Proposed Data Collection Submitted for Public Comment and Recommendations, 16857-16859 [2019-08150]
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16857
Federal Register / Vol. 84, No. 78 / Tuesday, April 23, 2019 / Notices
ATSDR will collect urine samples
pre- and post-activity. The urine
samples will be analyzed for
polyaromatic hydrocarbons and will
also be archived in case of future
development of new analytical methods
for potential chemicals of interest.
The research study will screen a total
of 220 participants for eligibility. The
target sample size is 150 for synthetic
turf field users and is 50 for the natural
grass field users. The total burden hours
for the research study is 184 hours
among all of the 220 respondents. There
is no cost to the respondents other than
their time in the study.
ESTIMATED ANNUALIZED BURDEN HOURS
Form name
Adult/Adolescent Field Users ..........................
Eligibility Screening Form ..............................
Adult and Adolescent Questionnaire .............
Exposure Measurement Form .......................
Eligibility Screening Form ..............................
Youth and Child Questionnaire ......................
Exposure Measurement Form .......................
Parents/Guardians of Youth/Child Field Users
Youth/Child Field Users ..................................
Jeffrey M. Zirger,
Lead, Information Collection Review Office,
Office of Scientific Integrity, Office of Science,
Centers for Disease Control and Prevention.
[FR Doc. 2019–08147 Filed 4–22–19; 8:45 am]
BILLING CODE 4163–18–P
DEPARTMENT OF HEALTH AND
HUMAN SERVICES
Agency for Toxic Substance and
Disease Registry
[60-Day–19–19ACF; Docket No. ATSDR–
2019–0004]
Proposed Data Collection Submitted
for Public Comment and
Recommendations
Agency for Toxic Substances
and Disease Registry (ATSDR),
Department of Health and Human
Services (HHS).
AGENCY:
ACTION:
Notice with comment period.
The Agency for Toxic
Substances and Disease Registry
(ATSDR), as part of its continuing effort
to reduce public burden and maximize
the utility of government information,
invites the general public and other
Federal agencies the opportunity to
comment on a proposed and/or
continuing information collection, as
required by the Paperwork Reduction
Act of 1995. This notice invites
comment on a proposed information
collection project titled ‘‘Human health
effects of drinking water exposures to
per- and polyfluoroalkyl substances
(PFAS): A multi-site cross-sectional
study (The Multi-site Study).’’ The
purpose of this research is to use sound
study methods to see if drinking water
exposure to PFAS is related to health
outcomes.
SUMMARY:
jbell on DSK3GLQ082PROD with NOTICES
Number of
respondents
Type of respondents
VerDate Sep<11>2014
17:49 Apr 22, 2019
Jkt 247001
ATSDR must receive written
comments on or before June 24, 2019.
ADDRESSES: You may submit comments,
identified by Docket No. ATSDR–2019–
0004 by any of the following methods:
• Federal eRulemaking Portal:
Regulations.gov. Follow the instructions
for submitting comments.
• Mail: Jeffrey M. Zirger, Information
Collection Review Office, Centers for
Disease Control and Prevention, 1600
Clifton Road NE, MS–D74, Atlanta,
Georgia 30329.
Instructions: All submissions received
must include the agency name and
Docket Number. ATSDR will post,
without change, all relevant comments
to Regulations.gov.
Please note: Submit all comments
through the Federal eRulemaking portal
(regulations.gov) or by U.S. mail to the
address listed above.
FOR FURTHER INFORMATION CONTACT: To
request more information on the
proposed project or to obtain a copy of
the information collection plan and
instruments, contact Jeffery M. Zirger,
Information Collection Review Office,
Centers for Disease Control and
Prevention, 1600 Clifton Road NE, MS–
D74, Atlanta, Georgia 30329; phone:
404–639–7570; Email: omb@cdc.gov.
SUPPLEMENTARY INFORMATION:
Under the Paperwork Reduction Act
of 1995 (PRA) (44 U.S.C. 3501–3520),
Federal agencies must obtain approval
from the Office of Management and
Budget (OMB) for each collection of
information they conduct or sponsor. In
addition, the PRA also requires Federal
agencies to provide a 60-day notice in
the Federal Register concerning each
proposed collection of information,
including each new proposed
collection, each proposed extension of
existing collection of information, and
each reinstatement of previously
approved information collection before
DATES:
PO 00000
Frm 00022
Fmt 4703
Sfmt 4703
Number of
responses per
respondent
110
100
100
110
100
100
Average
burden per
response
(in hrs.)
1
1
1
1
1
1
5/60
30/60
20/60
5/60
30/60
20/60
submitting the collection to the OMB for
approval. To comply with this
requirement, we are publishing this
notice of a proposed data collection as
described below.
The OMB is particularly interested in
comments that will help:
1. Evaluate whether the proposed
collection of information is necessary
for the proper performance of the
functions of the agency, including
whether the information will have
practical utility;
2. Evaluate the accuracy of the
agency’s estimate of the burden of the
proposed collection of information,
including the validity of the
methodology and assumptions used;
3. Enhance the quality, utility, and
clarity of the information to be
collected; and
4. Minimize the burden of the
collection of information on those who
are to respond, including through the
use of appropriate automated,
electronic, mechanical, or other
technological collection techniques or
other forms of information technology,
e.g., permitting electronic submissions
of responses.
5. Assess information collection costs.
Proposed Project
Human health effects of drinking
water exposures to per- and
polyfluoroalkyl substances (PFAS): A
multi-site cross-sectional study (The
Multi-site Study)—NEW—Agency for
Toxic Substances and Disease Registry
(ATSDR).
Background and Brief Description
Per- and polyfluoroalkyl substances
(PFAS) are a family of chemicals used
in industrial applications and consumer
products. PFAS contamination of
drinking water is widespread in the U.S.
Some estimates indicate that at least
E:\FR\FM\23APN1.SGM
23APN1
jbell on DSK3GLQ082PROD with NOTICES
16858
Federal Register / Vol. 84, No. 78 / Tuesday, April 23, 2019 / Notices
sixty million residents were served by
66 public water supplies that had at
least one sample at or above the US
Environmental Protection Agency (EPA)
Lifetime Health Advisory for
perfluorooctanoic acid (PFOA) and
perfluorooctane sulfonic acid (PFOS)
(individually or combined), which is 70
nanograms per liter (ng/L) of water.
Industrial facilities that manufacture or
use PFAS have contaminated drinking
water in surrounding communities in
several states. In addition, PFOS, PFOA,
perfluorohexane sulfonic acid (PFHxS)
and other PFAS chemicals are
constituents in aqueous film-forming
foam (AFFF), used to extinguish
flammable liquid fires. The use of AFFF
at military bases and other sites may
have resulted in the migration of PFAS
chemicals through soils to ground water
and/or surface water sources of drinking
water for the bases and/or surrounding
communities around the country.
In response to growing awareness of
the extent of PFAS contamination across
the U.S., the Section 316(a) of the 2018
National Defense Authorization Act
(Pub. L. 115–91) authorized the Agency
for Toxic Substances and Disease
Registry (ATSDR) to conduct a study on
the human health effects of PFAS
contamination in drinking water. The
existence of widespread contamination
at many sites around the U.S. makes this
a paramount effort in addressing the
health effects of exposures to PFAS from
contaminated drinking water.
Consequently, ATSDR is requesting a
three-year Paperwork Reduction Act
(PRA) clearance for the Multi-site Study.
The Multi-site Study will build on the
preceding proof-of-concept study at the
Pease International Tradeport in
Portsmouth, New Hampshire.
ATSDR will conduct this research
using a cooperative agreement titled
‘‘Multi-site Study of the Health
Implications of Exposure to PFASContaminated Drinking Water’’ (Notice
of Funding Opportunity [NOFO] No.
CDC–RFA–TS–19–002). The expected
number of research recipients (e.g.,
entities selected for funding) is six. The
program will be administered by the
CDC Extramural Research Program
Office (ERPO) at the National Center for
Injury Prevention and Control (NCIPC).
The research under this cooperative
agreement will be a two-part program.
First, a mandatory core research
protocol for all recipients is designed to
aggregate data across all sites and
designed to compare data between sites.
Next, each recipient will have the
option to propose additional
investigator-initiated research questions
and hypotheses related to the overall
goals of this NOFO.
VerDate Sep<11>2014
17:49 Apr 22, 2019
Jkt 247001
The main goal of this cross-sectional
multi-site study is to evaluate
associations between measured and
reconstructed historic serum levels of
PFAS including PFOA, PFOS, and
PFHxS, and selected health outcomes.
The health outcomes of interest include
lipids, renal function and kidney
disease, thyroid hormones and disease,
liver function and disease, glycemic
parameters and diabetes, as well as
immune response and function in both
children and adults. In addition, the
study will investigate PFAS differences
in sex hormones and sexual maturation,
vaccine response, and neurobehavioral
outcomes in children. In adults,
additional outcomes of interest include
cardiovascular disease, osteoarthritis
and osteoporosis, endometriosis, and
autoimmune disease.
Under the cooperative agreement,
each recipient shall propose candidate
study sites at communities whose
drinking water was impacted by AFFF
use or by industrial PFAS emissions.
Site selection will consider the
documented levels of PFAS drinking
water concentrations. The aim will be to
include sites so that a wide range in
PFAS exposures levels are included in
the study. This will enable the
evaluation of exposure-response trends
including effects at the lower range of
exposures. Ground water contaminant
fate and transport models and water
system distribution system models may
be necessary to identify the areas with
contaminated drinking water, to
determine the period when the drinking
water was contaminated, and to
reconstruct historical PFAS
contaminant concentrations.
For exposure estimation, participants
will be categorized based on their
measured serum concentration of PFAS
compounds or on modeled estimated
historical serum levels (e.g., referent or
low, medium, high). Measured and
estimated PFAS serum levels will also
be evaluated as continuous variables. At
sites with prior PFAS biomonitoring
data, the study will evaluate changes in
PFAS concentration over time.
Each recipient shall reconstruct
historic serum PFAS concentrations.
This may be done by estimating halflives and elimination rates as well as by
water contamination modeling to inform
pharmacokinetic (PK) or physiologically
based pharmacokinetic (PBPK) models.
Historical serum PFAS reconstruction
will enable the evaluation of exposure
lags and vulnerable periods as well as
statistical analyses that can control for
confounding and reverse causation due
to physiological factors.
Each recipient shall identify and
enumerate all households served by the
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Frm 00023
Fmt 4703
Sfmt 4703
contaminated drinking water supply in
the selected community to recruit
potential participants and to meet the
sample size requirements for children
and adults. If the selected community is
served by a PFAS-contaminated public
water system, then the recipient will
obtain a list of households served by the
water purveyor from its billing records.
If the community is served by
contaminated private wells, then the
recipient will obtain a list of households
with contaminated wells from the local
and/or state health and environmental
agencies.
Statistical sampling methods (e.g., a
two-stage cluster sample) may be used
for recruitment of study participants if
all the affected households can be
enumerated. If the PFAS drinking water
concentrations vary widely across the
community, then the recipient should
consider using targeted sampling
approaches—including oversampling of
areas with higher PFAS
concentrations—to ensure a sufficiently
wide distribution of exposure levels
among study participants to evaluate
exposure-response trends. If
enumeration of all households is not
feasible, or if participation rates are
expected to be low, then the recipient
can consider non-probabilistic sampling
approaches such as ‘‘judgment’’ and
‘‘snowball’’ sampling approaches.
The recipients should consider
requesting assistance from local and
state health departments in its
recruitment efforts. In addition, the
recipient should engage community
organizations to assist in conducting
outreach about the study and
recruitment of participants and consider
establishing a community assistance
panel (CAP). The CAP could provide
comments on any additional
investigator-initiated research questions
and hypotheses and facilitate the
involvement of the affected community
in decisions related to outreach about
the study, participant recruitment
strategies, and study logistics. The CAP
could also assist the recipient in the
dissemination of study findings to the
community.
In total, ATSDR seeks to enroll at least
8,000 participants (6,000 adults and
2,000 children and their parents) from
communities exposed to PFAScontaminated drinking water over the
first three years of the five-year
cooperative agreement program.
Annualized estimates are 2,667
participants (2,000 adults and 667
children). To restrict this study to
drinking water exposures, adults
occupationally exposed to PFAS will
not be eligible for the study (e.g., ever
firefighters or ever workers in an
E:\FR\FM\23APN1.SGM
23APN1
16859
Federal Register / Vol. 84, No. 78 / Tuesday, April 23, 2019 / Notices
industry using PFAS chemicals in its
manufacturing process). Likewise,
children whose birth mothers were
occupationally exposed will not be
eligible. ATSDR assumes that 5 percent
of the people who volunteer will not
meet eligibility requirements; therefore,
a total of 8,400 people will be screened.
To complete the data collection in three
years, annualized estimates for
eligibility screening are 2,800 people
(2,100 adults and 700 children) and an
annual time burden of 467 hours. The
recipients will provide appointment
reminder calls for each eligible person
who agrees to be enrolled (n = 2,667 per
year) for a time burden of 222 hours per
year.
At enrollment, each recipient will
obtain adult consent, parental
permission, and child assent before data
collection begins. For each participant,
the recipient will take body measures,
collect blood samples to measure PFAS
serum levels and several effect
biomarkers such as lipids, and thyroid,
kidney, immune and liver function. The
recipient will also obtain urine samples
from participants to measure PFAS
levels and kidney function biomarkers.
The study will archive leftover serum
and urine samples for additional
analyses of PFAS chemicals and specific
effect biomarkers. The National Center
for Environmental Health (NCEH)
laboratory will perform blood and urine
PFAS analyses for all Multi-site Study
participants. Thus, issues of interlaboratory variability for exposure
measures will be eliminated.
Adult participants and a parent of
child participants will complete a
questionnaire that includes residential
history, medical history, occupational
history, and water consumption habits
(n=2,000 adults and 667 children per
year). Ideally, the parent will be the
child’s birth mother, as ATSDR will ask
details about the child’s exposure,
pregnancy, and breastfeeding history.
For purposes of time burden
estimation, ATSDR assumes that 20
percent of parents will also enroll as
adults and can take the child short form
questionnaire (n=133 per year);
therefore, 534 parents will take the child
long form questionnaire per year.
Parents and children, with
administration by trained professionals,
will also complete neurobehavioral
assessments of the child’s attention and
behaviors (n=667 per year).
To facilitate access to medical and
school records, each recipient will reach
out to local medical societies, public
school systems, and private schools, to
enlist their cooperation with the study.
The recipient will ask for permission to
abstract participants’ medical records to
confirm self-reported health outcomes.
The recipient will also seek permission
to abstract and compare children’s
school records to their behavioral
assessment results. Based on ATSDR’s
experience from the Pease proof of
concept study, ATSDR estimates that it
will take 48 education specialists and
150 adult and 50 pediatric medical
record specialists to complete record
abstractions across all study sites. Given
the goal to enroll at least 2,000 adults
and 667 children per year, the annual
time burden for medical and
educational record abstraction is
estimated to be 1,091 hours.
The total annualized time burden
requested is 5,269 hours. There is no
cost to the respondents other than their
time.
ESTIMATED ANNUALIZED BURDEN HOURS
Number of
respondents
Average
burden per
response
(in hours)
Total burden
(in hours)
Form name
Multi-site Study Participants ..............................
Eligibility Screening Script ................................
Appointment Reminder Telephone Script .........
Update Contact Information Hardcopy Form ....
Medication List ..................................................
Body and Blood Pressure Measures Form ......
Blood Draw and Urine Collection Form ............
Adult Questionnaire ..........................................
Child Questionnaire—Long Form .....................
Child Questionnaire—Short Form .....................
Parent Neurobehavioral Test Battery ...............
Child Neurobehavioral Test Battery ..................
Child School Record Abstraction Form ............
Medical Record Abstraction Form—Adult ........
Medical Record Abstraction Form—Child ........
2,800
2,667
2,667
2,667
2,667
2,667
2,000
537
133
667
667
48
150
50
1
1
1
1
1
1
1
1
1
1
1
14
13
13
10/60
5/60
5/60
3/60
5/60
10/60
30/60
30/60
15/60
15/60
90/60
20/60
20/60
20/60
467
222
222
133
222
444
1,000
268
33
167
1,000
224
650
217
...........................................................................
........................
........................
........................
5,269
Education Specialists ........................................
Medical Record Specialists ...............................
Total ............................................................
Jeffrey M. Zirger,
Lead, Information Collection Review Office,
Office of Scientific Integrity, Office of Science,
Centers for Disease Control and Prevention.
[FR Doc. 2019–08150 Filed 4–22–19; 8:45 am]
DEPARTMENT OF HEALTH AND
HUMAN SERVICES
Centers for Disease Control and
Prevention
BILLING CODE 4163–18–P
[60-Day–19–0457; Docket No. CDC–2019–
0032]
jbell on DSK3GLQ082PROD with NOTICES
Number of
responses per
respondent
Type of respondents
Proposed Data Collection Submitted
for Public Comment and
Recommendations
Centers for Disease Control and
Prevention (CDC), Department of Health
and Human Services (HHS).
ACTION: Notice with comment period.
AGENCY:
VerDate Sep<11>2014
17:49 Apr 22, 2019
Jkt 247001
PO 00000
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Fmt 4703
Sfmt 4703
The Centers for Disease
Control and Prevention (CDC), as part of
its continuing effort to reduce public
burden and maximize the utility of
government information, invites the
general public and other Federal
agencies the opportunity to comment on
a proposed and/or continuing
information collection, as required by
the Paperwork Reduction Act of 1995.
This notice invites comment on
Aggregate Reports for Tuberculosis
Program Evaluation. The goal of the
study is to allow CDC to collect and
monitor indicators for key program
activities, such as finding tuberculosis
infections in recent contacts of cases
SUMMARY:
E:\FR\FM\23APN1.SGM
23APN1
Agencies
- DEPARTMENT OF HEALTH AND HUMAN SERVICES
- Agency for Toxic Substance and Disease Registry
[Federal Register Volume 84, Number 78 (Tuesday, April 23, 2019)]
[Notices]
[Pages 16857-16859]
From the Federal Register Online via the Government Publishing Office [www.gpo.gov]
[FR Doc No: 2019-08150]
-----------------------------------------------------------------------
DEPARTMENT OF HEALTH AND HUMAN SERVICES
Agency for Toxic Substance and Disease Registry
[60-Day-19-19ACF; Docket No. ATSDR-2019-0004]
Proposed Data Collection Submitted for Public Comment and
Recommendations
AGENCY: Agency for Toxic Substances and Disease Registry (ATSDR),
Department of Health and Human Services (HHS).
ACTION: Notice with comment period.
-----------------------------------------------------------------------
SUMMARY: The Agency for Toxic Substances and Disease Registry (ATSDR),
as part of its continuing effort to reduce public burden and maximize
the utility of government information, invites the general public and
other Federal agencies the opportunity to comment on a proposed and/or
continuing information collection, as required by the Paperwork
Reduction Act of 1995. This notice invites comment on a proposed
information collection project titled ``Human health effects of
drinking water exposures to per- and polyfluoroalkyl substances (PFAS):
A multi-site cross-sectional study (The Multi-site Study).'' The
purpose of this research is to use sound study methods to see if
drinking water exposure to PFAS is related to health outcomes.
DATES: ATSDR must receive written comments on or before June 24, 2019.
ADDRESSES: You may submit comments, identified by Docket No. ATSDR-
2019-0004 by any of the following methods:
Federal eRulemaking Portal: Regulations.gov. Follow the
instructions for submitting comments.
Mail: Jeffrey M. Zirger, Information Collection Review
Office, Centers for Disease Control and Prevention, 1600 Clifton Road
NE, MS-D74, Atlanta, Georgia 30329.
Instructions: All submissions received must include the agency name
and Docket Number. ATSDR will post, without change, all relevant
comments to Regulations.gov.
Please note: Submit all comments through the Federal eRulemaking
portal (regulations.gov) or by U.S. mail to the address listed above.
FOR FURTHER INFORMATION CONTACT: To request more information on the
proposed project or to obtain a copy of the information collection plan
and instruments, contact Jeffery M. Zirger, Information Collection
Review Office, Centers for Disease Control and Prevention, 1600 Clifton
Road NE, MS-D74, Atlanta, Georgia 30329; phone: 404-639-7570; Email:
[email protected].
SUPPLEMENTARY INFORMATION:
Under the Paperwork Reduction Act of 1995 (PRA) (44 U.S.C. 3501-
3520), Federal agencies must obtain approval from the Office of
Management and Budget (OMB) for each collection of information they
conduct or sponsor. In addition, the PRA also requires Federal agencies
to provide a 60-day notice in the Federal Register concerning each
proposed collection of information, including each new proposed
collection, each proposed extension of existing collection of
information, and each reinstatement of previously approved information
collection before submitting the collection to the OMB for approval. To
comply with this requirement, we are publishing this notice of a
proposed data collection as described below.
The OMB is particularly interested in comments that will help:
1. Evaluate whether the proposed collection of information is
necessary for the proper performance of the functions of the agency,
including whether the information will have practical utility;
2. Evaluate the accuracy of the agency's estimate of the burden of
the proposed collection of information, including the validity of the
methodology and assumptions used;
3. Enhance the quality, utility, and clarity of the information to
be collected; and
4. Minimize the burden of the collection of information on those
who are to respond, including through the use of appropriate automated,
electronic, mechanical, or other technological collection techniques or
other forms of information technology, e.g., permitting electronic
submissions of responses.
5. Assess information collection costs.
Proposed Project
Human health effects of drinking water exposures to per- and
polyfluoroalkyl substances (PFAS): A multi-site cross-sectional study
(The Multi-site Study)--NEW--Agency for Toxic Substances and Disease
Registry (ATSDR).
Background and Brief Description
Per- and polyfluoroalkyl substances (PFAS) are a family of
chemicals used in industrial applications and consumer products. PFAS
contamination of drinking water is widespread in the U.S. Some
estimates indicate that at least
[[Page 16858]]
sixty million residents were served by 66 public water supplies that
had at least one sample at or above the US Environmental Protection
Agency (EPA) Lifetime Health Advisory for perfluorooctanoic acid (PFOA)
and perfluorooctane sulfonic acid (PFOS) (individually or combined),
which is 70 nanograms per liter (ng/L) of water. Industrial facilities
that manufacture or use PFAS have contaminated drinking water in
surrounding communities in several states. In addition, PFOS, PFOA,
perfluorohexane sulfonic acid (PFHxS) and other PFAS chemicals are
constituents in aqueous film-forming foam (AFFF), used to extinguish
flammable liquid fires. The use of AFFF at military bases and other
sites may have resulted in the migration of PFAS chemicals through
soils to ground water and/or surface water sources of drinking water
for the bases and/or surrounding communities around the country.
In response to growing awareness of the extent of PFAS
contamination across the U.S., the Section 316(a) of the 2018 National
Defense Authorization Act (Pub. L. 115-91) authorized the Agency for
Toxic Substances and Disease Registry (ATSDR) to conduct a study on the
human health effects of PFAS contamination in drinking water. The
existence of widespread contamination at many sites around the U.S.
makes this a paramount effort in addressing the health effects of
exposures to PFAS from contaminated drinking water. Consequently, ATSDR
is requesting a three-year Paperwork Reduction Act (PRA) clearance for
the Multi-site Study. The Multi-site Study will build on the preceding
proof-of-concept study at the Pease International Tradeport in
Portsmouth, New Hampshire.
ATSDR will conduct this research using a cooperative agreement
titled ``Multi-site Study of the Health Implications of Exposure to
PFAS-Contaminated Drinking Water'' (Notice of Funding Opportunity
[NOFO] No. CDC-RFA-TS-19-002). The expected number of research
recipients (e.g., entities selected for funding) is six. The program
will be administered by the CDC Extramural Research Program Office
(ERPO) at the National Center for Injury Prevention and Control
(NCIPC). The research under this cooperative agreement will be a two-
part program. First, a mandatory core research protocol for all
recipients is designed to aggregate data across all sites and designed
to compare data between sites. Next, each recipient will have the
option to propose additional investigator-initiated research questions
and hypotheses related to the overall goals of this NOFO.
The main goal of this cross-sectional multi-site study is to
evaluate associations between measured and reconstructed historic serum
levels of PFAS including PFOA, PFOS, and PFHxS, and selected health
outcomes. The health outcomes of interest include lipids, renal
function and kidney disease, thyroid hormones and disease, liver
function and disease, glycemic parameters and diabetes, as well as
immune response and function in both children and adults. In addition,
the study will investigate PFAS differences in sex hormones and sexual
maturation, vaccine response, and neurobehavioral outcomes in children.
In adults, additional outcomes of interest include cardiovascular
disease, osteoarthritis and osteoporosis, endometriosis, and autoimmune
disease.
Under the cooperative agreement, each recipient shall propose
candidate study sites at communities whose drinking water was impacted
by AFFF use or by industrial PFAS emissions. Site selection will
consider the documented levels of PFAS drinking water concentrations.
The aim will be to include sites so that a wide range in PFAS exposures
levels are included in the study. This will enable the evaluation of
exposure-response trends including effects at the lower range of
exposures. Ground water contaminant fate and transport models and water
system distribution system models may be necessary to identify the
areas with contaminated drinking water, to determine the period when
the drinking water was contaminated, and to reconstruct historical PFAS
contaminant concentrations.
For exposure estimation, participants will be categorized based on
their measured serum concentration of PFAS compounds or on modeled
estimated historical serum levels (e.g., referent or low, medium,
high). Measured and estimated PFAS serum levels will also be evaluated
as continuous variables. At sites with prior PFAS biomonitoring data,
the study will evaluate changes in PFAS concentration over time.
Each recipient shall reconstruct historic serum PFAS
concentrations. This may be done by estimating half-lives and
elimination rates as well as by water contamination modeling to inform
pharmacokinetic (PK) or physiologically based pharmacokinetic (PBPK)
models. Historical serum PFAS reconstruction will enable the evaluation
of exposure lags and vulnerable periods as well as statistical analyses
that can control for confounding and reverse causation due to
physiological factors.
Each recipient shall identify and enumerate all households served
by the contaminated drinking water supply in the selected community to
recruit potential participants and to meet the sample size requirements
for children and adults. If the selected community is served by a PFAS-
contaminated public water system, then the recipient will obtain a list
of households served by the water purveyor from its billing records. If
the community is served by contaminated private wells, then the
recipient will obtain a list of households with contaminated wells from
the local and/or state health and environmental agencies.
Statistical sampling methods (e.g., a two-stage cluster sample) may
be used for recruitment of study participants if all the affected
households can be enumerated. If the PFAS drinking water concentrations
vary widely across the community, then the recipient should consider
using targeted sampling approaches--including oversampling of areas
with higher PFAS concentrations--to ensure a sufficiently wide
distribution of exposure levels among study participants to evaluate
exposure-response trends. If enumeration of all households is not
feasible, or if participation rates are expected to be low, then the
recipient can consider non-probabilistic sampling approaches such as
``judgment'' and ``snowball'' sampling approaches.
The recipients should consider requesting assistance from local and
state health departments in its recruitment efforts. In addition, the
recipient should engage community organizations to assist in conducting
outreach about the study and recruitment of participants and consider
establishing a community assistance panel (CAP). The CAP could provide
comments on any additional investigator-initiated research questions
and hypotheses and facilitate the involvement of the affected community
in decisions related to outreach about the study, participant
recruitment strategies, and study logistics. The CAP could also assist
the recipient in the dissemination of study findings to the community.
In total, ATSDR seeks to enroll at least 8,000 participants (6,000
adults and 2,000 children and their parents) from communities exposed
to PFAS-contaminated drinking water over the first three years of the
five-year cooperative agreement program. Annualized estimates are 2,667
participants (2,000 adults and 667 children). To restrict this study to
drinking water exposures, adults occupationally exposed to PFAS will
not be eligible for the study (e.g., ever firefighters or ever workers
in an
[[Page 16859]]
industry using PFAS chemicals in its manufacturing process). Likewise,
children whose birth mothers were occupationally exposed will not be
eligible. ATSDR assumes that 5 percent of the people who volunteer will
not meet eligibility requirements; therefore, a total of 8,400 people
will be screened. To complete the data collection in three years,
annualized estimates for eligibility screening are 2,800 people (2,100
adults and 700 children) and an annual time burden of 467 hours. The
recipients will provide appointment reminder calls for each eligible
person who agrees to be enrolled (n = 2,667 per year) for a time burden
of 222 hours per year.
At enrollment, each recipient will obtain adult consent, parental
permission, and child assent before data collection begins. For each
participant, the recipient will take body measures, collect blood
samples to measure PFAS serum levels and several effect biomarkers such
as lipids, and thyroid, kidney, immune and liver function. The
recipient will also obtain urine samples from participants to measure
PFAS levels and kidney function biomarkers. The study will archive
leftover serum and urine samples for additional analyses of PFAS
chemicals and specific effect biomarkers. The National Center for
Environmental Health (NCEH) laboratory will perform blood and urine
PFAS analyses for all Multi-site Study participants. Thus, issues of
inter-laboratory variability for exposure measures will be eliminated.
Adult participants and a parent of child participants will complete
a questionnaire that includes residential history, medical history,
occupational history, and water consumption habits (n=2,000 adults and
667 children per year). Ideally, the parent will be the child's birth
mother, as ATSDR will ask details about the child's exposure,
pregnancy, and breastfeeding history.
For purposes of time burden estimation, ATSDR assumes that 20
percent of parents will also enroll as adults and can take the child
short form questionnaire (n=133 per year); therefore, 534 parents will
take the child long form questionnaire per year. Parents and children,
with administration by trained professionals, will also complete
neurobehavioral assessments of the child's attention and behaviors
(n=667 per year).
To facilitate access to medical and school records, each recipient
will reach out to local medical societies, public school systems, and
private schools, to enlist their cooperation with the study. The
recipient will ask for permission to abstract participants' medical
records to confirm self-reported health outcomes. The recipient will
also seek permission to abstract and compare children's school records
to their behavioral assessment results. Based on ATSDR's experience
from the Pease proof of concept study, ATSDR estimates that it will
take 48 education specialists and 150 adult and 50 pediatric medical
record specialists to complete record abstractions across all study
sites. Given the goal to enroll at least 2,000 adults and 667 children
per year, the annual time burden for medical and educational record
abstraction is estimated to be 1,091 hours.
The total annualized time burden requested is 5,269 hours. There is
no cost to the respondents other than their time.
Estimated Annualized Burden Hours
----------------------------------------------------------------------------------------------------------------
Number of Average burden
Type of respondents Form name Number of responses per per response Total burden
respondents respondent (in hours) (in hours)
----------------------------------------------------------------------------------------------------------------
Multi-site Study Participants. Eligibility 2,800 1 10/60 467
Screening
Script.
Appointment 2,667 1 5/60 222
Reminder
Telephone
Script.
Update Contact 2,667 1 5/60 222
Information
Hardcopy Form.
Medication List. 2,667 1 3/60 133
Body and Blood 2,667 1 5/60 222
Pressure
Measures Form.
Blood Draw and 2,667 1 10/60 444
Urine
Collection Form.
Adult 2,000 1 30/60 1,000
Questionnaire.
Child 537 1 30/60 268
Questionnaire--
Long Form.
Child 133 1 15/60 33
Questionnaire--
Short Form.
Parent 667 1 15/60 167
Neurobehavioral
Test Battery.
Child 667 1 90/60 1,000
Neurobehavioral
Test Battery.
Education Specialists......... Child School 48 14 20/60 224
Record
Abstraction
Form.
Medical Record Specialists.... Medical Record 150 13 20/60 650
Abstraction
Form--Adult.
Medical Record 50 13 20/60 217
Abstraction
Form--Child.
---------------------------------------------------------------
Total..................... ................ .............. .............. .............. 5,269
----------------------------------------------------------------------------------------------------------------
Jeffrey M. Zirger,
Lead, Information Collection Review Office, Office of Scientific
Integrity, Office of Science, Centers for Disease Control and
Prevention.
[FR Doc. 2019-08150 Filed 4-22-19; 8:45 am]
BILLING CODE 4163-18-P