The inhalation toxicity of di- and triethanolamine upon repeated exposure.

Systemic and respiratory tract (RT) toxicity of triethanolamine (TEA) was assessed in a 28-day nose-only inhalation study in Wistar rats (10animals/sex, concentrations: 0, 20, 100, 500mg/m3; 5 days/week, 6h/day). In two nose-only 90-day inhalation studies, with similar exposure design, Wistar rats were exposed to 0, 15, 150, 400mg/m3 diethanolamine (DEA) (DEA Study 1:13animals/sex, general subchronic study) and to 0, 1.5, 3, 8mg/m3 (DEA Study 2:10animals/sex) to specifically investigate respiratory tract toxicity. Only DEA induced systemic toxicity at or above 150mg/m3 (body and organ weight changes, clinical- and histo-pathological changes indicative for mild blood, liver, kidney and testicular effects). Neurotoxicity was not observed for both substances. Exposure to both substances resulted in laryngeal epithelial changes starting from 3mg/m3 for DEA (reversible metaplasia at the base of the epiglottis, inflammation at higher concentrations extending into the trachea) or from 20mg/m3 for TEA (focal inflammation, starting in single male animals). TEA appears to be less potent with respect to systemic toxicity and RT irritancy than DEA. The 90-day no adverse effect concentration" (NOAEC) for changes due to TEA exposure in the respiratory tract was 4.7mg/m3 derived by extrapolation from the NOAEC of the 28day study.

Generation and characterization of test atmospheres with nanomaterials.

To ensure the product safety of nanomaterials, BASF has initiated an extensive program to study the potential inhalation toxicity of nanosize particles. As preparation work for upcoming inhalation studies, the following manufactured nanomaterials have been evaluated for their behavior in an exposure system designed for inhalation toxicity studies: titanium dioxide, carbon black, Aerosil R104, Aerosil R106, aluminum oxide, copper(II) oxide, amorphous silicon dioxide, zinc oxide, and zirconium(IV) oxide. As the physicochemical properties and the complex nature of ultrafine aerosols may substantially influence the toxic potential, the particle size, specific surface area, zeta potential, and morphology of each of the materials were determined. Aerosols of each material were generated using a dry powder aerosol generator and by nebulization of particle suspensions. The mass concentration of the particles in the inhalation atmosphere was determined gravimetrically and the particle size was determined using a cascade impactor, an optical particle counter, and a scanning mobility particle sizer. The dispersion techniques used generated fine aerosols with particle size distributions in the respiratory range. However, as a result of the significant agglomeration of nanoparticles in the test materials evaluated, no more than a few mass percent of the materials were present as single nanoparticles (i.e., < 100 nm). Considering the number, a greater percentage of nanoparticles was present. Based on the obtained results and experience with the equipment, a technical setup for inhalation studies with nanomaterials is proposed. Furthermore, a stepwise testing approach is recommended that also could reduce the number of animals used in testing.

Determination of pulmonary irritant threshold concentrations of hexamethylene-1,6-diisocyanate (HDI) prepolymers by bronchoalveolar lavage in acute rat inhalation studies according to TRGS 430.

Pulmonary irritant threshold concentrations of two hexamethylene-1,6-diisocyanate (HDI)-based prepolymers (I: polymeric emulsfier modified and II: oligomeric allophanate modified) were determined in acute inhalation studies according to TRGS 430 (Dangerous Substances Technical Rule, isocyanates, Germany), based on benchmark extrapolation of bronchoalveolar lavage fluid (BALF) total protein. It was also investigated if the method is robust enough to be transferred to an independent laboratory. Five male Wistar rats per group were exposed nose-only to the test substances as liquid aerosols to concentrations of 0, 0.5, 3, 15 mg/m(3) for both test substances with an additional test group at 50 mg/m(3) for test substance I. The duration of the exposure was 6h, followed by serial sacrifices 1 day, 3 days and 7 days post exposure. BALF was analyzed for biochemical and cytological markers indicative for injury of the bronchoalveolar region. The exposure of rats to test substance I and II caused dose depended lung irritation with BALF total protein concentration being the most sensitive indicator of pulmonary effects. The extrapolated no observed adverse effect level of test substance I was 1.1 mg/m(3) and that of test substance II 2.3 mg/m(3). The acute pulmonary irritant threshold concentrations were found to be similar to those reported by [Pauluhn, J., 2004. Pulmonary irritant potency of polyisocyanate aerosols in rats: comparative assessment of irritant threshold concentrations by bronchoalveolar lavage. J. Appl. Toxicol. 24, 231-247] for HDI-homopolymers and other HDI-based polyisocyanates, and were at least 30 times higher than the MAK (occupational exposure limit) value for the HDI monomer (0.035 mg/m(3)). Thus the EBW (exposure assessment value) for these two HDI-based prepolymers can be established at 10x MAK, i.e. at 0.35 mg/m(3).

The in vitro absorption of microfine zinc oxide and titanium dioxide through porcine skin.

Microfine metallic oxides such as titanium dioxide or zinc oxide have been found to be highly protective against harmful UV rays. Because their long-term use could potentially lead to health effects if significant amounts of these microfine metallic oxides would be absorbed through the skin, the in vitro absorption of microfine zinc oxide and titanium oxide in cosmetic formulations through porcine skin was investigated. In the experiments with a microfine zinc oxide formulation, the mean total recoveries of Zn were in the range from 102% to 107% of the total Zn applied. Virtually the total amount of applied Zn was recovered in the first five tape strips. The amounts of Zn found in the skin membrane and the receptor fluid were comparable in untreated, vehicle treated or test substance treated skin preparations. The absorption-time plots from diffusion cells treated with the vehicle did not differ from those treated with the ZnO containing formulation. In the experiments with microfine titanium dioxide formulations T-Lite SF-S and T-Lite SF, mean total recoveries of Ti ranged from 98% to 100% and 86% to 93% of the total Ti applied, respectively. Virtually the total amount of applied Ti could be removed from the skin surface by washing. The amounts of titanium found in the tape strips and skin preparations were in the order of the analytical determination limit. No Ti was found in the receptor fluid at any sampling time. The results show that neither zinc or titanium ions nor microfine zinc oxide or titanium dioxide particles were able to penetrate porcine stratum corneum. Therefore, from the absence of internal exposure we conclude that their use in sunscreens does not pose a health risk.

An European inter-laboratory validation of alternative endpoints of the murine local lymph node assay: first round.

The new OECD guideline 429 (skin sensitization: local lymph node assay) is based upon a protocol, which utilises the incorporation of radioactivity into DNA as a measure for cell proliferation in vivo. The guideline also enables the use of alternative endpoints in order to assess draining lymph node (LN) cell proliferation. Here we describe the first round of an inter-laboratory validation of alternative endpoints in the LLNA conducted in seven laboratories. The validation study was managed and supervised by the Swiss Agency for Therapeutic Products, Swissmedic. Statistical analyses of all data were performed by an independent centre at the University of Bern, Department of Statistics. Ear-draining, LN weight and cell count were used to assess proliferation instead of radioactive labeling of lymph node cells. In addition, the acute inflammatory skin reaction was measured by ear swelling and weight of circular biopsies of the ears to identify skin irritating properties of the test items. Hexylcinnamaldehyde (HCA) and three blinded test items were applied to female, 8--10 weeks old NMRI and BALB/c mice. Results were sent via the independent study coordinator to the statistician. The results of this first round showed that the alternative endpoints of the LLNA are sensitive and robust parameters. The use of ear weights added an important parameter assessing the skin irritation potential, which supports the differentiation of pure irritative from contact allergenic potential. There were absolute no discrepancies between the categorisation of the three test substances A--C determined by each single participating laboratories. The results highlighted also that many parameters do have an impact on the strength of the responses. Therefore, such parameters have to be taken into consideration for the categorisation of compounds due to their relative sensitizing potencies.

An European inter-laboratory validation of alternative endpoints of the murine local lymph node assay: 2nd round.

The original local lymph node assay (LLNA) is based on the use of radioactive labelling to measure cell proliferation. Other endpoints for the assessment of proliferation are also authorized by the OECD Guideline 429 provided there is appropriate scientific support, including full citations and description of the methodology (OECD, 2002. OECD Guideline for the Testing of Chemicals; Skin Sensitization: Local Lymph Node Assay, Guideline 429. Paris, adopted 24th April 2002.). Here, we describe the outcome of the second round of an inter-laboratory validation of alternative endpoints in the LLNA conducted in nine laboratories in Europe. The validation study was managed and supervised by the Swiss Agency for Therapeutic Products (Swissmedic) in Bern. Ear-draining lymph node (LN) weight and cell counts were used to assess LN cell proliferation instead of [3H]TdR incorporation. In addition, the acute inflammatory skin reaction was measured by ear weight determination of circular biopsies of the ears to identify skin irritation properties of the test items. The statistical analysis was performed in the department of statistics at the university of Bern. Similar to the EC(3) values defined for the radioactive method, threshold values were calculated for the endpoints measured in this modification of the LLNA. It was concluded that all parameters measured have to be taken into consideration for the categorisation of compounds due to their sensitising potencies. Therefore, an assessment scheme has been developed which turned out to be of great importance to consistently assess sensitisation versus irritancy based on the data of the different parameters. In contrast to the radioactive method, irritants have been picked up by all the laboratories applying this assessment scheme.

The effects of styrene on lung cells in female mice and rats.

Styrene has been shown to cause an increase in the incidence of lung tumors in CD-1 mice following chronic exposure at 40 and 160 ppm, whereas no treatment-related increase in tumors in any organ was seen in rats chronically exposed to up to 1000 ppm styrene. So far most of the mechanistic studies have been performed with male animals. The aim of the present study was to further elucidate the target cell population in mouse lungs exposed to styrene, and to investigate possible differential in vivo effects (e.g., glutathione depletion, increased lipid peroxidation, and oxidative DNA damage). Groups of female CD-1 mice were exposed to styrene at concentrations of 0, 172 or 688 mg/m3 (0, 40 or 160 ppm) for 6 h per day on 1 day, 5 consecutive days or for 20 days during a 4 week period. Groups of female Crl:CD rats were exposed to styrene at concentrations of 0, 688 or 2150 mg/m3 (0, 160 or 500 ppm) for a single 6 h period or for 6 h per day on 5 consecutive days. No signs of lung toxicity were observed in rats. The cytology of cells in lung lavage fluid provided no signs of an inflammatory response in either rats or mice. In mice, both exposure levels caused decreased CC16 protein concentrations in lung lavage fluid after 1 and 5 exposures and in mouse blood serum throughout the study, suggesting that styrene may cause destruction of Clara cells in mice. Degenerative lesions in mouse Clara cells (vacuolar cell degeneration, cell necrosis) were revealed by electronmicroscopy. After 5 and 20 exposures of mice at 160 ppm, cellular crowding, expressed as an irregular epithelial lining and indicative of a very early hyperplasia was noted. Although a depletion of glutathione was noted in mouse lung homogenates after 20 exposures, there was no evidence of oxidative stress as indicated by unchanged concentrations of 8-OH-deoxyguanosine. Malondialdehyde, an indicator of lipid peroxidation, was slightly increased in mice after 1 exposure at 160 ppm only.

Effect of cytochrome P-450 inhibition on tetrahydrofuran-induced hepatocellular proliferation in female mice.

The studies presented were designed to investigate the effects of cytochrome P450 inhibition on tetrahydrofuran-induced hepatocellular proliferation in female B6C3F(1) mice. Groups of female B6C3F(1) mice were exposed to dynamic atmospheres containing tetrahydrofuran (THF) concentrations of 0, 5,400 or 15,000 mg/m(3) for 6 h per day, for 5 consecutive days. One-half of the animals in each THF exposure group were pretreated with the cytochrome P450 inhibitor 1-aminobenzotriazole (ABT) at 100 mg/kg (i.p.) 1 h before the start of each THF exposure period. Treatment with THF at 15,000 mg/m(3) caused marked microsomal enzyme induction in the liver. The cytochrome P450 content was nearly doubled (+98%), pentoxyresorufin-O-depentylase (PROD) and ethoxyresorufin-O-deethylase (EROD) activities were increased by 600% and 160%, respectively. ABT pretreatment effectively blocked microsomal enzyme induction at 15,000 mg/m(3). THF exposure had no effect on the subcellular morphology of hepatocytes, whereas ABT-pretreatment caused centrilobular fatty change. THF at 15,000 mg/m(3) caused increased cell proliferation in zone 3 (central vein region) of the liver (according to Rappaport), as indicated by a significantly higher PCNA (Proliferating Cell Nuclear Antigen) labelling index, but there were no effects at 5,400 ppm. ABT pretreatment prior to THF exposure at 15,000 mg/m(3) caused an exacerbated proliferative response of mouse liver, significantly higher PCNA labelling indices being observed in zones 2 (midzonal region) and 3. The exacerbated proliferative response of mouse liver under conditions of inhibited THF metabolism suggests that the mitogenic effects are related to prevailing THF tissue concentrations and not to the generation of THF oxidative metabolite(s).

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.

Investigations on cell proliferation and enzyme induction in male rat kidney and female mouse liver caused by tetrahydrofuran.

To elucidate possible mechanism(s) of carcinogenic action of tetrahydrofuran (THF) that had been demonstrated in previous inhalation studies, groups of male F344 rats and female B6C3F(1) mice were exposed to dynamic atmospheric concentrations of 0, 600, 1800, or 5400 mg/m(3) for 6 h per day, either for 5 consecutive days or for a period of 4 weeks (5 days per week). The reversibility of treatment-related changes was investigated in rats and mice exposed for 5 days and sacrificed 21 days after the last exposure. Female B6C3F(1) mice exposed to 5400 mg/m(3) showed significantly increased cytochrome P450 content, increased ethoxyresorufin-O-deethylase and pentoxyresorufin-O-depentylase activities, increased cell proliferation (5-bromo-2'-deoxyuridine-method) and an increased mitotic index in liver zones 2 (midzonal region) and 3 (central vein region). The changes were found to be reversible after a 3-week treatment-free period (cell proliferation examined, only). Male F344 rats showed dose-related alpha2u-globulin (alpha2u) accumulation in the renal cortex after 5 or 20 exposures, and there were no signs of reversal after a 3-week treatment-free period. After 20 exposures at 5400 mg/m(3), the alpha2u accumulation was found to be associated with increased cell proliferation in "hot spots" of the renal cortex and increased apoptosis. Increased cell proliferation was also detected after 20 exposures at 1800 mg/m(3). There were no effects at 600 mg/m(3). It is concluded that THF enhances tumor formation in male rat kidney and female mouse liver via induction of cell proliferation. These features present essential elements that should be taken into account for the carcinogenic risk assessment of THF.

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.

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.