Long-lived spin waves in a metallic antiferromagnet

Collective spin excitations in magnetically ordered crystals, called magnons or spin waves, can serve as carriers in novel spintronic devices with ultralow energy consumption. The generation of well-detectable spin flows requires long lifetimes of high-frequency magnons. In general, the lifetime of spin waves in a metal is substantially reduced due to a strong coupling of magnons to the Stoner continuum. This makes metals unattractive for use as components for magnonic devices. Here, we present the metallic antiferromagnet CeCo2P2, which exhibits long-living magnons even in the terahertz (THz) regime. For CeCo2P2, our first-principle calculations predict a suppression of low-energy spin-flip Stoner excitations, which is verified by resonant inelastic X-ray scattering measurements. By comparison to the isostructural compound LaCo2P2, we show how small structural changes can dramatically alter the electronic structure around the Fermi level leading to the classical picture of the strongly damped magnons intrinsic to metallic systems. Our results not only demonstrate that long-lived magnons in the THz regime can exist in bulk metallic systems, but they also open a path for an efficient search for metallic magnetic systems in which undamped THz magnons can be excited.

The effects of inhalation anaesthetics on common clinical pathology parameters in laboratory rats

Effects of common anaesthetics such as ether, methoxyflurane, isoflurane, carbon dioxide (at 100%, 80% or 60% admixed with O(2)) on toxicity and clinical pathology parameters in rats were investigated. Ether, methoxyflurane and 100% CO(2) induced toxicity in some animals. Erythrocyte, haemoglobin and haematocrit were reduced in females by 100% CO(2), methoxyflurane and isoflurane. Glucose was increased by 60% CO(2), 80% CO(2), ether, isoflurane and methoxyflurane in males. Chloride was reduced by isoflurane and all CO(2) concentrations in females. Serum proteins were reduced by isoflurane and methoxyflurane. Sodium, inorganic phosphate, calcium and magnesium were reduced by methoxyflurane and isoflurane, but increased by all CO(2) concentrations. Potassium was reduced by ether, methoxyflurane or isoflurane. Triiodothyronine and thyroxine were reduced by all anaesthetics. Prolactin was reduced by methoxyflurane, but raised by ether and isoflurane. Erythrocyte cholinesterase (E-ChE) activity is markedly reduced (20-40%) after anaesthesia with all CO(2) concentrations in both sexes. E-ChE was unaffected by ether, methoxyflurane, or isoflurane. Serum and brain cholinesterase activities were not affected. E-ChE inhibition correlated with decreased blood pH, suggesting that this was caused by acidosis. This is of practical relevance in the risk assessment of cholinesterase inhibitors.

CONCLUSIONS

Clinical pathology data were affected by all anaesthetics. CO(2)/O(2) (80%/20%) and isoflurane are the most suitable anaesthetics. If E-ChE activity is to be determined, isoflurane is the anaesthetic of choice.

Developmental toxicity of oral n-butylamine hydrochloride and inhaled n-butylamine in rats

Pregnant Wistar rats were administered 0, 100, 400 or 1000 mg mono-n-butylamine hydrochloride/kg body weight/day by gavage on days 6 through 15 post coitum (sperm-positive=day 0), or inhaled mono-n-butylamine 0, 17, 50 or 152 ppm (whole-body exposure), 6 h/day on days 6 through 19 post coitum. Oral n-butylamine HCl 1000 mg/kg reduced maternal feed consumption, increased early post-implantation losses (embryonic resorptions), reduced fetal and placental weight, and retarded skeletal development (incomplete skull and sternebral ossification), and produced malformations (filiform/kinked tail, enlarged cardiac ventricular chamber(s), malpositioned heart, aortic arch atresia, diaphragmatic hernia); 100 mg/kg was the no-observed-adverse effect level (NOAEL) for prenatal developmental toxicity; 400 mg/kg, the maternal no-effect level, produced only malformations (aortic arch atresia, malpositioned heart, diaphragmatic hernia). Inhaled n-butylamine produced concentration-dependent nasal epithelial hyperplasia and squamous metaplasia, inflammation and necrosis; the maternal NOAEL was less than 17 ppm. There were no treatment-related signs of embryo/fetotoxicity, particularly, no effects on fetal morphology. The developmental NOAEL was 152 ppm. The neutralization of n-butylamine by hydrochloride converts it from a strong alkali causing tissue burns into a weak acid/base which is fetotoxic. Possible mechanisms of fetotoxicity are free radical production, metabolic acidosis, and lysosomotrophy.

Tetrahydrofuran: two-generation reproduction toxicity in Wistar rats by continuous administration in the drinking water

In a two-generation reproduction toxicity study, 25 male and 25 female Wistar rats per dose group and generation were exposed continuously to tetrahydrofuran in the drinking water for at least 70 days prior to and during mating, gestation, parturition and lactation to weaning, at concentrations of 0, 1000, 3000 or 9000 ppm (approximately 100, 300 and 700 mg/kg/day in males and females premating, 100, 300 and 800 mg/kg/day in females during gestation, and 200, 500 and 1300 mg/kg/day in females during lactation) through two successive generations. In both generations and sexes, water consumption was dose-relatedly reduced at all doses; food consumption and body weight were reduced at 9000 ppm. Necropsy kidney weights were increased in 9000 ppm F0 males. Pup body weight gain during lactation was reduced in both generations (F1 and F2 pups) and eye opening delayed in the first generation (F1 pups) at 9000 ppm; there were no treatment-related malformations. The NOAEL of tetrahydrofuran in drinking water is 9000 ppm for parental fertility and reproductive performance, and 3000 ppm for systemic parental and developmental toxicity.

Harmonisation of rat fetal skeletal terminology and classification. Report of the Third Workshop on the Terminology in Developmental Toxicology. Berlin, 14-16 September 2000

The initial efforts of the Federal Institute for Health Protection of Consumers and Veterinary Medicine (BgVV) and the Free University of Berlin to standardise terminology in the field of developmental toxicology began in 1995. Procedures were undertaken to harmonise the terminology used by the International Federation of Teratology Societies (IFTS) and the International Programme on Chemical Safety (IPCS). This article reflects these activities and is a report on the Third Workshop on the Terminology in Developmental Toxicology held in September 2000. This Workshop served as a forum to discuss the results of a survey on the classification of skeletal anomalies that had been previously sent to scientists active in the field. Although high agreement was reached among the evaluators for several terms, the use of a number of terms was rather variable. Therefore, the discussions at the workshop among the experts from research institutions, regulatory agencies, and industry were mainly focussed on those terms for which there was disagreement and/or uncertainties and the possible reasons. Pictures provided by the participants for the illustration of "grey zone" anomalies constituted the basis for detailed discussions. In many of the cases with lower agreement, decisions were facilitated by the provision of the corresponding picture. The main reasons for lower agreement were imprecise terms, insufficient knowledge on postnatal consequences, theoretical terms that are unlikely to occur in isolation, and the possibility of observing a range of severity that might be decisive for the classification of either a malformation or variation. The attendees concluded that "grey-zone" anomalies will never disappear completely and that for the assessment, the grade of severity and/or the frequency of the observation can be decisive for the terminology chosen. A Joint IPCS/IFTS Project was proposed to further consensus of terminology and classification and to link these anomalies to pictures at different skeletal sites. In order to support the harmonisation of regulatory decisions, it was proposed to establish a "Clearinghouse" System under the umbrella of the IPCS. The Clearinghouse could be contacted either by the regulatory authorities or by any company to clarify their queries, particularly with regard to registration or authorisation processes. Finally, it was recommended to also carry out a similar survey on "soft tissue anomalies" and "external findings." The results of this survey will be discussed at a Joint IPCS/IFTS Workshop in Berlin in 2002.

Reproductive toxicity of MCPA (4-chloro-2-methylphenoxyacetic acid) in the rat

The reproductive effects of the administration of 4-chloro-2-methylphenoxyacetic acid (MCPA) to rats were evaluated through two generations, from prior to mating, throughout mating, to gestation and lactation. MCPA was administered in the diet at doses of 0, 50, 150, or 450 ppm to 25 male and female immature rats (F0 parents) for 10 weeks. F0 parents were then mated to produce a first litter (F1a), retained only until weaning, and were subsequently remated to produce a second litter, F1b. Groups of male and female F1b animals were then dosed as were their parents for 10 weeks postweaning, and the breeding was repeated to produce F2a and F2b animals. The study concluded with the F2b weanlings. MCPA was administered continuously throughout the study. Only minimal, non-treatment-related observations were noted, which included rhinorrhea (in both treated and control animals in the F0 generation) and malocclusion and alopecia (in both the F0 and F1b generations). There were no consistent dose-related effects on reproductive function for parental animals of either sex in either generation. Statistically significant differences were noted in body weights and body weight gains in the 450-ppm dose group for both male and female pups in F2a and F2b. There were no treatment-related macroscopic or microscopic observations noted for any animal in this study. The no-observable-effect level (NOEL) for reproductive function in rats administered MCPA continuously for two successive generations was determined to be 450 ppm (approximately 22 mg/kg/day). The NOEL for general systemic toxicity, based on body weight effects in adult animals in the F1b generation was 150 ppm. The NOEL for effects on the offspring of the F1b generation, manifested as reduced pup weights and pup weight gains was also 150 ppm (approximately 8 mg/kg/day). Based upon the results of this study, MCPA, administered for two generations to Crl:CD(SD)BR Albino rats, is considered not to be a reproductive toxicant.

Developmental toxicity of dimethylacetamide in rabbits following inhalation exposure

(1) Dimethylacetamide was tested for developmental toxicity after inhalation exposure of pregnant Himalayan rabbits. Fifteen female rabbits per main group were exposed to dimethylacetamide vapours at concentrations of 0, 0.2, 0.7 or 2.0 mg/l (equivalent to 0, 57, 199.5 or 570 ppm) and five female rabbits per satellite group to 0 or 2.0 mg/l 6 h/day from day 7 post-insemination (p.i.) to day 19 p.i. All animals were observed until day 29 p.i. (2) No signs of maternal toxicity were seen in the does of the main groups (body weight and gross pathology) or in the does of the satellite groups (body weight, blood chemistry, histopathological findings of the liver). (3) Fetotoxic effects were caused at a concentration of 0.7 mg/l (e.g., increased skeletal variations) and 2.0 mg/l (e.g., significantly decreased fetal and placental weights, increase in soft tissue and skeletal variations). At 2.0 mg/l, there were also signs of a weak teratogenic effect expressed as a marginal, statistically not significant increase in soft tissue malformations (regarding the heart and great vessels). No compound-related effects were observed in the fetuses after exposure to 0.2 mg/l. (4) The highest concentration tested under these conditions (2.0 mg/l) was found to be a no-observable-adverse-effect-level (NOAEL) for the maternal Himalayan rabbit, whereas 0.2 mg/l was defined as the NOAEL for the developing organism.

Pre- and postnatal oral toxicity of vinclozolin in Wistar and Long-Evans rats

Vinclozolin administered to pregnant Wistar and Long-Evans rats from day 14 postcoitum to day 3 postpartum at 200 mg/kg body wt/day was maternally toxic (reduced food consumption and body weight gain) and increased perinatal mortality; major adverse effects on sex-specific organs in male offspring were seen (reduced anogenital distance and index; persistence of nipples/areolas into adulthood; hypospadic penis; penile hypoplasia or development of a vaginal pouch; transient paraphimosis; hypoplasia and chronic inflammation of epididymides, prostate, seminal vesicles, and coagulating glands; and also testicular tubular atrophy and chronic inflammation of the urinary bladder in some Long-Evans) with isolated inflammation-related deaths due to pyelonephritis. At 12 mg/kg, prevalence of female areola/nipple anlagen in immature (preweaning) male offspring was increased in both strains; these persisted to adulthood in a few treated Long-Evans but not Wistar offspring. Adult Long-Evans but not Wistar at this dose also had hypoplasia of prostate, seminal vesicles, and coagulating glands, and a minority had testicular tubular atrophy. The no-observed-adverse-effect levels (NOAEL) were 12 and 6 mg/kg body wt in Wistar and Long-Evans rats, respectively, in these studies. The data suggest that both the Long-Evans and the Wistar rats are comparably sensitive to the antiandrogenic effects of vinclozolin. At dose levels below the NOAEL (1 and 3 mg/kg, respectively), there were no indications of any test-substance-related effects.

Prenatal toxicity of inhaled polymeric methylenediphenyl diisocyanate (MDI) aerosols in pregnant wistar rats

Mated Wistar rats, 25/group, were exposed to polymeric methylenediphenyl diisocyanate (MDI) aerosol of respirable size for 6 h/day, on gestational days (gd) 6 through 15, at 0, 1, 4, and 12 mg/m3. Maternal clinical signs, body weights, and feed and water consumption were measured throughout gestation. At scheduled sacrifice on gd 20, maternal body, gravid uterine, liver, and paired lung weights were documented. Corpora lutea were counted, implantation sites were identified: resorptions, dead and live fetuses, and placentas were weighed. All live fetuses were counted, sexed, weighed, and examined for external alterations; approximately 50% of the live fetuses/litter were preserved in Bouin's fixative and examined for visceral alterations, and the remaining live fetuses/ litter were cleared and stained with alizarin red S and examined for ossified skeletal alterations. Maternal toxicity was observed at 12 mg/m3, including mortality (2 of 24 pregnant), damage to the respiratory tract, reduced body weights and weight gain, reduced liver and increased lung weights, and reduced gravid uterine weight (the last not statistically significantly different from the control value). Developmental toxicity was also observed at 12 mg/m3, including reduced placental and fetal body weights and an increased incidence of fetal skeletal variations and skeletal retardations. There was no evidence of maternal or developmental toxicity at 1 or 4 mg/m3. The no observed adverse effect concentration for maternal and developmental toxicity was therefore 4 mg/m3. There were no treatment-related teratogenic effects at any concentrations evaluated.

Protection against murine tuberculosis by an attenuated recombinant Salmonella typhimurium vaccine strain that secretes the 30-kDa antigen of Mycobacterium bovis BCG

A recombinant (r-) Salmonella typhimurium aroA vaccine that secretes the naturally secreted protein of Mycobacterium bovis strain BCG, Ag85B, by means of the HlyB/HlyD/TolC export machinery (termed p30 in the following) was constructed. In contrast to r-S. typhimurium control, oral vaccination of mice with the r-S. typhimurium p30 construct induced partial protection against an intravenous challenge with the intracellular pathogen Mycobacterium tuberculosis, resulting in similar vaccine efficacy comparable to that of the systemically administered attenuated M. bovis BCG strain. The immune response induced by r-S. typhimurium p30 was accompanied by augmented interferon-gamma (IFN-gamma) and tumor necrosis factor-alpha (TNF-alpha) levels produced by restimulated splenocytes. These data suggest that the HlyB/HlyD/TolC-based antigen delivery system with attenuated r-S. typhimurium as carrier is capable of inducing an immune response against mycobacterial antigens.

Uterotrophic assay of two concentrations of migrates from each of 23 polystyrenes administered orally (by gavage) to immature female Wistar rats

The Styrene Steering Committee (SSC) of the European Chemical Industry Council (CEFIC) sponsored this work to address any concern that styrene dimers and trimers that might migrate from polystyrene containers into food could possess some estrogenic activity and thus possibly affect human health. All phases of the study were conducted in conformance with GLP regulations and without knowledge of the oligomer migrates tested. All activities were managed and audited under a third-party contract between the SSC and Argus International. Low and high doses of the styrene oligomer migrates of 23 polystyrene samples [i.e. 9 general purpose polystyrenes (GPPS), 8 high impact polystyrenes (HIPS) and 6 expandable polystyrenes (EPS)] were tested for estrogenicity in an in vivo uterotrophic assay (immature female rat model). This model is considered to be the "gold standard" for use in screening for estrogenic effects because it evaluates both direct and indirect potential effects. The two concentrations of migrates of each of the 23 polystyrenes tested were selected to simulate daily human consumption of a low and high amount of food. Representative dimer and trimer concentrations were obtained in conformance with EEC Council Directives and calculated to be at levels simulating human consumption of 0.5 or 5 kg of food for the GPPS and the HIPS samples and of 0.5 or 3.15 kg of food for the EPS samples, respectively. The study was conducted in a series of three blocks. Each block included concurrent untreated control (negative control), vehicle control (25% ethanol, 20 ml/kg/day) and positive control (diethylstilbestrol-dipropionate, DES-DP, 5 micrograms/kg/day) groups, and low and high doses of each of 7 (1 block) or 8 (2 blocks) polystyrene oligomer migrates. Each group in each block consisted of 10 immature Wistar (Chbb: THOM-SPF) female rats. Beginning when the rats were 22 +/- 1 days of age, each rat was appropriately handled (untreated control group) or administered twice daily oral (gavage) dosages of the vehicle, positive control agent or one of the two doses of the migrates of each polystyrene for 4 consecutive days and then sacrificed at 26 +/- 1 days of age. The uterus of each rat was weighed, and the uterine weight was compared with the terminal body weight. The positive control agent (DES-DP, 5 micrograms/kg/day) significantly increased both absolute and relative (to terminal body weight) uterine weights, as compared to the untreated and vehicle control group values in each block, demonstrating sensitivity and response of the animals to an estrogenic agent. None of the 23 polystyrene oligomer migrates tested at low and high doses demonstrated biologically important or statistically significant differences from the untreated or vehicle control group values for absolute or relative (to body weight) uterine weights. Based on these data, it is concluded that low and high doses of the 23 polystyrene oligomer migrates tested did not induce an estrogenic response.

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.

Evaluation of the pre-, peri-, and postnatal toxicity of monoethanolamine in rats following repeated oral administration during organogenesis

Pregnant Wistar rats (40/group) were administered monoethanolamine (MEA) as an aqueous solution by gavage at dose levels of 0, 40, 120, and 450 mg/kg/day on days 6 through 15 of gestation. On day 20 of gestation, 25 dams/group were euthanized and the fetuses were delivered by cesarean section, weighted, sexed, and examined for external, visceral, and skeletal alterations. The remaining dams (15/group) were allowed to litter and rear their pups to day 21 postpartum. The dams and pups were then euthanized and examined for gross pathologic changes. Gavage administration of 450 mg MEA/kg/day to pregnant rats resulted in maternal toxicity as evidenced by statistically significant (alpha = 0.05) decreases in feed consumption on gestation days 6-8 and 17-20 and on postpartum days 0-4. Additionally, statistically significant decreases in mean maternal body weights were observed on gestation days 15, 17, and 20 and on lactation days 0, 4, 7, and 21. Body weight gains of the 450 mg/kg/day dams were also significantly decreased (13% relative to controls) on gestation days 15-20. There was no evidence of maternal toxicity at 40 or 120 mg/kg/day of MEA. Despite the maternal effects observed at 450 mg/kg/day, no significant fetal effects were observed at this or any dose level tested, nor were there any indications of a treatment-related effect on postnatal growth or on the viability of offspring. Thus, it was concluded that MEA was not developmentally toxic to Wistar rats following repeated oral administration, even at maternally toxic dose levels as high as 450 mg/kg/day.

Acrylic acid: two-generation reproduction toxicity study in Wistar rats with continuous administration in the drinking water

In a two-generation reproduction toxicity study, groups of 25 male and 25 female Wistar rats (for both F0 and F1 generations) received acrylic acid (AA) in the drinking water at concentrations of 0 (control), 500, 2500 and 5000 ppm for at least 70 days prior to mating, through mating, gestation, lactation and to weaning. The study continued through to weaning of the F2 offspring at 21 days of age. Achieved intakes of AA for the F0 and F1 parents during premating ranged from 46 (500 ppm) to 502 (5000 ppm) mg/kg/day. AA had no adverse effects on fertility and reproductive performance of the parent rats at doses up to 5000 ppm. General systemic toxicity was apparent with reduced body weights, food and water consumption in F0 parents at 5000 ppm and in F1 parents at 2500 and 5000 ppm; the only treatment-related pathological finding was a minimal hyperkeratosis of the limiting ridge of the forestomach with a minimal oedema of the submucosa of the glandular stomach in both parental generations at 5000 ppm. Dose-related signs of developmental toxicity were detected in F1 and F2 pups at 2500 and 5000 ppm in the form of retarded growth and some delay in the eye/auditory canal opening in F2 pups, but there was no evidence that AA had an adverse influence on pup morphology. Thus, the no-observed-adverse-effect level (NOAEL) is 5000 ppm for fertility and reproductive performance of the parents, 2500 ppm (F0 parents) or 500 ppm (F1 parents) for general systemic toxicity and 500 ppm for developmental toxicity.

Developmental toxicity of 2-butin-1,4-diol following oral administration to the rat

Developmental toxicity of 2-butin-1,4-diol was determined in groups of 18-22 pregnant Wistar rats at dose levels of 10, 40 and 80 mg/kg bw/day administered by gavage from days 6 to 15 pc. At 80 mg/kg bw/day food consumption and maternal body weight were reduced and one dam died during the treatment period. At this dose level the incidence of affected fetuses per litter with accessory 14th ribs was increased. This variation is assessed as an embryotoxic effect resulting from non-specific stress on the dams. No teratogenic effects were caused by 2-butin-1,4-diol. The NOAEL on the maternal and the developing organism was 40 mg/kg bw/day.

Study on the developmental toxicity of orally administered isobutylidenediurea in rats

Developmental toxicity of isobutylidenediurea (IBDU) was determined by oral administration to Wistar rats. The substance was administered as an aqueous suspension to 22-24 pregnant rats per group by gavage in daily doses of 100, 400 and 1000 mg/kg body weight from day 6 post-coitum (p.c.) to day 15 p.c. The control group received the vehicle only (0.5% aqueous carboxymethyl cellulose solution). There were no substance-related effects in the dams concerning food consumption, body weight, body weight gain, uterine weights and clinical or autopsy observations even at the highest dose of 1000 mg/kg body weight/day. The reproduction data revealed no biologically relevant differences between the control and treated groups. The incidence and type of the foetal external, soft tissue and skeletal findings, which were classified as malformations, variations and/or retardations observed in the treated foetuses were similar to the concurrent and/or historical control data. Thus, under the conditions of this study, no signs of maternal toxicity or embryo/foetotoxicity were induced by IBDU and the no-observable-adverse-effect level on the maternal and developing organism was 1000 mg/kg body weight/day.

Differential prenatal toxicity of one straight-chain and five branched-chain primary alcohols in rats

One straight-chain alcohol (n-octanol) and five branched-chain alcohols [2-ethylhexanol (2-EH), isodecanol, two types of isononanol and a C7-9-11 alcohol] were investigated for developmental effects in Wistar rats at equimolar dose levels (0, 1, 5 and 10 mmol/kg by gavage from gestation day 6 to 15; 10 animals per group). n-Octanol and both isononanols were also investigated in a supplementary experiment at 7.5 mmol/kg/day. Pronounced maternal but no developmental toxicity was achieved with n-octanol. C7-9-11 alcohol, which is a mixture of isomers mostly of a low degree of branching (alpha-methyl), showed no adverse effects at any dose levels. The two types of isononanols (typical mixtures of two different sets of isomers originating from two different production routes) exhibited a marked degree of maternal and foetal toxicity at 7.5 and 10 mmol/kg and slight foetal effects at 5 mmol/kg. Because of maternal toxicity in the top dose, a statistically significant increase in malformations was obtained only in the dose window of 7.5 mmol/kg in the supplementary experiment. Isodecanol (a mixture of different isomers) elicited maternal toxicity at 10 mmol/kg and caused a low incidence of retardations and rare malformations at that dose level. Some maternal signs but no foetal effects were observed at 5 mmol/kg. 2-EH showed strong maternal and also foetal toxicity at 10 mmol/kg and slight maternal and foetal toxicity at 5 mmol/kg. The differential responses to the test materials indicate that, at present, within this chemical class of alcohols, the potential for developmental toxicity has to be investigated case by case for each individual structure.

Differential prenatal toxicity of branched phthalate esters in rats

Several phthalate esters with alcohol moieties ranging from C5-C10 chains were investigated for prenatal toxicity in 10 rats per group after gavage administration of 0, 40, 200 and 1000 mg/kg/day from gestation day 6 to 15. At 1000 mg/kg di(2-ethylhexyl) phthalate showed clear foetotoxicity, embryolethality and teratogenicity. No significant effects were recorded at 40 and 200 mg/kg. Di-711-phthalate, a phthalic ester with linear components and a predominantly alpha-methyl branching type, and di-isopentylphthalate showed a very similar spectrum of effects. Interestingly, the alcohol moiety of di-711-phthalate, 711-alcohol was developmentally inactive in a previous experiment. Di-iso-decylphthalate and three types of di-iso-nonylphthalate showed foetal effects of borderline significance at 1000 mg/kg/day.

Oncogenicity testing of 2-ethylhexanol in Fischer 344 rats and B6C3F1 mice

2-Ethylhexanol (2EH) is a weak nongenotoxic hepatic peroxisome proliferator in the rat. It is a high-volume chemical intermediate in the preparation of the plasticizers bis-(2-ethylhexyl) adipate (DEHA), bis-(2-ethylhexyl) phthalate (DEHP), and tris-(2-ethylhexyl) phosphate (TEHP), which are weak hepatocellular tumorigens in female mice. In consequence, the oncogenic potential of 2EH was evaluated in male (M) and female (F) rats and mice (50 animals/sex/group). Oral gavage doses of 2EH in 0.005% aqueous Cremophor EL (polyoxyl-35 castor oil) were given five times a week to rats: 0 (water), 0 (vehicle), 50, 150, and 500 mg/kg for 24 months, and to mice: 0 (water), 0 (vehicle), 50, 200, and 750 mg/kg for 18 months. Statistical comparisons of data were made between vehicle controls and treatment groups. There were no differences of biological significance between data from vehicle and water control groups. In rats, there were no dose-related changes at 50 mg/kg. There was reduced body weight gain at 150 mg/kg (M, 16; F, 12%) and 500 mg/kg (M, 33; F, 31%) and an increased incidence of lethargy and unkemptness. There were dose-related increases in relative liver, stomach, brain, kidney, and testis weights at sacrifice. Female rat mortality was markedly increased at 500 mg/kg. There was marked aspiration-induced bronchopneumonia in rats at 500 mg/kg; hematologic, gross, and microscopic changes, including tumors, were otherwise comparable among all rat groups. In mice at 50 and 200 mg/kg there were no dose-related changes and essentially no time-dependent or time-independent adverse trends in liver tumor incidence at the 5% significance level. At 750 mg/kg mouse body weight gain was reduced (M, 26; F, 24%), and mortality increased (M and F, 30%) versus vehicle controls. At 750 mg/kg there was a slight increase in nonneoplastic focal hyperplasia in the forestomach of mice (M 5/50, F 4/50) versus vehicle controls (M 1/50, F 1/50). There were increases in mouse relative liver (F, 21%) and stomach (M, 13%; F, 19%) weights at 750 mg/kg. There was a 12% incidence of hepatic basophilic foci and an 18% incidence of hepatocellular carcinomas in male mice at 750 mg/kg, not statistically significant compared with either control by Fisher's exact test. There was a 12% incidence of hepatic basophilic foci and a 10% incidence of hepatocellular carcinomas in female mice at 750 mg/kg, statistically significant (p < 0.05) compared with vehicle but not with water controls by Fisher's exact test. There were no metastases. Time-dependent and -independent statistical analyses showed an adverse trend in the incidence of hepatocellular carcinomas in male and female mice, correlated with toxicity (expressed as mortality) at 750 mg/kg. The time-adjusted incidence of hepatocellular carcinomas in male mice (18.8%) was within the historical normal range at the testing facility (0-22%), but that in females (13.1%) lay outside the normal range (0-2%). Under the conditions of these studies 2EH was not oncogenic in rats, but there were weak adverse trends in hepatocellular carcinoma incidence in mice at high dose levels which may have been associated with toxicity. The major effects of chronic dosing were mortality in female rats at 500 mg/kg and in male and female mice at 750 mg/kg, accompanied by reductions in body weight gain in rats at 150 and 500 mg/kg and in mice at 750 mg/kg. Direct comparison of any tumorogenic effects of 2EH given alone to female mice with those due to 2EH formed in vivo from DEHA, DEHP, or TEHP is limited by the high mortality caused by 2ER in female mice at equivalent doses of 2EH. While 2EH may be a contributing factor in the hepatocellular carcinogenesis in female mice associated with the chronic administration of DEHA and DEHP, it is unlikely to be the entire proximate carcinogen.

Investigation of the prenatal toxicity of orally administered diethylene glycol in rabbits

Diethylene glycol was tested for prenatal toxicity after oral administration (gavage) to pregnant Himalayan rabbits. The substance was administered to 15 female rabbits per group by stomach tube in daily doses of 100, 400, or 1000 mg/kg body wt from Day 7 postinsemination (p.i.) through Day 19 p.i. The control group received the vehicle only (twice distilled water). There were no compound-related effects on the dams concerning food consumption, body weight, body weight gain, or clinical or necropsy observations even at the highest dose of 1000 mg/kg body wt/day. All data obtained on gestational parameters also revealed no biologically relevant differences between the control and treated groups. The fetal external, soft tissue, and skeletal findings, which were classified as malformations, variations, and/or retardations, were seen in the treated fetuses at a frequency similar to the corresponding and/or historical controls. Thus, under the conditions of this study, no signs of maternal toxicity or embryo-/fetotoxicity were induced by diethylene glycol. Therefore, a no-observable-adverse-effect level for diethylene glycol of > 1000 mg/kg body wt/day was established for both the maternal and the developing Himalayan rabbit.

Studies on the prenatal toxicity of 3-methyl-1-butanol and 2-methyl-1-propanol in rats and rabbits following inhalation exposure

3-Methyl-1-butanol (MEB) and 2-methyl-1-propanol (MEP) were tested for their prenatal inhalation toxicity in pregnant Wistar rats or Himalayan rabbits. Twenty-five female rats and 15 female rabbits per group were exposed to MEB and MEP vapors at concentrations of 10, 2.5, or 0.5 mg/liter, 6 hr/day. The rats were exposed on Days 6-15 postcoitum (pc) and the rabbits were exposed on Days 7-19 postinsemination (pi). Control groups were exposed to clean air. The body weights of the animals of either species were determined several times throughout the studies. All rats and all rabbits were killed on Day 20 pc and Day 29 pi, respectively. The fetuses were removed from the uterus and examined for compound-related effects. The high concentration of 10 mg/liter caused a slight retardation of body weight gain in the dams of either species exposed to MEB and in the dams of rabbits exposed to MEP during the first days of the exposure period. Eye irritation was observed only in the MEB-treated rabbits during the period of exposure to 10 mg/liter. The fetuses of either species exhibited no signs of embryo-/fetotoxicity or teratogenic effects caused by MEP or MEB. Under the experimental conditions, 2.5 mg/liter was found to be a no-observable-adverse-effect level (NOAEL) for the dams of either species exposed to MEB and for the does exposed to MEP, whereas 10 mg/liter MEP was the NOAEL for the maternal rats. For both substances 10 mg/liter was defined as the NOAEL for the conceptuses of either species.

Prenatal toxicity of inhalation exposure to 2-methoxypropanol-1 in rabbits

2-Methoxypropanol-1 was investigated for prenatal toxicity in Himalayan rabbits after inhalation exposure to 0, 145, 225, 350, and 545 ppm for 6 hr per day from Gestation Day 6 through 18. Maternally toxic effects were found with decreased body weights from Day 12 of gestation through the end of the study at 545 ppm. A dose-dependent increase of resorptions, fetal malformations, and variations was observed at 225, 350, and 545 ppm, whereas 145 ppm was devoid of exposure-related effects. The malformation rate at 545 ppm was 100%. The types of malformations mainly consisted of absent phalanges and absent or rudimentary metatarsal bones, malformed ribs, and a unique enlargement of sternebrae. The effects are very similar to those previously found with 2-methoxypropyl-acetate-1. The results of this study may have implications for the quantitative estimation of risks associated with 2-methoxy-propanol-1 impurities in the widely used isomer 1-methoxypropanol-2 which itself does not show developmental toxicity.

Subchronic and chronic studies of the effects of oral administration of acrylic acid to rats

In a 3-month study, groups of 10 male and 10 female Wistar rats were dosed by gavage, 5 times per week, with acrylic acid at doses of 150 or 375 mg/kg body weight. Five male and five female rats in the low-dose group died and six males and nine females given 375 mg/kg died. Pathological examination revealed a dose-dependent pronounced irritation in the forestomach and glandular stomach with ulcerations and purulent rhinitides and tubular necroses. Therefore, in comparison with drinking water administration using approximately equivalent doses (2000 or 5000 ppm; see below), administration by gavage was determined not to be suitable for long-term studies using as high as possible doses. In a 12-month study, Wistar rats (20 rats/group/sex) were given drinking water containing 120, 800, 2000 or 5000 ppm acrylic acid (providing doses of about 9, 61, 140 and 331 mg/kg body weight/day, respectively). Satellite groups (10 rats/group/sex) were treated concurrently for 3 months. Acrylic acid at 5000 ppm, and temporarily also at 2000 ppm, led to reduced drinking water consumption in male rats and, to a slight extent, also in female rats. In the males, feed consumption was reduced at 5000 ppm and body weight gain was retarded at 5000 ppm and marginally also at 2000 ppm. These findings indicate palatability problems and their consequences. There were no indications of systemic toxicity and/or any carcinogenic potential. In a carcinogenicity study, Wistar rats (50/group/sex) were given acrylic acid in the drinking water at concentrations of 0, 120, 400 or 1200 ppm (8, 27 or 78 mg/kg body weight/day, respectively) over 26 (males) or 28 (females) months. The concentrations were chosen on the basis of the interim results from the 12-month drinking water study, which had started earlier, and taking into account the longer study duration and geriatric effects to be expected. This carcinogenicity study did not reveal any toxic changes or indications of a carcinogenic potential of acrylic acid with the exception of slightly reduced (statistically not significant) consumption of drinking water.

Di-(2-ethylhexyl) phthalate: a short-term repeated inhalation toxicity study including fertility assessment

In a study of the 28-day inhalation toxicity of di-(2-ethylhexyl) phthalate (DEHP) aerosols, 9-wk-old Wistar rats, 27 males (mean weight 226 g) and 17 females (mean weight 155 g) per group, were exposed in head-nose inhalation systems to DEHP aerosols of respirable particle size (mass median aerodynamic diameter < or = 1.2 microns) or air (controls). Exposure for 6 hr per day, 5 days per wk for 4 wk to target concentrations of 0, 0.01, 0.05 and 1.0 mg/litre gave estimated doses of 230, 11 and 2.3 mg/kg/day for the males, and 360, 18 and 3.6 mg/kg/day for females, on the assumption of 100% deposition and absorption. Clinical investigation and blood chemistry parameters did not reveal any treatment-related effects. At the end of exposure a statistically significant (16%) increase in relative lung weights, accompanied by increased foam-cell proliferation and thickening of the alveolar septi, was found in the males of the highest dose group. Absolute liver weights were significantly (8.75%) increased in females and relative liver weights were increased in both sexes in the highest dose group, but there were no corresponding histological effects. All these effects were reversed during the 8-wk post-exposure period. No testicular toxicity was observed histologically and no impact on mating performance and male fertility was detected after two matings of treated males with untreated females, 2 and 6 wk after the end of exposure. Electron microscopic examination of liver samples from two male and two female rats per group at the end of exposure and after the 8-wk post-exposure period did not reveal clear substructural changes that could be attributed to exposure or to peroxisome proliferation. The no-observed-effect level for all exposure-related findings was 0.05 mg/litre under the conditions used.

Studies on the prenatal toxicity of toluene in rabbits following inhalation exposure and proposal of a pregnancy guidance value

Prenatal toxicity of toluene was determined in two separate studies by inhalation exposure of Himalayan rabbits. In the first study 15 artificially inseminated females per group were exposed to 30, 100, or 300 ppm and in the second study 20 artificially inseminated females per group inhaled 100 or 500 ppm. In each case the rabbits were exposed for 6 hours per day from day 6 post-insemination (p.i.) to day 18 p.i. The respective controls inhaled conditioned clean air under the same exposure conditions. No signs of maternal toxicity were observed. All data obtained on gestational parameters were found to be within the variation range reported for this rabbit strain. The fetal external, soft tissue and skeletal findings were seen in toluene exposed fetuses in a frequency similar to the corresponding and/or historical controls. Differences observed between the groups were not concentration dependent and were considered incidental rather than compound related. Therefore, toluene was not embryotoxic, fetotoxic, or teratogenic for rabbits exposed during the period of organogenesis. The highest concentration tested under these conditions (500 ppm) was found to be a no-observable-adverse-effect level (NOAEL) for both the adult and the fetal Himalayan rabbit. Based on these and previous results of animal studies of prenatal toxicity, a safety or uncertainty factor approach is considered for setting limits of exposure for women at workplaces. A pregnancy guidance value of 20 ppm is proposed.

The prenatal inhalation toxicity of acrylic acid in rats

Pregnant Sprague-Dawley rats (5 per groups) were exposed in a pretest to 0, 225, and 450 ppm acrylic acid (AA) and in a main study (30 per group) to 0, 40, 120, and 360 ppm acrylic acid. Exposures were for 6 hr/day, during Days 6 to 15 of gestation (period of organogenesis), with further observation up to Day 20 after mating. Maternal toxicity occurred in animals exposed at 450 and 225 ppm in the pretest. At 360 ppm in the main study maternal toxicity consisted of sensory irritation (discharge from the eyes, snout wiping, and restless behavior) with significant reductions in body weight (p less than 0.01), body weight gain (p less than 0.01), and food consumption (p less than 0.01) relative to that of chamber controls. Effects on body weight and body weight gain were dose-related and when corrected for uterus weight were significant in animals exposed to 120 ppm (p less than 0.01), with an effect on body weight gain also at 40 ppm (p less than 0.05), indicating a minimal maternal toxic effect. There were no signs of group-related trends or significant differences between groups in terms of numbers of preimplantation losses, live fetuses, or resorptions, and no signs of group-related differences in the incidences of abnormalities, variations, or retardations in the fetuses in terms of general appearance and the condition of the internal organs or the skeletons. It is concluded that under the experimental conditions of the main study acrylic acid vapor at concentrations between 40 and 360 ppm had no embryotoxic teratogenic effects on Sprague-Dawley rats. Maternal toxicity was minimal at 40 ppm, clearer at 120 ppm, and more pronounced at 360 ppm.

Studies on the prenatal toxicity of N,N-dimethylformamide in mice, rats and rabbits

Prenatal toxicity studies with N,N-dimethylformamide (DMF) in rabbits, rats and mice were carried out using the oral (gavage), dermal, inhalation and ip injection routes of administration. Administration of DMF by gavage led to an increase in malformations in rats and mice in the absence of overt maternal toxicity. The lowest-observable-effect level was 182 mg/kg body weight/day in mice and 166 mg/kg body weight/day in rats. After dermal administration a dose-dependent incidence of teratogenicity was observed in rats at 94-944 mg/kg/body weight/day in the absence of overt maternal toxicity. In rabbits dermal administration led to a steeper increase in the dose-response relationship and at 400 mg/kg body weight/day to a clear teratogenic effect in the presence of slight maternal toxicity. The 200 mg/kg body weight/day dose appeared to be the no-adverse-effect level. Inhalation in rats caused foetotoxicity and embryolethality at 287 ppm. A clear teratogenic effect was shown in rabbits at 450 ppm and a marginal effect at 150 ppm. The no-effect level for does and foetuses was 50 ppm. Ip injection in mice caused clear teratogenicity at 944 mg/kg body weight/day and slight embryotoxicity at 378 mg/kg body weight/day. The rabbit appears to be more sensitive than the rat to DMF-related prenatal toxicity and should, therefore, be used as the basis for the evaluation of teratogenic risk in humans.

Effect of GIP on insulin release to intravenous glucose infusion in hyperthyroid rats

Triiodothyronine induced hyperthyroidism caused significantly elevated basal and stimulated glucose and insulin levels in rats. The release of Gastric Inhibitory Polypeptide (GIP) following an oral glucose load was not significantly different between euthyroid and hyperthyroid rats. The insulin response, however, was significantly higher in hyperthyroid rats. Following intravenous glucose hyperthyroid rats showed a diminished insulin response when compared with euthyroid rats but intravenous infusion of glucose together with GIP caused a significantly higher insulin response in hyperthyroid rats. It is hypothesized that in hyperthyroidism there is an increased sensitivity to the insulinotropic action of GIP and that this mechanism could emphasize the importance of the enteroinsular axis in pathophysiological states.

[Calcification in mass lesions in the kidney (author's transl)]

In 80 mass lesions of the kidney, we found 11 cases with calcification; six of these occurred amongst 48 tumours and five amongst 32 solitary cysts. In particular, the following were found: 1. The frequency of calcification of 12 to 14% corresponds with that given in the literature. If other radiological signs fail indicate the nature of the space-occupying lesion, then calcification may be of diagnostic value. 2. Calcified cyst walls appear as fine, even, curvi-linear lines, Dense, irregular and extensive calcification indicates a solid tumour. 3. Ring or curvi-linear calcification in not a reliable sign of a cyst. Tumours may also show this type of calcification indicates a solid tumour. 3. Ring or curvi-linear calcification is not a reliable sign of cyst. Tumours may also show this type of calcification. Calcification occurs in solitary cyst with about the same frequency as in tumours. 4. Histologically all calcified tumours were clear cell carcinomas, mostly hypervascular. Only one case showed central necrosis.