EPA’s Final CCL 4 of unregulated
drinking water contaminants and
provides a summary of the major
comments received on the February 4,
2015, Draft CCL 4 Federal Register
notice and EPA’s responses (80 FR 6076
(USEPA, 2015a)).
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B. How can I get copies of this document includes three components, the CCL, the
Unregulated Contaminant Monitoring
and other related information?
Rule (UCMR), and RD. In preparing the
1. Docket
CCL, EPA screens and evaluates
EPA has established a docket for this
unregulated contaminants to identify
action under Docket ID No. EPA–HQ–
those that may require future drinking
OW–2012–0217. Although listed in the
water regulations. Inclusion on the CCL
index, some information is not publicly does not mean that any particular
available, e.g., CBI or other information
contaminant will necessarily be
whose disclosure is restricted by statute. regulated in the future. The UCMR
Certain other material, such as
provides a mechanism to obtain
copyrighted material, will be publicly
nationally representative occurrence
available only in hard copy. Publicly
data for unregulated contaminants. The
available docket materials are available
data provided by UCMR is one of the
either electronically through
primary sources of occurrence
www.regulations.gov or in hard copy at
information used to evaluate
the Water Docket, EPA/DC, EPA West,
contaminants in the RD process.
Room 3334, 1301 Constitution Ave.
Under the RD process, EPA evaluates
NW., Washington, DC 20004. The Public UCMR and other occurrence data along
Reading Room is open from 8:30 a.m. to with health effects data for
4:30 p.m., Monday through Friday,
contaminants on the CCL to see which
excluding legal holidays. The telephone ones present the greatest public health
number for the Public Reading Room is
concern and have sufficient information
(202) 566–1744, and the telephone
for the agency to make a regulatory
number for the EPA Docket Center is
determination. EPA must make
(202) 566–2426.
regulatory determinations for at least
five contaminants listed on the CCL
2. Electronic Access
every five years. Today’s action
You may access this Federal Register
addresses only the CCL 4 and not the
document electronically from the
UCMR or RD stages of the SDWA
Government Publishing Office under the contaminant regulatory development
Federal Register listings at FDsys
process.
(https://www.gpo.gov/fdsys/browse/
2. Contaminant Candidate List
collection.action?collectionCode=FR).
Section 1412(b)(1) of the SDWA, as
C. What is the purpose of this action?
amended in 1996, requires EPA to
The Safe Drinking Water Act (SDWA), publish the CCL every five years. The
as amended in 1996, requires EPA to
SDWA specifies that the list must
publish a list every five years of
include contaminants that are not
currently unregulated contaminants that subject to any proposed or promulgated
may pose risks for drinking water
NPDWRs, are known or anticipated to
(referred to as the Contaminant
occur in public water systems (PWSs),
Candidate List, or CCL). This list is
and may require regulation under the
subsequently used to make regulatory
SDWA. The unregulated contaminants
determinations on whether or not to
considered for listing shall include, but
regulate at least five contaminants from
not be limited to, hazardous substances
the CCL with national primary drinking identified in section 101(14) of the
water regulations (NPDWRs) ((SDWA
Comprehensive Environmental
section 1412(b)(1)). The purpose of
Response, Compensation, and Liability
today’s action is to present EPA’s final
Act of 1980, and substances registered
list of contaminants on the CCL 4, a
as pesticides under the Federal
summary of the major public comments Insecticide, Fungicide, and Rodenticide
received on the Draft CCL 4 and EPA’s
Act.
responses. Today’s action only
The SDWA directs the agency to
addresses the Final CCL 4. Regulatory
consider the health effects and
Determination (RD) for contaminants on occurrence information for unregulated
the CCL is a separate agency action.
contaminants to identify those
contaminants that present the greatest
D. Statutory Requirements for CCL,
public health concern related to
Regulatory Determination and
exposure from drinking water. The
Unregulated Contaminant Monitoring
statute further directs the agency to take
1. Interrelationship of the CCL,
into consideration the effect of
Regulatory Determination and
contaminants upon subgroups that
Unregulated Contaminant Monitoring
comprise a meaningful portion of the
general population (such as infants,
Under the 1996 amendments to
children, pregnant women, the elderly
SDWA, Congress established a riskand individuals with a history of serious
based approach for determining which
illness or other subpopulations) that are
contaminants would become subject to
drinking water standards. The approach identifiable as being at greater risk of
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adverse health effects due to exposure to
contaminants in drinking water than the
general population. Additionally, EPA’s
1995 Policy on Evaluating Health Risks
to Children states that the agency will
consider the risks to infants and
children consistently and explicitly as a
part of risk assessments generated
during its decision-making process,
including the setting of standards to
protect public health (USEPA, 1995a).
EPA considers age-related subgroups as
‘‘lifestages’’ in reference to a
distinguishable time frame in an
individual’s life, characterized by
unique and relatively stable behavioral
and/or physiological characteristics that
are associated with development and
growth. Thus, childhood is viewed as a
sequence of lifestages, from conception
through fetal development, infancy and
adolescence (see https://www.epa.gov/
children/early-life-stages).
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3. Unregulated Contaminant Monitoring
Section 1445(a)(2) of the SDWA
mandates that EPA promulgate
regulations (known as the Unregulated
Contaminant Monitoring Rule or UCMR)
to establish criteria for a monitoring
program for unregulated contaminants.
This section, as amended in 1996,
requires that once every five years, EPA
issue a list of no more than 30
unregulated contaminants to be
monitored by PWSs. SDWA requires
that EPA enter the monitoring data into
the agency’s publicly available National
Contaminant Occurrence Database.
EPA’s UCMR program must ensure that
systems serving a population larger than
10,000 people, as well as a nationally
representative sample of PWSs serving
10,000 or fewer people, are required to
monitor.
4. Regulatory Determination
Section 1412(b)(1)(B)(ii) of the SDWA,
as amended in 1996, requires EPA at
five year intervals, to make
determinations of whether or not to
regulate no fewer than five
contaminants from the CCL. EPA
evaluates the CCL contaminants with
sufficient health effects and occurrence
information to determine whether a
regulation is required or not required.
The 1996 SDWA Amendments specify
three criteria to determine whether a
contaminant may require regulation:
• The contaminant may have an
adverse effect on the health of persons;
• the contaminant is known to occur
or there is a substantial likelihood that
the contaminant will occur in PWSs
with a frequency and at levels of public
health concern; and
• in the sole judgment of the
Administrator, regulation of such
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contaminant presents a meaningful
opportunity for health risk reduction for
persons served by PWSs.
If EPA determines that these three
statutory criteria are met and makes a
final determination to regulate a
contaminant, the agency has 24 months
to publish a proposed maximum
contaminant level goal 1 (MCLG) and
NPDWR.2 After the proposal, the agency
has 18 months to publish and
promulgate a final MCLG and NPDWR
(SDWA section 1412(b)(1)(E)).3 For
those contaminants without sufficient
information to allow the agency to make
a regulatory determination, EPA
encourages research to provide the
information needed to determine
whether to regulate the contaminant.
E. Where can I find information on
previous CCLs, UCMRs, and Regulatory
Determinations
1. Summary of previous CCLs, UCMRs,
and Regulatory Determinations
A brief summary of CCL 1, CCL 2,
Regulatory Determination 1 (RD 1) and
Regulatory Determination 2 (RD 2) was
published in the Federal Register for
the Draft CCL 4 notice (80 FR 6076,
February 4, 2015 (USEPA, 2015a)).
Information on previous UCMRs, can be
found at the following Web site: https://
www.epa.gov/dwucmr.
2. Summary of the CCL 3
The CCL 3 included 104 chemicals or
chemical groups and 12 microbiological
contaminants. In developing the CCL 3,
EPA implemented an improved process
from the process used for CCL 1 and
CCL 2. This new process built on
evaluations used for previous CCLs and
was based on substantial expert input
and recommendations from the National
Academy of Sciences’ National Research
Council (NRC) and the National
Drinking Water Advisory Council
(NDWAC). EPA used a multi-step CCL
process to identify contaminants for
inclusion on the Final CCL 3. The key
steps included:
1 The MCLG is the ‘‘maximum level of a
contaminant in drinking water at which no known
or anticipated adverse effect on the health of
persons would occur, and which allows an
adequate margin of safety. MCLGs are nonenforceable health goals.’’ (40 CFR 141.2; 42 U.S.C.
300g–1)
2 An NPDWR is a legally enforceable standard
that applies to public water systems. An NPDWR
sets a legal limit (called a maximum contaminant
level or MCL) or specifies a certain treatment
technique for public water systems for a specific
contaminant or group of contaminants. The MCL is
the highest level of a contaminant that is allowed
in drinking water and is set as close to the MCLG
as feasible, using the best available treatment
technology and taking cost into consideration.
3 The statute authorizes a nine month extension
of this promulgation date.
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• Identifying a broad universe of
potential drinking water contaminants
(called the CCL 3 Universe). EPA
initially considered approximately
7,500 potential chemical and microbial
contaminants (more information on the
identification of the CCL 3 Universe can
be found in USEPA, 2009a and USEPA,
2009b).
• Applying screening criteria to the
universe, EPA identified almost 600 of
those contaminants that should be
further evaluated (the preliminary CCL
or PCCL) based on a contaminant’s
potential to occur in PWSs and the
potential for public health concern
(more information on the CCL 3
screening process can be found in
USEPA, 2009c and USEPA, 2009d).
• Selecting the final list of 116
contaminants from the PCCL to include
on the CCL based on more detailed
evaluation of occurrence and health
effects and expert judgment as well as
public input (this step of the CCL 3
process is called the classification
process and more information can be
found in USEPA, 2009e and USEPA,
2009f).
The CCL 3 interpreted the criterion
that contaminants are known or
anticipated to occur in public water
systems broadly. In evaluating this
criterion, EPA considered not only
public water system monitoring data,
but also data on concentrations in
ambient surface and ground waters,
releases to the environment (e.g., Toxics
Release Inventory (TRI)), and
production. While such data may not
establish conclusively that
contaminants are known to occur in
public water systems, EPA believes
these data are sufficient to anticipate
that contaminants may occur in public
water systems and support their
inclusion on the CCL. The agency
considered adverse health effects that
may pose a greater risk to life stages and
other sensitive groups which represent
a meaningful portion of the population.
Adverse health effects associated with
infants, children, pregnant women, the
elderly, and individuals with a history
of serious illness were evaluated as part
of the screening and classification
processes. A detailed summary of the
CCL 3 process can be found in the Draft
CCL 3 (73 FR 9628, February 21, 2008
(USEPA, 2008a) and Final CCL 3 (74 FR
51850, October 8, 2009 (USEPA, 2009a))
Federal Register notices.
3. Summary of the Regulatory
Determination 3
EPA published the Announcement of
Final Regulatory Determinations for
Contaminants on CCL 3 in the Federal
Register on January 4, 2016 (81 FR 13
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(USEPA, 2016a)). The agency made final
determinations not to regulate four
contaminants: 1, 3-dinitrobenzene;
dimethoate; terbufos; and terbufos
sulfone. The agency delayed the final
regulatory determination for strontium
in order to consider additional data and
decide whether there is a meaningful
opportunity for health risk reduction by
regulating strontium in drinking water.
These five contaminants are not
included on the Final CCL 4.
This section provides an overview of
the process used for the Third
Regulatory Determination (RD 3). A
summary of the process can be found in
the Federal Register notice announcing
the preliminary regulatory
determinations (79 FR 62716, October
24, 2014 (USEPA, 2014a)), and a
detailed explanation of this process can
be found in the ‘‘Protocol for the
Regulatory Determination 3’’ support
document (USEPA, 2014b). This
overview of the RD process is provided
to give an understanding of how
contaminants have previously been
evaluated after they have been listed on
past CCLs. The RD 4 process may
continue to follow this process although
it is possible that some modifications
may be made to this process. The RD
process occurs subsequent to a Final
CCL, and is a separate agency action.
The RD 3 process, was divided into
three phases: (1) The Data Availability
Phase, (2) the Data Evaluation Phase and
(3) the Regulatory Determination
Assessment Phase.
The purpose of the first phase, the
Data Availability Phase, was to
determine if the agency may have
sufficient data to characterize the
potential health effects and known or
likely occurrence in drinking water.
With regard to sufficient health effects
data used to identify potential adverse
health effect(s), the agency considered
whether a peer reviewed health risk
assessment was available or in process
from an EPA or a comparable non-EPA
source. In regard to sufficient
occurrence data, the agency considered
the availability of nationally
representative finished water data and
whether other finished water data were
available that indicated known and/or
likely occurrence in PWSs. After
conducting the health and occurrence
data availability assessments, the agency
identified those contaminants and
contaminant groups that meet the
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following Phase 1 data availability
criteria:
(a) A peer reviewed health assessment
is available or in process, and
(b) A widely available analytical
method for monitoring exists, and
(c) Either nationally representative
finished water occurrence data are
available, or other finished water
occurrence data shows occurrence at
levels greater than one-half of the CCL
3 health reference level (HRL).
If a contaminant met these three
criteria, it was placed on a ‘‘short list’’
and proceeded to Phase 2. From the 116
CCL 3 contaminants, the agency
identified a short list of 37 contaminants
(35 CCL 3 contaminants and two nonCCL 3 contaminants 4) to further
evaluate in the second phase.
During the second phase, the Data
Evaluation Phase, the agency further
evaluated each of the 37 contaminants
on the short list to identify those that
had sufficient data (or were expected to
have sufficient data) for EPA to assess
the three statutory criteria listed in
section I.D.4 of this notice.
To identify the contaminants that
present the greatest public health
concern, the agency specifically focused
its efforts on identifying those
contaminants or contaminant groups
that are occurring or have substantial
likelihood to occur at levels and
frequencies of public health concern,
based on the best available peer
reviewed data. In addition to health and
occurrence information data assessed in
Phase 1, the agency collected additional
health and occurrence data and more
thoroughly evaluated this information to
identify a list of contaminants that
should proceed to Phase 3. If the agency
found that sufficient data were not
available or not likely to be available to
evaluate the three statutory criteria
during the first and second phases, then
the contaminant was not considered a
candidate for making a regulatory
determination during the current cycle,
and the agency will conduct research,
collect information or find other
avenues to fill the data and information
gaps. For these contaminants, additional
data that becomes available in the future
4 The non-CCL 3 contaminants, N-Nitroso-di-nbutylamine (NDBA) and NNitrosomethylethylamine (NMEA), were included
because they are part of a larger group
(nitrosamines) that also includes a number of CCL
3 contaminants.
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may be considered for future CCLs and
RDs.
If sufficient data were available for a
contaminant to characterize the
potential health effects and known or
likely occurrence in drinking water, the
contaminant was evaluated against the
three statutory criteria (listed in section
I.D.4) in the third phase of the process,
the Regulatory Determination
Assessment Phase.
II. What is on EPA’s Drinking Water
Contaminant Candidate List 4?
The Final CCL 4 and a Cross-Walk of
Contaminants Between the CCL 4,
Regulatory Determination 3, and
UCMRs
The Final CCL 4 includes 97
chemicals or chemical groups and 12
microbes listed in Exhibit 1. Exhibit 1
also shows chemical abstract service
registry numbers (CASRNs) of the
contaminants on the Final CCL 4 and
their status across other EPA programs
related to CCL (i.e., RD and UCMR). The
list of contaminants is presented by
CASRN when available, common name,
or by aggregate groupings (e.g.,
cyanotoxins). Further data and
information for the contaminants
included on the CCL 4 are available in
the technical support documents and
Contaminant Information Sheets
available on EPA’s CCL 4 Web site and
in the docket for this action (EPA–HQ–
OW–2012–0217). All contaminants
listed on the Final CCL 4 were also
included on CCL 3, with the exception
of manganese and nonylphenol, which
were nominated by the public and
added to the CCL 4. Twenty-eight CCL
4 chemicals that were carried forward
from CCL 3 had been further analyzed
and evaluated under the RD 3 process
and included on the RD 3 Short List
(further described in section I.E.3. of
this notice). The RD 3 process also
included an evaluation of occurrence
data from the UCMR 2 for 13 CCL 4
chemicals. Twenty-one CCL 4
contaminants were monitored under
UCMR 3 (19 chemicals and 2 microbes).
The UCMR data will be used to further
evaluate CCL 4 contaminants during the
RD 4 process. In addition, EPA has
proposed gathering occurrence data for
16 individual CCL 4 chemicals and
several cyanotoxins, including anatoxina, cylindrospermopsin, nodularin, total
microcystin and several microcystin
congeners under the proposed UCMR 4.
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81103
EXHIBIT 1—CONTAMINANTS ON THE FINAL CCL 4, REGULATORY DETERMINATION 3, UCMR 2, UCMR 3 AND PROPOSED
UCMR 4
Chemical or chemical group
CCL 4
nomination
RD 3 short list
UCMR 2
UCMR 3
Proposed
UCMR 4 a
630–20–6 ......
75–34–3 ........
96–18–4 ........
106–99–0 ......
123–91–1 ......
57–91–0 ........
71–36–3 ........
109–86–4 ......
107–18–6 ......
16655–82–6 ..
101–77–9 ......
30560–19–1 ..
75–07–0 ........
60–35–5 ........
34256–82–1 ..
187022–11–3
194992–44–4
107–02–8 ......
142363–53–9
171262–17–2
319–84–6 ......
62–53–3 ........
741–58–2 ......
100–44–7 ......
25013–16–5 ..
133–06–2 ......
14866–68–3 ..
74–87–3 ........
110429–62–4
7440–48–4 ....
80–15–9 ........
N/A ................
141–66–2 ......
55290–64–7 ..
330–54–1 ......
517–09–9 ......
474–86–2 ......
114–07–8 ......
50–28–2 ........
50–27–1 ........
53–16–7 ........
57–63–6 ........
asabaliauskas on DSK3SPTVN1PROD with NOTICES
CASRN
1,1,1,2-Tetrachloroethane ........................
1,1-Dichloroethane ...................................
1,2,3-Trichloropropane .............................
1,3-Butadiene ...........................................
1,4-Dioxane ..............................................
17 alpha-Estradiol ....................................
1-Butanol ..................................................
2-Methoxyethanol .....................................
2-Propen-1-ol ...........................................
3-Hydroxycarbofuran ................................
4,4′-Methylenedianiline ............................
Acephate ..................................................
Acetaldehyde ...........................................
Acetamide ................................................
Acetochlor ................................................
Acetochlor ethanesulfonic acid (ESA) .....
Acetochlor oxanilic acid (OA) ...................
Acrolein ....................................................
Alachlor ethanesulfonic acid (ESA) .........
Alachlor oxanilic acid (OA) .......................
alpha-Hexachlorocyclohexane .................
Aniline ......................................................
Bensulide .................................................
Benzyl chloride .........................................
Butylated hydroxyanisole .........................
Captan ......................................................
Chlorate ....................................................
Chloromethane (Methyl chloride) .............
Clethodim .................................................
Cobalt .......................................................
Cumene hydroperoxide ............................
Cyanotoxins a ...........................................
Dicrotophos ..............................................
Dimethipin ................................................
Diuron .......................................................
Equilenin ..................................................
Equilin ......................................................
Erythromycin ............................................
Estradiol (17-beta estradiol) .....................
Estriol .......................................................
Estrone .....................................................
Ethinyl Estradiol (17-alpha ethynyl estradiol).
Ethoprop ...................................................
Ethylene glycol .........................................
Ethylene Oxide .........................................
Ethylene thiourea .....................................
Formaldehyde ..........................................
Germanium ..............................................
Halon 1011 (bromochloromethane) .........
HCFC–22 .................................................
Hexane .....................................................
Hydrazine .................................................
Manganese ..............................................
Mestranol .................................................
Methamidophos ........................................
Methanol ..................................................
Methyl bromide (Bromomethane) ............
Methyl tert-butyl ether ..............................
Metolachlor ...............................................
Metolachlor ethanesulfonic acid (ESA) ....
Metolachlor oxanilic acid (OA) .................
Molybdenum .............................................
Nitrobenzene ............................................
Nitroglycerin .............................................
N-Methyl-2-pyrrolidone .............................
N-Nitrosodiethylamine (NDEA) ................
N-Nitrosodimethylamine (NDMA) .............
N-Nitroso-di-n-propylamine (NDPA) .........
N-Nitrosodiphenylamine ...........................
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13194–48–4 ..
107–21–1 ......
75–21–8 ........
96–45–7 ........
50–00–0 ........
7440–56–4 ....
74–97–5 ........
75–45–6 ........
110–54–3 ......
302–01–2 ......
7439–96–5 ....
72–33–3 ........
10265–92–6 ..
67–56–1 ........
74–83–9 ........
1634–04–4 ....
51218–45–2 ..
171118–09–5
152019–73–3
7439–98–7 ....
98–95–3 ........
55–63–0 ........
872–50–4 ......
55–18–5 ........
62–75–9 ........
621–64–7 ......
86–30–6 ........
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EXHIBIT 1—CONTAMINANTS ON THE FINAL CCL 4, REGULATORY DETERMINATION 3, UCMR 2, UCMR 3 AND PROPOSED
UCMR 4—Continued
CASRN
Chemical or chemical group
CCL 4
nomination
RD 3 short list
UCMR 2
UCMR 3
Proposed
UCMR 4 a
930–55–2 ......
25154–52–3 b
68–22–4 ........
103–65–1 ......
95–53–4 ........
75–56–9 ........
301–12–2 ......
42874–03–3 ..
1763–23–1 ....
335–67–1 ......
52645–53–1 ..
41198–08–7 ..
91–22–5 ........
121–82–4 ......
135–98–8 ......
107534–96–3
112410–23–8
13494–80–9 ..
59669–26–0 ..
23564–05–8 ..
26471–62–5 ..
78–48–8 ........
121–44–8 ......
76–87–9 ........
51–79–6 ........
7440–62–2 ....
50471–44–8 ..
137–30–4 ......
N-Nitrosopyrrolidine (NPYR) ....................
Nonylphenol .............................................
Norethindrone (19-Norethisterone) ..........
n-Propylbenzene ......................................
o-Toluidine ...............................................
Oxirane, methyl- .......................................
Oxydemeton-methyl .................................
Oxyfluorfen ...............................................
Perfluorooctane sulfonic acid (PFOS) .....
Perfluorooctanoic acid (PFOA) ................
Permethrin ................................................
Profenofos ................................................
Quinoline ..................................................
RDX ..........................................................
sec-Butylbenzene .....................................
Tebuconazole ...........................................
Tebufenozide ...........................................
Tellurium ...................................................
Thiodicarb ................................................
Thiophanate-methyl ..................................
Toluene diisocyanate ...............................
Tribufos ....................................................
Triethylamine ............................................
Triphenyltin hydroxide (TPTH) .................
Urethane ..................................................
Vanadium .................................................
Vinclozolin ................................................
Ziram ........................................................
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a Anatoxin-a,
cylindrospermopsin, nodularin, total microcystin and several microcystin congeners are proposed for monitoring under UCMR 4.
organization that nominated ‘‘nonylphenol’’ for CCL 4 provided the CASRN of 25451–52–3. The name ‘‘nonylphenol’’ does not allow for a
definitive identification of chemical structure since nonylphenol can exhibit two forms of isomerism. There are at least five CASRNs known to be
associated with ‘‘nonylphenol’’: In addition to 25154–52–3 (which represents n-nonylphenol with the ortho-, meta-, or para-substitution unspecified), other CASRNs include: 104–40–5 (4-n-nonylphenol); 84852–15–3 (4-nonylphenol, branched); 91672–41–2 (2-nonylphenol, branched); and
139–84–4 (3-n-nonylphenol). None of these five CASRNs is adequately general enough to represent both forms of isomerism. For the sake of
consistency, the CASRN provided by the nominator was selected and the additional possible CASRNs and structures are delineated here.
b The
Microbe *
CCL 4
nomination
UCMR 3
Adenovirus ...............................................................................................................................................................
Caliciviruses .............................................................................................................................................................
Campylobacter jejuni ...............................................................................................................................................
Enterovirus ...............................................................................................................................................................
Escherichia coli (O157) ...........................................................................................................................................
Helicobacter pylori ...................................................................................................................................................
Hepatitis A virus .......................................................................................................................................................
Legionella pneumophila ...........................................................................................................................................
Mycobacterium avium ..............................................................................................................................................
Naegleria fowleri ......................................................................................................................................................
Salmonella enterica .................................................................................................................................................
Shigella sonnei ........................................................................................................................................................
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asabaliauskas on DSK3SPTVN1PROD with NOTICES
* There were no CCL 4 microbes monitored under UCMR 2, and none are proposed for monitoring under UCMR 4. The UCMR 4 Candidate
Contaminants Information Compendium (USEPA, 2015b) provides a rationale for why contaminants, including microbes, were not included in the
proposed UCMR 4. No CCL 4 microbes were included in the RD 3 Short List. Norovirus, a member of the calicivirus family, was included on
UCMR 3 pre-screen testing.
III. Summary of the Approach Used To
Identify and Evaluate Candidates for
the Draft CCL 4
The Draft CCL 4 was published in the
Federal Register on February 4, 2015
(80 FR 6076 (USEPA, 2015a)). EPA used
a three step evaluation and selection
process to identify candidates for the
Draft CCL 4: (1) Carry forward CCL 3
contaminants (except those with
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regulatory determinations), (2) seek and
evaluate nominations from the public
for additional contaminants to consider,
(3) evaluate any new data for those
contaminants with previous negative
regulatory determinations from CCL 1 or
CCL 2 for potential inclusion on the
CCL 4. The CCL 3 process is
summarized in section I.E.2. A brief
summary of steps 1–3 that were used to
develop the Draft CCL 4 is provided in
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the section that follows, and a more
detailed summary is provided in the
Draft CCL 4 Federal Register notice (80
FR 6076 (USEPA, 2015a)). A summary
of the public comments on the Draft
CCL 4 and EPA’s responses can be
found in section IV.
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A. Carry Forward of CCL 3
Contaminants to the Draft CCL 4
EPA carried forward all contaminants
listed on CCL 3 to the Draft CCL 4 with
the exception of perchlorate, for which
the agency made a positive regulatory
determination, and the five CCL 3
contaminants with preliminary
regulatory determinations at that time,
pending their final regulatory
determinations. This carry forward
process is consistent with that
previously used in CCL 2. The agency
took this approach based on the
following considerations: (1) In
developing the CCL 3, the agency
implemented a robust process
recommended by the NRC and the
NDWAC to screen and score the
universe of potential contaminants; (2)
EPA used the best available, peer
reviewed data and information to
evaluate contaminants for CCL 3; and
(3) Carrying forward CCL 3
contaminants allowed the agency to
focus resources on evaluating
contaminants nominated by the public
for CCL 4 and review new data for CCL
1 or CCL 2 contaminants with previous
negative regulatory determinations (68
FR 42897, July 18, 2003 (USEPA, 2003);
73 FR 44251, July 30, 2008 (USEPA,
2008b)). Carrying forward CCL 3
contaminants also allowed EPA to focus
resources on UCMR 3 monitoring and
analysis and RD 3 analyses.
B. Summary and Evaluation of CCL 4
Nominated Contaminants
asabaliauskas on DSK3SPTVN1PROD with NOTICES
1. CCL 4 Nominations Summary
EPA sought public nominations in a
Federal Register notice on May 8, 2012
(77 FR 27057), for contaminants to be
considered for possible inclusion in the
CCL 4 (USEPA, 2012)). EPA received
nominations for 59 unique
contaminants for the CCL 4, including
54 chemical and five microbial
contaminants. After carefully reviewing
and evaluating the information and data
for the nominated contaminants, EPA
added two of the nominated chemicals
(manganese and nonylphenol) to the
Draft CCL 4. Detailed information on the
nominations is contained in the
‘‘Summary of Nominations for the
Fourth Contaminant Candidate List’’
support document (USEPA, 2016b).
2. How Nominated Contaminants Were
Evaluated for the Draft CCL 4
Four nominated contaminants were
already covered by a proposed or
existing NPDWR and were not eligible
for the CCL 4 since the SDWA specifies
that the CCL only include those
contaminants without any proposed or
promulgated NPDWRs. Seven of the
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nominated contaminants were on CCL 3
and were carried forward to the Draft
CCL 4. EPA reviewed the nominations
and supporting information to
determine if any new data were
provided that had not been previously
evaluated for CCL 3. The agency also
collected and evaluated additional data
for the nominated contaminants, when
it was available, including the seven
nominated contaminants carried
forward from CCL 3. The additional data
was obtained from both updated CCL 3
data sources and from new data sources
that were not available at the time the
agency finalized CCL 3. These data
sources are listed in the ‘‘Data Sources
for the Contaminant Candidate List 4’’
support document (USEPA, 2016c).
Nominated contaminants with new
data were screened and scored using the
same process used in CCL 3. Through
this analysis, EPA added manganese
and nonylphenol to the Draft CCL 4
because, as discussed in more detail in
the Draft CCL 4 Federal Register notice
(80 FR 6076 (USEPA, 2015a)), EPA
determined that the new and updated
health effects information and
additional occurrence data merited
listing the contaminants. Detailed
information on the data used to screen
the nominated contaminants to
determine whether or not they were
included in the PCCL 4 is available in
the ‘‘Screening Document for the PCCL
4 Nominated Contaminants’’ (USEPA,
2016d). More detailed information on
the process and the data used to
evaluate nominated contaminants for
listing on the CCL 4 can be found in the
‘‘Contaminants Information Sheets
(CISs) for the Final Contaminant
Candidate List 4 (CCL 4)’’ support
documents (USEPA, 2016e).
C. Evaluation of Previous Negative
Regulatory Determinations for the Draft
CCL 4
EPA evaluated the 20 contaminants
from CCL 1 and CCL 2 for which the
agency made negative regulatory
determinations. EPA collected and
evaluated new or updated data for the
previous negative regulatory
determination chemicals. Since RD 3
was recently published using the best
available data, EPA did not include the
RD 3 negative regulatory determinations
in this evaluation. The agency
concluded there was not sufficient new
information for 19 of the 20
contaminants with previous negative
regulatory determinations to justify
including them on the Draft CCL 4.
Because commenters also did not
identify such information, EPA has not
included these contaminants on the
Final CCL 4. EPA added manganese, a
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81105
previous negative regulatory
determination from RD 1, to the Draft
and Final CCL 4 as previously discussed
in section III.B.
IV. What comments did EPA receive on
the Draft CCL 4 and how did the
Agency respond?
EPA requested comment on the Draft
CCL 4 and how to further improve upon
the selection process developed for CCL
3 as a tool for future CCLs. The agency
received 27 public comment letters on
the Draft CCL 4. EPA considered all
public comments and evaluated the data
and information provided by
commenters in selecting the Final CCL
4. EPA used the same process used in
the CCL 3 to screen and score any
contaminants with new data or
information provided by commenters.
EPA prepared responses to all public
comments that are in the ‘‘Comment
Response Document for the Fourth
Drinking Water Contaminant Candidate
List (Categorized Public Comments)’’
document, which is available in the
docket for this action (USEPA, 2016f).
Based on the analyses conducted as a
result of public comments, EPA
determined not to list three cancelled
pesticides (disulfoton, fenamiphos, and
molinate) on the Final CCL 4 that were
included on the Draft CCL 4 because, as
discussed more fully in the following
sections, these chemicals are not known
or anticipated to occur in PWSs and are
not anticipated to require regulation.
With the exception of these three
pesticides, all of the contaminants listed
on the Draft CCL 4 are listed on the
Final CCL 4.
A summary of some of the key public
comments received, recommendations
from EPA’s Science Advisory Board
(SAB) on the CCL 4, and EPA’s
responses are provided in this section.
Data used to evaluate the contaminants
for the CCL 4 can be found in the
Contaminant Information Sheets (CISs)
for the Final Fourth Contaminant
Candidate List (CCL 4) (USEPA, 2016e),
which can be found in the docket for
this action available at
www.regulations.gov by searching for
docket EPA–HQ–OW–2012–0217.
A. Recommendations From the EPA
Science Advisory Board
The EPA SAB and its Drinking Water
Committee (DWC) reviewed the Draft
CCL 4 and provided recommendations
to the Administrator on January 11,
2016, in their report ‘‘Review of the
EPA’s Draft Fourth Drinking Water
Contaminant Candidate List (CCL 4)’’
(USEPA, 2016g). On April 29–30, 2015,
the SAB DWC held a public meeting to
discuss responses to EPA charge
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questions. During this meeting, EPA
provided an overview of the process
used to develop the Draft CCL 4 and
answered questions from the
Committee.
The SAB’s recommendations and
comments on the overall CCL 4 process
and documentation are summarized in
the following bullet points:
• The SAB stated that the general
protocol used to evaluate contaminants
on the CCL 4 is well described and
conceptually clear. They concluded the
transparency and clarity of the process
has improved since CCL 3 was finalized.
• The SAB said that the
documentation for CCL 4 lacked specific
information necessary in order to follow
the decision-making process for listing
an individual contaminant on the Draft
CCL 4. Specific suggestions to improve
transparency and clarity of the support
documents include:
Æ Develop a summary table that
consolidates summary information on
all carried forward and nominated
contaminants.
Æ Display results of the CCL 4
screening and classification process in a
manner that explicitly outlines the
scoring schemes used and the scientific
rationale in applying the selection
criteria.
Æ Provide examples for both
microbial and chemical contaminants
that display the process of how
contaminants were included on or
eliminated from the Draft CCL 4.
Æ Clearly describe and improve the
process for removing contaminants from
prior CCLs, where appropriate, when
such lists serve as the basis for a new
CCL.
Æ Explain the evaluation of CCL
contaminants during the RD process.
• The SAB recommended that EPA
should utilize data from UCMR 3
monitoring as it becomes available.
• The SAB stated that the CCL 4 list
includes a number of contaminants
carried forward from the CCL 3 without
providing a sense of the relative priority
of the listed chemicals. The SAB
recommended EPA prioritize the list to
inform future regulatory decisionmaking and to help researchers focus
their efforts.
EPA Response: EPA has provided a
more detailed response to the SAB in
the document, ‘‘Response to SAB
recommendations on the Draft CCL 4’’
(USEPA, 2016h), which can be found in
the docket for this action available at
www.regulations.gov by searching for
docket EPA–HQ–OW–2012–0217. This
section summarizes EPA’s response to
some of the key SAB recommendations.
The agency has updated the technical
support documents for the CCL 4 to
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increase the transparency of its
decisions relative to the contaminants
included on the Final CCL 4. For
instance, the CIS support document
provides examples showing the criteria
and process for including or excluding
chemical and microbial contaminants
from the CCL 4. Additionally, a
summary table in the same support
document presents factors used to
determine how the CCL 4 contaminants
were selected. The agency also
summarizes the process used to evaluate
contaminants under RD 3 in section
I.E.3 of this notice.
While EPA agrees with the SAB about
the importance of using UCMR data to
inform the CCL, the agency does not
believe it is appropriate to use
preliminary UCMR 3 data to make final
CCL 4 decisions. The UCMR 3 data set
was not finalized within the timeframe
for use and analysis under CCL 4. The
UCMR 3 monitoring period ended in
December 2015 and results are reported
to EPA through 2016. After the
monitoring period is completed, the
results undergo review for quality
assurance and are subject to change
following further review by the
analytical laboratory, the PWS, the State
and EPA. The agency will perform
further analysis of both the health
effects and occurrence of contaminants
monitored under UCMR 3 during the RD
4 and CCL 5 development process.
EPA identified the current
occurrence, health effects and analytical
methods data needs of CCL 4
contaminants for RD 4 evaluations in
section V of this notice. This data needs
table is presented to provide a sense of
relative priority for listed contaminants
by identifying those contaminants likely
to have sufficient data for further
evaluation under the next RD and those
that have research needs. As the agency
continues to evaluate contaminants on
the CCL 4, EPA will work with agency
and non-EPA scientists to develop and
collect the best available science to
support decision-making for future
determinations.
B. Public Comments
1. General Comments on CCL 4
EPA received comments, both in
support of and against the carry forward
of contaminants from the CCL 3 to the
Draft CCL 4. One commenter asked for
more information on the decision to
carry forward CCL 3 contaminants to the
Draft CCL 4. Commenters not in support
of the carry forward of CCL 3
contaminants thought EPA should
reassess the science on all the CCL 3
contaminants. One commenter also
thought EPA should limit the number of
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contaminants on the CCL so that
research for the contaminants could be
completed between one CCL and the
next. One commenter supported the
carry forward approach because the CCL
3 contaminants already have data
available that shows there may be a
potential public health impact. They
also suggested that EPA should continue
to evaluate these contaminants until
enough data are collected to support a
regulatory determination.
EPA response: The reasons for
carrying forward contaminants from the
CCL 3 to the CCL 4 are presented in
section III.A of this notice. EPA has
continued to collect data and further
evaluate the science for many of the
contaminants that were carried forward
from the CCL 3 to the CCL 4. For
example, since the listing of
contaminants on CCL 3, EPA has
monitored and collected occurrence
data for several CCL contaminants
through the UCMR program. EPA has
also further analyzed and evaluated
many of the CCL 3 contaminants that
were carried forward to CCL 4 under the
RD 3 process. Exhibit 1 in section II.A
of this notice lists CCL 4 contaminants
that were evaluated under these other
agency efforts. Although EPA carried
forward contaminants from the CCL 3 to
the CCL 4, EPA intends to collect new
data and conduct further evaluations of
unregulated contaminants for CCL 5.
EPA does not agree that the CCL
should be limited to a certain number of
contaminants. The CCL identifies
contaminants that are ‘‘known, or
anticipated to occur in PWSs,’’ and is
the first step in identifying
contaminants that may require
regulation. Some of the contaminants on
the list may have sufficient information
to make regulatory determinations in
the near term and some of the
contaminants on the list need additional
data in order to determine the
appropriate agency action. While the
SDWA does not limit the CCL to a
particular number of contaminants, the
agency recognizes the need to
communicate data needs for
contaminants included on the Final CCL
4. Therefore, EPA has provided a
summary of the current data needs for
RD 4 evaluations in section V of this
notice. The agency will continue to
evaluate data needs through the RD 4
process and will continue to work with
internal and external researchers to
discuss research needs and priorities.
2. Chemical Contaminants
a. Contaminants With Release Data
EPA received comments that several
contaminants listed based on
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environmental release data for
evaluating occurrence (e.g., ethylene
oxide, ethylene glycol, and toluene
diisocyanate) should not be on the CCL
4 because one or more of their intrinsic
physical or chemical properties would
result in limited occurrence in water.
Commenters cited the hydrolysis and
biodegradation rate, or quick
volatilization from water as reasons
these chemicals should be removed
from the Final CCL 4. Additionally,
commenters noted that some of these
contaminants have relatively short halflives in water or may not be long-lived
in the environment and thus should not
be listed on the Final CCL 4.
EPA Response: EPA is including
ethylene oxide, ethylene glycol, and
toluene diisocyanate on the Final CCL 4
because these contaminants may be
anticipated to occur in PWSs and may
require regulation. Although no
occurrence information in finished or
ambient water is available for these
contaminants, to be consistent with the
CCL 4 protocol, EPA used total
environmental release data reported in
the TRI to evaluate and score the
occurrence attributes. In response to
comments citing that EPA should
consider physical and chemical
properties, EPA conducted additional
analyses that considers physical and
chemical properties and environmental
fate parameters to provide an alternate
score for the magnitude attribute. For
this additional analysis on the specific
contaminants commented on (e.g.,
ethylene oxide, ethylene glycol, and
toluene diisocyanate), EPA used the
persistence and mobility scoring
protocol (which is the protocol used for
those chemicals with only production
data) as the basis for scoring the
magnitude attribute as described in the
Final CCL 3: Classification of the PCCL
to the CCL (USEPA, 2009e), available in
the docket for this action. The model
results for these contaminants using this
alternate magnitude score still indicated
that the contaminants should be listed
(for a summary of how the classification
model results were used to select
contaminants for CCL 4, please see
USEPA, 2016e, available in the docket
for this action). These additional
analyses are further described in the
‘‘Comment Response Document for the
Fourth Drinking Water Contaminant
Candidate List (Categorized Public
Comments)’’ document, which is
available in the docket for this action
(USEPA, 2016f). Additionally, as the
SAB (USEPA, 2016h) noted,
‘‘contaminants with a half-life in
drinking water sources of days to weeks
may still pose a public health concern.’’
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Considering the comments received
on the Draft CCL 4, in future CCLs, EPA
may refine analyses to consider if
physical and chemical properties can be
incorporated into the evaluations of
contaminants listed based on
environmental release data for
occurrence.
b. Cyanotoxins
EPA received comments supporting
the inclusion of cyanotoxins on the CCL
4. Some comments requested that
cyanotoxins be listed by individual
toxins rather than including
cyanotoxins as a group on the Final CCL
4 in order to prioritize research on
health effects, analytical methods,
occurrence and treatment. Comments
specifically requested listing the key
variants of microcystins,
cylindrospermopsin, anatoxin-a,
saxitoxin and euglenophycin.
EPA Response: EPA agrees that
cyanotoxins should be included on the
CCL 4, and has included cyanotoxins as
a group on the Final CCL 4. The group
of cyanotoxins includes all toxins
produced by cyanobacteria including
but not limited to microcystins,
cylindrospermopsin, anatoxin-a and
saxitoxin. EPA has provided CIS sheets
for microcystin-LR,
cylindrospermopsin, anatoxin-a and
saxitoxin. Under CCL 3, cyanotoxins
were listed as a group and EPA released
CIS sheets for microcystin-LR,
cylindrospermopsin and anatoxin-a.
Based on data submitted in public
comments, EPA updated previous CIS
sheets and developed a CIS sheet for
saxitoxin. EPA was unable to develop a
CIS sheet for euglenophycin due to
insufficient information on health and
occurrence. EPA acknowledges the
comments to list specific cyanotoxin
compounds on the CCL instead of
listing cyanotoxins as a group. However,
because of the similar sources of
cyanotoxins (i.e., cyanobacteria) their
management may be similar.
Furthermore, due to significant
information gaps for some cyanotoxins
(e.g., euglenophycin and nodularin and
many microcystin congeners), EPA has
determined it most appropriate to
continue to list cyanotoxins as a group
at this time. EPA agrees that
microcystins, cylindrospermopsin,
anatoxin-a and saxitoxin can be of
concern for drinking water supplies.
EPA acknowledges associated data gaps
for euglenophycin as well as those for
other cyanotoxins. EPA included total
microcystins and six microcystin
congeners (-LA, -LF, -LR, -LY, -RR, and
-YR), cylindrospermopsin, anatoxin-a
and nodularin on the proposed UCMR
4 for monitoring by PWSs. The
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occurrence information collected under
the UCMR 4 will be used to further
evaluate the appropriate agency
regulatory determination and research
actions.
c. Perfluorinated Compounds (PFOA
and PFOS)
EPA received a comment supporting
the inclusion of perfluorooctanoic acid
(PFOA) and perfluorooctane sulfonic
acid (PFOS) on the CCL 4. EPA also
received comments that PFOS and/or
PFOA should not be listed on the Final
CCL 4. The commenter supporting
inclusion of these chemicals on the CCL
4 cited their persistence in the
environment and toxicological effects as
reasons to include them on the Final
CCL 4, and encouraged EPA to consider
these chemicals for drinking water
regulation. Commenters supporting
removal of PFOA and/or PFOS from the
CCL 4 cited the low frequency of
detections of PFOA and/or PFOS under
the UCMR 3 monitoring as of January
2015. Additional reasons cited by
commenters that these chemicals should
not be listed on the Final CCL 4 are the
voluntary efforts by manufacturers to
reduce emissions and work towards
elimination of these chemicals from
products.
EPA Response: EPA is including
PFOA and PFOS on the Final CCL 4
because these contaminants are known
to occur in drinking water, are
persistent in the environment and in the
human body, have shown to be toxic in
animal studies and may require
regulation.
As discussed in the summary of EPA
responses to the SAB in this section
(IV.A) of the notice, EPA did not use
preliminary UCMR 3 monitoring results
for the CCL 4.
EPA acknowledges the industry
commitments to voluntarily reduce the
use and production of PFOA and PFOS;
however, there are still a limited
number of ongoing uses of PFOA and
PFOS. Additionally, these chemicals are
persistent in the environment and in the
human body, which indicates they may
be present in water or migrate to
drinking water sources even after uses
and production have been reduced or
ceased, and therefore potential exposure
may still be of concern.
In May 2016, EPA released lifetime
health advisories for PFOA and PFOS
(USEPA, 2016i, available in the docket
for today’s action) and Health Effects
Support Documents based on the
agency’s assessment of the latest peer
reviewed science. The health advisories
provide federal, state, tribal and local
officials with information on the health
risks of these chemicals, occurrence,
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analytical methods and treatment
technologies so that they can determine
what actions to take to protect
consumers.
In accordance with the SDWA, EPA
will consider the occurrence data from
the final UCMR 3 data set, along with
the peer reviewed health effects
assessments supporting the May 2016
PFOA and PFOS Health Advisories, to
make a regulatory determination
whether or not PFOA and PFOS require
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d. Pesticides
Several public commenters requested
that specific pesticides be removed from
the Final CCL 4. EPA agrees with
commenters that three of these
pesticides (disulfoton, fenamiphos, and
molinate) should not be listed on the
Final CCL 4; therefore, EPA is removing
them from the Final CCL 4. The
evaluation of these three pesticides is
summarized in the following
paragraphs.
(i) Disulfoton
EPA received a comment from the
public that disulfoton should not be
included on the Final CCL 4. The
commenter noted that disulfoton had
zero or very few detections nationally
on any previous round of UCMR
monitoring and therefore does not
warrant national regulation.
EPA Response: EPA agrees with the
commenter that disulfoton should not
be included on the Final CCL 4.
Disulfoton sales and distribution were
cancelled in the U.S., effective
December 31, 2010, with remaining
product stocks to be used until depleted
(74 FR 48551, September 23, 2009
(USEPA, 2009g)). The UCMR 1 finished
water screening survey (SS) found no
detections of disulfoton in 2,300
samples from 295 PWSs. The United
States Geological Survey (USGS) has
detected disulfoton infrequently in
ambient water. During the 1992–2001
USGS National Water-Quality
Assessment (NAWQA) Program
monitoring, disulfoton was detected in
only 17 sites out of 7,118 ambient water
sites sampled (see the CIS for this
contaminant (USEPA, 2016e)). Out of
the 17 sites with detections, only two
sites had detects at levels greater than
the health reference level of potential
concern for drinking water. Given that
disulfoton was detected in those two
sites prior to its cancellation, the agency
expects that any potential disulfoton
occurrence in water will likely continue
to decrease in the future. Although
persistent environmental contaminants
may occur in a PWS after its uses are
cancelled, based on its physical and
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chemical properties, disulfoton has low
to moderate mobility in water and it is
only moderately persistent in the
environment (see the CIS for this
contaminant (USEPA, 2016e), which
can be found in the docket for this
action). Therefore its occurrence is
expected to decrease over time.
EPA is not including disulfoton on
the Final CCL 4 because it is not known
or anticipated to occur in drinking
water. Disulfoton likely has low
potential for public health concern
based on its cancellation status, zero
detections in PWSs (from UCMR 1 data),
and very few detections in ambient
water from a large number of sites
sampled (by the USGS NAWQA
program).
(ii) Fenamiphos
EPA received a comment from the
public that fenamiphos should not be
included on the Final CCL 4. The
commenter stated that the registrant for
fenamiphos agreed to cancel all uses,
and all existing stocks are to be used by
October 6, 2017. The commenter stated
that very limited uses remain of
products containing fenamiphos in the
U.S. and use will be discontinued after
2017.
EPA Response: EPA agrees with the
commenter that fenamiphos should not
be included on the Final CCL 4 because
it is not anticipated to occur in drinking
water and is not likely to require
regulation. Fenamiphos product
registrations were cancelled, and the
sale and distribution of fenamiphos by
the registrant was prohibited on May 31,
2007. This cancellation followed a fiveyear phase-out period, beginning in
2003, intended to limit and reduce
production of fenamiphos. The sale and
distribution of any remaining stocks
will be prohibited after October 6, 2017
(79 FR 59262, October 1, 2014; USEPA,
2014c). Fenamiphos was not monitored
under UCMR, thus no national scale
monitoring has been conducted in
PWSs. While fenamiphos was not
included in the USGS NAWQA
national-scale ambient water monitoring
(1992–2001), based on the USGS
Pesticide National Synthesis Project
(USGS, 2012), fenamiphos use is
estimated to have steadily declined. The
USGS estimated a usage level of
approximately 1.0 million pounds/year
of widespread use in certain regions per
year in 1992, which declined to an
estimated 0.2 million pounds/year in
2002 and further declined to an
estimated 0.03 million pounds/year of
limited regional uses in 2012. EPA
expects fenamiphos occurrence in water
will likely continue to decrease due to
the declining trend in usage for many
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years and the prohibition on usage of
existing stocks in the U.S. effective after
October 6, 2017.
In summary, due to its registration
cancellation status, significant decline
in usage (based on estimated data from
1992–2013), moderate persistence in the
environment, and the prohibition of
existing stocks (effective after October 6,
2017), EPA does not anticipate
fenamiphos to occur in PWSs or to
require regulation, therefore, it is not
included on the Final CCL 4.
(iii) Molinate
EPA received a comment from the
public that molinate should not be
included on the Final CCL 4. The
commenter noted that molinate had zero
or very few detections nationally on any
previous round of UCMR monitoring
and therefore does not warrant national
regulation.
EPA Response: EPA agrees with the
commenter that molinate should not be
included on the Final CCL 4. The UCMR
1 finished water assessment monitoring
found only one sample with a detection
of molinate out of 33,799 samples taken
from 3,873 PWSs. The single sample
detection was below the health
reference level of potential concern for
molinate in drinking water. Further,
molinate sales and distribution were
cancelled in the U.S. effective July 1,
2009, with remaining stocks required to
be used by August 31, 2009, (73 FR
44261, July 30, 2008 (USEPA, 2008c)).
This cancellation action concluded a
six-year scheduled phaseout of
molinate. The agency is not including
molinate on the Final CCL 4 because it
is not anticipated to occur in PWSs at
levels of public health concern. The
agency expects the potential for
molinate to occur in water will likely
continue to decrease due to the
prohibition on product use in the U.S.
since 2009.
e. Manganese
EPA received four comments that
support the inclusion of manganese and
two comments that do not support the
inclusion of manganese on CCL 4.
Commenters supporting the inclusion of
manganese on CCL 4 cited recent
studies that showed neurological effects
in children and infants exposed to
excess manganese via drinking water.
Commenters also noted manganese
frequently occurs in water and should
be included on CCL 4 so that national
occurrence data can be obtained through
UCMR monitoring. Commenters who
did not support the inclusion of
manganese on the CCL 4 cited that the
primary route of human exposure to
manganese is through food, not drinking
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water. Also, commenters question the
link between the consumption of
drinking water and developmental
neurotoxicity from manganese exposure
to warrant inclusion on the CCL 4.
EPA Response: EPA agrees with the
commenters that support manganese
inclusion on the CCL 4, and is including
manganese on the Final CCL 4 because
it is known to occur in PWSs and may
require regulation. The evidence from
the studies provided by commenters
indicate that exposure to excess
manganese may present a substantial
health threat to children and infants.
EPA is continuing to evaluate the
potential risks to children and infants
based on over 30 recent studies cited by
the public during the nomination and
comment period including those by
Bouchard et al. (2011), Oulhote et al.
(2014) and Kern and colleagues (2010,
2011), whom have indicated
neurological effects stemming from the
exposure to excess manganese.
EPA also agrees with the commenters
assertion that manganese is known to
occur in PWSs. EPA has included the
occurrence data used to evaluate
manganese in the CIS for this
contaminant. This data includes USGS
monitoring of ambient water, as well as
drinking water data from several states.
The data indicates that manganese is
known to occur in public drinking water
supply wells and supports the previous
information from the National
Inorganics and Radionuclides Survey
(NIRS). EPA has proposed to monitor
manganese under UCMR 4.
EPA has reviewed all of the current
data submitted by commenters on the
manganese health effects and found that
the existing 2004 Health Advisory could
warrant an update. Since manganese is
not a regulated contaminant in drinking
water, the Secondary Maximum
Contaminant Level of 0.05 mg/L is not
mandatory and does not require
monitoring. The current IRIS assessment
for manganese dates to 1995 (USEPA,
1995b) and the Health Advisory to 2004.
The Agency for Toxic Substances and
Disease Registry 2012 Toxicological
Profile did not establish guidelines that
applied to oral exposures and the
Institute of Medicine (2001) provides
Tolerable Upper Intake Levels for
developmental lifestages and adults.
The database of health effects studies for
oral manganese exposures has expanded
considerably since the last EPA
assessment, therefore manganese is a
good candidate for re-evaluation. EPA
intends to evaluate the new
toxicological findings and UCMR 4
monitoring data and will use this
information in future regulatory
decision-making, and to revise the
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current Health Advisory, if appropriate.
More detailed evaluations of the routes
of exposure usually occur in the
regulatory determination and regulatory
development processes.
f. Nonylphenol
EPA received two comments
supporting the inclusion of nonylphenol
and three comments that nonylphenol
should not be included on the Final
CCL 4. The commenters supporting
inclusion of nonylphenol on the CCL 4
cited new health effects and occurrence
data as reasons to include them on the
Final CCL 4 and stated that EPA has
adequate justification to include
nonylphenol on the CCL based on this
information. The commenters
requesting that nonylphenol not be
included on the Final CCL 4 cited a
surface water monitoring study from
2002 and industry efforts to reduce
surfactant usage as reasons nonylphenol
should not be listed on the Final CCL
4. The main use of nonylphenol is in the
manufacture of nonylphenol
ethoxylates, which have been used in a
wide range of industrial applications
and consumer products including
laundry detergents, cleaners, degreasers,
paints and coatings and other uses (79
FR 59186, October 1, 2014 (USEPA,
2014d)).
EPA Response: EPA is including
nonylphenol on the Final CCL 4 as
proposed because it is anticipated to
occur in drinking water, has potential
adverse health effects (Bontje et al.,
2005), and may require regulation. EPA
evaluated the 2002 USGS
reconnaissance study (Kolpin et al.,
2002) identified by the commenter and
used it to evaluate the occurrence of
nonylphenol. While there were more
recent finished water studies available,
EPA considers the 2002 USGS study as
the most appropriate study to evaluate
the occurrence of nonylphenol for CCL
4 given the greater number of samples
and larger geographic scale.
Additionally, more recent studies
indicate that nonylphenol has been
detected in drinking water. While EPA
appreciates the information from
commenters on reduced usage of
nonylphenol, we believe measured
occurrence data from water sources are
preferred over production or usage
information when evaluating the
likelihood of occurrence in drinking
water.
3. Microbial Contaminants
a. Overall Process Comments
EPA received comments arguing that
the follow-through on the microbes
listed in previous CCLs has been
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inadequate, that EPA should identify
high priority pathogens on the CCL 4
and identify information gaps and
barriers to obtaining information
associated with each pathogen. EPA
received comments requesting an open
process for prioritizing and collecting
information, to adopt a collaborative
method development process and to
rank microbes by treatability. EPA also
received comments to focus priorities
on distribution and plumbing system
biofilm concerns and to evaluate
microbial contaminants in the context of
diverse water supplies such as drinking
water sources from water reuse
treatment facilities.
EPA Response: EPA’s criteria for
evaluating and prioritizing pathogens
for inclusion in the CCL 3 included
health effects, waterborne disease
outbreaks (WBDO) and occurrence
information (73 FR 9628 (USEPA,
2008a)). EPA developed and
implemented a systematic strategy and
set of criteria for selecting the pathogens
for CCL 3. This is the screening and
scoring process described in detail in
the support documents in the docket of
the Final CCL 3 (e.g., see the Final
Contaminant Candidate List 3 Microbes:
PCCL to CCL Process for more
information on all of the scores). The
CCL 3 and CCL 4 processes provided
multiple opportunities for public input
(e.g., nominations, public comment) to
allow for an open process. In order to
provide additional clarity to the scoring
process, EPA is including an example
schematic describing the process of
evaluating a pathogen for inclusion on
the list and a pathogen for exclusion
from the list. This schematic can be
found in the CIS’s for the Final Fourth
Contaminant Candidate List (USEPA,
2016e). EPA acknowledges the request
to identify information gaps; therefore,
data needs are described in section V of
this Federal Register notice.
The EPA’s Office of Water coordinates
with EPA’s Office of Research and
Development to discuss research needs
and priorities. Research on distribution
system and premise plumbing biofilm
concerns has been incorporated into
EPA’s strategic research plan. EPA
acknowledges the comments on diverse
water supplies and method
development and will consider these
comments as it develops future research
priorities.
b. Pathogens for Inclusion
EPA received comments supporting
the proposed inclusion of
Mycobacterium avium, Legionella
pneumophila, Naegleria fowleri,
enteroviruses and Heterotrophic Plate
Count (HPC). EPA also received
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comments requesting recommendations
for Legionella pneumophila
management.
EPA Response: EPA included
Mycobacterium avium, Legionella
pneumophila, Naegleria fowleri, and
enteroviruses on the Final CCL 3 and
were therefore carried forward to the
draft and Final CCL 4. While the
broader issue of the management of
Legionella pneumophila is outside the
scope of today’s action, the agency
agrees it is of great importance and
Legionella remains a risk to building
water systems. In September 2016, EPA
released a document reviewing the
available technology to treat Legionella
titled Technologies for Legionella
Control in Premise Plumbing Systems:
Scientific Literature Review (USEPA,
2016j). This document provides
information to state and local decisionmakers about how they might utilize
treatment as part of their efforts to
manage Legionella risks in building
water systems.
EPA disagrees that HPC should be
included on CCL 4. The group of HPC
usually includes a diverse group of
microorganisms that are part of the
natural environment in water. Available
epidemiological evidence shows no
relationship between gastrointestinal
illness and HPC bacteria in drinking
water (Calderon, 1988; Calderon and
Mood, 1991; Payment et al., 1997;
Bartram J et al., 2003). Thus, EPA
considers the potential health risk of
HPC bacteria in drinking water as likely
negligible and is not including HPC on
the Final CCL 4. In addition, HPC
bacteria are addressed under the Surface
Water Treatment Rule as a treatment
technique where they can be monitored
in lieu of a disinfectant residual because
HPC is an alternative method of
determining disinfectant residual levels.
c. Pathogens for Exclusion
EPA received comments not
supporting the proposed inclusion of
Escherichia coli O157 and Helicobacter
pylori, noting these pathogens were
unlikely to occur in treated drinking
water.
EPA Response: EPA’s criteria for
evaluating and prioritizing pathogens
for inclusion in the Draft CCL 3 Federal
Register notice, included health effects,
WBDO and occurrence information (73
FR 9628 (USEPA, 2008a)). Treatability
was not part of the scoring criteria
considered for CCL 3 inclusion.
Although some of the microbes listed in
the Draft CCL 4 may be well controlled
by drinking water treatment (i.e.,
disinfection), not all PWSs in the U.S.
are required to treat. For example,
approximately thirty percent of the
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40,000 community ground water
systems do not have disinfection
treatment (USEPA, 2013). For the
reasons discussed in detail in the Draft
CCL 3 Federal Register notice (73 FR
9628 ((USEPA, 2008a)), EPA did not
preclude pathogens from CCL 3 and
CCL 4 based on their potential to be
controlled by existing treatment
technique regulations.
V. Data Needs for CCL 4 Contaminants
After the listing process, the CCL 4
contaminants will be further evaluated
in a separate action called Regulatory
Determination 4 (RD 4). The process
used to previously evaluate CCL 3
contaminants under RD 3 is described
in section I.E.3 of this notice. EPA
anticipates using a similar process to
evaluate CCL 4 contaminants under RD
4, although it is possible that some
modifications may be made to this
process. In the initial phases of this
process, EPA determines if sufficient
data are available to meet the three RD
criteria set forth in SDWA section
1412(b)(1) and previously outlined in
section I.D.4 of this notice. If sufficient
data are available to meet all three
statutory criteria, a regulatory
determination may be made. As
discussed in section I.D.4, SDWA
requires EPA to make regulatory
determinations every five years on at
least five CCL contaminants.
The SAB and other commenters have
recommended additional prioritization
of the CCL 4 contaminants to
communicate research needs, help focus
efforts for researchers, and inform future
regulatory decision-making. EPA
acknowledges that many contaminants
on the CCL 4 have substantial data and
information needs to fulfill in order for
the agency to make a regulatory
determination in accordance with
SDWA 1412 (b)(1)(A). These current
data needs are described in the
following section, and are presented in
Exhibit 2. By identifying those
contaminants that need additional
research and information, EPA is
communicating to stakeholders both
research priorities and gaps for these
contaminants.
Categorization of Contaminants
EPA assessed the data and
information gathered on the CCL 4
contaminants and generated a table
(Exhibit 2) to help identify data/
information needs for further evaluation
under RD 4. To develop this table, EPA
began with the information contained in
the data availability/Phase 1 table
included in Appendix D of the Protocol
for the RD 3 (USEPA, 2014b), which
describes the status of the best available
PO 00000
Frm 00058
Fmt 4703
Sfmt 4703
occurrence data and health effects
assessments for CCL 3 contaminants.
EPA updated the occurrence data needs
for CCL 4 contaminants by including
which contaminants were monitored on
the UCMR 3, and updated the health
effects data needs based on available
EPA or other non-EPA peer reviewed
assessments as of May 2016. Since
manganese and nonylphenol were
nominated and added to the CCL 4 (not
carried forward from CCL 3), data
collected under CCL 4 was included in
the Contaminant Information Sheets
(USEPA, 2016e) for these contaminants
and was used to assess the data needs.
EPA characterized each chemical
contaminant included on the Final CCL
4 based on their health effects,
occurrence and analytical methods data
needs.
EPA then categorized contaminants
into six categories depending upon the
availability of their occurrence data and
health assessment. Contaminants in
Group A have nationally representative
finished drinking water data and a peer
reviewed health assessment and are
likely to have sufficient data available to
be placed on a short list for further
assessment under RD 4. Contaminants
in Group B have finished drinking water
data that is not nationally representative
and peer reviewed health assessments.
These contaminants may have sufficient
data to be placed on a short list for
further assessment under RD 4,
particularly if the non-nationally
representative occurrence data shows
detections at levels of public health
concern. Contaminants in groups C, D,
E, and F of Exhibit 2 that lack either a
peer reviewed health assessment or
finished water data have more
substantial data needs and are unlikely
to have sufficient information to allow
further assessment under the RD 4. For
these contaminants, EPA plans to
identify them as research priorities and
work to fill their research needs such as
evaluating the potential for monitoring
under the UCMR or identifying those
contaminants as priorities for health
effects research. The health effects and
occurrence data sources used to classify
data needs are featured in Appendix 6
of the CISs for the Final Fourth CCL in
the docket (USEPA, 2016e). The
following sections describe the types of
data or information gaps outlined in
Exhibit 2 and provide examples.
A. Health Effects
Under the RD process, EPA relies on
external peer-reviewed health
assessments to determine if and at what
level a contaminant ‘‘may have an
adverse effect on the health of persons.’’
Health effects data sources evaluated for
E:\FR\FM\17NON1.SGM
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Federal Register / Vol. 81, No. 222 / Thursday, November 17, 2016 / Notices
RD 3 included EPA health assessments,
or peer reviewed health assessments
developed by other organizations such
as the National Academy of Sciences,
the Agency for Toxic Substances and
Disease Registry, World Health
Organization, the California EPA’s
Office of Environmental Health Hazard
Assessment, Registry of Toxic Effects of
Chemical Substances, and/or
supplemental data from a single study,
if the health assessment is peer
reviewed and uses comparable methods,
standards and guidelines to an EPA
health assessment.
As shown in Exhibit 2, EPA
categorized the health effects data needs
in the following way:
1. If a peer reviewed health
assessment is available or is in the
process of being revised, the
contaminant is considered to have
health effects data available.
2. If a peer reviewed health
assessment is not available, then the
contaminant is considered to not have
health effects data currently available.
B. Occurrence
For RD evaluations, the occurrence
data availability assessment is used to
identify contaminants that may have
sufficient data and information to
characterize their status as known or
likely to occur in PWSs. EPA uses data
from many sources to evaluate
occurrence for contaminants considered
for RD (see Appendix C of USEPA,
2014b for occurrence data sources
evaluated under RD 3). For this
evaluation, EPA prefers to have
nationally representative finished
drinking water occurrence data, but
finished drinking water data that are not
nationally representative may also be
used to determine if the contaminant
occurs frequently at levels of public
health concern. In addition, the agency
evaluates supplemental sources of
information (e.g., ambient/source water
occurrence, production/use and
environmental release data). For the
purposes of identifying current data
needs for RD 4, as shown in Exhibit 2,
EPA categorized the occurrence data
needs in the following way:
• Finished drinking water occurrence
data that are nationally representative
are available.
Æ Data sources may include UCMRs
(i.e., UCMR 1, UCMR 2 and UCMR 3),
the Unregulated Contaminant
Monitoring Program (Round 1 and
Round 2) and NIRS.
• Finished drinking water occurrence
data that are not nationally
representative are available. These data
may include:
Æ Finished water assessments by
federal agencies (e.g., EPA, the U.S.
Department of Agriculture and USGS).
These may include assessments that are
geographically distributed across the
nation but are not intended to be
statistically representative of the nation
(e.g., the Disinfection By-Product Rule
Information Collection Request).
Æ State-level finished water
monitoring data.
Æ Research performed by institutions
and universities (e.g., scientific
literature), including targeted or local
monitoring studies.
Æ Various reports from the Centers for
Disease Control and the scientific
literature for microbes.
• Finished drinking water occurrence
data are not available.
Æ The best available data sources may
include environmental release data
(such as TRI data or pesticide
application data) or ambient water data.
EPA has also indicated with a
footnote in the occurrence data column,
highlighting which contaminants are
proposed for monitoring under the
UCMR 4 from 2018–2020. Therefore,
although some of the contaminants that
may be monitored under UCMR 4 are
shown in this table as currently having
data gaps for occurrence (e.g., they only
have drinking water data that is not
nationally representative or release
data), EPA has proposed to fill those
occurrence data needs for future RD
evaluations.
C. Analytical Methods
To conduct nationally representative
drinking water occurrence studies that
could support a regulatory
determination, EPA needs to have an
analytical method that is suitable for the
drinking water matrix and is robust
enough to be used by many laboratories
to conduct national studies and/or
compliance monitoring. For the purpose
of CCL 4, EPA assessed the status of the
development of analytical methods for
drinking water and determined
estimated reporting levels for each
contaminant. EPA also assessed method
sensitivity with respect to the HRL for
the chemical contaminants. Method
sensitivity is measured by using method
specific reporting levels, lowest
concentration minimum reporting
levels, and promulgated minimum
reporting level. While there are many
methods for monitoring the CCL 4
pathogens available from scientific
papers and consensus organizations, not
all of them may be appropriate for use
in drinking water or for a national
monitoring effort. Of the CCL 4
pathogens, only enterovirus and
caliciviruses have an EPA-approved
method for drinking water. The status of
drinking water analytical methods for
the CCL chemical contaminants, as of
May 2016, is presented in Exhibit 2.
EPA categorized the analytical method
needs in the following way:
• An EPA drinking water method,
with estimated reporting levels that are
adequate for analysis relative to the
current HRL or health assessment is
available.
• An EPA drinking water method is
available but the minimum reporting
level (MRL) does not allow for
quantitation of the contaminant at a
concentration below the current HRL.
These methods are denoted in Exhibit 2
by ‘‘(MRL>HRL)’’.
• An EPA drinking water method is
currently being developed.
• An EPA drinking water method is
not available.
Although not shown in Exhibit 2, EPA
also considers other government and
consensus methods (e.g., Standard
Methods and ASTM, International)
when considering analytical methods
that may be used or modified for UCMR
monitoring.
EXHIBIT 2—REGULATORY DETERMINATION DATA/INFORMATION NEEDS FOR CCL 4 CONTAMINANTS
asabaliauskas on DSK3SPTVN1PROD with NOTICES
CASRN
What is the best available
occurrence data?
Common name
Is a health assessment
available?
Is an EPA analytical
method available?
(A) Contaminants with Nationally Representative Finished Water Occurrence Data and Peer Reviewed Health Assessments
630–20–6 ...................
96–18–4 .....................
123–91–1 ...................
16655–82–6 ...............
34256–82–1 ...............
187022–11–3 .............
VerDate Sep<11>2014
1,1,1,2-Tetrachloroethane ....................
1,2,3-Trichloropropane .........................
1,4-Dioxane ..........................................
3-Hydroxycarbofuran ............................
Acetochlor ............................................
Acetochlor ethanesulfonic acid (ESA)
21:24 Nov 16, 2016
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National
National
National
National
National
National
Fmt 4703
...........................
...........................
...........................
...........................
...........................
...........................
Sfmt 4703
Yes a ................................
Yes ..................................
Yes ..................................
Yes b ................................
Yes ..................................
Yes b ................................
E:\FR\FM\17NON1.SGM
17NON1
Yes.
Yes (MRL > HRL).
Yes.
Yes.
Yes.
Yes.
81112
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EXHIBIT 2—REGULATORY DETERMINATION DATA/INFORMATION NEEDS FOR CCL 4 CONTAMINANTS—Continued
What is the best available
occurrence data?
CASRN
Common name
194992–44–4 .............
142363–53–9 .............
171262–17–2 .............
14866–68–3 ...............
7440–48–4 .................
NA ..............................
7439–96–5 .................
74–83–9 .....................
51218–45–2 ...............
171118–09–5 .............
152019–73–3 .............
7439–98–7 .................
98–95–3 .....................
55–18–5 .....................
62–75–9 .....................
621–64–7 ...................
930–55–2 ...................
1763–23–1 .................
335–67–1 ...................
121–82–4 ...................
7440–62–2 .................
Acetochlor oxanilic acid (OA) ..............
Alachlor ethanesulfonic acid (ESA) .....
Alachlor oxanilic acid (OA) ..................
Chlorate ................................................
Cobalt ...................................................
Enterovirus ...........................................
Manganese ..........................................
Methyl bromide (Bromomethane) ........
Metolachlor ...........................................
Metolachlor ethanesulfonic acid (ESA)
Metolachlor oxanilic acid (OA) .............
Molybdenum .........................................
Nitrobenzene ........................................
N-Nitrosodiethylamine (NDEA) ............
N-nitrosodimethylamine (NDMA) .........
N-Nitroso-di-n-propylamine (NDPA) ....
N-nitrosopyrrolidine (NPYR) ................
Perfluorooctane sulfonic acid (PFOS)
Perfluorooctanoic acid (PFOA) ............
RDX ......................................................
Vanadium .............................................
National
National
National
National
National
National
National
National
National
National
National
National
National
National
National
National
National
National
National
National
National
...........................
...........................
...........................
...........................
...........................
...........................
c ...................
...........................
...........................
...........................
...........................
...........................
...........................
...........................
...........................
...........................
...........................
...........................
...........................
...........................
...........................
Is a health assessment
available?
Yes b ................................
Yes ..................................
Yes b ................................
Yes ..................................
Yes a ................................
Yes ..................................
In Development ...............
Yes a ................................
Yes ..................................
Yes ..................................
Yes ..................................
In Development ...............
Yes ..................................
Yes ..................................
Yes a ................................
Yes ..................................
Yes a ................................
Yes ..................................
Yes ..................................
In Development ...............
Yes a ................................
Is an EPA analytical
method available?
Yes.
Yes.
Yes (MRL
Yes.
Yes.
Yes.
Yes.
Yes.
Yes.
Yes.
Yes.
Yes.
Yes.
Yes (MRL
Yes (MRL
Yes (MRL
Yes.
Yes.
Yes.
Yes.
Yes.
> HRL).
> HRL).
> HRL).
> HRL).
(B) Contaminants With Non-Nationally Representative Finished Water Occurrence Data and Peer Reviewed Health Assessments
71–36–3 .....................
30560–19–1 ...............
107–02–8 ...................
NA ..............................
319–84–6 ...................
741–58–2 ...................
100–44–7 ...................
NA ..............................
133–06–2 ...................
NA ..............................
1-Butanol ..............................................
Acephate ..............................................
Acrolein ................................................
Adenovirus ...........................................
alpha-Hexachlorocyclohexane .............
Bensulide .............................................
Benzyl chloride .....................................
Caliciviruses .........................................
Captan ..................................................
Cyanotoxins .........................................
Non-National c .................
Non-National ...................
Non-National ...................
Non-National ...................
Non-National c .................
Non-National ...................
Non-National ...................
Non-National ...................
Non-National ...................
Non-National d .................
141–66–2 ...................
330–54–1 ...................
13194–48–4 ...............
107–21–1 ...................
96–45–7 .....................
50–00–0 .....................
NA ..............................
10265–92–6 ...............
NA ..............................
86–30–6 .....................
301–12–2 ...................
42874–03–3 ...............
52645–53–1 ...............
41198–08–7 ...............
107534–96–3 .............
78–48–8 .....................
50471–44–8 ...............
137–30–4 ...................
Dicrotophos ..........................................
Diuron ...................................................
Ethoprop ...............................................
Ethylene glycol .....................................
Ethylene thiourea .................................
Formaldehyde ......................................
Legionella pneumophila .......................
Methamidophos ....................................
Mycobacterium avium ..........................
N-Nitrosodiphenylamine (NDPhA) .......
Oxydemeton-methyl .............................
Oxyfluorfen ...........................................
Permethrin ............................................
Profenofos ............................................
Tebuconazole .......................................
Tribufos ................................................
Vinclozolin ............................................
Ziram ....................................................
Non-National ...................
Non-National ...................
Non-National c .................
Non-National ...................
Non-National ...................
Non-National ...................
Non-National ...................
Non-National ...................
Non-National ...................
Non-National ...................
Non-National ...................
Non-National c .................
Non-National c .................
Non-National c .................
Non-National c .................
Non-National c .................
Non-National ...................
Non-National ...................
In Development ...............
Yes ..................................
Yes a ................................
Yes ..................................
Yes ..................................
Yes ..................................
Yes a ................................
Yes ..................................
Yes ..................................
Yes for microcystins and
cylindrospermopsin, no
for other cyanotoxins.
Yes ..................................
Yes ..................................
Yes ..................................
Yes ..................................
Yes ..................................
Yes ..................................
Yes ..................................
Yes ..................................
Yes ..................................
Yes a ................................
Yes ..................................
Yes ..................................
Yes ..................................
Yes ..................................
Yes ..................................
Yes ..................................
Yes ..................................
Yes ..................................
Yes.
Yes.
No.
No.
Yes (MRL > HRL).
Yes.
No.
Yes.
No.
Yes.
Yes.
Yes.
Yes.
No.
No.
Yes.
In Development.
Yes.
In Development.
No.
Yes.
Yes.
Yes.
Yes.
Yes.
Yes.
Yes.
No.
asabaliauskas on DSK3SPTVN1PROD with NOTICES
(C) Contaminants With Nationally Representative Finished Water Occurrence Data Lacking Peer Reviewed Health Assessments
75–34–3 .....................
106–99–0 ...................
74–87–3 .....................
474–86–2 ...................
50–28–2 .....................
50–27–1 .....................
53–16–7 .....................
57–63–6 .....................
7440–56–4 .................
74–97–5 .....................
75–45–6 .....................
1634–04–4 .................
103–65–1 ...................
VerDate Sep<11>2014
1,1-Dichloroethane ...............................
1,3-Butadiene .......................................
Chloromethane (Methyl chloride) .........
Equilin ..................................................
Estradiol (17-beta estradiol) .................
Estriol ...................................................
Estrone .................................................
Ethinyl Estradiol (17-alpha ethynyl estradiol).
Germanium ..........................................
Halon 1011 (bromochloromethane) .....
HCFC–22 .............................................
Methyl tert-butyl ether (MTBE) ............
n-Propylbenzene ..................................
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...........................
...........................
...........................
...........................
...........................
...........................
...........................
...........................
No a ..................................
No ....................................
No ....................................
No ....................................
No ....................................
No ....................................
No ....................................
No ....................................
Yes.
Yes (MRL > HRL).
Yes.
Yes.
Yes.
Yes.
Yes.
Yes.
National c .........................
National ...........................
National ...........................
National ...........................
National ...........................
No ....................................
No ....................................
No ....................................
No ....................................
No a ..................................
Yes.
Yes.
Yes.
Yes.
Yes.
National
National
National
National
National
National
National
National
Fmt 4703
Sfmt 4703
E:\FR\FM\17NON1.SGM
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81113
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EXHIBIT 2—REGULATORY DETERMINATION DATA/INFORMATION NEEDS FOR CCL 4 CONTAMINANTS—Continued
CASRN
Common name
What is the best available
occurrence data?
Is a health assessment
available?
135–98–8 ...................
13494–80–9 ...............
sec-Butylbenzene .................................
Tellurium ..............................................
National ...........................
National ...........................
No a ..................................
No ....................................
Is an EPA analytical
method available?
Yes.
No.
(D) Contaminants With Non-Nationally Representative Finished Water Occurrence Data Lacking Peer Reviewed Health Assessments
57–91–0 .....................
75–07–0 .....................
62–53–3 .....................
25013–16–5 ...............
517–09–9 ...................
114–07–8 ...................
110–54–3 ...................
72–33–3 .....................
NA ..............................
25154–52–3 ...............
68–22–4 .....................
17alpha-estradiol ..................................
Acetaldehyde .......................................
Aniline ..................................................
Butylated hydroxyanisole .....................
Equilenin ..............................................
Erythromycin ........................................
Hexane .................................................
Mestranol .............................................
Naegleria fowleri ..................................
Nonylphenol .........................................
Norethindrone (19-Norethisterone) ......
Non-National ...................
Non-National ...................
Non-National ...................
Non-National c .................
Non-National ...................
Non-National ...................
Non-National ...................
Non-National ...................
Non-National ...................
Non-National ...................
Non-National ...................
No ....................................
No ....................................
No a ..................................
No ....................................
No ....................................
No ....................................
No a ..................................
No ....................................
No ....................................
No ....................................
No ....................................
In Development.
Yes.
No.
Yes.
In Development.
In Development.
No.
No.
No.
No.
In Development.
(E) Contaminants With Peer Reviewed Health Assessments Lacking Finished Water Occurrence Data
107–18–6 ...................
110429–62–4 .............
55290–64–7 ...............
NA ..............................
NA ..............................
NA ..............................
302–01–2 ...................
67–56–1 .....................
55–63–0 .....................
872–50–4 ...................
75–56–9 .....................
91–22–5 .....................
112410–23–8 .............
59669–26–0 ...............
23564–05–8 ...............
76–87–9 .....................
2-Propen-1-ol .......................................
Clethodim .............................................
Dimethipin ............................................
Escherichia coli (O157) ........................
Helicobacter pylori e .............................
Hepatitis A virus ...................................
Hydrazine .............................................
Methanol ..............................................
Nitroglycerin .........................................
N-Methyl-2-pyrrolidone .........................
Oxirane, methyl- ...................................
Quinoline ..............................................
Tebufenozide .......................................
Thiodicarb ............................................
Thiophanate-methyl .............................
Triphenyltin hydroxide (TPTH) .............
Release c .........................
Release ...........................
Release c .........................
No Data ...........................
No Data ...........................
No Data ...........................
Release ...........................
Release ...........................
Release ...........................
Release ...........................
Release ...........................
Release c .........................
Release ...........................
Release ...........................
Release ...........................
Release ...........................
Yes a ................................
Yes ..................................
Yes ..................................
Yes ..................................
Yes ..................................
Yes ..................................
Yes a ................................
Yes ..................................
Yes a ................................
Yes ..................................
Yes ..................................
Yes ..................................
Yes ..................................
Yes ..................................
Yes ..................................
Yes ..................................
Yes.
No.
Yes.
No.
No.
No.
No.
No.
No.
No.
No.
Yes (MRL > HRL).
Yes.
No.
No.
No.
(F) Contaminants Lacking Finished Water Occurrence Data and Current, Peer Reviewed Health Assessments
109–86–4 ...................
101–77–9 ...................
60–35–5 .....................
NA ..............................
80–15–9 .....................
75–21–8 .....................
95–53–4 .....................
NA ..............................
NA ..............................
26471–62–5 ...............
121–44–8 ...................
51–79–6 .....................
2-Methoxyethanol .................................
4,4′-Methylenedianiline ........................
Acetamide ............................................
Campylobacter jejuni ...........................
Cumene hydroperoxide ........................
Ethylene oxide .....................................
o-Toluidine ...........................................
Salmonella enteric ...............................
Shigella sonnei .....................................
Toluene diisocyanate ...........................
Triethylamine ........................................
Urethane ..............................................
Release c .........................
Release ...........................
Release ...........................
No Data ...........................
Release ...........................
Release ...........................
Release c .........................
No Data ...........................
No Data ...........................
Release ...........................
Release ...........................
Release ...........................
No a ..................................
No ....................................
No ....................................
No ....................................
No ....................................
No ....................................
No a ..................................
No ....................................
No ....................................
No ....................................
No ....................................
No ....................................
Yes.
No.
No.
No.
No.
No.
Yes.
No.
No.
No.
No.
No.
asabaliauskas on DSK3SPTVN1PROD with NOTICES
Key to Exhibit:
National = Finished drinking water occurrence data that are nationally representative are available.
Non-National = Finished drinking water occurrence data that are not nationally representative are available.
In Development = Revised health assessment or analytical method is currently being developed.
a Provisional Peer Reviewed Toxicity Value (PPRTV) in the form of chronic, oral RfD subchronic, oral RfD, cancer weight evidence, or cancer
slope factor available.
b The parent health assessment was used for the metabolite. There is no independent health assessment available for the metabolite.
c Proposed for UCMR 4.
d Evaluations of occurrence data availability for cyanotoxins in this table are based on anatoxin-a, cylindrospermopsin, and microcystin-LR.
Cyanotoxins proposed for UCMR 4 monitoring include total microcystins (MC), MC-LA, MC-LF, MC-LR, MC-LY, MC-RR, MC-YR, nodularin,
anatoxin-a and cylindrospermopsin.
VI. Next Steps and Future Contaminant
Candidate Lists
The CCL process is critical to shaping
the future direction of the drinking
water program. The agency will
continue to gather information and
evaluate contaminants on the CCL 4 to
VerDate Sep<11>2014
21:24 Nov 16, 2016
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make regulatory determinations for at
least five contaminants. The agency will
also continue to refine the CCL process
and gather more data to identify
contaminants for CCL 5. EPA will
continue to work to prioritize
contaminants on the CCL 4, both for RD
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and for additional research and data
collection.
References
Bartram, J., Cotruvo, J., Exner, M., Fricker, C.
and Glasmacher, A. 2003. Heterotrophic
plate count measurement in drinking
water safety. WHO Emerging issues in
E:\FR\FM\17NON1.SGM
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asabaliauskas on DSK3SPTVN1PROD with NOTICES
81114
Federal Register / Vol. 81, No. 222 / Thursday, November 17, 2016 / Notices
Water and Infectious Disease Series,
IWA Publishing, London, pp. 119–122.
Bontje, D., Hermens, J., Vermeire, T. and
Damstra, T. 2005. Integrated risk
assessment: Nonylphenol case study.
Report prepared for the WHO/UNEP/ILO
International programme on chemical
safety.
´
Bouchard, M.F., Sauve, S., Barbeau, B.,
`
Legrand, M., Brodeur, M.E., Bouffard, T.,
Limoges, E., Bellinger, D.C. and Mergler,
D. 2011. Intellectual impairment in
school-age children exposed to
manganese from drinking water.
Environmental health perspectives,
119(1), p. 138.
Calderon, R.L. 1988. Bacteria colonizing
point-of-entry granular activated carbon
filters and their relationship to human
health. EPA CR–813978–01–0, U.S.
Environmental Protection Agency,
Washington, DC.
Calderon, R.L. and Mood, E.W. 1991. Bacteria
colonizing point-of-use granular
activated carbon filters and their
relationship to human health. EPA CR
811904–01–0, U.S. Environmental
Protection Agency, Washington, DC.
Kern, C.H., Stanwood, G.D. and Smith, D.R.
2010. Preweaning manganese exposure
causes hyperactivity, disinhibition, and
spatial learning and memory deficits
associated with altered dopamine
receptor and transporter levels. Synapse,
64(5), pp. 363–378.
Kern, C.H. and Smith, D.R. 2011. Preweaning
Mn exposure leads to prolonged
astrocyte activation and lasting effects on
the dopaminergic system in adult male
rats. Synapse, 65(6), pp. 532–544.
Kolpin, D.W., Furlong, E.T., Meyer, M.T.,
Thurman, E.M., Zaugg, S.D., Barber, L.B.
and Buxton, H.T. 2002. Pharmaceuticals,
hormones, and other organic wastewater
contaminants in U.S. streams, 1999–
2000: A national reconnaissance.
Environmental science & technology,
36(6), pp. 1202–1211.
Oulhote, Youssef, Donna Mergler, Benoit
´ `
Barbeau, David C. Bellinger, Therese
`
Bouffard, Marie-Eve Brodeur, Dave
´
Saint-Amour, Melissa Legrand, Sebastien
´
Sauve, and Maryse F. Bouchard. 2014.
‘‘Neurobehavioral function in school-age
children exposed to manganese in
drinking water.’’ Environmental Health
Perspectives 122(12): 1343–1350.
Payment, P., Siemiatycki, J., Richardson, L.,
Renaud, G., Franco, E. and Prevost, M.
1997. A prospective epidemiological
study of gastrointestinal health effects
due to the consumption of drinking
water. International Journal of
Environmental Health Research, 7(1),
pp. 5–31.
USEPA. 1995a. EPA’s Policy on Evaluating
Risk to Children. Available online at:
https://www.epa.gov/children/epaspolicy-evaluating-risk-children.
USEPA. 1995b. Manganese; CASRN 7439–
96–5. Integrated Risk Information System
(IRIS), Chemical Assessment Summary.
Available online at: https://
cfpub.epa.gov/ncea/iris/iris_documents/
documents/subst/0373_summary.pdf.
Accessed July 27, 2016.
VerDate Sep<11>2014
21:24 Nov 16, 2016
Jkt 241001
USEPA. 2003. Announcement of Regulatory
Determinations for Priority
Contaminants on the Drinking Water
Contaminant Candidate List; Notice.
Federal Register. Vol. 68, No. 138, p.
42898. July 18, 2003.
USEPA. 2008a. Drinking Water Contaminant
Candidate List 3—Draft. Federal
Register. Vol. 73, No. 35. p. 9628.
February 21, 2008.
USEPA. 2008b. Drinking Water: Regulatory
Determinations Regarding Contaminants
on the Second Drinking Water
Contaminant Candidate List—Final
Determinations. Federal Register. Vol.
73, No. 147, p. 44251. July 30, 2008.
USEPA. 2008c. Molinate; Product
Cancellation Order and Amendment to
Terminate Uses. Federal Register. Vol.
73 No. 147. p. 44261. July 30, 2008.
USEPA. 2009a. Final Contaminant Candidate
List 3 Chemicals: Identifying the
Universe. EPA 815–R09–006. August
2009.
USEPA. 2009b. Final Contaminant Candidate
List 3 Microbes: Identifying the
Universe. EPA 815–R09–004. August
2009.
USEPA. 2009c. Final Contaminant Candidate
List 3 Chemicals: Screening to a PCCL.
EPA 815–R–09–007. August 2009.
USEPA. 2009d. Final Contaminant Candidate
List 3 Microbes: Screening to the PCCL.
EPA 815–R–09–005. August 2009.
USEPA. 2009e. Final Contaminant Candidate
List 3 Chemicals: Classification of the
PCCL to CCL. EPA 815–R–09–008.
August 2009.
USEPA. 2009f. Final Contaminant Candidate
List 3 Microbes: Classification of the
PCCL to CCL. EPA 815–R–09–009.
August 2009.
USEPA. 2009g. Disulfoton and
Methamidophos; Product Cancellation
Order. Federal Register. Volume 74. No.
183. p. 48551. September 23, 2009.
USEPA. 2012. Request for Nominations of
Drinking Water Contaminants for the
Fourth Contaminant Candidate List.
Federal Register. Vol. 77, No. 89. p.
27057. May 8, 2012.
USEPA. 2013. National Primary Drinking
Water Regulations: Revisions to the Total
Coliform Rule. Federal Register. Volume
78. No. 30. p. 10306. February 13, 2013.
USEPA. 2014a. Announcement of
Preliminary Regulatory Determination
for Contaminants on the Third Drinking
Water Contaminant Candidate List.
Federal Register. Vol. 79, No. 202, p.
62715. October 20, 2014.
USEPA. 2014b. Protocol for the Regulatory
Determinations 3. Including Appendices
A–F. EPA– 815–R–14–005. April 2014.
USEPA. 2014c. Fenamiphos; Amendment to
Existing Stocks Provision of Use Deletion
and Product Cancellation Order. Federal
Register. Vol. 79, No. 190, p. 59261.
October 1, 2014.
USEPA. 2014d. Certain Nonylphenols and
Nonylphenol Ethoxylates; Significant
New Use Rule Federal Register. Vol. 79,
No. 190, p. 59186. October 1, 2014.
USEPA. 2015a. Drinking Water Contaminant
Candidate List 4—Draft Notice. Federal
Register. Volume 80, No. 23 p. 6076.
PO 00000
Frm 00062
Fmt 4703
Sfmt 9990
February 4, 2015.
USEPA. 2015b. UCMR 4 Candidate
Contaminants—Information
Compendium. EPA 815–B–15–005.
November 2015.
USEPA. 2016a. Announcement of Final
Regulatory Determinations for
Contaminants on the Third Drinking
Water Contaminant Candidate List.
Federal Register. Vol. 81, No. 1, p. 13.
January 4, 2016.
USEPA. 2016b. Summary of Nominations for
the Fourth Contaminant Candidate List
(CCL 4). EPA 815–R–16–006. November
2016.
USEPA. 2016c. Data Sources for the Fourth
Contaminant Candidate List (CCL 4).
EPA 815–R–16–007. November 2016.
USEPA. 2016d. Screening Document for the
Fourth Preliminary Contaminant
Candidate List (PCCL 4). EPA 815–R–16–
008. November 2016.
USEPA. 2016e. Contaminant Information
Sheets (CISs) for the Final Fourth
Contaminant Candidate List (CCL 4).
EPA 815–R–16–003. November 2016.
USEPA. 2016f. Comment Response
Document for the Fourth Drinking Water
Contaminant Candidate List (Categorized
Public Comments). EPA 815–R–16–004.
November 2016.
USEPA. 2016g. Review of the EPA’s Draft
Fourth Drinking Water Contaminant
Candidate List (CCL 4). EPA–SAB–16–
002. January 11, 2016.
USEPA. 2016h. Response to the Science
Advisory Board’s Recommendations on
the Draft Fourth Contaminant Candidate
List (CCL 4). EPA 815–R–16–005.
November 2016.
USEPA. 2016i. Lifetime Health Advisories
and Health Effects Support Documents
for Perfluorooctanoic Acid and
Perfluorooctane Sulfonate. Federal
Register. Vol. 81, No. 101, p. 33250. May
25, 2016.
USEPA. 2016j. Technologies for Legionella
Control in Premise Plumbing Systems:
Scientific Literature Review. EPA 810–
R–16–001. September 2016.
USGS. 2012. National Water-Quality
Assessment (NAWQA) Program,
Pesticide National Synthesis Project.
Available on the Internet at: https://
water.usgs.gov/nawqa/pnsp/usage/
maps/show_map.php?year=2012&map=
FENAMIPHOS&hilo=L.
Dated: November 9, 2016.
Joel Beauvais,
Deputy Assistant Administrator, Office of
Water.
[FR Doc. 2016–27667 Filed 11–16–16; 8:45 am]
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E:\FR\FM\17NON1.SGM
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[Federal Register Volume 81, Number 222 (Thursday, November 17, 2016)]
[Notices]
[Pages 81099-81114]
From the Federal Register Online via the Government Publishing Office [www.gpo.gov]
[FR Doc No: 2016-27667]
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ENVIRONMENTAL PROTECTION AGENCY
[EPA-HQ-OW-2012-0217; FRL-9955-27-OW]
Drinking Water Contaminant Candidate List 4--Final
AGENCY: Environmental Protection Agency (EPA).
ACTION: Notice.
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SUMMARY: The U.S. Environmental Protection Agency (EPA) is publishing a
final list of contaminants that are currently not subject to any
proposed or promulgated national primary drinking water regulation.
These contaminants are known or anticipated to occur in public water
systems and may require regulation under the Safe Drinking Water Act
(SDWA). This list is the Fourth Contaminant Candidate List (CCL 4)
published by EPA since the SDWA amendments of 1996. This Final CCL 4
includes 97 chemicals or chemical groups and 12 microbial contaminants.
FOR FURTHER INFORMATION CONTACT: For information on chemical
contaminants contact Meredith Russell, Office of Ground Water and
Drinking Water, Standards and Risk Management Division, at (202) 564-
0814 or email russell.meredith@epa.gov. For information on microbial
contaminants contact Hannah Holsinger, Office of Ground Water and
Drinking Water, Standards and Risk Management Division, at (202) 564-
0403 or email holsinger.hannah@epa.gov. For general information contact
the EPA Safe Drinking Water Hotline at (800) 426-4791. The Safe
Drinking Water Hotline is open Monday through Friday, excluding legal
holidays, from 10 a.m. to 4 p.m. eastern time.
Abbreviations and Acronyms
CASRN--Chemical Abstract Services Registry Number
CCL--Contaminant Candidate List
CCL 1--EPA's First Contaminant Candidate List
CCL 2--EPA's Second Contaminant Candidate List
CCL 3--EPA's Third Contaminant Candidate List
CCL 4--EPA's Fourth Contaminant Candidate List
CFR--Code of Federal Regulations
CIS--Contaminant Information Sheet
DWC--Drinking Water Committee
EPA--United States Environmental Protection Agency
ESA--Ethanesulfonic acid
FR--Federal Register
HPC--Heterotrophic Plate Count
HRL--Health Reference Level
MCL--Maximum Contaminant Level
MCLG--Maximum Contaminant Level Goal
MRL-- Minimum Reporting Level
NAWQA--National Water-Quality Assessment
NDEA--N-Nitrosodiethylamine
NDMA--N-nitrosodimethylamine
NDPA--N-Nitroso-di-n-propylamine
NDPhA--N-Nitrosodiphenylamine
NDWAC--National Drinking Water Advisory Council
NIRS--National Inorganics and Radionuclides Survey
NRC--National Academy of Science's National Research Council
NPDWR--National Primary Drinking Water Regulation
NPYR--N-nitrosopyrrolidine
PCCL 4--Preliminary Contaminant Candidate List 4
PFOA--Perfluorooctanoic Acid
PFOS--Perfluorooctane Sulfonic Acid
PWS--Public Water System
RD--Regulatory Determination
RD 1--Regulatory Determination 1
RD 2--Regulatory Determination 2
RD 3--Regulatory Determination 3
SAB--Science Advisory Board
SDWA--Safe Drinking Water Act
SS--Screening Survey
TRI--Toxics Release Inventory
UCMR 1--First Unregulated Contaminant Monitoring Rule
UCMR 2--Second Unregulated Contaminant Monitoring Rule
UCMR 3--Third Unregulated Contaminant Monitoring Rule
USGS--United States Geological Survey
WBDO--Waterborne Disease Outbreaks
SUPPLEMENTARY INFORMATION:
Table of Contents
I. General Information
A. Does this action apply to me?
B. How can I get copies of this document and other related
information?
1. Docket
2. Electronic Access
C. What is the purpose of this action?
[[Page 81100]]
D. Statutory Requirements for CCL, Regulatory Determination and
Unregulated Contaminant Monitoring
1. Interrelationship of the CCL, Regulatory Determination and
Unregulated Contaminant Monitoring
2. Contaminant Candidate List
3. Unregulated Contaminant Monitoring
4. Regulatory Determinations
E. Where can I find information on previous CCLs and Regulatory
Determinations?
1. Summary of Previous CCLs and Regulatory Determinations
2. Summary of the CCL 3
3. Summary of the Regulatory Determination 3
II. What is on EPA's Drinking Water Contaminant Candidate List 4?
The Final CCL 4 and a Cross-Walk of Contaminants Between the CCL
4, Regulatory Determination 3, and UCMRs
III. Summary of the Approach Used To Identify and Evaluate
Candidates for the Draft CCL 4
A. Carry Forward of CCL 3 Contaminants
B. Summary and Evaluation of CCL 4 nominated contaminants
1. CCL 4 Nominations Summary
2. How Nominated Contaminants Were Evaluated for the Draft CCL 4
C. Evaluation of Previous Negative Regulatory Determinations
IV. What comments did EPA receive on the Draft CCL 4 and how did the
Agency respond?
A. Recommendations From the EPA Science Advisory Board
B. Public Comments
1. General Comments on CCL 4
2. Chemical Contaminants
a. Contaminants With Release Data
b. Cyanotoxins
c. Perfluorinated Compounds (PFOA and PFOS)
d. Pesticides
e. Manganese
f. Nonylphenol
3. Microbial Contaminants
a. Overall Process Comments
b. Pathogens for Inclusion
c. Pathogens for Exclusion
V. Data Needs for CCL 4 Contaminants
Categorization of Contaminants
A. Health Effects
B. Occurrence
C. Analytical Methods
VI. Next Steps and Future Contaminant Candidate Lists
VII. References
I. General Information
A. Does this action apply to me?
The Final CCL 4 will not impose any requirements on anyone.
Instead, this action notifies interested parties of the EPA's Final CCL
4 of unregulated drinking water contaminants and provides a summary of
the major comments received on the February 4, 2015, Draft CCL 4
Federal Register notice and EPA's responses (80 FR 6076 (USEPA,
2015a)).
B. How can I get copies of this document and other related information?
1. Docket
EPA has established a docket for this action under Docket ID No.
EPA-HQ-OW-2012-0217. Although listed in the index, some information is
not publicly available, e.g., CBI or other information whose disclosure
is restricted by statute. Certain other material, such as copyrighted
material, will be publicly available only in hard copy. Publicly
available docket materials are available either electronically through
www.regulations.gov or in hard copy at the Water Docket, EPA/DC, EPA
West, Room 3334, 1301 Constitution Ave. NW., Washington, DC 20004. The
Public Reading Room is open from 8:30 a.m. to 4:30 p.m., Monday through
Friday, excluding legal holidays. The telephone number for the Public
Reading Room is (202) 566-1744, and the telephone number for the EPA
Docket Center is (202) 566-2426.
2. Electronic Access
You may access this Federal Register document electronically from
the Government Publishing Office under the Federal Register listings at
FDsys (https://www.gpo.gov/fdsys/browse/collection.action?collectionCode=FR).
C. What is the purpose of this action?
The Safe Drinking Water Act (SDWA), as amended in 1996, requires
EPA to publish a list every five years of currently unregulated
contaminants that may pose risks for drinking water (referred to as the
Contaminant Candidate List, or CCL). This list is subsequently used to
make regulatory determinations on whether or not to regulate at least
five contaminants from the CCL with national primary drinking water
regulations (NPDWRs) ((SDWA section 1412(b)(1)). The purpose of today's
action is to present EPA's final list of contaminants on the CCL 4, a
summary of the major public comments received on the Draft CCL 4 and
EPA's responses. Today's action only addresses the Final CCL 4.
Regulatory Determination (RD) for contaminants on the CCL is a separate
agency action.
D. Statutory Requirements for CCL, Regulatory Determination and
Unregulated Contaminant Monitoring
1. Interrelationship of the CCL, Regulatory Determination and
Unregulated Contaminant Monitoring
Under the 1996 amendments to SDWA, Congress established a risk-
based approach for determining which contaminants would become subject
to drinking water standards. The approach includes three components,
the CCL, the Unregulated Contaminant Monitoring Rule (UCMR), and RD. In
preparing the CCL, EPA screens and evaluates unregulated contaminants
to identify those that may require future drinking water regulations.
Inclusion on the CCL does not mean that any particular contaminant will
necessarily be regulated in the future. The UCMR provides a mechanism
to obtain nationally representative occurrence data for unregulated
contaminants. The data provided by UCMR is one of the primary sources
of occurrence information used to evaluate contaminants in the RD
process.
Under the RD process, EPA evaluates UCMR and other occurrence data
along with health effects data for contaminants on the CCL to see which
ones present the greatest public health concern and have sufficient
information for the agency to make a regulatory determination. EPA must
make regulatory determinations for at least five contaminants listed on
the CCL every five years. Today's action addresses only the CCL 4 and
not the UCMR or RD stages of the SDWA contaminant regulatory
development process.
2. Contaminant Candidate List
Section 1412(b)(1) of the SDWA, as amended in 1996, requires EPA to
publish the CCL every five years. The SDWA specifies that the list must
include contaminants that are not subject to any proposed or
promulgated NPDWRs, are known or anticipated to occur in public water
systems (PWSs), and may require regulation under the SDWA. The
unregulated contaminants considered for listing shall include, but not
be limited to, hazardous substances identified in section 101(14) of
the Comprehensive Environmental Response, Compensation, and Liability
Act of 1980, and substances registered as pesticides under the Federal
Insecticide, Fungicide, and Rodenticide Act.
The SDWA directs the agency to consider the health effects and
occurrence information for unregulated contaminants to identify those
contaminants that present the greatest public health concern related to
exposure from drinking water. The statute further directs the agency to
take into consideration the effect of contaminants upon subgroups that
comprise a meaningful portion of the general population (such as
infants, children, pregnant women, the elderly and individuals with a
history of serious illness or other subpopulations) that are
identifiable as being at greater risk of
[[Page 81101]]
adverse health effects due to exposure to contaminants in drinking
water than the general population. Additionally, EPA's 1995 Policy on
Evaluating Health Risks to Children states that the agency will
consider the risks to infants and children consistently and explicitly
as a part of risk assessments generated during its decision-making
process, including the setting of standards to protect public health
(USEPA, 1995a). EPA considers age-related subgroups as ``lifestages''
in reference to a distinguishable time frame in an individual's life,
characterized by unique and relatively stable behavioral and/or
physiological characteristics that are associated with development and
growth. Thus, childhood is viewed as a sequence of lifestages, from
conception through fetal development, infancy and adolescence (see
https://www.epa.gov/children/early-life-stages).
3. Unregulated Contaminant Monitoring
Section 1445(a)(2) of the SDWA mandates that EPA promulgate
regulations (known as the Unregulated Contaminant Monitoring Rule or
UCMR) to establish criteria for a monitoring program for unregulated
contaminants. This section, as amended in 1996, requires that once
every five years, EPA issue a list of no more than 30 unregulated
contaminants to be monitored by PWSs. SDWA requires that EPA enter the
monitoring data into the agency's publicly available National
Contaminant Occurrence Database. EPA's UCMR program must ensure that
systems serving a population larger than 10,000 people, as well as a
nationally representative sample of PWSs serving 10,000 or fewer
people, are required to monitor.
4. Regulatory Determination
Section 1412(b)(1)(B)(ii) of the SDWA, as amended in 1996, requires
EPA at five year intervals, to make determinations of whether or not to
regulate no fewer than five contaminants from the CCL. EPA evaluates
the CCL contaminants with sufficient health effects and occurrence
information to determine whether a regulation is required or not
required. The 1996 SDWA Amendments specify three criteria to determine
whether a contaminant may require regulation:
The contaminant may have an adverse effect on the health
of persons;
the contaminant is known to occur or there is a
substantial likelihood that the contaminant will occur in PWSs with a
frequency and at levels of public health concern; and
in the sole judgment of the Administrator, regulation of
such contaminant presents a meaningful opportunity for health risk
reduction for persons served by PWSs.
If EPA determines that these three statutory criteria are met and
makes a final determination to regulate a contaminant, the agency has
24 months to publish a proposed maximum contaminant level goal \1\
(MCLG) and NPDWR.\2\ After the proposal, the agency has 18 months to
publish and promulgate a final MCLG and NPDWR (SDWA section
1412(b)(1)(E)).\3\ For those contaminants without sufficient
information to allow the agency to make a regulatory determination, EPA
encourages research to provide the information needed to determine
whether to regulate the contaminant.
---------------------------------------------------------------------------
\1\ The MCLG is the ``maximum level of a contaminant in drinking
water at which no known or anticipated adverse effect on the health
of persons would occur, and which allows an adequate margin of
safety. MCLGs are non-enforceable health goals.'' (40 CFR 141.2; 42
U.S.C. 300g-1)
\2\ An NPDWR is a legally enforceable standard that applies to
public water systems. An NPDWR sets a legal limit (called a maximum
contaminant level or MCL) or specifies a certain treatment technique
for public water systems for a specific contaminant or group of
contaminants. The MCL is the highest level of a contaminant that is
allowed in drinking water and is set as close to the MCLG as
feasible, using the best available treatment technology and taking
cost into consideration.
\3\ The statute authorizes a nine month extension of this
promulgation date.
---------------------------------------------------------------------------
E. Where can I find information on previous CCLs, UCMRs, and Regulatory
Determinations
1. Summary of previous CCLs, UCMRs, and Regulatory Determinations
A brief summary of CCL 1, CCL 2, Regulatory Determination 1 (RD 1)
and Regulatory Determination 2 (RD 2) was published in the Federal
Register for the Draft CCL 4 notice (80 FR 6076, February 4, 2015
(USEPA, 2015a)). Information on previous UCMRs, can be found at the
following Web site: https://www.epa.gov/dwucmr.
2. Summary of the CCL 3
The CCL 3 included 104 chemicals or chemical groups and 12
microbiological contaminants. In developing the CCL 3, EPA implemented
an improved process from the process used for CCL 1 and CCL 2. This new
process built on evaluations used for previous CCLs and was based on
substantial expert input and recommendations from the National Academy
of Sciences' National Research Council (NRC) and the National Drinking
Water Advisory Council (NDWAC). EPA used a multi-step CCL process to
identify contaminants for inclusion on the Final CCL 3. The key steps
included:
Identifying a broad universe of potential drinking water
contaminants (called the CCL 3 Universe). EPA initially considered
approximately 7,500 potential chemical and microbial contaminants (more
information on the identification of the CCL 3 Universe can be found in
USEPA, 2009a and USEPA, 2009b).
Applying screening criteria to the universe, EPA
identified almost 600 of those contaminants that should be further
evaluated (the preliminary CCL or PCCL) based on a contaminant's
potential to occur in PWSs and the potential for public health concern
(more information on the CCL 3 screening process can be found in USEPA,
2009c and USEPA, 2009d).
Selecting the final list of 116 contaminants from the PCCL
to include on the CCL based on more detailed evaluation of occurrence
and health effects and expert judgment as well as public input (this
step of the CCL 3 process is called the classification process and more
information can be found in USEPA, 2009e and USEPA, 2009f).
The CCL 3 interpreted the criterion that contaminants are known or
anticipated to occur in public water systems broadly. In evaluating
this criterion, EPA considered not only public water system monitoring
data, but also data on concentrations in ambient surface and ground
waters, releases to the environment (e.g., Toxics Release Inventory
(TRI)), and production. While such data may not establish conclusively
that contaminants are known to occur in public water systems, EPA
believes these data are sufficient to anticipate that contaminants may
occur in public water systems and support their inclusion on the CCL.
The agency considered adverse health effects that may pose a greater
risk to life stages and other sensitive groups which represent a
meaningful portion of the population. Adverse health effects associated
with infants, children, pregnant women, the elderly, and individuals
with a history of serious illness were evaluated as part of the
screening and classification processes. A detailed summary of the CCL 3
process can be found in the Draft CCL 3 (73 FR 9628, February 21, 2008
(USEPA, 2008a) and Final CCL 3 (74 FR 51850, October 8, 2009 (USEPA,
2009a)) Federal Register notices.
3. Summary of the Regulatory Determination 3
EPA published the Announcement of Final Regulatory Determinations
for Contaminants on CCL 3 in the Federal Register on January 4, 2016
(81 FR 13
[[Page 81102]]
(USEPA, 2016a)). The agency made final determinations not to regulate
four contaminants: 1, 3-dinitrobenzene; dimethoate; terbufos; and
terbufos sulfone. The agency delayed the final regulatory determination
for strontium in order to consider additional data and decide whether
there is a meaningful opportunity for health risk reduction by
regulating strontium in drinking water. These five contaminants are not
included on the Final CCL 4.
This section provides an overview of the process used for the Third
Regulatory Determination (RD 3). A summary of the process can be found
in the Federal Register notice announcing the preliminary regulatory
determinations (79 FR 62716, October 24, 2014 (USEPA, 2014a)), and a
detailed explanation of this process can be found in the ``Protocol for
the Regulatory Determination 3'' support document (USEPA, 2014b). This
overview of the RD process is provided to give an understanding of how
contaminants have previously been evaluated after they have been listed
on past CCLs. The RD 4 process may continue to follow this process
although it is possible that some modifications may be made to this
process. The RD process occurs subsequent to a Final CCL, and is a
separate agency action. The RD 3 process, was divided into three
phases: (1) The Data Availability Phase, (2) the Data Evaluation Phase
and (3) the Regulatory Determination Assessment Phase.
The purpose of the first phase, the Data Availability Phase, was to
determine if the agency may have sufficient data to characterize the
potential health effects and known or likely occurrence in drinking
water. With regard to sufficient health effects data used to identify
potential adverse health effect(s), the agency considered whether a
peer reviewed health risk assessment was available or in process from
an EPA or a comparable non-EPA source. In regard to sufficient
occurrence data, the agency considered the availability of nationally
representative finished water data and whether other finished water
data were available that indicated known and/or likely occurrence in
PWSs. After conducting the health and occurrence data availability
assessments, the agency identified those contaminants and contaminant
groups that meet the following Phase 1 data availability criteria:
(a) A peer reviewed health assessment is available or in process,
and
(b) A widely available analytical method for monitoring exists, and
(c) Either nationally representative finished water occurrence data
are available, or other finished water occurrence data shows occurrence
at levels greater than one-half of the CCL 3 health reference level
(HRL).
If a contaminant met these three criteria, it was placed on a
``short list'' and proceeded to Phase 2. From the 116 CCL 3
contaminants, the agency identified a short list of 37 contaminants (35
CCL 3 contaminants and two non-CCL 3 contaminants \4\) to further
evaluate in the second phase.
---------------------------------------------------------------------------
\4\ The non-CCL 3 contaminants, N-Nitroso-di-n-butylamine (NDBA)
and N-Nitrosomethylethylamine (NMEA), were included because they are
part of a larger group (nitrosamines) that also includes a number of
CCL 3 contaminants.
---------------------------------------------------------------------------
During the second phase, the Data Evaluation Phase, the agency
further evaluated each of the 37 contaminants on the short list to
identify those that had sufficient data (or were expected to have
sufficient data) for EPA to assess the three statutory criteria listed
in section I.D.4 of this notice.
To identify the contaminants that present the greatest public
health concern, the agency specifically focused its efforts on
identifying those contaminants or contaminant groups that are occurring
or have substantial likelihood to occur at levels and frequencies of
public health concern, based on the best available peer reviewed data.
In addition to health and occurrence information data assessed in Phase
1, the agency collected additional health and occurrence data and more
thoroughly evaluated this information to identify a list of
contaminants that should proceed to Phase 3. If the agency found that
sufficient data were not available or not likely to be available to
evaluate the three statutory criteria during the first and second
phases, then the contaminant was not considered a candidate for making
a regulatory determination during the current cycle, and the agency
will conduct research, collect information or find other avenues to
fill the data and information gaps. For these contaminants, additional
data that becomes available in the future may be considered for future
CCLs and RDs.
If sufficient data were available for a contaminant to characterize
the potential health effects and known or likely occurrence in drinking
water, the contaminant was evaluated against the three statutory
criteria (listed in section I.D.4) in the third phase of the process,
the Regulatory Determination Assessment Phase.
II. What is on EPA's Drinking Water Contaminant Candidate List 4?
The Final CCL 4 and a Cross-Walk of Contaminants Between the CCL 4,
Regulatory Determination 3, and UCMRs
The Final CCL 4 includes 97 chemicals or chemical groups and 12
microbes listed in Exhibit 1. Exhibit 1 also shows chemical abstract
service registry numbers (CASRNs) of the contaminants on the Final CCL
4 and their status across other EPA programs related to CCL (i.e., RD
and UCMR). The list of contaminants is presented by CASRN when
available, common name, or by aggregate groupings (e.g., cyanotoxins).
Further data and information for the contaminants included on the CCL 4
are available in the technical support documents and Contaminant
Information Sheets available on EPA's CCL 4 Web site and in the docket
for this action (EPA-HQ-OW-2012-0217). All contaminants listed on the
Final CCL 4 were also included on CCL 3, with the exception of
manganese and nonylphenol, which were nominated by the public and added
to the CCL 4. Twenty-eight CCL 4 chemicals that were carried forward
from CCL 3 had been further analyzed and evaluated under the RD 3
process and included on the RD 3 Short List (further described in
section I.E.3. of this notice). The RD 3 process also included an
evaluation of occurrence data from the UCMR 2 for 13 CCL 4 chemicals.
Twenty-one CCL 4 contaminants were monitored under UCMR 3 (19 chemicals
and 2 microbes). The UCMR data will be used to further evaluate CCL 4
contaminants during the RD 4 process. In addition, EPA has proposed
gathering occurrence data for 16 individual CCL 4 chemicals and several
cyanotoxins, including anatoxin-a, cylindrospermopsin, nodularin, total
microcystin and several microcystin congeners under the proposed UCMR
4.
[[Page 81103]]
Exhibit 1--Contaminants on the Final CCL 4, Regulatory Determination 3, UCMR 2, UCMR 3 and Proposed UCMR 4
--------------------------------------------------------------------------------------------------------------------------------------------------------
CCL 4 Proposed UCMR
CASRN Chemical or chemical group nomination RD 3 short list UCMR 2 UCMR 3 4 \a\
--------------------------------------------------------------------------------------------------------------------------------------------------------
630-20-6............................... 1,1,1,2-Tetrachloroethane. ............... X ............... ............... ...............
75-34-3................................ 1,1-Dichloroethane........ ............... ............... ............... X ...............
96-18-4................................ 1,2,3-Trichloropropane.... ............... X ............... X ...............
106-99-0............................... 1,3-Butadiene............. ............... ............... ............... X ...............
123-91-1............................... 1,4-Dioxane............... ............... X ............... X ...............
57-91-0................................ 17 alpha-Estradiol........ ............... ............... ............... ............... ...............
71-36-3................................ 1-Butanol................. ............... ............... ............... ............... X
109-86-4............................... 2-Methoxyethanol.......... ............... ............... ............... ............... X
107-18-6............................... 2-Propen-1-ol............. ............... ............... ............... ............... X
16655-82-6............................. 3-Hydroxycarbofuran....... ............... ............... ............... ............... ...............
101-77-9............................... 4,4'-Methylenedianiline... ............... ............... ............... ............... ...............
30560-19-1............................. Acephate.................. ............... X ............... ............... ...............
75-07-0................................ Acetaldehyde.............. ............... ............... ............... ............... ...............
60-35-5................................ Acetamide................. ............... ............... ............... ............... ...............
34256-82-1............................. Acetochlor................ ............... X X ............... ...............
187022-11-3............................ Acetochlor ethanesulfonic ............... X X ............... ...............
acid (ESA).
194992-44-4............................ Acetochlor oxanilic acid ............... X X ............... ...............
(OA).
107-02-8............................... Acrolein.................. ............... ............... ............... ............... ...............
142363-53-9............................ Alachlor ethanesulfonic ............... X X ............... ...............
acid (ESA).
171262-17-2............................ Alachlor oxanilic acid ............... X X ............... ...............
(OA).
319-84-6............................... alpha- X ............... ............... ............... X
Hexachlorocyclohexane.
62-53-3................................ Aniline................... ............... ............... ............... ............... ...............
741-58-2............................... Bensulide................. ............... ............... ............... ............... ...............
100-44-7............................... Benzyl chloride........... ............... ............... ............... ............... ...............
25013-16-5............................. Butylated hydroxyanisole.. ............... ............... ............... ............... X
133-06-2............................... Captan.................... ............... ............... ............... ............... ...............
14866-68-3............................. Chlorate.................. ............... X ............... X ...............
74-87-3................................ Chloromethane (Methyl ............... ............... ............... X ...............
chloride).
110429-62-4............................ Clethodim................. ............... ............... ............... ............... ...............
7440-48-4.............................. Cobalt.................... ............... X ............... X ...............
80-15-9................................ Cumene hydroperoxide...... ............... ............... ............... ............... ...............
N/A.................................... Cyanotoxins \a\........... X ............... ............... ............... X
141-66-2............................... Dicrotophos............... ............... ............... ............... ............... ...............
55290-64-7............................. Dimethipin................ ............... ............... ............... ............... X
330-54-1............................... Diuron.................... ............... X ............... ............... ...............
517-09-9............................... Equilenin................. ............... ............... ............... ............... ...............
474-86-2............................... Equilin................... ............... ............... ............... X ...............
114-07-8............................... Erythromycin.............. ............... ............... ............... ............... ...............
50-28-2................................ Estradiol (17-beta ............... ............... ............... X ...............
estradiol).
50-27-1................................ Estriol................... ............... ............... ............... X ...............
53-16-7................................ Estrone................... ............... ............... ............... X ...............
57-63-6................................ Ethinyl Estradiol (17- ............... ............... ............... X ...............
alpha ethynyl estradiol).
13194-48-4............................. Ethoprop.................. ............... ............... ............... ............... X
107-21-1............................... Ethylene glycol........... ............... ............... ............... ............... ...............
75-21-8................................ Ethylene Oxide............ ............... ............... ............... ............... ...............
96-45-7................................ Ethylene thiourea......... ............... ............... ............... ............... ...............
50-00-0................................ Formaldehyde.............. ............... ............... ............... ............... ...............
7440-56-4.............................. Germanium................. ............... ............... ............... ............... X
74-97-5................................ Halon 1011 ............... ............... ............... X ...............
(bromochloromethane).
75-45-6................................ HCFC-22................... ............... ............... ............... X ...............
110-54-3............................... Hexane.................... ............... ............... ............... ............... ...............
302-01-2............................... Hydrazine................. ............... ............... ............... ............... ...............
7439-96-5.............................. Manganese................. X ............... ............... ............... X
72-33-3................................ Mestranol................. ............... ............... ............... ............... ...............
10265-92-6............................. Methamidophos............. ............... ............... ............... ............... ...............
67-56-1................................ Methanol.................. ............... ............... ............... ............... ...............
74-83-9................................ Methyl bromide ............... X ............... X ...............
(Bromomethane).
1634-04-4.............................. Methyl tert-butyl ether... X X ............... ............... ...............
51218-45-2............................. Metolachlor............... ............... X X ............... ...............
171118-09-5............................ Metolachlor ethanesulfonic ............... X X ............... ...............
acid (ESA).
152019-73-3............................ Metolachlor oxanilic acid ............... X X ............... ...............
(OA).
7439-98-7.............................. Molybdenum................ ............... X ............... X ...............
98-95-3................................ Nitrobenzene.............. ............... X ............... ............... ...............
55-63-0................................ Nitroglycerin............. ............... ............... ............... ............... ...............
872-50-4............................... N-Methyl-2-pyrrolidone.... ............... ............... ............... ............... ...............
55-18-5................................ N-Nitrosodiethylamine ............... X X ............... ...............
(NDEA).
62-75-9................................ N-Nitrosodimethylamine ............... X X ............... ...............
(NDMA).
621-64-7............................... N-Nitroso-di-n-propylamine ............... X X ............... ...............
(NDPA).
86-30-6................................ N-Nitrosodiphenylamine.... ............... X ............... ............... ...............
[[Page 81104]]
930-55-2............................... N-Nitrosopyrrolidine ............... X X ............... ...............
(NPYR).
25154-52-3 \b\......................... Nonylphenol............... X ............... ............... ............... ...............
68-22-4................................ Norethindrone (19- ............... ............... ............... ............... ...............
Norethisterone).
103-65-1............................... n-Propylbenzene........... ............... ............... ............... ............... ...............
95-53-4................................ o-Toluidine............... ............... ............... ............... ............... X
75-56-9................................ Oxirane, methyl-.......... ............... ............... ............... ............... ...............
301-12-2............................... Oxydemeton-methyl......... ............... ............... ............... ............... ...............
42874-03-3............................. Oxyfluorfen............... ............... ............... ............... ............... X
1763-23-1.............................. Perfluorooctane sulfonic ............... X ............... X ...............
acid (PFOS).
335-67-1............................... Perfluorooctanoic acid X X ............... X ...............
(PFOA).
52645-53-1............................. Permethrin................ X ............... ............... ............... X
41198-08-7............................. Profenofos................ ............... ............... ............... ............... X
91-22-5................................ Quinoline................. ............... ............... ............... ............... X
121-82-4............................... RDX....................... ............... X X ............... ...............
135-98-8............................... sec-Butylbenzene.......... ............... ............... ............... ............... ...............
107534-96-3............................ Tebuconazole.............. ............... ............... ............... ............... X
112410-23-8............................ Tebufenozide.............. ............... ............... ............... ............... ...............
13494-80-9............................. Tellurium................. ............... ............... ............... ............... ...............
59669-26-0............................. Thiodicarb................ ............... ............... ............... ............... ...............
23564-05-8............................. Thiophanate-methyl........ ............... ............... ............... ............... ...............
26471-62-5............................. Toluene diisocyanate...... ............... ............... ............... ............... ...............
78-48-8................................ Tribufos.................. ............... ............... ............... ............... X
121-44-8............................... Triethylamine............. ............... ............... ............... ............... ...............
76-87-9................................ Triphenyltin hydroxide ............... ............... ............... ............... ...............
(TPTH).
51-79-6................................ Urethane.................. ............... ............... ............... ............... ...............
7440-62-2.............................. Vanadium.................. ............... X ............... X ...............
50471-44-8............................. Vinclozolin............... ............... ............... ............... ............... ...............
137-30-4............................... Ziram..................... ............... ............... ............... ............... ...............
--------------------------------------------------------------------------------------------------------------------------------------------------------
\a\ Anatoxin-a, cylindrospermopsin, nodularin, total microcystin and several microcystin congeners are proposed for monitoring under UCMR 4.
\b\ The organization that nominated ``nonylphenol'' for CCL 4 provided the CASRN of 25451-52-3. The name ``nonylphenol'' does not allow for a definitive
identification of chemical structure since nonylphenol can exhibit two forms of isomerism. There are at least five CASRNs known to be associated with
``nonylphenol'': In addition to 25154-52-3 (which represents n-nonylphenol with the ortho-, meta-, or para-substitution unspecified), other CASRNs
include: 104-40-5 (4-n-nonylphenol); 84852-15-3 (4-nonylphenol, branched); 91672-41-2 (2-nonylphenol, branched); and 139-84-4 (3-n-nonylphenol). None
of these five CASRNs is adequately general enough to represent both forms of isomerism. For the sake of consistency, the CASRN provided by the
nominator was selected and the additional possible CASRNs and structures are delineated here.
------------------------------------------------------------------------
CCL 4
Microbe * nomination UCMR 3
------------------------------------------------------------------------
Adenovirus............................ X ...............
Caliciviruses......................... ............... X
Campylobacter jejuni.................. ............... ...............
Enterovirus........................... ............... X
Escherichia coli (O157)............... ............... ...............
Helicobacter pylori................... ............... ...............
Hepatitis A virus..................... ............... ...............
Legionella pneumophila................ ............... ...............
Mycobacterium avium................... ............... ...............
Naegleria fowleri..................... X ...............
Salmonella enterica................... ............... ...............
Shigella sonnei....................... ............... ...............
------------------------------------------------------------------------
* There were no CCL 4 microbes monitored under UCMR 2, and none are
proposed for monitoring under UCMR 4. The UCMR 4 Candidate
Contaminants Information Compendium (USEPA, 2015b) provides a
rationale for why contaminants, including microbes, were not included
in the proposed UCMR 4. No CCL 4 microbes were included in the RD 3
Short List. Norovirus, a member of the calicivirus family, was
included on UCMR 3 pre-screen testing.
III. Summary of the Approach Used To Identify and Evaluate Candidates
for the Draft CCL 4
The Draft CCL 4 was published in the Federal Register on February
4, 2015 (80 FR 6076 (USEPA, 2015a)). EPA used a three step evaluation
and selection process to identify candidates for the Draft CCL 4: (1)
Carry forward CCL 3 contaminants (except those with regulatory
determinations), (2) seek and evaluate nominations from the public for
additional contaminants to consider, (3) evaluate any new data for
those contaminants with previous negative regulatory determinations
from CCL 1 or CCL 2 for potential inclusion on the CCL 4. The CCL 3
process is summarized in section I.E.2. A brief summary of steps 1-3
that were used to develop the Draft CCL 4 is provided in the section
that follows, and a more detailed summary is provided in the Draft CCL
4 Federal Register notice (80 FR 6076 (USEPA, 2015a)). A summary of the
public comments on the Draft CCL 4 and EPA's responses can be found in
section IV.
[[Page 81105]]
A. Carry Forward of CCL 3 Contaminants to the Draft CCL 4
EPA carried forward all contaminants listed on CCL 3 to the Draft
CCL 4 with the exception of perchlorate, for which the agency made a
positive regulatory determination, and the five CCL 3 contaminants with
preliminary regulatory determinations at that time, pending their final
regulatory determinations. This carry forward process is consistent
with that previously used in CCL 2. The agency took this approach based
on the following considerations: (1) In developing the CCL 3, the
agency implemented a robust process recommended by the NRC and the
NDWAC to screen and score the universe of potential contaminants; (2)
EPA used the best available, peer reviewed data and information to
evaluate contaminants for CCL 3; and (3) Carrying forward CCL 3
contaminants allowed the agency to focus resources on evaluating
contaminants nominated by the public for CCL 4 and review new data for
CCL 1 or CCL 2 contaminants with previous negative regulatory
determinations (68 FR 42897, July 18, 2003 (USEPA, 2003); 73 FR 44251,
July 30, 2008 (USEPA, 2008b)). Carrying forward CCL 3 contaminants also
allowed EPA to focus resources on UCMR 3 monitoring and analysis and RD
3 analyses.
B. Summary and Evaluation of CCL 4 Nominated Contaminants
1. CCL 4 Nominations Summary
EPA sought public nominations in a Federal Register notice on May
8, 2012 (77 FR 27057), for contaminants to be considered for possible
inclusion in the CCL 4 (USEPA, 2012)). EPA received nominations for 59
unique contaminants for the CCL 4, including 54 chemical and five
microbial contaminants. After carefully reviewing and evaluating the
information and data for the nominated contaminants, EPA added two of
the nominated chemicals (manganese and nonylphenol) to the Draft CCL 4.
Detailed information on the nominations is contained in the ``Summary
of Nominations for the Fourth Contaminant Candidate List'' support
document (USEPA, 2016b).
2. How Nominated Contaminants Were Evaluated for the Draft CCL 4
Four nominated contaminants were already covered by a proposed or
existing NPDWR and were not eligible for the CCL 4 since the SDWA
specifies that the CCL only include those contaminants without any
proposed or promulgated NPDWRs. Seven of the nominated contaminants
were on CCL 3 and were carried forward to the Draft CCL 4. EPA reviewed
the nominations and supporting information to determine if any new data
were provided that had not been previously evaluated for CCL 3. The
agency also collected and evaluated additional data for the nominated
contaminants, when it was available, including the seven nominated
contaminants carried forward from CCL 3. The additional data was
obtained from both updated CCL 3 data sources and from new data sources
that were not available at the time the agency finalized CCL 3. These
data sources are listed in the ``Data Sources for the Contaminant
Candidate List 4'' support document (USEPA, 2016c).
Nominated contaminants with new data were screened and scored using
the same process used in CCL 3. Through this analysis, EPA added
manganese and nonylphenol to the Draft CCL 4 because, as discussed in
more detail in the Draft CCL 4 Federal Register notice (80 FR 6076
(USEPA, 2015a)), EPA determined that the new and updated health effects
information and additional occurrence data merited listing the
contaminants. Detailed information on the data used to screen the
nominated contaminants to determine whether or not they were included
in the PCCL 4 is available in the ``Screening Document for the PCCL 4
Nominated Contaminants'' (USEPA, 2016d). More detailed information on
the process and the data used to evaluate nominated contaminants for
listing on the CCL 4 can be found in the ``Contaminants Information
Sheets (CISs) for the Final Contaminant Candidate List 4 (CCL 4)''
support documents (USEPA, 2016e).
C. Evaluation of Previous Negative Regulatory Determinations for the
Draft CCL 4
EPA evaluated the 20 contaminants from CCL 1 and CCL 2 for which
the agency made negative regulatory determinations. EPA collected and
evaluated new or updated data for the previous negative regulatory
determination chemicals. Since RD 3 was recently published using the
best available data, EPA did not include the RD 3 negative regulatory
determinations in this evaluation. The agency concluded there was not
sufficient new information for 19 of the 20 contaminants with previous
negative regulatory determinations to justify including them on the
Draft CCL 4. Because commenters also did not identify such information,
EPA has not included these contaminants on the Final CCL 4. EPA added
manganese, a previous negative regulatory determination from RD 1, to
the Draft and Final CCL 4 as previously discussed in section III.B.
IV. What comments did EPA receive on the Draft CCL 4 and how did the
Agency respond?
EPA requested comment on the Draft CCL 4 and how to further improve
upon the selection process developed for CCL 3 as a tool for future
CCLs. The agency received 27 public comment letters on the Draft CCL 4.
EPA considered all public comments and evaluated the data and
information provided by commenters in selecting the Final CCL 4. EPA
used the same process used in the CCL 3 to screen and score any
contaminants with new data or information provided by commenters. EPA
prepared responses to all public comments that are in the ``Comment
Response Document for the Fourth Drinking Water Contaminant Candidate
List (Categorized Public Comments)'' document, which is available in
the docket for this action (USEPA, 2016f).
Based on the analyses conducted as a result of public comments, EPA
determined not to list three cancelled pesticides (disulfoton,
fenamiphos, and molinate) on the Final CCL 4 that were included on the
Draft CCL 4 because, as discussed more fully in the following sections,
these chemicals are not known or anticipated to occur in PWSs and are
not anticipated to require regulation. With the exception of these
three pesticides, all of the contaminants listed on the Draft CCL 4 are
listed on the Final CCL 4.
A summary of some of the key public comments received,
recommendations from EPA's Science Advisory Board (SAB) on the CCL 4,
and EPA's responses are provided in this section. Data used to evaluate
the contaminants for the CCL 4 can be found in the Contaminant
Information Sheets (CISs) for the Final Fourth Contaminant Candidate
List (CCL 4) (USEPA, 2016e), which can be found in the docket for this
action available at www.regulations.gov by searching for docket EPA-HQ-
OW-2012-0217.
A. Recommendations From the EPA Science Advisory Board
The EPA SAB and its Drinking Water Committee (DWC) reviewed the
Draft CCL 4 and provided recommendations to the Administrator on
January 11, 2016, in their report ``Review of the EPA's Draft Fourth
Drinking Water Contaminant Candidate List (CCL 4)'' (USEPA, 2016g). On
April 29-30, 2015, the SAB DWC held a public meeting to discuss
responses to EPA charge
[[Page 81106]]
questions. During this meeting, EPA provided an overview of the process
used to develop the Draft CCL 4 and answered questions from the
Committee.
The SAB's recommendations and comments on the overall CCL 4 process
and documentation are summarized in the following bullet points:
The SAB stated that the general protocol used to evaluate
contaminants on the CCL 4 is well described and conceptually clear.
They concluded the transparency and clarity of the process has improved
since CCL 3 was finalized.
The SAB said that the documentation for CCL 4 lacked
specific information necessary in order to follow the decision-making
process for listing an individual contaminant on the Draft CCL 4.
Specific suggestions to improve transparency and clarity of the support
documents include:
[cir] Develop a summary table that consolidates summary information
on all carried forward and nominated contaminants.
[cir] Display results of the CCL 4 screening and classification
process in a manner that explicitly outlines the scoring schemes used
and the scientific rationale in applying the selection criteria.
[cir] Provide examples for both microbial and chemical contaminants
that display the process of how contaminants were included on or
eliminated from the Draft CCL 4.
[cir] Clearly describe and improve the process for removing
contaminants from prior CCLs, where appropriate, when such lists serve
as the basis for a new CCL.
[cir] Explain the evaluation of CCL contaminants during the RD
process.
The SAB recommended that EPA should utilize data from UCMR
3 monitoring as it becomes available.
The SAB stated that the CCL 4 list includes a number of
contaminants carried forward from the CCL 3 without providing a sense
of the relative priority of the listed chemicals. The SAB recommended
EPA prioritize the list to inform future regulatory decision-making and
to help researchers focus their efforts.
EPA Response: EPA has provided a more detailed response to the SAB
in the document, ``Response to SAB recommendations on the Draft CCL 4''
(USEPA, 2016h), which can be found in the docket for this action
available at www.regulations.gov by searching for docket EPA-HQ-OW-
2012-0217. This section summarizes EPA's response to some of the key
SAB recommendations.
The agency has updated the technical support documents for the CCL
4 to increase the transparency of its decisions relative to the
contaminants included on the Final CCL 4. For instance, the CIS support
document provides examples showing the criteria and process for
including or excluding chemical and microbial contaminants from the CCL
4. Additionally, a summary table in the same support document presents
factors used to determine how the CCL 4 contaminants were selected. The
agency also summarizes the process used to evaluate contaminants under
RD 3 in section I.E.3 of this notice.
While EPA agrees with the SAB about the importance of using UCMR
data to inform the CCL, the agency does not believe it is appropriate
to use preliminary UCMR 3 data to make final CCL 4 decisions. The UCMR
3 data set was not finalized within the timeframe for use and analysis
under CCL 4. The UCMR 3 monitoring period ended in December 2015 and
results are reported to EPA through 2016. After the monitoring period
is completed, the results undergo review for quality assurance and are
subject to change following further review by the analytical
laboratory, the PWS, the State and EPA. The agency will perform further
analysis of both the health effects and occurrence of contaminants
monitored under UCMR 3 during the RD 4 and CCL 5 development process.
EPA identified the current occurrence, health effects and
analytical methods data needs of CCL 4 contaminants for RD 4
evaluations in section V of this notice. This data needs table is
presented to provide a sense of relative priority for listed
contaminants by identifying those contaminants likely to have
sufficient data for further evaluation under the next RD and those that
have research needs. As the agency continues to evaluate contaminants
on the CCL 4, EPA will work with agency and non-EPA scientists to
develop and collect the best available science to support decision-
making for future determinations.
B. Public Comments
1. General Comments on CCL 4
EPA received comments, both in support of and against the carry
forward of contaminants from the CCL 3 to the Draft CCL 4. One
commenter asked for more information on the decision to carry forward
CCL 3 contaminants to the Draft CCL 4. Commenters not in support of the
carry forward of CCL 3 contaminants thought EPA should reassess the
science on all the CCL 3 contaminants. One commenter also thought EPA
should limit the number of contaminants on the CCL so that research for
the contaminants could be completed between one CCL and the next. One
commenter supported the carry forward approach because the CCL 3
contaminants already have data available that shows there may be a
potential public health impact. They also suggested that EPA should
continue to evaluate these contaminants until enough data are collected
to support a regulatory determination.
EPA response: The reasons for carrying forward contaminants from
the CCL 3 to the CCL 4 are presented in section III.A of this notice.
EPA has continued to collect data and further evaluate the science for
many of the contaminants that were carried forward from the CCL 3 to
the CCL 4. For example, since the listing of contaminants on CCL 3, EPA
has monitored and collected occurrence data for several CCL
contaminants through the UCMR program. EPA has also further analyzed
and evaluated many of the CCL 3 contaminants that were carried forward
to CCL 4 under the RD 3 process. Exhibit 1 in section II.A of this
notice lists CCL 4 contaminants that were evaluated under these other
agency efforts. Although EPA carried forward contaminants from the CCL
3 to the CCL 4, EPA intends to collect new data and conduct further
evaluations of unregulated contaminants for CCL 5.
EPA does not agree that the CCL should be limited to a certain
number of contaminants. The CCL identifies contaminants that are
``known, or anticipated to occur in PWSs,'' and is the first step in
identifying contaminants that may require regulation. Some of the
contaminants on the list may have sufficient information to make
regulatory determinations in the near term and some of the contaminants
on the list need additional data in order to determine the appropriate
agency action. While the SDWA does not limit the CCL to a particular
number of contaminants, the agency recognizes the need to communicate
data needs for contaminants included on the Final CCL 4. Therefore, EPA
has provided a summary of the current data needs for RD 4 evaluations
in section V of this notice. The agency will continue to evaluate data
needs through the RD 4 process and will continue to work with internal
and external researchers to discuss research needs and priorities.
2. Chemical Contaminants
a. Contaminants With Release Data
EPA received comments that several contaminants listed based on
[[Page 81107]]
environmental release data for evaluating occurrence (e.g., ethylene
oxide, ethylene glycol, and toluene diisocyanate) should not be on the
CCL 4 because one or more of their intrinsic physical or chemical
properties would result in limited occurrence in water. Commenters
cited the hydrolysis and biodegradation rate, or quick volatilization
from water as reasons these chemicals should be removed from the Final
CCL 4. Additionally, commenters noted that some of these contaminants
have relatively short half-lives in water or may not be long-lived in
the environment and thus should not be listed on the Final CCL 4.
EPA Response: EPA is including ethylene oxide, ethylene glycol, and
toluene diisocyanate on the Final CCL 4 because these contaminants may
be anticipated to occur in PWSs and may require regulation. Although no
occurrence information in finished or ambient water is available for
these contaminants, to be consistent with the CCL 4 protocol, EPA used
total environmental release data reported in the TRI to evaluate and
score the occurrence attributes. In response to comments citing that
EPA should consider physical and chemical properties, EPA conducted
additional analyses that considers physical and chemical properties and
environmental fate parameters to provide an alternate score for the
magnitude attribute. For this additional analysis on the specific
contaminants commented on (e.g., ethylene oxide, ethylene glycol, and
toluene diisocyanate), EPA used the persistence and mobility scoring
protocol (which is the protocol used for those chemicals with only
production data) as the basis for scoring the magnitude attribute as
described in the Final CCL 3: Classification of the PCCL to the CCL
(USEPA, 2009e), available in the docket for this action. The model
results for these contaminants using this alternate magnitude score
still indicated that the contaminants should be listed (for a summary
of how the classification model results were used to select
contaminants for CCL 4, please see USEPA, 2016e, available in the
docket for this action). These additional analyses are further
described in the ``Comment Response Document for the Fourth Drinking
Water Contaminant Candidate List (Categorized Public Comments)''
document, which is available in the docket for this action (USEPA,
2016f). Additionally, as the SAB (USEPA, 2016h) noted, ``contaminants
with a half-life in drinking water sources of days to weeks may still
pose a public health concern.''
Considering the comments received on the Draft CCL 4, in future
CCLs, EPA may refine analyses to consider if physical and chemical
properties can be incorporated into the evaluations of contaminants
listed based on environmental release data for occurrence.
b. Cyanotoxins
EPA received comments supporting the inclusion of cyanotoxins on
the CCL 4. Some comments requested that cyanotoxins be listed by
individual toxins rather than including cyanotoxins as a group on the
Final CCL 4 in order to prioritize research on health effects,
analytical methods, occurrence and treatment. Comments specifically
requested listing the key variants of microcystins, cylindrospermopsin,
anatoxin-a, saxitoxin and euglenophycin.
EPA Response: EPA agrees that cyanotoxins should be included on the
CCL 4, and has included cyanotoxins as a group on the Final CCL 4. The
group of cyanotoxins includes all toxins produced by cyanobacteria
including but not limited to microcystins, cylindrospermopsin,
anatoxin-a and saxitoxin. EPA has provided CIS sheets for microcystin-
LR, cylindrospermopsin, anatoxin-a and saxitoxin. Under CCL 3,
cyanotoxins were listed as a group and EPA released CIS sheets for
microcystin-LR, cylindrospermopsin and anatoxin-a. Based on data
submitted in public comments, EPA updated previous CIS sheets and
developed a CIS sheet for saxitoxin. EPA was unable to develop a CIS
sheet for euglenophycin due to insufficient information on health and
occurrence. EPA acknowledges the comments to list specific cyanotoxin
compounds on the CCL instead of listing cyanotoxins as a group.
However, because of the similar sources of cyanotoxins (i.e.,
cyanobacteria) their management may be similar. Furthermore, due to
significant information gaps for some cyanotoxins (e.g., euglenophycin
and nodularin and many microcystin congeners), EPA has determined it
most appropriate to continue to list cyanotoxins as a group at this
time. EPA agrees that microcystins, cylindrospermopsin, anatoxin-a and
saxitoxin can be of concern for drinking water supplies. EPA
acknowledges associated data gaps for euglenophycin as well as those
for other cyanotoxins. EPA included total microcystins and six
microcystin congeners (-LA, -LF, -LR, -LY, -RR, and -YR),
cylindrospermopsin, anatoxin-a and nodularin on the proposed UCMR 4 for
monitoring by PWSs. The occurrence information collected under the UCMR
4 will be used to further evaluate the appropriate agency regulatory
determination and research actions.
c. Perfluorinated Compounds (PFOA and PFOS)
EPA received a comment supporting the inclusion of
perfluorooctanoic acid (PFOA) and perfluorooctane sulfonic acid (PFOS)
on the CCL 4. EPA also received comments that PFOS and/or PFOA should
not be listed on the Final CCL 4. The commenter supporting inclusion of
these chemicals on the CCL 4 cited their persistence in the environment
and toxicological effects as reasons to include them on the Final CCL
4, and encouraged EPA to consider these chemicals for drinking water
regulation. Commenters supporting removal of PFOA and/or PFOS from the
CCL 4 cited the low frequency of detections of PFOA and/or PFOS under
the UCMR 3 monitoring as of January 2015. Additional reasons cited by
commenters that these chemicals should not be listed on the Final CCL 4
are the voluntary efforts by manufacturers to reduce emissions and work
towards elimination of these chemicals from products.
EPA Response: EPA is including PFOA and PFOS on the Final CCL 4
because these contaminants are known to occur in drinking water, are
persistent in the environment and in the human body, have shown to be
toxic in animal studies and may require regulation.
As discussed in the summary of EPA responses to the SAB in this
section (IV.A) of the notice, EPA did not use preliminary UCMR 3
monitoring results for the CCL 4.
EPA acknowledges the industry commitments to voluntarily reduce the
use and production of PFOA and PFOS; however, there are still a limited
number of ongoing uses of PFOA and PFOS. Additionally, these chemicals
are persistent in the environment and in the human body, which
indicates they may be present in water or migrate to drinking water
sources even after uses and production have been reduced or ceased, and
therefore potential exposure may still be of concern.
In May 2016, EPA released lifetime health advisories for PFOA and
PFOS (USEPA, 2016i, available in the docket for today's action) and
Health Effects Support Documents based on the agency's assessment of
the latest peer reviewed science. The health advisories provide
federal, state, tribal and local officials with information on the
health risks of these chemicals, occurrence,
[[Page 81108]]
analytical methods and treatment technologies so that they can
determine what actions to take to protect consumers.
In accordance with the SDWA, EPA will consider the occurrence data
from the final UCMR 3 data set, along with the peer reviewed health
effects assessments supporting the May 2016 PFOA and PFOS Health
Advisories, to make a regulatory determination whether or not PFOA and
PFOS require NPDWRs.
d. Pesticides
Several public commenters requested that specific pesticides be
removed from the Final CCL 4. EPA agrees with commenters that three of
these pesticides (disulfoton, fenamiphos, and molinate) should not be
listed on the Final CCL 4; therefore, EPA is removing them from the
Final CCL 4. The evaluation of these three pesticides is summarized in
the following paragraphs.
(i) Disulfoton
EPA received a comment from the public that disulfoton should not
be included on the Final CCL 4. The commenter noted that disulfoton had
zero or very few detections nationally on any previous round of UCMR
monitoring and therefore does not warrant national regulation.
EPA Response: EPA agrees with the commenter that disulfoton should
not be included on the Final CCL 4. Disulfoton sales and distribution
were cancelled in the U.S., effective December 31, 2010, with remaining
product stocks to be used until depleted (74 FR 48551, September 23,
2009 (USEPA, 2009g)). The UCMR 1 finished water screening survey (SS)
found no detections of disulfoton in 2,300 samples from 295 PWSs. The
United States Geological Survey (USGS) has detected disulfoton
infrequently in ambient water. During the 1992-2001 USGS National
Water-Quality Assessment (NAWQA) Program monitoring, disulfoton was
detected in only 17 sites out of 7,118 ambient water sites sampled (see
the CIS for this contaminant (USEPA, 2016e)). Out of the 17 sites with
detections, only two sites had detects at levels greater than the
health reference level of potential concern for drinking water. Given
that disulfoton was detected in those two sites prior to its
cancellation, the agency expects that any potential disulfoton
occurrence in water will likely continue to decrease in the future.
Although persistent environmental contaminants may occur in a PWS after
its uses are cancelled, based on its physical and chemical properties,
disulfoton has low to moderate mobility in water and it is only
moderately persistent in the environment (see the CIS for this
contaminant (USEPA, 2016e), which can be found in the docket for this
action). Therefore its occurrence is expected to decrease over time.
EPA is not including disulfoton on the Final CCL 4 because it is
not known or anticipated to occur in drinking water. Disulfoton likely
has low potential for public health concern based on its cancellation
status, zero detections in PWSs (from UCMR 1 data), and very few
detections in ambient water from a large number of sites sampled (by
the USGS NAWQA program).
(ii) Fenamiphos
EPA received a comment from the public that fenamiphos should not
be included on the Final CCL 4. The commenter stated that the
registrant for fenamiphos agreed to cancel all uses, and all existing
stocks are to be used by October 6, 2017. The commenter stated that
very limited uses remain of products containing fenamiphos in the U.S.
and use will be discontinued after 2017.
EPA Response: EPA agrees with the commenter that fenamiphos should
not be included on the Final CCL 4 because it is not anticipated to
occur in drinking water and is not likely to require regulation.
Fenamiphos product registrations were cancelled, and the sale and
distribution of fenamiphos by the registrant was prohibited on May 31,
2007. This cancellation followed a five- year phase-out period,
beginning in 2003, intended to limit and reduce production of
fenamiphos. The sale and distribution of any remaining stocks will be
prohibited after October 6, 2017 (79 FR 59262, October 1, 2014; USEPA,
2014c). Fenamiphos was not monitored under UCMR, thus no national scale
monitoring has been conducted in PWSs. While fenamiphos was not
included in the USGS NAWQA national-scale ambient water monitoring
(1992-2001), based on the USGS Pesticide National Synthesis Project
(USGS, 2012), fenamiphos use is estimated to have steadily declined.
The USGS estimated a usage level of approximately 1.0 million pounds/
year of widespread use in certain regions per year in 1992, which
declined to an estimated 0.2 million pounds/year in 2002 and further
declined to an estimated 0.03 million pounds/year of limited regional
uses in 2012. EPA expects fenamiphos occurrence in water will likely
continue to decrease due to the declining trend in usage for many years
and the prohibition on usage of existing stocks in the U.S. effective
after October 6, 2017.
In summary, due to its registration cancellation status,
significant decline in usage (based on estimated data from 1992-2013),
moderate persistence in the environment, and the prohibition of
existing stocks (effective after October 6, 2017), EPA does not
anticipate fenamiphos to occur in PWSs or to require regulation,
therefore, it is not included on the Final CCL 4.
(iii) Molinate
EPA received a comment from the public that molinate should not be
included on the Final CCL 4. The commenter noted that molinate had zero
or very few detections nationally on any previous round of UCMR
monitoring and therefore does not warrant national regulation.
EPA Response: EPA agrees with the commenter that molinate should
not be included on the Final CCL 4. The UCMR 1 finished water
assessment monitoring found only one sample with a detection of
molinate out of 33,799 samples taken from 3,873 PWSs. The single sample
detection was below the health reference level of potential concern for
molinate in drinking water. Further, molinate sales and distribution
were cancelled in the U.S. effective July 1, 2009, with remaining
stocks required to be used by August 31, 2009, (73 FR 44261, July 30,
2008 (USEPA, 2008c)). This cancellation action concluded a six-year
scheduled phaseout of molinate. The agency is not including molinate on
the Final CCL 4 because it is not anticipated to occur in PWSs at
levels of public health concern. The agency expects the potential for
molinate to occur in water will likely continue to decrease due to the
prohibition on product use in the U.S. since 2009.
e. Manganese
EPA received four comments that support the inclusion of manganese
and two comments that do not support the inclusion of manganese on CCL
4. Commenters supporting the inclusion of manganese on CCL 4 cited
recent studies that showed neurological effects in children and infants
exposed to excess manganese via drinking water. Commenters also noted
manganese frequently occurs in water and should be included on CCL 4 so
that national occurrence data can be obtained through UCMR monitoring.
Commenters who did not support the inclusion of manganese on the CCL 4
cited that the primary route of human exposure to manganese is through
food, not drinking
[[Page 81109]]
water. Also, commenters question the link between the consumption of
drinking water and developmental neurotoxicity from manganese exposure
to warrant inclusion on the CCL 4.
EPA Response: EPA agrees with the commenters that support manganese
inclusion on the CCL 4, and is including manganese on the Final CCL 4
because it is known to occur in PWSs and may require regulation. The
evidence from the studies provided by commenters indicate that exposure
to excess manganese may present a substantial health threat to children
and infants. EPA is continuing to evaluate the potential risks to
children and infants based on over 30 recent studies cited by the
public during the nomination and comment period including those by
Bouchard et al. (2011), Oulhote et al. (2014) and Kern and colleagues
(2010, 2011), whom have indicated neurological effects stemming from
the exposure to excess manganese.
EPA also agrees with the commenters assertion that manganese is
known to occur in PWSs. EPA has included the occurrence data used to
evaluate manganese in the CIS for this contaminant. This data includes
USGS monitoring of ambient water, as well as drinking water data from
several states. The data indicates that manganese is known to occur in
public drinking water supply wells and supports the previous
information from the National Inorganics and Radionuclides Survey
(NIRS). EPA has proposed to monitor manganese under UCMR 4.
EPA has reviewed all of the current data submitted by commenters on
the manganese health effects and found that the existing 2004 Health
Advisory could warrant an update. Since manganese is not a regulated
contaminant in drinking water, the Secondary Maximum Contaminant Level
of 0.05 mg/L is not mandatory and does not require monitoring. The
current IRIS assessment for manganese dates to 1995 (USEPA, 1995b) and
the Health Advisory to 2004. The Agency for Toxic Substances and
Disease Registry 2012 Toxicological Profile did not establish
guidelines that applied to oral exposures and the Institute of Medicine
(2001) provides Tolerable Upper Intake Levels for developmental
lifestages and adults. The database of health effects studies for oral
manganese exposures has expanded considerably since the last EPA
assessment, therefore manganese is a good candidate for re-evaluation.
EPA intends to evaluate the new toxicological findings and UCMR 4
monitoring data and will use this information in future regulatory
decision-making, and to revise the current Health Advisory, if
appropriate. More detailed evaluations of the routes of exposure
usually occur in the regulatory determination and regulatory
development processes.
f. Nonylphenol
EPA received two comments supporting the inclusion of nonylphenol
and three comments that nonylphenol should not be included on the Final
CCL 4. The commenters supporting inclusion of nonylphenol on the CCL 4
cited new health effects and occurrence data as reasons to include them
on the Final CCL 4 and stated that EPA has adequate justification to
include nonylphenol on the CCL based on this information. The
commenters requesting that nonylphenol not be included on the Final CCL
4 cited a surface water monitoring study from 2002 and industry efforts
to reduce surfactant usage as reasons nonylphenol should not be listed
on the Final CCL 4. The main use of nonylphenol is in the manufacture
of nonylphenol ethoxylates, which have been used in a wide range of
industrial applications and consumer products including laundry
detergents, cleaners, degreasers, paints and coatings and other uses
(79 FR 59186, October 1, 2014 (USEPA, 2014d)).
EPA Response: EPA is including nonylphenol on the Final CCL 4 as
proposed because it is anticipated to occur in drinking water, has
potential adverse health effects (Bontje et al., 2005), and may require
regulation. EPA evaluated the 2002 USGS reconnaissance study (Kolpin et
al., 2002) identified by the commenter and used it to evaluate the
occurrence of nonylphenol. While there were more recent finished water
studies available, EPA considers the 2002 USGS study as the most
appropriate study to evaluate the occurrence of nonylphenol for CCL 4
given the greater number of samples and larger geographic scale.
Additionally, more recent studies indicate that nonylphenol has been
detected in drinking water. While EPA appreciates the information from
commenters on reduced usage of nonylphenol, we believe measured
occurrence data from water sources are preferred over production or
usage information when evaluating the likelihood of occurrence in
drinking water.
3. Microbial Contaminants
a. Overall Process Comments
EPA received comments arguing that the follow-through on the
microbes listed in previous CCLs has been inadequate, that EPA should
identify high priority pathogens on the CCL 4 and identify information
gaps and barriers to obtaining information associated with each
pathogen. EPA received comments requesting an open process for
prioritizing and collecting information, to adopt a collaborative
method development process and to rank microbes by treatability. EPA
also received comments to focus priorities on distribution and plumbing
system biofilm concerns and to evaluate microbial contaminants in the
context of diverse water supplies such as drinking water sources from
water reuse treatment facilities.
EPA Response: EPA's criteria for evaluating and prioritizing
pathogens for inclusion in the CCL 3 included health effects,
waterborne disease outbreaks (WBDO) and occurrence information (73 FR
9628 (USEPA, 2008a)). EPA developed and implemented a systematic
strategy and set of criteria for selecting the pathogens for CCL 3.
This is the screening and scoring process described in detail in the
support documents in the docket of the Final CCL 3 (e.g., see the Final
Contaminant Candidate List 3 Microbes: PCCL to CCL Process for more
information on all of the scores). The CCL 3 and CCL 4 processes
provided multiple opportunities for public input (e.g., nominations,
public comment) to allow for an open process. In order to provide
additional clarity to the scoring process, EPA is including an example
schematic describing the process of evaluating a pathogen for inclusion
on the list and a pathogen for exclusion from the list. This schematic
can be found in the CIS's for the Final Fourth Contaminant Candidate
List (USEPA, 2016e). EPA acknowledges the request to identify
information gaps; therefore, data needs are described in section V of
this Federal Register notice.
The EPA's Office of Water coordinates with EPA's Office of Research
and Development to discuss research needs and priorities. Research on
distribution system and premise plumbing biofilm concerns has been
incorporated into EPA's strategic research plan. EPA acknowledges the
comments on diverse water supplies and method development and will
consider these comments as it develops future research priorities.
b. Pathogens for Inclusion
EPA received comments supporting the proposed inclusion of
Mycobacterium avium, Legionella pneumophila, Naegleria fowleri,
enteroviruses and Heterotrophic Plate Count (HPC). EPA also received
[[Page 81110]]
comments requesting recommendations for Legionella pneumophila
management.
EPA Response: EPA included Mycobacterium avium, Legionella
pneumophila, Naegleria fowleri, and enteroviruses on the Final CCL 3
and were therefore carried forward to the draft and Final CCL 4. While
the broader issue of the management of Legionella pneumophila is
outside the scope of today's action, the agency agrees it is of great
importance and Legionella remains a risk to building water systems. In
September 2016, EPA released a document reviewing the available
technology to treat Legionella titled Technologies for Legionella
Control in Premise Plumbing Systems: Scientific Literature Review
(USEPA, 2016j). This document provides information to state and local
decision-makers about how they might utilize treatment as part of their
efforts to manage Legionella risks in building water systems.
EPA disagrees that HPC should be included on CCL 4. The group of
HPC usually includes a diverse group of microorganisms that are part of
the natural environment in water. Available epidemiological evidence
shows no relationship between gastrointestinal illness and HPC bacteria
in drinking water (Calderon, 1988; Calderon and Mood, 1991; Payment et
al., 1997; Bartram J et al., 2003). Thus, EPA considers the potential
health risk of HPC bacteria in drinking water as likely negligible and
is not including HPC on the Final CCL 4. In addition, HPC bacteria are
addressed under the Surface Water Treatment Rule as a treatment
technique where they can be monitored in lieu of a disinfectant
residual because HPC is an alternative method of determining
disinfectant residual levels.
c. Pathogens for Exclusion
EPA received comments not supporting the proposed inclusion of
Escherichia coli O157 and Helicobacter pylori, noting these pathogens
were unlikely to occur in treated drinking water.
EPA Response: EPA's criteria for evaluating and prioritizing
pathogens for inclusion in the Draft CCL 3 Federal Register notice,
included health effects, WBDO and occurrence information (73 FR 9628
(USEPA, 2008a)). Treatability was not part of the scoring criteria
considered for CCL 3 inclusion. Although some of the microbes listed in
the Draft CCL 4 may be well controlled by drinking water treatment
(i.e., disinfection), not all PWSs in the U.S. are required to treat.
For example, approximately thirty percent of the 40,000 community
ground water systems do not have disinfection treatment (USEPA, 2013).
For the reasons discussed in detail in the Draft CCL 3 Federal Register
notice (73 FR 9628 ((USEPA, 2008a)), EPA did not preclude pathogens
from CCL 3 and CCL 4 based on their potential to be controlled by
existing treatment technique regulations.
V. Data Needs for CCL 4 Contaminants
After the listing process, the CCL 4 contaminants will be further
evaluated in a separate action called Regulatory Determination 4 (RD
4). The process used to previously evaluate CCL 3 contaminants under RD
3 is described in section I.E.3 of this notice. EPA anticipates using a
similar process to evaluate CCL 4 contaminants under RD 4, although it
is possible that some modifications may be made to this process. In the
initial phases of this process, EPA determines if sufficient data are
available to meet the three RD criteria set forth in SDWA section
1412(b)(1) and previously outlined in section I.D.4 of this notice. If
sufficient data are available to meet all three statutory criteria, a
regulatory determination may be made. As discussed in section I.D.4,
SDWA requires EPA to make regulatory determinations every five years on
at least five CCL contaminants.
The SAB and other commenters have recommended additional
prioritization of the CCL 4 contaminants to communicate research needs,
help focus efforts for researchers, and inform future regulatory
decision-making. EPA acknowledges that many contaminants on the CCL 4
have substantial data and information needs to fulfill in order for the
agency to make a regulatory determination in accordance with SDWA 1412
(b)(1)(A). These current data needs are described in the following
section, and are presented in Exhibit 2. By identifying those
contaminants that need additional research and information, EPA is
communicating to stakeholders both research priorities and gaps for
these contaminants.
Categorization of Contaminants
EPA assessed the data and information gathered on the CCL 4
contaminants and generated a table (Exhibit 2) to help identify data/
information needs for further evaluation under RD 4. To develop this
table, EPA began with the information contained in the data
availability/Phase 1 table included in Appendix D of the Protocol for
the RD 3 (USEPA, 2014b), which describes the status of the best
available occurrence data and health effects assessments for CCL 3
contaminants. EPA updated the occurrence data needs for CCL 4
contaminants by including which contaminants were monitored on the UCMR
3, and updated the health effects data needs based on available EPA or
other non-EPA peer reviewed assessments as of May 2016. Since manganese
and nonylphenol were nominated and added to the CCL 4 (not carried
forward from CCL 3), data collected under CCL 4 was included in the
Contaminant Information Sheets (USEPA, 2016e) for these contaminants
and was used to assess the data needs. EPA characterized each chemical
contaminant included on the Final CCL 4 based on their health effects,
occurrence and analytical methods data needs.
EPA then categorized contaminants into six categories depending
upon the availability of their occurrence data and health assessment.
Contaminants in Group A have nationally representative finished
drinking water data and a peer reviewed health assessment and are
likely to have sufficient data available to be placed on a short list
for further assessment under RD 4. Contaminants in Group B have
finished drinking water data that is not nationally representative and
peer reviewed health assessments. These contaminants may have
sufficient data to be placed on a short list for further assessment
under RD 4, particularly if the non-nationally representative
occurrence data shows detections at levels of public health concern.
Contaminants in groups C, D, E, and F of Exhibit 2 that lack either a
peer reviewed health assessment or finished water data have more
substantial data needs and are unlikely to have sufficient information
to allow further assessment under the RD 4. For these contaminants, EPA
plans to identify them as research priorities and work to fill their
research needs such as evaluating the potential for monitoring under
the UCMR or identifying those contaminants as priorities for health
effects research. The health effects and occurrence data sources used
to classify data needs are featured in Appendix 6 of the CISs for the
Final Fourth CCL in the docket (USEPA, 2016e). The following sections
describe the types of data or information gaps outlined in Exhibit 2
and provide examples.
A. Health Effects
Under the RD process, EPA relies on external peer-reviewed health
assessments to determine if and at what level a contaminant ``may have
an adverse effect on the health of persons.'' Health effects data
sources evaluated for
[[Page 81111]]
RD 3 included EPA health assessments, or peer reviewed health
assessments developed by other organizations such as the National
Academy of Sciences, the Agency for Toxic Substances and Disease
Registry, World Health Organization, the California EPA's Office of
Environmental Health Hazard Assessment, Registry of Toxic Effects of
Chemical Substances, and/or supplemental data from a single study, if
the health assessment is peer reviewed and uses comparable methods,
standards and guidelines to an EPA health assessment.
As shown in Exhibit 2, EPA categorized the health effects data
needs in the following way:
1. If a peer reviewed health assessment is available or is in the
process of being revised, the contaminant is considered to have health
effects data available.
2. If a peer reviewed health assessment is not available, then the
contaminant is considered to not have health effects data currently
available.
B. Occurrence
For RD evaluations, the occurrence data availability assessment is
used to identify contaminants that may have sufficient data and
information to characterize their status as known or likely to occur in
PWSs. EPA uses data from many sources to evaluate occurrence for
contaminants considered for RD (see Appendix C of USEPA, 2014b for
occurrence data sources evaluated under RD 3). For this evaluation, EPA
prefers to have nationally representative finished drinking water
occurrence data, but finished drinking water data that are not
nationally representative may also be used to determine if the
contaminant occurs frequently at levels of public health concern. In
addition, the agency evaluates supplemental sources of information
(e.g., ambient/source water occurrence, production/use and
environmental release data). For the purposes of identifying current
data needs for RD 4, as shown in Exhibit 2, EPA categorized the
occurrence data needs in the following way:
Finished drinking water occurrence data that are
nationally representative are available.
[cir] Data sources may include UCMRs (i.e., UCMR 1, UCMR 2 and UCMR
3), the Unregulated Contaminant Monitoring Program (Round 1 and Round
2) and NIRS.
Finished drinking water occurrence data that are not
nationally representative are available. These data may include:
[cir] Finished water assessments by federal agencies (e.g., EPA,
the U.S. Department of Agriculture and USGS). These may include
assessments that are geographically distributed across the nation but
are not intended to be statistically representative of the nation
(e.g., the Disinfection By-Product Rule Information Collection
Request).
[cir] State-level finished water monitoring data.
[cir] Research performed by institutions and universities (e.g.,
scientific literature), including targeted or local monitoring studies.
[cir] Various reports from the Centers for Disease Control and the
scientific literature for microbes.
Finished drinking water occurrence data are not available.
[cir] The best available data sources may include environmental
release data (such as TRI data or pesticide application data) or
ambient water data.
EPA has also indicated with a footnote in the occurrence data
column, highlighting which contaminants are proposed for monitoring
under the UCMR 4 from 2018-2020. Therefore, although some of the
contaminants that may be monitored under UCMR 4 are shown in this table
as currently having data gaps for occurrence (e.g., they only have
drinking water data that is not nationally representative or release
data), EPA has proposed to fill those occurrence data needs for future
RD evaluations.
C. Analytical Methods
To conduct nationally representative drinking water occurrence
studies that could support a regulatory determination, EPA needs to
have an analytical method that is suitable for the drinking water
matrix and is robust enough to be used by many laboratories to conduct
national studies and/or compliance monitoring. For the purpose of CCL
4, EPA assessed the status of the development of analytical methods for
drinking water and determined estimated reporting levels for each
contaminant. EPA also assessed method sensitivity with respect to the
HRL for the chemical contaminants. Method sensitivity is measured by
using method specific reporting levels, lowest concentration minimum
reporting levels, and promulgated minimum reporting level. While there
are many methods for monitoring the CCL 4 pathogens available from
scientific papers and consensus organizations, not all of them may be
appropriate for use in drinking water or for a national monitoring
effort. Of the CCL 4 pathogens, only enterovirus and caliciviruses have
an EPA-approved method for drinking water. The status of drinking water
analytical methods for the CCL chemical contaminants, as of May 2016,
is presented in Exhibit 2. EPA categorized the analytical method needs
in the following way:
An EPA drinking water method, with estimated reporting
levels that are adequate for analysis relative to the current HRL or
health assessment is available.
An EPA drinking water method is available but the minimum
reporting level (MRL) does not allow for quantitation of the
contaminant at a concentration below the current HRL. These methods are
denoted in Exhibit 2 by ``(MRL>HRL)''.
An EPA drinking water method is currently being developed.
An EPA drinking water method is not available.
Although not shown in Exhibit 2, EPA also considers other
government and consensus methods (e.g., Standard Methods and ASTM,
International) when considering analytical methods that may be used or
modified for UCMR monitoring.
Exhibit 2--Regulatory Determination Data/Information Needs for CCL 4 Contaminants
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What is the best Is a health
CASRN Common name available assessment Is an EPA analytical method
occurrence data? available? available?
----------------------------------------------------------------------------------------------------------------
(A) Contaminants with Nationally Representative Finished Water Occurrence Data and Peer Reviewed Health
Assessments
----------------------------------------------------------------------------------------------------------------
630-20-6.................... 1,1,1,2- National........ Yes \a\......... Yes.
Tetrachloroethan
e.
96-18-4..................... 1,2,3- National........ Yes............. Yes (MRL > HRL).
Trichloropropane.
123-91-1.................... 1,4-Dioxane...... National........ Yes............. Yes.
16655-82-6.................. 3- National........ Yes \b\......... Yes.
Hydroxycarbofura
n.
34256-82-1.................. Acetochlor....... National........ Yes............. Yes.
187022-11-3................. Acetochlor National........ Yes \b\......... Yes.
ethanesulfonic
acid (ESA).
[[Page 81112]]
194992-44-4................. Acetochlor National........ Yes \b\......... Yes.
oxanilic acid
(OA).
142363-53-9................. Alachlor National........ Yes............. Yes.
ethanesulfonic
acid (ESA).
171262-17-2................. Alachlor oxanilic National........ Yes \b\......... Yes (MRL > HRL).
acid (OA).
14866-68-3.................. Chlorate......... National........ Yes............. Yes.
7440-48-4................... Cobalt........... National........ Yes \a\......... Yes.
NA.......................... Enterovirus...... National........ Yes............. Yes.
7439-96-5................... Manganese........ National \ c\... In Development.. Yes.
74-83-9..................... Methyl bromide National........ Yes \a\......... Yes.
(Bromomethane).
51218-45-2.................. Metolachlor...... National........ Yes............. Yes.
171118-09-5................. Metolachlor National........ Yes............. Yes.
ethanesulfonic
acid (ESA).
152019-73-3................. Metolachlor National........ Yes............. Yes.
oxanilic acid
(OA).
7439-98-7................... Molybdenum....... National........ In Development.. Yes.
98-95-3..................... Nitrobenzene..... National........ Yes............. Yes.
55-18-5..................... N- National........ Yes............. Yes (MRL > HRL).
Nitrosodiethylam
ine (NDEA).
62-75-9..................... N- National........ Yes \a\......... Yes (MRL > HRL).
nitrosodimethyla
mine (NDMA).
621-64-7.................... N-Nitroso-di-n- National........ Yes............. Yes (MRL > HRL).
propylamine
(NDPA).
930-55-2.................... N- National........ Yes \a\......... Yes.
nitrosopyrrolidi
ne (NPYR).
1763-23-1................... Perfluorooctane National........ Yes............. Yes.
sulfonic acid
(PFOS).
335-67-1.................... Perfluorooctanoic National........ Yes............. Yes.
acid (PFOA).
121-82-4.................... RDX.............. National........ In Development.. Yes.
7440-62-2................... Vanadium......... National........ Yes \a\......... Yes.
----------------------------------------------------------------------------------------------------------------
(B) Contaminants With Non-Nationally Representative Finished Water Occurrence Data and Peer Reviewed Health
Assessments
----------------------------------------------------------------------------------------------------------------
71-36-3..................... 1-Butanol........ Non-National \c\ In Development.. Yes.
30560-19-1.................. Acephate......... Non-National.... Yes............. Yes.
107-02-8.................... Acrolein......... Non-National.... Yes \a\......... No.
NA.......................... Adenovirus....... Non-National.... Yes............. No.
319-84-6.................... alpha- Non-National \c\ Yes............. Yes (MRL > HRL).
Hexachlorocycloh
exane.
741-58-2.................... Bensulide........ Non-National.... Yes............. Yes.
100-44-7.................... Benzyl chloride.. Non-National.... Yes \a\......... No.
NA.......................... Caliciviruses.... Non-National.... Yes............. Yes.
133-06-2.................... Captan........... Non-National.... Yes............. No.
NA.......................... Cyanotoxins...... Non-National \d\ Yes for Yes.
microcystins
and
cylindrospermop
sin, no for
other
cyanotoxins.
141-66-2.................... Dicrotophos...... Non-National.... Yes............. Yes.
330-54-1.................... Diuron........... Non-National.... Yes............. Yes.
13194-48-4.................. Ethoprop......... Non-National \c\ Yes............. Yes.
107-21-1.................... Ethylene glycol.. Non-National.... Yes............. No.
96-45-7..................... Ethylene thiourea Non-National.... Yes............. No.
50-00-0..................... Formaldehyde..... Non-National.... Yes............. Yes.
NA.......................... Legionella Non-National.... Yes............. In Development.
pneumophila.
10265-92-6.................. Methamidophos.... Non-National.... Yes............. Yes.
NA.......................... Mycobacterium Non-National.... Yes............. In Development.
avium.
86-30-6..................... N- Non-National.... Yes \a\......... No.
Nitrosodiphenyla
mine (NDPhA).
301-12-2.................... Oxydemeton-methyl Non-National.... Yes............. Yes.
42874-03-3.................. Oxyfluorfen...... Non-National \c\ Yes............. Yes.
52645-53-1.................. Permethrin....... Non-National \c\ Yes............. Yes.
41198-08-7.................. Profenofos....... Non-National \c\ Yes............. Yes.
107534-96-3................. Tebuconazole..... Non-National \c\ Yes............. Yes.
78-48-8..................... Tribufos......... Non-National \c\ Yes............. Yes.
50471-44-8.................. Vinclozolin...... Non-National.... Yes............. Yes.
137-30-4.................... Ziram............ Non-National.... Yes............. No.
----------------------------------------------------------------------------------------------------------------
(C) Contaminants With Nationally Representative Finished Water Occurrence Data Lacking Peer Reviewed Health
Assessments
----------------------------------------------------------------------------------------------------------------
75-34-3..................... 1,1- National........ No \a\.......... Yes.
Dichloroethane.
106-99-0.................... 1,3-Butadiene.... National........ No.............. Yes (MRL > HRL).
74-87-3..................... Chloromethane National........ No.............. Yes.
(Methyl
chloride).
474-86-2.................... Equilin.......... National........ No.............. Yes.
50-28-2..................... Estradiol (17- National........ No.............. Yes.
beta estradiol).
50-27-1..................... Estriol.......... National........ No.............. Yes.
53-16-7..................... Estrone.......... National........ No.............. Yes.
57-63-6..................... Ethinyl Estradiol National........ No.............. Yes.
(17-alpha
ethynyl
estradiol).
7440-56-4................... Germanium........ National \c\.... No.............. Yes.
74-97-5..................... Halon 1011 National........ No.............. Yes.
(bromochlorometh
ane).
75-45-6..................... HCFC-22.......... National........ No.............. Yes.
1634-04-4................... Methyl tert-butyl National........ No.............. Yes.
ether (MTBE).
103-65-1.................... n-Propylbenzene.. National........ No \a\.......... Yes.
[[Page 81113]]
135-98-8.................... sec-Butylbenzene. National........ No \a\.......... Yes.
13494-80-9.................. Tellurium........ National........ No.............. No.
----------------------------------------------------------------------------------------------------------------
(D) Contaminants With Non-Nationally Representative Finished Water Occurrence Data Lacking Peer Reviewed Health
Assessments
----------------------------------------------------------------------------------------------------------------
57-91-0..................... 17alpha-estradiol Non-National.... No.............. In Development.
75-07-0..................... Acetaldehyde..... Non-National.... No.............. Yes.
62-53-3..................... Aniline.......... Non-National.... No \a\.......... No.
25013-16-5.................. Butylated Non-National \c\ No.............. Yes.
hydroxyanisole.
517-09-9.................... Equilenin........ Non-National.... No.............. In Development.
114-07-8.................... Erythromycin..... Non-National.... No.............. In Development.
110-54-3.................... Hexane........... Non-National.... No \a\.......... No.
72-33-3..................... Mestranol........ Non-National.... No.............. No.
NA.......................... Naegleria fowleri Non-National.... No.............. No.
25154-52-3.................. Nonylphenol...... Non-National.... No.............. No.
68-22-4..................... Norethindrone (19- Non-National.... No.............. In Development.
Norethisterone).
----------------------------------------------------------------------------------------------------------------
(E) Contaminants With Peer Reviewed Health Assessments Lacking Finished Water Occurrence Data
----------------------------------------------------------------------------------------------------------------
107-18-6.................... 2-Propen-1-ol.... Release \c\..... Yes \a\......... Yes.
110429-62-4................. Clethodim........ Release......... Yes............. No.
55290-64-7.................. Dimethipin....... Release \c\..... Yes............. Yes.
NA.......................... Escherichia coli No Data......... Yes............. No.
(O157).
NA.......................... Helicobacter No Data......... Yes............. No.
pylori \e\.
NA.......................... Hepatitis A virus No Data......... Yes............. No.
302-01-2.................... Hydrazine........ Release......... Yes \a\......... No.
67-56-1..................... Methanol......... Release......... Yes............. No.
55-63-0..................... Nitroglycerin.... Release......... Yes \a\......... No.
872-50-4.................... N-Methyl-2- Release......... Yes............. No.
pyrrolidone.
75-56-9..................... Oxirane, methyl-. Release......... Yes............. No.
91-22-5..................... Quinoline........ Release \c\..... Yes............. Yes (MRL > HRL).
112410-23-8................. Tebufenozide..... Release......... Yes............. Yes.
59669-26-0.................. Thiodicarb....... Release......... Yes............. No.
23564-05-8.................. Thiophanate- Release......... Yes............. No.
methyl.
76-87-9..................... Triphenyltin Release......... Yes............. No.
hydroxide (TPTH).
----------------------------------------------------------------------------------------------------------------
(F) Contaminants Lacking Finished Water Occurrence Data and Current, Peer Reviewed Health Assessments
----------------------------------------------------------------------------------------------------------------
109-86-4.................... 2-Methoxyethanol. Release \c\..... No \a\.......... Yes.
101-77-9.................... 4,4'- Release......... No.............. No.
Methylenedianili
ne.
60-35-5..................... Acetamide........ Release......... No.............. No.
NA.......................... Campylobacter No Data......... No.............. No.
jejuni.
80-15-9..................... Cumene Release......... No.............. No.
hydroperoxide.
75-21-8..................... Ethylene oxide... Release......... No.............. No.
95-53-4..................... o-Toluidine...... Release \c\..... No \a\.......... Yes.
NA.......................... Salmonella No Data......... No.............. No.
enteric.
NA.......................... Shigella sonnei.. No Data......... No.............. No.
26471-62-5.................. Toluene Release......... No.............. No.
diisocyanate.
121-44-8.................... Triethylamine.... Release......... No.............. No.
51-79-6..................... Urethane......... Release......... No.............. No.
----------------------------------------------------------------------------------------------------------------
Key to Exhibit:
National = Finished drinking water occurrence data that are nationally representative are available.
Non-National = Finished drinking water occurrence data that are not nationally representative are available.
In Development = Revised health assessment or analytical method is currently being developed.
\a\ Provisional Peer Reviewed Toxicity Value (PPRTV) in the form of chronic, oral RfD subchronic, oral RfD,
cancer weight evidence, or cancer slope factor available.
\b\ The parent health assessment was used for the metabolite. There is no independent health assessment
available for the metabolite.
\c\ Proposed for UCMR 4.
\d\ Evaluations of occurrence data availability for cyanotoxins in this table are based on anatoxin-a,
cylindrospermopsin, and microcystin-LR. Cyanotoxins proposed for UCMR 4 monitoring include total microcystins
(MC), MC-LA, MC-LF, MC-LR, MC-LY, MC-RR, MC-YR, nodularin, anatoxin-a and cylindrospermopsin.
VI. Next Steps and Future Contaminant Candidate Lists
The CCL process is critical to shaping the future direction of the
drinking water program. The agency will continue to gather information
and evaluate contaminants on the CCL 4 to make regulatory
determinations for at least five contaminants. The agency will also
continue to refine the CCL process and gather more data to identify
contaminants for CCL 5. EPA will continue to work to prioritize
contaminants on the CCL 4, both for RD and for additional research and
data collection.
References
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granular activated carbon filters and their relationship to human
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Kern, C.H. and Smith, D.R. 2011. Preweaning Mn exposure leads to
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Use Deletion and Product Cancellation Order. Federal Register. Vol.
79, No. 190, p. 59261. October 1, 2014.
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Dated: November 9, 2016.
Joel Beauvais,
Deputy Assistant Administrator, Office of Water.
[FR Doc. 2016-27667 Filed 11-16-16; 8:45 am]
BILLING CODE 6560-50-P