WIL Research Laboratories Joseph F. Holson Contributions By: Mark D. Nemec Chris P. Chengelis Bennett J. Varsho Features of safety assessment studies to be considered in assessing thyroid effects of reproduction and their relevance to human health
Jun 09, 2015
WIL Research Laboratories
Joseph F. HolsonContributions By: Mark D. Nemec
Chris P. Chengelis
Bennett J. Varsho
Features of safety assessment studies to be considered in assessing thyroid
effects of reproduction and their relevance to human health
National Toxicology Program
Fucus vesiculosus Seaweed Site© 1995-2003 Michael D. Guiry / Seaweed Site/October 09, 1975
Iodide Concentrating Ability Key to Thyroid Function
Fundamental Key isSymporter Molecule
Phylogenetically as early as Brown Algae – Fucus
Iodide Concentrating Occurs also in Salivary Glands, Gastric Mucosa, Choroid Plexus,
Lactating Mammary Tissue
Symporter Origin and Function
Sodium/Iodide Symporter: Transports I-
Na+/K+ ATPase, Quabain-sensitive system in thyroid plasma membrane vesicles
Rat Symporter: 618 amino acids Human Symporter: 643 amino acids
84% Sequence Identity Iodine transport is against an electrochemical gradient Symporter also expected to be in other mammalian
iodide-concentrating tissues: salivary gland, gastric mucosa, choroid plexus & algae such as Fucus sp.
Wolfe, 1998
Phylogeny
http://www.thyroidmanager.org
*
Endostyle
Ammocoete
Importance of iodide sequestration is ubiquitous in our ancestral tree
Prenatal Developmental Defects of Thyroid
Congenital hypothyroidism may be classified as permanent or transient. The most common cause of CH is iodine deficiency, which can be eradicated by iodine supplementation.
In iodine sufficient regions thyroid dysgenesis is the most common cause. Thyroid dysgenesis presents as
1. Athyrosis (absence of thyroid tissue) 2. Ectopic thyroid or 3. Hypoplasia of thyroid
Thyroid dysgenesis account for about 80 - 90% of infants with CH. Familial dyshormonogenesis occur in 10% in infants with CH. Enzyme defects
that affect the synthesis of T4 and T3 lead to hypothyroidism. Hypothalamo-pituitary dysfunction is the cause of CH in a small number of
infants (5 %). In some infants (10 %) hypothyroidism is transient. Iodine, drugs, maternal
antibodies or transient defect in hormonogenesis can lead to transient hypothyroidism. These infants also need prompt replacement therapy.
Sperling, 1996
Athyrotic Hypothyroidism Sequence
K. Jones in Smith’s Recognizable Patters of Human Malformation, 1988
K. Jones in Smith’s Recognizable Patters of Human Malformation, 1988
After Cao, et al., 1994
Timing of Vulnerability to Iodine Deficiency in Endemic Cretinism
Time of Treatment(Mo. Before Delivery)
No.Head
CircumferenceDQ Height
No. with Mild Neurologic
Abnormality
6 (included in second trimester)
18 -1.5±1.1 88±8 -2.5 ±0.8 0
>6-7 10 -1.9±1.2 77±9 -3.5 ±0.8 1
>7-8 10 -2.8±1.3 76±11 -2.6 ±0.9 1
>8-9 8 -2.6±1.4 77±16 -3.7 ±2.3 2
P Value (6 vs.>6-9 Mo.)
-- 0.02† <0.001† 0.04† 0.20‡
*Head circumference and height are expressed in standard deviations from the U.S. mean for children of the same age; DQ denotes developmental quotient. For neurologic abnormalities, the number with mild abnormality is shown; none of these children had moderate or severe abnormality.
†By Student’s t-test ‡By the chi-square test
Timing of Vulnerability to Iodine Deficiency in Endemic Cretinism
Cao, et al., 1994
Incidence of Athyrosis in Animal Models and Human Newborns Crl:CD(SD)BR Rats (WIL)
0 Thyroid Findings/39,442 Visceral Exams Crl:CD(SD)BR Rats (MTA/MARTA)
0 Thyroid Findings/24,340 Visceral Exams Crl:CD®(SD)IGS BR Rats (WIL)
0 Thyroid Findings/16,824 Visceral Exams Hra:(NZW)SPF Rabbits (WIL)
0 Thyroid Findings/8,936 Visceral Exams Human Newborns
1 in 4,000 Congenital Hypothyroidism in human newborns worldwide Actual reported ranges 1 in 2,000 in Native Americans
to 1 in 20,000 African Americans Thyroid Dysgenesis accounts for 90%;
of these, 1/3 aplastic and 2/3 rudimentary (Kenneth L. Jones, M.D. – Personal Communication, 2003)
Comparison of Overall Spontaneous Malformation Rates in Different Species
Species Mean % Range (%) N
Rat 0.33 0-1.6 9643
Mouse 1.2 0-3 5207
Rabbit 3.2 0-10 4708
Dog 5.5 5.3-5.7 167
Human 4.0 3-9 Multiple Surveys
From Casarett and Doull, Dr. Capen’s Chapter Species Difference in Thyroid Hormone Economy “The greater sensitivity of the rodent thyroid to derangement by
drugs, chemicals, and physiological perturbations also is related to the shorter plasma half-life of thyroxine T4 in rats than in humans due to the considerable differences in the transport proteins for thyroid hormones between these species (Döhler et al., 1979).”
Caution: To demonstrate directly true species differences in sensitivity, the following should be shown:
Internal DoseAUC/Cmax
Response[T3, T4] Δ
Rat is most “successful” of mammals in terms of number and environment
Guideline Developmental (Prenatal) Reproduction Study*
OECDMaternal & Fetal:
None Specified (N.S.)1-G (1983) Adult/Weanling: N.S.
2-G (2001) Weight Only
ICH (1994) Maternal & Fetal: N.S.Fertility: Adult: N.S.
Pre-/Postnatal: Adult/Weanling: N.S.
JMAFF (2001) Maternal & Fetal: N.S.Adult: Weight Only
Weanling: N.S.
EC (1989) Maternal & Fetal: N.S. Seg I/Seg III: Adult/Weanling: N.S.
OPPTS (1998) Maternal & Fetal: N.S. 2-G: Adult/Weanling: N.S.
MHLW (1994) Maternal & Fetal: N.S. Seg I/Seg III: Adult/Weanling: N.S.
Redbook I (1984) Maternal & Fetal: N.S. Adult/Weanling: N.S.
Redbook 2000 Maternal & Fetal: N.S. Adult/Weanling: N.S.
Guideline-Required Thyroid Evaluations for Developmental and Reproductive Toxicity Studies
*Target organs are identified by further study in generation suspected to be affected, but not required transgenerationally
Guideline-Required Thyroid Evaluations for Subchronic and Chronic Toxicity Studies
Agency/ Guideline
Thyroid Weights
Histopathology Hormones
OECD Non-rodents Control and High Dose Animals
If effect suspected
EPA Non-rodents Control and High Dose Animals
If effect suspected
FDA Redbook II
Rodents and Non-rodents
All Animals If effect suspected
MOHW Often on Rodents and Non-rodents
Control and High Dose Animals
If effect suspected
JMAFF Non-rodents Control and High Dose Rodents and All Non-rodents
If effect suspected
1) Class Effects2) SAR3) Physiologic/Pharmacologic Data4) Results from Previous Studies
In our experience, most often from 28- or 90-day studies
Snapshot of Major Toxicologic Studies: 10 Years at CRO - WIL
Study Type Number
SubchronicGeneral Toxicology
777
Chronic/OncoGeneral Toxicology
67
Reproduction 145
Developmental 531
Total 1520 (912 Drugs/608 Chem)
Experience by Agent or Type
Expected and for Validation of EPA DNT Protocol PTU Methimazole
Anticipated Resorcinol Underway, Historical Human-Use Drug – Tetracycline Class Effects Pesticide Replacement Chemical - Iodinated
Unanticipated Drug – Miscrosomal Enzyme Inducer Drug – GABAnergic Agonist Herbicide – Unknown and ceased development 3 Drugs suspected of microsomal enzyme induction
A B C D E F
Premating to Conception
Conception to Implantation
Implantation to Closure of Hard Palate
Hard-Palate Closure to End of Pregnancy
Birth to Weaning Weaning to Sexual Maturity
Parturition Litter Size Landmarks of Sexual DevelopmentGestation Length Pup Viability Neurobehavioral Assessment F1 Mating and Fertility Pup Weight Acoustic Startle Response
Organ Weights Motor Activity Learning & Memory
ParturitionGestation Length Pup Viability Litter SizeLandmarks of Sexual Development Pup WeightNeurobehavioral Assessment Organ Weights Acoustic Startle Response F1 Mating and Fertility Motor Activity Hormonal Analyses Learning & Memory Ovarian QuantificationHistopathology Premature Senescence
Postimplantation LossViable FetusesMalformations & VariationsFetal Weight
Postimplantation LossViable FetusesMalformationsVariationsFetal Weight
Estrous Cyclicity Mating Corpora Lutea Fertility Implantation SitesPre-Implantation Loss Spermatogenesis
Estrous CyclicityMatingFertilityCorpora LuteaImplantation SitesPre-Implantation LossSpermatogenesis
Denotes Dosing Period
Standard Repro/Development Designs
Single- and Multigenerational
Satellite Phase
OECD 415, OECD 416, OPPTS 870.3800, FDA Redbook I, NTP RACB
F1
F2 ????????????????
????????????????
Pre- and Postnatal Development
F1
ICH 4.1.2F0
????????????????
Prenatal DevelopmentICH 4.1.3 OECD 414
OPPTS 870.3600 870.3700
Fertility StudyICH 4.1.110W 2W4W
CMAX
AUC
CMAX
AUC
Basic (EPA) Developmental Neurotoxicity Study Design
Conception to
Implantation
Implantation to Closure of Hard
Palate
Hard-Palate Closure to End of
PregnancyBirth to Weaning
Weaning to Sexual Maturity
Indirect Exposure (Maternal)
Gestational and LactationalGD 6 PND 11 PND 72
10/sex/group for each assessment: PND 4, 11, 21, 35, 45, 62 - FOB PND 20, 60 - Auditory Startle PND 13, 17, 21, 61 - Locomotor Activity PND 22, 62 - Learning and Memory
On PND 11, 10 pups/sex/litter Brain weights From these, 6/sex in control and high dose: Neuropathology, Morphometry
On PND 72, 10 pups/sex/litter Brain weights From these, 6/sex in control and high dose: Neuropathology, Morphometry
Schematic Depiction of Study Design/Exposure Regime of Report by R. Lavado-Autric, et al.,
R. Lavado-Autric, et al., JCI, 2003
M C F1
1M C F1
M C F1
2M C F1
M C F1
3M C F1
M C F1
4
M C F1
= 10 Days of LID + 1% KClO4
M = Mated with Untreated Males
C = Cull on PND 3-4 to 8 Pups/Dam
Euthanize 4 Dams/Subgroup - T4 & T3
Stratal Analysis of Cortical Cell Migration
Group Gestation LactationPre-Breeding Post-weaning
KEY
GD 21
Euthanasia
Immunohistochemistry
PND 21
Weaning
PND 40
Pup Weight
BrdU on GD 14, 15 or 16
BrdU on GD 17, 18 or 19
BrdU on GD 14, 15 or 16
BrdU on GD 17, 18 or 19
BrdU on GD 14, 15 or 16
BrdU on GD 17, 18 or 19
BrdU on GD 14, 15 or 16
BrdU on GD 17, 18 or 193 Months of LID + KI (~10ug I/Day)
3 Months of LID
3 Months of LID + 0.005% KClO4
Untreated Control Group
10 D
10 D
10 D
Comparison of Prenatal and Postnatal Modes of Exposure
Drug Transfer to Offspring
Drug Levels in Offspring
Maternal Blood vs.Offspring Levels
Exposure Route toOffspring
Commentary
Prenatal
Nearly all transferred
Cmax and AUC measured
Maternal often a surrogate
Modulated IV exposure, via placenta
Timing of exposure is critical
Postnatal
Apparent selectivity (“barrier”)
Not routinely measured
Maternal levels probably NOT a good predictor
Oral, via immature GI tract
Extent of transfer to milk and neonatal bioavailability is key to differentiating indirect (maternal) effects from neonatal sensitivity
Prenatal Treatment Postnatal
Embryo/Fetus Placenta Mother Mammae Neonate
Proposed 15-day Intact Male Screening Assay (Currently undergoing multi-lab evaluation)
15 Intact Males/Group
BW & Dose 15 Days
Necropsy & OW following
Last Dosing
Collect Blood for Hormone Analyses
Spectrum of Effects
(10 weeks old)
O’Connor, et al., 1999
Hormonal Fingerprint
Thyroid Agent TDHT
E2
PRL
LH
FSH
TSH
T3
T4
Excretion Enhancer
Synthesis Inhibitor
O’Connor, et al., 1999
Relationship Between Developmentand Phenotypic Diversity
Phenotypic Expression
and Diversity
Time in Development (Age)
EmbryonicPeriod
EmbryonicPeriod
FetalPeriodFetal
PeriodPostnatal
PeriodPostnatal
Period
Extent of Differentiation
BirthBirth
Commentary
Thyroid essential immediately postnatal for thermiogenic shivering providing thermiogenesis
But rarely is cause of death in progeny of reproduction studies established or even investigated
Essential role of thyroid postnatally logically makes a probable contributor to postnatal wastage
The former vulnerability may not be analogous to the human situation Important questions need to be answered relative to the role of
brown adipose fat in different species Interestingly Leptin affected white but not brown adipose tissue
in extensive reproduction studies at WIL Research
Needs for Thyroid Toxicity Assessment
Our ability to detect, demonstrate, validly identify and apply appropriate risk analyses of adverse reproductive effects of anti-thyroidal agents and conditions is dependent on the following: Strong scientific knowledge base of thyroid function Conduct of the appropriate studies, exposure regime
important Utilization of protocols guiding valid measures Appropriate use of experimental models Good risk assessment processes
To do the former for the thyroid in reproductive toxicology, the inherent problems differ little from other arenas of debate in toxicology and risk assessment
Commonalities include: Use of validated models Inter-study (species) comparisons and generalization must be
cognizant of internal dose (exposure) variables Care to make comparisons from studies with equivalent powers In particular with rodents and the thyroid, sensitivity to metabolic
induction (T3 & T4) concomitant with high applied dose (pk issues) studies
Need to ensure study integrity and quality In particular for this instance the validity and sensitivity of several of the
reproductive measures to human reproduction Neonatal adaptation Postnatal exposure via milk vs. human in-utero exposures
Needs for Thyroid Toxicity Assessment (continued)
Summary and Inferences
Review of one CRO’s database indicates that primary guideline-driven detectors of anti-thyroid agents are subchronic toxicity studies
Subclinical hypothyroxinemia-inducing agents may be detected by the former type studies
The recent work by Lavado-Autric, if confirmed in other laboratories and current DNT protocols applied to those findings and are shown to be sensitive to detect to detect such consequences of subclinical hypothyroxinemia, these developmental CNS derangements would represent the most sensitive of hypothyroidal conditions
A somewhat modified two-generation reproductive toxicity study would be the best extant guideline-driven protocol to detect such effects of xenobiotics because of the early and protracted premating exposure regime in conjunction with the extended generational exposure and the addition of the DNT component to the second generation progeny
The thyroid, unlike much of the other endocrine glands functions in a more tonic fashion and is less evaluable from an acute exposure and pathogenesis perspective
Gull WW: On a cretinoid state supervening in adult life in women. Trans Clin Soc London 1874; 7: 180.
“My theory maintains that if the thyroid is impaired, or as in this
instance, removed entirely, then iodine will accumulate in
the female body…causing impairment of the brain with
consequential loss of faculties.
Does not the concept spur you to HUMILITY?
Think of it Acland…less than a thimble full of iodine divides the intellectual from the imbecile.”
“From Hell” Moore & Campbell, 1999
Awareness of Developmental Toxicity of Selected Agents
Agent Year First Reported Species*
Alcohol(ism)
Aminopterin
Cigarette Smoking
Diethylstilbestrol
Heroin/Morphine
Ionizing Radiation
Methylmercury
Polychlorinated Biphenyls
Steroidal Hormones
Thalidomide
1957
1950
1941
1940
1969
1950
1953
1969
1943
1961
(gp), ch, hu, mo, rat
(mo & rat), ch, hu
(rab), hu, rat
(rat), hu, mi, mo
(rat), ha, hu, rab
(mo), ha, hu, rat, rab
(rat), ca, hu, mo
(hu), rat
(monk), ha, hu, mo, rat, rab
(hu), mo, monk, rab
*ca - cat, ch - chicken, ha - hamster, gp - guinea pig, hu - human, mi - mink, mo - mouse, monk - monkey, rat - rat, rab - rabbit
Reasons for Apparent Failed Predictions
Appropriate studies not conducted Incidence of effect too low for experimental
detection Unknown/unstudied type(s) of effect Hypersensitive individuals in human population Interaction of multiple agents Unfounded/nonexistent claims or effects Human exposure is overestimated by
experimental design
Animal:Human Concordance Studies for Prenatal Toxicity
Nisbet & Karch, 1983 Many chemicalsRelied on authors’ conclusionsEmphasis on fertilityNo measures of internal dose
Attributes
Interdisciplinary team Criteria for acceptance of data/conclusionsConcept of multiple developmental toxicology endpoints No measures of internal dose
Authors
Holson et al., 1981 (Tox Forum)Kimmel et al., 1984 (NCTR Report)
Attributes
Interspecies inhalatory doses adjustedRelied on authors’ conclusions23 occupational chemicals and mixtures No measures of internal dose
Provided detailed informationOnly 4 drugsEmphasis on morphologyFocus on NOAELsNo measures of internal dose
Many chemicals and agentsVariably relied on authors’ conclusionsNo measures of internal dose nor criteria for inclusion or exclusion of studies
Authors
Hemminki & Vineis, 1985
Newman et al., 1993
Schardein, 1995 & 2000*
Animal:Human ConcordanceStudies for Prenatal Toxicity
*Misnomer to refer to thousands of experimental developmental toxicants
WIL Recommendations
Dose GD 6 through LD 20 Pre-weaning motor activity: PND 13, 17, 21 No reflex ontogeny Assign 1 pup/sex/litter/test for behavior
(20/sex/group) Behavioral tests performed on same animals for
all but one session of learning and memory Neuropathology after last dose (PND 21) and at
young adulthood (72 days of age) using 10 rats/sex/group, with morphometry at both ages
Figure 14-10. A schematic and integrated representation of the three sets of clinical conditions that may affect thyroid function in mother alone, fetus alone, or both (i. e. the feto-maternal unit), to show how the relative contributions of an impaired maternal and/or fetal thyroid function may eventually lead to alterations in the fetal thyroxinemia during its development. (reproduced from Glinoer & Delange, Ref N° 63, with permission of the authors and the Editor).
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Comparison of Prenataland Postnatal Toxicity Profiles
Toxicity
Log of Dose
Maternal
DevelopmentalDevelopmental
Prenatal – valid and insightful – Embryonic exposure – Mode of action
Postnatal – valid only – when xenobiotic level is measured in both mother and
offspring
ACE Inhibition-Induced Fetopathy (Human)
Organogenesis (classically defined) is unaffected
Effects are severe
Risk is low
Caused by ACEinh that cross placenta
ACEinhFetal
Hypotension
RenalCompromise
(Anuria)Oligohydramnios
Calvarial Hypoplasia
Neonatal Anuria
IUGR
Death
ACE Inhibition in Developing Rats
RAS (renin-angiotensin system) matures around GD17
No ‘apparent’ effect in initial reproductive studies
Subsequent postnatal studies with direct administration to pups
Growth retardation
Renal alterations (anatomic and functional)
Death
Selective Juvenile Toxicity of Quinilones
Drug
Ofloxacin (and other quinilones)
Modified from Stahlmann et al., 1997.
Species &Treatment
Multiple species,postnatal exposure.20 mg/kg (dog, 3 mo.)600 mg/kg (rat, 5 wk)
Effects
Chondrotoxic effects. Cartilage erosion in weight-bearing joints.
Gait alterations in juvenile dogs only.
Remarks
Human relevance unknown; drugs contraindicated in juvenile patients.
Mechanism: Probable deficiency of bioavailable Mg2+ in cartilage (quinilones chelate divalent cations).
No effect in routine segment III studies.
EPA vs. OECD Harmonization Issues Dose GD6 through LD 10 Pre-weaning motor activity: PND
13, 17, 21 No reflex ontogeny
10/sex/group
Neuropathology after last dose using 6 rats/sex/group, with morphometry
Assign 1 pup/litter/test for behavior Behavioral tests performed on
different animals
Dose GD 6 through LD 20 Pre-weaning motor activity: once
before PND 21 Two measures of reflex ontogeny -
i.e., righting reflex, air righting 20/sex/group for all behaviors
except learning and memory - at least 10/sex/group
Neuropathology on PND 11 and optional after last dose using 10 rats/sex/group, tiered approach to morphometry
Assign 1 pup/sex/litter/test for behavior
Behavioral tests performed on same animals for all but one session of learning and memory
Sledgehammer Thyroid Toxicity
Short Ventral Limb of Dentate Gyrus
HypercellularControlPND 11
100 ppm MethimazolePND 11
Figure 15-7. Brain neurologic development relative to thyroid function in the rat and human. TH, thyroid hormones; dpc, days postconception; dpn, days postnatal. (From Porterfield and Hendrich, with permission.)
Figure 15-6. Maturation of thyroid hormone effects in the human fetus and neonate. The left edge of the bars indicate the approximate time the effects of thyroid hormone become manifest (Used with permission from Fisher DA, Polk DH, Wu SY: Fetal thyroid metabolism: a pluralistic system. Thyroid 4:367,1994 ).
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The Symporter
www.colostate.edu
Rat; GD20; Bouin’s Fixed; Wilson’s Sectioning Technique
Rat; GD20; Fresh Dissection Technique
Size: 0.5 to 1 mm
Rat; PND 4; Fresh Dissection Technique
Rat; PND 21; Fresh Dissection Technique