Degradation of p-benzyloxyphenol by Acinetobacter sp.

Abstract Acinetobacter sp. utilized p -benzyloxyphenol as sole carbon source and degraded it to p -hydroxybenzaldehyde, p -hydroxybenzoic acid, protocatechuic acid and catechol. The intermediates were identified by paper chromatography, TLC, IR, GC and HPLC. Acinetobacter sp. produced protocatechuate 3,4-dioxygenase and catechol 1,2-dioxygenase during the degradation of p -benzoloxyphenol.     

Oxidation of zearalenone by extracellular enzymes from Acinetobacter sp. SM04 into smaller estrogenic products

Zearalenone is a mycotoxin mainly produced by Fusarium mold, which has been associated with hyperestrogenism and other reproductive disorders in pigs, sheep, and other farm animals. Since zearalenone engendered economic losses to farm animal production, its detoxification in contaminated grains or by-products would be advantageous. In this study, enzymes from the Acinetobacter sp. SM04 extracellular extracts of liquid cultures were isolated by Sephadex G-100 column, and an active fraction capable of efficiently degrading zearalenone was obtained. Zearalenone could be oxidized into smaller estrogenic products by the active fraction, and two intermediate products, ZEN-1([M-H]⁻ at m/z 489) and ZEN-2([M-H]⁻ at m/z 405), were found. Zearalenone degradation activity of the active fraction was significantly inhibited by low oxygen gas content, protease, SDS, and EDTA treatment. Further, enzymes in the active fraction were analysed by SDS–PAGE and MALDI-TOF/TOF/MS, and three proteins were found that matched the database for Acinetobacter genus with great homology. They were identified as peroxiredoxin, a possible cytochrome and a putative fimbrial protein precursor.     

Degradation of lignin and lignin derivatives by Acinetobacter sp.

An Acinetobacter sp. utilized 2-methoxy-4-formylphenoxyacetic acid, dehydrodivanillyl alcohol, dehydrodiisoeugenol and conidendrin as sole carbon source. It also degraded ¹⁴C-labelled DHP lignin and teakwood lignin. Vanillic acid, protocatechuic acid and catechol were separated from 2-methoxy-4-formylphenoxyacetic acid grown cultures. Both protocatechuic acid and catechol were formed from dehydrodivanillyl alcohol, dehydrodiisoeugenol and conidendrin. On the dimeric lignin model substances this Acinetobacter sp. produced protocatechuate 3,4-dioxygenase and catechol 1,2-dioxygenase.     

Utilization of complex phenolic compounds by Acinetobacter sp.

Summary Acinetobacter sp. utilized the [ring-¹⁴C]dehydropolymer of coniferyl alcohol (DHP) (sp. act. 1.4 × 10⁴ dpm/mg), ¹⁴C-labelled teakwood lignin (sp. act. 2.5 × 10⁴ dpm/mg), guaiacolglyceryl ether, 2-methoxy-4-formylphenoxyacetic acid, p-benzyloxyphenol, dehydrodivanillyl alcohol, dehydrodiisoeugenol, veratrylglycerol--guaiacyl ether, conidendrin, black liquor lignin and indulin as sole carbon sources. The bacterium produced p-coumaric acid, p-hydroxybenzoic acid, vanillic acid, protocatechuic acid and catechol as intermediates from lignins. Acinetobacter sp. produced catechol 1,2-dioxygenase and protocatechuate 3,4-dioxygenase during the degradation of lignins. Correspondence to: A. Mahadevan     

The distribution of chlorophylls, carotenoids and their breakdown products in Lake Kinneret (Israel) sediments

SUMMARY. 1. The sedimentary distribution of chlorophylls, carotenoids and their breakdown products following the winter-spring bloom of the dinoflagellate Peridinium gatunense in Lake Kinneret was determined both spatially and vertically within the sediments, using high-pressure liquid chromatography (HPLC).
2. All four stations (epilimnic, oxic St. J (depth = 8m) and D (12m) and hypolimnic, anoxic St. F (21 m) A (41 m) were characterized by the presence of chlorophyll a (chl-a) chl- b , chl- c , phaeophytins a (ph'tin- a ) and b , phaeophorbide a (ph'bide- a ) and lutein, fucoxanthin, diatoxanthin and β-carotene together with spectrally similar, but HPLC-resolved, breakdown products in the surface sediments. The central deep station A (41 m), which is seasonally anoxic, trapped and preserved significantly more pigments (e.g. chl- a = 16.35 μg g⁻¹ organic matter) than the more erosive, oxic littoral stations (chl- a = 1.10 and 0.76μg g^−l OM at St. D and J, respectively).
3. Whereas it was possible to ascribe the presence of lutein and chl- b to inputs of green algae and higher plants from the catchment, and fucoxanthin and chl- c ₁, c ₂ to winter diatom blooms (e.g. Melosira granulata ), there was a remarkable absence of peridinin and dinoxanthin from sediments, despite the dominance of dinoflagellates in the phytobiomass. This is consistent with the well-known oxic lability of this epoxy carotenoid in aquatic systems, and indicates efficient breakdown of this dinoflagellate organic matter in the water column, prior to sedimentation.
4. Although pigment concentrations all decreased with depths within sediments, lutein and β-carotene were selectively preserved compared to chl-a and fucoxanthin which, at 40m depth at St. A, decreased to < 1% of their surface concentrations.     

Motility and chemotaxis of Pseudomonas sp. B4 towards polychlorobiphenyls and chlorobenzoates

The polychlorinated biphenyl (PCB)-degrading Pseudomonas sp. B4 was tested for its motility and ability to sense and respond to biphenyl, its chloroderivatives and chlorobenzoates in chemotaxis assays. Pseudomonas sp. B4 was attracted to biphenyl, PCBs and benzoate in swarm plate and capillary assays. Chemotaxis towards these compounds correlated with their use as carbon and energy sources. No chemotactic effect was observed in the presence of 2- and 3-chlorobenzoates. Furthermore, a toxic effect was observed when the microorganism was exposed to 3-chlorobenzoate. A nonmotile Pseudomonas sp. B4 transformant and Burkholderia xenovorans LB400, the laboratory model strain for PCB degradation, were both capable of growing in biphenyl as the sole carbon source, but showed a clear disadvantage to access the pollutants to be degraded, compared with the highly motile Pseudomonas sp. B4, stressing the importance of motility and chemotaxis in this environmental biodegradation.     

不动杆菌（Acinetobacters sp）51—2降解乙腈的研究

A strain of Acinetobacter sp. 51-2 was capable of degrading acetonitrile and utilizing various nitrile compounds, such as propionitrile, butyronitrile, acrylonitrile and so on. The ability and speed of degrading acetonitrile were quite strong and fast. Strain 51-2 could degrade 25 g/L acetonitrile in 48 h by adapted cells. The efficiency of degrading acetonitrile was closely related to the conditions of culturing bacterial cells. The reaction temperature and present metals appeared to have a little effect on degradation of acetonitrile.     

一株根瘤菌培养条件优化及代谢调控研究

研究了柠条根瘤菌的生理学特性 ,通过摇瓶试验确定了最佳培养基配方和最适培养条件 ,应用 10L -自动控制发酵罐在优化条件下进行了分批发酵试验 ,并以月桂酸盐为调节剂进行底物水平的代谢调控。试验结果表明 ,该菌株生长速率快 (0 .6 6 0 8g·L- 1 ·h- 1 )、发酵周期短 (2 7h)、产物PHB产量高 (6 .6 1g L) ,通过代谢调控可获得 3-羟基丁酸和 3-羟基辛酸异型共聚体 [P(HB -HO) ],是一株生产性状优良的生产菌株 ,有着良好的开发应用前景     

Anaerobic dechlorination of polychlorobiphenyls (Aroclor 1242) by pasteurized and ethanol-treated microorganisms from sediments.

A polychlorobiphenyl (PCB)-dechlorinating inoculum eluted from upper Hudson River sediments was treated with either heat or ethanol or both. The treated cultures retained the ability to dechlorinate PCBs (Aroclor 1242) under strictly anaerobic conditions. The dechlorination activity was maintained in serial cultures inoculated with transfers of 1% inoculum when the transferred inoculum was treated each time in the same manner. No methane production was detected in any treated culture, although dechlorination of PCBs in the untreated cultures was always accompanied by methane production. All treated cultures preferentially removed meta chlorines, yielding a dechlorination pattern characterized by accumulation of certain ortho- and para-subsituted congeners such as 2-4-chlorobiphenyl (2-4-CB), 2,4-2-CB, and 2,4-4-CB. In contrast, the untreated cultures showed more extensive dechlorination activities, which almost completely removed both meta and para chlorines from Aroclor 1242. These results suggest that microorganisms responsible for the dechlorination of PCBs in the upper Hudson River sediments can be grouped into two populations according to their responses to the heat and ethanol treatments. Microorganisms surviving the heat and ethanol treatments preferentially remove meta chlorines, while microorganisms lost from the enrichment mainly contribute to the para dechlorination activity. These results indicate that anaerobic sporeformers are at least one of the physiological groups responsible for the reductive dechlorination of PCBs. The selection of a dechlorinating population by such treatments may be an important step in isolation of PCB-dechlorinating microorganisms.     

Anaerobic dechlorination of polychlorobiphenyls (Aroclor 1242) by pasteurized and ethanol-treated microorganisms from sediments.

A polychlorobiphenyl (PCB)-dechlorinating inoculum eluted from upper Hudson River sediments was treated with either heat or ethanol or both. The treated cultures retained the ability to dechlorinate PCBs (Aroclor 1242) under strictly anaerobic conditions. The dechlorination activity was maintained in serial cultures inoculated with transfers of 1% inoculum when the transferred inoculum was treated each time in the same manner. No methane production was detected in any treated culture, although dechlorination of PCBs in the untreated cultures was always accompanied by methane production. All treated cultures preferentially removed meta chlorines, yielding a dechlorination pattern characterized by accumulation of certain ortho- and para-subsituted congeners such as 2-4-chlorobiphenyl (2-4-CB), 2,4-2-CB, and 2,4-4-CB. In contrast, the untreated cultures showed more extensive dechlorination activities, which almost completely removed both meta and para chlorines from Aroclor 1242. These results suggest that microorganisms responsible for the dechlorination of PCBs in the upper Hudson River sediments can be grouped into two populations according to their responses to the heat and ethanol treatments. Microorganisms surviving the heat and ethanol treatments preferentially remove meta chlorines, while microorganisms lost from the enrichment mainly contribute to the para dechlorination activity. These results indicate that anaerobic sporeformers are at least one of the physiological groups responsible for the reductive dechlorination of PCBs. The selection of a dechlorinating population by such treatments may be an important step in isolation of PCB-dechlorinating microorganisms.     

Studies on the Metabolic Products of Oospora sp. (Oospora astringenes)

The chemical structure of another metabolic product (0-2) which was isolated from the culture filtrate of Oospora astringenes was studied. This compound irritates the skins and has the constrictive actions on the tracheal muscle of the guinea pigs. It has ketone and hydroxyl groups, and thereby has been named oosponol. From the results of the degradation experiments, oosponol is supposed to have the following structure (II).     

Studies on the Metabolic Products of Oospora sp. (Oospora astringenes)

The chemical structure of oospolactone which is the metabolic product of Oospora astringenes was confirmed by the synthetical approach.     

Characterization of the aac(6'')-Ik gene of Acinetobacter sp. 6

Abstract Chromosomal DNA of different species of mycobacteria, Mycobacterium tuberculosis, Mycobacterium leprae, Mycobacterium avium and Mycobacterium smegmatis , has been submitted to polymerase chain reaction using two oligonucleotide primers highly homologous to DNA sequences flanking the quinolone resistance-determining region in the gyrA gene of Escherichia coli and Staphylococcus aureus . For each of these mycobacterial species, a 150-bp DNA fragment hybridizing with an intragenic probe of the gyrA gene of E. coli K12 was obtained. The nucleotide sequences of the 108-bp fragments amplified from M. tuberculosis and M. avium were determined. The two sequences were 87% homologous. Except for one residue, their deduced amino acid sequences were identical and shared 67% homology with the quinolone resistance-determining region of the gyrase A subunits of E. coli and S. aureus . Sequencing of the 108-bp fragment amplified from an in vitro mutant of M. avium , highly resistant to fluoroquinolones, showed a point mutation leading to the substitution of Ala for Val at a position corresponding to residues involved in quinolone resistance in E. coli and S. aureus , i.e. Ser 83 for E. coli and Ser 84 for S. aureus .     

Microbial degradation of lipid by Acinetobacter sp. strain SOD-1

Acinetobacter sp. strain SOD-1, capable of rapidly degrading salad oil, was isolated from soil. Strain SOD-1 showed good growth and degraded 68.7+/-2.7 and 83.0% of an initial 3000 ppm salad oil suspension in 24 h at 20 degrees C and pH 7.0 and at 35 degrees C and pH 8.0, respectively. The degradation rate depended on pH, temperature, phosphate concentration, and initial cell density.     

Metabolic labeling of Dirofilaria immitis third- and fourth-stage larvae and their excretory-secretory products.

Infective third-stage larvae of Dirofilaria immitis were collected from Aedes aegypti and cultured in vitro to the fourth stage. Larval proteins were labeled metabolically using [35S]cysteine and methionine in different media and for different lengths of time. Labeled proteins in the excretory-secretory component and the larval homogenates were evaluated by sodium dodecyl sulfate-polyacrylamide gel electrophoresis under reducing and nonreducing conditions and by 2-dimensional gel electrophoresis. Numerous proteins ranging from 14 to greater than 200 kDa were identified from both the excretory-secretory components and the larval homogenates. Both fractions demonstrated shared and unique proteins. Using timed labeling, age- and stage-specific proteins were identified; at least 2 proteins of approximately 20.5 and 22 kDa were associated in time with the molt from the third to fourth stage. Two proteins of the same molecular weight were specifically recognized by immune dog sera, but not by sera of their infected nonimmune cohorts.     

Simultaneous Removal of Mn(II) and Nitrate by the Manganese-Oxidizing Bacterium Acinetobacter sp. SZ28 in Anaerobic Conditions

A novel bacterium, strain SZ28, identified as Acinetobacter sp., showed anaerobic denitrification ability using Mn(II) as the electron donor. Nitrate-nitrogen concentration decreased from nearly 16.52–mg L^?1 to 4.4–mg L^?1, without accumulation of nitrite as an intermediate, with a maximum of 0.063–mg NO₃^?-N L^?1 h^?1, reaching a peak of 0.085–mg NO₃^?-N L^?1 h^?1 in sodium acetate. The nitrate removal rate reached 0.067–mg NO₃^?-N L^?1 h^?1, 0.059–mg NO₃^?-N L^?1 h^?1, and 0.078 mg NO₃^?-N L^?1 h^?1 using Mn(II), S(II), and Fe(II) as electron donors, respectively. The optimum pH was 6.0, with a removal rate of 0.063–mg NO₃^?-N L^?1 h^?1     

Delineation of a novel environmental phylogroup of the genus Acinetobacter encompassing Acinetobacter terrae sp. nov., Acinetobacter terrestris sp. nov. and three other tentative species

This study aimed to define the taxonomic position and structure of a novel, taxonomically unique group of 26 Acinetobacter strains, provisionally designated Taxon 24 (T24). The strains were recovered from soil and freshwater ecosystems (n = 21) or animals (n = 5) in Czechia, Scotland, Germany, the Netherlands and Turkey between 1993 and 2015. They were non-glucose-acidifying, nonhemolytic, nonproteolytic, growing at 32 °C and on acetate and ethanol as single carbon sources, but not on 4-hydroxybenzoate and mostly not at 37 °C. Their whole-genome sequences were 3.0–3.7 Mb in size, with GC contents of 39.8–41.3%. Based on core genome phylogenetic analysis, the 26 strains formed a distinct clade within the genus Acinetobacter, with strongly supported subclades termed T24A (n = 11), T24B (n = 8), T24C (n = 2), T24D (n = 3) and T24E (n = 2). The internal genomic ANIb values for these subclades were >94.8%, while the ANIb values between them were <92.5%. The results of MALDI-TOF MS-based analyses agreed with this classification. The five subclades differed from each other in the results of one to six carbon source assimilation tests. Given the genomic and phenotypic distinctness, internal coherence, numbers of available strains and geographically diverse origin of T24A and T24B, we propose the names Acinetobacter terrae sp. nov. and Acinetobacter terrestris sp. nov. for these two taxa, respectively. The type strains are ANC 4282^v (= CCM 8986^T = CCUG 73811^T = CNCTC 8082^T) and ANC 4471^T (= CCM 8985^T = CCUG 73812^T = CNCTC 8093^T), respectively. We conclude that these two species together with the other T24 strains represent a widely dispersed Acinetobacter clade primarily associated with terrestrial ecosystems.     

Degradation of chlorinated biphenyls and products of their bioconversion by Rhodococcus sp. B7a strain

Strain Rhodococcus sp. B7a isolated from artificially polluted soil destructs mono- and di-substituted ortho- and/or para-chlorinated biphenyls with utilization of chlorinated benzoic acids and shows high degradation activity as regards trichlorinated biphenyls. It is shown that p-hydroxybenzoic and protocatehoic acids are the products of p-chlorobenzoic acid catabolism.     

Cometabolism of 3,4-dichlorobenzoate by Acinetobacter sp. strain 4-CB1.

When Acinetobacter sp. strain 4-CB1 was grown on 4-chlorobenzoate (4-CB), it cometabolized 3,4-dichlorobenzoate (3,4-DCB) to 3-chloro-4-hydroxybenzoate (3-C-4-OHB), which could be used as a growth substrate. No cometabolism of 3,4-DCB was observed when Acinetobacter sp. strain 4-CB1 was grown on benzoate. 4-Carboxyl-1,2-benzoquinone was formed as an intermediate from 3,4-DCB and 3-C-4-OHB in aerobic and anaerobic resting-cell incubations and was the major transient intermediate found when cells were grown on 3-C-4-OHB. The first dechlorination step of 3,4-DCB was catalyzed by the 4-CB dehalogenase, while a soluble dehalogenase was responsible for dechlorination of 3-C-4-OHB. Both enzymes were inducible by the respective chlorinated substrates, as indicated by oxygen uptake experiments. The dehalogenase activity on 3-C-4-OHB, observed in crude cell extracts, was 109 and 44 nmol of 3-C-4-OHB min-1 mg of protein-1 under anaerobic and aerobic conditions, respectively. 3-Chloro-4-hydroxybenzoate served as a pseudosubstrate for the 4-hydroxybenzoate monooxygenase by effecting oxygen and NADH consumption without being hydroxylated. Contrary to 4-CB metabolism, the results suggest that 3-C-4-OHB was not metabolized via the protocatechuate pathway. Despite the ability of resting cells grown on 4-CB or 3-C-4-OHB to carry out all of the necessary steps for dehalogenation and catabolism of 3,4-DCB, it appeared that 3,4-DCB was unable to induce the necessary 4-CB dehalogenase for the initial p-dehalogenation step.(ABSTRACT TRUNCATED AT 250 WORDS)