An environmentally friendly method for the enantioseparation and determination of benalaxyl in tobacco and soil by ultra-performance convergence chromatography with tandem mass spectrometry.

For the purpose of chiral separation and determination of benalaxyl enantiomers in tobacco and soil, we developed a rapid, green, and sensitive method using ultra-performance convergence chromatography with tandem mass spectrometry. The samples were extracted and purified by the quick, easy, cheap, effective, rugged, and safe method before injection. The baseline separation was obtained on a chiral column in 5 min with carbon dioxide and ethanol as mobile phase. Separation parameters were optimized for the best separation efficiency. Under optimal conditions, the recoveries of both enantiomers were 77.1-98.4% with relative standard deviations <5.0% at spiked level of 0.1, 2.0, and 5.0 mg/kg in two matrices. Good coefficients of determination were achieved over the concentration range of 10-250 ng/mL. The limit of detection and the limit of quantification for all enantiomers ranged from 0.43 to 0.72 µg/kg and from 1.25 to 2.15 µg/kg, respectively. The results show that ultra-performance convergence chromatography with tandem mass spectrometry provides a reliable, green, and rapid method for the separation and determination of benalaxyl enantiomers in tobacco and soil. This method has important theoretical significance for studying the enantioselectivity and bioactivity of benalaxyl in the environment and in organisms.

In vitro metabolism of [14C]-benalaxyl in hepatocytes of rats, dogs and humans.

The in vitro comparative animal metabolism study is now a data requirement under EU Directive 1107/2009 for registration of plant protection products. This type of study helps determine the extent of metabolism of a chemical in each surrogate species and whether any unique human metabolite(s) are formed. In the present study, metabolism of racemic [14C]-benalaxyl, a fungicide was investigated in cryopreserved rat, dog and human hepatocytes. The metabolites generated were identified/characterized by LC/MS/MS with radiometric detection and comparison with reference standards. [14C]-glucuronide conjugates of benalaxyl metabolites in rat, dog and human hepatocytes were confirmed via additional experiments in which known reference standards were incubated with dog liver microsomes in the presence of UDPGA. After 4 h of incubation, benalaxyl was extensively metabolized in all the species with the following trend: dog (100%) > human (86%) > rat (75%). In all species, the major metabolic pathways consisted of hydroxylation of the methyl group in the xylene moiety to 2-hydroxymethyl-benalaxyl, further oxidation to its carboxylic acid analogue (benalaxyl-2-benzoic acid), and hydrolysis of the methyl ester to yield benalaxyl acid or 2-hydroxymethyl benalaxyl acid. In addition, glucuronidation of phase I metabolites occurred in all species, to a higher extent in dog hepatocytes in which 2-hydroxymethyl-benalaxyl-glucuronide conjugate constituted the most significant metabolite. No major unique metabolite was observed in human hepatocytes. Also, benalaxyl did not undergo stereo-selective metabolism in rat or human hepatocytes.

Stereoselective Behavior of the Fungicide Benalaxyl During Grape Growth and the Wine-Making Process.

Benalaxyl is widely applied as a fungicide during grape planting processing. In this experiment, the stereoselective behavior of benalaxyl was studied during the grape growth and wine-making process. A simple method based on high-performance liquid chromatography (HPLC) equipped with a chiral column and UV detector was established to separate and determine the enantiomers of benalaxyl. Stereoselective degradation of the two enantiomers of benalaxyl was found in grapes. The degradation of both enantiomers followed pseudofirst-order kinetics, and the degradation rate of R-(-)-benalaxyl was faster than S-(+)-benalaxyl. The half-life of R-(-)-benalaxyl was 27 h, while the half-life of S-(+)-benalaxyl was 31 h. The enantiomer fraction value decreased from 0.50 to 0.34 and finally only S-(+)-benalaxyl could be detected. In the fermentation process, both enantiomers of benalaxyl were hardly degraded, and no configuration interconversion was observed. Meanwhile, both enantiomers of benalaxyl showed little influence on the growth of the yeast, consumption of carbon sources, or production of alcohol. The result of this study might provide more sufficient data for the evaluation of food safety and potential risk. Chirality 28:394-398, 2016. © 2016 Wiley Periodicals, Inc.

Environmental behavior of benalaxyl and furalaxyl enantiomers in agricultural soils.

The enantioselective environmental behavior of the chiral fungicides benalaxy and furalaxyl in agricultural soils in China was studied. Although sorption onto soils was non-enantioselective, the leaching of benalaxy and furalaxyl was enantioselective in soil columns. The concentrations of the S-enantiomers of both fungicides in the leachates were higher than the R-enantiomers. This can be attributed to enantioselective degradation of the two fungicides in the soil column. Enantioselective degradation of the two fungicides was verified by soil dissipation experiments, and the R-enantiomers degraded faster than the S-enantiomers in partial soils. The half-life was 27.7-57.8 days for S-benalaxyl, 20.4-53.3 days for R-benalaxyl, 19.3-49.5 days for S-furalaxyl and 11.4-34.7 days for R-furalaxyl. The degradation process of the two fungicide enantiomers followed the first-order kinetics (R(2) > 0.96). Compared to furalaxyl, benalaxyl degraded more slowly and degradation was less enantioselective. These results are attributed to the influence of soil physicochemical properties, soil microorganisms, and environmental factors.

Review of the existing maximum residue levels for benalaxyl-M according to Article 12 of Regulation (EC) No 396/2005.

According to Article 12 of Regulation (EC) No 396/2005, EFSA has reviewed the maximum residue levels (MRLs) currently established at European level for the pesticide active substance benalaxyl-M. To assess the occurrence of benalaxyl-M residues in plants, processed commodities, rotational crops and livestock, EFSA considered the conclusions derived in the framework of Commission Regulation (EU) No 188/2011, the European authorisations for benalaxyl-M reported by Member States (including the supporting residues data) and also the authorised uses of benalaxyl reviewed by EFSA in the past (as they may generate common residues with benalaxyl-M) and the MRLs established for benalaxyl by the Codex Alimentarius Commission. Based on the assessment of the available data, MRL proposals were derived and a consumer risk assessment was carried out. Although no apparent risk to consumers was identified, some information required by the regulatory framework was missing. Hence, the consumer risk assessment is considered indicative only and all MRL proposals derived by EFSA still require further consideration by risk managers.

Subacute oral toxicity assessment of benalaxyl in mice based on metabolomics methods.

In this study, the metabolic responses of mice after 30 days of exposure to benalaxyl were assessed using NMR-based untargeted metabolomics and LC-MS-based targeted profiling of 20 amino acids. Urinary 1H NMR analyses revealed alterations in energy metabolism, lipid metabolism, vitamin B metabolism, the urea cycle and amino acid metabolism, and targeted analyses indicated that the serum levels of asparagine, histidine, lysine and aspartic acid were significantly altered. Additionally, significant oxidative stress was observed in the liver and kidney, although no apparent histopathological injury was observed. The tissue distribution indicated a significant stereoselectivity in the brain, where (-)-R-benalaxyl was enriched. These data provide a comprehensive picture of the subacute toxic effects of benalaxyl in mice. The results of this study suggested that, for a toxicity evaluation, metabolomics analysis is much more sensitive than traditional toxicological methods. The results also highlight the combined use of untargeted and targeted metabolomics approaches in evaluating the health risks of xenobiotics.

Effects of wastewater irrigation and sewage sludge application on soil residues of chiral fungicide benalaxyl.

The effects of wastewater irrigation and sewage sludge on the dissipation behavior of the fungicide benalaxyl and its primary metabolite benalaxyl acid in soil were studied on an enantiomeric level during a 148-day exposure experiment. Chiral separation and analysis of the two pairs of enantiomers were achieved using HPLC-MS/MS with a chiralpak IC chiral column. Benalaxyl decreased with half-life of 16.1 days in soil under tap water irrigation with preferential residue of S-benalaxyl. Benalaxyl acid was formed with great preference of R-enantiomer before 21 days while enriched in S-enantiomer afterwards. The degradation of benalaxyl was restrained by both wastewater and treated wastewater irrigation, but the enantioselectivity in S-benalaxyl residue was enhanced. Benalaxyl acid was also formed with similar enantioselectivity as in tap water irrigation. Sewage sludge could accelerate benalaxyl degradation with shorter half-life. Surprisingly, the enantioselectivity with preference degradation of S-enantiomer in sewage sludge was opposite to that in soil. More benalaxyl acid was generated with EF values always lower than 0.5 and remained longer in sewage sludge than in soil. A sterilization experiment indicated that the conversion of benalaxyl to benalaxyl acid and the enantioselectivity were determined by the microorganisms in soil or sewage sludge. Farming practices like wastewater irrigation and sewage sludge application might not only influence the fate of pesticide, but also the enantioselectivity of chiral pesticide enantiomers and thus the risks of pesticide residues posed to the environment.

Enantioselective metabolism and enantiomerization of benalaxyl in mice.

The enantiomerization and enantioselective metabolism of benalaxyl in mice after a single gavage administration were investigated in the present study. The pharmacokinetic result indicated that elimination of (-)-R-benalaxyl in plasma was slightly faster with the t1/2 of 26.65 h and 28.88 h for (-)-R- and (+)-S-benalaxyl, respectively. Consistent with this, elimination in tissues and excretion were also enantioselective, with (+)-S-benalaxyl enriched in all tissues, urine and feces. And formation of the metabolites also exhibited an enantioselective manner. Both benalaxyl and most of its metabolites exhibited a potent excretion to feces and urine. In addition, significant enantiomerization of benalaxyl enantiomers was observed in plasma, with a larger extent from R to S than S to R. Thus, this difference in enantiomerization may be one of the reasons to explain the enantioselective enrichment of (+)-S-benalaxyl in mice observed in this study. Data from this study proves that besides metabolic enzymes, enantiomerization could be another important factor that contributes to the enantioselective metabolism of a chiral pesticide. Thus, research at enantiomeric level is necessary for efficient risk assessment of chiral pesticides.

A combined non-targeted and targeted metabolomics approach to study the stereoselective metabolism of benalaxyl enantiomers in mouse hepatic microsomes.

Understanding of xenobiotic metabolism is necessary for risk assessment as well as toxicological research. In the present study, nanoLC/LTQ-Orbitrap mass based non-targeted metabolomics method coupled with ultra-performance liquid chromatography (UPLC)/triple quadrupole mass based targeted metabolomics method was carried out to investigate the stereoselective metabolism of benalaxyl in mouse hepatic microsomes. As a result, 7 metabolites of benalaxyl were identified, including 5 previously reported and 2 newly identified metabolites in present work. Hydroxylation, oxidation and esterolysis were major biotransformation reactions of benalaxyl in mouse hepatic microsomes. For stereoselective metabolism study, (-)-R-benalaxyl degraded much faster than its antipode with the t1/2 of 81.24 and 190.38 min for (-)-R- and (+)-S-benalaxyl, respectively. More importantly, stereoselectivity was also observed in the formation of the identified metabolites. In conclusion, the combined use of the mass spectrometry based targeted and non-targeted metabolomics provided a new approach to investigate stereoselective metabolism and identify novel metabolites of chiral pesticides. This study highlights the stereoselective metabolic profile of benalaxyl enantiomers and provides reliable data for benalaxyl toxicological risk assessment in mammal.

Fate and stereoselective behavior of benalaxyl in a water-sediment microcosm.

The environmental behavior and stereoselectivity of the chiral fungicide benalaxyl and its chiral metabolite benalaxyl acid in water, sediment, and water-sediment microcosms were studied. The microcosms were incubated at 25 °C with light or under darkness. The influencing factors such as light and microorganism were investigated. The results showed that benalaxyl had half-lives of >21 days in the microcosm system and that the metabolite benalaxyl acid could exist in the microcosm for >70 days. Benalaxyl was mainly transformed through microbial degradation, and thus sediment microorganisms played a major role in the dissipation of benalaxyl in the aquatic microcosm. The stereoselective behavior of benalaxyl and benalaxyl acid was also investigated. (-)-Benalaxyl was preferentially degraded in the microcosm, resulting in an enrichment of the more toxic enantiomer (+)-benalaxyl, which may cause higher risk to the aquatic system. Moreover, (-)-benalaxyl acid was preferentially formed in the microcosm. The enantioselectivity of the enantiomers in the microcosm should be taken into consideration for an accurate risk assessment.