Enrichment and characterization of a bacterial culture that can degrade 4-aminopyridine
© Takenaka et al.; licensee BioMed Central Ltd. 2013
Received: 4 January 2013
Accepted: 11 March 2013
Published: 21 March 2013
The agrichemical 4-aminopyridine is used as a bird repellent in crop fields and has an epileptogenic action in a variety of animals, including man and mouse. 4-Aminopyridine is biodegraded in the environment through an unknown mechanism.
A 4-aminopyridine-degrading enrichment culture utilized 4-aminopyridine as a carbon, nitrogen, and energy source, generating 4-amino-3-hydroxypyridine, 3,4-dihydroxypyridine, and formate as intermediates. 4-Amino-3-hydroxypyridine could not be further metabolized and probably accumulated as a dead-end product in the culture. Biodegradability tests and partial sequence analysis of the enrichment culture indicated that 4-aminopyridine was mainly degraded via 3,4-dihydroxypyridine and that the metabolite is probably cleaved by 3-hydroxy-4-pyridone dioxygenase. Seven culturable predominant bacterial strains (strains 4AP-A to 4AP-G) were isolated on nutrient agar plates. Changes in the bacterial populations of 4-aminopyridine, 3,4-dihydroxypyridine, or formate/ammonium chloride enrichment cultures were monitored by denaturing gradient gel electrophoresis (DGGE) profiling of PCR-amplified 16S rRNA gene fragments. Sequence analysis of the 16S rRNA gene fragments derived from predominant DGGE bands indicated that Pseudomonas nitroreducens 4AP-A and Enterobacter sp. 4AP-G were predominant in the three tested enrichment cultures and that the unculturable strains Hyphomicrobium sp. 4AP-Y and Elizabethkingia sp. 4AP-Z were predominant in 4-aminopyridine and formate/ammonium chloride enrichment cultures and in the 3,4-dihydroxypyridine enrichment culture, respectively. Among the culturable strains, strain 4AP-A could utilize 3,4-dihydroxypyridine as a growth substrate. Although we could not isolate strain 4AP-Y on several media, PCR-DGGE analysis and microscopy indicated that the unique bi-polar filamentous bacterial cells gradually became more dominant with increasing 4-aminopyridine concentration in the medium.
Hyphomicrobium sp. 4AP-Y, P. nitroreducens 4AP-A, and Elizabethkingia sp. 4AP-Z probably play important roles in 4-aminopyridine degradation in crop fields. In the enrichment culture, 3,4-dihydroxypyridine and its metabolites including formate might be shared as growth substrates and maintain the enrichment culture, including these indispensable strains.
Pyridine and its derivatives are mainly produced on an industrial scale from coal tar. These compounds are major industrial raw materials and intermediates used for organic solvents and the production of agrichemicals, medicines, and active surfactants . Pyridines are soluble in polar and nonpolar solvents, and most are toxic .
Pyridine and its derivatives are also environmental pollutants, and their biodegradation has been studied in detail . The biodegradability of pyridine derivatives follows the order pyridinecarboxylic acids > pyridine = monohydroxypyridines > methylpyridines > aminopyridines = chloropyridines . Generally, pyridines are degraded via pyridine-ring reduction and fission steps  or via pyridine-ring hydroxylation and fission steps [6–8]. Nocardia sp. strain Z1 directly cleaves the pyridine ring between N and position C-2 and further metabolizes the product via glutaric dialdehyde, and Bacillus sp. strain 4 cleaves the ring between positions C-2 and C-3 and the product it further via succinate semialdehyde . Gordonia nitida strain LE31 metabolizes 3-methyl- or 3-ethyl-pyridine without a hydroxylation step . Rhodococcus opacus (VKM Ac-1333D) and Arthrobacter crystallopoietes (VKM Ac-1334D) hydroxylate the pyridine ring . In Agrobacterium sp. strain NCIB 10413, 4-hydroxypyridine is metabolized by a hydroxylase and an N-heterocyclic ring-cleavage dioxygenase [6, 7]. Thus, the biodegradation of pyridines by single bacterial species has been studied, but little is known about the biodegradation of pyridines by microbial communities , which could include unculturable bacteria.
Organisms and growth conditions
Enrichments of 4-aminopyridine-degrading bacteria were set up with 0.2 g normal farm soils such as rice field soil and corn field soils from the Hyogo Prefecture, Japan in 7 ml basal medium containing 2.13 mM (0.02% wt/vol) 4-aminopyridine as described previously . Briefly, solutions A (sodium-potassium phosphate solution), B (metal-salt solution containing 1 ml of a soil extract), and C (4-aminopyridine solution) were prepared separately. The soil extract used in solution B was prepared by adding 15 g of a normal rice field soil to 200 ml of deionized water and mixing for 30 min, followed by filtration through Whatman No. 2 filter paper (Maidstone, UK) and autoclaving.
Ten 4-aminopyridine-degrading enrichment cultures, KM20-14A to KM20-14J, were incubated at 30°C with shaking at 140 rpm. Every 4 days, 500 μl of the enrichment culture was used to inoculate 7 ml fresh medium, to maintain 4-aminopyridine degradation ability. We selected one enrichment culture derived from a normal rice field soil, No. KM 20-14E for further study and examined its utilization of the identified metabolites (4-amino-3-hydroxypyridine and 3,4-hydroxypyridine) by the enrichment culture (No. KM20-14E) was examined. The tested substrate was added to the basal medium instead of 4-aminopyridine.
Isolation and identification of culturable and unculturable strains from the 4-aminopyridine-degrading enrichment culture
Samples taken from the 4-aminopyridine-degrading enrichment culture were serially diluted 106- to 108-fold with 0.8% (wt/vol) NaCl solution and spread onto nutrient agar plates (1.0 g polypeptone, 1.0 g meat extract, 0.5 g NaCl, and 1.5 g agar per 100 ml), 0.1% (wt/vol) 4-aminopyridine agar plates, and 0.1% (wt/vol) 3,4-dihydroxypyridine agar plates. The plates were incubated at 30°C for 4 to 7 days, and colonies were picked up for 16S rRNA gene analysis. We designated seven dominant bacterial strains isolated from the nutrient agar plate as dominant bacterial strains 4AP-A to 4AP-G. The 16S rRNA gene V3 regions derived from these strains were used as a PCR-DGGE analysis makers as described below.
Oligonucleotide primers used in this study
Sequence (5' to 3')
Isolation, and identification of metabolites from 4-aminopyridine
The enrichment culture was cultivated in basal medium containing 2.13 mM 4-aminopyridine at 30°C with shaking, and the culture was diluted 106 to 108-fold with 0.8% (wt/vol) NaCl solution. The diluted culture (500 μl) was used to inoculate fresh basal medium containing 4-aminopyridine, and the subculture was incubated at 30°C. The culture was centrifuged at 20,000 × g for 10 min, and the supernatant was dried using a rotary evaporator. The dried residues were dissolved in n-butanol and then dried again. The accumulated products in the dried residue were incubated with N,O-bis(trimethylsilyl)trifluoroacetamide at 100°C for 1.5 h. The trimethylsilylated products were analyzed by GC-MS as described below.
Measurement and identification of 4-aminopyridine and its metabolites
Concentrations of pyridines, including 4-aminopyridine and 4-amino-3-hydroxypyridine (Figure 1, compound IV), were measured using a Hitachi L-6200 HPLC system (Tokyo, Japan) equipped with a Cosmosil 5C18 PAQ column (4.6 × 150 mm; Nacalai Tesque, Kyoto). The eluent was 20 mM potassium phosphate buffer (pH 2.5) containing 5 mM pentanesulfonate; the flow rate was 1.0 ml/min. 4-Aminopyridine and 4-amino-3-hydroxypyridine were detected at 254 nm and had retention times of 5.4 and 7.6 min, respectively. The metabolites from 4-aminopyridine (4-amino-3-hydroxypyridine and 3,4-dihydroxypyridine; Figure 1) were identified and quantified using a GCMS-QP2010 Ultra (Shimadzu, Kyoto, Japan). A fused silica capillary column (InertCap 1MS; 0.25 mm × 30 m; GL Science) was used. Helium gas was the carrier at a linear velocity of 35 cm/s. The column temperature was programed from 50°C (held for 1 min) to 280°C at a rate of 5°C/min and then held at 280°C for 20 min. The peaks derived from the trimethylsilylated derivatives of 4-aminopyridine, 4-amino-3-hydroxypyridine, and 3,4-dihydroxypyridine appeared at 18.2, 24.5, and 20.9 min, respectively. The organic acids in the culture supernatant were derivatized by pentafluorobenzyl bromide according to a previously reported method  and analyzed by GC-MS as described above. The peaks derived from the pentafluorobenzyl formate appeared at 8.5 min.
DNA extraction and PCR
Cloning of PCR product and sequencing
Prominent DNA bands from the DGGE gels were extracted and used as PCR templates with the forward primer PRBA338f without a GC clamp and the reverse primer PRUN518r. The nucleotide sequences obtained were compared with those of the 16S rRNA genes of the strains isolated. To analyze the full-length 16S rRNA gene sequences, specific primers were designed based on the partial sequences of the isolate that became more dominant in the culture during continuous growth in basal medium containing 4-aminopyridine (Table 1).
PCR amplification of part of the 3-hydroxy-4-pyridone dioxygenase gene
The enrichment culture grown in 4-aminopyrdine-containing medium was harvested in the mid-exponential growth phase by centrifugation. Mixed genomic DNA in the cell pellets was extracted using Qiagen DNeasy Blood & Tissue Kit (Hilden, Germany) according to the manufacturer’s instructions and was used as a template for PCR. To amplify part of the 3-hydroxy-4-pyridone dioxygenase (3,4-dihydroxypyridine 2,3-dioxygenase) gene, pydA, the primers PydAf and PydAr were designed based on the conserved region of previously reported dioxygenases from Rhizobium sp. TAL1145 (DDBJ/EMBL/GenBank accession no. AY729020), Hyphomicrobium sp. MC1 (YP_004673996), Bordetella bronchiseptica RB50 (NP_890665), and Bordetella parapertussis 12822 (NP_885852) (Table 1). The following PCR protocol was used: initial denaturation at 95°C for 2 min; 35 cycles of denaturation at 95°C for 60 s, annealing at 45°C for 30 s, extension at 72°C for 30 s; and final extension at 72°C for 5 min. Harvesting of cells, preparation of mixed genomic DNA, and amplification were carried out in triplicate.
The optical density (OD660) of the cultures was measured using a Hitachi U-2800 spectrophotometer. The 1H-NMR spectra of the isolated metabolites and the prepared standard compounds were measured with a Joel JNM-AL300 spectrometer (300 MHz, Joel Ltd., Tokyo, Japan). Released ammonia in the culture fluid was measured using the indophenol blue method . Total protein in the culture was measured using the modified Lowry method, to confirm the utilization of 4-aminopyridine as a carbon, nitrogen, and energy source by the enrichment culture .
Nucleotide sequence accession numbers
The nucleotide sequences of the 16S rRNA genes obtained in this study were deposited in the DDBJ/EMBL/GenBank databases under accession numbers AB695349 through AB695357.
4-Aminopyridine and methyl chloroformate were purchased from Tokyo Chemical Industry (Tokyo, Japan). 4-Amino-3-hydroxypyridine hydrochloride was from SynChem OHG (Felsberg, Germany). L-Mimosine from Koa Hoale seeds and pentafluorobenzyl bromide were from Sigma Aldrich (St. Louis, MO, USA). 3,4-Dihydroxypyridine was prepared from L-mimosine according to a previously reported method . The 1H-NMR spectrum of the prepared 3,4-dihydroxypyridine was measured at NMR δH (DMSO-d6): dH = 7.35 ppm (d, J = 6.0 Hz, 1H; H-6); 7.47 ppm (S, 1H; H-2); 6.21 ppm (d, J = 6.0 Hz; H-5). N,O-bis(trimethylsilyl)trifluoroacetamide and pyridine derivatives were purchased from Wako Pure Chemicals (Osaka, Japan).
Degradation of 4-aminopyridine by the enrichment culture
Identification and degradation of metabolites from 4-aminopyridine
Two metabolites in the enrichment culture in medium containing 4-aminopyridine were detected using GC and GC-MS. The trimethylsilylated metabolites, compounds I and II, had GC retention times of 20.9 and 24.4 min, respectively. Compound I was detected in the culture on the first day and accumulated during the cultivation. Compound II accumulated temporarily and was gradually degraded during cultivation. The mass spectrum of trimethylsilylated compound I showed a molecular ion at m/z 254 (M+, relative intensity 81.3%). Major fragment ions appeared at m/z 239 (M+-CH3, 90%) and 73 ([Si(CH3)3]+, 100%). The mass spectrum of trimethylsilylated compound II showed a molecular ion at m/z 255 (M+, relative intensity 25.7%). Major fragment ions appeared at m/z 240 (M+-CH3, 59.9%), 182 (M+-Si(CH3)3, 1.1%), 147 ([(CH3)2Si = O–Si(CH3)3]+, 2.1%), and 73 ([Si(CH3)3]+, 100%). The GC retention times and MS spectra of trimethylsilylated compounds I and II agreed with those of trimethylsilylated authentic 4-amino-3-hydroxypyridine and 3,4-dihydroxypyridine, respectively.
Pyridines are metabolized into an organic acid, such as acetate, formate, or dicarboxylic acids . The culture supernatant of the enrichment culture was mixed with pentafluorobenzyl bromide and then analyzed. The mass spectrum of the pentafluorobenzyl derivative showed a molecular ion at m/z 226 (M+). The GC retention time and MS spectrum of the derivatized compound agreed with those of formate derivatized by pentafluorobenzyl bromide. In the enrichment cultures grown on 2.12, 6.38, and 10.6 mM 4-aminopyridine for 10 days, 0.05 ± 0.012 mM formate accumulated in 10.6 mM 4-aminopyridine medium.
Although the enrichment culture gradually degraded 4-aminopyridine with growth, 4-amino-3-hydroxypyridine accumulated in the culture to a final concentration of 6.4 × 10−3 mM after 5 days of cultivation. When we cultivated the enrichment culture in basal medium containing 4-amino-3-hydroxypyridine or 3,4-dihydroxypyridine (final concentration, 0.05% wt/vol) with and without 4-aminopyridine, the culture completely degraded 3,4-dihydroxypyridine in both media in 4 days but did not degrade 4-amino-3-hydroxypyridine in either medium.
Identification of the gene encoding 3-hydroxy-4-pyridine dioxygenase in the isolated strains
We hypothesized that 4-aminopyridine is metabolized to 3,4-dihydroxypyridine, and that the pyridine ring is then cleaved by 3-hydroxy-4-pyridone dioxygenase, as described below. The fragment amplified by pydA-specific primers was isolated and analyzed to determine whether some predominant strain in the enrichment culture carries the dioxygenase gene. The same sequence fragment was amplified from three different samples. The amino acid sequence deduced from the determined 801-bp sequence showed a high level of identity with sequences of the extradiol-dioxygenase-3B-like superfamily of proteins, especially with that of the putative PydA from Hyphomicrobium sp. MC1 (YP_004673996) (see Additional file 2: Figure S1).
Isolation of culturable bacterial strains from the enrichment culture
Identification of bacteria constituting the 4-aminopyridine-degrading enrichment culture
Genus or species affiliation (RDP II classifier)
Best database match
P. nitroreducens IAM 1439 (AM088473)
S. maltophilia e-p13 (AJ293473)
E. agglomerans JCM1236 (AB004691)
T. pulmonis NIPHL170804 (AY741505)
B. cenocepacia J2315 (AM747721)
M. esteraromaticum S29 (AB099658)
Enterobacter sp. SPh (FJ405367)
Uncultured Hyphomicrobium sp. (FJ889298)
E. meningoseptica R3-4A (HQ154560)
When ten-fold-diluted enrichment culture was spread on agar plates containing 4-aminopyridine, several small colonies appeared. Colony PCR analysis of the 16S rRNA gene indicated that these were colonies of strains 4AP-A, identified as a species of Pseudomonas and 4AP-G, identified as a species of Enterobacter. Attempts to isolate 4-aminopyridine-degrading bacteria by changing the concentration of 4-aminopyridine and the incubation period at 30°C were unsuccessful. We could, however, isolate large colonies of strain 4AP-A on an agar plate containing 3,4-dihydroxypyridine.
DGGE analysis of the enrichment culture
The full-length sequence of the 16S rRNA gene of strain 4AP-Y showed a high level of identity with that of a Hyphomicrobium species detected in a waste-treatment plant (AF098790, ) and of unculturable Hyphomicrobium species detected by PCR-DGGE (FJ889298, 4; FJ536932, ) (Additional file 1: Table S2). Species of the genus Hyphomicrobium form characteristic mother cells with hyphae and can utilize C1 compounds, e.g., methanol, formate, or methylamine . We observed bi-polar filamentous cells with this shape in the culture grown with 4-aminopyridine (see Additional file 2: Figure S2). Our attempts to isolate Hyphomicrobium sp. strain 4AP-Y using medium containing methanol, formate, or formamide according to previously reported methods  failed.
The pyridine-ring hydroxylation step is one of main initial steps in the degradation of pyridines . Our analyses of the accumulated metabolites from 4-aminopyridine and the growth substrate specificity suggested that 4-aminopyridine was converted to 4-amino-3-hydroxypyridine and 3,4-dihydroxypyridine (Figure 1). We hypothesized that 4-hydroxypyridine is another possible metabolite based on the previously reported metabolic pathways of pyridines . The enrichment culture could not degrade 4-amino-3-hydroxypyridine and 4-hydroxypyridine, even when 4-aminopyridine was added to the medium. Therefore, 4-amino-3-hydroxypyridine must be a dead-end product. In the enrichment culture, 4-aminopyridine probably would be directly converted to 3,4-dihydroxypyridine mainly by dehydroxylation and the release of ammonia (Figure 1), similar to the conversion of aniline to benzenediol (catechol) by a dioxygenase .
How 3,4-dihydroxypyridine is further metabolized in the enrichment culture is not known, but in Agrobacterium sp. NCIB 10413, 3,4-dihydroxypyridine is converted to 3-formiminopyruvate via the putative intermediate 3-(N-formyl)-formiminopyruvate by the N-heterocyclic ring-cleavage dioxygenase, 3-hydroxy-4-pyridone dioxygenase (3,4-dihydroxypyridine 2,3-dioxygenase) [6, 7]. The gene encoding 3-hydroxy-4-pyridone dioxygenase, pydA, from Rhizobium sp. TAL1145 has been cloned, and the pyd gene cluster (AY729020) involved in the degradation and transport of 3-hydroxy-4-pyridone has been functionally analyzed . However, the dioxygenases from strains NCIB 10413 and TAL1145 have not yet been purified and characterized. This enzyme is unstable and easily loses activity during cell extract preparation [6, 7]. PydA from strain TAL1145 shows a high level of sequence identity with previously reported class III type meta-cleavage dioxygenases including putative 3-hydroxy-4-pyridone dioxygenase (YP_004673996) from Hyphomicrobium sp. MC1. Here, we did not detect dioxygenase activity in the mixed cells harvested from the enrichment culture. In a preliminary study, the partial pydA gene fragment could be amplified from the cells by using pydA-specific primers. In future studies, we plan on sequencing the entire gene and analyzing its expression with northern blots instead of detecting dioxygenase activity, to obtain support for our proposed metabolic pathway for 4-aminopyridine.
DGGE analyses indicated that Hyphomicrobium sp. strain 4AP-Y is a prominent degrader of 4-aminopyridine in the enrichment culture (Figures 3, 4, and 5) and that strain 4AP-Y is outnumbered in 3,4-dihydroxypyridine medium (Figure 6A). Therefore, strain 4AP-Y probably converts 4-aminopyridine to 3,4-dihydroxypyridine (Figure 1). 3,4-Dihydroxypyridine, which is also formed from L-mimosine by intestinal bacteria, can be degraded by a much wider range of soil bacteria and ruminal bacteria than has been recognized previously [23, 29, 30]. 3,4-Dihydroxypyridine might be more easily degraded than 4-aminopyridine by the other strains in our enrichment culture, including strains 4AP-A and 4AP-Z (Figure 1).
Hyphomicrobium spp. closely related to strain 4AP-Y have been isolated from waste-water plants  or detected as unculturable bacteria by PCR-DGGE [25, 31]. Species of the genus Hyphomicrobium are oligocarbophilic and can grow on mineral salt medium, and the growth can be stimulated by soil extract . In addition, they grow well on C1 compounds, such as methanol, methylated amines or formate . However, little is known about the assimilation of aromatic compounds by Hyphomicrobium spp. . The unculturable Hyphomicrobium sp. Y17-2 becomes numerically dominant in enrichment cultures containing toluene and o-xylene . In our enrichment culture, Hyphomicrobium sp. 4AP-Y probably plays an important role in the initial step of 4-aminopyridine degradation. Other dominant strains, such as strains 4AP-A and 4AP-Z probably share 3,4-dihydroxypyridine and its metabolites as growth substrates. Strain 4AP-Y probably utilizes one of final metabolites from 3,4-dihydroxypyridine, i.e., formate, via the further degradation of this intermediate by other dominant strains.
The phytotoxicity, absorption, and translocation of 4-aminopyridine in corn and sorghum growing in treated nutrient cultures and soils have been examined by Starr and Cunningham . Although aerobic and anaerobic degradation of 4-aminopyridine in soil had been expected, the authors found little evidence to support biodegradation. Our data reported here indicated that 4-aminopyridine can be mineralized by soil microbiota, and we identified bacteria possibly involved in the degradation. To further elucidate the degradation, we will need to establish culture conditions for the isolation of strain 4AP-Y to be able to study the enzymes involved in the degradation of 4-aminopyridine.
We isolated a 4-aminopyridine-degrading enrichment culture from a normal soil sample, revealed the metabolic fate of 4-aminopyridine, and characterized the bacterial population in the culture. GC-MS analysis and growth substrate specificity indicated that 4-aminopyridine was probably metabolized to 3,4-dihydroxypyridine and that formate probably is one of metabolites. DGGE analysis revealed that the unculturable strain, Hyphomicrobium sp. strain 4AP-Y became more dominant with increasing 4-aminopyridine concentration in the culture and in the presence of formate and Elizabethkingia sp. 4AP-Z was dominant in the presence of 3,4-dihydroxypyridine. Hyphomicrobium sp. strain 4AP-Y, Elizabethkingia sp. 4AP-Z, and the culturable 3,4-dihydroxypyridine-degrading bacterium, Pseudomonas nitroreducens 4AP-A and Enterobacter sp. 4AP-G probably play important roles in 4-aminopyridine degradation.
We would like to thank Prof. Hirosato Takiwaka for helping with the chemical synthesis of 3,4-dihydroxypyridine and NMR analysis.
- Hollins RA, Merwin LH, Nissan RA, Wilson WS, Gilardi R: Aminonitropyridines and their N-oxides. J Heterocycl Chem. 1996, 33 (3): 895-904. 10.1002/jhet.5570330357.View ArticleGoogle Scholar
- Liu S-M, Wu C-H, Hung H-J: Toxicity and anaerobic biodegradability of pyridine and its derivatives under sulfidogenic conditions. Chemosphere. 1998, 36 (10): 2345-2357. 10.1016/S0045-6535(97)10203-X.PubMedView ArticleGoogle Scholar
- Kaiser JP, Feng Y, Bollag JM: Microbial metabolism of pyridine, quinoline, acridine, and their derivatives under aerobic and anaerobic conditions. Microbiol Rev. 1996, 60 (3): 483-498.PubMedPubMed CentralGoogle Scholar
- Fetzner S: Bacterial degradation of pyridine, indole, quinolone, and their derivatives under different redox conditions. Appl Microbiol Biotechnol. 1998, 49 (3): 237-250. 10.1007/s002530051164.View ArticleGoogle Scholar
- Lee JJ, Rhee S-K Lee S-T: Degradation of 3-methylpyridine and 3-ethylpyridine by Gordonia nitida LE31. Appl Environ Microbiol. 2001, 67 (9): 4342-4345. 10.1128/AEM.67.9.4342-4345.2001.PubMedPubMed CentralView ArticleGoogle Scholar
- Watson GK, Houghton C, Cain RB: The hydroxylation of 4-hydroxypyridine to pyridine-3,4-diol (3,4-dihydroxypyridine) by 4-hydroxypyridine-3-hydroxylase. Biochem J. 1974, 140 (2): 265-276.PubMedPubMed CentralView ArticleGoogle Scholar
- Watson GK, Houghton C, Cain RB: Microbial metabolism of the pyridine ring. The metabolism of pyridine-3,4-diol (3,4-dihydroxypyridine) by Agrobacterium sp. Biochem J. 1974, 140 (2): 277-292.PubMedPubMed CentralView ArticleGoogle Scholar
- Zefirov NS, Agapova SR, Terentiev PB, Bulakhova IM, Vasyukova NI, Modyano LV: Degradation of pyridine by Arthrobacter crystallopoietes and Rhodococcus opacus strains. FEMS Microbiol Lett. 1994, 118 (1–2): 71-74.View ArticleGoogle Scholar
- Bai Y, Sun Q, Zhao C, Wen D, Tang X: Simultaneous biodegradation of pyridine and quinoline by two mixed bacterial strains. Appl Microbial Biotechnol. 2009, 82 (5): 963-973. 10.1007/s00253-009-1892-0.View ArticleGoogle Scholar
- Lodlha B, Bhadane R, Patel B, Killedar D: Biodegradation of pyridine by an isolated bacterial consortium/strain and bio-augmentation of strain into activated sludge to enhance pyridine biodegradation. Biodegradation. 2008, 19 (5): 717-723. 10.1007/s10532-008-9176-4.View ArticleGoogle Scholar
- Vanhoenacker G, Dumont E, David F, Baker A, Sandra P: Determination of arylamines and aminopyridines in pharmaceutical products using in-situ derivatization and liquid chromatography-mass spectrometry. J Chromatog A. 2009, 1216 (16): 3563-3570. 10.1016/j.chroma.2008.08.102.View ArticleGoogle Scholar
- Stickley AR, Mitchell RT, Health RG, Ingram CR, Bradly EL: A method for appraising the bird repellency of 4-aminopyridine. J Wildlife Manage. 1972, 36 (4): 1313-1316. 10.2307/3799273.View ArticleGoogle Scholar
- Ogita K, Okuda H, Watanabe M, Nagashima R, Sugiyama C, Yoneda Y: In vivo treatment with the K+ channel blocker 4-aminopyridine protects against kainate-induced neuronal cell death through activation of NMDA receptors in murine hippocampus. Neuropharmacology. 2005, 48 (6): 810-821. 10.1016/j.neuropharm.2004.12.018.PubMedView ArticleGoogle Scholar
- Yamaguchi S, Rogawski MA: Effects of anticonvulsant drugs on 4-aminopyridine-induced seizures in mice. Epilepsy Res. 1992, 11 (1): 9-16. 10.1016/0920-1211(92)90016-M.PubMedView ArticleGoogle Scholar
- Fragoso-Veloz J, Massieu L, Alvarado R, Tapia R: Seizures and wet-dog shake induced by 4-aminopyridine, and their potentiation by nifedipine. Euro J Pharmacol. 1990, 178 (3): 275-284. 10.1016/0014-2999(90)90106-G.View ArticleGoogle Scholar
- Betts PM, Giddings CW, Fleeker JR: Degradation of 4-aminopyridine in soil. J Agric Food Chem. 1976, 24 (3): 571-574. 10.1021/jf60205a014.PubMedView ArticleGoogle Scholar
- Takenaka S, Asami T, Orii C, Murakami S, Aoki K: A novel meta-cleavage dioxygenase that cleaves a carboxyl-group-substituted 2-aminophenol. Eur J Biochem. 2002, 269 (23): 5871-5877. 10.1046/j.1432-1033.2002.03306.x.PubMedView ArticleGoogle Scholar
- Edward U, Rogall T, Blöcker H, Emde M, Böttger EC: Isolation and direct complete nucleotide determination of entire genes. Characterization of a gene coding for 16S ribosomal RNA. Nuc Acids Res. 1989, 17 (19): 7843-7853. 10.1093/nar/17.19.7843.View ArticleGoogle Scholar
- Kage S, Kudo K, Ikeda H, Ikeda N: Simultaneous determination of formate and acetate in whole blood and urine from humans using gas chromatography–mass spectrometry. J Chromatogr B. 2004, 805 (1): 113-117. 10.1016/j.jchromb.2004.02.029.View ArticleGoogle Scholar
- Ovreås L, Forney L, Daae FL, Torsvik V: Distribution of bacterioplankton in meromictic Lake Saelenvannet, as determined by denaturing gradient gel electrophoresis of PCR-amplified gene fragments coding for 16S rRNA. Appl Environ Microbiol. 1997, 63 (9): 3367-73.PubMedPubMed CentralGoogle Scholar
- Weatherburn MW: Phenol-hypochlorite reaction for determination of ammonia. Anal Chem. 1967, 39 (8): 971-4. 10.1021/ac60252a045.View ArticleGoogle Scholar
- Hartree EF: Determination of protein: a modification of the Lowry method that gives a linear photometric response. Anal Biochem. 1985, 48 (2): 422-427.View ArticleGoogle Scholar
- Allison MJ, Hammond AC, Jones RJ: Detection of ruminal bacteria that degrade toxic dihydroxypyridine compounds produced from mimosine. Appl Environ Microbiol. 1990, 56 (3): 590-594.PubMedPubMed CentralGoogle Scholar
- Layton AC, Karanth PN, Lajoie CA, Meyers AJ, Gregory IR, Stapleton RD, Taylor DE, Sayler GS: Quantification of Hyphomicrobium populations in activated sludge from an industrial wastewater treatment system as determined by 16S rRNA analysis. Appl Environ Microbiol. 2000, 66 (3): 1167-1174. 10.1128/AEM.66.3.1167-1174.2000.PubMedPubMed CentralView ArticleGoogle Scholar
- Hayes AC, Zhang Y, Liss SN, Allen DG: Linking performance to microbiology in biofilters treating dimethyl sulphide in the presence and absence of methanol. Appl Microbiol Biotechnol. 2010, 85 (4): 1151-1166. 10.1007/s00253-009-2272-5.PubMedView ArticleGoogle Scholar
- Gliesche C, Fesefeldt A, Hirsch P: Genus I. Hyphomicrobium Stutzer and Hartleb 1898, 76AL. Bergey’s manual of systematic bacteriology. The proteobacteria, part C, The alpha-, beta-, delta-, and epsilonproteobacteria. Volume 2. Edited by: Brenner DJ, Krieg NR Staley JT. 1993, New York: Springer, 476-494. 2Google Scholar
- Murakami S, Hayashi T, Maeda T, Takenaka S, Aoki K: Cloning and functional analysis of aniline dioxygenase gene cluster, from Frateuria species ANA-18, that metabolizes aniline via an ortho-cleavage pathway of catechol. Biosci Biotech Biochem. 2003, 67 (11): 2351-2358. 10.1271/bbb.67.2351.View ArticleGoogle Scholar
- Awaya JD, Fox PM Borthakur D: pyd genes of Rhizobium sp. strain TAL1145 are required for degradation of 3-hydroxy-4-pyridone, an aromatic intermediate in mimosine metabolism. J Bacteriol. 2005, 187 (13): 4480-4487. 10.1128/JB.187.13.4480-4487.2005.PubMedPubMed CentralView ArticleGoogle Scholar
- Dominguez-Bello GM, Stewart CS: Degradation of mimosine, 2,3-dihydroxy pyridine and 3-hydroxy-4(1H)-pyridine by bacteria from the rumen of sheep in Venezuela. FEMS Lett. 1990, 73 (4): 283-289. 10.1111/j.1574-6968.1990.tb03951.x.View ArticleGoogle Scholar
- Hammond AC: Leucaena toxicosis and its control in ruminants. J Anim Sci. 1995, 73 (5): 1487-1492.PubMedGoogle Scholar
- Ceja-Navarro JA, Rivera-Orduna FN, Patino-Zuniga L, Vila-Sanjurjo A, Crossa J, Govaerts B, Dendooven L: Phylogenetic and multivariate analyses to determine the effects of different tillage and residue management practices on soil bacterial communities. Appl Environ Microbiol. 2010, 76 (11): 3685-3691. 10.1128/AEM.02726-09.PubMedPubMed CentralView ArticleGoogle Scholar
- Ralebitso TK, Yamazoe A, Reuling WF, Braster M, Senior E, van Verseveld HW: Insights into bacterial associations catabolizing atrazine by culture-dependent and molecular approaches. World J Microbiol Biotechnol. 2003, 19 (1): 59-67. 10.1023/A:1022531919239.View ArticleGoogle Scholar
- Ralebitso TK, Roling WFM, Braster M, van Senior E, Verseveld HW: 16S rDNA-based characterization of BTX-catabolizing microbial associations isolated from a South African sandy soil. Biodegradation. 2000, 11 (6): 351-357. 10.1023/A:1011611231633.PubMedView ArticleGoogle Scholar
- Starr RI, Cunningham DJ: Phytotoxicity, absorption, and translocation of 4-aminopyridine in corn and sorghum growing in treated nutrient cultures and soils. J Agric Food Chem. 1974, 22 (3): 409-413. 10.1021/jf60193a034.View ArticleGoogle Scholar
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