Opportunities for use of one species for longer-term toxicology testing during drug development: A cross-industry evaluation.

An international expert working group representing 37 organisations (pharmaceutical/biotechnology companies, contract research organisations, academic institutions and regulatory bodies) collaborated in a data sharing exercise to evaluate the utility of two species within regulatory general toxicology studies. Anonymised data on 172 drug candidates (92 small molecules, 46 monoclonal antibodies, 15 recombinant proteins, 13 synthetic peptides and 6 antibody-drug conjugates) were submitted by 18 organisations. The use of one or two species across molecule types, the frequency for reduction to a single species within the package of general toxicology studies, and a comparison of target organ toxicities identified in each species in both short and longer-term studies were determined. Reduction to a single species for longer-term toxicity studies, as used for the development of biologicals (ICHS6(R1) guideline) was only applied for 8/133 drug candidates, but might have been possible for more, regardless of drug modality, as similar target organ toxicity profiles were identified in the short-term studies. However, definition and harmonisation around the criteria for similarity of toxicity profiles is needed to enable wider consideration of these principles. Analysis of a more robust dataset would be required to provide clear, evidence-based recommendations for expansion of these principles to small molecules or other modalities where two species toxicity testing is currently recommended.

Surface roughness and EDS characterization of a Y-TZP dental ceramic treated with the CoJet™ Sand.

OBJECTIVES: (1) To determine the surface roughness and material loss of a Y-TZP ceramic before and after tribochemical grit blasting and (2) to characterize the changes in elemental surface composition and the phase transformations after tribochemical treatment. METHODS: Machined bar shaped specimens (Zeno, Wieland) were subdivided into three groups. After grit blasting for 10, 20 and 30s respectively, half of the specimens of each group were ultrasonically cleaned in ethanol for 10min. The other half was rinsed with a water spray. Surface roughness was measured using an electro-mechanical profilometer. The elemental composition of the samples was obtained by energy dispersive X-ray spectroscopy (EDS). X-ray diffraction (XRD) was used for phase transformations determination. RESULTS: The median Ra increased significantly from 0.24 to 0.32-0.38µm after grit blasting. Augmentations were also noted for R(max), R(v) and R(p). The highest roughness parameters were, obtained for water sprayed specimens and samples abraded for 30s. Loss of material ranged between 1 and 3µm for 30s grit blasting. Tetragonal and cubic phases were identified in 'as machined' specimens. Grit blasting resulted in domain switching and lattice deformations. The elemental composition comprised Si and Al. The duration of grit blasting did not significantly, influence the atomic percentages of Si or Al. Significantly lower values for both Si and Al were noted, after ultrasonic cleaning. SIGNIFICANCE: Grit blasting with CoJet™ Sand resulted in an increase of surface roughness, a removal of maximum 3µm of material and coated the surface with submicron silica and alumina particles.

Experience from a long-term carcinogenicity study with intraperitoneal injection of biosoluble synthetic mineral fibers.

The carcinogenic potential in the intraperitoneal cavity of three newly developed biosoluble insulation glass wool fibers (M, P, and V) and one newly developed biosoluble insulation stone wool fiber (O) was investigated and compared to that of a previously developed soluble glass fiber (B). The in vitro dissolution coefficient of the three glass wool fibers ranged from 450 to 1037 ng/cm(2) x h and was 523 ng/cm(2) x h for the stone wool fiber. The in vitro dissolution coefficient of the B fiber was 580 ng/cm(2) x h. Groups of female Wistar rats (strain Crl: Wi BR) were exposed by repeated injections to doses of 0.5, 2, and 5 x 10(9) WHO fibers, which corresponds to between 41 mg to 724 mg fiber injected. In addition, 2 groups of crocidolite were used as positive controls at doses of 0.1 x 10(9) and 1 x 10(9) WHO fibers (0.5 and 5 mg). The in vitro dissolution coefficient of crocidolite is estimated to be approximately 1 ng/cm(2) x h. The protocol of the study and the size distribution of the test samples conformed to the European Commission Protocol EUR 18748 EN, and the study was executed under Good Laboratory Practice conditions. Two of the new insulation wools, fibers M and 0, showed no statistically significant tumorigenic response even at the very high dose of 5 x 10(9) WHO fibers injected. Fibers P and V showed a small tumorigenic response in the ip cavity similar in magnitude to the B fiber, which has been declared in the German fiber regulations as a noncarcinogenic fiber. The response to the soluble insulation fibers was notably different from that of the known carcinogen crocidolite, which produced 53% tumors at a comparatively low dose of 0.1 x 10(9) WHO fibers. The incidence of mesothelioma was found to be highly correlated to the incidence of intra-abdominal nodules and masses at different sites. The incidence of abdominal nodules and masses was highly correlated to the number of animals with ascites. The incidence of chronic peritonitis with fibrotic nodules at different organs also correlated with the incidence of mesotheliomas. Differences in etiology were observed between the massive doses of the highly soluble insulation wools when injected directly into the ip cavity and the lower doses of the extremely insoluble fiber crocidolite. The variability in this reaction and the impairment of animal health put into question the value of these massive doses in evaluating the carcinogenic response of soluble insulation wools. All of the fibers tested fulfilled the exoneration criteria with respect to carcinogenicity according to the European Directive 97/69/EC ("an appropriate intra-peritoneal test has not expressed signs of excessive carcinogenicity"). The dose as defined in the EC-Protocol EUR 18748 EN was 1 x 10(9) WHO fibers with a defined geometric spectrum. The influence of fiber dimensions on the ip tumor response and the difficulty in assessing the influence of the difference in background levels between this and previous studies make direct application of the German TRGS 905 criteria difficult; however, by comparison to fiber B, which in the TRGS 905 is considered as a noncarcinogenic fiber, all of the synthetic mineral fiber types tested in this study also appear to meet the intended German criteria for exoneration.