Evaluation of in vitro biotransformation of propranolol with HPLC, MS/MS, and two bioassays.

The majority of human drugs enter aquatic systems after ingestion and subsequent excretion in the form of parent compounds and metabolites. Environmental exposure to drug metabolites has not been reported so far. The goal of the present study was to apply the in vitro method of biotransformation of compounds with S9 fraction to the ecotoxicological analysis. beta-adrenoceptor antagonist propranolol was metabolized with S9 rat liver fraction. The parent compound was quantified with HPLC, and the metabolites were identified with QToF MS. Propranolol was metabolized rapidly, during the first hour its level decreased by 80 and 50% of the initial 20 and 100 mg L(-1), respectively. Ten peaks were observed on the HPLC-RF chromatogram. Four peaks were identified with QToF MS/MS propranolol (m/z = 260), N-desisopropylpropranolol (m/z = 218), hydroxypropranolol (m/z = 276), and hydroxy N-desisopropranolol glycol (m/z = 235). Then the ecotoxicity of the reaction mixture was studied with two bioassays Spirotox with the protozoan Spirostomum ambiguum and Thamnotoxkit F with the anostracean crustacean Thamnocephalus platyurus. Propranolol is twofolds more toxic to Spirotox than to Thamnotoxkit F with 24 h-EC50 = 1.77 mg L(-1) and 24 h-LC50 = 3.86 mg L(-1), respectively. No statistically significant differences were found between the toxicity of the reaction mixtures after S9 biotransformation and the propranolol solution. These results indicate that the biological activity of the metabolites is similar to that of the parent drug. The presented method of in vitro biotransformation of drugs with S9 fraction followed by HPLC and ecotoxicity tests, may be used as screening method for evaluation of the toxicity of drug metabolites.

Photodegradation and phototoxicity of thioridazine and chlorpromazine evaluated with chemical analysis and aquatic organisms.

The photochemical behaviour of chlorpromazine (CPZ) and thioridazine (THR) incubated under VIS light and a UV-A lamp was investigated with a high-performance liquid chromatography photodiode array detector (HPLC-PAD) and two bioassays. VIS light caused the decrease of CPZ and THR to 25% and 34% of the initial level, respectively, while UV-A degraded the drugs almost totally. CPZ and THR were very toxic to the protozoan Spirostomum ambiguum (Spirotox) and anostracan crustacean Thamnocephalus platyurus (Thamnotoxkit F) with 24-h LC50 values of around 0.5 mg l(-1). In spite of the drastic decrease of the concentration of the drugs, the irradiated samples were toxic to the protozoan, especially when a sublethal end-point was taken into consideration. Contrary to the protozoan the crustacean was not sensitive to the products of photodegradation. Mass spectrometry analysis showed the presence of dimers and trimers of the CPZ and mono-, di-, and tri-oxygenated derivatives of THR. The presented data give a strong indication of the importance of the investigation of the environmental fate of drugs, especially those known to be phototoxic.

Radiolytic degradation of herbicide 4-chloro-2-methyl phenoxyacetic acid (MCPA) by gamma-radiation for environmental protection.

Reversed-phase HPLC determination of the herbicide MCPA and its products of radiolytic degradation has been optimized. The radiolytic degradation was carried out using gamma-irradiation and was optimized in terms of irradiation dose and pH of irradiated MCPA solution. Decomposition of 100 ppm MCPA in pure solutions required irradiation with a 3 kGy dose. The main products of irradiation in the dose range up to 10-kGy were various phenolic compounds and carboxylic acids. The developed method was applied for treatment of industrial waste from production of MCPA. The 10-kGy dose was needed for decomposition of 500 ppm of MCPA in the industrial waste samples; however, the presence of stoichiometric amount of hydrogen peroxide in the irradiated waste allowed a 50% reduction of the gamma-irradiation dose. Despite complete decomposition of MCPA in the industrial waste, in order to reduce the toxicity of irradiated waste, measured by the Microtox bioluminescence test, higher than a 10 kGy irradiation dose was needed.

Monitoring of toxicity during degradation of selected pesticides using ionizing radiation.

The optimization of experimental conditions for radiolytic removal of organic pollutants from water and waste with the use of ionizing radiation via controlling the concentration of target compound(s) requires also monitoring the toxicity changes during the process. Commonly used herbicides 2,4-D and dicamba were shown to increase toxicity measured with the Microtox test at low irradiation doses resulting from formation of more toxic transient products, which can be decomposed at larger doses. The changes of toxicity were examined with respect to dose magnitude and the presence of commonly occurring scavengers of radiation.

Influence of pH on the toxicity of nitrophenols to Microtox and Spirotox tests.

The toxicity of mononitrophenols and dinitrophenols (DNP) to luminescent bacteria Vibrio fischeri (Microtox test) and ciliated protozoan Spirostomum ambiguum (Spirotox test) was evaluated. Spirotox was more sensitive to the tested nitrophenols (NPs) than the Microtox test. 2,5-DNP was the most toxic and 2-NP was the least toxic to the both bioindicators. The toxicity depended greatly on the pH of the medium. The highest changes were observed for DNPs, where the toxicity decreased more than 20-times when the pH increased from 6 to 8. No significant decrease of the toxicity was found for NPs, when the pH increased from 6 to 7. Greater increase of the pH to 8 caused from 1.5 to 4-fold decrease of the toxicity.

The toxicity of tri-substituted benzenes to the protozoan ciliate Spirostomum ambiguum.

The Spirotox test utilises a large ciliate protozoan Spirostomum ambiguum as a test organism. The goal of the present study was to evaluate the toxicity of tri-substituted benzenes in the Spirotox test. Twenty-six organic compounds were tested in this study and included: dimethylphenols (DMPs), dichlorophenols (DCMs), trichlorobenzenes (TCBs), dichloroanilines (DCAs), dinitrophenols (DNPs), dinitroaniline (DNA), dinitrochlorobenzene (DNCB) and dinitrofluorobenzene (DNFB). The toxicity of the compounds tested varied almost four orders of a magnitude. DMPs and DCAs were the least toxic, whereas dinitro derivatives were the most toxic to S. ambiguum. When chlorine or fluorine atoms were replaced by amino or hydroxy substituents, the toxicity increased dramatically. The results of the Spirotox test were compared with three other bioassays that are widely used around the world: Microtox, Tetrahymena pyriformis and Daphnia magna. The Spirotox was less sensitive than these other bioassays for the majority of these compounds, with an exception found for the dinitro derivatives.