Synthetic studies in the series of polyene macrolide antibiotics. 6. Synthesis of methyl-2,4,6-trideoxy-2,4-dimethyl-alpha-altro- hexopyranoside, the C33-C38 fragment of amphotericin B

The synthesis of methyl 2,4,6-trideoxy-2,4-dimethyl-alpha-L-altro-hexopyranoside, having the configuration of the C33-C38 fragment of amphotericin B, is described.     

Synthesis of 2,4-diacetamido-2,4,6-trideoxy-L-altrose, -L-idose, and -L-talose from benzyl 6-deoxy-3,4-O-isopropylidene-beta-L-galactopyranoside

Acetylation of benzyl 6-deoxy-3,4O-isopropylidene-β-L-galactopyranoside gave benzyl 2-O-acetyl-6-deoxy-3,4-O-isopropylidene-β-L-galactopyranoside (1). Removal of the isopropylidene group afforded benzyl 2-O-acetyl-6-deoxy-β-L-galactopyranoside (2), which was converted into benzyl 2-O-acetyl-6-deoxy-3,4-di-O-(methyl-sulfonyl)-β-L-galactopyranoside (3). Benzyl 2,3-anhydro-6-deoxy-4-O-(methyl-sulfonyl)-β-L-gulopyranoside (4) was obtained from 3 by treatment with alkali. Reaction of 4 with sodium azide in N,N-dimethylformamide gave a mixture of two isomeric benzyl 2,4-diazido-2,4,6-trideoxy hexoses, the syrupy diazido derivative 5 and the crystalline benzyl 2,4-diazido-2,4,6-trideoxy-β-L-idopyranoside (6). Acetylation of 6 afforded a compound whose n.m.r. spectrum was completely first order and in agreement with the structure of benzyl 3-O-acetyl-2,4-diazido-2,4,6-trideoxy-β-L-idopyranoside (7). Lithium aluminium hydride reduction of 5, followed by acetylation, afforded a crystalline product (8), shown by n.m.r. spectroscopy to be benzyl 2,4-diacetamido-3-O-acetyl-2,4,6-trideoxy-β-L-altropyranoside. Similar treatment of the diazido derivative 6 afforded benzyl 2,4-diacetamido-3-O-acetyl-2,4,6-trideoxy-β-L-idopyranoside (9). Compounds 8 and 9 could also be obtained from 4 by treatment of the crude diazido mixture with lithium aluminium hydride, with subsequent N-acetylation. The syrupy benzyl 2,4-diacetamido-2,4,6-trideoxy-β-L-altropyranoside (10) and the crystalline benzyl 2,4-diacetamido-2,4,6-trideoxy-β-L-idopyranoside (11) thus obtained were then O-acetylated to give 8 and 9 respectively. Benzyl 2,4-diacetamido-2,4,6-trideoxy-β-L-talopyranoside (15) was obtained from 11 by treatment with methanesulfonyl chloride and subsequent solvolysis. Compound 15 was O-acetylated to yield benzyl 2,4-diacetamido-3-O-acetyl-2,4,6-trideoxy-β-L-talopyranoside (16). the n.m.r. spectrum of which was in full agreement with the assigned structure. The mass spectra of compounds 8–11, 15, and 16 were also in agreement with their proposed structures. Removal of the benzyl groups from 10, 11 and 15 afforded the corresponding 2,4-diacetamido-2,4,6-trideoxyhexoses 12, 13, and 17, having the L-altro, L-ido, and L-talo configurations, respectively.     

Synthesis of 2,4-diacetamido-2,4,6-trideoxy-D-Galactose

Treatment of benzyl 2-acetamido-3-O-benzyl-2,6-dideoxy-4-O-(methylsulfonyl)-α-D-glucopyranoside (1) with sodium azide in hexamethylphosphoric triamide gave the 4-azido-α-D-galacto derivative (2), which was converted into benzyl 2,4-di-acetamido-3-O-benzyl-2,3,6-trideoxy-α-D-galactopyranoside (3) by hydrogenation and subsequent acetylation. Hydrogenolysis of 3 at atmospheric pressure afforded benzyl 2,4-diacetamido-2,4,6-tridcoxy-α-D-galactopyranoside (4), which was acetylated to give the 3-O-acetyl derivative (5). The n.m.r. spectrum of 5 was in agreement with the assigned structure and different from that of benzyl 2,4-di-acetamido-3-O-acetyl-α-D-glucopyranoside (9), which was prepared from the known benzyl 2,4-diacetamido-3-O-benzyl-2,4,6-trideoxy-α-D-glucopyranoside. Catalytic hydrogenolysis of 4 gave 2,4-diacetamido-2,4,6-trideoxy-D-galactose (6).     

Synthesis of 2,6,7-trideoxy-7-C-(2,4-dichlorophenyl)-D-xylo-heptonic acid and 6-(2,4-dichlorophenyl)-D-xylo-2,3,4-tri-hydroxyhexanesulfonic acid.

2,4-O-Benzylidene-L-xylose was converted via a Wittig reaction into Z-2,4-O-benzylidene-5,6-dideoxy-6-C-(2,4-dichlorophenyl)-D-xylo-hex-5-++ +enitol (17), which, on hydrogenation, gave 5,6-dideoxy-6-C-(2,4-dichlorophenyl)-D-xylo- hexitol (33). tert-Butyldimethylsililation of the primary hydroxyl group of 33, followed by 4-methoxybenzylation, and desilylation afforded 5,6-dideoxy-6-C-(2,4-dichlorophenyl)-2,3,4-tri-O-(4-methoxybenzyl)-D-xyl o- hexitol (54). A Mitsunobu-type reaction of 54 replaced HO-1 by cyanide to give, after hydrolysis and hydrogenolysis, 2,6,7-trideoxy-7-C-(2,4- dichlorophenyl)-D-xylo-heptono-1,4-lactone (55). Mesylation of 33 and then acetylation gave 2,3,4-tri-O-acetyl-5,6-dideoxy- 6-C-(2,4-dichlorophenyl)-1-O-methanesulfonyl-D-xylo-hexitol (63), which was converted via its 1-thiobenzoate into bis[1,5,6-trideoxy-6-C-(2,4-dichlorophenyl)-D-xylo-hexitol] 1,1'-disulfide (65). Acetylation of 65, followed by permanganate oxidation and deacetylation, afforded sodium 6-(2,4-dichlorophenyl)-D-xylo- 2,3,4-trihydroxy-hexanesulfonate (67). Both 57 (obtained from 55 by hydrolysis with NaOH) and 67 are weak inhibitors of HMG-CoA reductase.     

Fungal transformation of 2,4-dinitrotoluene and 2,4,6-trinitrotoluene.

Screening of 190 fungi representing 98 genera showed that the ability to transform 2,4,6-trinitrotoluene was common, whereas transformation of 2,4-dinitrotoluene was rare.     

Escherichia coli bioreporters for the detection of 2,4-dinitrotoluene and 2,4,6-trinitrotoluene

The primary explosive found in most land mines, 2,4,6-trinitrotoluene (2,4,6-TNT), is often accompanied by 2,4-dinitrotoluene (2,4-DNT) and 1,3-dinitrobenzene (1,3-DNB) impurities. The latter two compounds, being more volatile, have been reported to slowly leak through land mine covers and permeate the soil under which they are located, thus serving as potential indicators for buried land mines. We report on the construction of genetically engineered Escherichia coli bioreporter strains for the detection of these compounds, based on a genetic fusion between two gene promoters, yqjF and ybiJ, to either the green fluorescent protein gene GFPmut2 or to Photorhabdus luminescens bioluminescence luxCDABE genes. These two gene promoters were identified by exposing to 2,4-DNT a comprehensive library of about 2,000 E. coli reporter strains, each harboring a different E. coli gene promoter controlling a fluorescent protein reporter gene. Both reporter strains detected 2,4-DNT in an aqueous solution as well as in vapor form or when buried in soil. Performance of the yqjF-based sensor was significantly improved in terms of detection threshold, response time, and signal intensity, following two rounds of random mutagenesis in the promoter region. Both yqjF-based and ybiJ-based reporters were also induced by 2,4,6-TNT and 1,3-DNB. It was further demonstrated that both 2,4,6-TNT and 2,4-DNT are metabolized by E. coli and that the actual induction of both yqjF and ybiJ is caused by yet unidentified degradation products. This is the first demonstration of an E. coli whole-cell sensor strain for 2,4-DNT and 2,4,6-TNT, constructed using its own endogenous sensing elements.     

Biodegradation of 2,4,6-tribromophenol by Ochrobactrum sp. strain TB01

A bacterium that utilizes 2,4,6-tribromophenol (2,4,6-TBP) as sole carbon and energy source was isolated from soil contaminated with brominated pollutants. This bacterium, designated strain TB01, was identified as an Ochrobactrum species. The organism degraded 100 microM of 2,4,6-TBP within 36 h in a growing culture. In addition, it released 3 mol of bromine ions from 1 mol of 2,4,6-TBP during the complete degradation of 2,4,6-TBP in a resting cell assay. Moreover, cells grown on 2,4,6-TBP degraded 2,6-dibromophenol (2,6-DBP), 4-bromophenol (4-BP), 2,4,6-trichlorophenol (2,4,6-TCP) and phenol. Metabolic intermediates were detected in the reaction mixture of an in vitro assay for 2,4,6-TBP, and they were identified as 2,4-DBP and 2-BP. NADH was required for the debromination of 2,4,6-TBP. These results suggest that 2,4,6-TBP is converted to phenol through sequential reductive debromination reactions via 2,4-DBP and 2-BP by this strain.     

Biodegradation of 2,4,6-Tribromophenol by Ochrobactrum sp. Strain TB01

A bacterium that utilizes 2,4,6-tribromophenol (2,4,6-TBP) as sole carbon and energy source was isolated from soil contaminated with brominated pollutants. This bacterium, designated strain TB01, was identified as an Ochrobactrum species. The organism degraded 100 μM of 2,4,6-TBP within 36 h in a growing culture. In addition, it released 3 mol of bromine ions from 1 mol of 2,4,6-TBP during the complete degradation of 2,4,6-TBP in a resting cell assay. Moreover, cells grown on 2,4,6-TBP degraded 2,6-dibromophenol (2,6-DBP), 4-bromophenol (4-BP), 2,4,6-trichlorophenol (2,4,6-TCP) and phenol. Metabolic intermediates were detected in the reaction mixture of an in vitro assay for 2,4,6-TBP, and they were identified as 2,4-DBP and 2-BP. NADH was required for the debromination of 2,4,6-TBP. These results suggest that 2,4,6-TBP is converted to phenol through sequential reductive debromination reactions via 2,4-DBP and 2-BP by this strain.     

Fluorinated carbohydrates as potential plasma membrane modifiers. Synthesis of 4- and 6-fluoro derivatives of 2-acetamido-2-deoxy-D-hexopyranoses

2-Amino-2,4-dideoxy-4-fluoro- and 2-amino-2,4,6-trideoxy-4, 6-difluoro-D-galactose, and 2-amino-2,4-dideoxy-4-fluoro- and 2-amino-4-deoxy-4, 4-difluoro-D-xylo-hexose were synthesized, as potential modifiers of tumor cell-surface glyco-conjugate, from benzyl 2-acetamido-3-O-benzyl-2-deoxy-4, 6-di-O-mesyl-alpha-D-glucopyranoside and benzyl 2-acetamido-3, 6-di-O-benzyl-2-deoxy-4-O-mesyl-alpha-D-glucopyranoside, which were converted into the corresponding 4,6-difluoro-2,4, 6-trideoxy and 2,4-dideoxy-4-fluoro derivatives. Benzyl 2-acetamido-2-deoxy-4-O-mesyl-alpha-D-galactopyranoside and benzyl 2-acetamido-3,6-di-O-benzyl-2-deoxy-alpha-D-xylo-hexo-4-ulopyra noside were treated with diethylaminosulfur trifluoride to give 2-amino-2,4-dideoxy-4-fluoro-D-glucose and 2-amino-2,4-dideoxy-4, 4-di-fluoro-D-xylo-hexose derivatives, respectively, to give after deprotection the target compounds. Several of the peracetylated sugar derivatives inhibited L1210 tumor-cell growth in vitro at concentrations of 1-5 10(-5) M. The peracetylated derivative of 2-amino-2,4-dideoxy-4-fluoro-D-galactose inhibited protein and glycoconjugate biosynthesis, and also exhibited antitumor activity in mice with L1210 leukemia.     

Beta-oxidation of polyunsaturated fatty acids with conjugated double bonds. Mitochondrial metabolism of octa-2,4,6-trienoic acid.

The mitochondrial beta-oxidation of octa-2,4,6-trienoic acid was studied with the aim of elucidating the degradation of unsaturated fatty acids with conjugated double bonds. Octa-2,4,6-trienoic acid was found to be a respiratory substrate of coupled rat liver mitochondria, but not of rat heart mitochondria. Octa-2,4,6-trienoyl-CoA, the product of the inner-mitochondrial activation of the acid, was chemically synthesized and its degradation by purified enzymes of beta-oxidation was studied spectrophotometrically and by use of h.p.l.c. This compound is a substrate of NADPH-dependent 2,4-dienoyl-CoA reductase or 4-enoyl-CoA reductase (EC 1.3.1.34), which facilitates its further beta-oxidation. The product obtained after the NADPH-dependent reduction of octa-2,4,6-trienoyl-CoA and one round of beta-oxidation was hex-4-enoyl-CoA, which can be completely degraded via beta-oxidation. It is concluded that polyunsaturated fatty acids with two conjugated double bonds extending from even-numbered carbon atoms can be completely degraded via beta-oxidation because their presumed 2,4,6-trienoyl-CoA intermediates are substrates of 2,4-dienoyl-CoA reductase.     

Nitrite elimination and hydrolytic ring cleavage in 2,4,6-trinitrophenol (picric acid) degradation

Two hydrogenation reactions in the initial steps of degradation of 2,4,6-trinitrophenol produce the dihydride Meisenheimer complex of 2,4,6-trinitrophenol. The npdH gene (contained in the npd gene cluster of the 2,4,6-trinitrophenol-degrading strain Rhodococcus opacus HL PM-1) was shown here to encode a tautomerase, catalyzing a proton shift between the aci-nitro and the nitro forms of the dihydride Meisenheimer complex of 2,4,6-trinitrophenol. An enzyme (which eliminated nitrite from the aci-nitro form but not the nitro form of the dihydride complex of 2,4,6-trinitrophenol) was purified from the 2,4,6-trinitrophenol-degrading strain Nocardioides simplex FJ2-1A. The product of nitrite release was the hydride Meisenheimer complex of 2,4-dinitrophenol, which was hydrogenated to the dihydride Meisenheimer complex of 2,4-dinitrophenol by the hydride transferase I and the NADPH-dependent F(420) reductase from strain HL PM-1. At pH 7.5, the dihydride complex of 2,4-dinitrophenol is protonated to 2,4-dinitrocyclohexanone. A hydrolase was purified from strain FJ2-1A and shown to cleave 2,4-dinitrocyclohexanone hydrolytically to 4,6-dinitrohexanoate.     

厌氧微生物菌群XH-1对2,4,6-三氯苯酚的降解特性

有机污染物2,4,6-三氯苯酚(2,4,6-TCP)普遍存在于地下水和河流底泥等厌氧环境中。为了探究厌氧微生物菌群XH-1对2,4,6-TCP的降解能力,本研究以2,4,6-TCP为底物,接种XH-1建立微宇宙培养体系,并以中间产物4-氯苯酚(4-CP)和苯酚为底物分别进行分段富集培养,利用高效液相色谱分析底物的降解转化,同时基于16S rRNA基因高通量测序分析微生物群落结构变化。结果表明: 2,4,6-TCP(122 μmol·L^-1)以0.15 μmol·d^-1的速率在80 d内被完全降解转化,降解中间产物分别为2,4-二氯苯酚(2,4-DCP)、4-氯苯酚和苯酚,所有中间产物最终在325 d被完全降解。高通量测序结果表明,脱卤杆菌和脱卤球菌可能驱动2,4,6-TCP还原脱氯,其中,脱卤球菌可能在4-CP的脱氯转化中发挥重要作用,并与丁酸互营菌和产甲烷菌联合作用彻底降解2,4,6-TCP。     

Final stages of the preliminary metabolism of 2,4,6-trinitrotoluene in Pseudomonas fluorescens

The work was aimed at studying the transformation of 2,4-diamino-6-nitrotoluene (2,4-DA), an intermediate product in 2,4,6-trinitrotoluene catabolism by microorganisms. The results allow one to propose the following scheme for the terminal steps of TNT preparatory metabolism: 2,4-DA----[phloroglucinol carboxylic acid]----phloroglucinol----pyrogallol----ring cleavage.     

Stability of hydroxylamino- and amino-intermediates from reduction of 2,4,6-trinitrotoluene, 2,4-dinitrotoluene, and 2,6-dinitrotoluene

Hydroxylamines, produced as intermediates in the reductive metabolism of 2,4,6-trinitrotoluene, 2,4-dinitrotoluene, and 2,6-dinitrotoluene between nitroaromatic parent compounds and corresponding amines, were unstable in aqueous solution in the presence of O₂. Reactions of hydroxylamines to compounds other than amines may be the major cause of poor mass balance observations in bioremediation systems where only aminated products are monitored. Results demonstrate the formation of azoxy compounds as products of abiotic aryl-hydroxylamine reactions.     

Reaction of 1-fluoro-2,4-dinitrobenzene and 2,4,6-trinitrobenzenesulphonic acid with membranes of sarcoplasmic reticulum.

Membranes of sarcoplasmic reticulum were labelled with 1-fluoro-2,4-dinitro[3H]benzene at pH 6.5 and with 2,4,6-trinitrobenzenesulphonate at pH 9.2. Conditions were chosen to restrict reaction to amino groups, and the effect of blockings of these groups by methyl acetimidate was determined. All proteins were labelled to some extent by both reagents, but, whereas the trinitrophenylation of both lipid and protein amino groups was almost completely blocked by methyl acetimidate, the dinitrophenylation of the ATPase at pH 6.5 was much less affected. The seven amino groups on the ATPase that were labelled under these conditions did not react with methyl acetimidate. This reagent can therefore be used to enhance the specificity of fluorodinitrobenzene for amino groups in a hydrophobic environment. The amino groups on the minor proteins and on the phospholipids that reacted with fluorodinitrobenzene at pH 6.5 were probably in an aqueous environment, since the reaction was blocked by methyl acetimidate.     

Drosophila GSTs display outstanding catalytic efficiencies with the environmental pollutants 2,4,6-trinitrotoluene and 2,4-dinitrotoluene

The nitroaromatic explosive 2,4,6-trinitrotoluene (TNT) and the related 2,4-dinitrotoluene (DNT) are toxic environmental pollutants. The biotransformation and detoxication of these persistent compounds in higher organisms are of great significance from a health perspective as well as for the biotechnological challenge of bioremediation of contaminated soil. We demonstrate that different human glutathione transferases (GSTs) and GSTs from the fruit fly Drosophila melanogaster are catalysts of the biotransformation of TNT and DNT. The human GSTs had significant but modest catalytic activities with both DNT and TNT. However, D. melanogaster GSTE6 and GSTE7 displayed outstanding high activities with both substrates.     

Nitrite Elimination and Hydrolytic Ring Cleavage in 2,4,6-Trinitrophenol (Picric Acid) Degradation

Two hydrogenation reactions in the initial steps of degradation of 2,4,6-trinitrophenol produce the dihydride Meisenheimer complex of 2,4,6-trinitrophenol. The npdH gene (contained in the npd gene cluster of the 2,4,6-trinitrophenol-degrading strain Rhodococcus opacus HL PM-1) was shown here to encode a tautomerase, catalyzing a proton shift between the aci-nitro and the nitro forms of the dihydride Meisenheimer complex of 2,4,6-trinitrophenol. An enzyme (which eliminated nitrite from the aci-nitro form but not the nitro form of the dihydride complex of 2,4,6-trinitrophenol) was purified from the 2,4,6-trinitrophenol-degrading strain Nocardioides simplex FJ2-1A. The product of nitrite release was the hydride Meisenheimer complex of 2,4-dinitrophenol, which was hydrogenated to the dihydride Meisenheimer complex of 2,4-dinitrophenol by the hydride transferase I and the NADPH-dependent F₄₂₀ reductase from strain HL PM-1. At pH 7.5, the dihydride complex of 2,4-dinitrophenol is protonated to 2,4-dinitrocyclohexanone. A hydrolase was purified from strain FJ2-1A and shown to cleave 2,4-dinitrocyclohexanone hydrolytically to 4,6-dinitrohexanoate.     

Enhanced dechlorination of 2,4,6-trichlorophenol by anaerobic microbial populations in the presence of ethanol

Summary A consortium of anaerobic microorganisms was grown on acetate, ethanol, glucose or methanol and dechlorinated 50 umol 2,4,6-trichlorophenol, through 2,4-dichlorophenol, to 4-chlorophenol. The highest rate of dechlorination of 2,4,6-trichlorophenol was observed when ethanol was used as a growth substrate.     

Role of mycelium and extracellular protein in the biodegradation of 2,4,6-trichlorophenol by Phanerochaete chrysosporium.

The biodegradation of 2,4,6-trichlorophenol (2,4,6-TCP) by Phanerochaete chrysosporium was studied in batch systems. In experiments with mycelial suspension, the degradation of 2,4,6-TCP was found to occur in the absence of ligninase. Chloride ion was recovered in nearly stoichiometric amounts at the end of the process. The microorganism did not retain its degradation ability for more than 6 days under substrate-deficient conditions. Neither the mycelium nor the extracellular protein alone could degrade 2,4,6-TCP; both were required for complete degradation to occur. In experiments in which 2,4,6-TCP was exposed to the culture supernatant separated from its mycelium, negligible degradation was obtained and no chloride ion was recovered. No degradation was observed even when the supernatant was supplemented with hydrogen peroxide as a possible cosubstrate. In experiments performed with washed mycelium separated from its supernatant, no degradation took place until the mycelium released additional extracellular protein 5 to 6 h into the incubation. Additions of washed mycelium separated from its supernatant to active cultures also produced an increase in the rate of degradation in correspondence with the protein release. The protein release was independent of the presence of 2,4,6-TCP. The addition of cycloheximide to inhibit the synthesis of de novo proteins completely suppressed the release of protein by the mycelium and resulted in no 2,4,6-TCP degradation. Additions of culture supernatants containing a high concentration of extracellular protein to active cultures produced an increase in the rate of 2,4,6-TCP degradation.(ABSTRACT TRUNCATED AT 250 WORDS)     

Aerobic Biodegradation of 2,4-Dinitroanisole by Nocardioides sp. Strain JS1661

2,4-Dinitroanisole (DNAN) is an insensitive munition ingredient used in explosive formulations as a replacement for 2,4,6-trinitrotoluene (TNT). Little is known about the environmental behavior of DNAN. There are reports of microbial transformation to dead-end products, but no bacteria with complete biodegradation capability have been reported. Nocardioides sp. strain JS1661 was isolated from activated sludge based on its ability to grow on DNAN as the sole source of carbon and energy. Enzyme assays indicated that the first reaction involves hydrolytic release of methanol to form 2,4-dinitrophenol (2,4-DNP). Growth yield and enzyme assays indicated that 2,4-DNP underwent subsequent degradation by a previously established pathway involving formation of a hydride-Meisenheimer complex and release of nitrite. Identification of the genes encoding the key enzymes suggested recent evolution of the pathway by recruitment of a novel hydrolase to extend the well-characterized 2,4-DNP pathway.