Three anatase titanium dioxide (TiO(2)) nanoparticles (NPs) were prepared; nanospheres (NSs), short nanobelts (NB1), and long nanobelts (NB2). These NPs were used to investigate the effect of NP shape and length on lung toxicity. Mice were exposed (0-30 µg per mouse) by pharyngeal aspiration and pulmonary toxicity was assessed over a 112-day time course. Whole lung lavage data indicated that NB1- and NB2-exposed mice, but not NS-exposed mice, had significant dose- and time-dependent pulmonary inflammation and damage. Histopathological analyses at 112 days postexposure determined no interstitial fibrosis in any NS-exposed mice, an increased incidence in 30 µg NB1-exposed mice, and significant interstitial fibrosis in 30 µg NB2-exposed mice. At 112 days postexposure, lung burden of NS was decreased by 96.4% and NB2 by 80.5% from initial deposition levels. At 112 days postexposure, enhanced dark field microscopy determined that alveolar macro- phages were the dominant deposition site, but a fraction of NB1 and NB2 was observed in the alveolar interstitial spaces. For the 30 µg exposure groups at 112 days postexposure, confocal micro- scopy and immunofluorescent staining demonstrated that retained NB2 but not NS were present in the interstitium subjacent to the terminal bronchiole near the normal location of the smallest lymphatic capillaries in the lung. These lymphatic capillaries play a critical role in particle clearance, and the accumulation of NB2, but not NS, suggests possible impaired lymphatic clearance by the high aspect ratio particles. In summary, our data indicate that TiO(2) NP shape alters pulmonary responses, with severity of responses being ranked as NS < NB1 < NB2.

The prophylactic use of zidovudine (3'-azido-3'-deoxythymidine, AZT) during pregnancy greatly reduces transmission of HIV-1 from infected mothers to their infants; however, the affinity of host cell DNA polymerases for AZT also allows for its incorporation into host cell DNA, predisposing to cancer development. To expand upon previous transplacental carcinogenesis assays performed in CD-1 mice, the transplacental carcinogenicity of AZT was evaluated in a second mouse strain and a second rodent species. Date-mated female mice and rats were gavaged daily with 0, 80, 240, or 480 mg AZT/kg bw during the last 7 days of gestation. At 2 years postpartum, male and female B6C3F1 mouse and F344 rat offspring (n = 44-46 of each sex and species/treatment group) were necropsied for gross and microscopic tissue examinations. Under the conditions of these two-year studies, there was clear evidence of carcinogenic activity based upon significant dose-related trends and increases in the incidences of hemangiosarcoma in male mice and mononuclear cell leukemia in female rats. There was some evidence of carcinogenic activity in the livers of male mice based upon a positive trend and an increased incidence of hepatic carcinoma in the high-dose AZT group. The incidence of gliomas in female rats exceeded the historical background rates for gliomas in F344 rats. P53 overexpression was detected in some AZT-treated mouse neoplasms. These and other cancer-related findings confirm and extend those of previous transplacental carcinogenicity studies of AZT in mice, support the need for long-term follow-up of nucleoside reverse transcriptase inhibitor (NRTI)-exposed children, and indicate the necessity for effective protective strategies against NRTI-induced side effects.

A recent study further investigated the potential effects of maternal thyroid function and morphology on fetal development upon maternal exposure to ammonium perchlorate during gestation and lactation. Female Sprague-Dawley rats (25/group) were given continual access to 0 (carrier), 0.01, 0.1, 1.0, and 30.0 mg/kg-day perchlorate in drinking water beginning 2 weeks prior to cohabitation through lactation day 10. Maternal, fetal, and pup serum thyroid hormone (thyroid-stimulating hormone [TSH], triiodo thyronine [T(3)], thyroxine [T(4)]) levels and thyroid histopathology were evaluated on gestation day 21, and lactation days 5, 10, and 22. No effects of exposure were observed on cesarean-sectioning, litter parameters, or fetal alterations. Reproductive parameters, including gestation length, number of implants, litter size, pup viability, and lactation indices, were comparable among all groups. Thyroid weights of dams sacrificed on gestation day 21, and lactation days 10 and 22 were significantly increased at 30.0 mg/kg-day. Increased thyroid weights were observed in male and female pups as early as postpartum days 5 and 10, respectively. Changes in maternal and neonatal thyroid histopathology were detectable at 1.0 mg/kg-day exposure. The maternal no-observable-effect level (NOEL) was 0.1 mg/kg-day (follicular cell hyperplasia was present at 1.0 and 30.0 mg/kg-day). The developmental NOEL was less than 0.01 mg/kg-day; thyroid weights of postpartum day 10 pups were increased at all exposures. Colloid depletion at 1.0 and 30.0 mg/kg-day exposures and changes of hormone levels at all exposures were considered an adaptive effect and appeared reversible in the rodent.

The development of biomaterials, medical device components, finished medical products, and 3-D printed and regenerative medicine products is governed by a variety of international and country-specific standards and guidelines. Of greatest importance to planning, executing, and reporting biocompatibility, safety and efficacy studies for most biomaterials and medical components or products are the International Organization for Standardization guidelines, U.S. Pharmacopeial Convention, ASTM International, and Conformité Européenne (European Conformity) marking. The International Medical Device Regulators Forum publishes harmonized standards similar to the International Council for Harmonization. Good Laboratory Practices are applicable and guidance documents for the development of drugs and biologics can also be relevant to biomaterials, medical device components, and medical products and more recently to products produced by 3-D printing or additive manufacturing. Regenerative products may have medical device–based scaffolding and may be treated as biologics, reflecting the cell and tissue components. This compilation of international standards and guidelines provides toxicologic pathologists, toxicologists, bioengineers, and allied professionals with an overview of and source for important regulatory documents that may apply to the nonclinical development of their products.

To examine the phenomenon of apparent age resistance of young chicks to organophosphate-induced delayed neuropathy (OPIDN), groups of either 2- or 10-week-old chicks were exposed subcutaneously daily for 4 days to the neuropathic organophosphate (OP), di-isopropylfluorophosphate (DFP, 1 mg/kg), the non-neuropathic OP, paraoxon (PO, 0.25 mg/kg) or atropine (20 mg/kg). Subsequently, all birds were examined at post-exposure intervals (calculated from the last day of exposure) for up to 56 days for neurological deficits and morphological lesions in the central and peripheral nervous systems (CNS, PNS). Clinically, none of the birds in the 2-week-old groups, or in the 10-week-old PO or atropine exposed groups had neurological deficits. However, all birds in the 10-week-old DFP exposed group developed ataxia by 7 days post-exposure (DPE) and then progressive paralysis. Therefore, all birds in the 10-week-old groups were killed at 14 DPE. Pathologically, the 2-week-old DFP exposed chicks had increasingly severe lesions of Wallerian-like degeneration predominantly in the spinal cord from 7 DPE and subsequently. In the 10-week-old DFP exposed chicks, the degenerative lesions of OPIDN were first detected in the CNS at 3 DPE and then with equally increasing severity in the CNS and PNS up to 14 DPE. A higher incidence of neuronal necrosis and chromatolysis in ventral motor horn neurons of spinal cord grey matter and in dorsal root ganglia occurred in both the DFP exposed age groups compared with those lesions in other groups.(ABSTRACT TRUNCATED AT 250 WORDS)

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A developmental toxicity study was conducted with ammonium perchlorate (AP) in the drinking water at doses of 0.0, 0.01, 0.1, 1.0, and 30.0 mg/kg-day beginning 14 days before cohabitation and continuing through sacrifice. Twenty-four rats/group were cesarean-sectioned on day of gestation (DG) 21 and fetuses examined for visceral and skeletal alterations. An additional 16 litters/group were sacrificed on DG 21 for maternal and fetal serum TSH, T(3), and T(4) (thyroid-stimulating hormone, triiodothyronine, and thyroxine) levels and thyroid histopathology. Clinical and necropsy observations, body weights, feed and water consumption, and cesarean-sectioning parameters were comparable among the groups with only delays in ossification observed in the 30 mg/kg-day group. Maternal thyroid weights were increased in the 30.0 mg/kg-day group. Decreased colloid was present in male and female fetal thyroids in the 1.0 and 30.0 mg/kg-day groups. Maternal TSH was increased and T(4) was decreased at all levels, and T(3) was reduced at 30.0 mg/kg-day. Fetal TSH was increased at 1.0 and 30.0 mg/kg-day, T(4) was reduced at 30.0 mg/kg-day, and T(3) was decreased at all levels. The maternal no-observable-adverse-effect level (NOAEL) was 1.0 mg/kg-day; exposures of 30.0 mg/kg-day increased absolute and relative maternal thyroid weights and histopathology findings. The developmental NOAEL was 1.0 mg/kg-day; developmental delays in ossification occurred in the 30.0 mg/kg-day group. The colloid depletion in the thyroids and increased TSH and decreased T(3) and T(4) levels at lower exposures were considered adaptive and not adverse. No adverse effects on development at occurred levels that did not cause maternal toxicity. AP is not a selective developmental toxicant.

Female Fischer 344 (F344) rats were exposed to N-nitrosodiphenylamine (NDPA) by dietary feed at concentrations of 0, 250, 1000, 2000, 3000 or 4000 ppm for 5 days, 2, 4 and 13 weeks duration. Endpoints evaluated included clinical observations, body weights, urinary bladder weights, blood NDPA, gross pathology and urinary bladder histopathology. There were no NDPA exposure-related clinical signs of toxicity. The mean body weight decreased 3% to 5% compared with the control in the 4000 ppm group during study weeks 2 through to 13. Statistically significant increases in urinary bladder weight were observed as early as after 5 days exposure and were concentration dependent at ≥ 3000 ppm. NDPA-related urinary bladder microscopic alterations consisted of mixed cell infiltrates, increased mitosis, increased necrosis of epithelial cells, diffuse and/or nodular transitional epithelial hyperplasia and squamous metaplasia of transitional epithelium. These changes affected only rats exposed to NDPA concentrations ≥ 2000 ppm. Blood NDPA concentrations were negligible in animals exposed to ≤ 1000 ppm and ranged from 0.12 to 0.19 µg ml(-1) in rats of the ≥ 2000 ppm groups at the 5 days and 2 weeks time points. A no observable adverse effect level (NOAEL) of 1000 ppm NDPA (60 mg kg(-1) day(-1) ) was selected based on the absence of urinary bladder histopathology.