Stereoselective degradation of fungicide triadimenol in cucumber plants

The stereoselective degradation of triadimenol in different cucumber plant tissues (root, stem, leaf, and fruit) has been investigated. Rac‐triadimenol was applied to cucumber plants by root irrigation mode under field conditions. The degradation kinetics and the enantiomer fraction were determined by normal‐phase high‐performance liquid chromatography with diode array detector and on‐line optical rotatory dispersion detector on Chiralpak® AS‐H column. It has been shown that the degradation of triadimenol in cucumber plants was stereoselective under field conditions. The results indicated that RS enantiomer was degraded faster than SR enantiomer, and SS enantiomer was degraded faster than RR enantiomer, which resulted in plants enriched with SR and RR enantiomers. Furthermore, it was found that leaf was the dominating location for triadimenol enantiomer accumulation and stereoselective degradation, comparing with the root, stem, and fruit tissue. Chirality 2010. © 2009 Wiley‐Liss, Inc.     

Stereoselective bioaccumulation,transformation, and toxicity of triadimefon in Scenedesmus obliquus

In this study the stereoselective bioaccumulation and transformation of triadimefon and the toxicity of triadimefon and its metabolite triadimenol to the green algae Scenedesmus obliquus were studied. In growth inhibition experiments, triadimenol was more toxic than triadimefon, and (1S,2R)‐triadimenol, which has the largest fungicidal activity, presented the highest toxicity to the algae. In bioaccumulation experiments, triadimefon was rapidly taken up by algae cells, and the decrease in the concentration of triadimefon was accompanied by an increase in triadimenol. The transformation of S‐(+)‐ triadimefon was faster than that of the R‐(−)‐enantiomer, resulting in four triadimenol stereoisomers at different forming rates: B2 (1S, 2S) > B1 (1R, 2R) > A2 (1S, 2R) > A1 (1R, 2S). Thus, it is necessary to explore the enantioselective toxicology and ecological fate of these chiral pesticides in an environmental risk assessment. Also, their metabolites should be paid specific attention to since they may pose higher ecological risks.     

Epimerization in peptide thioester condensation

Peptide segment couplings are now widely utilized in protein chemical synthesis. One of the key structures for the strategy is the peptide thioester. Peptide thioester condensation, in which a C‐terminal peptide thioester is selectively activated by silver ions then condensed with an amino component, is a powerful tool. But the amino acid adjacent to the thioester is at risk of epimerization. During the preparation of peptide thioesters by the Boc solid‐phase method, no substantial epimerization of the C‐terminal amino acid was detected. Epimerization was, however, observed during a thioester–thiol exchange reaction and segment condensation in DMSO in the presence of a base. In contrast, thioester–thiol exchange reactions in aqueous solutions gave no epimerization. The epimerization during segment condensation was significantly suppressed with a less polar solvent that is applicable to segments in thioester peptide condensation. These results were applied to a longer peptide thioester condensation. The epimer content of the coupling product of 89 residues was reduced from 27% to 6% in a condensation between segments of 45 and 44 residues for the thioester and the amino component, respectively. Copyright © 2012 European Peptide Society and John Wiley & Sons, Ltd.     

Chiral Separation and Enantioselective Degradation of Vinclozolin in Soils

Vinclozolin is a chiral fungicide with potential environmental problems. The chiral separation of the enantiomers and enantioselective degradation in soil were investigated in this work. The enantiomers were separated by high‐performance liquid chromatography (HPLC) on Chiralpak IA, IB, and AZ‐H chiral columns under normal phase and the influence of the mobile phase composition on the separation was also studied. Complete resolutions were obtained on all three chiral columns under optimized conditions with the same elution order of (+)/(?). The residual analysis of the enantiomers in soil was conducted using accelerate solvent extraction followed by HPLC determination. The recoveries of the enantiomers ranged from 85.7–105.7% with relative standard deviation (SD) of 0.12–3.83%, and the limit of detection (LOD) of the method was 0.013 µg/g. The results showed that the degradations of vinclozolin enantiomers in the soils followed first‐order kinetics. Preferential degradation of the (?)‐enantiomer was observed only in one soil with the largest |ES| value of 0.047, and no obvious enantioselective degradation was observed in other soils. It was found that the persistence of vinclozolin in soil was related to pH values based on the half‐lives. The two enantiomers disappeared about 8 times faster in basic soils than that in neutral or acidic soils. Chirality 26:155–159, 2014. © 2014 Wiley Periodicals, Inc.     

Stereoselective Degradation of alpha‐Cypermethrin and Its Enantiomers in Rat Liver Microsomes

Alpha‐cypermethrin (α‐CP), [(RS)‐a‐cyano‐3‐phenoxy benzyl (1RS)‐cis‐3‐(2, 2‐dichlorovinyl)‐2, 2‐dimethylcyclopropanecarboxylate], comprises a diastereoisomer pair of cypermethrin, which are (+)‐(1R‐cis‐αS)–CP (insecticidal) and (?)‐(1S‐cis‐αR)–CP (inactive). In this experiment, the stereoselective degradation of α‐CP was investigated in rat liver microsomes by high‐performance liquid chromatography (HPLC) with a cellulose‐tris‐ (3, 5‐dimethylphenylcarbamate)‐based chiral stationary phase. The results revealed that the degradation of (?)‐(1S‐cis‐αR)‐CP was much faster than (+)‐(1R‐cis‐αS)‐CP both in enantiomer monomers and rac‐α‐CP. As for the enzyme kinetic parameters, there were some variances between rac‐α‐CP and the enantiomer monomers. In rac‐α‐CP, the V_max and CL_int of (+)‐(1R‐cis‐αS)–CP (5105.22 ± 326.26 nM/min/mg protein and 189.64 mL/min/mg protein) were about one‐half of those of (?)‐(1S‐cis‐αR)–CP (9308.57 ± 772.24 nM/min/mg protein and 352.19 mL/min/mg protein), while the K_m of the two α‐CP enantiomers were similar. However, in the enantiomer monomers of α‐CP, the V_max and K_m of (+)‐(1R‐cis‐αS) ‐CP were 2‐fold and 5‐fold of (?)‐(1S‐cis‐αR)‐CP, respectively, which showed a significant difference with rac‐α‐CP. The CL_int of (+)‐(1R‐cis‐αS)–CP (140.97 mL/min/mg protein) was still about one‐half of (?)‐(1S‐cis‐αR)–CP (325.72 mL/min/mg protein) in enantiomer monomers. The interaction of enantiomers of α‐CP in rat liver microsomes was researched and the results showed that there were different interactions between the IC₅₀ of (?)‐ to (+)‐(1R‐cis‐αS)‐CP and (+)‐ to (?)‐(1S‐cis‐αR)‐CP(IC_50(?)/(+) / IC_50(+)/(?) = 0.61). Chirality 28:58–64, 2016. © 2015 Wiley Periodicals, Inc.     

Organic Amendments to Enhance Atrazine and Metamitron Degradation in Two Contaminated Soils with Contrasting Textures

Among all types of xenobiotics, pesticides such as herbicides play a significant role in soil and water pollution due to their wide usage all over the world. This study addresses the ability of organic amendments to enhance atrazine and metamitron degradation in two herbicide-contaminated soils with contrasting textures under laboratory conditions. Soil samples were collected from surface soils with textures of sandy loam and silty clay, from northeastern Iran. Initial concentration of herbicides was 50 mg · kg^{? 1} soil. Contaminated soil samples were treated with manure, compost and vermicompost at rates of 0, 0.5, and 2% (w/w). Residual concentrations of atrazine and metamitron were determined by HPLC at the end of incubation periods of 20, 40, and 60 days. Residual concentrations of atrazine were 46.5, 38.9, and 36.2 mg · kg^{? 1} after 20, 40, and 60 days incubation, respectively. Residual metamitron concentrations were clearly lower than atrazine. After 20, 40, and 60 days, concentrations of metamitron were 2.9, 1.0, and 0.6 mg · kg^{? 1}, respectively. Organic amendments at the rates of 0.5 and 2% showed similar effects on the enhancement of herbicide degradation in soils. However, no statistically significant effect was observed among types of organic amendments (α = 0.05). Degradation was affected by soil textures. Residual concentrations of herbicides were higher in sandy loam than in silty clay soil.     

油脂下脚料中残油微生物降解初步研究

以油脂降解菌Bacillus sp DE-8为出发菌,对油脂下脚料中的残油生物降解条件进行初步研究。结果表明:该菌对油脂下脚料降解条件为:起始pH值为8,接种量4%、摇床转速为150r.min-1、温度为32℃、发酵72h,该菌株对菜籽饼的降解率可达78.8%。     

有机磷农药的微生物降解研究进展

微生物因种类和代谢多样性在有机磷农药降解中表现出独特的优势。对微生物降解有机磷农药的机制、微生物的获得、基因工程菌的构建及研究展望进行了综述。     

Stereoselective Degradation of Chiral Fungicide Myclobutanil in Rat Liver Microsomes

Myclobutanil, (RS)‐2‐(4‐chlorophenyl)‐2‐(1H‐1, 2, 4‐triazol‐1‐ylmethyl)hexanenitrile is a broad‐spectrum systemic triazole fungicide which consists of a pair of enantiomers. The stereoselective degradation of myclobutanil was investigated in rat liver microsomes. The concentrations of myclobutanil enantiomers were determined by high‐performance liquid chromatography (HPLC) with a cellulose‐tris‐(3,5‐dimethyl‐phenylcarbamate)‐based chiral stationary phase (CDMPC‐CSP) under reversed phase condition. The t_1/2 of (+)‐myclobutanil is 8.49 min, while the t_1/2 of (–)‐myclobutanil is 96.27 min. Such consequences clearly indicated that the degradation of myclobutanil in rat liver microsomes was stereoselective and the degradation rate of (+)‐myclobutanil was much faster than (–)‐myclobutanil. In addition, significant differences between two enantiomers were also observed in enzyme kinetic parameters. The V_max of (+)‐myclobutanil was about 4‐fold of (–)‐myclobutanil and the CL_int of (+)‐myclobutanil was three times as much as (–)‐myclobutanil after incubation in rat liver microsomes. Corresponding consequences may shed light on the environmental and ecological risk assessment for myclobutanil and may improve human health. Chirality 26:51–55, 2013. © 2013 Wiley Periodicals, Inc.     

废水中硫氰酸盐的微生物降解研究进展

硫氰酸盐(SCN-)是一种常见的金矿、纺织、印染和焦化工业污染物,有毒性、给生物安全带来危害.目前,随着现代生物技术的发展,通过高通量测序、转录组测序、DNA指纹图谱和靶向基因扩增等技术已经阐明了微生物降解硫氰酸盐的群落结构、遗传和代谢多样性,表明微生物降解硫氰酸盐是最可行的修复方法.综述了降解硫氰酸盐的微生物种类,碳...     

Stereoselective pharmacokinetics of diniconazole enantiomers in rabbits

Diniconazole [(E)-(RS)-1-(2,4,-dichlorophenyl)-4,4-dimethyl-2-(1H-1,2,4-triazole-1-yl)pent-1-en-3-ol)] is a potent triazole fungicide. The enantioselective pharmacokinetics of diniconazole enantiomers in rabbits was studied via intravenous (i.v.) injection. The pharmacokinetics and the enantiomer fraction (EF) were determined using normal high-performance liquid chromatography with diode array detection and a cellulose-tris-(3,5-dimethylphenylcarbamate)-based chiral stationary phase (CDMPC-CSP). The time-concentration curves in plasma were fitted by a two-compartment open mode. The results showed that the concentration of S-diniconazole in plasma decreased faster than that of R-diniconazole, and EFs increased with time after administration of racemic diniconazole (rac-diniconazole). The R-/S-enantiomer ratio of the area under the time-plasma concentration curve (AUC(0-infinity)) after administration was 1.52. The total plasma clearance value of S-enantiomer was 1.57-fold higher than that of the R-diniconazole. These results indicate substantial stereoselectivity in the kinetics of diniconazole enantiomers in rabbit.     

Stereoselective degradation of benalaxyl in tomato, tobacco, sugar beet, capsicum, and soil

The stereoselective degradation of the racemic benalaxyl in vegetables such as tomato, tobacco, sugar beet, capsicum, and the soil has been investigated. The two enantiomers of benalaxyl in the matrix were extracted by organic solvent and determined by validated chiral high-performance liquid chromatography with a cellulose-tris-(3, 5-dimethylphenylcarbamate)-based chiral column. Rac-benalaxyl was fortified into the soil and foliar applied to vegetables. The assay method was linear over a range of concentrations (0.5-50 microg ml(-1)) and the mean recoveries in all the samples were more than 70% for the two enantiomers. The limit of detection for both enantiomers was 0.05 microg g(-1). The results in soil showed that R-(-)-enantiomer dissipated faster than S-(+)-enantiomer and the stereoselectivity might be caused by microorganisms. In tomato, tobacco, sugar, beet, and capsicum plants, there was significantly stereoselective metabolism. The preferential absorption and degradation of S-(+)-enantiomer resulted an enrichment of the R-(-)-enantiomer residue in all the vegetables.     

氰化物在土壤中的自然降解模拟实验

通过对3种含不同氰化物浓度的粘黄土泥样的测定,探索氰化物在粘土中的降解规律。结果表明：粘黄土对氰化物（CN^-）有较强的吸附与净化作用;CN^-浓度随时间的变化符合一级动力学模式;制备土样中CN^-的初始浓度高降解慢,初始浓度低降解快。     

微生物信号分子降解酶研究进展

微生物细胞之间存在的信息交流称为群体感应。群体感应在实现微生物的生物学功能方面具有重要作用,包括调节致病性、参与生物膜的形成等。微生物能够分泌特定的信号分子,通过对信号分子的检测及应答,调控目的基因的表达。抑制信号分子的积累,能够干扰群体感应系统,使微生物丧失生物学功能。研究较为全面的一类信号分子是酰基高丝氨酸内酯(acylhomoserine lactone,AHL),此类信号分子可以通过酶法降解。目前已鉴定出的AHL降解酶主要分为AHL内酯酶和AHL酰化酶两类。综述了信号分子降解酶的来源、筛选方法、纯化技术、酶学性质、作用机制及在病害防治方面的应用。对信号分子降解酶的研究有助于完善群体感应系统的调控机制,并为微生物疾病的防治提供新策略。     

Biostimulation of n-Alkane Degradation in Diesel Fuel-Spiked Soils

Nutrient enhancement of bioremediation with nitrogen, namely biostimulation, increases process performance. Selection of a proper nitrogen source is critical for bioremediation applications. In this study, the effects of different nitrogen sources on biodegradation of C₁₀–C₂₅ n-alkane compounds in diesel fuel-spiked soil were revealed, and the most appropriate nitrogen source for biodegradation of semi- and non-volatile n-alkanes was investigated. Bioremediation of diesel fuel contaminated soil was monitored in lab-scale reactors for 15 days. Ammonium sulfate, potassium nitrate and urea were used as nitrogen sources. Carbon dioxide and oxygen levels in the reactors were recorded to monitor microbiological activity. Contaminant removal process was investigated by pH, heterotrophic plate count, total petroleum hydrocarbons (TPH) and C₁₀–C₂₅ n-alkane analyses. First-order kinetic constants were calculated via respirometric and contaminant concentration data. According to total C₁₀–C₂₅ n-alkane removal levels and degradation rate constants, ammonium sulfate addition resulted in the most efficient contaminant removal followed by potassium nitrate and urea. Simultaneous degradation of individual n-alkanes was observed for all of the nitrogen sources. Urea addition changed the distribution of individual n-alkane concentrations relative to the pre-experimental concentrations. Nitrogen source type had no differential effect on degradation rates of semi- (C₁₀–C₁₆) and non-volatile (C₁₇–C₂₅) fractions.     

环境中拟除虫菊酯类农药微生物降解技术研究进展

近年来,随着拟除虫菊酯类农药的大量及不合理使用,环境及食品中的农药残留对人类健康造成的负面影响日益显著。微生物降解农药作为去除农药污染安全高效的方法已成为当前研究热点之一。综述了国内外拟除虫菊酯类农药微生物降解菌的种类、降解机制、降解酶及降解菌应用的最新研究进展,并对亟须解决的重要问题进行了展望。     

Augmentation of a Microbial Consortium for Enhanced Polylactide (PLA) Degradation

Bioplastics are eco-friendly and derived from renewable biomass sources. Innovation in recycling methods will tackle some of the critical issues facing the acceptance of bioplastics. Polylactic acid (PLA) is the commonly used and well-studied bioplastic that is presumed to be biodegradable. Considering their demand and use in near future, exploration for microbes capable of bioplastic degradation has high potential. Four PLA degrading strains were isolated and identified as Penicillium chrysogenum, Cladosporium sphaerospermum, Serratia marcescens and Rhodotorula mucilaginosa. A consortium of above strains degraded 44 % (w/w) PLA in 30 days time in laboratory conditions. Subsequently, the microbial consortium employed effectively for PLA composting.

Electronic supplementary material

The online version of this article (doi:10.1007/s12088-015-0559-z) contains supplementary material, which is available to authorized users.     

Stereoselective degradation of fungicide benalaxyl in soils and cucumber plants

The enantioselective degradation of benalaxyl has been investigated to elucidate its behavior in several agricultural soils and plants (cucumber). Racemic benalaxyl was fortified into five types of agricultural soils and sprayed leaves of cucumber plants, respectively. The degradation kinetics and the enantiomer fraction (EF) were determined by normal-phase high-performance liquid chromatography (HPLC) with diode array detection (DAD) on the chiral column filled cellulose-tri-(3,5-dimethylphenylcarbamate)-based chiral stationary phase (CDMPC-CSP). The process of the degradation of benalaxyl enantiomers followed pseudo-first-order kinetics in cucumber plant. However, the dissipation phases of benalaxyl enantiomers in soils were biphasic ("slow-fast-slow" process). It has been shown that the degradation of benalaxyl was stereoselective. The results indicated that the (+)-S-benalaxyl showed a faster degradation in plants, while the (-)-R-benalaxyl showed a faster degradation in Soils 3, 4, and 5. No stereoselective degradation was observed in other soils.     

瘤胃微生物对纤维素的降解及其应用

瘤胃微生物主要包括细菌、真菌和原生动物。其中,瘤胃细菌和瘤胃真菌能分泌纤维素酶,对纤维素有较强的降解能力,主要介绍了瘤胃微生物对纤维素的降解作用及其广阔的应用前景。     

Enantioselective determination of triazole fungice tetraconazole by chiral high-performance liquid chromatography and its application to pharmacokinetic study in cucumber, muskmelon, and soils

A simple chiral high-performance liquid chromatography method with diode array detector was developed and validated for stereoselective determination of tetraconazole enantiomers in cucumber, muskmelon, and soils. Good separation was achieved at 20°C using cellulose tris-(4-methylbenzoate) as chiral stationary phase, a mixture of n-hexane and ethanol (90:10) as mobile phase at a flow rate of 0.8 ml/min. The assay method was linear over a range of concentrations (0.5-50 μg/ml) and the mean recoveries in all samples were more than 85% for the two enantiomers. The limits of detection for both enantiomers in plant and soil samples were 0.06 and 0.12 μg/g, respectively. Then, the proposed method was successfully applied to the study of enantioselective degradation of rac-tetraconazole in cucumber, muskmelon, and soils. The results showed that the degradation of two enantiomers of tetraconazole followed first-order kinetics and significantly stereoselective behavior was observed in cucumber, muskmelon, and Beijing soil. The preferential absorption and degradation of (-)-S-tetraconzole resulted in an enrichment of the (+)-R-tetraconazole residue in plant samples, whereas the (+)-R-tetraconazole showed a faster degradation in Beijing soil and the stereoselectivity might be caused by microorganisms. No stereoselective degradation was observed in Heilongjiang soil.