Abstract

Ethical and legal considerations have led to increased use of non-animal methods to evaluate the safety of chemicals for human use. We describe the development and qualification of a physiologically-based kinetics (PBK) model for the cosmetic UV filter ingredient, homosalate, to support its safety without the need of generating further animal data. The intravenous (IV) rat PBK model, using PK-Sim®, was developed and validated using legacy in vivo data generated prior to the 2013 EU animal-testing ban. Input data included literature or predicted physicochemical and pharmacokinetic properties. The refined IV rat PBK model was subject to sensitivity analysis to identify homosalate-specific sensitive parameters impacting the prediction of Cmax (more sensitive than AUC(0-∞)). These were then considered, together with population modeling, to calculate the confidence interval (CI) 95% Cmax and AUC(0-∞). Final model parameters were established by visual inspection of the simulations and biological plausibility. The IV rat model was extrapolated to oral administration, and used to estimate internal exposures to doses tested in an oral repeated dose toxicity study. Next, a human PBK dermal model was developed using measured human in vitro ADME data and a module to represent the dermal route. Model performance was confirmed by comparing predicted and measured values from a US-FDA clinical trial (Identifier: NCT03582215, https://clinicaltrials.gov/). Final exposure estimations were obtained in a virtual population and considering the in vitro and input parameter uncertainty. This model was then used to estimate the Cmax and AUC(0–24 h) of homosalate according to consumer use in a sunscreen. The developed rat and human PBK models had a good biological basis and reproduced in vivo legacy rat and human clinical kinetics data. They also complied with the most recent WHO and OECD recommendations for assessing the confidence level. In conclusion, we have developed a PBK model which predicted reasonably well the internal exposure of homosalate according to different exposure scenarios with a medium to high level of confidence. In the absence of in vivo data, such human PBK models will be the heart of future completely non-animal risk assessments; therefore, valid approaches will be key in gaining their regulatory acceptance.Clinical Trial Registration: https://clinicaltrials.gov/, identifier, NCT03582215

Highlights

  • All chemicals should be assessed for potential toxicity to humans before they are used in products

  • The automated parameter identification function in PK-Sim was used to optimize several homosalate-specific parameters to fit the observed concentration-time profile of homosalate in rats. These included, fraction unbound (Fu) and permeability between compartments, which were shown to significantly impact the distribution of homosalate and were optimized using predicted values based on compound properties

  • The optimized permeability values were: interstitial-to-intracellular and intracellular-to-interstitial permeability (4.83 cm/ min); endothelial permeability (1.9 cm/ min); and blood cell-to-plasma partition coefficient (21.28). These optimized values resulted in a concentration-time profile of homosalate that was similar to that measured in rats after IV administration of 0.5 mg/ kg (Figure 1B), with similar mean Cmax (320 ng/ ml predicted compared to the measured value of 338.3 ± 106.8 ng/ ml) and AUC(0-∞) values (123.1 ng h/ ml predicted compared to the measured value of 113.6 ± 22.9 ng h/ ml)

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Summary

Introduction

All chemicals should be assessed for potential toxicity to humans before they are used in products This has been achieved using standardized animal studies for evaluation of local and systemic effects. These are used to identify adverse effects, target organs, as well as the dose below which no adverse effects are observed (the no observed adverse effect level [NOAEL]). Ethical and legal considerations have led to a change in paradigm towards non-animal methods to evaluate the safety of chemicals for human use This change is important for cosmetics ingredients, for which animal testing has been banned since March 2013 (Eu, 2009), non-animal approaches are increasingly of interest for other sectors, such as industrial chemicals and environmental contaminants (Thomas et al, 2019)

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