Analytische Chemie
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- 2017 (2) (entfernen)
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- Photodegradation (2) (entfernen)
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In the aquatic environment, pharmaceutical drugs are submitted to degradation processes, where pho-todegradation is one of the most important mechanisms affecting the fate, persistence and toxicity of thecompounds. Carbamazepine, a widely used antiepileptic, is known to suffer photodegradation in waterbodies and generate photoproducts, some of them with higher potential toxicity than the parent com-pound. Therefore, to evaluate the toxic effects of CBZ when combined with its photoproducts, an acuteexposure (96 h) with the edible clam Scrobicularia plana was performed using environmental concentra-tions of CBZ (0.00–9.00 µg/L) irradiated (and non-irradiated) with simulated solar radiation. The analysisof the irradiated CBZ solutions by mass spectrometry revealed the formation of 5 photoproducts, includ-ing acridine (a compound known to be carcinogenic). Oxidative stress results showed that the exposureto CBZ photoproducts did not increase the toxicity to clams, by comparison with the parent compound.
Nowadays, electrochemistry coupled online to mass spectrometry (EC-MS) or to liquid chromatography-mass spectrometry (EC-LC-MS) is a technique of interest to investigate metabolic transformation of xenobiotics in living organisms. It enables the production of redox products in an electrochemical cell, the separation by an analytical column and the detection by mass spectrometry online. Furthermore, EC-LC-MS enables to determine short lived transformation products (TPs) and their bioconjugates in a fully automated way. Although the EC-MS selectivity is incomparable to enzymatic reactions, it is advantageous by reducing analysis time and matrix complexity compared to cytochrome based metabolism. However, in the development of EC-MS, most efforts are devoted for prediction of drug metabolism in the human body and there is very limited work on agrochemicals in general.
The main objective of this work was to develop an online EC-LC-MS method that could predict the metabolism of fluopyram (fungicide) and chlorpyrifos (insecticide). Oxidation products were produced by using a boron doped diamond electrode and characterized by either online LC-MS or offline LC-MS/MS. After incubation with rat and human liver microsomes, different targeted and suspected metabolites were identified by LC-MS/MS and high resolution-mass spectrometry (HR-MS) and compared with the EC based methods. Additionally, conjugation reactions with a variety of biomolecules such as glucoside and glutathione were investigated by trapping the oxidized species before entering to mass spectrometry.
In summary, phase-I metabolism by N-dealkylation, O-dealkylation, P-oxidation, hydroxylation and dearylation and phase-II metabolism by conjugation with glutathione mechanisms were successfully mimicked by EC-LC-MS. Fluopyram is primarily metabolized to 7- and 8-mono- hydroxyl, 7,8-di-hydroxyl and 2-trifluoromethyl benzamide, and chlorpyrifos is metabolized to chlorpyrifos oxon, trichloropyridinol, diethylthiophosphate and diethylphosphate.