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1
Bacterial o-methylation of chloroguaiacols: effect of substrate concentration, cell density, and growth conditions.细菌对愈创木酚的 O-甲基化:基质浓度、细胞密度和生长条件的影响。
Appl Environ Microbiol. 1985 Feb;49(2):279-88. doi: 10.1128/aem.49.2.279-288.1985.
2
Transformations of chloroguaiacols, chloroveratroles, and chlorocatechols by stable consortia of anaerobic bacteria.厌氧细菌稳定菌群对氯代愈创木酚、氯代藜芦醚和氯代儿茶酚的转化作用
Appl Environ Microbiol. 1987 Oct;53(10):2511-9. doi: 10.1128/aem.53.10.2511-2519.1987.
3
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Bacterial O-methylation of halogen-substituted phenols.卤素取代酚类的细菌O-甲基化作用。
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Chlorophenols, chlorocatechols and chloroguaiacols induce DNA base oxidation in human lymphocytes (in vitro).氯酚、氯邻苯二酚和氯愈创木酚诱导人淋巴细胞中的 DNA 碱基氧化(体外)。
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Appl Environ Microbiol. 1993 Oct;59(10):3424-9. doi: 10.1128/aem.59.10.3424-3429.1993.

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1
Degradation of 4,5-dichloroguaiacol by soil microorganisms.土壤微生物对 4,5-二氯愈创木酚的降解。
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Methylation of halogenated phenols and thiophenols by cell extracts of gram-positive and gram-negative bacteria.革兰氏阳性菌和革兰氏阴性菌细胞提取物对卤代酚和硫代酚的甲基化作用。
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6
Biotransformations of chloroguaiacols, chlorocatechols, and chloroveratroles in sediments.沉积物中愈创木酚、邻苯二酚和藜芦醇的生物转化。
Appl Environ Microbiol. 1986 Mar;51(3):552-8. doi: 10.1128/aem.51.3.552-558.1986.
7
Metabolism of chlorinated guaiacols by a guaiacol-degrading Acinetobacter junii strain.一株降解愈创木酚的琼氏不动杆菌对氯代愈创木酚的代谢
Appl Environ Microbiol. 1993 Oct;59(10):3424-9. doi: 10.1128/aem.59.10.3424-3429.1993.
8
Bacterial O-methylation of halogen-substituted phenols.卤素取代酚类的细菌O-甲基化作用。
Appl Environ Microbiol. 1987 Apr;53(4):839-45. doi: 10.1128/aem.53.4.839-845.1987.
9
Transformations of chloroguaiacols, chloroveratroles, and chlorocatechols by stable consortia of anaerobic bacteria.厌氧细菌稳定菌群对氯代愈创木酚、氯代藜芦醚和氯代儿茶酚的转化作用
Appl Environ Microbiol. 1987 Oct;53(10):2511-9. doi: 10.1128/aem.53.10.2511-2519.1987.
10
Hydroxylation and dechlorination of chlorinated guaiacols and syringols by Rhodococcus chlorophenolicus.嗜氯红球菌对氯代愈创木酚和丁香酚的羟基化和脱氯作用
Appl Environ Microbiol. 1988 Mar;54(3):683-7. doi: 10.1128/aem.54.3.683-687.1988.

本文引用的文献

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Observations on the distinction between oligotrophic and eutrophic marine bacteria.富营养化和贫营养化海洋细菌的区别观察。
Appl Environ Microbiol. 1984 May;47(5):1017-22. doi: 10.1128/aem.47.5.1017-1022.1984.
2
Suicide Inactivation of Catechol 2,3-Dioxygenase from Pseudomonas putida mt-2 by 3-Halocatechols.假单胞菌 mt-2 儿茶酚 2,3-双加氧酶的自杀失活作用 3-卤代儿茶酚。
Appl Environ Microbiol. 1984 Mar;47(3):500-5. doi: 10.1128/aem.47.3.500-505.1984.
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Novel Biotransformations of 7-Ethoxycoumarin by Streptomyces griseus.灰色链霉菌对 7-乙氧基香豆素的生物转化。
Appl Environ Microbiol. 1983 Aug;46(2):468-74. doi: 10.1128/aem.46.2.468-474.1983.
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Bacterial methylation of chlorinated phenols and guaiacols: formation of veratroles from guaiacols and high-molecular-weight chlorinated lignin.细菌对氯代苯酚和愈创木酚的甲基化:愈创木酚与高分子量氯化木质素生成藜芦醇。
Appl Environ Microbiol. 1983 Mar;45(3):774-83. doi: 10.1128/aem.45.3.774-783.1983.
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Structure-activity relationships in microbial transformation of phenols.酚类微生物转化中的构效关系。
Appl Environ Microbiol. 1982 Jul;44(1):153-8. doi: 10.1128/aem.44.1.153-158.1982.
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Kinetics and extent of mineralization of organic chemicals at trace levels in freshwater and sewage.痕量水平的有机化学品在淡水和污水中的矿化动力学和程度。
Appl Environ Microbiol. 1982 May;43(5):1139-50. doi: 10.1128/aem.43.5.1139-1150.1982.
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Rates of mineralization of trace concentrations of aromatic compounds in lake water and sewage samples.水中痕量芳香族化合物的矿化率。湖水和污水样品。
Appl Environ Microbiol. 1982 May;43(5):1133-8. doi: 10.1128/aem.43.5.1133-1138.1982.
8
Second-order model to predict microbial degradation of organic compounds in natural waters.预测天然水中有机化合物微生物降解的二阶模型。
Appl Environ Microbiol. 1981 Mar;41(3):603-9. doi: 10.1128/aem.41.3.603-609.1981.
9
Effect of concentration of organic chemicals on their biodegradation by natural microbial communities.有机化学品浓度对自然微生物群落生物降解的影响。
Appl Environ Microbiol. 1979 Jun;37(6):1211-6. doi: 10.1128/aem.37.6.1211-1216.1979.
10
Production of methanol from aromatic acids by Pseudomonas putida.恶臭假单胞菌利用芳香酸生产甲醇。
J Bacteriol. 1980 Jun;142(3):916-24. doi: 10.1128/jb.142.3.916-924.1980.

细菌对愈创木酚的 O-甲基化:基质浓度、细胞密度和生长条件的影响。

Bacterial o-methylation of chloroguaiacols: effect of substrate concentration, cell density, and growth conditions.

机构信息

Swedish Environmental Research Institute, Box 21060, S-100 31 Stockholm, Sweden.

出版信息

Appl Environ Microbiol. 1985 Feb;49(2):279-88. doi: 10.1128/aem.49.2.279-288.1985.

DOI:10.1128/aem.49.2.279-288.1985
PMID:16346715
原文链接:https://pmc.ncbi.nlm.nih.gov/articles/PMC238394/
Abstract

O-methylation of chloroguaiacols has been examined in a number of gram-positive and gram-negative bacteria to elucidate the effects of substrate concentration, growth conditions, and cell density. Substrate concentrations between 0.1 and 20.0 mg liter were used, and it was found that (i) yields of the O-methylated products were significantly higher at the lowest concentrations and (ii) rates of O-methylation were not linear functions of concentration. With 3,4,5-trichloroguaiacol, the nature of the metabolites also changed with concentration. During growth with a range of substrates, O-methylation of chloroguaiacols also took place. With vanillate, however, de-O-methylation occurred: the chlorocatechol formed from 4,5,6-trichloroguaiacol was successively O-methylated to 3,4,5-trichloroguaiacol and 3,4,5-trichloroveratrole, whereas that produced from 4,5-dichloroguaiacol was degraded without O-methylation. Effective O-methylation in nonproliferating suspensions occurred at cell densities as low as 10 cells ml, although both the yields and the rates were lower than in more dense cultures. By using disk assays, it was shown that, compared with their precursors, all of the O-methylated metabolites were virtually nontoxic to the strains examined. It is therefore proposed that O-methylation functions as a detoxification mechanism for cells exposed to chloroguaiacols and chlorophenols. In detail, significant differences were observed in the response of gram-positive and gram-negative cell strains to chloroguaiacols. It is concluded that bacterial O-methylation is to be expected in the natural environment subjected to discharge of chloroguaiacols.

摘要

已在许多革兰氏阳性和革兰氏阴性细菌中研究了对氯愈创木酚的 O-甲基化作用,以阐明底物浓度、生长条件和细胞密度的影响。使用了 0.1 至 20.0mg 升之间的底物浓度,结果发现:(i)在最低浓度下,O-甲基化产物的产率显著更高;(ii)O-甲基化速率不是浓度的线性函数。用 3,4,5-三氯愈创木酚,代谢物的性质也随浓度而变化。在一系列底物的生长过程中,氯愈创木酚的 O-甲基化也发生了。然而,用香草酸盐时,发生了去 O-甲基化:从 4,5,6-三氯愈创木酚形成的氯邻苯二酚相继被 O-甲基化为 3,4,5-三氯愈创木酚和 3,4,5-三氯藜芦醇,而从 4,5-二氯愈创木酚形成的产物则在没有 O-甲基化的情况下被降解。在细胞密度低至 10 个细胞/ml 的非增殖悬浮液中有效进行 O-甲基化,尽管产率和速率均低于更密集的培养物。通过使用圆盘测定法,表明与它们的前体相比,所有 O-甲基化代谢物对所检查的菌株几乎都没有毒性。因此,提议 O-甲基化是暴露于对氯愈创木酚和氯苯酚的细胞的解毒机制。详细地,观察到革兰氏阳性和革兰氏阴性细胞株对氯愈创木酚的反应有显著差异。结论是,在受到氯愈创木酚排放影响的自然环境中,预计会发生细菌 O-甲基化。