The Toxicologist - Society of Toxicology
The Toxicologist - Society of Toxicology
The Toxicologist - Society of Toxicology
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ats. <strong>The</strong> majority <strong>of</strong> the studies focusing on DEHP toxicity used the oral route <strong>of</strong><br />
administration; however, the human sub-population with the highest exposure to<br />
DEHP is infants being treated in neonatal intensive care units, where exposure is<br />
mainly intravenous. Since DEHP is efficiently hydrolyzed in the gut to its active<br />
metabolite MEHP, the route <strong>of</strong> exposure can have a significant impact on the toxicological<br />
pr<strong>of</strong>ile <strong>of</strong> DEHP. We investigated the effects <strong>of</strong> oral and intravenous (IV)<br />
administration <strong>of</strong> DEHP in the lungs <strong>of</strong> a neonatal male rat model. Following a<br />
modification <strong>of</strong> a study design by Cammack et al. (2003), five-day-old male<br />
Sprague-Dawley rats were dosed either by oral gavage or tail vein injection with 0,<br />
60, 300, or 600 mg DEHP/kg bw/day for 5 or 21 consecutive days. Body weights<br />
were reduced relative to control in pups dosed for 21 days with 600 mg/kg/d<br />
DEHP, independent <strong>of</strong> the route <strong>of</strong> administration. Lung weights were not<br />
changed by any treatment. Five and 21 doses <strong>of</strong> IV, but not oral, 600 mg/kg/d<br />
DEHP caused lung interstitial inflammation and hemorrhage. Multifocal granuloma<br />
centered on capillary emboli were also observed in the alveoli <strong>of</strong> rats treated<br />
with IV, but not oral, DEHP in a dose-responsive manner, with a LOAEL <strong>of</strong> 300<br />
mg/kg/d for 5 doses and 60 mg/kg bw/d for 21 doses. No effects were observed in<br />
testis <strong>of</strong> pups exposed to IV DEHP below 300 mg/kg bw/d for 5 or 21 doses. <strong>The</strong>se<br />
data suggest that IV DEHP is more toxic to the lung than an equivalent oral dose,<br />
and that the lung may be more sensitive to IV DEHP than the testis in the neonatal<br />
rat model. Funded in part by NTP IAG 224-07-0007 between the FDA/NCTR<br />
and the NIEHS/NTP.<br />
618 JUVENILE TOXICITY ASSESSMENT OF<br />
ANIDULAFUNGIN IN RATS.<br />
G. Chmielewski 1 , C. J. Bowman 1 , S. L. Ripp 1 , E. M. Lewis 2 , C. M. Sawaryn 1<br />
and D. M. Cross 3 . 1 Pfizer Inc., Groton, CT, 2 Charles River Laboratories Preclinical<br />
Services, Horsham, PA and 3 Pfizer Inc., Sandwich, United Kingdom.<br />
Anidulafungin (a marketed, non-competitive inhibitor <strong>of</strong> (1,3)-β-D-glucan synthase)<br />
is being evaluated for pediatric treatment <strong>of</strong> fungal infections, including<br />
neonates. Juvenile toxicity studies with anidulafungin were conducted to support<br />
neonatal dosing in the clinic as well as to evaluate long-term safety considerations.<br />
<strong>The</strong> first study was a single dose pilot study administered on Postnatal Day (PND)<br />
7 either intravenously (IV), subcutaneously, or intraperitoneally to Fisher rats to determine<br />
a route <strong>of</strong> administration with exposure most consistent to intravenous infusion<br />
used in the clinic and adult nonclinical studies (not technically feasible in<br />
young rats). Subcutaneous administration was determined the most appropriate<br />
route and was utilized in a subsequent repeat dose range-finding study from PND<br />
4 to 28 at 0, 10, 30, or 60 mg/kg/day. Pups at ≥30 mg/kg/day had reduced body<br />
weights. In satellite animals, anidulafungin was detected in brain, bone, and heart<br />
following a single dose, while plasma exposure on PND 4 and 28 increased in proportion<br />
with dose. In the pivotal juvenile study, rat pups were treated from PND 4<br />
to 62 (followed by a 5 week recovery period) at 0, 3, 10, or 30 mg/kg/day to evaluate<br />
potential liver toxicity (adult rat target organ) and possible permanent effects on<br />
neurological function due to uncertainties associated with the blood brain barrier<br />
development in neonates. Anidulafungin-related effects included slightly reduced<br />
body weights, increased liver weights, and mild decreases in red blood cell mass<br />
with increased reticulocyte counts. <strong>The</strong>re was no liver pathology and in the post<br />
treatment phase there were no effects on neurological function and no lasting effects<br />
on body weight or hematology. In conclusion, the juvenile rat no-adverse-effect-level<br />
(NOAEL) was 30 mg/kg/day (exposures similar to adult rat NOAEL)<br />
suggesting that juvenile rats are not more sensitive than adult rats to anidulafungin<br />
and that there are no permanent changes to neurological function.<br />
619 ORGAN SYSTEM ASSESSMENTS IN JUVENILE DOG<br />
TOXICOLOGY STUDIES.<br />
K. Robinson, H. Penton, S. Y. Smith and M. Adamo. <strong>Toxicology</strong>, Charles River<br />
Preclinical Services, Montreal, QC, Canada. Sponsor: M. Vézina.<br />
For some juvenile toxicology studies the dog is considered the most appropriate<br />
species. To meet regulatory guidances/requests from US FDA and EMA there may<br />
be a need to study the development <strong>of</strong> organ systems, including nervous, cardiovascular,<br />
gastro-intestinal, pulmonary, renal, immune, skeletal (growth) and reproductive,<br />
that develop in the postnatal period. Techniques for assessment <strong>of</strong> the development<br />
<strong>of</strong> many <strong>of</strong> these organ systems are readily available along with historical<br />
control data. However there are limitations in assessing some endpoints in the juvenile<br />
dog. For cardiovascular testing collection <strong>of</strong> direct or indirect blood pressure<br />
and electrocardiographs (ECG) is feasible. Direct assessment <strong>of</strong> blood pressure (BP)<br />
however has only been performed in dogs from 4 months <strong>of</strong> age. Considerations for<br />
this method include the size <strong>of</strong> the transmitter to implant relative to animal size as<br />
well as the BP catheter and ECG lead length to accommodate for rapid growth.<br />
Jacketed external telemetry has been conducted from 2 months <strong>of</strong> age with data<br />
collection for at least 24 hours. Pre-weaning ECG and indirect blood pressure using<br />
a tail cuff can also be performed. Variability is reduced when using direct recording.<br />
A full battery <strong>of</strong> assessments <strong>of</strong> skeletal growth ranging from measurements <strong>of</strong><br />
height and length to imaging (bone densitometry) techniques and histomorphometry<br />
can be applied. For other evaluations, such as <strong>of</strong> the reproduction, the physiology<br />
<strong>of</strong> the dog precludes the conduct <strong>of</strong> meaningful testing. Screens for several systems<br />
such as renal and gastrointestinal are available. In others, such as the nervous<br />
and immune systems, tests such as neurological screens and phenotyping, respectively,<br />
are available. Neurological tests <strong>of</strong> learning and memory and immune function<br />
testing with T-cell dependent antibody response (TDAR) are under development.<br />
In conclusion, screening for effects on most major organ systems is feasible<br />
being mindful that there are limitations for some assessments due to age, test availability<br />
in toxicology laboratories and historical control data.<br />
620 CHEMICAL INTOLERANCE, ATTENTION<br />
DEFICIT/HYPERACTIVE DISORDER AND AUTISM—<br />
A LINK?<br />
L. P. Heilbrun, R. F. Palmer and C. S. Miller. Family Community Medicine,<br />
University <strong>of</strong> Texas Health Science Center at San Antonio, San Antonio, TX. Sponsor:<br />
G. Gould.<br />
Background: Chemical intolerance—the inability to tolerate a wide variety <strong>of</strong><br />
everyday chemical exposures (fragrances, auto exhaust, cleaning compounds,<br />
etc.)—has been associated in numerous studies with multi-system symptoms including:<br />
asthma, chronic fatigue, cognitive and memory problems, etc. <strong>The</strong> primary<br />
objective <strong>of</strong> this study was to investigate the possible association between<br />
chemical intolerance and Attention Deficit/ Hyperactivity Disorder (AD/HD) and<br />
Autism Spectrum Disorder (ASD). Methods: A case-control study was used to test<br />
the hypothesis that mothers <strong>of</strong> children with AD/HD or ASD would score higher<br />
on the Quick Environmental Exposure and Sensitivity Inventory (QEESI©)—a<br />
validated tool for diagnosing chemical intolerance—than mothers whose children<br />
do not have either ASD or AD/HD. Mothers with (n =183) and without (n= 146)<br />
AD/HD children, and mothers with (n=282) and without (n=72) ASD children<br />
participated in separate online surveys. Results: Compared to control mothers, case<br />
mothers had significantly higher mean scale scores for Chemical Intolerance (p <<br />
.001), Other Intolerances (food, drug, caffeine, alcohol etc.) (p=.01), and<br />
Symptoms (p