Defining and Controlling Exposure During In Vitro Toxicity Testing and the Potential of Passive Dosing.

Toxicity testing using in vitro bioassays is assuming an increasingly important role. Nevertheless, several issues remain with regard to their proper application, which mainly relate to the proper definition and control of the test chemical(s) concentrations to which the cells or tissues are exposed. This has fundamental implications for understanding the underlying relationship between the in vitro exposure regime and response, and leads to uncertainty in the resulting bioassay data. This chapter covers the definition and control of exposure of hydrophobic organic chemicals (HOCs) in in vitro bioassays aimed at measuring their toxicity. A review of the fate of HOCs in typical in vitro set-ups is followed by a discussion of how to define the test exposure. Currently applied approaches for introducing HOCs into in vitro bioassays are then related to these different definitions of test exposure. Finally, passive dosing as one possible approach for giving defined and constant dissolved concentrations of HOCs in in vitro toxicity tests is introduced, using examples taken from the literature, and how this might be better integrated into high throughput in vitro toxicity testing is discussed.

Microplastics as vectors for bioaccumulation of hydrophobic organic chemicals in the marine environment: A state-of-the-science review.

A state-of-the-science review was conducted to examine the potential for microplastics to sorb hydrophobic organic chemicals (HOCs) from the marine environment, for aquatic organisms to take up these HOCs from the microplastics, and for this exposure to result in adverse effects to ecological and human health. Despite concentrations of HOCs associated with microplastics that can be orders of magnitude greater than surrounding seawater, the relative importance of microplastics as a route of exposure is difficult to quantify because aquatic organisms are typically exposed to HOCs from various compartments, including water, sediment, and food. Results of laboratory experiments and modeling studies indicate that HOCs can partition from microplastics to organisms or from organisms to microplastics, depending on experimental conditions. Very little information is available to evaluate ecological or human health effects from this exposure. Most of the available studies measured biomarkers that are more indicative of exposure than effects, and no studies showed effects to ecologically relevant endpoints. Therefore, evidence is weak to support the occurrence of ecologically significant adverse effects on aquatic life as a result of exposure to HOCs sorbed to microplastics or to wildlife populations and humans from secondary exposure via the food chain. More data are needed to fully understand the relative importance of exposure to HOCs from microplastics compared with other exposure pathways. Environ Toxicol Chem 2016;35:1667-1676. © 2016 SETAC.

Modelling bioaccumulation of oil constituents in aquatic species.

Crude oil poses a risk to marine ecosystems due to its toxicity and tendency to accumulate in biota. The present study evaluated the applicability of the OMEGA model for estimating oil accumulation in aquatic species by comparing model predictions of kinetic rates (absorption and elimination) and bioconcentration factors (BCF) with measured values. The model was a better predictor than the means of the measurements for absorption and elimination rate constants, but did not outperform the mean measured BCF. Model estimates and measurements differed less than one order of magnitude for 91%, 80% and 61% of the absorption and elimination rates and BCFs of all oil constituents, respectively. Of the "potentially modifying" factors: exposure duration, biotransformation, molecular mass, and water temperature, the last two tended to influence the performance of the model. Inclusion of more explanatory variables in the bioaccumulation model, like the molecular mass, is expected to improve model performance.