(S)-(-)-Ofloxacin and (R)-(+)-ofloxacin concentrations in the plasma of Pagrosomus major after drug treatment were detected by chiral high-performance liquid chromatography, and various pharmacokinetic parameters were calculated from these data. The elimination half-life of (S)-(-)-ofloxacin was significantly shorter than that of the (R)-(+) enantiomer. (S)-(-)-Ofloxacin also had a significantly lower maximum plasma concentration, area under the concentration-time curve from zero to infinity, and mean residence time than (R)-(+)-ofloxacin. However, the apparent volume of distribution and total body clearance of (S)-(-)-ofloxacin were greater than those of (R)-(+)-ofloxacin. The ratio of the (S)-(-)- to (R)-(+)-ofloxacin plasma concentration was always <1.0. Together, these data suggest that (S)-(-)-ofloxacin was preferentially excreted and (R)-(+)-ofloxacin was preferentially absorbed. Although the difference in pharmacokinetic parameters was small, the metabolic behavior of the ofloxacin enantiomers in P. major was enantioselective.

In this work, flumequine (FLU) enantiomers were separated using a Chiralpak OD-H column, with n-hexane-ethanol (20:80, v/v) as the mobile phase at a flow rate of 0.6 mL/min. Solid phase extraction (SPE) was used for cleanup and enrichment. The limit of detection, limit of quantitation, linearity, precision, and intra/interday variation of the chiral high-performance liquid chromatography (HPLC) method were determined. The developed method was then applied to investigate the degradation behavior of FLU enantiomers in mariculture pond water samples. The results showed that the degradation of FLU enantiomers under natural, sterile, or dark conditions was not enantioselective. Chirality 28:649-655, 2016. © 2016 Wiley Periodicals, Inc.

Trichlorfon (TF), an organophosphorus insecticide, has been widely used in seawater aquaculture; it is easily degraded to the highly toxic insecticide, dichlorvos (DDVP). In this study, the enantioseparation of TF enantiomers, as well as their degradation behavior and product (DDVP) formation in mariculture pond sediments, was investigated. The results show that both TF enantiomers degrade into DDVP, which is the main degradation product. Furthermore, S-(+)-TF is preferentially degraded under natural conditions, suggesting that TF enantiomers degrade enantioselectively. Nevertheless, the degradation behavior of TF enantiomers is not enantiospecific under sterile conditions. The formation of DDVP and the enantiospecific degradation of TF enantiomers are attributed to the activities of microbes present in the sediments.