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1
Location and consequences of 1,1,1-trichloro-2,2-bis(p-chlorophenyl) ethane uptake by Bacillus megaterium.巨大芽孢杆菌对1,1,1-三氯-2,2-双(对氯苯基)乙烷的摄取位置及后果
Appl Microbiol. 1973 Mar;25(3):381-7. doi: 10.1128/am.25.3.381-387.1973.
2
Extraction of DDT [1,1,1,-trichloro-2,2-bis(p-chlorophenyl)ethane] and its metabolites DDE [1,1-dichloro-2,2-bis(p-chlorophenyl)-ethylene] and DDD [1,1-dichloro-2,2-bis(p-chlorophenyl)-ethane]) from aged contaminated soil.从老化污染土壤中提取滴滴涕[1,1,1-三氯-2,2-双(对氯苯基)乙烷]及其代谢产物滴滴伊[1,1-二氯-2,2-双(对氯苯基)乙烯]和滴滴滴[1,1-二氯-2,2-双(对氯苯基)乙烷] 。
J Chromatogr A. 2000 Apr 7;874(2):257-64. doi: 10.1016/s0021-9673(00)00101-1.
3
Metabolism of 1,1,1-trichloro-2,2-bis(p-chlorophenyl)ethane (DDT), 1,1-dichloro-2,2-bis(p-chlorophenyl)ethane, and 1-chloro-2,2-bis(p-chlorophenyl)ethene in the hamster.仓鼠体内1,1,1-三氯-2,2-双(对氯苯基)乙烷(滴滴涕)、1,1-二氯-2,2-双(对氯苯基)乙烷及1-氯-2,2-双(对氯苯基)乙烯的代谢
Cancer Res. 1983 Jun;43(6):2644-7.
4
Metabolism of 1,1,1-trichloro-2,2-bis(p-chlorophenyl)-ethane and 1,1-dichloro-2,2-bis(p-chlorophenyl)ethane in the mouse.1,1,1-三氯-2,2-双(对氯苯基)乙烷和1,1-二氯-2,2-双(对氯苯基)乙烷在小鼠体内的代谢
Chem Biol Interact. 1982 Sep;41(3):327-39. doi: 10.1016/0009-2797(82)90109-0.
5
The metabolism in vivo of 1,1,1-trichloro-2,2-bis(p-chlorophenyl)ethane (DDT), 1,1-dichloro-2,2-bis(p-chlorophenyl)ethane (DDD) and 1,1-dichloro-2,2-bis(p-chlorophenyl)ethylene (DDE) in the chick by embryonic injection and dietary ingestion.通过胚胎注射和饮食摄入,研究1,1,1-三氯-2,2-双(对氯苯基)乙烷(滴滴涕)、1,1-二氯-2,2-双(对氯苯基)乙烷(滴滴滴)和1,1-二氯-2,2-双(对氯苯基)乙烯(滴滴伊)在雏鸡体内的代谢情况。
Biochem Pharmacol. 1968 Oct;17(10):2143-61. doi: 10.1016/0006-2952(68)90189-5.
6
Bacterial and fungal cometabolism of 1,1,1-trichloro-2,2-bis(4-chlorophenyl)ethane (DDT) and its breakdown products.1,1,1-三氯-2,2-双(4-氯苯基)乙烷(滴滴涕)及其分解产物的细菌和真菌共代谢作用
Appl Environ Microbiol. 1985 Mar;49(3):509-16. doi: 10.1128/aem.49.3.509-516.1985.
7
Biodegradation of DDT [1,1,1-trichloro-2,2-bis(4-chlorophenyl)ethane] by the white rot fungus Phanerochaete chrysosporium.白腐真菌黄孢原毛平革菌对滴滴涕[1,1,1-三氯-2,2-双(4-氯苯基)乙烷]的生物降解作用。
Appl Environ Microbiol. 1987 Sep;53(9):2001-8. doi: 10.1128/aem.53.9.2001-2008.1987.
8
Characterization of new bacterial transformation products of 1,1,1-trichloro-2,2-bis-(4-chlorophenyl) ethane (DDT) by gas chromatography/mass spectrometry.气相色谱/质谱法对1,1,1-三氯-2,2-双(4-氯苯基)乙烷(滴滴涕)新细菌转化产物的表征
Biomed Environ Mass Spectrom. 1989 Sep;18(9):741-52. doi: 10.1002/bms.1200180917.
9
Thiol stimulation of the cytochrome P-450-dependent reduction of 1,1,1-trichloro-2,2-bis(p-chlorophenyl)ethane (DDT) to 1,1-dichloro-2,2-bis(p-chlorophenyl)ethane (DDD).
Biochem Pharmacol. 1986 Jun 1;35(11):1805-7. doi: 10.1016/0006-2952(86)90296-0.
10
Distribution and effects of 2,4,5-trichlorophenoxyacetic acid in cells of Bacillus megaterium.2,4,5-三氯苯氧乙酸在巨大芽孢杆菌细胞中的分布及作用
Appl Microbiol. 1975 Dec;30(6):959-63. doi: 10.1128/am.30.6.959-963.1975.

引用本文的文献

1
Products Formed from Analogues of 1,1,1-Trichloro-2,2-Bis(p-Chlorophenyl) Ethane (DDT) Metabolites by Pseudomonas putida.由假单胞菌产生的 1,1,1-三氯-2,2-双(对氯苯基)乙烷(DDT)代谢物类似物形成的产物。
Appl Environ Microbiol. 1977 Jan;33(1):101-8. doi: 10.1128/aem.33.1.101-108.1977.
2
Synergism in the inhibition of Bacillus subtilis by combinations of lipophilic weak acids and fatty alcohols.亲脂性弱酸与脂肪醇组合对枯草芽孢杆菌抑制作用中的协同效应。
Antimicrob Agents Chemother. 1981 Jun;19(6):1082-5. doi: 10.1128/AAC.19.6.1082.
3
Accumulation, metabolism, and effects of organochlorine insecticides on microorganisms.有机氯杀虫剂在微生物上的积累、代谢及影响
Microbiol Rev. 1982 Mar;46(1):95-127. doi: 10.1128/mr.46.1.95-127.1982.
4
Bacterial and fungal cometabolism of 1,1,1-trichloro-2,2-bis(4-chlorophenyl)ethane (DDT) and its breakdown products.1,1,1-三氯-2,2-双(4-氯苯基)乙烷(滴滴涕)及其分解产物的细菌和真菌共代谢作用
Appl Environ Microbiol. 1985 Mar;49(3):509-16. doi: 10.1128/aem.49.3.509-516.1985.
5
Distribution and effects of 2,4,5-trichlorophenoxyacetic acid in cells of Bacillus megaterium.2,4,5-三氯苯氧乙酸在巨大芽孢杆菌细胞中的分布及作用
Appl Microbiol. 1975 Dec;30(6):959-63. doi: 10.1128/am.30.6.959-963.1975.

本文引用的文献

1
Protein measurement with the Folin phenol reagent.使用福林酚试剂进行蛋白质测定。
J Biol Chem. 1951 Nov;193(1):265-75.
2
Enzyme localization in Bacillus megaterium.巨大芽孢杆菌中的酶定位
J Bacteriol. 1957 Jun;73(6):784-90. doi: 10.1128/jb.73.6.784-790.1957.
3
Accumulation of DDT and dieldrin by microorganisms.微生物对滴滴涕和狄氏剂的积累。
Can J Microbiol. 1967 Aug;13(8):1123-6. doi: 10.1139/m67-153.
4
Effects of diphenylamine on carotenoids and menaquinones in bacterial membranes.
Biochim Biophys Acta. 1967 May 2;135(2):196-207. doi: 10.1016/0005-2736(67)90114-9.
5
Hemolytic actions of short-chain alkylamine hydrochlorides.
J Pharm Sci. 1969 Feb;58(2):255-6. doi: 10.1002/jps.2600580229.
6
Yields of bacterial cells from hydrocarbons.由碳氢化合物产生的细菌细胞产量。
Appl Microbiol. 1968 Dec;16(12):1886-91. doi: 10.1128/am.16.12.1886-1891.1968.
7
Accumulation and concentration of chlorinated hydrocarbon pesticides by microorganisms in soil.土壤中微生物对氯代烃类农药的累积与富集
Can J Microbiol. 1968 Oct;14(10):1075-8. doi: 10.1139/m68-181.
8
Conversion of DDT to DDD in soil and the effect of these compounds on soil microorganisms.
Can J Microbiol. 1968 Oct;14(10):1069-73. doi: 10.1139/m68-180.
9
Influence of sucrose on protein determination by the Lowry procedure.蔗糖对采用洛瑞法测定蛋白质的影响。
Anal Biochem. 1968 Aug;24(2):337-9. doi: 10.1016/0003-2697(68)90187-5.
10
Interactions between DDT and river fungi. I. Effects of p,p'-DDT on the growth of aquatic hyphomycetes.滴滴涕与河流真菌之间的相互作用。I. 对,对'-滴滴涕对水生真菌生长的影响。
Appl Microbiol. 1970 Nov;20(5):662-6. doi: 10.1128/am.20.5.662-666.1970.

巨大芽孢杆菌对1,1,1-三氯-2,2-双(对氯苯基)乙烷的摄取位置及后果

Location and consequences of 1,1,1-trichloro-2,2-bis(p-chlorophenyl) ethane uptake by Bacillus megaterium.

作者信息

Hicks G F, Corner T R

出版信息

Appl Microbiol. 1973 Mar;25(3):381-7. doi: 10.1128/am.25.3.381-387.1973.

DOI:10.1128/am.25.3.381-387.1973
PMID:4633425
原文链接:https://pmc.ncbi.nlm.nih.gov/articles/PMC380815/
Abstract

No detrimental effects of 1,1,1-trichloro-2,2-bis(p-chlorophenyl)ethane (DDT) were observed when cells of Bacillus megaterium were grown from small inocula in nutrient media containing up to 100 mug of DDT/ml. However, when the ratio of DDT to biomass of resting cells was held constant, levels of DDT as low as 1 mug/ml (0.5 mug/mg of cell dry weight) enhanced the rate of death in the population. The lethal action of DDT was both time- and dose-dependent so that higher doses required less time to effect the same killing than did lower doses. Intact cells bound a maximum of about 1.7 mug of DDT/mg of cell dry weight, of which about 75% was localized in the protoplast membrane. Much of the bound DDT was subsequently lost to the suspending medium and the aqueous stability of the returned DDT was enhanced, possibly by association with solubilized cell materials. A small quantity of bound DDT was converted to 1,1-dichloro-2,2-bis(p-chlorophenyl)ethane, which was released from cells somewhat faster than DDT. Apparently the lethal action of DDT was related to its binding in the membrane, but respiration was not inhibited. The atypical macroscopic appearance of membranes isolated from treated cells suggested that cell death may result from altered membrane chemistry.

摘要

当巨大芽孢杆菌细胞在含有高达100微克滴滴涕/毫升的营养培养基中从小接种量开始生长时,未观察到1,1,1-三氯-2,2-双(对氯苯基)乙烷(滴滴涕)的有害影响。然而,当滴滴涕与静止细胞生物量的比例保持恒定时,低至1微克/毫升(0.5微克/毫克细胞干重)的滴滴涕水平会提高群体中的死亡率。滴滴涕的致死作用具有时间和剂量依赖性,因此较高剂量比较低剂量所需的时间更短就能达到相同的杀伤效果。完整细胞结合的滴滴涕最多约为1.7微克/毫克细胞干重,其中约75%定位于原生质体膜中。许多结合的滴滴涕随后会释放到悬浮培养基中,并且返回的滴滴涕的水稳定性增强,这可能是由于与溶解的细胞物质结合所致。少量结合的滴滴涕会转化为1,1-二氯-2,2-双(对氯苯基)乙烷,其从细胞中释放的速度比滴滴涕略快。显然,滴滴涕的致死作用与其在膜中的结合有关,但呼吸作用并未受到抑制。从处理过的细胞中分离出的膜的非典型宏观外观表明,细胞死亡可能是由于膜化学性质的改变所致。