Download:
pdf |
pdfNational Institute of Environmental Health Sciences (NIEHS)
GuLF Study - to IRB
11/3/2010
GuLF Study:
Gulf Long-Term Follow-Up Study for Oil Spill Clean-Up
Workers and Volunteers
Dale P. Sandler, Ph.D.
Principal Investigator
Division of Intramural Research
Epidemiology Branch
National Institute of Environmental Health Sciences
Richard K. Kwok, Ph.D.
Lead Associate Investigator
Epidemiology Branch
Division of Intramural Research
National Institute of Environmental Health Sciences
Lawrence S. Engel, Ph.D.
Associate Investigator
Epidemiology Service
Memorial Sloan-Kettering Cancer Center
and
Epidemiology Branch
Division of Intramural Research
National Institute of Environmental Health Sciences
Christine Parks, Ph.D.
Associate Investigator
Epidemiology Branch
National Institute of Environmental Health Sciences
Stephanie J. London, M.D., Dr.P.H.
Associate Investigator
Epidemiology Branch
National Institute of Environmental Health Sciences
Aubrey K. Miller, M.D., M.P.H.
Associate Investigator
Office of the Director
National Institute of Environmental Health Sciences
Aaron Blair, Ph.D.
Consultant
Occupational and Environmental Epidemiology Branch
National Cancer Institute
Page 1 of 98
National Institute of Environmental Health Sciences (NIEHS)
John Hankinson, Ph.D.
Consultant
Hankinson Consulting, Inc.
Mark Stenzel
Consultant
Exposure Assessment Applications, LLC.
Patricia A. Stewart, Ph.D.
Consultant
Stewart Exposure Assessments, LLC.
Page 2 of 98
GuLF Study - to IRB
11/3/2010
National Institute of Environmental Health Sciences (NIEHS)
GuLF Study - to IRB
11/3/2010
Table of Contents
Table of Contents................................................................................................ 3
List of Acronyms................................................................................................. 7
Protocol Summary .............................................................................................. 9
Précis ................................................................................................................. 10
Schematic of Study Design.............................................................................. 12
Background Information and Scientific Rationale ......................................... 13
1
Study Objectives .................................................................................... 15
1.1 Primary Objective ................................................................................. 16
1.2 Secondary Objectives........................................................................... 16
1.3 Sub-study Objectives............................................................................ 16
2
Study Design .......................................................................................... 17
2.1 Description of the Study Design ........................................................... 17
2.1.1
Study Population ...........................................................................17
2.1.2
Study Cohort and Sub-cohorts ......................................................18
2.1.3
Exposure Reconstruction ..............................................................20
2.2 Eligibility Criteria ................................................................................... 23
2.2.1
Rationale for including only workers or those who were trained ....23
2.2.2
Rationale for Exclusions ................................................................24
2.3 Recruitment .......................................................................................... 24
2.3.1
Recruitment Database...................................................................24
2.4 Community and Scientific Outreach ..................................................... 26
2.4.1
Meetings with potentially affected groups......................................26
2.4.2
Community Advisory Group...........................................................29
2.4.3
Communicating the Study to the Community ................................29
2.4.4
Scientific Outreach ........................................................................31
2.5 Enrollment Procedures and Enrollment Questionnaire ......................... 31
2.6 Tracing.................................................................................................. 32
2.7 Procedures for Enrolling Cohort Members............................................ 33
2.7.1
Recruitment and Retention............................................................33
2.7.2
Recruitment/Retention Strategies and Approach ..........................34
2.8 Recruitment of Special Populations...................................................... 34
2.8.1
Special Issues in Recruiting Vietnamese Participants ...................35
2.8.2
Special Issues in Recruiting Creole-Speaking Persons.................36
2.8.3
Special Issues in Recruiting Women .............................................36
2.8.4
Special Issues in Persons with Reactive Airways Disease............37
2.8.5
Other Special Populations .............................................................37
2.9 Home Visit ............................................................................................ 37
National Institute of Environmental Health Sciences (NIEHS)
GuLF Study - to IRB
11/3/2010
2.9.1
Advance Study Packet ..................................................................37
2.9.2
In-Home Visit .................................................................................38
2.9.3
Baseline Questionnaire .................................................................39
2.9.4
Anthropometric/Physiological Measures........................................40
2.9.5
Collection of Biological Samples ...................................................43
2.9.6
Home Environment Sampling........................................................44
2.9.7
In-Home Biospecimen Processing and Shipment .........................45
2.10 Reports to Participants, Health Care Referrals and Incident Reports... 45
2.10.1 Overview .......................................................................................45
2.10.2 Home Visits or Participant Evaluations at other Locations ............46
2.10.3 Home Visit/Evaluation Measurements & Testing...........................48
2.10.4 Follow-up Actions for Abnormal Findings ......................................48
2.10.5 Abnormal Findings Form ...............................................................53
2.10.6 Follow-up Reports & Information ...................................................53
2.11 Laboratory Biospecimen Processing and Storage................................ 54
2.11.1 Central Laboratory Processing ......................................................54
2.11.2 Study Sample Long-Term Storage at the NIEHS Repository ........55
2.11.3 Analyses (including future studies) ................................................55
2.12 Follow-Up of Cohorts ............................................................................ 56
2.12.1 Telephone Questionnaires (Year 2 and 4).....................................56
2.12.2 Biomedical Surveillance Sub-cohort Follow-up (Year 1 and 3)......57
2.12.3 Annual Morbidity and Mortality Outcomes (Year 2 and later) ........57
2.12.4 Follow-up in Years 6-10.................................................................57
2.13 Retention Strategies ............................................................................. 57
2.13.1 Annual Update of Contact Information...........................................57
2.13.2 Newsletters and Other Mailings.....................................................58
2.13.3 Study Website ...............................................................................58
2.13.4 Social Media..................................................................................58
2.13.5 Community Partnerships and Outreach.........................................59
2.14 Remuneration ....................................................................................... 59
2.15 Study Timeline...................................................................................... 60
3
Evaluation of Benefits and Risks.......................................................... 62
3.1 Potential Benefits.................................................................................. 62
3.2 Potential Risks...................................................................................... 62
4
Adverse Event Reporting ...................................................................... 63
5
Study Oversight ..................................................................................... 63
6
Statistical Analysis Methods................................................................. 64
Treatment of Exposure Status and Health Outcomes .......................... 64
Statistical Methods to Address Study Objectives.................................. 64
Interim and Safety Analyses ................................................................. 66
Laboratory QA/QC Analyses ................................................................ 66
Sample Size Considerations and Power............................................... 67
6.1
6.2
6.3
6.4
6.5
Page 4 of 98
National Institute of Environmental Health Sciences (NIEHS)
6.5.1
6.5.2
GuLF Study - to IRB
11/3/2010
Estimated sizes of worker (exposed) and non-worker (unexposed)
groups ...........................................................................................67
Sample Power ...............................................................................68
7
Analysis Plan.......................................................................................... 71
7.1 Primary Endpoints ................................................................................ 71
8
Training, Quality Control, and Quality Assurance .............................. 74
8.1 Staff Recruitment and Enrollment Process ........................................... 74
8.1.1
Telephone Interviewers .................................................................74
8.1.2
Home Visit Personnel ....................................................................75
8.1.3
Monitoring of Recruitment and Field Activities...............................76
8.1.4
Personal Safety .............................................................................76
8.1.5
Mandatory Reporting Requirements..............................................77
8.1.6
Identifying and Dealing with Mental Health Issues ........................77
8.1.7
Reporting Individual Results to the Participants ............................78
8.2 Data Quality Control ............................................................................. 79
8.2.1
Data Collection Quality Control .....................................................79
8.2.2
Data Storage .................................................................................79
8.2.3
Data Management & Communications ..........................................79
8.3 Laboratory Procedures ......................................................................... 80
8.3.1
Laboratory Data Quality Control ....................................................80
8.3.2
Quality Control Specimen Collection .............................................81
8.4 Run-in Period........................................................................................ 81
9
Human Subjects Protections ................................................................ 82
Institutional Review Board .................................................................... 82
Informed Consent Process ................................................................... 82
Participant Confidentiality ..................................................................... 83
Study Discontinuation ........................................................................... 83
9.1
9.2
9.3
9.4
10
Data Handling and Record Keeping ..................................................... 84
10.1 Data Capture Methods.......................................................................... 84
10.2 Data Management Responsibilities ...................................................... 85
10.3 Data Access and Sharing ..................................................................... 86
10.3.1 Access to Biospecimens and Use of Cohort for Add-on Studies ...86
10.4 Study Records Retention...................................................................... 86
Appendix A: Scientific References............................................................... 88
Appendix B: Schedule of Procedures/Evaluations..................................... 95
Appendix C: Lab Processing Flow Sheet/Template for Specimen
Collection................................................................................................ 96
Appendix D: Informed Consent Form ................ Error! Bookmark not defined.
Appendix E: Informed Consent Quick Reference GuideError! Bookmark not defined.
Page 5 of 98
National Institute of Environmental Health Sciences (NIEHS)
Appendix F:
GuLF Study - to IRB
11/3/2010
Lead Letter ..................................... Error! Bookmark not defined.
Appendix G: Brochure......................................... Error! Bookmark not defined.
Appendix H: Frequently Asked Questions ........ Error! Bookmark not defined.
Appendix I:
Enrollment Questionnaire ............. Error! Bookmark not defined.
Appendix J:
Baseline Questionnaire ................. Error! Bookmark not defined.
Appendix K: Work Events Calendar................... Error! Bookmark not defined.
Appendix L:
Report to Participants (In-Home).. Error! Bookmark not defined.
Appendix M: Participant Blood Pressure Report (in home)Error! Bookmark not defined.
Appendix N: Report to Participant – Referral Guide (Examples)Error! Bookmark not defined.
Appendix O: Example of the Physician Notification LetterError! Bookmark not defined.
Appendix P: Report to Participant – Normal Values (Mailed Follow-up)Error! Bookmark not d
Appendix Q: Report to Participant – Abnormal Values (Mailed Followup)
Error! Bookmark not defined.
Appendix R: Example of Available Environmental Monitoring DataError! Bookmark not defin
Page 6 of 98
National Institute of Environmental Health Sciences (NIEHS)
List of Acronyms
ACD
AE
AAPOR
AIHA
ASTHO
ATS
ATSDR
BFR
BISCO
BP
BPA
BPSOS
BRFSS
CAG
CAI
CAPI
CATI
CBC
CDC
CLSI
CNS
CPL
CS
DMS
DNA
EPA
EPL
ERS
FDA
FEV1
FMV
FVC
GCF
GCP
GIS
GPS
HVA
HVAC
IL-18
IOM
IRB
JEM
Acid/Citrate/Dextrose
Adverse event
American Association for Public Opinion Research
American Industrial Hygiene Association
Association of State and Territorial Healthcare Officials
American Thoracic Society
Agency for Toxic Substances and Disease Registry
Brominated flame retardant
Bayou Interfaith Shared Community Organizing
British Petroleum
Bisphenol A
Boat People SOS
Behavioral Risk Factor Surveillance System
Community Advisory Group
Computer-Assisted Interview
Computer-Assisted Personal Interview
Computer-Assisted Telephone Interview
Complete blood count
Centers for Disease Control and Prevention
Clinical Laboratory Standard Institute
Central Nervous System
Central processing lab
Clinical specialist
Data management system
Deoxyribonucleic acid
Environmental Protection Agency
Environmental Pathology Laboratories
European Respiratory Society
Food and Drug Administration
Forced Expiratory Volume in First Second
First morning void
Forced Vital Capacity
Gulf Coast Fund
Good Clinical Practices
Geographic Information System
Global Positioning System
Home Visit Agent
Heating, ventilating, and air conditioning
Interleukin-18 (IL-18)
Institutes of Medicine
Institutional Review Board
Job-exposure matrix
GuLF Study - to IRB
11/3/2010
National Institute of Environmental Health Sciences (NIEHS)
KIM-1
LFT
LN2
MQVN CDC
MVV
NAGs
NDI
NGAL
NGO
NHANES
NIEHS
NIH
NIOSH
NOAA
NSDUH
NTP
OSHA
PAH
PEC
PFT
PTSD
QEESI
RBC
RFP
RNA
VOC
WBC
GuLF Study - to IRB
11/3/2010
Kidney injury molecule-1
Liver function test
Liquid Nitrogen
Mary Queen of Vietnam Community Development Corporation
Maximum Voluntary Ventilation
N-acetyl-beta-D-glucosaminidase
National Death Index
Neutrophil gelatinase-associated lipocalin
Non-governmental organization
National Health and Nutrition Examination Survey
National Institute of Environmental Health Sciences
National Institutes of Health
National Institute of Occupational Safety and Health
National Oceanic and Atmospheric Administration
National Survey on Drug Use and Health
National Toxicology Program
Occupational Safety and Health Administration
Polycyclic aromatic hydrocarbon
Petroleum Education Council
Pulmonary Function Testing
Post traumatic stress syndrome
Quick Environment Exposure Sensitivity Inventory
Red blood cells
Request for proposal
Ribonucleic Acid
Volatile organic compound
White blood cells
Page 8 of 98
National Institute of Environmental Health Sciences (NIEHS)
GuLF Study - to IRB
11/3/2010
Protocol Summary
Full Title:
Gulf Long-Term Follow-Up Study for Oil Spill CleanUp Workers and Volunteers
Short Title:
GuLF Study
Conducted by:
NIEHS and SRA (NIEHS Epidemiology Branch
Clinical Research Contractor)
Principal Investigator:
Dale Sandler, Ph.D.
Division of Intramural Research
Epidemiology Branch
National Institute of Environmental Health Sciences
Sample Size:
55,000
Study Population:
Workers and volunteers engaged or potentially
engaged in oil spill clean-up operations in the Gulf of
Mexico
Accrual Period:
11 or 12/2010 – 5 or 6/2012
Study Design:
Closed prospective cohort
Study Duration:
10 years initially, with the possibility of extending the
follow-up period
Primary Objective:
To investigate potential short- and long-term health
effects associated with oil spill clean-up
activities/exposures surrounding the Deepwater
Horizon disaster
Secondary Objectives:
To investigate biomarkers of potentially adverse
biological effect in relation to oil spill clean-up
activities/exposures
To create a resource for additional collaborative
research on focused hypotheses or subgroups
To create a resource to better understand the short
and long-term human health effects of oil and oil
dispersants in the environment
Primary Endpoints:
Respiratory, genotoxic, hematologic, neurologic,
immunologic, and mental health
Secondary Endpoints:
Cancer, reproductive, cardiovascular, hepatic, and
renal effects
Page 9 of 98
National Institute of Environmental Health Sciences (NIEHS)
GuLF Study - to IRB
11/3/2010
Précis
The Gulf Longitudinal Follow-up (“GuLF”) Study will investigate potential short- and longterm health effects associated with the clean-up activities of the oil spill among a cohort
of workers and volunteers involved in the Deepwater Horizon disaster. Over 100,000
persons have completed safety training in preparation for participation in clean-up
activities related to the spill. Crude oil, burning oil, and the dispersants used during
clean-up efforts contain a range of known and suspected toxins. Exposures among
persons involved in clean-up range from negligible to potentially significant, especially
for workers involved in tasks associated with direct exposure to crude or burning oil, or
to chemical dispersants. However, prediction of adverse health effects is not possible
because the long-term human health consequences of oil spills are largely unknown due
to the dearth of research in this area. The potential health effects associated with the
levels of exposure experienced by clean-up workers are largely unstudied. Heat and
stress experienced by these workers may also have adverse long-term health effects. In
addition to the oil itself, the widespread economic and lifestyle disruption caused by the
oil spill may contribute to mental health problems among this population.
The over-arching hypotheses of this study are:
1. Exposure to constituents of oil, dispersants, and oil-dispersant mixtures, and to
spill-related stress by workers engaged in clean-up of the Deepwater Horizon oil
spill are associated with adverse health effects, particularly respiratory,
neurological, hematologic, and psychological or mental health.
2. There are exposure-response relationships between the above exposures and
health effects.
3. Biomarkers of potentially adverse biologic effects are associated with the above
exposures.
Based on what is known about individuals involved in clean-up efforts, the cohort will
consist primarily of English-, Spanish-, or Vietnamese-speaking adults who performed
oil-spill clean-up-related work (“exposed”) and similar persons who did not engage in
clean-up-related work (“unexposed” controls). Accommodations for enrolling
participants speaking other languages will be developed through community
collaborations as appropriate. Workers will be sampled from across job/potential
exposure groups. A total of approximately 55,000 persons are expected to be enrolled
into the cohort. A random sample of the full cohort, stratified by category of job/potential
exposure (including N~7,000 with no oil-spill work to serve as controls) and oversampled
for workers with higher potential exposures, will be enrolled into an Active Follow-up
Sub-cohort (N~27,000). A random sample of the Active Follow-up Sub-cohort, also
stratified by category of job/potential exposure and oversampled for workers with higher
potential exposures, will be enrolled into a Biomedical Surveillance Sub-cohort
(N~5,000). Participants will be interviewed about their clean-up-related tasks,
demographic and socioeconomic factors, occupational and health histories,
psychosocial factors, and physical and mental health. Members of the Active Follow-up
Sub-cohort will also be asked to provide biological samples (blood, urine, hair, toe nail
clippings, and possibly saliva) and environmental samples (house dust) and will have
basic clinical measurements (height, weight, waist and hip circumference, blood
pressure, urinary glucose levels, FEV1 and FVC as a measure of pulmonary function)
taken during home visits at baseline. The Biomedical Surveillance Sub-cohort will
participate in a more comprehensive clinical assessment after the initial home visit,
including more comprehensive pulmonary function testing, neurological testing, and
Page 10 of 98
National Institute of Environmental Health Sciences (NIEHS)
GuLF Study - to IRB
11/3/2010
collection of additional biological and environmental samples. The specific tests to be
performed and clinical protocols will be developed in collaboration with extramural
investigators selected through a request for proposals (RFP). When developed, the
protocol for this portion of the study will be submitted separately to the Institutional
Review Board as a study amendment.
Exposures will be estimated using detailed job-exposure matrices developed from data
from monitoring performed by different agencies and organizations during the crisis, as
well as information on recommended or actual use of personal protection, information
obtained by interview, and the available scientific literature. It should be noted that, in the
absence of individual or group monitoring data for most workers, estimates of exposure,
whether based on job activities or on more refined job-exposure matrices, will indicate
the degree of potential exposure (i.e., exposure opportunity) rather than known
exposure. We will investigate acute health effects via self-report from the enrollment
interview among all cohort members and also via clinical measures and biological
samples from Active Follow-up Sub-cohort members. All cohort members will be
followed for development of a range of health outcomes through record linkage (cancer,
mortality) and if feasible, through linkage with electronic medical records that may
become available during the course of follow-up. Health outcomes among the Active
Follow-up Sub-cohort will also be identified through self-report via periodic follow-up
interviews. Additional outcome information will be obtained on the Biomedical
Surveillance Sub-cohort from periodic follow-up clinical evaluations (e.g., spirometry,
neurological testing) and analysis of follow-up biospecimens (e.g., immunologic
parameters, liver function, renal function, DNA damage). Follow-up of the entire cohort
is initially planned for 10 years, with extended follow-up possible depending upon
scientific and public health needs and the availability of funds.
Recruitment of subjects should begin in November or December 2010, with the
telephone interviews expected to be completed within 9-12 months and the baseline
home visits within 18 months. We will initially target workers residing in the five most
affected Gulf States (LA, MS, AL, FL, and TX), although we may expand to other states
if further information about the geographic distribution of workers and their potential
exposures warrants additional follow-up in these states. We will work closely with a
Community Advisory Board to develop community support for this study and appropriate
communications and study materials.
Page 11 of 98
National Institute of Environmental Health Sciences (NIEHS)
Schematic of Study Design
Page 12 of 98
GuLF Study - to IRB
11/3/2010
National Institute of Environmental Health Sciences (NIEHS)
GuLF Study - to IRB
11/3/2010
Background Information and Scientific Rationale
There has been little research of the long-term health effects from oil spills despite the
fact that between 1970 and 2009, there were 356 spills of more than 700 tons from oil
tankers, with approximately 38 of these spills affecting coastal populations [International
Tanker Owners Pollution Federation Limited (ITOPF) 2009, Aguilera, et al. 2010]. The
Deepwater Horizon disaster, with its release of approximately 5 million barrels (~680,000
tons) of crude oil into the Gulf of Mexico, is far larger than any of these tanker spills.
Given the magnitude of this spill and the scope of the potential exposures – at least
55,000 workers involved in clean-up efforts and countless residents of the affected areas
– study of the human health effects of this spill is urgently needed to monitor Gulf cleanup workers and to understand the adverse consequences of oil spills in general.
Crude oil is a complex mixture containing a range of known and suspected toxins,
including volatile organic compounds (VOCs), polycyclic aromatic hydrocarbons (PAHs),
hydrogen sulfide, and heavy metals. VOCs, particularly benzene, have been linked to
lymphohematopoietic malignancies [Savitz and Andrews 1997, Hayes, et al. 2001,
Glass, et al. 2003, Steinmaus, et al. 2008, Baan, et al. 2009] and kidney dysfunction
[Chang, et al. 2010]. They can also cause central nervous system (CNS) depression,
respiratory irritation, and immune system alterations [Kirkeleit, et al. 2006, Gillis, et al.
2007, Lee, et al. 2007, Cho 2008]. Naphthalene, which causes olfactory
neuroblastomas, nasal tumors, and lung tumors in rodents, is listed as possibly
carcinogenic to humans (Group 2B) by IARC [IARC 2002]. Polycyclic aromatic
hydrocarbons (PAHs) include known carcinogens and may alter reproductive and
immune functions [Agency for Toxic Substances and Disease Registry (ATSDR) 1995].
Hydrogen sulfide can cause acute and chronic CNS effects such as headaches, poor
attention span, poor memory, and poor motor function [Agency for Toxic Substances
and Disease Registry (ATSDR) 2006]. Heavy metals found in crude oil, including
arsenic, cadmium, chromium, manganese, copper, nickel, vanadium, and lead, have a
range of adverse health effects, including neurotoxicity and carcinogenicity, renal and
immunotoxicity [ATSDR 1999, 2004, 2005, 2007a, 2007b, 2008a, 2008b, 2009, Hazen,
et al. 2010, Camilli, et al. 2010, Botello, et al. 1997].
Burning oil produces particulates, which have adverse cardiac and respiratory effects,
and may generate dioxins because of incomplete combustion in the presence of chlorine
in the sea water (Howard 2010).
The dispersants used to break up the oil contain a number of respiratory irritants,
including 2-butoxyethanol, propylene glycol, and sulfonic acid salts. Heat and stress
experienced by the clean-up workers may also have adverse health effects. In addition
to exposures from the oil itself, the widespread economic disruption caused by the oil
spill may also contribute to mental health problems in a population with potentially
increased vulnerability due to prior exposures to trauma, financial strain and social
stressors arising from other recent disasters [Galea, et al. 2008]. Such stressors may
also adversely impact physical health.
The few studies that have evaluated the human health consequences of oil spills have
primarily focused on acute physical effects and psychological sequelae. These studies
have examined the Exxon Valdez (Alaska, 1989), Braer (Shetland Islands, UK, 1993),
Sea Empress (Wales, UK, 1996), Nakhodka (Oki Islands, Japan, 1997), Erika (Brittany,
France, 1999), Prestige (Galicia, Spain, 2002) and Tasman Spirit (Karachi, Pakistan,
2003) oil tanker spills. Most of these studies were cross-sectional. A number of the
studies reported respiratory symptoms, including cough and shortness of breath
Page 13 of 98
National Institute of Environmental Health Sciences (NIEHS)
GuLF Study - to IRB
11/3/2010
[Carrasco, et al. 2006, Janjua, et al. 2006, Meo, et al. 2009, Sim, et al. 2010]. In a followup study among clean-up workers of the Prestige oil spill, Zock et al [2007] observed
that lower respiratory tract symptoms persisted 1 to 2 years after exposure had ended
(although the excess risk decreased with increasing time from last exposure) and that
the symptoms showed exposure-response patterns in relation to number of exposed
days, exposed hours per day, and number of activities. Meo et al [2008, 2009] reported
a reduction in forced vital capacity (FVC), forced expiratory volume in first second
(FEV1), and forced expiratory flow and maximum voluntary ventilation (MVV), including
exposure-response trends, in a small study of workers involved in the clean-up of the
Tasman Spirit oil spill. Other commonly reported symptoms in these studies include itchy
eyes, nausea/vomiting, dizziness, and headaches [Campbell, et al. 1993, Lyons, et al.
1999, Morita, et al. 1999, Carrasco, et al. 2006, Janjua, et al. 2006, Meo, et al. 2009,
Sim, et al. 2010], and skin irritation/dermatitis [Campbell, et al. 1993, Janjua, et al. 2006,
Sim, et al. 2010]. It is worth noting that, among Prestige oil spill clean-up workers, proper
safety training was associated with greater use of protective equipment and a lower
frequency of health problems [Carrasco, et al. 2006], which indicates that training can be
effective in prevention.
In addition to health effects induced by chemical and physical exposures, physical and
mental health may be adversely affected through pathways involving physiological and
psychological responses to acute and chronic stressors related to the disaster. Adverse
psychological consequences have frequently been linked to previous oil spills. Excess
prevalence of generalized anxiety disorder, posttraumatic stress disorder (PTSD), and
depressive symptoms were observed among communities affected by the Exxon Valdez
oil spill approximately one year after the spill occurred [Palinkas, et al. 1993]. Similar
patterns of higher anxiety and depression scores and worse mental health were
observed among communities near the Sea Empress spill [Lyons, et al. 1999]. The
Braer spill was associated with increased somatic symptoms, anxiety, and insomnia, but
not personal dysfunction or severe depression [Campbell, et al. 1994]. Worse mental
health scores were related to proximity to the Prestige spill [Sabucedo, et al. 2010].
In studying stress-related effects, it will be important to consider measures of mental
health and biological response to evaluate both subjective and objective outcomes. In a
community-based study of residents living near a petrochemical complex, perceived
health was related to perceived risks due to chemical exposures, while inflammatory
cytokine levels were related to objective proximity to the complex [Peek, et al. 2009]. In
the same community, interviews after a petrochemical accident revealed significant
decreases in perceived physical and mental health associated with multiple covariates,
including lower education, distance and impact of the disaster [Peek, et al. 2008].
Susceptibility to the adverse effects of disasters may be increased by a variety of
factors, including extent of exposure, female gender, middle age, ethnicity or minority
status, pre-existing mental and physical health, economic and psychosocial resources
[Norris, et al. 2002]. Consequently, the stress-related effects of the Deepwater Horizon
Disaster may be amplified in a population still recovering from the impact of other recent
disasters and in vulnerable subpopulations [King and Steinmann 2007, Galea, et al.
2008]. Research in the affected region also needs to take into account the unique
history and potential vulnerability of migrants, ethnic or cultural minorities in the study
population, e.g., Vietnamese [Palinkas, et al. 1992, Do, et al. 2009, Norris, et al. 2009].
Studies of genotoxicity and endocrine toxicity also point to potential adverse effects
among oil spill clean-up workers. All but one of these studies were conducted among
Page 14 of 98
National Institute of Environmental Health Sciences (NIEHS)
GuLF Study - to IRB
11/3/2010
clean-up workers involved in the Prestige incident. Findings include significantly higher
DNA damage, as measured by the comet assay, but not cytogenetic damage, as
measured by the micronucleus test, among exposed individuals compared to controls,
which was related to duration of exposure [Laffon, et al. 2006, Perez-Cadahia, et al.
2006]. Clean-up workers were also found to have significantly elevated blood levels of
aluminum, nickel, and lead, but decreased levels of zinc [Perez-Cadahia, et al. 2008]. In
addition, exposed workers had significant decreases in blood prolactin and cortisol levels
[Perez-Cadahia, et al. 2007]. A recently published study of the Prestige cohort
[Rodriguez-Trigo, et al. 2010] found an increased risk of structural chromosomal
alterations in circulating lymphocytes among exposed workers two years after the spill.
These results are consistent with studies showing increased DNA damage in relation to
low level exposure to benzene [Bagryantseva, et al. , Maffei, et al. 2005, Chen, et al.
2008, Fracasso, et al. 2010] and PAHs [Bagryantseva, et al. , Novotna, et al. 2007,
Gamboa, et al. 2008]. On the other hand, a study of persons affected by the Braer spill
[Cole, et al. 1997] found no evidence of genotoxicity through either DNA adducts in
peripheral blood mononuclear cells or mutations at the HPRT locus in T lymphocytes.
Studies of upstream petrochemical workers, who are likely to have many exposures
similar to that of oil spill clean-up workers, have reported excesses of leukemia, multiple
myeloma, melanoma, and esophageal adenocarcinoma [Schnatter, et al. 1992, Kirkeleit,
et al. 2008]. While such rare outcomes may take years to develop, immediate and
lasting changes may be seen in intermediate biomarkers indicating toxic effects and
potential for future disease risk. The immune system may represent a particularly
sensitive and accessible system for determining physiological impact of oil spill
exposures. For example, the hematotoxic and immunotoxic effects of benzene
exposure have been well-described, occurring even at relatively low levels of exposure
[Lan, et al. 2004]. These effects, indicated by downward shifts in leukocyte and red
blood cell counts, may also be more apparent in susceptible subgroups defined by
genetic variation in inflammatory, apoptotic, or metabolizing pathways [Lan, et al. 2005,
Kim, et al. 2007, Lan, et al. 2009, Zhang, et al. 2010]. Benzene’s toxicity to
hematopoietic progenitor cells may also impart long-term effects on the immune system
leading to premature immunosenescence. This idea is supported by the finding that
higher personal benzene exposures in traffic officers were associated with significantly
shorter leukocyte DNA telomere length [Hoxha, et al. 2009], a marker of immune aging
that has been related to risk of multiple chronic disease outcomes and mortality. Other
intermediate markers related to chronic disease risk include inflammatory cytokines,
antibodies indicating reduced immunity to latent viral infections, or auto-antibodies,
though limited information exists on these measures in past studies of oil spill or
petrochemical workers.
1
Study Objectives
This research effort is designed to investigate potential short- and long-term health
effects among workers engaged in clean-up activities surrounding the Deepwater
Horizon oil spill. Given the very limited health effects research conducted to date on oil
spill clean-up workers, the GuLF Study is designed not to study a few narrow a priori
hypotheses, but rather to allow the investigation of a wide range of potential adverse
health effects, including physical, psychological, and biological effects. The long-term
goal of this study is not only to identify adverse health outcomes related to clean-up
activities among the Deepwater Horizon responders, but also to assemble information
Page 15 of 98
National Institute of Environmental Health Sciences (NIEHS)
GuLF Study - to IRB
11/3/2010
that can be used for prevention and intervention of adverse health outcomes in any
future similar disasters.
The over-arching hypotheses of this study are:
1. Exposure to constituents of oil, dispersants, and oil-dispersant mixtures, and to
spill-related stress by workers engaged in clean-up of the Deepwater Horizon oil
spill are associated with adverse health effects, particularly respiratory,
neurological, hematologic, and psychological or mental health.
2. There are exposure-response relationships between the above exposures and
health effects.
3. Biomarkers of potentially adverse biologic effects are associated with the above
exposures.
1.1
Primary Objective
The primary objective of the GuLF Study is to assess a wide range of potential shortand long-term human health effects associated with clean-up and disposal activities
surrounding the Deepwater Horizon oil spill in the Gulf of Mexico. Health areas of
interest include, but are not limited to, respiratory, cardiovascular, hematologic,
dermatologic, neurologic, cancer, reproductive, mental health, substance abuse,
immunologic, hepatic, and renal effects.
1.2
Secondary Objectives
A key aspect of assessing these health effects will be to investigate biomarkers of
potentially adverse biological effect, including DNA damage, aberrant epigenetic profiles,
and alterations in gene expression, some of which have been observed in previous
studies of oil spill clean-up workers.
Additionally, secondary objectives of the study are to: 1) create a resource for additional
collaborative research on specific scientific hypotheses or on subgroups of interest. We
will work with external scientists to facilitate nested sub-studies within the existing cohort
to examine outcomes and exposure subgroups of interest; and 2) create a resource to
better understand the short and long-term human health effects of oil and oil dispersants
in the environment.
1.3
Sub-study Objectives
At this time, one sub-study, the Biomedical Surveillance Sub-cohort, is planned as an
integral part of the study proposal although the specific tests to be carried out and the
implementation details are not yet designed. The detailed protocol (s) for this Subcohort will be developed in collaboration with extramural partners and will be separately
peer-reviewed. Objectives of the Biomedical Surveillance Sub-cohort will include
investigating immediate and ongoing physiological and clinical parameters in a group of
highly exposed workers and a smaller number of unexposed workers. Establishing this
exposure-enriched group that contains more detailed information on adverse outcomes
and repeated biological measures will provide an important resource for longitudinal
studies and enable nested comparisons with measures obtained on the larger cohort.
Page 16 of 98
National Institute of Environmental Health Sciences (NIEHS)
2
Study Design
2.1
Description of the Study Design
GuLF Study - to IRB
11/3/2010
The GuLF Study has been designed to allow investigation of potential short- and longterm health effects associated with the oil spill clean-up work and to create a resource
for collaborative research on specific scientific hypotheses or subgroups. It is an
observational prospective cohort study that will create opportunities for both analyses of
the full cohort as well as numerous nested analyses. The design will enable investigators
to efficiently address specific hypotheses generated from previous studies of oil spill
exposures and, importantly for an exposure that has not been studied in relation to longterm health outcomes, allow them more generally to identify new symptoms and
conditions that may occur in excess among the exposed participants and determine the
extent to which any physical and mental health conditions persist. The data and the
biological and environmental samples that will be collected will allow examination of a
wide range of health areas of interest, including respiratory, cardiovascular, hematologic,
dermatologic, neurologic, cancer, reproductive, mental health, immunologic, hepatic, and
renal. The study is planned to be at least 10 years in duration, although it is anticipated
that the study may continue for 20 years or more, through record linkage, at a minimum.
Prospective studies typically have a long-term design because some diseases of
interest, such as cancer, generally have long latency periods, e.g., 15-20 years or more.
Consequently, we will consider extending this study, based on what we learn during the
initial study period, scientific and public health needs, and on the availability of funds.
2.1.1
Study Population
To capture a representative sample of the clean-up workers and controls, we will target
individuals across the various categories of job/potential exposure from the Petroleum
Education Council (PEC), National Institute of Occupational Safety and Health (NIOSH),
or other worker/volunteer rosters and administrative lists. These individuals are potential
participants because they are believed to have engaged in clean-up work or participated
in worker training modules in anticipation of such work. We will exclude individuals such
as journalists who did not engage in clean-up activities but were required to undergo
safety training to gain access to worker staging areas (and, therefore, may appear on
the PEC list). These individuals will be determined from either the training lists (i.e.,
individuals who indicated that they intended to work for less than one week) or via
screening questions during the enrollment telephone interview. We will use data from
our planned mini-pilot (at the beginning of field work) to determine the feasibility of also
efficiently identifying and excluding individuals such as caterers and administrative/office
staff who engaged in clean-up related activities, but not clean-up activities per se;
however, this issue is complex and requires data that will become available only after we
go into the field. We define potentially exposed subjects as individuals who completed
at least one day of oil-spill clean-up-related work, either paid or volunteer. We define
unexposed subjects as eligible individuals who completed safety training in anticipation
of performing clean-up work but did not do so. Additional unexposed subjects will be
recruited from among Federal workers eligible for clean-up work but ultimately not
deployed. Selection for the Active Follow-up Sub-cohort will cover all levels of potential
exposure but will oversample workers with the highest potential exposures to oil, oil
byproducts and dispersants. We will conduct interviews in English, Spanish, and
Vietnamese. Special accommodation will be made for those speaking other languages
Page 17 of 98
National Institute of Environmental Health Sciences (NIEHS)
GuLF Study - to IRB
11/3/2010
(e.g. Haitian Creole, etc.), if feasible and warranted by the number of workers speaking
these languages. PEC training was conducted in English, Spanish, and Vietnamese
only so we do not anticipate a large number of those speaking other languages.
However, should this change based on data from the PEC list or input from community
groups, we will submit an amendment to the IRB with appropriate translated documents
for approval.
2.1.2
Study Cohort and Sub-cohorts
After administering a screening enrollment questionnaire to each potential cohort
member, we will use a two-stage sampling design to randomly sample individuals across
categories of job/potential exposure for invitation to participate in the Active Follow-up
Sub-cohort (N~27,000), which will be nested within the full cohort (N~55,000). We will
also randomly sample individuals within the Active Follow-up Sub-cohort across
categories of job/potential exposure for inclusion in the Biomedical Surveillance Subcohort (“tagging” N~6,250 with the expectation of obtaining agreement from N~5,000).
This nested design represents an efficient and cost-effective way to include most of the
clean-up workers in a prospective study and also to obtain comprehensive and detailed
clinical and biologic information on a scientifically appropriate sample of the total group
while maintaining statistical integrity through the use of the two-stage random sampling
design. The study effort, participant commitment, and potential knowledge gain
increases from passively followed members of the full cohort to members of the Active
Follow-up Sub-cohort to members of the Biomedical Surveillance Sub-cohort. For each
sub-cohort, we will oversample from job categories that had higher potential exposures
and/or were smaller to ensure adequate representation of higher potential exposures
and of all tasks performed.
Workers will primarily be identified from a combined list of workers who completed a
voluntary NIOSH Roster form and additional workers identified through the PEC list and
other lists that may become available of persons who may have been involved in cleanup activities (see Section 2.3.1 for a description of the lists of potential subjects.)
The Active Follow-up Sub-cohort will contain ~20,000 workers (“exposed”) from across
all job categories and ~7,000 controls (“unexposed”). While these groups are selected
on the basis of their potential exposure to oil or dispersants used in clean-up, both
groups will contain individuals who are “exposed” and not exposed to the stresses
associated with having lost their source of income due to the oil spill or living with
economic or social uncertainty due to their residential proximity to the spill. This cohort
may be largely restricted to persons residing in one of the five Gulf States primarily
engaged in clean-up activities (LA, MS, AL, FL and TX), prioritizing workers closest to
the spill area. Based on data on approximately 44,000 workers from the NIOSH roster,
all but 5% of workers were from these five states. Eligibility may later be expanded to
include other states based on information on the geographic distribution of workers that
we will receive from the PEC list and other worker lists. We will recruit workers from
other states only if it is determined, upon receipt of the potential subject lists that a large
number of workers with potential high exposures came from a given state. For logistical
reasons, we will not recruit non-Federal employee controls from outside of the Gulf
States. Federal workers (e.g. Coast Guard, Occupational Safety and Health
Administration (OSHA), Fish and Wildlife Service (FWS), National Oceanic and
Atmospheric Administration (NOAA), Environmental Protection Agency (EPA), and
others) residing outside of the five Gulf States will be included. A Federal control group
of ~1,000 workers will also be recruited from among individuals eligible for clean-up work
Page 18 of 98
National Institute of Environmental Health Sciences (NIEHS)
GuLF Study - to IRB
11/3/2010
but ultimately not deployed. We will oversample certain categories of job/potential
exposure of particular interest (e.g., those with potential direct exposure to fresh crude or
burning oil or to chemical dispersants). Because there is a lack of centralized data
concerning the distribution of categories of work/potential exposure and we are likely to
determine this distribution only when the enrollment interviews are underway, we will
periodically evaluate and revise as appropriate our sampling probabilities. These
probabilities will take into account the distribution of jobs/potential exposures and
statistical power. Participants in the Active Follow-up Sub-cohort will 1) be administered
detailed interviews, 2) provide biological samples (blood, urine, hair, toe nail clippings,
and possibly saliva) and environmental samples (house dust), and 3) have basic clinical
measurements taken at enrollment, and 4) will be administered two follow-up interviews.
In contrast, passively followed members of the full cohort will be administered only a
brief telephone interview at enrollment. Disease and mortality during follow-up will be
obtained via linkage with cancer registries and State vital statistics records.
The controls will preferentially be drawn from the PEC/NIOSH lists, which include some
individuals who were trained in anticipation of being hired for clean-up work but were
never hired. At some time during the peak work weeks, employers were advised that
heat related health issues might be especially problematic for obese workers or those
with high blood pressure. Although pre-employment screening may have been advised,
it is uncertain whether or not it was systematically carried out, and if done, may have
been contractor specific. Therefore, because some potential workers may have been
turned away due to health concerns, potential controls will be asked why they did not
participate in clean-up activities. Those indicating they did not qualify for medical
reasons will be excluded as will those who completed training to facilitate receipt of a
badge to enter the area, with no intention of performing any clean-up related tasks.
Should these lists yield insufficient numbers of unexposed individuals, we will explore
strategies to identify unexposed community residents through friends/relatives identified
by workers in the cohort or though neighborhood or telephone sampling (e.g. random
digit dialing).
Because some workers from the five Gulf States will come from areas away from the
affected communities and because controls from the affected communities may have
experienced some spill-related exposures, including stress and social disruption, we will
establish two control groups. Persons from the lists described in Section 3.3.1 who are
determined to have not engaged in clean-up activities and are eligible for this study will
be placed in either a “local” control group or a “non-local” control group. The “local”
control group will consist of controls residing within the affected communities. Their
inclusions in analyses of the health effects of chemical exposures will account for the
stress and other psychosocial factors experienced by clean-up workers residing in the
affected communities. The “non-local” control group will consist of individuals residing
within the affected states, but outside of the affected communities. These individuals will
serve as a control group in evaluation of spill-related stress and other societal effects
that may affect both exposed clean-up workers and unexposed controls residing in the
affected communities. Based on residence information from the 44,000 persons in the
NIOSH roster, 77% of the workers were “local” (i.e. lived in a coastal county in one of the
five states). Consequently, we will oversample “non-local” trainee controls to provide
sufficient statistical power for analyses involving this group. A third smaller control group
will be established from among Federal workers (e.g. Coast Guard) who were eligible to
participate in clean-up but were not deployed. Federal workers involved in the clean-up
effort represent a number of agencies and may come from states outside of the Gulf. For
logistical reasons, we will recruit shared controls for all Federal workers (i.e., from a
Page 19 of 98
National Institute of Environmental Health Sciences (NIEHS)
GuLF Study - to IRB
11/3/2010
subset of Federal agencies involved in the clean-up). We will work with the agency
representatives to identify a source of controls that best represents these various
workers, such as Coast Guard members or Fish and Wildlife Service workers who were
not sent to the Gulf for clean-up operations but were otherwise eligible or given notice of
potential deployment.
Passively followed members of the full cohort will be those individuals who completed an
enrollment interview but were not included in the Active Follow-up Sub-cohort because
1) they did not reside in one of the targeted Gulf States, 2) they were not randomly
sampled for inclusion in the Active Follow-up Sub-cohort, or 3), they were unable or
unwilling to participate in active follow-up but are willing to be tracked over time.
Outcomes follow-up will be obtained via linkage with State cancer registries and vital
statistics databases.
The Biomedical Surveillance Sub-cohort will be an intensively evaluated subgroup
nested within the Active Follow-up Sub-cohort. It will be sampled from across the
categories of job/potential exposure and from controls, with oversampling of workers
with the highest potential exposures. Potential members of this sub-cohort will be
identified during the enrollment interview, based on their reported clean-up activities. To
achieve our target of ~5,000 members in this sub-cohort, we will identify ~6,250 potential
members during the enrollment interview, assuming that ~80% will ultimately agree to
participate in the further procedures required of the Biomedical Surveillance Sub-cohort
(given that they already agreed to participate in the Active Follow-up Sub-cohort and will
receive the benefit of more detailed health monitoring during the study) when they are
re-contacted later by extramural collaborators. This sub-cohort will undergo the same
baseline and follow-up procedures as the rest of the Active Follow-up Sub-cohort, but
will additionally participate in multiple follow-up visits involving health assessments that
include spirometry with bronchodilator challenge and neurological testing and collection
of repeat biological and environmental samples. This sub-cohort will undergo more
intensive biomonitoring than the rest of the Active Follow-up Sub-cohort, including
having their complete blood counts (CBCs), white blood cell (WBC) differentials and
more comprehensive urinalysis measured at baseline. [Note: These tests will be
performed for all 6,250 identified as potentially eligible for the Biomedical Surveillance
Sub-cohort as they must be performed on fresh samples. Similarly, lymphocytes will be
extracted and cryopreserved for the larger sample of potential participants.]
Protocols for the additional clinical examinations will be developed and implemented in
collaboration with local university partners identified through a request for proposals
(RFP) and, therefore, will not be discussed further in this protocol. These will undergo
separate scientific and Institutional Review Board (IRB) review. Consideration will be
given to focusing on the more highly exposed Gulf States (e.g. Louisiana and Alabama)
to facilitate comprehensive health examinations. We anticipate a standardized core
protocol with room for unique investigator initiated options to address additional
hypotheses.
2.1.3
Exposure Reconstruction
Although monitoring data will be available on some individuals for some exposures, most
participants in the study cohorts will lack such measurements. Because it is critical to
have some indication of quantitative levels of exposure, it will be necessary to construct
exposure indicators from the available individual and environmental monitoring data,
characteristics of clean-up tasks, work locations, and times that these events occurred.
Page 20 of 98
National Institute of Environmental Health Sciences (NIEHS)
GuLF Study - to IRB
11/3/2010
Given the absence of individual or area/group monitoring data for most workers, it is
important to note that estimates of exposure, whether dichotomous
(exposed/unexposed) or semi-quantitative (e.g., none, low, medium, high), will reflect
potential exposure rather than known exposure and references in this protocol to
exposures, except where indicated otherwise, should be interpreted as such. We will
validate the self-reported clean-up activities with security badge and payroll records to
the extent possible using available data. Moreover, we will work with survey
methodologists to ensure valid data collection. Investigators who are experts in industrial
hygiene exposure assessment will assemble exposure data and construct job-exposure
matrices for the exposures of interest using monitoring data from multiple sources.
These monitoring data, including individual measurements for some workers, area
measurements, and Health Hazard Evaluations, were collected during clean-up activities
and monitoring by OSHA, NIOSH, NOAA, EPA, Fish and Wildlife Service, US Geologic
Survey, the Coast Guard, and British Petroleum (BP). An interagency meeting was
convened on August 19 in Washington, DC to discuss these issues and identify sources
of data that could be used to reconstruct worker exposures across all tasks. An example
of these environmental monitoring data is provided in Appendix R. This spreadsheet was
first created by EPA as a way to identify data streams and later expanded to identify any
sampling within the Deepwater Horizon Response that may be redundant or
complementary. It will serve as a useful springboard from which to start cataloging the
available environmental data and will aid in the exposure assessment process.
In addition, available chemical analysis data of oil from the well, the dispersants used,
samples of weathered oil, and weather data from the period of the spill clean-up will be
considered in relation to exposure opportunities. This information will be assembled for
the exposure panel and may be used in exposure estimation and reconstruction. By
linking this exposure information with self-reported activity data, exposures will be
estimated for all included workers, including those from Federal agencies/institutions.
We will also use environmental samples (house dust), if available and appropriate, and
questionnaire data to identify relevant occupational and non-occupational exposures.
Lastly, we will evaluate existing exposure measurements on beach clean-up workers
and consider collection of additional biomonitoring data for this large subgroup if cleanup efforts are still underway at the time of cohort enrollment. A detailed protocol of
exposure assessment procedures will be developed by the study investigators in close
collaboration with the panel of experts described above.
We will work closely with academic and federal partners such as OSHA and NIOSH to
convene a panel of experts to systematically work through these exposure assessment
issues and develop a scientifically sound method for assigning exposures to the study
participants. This expert panel will develop a Job-Exposure Matrix (JEM) based on the
varied work tasks of cleanup workers and volunteers. Different dichotomous and ordinal
ranking metrics may need to be developed for the different chemicals and exposure
pathways that may be associated with different health effects. For example, a single
metric will probably not capture important differences in PAH exposure from particle
inhalation among oil burn workers versus dermal PAH exposure of absorbent boom
operators. The exposure metrics will not only need to consider differential exposures
based on job task, but will also need to consider the duration of exposures (e.g., hours
per day, total days of work).
One of the challenges of this research is that most workers and controls will have
exposures to many of the chemicals of interest that are unrelated to the oil spill. Most
persons are exposed to benzene in ambient air (usually at very low levels) and to PAHs
Page 21 of 98
National Institute of Environmental Health Sciences (NIEHS)
GuLF Study - to IRB
11/3/2010
from inhalation, dietary ingestion, and house dust. Such exposures are particularly
common among residents along the Gulf coast in Louisiana. There are also a number of
consumer products that contain 2-butoxyethanol or propylene glycol, two dispersant
ingredients of potential interest. Some workers and controls could have significant
occupational (non-spill related) exposures to some of these chemicals. In most cases,
these types of “background” exposures are likely to have similar distributions among the
worker and control populations. However, the study will need to carefully consider and
collect information to characterize these exposures. For example:
Commercial boat operators who participated in cleanup activities could
potentially receive higher long-term exposures to fuel oil and engine exhaust,
with many of the same chemical constituents as found in the spilled oil,
compared to a control group that did not include active boat operators.
Workers may come from Gulf coast locations affected by point sources of
petrochemical pollution not experienced by control living inland or in other states.
Workers hired directly by BP or its long-term contractors may have had other oil
industry jobs.
Workers hired early on may include those with prior training in hazard
remediation and may have been involved in cleanup from other smaller spills.
This potential confounding will be addressed through questionnaire data (occupational
and other relevant activities/exposures), GIS mapping as appropriate, and analysis of
biological and environmental samples. The expert panel will need to address these and
other challenges that face this critical component of the study.
While we have already consulted individually with other researchers who have examined
health effects associated with past oil spills, we are exploring the possibility of convening
an exposure assessment workshop of all of these study investigators to explore lessons
learned and to discuss findings to ensure that the GuLF Study is conducted to the stateof-the-science.
It is important to note that many scientifically rigorous epidemiologic studies have
successfully used qualitative or semi-quantitative data derived from job-exposure
matrices to investigate exposure-disease associations [Coble, et al., 2009, Allen, et al.,
2006, Baris, et al., 2004, Kromhout, et al., 1995, Laakkonen, et al., 2008, Young, et al.,
2004, Richardson, et al., 2008, Lee, et al., 2003, Elci, et al., 2003]. This representative
sample of studies linked job titles and usual job activities to available monitoring data to
create job-exposure matrices that were used to estimate exposures in the study
population. Indeed, the epidemiologic investigations surrounding the Prestige oil spill
response in Spain utilized self-reported exposure information to assess health outcomes
that otherwise might have been missed [Suarez, et al. 2005, Carrasco, et al. 2006, Zock,
et al., 2007], Such studies have yielded scientifically valuable information and
demonstrate the important role that qualitative and semi-quantitative exposure data
and/or job-exposure matrices can play in epidemiologic research.
Although the development and evaluation of job-exposure matrices for the present
worker population would ideally have been done prior to beginning subject recruitment,
this was not a feasible option for this study, as is typically the case for studies
responding to disasters. A large amount of monitoring data has already been collected,
is currently being aggregated, and will be available to us. Our main concern to this point
has been to design a scientifically rigorous study that we can get into the field as quickly
as possible and 1) capture the self-reported activities, dates, times, locations, etc. of
Page 22 of 98
National Institute of Environmental Health Sciences (NIEHS)
GuLF Study - to IRB
11/3/2010
clean-up work that these workers engaged in before their memories fade and 2) enroll
these workers into the study before they move, change phone numbers, or otherwise
become lost to follow-up.
2.2
Eligibility Criteria
We anticipate screening as many as 90,000 individuals in order to recruit approximately
55,000 volunteers primarily from five Gulf States* (LA, MS, AL, FL and TX) into the
cohort, which will include a randomly sampled Active Follow-up Sub-cohort of
approximately 27,000 individuals nested within it. Eligibility criteria for the cohort include:
18 years of age or older (i.e., state-specific minimum age of consent)
Not medically excluded from participating in clean-up activities
Fall into one of two oil-related exposure categories:
Potentially exposed subjects must have completed at least one day of oil-spill
clean-up-related work (other than safety training), either paid or volunteer.
Unexposed subjects will be individuals who completed safety training in
anticipation of performing clean-up work but did not perform any clean-up related
tasks, or other unexposed individuals invited to participate, if needed.
Invitation to enroll in the Active Follow-up Sub-cohort will be made based primarily on
level of potential exposure as well as state of residence. Sampling probabilities will vary
across categories of job/potential exposure, with probabilities of up to 100% for persons
who report having engaged in oil clean-up related activities that are suspected of having
high exposures (e.g. working at the source, skimming, incineration, booming (specifically
retrieval of contaminated boom), wildlife clean-up, etc.). Available funding imposes an
upper limit on the size of the Active Follow-up Sub-cohort, but the number of workers in
different categories of job/potential exposure is currently unknown (and will likely remain
unknown until interviewing commences). Consequently, sampling probabilities will be reevaluated and adjusted periodically as study enrollment proceeds in order to realize the
study objectives and achieve the target size of the Active Follow-up Sub-cohort.
Because of 1) the small proportion of non-Federal clean-up workers from outside of the
Gulf States (< 5%, based on current data) and 2) the substantial logistical challenges of
including these workers in the Active Follow-up Sub-cohort, we will include these
individuals in the Active Follow-up Sub-cohort only if we determine that an appreciable
number of them engaged in clean-up activities with high potential exposure. Otherwise,
these individuals will be enrolled into the passive follow-up portion of the cohort. This
strategy is the same as that employed for the non-Federal workers in this cohort.
2.2.1
Rationale for including only workers or those who were trained
Morbidity and mortality rates from the general population include individuals who are
often too sick to work. Thus, those who are hired, or trained to be hired, are generally
healthier than those who aren’t trained because relatively healthy individuals are more
likely to gain employment and remain employed – a phenomenon known as the “healthy
worker effect.” The healthy worker effect is particularly relevant in the selection of
unexposed controls. In order to obtain comparable controls for workers engaged in oil
Page 23 of 98
National Institute of Environmental Health Sciences (NIEHS)
GuLF Study - to IRB
11/3/2010
spill clean-up activities, we would need to find individuals who otherwise would have
been able to work (i.e., were healthy enough to work), but weren’t hired to do so, thus
limiting their exposure. We plan to recruit from a master list that incorporates training
and badging information (e.g., the NIOSH roster, PEC training lists, Coast Guard
deployment logs, etc.) to identify workers who were trained to participate but may or may
not have been engaged in clean-up activities (“exposed” and “unexposed,” respectively).
Since everyone in the spill area was required to have a badge, and completion of a basic
training module was required to receive a badge, volunteers should have also completed
one or more training modules before engaging in clean-up activities. Others who worked
but were not trained through the PEC will also be eligible. This includes workers whose
training was separately administered through Parish organizations and individuals who
might not have completed required training modules for language or other reasons (e.g.
crew on Vessels of Opportunity whose captains, only, received formal worker training).
While exposed and unexposed individuals will be recruited during the same enrollment
period, if we aren’t able to find suitable non-exposed individuals from this master list, we
will seek matched controls in the community through references provided by the
participants themselves, individuals from the BP claims databases, or other community
selection techniques such as random digit dialing. This may involve more time than
identification of controls from the clean-up training lists. We have planned for these
activities to occur in the later months of recruitment so that we can focus on enrolling
exposed workers first.
We will actively enroll any individual, 18 years or older (except in states where the age of
consent is older), who is on a worker or volunteer list describing any potential contact
with oil and dispersants, regardless of their gender, racial and ethnic background, or
pregnancy status. Approximately 19% of the 44,000 workers enumerated by NIOSH
were women. Although we do not anticipate a large pregnant population, there may be
individuals who were not aware that they were pregnant or who otherwise engaged in
clean-up related activities despite knowing that they were pregnant and who may be
recruited into the study.
2.2.2
Rationale for Exclusions
Participant selection and rationale for eligibility criteria have been described in detail in
Section 3.2 - Eligibility Criteria. Enrollment is open to adults of all racial and ethnic
background. Children will not be enrolled because they were not allowed to participate in
clean-up activities. Study activities present minimal risk to pregnant women. Therefore,
pregnant women will be allowed to enroll in the study, and women who become
pregnant during the study will not be withdrawn.
Those who were deemed medically ineligible to participate in clean-up activities because
of pre-existing conditions are excluded because they won’t be representative of those
individuals who were engaged in clean-up activities.
2.3
2.3.1
Recruitment
Recruitment Database
The cohort will be recruited over a 12-18 month period, starting in November or
December 2010 with the baseline home visits completed within 18 months and will
Page 24 of 98
National Institute of Environmental Health Sciences (NIEHS)
GuLF Study - to IRB
11/3/2010
These databases will be merged into a master recruitment file to identify and remove
duplicates. We expect a total of about 130,000 names from the PEC list and other
worker lists combined, which we are assuming will be reduced to about 90,000 after
eliminating duplicate names and, if possible, those who completed training only to obtain
access to the spill site, with no intention of engaging in clean-up work (e.g. reporters,
government visitors, etc.). Where possible, we will infer potential exposure through the
training the individuals obtained, their reported or anticipated activities (collected on the
NIOSH roster), and/or location in which they reported for work. However, we may not be
Page 25 of 98
GuLF Study - to IRB
11/3/2010
National Institute of Environmental Health Sciences (NIEHS)
able to definitively confirm oil spill clean-up related activities until we interview the
participant and ascertain the types of activities that they performed. Thus, initial
exposure characterization will involve a two-stage process where a participant is flagged
for potentially being exposed/non-exposed which may later be modified based on
information from the telephone enrollment questionnaire will include a series of
questions which will ascertain exposure. Exposure classification for enrollment purposes
into the Active Follow-up Sub-cohort will be based on the participant’s answers to these
exposure questions. We will try to identify and prioritize enrollment of individuals with
likely exposures so that we can better characterize their exposures, but given the
limitation of not knowing a participant’s true exposure status prior to their interview, we
will most likely be enrolling exposed participants and unexposed controls at a
comparable rate.
2.4
Community and Scientific Outreach
The goal of the community outreach efforts is to fully apprise the community of study
activities, to ensure community collaboration and support in all aspects of the study
including design, implementation, evaluation, translation, and to disseminate findings
and results. Close and ongoing community engagement is expected to enhance the
scientific validity of the study, make it more broadly relevant from a public health
perspective, and expand its benefits to the affected communities.
2.4.1
Meetings with potentially affected groups
We have already established contacts and are continuing to solicit new contacts with
several community organizations, representative worker organizations, advocacy
groups, and state and local government representatives to identify the primary health
issues of concern locally and to discuss study implementation issues across the five
state area.
We have conducted a series of meetings with state and local health department
representatives as well as with the NGOs that span the various advocacy and
occupational groups representing the workers involved in clean-up throughout the Gulf.
We met with groups in Mississippi and Alabama during the week of September 12, 2010;
Florida the week of September 19, 2010; and Louisiana during the week of October 3,
2010. Although we have been in contact by telephone and email, we are currently
working to schedule in-person meetings in Texas.
The groups we have contacted span cultural, religious, occupational, and state and local
government sectors and are continuously updated as more information and contacts are
made (current as of 10/22/2010). These groups serve as important links into the
community and can act as an informal Community Advisory Board for study protocol
issues and concerns for study investigators until a more formal Board can be
established. The groups listed below the groups that we have identified and established
contact with:
Advocates for Environmental
Human Rights
Page 26 of 98
Alabama State Health
Department
Alliance Institute
GuLF Study - to IRB
11/3/2010
National Institute of Environmental Health Sciences (NIEHS)
Asian Americans for Change,
Mississippi
Bayou Grace Community
Services
Bayou Interfaith Shared
Community Organizing (BISCO)
Louisiana Shrimp Association
Mary Queen of Vietnam
Community Development
Corporation (MQVN CDC)
Mississippi Center for Justice
Mississippi Commission on
Volunteer Service
Boat People SOS (BPSOS)
Coastal Family Health Center
Commercial Fisherman of
America
Mississippi Gulf Coast
Community College
Mobile BayKeeper
Moving Forward Gulf Coast, Inc.
Parish Presidents
South Bay Communities
Alliance, Inc.
SeaGrant Programs in LA, MS
and AL
St. Bernard Project
Steps Coalition
The Village/El Pueblo
Tri-Coastal Community Outreach
Turkey Creek Community
Initiatives
Deep South Center for
Environmental Justice
Gulf Coast Fund for Community
Renewal and Ecological Health
(GCF)
Gulf Restoration Network
Interfaith Disaster Network
Isle de Jean Charles Band of the
Biloxi Chitimacha
Local chambers of commerce
Louisiana Bayoukeeper
Louisiana Bucket Brigade
Louisiana Department of Health
and Hospitals, Region 1
United Commercial Fisherman
Association of Louisiana
Louisiana Department of Health
and Hospitals, Region 3
United Houma Nation
Louisiana Disaster Recovery
Foundation, Oil Spill Recovery
Policy & Advocacy Initiative
Vietnamese American Young
Leaders Association of New
Orleans
Louisiana Justice Institute
Vietnamese Martyr's Church
Louisiana Oystermen
Association
Zion Travelers Cooperative
Center
The meetings conducted to date with state and local health department and community
group representatives have already led to several improvements in questionnaire
development and study design. For example, the questionnaire has been revised to:
Page 27 of 98
National Institute of Environmental Health Sciences (NIEHS)
GuLF Study - to IRB
11/3/2010
Better define labor categories;
Better characterize definitions of exposure;
Improve the ability with which the workers can recall key dates in their work
history; and
Include questions about the symptoms that are of the greatest concern to the
workers so that prevalence rates can be reported to the community.
Additionally, these meetings have allowed us to expand the resources included in the
health referral network and enabled us to better tailor messages to participants about the
study’s purpose and the importance of their participation. They have also provided us
with a better understanding of the barriers in recruitment and enrollment and how to use
community-based strategies to avoid these barriers.
As we further extend community outreach efforts, we will identify Community Outreach
Coordinators to organize and implement outreach activities in each of the Gulf States
who will:
Help to build strong relationships with NGOs representing the worker and
volunteer populations across the five Gulf Coast States.
Augment an advertising campaign (as described in Section 3.4.3) with grassroots promotional activities including local media placement (church bulletins,
community newspapers, etc) and community presentations.
Assist in recruitment of special populations as needed.
In addition to the continuing efforts with public health and community group
representatives, we have been conducting outreach in the following ways:
Webinars. NIEHS hosted a 90-minute webinar with local researchers, community
organizations and others interested in the GuLF Study on August 17, 2010 and a twohour Webinar on September 15, 2010. The purpose of the webinars was to announce
publicly the plans for the GuLF Study and obtain feedback on study design and
implementation from interested stakeholders. Prior to the webinar, NIEHS distributed a
draft GuLF Study Concept document and a Key Points document. Each webinar was
well attended by over 100 participants and we have received multiple offers from
community organizations to provide assistance for the study. Suggestions made during
and after the webinar have been incorporated into the study design. Additional webinars
are planned at future dates to be determined to continue information exchange and
dialog.
Phone briefing. As a follow-up to the first webinar and next step in the community
outreach efforts, we will invite key stakeholder groups, such as from the list above to a
follow-up phone briefing. The purpose of the phone briefing is to meet individually with
each stakeholder group to review the study aims and implementation, answer any
question or concerns about the study, establish a dialog with stakeholders, and begin
discussions on the primary health issues of concern for their constituents. Approximately
10-15 phone briefings will be conducted each lasting up to 30 minutes. At the end of the
call, we will document any action items and discuss plans for future meetings in person.
In-person meetings. As a follow-up to the phone briefings, we will travel to the five Gulf
States to meet in person with the community stakeholder groups. During the in-person
sessions, we will request to meet both with organizational leadership in addition to their
constituents. The purpose of these meetings is to further build strong community ties
and gather information to finalize the study design. Due to the short timeline to study
Page 28 of 98
National Institute of Environmental Health Sciences (NIEHS)
GuLF Study - to IRB
11/3/2010
launch we will immediately conduct informal discussions with leadership and listening
sessions with their constituents. The topics of these discussions are expected to broadly
include possible barriers to study implementation, resolutions to those barriers and the
best methods to communicate with study participants and publicize the study.
HRSA and State Health Department meetings. Meetings were conducted with State and
local Health Department representatives beginning the second week in September,
2010, including a combined meeting of leadership from Health Service Regions covering
the Gulf States on September 9-10, 2010. These meetings were intended to inform
state and local leadership about study plans and to obtain input into study design and
implementation. A specific focus of these meetings was to develop strategies for
community based health and mental health referrals for participants identified as
needing follow-up medical care (e.g. for follow-up of elevated blood pressure, or
glucosuria) or identified as having unmet mental health or social service needs. While
the GuLF Study is not designed to provide medical care to its participants, we will work
closely with local health officials to provide the appropriate referral information to
participants identified as having unmet medical and/or mental health needs.
Dockside Chats. Study staff joined the Unified Command in several Dockside chats with
workers during the week of August 22, 2010. These informal sessions provided insight
into some of the health and community concerns of workers from the affected region.
2.4.2
Community Advisory Group
A Community Advisory Group will be created to provide continued advice on the study
and outreach efforts. The group will consist of up to 15 members representing
communities as well as organizations representing worker groups from all five states as
well as various occupational groups and is expected to engage in the following activities:
Facilitate dialogue between community members and the study team
Identify effective communication strategies and vehicles tailored to the communities’
needs
Assist in the dissemination of study related information locally and regionally
Host community neighborhood meetings
Proactively identify issues of concern with study implementation and options for
resolutions
Retain participants in the study over time
A Community Advisory Group chair will be carefully selected from among its members
and will work in close collaboration with the study investigators. The Community
Advisory Group will meet regularly throughout the entire study duration. Meetings are
expected to occur more frequently during study planning and initiation and then less
frequently in the out years of the study.
2.4.3
Communicating the Study to the Community
Communication of the study activities to oil spill clean-up workers and affected
communities is essential. Many of these efforts will involve communications through
community leaders directly to their constituents, some will involve targeted outreach by
Page 29 of 98
National Institute of Environmental Health Sciences (NIEHS)
GuLF Study - to IRB
11/3/2010
the study and NIEHS, and other efforts will involve media-based outreach. Typically, it
takes multiple points of contact to build study credibility and motivate an individual to
participate in a health study, particularly a longitudinal health study. Although we will be
working from a known population of oil spill clean-up workers, media-based efforts will
afford the study legitimacy in an environment fraught with competing Katrina-focused
studies, distrust of the government, and scientific complexity. Additionally, media-based
outreach in conjunction with more direct-to-worker outreach will allow for the ability to
reach a larger number of individuals in a very short time frame. The Community Advisory
Group will be crucial in designing this process and enhancing its effectiveness.
Brochure. A study brochure (Appendix G) will be developed in English, Spanish and
Vietnamese. The purpose of the brochure is to introduce the study and provide contact
information though the hotline and website. The brochure will be sent with the lead letter
inviting study participants during enrollment but may also serve a variety of other
purposes for community outreach.
Hotline. We will establish a toll free hotline for the study. During enrollment, the hotline
will be used for workers to return a call to participate in the study. A call center
representative will answer the hotline during call center hours of operation, i.e. from 9
AM to 9 PM, Monday through Saturday and from 12 noon to 6 PM on Sundays. It will roll
to an answering machine after hours with all calls to potential participants returned the
following day. Call center hours will be determined based on input from the community
groups as to what would be acceptable.
Internet. We will maintain a website to provide information about the study. The website
will be updated regularly with details on recruitment efforts, study findings, and links to
other organizations and information resources. Additionally, we will seek to have each of
our community partners have a link on their website to the study website. We will also
explore the possibility of using Web 2.0 resources such as Facebook and Twitter if we
can be assured that participant confidentiality can be maintained and there are sufficient
numbers of individuals within our study population and community who would be using
these sites.
Advertising. Additional forms of media-based advertising will be determined in
collaboration with key stakeholder groups. Based on preliminary conversations with
various community groups, we anticipate utilizing media-based advertising to both
increase awareness and credibility of the study as well as motivate participation. Radio
may provide a good medium for communicating the study to certain segments of the
population while outdoor advertising may appeal better to other segments. Whenever
feasible, we will capitalize on opportunities to collaborate with community partners on
radio or TV show interviews, local newspaper articles, and other media as a form of
generating awareness and credibility for the study. Media outlets that have been
suggested by community members thus far include:
Radio stations: Q93, 98.5, 102.9, 106.7 (New Orleans, LA)
Newspapers: Sun Herald, Mobile Press Register
Television: WLOX, WDSU, WGNO
As a first step in developing a media campaign, we will enlist the support of a public
relations/communications firm with an understanding of the various communities along
the Gulf Coast in the post-Katrina era and experience using print, electronic and
broadcast media to recruit for public health studies. To develop culturally competent
materials, this firm will develop key messages for different segments of the worker and
Page 30 of 98
National Institute of Environmental Health Sciences (NIEHS)
GuLF Study - to IRB
11/3/2010
volunteer populations and a communications plan to disseminate these messages.
Prototype materials will be submitted for IRB review once they are developed along with
details regarding the implementation of the communications campaign when the plan is
determined at a later date.
2.4.4
Scientific Outreach
The Webinars specifically targeted members of the scientific community, including
researchers from local universities, NIEHS grantees, and researchers with past
experience studying communities involved in other environmental disasters such as the
World Trade Center cohort. The study concept was reviewed by the National Institutes of
Health (NIH) Institutes and Centers Directors at a regularly scheduled meeting. An early
draft of the protocol outline was reviewed at a meeting August 12, 2010 with NIOSH and
CDC. The proposal was discussed August 19, 2010 at a meeting of multiple federal
agencies involved in some aspect of the Oil Spill response. Suggestions received during
those meetings have been incorporated into the current protocol draft. The proposed
study builds on ideas generated during a scientific meeting hosted by the Institute of
Medicine (IOM) on June 22, 2010. In addition to undergoing scientific peer-review prior
to submission of the study for NIEHS IRB review, the study received additional review by
an IOM panel at a meeting held in Tampa, FL on September 22, 2010. Additionally,
presentations of the study design have been (and will continue to be) made to a number
of Federal panels and committees (e.g., Association of State and Territorial Healthcare
Officials (ASTHO) and National Association of County and City Health Officials
(NACCHO)). The IOM is expected to provide ongoing scientific oversight. Oversight will
also be provided (see below) by a Scientific Advisory Board appointed by the Chair of
the NIEHS Board of Scientific Counselors, operating as a subcommittee of that Board.
2.5
Enrollment Procedures and Enrollment Questionnaire
Initial contact with participants will be through a mailing which includes: 1) a one-page
lead letter (Appendix F); 2) a study brochure (Appendix G) that will briefly outline the
study purpose, study benefits, study sponsorship, contractor name, what will be asked of
the participant, compensation if they participate, confidentiality assurance, importance of
their participation, and contact information (contact names, toll-free telephone number,
and web site address) if they would like more information; and 3) a work events calendar
(Appendix K). Both the lead letter and the study brochure will contain instructions
together with the toll-free telephone number for opting out of being contacted about
participating in the study. Every attempt will be made to have the lead letter have the
same message in English and either Spanish or Vietnamese, using both the front and
back of the page. The lead letter will introduce the enclosed four-color, tri-fold study
brochure which will contain instructional graphics and more details of the study. The
lead letter and brochure will both point to the website address for additional information.
The lead letter will also introduce the work events calendar. The work events calendar
will be provided to the participant since the enrollment questionnaire focuses on time
periods before, during and after each participant’s clean-up related activities, to get a full
accounting of potential exposures to these chemicals. The work events calendar will
serve as a memory aid and facilitate recall of the participants’ clean-up related activities.
The telephone contact schedule will be coordinated with the lead letter mailing by
parsing the sample into batches and working the mailing and then calling one a batch at
a time. Mailing of letters to each batch of names will precede calling by several days to
Page 31 of 98
National Institute of Environmental Health Sciences (NIEHS)
GuLF Study - to IRB
11/3/2010
allow the letter and brochure to be delivered. The letter envelopes will request USPS to
forward mail and to provide us with an address update. Mail returned as undeliverable
and with address update notifications will be flagged for tracing.
Several days after the lead letter mailings, the associated telephone numbers will be
released to telephone interviewers to commence screening and enrollment dialing and
interviewing. Interviewers will discover unusable telephone numbers – fast busy,
disconnected, no one by that name, etc. Telephone numbers with outcome codes
indicating they are unusable will be flagged for tracing. The telephone number
management system will apply calling algorithm rules to each telephone number based
on the pattern of interim outcome codes assigned by the interviewers at each dialing
(e.g., no more than two calls per day), varied times of day and weekend, weekend only,
once-a-day only, wait for a cool down period (initial refusal), scheduled call-backs, soft
appointments, etc. The telephone number management system will enforce these rules
when delivering telephone numbers to the interviewers. Calls will be conducted from 9
AM to 9 PM (local), Monday through Saturday, and 12 PM to 6 PM (local) on Sunday, if
acceptable to the community.
The interviewing staff will include a group of interviewers who are bilingual in English
and either Spanish or Vietnamese. We will attempt to identify the primary language of
each potential participant in advance of assigning calls to interviewers by considering
surname and other information that may be available in the master recruitment dataset
(e.g. variable indicating primary language in the NIOSH roster data). Potential
participants will be assigned to an interviewer who is fluent in their primary language and
English. In some cases, the call assignment process may fail to overcome language
barriers between the interviewer and the participant, and the interviewer may be forced
to abort the call. If the call is aborted, the interviewer will make notes about the call and
attempt to classify the primary language of the potential participant so that the call can
be reassigned to the appropriate interviewer.
The entire screening and enrollment telephone call will take approximately 30 minutes to
complete. Should the respondent be selected for active follow-up and agree to
participate, their contact information and scheduling information will be transmitted to
one of 14 regionally distributed clinical field supervisors who will assign the respondent
to the most geographically proximate Home Visit Agents (HVA) under their supervision.
Alternative strategies may be employed to enroll potential participants without phone
numbers or who cannot be reached by telephone, especially those from populations of
special interest such as Vietnamese fishermen involved in the Vessels of Opportunity
Program. We will work with community partners to bring such workers to community
centers where they may be interviewed by phone or in person or arrange for home visits
to complete the enrollment questionnaire (please see section 2.8 for additional details).
2.6
Tracing
Tracing will be conducted if we are unable to contact the participant by telephone or
reach them through the contact person they named on the NIOSH roster data.
Participants who cannot be initially reached with roster information will be flagged and
submitted for tracing in monthly batches. Fortunately, we have cell phone numbers (at
least for those listed on the NIOSH roster) which should significantly improve our ability
to contact participants. However, we are aware that participants may follow regional
practices found post Katrina and use “disposable” cell phones only for the time needed.
Page 32 of 98
National Institute of Environmental Health Sciences (NIEHS)
GuLF Study - to IRB
11/3/2010
We have projected the need to conduct tracing for as much as 15 percent of the sample
and expect that we subsequently will be unsuccessful in tracing 5 percent of this group.
Recruitment and tracing efforts will be carried about by different staff members so that
the time required for tracing does not disrupt the recruitment process.
Rigorous locating operations will be instituted to reach study participants based on the
contact information obtained through the automated batch tracing databases, such as
Lexis Nexis Accurint, Telematch, Pension Benefit Information, National Change of
Address, and Trans-union as well as InfoUSA and Experian.
2.7
Procedures for Enrolling Cohort Members
Participants will be randomly sampled across categories of job/potential exposure
reported during the enrollment interview, with oversampling of categories with higher
potential exposures, for invitation to participate in the Active Follow-up Sub-cohort.
Additionally, controls will be randomly sampled for invitation to participate in the Active
Follow-up Sub-cohort.
Persons who are not randomly selected for inclusion in the Active Follow-up Sub-cohort
or who decline to participate in the Active Follow-up Sub-cohort will be enrolled as
passively followed members of the full cohort. They will have given verbal consent for
completing the telephone interview, providing annual updates on contact information,
and having their health and vital status tracked via electronic data. They will include
individuals across the range of exposures, including controls. Because this group will
include persons not selected into the Active Follow-up Sub-cohort, it will likely be
disproportionately weighted towards workers with lower potential exposures to oil-spill
related chemicals.
2.7.1
Recruitment and Retention
Effective recruitment is critical to the success of this study yet the nature of the study
population, protocol, and the long follow-up period present inherent challenges to
recruiting and retention. A multi-faceted approach to participant recruitment and
retention will take into account best practices in the participant recruitment literature as
well as proven methods utilized in past studies conducted in similar populations.
Participation rates in health studies and surveys have been declining for the last several
decades. This general trend serves as backdrop to several specific challenges inherent
to this study.
One significant challenge in recruiting and retaining participants will be to address the
unique circumstances faced by Gulf Coast families both prior and subsequent to the
Deepwater Horizon Oil Spill. Many of the affected communities were already under
economic stress because of Hurricane Katrina and the recent recession, which makes it
difficult to engage them in research even under the best circumstances. Gulf Coast
families are experiencing further environmental, financial, and health-related impacts
since the disaster. Recruitment and retention strategies must take into account these
day-to-day circumstances and other obligations such as employment, childcare, etc. to
mitigate known barriers to participation.
A related challenge will lie in gaining credibility and cooperation from a population that
may be wary of research studies conducted by outsiders, particularly government-based
studies. It will be important to demonstrate an understanding of the circumstances these
Page 33 of 98
National Institute of Environmental Health Sciences (NIEHS)
GuLF Study - to IRB
11/3/2010
individuals face. Recruitment strategies are needed that position the team to capitalize
on community outreach efforts as well as efforts to brand the study as something other
than “just another government study.” As with all studies, potential participants may be
reluctant or unable to spend the time or experience the inconvenience involved in study
participation. Recruitment strategies are needed to overcome these sources of
reluctance and present the study as beneficial.
After participants are enrolled in the study, maintaining their continued participation over
the full follow-up period is critical. Participants will relocate, experience family disruptions
such as divorce, death or illness, undergo economic changes, and realize logistical
difficulties. Strategies are needed that motivate continued participation and alleviate
logistical constraints.
For all of these reasons, this study will develop a comprehensive recruiting and retention
plan designed to maximize participation for the entire duration of the study with
assistance from the Scientific and Community Advisory Committees, while using study
resources efficiently. Although monetary incentives may be necessary, an array of other
strategies will be applied to cultivate a sense of loyalty, commitment, and appreciation
among study participants and oil-spill communities to the study. We will work closely with
state and local officials and local community groups to tailor an approach that will
resonate with the local community and foster participation in the study.
2.7.2
Recruitment/Retention Strategies and Approach
Importance. Recruitment interviewers will be trained to convey an appropriate sense of
the importance of the research among both exposed and unexposed individuals. This
importance relates not only to the oil spill, but also, more generally, to all of the health,
environmental, and psychological impacts (e.g., displacement, stress, exposures)
associated with disasters, ultimately to support a better understanding of how to respond
to such disasters. This will be reinforced throughout the study with communications from
health officials and study investigators.
Direct Benefit. The main benefit is pride in having participated in an important public
health research effort for their communities. Participants will receive some results from
the medical testing. Recruitment approaches will be designed to minimize any potential
gap in perceived study benefit between the exposed and unexposed.
Study Identification and Branding. The study will be presented publicly in a manner
that appropriately conveys its importance both to participants and to other audiences.
The study website will include information for the public as well as a place for
participants to learn more about the study, receive important study information, and
allow for the opportunity to email study investigators to schedule visits and update
contact information. Scientific publications and results will be posted on the website.
News items and press releases will announce and publicize the study while reflecting
local interest group and health department participation. Participants will also receive
annual newsletters to keep them informed about the progress of the study.
2.8
Recruitment of Special Populations
Based on data from the NIOSH roster and from reports from the field, we are currently
planning to recruit Vietnamese, Spanish, and English speaking participants. Speakers of
Page 34 of 98
National Institute of Environmental Health Sciences (NIEHS)
GuLF Study - to IRB
11/3/2010
other languages may be targeted later through special accommodations such as
facilitated interviews by a relative or community representative speaking one of these
languages or through RFPs (and funded via subcontracts), as described below.
Although they may represent a small fraction of the worker population, it may be
important to include the Vietnamese and other unique ethnic subpopulations in the Gulf
region who may have participated in oil spill clean-up. Based on initial feedback from
the community, a multi-modal approach may be needed to ensure sufficient participation
amongst these groups that may have had elevated exposure through the Vessels of
Opportunity program and other clean-up related activities. Our planned multi-modal
recruitment approach would consist of the standard recruitment package of a mailed
recruitment letter and study brochure, but also additional community meetings to explain
the purpose of the study, opportunities to enroll in-person and/or at a centralized
recruitment facility, and other techniques to be developed in conjunction with input from
community representatives and state and local health officials. These groups will be
included in our pilot effort to provide adequate feedback to the rest of the study.
2.8.1
Special Issues in Recruiting Vietnamese Participants
To address issues around literacy, outreach, and access to the Vietnamese population
specifically, we will identify and work with NGOs having connections to, and
understanding of, this community. For example, in analysis of data from the NIOSH
roster and anecdotal reports from persons in the field it appears that Vietnamese
workers are substantially underrepresented on the NIOSH roster and may be similarly
underrepresented on the PEC list relative to the general population. This may be due to
language barriers that resulted in Vietnamese workers not receiving the worker training
or completing the NIOSH roster. To help identify these workers and suitable controls,
and to overcome language and cultural barriers to their participation in this study, we will
work closely with community groups, enlisted via RFPs (and funded via subcontracts to
the study contractor), that are integrated in the Vietnamese community/communities.
These groups include Asian Americans for Change, Boat People SOS, Mary Queen of
Vietnam Community Development Corporation, Vietnamese American Young Leaders
Association of New Orleans, and Vietnamese Martyr's Church. Many of these
community groups, along with Parish governments in Louisiana, have maintained
separate lists of clean-up workers from their communities. We will meet with these
community groups to explain the purpose of the study, the importance of participation of
Vietnamese clean-up workers, the study methods, what will be expected of the
participants, and how these groups can help us, and we will attempt to address their
concerns.
For groups that agree to assist us in recruitment, we will work with their staff to develop
strategies and resources that are both culturally and scientifically appropriate for
promoting the study and identifying potential study participants. These groups will be
asked not to recruit study participants per se, but rather to assist in developing interest
and support for the study so that study staff can then approach potential participants in a
methodologically rigorous manner. They may be asked to produce and provide to study
investigators regularly updated lists of persons who they know or believe to have
participated in oil spill clean-up activities, including names, telephone numbers,
addresses, and other appropriate contact information (especially for any persons without
telephones). They will be requested to provide some basic demographic information and
reason for refusal for any workers who indicate that they are unwilling or unable to
participate in this study. They will also be asked to provide similar lists of Vietnamese
Page 35 of 98
National Institute of Environmental Health Sciences (NIEHS)
GuLF Study - to IRB
11/3/2010
controls who are comparable to the clean-up workers they identify, based on criteria that
they will develop together with study investigators. However, it may prove necessary to
carry out a parallel supervised process to enroll this group, allowing subcontractors to
conduct in-person screening interviews rather than telephone interviews. In that case,
we will work with community groups to implement enrollment and data collection directly
but provide sufficient oversight to ensure protocol standardization.
To minimize bias in subject selection and data collection, we will attempt to conduct all
telephone interviews and in-home visits by study staff in Vietnamese. We will work with
community group staff to approach persons who do not have telephones or other
individuals recommended by the community group staff who could serve as liaisons. For
persons for whom telephone interviews are not appropriate or possible, interviews will be
conducted in-person, either at the subject’s home or at another suitable location. While
we will make every effort to provide Vietnamese-speaking phlebotomists/interviewers, it
may be necessary in some cases to provide a trained Vietnamese translator with
English-speaking phlebotomists/interviewers. In order to ensure full enumeration of the
potential cohort, participants and those who decline to participate will be asked to
provide names and contact information of any other Vietnamese clean-up workers they
may know. In order to facilitate engagement, commitment, and valid data collection
within this community, we will take the necessary steps to maintain as much
transparency as possible including inviting community stakeholder groups to the
interviewer training sessions and inviting them to assist in developing the training
materials to ensure cultural competency among the study staff. We will review these
procedures on an ongoing basis and modify them as needed to achieve the dual goals
of enumerating as fully as possible the workers and suitable controls in this community,
and recruiting and interviewing them in a scientifically rigorous manner.
2.8.2
Special Issues in Recruiting Creole-Speaking Persons
Anecdotal reports indicate that Creole-speaking persons in the Gulf have also been
involved in clean-up activities. These persons are likely to be substantially
underrepresented on the NIOSH, PEC, and other worker training lists because most of
these trainings have been conducted only in English, Spanish, and Vietnamese. We
have no information on how many such workers there were nor on what types of cleanup activities did they engage in. To fill in these critical information gaps, we will issue
RFPs to local community groups to help us enumerate these population(s) that may be
under-represented in other worker lists. If we determine through these means that there
are sufficient numbers of potentially exposed workers in this population, we will work
with community stakeholder groups to promote the study and help recruit the workers
and appropriate controls from this population in a similar manner to that described above
for the Vietnamese.
2.8.3
Special Issues in Recruiting Women
Women will be recruited into the cohort by the same eligibility and selection criteria as
men. However, some additional sex-specific questions, focusing on menopausal status,
reproductive history, and pregnancy status, will be included in the enrollment
questionnaire. Potential sub-studies of women will be considered later, based on the
number of women, their exposure profiles, and the numbers of outcomes of interest.
Page 36 of 98
National Institute of Environmental Health Sciences (NIEHS)
2.8.4
GuLF Study - to IRB
11/3/2010
Special Issues in Persons with Reactive Airways Disease
We may consider focused sub-studies among persons identified with, or suspected to
have, reactive airways disease at enrollment. The timing and nature of these sub-studies
will depend on the number of such persons identified during enrollment and will be
described in more detail at a later date.
2.8.5
Other Special Populations
Other subgroups may be identified for add-on studies of focused hypotheses related to
specific exposures or health outcomes. These studies may be initiated by us or by
extramural collaborators. Participants will be informed that such add-on studies may be
possible and that separate informed consent to participate will be obtained.
2.9
Home Visit
Participants selected for the Active Follow-up Sub-cohort will be scheduled for an inhome visit by a field staff member (i.e., a home visit agent or HVA). We will ensure that
Home Visit Assistants (HVAs) hired for this study have the necessary education,
qualifications and experience to conduct the required home visit activities, or we will
provide additional training as needed. We currently plan to hire LPNs who can do both
phlebotomy and interviewing. Home visits will be scheduled seven days a week
between the hours of 8 AM and 9 PM local time. Sunday visits will not be scheduled in
communities for which this is considered socially unacceptable. We anticipate that the
home visit will take 2-3 hours to complete. By going to participants’ homes to complete
data collection for the Active sub-cohort rather than requiring that they make their own
arrangements for specimen collection or visit a central location, we minimize their
burden for study participation while maximizing the likelihood that we will be able to
collect the desired study data, biospecimens, and environmental samples.
During the home visit, the HVA will administer informed consent (Appendix D). Should
the participant be unable to read, the HVA will read the informed consent verbatim to the
participant in front of a witness to ensure the participant understands all aspects of the
study. The HVA will return the signed consent document and completed questionnaires
to the study office by overnight carrier. Present plans are for biospecimens and
environmental samples to be sent by priority overnight carrier to the central processing
laboratory (CPL) for additional processing and storage. Because commercial carriers do
not operate on Sundays, we are investigating use of specialty couriers that can make
these off-hour pick-ups and deliveries, but typically at a premium price. We are currently
exploring options for batching Sunday collections or having samples delivered to a
central site for shipping to minimize specialty courier costs.
2.9.1
Advance Study Packet
In advance of the home visits, we will assemble and mail to each participant a home visit
kit containing the following materials needed to conduct the visit:
Appointment cover letter (Appendix F);
Home visit preparation instruction sheet;
FAQs (Appendix H);
Informed consent form for the participant to review in advance (Appendix D);
Page 37 of 98
GuLF Study - to IRB
11/3/2010
National Institute of Environmental Health Sciences (NIEHS)
Informed consent quick reference guide (Appendix E)
Urine collection container and lid along with detailed instructions for collecting a
first morning void (FMV);
ID labels for participant -specific documents and specimens/samples.
The HVA will bring all other materials needed for the home visit.
2.9.2
In-Home Visit
At the beginning of the visit, the HVA will obtain informed consent prior to conducting
any study procedures. Additional details concerning the informed consent procedure can
be found in Section 10.2. After consent is obtained, the HVA will ask if the participant
wants abnormal test results for clinical and laboratory assessments conducted at the
time of baseline visit reported to their health care provider and obtain contact information
for that provider. The HVA will collect physiologic and anthropometric measures;
biological specimens (e.g., blood, hair, nail, and urine); environmental samples (e.g.
house dust); and administer a baseline questionnaire. The HVA will also determine and
record the latitude and longitude of the home using a handheld Global Positioning
System (GPS) device; this information will be used in later Geographic Information
System (GIS)-based studies to determine residential proximity to sites of potentially
relevant environmental exposures, such as petroleum refineries and toxic waste dumps
and incinerators. If a subject is interviewed away from the home, their residential
address will be collected (along with nearest cross-street and landmarks) so that it can
be more accurately geocoded using existing software geocoding tools; this will also be
done for previous addresses as indicated in the subjects residential history. Table 1
provides an overview and approximate timeline of the home visit activities.
Table 1.
Home Visit Overview
Activity
Estimated
Time
Notes
Interview is assigned to HVA, and HVA
calls participant to schedule in-home visit
N/A
Scheduled at least 3-5 days
in advance. Provide toll free
number and website to
reschedule if necessary
Mail Home Visit Kit
N/A
Packet arrives 3-5 days in
advance of scheduled home
visit
First morning void urine collection*
N/A
Collected by the participant
using urine collection kit
provided
Arrival, greeting and set-up
5 minutes
Informed consent
15 minutes
Page 38 of 98
Review and obtain informed
consent
GuLF Study - to IRB
11/3/2010
National Institute of Environmental Health Sciences (NIEHS)
Estimated
Time
Notes
Anthropometric / Physiologic measures
collection
20 minutes
Ht, Wt, BP, Waist and Hip
Circumference, Spirometry
Biological specimen collection and
labeling
20 minutes
Hair, Nail, Blood, Toenail
Clippings
Questionnaire measures collection
60 minutes
Environmental sample collection and
labeling
10 minutes
Biological specimen processing and
labeling
10 minutes
Dust wipe
†
Urine dipstick analysis for glucosuria and
writing of report
5 minutes
Debriefing of blood pressure, pulmonary
function, urinary glucose and BMI results
report to the participant
10 minutes
Clean-up and packing
10 minutes
Departure
Total time:
2 hours,
45 minutes
Post-visit processing
Shipping and data back-up
* If first morning void collection has not been obtained when the study staff arrive, the HVA will
request that the participant provide a random or “spot” urine during the home visit instead.
†
Blood will be allowed to clot for at least 30 minutes while the baseline questionnaire is being
administered to the study participant and will be centrifuged for 15 minutes following the
questionnaire administration (and during the environmental sample collection) in order to
minimize the biospecimen processing time and overall time spent in the home during this visit.
2.9.3
Baseline Questionnaire
The baseline questionnaire elicits information not included in the enrollment
questionnaire, including more detailed information on residential and occupational
history, personal and family medical history, alcohol and tobacco consumption, mental
health and anxiety, and recent eating and drinking and use of medications.
Page 39 of 98
National Institute of Environmental Health Sciences (NIEHS)
GuLF Study - to IRB
11/3/2010
Before designing the questionnaires, study investigators referred to questionnaires used
by other data collection efforts occurring in the Gulf States, regionally, and nationally in
order to facilitate regional and national comparisons and potential cross-study analyses.
National studies such as the National Health and Nutrition Examination Survey
(NHANES), Behavioral Risk Factor Surveillance System (BRFSS), and National Survey
on Drug Use and Health (NSDUH) were used. We also referred to measures provided in
the PhenX Toolkit in developing some sections of the questionnaire. We substituted
sections from other questionnaires when we found something that appeared to work
better or to better capture our study interests.
Detailed information on oil spill clean-up related activities in the enrollment telephone
questionnaire completed by all participants; Questions collected at baseline during the
home visit include: residential history; personal and family medical history; occupational
history; reproductive history; history of military service; demographic and socioeconomic
factors; alcohol consumption; mental health status; a neurocognitive screener; and other
information, including hobbies, sleep patterns, tobacco use and environmental tobacco
smoke exposure, and consumption of seafood from the Gulf of Mexico. Occupational
histories will enable us to identify, and infer relevant exposures from, occupations such
as employment in the petrochemical industry and commercial fishing. Separate
questionnaire modules will be developed and administered to subgroups reporting prior
employment in the petrochemical industry and prior experience in hazard remediation,
including other oil spills or other substances such as lead or asbestos. Residential
histories, together with Geographic Information Systems, will help us to infer potentially
relevant environmental exposures from sites such as petroleum refineries and toxic
waste dumps and incinerators. Additionally, hobbies and use and storage location of
gasoline can be important indicators of non-occupational exposures. This exposure
information will be incorporated into analyses of health outcomes related to the clean-up
work. Information on history of military service will identify persons who may have prespill serum samples and medical data available through the Department of Defense
Serum Repository and health care system and identify workers with potentially
confounding military exposures. Although the interview asks for identifying information
from the participant to facilitate follow-up and future linkage with external databases for
GIS-based studies, the computer-assisted interview will be programmed to create a
separate data file for identifying information in order to maintain a secure data system.
In developing our questions on environmental and occupational exposures, we first
considered the chemicals that have been identified in the crude oil and also in the
dispersants as identified by the National Toxicology Program (NTP). By linking to various
national databases, we will be able to identify the potential toxicity of these agents. We
also considered the frequency with which participants were engaged in oil-spill clean-up
related activities and their past occupational and recreational exposures to these agents.
2.9.4
Anthropometric/Physiological Measures
The HVA will weigh (kg) participants and measure height (m), hip and waist
circumference (cm), and take the participant’s heart rate and blood pressure. Height (m)
and weight (kg) will be measured using a metal tape measure and digital scale using
standard methods from the NHANES IV national survey. All measurements will be taken
three times. If a person is unable to stand, we will measure waist circumference and
sitting height using the crown to rump method with a cloth tape measure, but we will not
Page 40 of 98
National Institute of Environmental Health Sciences (NIEHS)
GuLF Study - to IRB
11/3/2010
measure their weight. Instead, we will collect their self-reported weight). We will use a
cloth tape measure to collect waist circumference. We will provide participants with a
report of their anthropometric measures during the field visit. To reduce the amount of
equipment needed and facilitate training and scheduling, we plan to perform pulmonary
function testing during the home visit on members of the Active Follow-up Sub-cohort
who live within the immediately affected areas, which represents approximately 75% of
the members of this cohort.
2.9.4.1 Heart Rate and Blood Pressure Measurement
Three blood pressure and heart rate measurements will be collected by trained study
staff. Heart rate will always be measured prior to respiratory testing. If a person’s resting
heart rate is > 120 beats/minute, they will be excluded from participating in the
respiratory testing. Blood pressure will be measured three times using standard clinical
oscillometric (not mercury-based) equipment and these results will be provided to the
participant at the home visit along with information regarding what these blood pressure
results mean using a form similar to that being used in the NIEHS Sister Study. Seated
heart rate and blood pressure will be taken three times in rapid succession after a 5
minute rest period and the second and third readings will generally be used to calculate
average values for analysis and reporting.
2.9.4.2 Pulmonary Function Testing
Pulmonary function testing (PFT) will consist of spirometry data collection. All PFT will
be conducted using American Thoracic Society/European Respiratory Society
(ATS/ERS) guidelines [Pellegrino, et al. 2005].
The PFT will be performed using a portable, ultrasound transit-time based spirometer
(EasyOn; NDD Medical Technologies, Chelmsford MA, USA, or a comparable model). A
full Forced Vital Capacity maneuver will be used. We will obtain three ATS acceptable
forced expiratory maneuvers out of a maximum of eight attempts. All spirometry
examinations will be done with the person seated and wearing a disposable nose clip.
We will use new individually packaged, disposable mouthpieces for each subject and a
new spacer for each subject.
Combined with the symptom and medical history information, this objective measure of
respiratory status will allow for an assessment of obstructive lung disease. By detecting
these small changes in pulmonary function in the population as a whole, we will be able
to make comparisons to other environmental exposures including air pollution and
environmental tobacco smoke in order to assess the potential severity of their disease.
To the extent possible, we will ask participants to withhold their asthma inhalers on the
day of the examination (a commonly used protocol). For those participants unwilling or
unable to withhold medications, we will document this during the home visit. For all
participants, we will record the timing and dosage of all asthma medications over the
preceding seven days.
To ensure quality results, we will conduct formal training and recertification on all field
procedures. The HVA will be required to take a NIOSH-approved spirometry course,
which is a well recognized training among medical professionals. In addition, all HVAs
will complete the online exam and submit 10 practice tests administered by Hankinson
Consulting, Inc (Athens, GA, USA). All spirometers will undergo standard quality checks
before use in the field. To ensure high quality control and HVA feedback, we will use the
reviewing software recently developed specifically for the EasyOn spirometer by
Page 41 of 98
National Institute of Environmental Health Sciences (NIEHS)
GuLF Study - to IRB
11/3/2010
Hankinson Consulting, Inc (Athens, GA). An expert in pulmonary function quality control
will review all tracings on a weekly basis and override any software-provided readings if
needed. The quality scores and other results will be electronically forwarded to field
coordinators who will feed the quality information to the HVAs. If an unexpected number
of unacceptable tracings occur, the HVA in question will be retrained.
Participants who answer yes to any of the following questions will not undergo
spirometry during the visit:
• In the past three months, have you had any surgery to your chest or abdomen?
• In the past three months, have you had a heart attack or stroke?
• In the past three months, have you had a detached retina or have you had eye
surgery?
• In the past three months, have you been hospitalized for any other heart problem?
• Are you pregnant?
• Are you currently taking medication for tuberculosis?
Additionally, if a participants resting heart rate is >120 beats/minute, they will be
excluded from PFT.
Our exclusion questions include all of those used in BOLD [Buist, et al. 2007] and
PLATINO [Menezes, et al. 2005], multinational studies that enrolled over 14,000 adults
over age 40 years for pre and post bronchodilator spirometry with only trained
technicians. No adverse events occurred in either the BOLD or PLATINO studies. These
exclusions are considered very conservative and these questions are not generally
asked before spirometry is done in clinical practice.
Figure 1. Example of EasyOn Spirometer and Disposable Mouthpiece
2.9.4.3 Glucosuria Testing
During the in-home visit, a small amount of the urine collected from each participant
(described in section 2.9.5 below) will be transferred to a sterile cup. A commercially
available dipstick will then be used by the trained study staff to measure the urinary
Page 42 of 98
National Institute of Environmental Health Sciences (NIEHS)
GuLF Study - to IRB
11/3/2010
glucose level. The result will be provided to the participant at the home visit, along with
information regarding the meaning of the result, using the form in Appendix L.
2.9.5
Collection of Biological Samples
Biological specimens will be collected from participants in their homes by a trained HVA.
The HVA will draw blood, retrieve urine specimens, and direct the participant to collect
hair and nail samples. The following specimens will be collected:
Blood samples: The HVA will collect 52.5 mL of venous blood into eight
Vacutainer tubes:
o Lavender Top EDTA Tubes: Three purple-topped tubes will be collected:
One 10 mL and one 6 mL tube will provide plasma, buffy coat, and red
blood cells (RBCs) for future analyses.
One 2 mL tube will either be 1) analyzed for CBC with WBC differentials
upon arrival in the central laboratory for persons tagged to be recruited for
the Biomedical Surveillance Sub-cohort (N=6,250) or 2) processed for
plasma, buffy coat, and RBCs for future analyses for the rest of the Active
Follow-up Sub-cohort.
o Royal Blue Top EDTA Tube: One 6 mL trace metals tube will frozen for future
selected measurement of As, Ca, Cd, Cr, Cu, Fe, Mg, Mn, Pb, Sb, and/or Zn
(i.e., all of the metals for which these trace metal tubes have been validated).
o Red Top Serum Tube: Two 10 mL tubes with no additives will provide serum
and clots, which will be frozen for future analyses.
o Yellow Top ACD-B Tube: One 6 mL tube with Acid/Citrate/Dextrose Solution
B tube will be collected from each participant for future analyses. How the
specimen is processed will depend on whether the participant is a member of
the Biomedical Surveillance Sub-cohort, as described below.
o PAXgene RNA Tube: One 2.5 mL PAXgene blood RNA tube will provide
stabilized whole blood for mRNA isolation for future analyses.
Urine: Each participant will be asked to collect a first morning void (FMV) urine
sample on the day of the scheduled visit in the collection container from the
Home Visit Kit. If an FMV was not collected, the HVA will ask the participant to
provide a “spot” urine. A small amount of the specimen will be transferred to a
sterile cup during the home visit and used to measure glucose levels with a
commercially available dipstick. Another portion will used for a more complete
basic chemistry urinalysis (by dipstick) upon arrival in the central laboratory to
measure protein, glucose, and several other parameters among persons tagged
to be part of the Biomedical Surveillance Sub-cohort. The remainder of the urine
sample will be processed in the Central Processing Laboratory for storage as
described in Section 2.11 and as illustrated in Appendix C2.
Toenails: The HVA will ask each participant to collect toenail clippings from each
toe unless they have a medical or physical condition (e.g., diabetes) that would
prohibit collection. Toenail clippings will be stored as described in Section 2.11
for future analysis of metals. Participants will be advised in advance of the visit
not to clip their toenails before the visit.
Hair: Each participant will be ask to collect a small hair sample as close to their
scalp as possible. Hair will be clipped to indicate which end is closest to the scalp
and stored as described in Section 2.11 for future analysis of metals and cortisol.
Page 43 of 98
National Institute of Environmental Health Sciences (NIEHS)
GuLF Study - to IRB
11/3/2010
Substantial volumes of biospecimens will be required for quality control, cross-sectional
surveys, and assay validation over time, but will not directly contribute to addressing the
specific aims of this study. To meet this additional need, we will collect another set of
each of the blood and urine specimens listed above (i.e., an additional 52.5 mL blood
and 40 mL urine) from a 3% random sample of the Biomedical Surveillance Sub-cohort
(N≈150) and a ~0.7% random sample of the remaining Active Follow-up Sub-cohort
(N≈150). These samples will be processed and banked in the same manner as the main
study samples. For these randomly selected individuals, an addendum to the consent
document detailing this additional biospecimen collection will be administered and they
will be remunerated with an extra $10 for these additional samples.
Saliva: All study participants who are unwilling or unable to provide a blood sample
during the home visit will subsequently be mailed an Oragene OG-250 DNA SelfCollection kit, together with instructions for using and returning the kit, and a stamped,
self-addressed padded envelope for returning the kit to the central processing lab (CPL).
The CPL will store these samples as described in Section 2.11 and as illustrated in
Appendix C.2.
2.9.6
Home Environment Sampling
The HVA will be trained to collect the following home environmental samples according
to detailed sample collection protocols. These samples will provide valuable information
about the home environment and enable researchers to better characterize and control
for confounding based on residential exposures as opposed to exposure related to
clean-up activities.
Household Dust: The HVA will collect a household dust sample using a
sterilized electrostatic dust wipe (e.g., the Swiffer™ Dusters, or a comparable
model). The HVA will dust surfaces that may not frequently be dusted such as
the tops of door sills or window sills, the tops of wall-hung picture frames, the
tops of refrigerators, etc. The HVA will use the dust wipe to collect dust samples
for approximately 5-7 minutes. The wipe will be shipped to the CPL along with
the biospecimens for further processing and storage as described in Section 2.11
and illustrated in Appendix C.
Collecting household dust samples will enable a snapshot view of exposure to
potential environmental confounders such as heavy metals, persistent organic
pollutants, and endotoxins. While other studies have collected samples using
high power vacuum cleaners under a standard protocol, investigations have
demonstrated good agreement between dust collected from household vacuum
cleaner bags and the more industrial vacuum samples, typically considered the
gold standard. In addition to greater cost, the collection and processing (or
storage) of bulky vacuum cleaner bags presents logistical challenges and not
everyone owns a vacuum cleaner or one with a bag. Studies such as the
Agricultural Health Study and the Sister Study have used various techniques to
collect samples of dust that settles onto household surfaces. The Sister Study
piloted the ability of women to collect dust samples themselves using an alcoholwipe approach. In conjunction with Southwest Research Laboratories, the Sister
Study tested several brands for interferences with the chemicals of interest and
to determine if pesticide and phthalates are detectable in homes.
The Biomedical Surveillance Sub-cohort affords the opportunity to validate the
suitability of our proposed approach for rank-ordering exposure levels looking at
Page 44 of 98
National Institute of Environmental Health Sciences (NIEHS)
GuLF Study - to IRB
11/3/2010
potential confounders such as persistent organic pollutant levels using alcohol
wipes and vacuum cleaner bags compared to electrostatic dust wipes. We will
explore the feasibility of other methods to assess household exposures, including
a dipstick test of nitrates in water, and a semi-permeable membrane being
developed at the EPA for the detection of volatile compounds, and a small
vacuum cleaner hose attachment that can be used with a variety of home
vacuum cleaners to collect a small dust sample.
2.9.7
In-Home Biospecimen Processing and Shipment
After blood collection, the HVA will allow the blood in the serum tubes to clot for 30
minutes before centrifuging the tubes in the participant’s home and separating the serum
and clot, which will be retained. The HVA will then package all of the biospecimens and
environmental samples for shipment to the CPL. The ACD-B tube and the 2 mL
lavender top EDTA tube will be shipped at ambient temperature. The remaining
specimens and environmental samples will be shipped cool but not frozen, accompanied
by a frozen cold pack. These materials will be shipped by priority overnight service to the
central processing laboratory. All biological samples will be shipped according to local,
state, and federal requirements governing shipment of biological specimens. In the event
that specimens or samples are lost or damaged during shipment, the participant will be
offered the opportunity to have specimens recollected, with a small compensation.
2.10 Reports to Participants, Health Care Referrals and Incident
Reports
2.10.1
Overview
All HVA personnel will be licensed practical nurses (LPNs) with up-to-date CPR
certifications. HVAs will receive additional training prior to beginning the study regarding
the evaluation and testing procedures, form completion, handling of emergency
situations, personal safety, signs of abusive behavior, and appropriate referral strategies
for the locality. Prior to any home visits participants will receive information about the
study including a brochure (see Appendix N) that lists healthcare providers in their area
that can provide health care services, including any that can assist with free or reducedcost services.
During each home visit, or participant encounter, the HVA will measure BMI, blood
pressure, urinary glucose, and spirometry. With the exception of spirometry, which
requires a specially trained reader to properly interpret the test results, the HVA will
inform participants of their test results at the time of evaluation, as well as any needed
actions for identified abnormalities. The HVA will also observe participant behavior in
case of any urgent physical or mental health behaviors requiring emergency
intervention. Urgent observations or test findings (such as hypertensive crisis, acute
mental or physical distress, abusive behavior, etc.) identified at the time of the home visit
will be handled immediately as discussed below (Section 2.10.6.1, Follow-up of
Urgent/Emergency Situations During In-person Encounter).
In addition to providing the participant with a written summary of test results and
recommended actions (Appendix L and M), the HVA will perform the following actions:
Page 45 of 98
National Institute of Environmental Health Sciences (NIEHS)
GuLF Study - to IRB
11/3/2010
1) Complete an Incident Report for any acute medical, mental health, or social
problems (Appendix J, Baseline Questionnaire, Section N) and report the
incident to their RM and the Coordinating Center to inform them of this action.
The Project Manager will then immediately notify the NIEHS Principal
Investigator of what transpired.
2) Enter the results of evaluations and their interpretations provided to participants,
and actions taken about abnormal results into the CAPI system (Appendix J,
Baseline Questionnaire, Section N).
3) Provide referrals for medical and mental health care, as needed, and document
referrals (see sample referral handout in Appendix N).
Additionally, all participants will receive a follow-up letter and report within 1 month of the
visit that reiterate the evaluation results (i.e. BMI, blood pressure, urinary glucose, and
spirometry) and recommended actions (Section 2.10.6, Follow-up Reports and
Information and Appendix P and Q). The participant’s health care provider will also
receive a copy of the report within one month of the encounter, if any significant
abnormalities are detected and provided that the participant has indicated that they have
a health care provider, consented to sharing this information with their provider, and
have given their provider’s name and contact information (Appendix O). For individuals
in the Biomedical Surveillance Sub-cohort, CBC results and interpretations will be
included in the report that accompanies the follow-up letter. Urgent findings identified by
the laboratory will be phoned to individuals by the HVA or Call Center within one week of
receipt from the laboratory (Section 2.10.6.3, Reporting of CBC Laboratory Tests).
2.10.2
Home Visits or Participant Evaluations at other Locations
2.10.2.1 Participant Mental and Physical Condition Observations
HVAs will be trained to remain neutral when asking questions about health conditions
and to reply to responses with sensitivity. In most situations, empathetic and respectful
listening and an understanding tone will help to calm the participant and allow him or her
to proceed with the interview. However, we will train HVAs on several specific steps they
can follow if a participant becomes distressed, such as:
Reminding participants that their answers are confidential,
Providing neutral feedback, such as “Thank you; I understand; We appreciate
your participation in this important study,”
Acknowledging a participant’s hesitancy in answering a question, such as, “I
understand that this may be difficult for you, so please take your time”, and
Reminding participants that it is okay to skip any question he or she does not feel
comfortable answering.
Upon arrival for the home visit (or participant evaluation at another location), the HVA
will quickly observe the participant’s physical condition and mental health disposition. If
the participant appears to be in physical or mental distress, the HVA will note their
condition and ask the participant if they need immediate medical assistance or
determine urgent care needs if the participant is unable to effectively communicate.
If a need for immediate care is identified, the HVA should call 911 or assist the
participant in contacting emergency services, their healthcare provider, or other health
care resources as appropriate. Information about the incident and disposition of the
Page 46 of 98
National Institute of Environmental Health Sciences (NIEHS)
GuLF Study - to IRB
11/3/2010
participant will be recorded in the Incident Reporting Form in the CAPI system (Appendix
J, Baseline Questionnaire, Section N).
In circumstances when an HVA or interviewer identifies a participant who may be
experiencing mental health issues—or more significantly, suicidal ideation, we will
provide them with contact information for local, regional, state and national mental health
resources that are available to help them deal with their issues. If the participant
appears to be in imminent risk for self-injury (e.g., suicide), the HVA or interviewer will
contact local emergency officials by calling 911 or other intervention hotlines as
appropriate. As noted in the previous section, the HVA will immediately fill out an
incident report in the CAPI system and also report the incident by phone, as described
above.
If the HVA contacted 911 for an emergency situation, the HVA or Study Center
representatives may immediately follow-up, or as soon as possible with respect to the
situation, with the participant or their spouse to check on their current condition and
determine future interest and ability to participate in the study. For non-urgent situations,
the HVA will determine if the assessment should continue or be rescheduled to a better
time.
2.10.2.2 Other Social Behavior Observations
During the encounter, the HVA will observe the household and be alert for unusual
situations suggesting the existence of reportable (varies by state) social or abusive
behaviors. If anyone in the home environment is in immediate danger, the HVA will end
the visit, call 911, complete an incident report, and report the event by phone. Should a
HVA witness signs that lead to suspicion of child, spouse or elder abuse while in the
participant’s home, the HVA will generate an incident report in the CAPI system at the
conclusion of the visit and report the incident by phone, as discussed above. Such
situations will not be discussed with the participant, except in instances where it appears
that the study participant is the victim of abuse. In those cases, the HVA will discreetly
ask if the participant would like to be put in touch with someone who might be of
assistance.
2.10.2.3 Incident Report Form
An incident report form will be completed by the HVA for all acute medical, mental
health, and social problems that are observed during encounters with participants
(Appendix J, Baseline Questionnaire, Section N). This report will be accessible in the
CAPI system on the HVA’s laptop, and it will include workflow features that prompt the
HVA to take appropriate action based on evaluation findings, observed behaviors, or
noted circumstances. The CAPI system will also be programmed with automated data
checks that alert Coordinating Center staff to problems that require immediate attention
and follow-up, such as telephone follow-up to a participant who required a 911 response
for a hypertensive crisis. The principal investigator will be responsible for reporting to the
IRB all acute medical, mental health, and social problems that are observed during
encounters with participants that result in a call to 911 or social services as well as any
adverse events that result from study interventions or protocol violations. Due to the
unique nature of the study population which is under substantial stress due to job losses
Page 47 of 98
National Institute of Environmental Health Sciences (NIEHS)
GuLF Study - to IRB
11/3/2010
associated with the oil spill and major hurricanes and is medically underserved, it is
expected that the majority of emergency contacts will be unrelated to the study per se,
but due to the fact that we are screening for medical conditions among individuals
without access to care and have an opportunity to observe individual and family
behaviors because we will spend several hours in a participants’ home. Such adverse
events will be reported to the IRB within a month of occurrence allowing us to also
provide information on the outcomes of the referrals. Adverse events resulting from the
study protocol or any protocol violations will be reported to the IRB as soon the PI is
made aware of the event.
2.10.3
Home Visit/Evaluation Measurements & Testing
Participant evaluations will include several measures and tests for which the results can
be conveyed during the time of the HVA encounter providing potential health benefits for
early recognition of disease, as well as enhanced opportunities for health education and
utilization of health care resources. HVAs will be trained to provide participants with
appropriate and standard feedback about their individual blood pressure and BMI
measurements, and urine glucose results before departing the participant’s home. HVAs
will be trained to record all observations and in-home test results in the data
management application as well as on participant Test Result Forms that provide the
participant with a basic interpretation of the various measurements and test results.
HVAs will also be trained to strictly follow scripts when conveying results to participants.
The participant Test Result Forms will include scripts that provide recommended actions
for participants to take depending on the measured values for each test. For each test
result, we provide standard recommendations depending on the result value (see Test
Results Forms in Appendix L).
As the HVA performs the various measurements and tests during the visit, the results
will be recorded into the data management system and also transcribed onto pre-printed
test result forms for each test. The HVA will provide these forms filled-in with the
measured results to each participant and go over the results with the participants and
any suggested follow-up actions. If any of these results are abnormal, the relevant test
result form indicates what actions the participant should take and how soon. With the
possible exception of extremely elevated blood pressure, most abnormal findings will
lead to a recommendation to contact their health care provider or other community
healthcare providers for additional evaluation within a specified time interval.
2.10.4
Follow-up Actions for Abnormal Findings
2.10.4.1 Medical Referral Guidelines
During the home visit or encounters at other locations, participants will receive handouts
that provide results of their evaluations, interpretation of findings, recommended action
based on findings, and health care referrals for any abnormal results (if needed). These
results will be also summarized in a follow-up mailing to participants one month after the
visit. The letter will thank participants for their participation in the study, introduce the
summary report of findings and recommended actions, and remind them of study
activities in the coming years. The handouts and summary report will provide information
Page 48 of 98
National Institute of Environmental Health Sciences (NIEHS)
GuLF Study - to IRB
11/3/2010
on BMI, blood pressure, urinary glucose, and pulmonary function test results. The CBC
results for the Biomedical Surveillance Sub-cohort will also be included in the summary
report, along with recommended actions. The CBC analysis will be done in a Clinical
Laboratory Improvement Amendments (CLIA) certified laboratory (as will any future
clinical tests that may be reported back to participants). The urine glucose screening
test performed in-home has a CLIA waiver (FDA 2010).
During the consent process, participants will be asked if they are willing to allow the
study to send abnormal evaluation findings to their health care provider and whether
they are willing to receive a referral for health care, if they do not have a health care
provider but need to see one based on evaluation findings.
If the participant consents to sharing evaluation results with their health care provider,
the HVA will collect the name and contact information for the health care provider and
record the information in the CAPI system. Within a month of the visit, the results of
evaluations and advice regarding health care referrals will be shared with the
participant’s health care provider, if any abnormal evaluation findings were detected. Any
evaluation finding that does not fall within the normal ranges will result in a letter to the
health care provider. The health care provider will receive a cover letter that briefly
describes the study and the reason the results are being sent, as well as a copy of the
summary report that all participants will receive by mail. If the participant does not have
a health care provider, the HVA will provide information about local health care
resources, if warranted, based on abnormal evaluation findings. Participants who
receive a referral will be instructed to present the health care provider with the results
handouts at the time of the referral visit.
The advice that participants receive about medical referrals will be based on level of
urgency of their findings. Levels are currently set based on established, published
guidelines such as those from the American Heart Association for blood pressure. We
tended to select the more conservative guidelines when there were several choices,
given the fact that the community under study includes many without access to care and
the fact that our study will be highly visible and we want to err on the side of caution.
Nonetheless, levels of urgency can vary across practitioners and communities; setting
levels too low may unnecessarily over-burden area medical care systems, while setting
them too high may put participants at risk. The frequency of referral for care will be
monitored as will the outcomes for referrals deemed urgent. If it is determined that we
are making too many unnecessary referrals or that these guidelines are inconsistent with
local practice, we will consider other less conservative standards. Any proposed
changes would be brought back to the IRB for evaluation. Participant referrals or followup instructions will be categorized into one of the five classifications below, based upon
their test results or findings (see Table 2 below).
1. Emergency: The HVA is instructed to terminate the interview immediately and assist
the participant or family members in contacting emergency medical services or their
treating physician.
2. Urgent: The participant is asked to see their health care provider within one to two
weeks. HVA or Call Center staff will follow-up with participant by phone to assess
disposition.
3. Check-Up: The participant is asked to follow-up with their health care provider within
one to two months.
Page 49 of 98
National Institute of Environmental Health Sciences (NIEHS)
GuLF Study - to IRB
11/3/2010
4. Routine Care: The participant is advised to seek guidance from health care providers
to learn about healthy lifestyle choices to help prevent disease.
5. No Referral: Results are within the normal range.
Alert Levels for Laboratory Results & Spirometry Interpretations:
CBC Abnormalities:
Alert levels for CBC abnormalities and post-exam spirometry interpretations will trigger
“Urgent” referrals. Within one week of Alert Level findings being reported by the
laboratory or spirometry reviewers, participants will be notified by phone and advised to
follow-up with a health care provider within one to two weeks (as indicated in Table 2).
The urgent referral action levels chosen were based upon the Jackson Heart Study of
African-American males and females ages 35-84 living in the Jackson, Mississippi area.
A study evaluating NHANES III data for persons over age 65 shows that about 3% of
men have Hgblevels below 12 g/dl and about 2% of women have Hgb below10 g/dl
(Guralnik 2004). It is anticipated that the rates of severe anemia in younger working
populations may be lower. However, we were not able to identify any clear guidance
from trusted sources with respect to this issue in the populations of concern for this
study. As noted above, we have typically erred on being conservative in this protocol.
Spirometry Abnormalities:
Alert Level for post-exam spirometry interpretations will be reported to participants by
phone within one week of receipt from the central laboratory. Participants will be advised
to follow-up with a health care provider within one week (as indicated in Table 2). The
spirometry alert level for an urgent referral utilizes the lower limits of normal (LLN) which
is an index derived from population data based on race, age, sex, and height. The LLN
is designed to be the 5th percentile for the index (FEV1, FVC, & Fev1/FVC) of interest
(Roberts 2006). The use of FEV1 < 50% results in a “severe classification” regardless of
obstructive or restrictive conditions and is consistent with ATS guidelines, assuming a
valid and interpretable test (Pellegrino 2005). Given the nature of worker cohorts we do
not expect to see very many participants in the severe category
Table 2.
Medical Care Referral Guidelines
Evaluation
Findings
Referral
Comments
Blood Pressure
SBP > 180 or
Emergency*. Seek
emergency care
immediately.
HVA to contact 911 or help
assist with referral as indicated.
HVA / Call Center to follow up
with participant by phone ASAP.
DBP ≥ 110
*Based on AHA 2010
guidelines
SBP 160 to 179 or
DBP 100 to 109
SBP 140 to 159 or
DBP 90 to 99
SBP 120 to 139 or
DBP 80 to 89
Check-up. See health care
provider within one month.
Results provided to participant
during encounter and mailed to
participant within one month.
Check-up. See health care
provider within two months.
Results provided to participant
during encounter and mailed to
participant within one month.
Routine. Those with slightly
high BP advised to discuss
need for any additional
Results provided to participant
during encounter and mailed to
Page 50 of 98
National Institute of Environmental Health Sciences (NIEHS)
GuLF Study - to IRB
11/3/2010
evaluations of lifestyle
changes with HCP.
participant within one month.
No Referral.
Results provided to participant
during encounter and mailed to
participant within one month.
Urgent. See health care
provider within one week.
Results provided to participant
during encounter and mailed to
participant within one month.
HVA / Call Center to follow up
with participant by phone
within two weeks of
encounter.
Of Potential Concern. See
health care provider within
one month
Results provided to participant
during encounter and mailed to
participant within one month.
Glucose negative, no
symptoms* of diabetes,
Normal. No Referral.
Results provided to participant
during encounter and mailed to
participant within one month.
Obese (≥ 30)
Routine. If overweight or
underweight, discuss
results and potential
lifestyle changes with
health care provider.
Results provided to participant
during encounter and mailed to
participant within one month.
Urgent Referral. See health
care provider within one
week.
Participant advised to see HCP
within one week of receiving
phone call.
HVA / Call Center contacts
participant by phone within
one week of receiving
spirometry evaluation
Results mailed to participant
within one month.
Check-up. See health care
provider within one month.
Results mailed to participant
within one month.
FEV 1 , FVC, and
FEV1/FVC all above lower
limits of normal
No Referral.
Results mailed to participant
within one month.
CBC
ALERT LEVEL
Urgent Referral.
Hemoglobin
Males: <12; >20
HVA / Call Center contacts
participant by phone within
one week of receiving
results.
Participant advised to see HCP
within two weeks of receiving
phone call.
SBP < 120 AND
DPB < 80
Urine Glucose
Glucose > trace OR
Trace glucose with specific
symptoms* of diabetes.
*frequent urination & thirst
Negative glucose with
symptoms of diabetes OR
Trace glucose with no
symptoms* of diabetes
BMI
Overweight (BMI 25 to
29.9)
Normal (18.6 to 24.9)
Underweight (BMI < 18.5)
Spirometry
ALERT LEVEL
Either FEV 1 , FVC, or
FEV1/FVC below lower
limits of normal AND
FEV 1 , < 50% predicted
Either FEV 1 , FVC, or
FEV1/FVC below lower
limits of normal AND
FEV 1 , ≥ 50% predicted
Females: <10; >17
Page 51 of 98
Letter with results mailed to
participant within one month of
receipt from lab.
National Institute of Environmental Health Sciences (NIEHS)
GuLF Study - to IRB
11/3/2010
Results between alert level
and normal reference
range
Check-up. See health care
provider within two months.
Letter with results mailed to
participant within one month of
receipt from lab..
Within lab normal reference
range
No Referral.
Letter with results mailed to
participant within one month of
receipt from lab.
CBC
ALERT LEVEL
Urgent Referral.
Hematocrit
Males <35; >53
HVA / Call Center
contacts participant by
phone within one week of
receiving results.
Participant advised to see HCP
within two weeks of receiving
phone call.
Females <30; >50
CBC
Platelets
Letter with results mailed to
participant within one month of
receipt from lab.
Results between alert level
and normal reference
range
Check-up. See health care
provider within two months.
Letter with results mailed to
participant within one month of
receipt from lab.
Within lab normal reference
range
No Referral.
Letter with results mailed to
participant within one month of
receipt from lab.
ALERT LEVEL
Urgent Referral.
Participant advised to see HCP
within two weeks of receiving
phone call.
3
3
<50 x 10 ; >500 x 10
HVA / Call Center
contacts participant by
phone within one week of
receiving results.
Letter with results mailed to
participant within one month of
receipt from lab.
Results between alert level
and normal reference
range
Check-up. See health care
provider within two months.
Letter with results mailed to
participant within one month of
receipt from lab.
Within lab normal reference
range
No Referral.
Letter with results mailed to
participant within one month of
receipt from lab.
If the participant has abnormal test results, the HVA will suggest appropriate follow-up
with their healthcare provider. If the participant does not have a healthcare provider, they
will receive referrals for medical and mental health care providers, as needed, including
those providers that can assist with free or reduced-cost services (see Appendix N for
example of Healthcare Provider Resource Information).
For example, Louisiana State Health officials in District 1 have indicated that they are
willing and able to help individuals identify and access healthcare providers in their
community, if needed, and a growing list of community clinics are available to see
participants at little or no cost. Such referral information is being developed on an
ongoing basis, in close coordination with state and local health departments, nongovernmental organizations, and the local communities to help ensure appropriate
medical and mental healthcare referrals. It is anticipated that such information will
continue to evolve and require frequent updating. In order to ensure that this task is
being explicitly addressed, Study Coordinators located in the Gulf States will work with
health officials and communities in this matter.
Page 52 of 98
National Institute of Environmental Health Sciences (NIEHS)
GuLF Study - to IRB
11/3/2010
Additionally, we are working with state and local public health officials to identify any
additional public health information and resources related to weight control,
hypertension, diabetes, and other conditions that the HVAs can provide to the study
participants for educational and public health benefit.
2.10.5
Abnormal Findings Form
The HVA will document all evaluation findings in the CAPI system while they are
conducting the visit. This CAPI module that collects evaluation findings will contain
workflow features that prompt the HVA on how to proceed when abnormal findings are
obtained. The HVA will review the actions and check the appropriate items on the
checklist for cues as to subsequent steps to be taken depending on the findings or
situation (Appendix J, Baseline Questionnaire, Section N). Once this information has
been uploaded to the central database, selected responses will trigger further actions for
the HVA and Coordinating Center staff, such as follow-up phone calls, follow-up letters,
and assistance with referrals.
2.10.6
Follow-up Reports & Information
2.10.6.1 Follow-up of Urgent/Emergency Situations During In-person Encounter
If the HVA contacts 911 for an emergency situation, the HVA or Study Center
representatives may immediately follow-up, or as soon as possible with respect to the
situation, with the participant or their spouse to express our concern, check on their
current condition and determine future interest and ability to participate in the study.
2.10.6.2 Follow-up Letters to Summarize Evaluation Findings and Encourage
Recommended Actions
Within one month of the home visit, we will mail the participant a follow-up letter with a
summary of their evaluation results (see Appendix P and Q). This letter will also contain
information reiterating their results and recommended actions.
2.10.6.3 Reporting of CBC Laboratory Tests
For individuals in the Biomedical Surveillance Sub-cohort, CBC results and
interpretations will be included in the report that accompanies the follow-up letter.
Urgent findings identified by the laboratory will be phoned to individuals by the HVAs or
Call Center within one week of receipt from the laboratory. HVAs or Call Center staff will
also follow-up with participants within two weeks of sharing the results by phone to see if
they need additional assistance scheduling an appointment with a health care provider.
The date of all follow-up mailings will be recorded in the data system, any returned
mailings will be noted, and those that cannot be reached by mail will be contacted by
phone, if possible. Results of follow-up phone calls, including dates and times of calls,
responses, advice, and referrals given to participants will also be entered into the data
system.
2.10.6.4 Reporting of Spirometry Results to Participants
For participants that complete spirometry evaluations, interpretations of their results will
be included in the report that accompanies the follow-up letter. Alert Findings identified
Page 53 of 98
National Institute of Environmental Health Sciences (NIEHS)
GuLF Study - to IRB
11/3/2010
during evaluation of their measurements will be phoned to individuals by the HVAs or
Call Center within one week of receipt from trained pulmonary study reviewers. Urgent
Referrals for participants to see their HCPs within one week will have HVAs or Call
Center staff follow-up with participants within two weeks of sharing the results by phone
to see if they need additional assistance scheduling an appointment with a health care
provider. The date of all follow-up mailings will be recorded in the data system, any
returned mailings will be noted, and those that cannot be reached by mail will be
contacted by phone, if possible. Results of follow-up phone calls, including dates and
times of calls, responses, advice, and referrals given to participants will also be entered
into the data system.
2.10.6.5 Results Reporting to Physicians
If any of the participants’ evaluation findings are abnormal and the participant has a
health care provider and consents to sharing evaluation findings, we will mail the health
care provider a cover letter explaining the study and a copy of the summary of results
and recommended actions that was sent to the participant. This report will be sent to the
health care provider within one month of the home visit along with relevant contextual
information such as normal value ranges (see Appendix O) so that the physician can
provide the appropriate care to their patients.
2.11 Laboratory Biospecimen Processing and Storage
Once the biospecimens have arrived in the Central Processing Laboratory they will
undergo additional processing to separate out the various components (serum, plasma,
cell fractions) and aliquoting of samples into small volumes for cryostorage, before being
transferred to the long-term storage facility.
2.11.1
Central Laboratory Processing
Active Follow-up Sub-cohort Sample Processing: The three EDTA tubes will undergo
centrifugation to separate plasma, buffy coat, and RBCs, which will be aliquotted and
stored in cryovials, with the plasma in LN2 and the buffy coat and RBCs at -80°C. The
ACD tube will be cryopreserved with 10% DMSO and aliquotted into cryovials, which will
be subjected to programmed cryopreservation and stored in LN2. The Trace Metal and
PAXgene samples will be frozen in their original tubes at -20° C. The serum will be
aliquotted into cryovials and stored in LN2. The urine and saliva samples will be
aliquotted and stored at -80°C. The blood clots will be stored at -80°C. The hair samples,
and dust wipes will be stored at -20°C. Toenail samples will be stored with desiccant,
under controlled ambient temperature and humidity.
Biomedical Surveillance Sub-cohort Sample Processing: Samples from persons
tagged as eligible for inclusion in this sub-cohort will be processed in the same manner
as those of the rest of the Active Follow-up Sub-cohort except that, promptly upon
receipt at the central processing laboratory, 1) A portion of the urine sample will undergo
a more comprehensive dipstick urinalysis, 2) The 2 mL EDTA tube will be analyzed for
CBC with WBC differential, and 3) The ACD-B tube will undergo centrifugation to
separate plasma, buffy coat, and RBCs. The buffy coat will be mixed with 15% DMSO
cryoprotectant, aliquotted, and subjected to programmed freezing and storage in LN2, as
described above. The plasma and RBCs will be aliquotted into cryovials and stored at
-80°C.
Page 54 of 98
National Institute of Environmental Health Sciences (NIEHS)
GuLF Study - to IRB
11/3/2010
The CPL will prepare the accumulated samples for transport in bulk for archive storage
at the NIEHS Repository. All samples will be transferred to the NIEHS Repository for
storage in liquid nitrogen or -20°C/-80°C mechanical freezers, as appropriate for each
sample, within one week of receipt.
2.11.2
Study Sample Long-Term Storage at the NIEHS Repository
Environmental Pathology Laboratories (EPL) is the contractor that operates the NIEHS
Repository. EPL is located in Keystone Park, in close proximity to the NIEHS campus in
the Research Triangle Park in North Carolina.
The EPL Repository is a state of the art storage facility which integrates structural,
mechanical, electrical, HVAC, liquid nitrogen (LN2), and backup and monitoring systems
to maintain ideal storage temperatures. These systems ensure specimen integrity and
long-term preservation while supporting the safe and efficient storage of frozen
specimens.
EPL’s Repository houses a wide variety of biological and environmental samples and
provides storage space for frozen, refrigerated, and room temperature specimens and
associated data. The 17,000 square foot facility provides space for ultra-low temperature
mechanical and liquid nitrogen freezers, data and specimen storage, and a processing
laboratory. Nearly 10,500 square feet of space is dedicated to frozen storage, with a
capacity of approximately 185 ultra-low temperature mechanical and liquid nitrogen
freezers depending on the types of specimens to be stored. Additionally, the facility has
three -20°C walk-in freezers totaling 675 square feet of space. Currently, EPL has over
3.5 million frozen specimens stored in archival storage.
EPL has over 25 years experience managing and operating archives and repository
storage facilities for government and commercial clients. EPL provides qualified
professional and technical personnel, materials, equipment and facilities for the receipt
and long term, secure storage of samples, packaging of the samples for shipment,
processing requests for samples and for aliquoting and labeling new samples, as well as
distributing requested data and specimens.
Aliquots of a given type will be divided across liquid nitrogen and -20°C/-80°C
mechanical freezers, as appropriate for each sample, to maximize integrity of the
samples during long-term storage and to reduce risk of complete loss due to freezer
failure.
2.11.3
Analyses (including future studies)
Subjects targeted for the Biomedical Surveillance Sub-cohort (exposed and unexposed
participants) will have their CBC and WBC differentials measured in the 2 mL lavender
top tube promptly upon receipt of the tube by the central processing laboratory. This will
allow assessment of these measures among many, if not all, workers with the highest
expected benzene exposure (e.g., from exposure to crude oil or burning oil). These sets
of samples will be flagged prior to shipping and the lab will be separately notified of
these samples. The 2 mL lavender top tubes from all other subjects will be processed in
the same manner as the other lavender top tubes. Future analyses performed on
incoming fresh blood specimens in the sub-cohort may also include flow-cytometry to
determine changes to specific cell populations, such as CD4 or CD8, CD17, and
regulatory T-cells.
Page 55 of 98
National Institute of Environmental Health Sciences (NIEHS)
GuLF Study - to IRB
11/3/2010
Subjects targeted for the Biomedical Surveillance Sub-cohort also will have a portion of
their urine samples used for a basic chemistry urinalysis (Multistix Pro 10LS reagent
strips) to measure protein, creatinine, blood, leukocytes, nitrite, glucose, ketone, pH, and
specific gravity immediately upon receipt of the urine samples at the central laboratory.
All other samples will be processed and banked for future analyses.
Future analyses, to be conducted among targeted subsets of the cohort, may include
assessment of DNA damage via assays such as the alkaline comet assay and the
micronucleus test on the cryopreserved lymphocytes [Chang, et al. 2006, Zijno, et al.
2007]; global hypomethylation and average telomere length in DNA from buffy coat; liver
function tests (LFT) on serum; total immunoglobulins, autoantibodies, and inflammatory
markers in the serum; antibodies indicating loss of latency of chronic infections such as
Epstein-Barr virus and herpes viruses; gene expression related to exposure to benzene
and other VOCs using the sample in the PAXgene tube; N-acetyl-beta-Dglucosaminidase (NAGs), beta-2 microglobulin, microalbuminuria, neutrophil gelatinaseassociated lipocalin (NGAL), interleukin-18 (IL-18), kidney injury molecule-1 (KIM-1),
liver-type fatty acid binding protein in the urine to assess kidney injury; polymorphisms in
genes encoding metabolizing enzymes for benzene, other VOCs, and PAHs. The
specific assays and markers listed here are intended only to give an indication of the
types of test that we may want to perform later and that are being performed now in
similar contexts. In order to take best advantage of rapidly emerging technologies, we
will determine – and justify – the specific approaches to use around the time that we are
ready to undertake such analyses. We have developed our biospecimen collection,
processing, and storage protocols to allow as wide a range of analyses as can be
anticipated, including those not yet developed.
Exposure markers measured in stored specimens may include As, Cd, Cr, Mn, and Pb,
in the whole blood (royal blue top tubes, which have been validated for these metals), to
be based on toxicological analyses by other agencies of the oil from this spill; more
distant exposure to metals in the toe nail clippings; cortisol and more distant exposure to
metals in the hair; cortisol and urinary catecholamines in urine specimens.
If any workers are still engaged in clean-up or terminated clean-up within 30 days of
enrollment in the cohort, we may also examine more transient markers of exposure,
including urinary levels of benzene, toluene, mandelic acid, trans-muconic acid, hippuric
acid; and hemoglobin-PAH adducts.
2.12 Follow-Up of Cohorts
2.12.1
Telephone Questionnaires (Year 2 and 4)
Biennial follow-up of all Active Follow-up Sub-cohort participants will be conducted via
telephone. In-person interviewing, self-reported mailed questionnaires, and web-based
questionnaire options will be explored as needed to increase response rates. These
individuals will be asked to provide updates information on risk factors and outcomes
that they have experienced since their last study interview. Additional follow-up
questions can be developed based on the results of the baseline assessment. We plan
on developing and seeking the necessary approvals for this questionnaire closer to the
time of administration.
Page 56 of 98
National Institute of Environmental Health Sciences (NIEHS)
2.12.2
GuLF Study - to IRB
11/3/2010
Biomedical Surveillance Sub-cohort Follow-up (Year 1 and 3)
Participants selected for the Biomedical Surveillance Sub-cohort will undergo more
extensive testing and follow-up. These exams will be administered through an external
contract or contracts run in collaboration with extramural collaborators. Detailed
neurobehavioral, neurocognitive, and peripheral neuropathy measures will be collected.
More thorough respiratory function testing, including bronchodilator challenge, will be
performed. Additional tests and follow-up questionnaires and protocols will be
determined with the extramural collaborators and necessary approvals will be obtained
through the respective organizations.
2.12.3
Annual Morbidity and Mortality Outcomes (Year 2 and later)
Routine surveillance of GuLF study participants will be conducted beginning in Year 2.
Follow-up will include linkage with State Cancer Registries and state vital statistics as
well as linkage with the National Death Index (NDI). We will explore the feasibility of
other passive monitoring for changes in health via linkage with other routinely collected
surveillance data and electronic medical records that may become available.
2.12.4
Follow-up in Years 6-10
Routine surveillance of all GuLF study participants, using the NDI, potentially available
electronic medical records, and state cancer registries (among others), will be conducted
to investigate any morbidity and mortality associated with clean-up related activities.
Telephone interviews may be administered to all Active Follow-up Sub-cohort
participants in Years 6-7 and 9-10, using questionnaires similar to those used in Years 2
and 4 (see 2.12.1 above), but possibly including additional questions based on the
results of follow-up to date.
2.13 Retention Strategies
The strategies outlined in this section are intended to maximize retention, and in some
cases recruitment, efforts. These strategies will capitalize on the community outreach
effort as a core activity of the study design and implementation activities and build on the
trust and rapport between the local members of the research team, the target
communities and public health leadership across all five states.
A key to high response rates and long-term participation is not to simply contact
participants when data are needed but rather to maintain contact in small ways and
provide useful information including study results back to participants on a regular basis.
We will provide regular feedback about study progress and group results as well as
make sure we show our appreciation to the participants for their tremendous
commitment to this study. We will also meet regularly as a study team to review
progress made on retention efforts and obtain direct feedback to follow-up where
necessary.
2.13.1
Annual Update of Contact Information
In order to minimize loss to follow-up, we will provide participants with contact
information update forms that they can use to inform us of changes in their contact
Page 57 of 98
National Institute of Environmental Health Sciences (NIEHS)
GuLF Study - to IRB
11/3/2010
information. Update forms will be sent to participants once they have completed the
interviews and home visit and will be included with all subsequent study mailings for use
as needed. Thank you letters following the initial visit will include a GuLF Study magnet
that reminds participants to “keep in touch” and includes pertinent contact information.
The study website will also feature an “update contact information” button on the
homepage to register changes in contact information.
In addition, efforts will be made to update contact information annually. Participants will
be asked to complete a one-page update form annually, whether or not they have had
any changes in their contact information. Any mailings that have been “returned to
sender” will undergo tracing to identify updated address information. These annual
mailings will allow us to track changes in address and minimize losses-to-follow-up. We
will send reminder post-cards to participants who do not return the annual follow-up
form.
2.13.2
Newsletters and Other Mailings
Similar to the study website, annual newsletters will provide information on study
progress and findings. Additionally, we will send birthday cards or holiday cards every
year to enrolled participants along with small incentives/tokens of appreciation such as
pens, notepads, calendars, and magnets with the study logo on them to maintain contact
and long-term study interest.
2.13.3
Study Website
We will maintain a website to provide information about the study. The website will be
updated regularly with details on recruitment efforts, study findings, and links to other
organizations and information resources. Additionally, we will seek to have each of our
community partners have a link on their website to the study website. As feasible, the
website may contain details on upcoming or ongoing health research studies of oil spill
workers. In order to support retention efforts, study participants will also be able to
provide study investigators updates to their contact information via a secured web form
on the website.
2.13.4
Social Media
Segments of the oil clean-up worker population are active social media users partly due
to long trips away from home. Social media such as Facebook can be used to reach
these workers to build study credibility, provide more frequent updates, and prompt
participation in the out years of the study. However, as we expect web access to be
quite incomplete, this approach is not expected to be effective across the cohort. As
part of our retention efforts, we will explore the use of Web 2.0 resources (e.g.
Facebook, Twitter, etc.) to encourage retention and facilitate follow-up. We will explore
the possibility of establishing a presence on a site such as Facebook and maintain study
updates as well as other information related to the spill. We envision that study
participants can opt to be emailed when updates are provided to the social media site or
may even chose to be a “friend” of the site. Additionally, we envision that we will be able
to reach out to community organizations and invite them to be a “friend” of the site.
Because the social media landscape will undoubtedly change during the study duration,
we will continue to monitor for opportunities to utilize this technology for maintaining
contact and encouraging retention in study activities. However, we must be assured that
Page 58 of 98
GuLF Study - to IRB
11/3/2010
National Institute of Environmental Health Sciences (NIEHS)
participant confidentiality will be maintained and that a significant proportion of
participants are actively participating in these media to justify the feasibility of creating
and maintaining these resources. We will seek IRB approval for all social media
advertising activities.
2.13.5
Community Partnerships and Outreach
As described in Section 3.4 - Community Outreach, we will utilize linkages with the
communities in all five states to augment recruitment efforts. Similarly, we will utilize
community partnerships and relationships with other organizations to support retention
efforts. First, we will continue to convene the Community Advisory Group (CAG) on at
least a semi-annual basis throughout the life of the project. Subcommittees of the CAG
may be created where necessary to address retention activities and other challenging
situations regarding the cohort. We will rely on the leaders within each community to
recommend retention strategies best utilized with their constituents. As we continue to
develop relationships with communities, we will incorporate these strategies and revise
the plans for study retention.
2.14 Remuneration
In addition to non-monetary incentives such as refrigerator magnets, chip clips,
stationery, and pens, participants in the Active Follow-up Sub-cohort will receive
remuneration for their time and effort in the form of pre-paid gift cards or phone cards.
Remuneration will be offered to participants at the baseline home visit and for each
completed follow-up questionnaire. We will explore options in terms of distributing the
gift cards immediately upon completion of their visit or mailing the gift cards within 2 to 3
weeks of each completed study event. The amount of remuneration for each study event
is provided in the table below. A separate remuneration schedule will be developed for
the more comprehensive activities of the Biomedical Surveillance Sub-cohort.
Additional incentives for recruitment and participation such as drawings for prizes such
as sporting event tickets, and recruitment events featuring food bank distributions,
community health fairs, or other community events will be explored based on feedback
from the community and assessment during the run-in phase of the study. We will
confer with the appropriate scientific, community, institutional and ethical advisory
boards to determine the appropriateness of these additional incentives.
Table 3.
Remuneration for Completion of Study Events
Active Follow-up
Sub-cohort
Passively followed
members of full cohort
Baseline Home Visit
$25
N/A
Duplicate Biospecimen Collection
at Baseline Home Visit*
$10*
Year 2 Follow-Up Questionnaire
$10
N/A
Year 4 Follow-Up Questionnaire
$10
N/A
$45 or $55*
N/A
Study Event
Total in first 5 years
Page 59 of 98
National Institute of Environmental Health Sciences (NIEHS)
GuLF Study - to IRB
11/3/2010
* Only for the randomly selected individuals participating in the duplicate biospecimen
collection.
2.15 Study Timeline
The GuLF Study investigators will engage community and scientific leaders during the
study design process for input and refinement. A timeline of study activities is presented
in Table 4.
Page 60 of 98
GuLF Study - to IRB
National Institute of Environmental Health Sciences (NIEHS)
11/3/2010
Table 4.
Study timeline
Study Design
and Scientific
Input
Community
Outreach
Study Start
Subject
Recruitment
Enrollment
Questionnaires
Home Visits
Biomedical
Surveillance
Sub-Cohort
Follow-up
Newsletter
Follow-up
Year 2 Followup
Newsletter
Follow-up
Year 4 Followup
Q3
2010
Q4
Q1
2011
Q2
Q3
Q4
Q1
2012
Q2
Q3
Q4
Q1
2013
Q2
Q3
Q4
Q1
2014
Q2
Q3
Q4
Q1
2015
Q2
Q3
Q4
●
●
●
●
●
●
●
●
●
●
●
●
●
●
●
●
●
●
●
●
●
●
●
●
●
●
●
●
●
●
●
●
●
●
●
●
●
●
●
●
●
●
●
●
●
●
●
●
●
●
●
●
●
●
●
●
●
●
●
●
●
●
●
●
●
●
Page 61 of 98
National Institute of Environmental Health Sciences (NIEHS)
3
Evaluation of Benefits and Risks
3.1
Potential Benefits
GuLF Study - to IRB
11/3/2010
All study participants may benefit from positive feelings associated with participating in a
study of the health effects of the oil spill that may be of value to their community. In
addition the knowledge gained from this study may have a significant impact on future
public health responses to similar disasters. It is also possible that participants may
benefit directly from public health responses that are based on early findings from this
study.
Participants in the Active Follow-up Sub-cohort may benefit from receiving results of
medical evaluations and health care referrals that they may not otherwise receive (see
Section 3.10. - Reports to Participants and Health Care Referrals).
3.2
Potential Risks
The questionnaires and procedures in this observational study present minimal risks to
study participants. The questionnaires are based on instruments that are widely used in
epidemiological studies. Adverse events associated with study procedures are expected
to be uncommon and limited to mild and transient discomforts. In order to minimize risks
to participants, all study procedures will be conducted by qualified, experienced, and
well-trained field staff.
The main risk in questionnaire administration involves questions about sensitive health
topics or personal experiences that may be traumatic. Participants will be told that they
can skip any questions that make them feel uncomfortable or end the interview at any
time. Participants will also be warned of the possibility of loss of privacy should their deidentified data distributed through controlled access procedures (see section 11.2a) be
linked back to them in ways that cannot be foreseen at present.
Pulmonary function testing is considered safe. The primary risk, which is exceedingly
rare, is fainting in older participants with impaired lung function. We minimize the chance
that this rare event will occur first through our very conservative exclusions for
pulmonary function testing – any heart attack or hospitalization for other heart problem
or stroke in the past 3 months. Pregnant women will not undergo pulmonary function
testing until at least 3 months post-partum. To further minimize risk of fainting,
pulmonary function testing is done in a seated position, and study staff are trained to
look for signs of dizziness or other problems and to stop the maneuver if necessary. The
risk of infection is all but eliminated by using disposable mouthpieces (spirettes). These
disposable mouthpieces have the additional protection of having a built-in bacterial filter.
In the PLATINO [Menezes, et al. 2005] and BOLD [Buist, et al. 2007] studies, home
visits were conducted on 14,000 adults over age 40 by trained technicians only, without
physicians present, and no adverse events were associated with in-home spirometry.
There may be some minor discomfort associated with blood collection, including
temporary pain, bruising, or swelling at the phlebotomy site. Fainting during blood
collection is exceeding rare.
Page 62 of 98
National Institute of Environmental Health Sciences (NIEHS)
GuLF Study - to IRB
11/3/2010
There is also a remote risk of accidental disclosure of study information. Measures that
will be taken to guard against accidental disclosures include maintaining complete
confidentiality of the questionnaires and laboratory samples, use of secure data
systems, and staff training (see Section 10.3 – Participant Confidentiality). Participants
will also be warned of the possibility of loss of privacy should their de-identified data
distributed through controlled access procedures be linked back to them in ways that
cannot be foreseen at present.
4
Adverse Event Reporting
Adverse events associated with this study protocol are expected to occur very
infrequently. Field staff will be trained to detect and respond to adverse events. They will
also expect to promptly report clinically significant adverse events. The principal
investigator will be responsible for reporting clinically significant adverse events to the
IRB according to NIEHS policy.
Study Oversight
5
The Principal Investigator will monitor and evaluate the progress of the study, including
periodic assessments of data quality and timeliness, participant recruitment,
administration of informed consent, accrual and retention, participant risk versus benefit,
performance of contractors and other factors that can affect study outcome. This
monitoring will also consider factors external to the study when interpreting the data,
such as scientific or therapeutic developments that may have an impact on the safety of
the participants or the ethics of the study.
The study team, all of whom will contribute to study oversight, has the experience
necessary to provide this oversight:
Dale Sandler, Ph.D. Principal Investigator NIEHS
Richard Kwok, Ph.D., Lead Associate Investigator, NIEHS
Lawrence Engel, Ph.D., Associate Investigator, Memorial Sloan-Kettering and
NIEHS
Stephanie London, M.D., Dr.P.H., Associate Investigator, NIEHS
Aubrey Miller, M.D., M.P.H. Associate Investigator, NIEHS
Christine Parks, Ph.D., Associate Investigator, NIEHS
Aaron Blair, Ph.D., Consultant, NCI
John Hankinson, Ph.D., Consultant, Hankinson Associates
Mark Stenzel, Consultant, Exposure Assessment Applications, LLC.
Patricia A. Stewart, Ph.D., Consultant, Stewart Exposure Assessments, LLC.
SRA International (“SRA”), a provider of professional research services, will provide
support for this study through an existing contract with the NIEHS. SRA will oversee the
day-to-day activities of the study with oversight from the NIEHS investigators. SRA will
be responsible for hiring, training, and managing call center and field staff. SRA will
ensure that all staff members have the proper education, experience, and training
Page 63 of 98
National Institute of Environmental Health Sciences (NIEHS)
GuLF Study - to IRB
11/3/2010
required for their role in the study. All staff will be trained in human subject protections,
the study protocol, and study procedures relevant to their role. They will also be required
to sign confidentiality agreements. Whether SRA hires staff directly or subcontracts with
a staffing agency, SRA will manage and oversee all study operations and training. SRA
will also provide data management services and subcontract for lab processing services.
A GuLF Study Scientific Advisory Board will be established as a subcommittee of the
NIEHS Board of Scientific Counselors to provide additional oversight. This Board will
include one or more members of the Board of Scientific Counselors, scientific experts,
community representatives and Federal agency representatives. A separate Community
Advisory Board, consisting of representatives of key study populations in the affected
states, also will be established. Through funding made possible by a Gift to the NIH, the
NIH has arranged to have the Institute of Medicine review the initial plans for the study
and monitor study progress. The IOM held its first meeting focused on the GuLF Study
on September 22, 2010. It is expected that the IOM will meet twice a year for several
years, and then annually to review study progress and findings. An Interagency working
group made up of representatives from each Federal Agency involved in some aspect of
the oil spill response met on August 19, and is also expected to meet regularly to provide
study oversight.
6 Statistical Analysis Methods
6.1
Treatment of Exposure Status and Health Outcomes
Estimates of quantitative levels for specific exposures will be developed to the extent
possible by the industrial hygiene team. Exposure status (e.g. any contact with crude oil,
dispersants, or relevant crude oil specific chemicals, e.g., benzene, heavy metals, etc.)
will also be defined dichotomously as “exposed” or “unexposed” based on the definitions
given above for the study population and an activity-based exposure reconstruction
(Sections 3.1.1 and 3.1.3). Similarly, health outcomes will be examined quantitatively
where appropriate (e.g., FEV1/FVC, CBC measures), and will also be defined as
“present” or “not present” based on the existence of specific endpoints within each
disease area of interest (respiratory, cardiovascular, hematologic, dermatologic,
neurologic, cancer, reproductive, mental health, immunologic, renal, liver).
We expect that very few workers engaged in clean-up related tasks, but not in clean-up
per se, such as those providing only administrative, logistical, or personnel support, will
be enrolled in the cohort because of the initial screening. However, any such workers
found to be enrolled in the cohort will be placed in an “unexposed worker” category and
excluded from most analyses because their exposure profile will be fundamentally
different from that of the other clean-up workers and they are likely to differ in important,
potentially unmeasured, respects (e.g., physical activity, socioeconomic status, health
care access or quality) from the other clean-up workers. We will revisit this approach
after examining results from the mini-pilot to determine whether this should be
incorporated into the full study.
6.2
Statistical Methods to Address Study Objectives
The objectives of this study are to evaluate and characterize relationships between
exposures to oil, oil byproducts and/or chemical dispersants, and stress associated with
Page 64 of 98
National Institute of Environmental Health Sciences (NIEHS)
GuLF Study - to IRB
11/3/2010
the disaster and short- and long-term health effects. General analysis methods to
address these objectives are as follows:
Descriptive analyses will be conducted as a precursor to other investigations.
Rates and proportions will be estimated and bivariate relationships will be explored
using cross tabulations. 95% confidence intervals (CIs) will be estimated where
appropriate.
Acute- and Short-term Outcomes: Acute- and short-term health effects that may
have been incurred during or immediately following exposure will primarily be
assessed during baseline data collection and in the immediate follow-up time-period.
Relationships between exposures and these outcomes will be investigated at the
most basic level by fitting regression models: logistic regression models for
dichotomous outcomes to estimate odds ratios (ORs) and 95% confidence intervals
(CIs) for each exposure and least squares regression for continuous outcomes to
estimate betas and standard errors (SEs) for each exposure. Relevant demographic
variables (e.g., sex, age, race, socioeconomic status indicators) and other exposures
will be included in the regression models as covariates and effect modifiers. More
refined analyses will incorporate specific characterizations of exposure, such as type
of work performed, location, nature, and duration of exposure, protective equipment
used, and ultimately a quantitative index of exposures developed by a panel of
industrial hygienists and other exposure experts to reflect the risk factors of interest.
Outcomes that will be evaluated include respiratory symptoms, nausea, headaches,
dermatitis, depressive symptoms, anxiety, FEV1/FVC, CBC components, WBC
differentials, DNA damage, etc.
Long-term Outcomes: Long-term health effects that may be incurred in the years
following the exposure will be assessed at regular intervals through follow-up by
interview or linkage with disease/mortality registries. Relationships between
exposures and dichotomous health outcomes will be investigated by fitting binomial
repeated measures models to each outcome, using standard statistical software
such as SAS Proc GENMOD and Proc MIXED. Exposure effects will be assessed
via ORs for each observation period. Non-dichotomous outcome measures will be
investigated using generalized linear models; appropriate transformations will be
used to satisfy model assumptions. Relevant demographic variables (e.g., sex, age,
race, SES indicators) and other exposures (including ongoing, repeated
environmental variables where available) will be included in the repeated measures
models as covariates. These outcomes will include cancer, neurological
(neurocognitive, neurobehavioral, neurophysiological) deficits, cardiovascular injury,
reproductive effects, persistence of early effects, among others.
Various refinements to these basic methods as well as these additional analyses will
also be pursued:
Confounding and Effect Modification: Potential confounders and effect modifiers
will be introduced into the models to determine the extent to which they might
influence any effect. A potential confounder will be retained in the model if its
inclusion changes the estimated effect of an exposure or the length of its 95%
Page 65 of 98
National Institute of Environmental Health Sciences (NIEHS)
GuLF Study - to IRB
11/3/2010
confidence interval by 10% or more. Stratified analyses will also be used, as
appropriate. Information on many of these factors will be obtained by interview, but
others may come from analysis of biologic specimens. . In addition, we will perform
sensitivity analyses to assess the impact of unmeasured confounders, classification
errors (for both exposures and outcomes), and selection bias on estimates of
exposure-disease association. This will be done in part using probabilistic methods
to quantify the likely effects of misclassification of dichotomous measures [Fox, et al.
2005, Chu, et al. 2006] and polytomous measures [Arah, et al. 2008].
Repeated measures: Repeated measurements on individual components of longterm health outcomes (examples: reported numbers of days experiencing asthma
symptoms, FEV1/FVC) will be investigated for association with exposure through
repeated measures mixed-effect models, while introducing appropriate effect
modifiers. In particular, pulmonary function measures provide objective data that
complement less objective self-reported symptom data, but are typically quite
variable. Results from other studies suggest that, at a given time point, we can
expect to detect differences in FEV1 as low as 5% between subgroups of about 250
participants per group with 80% power. Analyses to compare larger subgroups,
compare groups across multiple time points, detect changes over time, or investigate
the FEV1/FVC ratio all involve more stable measures or comparisons and so will
exhibit greater statistical power.
Non-reversing binary prospective outcomes, such as incident diagnoses, will also be
modeled using Cox proportional hazards models.
6.3
Interim and Safety Analyses
Adverse events associated with study procedures such as blood draws and pulmonary
function testing are expected to be uncommon and limited to mild and transient
discomforts. Such events will be monitored through interim reports. Interim reports will
also be used to monitor parameters that characterize the conduct of the study, such as
pace of recruitment, completeness of scheduled activities, time lags associated with data
entry and laboratory testing, as well as QC reports for issues such as inter-observer
variability and inter- and intra-laboratory variability. Study statisticians will develop these
and other reports. No early stopping rules are in place for this study since there is no
treatment and no anticipated risk to participants. Analyses of short-term health outcomes
will be conducted after completion of baseline visits. Other interim analyses may be
conducted in a blinded fashion so as not to influence investigators or study staff with
respect to the conduct or completion of the study.
6.4
Laboratory QA/QC Analyses
Laboratory QA/QC data will be reviewed for evidence of excessive variability and for
trends indicating shifts in process control. Data from blind QC samples submitted to
laboratories will be analyzed and within-pair coefficients of variation (CV) for internal
(within laboratory) consistency samples will be calculated. Inter-laboratory reliability will
Page 66 of 98
National Institute of Environmental Health Sciences (NIEHS)
GuLF Study - to IRB
11/3/2010
be investigated by analysis of results of laboratory same-sample analyses. The
duplicate blood and urine samples collected from randomly selected individuals in the
study (mentioned in Section 2.9.5) will provide specimens for these QA/QC efforts.
These individual and pooled samples will be used for quality control purposes such as
assessing long-term storage effects and assay batch variability.
6.5
6.5.1
Sample Size Considerations and Power
Estimated sizes of worker (exposed) and non-worker (unexposed)
groups
Based on currently available information, we anticipate that when we merge the PEC list,
the NIOSH list, the lists of workers from Federal agencies that may be included in this
study (e.g., Coast Guard, Fish and Wildlife Service, US Geologic Survey), and other
worker lists, and then remove duplicates, persons who provided no contact information,
and persons who indicated that they intended to work on clean-up for less than one
week (< 0.2% of the early NIOSH roster, but possibly a larger number; likely to be
persons with no intention of engaging in clean-up work), the merged list will contain
approximately 90,000 names. Based on early NIOSH information, approximately 95% of
these persons will be from one of the five Gulf States. Restriction of the workers, for
logistical reasons, to persons from the five Gulf States and to those workers from outside
of those states who experienced certain high exposures such as to benzene, burning oil,
and dispersants will produce a list of approximately 86,000 persons. It is expected that
after loss to follow-up, non-response, and refusal, about 54,000 eligible persons (a 6065% participation rate) will complete the enrollment questionnaire. Among this group, we
estimate that about 43,000 (80%) will have engaged in clean-up activities while the
remaining 11,000 (~20%) did not. We anticipate recruitment of an additional
approximately 1,000 unexposed Federal workers (as controls) from among an additional
pool of about 1,550 Federal workers (65% response rate) who were eligible for clean-up
work but were ultimately not deployed by their agencies that participated in the clean-up.
This will result in a total of approximately 12,000 unexposed individuals (i.e.,
11,000+1,000) and a full cohort size of ~55,000.
There are sufficient eligible persons to recruit 20,000 workers and 7,000 controls into the
Active Follow-up Sub-cohort, assuming a 70% participation rate among persons who
have already enrolled in the full cohort by participating in the telephone interview. The
size of the Active Follow-up Sub-cohort has been capped at 27,000 in light of available
funding and statistical power considerations; the base population is large enough that
this target is achievable even with a modestly lower participation rate. Based on current
information, we estimate that about 26% of the eligible controls are from outside the
immediately affected communities. By oversampling these non-local controls, we expect
to recruit approximately 2,000 non-local controls and 4,000 local controls, in addition to
the 1,000 Federal controls described above.
The expected participation rates provided above are reasonable, given anecdotal reports
from collaborating federal agencies, media reports, and feedback from community
groups and focus groups of clean-up workers that indicate widespread concern about
potential health effects from the oil spill among clean-up workers and members of the
affected communities. Furthermore, it is possible that the eventual cumulative total of
workers will be greater than is currently estimated. We will know the real total only after
we have obtained worker lists from other agencies and local communities engaged in
Page 67 of 98
National Institute of Environmental Health Sciences (NIEHS)
GuLF Study - to IRB
11/3/2010
clean-up and crossed the lists to identify unique additional workers who did not complete
PEC training. In any case, power calculations indicate that even if actual participation
rates turn out to be as much as 20% lower than those indicated above, this study will still
be sufficiently powered to achieve its specified aims, with an increase in minimum
detectable ORs or differences of less than 10-15%.
The rest of the full cohort (N~28,000) will comprise individuals to be passively followed
who either were not randomly sampled to be part of the Active Follow-up Sub-cohort or
who refused to be part of the Active Follow-up Sub-cohort (but participated in the
enrollment telephone interview). This represents about 23,000 workers and about 5,000
controls.
Thus, the total size of the full cohort is anticipated to be approximately 55,000 persons
(43,000 workers and 12,000 controls), consisting of 27,000 members of the Active
Follow-up Sub-cohort (20,000 workers and 7,000 controls [4,000 local, 2,000 non-local,
and 1,000 Federal]) and 28,000 passively followed members of the full cohort (23,000
workers and 5,000 controls).
Based on other prospective observational studies, we anticipate 90% follow-up and
participation in telephone interviews after enrollment for the Active Follow-up Sub-cohort.
Thus, completed follow-up interviews are expected for approximately 18,000 workers
and 5,400 controls in Years 2 and 4.
6.5.2
Sample Power
This study is designed not around a few narrow a priori hypotheses, but rather to allow
the investigation of a wide range of potential adverse health effects. The study size and
the number of individuals who experienced a given exposure – and the consequent
statistical power – have largely been determined by the number of individuals involved in
the clean-up operations and their distribution by task/exposure. While this study will have
limited power to examine certain rarer exposures or outcomes in the near future, this is
the largest study to date of oil spill clean-up workers and it is important that we address,
to the extent feasible, the wide range of public health concerns. It is a prospective study
and as time passes, if the exposure continues to exert an impact on some health
outcomes, power will increase.
Table 3 presents minimum detectable odds ratios across a range of proportions of
exposure among the workers and of health outcome among the controls. Estimates are
shown separately for analyses of the full cohort and of the Active Follow-up Sub-cohort,
including all controls or including only the non-local controls. Estimates are also shown
for analyses of the Biomedical Surveillance Sub-cohort. All estimates are based on a
two-sided test with α=5% and power=80%. As the table shows, this study has excellent
power to detect small risks, except when exposure or outcome is rare. For example, in
an analysis of the full cohort, if 10% of the workers received a given exposure (e.g., high
exposure to VOCs) and the incidence or prevalence of disease is 1%, this study would
have sufficient power to detect an OR of at least 1.56 when using all 12,000 controls,
1.78 when using the 3,300 non-local controls (i.e., assuming 80% [N=800] of Federal
worker controls plus the 2,500 other non-local controls) and 1.86 when using only the
2,500 non-local controls (i.e., excluding the non-local Federal worker controls). In an
analysis restricted to the Active Follow-up Sub-cohort, with proportion of exposure of
10% and disease incidence/prevalence of 10%, the minimum detectable OR would be
only 1.25-1.32 when using the full control group (N=7,000) or the non-local control
groups (N=2,000-2,800). The Biomedical Surveillance Sub-cohort, with 4,500 workers
Page 68 of 98
GuLF Study - to IRB
11/3/2010
National Institute of Environmental Health Sciences (NIEHS)
and 500 controls, provides adequate statistical power to detect odds ratios of at least
1.58 when 25% of workers received a given exposure and the incidence or prevalence
of disease is 10%. For perspective, estimated relative risks of lower respiratory tract
symptoms observed among clean-up workers in previous oil spills ranged from 1.5 to 3.6
[Janjua, et al. 2006, Zock, et al. 2007, Meo, et al. 2009, Sim, et al. 2010]. Thus GuLF
Study is sufficiently powered to observe such relative risks for these outcomes.
Table 3. Minimum detectable odds ratios for a range of proportions of exposure among
the workers and for all controls vs. non-local controls, based on a two-sided test with
α=5% and power=80%
Size of
control group
(i.e., all vs.
non-local)
5%
Proportion (N) of workers exposed to a given agent
10%
25%
50%
75%
100%
Full cohort: 43,000 workers, 12,000 controls:
N=2,150
N=4,300
N=10,750
N=21,500
N=32,250
N=43,000
1.41
1.66
1.76
1.35
1.62
1.72
1.33
1.61
1.71
1.32
1.60
1.70
1.13
1.20
1.22
1.11
1.19
1.21
1.10
1.18
1.21
1.10
1.18
1.21
1.08
1.13
1.14
1.07
1.12
1.14
1.07
1.12
1.14
1.07
1.12
1.13
N=10,000
N=15,000
N=20,000
1.59
1.80
1.93
1.50
1.72
1.86
1.46
1.70
1.83
1.44
1.68
1.82
1.18
1.24
1.27
1.15
1.21
1.25
1.14
1.21
1.24
1.14
1.20
1.24
Proportion of controls with outcome=1%
12,000a
3,300b
2,500c
1.74
1.94
2.02
1.56
1.78
1.86
Proportion of controls with outcome=10%
12,000a
3,300b
2,500c
1.23
1.28
1.30
1.17
1.23
1.25
Proportion of controls with outcome=30%
12,000a
3,300b
2,500c
1.15
1.18
1.19
1.11
1.15
1.16
Active Follow-up Sub-cohort: 20,000 workers, 7,000 controls:
N=1,000
N=2,000
N=5,000
Proportion of controls with outcome=1%
7,000a
2,800b
2,000c
2.12
2.28
2.38
1.82
2.00
2.12
Proportion of controls with outcome=10%
7,000a
2,800b
2,000c
1.34
1.38
1.40
1.25
1.30
1.32
Page 69 of 98
GuLF Study - to IRB
11/3/2010
National Institute of Environmental Health Sciences (NIEHS)
Proportion of controls with outcome=30%
7,000a
2,800b
2,000c
1.22
1.25
1.26
1.17
1.19
1.21
1.12
1.15
1.17
1.10
1.14
1.16
1.09
1.13
1.16
1.09
1.13
1.15
Biomedical Surveillance Sub-cohort: 4,500 workers, 500 controls:
N=250
N=500
N=1,250
N=2,500
N=3,750
N=5,000
3.28
3.09
3.02
2.99
1.58
1.54
1.52
1.51
1.37
1.34
1.33
1.33
Proportion of controls with outcome=1%
500a
4.48
3.78
Proportion of controls with outcome=10%
500a
1.89
1.71
Proportion of controls with outcome=30%
500a
a
b
c
1.58
1.46
All controls in cohort/sub-cohort
Non-local controls in cohort/sub-cohort, including estimated 80% of Federal worker
controls
Non-local controls in cohort/sub-cohort
Minimum detectable differences for continuous outcomes are presented in Table 4.
Differences are expressed in standard deviations (SDs) and are based on a two-sided
test with α=5% and power=80%. Results are shown separately for analyses of the full
cohort and of the Active Follow-up Sub-cohort including all controls or including only the
non-local controls. In addition, estimates are shown for analyses of the Biomedical
Surveillance Sub-cohort. This table demonstrates that the present study has sufficient
power to detect small differences in continuous outcomes. For example, in an analysis of
the full cohort that examines an exposure of 10% prevalence, we will be able to detect
minimum differences of less than 0.050-0.071 SD. A similar analysis in the Active
Follow-up Sub-cohort will be able to detect minimum differences of less than 0.09 SD
(0.071 when using all 7,000 controls; 0.082 when using the 2,800 non-local controls (i.e.,
assuming 80% of Federal worker controls plus the 2,000 other non-local controls); and
0.089 when using the 2,000 non-local controls (i.e., excluding the non-local Federal
worker controls)). Such an analysis in the Biomedical Surveillance Sub-cohort will have
sufficient power to detect a minimum difference of 0.177 SD. For perspective, in a study
of volunteers involved in the Prestige oil spill clean-up and unexposed controls [Laffon,
et al. 2006], results of the comet assay in peripheral blood leukocytes showed
differences between the two groups of approximately 4.3 SD in comet tail length. A study
of health effects related to the Tasman Spirit oil spill found a difference of about 0.6 SD
in symptom scores between coastal residents affected by the spill and persons living
away from the site of the spill [Janjua, et al. 2006]. The present study is very well
powered to detect such effects.
Table 4. Minimum detectable differences, in standard deviations, for continuous
Page 70 of 98
GuLF Study - to IRB
11/3/2010
National Institute of Environmental Health Sciences (NIEHS)
outcomes for a range of proportions of exposure among the workers and for all controls
vs. non-local controls, based on a two-sided test with α=5% and power=80%
Size of
control group
(full vs. nonlocal)
5%
Proportion of workers exposed to a given agent
10%
25%
50%
75%
100%
Full cohort: 43,000 workers, 12,000 controls:
12,000a
3,300b
2,500c
N=2,150
0.066
0.078
0.082
N=4,300
0.050
0.065
0.071
N=10,750
0.037
0.056
0.062
N=21,500
0.032
0.052
0.059
N=32,250
0.030
0.051
0.058
N=43,000
0.029
0.051
0.058
N=15,000
0.041
0.058
0.067
N=20,000
0.039
0.057
0.066
Active Follow-up Sub-cohort: 20,000 workers, 7,000 controls:
7,000a
2,800b
2,000c
N=1,000
0.095
0.103
0.109
N=2,000
0.071
0.082
0.089
N=5,000
0.052
0.066
0.074
N=10,000
0.044
0.060
0.069
Biomedical Surveillance Sub-cohort: 4,500 workers, 500 controls:
500
a
b
c
a
N=250
0.217
N=500
0.177
N=1,250
0.148
N=2,500
0.137
N=3,750
0.133
N=5,000
0.131
All controls in cohort/sub-cohort
Non-local controls in cohort/sub-cohort, including estimated 80% of Federal worker
controls
Non-local controls in cohort/sub-cohort
Finally, power calculations indicate that even if participation rates turn out to be as much
as 20% lower than expected, the minimum detectable ORs or differences will increase
by less than 10-15%.
7
Analysis Plan
7.1
Primary Endpoints
Given the very limited health effects research conducted to date on oil spill clean-up
workers, the GuLF Study is designed not around a particular a priori hypothesis, but
rather to allow investigation of a wide range of potential adverse health effects, including
physical, psychological, and biological effects. These include both short-term and longterm effects focused on, but not limited to, the following areas: respiratory,
cardiovascular, hematologic, dermatologic, neurologic, cancer, reproductive, mental
health, immunologic, hepatic, and renal. A priori outcomes of greatest interest based on
previous studies are respiratory effects, neurological dysfunction, and genotoxic and
hematologic effects.
Page 71 of 98
National Institute of Environmental Health Sciences (NIEHS)
GuLF Study - to IRB
11/3/2010
Questionnaire-based exposure information will be examined in relation to outcomes in
both prospective and cross-sectional analyses in the full cohort or sub-cohorts. Because
many biological and environmental assays are expensive and samples are limited, we
also plan to carry out nested case-control or case-cohort studies within the cohort.
Many of the primary exposure measures will be from job-exposure matrices (JEMs),
which will be developed by the investigators using time-specific task and exposure data
from a range of sources. These will be semi-quantitative (e.g., 5-point scale). They will
be treated in statistical analyses as ordinal values or, depending on distribution or
scientific considerations, collapsed into fewer categories (e.g., high vs. low).
Endpoints will be identified through several means. First, we will use the self-reported
health information provided in the enrollment interview(s) to define case groups or to
assign quantitative or semi-quantitative health categories for a given outcome or
constellation of outcomes, as appropriate. Self-reported health histories from this
interview will be used to identify outcomes with an onset or increase in severity after the
subject began clean-up work (i.e., not a pre-existing condition). Some self-reported
health information may be validated in sub-studies through subsequent information
provided, with participant permission, by the subject’s doctor, the subject’s medical
record, and/or the subject him/herself. Second, we will have clinic information such as
the FEV1/FVC results collected at enrollment from all subjects who live within the
immediately affected areas and the urinary glucose results obtained at enrollment from
all subjects.
We will examine results of a Complete Blood Count (CBC) with white blood cell
differentials among members of the Biomedical Surveillance Sub-cohort. Endpoints will
include total WBCs, individual WBC components, red cell measures, and platelets.
White blood cell and platelet counts have been found to be significantly reduced among
workers with low exposure to benzene, with reduced hemoglobin concentration among
workers with higher exposure to benzene [Lan, et al. 2004]. To explore potential effects
of metals, particulates, and stress, we will examine measures of the acute phase
response (C-reactive protein), inflammatory cytokines, as well as anti-nuclear and
thyroid antibodies. We will also examine results of the urinalysis (for protein, creatinine,
blood, leukocytes, nitrite, glucose, ketone, pH, and specific gravity) among members of
the Biomedical Surveillance Sub-cohort.
In subsets of the Active Follow-up Sub-cohort or the Biomedical Surveillance Sub-cohort
defined by higher or lower stress exposure and in vulnerable sub-populations, we will
also examine antibodies to latent viral infections as indicators of sub-clinical depressed
immunity. Antibodies to latent infections have been studied frequently in relation to the
physiological impact of stress, and may vary according to socioeconomic factors [Aiello,
et al. 2009, Dowd and Aiello 2009]. We will also examine stress-associated
immunosenescence as indicated by average leukocyte telomere length and stress
biomarkers [Epel, et al. 2004, Parks, et al. 2009], which along with viral antibodies may
be related to a variety of chronic disease outcomes. Such tests may be performed using
baseline samples or, for the Biomedical Surveillance Sub-cohort, samples collected at
subsequent visits may be utilized.
For a subset of subjects representing high and low exposures to agents known or
suspected to be nephrotoxic, including volatile organic compounds and heavy metals,
and also unexposed subjects, we will examine urinary markers of kidney injury, including
N-acetyl-beta-D-glucosaminidase (NAGs), beta-2 microglobulin, microalbuminuria,
Page 72 of 98
National Institute of Environmental Health Sciences (NIEHS)
GuLF Study - to IRB
11/3/2010
neutrophil gelatinase-associated lipocalin (NGAL), interleukin-18 (IL-18), kidney injury
molecule-1 (KIM-1), and liver-type fatty acid binding protein.
We will similarly conduct liver function tests using sera from a subset of subjects having
either high or low exposures to agents known or suspected to alter liver function,
including volatile organic compounds, PAHs, and heavy metals, and also unexposed
subjects.
For a subset of subjects representing high and low exposures to agents known or
suspected to be genotoxic, including volatile organic compounds, heavy metals, PAHs,
and hydrogen sulfide, and also unexposed subjects, we will examine results of DNA
damage assays, The specific assays will be determined, based on the current state of
the art around the time that we are ready to undertake these analyses, as described
above in section 3.11.3. They may include the comet assay and the micronucleus test.
Comet assay measures will include the tail moment, defined as the product of the
percentage of DNA in the comet tail and the tail length, and the tail intensity, defined as
the percentage of DNA in the tail. Micronucleus test measures will consist of the
frequency of micronuclei and the frequency of binucleated micronucleated cells.
During follow-up of the cohort, we will identify incident outcomes or changing severity of
those outcomes via self-reported health status in follow-up interviews, via linkage with
cancer and vital status registries, and via testing of follow-up biospecimens. Our
analyses will consider onset or changes in severity relative to both enrollment health
status and health history, as appropriate. For some subjects, such as Coast Guard
members, we may be able to obtain additional information from electronic medical
records.
Continuous outcome measures such as FEV1/FVC will be treated as continuous and/or
categorized according to appropriate cutpoints in statistical analyses. They will be logtransformed as needed.
Initial analyses will be largely descriptive, including examination of distributions of jobs,
exposures, demographic and lifestyle factors, health history, and recent health outcomes
at enrollment. We will quantify and examine patterns of missing data and outliers. We
will perform data cleaning as appropriate. To the extent possible, we will explore
potential bias in subject selection and reporting.
We will next conduct cross-sectional analyses, consisting primarily of comparisons of
prevalence or extent of a given outcome by clean-up task or estimated exposure to a
given factor (from the JEM). These will be performed using least squares regression for
continuous outcomes or logistic regression for dichotomous outcomes, adjusted for
confounders as appropriate. We will explore possible modifiers of effect such as race,
sex, baseline health characteristics, lifestyle factors, and access to health care by also
conducting stratified analyses by these factors, as appropriate and as numbers permit.
When follow-up data become available, we will also be able to perform prospective
analyses linking clean-up activities/exposures to incident outcomes using Cox
proportional hazards regression. We will use logistic regression for nested case-control
analyses. Extent of change of outcomes will be assessed using least squares
regression. Confounding and effect modification will be addressed as described above.
Clinical protocols for a number of outcomes, including respiratory and neurologic effects,
will be developed and carried out in collaboration with local university partners identified
through a request for proposals (RFP). Therefore, analysis of these outcomes will be
addressed in a later protocol.
Page 73 of 98
National Institute of Environmental Health Sciences (NIEHS)
GuLF Study - to IRB
11/3/2010
8
Training, Quality Control, and Quality Assurance
8.1
Staff Recruitment and Enrollment Process
8.1.1
Telephone Interviewers
Locating and screening tasks will be conducted by approximately 50 trained telephone
interviewers working part time over different shifts. Interview staff will be given training
on good practices in interviewing—locating, gaining cooperation, overcoming barriers to
participation and correctly coding outcomes, and American Association for Public
Opinion Research (AAPOR) code of ethics which includes training on confidentiality and
non-disclosure, and other training in human subjects research. Trainees also receive
interactive cultural competence training. Administrative aspects of the computer-assisted
telephone interviewing (CATI) system and time record keeping are practiced.
The training program will be tailored to meet the specific needs of this study, including a
discussion of successful approaches for conducting interviews with people facing the
continuing life disruptions following Hurricanes Rita/Katrina and now the BP oil spill.
Interviewers will learn the best methods for refusal avoidance and conversion
techniques, and will receive extensive hands-on training with the Computer-Assisted
Interviewing (CAI) questionnaire. They will also learn the most effective ways to explain
the importance of participating in the study, and how to best answer questions about the
study’s purpose and process. Interviewers will be trained to make respondents aware of
other sources of information about the study, such as the study website. Training will
include sensitivity exercises designed to ensure that interviewers show unconditional
positive regard for participants. Interviewers will be trained to use positive rather than
patronizing language, use structured probes, check for respondent fatigue, and offer
encouragement without leading the respondent to respond in a specific way. The training
will focus on the three general challenges in interviews—communication, stamina, and
cognitive challenges—and specific recommendations for overcoming these challenges.
Each training topic will be reinforced with group discussion and interaction, trainer
demonstrations, and classroom practice and discussion. Role-playing and practice will
be used.
Confidentiality safeguards will be maintained throughout the data collection period. All
study personnel will be trained in their responsibilities under HIPAA to protect the
confidentiality and privacy of each participant’s personal health information. The training
will also describe the civil and criminal penalties if an interviewer violates a participant’s
right to privacy. All interviewing staff will be required to sign a Confidentiality Agreement
and an Affidavit of Nondisclosure as part of their training on protecting the privacy and
rights of respondents. Training will also include identification of social and mental health
issues in need of intervention and appropriate protocols for seeking outside support or
making community referrals.
Individual Telephone Interviewer performance will be monitored by Telephone
Supervisors using Computer Assisted Telephone Interviewing (CATI) and telephony
technology that permits silent monitoring of voice together with key-stroke by key-stroke
monitoring within the CATI instrument. The supervisors will systematically select
interviewers for monitoring and will formally evaluate performance providing praise or
corrective feedback, as appropriate. Evaluations are maintained in individual
Page 74 of 98
National Institute of Environmental Health Sciences (NIEHS)
GuLF Study - to IRB
11/3/2010
interviewer performance files and are regularly reviewed by the call center manager for
purposes of performance recognition, performance improvement coaching or dismissal.
The call center manager will frequently review recruitment and enrollment statistics in
the study database to ensure that participants are being enrolled consistent with the
distribution of the various study populations of interest in the selected sampling frame.
Weekly reports will summarize recruitment statistics which also will be discussed at
weekly project meetings. If it appears that too many or not enough of given subgroups
are being enrolled, study staff, investigators will meet SRA’s statistical and
programming staff to consider adjusting the calling cue to rebalance the recruitment calls
as appropriate. SRA’s Director of Survey Activities will closely monitor day-to-day call
center activities to ensure that call center staff is closely adhering to recruitment and
enrollment quality and productivity goals.
8.1.2
Home Visit Personnel
Home visits will be conducted by as many as 60-80 home visit agents (HVA) and 8-12
Regional Managers (RM). In this study, it will be important to retain HVAs with particular
aptitude, skill, and sensitivity in working with persons having experienced natural
disaster, life disruption, and probable dislocation.
Training for home visit data collection will start with a Regional Manager training
sessions that precede the HVA training. This RM training will focus on data collection
procedures, management of HVAs, the importance of data quality and cost containment,
and reporting. Following the RM training, training sessions will be held for the HVAs. The
field data collection trainings will be conducted both in person and over the internet. The
training sessions will consist of large-group exercises, demonstrations, round-robin and
dyad mock interviews, and question-and-answer sessions. HVAs will be trained and
tested on their mastery of the ethics and protection of human subjects in research,
establishing rapport, setting visit dates, obtaining informed consent, and administering
questionnaires. They will also be trained in the clinical portion of the study protocol and
tested specifically on the clinical protocol components to include setup, preparation and
shipping of biological samples. The training will also include practice session. The HVA
will practice the complete baseline protocol under the close supervision of the field
supervisors and trainers.
Periodically, RMs will accompany the HVA for follow-up assessment of performance.
Deviations from protocol evidenced in the receipt of data or specimens will be reported
to project management staff at SRA and the RM will follow-up with corrective training or
dismissal of the HVA as appropriate. The investigators and the NIEHS IRB will be
informed of all deviations.
Field activities will be closely monitored by SRA’s Director of Laboratory Services and
the Home Visit Coordinator who will monitor field operations and the Storage
Coordinator, who will monitor activities of the central processing laboratory, the testing
laboratory and archiving of specimens at the NIEHS Repository, managed by
Experimental Pathology Laboratories.
The Home Visit Coordinator will monitor home visit activities to ensure that these are
proceeding according to schedule. The Home Visit Coordinator will interact with the
RMs on a frequent/near daily basis to ensure that HVAs are receiving home visit
assignments and that they are receiving the necessary home visit supplies to complete
the visits in a timely manner. The Storage Coordinator will also ensure that HVAs are
Page 75 of 98
National Institute of Environmental Health Sciences (NIEHS)
GuLF Study - to IRB
11/3/2010
processing and shipping the collected study specimens immediately upon completion of
the visits and closely monitor arrival of collected study specimens at the CPL and will
ensure that these are being processed according to the study protocol. The Storage
Coordinator will also ensure that processed samples are being routinely transferred to
the NIEHS Repository under appropriate transport conditions. The Storage Coordinator
will also work closely with the Repository Staff to ensure that study samples are entered
into storage and that final storage locations (e.g., freezer, shelf/rack/box/column/row) are
sent to SRA for import into the study database.
8.1.3
Monitoring of Recruitment and Field Activities
Recruitment, retention and field operations are a challenge in most studies. SRA will
generate routine reports for the investigators that summarize recruitment, enrollment,
and retention rates, as well as outcomes of operation processes. Frequent reviews of
study status reports will allow the investigators and SRA to identify problems early and
make adjustment to keep enrollment and study operations on track. Examples of the
types of reports that SRA will generate include:
Call center reports that monitor telephone questionnaire outcomes, such as call
rescheduling (soft refusal) rates, duration of interviews, and points of break-off for
incomplete interviews.
Enrollment reports that present contact and participation rates for the telephone
enrollment questionnaire both overall and for different demographic subgroups.
Home visit reports that monitor outcomes of field activities, such time required to
schedule appointments, no-show and reschedule rates, missed procedure rates,
and duration of visits.
8.1.4
Personal Safety
During our training sessions for HVAs, we will emphasize the importance of safety
during in-home visits and awareness of local laws and regulations. For example, we will
instruct the HVAs to stay on main thoroughfares and well-lighted routes as much as
possible when traveling and give them the option of terminating a visit if there are safety
concerns. The police and sheriff’s departments will be informed of the project’s
presence in their county/parish. Each HVA will be issued a cell phone that they can use
to make emergency calls during travel to or from subjects’ homes as well as during the
visit. SRA is also making provisions for HVAs to request an escort for home visits in
neighborhoods where there may be safety concerns or for home visits during evening
hours or to remote locations.
Regional managers will—if not already familiar with their assigned area of operation—
consult with local law enforcement officials to determine what, if any, “trouble spots” may
exist in their area. When participants who live in these areas are scheduled for home
visits, the Regional Managers will share this information with the HVAs so that escorting
arrangements can be made and extra travel precautions can be made as necessary. In
addition, we will work with local health departments and other community groups to find
alternate locations in which to conduct interviews if safety is a major concern.
After training, each HVA will have a fundamental and operational knowledge of the
following principles:
Page 76 of 98
National Institute of Environmental Health Sciences (NIEHS)
8.1.5
GuLF Study - to IRB
11/3/2010
Come prepared for the neighborhood, based on the informal information
gathered from the scheduling call, a preview of the neighborhood, and
information from your supervisor,
Always be aware of your environment
Leave the house and reschedule if you think it is necessary for your safety,
When concerned about an area or participant, keep your supervisor aware of
when you are to arrive and when you expect to leave,
Call your supervisor when you do leave.
Emergency telephone numbers are programmed for speed dial into each HVA’s
cell phone
Mandatory Reporting Requirements
In addition to personal safety training, the HVAs will be trained to detect signs of turmoil
and abuse in the homes. Should a HVA witness signs of child, spouse or elder abuse
while in the participant’s home, the HVA will immediately generate an incident report and
transmit this to their Regional Manager and to the Coordinating Center. The
Coordinating Center will immediately contact the NIEHS Project Officer and after
appropriate consultation will report the situation to local authorities in accordance with
applicable laws.
8.1.6
Identifying and Dealing with Mental Health Issues
It is possible that HVAs (and telephone interviewers) may encounter situations in which
a participant may be emotionally upset by recalling aspects of the oil spill that affected
them personally. We will train HVAs on how to identify and deal objectively with subjects
who may be anxious, stressed, or depressed because of their circumstances. HVAs will
be trained to remain neutral and focused and to present all survey questions in a
consistent manner so that response bias is not introduced. In most situations,
empathetic and respectful listening and an understanding tone will help to calm the
participant and allow him or her to proceed with the interview. However, we will train
HVAs on several specific steps they can follow if a participant becomes distressed, such
as:
Reminding participants that their answers are confidential,
Providing positive, neutral feedback, such as “Thank you; I understand; We
appreciate your participation in this important study,” etc.
Acknowledging a participant’s hesitancy in answering a question, such as, “I
understand that this may be difficult for you, so please take your time”, and
Reminding participants that it is okay to skip any question he or she does not feel
comfortable answering.
In circumstances when an HVA or interviewer identifies a participant that may be
experiencing mental health issues—or more significantly suicidal ideation—we will
provide them with contact information for local, regional, state and national mental health
resources that are available to help them deal with their issues. If the participant
appears to be at significant imminent risk for self-injury (e.g., suicide), the HVA or
interviewer will contact local emergency officials by calling 911 or other intervention
hotlines as appropriate. As in the previous section, the HVA will immediately fill out an
incident report and telephone their RM and Coordinating Center to inform them of this
Page 77 of 98
National Institute of Environmental Health Sciences (NIEHS)
GuLF Study - to IRB
11/3/2010
action. The Project Manager will then immediately notify the NIEHS Project Officer of
what transpired.
8.1.7
Reporting Individual Results to the Participants
HVAs will be trained to provide participants with appropriate and standard feedback
about their individual blood pressure and BMI measurements, preliminary pulmonary
function test observations, and urine glucose results before departing the participant’s
home. HVAs will be trained to record all observations and in-home test results in the
data management application as well as on participant Test Result Forms that provide
the participant with a basic interpretation of the various measurements and test results.
HVAs will also be trained to strictly follow scripts when conveying results to participants.
The participant Test Result Forms will include scripts that provide recommended actions
for participants to take depending on the measured values for each test. For each test
result, we provide standard recommendations depending on the result value (see also
section 2.11 and the Test Results Forms in Appendix X). “Normal” results or expected
test values will be relayed as such and the participant will be told that no additional
actions are necessary. If test results or measures are slightly or moderately elevated
or abnormal, the HVA will instruct the participant that he or she should consult with their
healthcare provider at an interval defined by the test in question to discuss the
significance of these results. If test results or measures are markedly elevated or
abnormal, the HVA will instruct the participant to seek medical evaluation as soon as
possible. HVAs will be trained not to offer any medical advice or to discuss study results
in more detail or to engage in general discussions with the participant about any healthrelated issues.
HVAs will ask the participant if they would like information on healthcare facilities in their
local area that can provide medical treatment or care. If they receive an affirmative
response, the HVA will use the GuLF Study Resource Guide to provide a list of local
providers. If the participant declines, the HVA will re-emphasize to the participant that
there are local providers available and that they can contact the study helpline at any
point to receive information about resources that are available to them.
The HVA will note in the CAPI system which resource contacts were provided to the
participant as well as what follow-up recommendations were given. When these data
are uploaded to the network, the system will auto-generate reports of participants who
should receive follow-up calls to assess whether the participant contacted their
healthcare provider or one of the healthcare/mental health resources provided by the
HVA (or interviewer).
Once specimens from participants who are members of the Biomedical Surveillance
Sub-cohort have been transported to and processed by the Central Processing
Laboratory, additional test results such as the complete blood count with white blood cell
differential and a complete urinalysis will be entered into the study database.
Additionally, pulmonologist interpretations of the pulmonary function test results will also
be captured in the study database. The data management system will then generate a
test result letter and an enclosure with a complete summary of all test findings along with
their interpretations and recommendations for follow-up that will be sent to the
participant.
Page 78 of 98
National Institute of Environmental Health Sciences (NIEHS)
8.2
8.2.1
GuLF Study - to IRB
11/3/2010
Data Quality Control
Data Collection Quality Control
At the core of our data collection efforts, we will use a commercially available survey
platform. The platform has the following features:
A flexible interface for loading complex sample data initiates and drives study
recruitment activities.
A Computer-Assisted Telephone Interview (CATI) component that guides project
personnel through the interview process to determine eligibility. This component
provides complex branching and algorithm support to collect data, make eligibility
determinations, schedule future contact and direct the management of the new recruit’s
case to regional field supervisors. The CATI system allows data managers to monitor the
recruitment process and all call center operations and success metrics. All CATI data
are updated and managed in the central data management system. A notification system
text-messages all receiving field representatives and managers when new cases are
assigned to them.
A CAPI component running on field laptop computers to administer study questionnaires
and capture clinical evaluations. The CAPI component guides field personnel through a
questionnaire that has complex and conditional branching as well as rostering. The CAPI
system provides real-time data validation, ensuring data are valid when captured and the
immediate correction of data after an error is detected.
A central management tool ensures that all CAPI and CATI data are collected into a
single repository and manages the aggregation of laptop interview data. Field
representatives connect to the communications portal (described below) using secure
internet technology, and automatically upload collected interview data and download
preparatory data for forthcoming interviews. CATI user data are managed via the same
software tool that reads and writes data directly to the database.
8.2.2
Data Storage
All study data are housed in a single SQL Server data repository stored in the secure
data center. This single database ensures that all system users are accessing the same
database; allows for greater control via role-based access privileges; provides a robust
architecture to support backup, security, and disaster recovery; and provides the
flexibility needed to change the data input mechanisms that could change during a
potentially very long study.
8.2.3
Data Management & Communications
The communications portal provides a single access point for all study data, reports,
status updates and communications. The communications portal provides the ability to
record, track, and analyze information associated with all types of case management
activities such as scheduling, field interviews, tracking, and data acquisition. Project field
personnel and other authorized project personnel connect to the communications portal
over the Internet, go through an authorization process to establish an SSL connection,
and have access to a variety of functions that support their work. These functions
include the ability to:
Page 79 of 98
National Institute of Environmental Health Sciences (NIEHS)
GuLF Study - to IRB
11/3/2010
Upload and download interview data
Update interview schedules; view upcoming workloads for self or field staff (for
supervisors)
View data completeness reports including status of lab data
Receive updates from project management including updated modules, with training
provided
Transmit laboratory data, receive validations
Report and track errors or technical support needs and follow them to closure
Receive warnings about overdue lab data transfers
Update participant profile information if within user rights
Keep track of project personnel; review training completeness reports and training
records
Monitor call center performance
Field representatives or managers connect to the Data Management System (DMS)
using laptops with real-time, whole-disk encryption. Data will be transferred from the
laptop to the DMS over the Internet or using smart phone tethering technology to gain
Internet access. The DMS is integrated with email, enabling key events to trigger emails
accessible via smart phones, ensuring that our distributed workforce is as current with
information as possible. Regular data transmissions are required of all field personnel
and phone email messaging prompt field staff to establish a data upload session if
overdue.
The communication portal is key to the success of this project as it provides the most
timely, accurate information and delivers it to project staff in real-time. For example, it is
crucial that supervisors monitor recruitment and enrollment trends, and compare these
results against various call center operations to improve overall recruitment success
rates. Furthermore, enrollment success measures are compared based on time of day,
call center operators, source of telephone number, and ordinal number of call attempts
in order to identify trends that suggest necessary modifications.
8.3
8.3.1
Laboratory Procedures
Laboratory Data Quality Control
The study laboratories that will be selected to analyze the study specimens will be
evaluated in part based upon their existing performance measures to assure the quality
of their testing results. This includes (1) internal and external quality control and
proficiency testing programs, (2) testing methodologies vis à vis industry standards such
as those published by the Clinical Laboratory Standard Institute (CLSI) and the
American Industrial Hygiene Association (AIHA), (3) assay standardization to ensure the
desired analytical range and sensitivity/specificity, and (4) methodology validation and
analytical instrument performance using CLSI standard GP-31A and others, and preand post-analytical processes such as specimen receipt and accessioning, sample
Page 80 of 98
National Institute of Environmental Health Sciences (NIEHS)
GuLF Study - to IRB
11/3/2010
aliquoting and batching, treatment of out-of-range results, reporting, and electronic data
transfer.
A continuing performance review on both external and internal quality control programs
will be conducted prior to commencing study data collection. Once home visits have
begun and biospecimens and environmental specimens are submitted for analyses, test
reproducibility and accuracy will be monitored as follows:
Assay Variability/Reproducibility: Intra-assay (measurement) variability will be
assessed through replicate assays conducted on the same day and in the same run.
Inter-assay variability will be assessed through replicate assays conducted on
different days in different runs.
Testing Accuracy: Assessing the accuracy of test results presumes that there are
available “gold standards” for each analyte of interest. While it is possible to
quantitatively determine the amount of some analytes present (generally chemical
compounds such as cotinine, lead, BFRs, and phthalates), definitively quantifying
biological analytes such as IgE allergens, endotoxins, mold, and fungi, or volatile
analytes such as formaldehyde and VOCs is more problematic and assay
dependent. Biospecimen controls, environmental controls, and split specimens will
be implemented for this purpose.
Laboratory testing quality will also be monitored by requiring submission of regular QC
results as well as periodic proficiency testing program results. Modifications to testing
procedures or sample processing/ extraction procedures will be avoided or minimized to
the extent possible.
8.3.2
Quality Control Specimen Collection
To preserve valuable study subject materials, we will collect biospecimens and
environmental samples from up to 200 randomly selected anonymous donors to use for
quality control. These will be used to create samples that can be inserted blindly for
quality control when laboratories process or analyze GuLF Study samples, to assess
drift over time in laboratory analyses, and to provide a sample source for assay
development and testing. These volunteers will be selected to be roughly similar to the
clean-up worker population. Each person will provide blood, urine, saliva, hair and nail
clippings, and household dust samples. Blood will be stored as serum, plasma, and
blood clots in cryovials in vapor phase liquid nitrogen. Urine will be stored in cryovials in
vapor phase liquid nitrogen. Dust wipes and hair samples will be stored at -20°C. Toenail
samples will be stored with desiccant under controlled ambient temperature and
humidity.
8.4
Run-in Period
Study personnel, procedures and forms will need to be tested in order to determine
whether planned data collection efforts will yield valid and reliable results in the most
time and cost efficient manner. We plan to conduct a 4-5 week run-in period of the study
in one geographic location within the study area. We aim to recruit N~500 participants
during the run-in period and schedule as many in-home visits as possible during this
time. This will establish a vanguard group of participants to allow us to test the
questionnaires and, as the participants move through the phases of the study, the
Page 81 of 98
National Institute of Environmental Health Sciences (NIEHS)
GuLF Study - to IRB
11/3/2010
protocols to ensure that the GuLF Study data collection efforts will work as planned. We
will evaluate the data from the field as it becomes available and any necessary
alterations in the study protocol that will need to be made can be identified and
adjudicated accordingly based on the results of this vanguard group. The IRB will be
notified of any necessary changes to the protocol.
9
Human Subjects Protections
9.1
Institutional Review Board
The investigator will submit the protocol, informed consent form, questionnaires,
proposed recruitment materials, and other materials for participants to the NIEHS IRB for
review and approval. Subjects will not be enrolled until the submission has been
approved in writing by the IRB chair. Once the protocol is approved, the principal
investigator will be responsible for obtaining IRB approval during annual Continuing
Review for the duration of the study.
The principal investigator will submit and obtain approval from the IRB for all
amendments to the protocol, informed consent form, and other study documentation
referenced above. Amendments will not be implemented without prior IRB approval,
except where necessary to eliminate immediate hazards to participants. The principal
investigator will report adverse events, protocol deviations, inadvertent loss or disclosure
of data, and loss of samples in accordance with IRB policies.
9.2
Informed Consent Process
Informed consent is an ongoing, interactive process that is initiated when the discussion
regarding study participation begins and continues throughout the study. The consent
process will begin with a lead letter and study brochure that provides an overview of the
study and what it means to participate. During the telephone enrollment call, recruiters
will explain the reason for the call, reference the lead letter and brochure that were sent
by mail in advance of the call, introduce the study, and seek verbal consent for the initial
screening and enrollment process. Participants will be informed that they will receive an
annual Newsletter for the duration of the study and be asked to provide periodic contact
information updates. The elements of passive follow-up via linkage with Cancer
Registries, Vital Statistics and other data sources will be described and verbal consent
will be obtained. They will also be informed about data sharing policies and that they
may be contacted for potential participation in related studies but that they would have
an opportunity to consent or not consent at that time.
Those who are eligible for participation in the Active Follow-up Sub-cohort will receive
additional information about the study and will be invited to schedule a home visit. Field
staff will obtain written informed consent from participants prior to conducting any study
activities during the home visit. In order to ensure that participants make an informed
decision about enrollment, field staff will review the study’s purpose, procedures, risks,
and benefits, as well as the rights of research participants. Explicit consent will be
sought for sharing individual-level data with qualified researchers committing to maintain
participant confidentiality and comply with their consent provisions, similar to NIH
policies for data sharing in genome-wide association studies
(http://grants.nih.gov/grants/gwas/).
Page 82 of 98
National Institute of Environmental Health Sciences (NIEHS)
GuLF Study - to IRB
11/3/2010
Field staff will allow the participant ample time to review the consent, ask questions, and
obtain clarifications regarding the study prior to agreeing to enrollment. After voluntarily
agreeing to take part in the study, participants will be asked to sign and date a current
IRB-approved informed consent form. Field staff will return the signed consent to SRA
for storage in the central study file. A copy of the consent form will be provided to the
subject along with a summary of the key points in the consent document and a study
FAQ document – a series of answers to questions participants may have about aspects
of the study.
The consent form will contain contact information (i.e., toll-free phone number) for study
staff that will be available to answer questions that may arise after the visit. Questions
about study participation will also be addressed at the time of follow-up interviews.
Passively followed participants will receive an enrollment packet after the enrollment call
is completed. The packet will contain information that describes the study and provides
contact information for study staff, including the toll-free study phone number and
address for the study website. They will receive a description of what they agreed to
during the telephone call and will be provided with information on how to withdraw from
the study if they have changed their mind about long-term passive participation.
All participants will receive an annual newsletter that contains updates about study
progress and findings (see Section 3.L.ii – Newsletters).
9.3
Participant Confidentiality
All study personnel will be required to complete on-line training in the protection of
human research subjects. The investigators and study staff will strictly maintain
participant confidentiality. This confidentiality will be extended to cover questionnaire
data, clinical assessments, biological samples, and environmental samples.
All study-related information will be stored securely. All study datasets, laboratory
specimens, and administrative forms will be identified by a coded number in order to
maintain participant confidentiality. All records that contain names or other personal
identifiers will be stored separately from study records identified by code number. All
databases will be secured behind firewalls with password-protected access systems.
Worksheets, lists, logbooks, appointment books, and any other documents that link
participant ID numbers to other identifying information will be stored in a separate,
locked file in an area with limited access.
A Federal Certificate of Confidentiality will be obtained for this study. The Certificate will
help protect against disclosures of study-related information by Federal, State or local
civil, criminal, administrative, legislative, or other proceedings, although it will not
guarantee that data cannot be released. Participants will be informed about the
certificate during the informed consent process.
9.4
Study Discontinuation
Participants may voluntarily withdraw from the study for any reason at any time.
Participants will be informed that unless explicit written instructions are received,
investigators will continue to use data and samples collected up to the point of
withdrawal although no new information will be collected from them. Study staff will
effectively destroy all known remaining biologic and environmental samples by
anonymizing the samples using a newly assigned ID number and report what was done
Page 83 of 98
National Institute of Environmental Health Sciences (NIEHS)
GuLF Study - to IRB
11/3/2010
to both the subject and to the IRB. This decision will not affect the subject’s participation
in this protocol or any other protocols at NIH. Anonymizing the samples will effectively
terminate any association the samples have with the study participant, fulfilling their
request, while simultaneously providing samples that can be used for laboratory QA/QC
procedures. However, should the subject specifically request it, we will physically
destroy all remaining samples.
Study staff will seek feedback from the participant to determine reasons for
discontinuation and to identify any barriers that can be addressed to keep the participant
in the study. The reasons for all discontinuations will be recorded in the data collection
system and routinely monitored by the investigators. Common barriers to ongoing
participation may be addressed by changes in retention strategies or study design.
10
Data Handling and Record Keeping
10.1 Data Capture Methods
The core of the data capture system will rely on an industry standard field data collection
system, using standard technologies. The system platform must allow for:
A flexible interface for loading complex sample data initiates and drives study
recruitment activities.
A Computer-Assisted Telephone Interview (CATI) component that guides project
personnel through the interview process to determine eligibility. This component
provides complex branching and algorithm support to collect data, make eligibility
determinations, schedule future contact and direct the management of the new
recruit’s case to regional field supervisors. The CATI system allows data managers
to monitor the recruitment process and all call center operations and success
metrics. All CATI data are updated and managed in the central data management
system. A notification system alerts all receiving field representatives and managers
when new cases are assigned to them.
A Computer-Assisted Personal Interview (CAPI) component running on field laptop
computers to administer study questionnaires and capture clinical evaluations. The
CAPI component guides field personnel through a questionnaire that has complex
and conditional branching as well as rostering. The CAPI system provides real-time
data validation, ensuring data are valid when captured and the immediate correction
of data after an error is detected. SRA will prepare all CAPI systems, ship them to
kickoff training, train personnel to use the system, and support the laptop PCs and
CAPI applications via a toll-free and email helpdesk function.
A central management tool that ensures that all CAPI and CATI data are collected
into a single repository. The centralized data management and aggregation tool will
manage the matriculation of data from field interview data platforms to the
centralized data repository. Field representatives will connect to the communications
portal (described below) using internet SSL technology, and automatically upload
collected interview data and download preparatory data for forthcoming interviews.
Page 84 of 98
National Institute of Environmental Health Sciences (NIEHS)
GuLF Study - to IRB
11/3/2010
10.2 Data Management Responsibilities
The captured data will be stored in a comprehensive data management system (DMS)
that centralizes study information into an integrated solution. From the time that
participants become part of the potential sample to the time they are complete, all
project data are managed and tracked in the DMS. Project personnel will have an
appropriate “view” into the data using role-based access control. The DMS will support
the full scope of study data management activities, including management of study
sampling; collection of field and laboratory data; management of participant activities
(case management); reporting of all data collection efforts and status; and preparation of
analysis datasets.
The heart of the DMS will be the database server. The database server will be
configured for 24/7 operation, and provide the capability of offsite backups.
The DMS also includes a communications portal which provides a single access point
for all study data, reports, status updates and communications. The communications
portal serves as the gateway between users and the data repository. The portal enables
the ability to record, track, and analyze information associated with all types of case
management activities such as scheduling, field interviews, tracking, and data
acquisition. Project field personnel and other authorized project personnel connect to the
communications portal over the Internet, go through an authorization process to
establish an SSL connection, and have access to a variety of functions that support their
work. These functions include the ability to:
Upload and download interview data
Update interview schedules; view upcoming workloads for self or field staff (for
supervisors)
View data completeness reports including status of lab data and abstracted medical
records
Receive updates from project management including updated modules, with training
provided
Transmit laboratory data, receive validations
Report and track errors or technical support needs and follow them to closure
Receive warnings about overdue lab data transfers
Update participant profile information if within user rights
Track project personnel; review training completeness reports and training records
Monitor call center performance
Field representatives or managers connect to the DMS using laptops over the Internet or
using smart phone tethering technology to gain Internet access. The DMS is integrated
with email, enabling key events to trigger emails accessible via smart phones, ensuring
that our distributed workforce is as current with information as possible. Regular data
transmissions are required of all field personnel, and field staff are prompted to establish
a data upload session if overdue.
Page 85 of 98
National Institute of Environmental Health Sciences (NIEHS)
GuLF Study - to IRB
11/3/2010
The communication portal is key to the success of this project as it provides the most
timely, accurate information and delivers it to project staff in real-time. For example, it is
crucial that supervisors monitor recruitment and enrollment trends, and compare these
results against various call center operations to improve overall recruitment success
rates. Furthermore, enrollment success measures are compared based on time of day,
call center operators, source of telephone number, and ordinal number of call attempts
in order to identify trends that suggest necessary modifications.
10.3 Data Access and Sharing
Given the public health importance of research on the health effects of the Deepwater
Horizon disaster and its aftermath, results from the GuLF Study will be made available
for research use by any interested and qualified investigator or organization, within the
limits of providing appropriate protection of research participants and compliance with
their informed consent. Policies for data access will build on NIH established policies for
controlled access to individual-level data in genome-wide association studies, as
described at http://grants.nih.gov/grants/gwas/ and open-access data sharing policies
developed for other NIH sponsored longitudinal studies. Researchers interested in
obtaining controlled-access GuLF data will agree to keep the data secure, use the data
only for the approved research purposes, and not to attempt to identify individual study
participants. In recognition of the rights and intellectual contributions of the GuLF
investigators to publish data within a reasonable timeframe, outside researchers will also
agree to observe a twelve month moratorium on submitting abstracts and publications
using the data. Data and documentation will be made publicly available soon after
collection along with information on all data that have been or will be collected. Typically
(e.g. as currently practiced on dbGaP, protocols, descriptions of data and files, and
counts of responses are available online. Summary descriptive tables may also be
posted. In order to prevent accidental disclosure of individual participant data, deidentified datasets are separately provided to qualified requesters; individual level data
are not posted online. Access to the data will be granted by an NIH Data Access
Committee which will ensure that these conditions are met initially and monitor
subsequent compliance during the study.
10.3.1
Access to Biospecimens and Use of Cohort for Add-on Studies
Additionally, other investigators (both at NIH and outside) may wish to study the stored
biologic and/or environmental samples or propose add-on studies that generate new
data and/or involve direct participant contact. In that case, NIEHS IRB approval must be
sought prior to any sharing of samples. Any clinical information shared about the
sample would similarly require prior NIEHS IRB approval. Procedures and guidelines for
proposing new assays or add-on studies will be established and posted. An
independent committee will be established to review proposals for scientific merit,
feasibility, and impact on the study cohort.
10.4 Study Records Retention
All study records will be retained indefinitely. Study records that will be retained include
IRB approvals and correspondence, signed informed consent forms, tracking logs,
contact information update forms, and other study documentation that may be developed
Page 86 of 98
National Institute of Environmental Health Sciences (NIEHS)
GuLF Study - to IRB
11/3/2010
during the course of the study. To protect against accidental or premature destruction of
these documents, the records will be maintained in a secure, locked storage areas that
are only accessible to study staff.
All study data will be housed in a single data repository. This single database ensures
that all system users are accessing the same database; allows for greater control via
role-based access privileges; provides a robust architecture to support backup, security,
and disaster recovery; and provides the flexibility needed to change the data input
mechanisms that could change during a potentially long study.
Any loss or unanticipated destruction of samples or data (for example, due to freezer
malfunction) that meets the NIH Intramural Protocol Violation definition or results in a
violation that compromises the scientific integrity of the data collected for the study; will
be reported to the NIEHS IRB.
At the completion of the protocol (termination), samples and data will either be
destroyed, or after IRB approval, transferred to another existing protocol where they will
be maintained in a repository as applicable.
Page 87 of 98
National Institute of Environmental Health Sciences (NIEHS)
Appendix A:
GuLF Study - to IRB
11/3/2010
Scientific References
Agency for Toxic Substances and Disease Registry (ATSDR) 1995. Toxicological profile
for Polycyclic Aromatic Hydrocarbons (PAHs) Atlanta, GA: U.S. Department of Health
and Human Services, Public Health Service.
Agency for Toxic Substances and Disease Registry (ATSDR) 1999. Toxicological profile
for Total Petroleum Hydrocarbons (TPH) Atlanta, GA: U.S. Department of Health and
Human Services, Public Health Service.
Agency for Toxic Substances and Disease Registry (ATSDR) 2004. Toxicological profile
for Copper. Atlanta, GA: U.S. Department of Health and Human Services, Public Health
Service
Agency for Toxic Substances and Disease Registry (ATSDR) 2005. Toxicological profile
for Nickel. Atlanta, GA: U.S. Department of Health and Human Services, Public Health
Service
Agency for Toxic Substances and Disease Registry (ATSDR) 2006. Toxicological profile
for Hydrogen Sulfide Atlanta, GA: U.S. Department of Health and Human Services,
Public Health Service.
Agency for Toxic Substances and Disease Registry (ATSDR) 2007a. Toxicological
profile for Arsenic. Atlanta, GA: U.S. Department of Health and Human Services, Public
Health Service
Agency for Toxic Substances and Disease Registry (ATSDR) 2007b. Toxicological
profile for Lead. Atlanta, GA: U.S. Department of Health and Human Services, Public
Health Service
Agency for Toxic Substances and Disease Registry (ATSDR) 2008a. Toxicological
profile for Cadmium (Draft for Public Comment). Atlanta, GA: U.S. Department of Health
and Human Services, Public Health Service
Agency for Toxic Substances and Disease Registry (ATSDR) 2008b. Toxicological
profile for Chromium (Draft for Public Comment). Atlanta, GA: U.S. Department of Health
and Human Services, Public Health Service
Agency for Toxic Substances and Disease Registry (ATSDR) 2009. Toxicological profile
for Vanadium (Draft for Public Comment). Atlanta, GA: U.S. Department of Health and
Human Services, Public Health Service
Aguilera F, Mendez J, Pasaro E, Laffon B. 2010. Review on the effects of exposure to
spilled oils on human health. J Appl Toxicol 30:291-301.
Aiello AE, Diez-Roux A, Noone AM, Ranjit N, Cushman M, Tsai MY, Szklo M. 2009.
Socioeconomic and psychosocial gradients in cardiovascular pathogen burden and
immune response: the multi-ethnic study of atherosclerosis. Brain Behav Immun 23:663671.
Allen RH, Mage DT, Gondy G, Kodali A, Christensen C, Coble J, Stewart P. 2006.
Investigation of job-related pesticide exposure in the third national health and nutrition
examination survey. Arch Environ Occup Health 61: 76-86.
Arah OA, Chiba Y, Greenland S. 2008. Bias formulas for external adjustment and
sensitivity analysis of unmeasured confounders. Ann Epidemiol 18:637-646.
Page 88 of 98
National Institute of Environmental Health Sciences (NIEHS)
GuLF Study - to IRB
11/3/2010
Baan R, Grosse Y, Straif K, Secretan B, El Ghissassi F, Bouvard V, Benbrahim-Tallaa L,
Guha N, Freeman C, Galichet L, Cogliano V. 2009. A review of human carcinogens-Part F: chemical agents and related occupations. Lancet Oncol 10:1143-1144.
Bagryantseva Y, Novotna B, Jr PR, Chvatalova I, Milcova A, Svecova V, Lnenickova Z,
Solansky I, Sram RJ. Oxidative damage to biological macromolecules in Prague bus
drivers and garagemen: impact of air pollution and genetic polymorphisms. In Press.
Toxicol Lett.
Baris D, Silverman DT, Brown LM, Swanson GM, Hayes RB, Schwartz AG, Liff JM,
Schoenberg JB, Pottern LM, Greenberg RD, Stewart PA. 2004. Occupation, pesticide
exposure and risk of multiple myeloma. Scand J Work Environ Health 30: 215-222.
Botello A, Villanueva S, Diaz G. 1997. Petroleum pollution in the Gulf of Mexico and
Caribbean Sea. Rev Environ Contam Toxicol 153: 91-118.
Buist AS, McBurnie MA, Vollmer WM, Gillespie S, Burney P, Mannino DM, Menezes
AM, Sullivan SD, Lee TA, Weiss KB, Jensen RL, Marks GB, Gulsvik A, NizankowskaMogilnicka E. 2007. International variation in the prevalence of COPD (the BOLD Study):
a population-based prevalence study. Lancet 370:741-750.
Camilli R, Reddy C, Yoerger D, Van Mooy B, Jakuba M, Kinsey J, et al. 2010. Tracking
hydrocarbon plume transport and biodegredation at Deepwater Horizon. Science.
August 19, 2010. Epub ahead of print: DOI: 10.1126/science.1195223.
Campbell D, Cox D, Crum J, Foster K, Christie P, Brewster D. 1993. Initial effects of the
grounding of the tanker Braer on health in Shetland. The Shetland Health Study Group.
BMJ 307:1251-1255.
Campbell D, Cox D, Crum J, Foster K, Riley A. 1994. Later effects of grounding of tanker
Braer on health in Shetland. BMJ 309:773-774.
Carrasco JM, Lope V, Perez-Gomez B, Aragones N, Suarez B, Lopez-Abente G,
Rodriguez-Artalejo F, Pollan M. 2006. Association between health information, use of
protective devices and occurrence of acute health problems in the Prestige oil spill
clean-up in Asturias and Cantabria (Spain): a cross-sectional study. BMC Public Health
6:1.
Chang JL, Chen G, Lampe JW, Ulrich CM. 2006. DNA damage and repair
measurements from cryopreserved lymphocytes without cell culture--a reproducible
assay for intervention studies. Environ Mol Mutagen 47:503-508.
Chang TY, Huang KH, Liu CS, Shie RH, Chao KP, Hsu WH, Bao BY. 2010. Exposure to
volatile organic compounds and kidney dysfunction in thin film transistor liquid crystal
display (TFT-LCD) workers. J Hazard Mater 178:934-940.
Chen CS, Hseu YC, Liang SH, Kuo JY, Chen SC. 2008. Assessment of genotoxicity of
methyl-tert-butyl ether, benzene, toluene, ethylbenzene, and xylene to human
lymphocytes using comet assay. J Hazard Mater 153:351-356.
Cho JY. 2008. Suppressive effect of hydroquinone, a benzene metabolite, on in vitro
inflammatory responses mediated by macrophages, monocytes, and lymphocytes.
Mediators Inflamm 2008:298010.
Chu H, Wang Z, Cole SR, Greenland S. 2006. Sensitivity analysis of misclassification: a
graphical and a Bayesian approach. Ann Epidemiol 16:834-841.
Page 89 of 98
National Institute of Environmental Health Sciences (NIEHS)
GuLF Study - to IRB
11/3/2010
Coble JB, Dosemeci M, Stewart PA, Blair A, Bowman J, Fine HA, Shapiro WR, Selker
RG, Loeffler JS, Black PM, Linet MS, Inskip PD. 2009. Occupational exposure to
magnetic fields and the risk of brain tumors. Neuro Oncol 11: 242-249.
Cole J, Beare DM, Waugh AP, Capulas E, Aldridge KE, Arlett CF, Green MH, Crum JE,
Cox D, Garner RC, Dingley KH, Martin EA, Podmore K, Heydon R, Farmer PB. 1997.
Biomonitoring of possible human exposure to environmental genotoxic chemicals:
lessons from a study following the wreck of the oil tanker Braer. Environ Mol Mutagen
30:97-111.
Do MP, Hutchinson PL, Mai KV, Vanlandingham MJ. 2009. Disparities in health care
among Vietnamese New Orleanians and the impacts of Hurricane Katrina. Res Sociol
Health Care 27:301-319.
Dowd JB, Aiello AE. 2009. Socioeconomic differentials in immune response.
Epidemiology 20:902-908.
Elci OC, Akpinar-Elci M, Blair A, Dosemeci M. 2003. Risk of laryngeal cancer by
occupational chemical exposure in Turkey. J Occup Environ Med 45: 1100-1106.
Epel ES, Blackburn EH, Lin J, Dhabhar FS, Adler NE, Morrow JD, Cawthon RM. 2004.
Accelerated telomere shortening in response to life stress. Proc Natl Acad Sci U S A
101:17312-17315.
FDA 2010. CLIA - Clinical Laboratory Improvement Amendments.
http://www.accessdata.fda.gov/scripts/cdrh/cfdocs/cfClia/Results.cfm?Analyte_Name=Ur
ine%20Qualitative%20Dipstick%20Glucose&Clia_Complexity=waived&SortColumn=DA
TE%5FEFFECTIVE%20DESC&PAGENUM=10 (Accessed Nov 3, 2010).
Fox MP, Lash TL, Greenland S. 2005. A method to automate probabilistic sensitivity
analyses of misclassified binary variables. Int J Epidemiol 34:1370-1376.
Fracasso ME, Doria D, Bartolucci GB, Carrieri M, Lovreglio P, Ballini A, Soleo L, Tranfo
G, Manno M. 2010. Low air levels of benzene: correlation between biomarkers of
exposure and genotoxic effects. Toxicol Lett 192:22-28.
Galea S, Tracy M, Norris F, Coffey SF. 2008. Financial and social circumstances and
the incidence and course of PTSD in Mississippi during the first two years after
Hurricane Katrina. J Trauma Stress 21:357-368.
Gamboa RT, Gamboa AR, Bravo AH, Ostrosky WP. 2008. Genotoxicity in child
populations exposed to polycyclic aromatic hydrocarbons (PAHs) in the air from
Tabasco, Mexico. Int J Environ Res Public Health 5:349-355.
Gillis B, Gavin IM, Arbieva Z, King ST, Jayaraman S, Prabhakar BS. 2007. Identification
of human cell responses to benzene and benzene metabolites. Genomics 90:324-333.
Glass DC, Gray CN, Jolley DJ, Gibbons C, Sim MR, Fritschi L, Adams GG, Bisby JA,
Manuell R. 2003. Leukemia risk associated with low-level benzene exposure.
Epidemiology 14:569-577.
Guralnik JM, Eisenstaedt RS, Ferrucci L, Klein HG, Woodman RC. 2004. Prevalence of
anemia in persons 65 years and older in the United States: evidence for a high rate of
unexplained anemia. Blood 104:2263-2268.
Hayes RB, Songnian Y, Dosemeci M, Linet M. 2001. Benzene and lymphohematopoietic
malignancies in humans. Am J Ind Med 40:117-126.
Page 90 of 98
National Institute of Environmental Health Sciences (NIEHS)
GuLF Study - to IRB
11/3/2010
Hazen T, Dubinsky E, DeSantis T, Andersen G, Piceno Y, Singh N, et al. 2010. Deepsea oil plume enriches indigenous oil-degrading bacteria. Science. August 24, 2010.
Epub ahead of print: DOI: 10.1126/science.1195979
Howard J. CDC Congressional Testimony; Evaluating the Health Impacts of the Gulf of
Mexico Oil Spill. June 15, 2010. Testimony to the Committee on Health, Education,
Labor and Pensions, United States Senate.
http://www.cdc.gov/washington/testimony/2010/t20100615a.htm. Accessed September
7, 2010.
Hoxha M, Dioni L, Bonzini M, Pesatori AC, Fustinoni S, Cavallo D, Carugno M, Albetti B,
Marinelli B, Schwartz J, Bertazzi PA, Baccarelli A. 2009. Association between leukocyte
telomere shortening and exposure to traffic pollution: a cross-sectional study on traffic
officers and indoor office workers. Environ Health 8:41.
IARC (International Agency for Research on Cancer). 2002. Some Traditional Herbal
Medicines, Some Mycotoxins, Naphthalene and Styrene. Lyon, France: International
Agency for Research on Cancer.
International Tanker Owners Pollution Federation Limited (ITOPF) 2009. Oil Tanker Spill
Statistics: 2009 London: International Tanker Owners Pollution Federation Limited.
Janjua NZ, Kasi PM, Nawaz H, Farooqui SZ, Khuwaja UB, Najam ul H, Jafri SN, Lutfi
SA, Kadir MM, Sathiakumar N. 2006. Acute health effects of the Tasman Spirit oil spill
on residents of Karachi, Pakistan. BMC Public Health 6:84.
Kim S, Lan Q, Waidyanatha S, Chanock S, Johnson BA, Vermeulen R, Smith MT,
Zhang L, Li G, Shen M, Yin S, Rothman N, Rappaport SM. 2007. Genetic
polymorphisms and benzene metabolism in humans exposed to a wide range of air
concentrations. Pharmacogenet Genomics 17:789-801.
King Ft, Steinmann WC. 2007. Why current medical management is failing victims of
Hurricane Katrina: a review of past successes and failures in postdisaster psychosocial
treatment. South Med J 100:991-998.
Kirkeleit J, Ulvestad E, Riise T, Bratveit M, Moen BE. 2006. Acute suppression of serum
IgM and IgA in tank workers exposed to benzene. Scand J Immunol 64:690-698.
Kirkeleit J, Riise T, Bratveit M, Moen BE. 2008. Increased risk of acute myelogenous
leukemia and multiple myeloma in a historical cohort of upstream petroleum workers
exposed to crude oil. Cancer Causes Control 19:13-23.
Kroumhout H, Loomis DP, Mihlan GJ, Peipins LA, Kleckner RC, Iriye R, Savitz DA.
1995. Assessment and grouping of occupational magnetic field exposure in five electric
utility companies. Scand J Work Environ Health 21: 43-50
Laffon B, Fraga-Iriso R, Perez-Cadahia B, Mendez J. 2006. Genotoxicity associated to
exposure to Prestige oil during autopsies and cleaning of oil-contaminated birds. Food
Chem Toxicol 44:1714-1723.
Laakkonen A, Verkasalo PK, Nevalainen A, Kauppinen T, Kyyronen P, Pukkala E. 2008.
Moulds, bacteria and cancer among Finns: an occupational cohort study. Occup
Environ Med 65: 489-493.
Lan Q, Zhang L, Li G, Vermeulen R, Weinberg RS, Dosemeci M, Rappaport SM, Shen
M, Alter BP, Wu Y, Kopp W, Waidyanatha S, Rabkin C, Guo W, Chanock S, Hayes RB,
Linet M, Kim S, Yin S, Rothman N, Smith MT. 2004. Hematotoxicity in workers exposed
to low levels of benzene. Science 306:1774-1776.
Page 91 of 98
National Institute of Environmental Health Sciences (NIEHS)
GuLF Study - to IRB
11/3/2010
Lan Q, Zhang L, Shen M, Smith MT, Li G, Vermeulen R, Rappaport SM, Forrest MS,
Hayes RB, Linet M, Dosemeci M, Alter BP, Weinberg RS, Yin S, Yeager M, Welch R,
Waidyanatha S, Kim S, Chanock S, Rothman N. 2005. Polymorphisms in cytokine and
cellular adhesion molecule genes and susceptibility to hematotoxicity among workers
exposed to benzene. Cancer Res 65:9574-9581.
Lan Q, Zhang L, Shen M, Jo WJ, Vermeulen R, Li G, Vulpe C, Lim S, Ren X, Rappaport
SM, Berndt SI, Yeager M, Yuenger J, Hayes RB, Linet M, Yin S, Chanock S, Smith MT,
Rothman N. 2009. Large-scale evaluation of candidate genes identifies associations
between DNA repair and genomic maintenance and development of benzene
hematotoxicity. Carcinogenesis 30:50-58.
Lee WJ, Baris D, Jarvholm B, Silverman DT, Bergdahl IA, Blair A. 2003. Multiple
myeloma and diesel and other occupational exposures in swedish construction workers.
Int J Cancer 107: 134-138.
Lee JY, Kim JY, Lee YG, Shin WC, Chun T, Rhee MH, Cho JY. 2007. Hydroquinone, a
reactive metabolite of benzene, reduces macrophage-mediated immune responses. Mol
Cells 23:198-206.
Lyons RA, Temple JM, Evans D, Fone DL, Palmer SR. 1999. Acute health effects of the
Sea Empress oil spill. J Epidemiol Community Health 53:306-310.
Maffei F, Hrelia P, Angelini S, Carbone F, Cantelli Forti G, Barbieri A, Sanguinetti G,
Mattioli S, Violante FS. 2005. Effects of environmental benzene: micronucleus
frequencies and haematological values in traffic police working in an urban area. Mutat
Res 583:1-11.
Menezes AM, Perez-Padilla R, Jardim JR, Muino A, Lopez MV, Valdivia G, Montes de
Oca M, Talamo C, Hallal PC, Victora CG. 2005. Chronic obstructive pulmonary disease
in five Latin American cities (the PLATINO study): a prevalence study. Lancet 366:18751881.
Meo SA, Al-Drees AM, Meo IM, Al-Saadi MM, Azeem MA. 2008. Lung function in
subjects exposed to crude oil spill into sea water. Mar Pollut Bull 56:88-94.
Meo SA, Al-Drees AM, Rasheed S, Meo IM, Al-Saadi MM, Ghani HA, Alkandari JR.
2009. Health complaints among subjects involved in oil cleanup operations during oil
spillage from a Greek tanker "Tasman Spirit". Int J Occup Med Environ Health 22:143148.
Meo SA, Al-Drees AM, Rasheed S, Meo IM, Khan MM, Al-Saadi MM, Alkandari JR.
2009. Effect of duration of exposure to polluted air environment on lung function in
subjects exposed to crude oil spill into sea water. Int J Occup Med Environ Health 22:3541.
Miller CS, Prihoda TJ. 1999. A controlled comparison of symptoms and chemical
intolerances reported by Gulf War veterans, implant recipients and persons with multiple
chemical sensitivity. Toxicol Ind Health 15:386-397.
Miller CS, Prihoda TJ. 1999. The Environmental Exposure and Sensitivity Inventory
(EESI): a standardized approach for measuring chemical intolerances for research and
clinical applications. Toxicol Ind Health 15:370-385.
Morita A, Kusaka Y, Deguchi Y, Moriuchi A, Nakanaga Y, Iki M, Miyazaki S, Kawahara
K. 1999. Acute health problems among the people engaged in the cleanup of the
Nakhodka oil spill. Environ Res 81:185-194.
Page 92 of 98
National Institute of Environmental Health Sciences (NIEHS)
GuLF Study - to IRB
11/3/2010
Norris FH, Friedman MJ, Watson PJ, Byrne CM, Diaz E, Kaniasty K. 2002. 60,000
disaster victims speak: Part I. An empirical review of the empirical literature, 1981-2001.
Psychiatry 65:207-239.
Norris FH, Vanlandingham MJ, Vu L. 2009. PTSD in Vietnamese Americans following
Hurricane Katrina: prevalence, patterns, and predictors. J Trauma Stress 22:91-101.
Novotna B, Topinka J, Solansky I, Chvatalova I, Lnenickova Z, Sram RJ. 2007. Impact of
air pollution and genotype variability on DNA damage in Prague policemen. Toxicol Lett
172:37-47.
Palinkas LA, Russell J, Downs MA, Petterson JS. 1992. Ethnic differences in stress,
coping, and depressive symptoms after the Exxon Valdez oil spill. J Nerv Ment Dis
180:287-295.
Palinkas LA, Petterson JS, Russell J, Downs MA. 1993. Community patterns of
psychiatric disorders after the Exxon Valdez oil spill. Am J Psychiatry 150:1517-1523.
Parks CG, Miller DB, McCanlies EC, Cawthon RM, Andrew ME, DeRoo LA, Sandler DP.
2009. Telomere length, current perceived stress, and urinary stress hormones in
women. Cancer Epidemiol Biomarkers Prev 18:551-560.
Peek MK, Cutchin MP, Freeman DH, Perez NA, Goodwin JS. 2008. Perceived health
change in the aftermath of a petrochemical accident: an examination of pre-accident,
within-accident, and post-accident variables. J Epidemiol Community Health 62:106-112.
Peek MK, Cutchin MP, Freeman D, Stowe RP, Goodwin JS. 2009. Environmental
hazards and stress: evidence from the Texas City Stress and Health Study. J Epidemiol
Community Health 63:792-798.
Pellegrino R, Viegi G, Brusasco V, Crapo RO, Burgos F, Casaburi R, Coates A, van der
Grinten CP, Gustafsson P, Hankinson J, Jensen R, Johnson DC, MacIntyre N, McKay R,
Miller MR, Navajas D, Pedersen OF, Wanger J. 2005. Interpretative strategies for lung
function tests. Eur Respir J 26:948-968.
Perez-Cadahia B, Laffon B, Pasaro E, Mendez J. 2006. Genetic damage induced by
accidental environmental pollutants. ScientificWorldJournal 6:1221-1237.
Perez-Cadahia B, Lafuente A, Cabaleiro T, Pasaro E, Mendez J, Laffon B. 2007. Initial
study on the effects of Prestige oil on human health. Environ Int 33:176-185.
Perez-Cadahia B, Mendez J, Pasaro E, Lafuente A, Cabaleiro T, Laffon B. 2008.
Biomonitoring of Human Exposure to Prestige Oil: Effects on DNA and Endocrine
Parameters. Environmental Health Insights 2008:83.
Richardson DB, Terschuren C, Hoffman W. 2008. Occupational risk factors for nonHodgkin's lymphoma: a population-based case-control study in Northern Germany. Am J
Ind Med 51: 258-268.
Roberts SD, Farber MO, Knox KS, Phillips GS, Bhatt NY, Mastronarde JG, Wood KL.
2006. FEV1/FVC ratio of 70% misclassifies patients with obstruction at the extremes of
age. Chest 130:200-206.
Rodriguez-Trigo G, Zock JP, Pozo-Rodriguez F, Gomez FP, Monyarch G, Bouso L, Coll
MD, Verea H, Anto JM, Fuster C, Barbera JA. 2010. Health Changes in Fishermen 2
Years After Clean-up of the Prestige Oil Spill. Ann Intern Med.
Page 93 of 98
National Institute of Environmental Health Sciences (NIEHS)
GuLF Study - to IRB
11/3/2010
Sabucedo JM, Arce C, Senra C, Seoane G, Vazquez I. 2010. Symptomatic profile and
health-related quality of life of persons affected by the Prestige catastrophe. Disasters
34:809-820.
Savitz DA, Andrews KW. 1997. Review of epidemiologic evidence on benzene and
lymphatic and hematopoietic cancers. Am J Ind Med 31:287-295.
Schnatter AR, Theriault G, Katz AM, Thompson FS, Donaleski D, Murray N. 1992. A
retrospective mortality study within operating segments of a petroleum company. Am J
Ind Med 22:209-229.
Sim MS, Jo IJ, Song HG. 2010. Acute health problems related to the operation mounted
to clean the Hebei Spirit oil spill in Taean, Korea. Mar Pollut Bull 60:51-57.
Steinmaus C, Smith AH, Jones RM, Smith MT. 2008. Meta-analysis of benzene
exposure and non-Hodgkin lymphoma: biases could mask an important association.
Occup Environ Med 65:371-378.
Suarez B, Lope V, Perez-Gomez B, Aragones N, Rodriguez-Artalejo F, Marques F, et al.
2005. Acute health problems among subjects involved in the cleanup operation
following the Prestige oil spill in Asturias and Cantabria (Spain). Environ Res 99: 413424.
Young HA, Mills PK, Riordan D, Cress R. 2004. Use of a crop and job specific exposure
matrix for estimating cumulative exposure to triazine herbicides among females in a
case-control study in the Central Valley of California. Occup Environ Med 61: 945-951.
Zhang J, Yin L, Liang G, Liu R, Pu Y. 2010. Detection of quinone oxidoreductase 1
(NQO1) single-nucleotide polymorphisms (SNP) related to benzene metabolism in
immortalized B lymphocytes from a Chinese Han population. J Toxicol Environ Health A
73:490-498.
Zijno A, Saini F, Crebelli R. 2007. Suitability of cryopreserved isolated lymphocytes for
the analysis of micronuclei with the cytokinesis-block method. Mutagenesis 22:311-315.
Zock JP, Rodriguez-Trigo G, Pozo-Rodriguez F, Barbera JA, Bouso L, Torralba Y, Anto
JM, Gomez FP, Fuster C, Verea H. 2007. Prolonged respiratory symptoms in clean-up
workers of the prestige oil spill. Am J Respir Crit Care Med 176:610-616.
Page 94 of 98
GuLF Study - to IRB
11/3/2010
National Institute of Environmental Health Sciences (NIEHS)
Appendix B:
Schedule of Procedures/Evaluations
Study Activities
Screening /
Enrollment
Consent
A, P, B
Baseline questionnaires
A, P, B
Home Visit
Year 1
Year 2
Year 3
Year 4
A, B
Biological samples
A, B
B
B
Anthropometric
measurements
A, B
B
B
Physiological
assessments
A, B
B
B
Environmental sampling
A, B
B
B
Test results report
A, B
B
B
Follow-up questionnaires
B
A, B
B
A, B
Health surveillance
B
A, P, B
B
A, P, B
Contact information
update
A, P, B
A, P, B
A, P, B
A, P, B
Newsletter
A, P, B
A, P, B
A, P, B
A, P, B
A = Active Follow-up Sub-cohort; P = Passively followed members of full cohort; B=Biomedical
Surveillance Sub-cohort
Page 95 of 98
National Institute of Environmental Health Sciences (NIEHS)
Appendix C:
GuLF Study - to IRB
11/3/2010
Lab Processing Flow Sheet/Template for
Specimen Collection
(Version 0.9)
In the attached diagrams, we show how the collected biospecimens are processed and
packaged in the field for transport to the Central Laboratory (Appendix C1); how
personnel at the central laboratory will further process the samples once they have been
received (Appendix C2); and how personnel at Environmental Pathology Laboratories
(EPL), the NIEHS Repository, will process the received samples prior to placing them
into liquid nitrogen (LN2) vapor phase (~-140° C), -80° C mechanical freezers, -20° C
walk-in freezers, or into temperature and humidity controlled ambient storage. Note that
wherever possible aliquots of the various specimen types are divided into two separate
storage locations to ensure that at least part of the sample will survive in the very
unlikely event that one storage device should fail catastrophically.
Appendix C1:
This diagram schematically illustrates processing of hair, blood, urine, toenails, and dust
samples by the home health agent (HVA) while in the study participant’s home.
Only the two red top blood collection tubes need processing in the field. After
clotting for 30 minutes, the HVA will centrifuge the samples for 10-15 minutes at
2500 x g, and removed the serum supernatant into two 5 ml aliquot tubes. The
stopper will be replaced on the red top tubes with the residual clots and these are
placed into biospecimen bag #1 along with the remaining 6 blood collection tubes
(2 lavender, 1 royal blue, 1 yellow, and one PAXgene tube). The 2 ml lavender
top tube will be placed in Biospecimen bag #2 for diagnostic testing (CBC with
WBC differential) at the central laboratory. Biospecimen Bag #1 is placed in the
foam shipper along with a frozen icepack.
The HVA will use a BD transfer straw to remove 8 ml of urine from the urine
collection cup and place it into an 8 ml urine transfer tube. The urine transfer tube
will be placed in Biospecimen Bag #3 along with the 2 ml lavender top tube. This
sample will be used for the dip stick urinalysis at the central lab. Biospecimen
Bag #2 is placed in the foam shipper.
The remaining urine sample (in the tightly re-sealed original collection cup) is
placed into Biospecimen Bag #3. Biospecimen Bag #3 is also placed in the foam
shipper. Once all three biospecimen bags are in the foam shipper along with the
frozen ice pack the lid is placed on the shipper and it is inserted into the outer
cardboard shipping box.
Hair and nail samples are sealed in labeled manila envelopes and placed on top
of the foam shipper lid in the exterior cardboard shipping box.
Dust is collected with a Swiffer™ wipe and placed in the ZipLoc™ bag, which is
also placed on top of the foam lid in the outer cardboard box.
The Cardboard shipping box is sealed and either labeled for overnight shipping via
FedEx, or the HVA can transport the box to a local Central Laboratory Patient Service
Center for further processing and shipping.
Page 96 of 98
National Institute of Environmental Health Sciences (NIEHS)
GuLF Study - to IRB
11/3/2010
Appendix C2.:
The Central Laboratory will follow the steps outlined in this appendix.
Biospecimen Bag #1: The various blood samples in Biospecimen Bag #1 will be
processed as shown.
o
Serum will be divided into two sets of five 1 ml aliquots in 1 ml cryovials.
Half of the serum aliquots will be placed in freezer storage Box A and the
other half in Box B.
o
The two EDTA (lavender top) and one ACD (yellow top) tubes will
undergo a discontinuous Percoll gradient separation to isolate the white
blood cells (buffy coat) from the plasma and red blood cells (RBC). The
EDTA and ACD plasma and RBC fractions will be aliquotted into two
different sets of 1 ml cryovials as shown. The EDTA and ADC buffy coat
pellets will be stored in separate 1 ml cryovials. The plasma, buffy and
RBC aliquots will be divided and half stored in Box A and half in Box B.
Boxes A and B will be stored at -80° C in the Central Laboratory until they
are shipped to EPL.
o
The two specialty tubes (royal blue-topped trace metals and PAXgene
mRNA) are placed in freezer storage Box C along with the two red topped
tubes with the red cell clots. Box C will be placed in a -20° C freezer until
shipped to EPL.
Biospecimen Bag #2: The samples in Biospecimen Bag #2 are sent directly to
the testing area of the laboratory for analysis. The purple-topped whole blood
specimen will be sent to the hematology section where it will undergo a complete
blood count (CBC) along with a white blood cell (WBC) differential enumeration.
The urine sample will be sent to chemistry for a dipstick urinalysis. The results of
both assays will be reported electronically to SRA.
Biospecimen Bag #3: The urine sample from Biospecimen Bag #3 will be
aliquotted into four 5 ml aliquot tubes and two tubes will be placed in Box D and
two in Box E. These samples will be stored at -80° C until shipped to EPL.
Hair, Nail and Dust Samples: The envelopes containing the hair and nail
samples will be placed in a cardboard Box G and stored at ambient temperature
until sufficient samples have accumulated to be shipped to EPL. Dust samples
will be placed in Cardboard Box H until sufficient samples have accumulated to
send to EPL.
Page 97 of 98
National Institute of Environmental Health Sciences (NIEHS)
GuLF Study - to IRB
11/3/2010
Appendix C3.
The top of this diagram illustrates how the Central Laboratory will package the various
specimens for shipment to the repository at Environmental Pathology Laboratories.
Foam Shipping Box #1 and Box #2 will contain the biospecimens contained in
Freezer Storage Boxes A and D, plus Boxes B and E respectively. These
samples are divided in case one or the other of the boxes is damaged or delayed
in shipment to the point that the samples thaw. Both boxes will be packaged with
~10 lbs of dry ice for overnight shipmen to EPL.
Foam Shipping Box #3 will contain Boxes C, F, and I, which will be transported
to EPL on frozen ice packs (not on dry ice).
Cardboard Shipping Box #4 will contain nail and hair samples. After a sufficient
number of these samples have been accumulated, the Central Laboratory will
ship these samples to EPL at ambient temperature.
Cardboard Shipping Box #5 will contain the dust samples. After a sufficient
number of these samples have been accumulated, the Central Laboratory will
ship these samples to EPL at ambient temperature.
Once shipments have been prepared, the Central Laboratory will send them to EPL
via overnight FedEx shipment. Foam Shipping Box #1 and Box #2 will never be sent
in the same shipment to preclude total loss of samples from a given set of subjects.
Once the samples have been received at EPL, each frozen sample will have a BSI
ID label (Biological Specimen Inventory System, http://www.bsi-ii.com/ ) cryolabel
applied and each sample will be logged into the BSI database. The BSI system will
track the exact location of each sample while in storage. The boxes of frozen
samples will be stored as shown. Care will be taken so that all samples from one
study participant will never be stored in one single storage device.
Samples from Boxes A, D, B, and E can be stored in LN2 vapor phase or at
-80° C in mechanical freezers.
Samples in Boxes C, F, and I will be stored in EPL’s -20° degree walk in
freezer.
Hair, nail and dust samples will be stored under ambient conditions in a secure
temperature and humidity controlled conditions (~+20° C and 50% humidity) room at
EPL.
Page 98 of 98
File Type | application/pdf |
File Title | TITLE |
Author | bridgeh |
File Modified | 2010-12-01 |
File Created | 2010-12-01 |