1

August 15 , 2014 EPA
- HSRB
- 14
- 02 Robert Kavlock, Ph.D. Interim EPA Science Advisor Office of the Science Advisor 1200 Pennsylvania Avenue, NW Washington, DC 20460 Subject: June 11 , 2014 EPA Human Studies Review Board Meeting Report Dear Dr. Kavlock, The United States Environmental Protection Agency (EPA or Agency) requested that the Human Studies Review Board (HSRB) provide scientific and ethics reviews of three pre
- Rule pub lications relating to oral ingestion of iodine. For each of these reports, the Agency charged the Board with specific scientific and ethics charges. These questions and the issue of the return of individual research results to study participants were discu ssed in the Board’s meeting held on June 11, 2014. The Board’s key responses to the charge questions are summarized in this letter and are detailed in the enclosed final meeting report. **A published report by Paul**  **et al (1988) of an intentional exposure human study measuring**  **the effects of small increases of dietary iodine on thyroid function** Science

 The Board determined that the study was scientifically

sound and does provide reliable data.  The Board determined that the study would be relevant for quantitative use in support of an assessment of th e oral risk of exposure to iodine. Ethics

 The Board concluded that the published report b y Paul et al (1988) submitted for review meets the applicable requirements of 40 CFR part 26 subpart Q.2

**A published report by Gardner**  **et al (1988) of an intentional exposure human study**  **measuring the effects of low dose oral iodide supplementation on thyroid function** Science  T he Board concurred that the study is scientifically

sound , providing reliable data. However, the lack of details in the analy tic methods and less than robust statistical anal ys is weakened the HSRB’s ability to evaluate all aspects of th e study’s scientific soundness. T he Board did not find clear and convincing e vidence that the conclusions drawn from this study are not reliable.  The HSRB concluded that this study is relevant for quantitative use in support of an assessment of the oral risk of exposure to iodine. However, the hormone levels and changes in T 4 obser

ved in this study

should be viewed as qualitative in nature. In contrast, the changes in thy roid function are sufficiently reliable to be used in a weight
of
- evidence anal ys is. Ethics

 The Board concluded that the published report b y Gardner et al (1988) s ubmitted for review meets the applicable requirements of 40 CFR part 26 subpart Q. **A published report by LeM**  **ar et al**  **(1995) of an intentional exposure human study measuring the effects of chronic tetraglycine hydroperiodide water purification tablet use**  **on thyroid function** Science Subjec t to several limitations , the Board concluded that :  T he study

is scientifically

sound and provides reliable data.  This study would be relevant in a weight
- of
- evidence approach for establishing the reversibility

of high do se iodine exposure.  This study would be relevant in a weight
- of
- evidence approach for establishing that there are no sustained adverse effects from high dose iodine exposure. Ethics

 The HSRB concurred that the published report by L eMar et al (1995) submitted for review mee ts the applicable requirements of 40 CFR part 26 subpart Q. Sincerel y,
Rebecca T. Parkin, PhD, MPH Chair EPA Human Studies Review Board3 NOTICE This report has been written as part of the activities of the EPA Human Stu dies Review Board, a Federal advisory

committee providing advice, information and recommendations on issues related to scientific and ethical aspects of human subjects research. This report has not been reviewed for approval b y the Agency and, hence, the c ontents of this report do not necessarily represent the view and policies of the Environmental Protection Agency , nor of other agencies in the Executive Branch of the Federal government, nor does the mention of trade names or commercial products constitute a recommendation for use. You may obtain further information about the EPA Human Studies Review Board from its website at http://www.epa.gov/osa/hsrb
. You may also contact the HSRB Designated Federal Officer, via e
- mail at ord
- osa hsrb@epa.gov In preparing this document, the Board carefull y considered all information provided and presented b y the Agency presenters, as well as information presented b y public commenters. This document addresses the information provided and presented within the structure of the charge b y the Agency
.4 US ENVIRONMENTAL PROTECTI ON AGENCY HUMAN STUDIES REVIEW BOARD Chair Rebecca Parkin, PhD, MPH, Professorial Lecturer, EOH and Epidemiology & Biostatistics , Milken Institute School of Public Health, The George Washington University , Washington, DC Vice Chair Jewell H. Halan ych, M.D., Assistant Professor, Internal Medicine Residency Program, Montgomery Regional Campus , University of Alabama at Birmingham , Montgomery , AL Members Liza Dawson, Ph.D., Research Ethics Team Leader , Division of AIDS National Institutes of Health (NIH) , National Institute of Allergy and Infectious Disease (NIAID) , Bethesda, MD *George Fernandez, PhD, Statistical Training Speci alist, SAS Institute, Statistical Training and Technical Services , Sparks, NV Kyle L. Galbraith, Ph.D., Manager, Human Subjects Protection, Carle Foundation Hospital, Urbana, IL Edward Gbur, Jr., Ph.D., Professor, Agricultural Statistics L aboratory , Uni versity of Arkansas, Fayetteville, AR Sidney Green, Jr., PhD, Fellow of the ATS, Professor (Retired), Department of Pharmacology , Howard University

College of Medicine, Washington, DC Elizabeth Heitman, Ph.D., Associate Professor of Medical Ethics, Center for Biomedical Bioethics and Society, Vanderbilt University Medical Center, Nashville, TN *John C. Kissel, PhD, Professor, Department of Environmental and Occupational Health, School of Public Health, University of Washington, Seattle, WA *Randy M addalena, Ph.D., Phy sical Research Scientist, Indoor Environment, Lawrence Berkeley National Laboratory , Berkeley , CA *William Popendorf, PhD, MPH, Professor Emeritus, Department of Biology , Utah State University , Logan, UT *Kenneth Ramos, M.D., Ph.D., PharmB, Associate Vice President, Precision Health Sciences , Professor of Medicine , Arizona Health Sciences Center , Tucson, AZ5

*L eonard Ritter, Ph.D., ATS , Professor Emeritus (Toxicology) , School of Environmental Sciences, Univers ity

of Guelph, Guelph, ON, Canada Linda J. Young, PhD, Chief Mathemati cal Statistician and Director, USDA National Agricultural Statistics Service, Research and Development Division , Fairfax VA Human Studies Review Board Staff Jim Downing, Executive Director, Human Studies Review Board Staff, Office of the Science Advisor, United States Environmental Protection Agency , Washington, DC *Participated via Adobe Connect.6

**INTRODUCTION** On June 11, 2014, the United States Environme ntal Protection Agency ’s (EPA or Agency) Human Studies Review Board (HSRB or Board) met to address the scientific and ethical charge questions related to three publications conducted before promulgation of the 2006 Human Studies Rule (U.S. Environmental Protection Agency (EPA), 2006)
. To conduct a quantitative risk assessment of oral exposure to iodine, the Agency must determine the toxic effects and point of departure for iodine exposure. EPA selected the three publications for HSRB review from larger set s of studies , examined by the Institute of Medicine (Institute of Medicine (IOM), 2001) and the Agency

for Toxic Substances and Disease Registry (Agency for Toxic Substances and Disease Registry

(ATSDR), 2004) , concerning the ingestion of iodine for nutritional purposes. The B oard also discussed its W ork Group ’s report on returning individual research results to study participants; this report was submitted to the HSRB duri ng their April 8
- 9, 2014, meeting and was appended to that meeting’s Final Report. T he four agenda items included in this meeting report are:

 A published report b y Paul et al (1988) of an intentional exposure human study measuring the effects of small increases of dietary iodine on thy roid function  A published report b y Gardner et al (1988) of an intentional exposure human study measuring the effects of low dose oral iodide supplementation on thy roid function  A published report b y LeM ar et al (1995) of an intentional exposure human study measuring the effects of chronic tetraglycine hydroperiodide water purification tablet use on thy roid function  HSRB Work Group Report on the Return of In dividual Research Results **REVIEW PROCESS** The Board conducted a pub lic meeting in Arlington, Virginia, on June 11, 2014; eight members were present in the meeting room and six members joined the meeting via Adobe Connect. Advance notice of the meeting was published in the Federal Register as “Human Studies Review Board; N otification of a Public Meeting ” (EPA , 2014 , pp. 30135
- 30137 ). Following welcoming remarks from Agency officials, the Board heard presentations from EPA on each of the first three published reports listed above. The HSRB Chair introduced the discussion of the fourth report. This Final Report of the meeting describes the discussion, recommendations and rationale in response to each charge question for the first three reports ; it summarizes the discussio n and consensus of the Board regarding the fourth ag enda item
. For each published report , Agency staff first presented their review of the sc ience components of the publication and the Board asked the Agency presenters clarifying questions about the science. The staff then described their review of the ethical aspects related to the publication and the Board asked clarifying questions about the ethical issues. The Board solicited public7

comments and next asked Agency staff to read the Charge Que stions for the published report under consideration. The B oard discussed the science question s first and then the ethics question. Upon conclusion of the discussion of each question, the Chair called for a vote to confirm concurrence on a summary statement in response to that question. For their evaluation and discussion, the Board considered materials presented at the meeting, oral comments, a comment from the public, the original published reports, and the Agency ’s science and ethics r eviews of the publication s. A comprehensive list of background documents is available online at http://www.epa.gov/hsrb/
. At the same website, a cop y of the Work Group report is appended to the Final Report of the HSRB’s April 8
- 9, 2104, mee ting. **CHARGE TO THE BOARD AND BOARD RESPONSE A**  **published report by Paul**  **et al (1988) of an intentional exposure human study measuring**  **the effects of small increases of dietary iodine on thyroid function Overview of the Study**  Paul et al (1988) conducted a study of euth yroid adults ( 9 males and 23 females 23
- 56 years old) to identify

a tolerable upper limit for iodine consumption. While maintain ing their usual diets over a 14
- day

period, the female participants took sodium iodide dissolved in water at one of thr ee dosages (250, 500 or 1500 μg per day) along with 5 mg/day of ascorbic acid. In the same manner the male participants received onl y the 1500 μ g per day dos e. The authors found no change in weight and no sy mptoms of thy

roid dy sfunction in any

of the study

participants
. Using the Student’s pai r ed t
- test , they reported small but statistically significant (p< 0 .01) decreases in serum T 4 and T 3 concentrations and the free T 4 index, as well as small but statistically significant increases in serum thy rotropin (TSH) and thy

rotropin
- releasing hormone (TRH)
- induced TSH. T he changes were within normal ranges for TSH and TRH; the findings were not indicative of adverse effects. This intentional exposure human toxicity study of iodine impacts on thy

roid function was conducted among adult subjects
. There is no information available about the population used to recruit these individuals. Subjects were told of the possible risks and were given the opt ion to withdraw at an y time. They provided written consent but were not paid for their participation i n the study
. Upon further investigation, n o record of Institutional Review Board (IRB) review, approval or ov ersight was reported or found
. **Science Charge to the Board** 
 Is this study

scientifically

sound, providing reliable data?  If so, is this study relevant for quantitative use in support of an assessment of the oral risk of exposure to iodine?8

**Board Response to the Charge** HSRB Recommendation s

 The Board determined that the study was scientifically

sound and does provide reliable data.  The Board determined that the study w ould be relevant for quantitative use in support of an assessment of the oral risk of exposure to iodine. HSRB Detailed Recommendations and Rationale Overall, the Board agreed with the Agency ’s scientific assessment of this study (Leshin, 2014a). The HSRB noted that its comments were in the context of the Agency ’s intended use of the study in a weight
- of

- evidence (WOE) approach
. Most of the Board’s discussion focused on limitations of the statistical anal ys is. Is this study scientifically sound, providing reliable data? 1. Second treatment one ye ar later Questions were raise d about the authors ’ statement that "some of the women were studied at two dose levels at least one year apart " (Paul et al , 1988, p. 122) . Why was this information included in the study

when no rationale was given for this second treatment ? 2. Statistical issues Based on the limited and inadequate descriptions regarding statistical design and the results reported in this study , it is difficult to assess the statistical validity of the findings thoroughl y. For example, it is unclear how the total sample size of 32 can be reconciled with the values in column N of Table 1. However, the reported findings could be co nsidered as statistical ly valid if we assume that (1) the duplicate assay values used in the study were treated as subsamples (not as true replications) , and (2) the paired difference means were anal yz ed in comparing treatments (0 and 15 day s on the same subject) and the reporte d p - values in Table 1 (Paul et al, 1988, p. 122) were associated with testing the null h ypothesis from a paired t
test where the paired differences between 0 and 15 day s means were compared (not based on the reported means for 0 and 15 day s in Table 1)
. If so, is this study relevant for quantitative use in support of an assessment of the oral risk of exposure to iodine? 1. Tolerable upper limit The Board agreed with the authors’ assertion (Paul et al , 1988 , p. 123 ) that there are groups of individuals who are uniquely susceptible to the adverse effects of iodine, and consequently thought it is difficult to define an upper limit of normal for the dail y iodine intake. This issue was emphasized because the EPA expres sl y desired to use this study in establishing a tolerable upper limit for the oral ingestion of iodine. The Agency explained that this study wo uld be used as part of a WOE approach to establish such an upper limit. The Board9

thought this was a reasonable app roach and , if used in this fashion , the study could support an assessment of the risk of oral exposure to iodine. **Ethics Charge to the Board** 
 Does the study

meet the applicable requirements of 40 CFR part 26 subpart Q? **Board Response to the Charge** HSRB Recommendation

 The Board concluded that the published report b y Paul et al (1988) submitted for review meets the applicable requirements of 40 CFR part 26 subpart Q. HSRB’s Detailed Recommendation and Rationale The standard outlined in 40 CFR 26 subpart Q (U.S. Environmental Protection Agency (EPA), 2010) r equires that EPA must not rely on data from a study

that either involves a) intentional exposure of pregnant or nursing women or children or b) clear and convincing evidence of unethical conduct, defined specificall y as one or more of the following: studies involving intentional serious harm to study participants; deficiencies in study conduct relative to prevailing ethical standards; or un ethical recruitment such that informed consent is impaired. The Board concluded that there is no evidence that the published report b y Paul et al (1988) submitted for review involved pregnant or nursing women, nor is there evidence of unethical conduct as defined above. Therefore, as defined by the regulation 40 CFR part 26 subpart Q , the study meets the requirements for use by EPA
. The article b y Paul et al , published in February 1988 in Metabolism , is the report of a trial intended to test the effects o f a small increase in dietary iodine on thy

roid function in normal (euthy roid) volunteers. The investigation was not intended as a study of intentional exposure to a toxin, but rather was identified by the Office of Pesticide Programs (OPP) as a potential source of data for EPA decision
- making
. The Board agreed with the OPP review ( Sherman, 2014 a) that the article fails to report on a number of facts relevant to ethical revie w. At the time that the study was carried out, the 1985 version of 45 CFR 46 (Williams, 2005) 1 required institutional review board (IRB) approval of human participant studies funded b y the Department of Health and Human Services (DHHS) which includes the National Institut es of Health (NIH). The authors reported that the study was funded b y NIH, which required documentation of IRB review as part of its grant
- making procedures. However, the article does not mention IRB review and, when interviewed by phone by EPA’s Jonathan Leshin (Sherman, 2014 a , p. 7), the study ’s senior author, L .E. Braverman, had no memory

of whether the study had undergone IRB review. Inquiries by EPA’s Kelly

1 For a timeline of the regulations related to the protection of human subjects in research, see http://history.nih.gov/about/timelines_laws_human.html#1983.10

Sherman, found that the IRBs at the three institutions 2 where this work might have been reviewed have no records from that peri od. NIH’s archived records from the period of the study do not include information on IRB review. The applicable regulations at 45 CFR Section 46.116 would also have required informed consent by participants and documentation with a consent form containi ng all required elements of consent, unless written documentation was waived b y an IRB (45 CFR 46.117); however, no records regarding informed consent are available. 1. The Board concurred with the conclusions of the OPP’s Ethics Review (Sherman, 2014 a ) that the reported research does not rel y on data from intentional exposure of any human subject who is a pregnant or nursing woman or a child. There is no clear and convincing evidence that the conduct of the research was fundamentally unethical. There is no e vidence that the research intentionally placed participants at risk of serious harm (based on the knowledge available at the time the study was conducted). Because the study most likely involved only

minimal risk, the possibility of unethical conduct is s ignificantly reduced. Regardless of risk level, it is still essential for study participants to be properly informed and given opp ortunity

to consent. N o information is available on the recruitment processes used for the study, nor is there any documentation regarding research participants’ ability to give informed consent or the informed consent process itself.
a. Assessment of risks and benefits : The authors stated that the quantity of iodine consumed by man y Americans in their regular diet is greater than that necessary for maintenance of n ormal thy

roid function, suggesting that knowledge of the effects of small incremental increases over the daily

requirement of i odine would be beneficial for determining a normal, acceptable, and clearl y excessive level of iodine intake , and thus would be of value to society. The authors did not address additional risks to human participants from ingesting small additional amounts of iodine, or any potential b enefit to participants. They made no statement about the balance between risk and benefit. However the amounts of iodine ingested by p articipants at the maximum dose over a two - week period were described as being within the range of the average American’s nor mal intake, suggesting that these amounts thus posed risk equivalent to the risks of everyday life, which meets the regulatory defi nition of minimal risk at 45 CFR 46 .102 (i). b. Voluntary

and inform ed consent of all participants : No information is available about recruitment or enrollment of the 37 participants, either from the article or from the interview with co
- investigator Braverman. It is not possible to tell whether participants from potentially

vulnerable populations were recruited or whether th e study protocol included mechanisms designed to minimize coercive recruitment and enrollment. To participate in the study , subjects nee ded to be healthy , non - pregnant, euthy roid adults. Women underwent pregnancy testing. Per Braverman (Sherman, 2014 a , p. 7), any woman whose pregnancy test was positive would have been excluded, and no women parti cipants were nursing (Sherman, 2014a, p. 8).

2 University of Massachusetts Medical School, the Medical College of Virginia, and Beth Israel Hospital: These were the affiliations listed by the authors.11

As stated above, no authoritative information was available about the study’s informed consent materials or process, although senior investigator Braverman reported that participants gave informed consent and signed documents (Sherman, 2014a, p. 7)
. c. Equitable selection of study participants : Itis not possible to determine whether members of vulnerable populations were recruited or enrolled in the study . Per Braverman (Sherman, 2014 a , p. 7) , participants were not compensated for taking part in the stu dy
. 2. The Board recommended that the data within this article be considered acceptable for EPA reliance, contingent upon the determination of its scientific validity
. **A published report by Gardner**  **et al (1988) of an intentional exposure human study**  **measuring the effects of low dose oral iodide supplementation on thyroid function Overview of the Study**  As in Paul et al (1988), this study was conducted to determine a tolerable upper limit for iodine consumption. Gardner et al (1988) examined 30 euthy roi d males (ages 22
- 40) who had no history of th yroid disease, had not been on medications that affected thyr oid function, or had a prior reaction to iodine. Each individual served as his own control. Over a 14
- day period while maintaining his normal diet , ea ch individual was randomly assigned to consume sodium iodide dissolved in water at 500, 1500 or 4500 μ g/ml. The assigned dose was administered, along with 1 mg/ml ascorbic acid , twice a day in 0.5 ml solutions. Compared to baseline measures, post
administration measures of thy roid function revealed that at 1500 and 4500 μg/ml statistically significant (p< 0 .02) decreases in serum and free thy roxine ( T 4 ) occurred. At all three dosages, basal and TRH
- induced TSH were found to be significantly (p< 0 .05 or less) increased. The study subjects were medical students or employees of the Medical College of Virginia , or were selected from a list of interested research candidates. The study protocol was reviewed and approved b y the Virginia Commonwealth University (VCU) Committee on the Conduct of Human Research. Although each subject provided written consent and was compensated for their participation, there is no information about whether subjects were told they could withdraw at any time. **Science Charge to the Board** 
 Is this study

scientifically

sound, providing reliable data?  If so, is this study

relevant for quantitative use in support of an assessment of the oral risk of exposure to iodine?12

**Board Response to the Charge** HSRB Recommendations  T he Board concurred th at the study is scientifically

sound , providing reliable data. H owever, the lack of details in the analy tic methods and less than robust statistical anal ys is weakened the HSRB’s ability to evaluate all aspects of the study ’s scient ific soundness. T he Board did not find clear and convincing evidence that the conclusions drawn from this study are not reliable.  The HSRB concluded that this study is relevant for quantitative use in support of an assessment of the oral risk of exposure to iodine. However , the hormone levels and changes in T 4 observed in this study should be viewed as qualitative in nature. In contrast, the changes in thy roid function are sufficiently reliable to be used in a weight
of
- evidence anal ys is. HSRB Detailed Recommendations and R ationale While the authors are experienced researchers in this field and designed a reasonable study, the Board expressed some concern that this particular publication did not provide sufficient details in their anal yt ic methodologies and in their rational e for the grouping of samples during anal ys is. Two additional limitations were the lack of statistical use of duplicate measurements and the finding that most of the mean thy roid response data did not correlate with the doses of iodine tested. Is this stu dy scientifically sound, providing reliable data? 1. Grouping The Board discussed the dose groups and the grouping of samples for analysis.
a. The first of the uncertainties of the publication is the actual distribution of the subjects within the three dose groups. On p. 284, Gardner et al (1988) state d that "Thirty normal men between the ages of 22 and 40 years (mean age 27) were randomly assigned to receive 500, 1500 or 4500 μg iodide/day ." However, the authors did not say in any text or table that these subjects were distributed evenl y at 10 people per dose. This distribution is reasonable, but it is an assumption made in this review due to its omission within the text. b. It is unusual for an article to mention how the samples were grouped during their anal ys is, suggesting that batch
- to - batch variabilit y within one or more analytical methods might be an issue. No information was provided regarding the various analytic methods’ variability . The methods used to measure serum hormone levels were cited but not provided for review; the methods used to measure serum iodide levels were not mentioned (only

that the samples were anal yz ed by a commercial lab). In contrast to the grouping of samples b y Paul et al in which “all serum samples for a given test were assayed in the same assay " (Paul et al , 1988, p. 122), in Gardner et al : "All samples from an individual man were anal yz ed in the same assay " (Gardner et al , 1988, p. 285). Anal yz ing all samples in the same assay has the advantage of eliminating13

the effect of an y batch
- to - batch variability within the anal yt ical method. By grouping all samples from a given individual together, batch
- to - batch variability in the measurements b y Gardner et al (1988) would not affect a given individual’s change in hormone level, but it still could leave the values of the group means vulnerable to batch
- to - batch variability
. 2. Duplicate measurements The HSRB considered the use of the duplicate mea surements , noting that the use of duplicate samples is very

important, especiall y for finding small differences in a method with intrinsic variability . A s above for Paul et al ( 1988), the authors of Gardner et al (1988) stated on p. 284 that serum hormone and T 3 - charcoal uptake ratios “were measured in duplicate,” but no paired data or information regarding the methods’ precision or typical intra
- personal variability

was provided. Furthermore, the Student's paired t - test did not allow the duplicate data to be used. For statistical purposes, the duplicate data should have been considered as repeated measures. If so, is this study relevant for quantitative use in support of an assessment of the oral risk of exposu re to iodine? 1. Lack of correlation Board members raised concerns about the lack of correlation between iodine levels and effects measured in either thy roid function or hormone levels.
a. The statistically

significant changes in hormone levels reported in Table 2 are in the range of 8 to 14%; all of these endpoints fall within normal limits. The coefficient of variation in the standard error of the inter
- personal mean T 4 levels on any day ranged from about ±5 to ±8%; but both the intra
- personal variability and the method variability are unknown. Prior research trying to measure similarly small changes in cholinesterase enzy me activity

with an imprecise assay

has shown that neglecting the e ffect of method variability

both within a person and from batch
- to - batch could yi eld incorrect conclusions ( Yager et al , 1976; Trundle and Marcial, 1988; Brock and Brock, 1990). It may be possible to estimate the statistical impact o f method variability in this case if some quantitative information on its magnitude can be obtained. b. The Board noted a lack of an expected dose
- response correlation within most of these authors’ data. A correlation between dose and effect (a change in either hormone level or thy roid function in this case) is axiomatic in the field of toxicology . Because the authors did not provide individu al data, the Board was re stricted to observing the consistency of trends and testing for correlations among the mean values. The urinary iodine excretion reported in Table 1 ( Gardner et al , 1988, p. 285 ) increased in relation to do se, 3 although even its c orrelation r2 value of 0.996 is not statistically significant with only

three mean values. In contrast, the statistically significant changes in mean serum thy roid hormone levels reported in Table 2 ( Gardner et al , 1988, p. 286 ) (decreases in T 4 and fr ee T 4 index) were not consonant with dose, either in their magnitude or in their level of

3 This would be expected based on mass
- balance considerations and as noted by the authors.14

statistical significance; in fact, b y both metrics, the changes in hormone levels at 4500 μg/day were less than at 1500 μg/day
. It should be noted that an inverse dose response is what was expected and was not clearl y established; i.e., as the dose of iodine increases, the levels of th yroxine T 4 and triiodothy ronine T 3 should have decreased. Most (4 out of 5) of the changes in the mean TRH
- stimulated TSH concentrations r eported in Table 3 4 i ncreased consistently

with dose, except at 15 minutes ; o nly the changes at 45 minutes were significantly

correlated with dose at a p < 0.01. The lack of a correlation between dose and response for either hormone levels or TSH respons e to TRH stimulation may be accounted for by

fluctuations in baseline values among study participants. While such fluctuations may be taken into consideration as part of a different statistical anal ys is than has been used thus far, questions about the bio logical fidelity of the findings remain given that , despite findings of statistical significance in the dataset, all values reported fall well within the range of normal clinical values. There seems to b e some disagreement among studie s about how ty pical such mixed results might be. On p. 287, Gardner et al (1988) state that “previous studies have demonstrated that pharmacological doses of 10 to 1000 mg/day for 2
- 11 weeks resulted in significant decreases in serum T 4 and free T 4 concentrations, and compensatory increases in serum TSH concentrations.” However, on p. 123, Paul et al (1988) 5 state that such doses result “in a small increase in both basal serum TSH concentrations and the TSH response to TRH, sometimes [emphasis added] in association with decreased serum concentrations of T 4 and T 3 .” Read in isolation, the statistical significance of changes in mean hormone levels observed by Gardner et al (1988) indicates that some change is probabl y occurring, but the lack of a dose
- response correlation in this study weakens the attribution of dose to the significant differences in reported hormone levels . Despite the weak correlation of changes in mean thy roid function with dose, the generall y coher ent trends in th ese changes are in agreement with other studies , cited by Paul et al (1988) and Gardner et al (1988), at higher dose levels. 2. The large number of t
- tests resulted in a higher than expected number of significant results. The statistical test results in this study should not be used quantitativel y for supporting an assessment of the oral risk of exposure to iodine
. **Ethics Charge to the Board** 
 Does the study

meet the applicable requirements of 40 CFR part 26 subpart Q?

4 According to the authors, this indicated “a d efinite anti
- thy roid effect” (Gardner et al , 1988, p. 287 ) . One Board member stated that the acute TSH reaction may not be an indicator of such an effect. 5 The authors cite d two more than the four references noted by Gardner et al (1988) on p. 287.15

**Board Response to the Charge** HSRB Recommendation

 The Board concluded that the published report b y Gardner et al (1988) submitted for review meets the applicable requirements of 40 CFR part 26 subpart Q. HSRB’s Detailed Recommendation and Rationale The requirements in 40 CFR 26 subpart Q (U.S. Environmental Protection Agency (EPA), 2010) , which guided this review, are listed above in the HSRB’s review of Paul et al (1988) above. The Board concluded that there is no evidence that the study reported in Gardner et al (1988) submitted for review involved pregnant or nursing women or children, and there is no evidence of unethical conduct as defined above. The study therefore meets the requirements of 40 CFR part 26 subpart Q for use b y EPA. The article b y Gardner et al , published in 1988 in Clinical Endocrinology , is the report of a trial intended to test the effects of very low dose iodine supplementation on thy roid function in normal (euth yroid) adult male volunteers. The investigation was not intended as a study of intentional exposure to a toxin, but rather was identified by the Office of Pesticide Programs as a potential source of data for EPA reliance. In the Materials and Methods section of the article , the authors report ed that the study was approved b y VCU’s IRB for the protection of human subjects (“The Committee on the Conduct of Human Research”), which at that time would have been operating under the 1985 version of 45 CFR 46 (Williams, 2005) . They also reported that “each man gave informed written consent” (Gardner et al , 1988, p. 284). When interviewed b y OP P staff in February 2014, the article’s first author, DF Gardner, reported that participants were given an opportunity to read the study

protocol and asked if they understood, and then each man signed a written informed consent document. No additional information was requested from VCU ’s IRB, but it may be assumed that the Committee followed the regulatory

requirements in place at the time the study was revi ewed. 1. The Board concurred with the conclusions of the OPP’s Ethics Review ( Sherman, 2014 b ) that the reported research does not rel y on data from intentional exposure of any human subject who was a pregnant or nursing woman or a child. There is no clear and convincing evidence that the conduct of the research was fundamentally unethical. There is no evidence that the research was conducted in a way that placed participants at increased risk of harm (based on the knowledge available at the time the study was conducted). Because recruitment processes were directed toward students and employees of the medical school where the study was conducted, the participants’ ability to give informed consent may have been impaired b y coercion.
a. Assessment of risks and benefits : The authors reported that the quantity of iodine consumed b y man y Americans in the ir regular diet is greater than that necessary for maintenance of normal thy roid function, suggesting that knowledge of the effects of16

small incremental increases over the daily requirement of iodine would be beneficial for determining a normal, acceptable , and clearl y excessive level of iodine intake, and thus would be o f value to society . The authors did not address additional risks to human participants from ingesting small additional amounts of iodine, or any potential benefit to participants. The Board found n o statement of the balance between risk and benefit in the article. However , the amounts of iodine ingested by study participants were described as being within the range of the average American’s nor mal intake, suggesting that the amounts thus p osed minimal risk equivalent to the risks of everyday life. b. Voluntary

and infor med consent of all participants : Participants were recruited from among students and employees of the Medical College of Virginia or a list of potential volunteers kept b y the institution’s Clinical Research Center. Itis not possible to tell whether participants from potentially vulnerable populations were recruited, or whether th e study protocol included mechanisms designed to minimize coercive recruitment and enrollment of s tudents and employees who may have been in a subordinate position to the researchers. To participate in the study , subjects were required to be healthy , euth yroid adult men with no history

of th yroid disease and who were not taking medications that affect thy roid function. No women and no children were enrolled. No authoritative information was available about the study ’s informed consent materials or process, although investigator Gardner reported that participants gave informed consent and signed consent documents.
c. Equitable selection of study p articipants : Itis not possible to determine whether selection of study participants was equitable or whether members of vulnerable populations were recruited or enrolled in the study
. According to investigator Gardner’s telephone interview with EPA’s Jonathan Leshin (Sherman, 2014b, p. 6) , participants were compensated approximately $150
- 200 for taking part in the 2
- week study that included multiple blood draws. 2. The Board recommended that the data within this article be considered acceptable for EPA decision making, contingent upon the determination of its scientific validity. **A published report by LeM**  **ar et al**  **(1995) of an intentional exposure human study measuring the effects of chronic tetraglycine**  **hydroperiodide water purification tablet use on thyroid function**  **Overview of the Study** As in the above two studies (Paul et al , 198 8; and Gardner et al , 1988), LeMar et al (1995) conducted a study of adults to identify a tolerable upper limit for iodine consumption, with a focus on effects of subchronic ingestion of iodine in water purification tablets (tetragl ycine hydroperiodide). All seven males and one female (ages 35
- 47) in the study were euthy

roid, had17

no prior thy

roid disease, had no chronic medical disorders, were not using medications which affected th yroid function, and had not had previous reactions to iodine. During the 90
- day study period, the subjects maintained their n ormal diets; daily they self
- administered four tablets ( totaling 32,000 μg) dissolved in water or juice. Measures which decreased during the study period included 24
- hour radioactive iodine uptake, mean serum T 4 and T 3 (triiodothy ronine), while serum TSH , and TSH
- 20 (measured after 20 minutes) increased by the seventh day

and remained elevated. Although no h ypo - or hy per - thy roidism was found, thy

roid volume increased an average of 37%. Among the 7 subjects for whom repeat measures were made ( an ywh ere from 0.5 to 16.1 months after the study period) , all thy

roid volumes had returned to baseline levels. The authors stated that this result suggests that TSH
- dependent thy roid enlargement is reversible following dail y use of water purification tablets. Particip ants in the study

were employees of the hospital where the study was conducted (Fitzsimons Army

Medical Center). T he protocol was reviewed and approved by the hospital’s IRB . All subjects were equitably selected; they signed a written consent form and were advised that they could withdraw at an y time. They were not compensated for their participation. **Science Charge to the Board** 
 Is this study

scientifically

sound, providing reliable data?  If so, is this study

relevant to establish the reversibility of high dose iodine exposure?  Also, is this study

sufficient to establish that there are no sustained adverse effects from high dose iodine exposure? **Board Response to the Charge** HSRB Recommendations Subject to the limitations noted below, the Board concluded that :  T he study

is scientifically

sound and provides reliable data.  This study would be relevant in a weight
- of
- evidence approach for establishing the reversibility

of high dose iodine exposure.  This study would be relevant in a weight
- of
- evidence approach for establishing that there are no sustained adverse effects from high dose iodine exposure. HSRB Detailed Recommendations and Rationale The HSRB members discussed each charge question individually , carefull y c onsidering the wording of each query

and their responses to each question . In particular, the Board disagreed with the word “sufficient” in the third question; no single study can be considered “sufficient” for establishing sustained adverse effects. A b ody of work is needed to evaluate a study in the context of other findings. Consequently , the HSRB requested permission from the Agency representatives to modify the wording of the third question; the request to change “sufficient” to “relevant” was grant ed.18

Is this study scientifically sound, providing reliable data? Subject to the limitations noted below, the Board conclud ed that the study is scientifically sound and provides reliable data. If so, is this study relevant to establish the reversibilit y of high dose iodine exposure? The w eaknesses noted here decrease d the Board’s confidence that the LeMar et al (1995) paper can be used quantitativel y . Following a detailed discussion, the HSRB decided that the study is relevant but not definitive by itself to establish the reversibility of high dose iodine exposure. Furthermore, the Board limited its response to the Agency ’s intended use of the data in a weight
of
- evidence (WOE) approach. T he HSRB determined that LeMar et al (1995) can be used qualitatively

in a WOE approach, noting that the results are not sufficiently reliable for estimat ing reversibility quantitative ly
. Board concern s related to the repeated measures study design and small sample size, the statistical methods used, and the thy roid volume reversibility

data. 1. Repeated measures Based on the study

description in LeMar et al (1995), the design of their experiment appears to have been a repeated measures study with either three or four unequall y spaced time points, depending on whether or not baseline data are included in the anal ysis. Eight subjects, seven males and one femal e, participated in the experiment. It is commonly assumed that repeated measurements on a subject over time are correlated. 2. Statistical analy sis The authors described their statistical anal ys is as “anal ys is of variance, followed by Student

– Newman
- Keuls multiple comparisons” (LeMar et al , 1995, p. 221). In general, the reported numerical estimates of the means do not contradict their statements regarding trends in the data. The HSRB’s concern lies in the effect of the correlation and variance issue s on the estimates of the standard errors and hence on the statistical significance of the results. The authors did not indicate the design on which their anal ys is was based nor did they indicate that an y consideration was given to the correlation and un equal variance issues. An y anal ys is of their data should take into account the potential repeated measures correlation structure as well as the potential for unequal variances. Failure to account for either may impact the significance or non
- significance o f the reported results. a. The Board acknowledges that, at the time the study was conducted, explicitly adjusting for the correlation was not generall y part of anal ysis of variance. b. The authors’ numerical results provide evidence that, for at least some variables, the variance changed with time. For example, using the serum protein
- bound iodine (PBI) data in Table 1 (LeMar et al , 1995, p. 221), the ratio of the largest to smallest variance is approximately

16 for the post
- baseline data and about 108 if the b aseline data are included.19

In an attempt to judge the effect of the potential unequal variance problem, the worst case scenario (i.e., most likely to contradict the stated statistical significance of p<0.05; LeMar et al , 1995, p. 221) would be to compare the reported means using the largest reported standard error among the treatments as the standard error for all treatments in the multiple comparison procedure. Using the largest reported standard error generally confirmed the conclusions reached in the te xt regarding statistical significance. The Board noted that the effects and potential corrective actions for unequal variances had been in the statistics literature since the 1950’s. By the 1990’s these methods were likely fairly well known outside the f ield of statistics and thus available at the time of the study anal ys is. 3. Thy roid volume reversibility Since there was no indication that the post
- experiment data on thy roid volume returning to normal were anal yz ed statistically , the results should be treated onl y as an observationall y – and not a statistically

– based indication of recovery
. a. Despite otherwise solid methods used by L eMar et al (1995, pp. 220
- 221), the paper contains a seriou s flaw in the thy roid volume data presented. The authors state that “The precision of the th yroid volume determined b y this method was assessed in five [of 8] study participants, each examined on five separate occasions before the treatment period. Coeff icients of variation for these thy roid volume measurements ranged from 3.6 to 13.2%” (LeMar et al , 1995, p. 221). However, in the next sentence they state: “The greatest volume for each of these five subjects was subsequently used as the pretreatment volume for that individual” (LeMar et al , 1995, p. 221). It is axiomatic in statistics that the most likely

value for any

single measurement is the mean for each subject. Thus, this decision to use the greatest volume for those five participants biased the r esults to decrease changes in th yr oid volume during treatment (because these subjects' baseline volume appeared to be larger) and increase the likelihood for complete recovery to pretreatment volumes. The Board commented that the mean pretreatment volumes (both individually

and collectively) were lower than the greatest volumes reported. 6 b. Furthermore, the authors did not state that a goal of their study was to support the kinetics of either th yroid enlargement or recovery. The wide range of their recove ry phase (from 0.5 to 16 months) suggests that thi s part of the research project was an unanticipated “add
- on” to the study . Given that wide range and an average of 7.1 months for 7 of 8 subjects, the authors’ observation that "the increase in thy roid volume was reversible" (LeMar et al , 1995, p. 222) is all the more remarkable. This bias weakens the usefulness of this study

to “provide information on the effects of excess iodine in humans, which include a form of reversible thy roid gland volume increase and decreases in T 4 levels ” (Leshin, 2014c, p. 5).

6 In Figure 2 (LeMar et al , 1995, p. 222), the "recovery" volumes appear to be lower than the "Week 0" volumes.20

Also, is this study sufficient to establish that there are no sustained adverse effects from high dose iodine exposure? It is unlikel y, from a scientific perspective, that any one study (i .e., LeMar et al , 1995) could be “sufficient to establish that there are no sustained adverse effects from high dose iodine exposure,” as the Agency posed to the Board in this question. However, the Board recognizes and accepts that LeMar et al (1995) contributes signif icantly to scientific understanding about the lack of sustained adverse effects from high dose iodine exposure. The Board also recognizes that L eMar et al (1995) has been a key study on which daily

maximum iodine intake levels have been established (e.g., in ATSDR, 2004). Therefore, the HSRB concluded that the study is relevant , but not sufficient, in a WOE approach for establishing whether there are sustained adverse effects for high dose iodine exposure. **Ethics Charge to the Board** 
 Does the study

meet the applicable requirements of 40 CFR part 26 subpart Q? **Board Response to the Charge** HSRB Recommendation

 The HSRB concurred that the published report b y LeMar et al (1995) submitted for review mee ts the applicable requirements of 40 CFR part 26 subpart Q. HSRB Detailed Recommendation and Rationale The LeMar et al (1995) manuscript published in the Journal of Clinical Endocrinology and Metabolism describes a study designed to determine the effects of daily subchronic ingestion of iodine purification tablets (tetragl ycine h ydroperiodide) on thy roid size, function, and radioactive iodine uptake in eight healthy volunteers over a three month period. EPA’s OPP has identified this study as a potential data source for EPA’s human health risk assessments for products containing iodine. In addition to this manuscript, OPP also provided the HSRB with the transcript of a February

2014 interview between EPA r epresentative Jonathan Leshin and a study co - investigator, Michael McDermott (Sherman, 2014 c, p. 6 ). The Agency ’s rules at 40 CFR part 26 subpart Q (U.S. Environmental Protection Agency (EPA), 2010) that are applica

ble to this review are stated above in the ethics review of the Paul et al (1988) study
. These rules identify

three ethical issues that were discussed by the HSRB: 1. Subject p rofiles
a. LeMar et al (1995, p. 220) report ed that their study enrolled eight partic ipants (seven men and one woman) between 35
- 47 years of age; thus, the study did not involve intentional exposure of an y subjects who were children.21

b. The manuscript makes no reference to the pregnancy or nursing status of the one female participant, b ut th e co - investigator indicated in the interview that female participants were tested for pregnancy before study

particip ation and that if a potential participant was pregnant, she was excluded from the study ( Sherman, 2014 c, p. 6 ). There is no indication that the subject became pregnant or was nursing in the course of the research.
c. In order to minimize risks to subjects enrolled in the study , all subjects were required to pass a ph ys ical exam prior to study activities, including thy

roid level tests to verify euthy roid status. Subjects were also required to have no chronic medical conditions, not taking an y m edications affecting th yroid function, and not have had an y reactions to iodine. 2. Introduction of intentional h arm a. The LeMar et al manuscript indicates that all participants provided their written informed consent prior to study

participation and that the study had been approved b y the institutional research committee (1995, p. 220). In his telephone conversation with EPA representatives, co
- investigator McDermott confirmed that the study was reviewed and approved b y the Fitzsimons Army Medical Center IRB. There was no evidence provided to the HSRB regarding the contents of informed consent processes, but applicable federal regulations at the time (Williams, 2005) specify required elements of informed consent, including a description of experimental procedures, potential risks to subjects, any potential benefits, and a notice that research participation is voluntary
. Additionall y, there was no documentation to verify I RB review and approval beyond the statements provided in the manuscript and b y the co
- investigator. b. The authors described the research protocol (administration of water purification tablets) and the subjects’ respo nses, including their serum and urine iodide levels, radioactive iodine uptake, and th yroid volume. Based on the data presented in LeMar et al (1995) , the EPA Science Review, and the discussion of scientists during the HSRB meeting, the risks to subjects posed by this study of intentional exposure to free iodine do not appear to be unreasonable, unethical, or intentionally designed to seriously

harm participants.
c. The HSRB considered whether the use of nuclear tracers in the RAIU procedures posed serious o r unnecessary

risks to participants, but after discussion among the group, the HSRB concluded that the small amount of radiation exposure (1
- **μ** Ci) as described in the LeMar et al manuscript (1995, p. 221) did not pose unreasonable risks to study participant s. 3. Prev alent ethical standards of the t ime
a. At the time in which this stu dy was conducted (early

1990’s) EPA’s rules for the protection of human subjects at 40 CFR part 26 were not yet in effect. However, the study was supported by

the United States Department of Defense, which adopted the Common Rule in 1991 (32 CFR part 219)
. As a result, the Common Rule provides the basic ethical regulatory

framework for this investigation at the time of its con duct.22

b. Common Rule provisions at the time required that a study such as this one undergo IRB review and approval prior to initiation. As noted above, the LeMar et al (1995) manuscript indicates that the investigation was reviewed and approved b y an institutional review committee, and co
- investigator McDermott indicated that the study had been under the oversight of the Fitzsimons Army Medical Center IRB. There was no official documentation provided to verify such IRB review an d approval; the HSRB rec ommended that the EPA’s OPP make an attempt to locate such records. However, given that Fitzsimons Army Medical Center is now closed, HSRB recommendations would not be contingent upon locating those records.
c. The Common Rule requires that participants in s tudies such as this must provide their informed consent prior to study participation. The Common Rule specifies elements that must be present in the consent process. Both the LeMar et al (1995) manuscript and the interview with co
- investigator McDermott in dicate that participants provided their informed consent p rior to study participation. However, given the lack of IRB and investigator records regarding the conduct of this study , there is no documentation to indicate that the consent process met Common Ru le requirements. As above, since the study location is now closed, HSRB recommendations are not contingent upon locating such records. d. Common Rule regulations also address the issue of participant compensation. In the interview with EPA, co
- investigator M cDermott notes that participants were not compensated for their participation in this study . Lack of compensation in a study such as this is consistent with Common Rule standards of the time.
e. The manuscript does not describe participant recruitment practices and the interview with co - investigator McDermott provided little information on this matter. In the interview, McDermott stated : “We asked if an yone wanted to volunteer to take part in a study about iodine water purification tablets” (Sherman, 2014 c, p. 6 ). While nothing provided to the HSRB indicates that participant recruitment was conducted in an ethical manner that was consistent with standards of the time, the information provided does not indicate that there were unethical recruitment prac tices taking place. As with many

of the points above, the HSRB ’s ability to assess the study

was somewhat limited by the lack of documentation provided to support the use of this study by the EPA. **HSRB Work Group Report**  **on the**  **Return of Individual Rese**  **arch Results Overview**  On several occasions the HSRB has discussed the return of individual research results. The Board determined that the topic merited in
- depth discus sion by a smaller group of HSRB members and representatives of study participants and their medical providers. A Work Group was formed to deliberate about this issue; the group’s workshop was held at EPA in January23

2013. The Work Group membership, its process and report are included in Appendix A of the HSRB’s April 8
- 9, 2014, Final Report. The return of individual research results has been addressed for clinical studies and some community
- based research but not for the types of laboratory or field studies within the HSRB’s purview. The return of results is a timely , unresolved and evolving issue in the ethics profession. The Work Group identified key ethical principles as the underpinnings of their deliberations: research participant’s autonomy and right to know, and researchers’ respon sibilities to ensure trust and respect. The group also discussed the potential impacts of results on participants and sponsors, as well as on the HSRB and the Agency
. Discussion The HSRB emphasized that the community and laboratory

contexts in which the HSRB
- related studies are conducted are quite different from the cl inical settings that served as the foundations for the Work Group ’s report
. The Board decided that this topic should be considered in newer contexts; for example, in light of the recent rep ort on handling incidental research findings (Presidential Commission for the Study of Bioethical Issues, 2013) and current risk communication knowledge. On e member noted that another committee with different expertise would be needed to discuss the “how” of returning results, whether the findings are aggregate or individual
. Board Con s ensus Before deciding whether the HSRB will address this topic at a later meeting, the Board asked the Agency to determine whether returning results is a priority concern for study

sponsors.24

**References** Agency for Toxic Substances and Disease Registry (ATSDR). (2004). Toxicologic profile of iodine. Atlanta, GA: AT SDR, Public Health Service, U.S. Department of Health and Human Services. Retrieved July 15, 2014, from http://www.atsdr.cdc.gov/toxprofiles/tp158.pdf Brock, A., & Brock, V. (1990). Plasma cholinesterase activity in a healthy population gro up with no occupational exposure to known cholinesterase inhibitors: relative influence of some factors related to normal inter
- and intra
- individual variations. Scandinavian Journal of Clinical & La boratory Inves tigation, 50 (4), 401
- 408. Gardner, D., Centor, R., & Utiger, R. D. (1988). Effects of low dose oral iodide supplementation on thyroid function in normal men. Clinical Endocrinology, 28 , 283
- 288. Institute of Medicine (IOM). (2001). Dietary reference intakes forvitamin A, vitamin K, arsenic, boron, chromium, copper, iodine, iron, manganese, molybdenum, nickel, silicon, vanadium, and zinc. Washington, DC: National Academy Press. Retrieved July 15, 2014, from http://www.nap.edu/openbook.php?isbn=0309072794 LeMar, H., Georgitis, W., & M cDermott, M. (1995). Thyroid adaptation to chronic tetraglycine hydroperiodide water purification tablet use. Journal of Clinical Endocrinol ogy and Metabolism., 80 (1), 220
- 223. Leshin, J. (2014a). Data Evaluation Record of human toxicity study of iodine. R ef: Paul et al. (1988) (MRID 48358603). Washington, DC: Office of Pesticide Programs, U.S. Environmental Protection Agency. Retrieved July 15, 2014, from http://epa.gov/hsrb/files/meeting
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- 1988.p df Leshin, J. (2014b). Data Evaluation Record of human toxicity study of iodine. Ref: Gardner et al. (1988) (MRID 47358601). Washington, DC: Office of Pesticide Programs, U.S. Environmental Protection Agency. Leshin, J. (2014c). Data Evaluation Record of h uman toxicity study of iodine. Ref: LeMar et al. (1995) (MRID 49318802). Washington, DC: Office of Pesticide Programs, U.S. Environmental Protection Agency. Retrieved July 15, 2014, from http://epa.gov/hsrb/files/meeting
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- 1995.pdf Paul, T., Meyers, B., Witorsch, R., Pino, S., Chipkin, S., Ingbar, S., & Braverman, L. (1988). The effect of small increases in dietary iodine on thyroid function in euthyroid subjects. Metabolism , 121
- 124. Presidential Commission for the Study of Bioethical Issues. (2013). Anticipate and communicate: Ethical management of incidental and secondary findings in the clinical, research, and direct

- to - consumer contexts. Washington, DC: Presidential Commission for the Study of Bioethical Issues. Retrieved July 15, 2014, from http://bioethics.gov/sites/default/files/FINALAnticipateCommunicate_PCSBI_0.pdf Sherman, K. (2014a). Ethics review of human toxicity study of iodine. Washington, DC: Office of Pesticide Programs, U.S. Envir onmental Protection Agency. Retrieved July 15, 2014, from http://epa.gov/hsrb/files/meeting
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- 1988.pdf Sherman, K. (2014b). Ethics review of human toxicity study with iodine. Ref: Gardner et al, 19 88. (MRID 47358601). Washington, DC: Office of Pesticide Programs, U.S. Environmental Protection Agency. Retrieved July 15, 2014, from http://epa.gov/hsrb/files/meeting
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Sherman, K. (2 014c). Ethics review of human toxicity study of iodine. Ref: LeMar et al, 1995. (MRID 49318802). Washington, DC: Office of Pesticide Programs, U.S. Environmental Protection Agency. Retrieved July 15, 2014, from http://epa.gov/hsrb/files/meeting
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