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Applied and Environmental Microbiology, June 2000, p. 2290-2296, Vol. 66, No. 6
0099-2240/00/$04.00+0
Copyright © 2000, American Society for Microbiology. All rights reserved.

Distribution of Aldoxime Dehydratase in Microorganisms

Yasuo Kato, Ryoko Ooi, and Yasuhisa Asano*

Biotechnology Research Center, Faculty of Engineering, Toyama Prefectural University, Kosugi, Toyama 939-0398, Japan

Received 20 December 1999/Accepted 21 March 2000


    ABSTRACT
Top
Abstract
Introduction
Materials and Methods
Results
Discussion
References

The distribution of phenylacetaldoxime-degrading and pyridine-3-aldoxime-degrading ability was examined with intact cells of 975 microorganisms, including 45 genera of bacteria, 11 genera of actinomyces, 22 genera of yeasts, and 37 genera of fungi, by monitoring the decrease of the aldoximes by high-pressure liquid chromatography. The abilities were found to be widely distributed in bacteria, actinomyces, fungi, and some yeasts: 98 and 107 strains degraded phenylacetaldoxime and pyridine-3-aldoxime, respectively. All of the active strains exhibited not only the aldoxime-dehydration activity to form nitrile but also nitrile-hydrolyzing activity. On the other hand, all of 19 nitrile-degrading microorganisms (13 species, 7 genera) were found to exhibit aldoxime dehydration activity. It is shown that aldoxime dehydratase and nitrile-hydrolyzing activities are widely distributed among 188 aldoxime and 19 nitrile degraders and that the enzymes were induced by aldoximes or nitriles.


    INTRODUCTION
Top
Abstract
Introduction
Materials and Methods
Results
Discussion
References

Nitrile compounds are discharged into the environment as industrial waste water, agricultural chemicals, etc. (23). Many microorganisms can use nitriles as a source of carbon and/or nitrogen for growth. Asano et al. have isolated various nitrile-degrading microorganisms from soil (2, 5, 24) and clarified that nitriles are converted to carboxylic acids either by a combination of nitrile hydratase (1, 3, 6) and amidase (4) or by nitrilase (8). These enzymes have been extensively evaluated from the viewpoint of chemical industry: the industrial production of acrylamide, nicotinamide, and 5-cyanovalelamide are typical examples (5, 6, 16, 26). Despite the importance of the nitrile-hydrolyzing enzymes in industry, information about their distribution in microorganisms is quite limited, and their physiological role has never been well understood since they have been screened only from nitrile-degrading microorganisms.

We have been studying aldoxime-degrading enzymes and isolated various aldoxime-degrading microorganisms, e.g., Bacillus sp. strain OxB-1 (7) and Rhodococcus sp. strain YH3-3 (12), from soil. The isolated strains metabolized aldoximes through nitriles into the corresponding carboxylic acid by a combination of a novel aldoxime dehydratase and nitrile-hydrolyzing enzymes (7, 12) (Fig. 1). The novel aldoxime dehydratase was purified and characterized from Bacillus sp. strain OxB-1 (7, 15). The enzyme from Rhodococcus sp. strain YH3-3 was applied to the enzymatic synthesis of nitriles from aldoximes under a mild condition (12, 13). A nitrile hydratase responsible for aldoxime metabolism was purified and characterized from Rhodococcus sp. strain YH3-3, and its properties were compared with the known nitrile hydratases (14).


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FIG. 1.   Microbial metabolism of aldoximes. Bacillus sp. strain OxB-1 metabolizes PAOx (R = PhCH2) to form PAN, which is successively hydrolyzed to PAA by the action of nitrilase (7). On the other hand, Rhodococcus sp. strain YH3-3 metabolizes PyOx (R = 3-pyridyl) as follows: the aldoxime is dehydrated to form CyPy, which is converted to NAm by nitrile hydratase, and the NAm is successively hydrolyzed to NA by amidase (12).

To elucidate the generality of the relationship of aldoxime dehydratase and nitrile-hydrolyzing enzymes in microorganisms, we examined the distribution of both enzyme activities with the intact cells of a variety of aldoxime- or nitrile-degrading microorganisms, monitoring the decrease of the aldoximes, and we studied the relationship among the enzymes.


    MATERIALS AND METHODS
Top
Abstract
Introduction
Materials and Methods
Results
Discussion
References

Chemicals. Meat and malt extracts were obtained from Kyokuto (Tokyo, Japan). Polypepton and yeast extract were purchased from Nippon Seiyaku (Tokyo, Japan). High-pressure liquid chromatography (HPLC) columns ODS-80Ts (4.6 by 150 mm) and Hibar LiChrosorb-NH2 (4.0 by 250 mm) were from Tosoh Corp. (Tokyo, Japan) and Kanto Chemicals (Tokyo, Japan), respectively. Aldoximes were synthesized as described previously (7, 12). All other chemicals were from commercial sources and used without further purification.

Microorganisms and culture media. A total of 975 strains from the following type culture collections were used: the Institute of Molecular and Cellular Biosciences (IAM), University of Tokyo, Tokyo, Japan; the Institute of Fermentation (IFO), Osaka, Japan; the Japan Collection of Microorganisms (JCM), Tokyo, Japan; the National Collections of Industrial Food and Marine Bacteria (NCIMB), Aberdeen, Scotland; the National Collections of Type Cultures and Pathogenic Fungi (NCTC) London, United Kingdom; the American Type Culture Collection (ATCC); and our own laboratory (TPU). These included 407 strains of 45 genera of bacteria, 133 strains of 11 genera of actinomyces, 333 strains of 22 genera of yeasts, and 102 strains of 37 genera of fungi.

The culture medium for the bacteria was composed of 1.0% of meat extract, 1.0% of Polypepton, and 0.5% NaCl (pH 7.2). The medium for actinomyces contained 1.0% malt extract, 0.4% yeast extract, and 0.4% D-glucose (pH 7.2). The medium for yeasts consisted of 1.0% D-glucose, 0.5% Polypepton, 0.3% yeast extract, and 0.3% malt extract (pH 5.6). The medium for fungi contained 20 g of sucrose and boiled extract from 200 g of potato per liter (pH 6.0). Tap water was used for the media described above, and the pH was adjusted by using HCl and NaOH. Each microorganism was inoculated into a test tube containing 10 ml of the medium with 0.05% concentrations of the inducers, i.e., phenylacetaldoxime (PAOx), pyridine-3-aldoxime (PyOx), phenylacetonitrile (PAN), and 3-cyanopyridine (CyPy), and then incubated with shaking for 2 to 14 days at 30°C until their growth reached maximum levels. For facultative anaerobic bacteria, the strains were also grown under static conditions.

Enzyme assay and definition of units. Microbial degradation of aldoxime was qualitatively analyzed by thin-layer chromatography (TLC). After the strain was cultured in the medium containing PAOx or PyOx, 1 µl of the culture was spotted onto silica gel TLC plates (Kieselgel 60; Merck) and then developed with 20% (vol/vol) ethyl acetate in hexane. The remaining aldoxime in the medium was visualized with iodine vapor.

Aldoxime dehydration and nitrile-hydrolyzing activities were quantitatively assayed by measuring the rate of consumption of aldoxime and nitrile, respectively. A standard assay solution contained 50 µmol of potassium phosphate buffer (pH 7.0), 25 µmol of substrate, and washed cells from 5 ml of culture in a total volume of 500 µl. After an incubation at 30°C with shaking, the reaction mixture was centrifuged (18,000 × g, 2 min) at 4°C to remove the cells. The supernatant was analyzed with a Waters 600E HPLC apparatus equipped with a Waters 486 absorbance detector (254 nm) at a flow rate of 1.0 ml/min. PAOx, PAN, phenylacetamide (PAAm), and phenylacetic acid (PAA) were detected with an ODS-80Ts column using an elution solvent consisting of 10 mM H3PO4 in 40% (vol/vol) CH3CN, and PyOx and 3-CyPy were measured with the same column using 10 mM H3PO4 in 10% (vol/vol) CH3CN. Nicotinamide (NAm) and nicotinic acid (NA) were detected with Hibar LiChrosorb-NH2 column with 2.5 mM potassium phosphate buffer (pH 2.8) in 75% (vol/vol) CH3CN. Single units of aldoxime dehydration and nitrile-hydrolyzing activities were defined as the amount of enzyme that catalyzed the dehydration of aldoxime and hydrolysis of nitrile, respectively, at a rate of 1 µmol/min. Reaction mixtures with the cells but without substrates served as blanks for both the assays. Under the assay conditions, the measurable detection limit of the enzyme activity was about 0.01 (in units/liter of culture).


    RESULTS
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Abstract
Introduction
Materials and Methods
Results
Discussion
References

Distribution of PAOx and PyOx dehydration activity in bacteria and actinomyces. We selected PAOx and PyOx as a model compound of alkylaldoxime and arylaldoxime, respectively. Bacterial and actinomycetal strains in our stock cultures were aerobically grown in the medium containing PAOx or PyOx, and the ability to degrade the aldoximes was screened by qualitative measurement of aldoxime disappearance in the culture medium by using TLC assay. Among the 540 strains tested, 37 strains were able to degrade PAOx, and this activity was distributed across 7 genera, while 96 strains, distributed across 30 genera, could degrade PyOx. Although some aerobically grown facultative anaerobes could degrade PyOx, none of the statically grown cells could degrade PAOx nor PyOx. We measured not only the aldoxime dehydration activities but also the PAN- and CyPy-hydrolyzing activities in the cells of PAOx- or PyOx-degrading strains. Since all of the aldoxime-degrading strains contained both aldoxime dehydratase and nitrile-hydrolyzing enzymes, nitriles formed by the dehydration of aldoximes were subsequently converted to amides and/or acids by the action of the latter enzymes. We therefore analyzed the dehydration activity by measuring the consumption of aldoxime in the assay. Nitrile-hydrolyzing activity was estimated by measuring the rate of consumption of nitrile, which was equal to the sum of nitrile hydratase and nitrilase activities. As shown in Tables 1 and 2, all of the strains grown with PAOx or PyOx exhibited the aldoxime dehydration activities, together with nitrile-hydrolyzing enzyme activities. The 21 strains marked with a number symbol (#) exhibited both PAOx and PyOx dehydration activities.

                              
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TABLE 1.   PAOx dehydration and PAN-hydrolyzing activities in bacteria and actinomyces grown with PAOxa


                              
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TABLE 2.   PyOx dehydration and CyPy-hydrolyzing activities in bacteria and actinomyces grown with PyOxa

By measuring the formation of PAAm and NAm in the reaction mixture, we determined the mode of nitrile degradation by the active strains. Totals of 10 and 21 strains, marked with an asterisk (*) in Tables 1 and 2, respectively, converted nitrile to acid-accumulating amide, indicating that the strains hydrolyzed the nitriles by a sequential action of nitrile hydratase and amidase. These results do not exclude the possibility of a coexistence of nitrilase in the strains. The other strains degraded PAN and CyPy without forming the corresponding amides. In these strains, the nitriles are hydrolyzed by nitrilase and/or the combination of nitrile hydratase and amidase in which amidase activity was stronger than that of nitrile hydratase.

Distribution of aldoxime dehydration activity in fungi. We next screened for fungal strains which degrade PAOx or PyOx. PAOx-degrading activity was widely distributed in various genera. Of the 102 strains, 52 among 28 genera were able to degrade PAOx, whereas PyOx-degrading activity was seen in only a limited number of fungal strains; it was seen in 11 strains among 3 genera. Tables 3 and 4 show both of the enzyme activities in all of the active strains. Some active fungal strains degraded PAN accumulating PAAm, suggesting that the strains hydrolyzed PAN by the combinatorial action of nitrile hydratase and amidase, whereas PyOx-degrading fungi converted CyPy into NA without forming NAm.

                              
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TABLE 3.   PAOx dehydration and PAN-hydrolyzing activities in fungi grown with PAOxa


                              
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TABLE 4.   PyOx dehydration and CyPy-hydrolyzing activities in fungi grown with PyOxa

Distribution of aldoxime dehydration activity in yeasts. Aldoxime degradation activity in yeasts is rare. We screened 333 strains, including 2 species of Brettanomyces, 29 species of Candida, 3 species of Cryptococcus, 3 species of Debaryomyces, 1 species of Endomycopsis, 1 species of Hanseniaspora, 24 species of Hanenula, 3 species of Kloeckera, 1 species of Lipomyces, 19 species of Pichia, 3 species of Rhodosporidium, 10 species of Rhodotorula, 32 species of Saccharomyces, 1 species of Saccharomycodes, 1 species of Saccharomycopsis, 3 species of Schizosaccharomyces, 1 species of Sporidiobolus, 4 species of Sporobolomyces, 12 species of Torulopsis, 3 species of Trichosporon, and 1 species of Zygosaccharomyces. Of these, two were active in degrading PAOx: Candida methanolica TPU 1217 and Pichia miso TPU 1306 showed PAOx dehydration activity at 1.31 and 0.9 (U/liter of culture), coexisting with a PAN-hydrolyzing activity at 0.5 and 0.2 (U/liter of culture), respectively, when they were grown with 0.05% of PAOx. It was also shown that both the strains degraded PAOx by a successive combination of aldoxime dehydration and nitrile-hydrolyzing enzymes. P. miso degraded PAN accumulating PAAm, while C. methanolica degraded it without the formation of PAAm. On the other hand, no yeast strain could degrade PyOx.

Based on these results, it is shown that all of the PAOx or PyOx degraders degraded the aldoximes by a combination of aldoxime dehydratase and nitrile-hydrolyzing enzymes.

Aldoxime dehydration enzyme activity in nitrile-degrading microorganisms. Nineteen microorganisms (13 species, 7 genera) which had been isolated as nitrile degraders were grown with aldoximes, such as PAOx and PyOx, or nitriles, such as PAN and CyPy, and the aldoxime dehydration and nitrile-hydrolyzing activities were measured. As shown in Table 5, all of the nitrile degraders thus examined showed either PAOx or PyOx dehydratase activities. A high PAOx dehydration activity was seen in alkylnitrile-degrader, e.g., Rhodococcus sp. strain N-774 (23), Corynebacterium sp. strain C-5 (22), R. rhodochrous J-1 (3, 19), and R. erythropolis BG-16 (Y. Asano, T. Yasuda, Y. Tani, and H. Yamada, Abstr. Ann. Meet. Japan Soc. Ferment. Technol., 1981). No aldoxime dehydratase activity was seen when the strains were grown without aldoximes or nitriles, although PAN- or CyPy-hydrolyzing activity was detected in the cells.

                              
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TABLE 5.   Aldoxime dehydration and nitrile-hydrolyzing activities in nitrile-degrading microorganisms when they were grown with or without inducersa


    DISCUSSION
Top
Abstract
Introduction
Materials and Methods
Results
Discussion
References

Aldoximes are considered to be intermediates in the biosynthesis of certain biologically active compounds such as indoleacetic acid, cyanogenic glucosides, and glucosinolates in plants (17, 20, 21); however, very little is known about aldoxime-degrading enzymes: indoleacetaldoxime (IAOx) hydrolyase (EC 4.2.1.29), catalyzing a specific dehydration reaction of IAOx to form indoleacetonitrile, has been detected in limited genera of fungi and higher plants (20, 21), and the enzyme has only been partially purified from Gibberella spp. (17). In our previous report, we isolated various aldoxime-degrading bacteria from soil by several-months' acclimation and clarified that the isolated strains degraded aldoximes by the combination of aldoxime dehydratase and nitrile-hydrolyzing enzymes (7, 12). Rhodococcus sp. strain YH3-3, isolated in a medium containing PyOx as a sole source of nitrogen, degrades PyOx to NA by a combination of aldoxime dehydratase, nitrile hydratase, and amidase (12) (Fig. 1), whereas Bacillus sp. strain OxB-1 degrades PAOx to PAA by the action of aldoxime dehydratase and nitrilase (7) (Fig. 1), although it could not utilize PAOx as a nitrogen or carbon source due to the toxicity of PAOx. In this report, we discovered that the novel aldoxime dehydratases acting on the aldoximes are distributed among a variety of microorganisms, together with nitrile-hydrolyzing enzymes. We also screened for the aldoxime dehydratase activity from the nitrile degraders hitherto known and clarified that all of the nitrile degraders contained not only nitrile-hydrolyzing enzymes but also aldoxime dehydratase by culturing with aldoxime. None of the active strains showed aldoxime dehydration activity when they were grown in the medium without aldoximes, suggesting that aldoxime dehydratase was inducibly formed in these strains. Although a number of studies had been done on the nitrile-hydrolyzing enzymes, their induction mechanisms remained unknown. Nitrile hydratases of P. chlororaphis B23 and R. rhodochrous J-1 are strongly induced by amides and their derivatives (26), although that of Rhodococcus sp. strain N-774 (23) is formed constitutively. Nitrilases are inducibly formed (2, 9, 10, 18, 24, 25, 27), except that the enzyme is constitutively produced in Acinetobacter sp. strain AK 226 (27). In the present study we found that aldoximes act as good inducers not only for aldoxime dehydratase but also for the nitrile-hydrolyzing enzymes. From the results presented here, we cannot clarify whether aldoxime dehydratase and nitrile-hydrolyzing enzymes are regulated separately or not in these strains. We have recently discovered that the genes for aldoxime dehydratase and nitrilase coexisted as a gene cluster in the genome of Bacillus sp. strain OxB-1 (15). It is important to genetically clarify the general relationship between aldoxime dehydratase and nitrile-hydrolyzing enzymes in the aldoxime- and nitrile-degrading strains.

A total of 31 bacterial and 9 fungal aldoxime and nitrile degraders showed both the PAOx and PyOx dehydration activities, together with PAN and CyPy hydrolyzing activities. It is not clear whether the differences between PAOx and PyOx dehydration activities observed in the strains were simply due to the substrate specificity of aldoxime dehydratase or to the possible existence of two or more aldoxime dehydratases having different substrate specificities. Purification and characterization of aldoxime dehydratase and nitrile-hydrolyzing enzymes from the strains will solve this problem.

It has been reported that about 70 strains of microorganisms were isolated to degrade nitrile compounds, and they were distributed across 37 species of 19 genera (6, 24). However, they appear frequently in limited genera, i.e., Arthrobacter, Bacillus, Rhodococcus, Fusarium, since the most common screening protocols involve enrichment isolation in the media containing nitriles as a carbon or a nitrogen source: this is inevitably skewing positive clones to groups of readily culturable microorganisms. By culturing the strains with aldoxime, we showed here that the occurrence of nitrile hydratase in various species of facultative anaerobes and fungi. Although it is reported that Rhodococcus sp. strain AK32 has only nitrilase (27), culturing the strain with PAOx showed that the strain also contains nitrile hydratase and amidase in addition to nitrilase. These findings encourage us to screen further cryptic nitrile-hydrolyzing enzymes in microorganisms by culturing with aldoxime.


    ACKNOWLEDGMENTS

This work was supported in part by a Grant-in-Aid for "Research for the Future" (JSPS-RFTF 96I00302) from the Japan Society for the Promotion of Science.


    FOOTNOTES

* Corresponding author. Mailing address: Biotechnology Research Center, Faculty of Engineering, Toyama Prefectural University, Kosugi, Toyama 939-0398, Japan. Phone: 81-766-56-7500, ext. 530. Fax: 81-766-56-2498. E-mail: asano{at}pu-toyama.ac.jp.


    REFERENCES
Top
Abstract
Introduction
Materials and Methods
Results
Discussion
References

1. Asano, Y., Y. Tani, and H. Yamada. 1980. A new enzyme "nitrile hydratase" which degrades acetonitrile in combination with amidase. Agric. Biol. Chem. 44:2251-2252.
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3. Asano, Y., K. Fujishiro, Y. Tani, and H. Yamada. 1982. Aliphatic nitrile hydratase from Arthrobacter sp. J-1. Purification and characterization. Agric. Biol. Chem. 46:1165-1174.
4. Asano, Y., M. Tachibana, Y. Tani, and H. Yamada. 1982. Purification and characterization of amidase which participates in nitrile degradation. Agric. Biol. Chem. 46:1175-1181.
5. Asano, Y., T. Yasuda, Y. Tani, and H. Yamada. 1982. A new enzymatic method of acrylamide production. Agric. Biol. Chem. 46:1183-1189.
6. Asano, Y. 1991. Studies on the synthesis of amides and amino acids by a novel microbial enzymes. Nippon Nogeikagaku Kaishi 65:1617-1626.
7. Asano, Y., and Y. Kato. 1998. Z-Phenylacetaldoxime degradation by a novel aldoxime dehydratase from Bacillus sp. strain OxB-1. FEMS Microbiol. Lett. 158:185-190[CrossRef].
8. Bandyopadhyay, A. K., T. Nagasawa, Y. Asano, K. Fujishiro, Y. Tani, and H. Yamada. 1986. Purification and characterization of benzonitrilases from Arthrobacter sp. strain J-1. Appl. Environ. Microbiol. 51:302-306[Abstract/Free Full Text].
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14. Kato, Y., T. Tsuda, and Y. Asano. 1999. Nitrile hydratase involved in aldoxime metabolism from Rhodococcus sp. strain YH3-3---purification and characterization. Eur. J. Biochem. 263:662-670[Medline].
15. Kato, Y., K. Nakamura, H. Sakiyama, S. G. Mayhew, and Y. Asano. 2000. A novel heme-containing lyase, phenylacetaldoxime dehydratase from Bacillus sp. strain OxB-1: purification, characterization, and molecular cloning of the gene. Biochemistry 39:800-809[CrossRef][Medline].
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19. Nagasawa, T., C. D. Mathew, J. Mauger, and H. Yamada. 1988. Nitrile hydratase-catalyzed production of nicotinamide from 3-cyanopyridine in Rhodococcus rhodochrous J1. Appl. Environ. Microbiol. 54:766-1769.
20. Rajagopal, R., and P. Larsen. 1972. Metabolism of indole-3-acetaldoxime in plants. Planta 103:45-54[CrossRef].
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22. Tani, Y., M. Kurihara, H. Nishise, and K. Yamamoto. 1989. Bioconversion of dinitrile to mononitrile, a tranexamic acid intermediate, by Corynebacterium sp. Agric. Biol. Chem. 53:3143-3149.
23. Watanabe, I., Y. Satoh, and K. Enomoto. 1987. Screening, isolation and taxonomical properties of microorganisms having acrylonitrile-hydrating activity. Agric. Biol. Chem. 51:3193-3199.
24. Yamada, H., Y. Asano, T. Hino, and Y. Tani. 1979. Microbial utilization of acrylonitrile. J. Ferment. Technol. 57:8-14.
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Applied and Environmental Microbiology, June 2000, p. 2290-2296, Vol. 66, No. 6
0099-2240/00/$04.00+0
Copyright © 2000, American Society for Microbiology. All rights reserved.



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