PubMed · 8451799
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A Geisler, P Arup. 1993-02-22. [Fluoxetine].. https://pubmed.ncbi.nlm.nih.gov/8451799/
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Fluorinated organic compounds have been frequently detected in aquatic environments, with the widespread use of fluorinated drugs. The existing processes of urban sewage treatment plants are difficult to completely remove these pollutants containing the persistent C-F bonds. In this work, an integrated system of UV-activated sulfite and UV-assisted electrochemical oxidation was innovatively constructed for efficient degradation of fluoxetine. For the UV-activated sulfite unit system, when the sulfite dosage was 0.5 mmol/L and the initial pH was about 10, the defluorination efficiency of 5 mg/L fluoxetine wastewater under nitrogen atmosphere was about 98 %. Subsequently, the UV-assisted electrochemical oxidation unit system was employed to treat the reduced wastewater mentioned above. When the sodium chloride dosage was 25 mmol/L, the initial pH was about 5, and the current density was 30 mA/cm2, the total organic carbon (TOC) removal of the wastewater arrived at 65 %. Active species capture experiments and ESR tests confirmed that hydrated electrons, hydroxyl, and chlorine radicals were the main components for the efficient degradation of fluoxetine. According to the analysis of Fukui function and HPLC-MS, the degradation pathway of pollutants was proposed including defluorination and mineralization. Meanwhile, the toxicity of intermediates was predicted using the ECOSAR program. In addition, the verification test of actual wastewater treatment indicated that the defluorination and TOC removal efficiency of fluorouracil by the integrated system were similar to those for fluoxetine. This work provided a new approach for the efficient degradation of fluorinated organic pollutants in pharmaceutical wastewater.
A simple and innovative assay is described which allows the chiral separation of the four enantiomers of fluoxetine and norfluoxetine, with performance characteristics adequate for therapeutic drug monitoring. The assay requires liquid-liquid extraction into acetonitrile/n-hexane/isopropylic alcohol and re-extraction into phosphoric acid for clean-up. The acidic layer is injected onto the HPLC system after filtering. Separation of the analytes is achieved with a Chiralcel ODR column and a mobile phase consisting of potassium hexafluorophosphate/acetonitrile. Detection is made by ultraviolet absorbance at 227 nm. Standard curves are linear for each enantiomer (r(2)>/=0.992) over the range of 10-1000 ng/ml with a limit of quantification of 10 ng/ml for each enantiomer. Within-day and between-day CV% are </=10% for each enantiomer.
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