Abstract
The kinetic bioconcentration of N-heterocyclic aromatic hydrocarbons and polycyclic aromatic hydrocarbons in mussels (Mytilus galloprovincialis) after short waterborne exposure was studied. Benzo[a]pyrene (BaP), its analogue azaarene 10-azabenzo[a]pyrene (AzaBaP), and their mixture (Mix), were selected to monitor the changes in water concentrations over three days. Decay of both PAHs concentrations in water after 24 h of waterborne exposure to mussels at levels of 10 and 100 μg/L follows a first order kinetic with half-lives of 4–5 h, with residual levels of PAHs below 7%. While steady-state scenarios are well studied, there is a lack of information of what happens under non-steady-state conditions, the main purpose of our paper. A synergistic bioconcentration of the mixture was found (around 800 in the mix vs. around 400 for individual PAHs at 100 μg/L of waterborne exposure). It could be explained by the following reasons. The most polar AzaBaP does not compete with the most non-polar BaP for the same tissue compartments. Whereas BaP aggregate in hydrophobic areas, AzaBaP can also do in hydrophilic areas. Moreover, a chance for complex formation between them by charge-transfer stabilization mechanisms could make possible a higher bioaccumulation as a mixture. Instead, toxicological results suggest an additive behaviour in the mixture performance, dominated by BaP, which is the key PAH controlling phase I metabolization in mussels, since is approx. three times more toxic. These experiments provide useful indications for a rapid assessment of PAHs kinetic bioconcentration in mussels.
Highlights
Azaarenes (N-heterocyclic aromatic hydrocarbons) are composed of an aromatic group and a six-membered ring structure, which contain one or more nitrogen atom (s) in place of a carbon atom (Bollag and Kaiser, 1991)
PAHs can enhance the intracellular generation of reactive oxygen species (ROS) with subsequent oxidative damage to macromolecules
Tissue compartments (Huckins et al, 1997). This fact increases the chances for overall kinetic bioconcentration, since −whereas BaP aggregate in hydrophobic areas- AzaBaP can do in hydrophilic areas (Carrell et al, 1997)
Summary
Azaarenes (N-heterocyclic aromatic hydrocarbons) are composed of an aromatic group and a six-membered ring structure, which contain one or more nitrogen atom (s) in place of a carbon atom (Bollag and Kaiser, 1991) They are generated, and released into the marine environment as the result of human activities, by incomplete combustion of fossil fuels, uncontrolled spills, surface runoff, and atmospheric deposition (Chen et al, 2008; Dong et al, 2015; Lintelmann et al, 2010; Yamamoto, 1992). The comparative performance is of key importance when oil spills and disasters take place in coastal areas to understand the environmental damage
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