OECD 414 supplementary prenatal developmental toxicity study of sodium molybdate dihydrate in the rat and benchmark dose evaluation.

In a continuing investigation of the potential for reproductive and developmental toxicity of molybdenum (Mo), consequent to the previous published OECD studies [1,2] and as directed by the European Chemicals Agency [3], a supplemental rat GLP-compliant Prenatal Developmental Toxicity (PNDT) study was conducted to investigate higher dose levels of sodium molybdate dihydrate (SMD) in an identical study design (OECD 414)[4] to Murray et al. 2014a [1], at dietary concentrations calculated to provide target Mo levels of 80 and 120 mg/kg bw/day (the maximum-tolerated dose). There was no effect on post-implantation loss, litter size, sex ratio or the incidence of external, visceral or skeletal fetal malformations or variations. Fetal weight was reduced proportionate to maternal dose. Minimal differences observed in the ossification status of some extremities of fetuses from females receiving 120 mg Mo/kg bw/day were confirmed as transient by skeletal examination of PND 21 pups from a further group of females receiving the same dose regime. There was no evidence of copper depletion in serum, placenta or liver. A benchmark dose evaluation using continuous and dichotomous approaches by combining the fetal body weight data from this study and the previous study determined that the BMD05 ranged from 47 to 57 mg Mo/kg bw/day, depending on the modelling approach and the BMDL05 estimates ranged from 37 to 47 mg Mo/kg bw/day. These levels are considered a more statistically robust point of departure for risk assessment for reproductive effects than the established NOAEL of 40 mg Mo/kg bw/day.

Toward a comparative retrospective analysis of rat and rabbit developmental toxicity studies for pharmaceutical compounds.

Based on a proposal made at the ICH Workshop in Tallinn, Estonia (2010), the value of the rabbit embryo-fetal development (EFD) versus the rodent EFD was examined by the HESI DART group. A cross-industry data survey provided anonymised EFD and toxicokinetic data from EFD studies on over 400 marketed and unmarketed drugs (over 800 studies) that were entered by experts at RIVM into US EPA's ToxRefDB style database. The nature and severity of findings at the lowest observed adverse effect level (LOAEL) are being reviewed to quantitate the frequency with which lesser signs of embryo-fetal effects (e.g., delays in ossification, minor changes in frequency of variants) are driving the LOAELs. Interpretation was based on exposure rather than administered dose. This paper provides an update of this ongoing project as discussed during a workshop of the European Teratology Society in Ispra, Italy (2013). This was the first presentation of the initial data set, allowing debate on future directions, to provide a better understanding of the implications of either delaying a rabbit EFD or waiving the need in particular circumstances.

Oral (drinking water) two-generation reproductive toxicity study of dibromoacetic acid (DBA) in rats.

In a two-generation study of dibromoacetic acid (DBA), Crl SD rats (30 rats/sex/group/generation) were provided DBA in drinking water at 0 (reverse osmosis-deionized water), 50, 250, and 650 ppm (0, 4.4 to 11.6, 22.4 to 55.6, and 52.4 to 132.0 mg/kg/day, respectively; human intake approximates 0.1 microg/kg/day [0.0001 mg/kg/day]). Observations included viability, clinical signs, water and feed consumption, body and organ weights, histopathology, and reproductive parameters (mating, fertility, abortions, premature deliveries, durations of gestation, litter sizes, sex ratios and viabilities, maternal behaviors, reproductive organ weights, sperm parameters and implantation sites, sexual maturation). Histopathological evaluations were performed on at least 10 P and F1 rats/sex at 0 and 650 ppm (gross lesions, testes, intact epididymis; 10 F1 dams at 0, 250, and 650 ppm for primordial follicles). Developmental observations included implantations, pup numbers, sexes, viabilities, body weights, morphology, and reproductive performance. At 50 ppm and higher, both sexes and generations had increased absolute and relative liver and kidneys weights, and female rats in both generations had reduced absolute and relative adrenal weights; adrenal changes were probably associated with physiological changes in water balance. The livers and kidneys (10/sex/group/generation) had no histopathological changes. Other minimal effects at 50 ppm were reduced water consumption and a transient reduction in body weight. At 250 and 650 ppm, DBA reduced parental water consumption, body weight gains, body weights, feed consumption, and pup body weights. P and F1 generation male rats at 250 and 650 ppm had altered sperm production (retained step 19 spermatids in stages IX and X tubules sometimes associated with residual bodies) and some epididymal tubule changes (increased amounts of exfoliated spermatogenic cells/residual bodies in epididymal tubules, atrophy, and hypospermia), although inconsistently and at much lower incidences. Unilateral abnormalities of the epididymis (small or absent epididymis) at 650 ppm in four F1 generation male rats were considered reproductive tract malformations. The no-observable-adverse-effect level (NOAEL) and reproductive and developmental NOAELs for DBA were at least 50 ppm (4.5 to 11.6 mg/kg/day), 45,000 to 116,000 times the human adult exposure level. Reproductive and developmental effects did not occur in female rats exposed to DBA concentrations as high as 650 ppm. Based on the high multiples of human exposure required to produce effects in male rats, DBA should not be identified as a human reproductive or developmental risk.

Oral (drinking water) two-generation reproductive toxicity study of bromodichloromethane (BDCM) in rats.

Bromodichloromethane (BDCM) was tested for reproductive toxicity in a two-generation study in CRL SD rats. Thirty rats/sex/ group/generation were continuously provided BDCM in drinking water at 0 (control carrier, reverse osmosis membrane-processed water), 50,150, and 450 ppm (0, 4.1 to 12.6, 11.6 to 40.2, and 29.5 to 109.0 mg/kg/day, respectively). Adult human intake approximates 0.8 microg/kg/day (0.0008 mg/kg/day). P and F1 rats were observed for general toxicity (viability, clinical signs, water and feed consumption, body weights, organ weights [also three weanling Fl and F2 pups/sex/litter], histopathology [10/sex, 0- and 450-ppm exposure groups]) and reproduction (mating, fertility, abortions, premature deliveries, durations of gestation, litter sizes, sex ratios, viabilities, maternal behaviors, reproductive organ weights [also three weanling Fl and F2 pups/sex/ litter], sperm parameters, and implantations. F1 rats were evaluated for age at vaginal patency or preputial separation. Ten P and F1 rats/sex from the 0- and 450-ppm exposure groups and rats at 50 and 150 ppm with reduced fertility were evaluated for histopathology (gross lesions, testes, intact epididymis, all F1 dams for number of primordial follicles). Developmental parameters in offspring included implantation and pup numbers, sexes, viabilities, body weights, gross external alterations, and reproductive parameters (Fl adults). Toxicologically important, statistically significant effects at 150 and/or 450 ppm included mortality and clinical signs associated with reduced absolute and relative water consumption, reduced body weights and weight gains, and reduced absolute and relative feed consumption (P and F1 rats). Significantly reduced body weights at 150 and 450 ppm were associated with reduced organ weights and increased organ weight ratios (% body and/or brain weight). Histopathology did not identify abnormalities. Small delays in sexual maturation (preputial separation, vaginal patency) and more Fl rats with prolonged diestrus were also attributable to severely reduced pup body weights. Mating, fertility, sperm parameters, and primordial ovarian follicular counts were unaffected. The no-observable-adverse-effect level (NOAEL) and the reproductive and developmental NOAELs for BDCM were at least 50 ppm (4.1 to 12.6 mg/kg/day), 5125 to 15,750 times the human adult exposure level, if delayed sexual maturational associated with severely reduced body weights is considered reproductive toxicity. If considered general toxicity, reproductive and developmental NOAELs for BDCM are greater than 450 ppm (29.5 to 109.0 mg/kg/day), or 36,875 to 136,250 times the human adult exposure level. Regardless, these data indicate that BDCM should not be identified as a risk to human reproductive performance or development of human conceptuses.

Oral (drinking water) developmental toxicity studies of bromodichloromethane (BDCM) in rats and rabbits.

Crl:CD(SD)IGS BR VAF/Plus (Crl SD) rats and Hra(NZW) SPF rabbits were tested for potential developmental toxicity from bromodichloromethane (BDCM) provided continuously in the drinking water during gestation (gestation days [GDs] 6 to 21 in rats and GDs 6 to 29 in rabbits). Concentrations of 0, 50, 150, 450, or 900 ppm of BDCM were used for rats; 0, 15, 150, 450, or 900 ppm were used for rabbits (in dose range-finding studies, 1350 ppm was excessively maternotoxic to both species). Investigated maternal parameters included viability, clinical signs, water and feed consumption, and body weights. Maternal gross lesions, gravid uterine weights, abnormal placentas, and numbers of corpora lutea, implantation sites, live and dead fetuses, and early and late resorptions were observed at time of Caesarean sectioning (GD 21 in rats; GD 29 in rabbits). Body weights, sex ratios, and morphological abnormalities (external, soft tissue, and skeletal) were noted in the fetuses. Mean consumed doses of BDCM were calculated to be 0, 2.2, 18.4, 45.0, or 82.0 mg/kg/day for the rats, and 0, 1.4, 13.4, 35.6, or 55.3 mg/kg/day for the rabbits (approximate human intake is 0.8 microg/kg/day [0.0008 mg/kg/day] in adults). In pregnant rats, toxicologically important, statistically significant effects included reduced absolute (g/day) and relative (g/kg/day) water consumption values at > or =50 ppm (2.2 mg/kg/day) and reduced body weight gains (also when corrected for gravid uterine weight) and absolute (g/day) and relative (g/kg/day) feed consumption values at >450 ppm (45.0 mg/kg/day). These parameters were also significantly reduced at > or =450 ppm (35.6 mg/kg/day) in pregnant rabbits (significant weight loss occurred in the rabbits at 900 ppm, i.e., 55.3 mg/kg/day). Thus, the maternal no-observable-adverse-effect level (NOAEL) for BDCM was 150 ppm, i.e., 18.4 and 13.4 mg/kg/day in rats and rabbits, respectively. No adverse effects on embryofetal viability, growth, sex ratio, gross external, soft tissue, or skeletal morphology occurred at 900 ppm in rats or rabbits. Minimal delays in the ossification of forepaw phalanges and hindpaw metatarsals and phalanges occurred in rat fetuses at 900 ppm; delays were considered marginal, reversible, and associated with severely reduced maternal weight gain. Therefore, the developmental NOAEL for rats was 450 ppm (45.0 mg/kg/day), whereas in rabbits it was 900 ppm (55.3 mg/kg/day). These NOAELs are 56,250 and 69,120 times the human adult exposure level of 0.0008 mg/kg/day, respectively. Based on the results of these studies, BDCM should not be identified as a risk to development of human conceptuses.

Biodisposition of dibromoacetic acid (DBA) and bromodichloromethane (BDCM) administered to rats and rabbits in drinking water during range-finding reproduction and developmental toxicity studies.

Dibromoacetic acid (DBA) and bromodichloromethane (BDCM), by-products of chlorine disinfection of water, were provided in drinking water in range-finding reproductive/developmental toxicity studies (rats) and a developmental toxicity study (BDCM) in rabbits. Studies included absorption and biodisposition of DBA and BDCM, including passage into placentas, amniotic fluid, fetuses (rats and rabbits), or milk (rats). The DBA and BDCM range-finding reproductive/developmental toxicity studies each included 50 Sprague-Dawley rats/sex/group. DBA (0, 125, 250, 500, or 1000 ppm) or BDCM (0, 50, 150, 450, or 1350 ppm) was provided in drinking water 14 days premating through gestation and lactation (63 to 70 days). The developmental toxicity range-finding study included 25 time-mated New Zealand white rabbits/group given 0, 50, 150, 450, or 1350 ppm BDCM in drinking water on gestation days (GDs) 6 through 29. Satellite groups (6 male, 17 female rats/group/study and 4 rabbits/group) were used for bioanalytical sampling. Rats and rabbits had exposure-related reduced water consumption caused by apparent taste aversion to DBA or BDCM, especially in the parental animals at the two highest exposure levels (500 and 1000 ppm DBA; 450 and 1350 ppm BDCM). Female rats consumed slightly higher mg/kg/day doses of DBA than male rats, especially during gestation and lactation; weanling rats consumed the highest mg/kg/day doses. DBA produced detectable and quantifiable concentrations in plasma, placentas, amniotic fluid, and milk. Plasma samples confirmed that rats drink predominately during the dark; this drinking pattern, not accumulation, produced detectable plasma concentrations for 18 to 24 hours/day. No quantifiable concentrations of BDCM occurred in plasma, placentas, amniotic fluid, or milk, suggesting that BDCM is rapidly degraded or metabolized in vivo. DBA (500 and 1000 ppm, rats) and BDCM (450 and 1350 ppm, rats and rabbits) produced secondary toxicity in the parental generation by reducing water consumption, which caused severe exposure-related apparent dehydration, reduced feed intake and weight gain. Reproductive and developmental parameters were essentially unaffected (mating possibly reduced [DBA at 1000 ppm]; exposure-related decreases in body weights of pups secondary to reduced water and feed consumption [DBA at 250, 500, and 1000 ppm; BDCM at 150, 450, and 1350 ppm]). No effects on development of rabbit fetuses occurred at BDCM concentrations as high as 1350 ppm. Results from these preliminary studies, in which DBA and BDCM were provided in the drinking water at concentrations thousands of times higher than those to which humans are exposed, suggest that neither DBA nor BDCM are reproductive/developmental risks for humans.

Developmental toxicity study of pentachlorophenol in the rabbit.

The potential for developmental toxicity of pentachlorophenol (penta) was studied in New Zealand white rabbits at doses of 0 (corn oil), 7.5, 15, and 30 mg/kg/day administered by gavage on days 6 to 18 of gestation. The rabbits were sacrificed on day 29 of presumed gestation and necropsied. Measurements included number of corpora lutea, pregnancy, number and distribution of implantations, early and late resorptions, live and dead fetuses, fetal weight, gender, and gross external, soft tissue, and skeletal alterations. The mid and high doses reduced maternal body weight gain; the high dose caused transient weight loss and reduced feed consumption. There were no effects on embryofetal development at any of the doses evaluated. Based on these data, the maternal no-observable-adverse-effect level (NOAEL) is 7.5 mg/kg/day, while the developmental NOAEL is 30 mg/kg/day. Penta is not a developmental toxicant in a nonrodent animal model.

A study of the developmental toxicity potential of pentachlorophenol in the rat.

Pentachlorophenol (penta, CAS #87-86-5) is primarily used as a wood preservative. As part of the USEPA pesticide reregistration process, the developmental toxicity (embryo-fetal toxicity and teratogenic potential) of commercially available penta was studied following oral gavage to presumed pregnant female Sprague-Dawley rats (Crl:CD BR VAF/Plus Subdivision F, 83-3). Both study design and penta purity met the requirements of the USEPA. Doses of 0 (corn oil), 10, 30, and 80 mg/kg/day were administered to the rats at concentrations of 0, 2, 6, and 16 mg/ml, respectively from day 6 to day 15 of presumed gestation. The dosage volume was 5 ml/kg, adjusted on each day of dosage based on individual body weights recorded immediately before intubation. The rats were sacrificed on day 20 of presumed gestation and necropsied. The number of corpora lutea in each ovary was recorded. The uterus was examined for pregnancy, number and distribution of implantations, early and late resorptions and live and dead fetuses. Each fetus was weighed, sexed, and examined for gross external, soft tissue and skeletal alterations. The no-observable-adverse-effect-level (NOAEL) for maternal toxicity in rats was determined to be 30 mg/kg/day of penta. The developmental NOAEL for penta in rats was also found to be 30 mg/kg/day. The lowest-observable-adverse-effect-level (LOAEL) for penta developmental toxicity (80 mg/kg/day) was associated with increased resorptions, reduced live litter size and fetal body weights, and caused increased malformations and variations. These NOAELs, derived using USEPA approved study designs, are higher than those previously reported using penta that is no longer commercially available in studies with non-approved experimental designs. Penta should not be identified as a selective developmental toxicant in the rat because adverse effects on development of rat conceptuses occurred only at maternally toxic dosages.

Lack of selective developmental neurotoxicity in rat pups from dams treated by gavage with chlorpyrifos.

Pregnant Sprague-Dawley rats were given chlorpyrifos (O:, O-diethyl-O:-[3,5,6-trichloro-2-pyridinyl] phosphorothioate; CPF) in corn oil by gavage from gestation day 6 (GD 6) through lactation day 10 (LD 10) at dosages of 0, 0.3, 1, or 5 mg/kg/day in a developmental neurotoxicity study that conformed to U.S. Environmental Protection Agency 1991 guidelines. GD 0 was the day when evidence of mating was observed and postnatal day 0 (PND 0) was the day of birth. Toxicity was limited to the highest dosage level (5 mg/kg/day) and, in the dams, consisted of muscle fasciculation, hyperpnea, and hyperreactivity. A nonsignificant overall trend toward weight gain and feed consumption was also observed in the high-dosage dams, with a statistically significant Group x Time interaction for reduced weight gain in the 5-mg/kg/day group near the end of gestation. Although many developmental indices were normal, pups from high-dosage dams had increased mortality soon after birth, gained weight more slowly than controls, and had several indications of slightly delayed maturation. The early deaths and delayed maturation were attributed to maternal toxicity, though a possible contributing role of direct pup toxicity in delayed development cannot be eliminated. In spite of the apparent delay in physical development, high-dosage pups tested just after weaning had normal learning and memory as tested on a T-maze spatial delayed-alternation task. Habituation, a primitive form of learning, was tested in 2 tasks (motor activity and auditory startle) and was not affected. No overt effects were noted in either dams or pups at 1 or 0.3 mg/kg/day. Based on these data, chlorpyrifos produced maternal and developmental toxicity in the 5-mg/kg/day-dosage group. There was no evidence of selective developmental neurotoxicity following exposure to chlorpyrifos.

Lack of effects of nose-only inhalation exposure on testicular toxicity in male rats.

Reductions in testicular mass, sperm motility, and mating frequency have been attributed to the stresses caused by confinement of Sprague-Dawley male rats in nose-only inhalation exposure tubes. Testicular changes, including an increase in testicular atrophy, have been detected at an increased incidence in male rats used in inhalation studies as compared with rats of the same age and strain used in oral toxicity studies. This study was designed to determine whether nose-only exposure of male rats caused testicular toxicity under conditions of cooling of the exposure room and appropriate acclimation to the exposure tubes. In order to acclimate the rats to the nose-only inhalation exposure apparatus, all male rats were placed in the exposure tubes for at least four successively increasing time intervals (15, 30, 45, and 60 min) on 4 separate days, with a rest period of approximately 48 h between the first and second acclimation. Twenty male rats were exposed nose-only to filtered air for approximately 2 h per day for 28 days before cohabitation and continuing throughout a 14-day cohabitation period. To reduce thermal stress, the exposure room temperature was maintained at 64 to 70 degrees F. Twenty control rats were housed in the same room as the exposed rats but were not placed in exposure tubes. End points monitored were body weight, testicular weight, sperm count, sperm motility, and histopathology of the testes, epididymides, prostate, and seminal vesicles. The control rats gained weight more rapidly than the exposed rats. All the rats in both groups mated successfully, and testicular weights, normalized to body weight, were similar for both groups. More importantly, there were no microscopic changes that could be considered an adverse effect on the reproductive tissues in the male rats placed in exposure tubes. Thus, nose-only exposure for up to 2 h per day for a total of 42 days did not cause adverse effects on the reproductive organs, fertility, or reproductive performance of male rats under the conditions of this study.

Lack of developmental neurotoxicity of MN rgp 120/HIV-1 administered subcutaneously to neonatal rats.

The potential for neurotoxic effects was evaluated in rat off-spring after exposure in utero and/or during the neonatal period to a recombinant subunit vaccine of gp120 prepared from the MN strain of HIV-1 (MN rgp 120/HIV-1). Thirty pregnant female rats were given MN rgp120/HIV-1 with alum adjuvant, and 30 rats were given vehicle, once every 3 days from Day 1 of presumed gestation until parturition. One pup/sex/litter from treated and control group dams were given a daily subcutaneous injection, from Day 1 through Day 22 postpartum (PP) of vehicle, MN rgp120/HIV-1, MN rgp120/HIV-1 with alum, or MN rgp120/HIV-1 with QS-21 adjuvant. Neurobehavioral and physical development were evaluated (preweaning reflex and development, sexual maturation, motor activity, acoustic startle, passive avoidance, functional observational battery, and water M-maze testing), and tissues were processed for anatomical examination (whole and regional brain weights, and neuropathology). Administration of MN rgp120/HIV-1, with or without adjuvant, to pups did not cause any persistent effect on any parameter evaluated. Neurohistological examination did not reveal any pathological effects related to treatment. Thus, MN rgp120/HIV-1 alone or formulated as a vaccine does not cause neurotoxicity or developmental toxicity in neonatal rats after exposure in utero and/or during the neonatal period.

Developmental toxicity studies of four fragrances in rats.

Four fragrances, 6-acetyl-1,1,2,4,4,7-hexamethyltetraline (AHTN), 1,3,4,6,7,8-hexahydro-4,6,6,7,8,8-hexamethylcyclopenta-gamma-2-ben zopyran (HHCB), musk ketone and musk xylene were tested for developmental toxicity in Sprague-Dawley rats (25/group, 3 groups/fragrance, 2 fragrances/corn oil control). Dosages tested were HHCB: 50, 150, 500 mg/kg per day; AHTN: 5, 15, 50 mg/kg per day; musk ketone: 15, 45, 150 mg/kg per day; musk xylene: 20, 60, 200 mg/kg per day. All dosages tested exceeded multiples of the estimated maximal daily human dermal exposure. Treatment (gavage, 5 ml/kg) occurred on GDs 7-17 and Caesarean-sectioning on GD 20. Based on the results of these studies, none of the four fragrances tested were more toxic in the conceptuses than in the dams. Maternal NOAELs were 50, 5, 15 and 20 mg/kg per day for HHCB, AHTN, musk ketone and musk xylene, respectively (150, 50, 45 and 60 mg/kg per day caused clinical signs and reduced weight gain and feed consumption). Developmental NOAELs were 150, 50, 45 and 200 mg/kg per day for HHCB, AHTN, musk ketone and musk xylene, respectively. No adverse effects on embryo-fetal viability, growth or morphology occurred at the highest dosages of AHTN (50 mg/kg per day) or musk xylene (200 mg/kg per day). Developmental toxicity occurred at the high-dosages of HHCB (axial skeletal malformations at 500 mg/kg per day) and musk ketone (increased postimplantation loss and reduced fetal body weight at 150 mg/kg per day). The results of this study indicate that under conditions of normal use, the tested fragrances do not pose a risk to human conceptuses.

Effect of dietary optimization on growth, survival, tumor incidences and clinical pathology parameters in CD Sprague-Dawley and Fischer-344 rats: a 104-week study.

Controversy regarding the use of ad libitum feeding in chronic rodent toxicity studies will soon result in issue of a FDA Points to Consider document. Caloric intakes are now recognized to be important uncontrolled variables in bioassays because rodents chronically fed ad libitum become obese, reproductively senile and have increased incidences of age-related diseases, higher tumor burdens and decreased survival. The available literature suggests that ad libitum feeding neither optimizes the health and well-being of rodents nor provides the best model for use in evaluation of pharmacological and toxicological profiles. Use of an optimized diet, restricted in terms of caloric intakes, has been proposed for chronic toxicity and carcinogenicity studies in rodents. It is suggested that limiting caloric intakes to 50-80% of ad libitum consumption would result in lower body weights, decreased tumor incidences and prolonged survival in the controls. To evaluate the influence of diet on chronic toxicity and carcinogenicity studies in rats, two 104-week studies were conducted. These studies consisted of 280 CD Sprague-Dawley and 280 Fischer-344 rats fed ad libitum, and 140 CD Sprague-Dawley and 140 Fischer-344 rats fed a diet that was optimized by limiting caloric intakes by 15-35%. Both diets consisted of certified commercial diet in meal form. The optimized diet reduced weight gain approximately 50% after 100 weeks. Clinical chemistry and hematology parameters showed negligible effects of reduced diet, with the exception that serum triglycerides were lower in males and females in both strains at weeks 52 and 104. The ad libitum-fed animals had a higher incidence of pseudopregnancy, aggressiveness, foot sores and abscesses than the animals fed an optimized diet. These effects were more pronounced in the CD Sprague-Dawley rats than in the Fischer-344 rats. At the completion of the 104-week study, survival in the ad libitum fed CD Sprague-Dawley rats was approximately one-half that of the animals fed an optimized diet (39% versus 76%). The difference in survival between Fischer-344 rats fed ad libitum and those fed an optimized diet was less pronounced (78% versus 89%). A reduced incidence of palpable tissue masses in the ad libitum-fed CD Sprague-Dawley rats versus the animals fed an optimized diet reflected inability to detect small masses in the obese ad libitum-fed animals. In contrast, the leaner Fischer-344 ad libitum-fed animals had an increased incidence of palpable tissue masses. After 52 weeks, 40 animals from each strain and feeding regimen were killed and subjected to complete necropsy and histopathological examination; the remainder of the survivors was examined at the completion of the study (104 weeks). Use of an optimized diet substantially reduced the incidences of endocrine-mediated tumors in both rat strains and delayed the onset of leukemia in Fischer-344 rats. These results indicate the need to further investigate the relationship of increased caloric intakes and endocrine-mediated or strain specific tumors and support FDA's and others' positions that use of diet optimization in chronic toxicity and carcinogenicity rodent bioassays has the potential to remarkably improve the scientific quality and relevance of these studies. It also identified that the small increases in cost associated with diet optimization are far exceeded by the advantages of increased survival of animals, reduced intercurrent disease and rumor burdens, and increased ease of histopathological processing and evaluation.

Variability in the uterotrophic response assay (an in vivo estrogenic response assay) in untreated control and positive control (DES-DP, 2.5 microG/kg, bid) Wistar and Sprague-Dawley rats.

Inclusion of biological outlier values was found to bias the results of rat uterotrophic assays towards false negatives, i.e., not identify uterotrophic effects in treated populations. The present investigation was conducted to identify the background variability in the rat uterotrophic assay and to evaluate the need to exclude biological outlier values in untreated control groups. The Styrene Steering Committee (SSC) of the European Chemical Industry Council (CEFIC) co-sponsored this work with Argus Research Laboratories (Argus). The rat uterotrophic response assay originally was used as a pharmacology screen to identify estrogenic agents. Classically, 5 to 10 immature female rats (18 to 22 days of age) are administered an agent for three or four days. At sacrifice on the following day (21 to 26 days of age), the uterus is removed, weighed and a uterine weight/terminal body weight ratio calculated. This in vivo assay has been adapted for use in identifying the potential estrogenicity of chemicals, generally using 10 immature female rats per group, more closely controlling the ages, and adding one or more positive control groups to demonstrate sensitivity and response of the test system. Statistically significant increases in the positive control group means for absolute and relative uterine weights, as compared with the untreated (or vehicle-treated) means, is generally interpreted as identifying a sensitive test system. The untreated (and/or vehicle-treated) control group is then compared with the various test groups, and statistically significant increases in the mean absolute and relative uterine weights are identified as evidence of estrogenicity of the agent. Although not fully described previously, the inherent biological variability existing in both untreated and treated animals, can confound interpretation of the data, especially when numbers are relatively small. Our laboratories have identified that under controlled GLP-compliant conditions, some Wistar rats [randomly assigned (weight-ordered) to groups of ten at 22 +/- 1 days of age, and sacrificed when 26 +/- 1 days of age] in untreated control groups have high relative uterine weights that skew data distributions such that statistically significant differences are not present between untreated control and positive control groups. Based on these observations, further evaluations of untreated control and positive control (DES-DP, 2.5 micrograms/kg, b.i.d.) populations of three rat strains [Wistar--Chbb:THOM-SPF, Wistar--Crl:(WI)BR and Sprague-Dawley--Crl:CD(SD)IBS BR VAF/Plus "International Genetic Standard"] were made to define when such normal findings should be considered biological outliers, and whether outlier values should be excluded from analyses. Our data indicate that body weight is not always predictive of uterine weight, that relative uterine weight outlier values occur in each of these rat strains, and that statistically significant differences exist between groups of untreated control animals when outlier values are included in analyses. Of 98, 60 and 60 untreated control rats in the three respective strains, 11 (11.2%), 16 (26.7%) and 15 (25.0%) had relative uterine weights > or = 0.150%, and 5 (5.1%), 4 (6.7%) and 9 (15.0%) of these rats had relative uterine weights > or = 0.200%, values within the positive control range. All positive control rats attained relative uterine weights > or = 0.100%. Of 50, 60 and 60 positive control rats in the three respective rat strains, 27 (54%), 47 (78.3%) and 36 (60%) had relative uterine weights > or = 0.200%, 9 (18%), 2 (3.3%) and 7 (11.7%) had relative uterine weights > or = 0.300% and 5 (10%), 1 (1.7%) and 3 (5%) had relative uterine weights > or = 0.400%. The incidences of relative uterine weights > or = 0.300% in the positive control group may indicate the presence of high responders. Histological evaluations of uteri of positive control rats and untreated control rats with relative uterine weights > or = 0.

Estrogen modulation: tiered testing for human hazard evaluation. American Industrial Health Council, Reproductive and Developmental Effects Subcommittee.

Recent concerns about the potential of certain chemicals to modulate estrogen-regulated processes have led to questions as to how chemicals should be tested for such effects. Therefore, AIHC has developed a comprehensive, resource-efficient, and flexible tiered strategy for estrogen modulation (EM) testing. Levels of evaluation include Tier 0, in which exposure, along with alerts based on structure-activity, persistence, bioaccumulation, and other data, are assessed to prioritize chemicals for preliminary testing. In Tier I, short term in vitro, ex vivo, and/or in vivo assays are used to obtain a preliminary indication of EM potential. Among these, an in vivo response assay is considered the most reliable at this time. However, none of these tests are intended for risk assessment, but rather to aid in choosing chemicals for further testing and in guiding the extent of that testing. Tier II is aimed at risk assessment and involves whole animal tests that contain EM-sensitive end points (e.g., two-generation reproduction study). Tier III consists of hypothesis-driven research reserved for situations where targeted research can reduce levels of uncertainty. This tiered approach provides a framework for the strategic and effective application of EM test methods to address specific information needs on a case by case basis.

Developmental toxicity of Exell, a surfactant mixture, in rats and rabbits.

A surfactant mixture (C.A.S No. 104559-06-2), is used in combination with foliar-acting herbicides to improve herbicidal performance by increasing plant uptake. It was administered by gavage as an aqueous solution to groups of 25 assumed pregnant Crl:CD BR rats from days 7-16 of gestation at daily dosage levels of 0, 3, 8, 20 or 50 mg/kg body weight. The dams were euthanized on Day 22 of gestation and the offspring were weighed and examined for external, visceral, and skeletal alterations. The surfactant mixture was maternally toxic at levels of 20 mg/kg/day and above as evidenced by reduced maternal weight gain and by an increased incidence of lung noise (wheezing and/or rattling) and sneezing. In addition, maternal food consumption was reduced in the high dosage group. There was no evidence of developmental toxicity at any dosage level. In the rabbit study, groups of 20 artificially inseminated adult Hra:(NZW)SPF rabbits were similarly dosed from Days 6-18 of gestation at daily dosage levels of 0, 12, 35, or 100 mg/kg body weight. The dose were euthanized on Day 29 of gestation and the offspring were weighed and examined for external, visceral, and skeletal alterations. Dosages of 35 and 100 mg/kg/day resulted in reduced maternal body weight gain, food consumption and fetal body weight. Thus, in the rat, the maternal and developmental no-observed-adverse-effect levels (NOAELs) were 8 mg/kg/day and greater than 50 mg/kg/day, respectively. In the rabbit, the maternal and developmental NOAELs were 12 mg/kg/day. This surfactant mixture was, therefore, not demonstrated to be uniquely toxic to either the rat or rabbit conceptus.

Reproductive effects of chronic administration of murine interferon-gamma.

Daily subcutaneous doses of 0.02, 0.2, or 2 mg/kg/d of recombinant murine interferon-gamma (rmuIFN-gamma) were given to mice on postnatal days 8 through 60 to determine effects on maturation, behavioral/ functional development, and reproductive capacity. Male mice receiving 2 mg/kg/d rmuIFN-gamma had delayed sexual maturation, reduced epididymal and testes weights, reduced sperm count and concentration, and sperm abnormalities (crimped flagellum). Mating performance and fertility were also reduced in the absence of altered histopathology of the testes. Males given 0.2 and 2 mg/kg/d had swelling and ulcerative dermatitis around the urogenital area, which were observed after sexual contact and attributed to a bacterial infection. Motor activity (time spent in movement) was decreased in all mice receiving 2 mg/kg/d. No microscopic changes observed in any organs were attributed to rmuIFN-gamma administration.

Developmental toxicity study of clarified slurry oil (CSO) in the rat.

Pregnant CD rats were exposed dermally to 0.05, 1, 10, 50, and 250 mg/kg/day of Clarified Slurry Oil (CSO) on Days 0-19 of gestation to determine its potential developmental toxicity. Untreated and vehicle controls were included in the study. Day 20 of gestation Caesarean-derived fetuses were examined for gross, external, and visceral or skeletal alterations. Dosages of 1 mg/kg/day and higher significantly decreased maternal body weight, body weight gain, feed consumption, gravid uterine weight, and live litter size and significantly increased resorption rate. These dosages also significantly reduced fetal weights and retarded development of the brain, kidney, thoracic and caudal vertebrae, metacarpals, and hindpaw phalanges in dosage groups with live fetuses (high dosage group dams resorbed all conceptuses). The 50- and 250-mg/kg/day dosage group dams had only placentas and/or dark red viscous fluid in the uterus or vagina and significant body weight loss (associated with resorption). The highest dosage also caused emaciation, slight dehydration, and swollen dark anogenital areas. These results indicate that CSO produces adverse developmental effects at maternally toxic dosages. The maternal and developmental NOAELs (no observed adverse effect levels) were 0.05 mg/kg/day. In a second study, groups of 10 mated female rats were exposed to "pulse" exposures and dosages of 1, 50, or 250 mg/kg/day of CSO applied dermally for 2- or 3-day intervals that spanned the gestation period. All dosages reduced maternal feed consumption and body weight gain during the treatment period. Dosages of 50 and 250 mg/kg/day also produced early resorptions when administered on Days 6 through 8 and 9 through 11 of gestation. However, no increase in fetal alterations occurred, indicating that the effects on embryo-fetal development were due to early death and not to the death of malformed conceptuses.

Interactive developmental toxicity of radiofrequency radiation and 2-methoxyethanol in rats.

Concurrent exposures to chemical and physical agents occur in the workplace; exposed workers include those involved with the microelectronics industry, plastic sealers, and electrosurgical units. Previous animal research indicates that hyperthermia induced by an elevation in ambient temperature can potentiate the toxicity and teratogenicity of some chemical agents. We previously demonstrated that combined exposure to radiofrequency (RF; 10 MHz) radiation, which also induces hyperthermia and is teratogenic to exposed animals, and the industrial solvent, 2-methoxyethanol (2ME), produces enhanced teratogenicity in rats. The present study replicates and extends the previous research investigating the enhanced teratogenicity of combined RF radiation and 2ME exposures. The interactive dose-related teratogenicity of RF radiation (sham exposure or maintaining colonic temperatures at 42.0 degrees C for 0, 10, 20, or 30 min) and 2ME (0, 75, 100, 125, or 150 mg/kg) was investigated by administering various combinations of RF radiation and 2ME to groups of rats on gestation days 9 or 13; gestation-day 20 fetuses were examined for external, skeletal, and visceral malformations. The results are consistent with and extend our previous research findings. Synergism was observed between RF radiation and 2ME for some treatment combinations, but not for others. The study also clarified which gestational periods, RF radiation exposure durations, and 2ME doses would be most informative in future interaction studies to determine the lowest interactive effect level. Day 9 exposures generally evidenced little effect by 2ME, either by itself or in combination with RF radiation. In contrast, day 13 exposures resulted in highly significant effects from 2ME and RF radiation. The structures showing strong evidence of effects from both 2ME and RF radiation after exposure on gestation day 13 were the forepaw digits, forepaw phalanges, hindpaw digits, hindpaw phalanges, hind limbs, metacarpals, and metatarsals. Statistical analyses did not show a global synergistic effect, but did show evidence for a synergistic effect at intermediate levels of the dose ranges. Future research will address potential interactions at lower doses.

[Reproductive and developmental toxicity studies of tazobactam/piperacillin or tazobactam (2)--Teratological study in rats with intravenously administration].

Tazobactam (TAZ) is a newly developed beta-lactamase inhibitor and piperacillin (PIPC) is an antibiotics which is used in clinical field widely. The combination of TAZ and PIPC (TAZ/PIPC), which is combined with TAZ and PIPC at rate of 1:4, has been developed because of PIPC is unstable to various beta-lactamases. Teratogenic potential were studied in rats given daily intravenous doses of TAZ/PIPC (625, 1250, 2500 or 3750 mg/kg/day) or TAZ (125, 500 or 3000 mg/kg/day). TAZ/PIPC or TAZ were given from day 7 to day 17 of pregnancy. Total daily doses were administered in two equally divided doses. The study includes postnatal evaluation of the growth and development and reproductive performance of the F1 generation. Maternal deaths occurred in all groups given TAZ/PIPC. The incidence (range of 3 to 6 animals/group) was not dose dependent. Maternal body weight was decreased in rats receiving 3000 mg/kg of TAZ and food consumption was reduced in all drug-treated groups. Slight decreases in fetal body weights were observed at some doses that caused maternal body-weight or food-consumption decreases (2500 or 3750 mg/kg of TAZ/PIPC, 3000 mg/kg of TAZ). But these depressions of fetal body weights were not significant from control data. There were no fetal malformations or variations attributable to the test articles. Postnatal growth and development, behavior and reproductive performance of the F1 generation were not affected by the administration of TAZ/PIPC or TAZ. In conclusion, TAZ/PIPC or TAZ was not teratogenic in the rats. It is seemed that non-observed effect dose levels (NOELs) of TAZ/PIPC and TAZ for dams is less than 625 and 125 mg/kg/day in general toxicity respectively, however, NOELs of TAZ/PIPC is 3750 mg/kg/day or more and that of TAZ is 300 mg/kg/day or more for their offspring under the condition of this study.