microbial metabolism of nitriles and its biotechnological...
TRANSCRIPT
"
Journal of Scientific & Industrial Research Vo1.58, December 1 999, pp 925-947
Microbial Metabolism of Nitriles and Its Biotechnological Potential
C Ramakrishna, (Mrs) Heena Dave and M Ravindranathan Research Centre, Indian Petrochemicals Corporation Limited, Vadodara 391 346, India
Biocatalysts display a remarkable capability to function under normal temperature and pressure with high specificity and are potentially very economical. Bioconversion of nitri le compounds to a number of economically important compounds is described. A wide variety of microorganisms having the ability to metabolize different nitriles and discovered during the last two decades are described. It is pointed out that the microbial degradation of nitriles proceeds through two distinct enzymatic pathways: nitrilase catalyzes the direct hydrolysis of nitriles to the corresponding carboxylic acids and ammonia, whil e nitrile hydratase catalyzes the hydration of nitriles to
"f- the corresponding amides, followed by their conversion to the corresponding carboxylic acids plus ammonia by amidase. It is mentioned that the versatile biocatalytic nature and applications of these enzymes are being increasingly recognised for the selective hydrolysis of various types of nitriles for the production of several fine chemicals, pharmaceuticals and optically active nitriles, amides and carboxylic acids, which are not generally feasible by chemical routes. A commercial process involving the multi-kiloton scale synthesis of acrylamide using Rhodococcus rhoc!ochrous J I nitrile hydratase is described, which is the best example of a fully developed industrial application of this biotechnology. Though, recent developments broadened the potential application of these versatile biocatalysts in chemical synthesis and bioremedi ation, further studies are required to fully harness their biotechnological potential.
Introduction
The nitrile compounds, the cyano group (-CN) containing organic compounds (organic cyanides) are numerous and wide spread in the environment. In nature, nitriles are mainly present in the form of cyanogenic glycosides which are produced by plants and animals, such as insects, etc. Plants also produce other type of nitrile compounds like cyanolipids, ricinine, phenylacetonitrile, p-cyanoalanine, etc . l .2 . More importantly, a number of nitrile compounds are manufactured by man for producing a variety of polymers and other chemicals . For example, acrylonitrile and adiponitrile are produced by the chemical industry on a large scale (world-wide production : about 45,00,000 and 1 0,00,000 MT per annum, respectively3) for the manufacture of polyacrylonitrile and nylon polymers. Some ni tri le compounds, such as bromoxyni l , ioxyni l and dichlorobenil , are herbicides .
Chemical Nature, Uses and Toxicity of Nitrites
Chemical Nature and Uses
The -CN functional group in the nitrile compounds, besides being highly reactive, is able to activate adjacent C-H bonds, which is the basis of their versatile reactivity. In general, nitriles are important organic compounds from economic point of view and exhibit broad IPCL Res Centre Communication No.341
chemical utility including their use as feed stocks, solvents, extractants, recrystall izing agents, pharmaceuticals, catalysts and pesticides. They are also h ighly significant intermediates for organic syntheses for preparing amines, ami des, amidines, carboxy acids and esters, aldehydes, ketones including cyclic ketones, imines, heterocyclic compounds, etc. 1 .3.4. Hydrogenation of nitriles to amines provides some important intermediates for both polyurethanes and polyamides . Acetonitrile is widely used for the preparation of a variety of compounds including pharmaceuticals, perfumes and photographic industry chemicals . It is also used for the separation of butadiene and other olefins from hydrocarbon streams, as a solvent for spinning fibres and for high pressure liquid chromatography (HPLC), etc. a-Aminonitriles are versatile intermediates to obtain amino acids, agrochemicals , chelants, radical in itiators and water treatment chemicals . Benzonitrile is used for the production of melamine, in protective coatings and molding resins, as additive in jet fuel, nickel-plating, cotton bleaching baths and for drying acrylic fibre, etc.3. 4 .
Toxicity
Most of the nitriles are highly toxic, mutagenic and carcinogenic in nature. They inhibit cell multipl ication of some algae and sensitive bacteria, such as Pseudomonas putida, but inhibitory concentrations vary for dif-
926 J SCI IND RES VOL-58 DECEMBER 1 999
ferent nitriles'. The toxicity and occupational hazard data for the commonly used ni triles are wel l documented45. The general tox icity of nitri les in humans is expressed as gastric distress and vomiting, bronchial irritation, respiratory distress, convulsions and coma6• The main toxicity concern for n itriles is their acute lethality, causing a disease, osteolathyrsm, which leads to lameness and skeletal deformities'. The toxic potency of nitri les varies with their chemical stmcture. Their acute toxicity is mainly related to their metabolism in the body that resu lts in the release of the 'cyanide' ion . Though most of the avai lable l iterature ascribes almost all the actions of nitriles to the l iberation of cyanide ions, recent reports confirm that both the -CN group and the entire molecule are important for their biological activity. While many of the neural effects are probably due to the -CN moiety, the i lTitating and necrotic effects on the skin, l iver and kidney may be associated with the nature of the alkyl group4 . Recently, the nature and biochemical mechanism of the toxicity and stmcture-activity relationships of nitri les have been reviewed by DeVitd'.
Microbial Nitrile Metabolism
The ni trile metabolism is widely distributed in nature2•7.K and many microorganisms, plants and some animals can degrade n itriles. A variety of actinomycetes, bacteria, and fungi , that metabolize n itri les as carbon and/or nitrogen source have been described in the literature. Actinomycetes such as Nocardia, Rhodococcus, bacteria such as Acinetobacter, Corynebacterium, Klebsiella, Pseudomonas and fungi l ike Fusarium and Trichodenna are the most prominent genera active in the n itri le metabolism. Three types of biochemical reactions eliminate the -CN group of nitri les: hydrolysis, oxidation and reduction2.K •
Hydrolysis
This is the most common reaction for the microbial metabolism of n i triles and it proceeds via the formation of the cOlTesponding carboxylic acid and ammonia. In fact, based on the product two types of hydrolysis reactions occur. In the first type, the end products are formed directly without any intermediate, catalyzed by an enzyme, n itri lase (EC 3 . 5 .5 . 1 nitri le aminohydrolase) as shown in Eq.( J ) .
Nitrilase R-CN ------..
Nitrile R-COOH + NH.l Carboxylic acid . . . ( 1 )
Nitrilases general ly act on aromatic or heterocycl ic nitri les and are shown in plants, fungi and bacleri a L'! 'o
The second type of hydrolysis is by the ac t ion o r a two-enzyme system, consisting of a nitri Ie hydratase ( EC .
4.2. 1 .84) that converts n itrile to amide and an am idase (EC. 3 .5 . 1 .4. ) that converts amide to the correspond ing carboxylic acid and ammonia [Eq.(2») :
N itri le hydratase
R-CN -. R-CON H , Nitrile + Hp Amide
Amida,e
--------. + H ,O
R-COOl-1 + N H , Carboxylic acid . . ( 2 )
Generally, aliphatic nitriles are metabolized through this pathway in several bacteriaL'!. J I l .
A new type of enzyme activity hydrolyzing all types of cyanide compounds, including n itriles, is reported in Acinetobacter sp. RFB J t t . This differs from the hi therto reported enzymes ill that, it is extracellu lar, constitutive, located in a l ipid complex and hydrolyzes all the three classes of cyanides such as simple and complex inorganic as well as organic cyanides (nitriles) " .
Oxidation
Many plants and insects oxidize some of the n i triles to cyanohydrins (or a-hydroxynitriles) by an oxygenase enzyme. The cyanohydrins are further decompl)sed spontaneously or by the action of another enzyme, oxynitri lase or hydroxy n itri le lyase l 2 to an aldehyde and hydrogen cyanide (HCN) .
Oxygenase Oxynitrilase
R-CHl-CN ------� -CHOH-CN ----� N i tri le + O2 a-Hydroxy nitri le
R-CHO + HCN
A ldehyde . . . (3 )
This type of enzyme system, that liberates HCN from n itri les, is almost non-existing in microorganisms. However, a fungus, Trichoderma sp. is reported to degrade diaminomaleonitrile releasing cyanideD .
Reduction
The N2-fixing organisms contain the enzyme ni trogenase, which hydrogenates N2 and a number of sub-
. '
RAMAKRISHNA et al. : MICROBIAL METABOLISM OF NITRILES 927
strates such as cyanide, nitriles, isonitriles, cyanogens, allenes, azides, etc. using ATP'4. The nitriles are converted to hydrocarbons, releasing ammonia. However, it is deactivated in the presence of oxygen [Eq.(4) ] .
R-CN Nitrile
Nitrogenase
---�. R-CH, + N H, + ATP Hydrocarbon
Enzymology of Nitrile Metabolism
. . . (4)
The enzymology of microbial n itrile metabolism is now well understood. The main enzymes that take part in the nitrile metabolism are described below:
NitriLases
Nitrilase, discovered barley about 40 years ago, i s the first nitrile metabol izing enzyme that converted indole-3-acetonitrile to indole-3-acetic acid, a plant growth hormone (an auxin) ' ) . Later, a number of microorganisms possessing nitrilase activity have been isolated with the capability to metabolize several natural and synthetic nitriles l . l s . Based on their substrate specificity, microbial nitrilases are of three types 1 5 :
Aromatic Nitri/ases - These preferentially hydrolyze aromatic or heterocyclic nitriles directly to the corresponding acid and ammon ia . M icrobial aromatic n itrilases have been purified and characterized from Pseudomonas Sp. 16. 1 7, Nocardia spp. NCIB 1 1 2 1 5 , 1 1 2 16, and Fusarium soLani ' K , which catabolized ricinine, benzonitrile and p-hydroxy benzonitrile, respectively. In Arthrobacter sp. J- l two types of n itrilases which specifically degrade benzonitrile and p-tolunitrile, have been characterized l 9. In Rhodococcus rhodochrous J 1 cells, high levels (up to 35% of the soluble protein) of aromatic nitrilase is induced by isovaleronitrile2o.2 1 .
Aliphatic Nitrilases - These nitrilases preferential ly catalyze hydrolysis of aliphatic nitriles directly to acid plus ammonia. This enzyme, first discovered in R. rhodochrous K22, i s a l so s t rong ly i nduced by isovaleronitrile22.23 . Similarly, an aliphatic nitrilase induced by £-caprolactam and converting acrylonitrile to acrylic acid, i s described in R. rhodochrous J ] 2\ while another aliphatic n itrilase active on adiponi trile and
cyanovaleric acid forming cyanovaleric acid and adipic ac id , re spec t i ve ly , is iden t i fied in Comamonas testosteroni strain ct2S.
Arylacetonitrilases - These nitrilases preferentially hydrolyze arylacetonitriles. This type of n itrilase, found in A Lca ligenes faecalis JM326. 27 , i s i nduced by isovaleronitrile, does not act upon aromatic or aliphatic nitriles but hydrolyzes only arylacetonitriles such as indole-3-acetonitrile, phenylacetonitrile, thiophene-acetonitrile, etc . , of which, some are natural precursors for plant hormones, auxins . Yamamoto and coworkers2K character ized an ary l aceton i tr i l ase c apable of enantioselective hydrolysis of mandelonitrile from ALcaligenes faecalis ATCC 8750.
The physicochemical characteristics of ni trilases reported i n the literature are l isted in Table I . They are multimeric, composed of one or two types of subunits of different sizes and numbers. Nitrilases do not show the presence of any metal cofactor or prosthetic group unl ike the other nitrile-metabolizing enzymes, nitrile hydratases. All the known nitrilases are reported to be sulphydryl enzymes I 5.2 1 ,29 and the eliminat ion of the -SH groups by chemical modification led to enzyme inactivation30. The n itrilases are reported to have a catalytically essential cysteine residue at or near their active site. In fact , the nitrilase from R. rhodochrous K22 is found to have a single cysteine, CYS l70 and when this is replaced by Ala or Ser by site directed mutagenesis, the enzyme lo ses i t s act i v i ty30 . The n i tri l ase from Rhodococcus sp. ATCC 39484 is also found to have two cysteines, one of which is catalytical ly essential" . A possible mechanism for the nitri lase reaction31 ..l2 indicates a nucleophilic attack on n itrile carbon atom by a sulphydryl group of enzyme, leading to the formation of a tetrahedral intermediate via enzyme-iminothiol ester format i on . Us i ng ion-spray mass spectroscopy, Stevenson and coworkers32 were able to detect the covalent enzyme-substrate intermediate in the hydrolysis reaction with the nitrilase purified from Rhodococcus sp. ATCC 39484. Though nitri lase by definition hydrolyzes nitrile substrates into the carboxylic acids plus ammonia, it must be noted that a small amount of amide is detected when poor substrates are used, possibly due to anomalous breakdown of the reaction intermediate, such as the case with the Rhodococcus sp . ATCC 39484 aromatic n i tri lase when reacted with a poor substrate, phenylacetonitrile3 l .
928 J SCI IND RES VOL.58 DECEMBER 1 999
Table I - Properties of nitrilases isolated and characterized from different nitrile-metabol izing microorganisms
Source of nitrilase Formation Properties of nitri lasesal Ref. type
Mol. Subunits Opt. Heat Opt. pH Substrate mass and mol. temp. stability pH stabi lity specificity (kDa) mass ( 0c) ( 0c)
(kDa)
Acinetobacter Inducible 5 80 NA b) 50 60 8.0 5 . 8-8 .0 Aliphatic 1 05 sp. AK226 (NA) aromatic &
heterocyclic �. nitriles
inducible 260 6 45 NA 7.5 NA Arylaceto- 27 Alcaligenes (44) nitriles
faecalis 1M3
Arthrobacter induc ible 53 2 40 NA 8.5 NA Aromatic 1 9
sp. J I (a,30) nitriles
(�,23)
Comamonas NA NA Oligomer 25 NA 7.0 NA Adiponi tri le 25 � testosteroni strain ct (38)
Klebsiella Inducible 72 2 35 NA 9.2 NA Bromoxynil 74 ozaenae (38 . 1 )
Nocardia sp.LL I 00-2 1 inducible 530 NA NA NA NA NA Benzonitrile 1 74
sp. NCIB 1 1 2 1 5 inducible 56 1 2 1 0-50 NA 7.0- 7 .0-9.5 Aromatic 1 8 ( NA ) 9.5
Rhodococcus " rhodochrous 11 constitutiv e 78 2 45 45 7 .5 NA A liphatic & 1 34
(4 1 .5 ) arom atic n itri les
rhodochrous K22 constituti ve 650 1 5- 1 6 5 0 40 5.5 NA A l i phati c 2 3 (4 1 ) ni tri les
Fusarium constituti ve 550 M any 4 N A 6- 1 1 N A A liphatic, 1 75 oxysporum
(27) arom atic & . ; heterocyc l i c
n itriles
solani inducible 620 8 1 0-50 N A 7.8- NA A romatic 1 8 (76) 9. 1 n i tri les
a) None of the nitrilases contain any metal cofactor or prosthetic group
b) NA - Not Available.
+
RAMAKRISHNA et at. : MICROBIAL METABOLISM OF NITRILES 929
Recently, a new family of carbon-nitrogen hydrolase enzymes (nitrilase/cyanide hydratase family) has been proposed33 . Extensive aminoacid database searches show that nitrilases are significantly similar to aliphatic amidases, cyanide hydratases and �-alanine synthase - all these enzymes appear to have a cysteine residue acting as an active site nucleophile33.
Nitrile Hydratases The reaction sequence for the conversion of nitrile to
amide by a n itrile hydratase and then to carboxylic acid plus ammonia by an amidase, was first proposed by a Japanese research group about 30 years ag034. Afterwards, a number of microorganisms containing nitrile hydratase have been isolated and their enzymes have been characterized. These studies show wide ranging physicochemical properties and substrate specificities of the nitrile hydratases, which are composed of two types of dissimilar subunits (a and �) varying in number (Table 2). Most importantly, they are metalloenzymes containing iron or cobalt and are classified accordingly.
Ferric Nitrile Hydratases The electron spin resonance (ESR) studies have shown
that the n i tr i l e hydratases from Pseudomonas chloro raphis B 2 3 and Rhodococcus sp. R 3 1 2 (Brevibacterium sp. R3 1 2) are non-heme iron enzymes with low-spin ferric ion35. The ferric nitri le hydratase from Rhodococcus sp. R3 1 2 is the most thoroughly characterized enzyme using several spectroscopic techniques including ESR, extended X-ray absorption fine structure (EXAFS) and electron nuclear double resonance (ENDOR) spectroscopies. These studies revealed that the enzyme is a (a �)2 - tetramer that contains two lowspin non-heme ferric (Fe3+) ions which exist in a tetragonally distorted octahedral l igand field of three histidine imidazoles, two cystein thiolates and the hydroxide36-40. The three-dimensional analysis of crystal structure of this enzyme also showed a novel iron centre in a novel fold4 1 . Ferric nitrile hydratases from Rhodococcus spp N-77 4 and R3 1 2 are reported to have identical amino acid sequences to that of Rhodococcus sp. N_77 1 42. The aminoacid sequences of the Rhodococcus sp. N-774 and R. erythropolis JCM 6823 nitrile hydratases are approximately 95% identical, while those of the Rhodococcus sp. N-774 and P. chlororaphis B23 are approximately 60% identical. The visible and ESR spectra associated with the metal centres in the acti ve form of ferric nitrile hydratases from Rhodococcus spp R3 1 2, N-774 and P.
chlororaphis B23 are also virtually identicap5.43.44. Although differences in the substrate specificity exist among these enzymes, it is very l ikely that the major features of protein structure, the coordination of the iron etc. are the same. However, one significant difference is that the ferric n itrile hydratases from Rhodococcus spp N-77 I , N-774 and R3 1 2 show the unique characteristic of photoreactivity; they lose their activity when stored in the dark as intact cells or crude extracts and this activity can be recovered by irradiation with UV l ight. Photoreactivation of the nitrile hydratase of the strain N-77 1 takes less than 1 Ils and a hypothetical model for this reaction has been proposed on the basis of the results of Mossbauer and ESR spectra42 . Nagamune and his group43 have purified the enzyme from strain N-77 1 in its inactive form and then transformed it to its active form by light irradiation . The absorption and fluorescence spectra indicates that the chromophore involved in the photoactivation i s an i ron complex and the photoactivation site is found to be located on the asubunit, which also contains the non-heme iron centre of the enzyme45.47 . Fourier transform infrared (FTIR) spectroscopy has revealed that the inactive n i tri Ie hydratase of strain N-77 1 intrinsically possesses n itric oxide (NO) molecule bound to non-heme iron4x.49 and its photo-dissociation has been suggested to activate the enzyme, while inactivation is due to binding of exogenous NO with the iron 50.
Some of the nitrile hydratases have been found to be quinoproteins contain ing the pyrroloquinoline quinone (PQQ) as prosthetic group5 1 . This group is suggested to participate in the hydration of the n itrile group by n itrile hydratase, which is a novel function for PQQ9.52 . Earl ier only enzymes like reductases and oxidases are known to have the PQQ as prosthetic group.
Cobalt Nitrile Hydratases Rhodococcus rhodochrous J I , one of the highly stud
ied and versatile n itrile degrader, has shown the presence of two types of cobalt hydratases: i) Aliphatic nitrile hydratase. which is a high molecular mass (505 kDa) enzyme, i s heat stable (up to 50°C) and preferentially acts on aliphatic nitriles such as acrylonitrile, and i i ) Aromatic nitrile hydratase, which is a low molecular mass ( 1 01 kDa) enzyme that preferentially hydrates aromatic n itriles such as benzonitrile2X.53. Al iphatic nitrile hydratase is composed of 1 0 a- and 1 0 �-subunits and is selecti vely induced by urea, whi le aromatic n i t ri l e hydratase consists of 2a- and 2�-subunits and is selec-
930 J SCI IND RES VOL.58 DECEMBER 1 999
Table 2 - Properties of nitri le hydratases from different nitrile-metabolizing microorganisms
Source of enzyme For m ation Properties o f N i trile hydratase R e f type r
M etal & M o l . N u . of Opt. H eat Opt . p H S u bstrate PQQ") m ass subun its temp stab il i ty p H stab i l i t y spe�ific i t y
( k D a ) & mo l . ( DC ) ( D C ) mass (k Da )
Agmbacterium tumefaciens inducible Co & Fe 1 0 2 4 N A h ) N A 7 . 5 N A I n d o l e - 3 - 60 IAMB-26 1 (+ ) ( 2 5 ) ac e t o n i tri le
tum�faciens i nducib le Fe 69 4 40 5 0 7 . 0 7 - 1 0 2 - arylpro- 1 2 1
strain d3 ( N A ) (2 7 ) p i o n itrile ( E n antio-select ive)
A rthmbacter i n d u c i b l e N A 420 2 3 5 N A 7 . 0 - N A A l ip hat ic 1 7 6 t sp. J I ( N A ) ( 2 4 ) 7 . 2 n i triles
( 2 7 )
Brevibacterium constitutive Fe 8 5 3 -4 25 20 7 . 8 6.5- 8 .5 A l i p h atic 1 7 7
sp. R 3 1 2') (+ ) ( a , 2 6 ) ni tr i les ( P ,27 . 5 )
sp. ACV2 consti tut ive Fe 80 2 3 5 N A 6.0 NA A l ip hati� 1 5 0
(+) ( 2 6 ) ni triles mutant of R3 1 2 (27.5)
Corynebacterium constitutive Fe 6 1 .4 2 N A N A 8 . 0 - N A A liphat ic 1 7 8 sp. C5 (+ ) 8 . 5 d i n i triles
Pseudomonas Inducible Fe 1 00 4 20 20 7 . 5 6.0 - 7 . 5 A l iphatic 1 7 9
ch/ororaphis B23 ( + ) (a,25 ) n itr i les
( P ,25 ) �
Pseudonocardia Inducible C o N A N A 60 60 N A N A A cryl o - 8 2 thermophila JCM3095 ( N A ) ( 2 9 ) nitrile
( 32 ) RhlldocoCCllS
r/lOdochrotis JI Low mol. mass Inducible Co 1 0 1 1 8 -20 40 N A 8 . 8 N A Preference Enzyme (+) (a,26) Arom atic
(P ,29) n i triles 5 0
High mol. Inducible C o 5 0 5 4-5 3 5 -40 5 0 6 . 5 6.0- 8 . 5 A liphatic mass enzyme A (+) (a,26) n i triles
( P , 2 9 ) sp. Inducible N A 5 2 2 N A N A N A N A A l iph atic 1 8 0
( N A ) ( 26 ) n i tr i les ( 2 3 )
sp. 7 Inducible N A 2 7 8 4 5 2 5 -4 5 7 . 0 5 .0-9.0 A l ip h a t i c & 1 8 1 ( N A ) ( 26 ) arom atic
( 3 2 ) n i tri l es
sp. N -77 1 Con stitutive Fe 60 2 30 0-35 7 . 8 6 . 0-8 .0 A l iphatic 4 2 ( +) (a,27 . S ) n i triles
( P , 2 8 ) Photores-
sp. N-774 p o n s i v e
Const i tu t ive Fe 70 2 < 30 N A 7 . 7 N A A l iph atic 1 8 2 ( + ) (a,2 8 . 5 ) n itri l es
( P , 29) Photores-p o n s i v e
Myrotheciwll verrucaria I n d u c i b l e Zn 1 7 0 6 5 5 N A 7.7 N A C yanam i d e 6 1 (NA ) ( 2 7 . 7 )
a ) PQQ - Pyrroloquinoline quinone prosthetic group (+ , presence)
b) NA - Not Availabl e , c ) same as RhodococclIs sp . R3 1 2
RAMAKRISHNA et at. : MICROBIAL METABOLISM OF NITRILES 93 1
lively induced by cyclohexanecarboxamide2XS1.54 . Approximately 40% of amino; lc id �;eqll �nces hctween th� two R. rhodochrous J I n itri le hydr;ltases ilnd that from Rhodococcus sp. N-774 are ident ical" . Recen t ly, the al i phatic nitrile hydratase has been shown to con tai n a low spin, non-corrin cobal t (Co '+) ion with oct ahedral S and N(O) l i gand fi eld'(' . In terest i ng ly, the pre- edge and EXAFS spectra of both cobal t and i ron n i t ri le hydratases have been found to be simi lar. suggest ing the same l igand environment of metal ions in both the enzymes,7
A stereoselecti ve nitri Ie hydratase from Pseudomo
nas putida NRRL l 8668'x that hydrolyzes (R,S )-2-( 4-chlorophenyl)-3-methylbutyronitrile to the correspond-
t- ing (S)-amide has been purified and characterized for the first time. This stereo-selective enzyme is found to have a- and �-subunits, exists as a� and (a�)l forms and contains a non-corrin low-spin cobalt (C03+) ion in a tetragonally-distorted octahedral ligand field)') . The three dimensional structure of this enzyme appears to be similar to R. rhodochrous J I and Rhodococclls sp. R3 1 2 hydratases59. However, the cobal t enzymes from R. rhodochrous J I and P. putida have threonine in their active site whereas the ferric enzymes from Rhodococcus
-<II sp. N-774 and P. chlororaphis B23 have serine5'J . The difference in the metal cofactor may be attributed to this difference in the active site aminoacid residue54.
A recent reaction model for nitrile hydratase54 shows that the catalysis proceeds without direct coordination of the substrate to the metal ion, where the metal ion activates a water molecule by acting as a Lewis acid and subsequently either the nitrile substrate approaches a metal-bound hydroxide ion that acts as a nucIeophile attacking the n itri le carbon or a metal bound hydroxide ion activates a water molecule, whieh can attack the n i trile carbon54. After both these reactions, the nitrile gets converted to an imidate intermediate which finally gives rise to amide.
A novel nitrile hydratase having both cobalt and ferric ions, which is involved in the biosynthesis of plant hormone, indole-3-acetic acid is found in Agrobacterium tumefaciens IAMB-26 1 60 . Another new hydratase having six identical subunits (27 .7 kDa) with zinc as cofactor, specifically degrading the herbicide, cyanamide to form urea ha s been reported from the fungus , Myrothecium verrucaria61 • The structural analysis of these enzymes may provide a better understanding of the metal functions in the nitrile metabol izing organisms.
Amidases A number of am idases ac t i ve ly partic ipating in the
hydrolysis or amides, and a l ways found l inked with nit ri le hydratases , have bee n puri fied and characterized . They exh ib i t d i f'ferent phy s i coc hemica l c h aracterest ics (Tab le 3 ) w i th a d i verse substrate spec i f ic i ty. Unl ike hydratases, the associat ion or am idases with metals such as cobalt and iro n has been reported only in organ isms l i ke Klebsiella pllellmoniae and RhodococclI.1 Sp.()2!,' . The enantioselect ive amidase characterized from Pseudomo
nas ch/ororaph is B 2 � has no as soc i ated metalM. Rhodococcus sp.R3 1 2 is reported to have a number of specific amidases: an a-amino amidase which hydrolyzes only L-a-amino amides to the corresponding acids()5, a wide-spectrum amidase hydrolyzing many al iphat ic amides!>" an enantioselec t i ve amidase hydrolyzing ary loxy propionamides6!J , a novel amidase ca l led adipamidase hydrolyzing dinitri les(17 and several enzymes specific for urea, formamide, L-glutamine, and n icot inamide!>7 . The wide- spectrum amidase from Rhodococcus sp. R3 1 26x is very simi lar to the amidase of Pseudomonas aeruginosa69• Another enantiomer select ive amidase i s descr ibed i n a newly i so lated Rhodococcus s p . , wh i ch is s i m i lar to that i n Rhodococcus sp. R3 1 270. I n R . rhodochrous J I two types of amidases differing in substrate specificity have been reported7 1 . Based on studies with inhibitors the amidases have also been found to be sulphydryl enzymes71. However, no active aminoacid residue has been identified in any of them. Only recently, the real active site residues of R. rhodochrous J I amidase have been identified as Asp ,,! , and Ser I 9" rather than the general ly accepted Cys residue72. Interestingly, besides hydrolyzing amides, different amidases exhibit acyl transfer activity in the presence of hydroxylamine. This reaction has been recently described for the amidases of Rhodococcus sp. R3 1 273 , which leads to the formation of a wide range of hydroxamic ac ids.
Genetics of Nitrile Metabolism The first among the n itrilase genes to be cloned was
the Klebsiella ozaenae plasmid born gene bxn, encoding a nitrilase that degrades bromoxynil 74 . Later, this gene was used to develop transgenic tobacco or tomato plants resistant to the herbicides 75 . The nitrilase genes (nitA) from Rhodococcus rhodochrous J I , K22 and ALcaligenes faecalis JM3 have been c loned and sequenced30.76.77 and show significant similarity to bxn gene. Another gene encoding an aliphatic n itrilase, active on
932 ] SCI INO RES VOL.58 DECEMBER 1 999
Table 3 - Properties of amidases purified and characterized from different nitrile-metabolizing microorganisms
Source of enzyme
A r,hrobacter sp. J l
Brevibacterium sp. R 3 1 2h)
sp. R 3 1 2h)
Klebsiella Jineul1loniae NCTR I
Pseudomonas A eruginosa
Formation type
inducible
i nducible
i nducible
Metal
NA
NA
inducible Co & Fe
i nducible NA
Mol. mass (kDa)
320
1 80
1 20
62
200
chLororaphis 823 i nducible no metal 1 05
sp. GDI 2 1 1
Rhodococcl/S
sr·
sr·
i nducib le NA
NA NA
constitutive Fe
43
1 1 8
360
a) NA - Not available ; b) same as Rhodococcus sp. R3 1 2
N o . of subunits & mol. mass (kOa)
8 (39)
4 (43)
2 (4.6)
monomer
8 (38)
2 (54)
NA (26)
2 ( 48 .5 )
NA (44.5)
adiponitri l e and cyanovaleric acid, i s c loned from Comamonas testosteron i ct25.
The genetics of nitrile metabolism to a large extent, has been studied in the industrially important microbial strains having nitrile hydratase and amidase system. M/s Nitto Chemical Industry have patented some of the genes encoding the nitrile metabolizing enzymes from p. chlororaphis B23 and R. rhodochrous J 1 7X.7<J. In all these strains, the amidase genes have been found adjacent to nitri le f.;,dratase genes in the same operon, except for aliphatic ni trile hydratase gen': cluster of R.
Properties of amidase
Opt. temp. ( 0C)
55
NA
NA
65
N A
Heat Opt. stabi l i ty p H
(uC)
30-45 7.0-9.0
N A N A
N A N A
30-65 7.0
N A N A
p H stabi l i ty
7.0
N A
N A
5 . 0-8 .5
N A
S ubstrate specificity
A l i phatic amides
Ref.
1 83
A l i phatic 1 84 amides
(wide spectrum)
Aryloxy 66
propionamides (enantio-selective)
A l i phatic amides
A l i phatic amides
63
1 85
50 25-50 7.0-8.6 5 .9-9.9 Al iphatic & 64
NA NA NA
NA NA NA
40 NA 8.5
NA
aromatic ami des
Aromatic amides
1 8 6
NA Aryl propionamide 70
NA Al iphatic ami des 62
rhodochrous J I which does not contain amidase gene. This is the reason why this organism is superior for the production of acrylamide. Overexpression ( 1 .7 times) of R. rhodochrous J I aliphatic nitrile hydratase gene has been achieved using a recombinant Rhodococcl/S host/vector system, in which the presence of amide compounds is essential for the assembly of active multi mer nitrile hydrataseRo.
The structural genes coding for the (X- and �-subunits of the stereoselecti ve cobalt n itri l e hydratase from Pseudomonas putida NRRL- 1 8668 have been c loned
.J..
RAMAKRISHNA et at. : MICROBIAL METABOLISM OF NITRILES 933
and sequenced59 . A 6-fold over-production of the active stereoselective enzyme has been obtained by the co-expression of a novel downstream gene encoding a protein (P1 4K) which appears to be a part of an operon that includes the structural genes of (X- and �-subunits of the nitrile hydratase and other potential coding sequencesX I • A nitrile hydratase gene from a moderate thermophile, Pseudonocardia thermophila JCM3095 has been cloned and sequenced for the first timex2. The nitrile hydratase of this organism has (X- and �-subunits, exhibits high optimum temperature (60°C), thermostabi lity and requires cobalt for high activity. The nucleotide sequences of this hydratase gene show high homology with the hydratase gene of a mesophilic bacterium, Rhodococcus Sp.70.X2 . Another ni trile hydratase gene cah, has been cloned from the fungus Myrothecium verruca ria, which degrades the herbicide, cyanamide to urea. These fungal genes have no sequence similarity with the hydratase genes of Rhodococcus sp . N-774, Pseudomonas chlororaphis B23, R. rhodochrous J I and Rhodococcus Sp.ol and have been used to develop transgenic tobacco plants resistant to high concentration of cyanamidex3.
The advances in the biosynthetic regulation, genetics and better understanding of the structure and reaction mechanism of the n itrile-metabolizing enzymes would not only lead to improved properties such as high activity, high tolerance to substrate and product and thermostability, etc . of the biocatalysts used in commercial processes, but also enable the development of novel nitrilehydrolyzing enzymes with stereo-, regio- and substrate specif ic i ty for chemica l syntheses or for bioremediation54•
Biotechnological Potential and Applications
The nitrile compounds can be easily prepared by a number of chemical methods and are commonly used as intermediates in the synthesis of several commercially important amides and/or acids X4. For these syntheses, the nitriles are hydrolyzed using traditional chemical methods that have several such drawbacks as : a) reactions need be carried out in strongly acidic or basic media, b) h igher reaction temperature, and c) formation of by-products such as toxic HCN or large amount of salt, etc. Compared with the chemical (non-enzymatic) route, the biotechnological route has the following advantages9•X4 : a) less severe (mild) reaction conditions, b) substrate and product specificity, c) formation of products with a very h igh purity, d) potential for conducting chemo-, stereo- and regio-selective transformations that
are difficult to achieve through non-enzymatic route, and e) non-polluting.
It has been shown that ni trilases, hydratases and amidases hydrolyze a number of structurally diverse nitriles. Several commercially important organic compounds such as p-aminobenzo ic ac id , benzamide , 2 ,6-difluorobenzamide, n icot inamide, i sonicotinamide, pyrazin amide , pyrazino i c ac id , qu i no l i nami de, thiophenamide, etc . have been prepared from the corresponding nitri les using the cells of R. rhodochroLis J I containing both nitri lase ' 5.52 and nitrile hydratasex,. The production of acids and amides using R. rhodochrolls J I enzymes has been patented by M/s Nitto Chemical IndustryXo.x7. Camitine has been prepared from the corresponding nitrile by another patented process using the nitrilase of Corynebacterium sp.xx. Vaughan et af. MY converted 3-cyanopyridine into nicotinic acid by n itrilase containing cells of Nocardia rhodochrous induced by benzonitrile, while Eyal and CharlesYO prepared nicotinamide from cyanopyridine by the whole cell n itri le hydratase. The Novo Industri NS of Denmark has developed two immobilized whole cell biocatalysts, SP36 1 and SP409 containing both nitri le hydratase and amidase but lacking nitrilase, for hydrolyzing nitriles. In fact, the immobilized biocatalysts have the advantages that they are very simple to use and can be easily recovered after the reaction for reuse. Using the biocatalyst SP409, Klempier et alYI and deRaadt et al.Y2 achieved mild and selective hydrolysis even in the presence of acid- or basesensitive groups contained in a broad range of aliphatic, alicyclic, heterocyclic and carbohydrate type nitriles under neutral conditions. Similarly, the biocatalyst is also found to be very effi c i en t and conven ien t for chemoselective and mild hydrolysis of a number of heterocyclic n itriles to either amides or carboxylic acids. Bulky substituents, insufficient solubil ity and possibly inhibition phenomena are some of the limitations observed in this studyY3. Recently, the biotransformation of nitriles into amides and/or acids using R. rhodochrous AJ270 was reportedY4• The range of substrates together with h igh product yields and selec t iv i t ies , makes Rhodococcus as one of the most valuable microbial systems for nitrile hydrolysis. This study has also defined useful limitations for the acceptabi lity of substrates for hydrolysisY4.
The hydrolysis of dinitriles by the nitrile-metabolizing enzymes presents an interesting means of synthesizing a wide range of organic compounds not amenable
934 J SCI IND RES VOL.58 DECEMBER 1 999
/ CN R
' CN
d initrile
hydratase
cyanoamide
amidase / COOH R
\ CN
cyano carboxyl ic acid
....
.
....
.
.
.
.
chemical reaction
.
.
.
.........
. ........
..
.
.............
.
..
1 hydratase hydratase
.� / CONH2 R
" CONH2
diamide
..•.
chemical reaction
.....
amidase
....... ...
.......
..•.
.-
-
.
.
�
/ COOH R
' CONHz
amido carboxylic acid
� amidase
/ COOH R
, COOH
dicarboxylic acid
Figure I - Formation of di fferent products from dinitriles through enzymatic and chemical route
for preparation i n h igh y ields by conventional chemical syntheses�·�5. Scient ists from Novo Industri AIS , Den
mark, found that a d in i tr i le could be converted i nto the corresponding amido-carboxyl ic ac id by applyi ng, in se
quence, a monoacid generating stra in and an amidase
free preparation from a diac id generati ng strain . About
five types of products coul d be prepared in h igh yie lds by apply ing these enzymes as shown in Figure I , whi le
only two products, a d iam i de or a d iacid are possible with chemical synthesis9.�5. Novo Scientists are able to synthesize precursors for ny lon-6 and nylon-6,6 poly
mers, adipic acid and caprolactam, from adiponi tri le by combini ng both chemical and enzymatic conversions')5.
The al i phat ic n i tri l ase from R. rhodochroll.\' K22 catalyzes the conversion of various a l iphatic n itri les including dini tri les l ike g lutaroni tri le which i s converted to 4-
cyano butyric acid (Figure 2a). Other d in i tri les such as b u t a d i e n e n i t r i l e , fu maron i t r i l e , ( F i g u re 2 b - c ) malononi tri le, succinonitri le, adiponi tri le, p imelonitrile, etc. are also attacked by K22 n itri l ase, forming the COITesponding cyano carboxyl ic acids%. The aromatic n itri lase
from R. rhodochrous J I is capable of conversion of
terephthalon itr i l e and i sophtha lon i tr i l e to 4- and 3-cyanobenzoic acids (Figure 2d-e) without formation of any d i ac i d�7, w h i le the b i ocata ly s t SP36 1 con verts i sophthalonitri le to 3-cyanobenzoic acid , from which a d iacid can also be prepared by esterification of the car
boxyl ic group fol lowed by re-exposure to the biocata
lyst for the hydrolys is of the second n itri l e group (Fig
ure 2e)X4.9x. DuPont company patented an enzymatic process for the b iocatalytic convers ion of azobi sn itri les to cyanoamides or diamides us ing n itri l e hydratases of Pseudomonas, Rhodococcus, or Brevibacleriul11')�.
Another very interesting aspect of n itri l e bioconversions is the capab i l i ty of these enzymes to carry out stereoselect ive transformations. First among the earl iest reported stereose lect i ve n itri le conversion is the product ion of optical ly act ive L-a-hydroxy acids from racemic a-hydroxy n itri les by Torulopsis candid({ I IX I . S i m i l arly, Rhodococcus sp. R3 1 2 has been u sed to produce opti
cal l y act ive L- or D-amino acids from racemic a-amino n i tri les 1 1 1 1
. Macadam and Knowles 1 1 12 showed the conversion of a-ami nopropioni tr i le to L-al an ine us ing immobi l ized cel l s of Acinetohacter sp. APN. Hydrolys is
-t
.....
RAMAKRISHNA ef al. : MICROBIAL METABOLISM OF NITRILES 935
Ca) Rhodococcus rhodochrous K22
glutaronitrile
(b)
NC� CN
1 ,3-butadiene nitrile
(e)
� /eN NC"'- -...:/
fumaronitrile
(d)
nitrilase or SP 361
K 22 nitrilase or SP 361
K 22 nitrilase
4-cy3nobutyric acid
NC, /='\ \=.I \COOH
5-cyanopenta 2 ,4-dienoic acid
NC�COOH 3-cyanofumaric acid
6 Rhodococcus rhodochrous J 1
• nitrilase CN
terephthalonitrile 4-cyanobenzoic acid
(e)
CN Rhodococcus COOH COOM. Q rhodochrous J 1 C\N CH2N, and Q � � CN or SP 361 SP 361 COOH
isophthalonitrile 3-cyanobenzoic acid isophthalic acid monoester
Figure 2 - Conversion of aliphatic dinitriles, (al glutaronitrile, (b) I ,3-butadiene nitrile and (cl fumaronitrile by Rhodococcus rhodochrolls K22 nitrilase and the biocatalyst SP3 6 1 and aromatic dinitri lcs, (d) terephthalonitrile, and (el isophthalonitrilc by Rlwdococcus rhodochrolls J I nitrilase and SP 36 1
of (R,S)-( + )-ibuprofen nitri le leading to the formation of the non-steroidal anti-inflammatory drug, (S)-( +)ibuprofen (Figure 3a) was achieved by the nitrilase of Acinetobacter sp. AK226 with an enantiomer excess (e.e) of above 95% for the (S)-( + )-product acid and the recovered (R)-( + )-nitrile'o:1. (R)-( -)-Mandelic acid, a commercially important bui lding block for preparation of some semi-synthetic cephalosporins, is prepared from racemic mandelonitrile (Figure 3b) by an enantioselective nitrilase from Alcaligenes faecalis ATCC 8750104 10' . In a strain of Pseudomonas sp. enantioselective nitrilase catalyzes hydrolysis of racemic O-acetylmandelonitrile (Figure 3c) to (R)-(-)-acetylmandelic acid ,06. Synthesis of optically active aminoacids (L-form, except for alan ine) from a-aminonitriles by a n i trilase system of R. rhodochrous PA-34 has been reported2Y• Gradley and
Knowles l()7 showed the enantioselective potential of R. rhodochrous NCIMB 1 1 2 1 6 nitrilase using a range of chiral nitriles including (R,S)-2-methylhexanitrile, which is converted to (S)-( + )-2-methyl hexanoic acid.
With the aid of enzyme system of R. butanica ATCC 2 1 1 97, kinetic resolution of a-arylpropionitriles has been shown successful ly for the first time, resulting in the formation of optically pure (R)-amides and (S)-carboxyl ic acids (Figure 4a), some of which are important as an t i - i n fl ammatory drugs l OX . Opt i c a l l y pure 2 -
arylhydroxypropionic acids (Figure 4b) which have high herbicidal activity have been prepared from corresponding racemic nitriles using Brevibacterium imperiale CBS 49874 cell s with nitrile hydratase and amidase lOY. During this study, it was observed that the hydratase converted the racemic n itrile substrate by a fast nonspe-
936 J SCI IND RES VOL.58 DECEMBER 1 999
(a) ,. �COOH (S)-(+)-ibuprofen
Acinetobacter sp, AK226 � +
(R,S)-ibuprofen nitrile [2-(4-isobutyl phenyl) propionitrile
S-selective nitrilas�e Me
I � CN �
(R)-(-)-ibuprofen nitrile
(b) OH Alcaligenes faecalis A TCC 8750 OH OH �CN . • M"'CN · +
R-selective nitrilase U � ���H (R,S)-mandelonitrile (S)-mandelonitrile
(c)
(R)-(-)-mandelic acid
/Ac o
Pseudomonas sp. �COOH (R,S)-O-acetyl mandelonitrile
R-selective nitrilase (R)-(-)- acetyl mandelic acid
Figure 3 - Preparation of (a) (R)-ibuprofen, (b) (R)-( -)-mandelic acid, and (c) (R)-( - )-acetyl mandelic acid, using stereo-specific nitrilase enzyme systems
cific hydrolysis while the amidase catalyzed a slow stereoselective conversion into the (R)-acids. The (S)amides were also recovered with h igh optical purity. The pharmaceutically active, non-steroidal anti-inflammatory substances, 2-arylpropionic acid such as (S)-( + )-2-phenyl propionic acid (e.e, 99.4%) was prepared by the combined action of a nitrile hydratase and stereoselective amidase system of Rhodococcus equi TG238 from (R,S)-2-phenylpropionitrile (Figure 4c) and the (R)-( -)-2-phenyl propionamide (e.e, 99%) is also isolated "0. Similarly, the enant ioselect ive hydrolysis of racemic 2-arylpropionitriles suC;;h as naproxen nitrile, ketoprofen nitrile, etc . was accomplished using the nitrile hydratase and amidase contain ing organisms, Agrobacterium tumefaciens d3 1 1 1 , Rhodococcus sp. C3II, R. erythropolis MPSO1 12. I I J and R. equi A4 "4, as shown in Figure Sa-d. The capab i l i ty of Rhodococcus sp . • C3I I and R. erythropolis MPSO for the regio- and stereo-selecti ve hydrolysis of various aliphatic and aromatic n itriles and acid amides has been elucidated in detail recently l " . The nitri le hydratase and amidase system of a Pseudomonas
sp. carried out enantioselective hydrolysis of (R,S)-2-i sopropyl-( 4-chlorophenyl)-acetoni trile to the corresponding S-acid"6. Pseudomonas sp. BC- 1 8 having nitrile hydratase and amidase enzyme system accomplished enantioselective hydrolysis of (R,S)-3-phenyllactonitrile to (S)-( -)-3-phenyllactic acid as shown in Figure 6a 1 17 . This compound is a versatile precursor for the synthesis of several pharmacophores such as rennin inhibitors, protease inhibitors and anti-human immunodeficiency virus reagents l l 7 .
In the case of stereoselective hydrolysis reactions of nitrile hydratase and amidase system, it is general ly observed that the stereoselectivity resides primarily in the amidase, not in the hydratase"o. 1 I 6. However, some of the recent studies have revealed that the hydratase can also carry out stereoselective transformations. For example, Blakely and coworkers" x have reported the formation of (R)-( + )-2-phenyl butyramidc with an e.e. of 83% from the corresponding n itri le by Rhodococcus sp. AJ270. During this transformation, the (R)-amide intermediate could not be hydrolyzed further, as it is not a
t
RAMAKRISHNA et al. : MICROBIAL METABOLISM OF NITRILES
(a)
R R R �CN RJ() hydratase
• �ON�2 . S-specific �OOH
Rvll� � ----II ... R1� (R,S)-aryl substituted
alkane nitrile
(b)
R'
(R)-amide
R = Me, Et R' = iso-bu, CI, OMe
Brevibacterium imperiale
... nonspecific hydratase
(R,S)-2-aryloxy n itrile
(S)-2-aryloxy amide
(e)
Rhodococcus equi TG 328
nonspecific hydratase
(R,S)-2-phenyl propionitrile
(R)-(-)-2-phenyl propionamide
amidase
(S)-acid
R' �:&OyCONH' (R,S)-2-aryloxy amide
I R-selective t amidase
(R)-2-aryloxy carboxylic acid
(R,S)-2-phenyl propionamide � S�I""'e a"",,,, �H3 VeOOH (S)-(+)-2-phenyl propionic acid
Figure 4(a) - General reaction showing the transformation of racemic aryl substituted alkane nitriles to optically pure Ramides and S-acids by Rhodococcus butallica or SP36 1
Figure 4(b) - Preparation of 2-aryloxy carboxylic acids by nonspecific hydratase and R-specific amidase system of Brevibacterium imperiale
Figure 4(c) - Bioconversion of racemic phenyl propionitri le to (R)-( -)-amide and (S)-( +)- acid by the nitrile hydratase and S-selective amidase system of Rhodococcus equi TG328
937
938 J SCI IND RES VOL.58 DECEMBER 1 999
(a) �H3 ofCN Agrobacterium tumefaciens d3
S'specific hydratase
�eONH2 (R.S)-2-phenyl propionitrile (S)-2-phenyl propionamide
� S-specific amidase
�H3 VeOOH (S)-2-phenyl propionic acid
(b)
Rhodococcus equi A4
hydratase + amidase
�eN RAJ . (R ,S)-aryl propionitrile (S)-aryl propionic acid (R)-aryl propionitrile
(c) CH �' Rhodococcus sp.
I '" '<::: CN C311 or MP 50 h h • H,CO
S-specific hydratase
(R,S)-naproxen nitrile [2-(6-methoxy 2-naphthy l propionitrile]
(d) CH, � Rhodococcus I '<::: I '"
. CN erythropolis MP50
h h -------i.�
(R,S)-ketoprofen nitrile [2-(3-benzyl phenyl) propionitrile]
S-specific hydratase
S-naproxen amide � S-specific amidase
�H3 �COOH H3CO� (S)-naproxen (acid)
(S)-ketoprofen amide
+ S-specific amidase
�H, o _ �COOH
V V (S)-ketoprofen (acid)
Figure 5 - Stereospecific biotransformation carried out by nitrile hydratase and amidase system leading to the formation of (a) (S)- 2-pheny[ propionic acid, (b) (S)-aryl propionic acid, (c) naproxen, and (d) ketoprofen
-
RAMAKRISHNA et al. : MICROBIAL METABOLISM OF NITRILES 939
(a)
eN eOOH � Pseudomonas sp. BC-1 8 � V OH . ---------i.� V &H hydratase + amidase
(R,S)-3-phenyl lactonitrile (S)-(-)-3-phenyl lactic acid
(b)
""I X eN Pseudomonas putida
eN '
S-selective hydratase (R,S)-2-(4-chlorophenyl)-3-methyl
butyronitrile (S)-2-(4-<:hlorophenyl)-methyl
butyramide
Figure 6 - Stereo-specitic hydrolysis of (a) phenyllactonitrile, and (b) 2-(4-chlorophenyl)-3-methyl butyronitrile
substrate for the amidase of this bacterium. This observation led to the recognition of the stereoselective nature of the nitrile hydratase activity l lx. S imi larly, Fal lon et al. 5x also reported the S-selective nitrile hydratase of p. putida NRRL l 8668, capable of hydrolyzing 2-(4-chlorophenyl)-3-methyl butyronitrile to the corresponding (S)-amide (Figure 6b). The S-selective hydratase from A. tumefaciens d3 involved in the hydration of 2-aryl propionitriles has been purified and characterized very recently I 1 9 . In fact, this organism also harbours Sspecific amidase I I I . A detai led i nvestigation of the stereoselective hydrolysis of both racemic and prochiral n i tr i les has been made w i th Novo ' s b i ocata lys t S P3 6 1 XOX. 1 211 . 1 2 1 . A seri es of proc h i ral 3 -hydroxyglutaronitrile derivatives have been hydrolyzed u s i ng t h i s ca ta lys t to t he correspond ing ( S )cyanocarboxylic acids (Figure 7a) with e.e ranging from 22 to 84%1211. With the same biocatalyst, Beard and coworkers l2 1 also carried out stereoselective hydrolysis of several racemic and prochiral nitrile substrates . 2-Alkylarylacetonitriles were hydrolyzed to (S)-acids and (R)amides whereas the c lo se ly rel ated (±) -2 - ( 4-isobutylphenyl)-propionitri le gave the (R)-acid. In some of these conversions the recovered nitrile was also found to be optically active. Regioselective hydrolysis of aromatic dinitriles also has been demonstrated using SP36 1 with fluoro dinitriles and their methyl or amino substituted compounds as substratesK4 • The R. rhodochrous IFO 1 5564 mediated stereo-selective hydrolysis of ali-
cyclic nitriles and amides and its use for kinetic resolut i on and asymmetrizat ion h as been described 1 22 . Rhodococcus sp. R3 l 2 has been reported to have the capabil i ty to transform various prochiral dinitriles to enantiomerically pure (S)-cyanoacids 1 23 . For example, the lactone moiety of mevinic acids, which are pharmaceutically important as effective hypocholestrolemic agents, can be conveniently synthesized by combination of chemical and enzymatic reactions (Figure 7b) involving the hydratase and amidase system of the strain R3 l 2 or the biocatalyst SP36 1 from the corresponding prochiral dinitri le124 .
A new b ioc ata lys t , Ochrobactru111 a n th ropi NCIMB4032 I , which has a broad-spectrum L-specific amidase activity hydrolyzing a large variety of amides ranging from a-H-a-amino-, a-alkyl, a-amino, N-hydroxy-a-amino acid amides to a-hydroxy-acid ami des has been reported 1 25 . Interestingly, the presence of an enantioselective amidase converting several racemic aromatic amides such as 2-phenylpropionamide etc . to the corresponding optical ly pure carboxylic acids has been shown in P. chlororaphis B2364. 5-Hydroxy- pyrazine-2-carboxylic acid, a versati le building block for the synthesis of new antituberculous agents has been prepared by whole cell biotransformation from 2-cyanopyrazine via pyrazine carboxylic acid (Fig. 7c) using the nitrilase and regioselective dehydrogenase enzymes present in the bacterium Agrobacterium sp. DSM 6336 126.
940 J SCI IND RES VOL.58 DECEMBER 1 999
(a) OR SP 361
�R NC�COOH NC�CN hydratase + amidase
Substituted 3-hydroxy glutaronitrile
(b)
(S)-cyano carboxylic acid
08z
(j S-specific hydratase + amidase
08z
Brevibacterium sp. R312 or
SP 361
o A Chemical Synthes: + 0 I I k " " 0 HOOC CN SP 361 non ,- ,' 0 NC CN
3-(benzyloxy) g lutaronitrile
(e)
(S)-3-cyano acid
specific hydratase + amidase
lactone moiety of mevinic acids
�NyCN __ A
_
9/1
_
0b
_
a
_
c
_
te
_
riu
_
m
--l
s
.�
p .
�N) nitrilase . fNYCOOH regiospecific
. fNYCOOH �N) dehydrogenase HO�N)
2-cyanopyrazine pyrazine-2-carboxylic acid
5-hydroxy pyrazine-2-carboxylic acid
Figure 7 - Enantioselective syntheses of (a) S-cyanoacids, and (b) lactone moiety of mevinic acids using nitri le hydrolyzing enzymes and chemical synthesis, and (c) Synthesis of 5-hydroxy pyrazine-2-carboxylic acid by nonspecific hydrolysis followed by regio-specific hydroxylation of 2-cyanopyrazine
Enzymatic nitri le hydrolysis in low water systems using nitri le hydratase from Rhodococcus sp. DSM 1 1 397 and nitrilase from Pseudomonas sp. DSM 1 1 387 has been studied by Layh and Wil lets 1 27 . This is a very fascinating and emerging area in which information is highly essential . In the patent li terature also several stereoselective whole-cel l biocatalysts for acid production from nitriles have been described 'O I . 1 2x . i 32, Thus, a great commercial potential is envisaged for the nitrilemetabol izing enzymes as catalysts for converting nitriles to higher value amides and/or acids on an industrial scale. A few of the potential applications of nitrile biotransformations are discussed below.
Acrylamide Acrylamide monomer is an important commodity
chemical used to make synthetic fibres, flocculent agents and polymers for petroleum recovery, with a world-wide
demand of 200,000 tpa. It is conventionally synthesized by the hydrolysis of acrylonitrile using the catalyst, raney copper at about 1 00°C. The production of this commodity chemical is desirable under mild conditions as the chemical method has several draw-backs like the use of high temperature, etc.52,)3 . Nitto Chemical Industry, Japan, started the industrial production of acrylamide through a biotechnological route in 1 985 using Corynebacterium sp. N-774 (Rhodococcus sp. N-774), Later, the second generation acrylamide process using a superior bacterium, P chlororaphis B23 with a production capacity of 6,000 tpa has been establ ished in 1 988. The productivity of this process has been further enhanced in 1 99 1 by another more powerfu l b iocatalyst , R. rhodochrous J I in the third generation process, The cobalt nitrile hydratase of this organism is a robust and superior enzyme for acrylamide production as it is more heat stable, up to 50°C and tolerates high concentrations
••
RAMAKRISHNA et at. : MICROBIAL METABOLISM OF NITRILES 94 1
of not only acrylonitrile but also the product, acrylamide up to the concentration of 50% (w/v). As a result of the high productivity of the cel ls, the capacity could be increased to 30,000 tpa without any major change in the plan t53. A comparison of the three generations of biocatalysts used for Nitto's acrylamide process clearly shows the superiority of R. rhodochrous J 1 in terms of specific activity, productivity and final concentration of acrylamide achievable, etc.53.K5. 1 34. Overall , the biotechnological process is much simpler and economical , the recovery ofunreacted acrylonitrile is unnecessary as the conversion is more than 99.99% and a very pure product is obtained53. The Nitto's acrylamide plant using the biocatalyst continues to be operated successful ly.
Nicotinamide, Nicotinic Acid and p-Aminobenzoic Acid
Nicotinamide is a useful v itamin and is also used as animal feed supplement. Nagasawa and coworkers 1 35 showed 1 00% molar conversion of 3-cyanopyridine to nicotinamide by R. rhodochrous 1 1 nitrile hydratase. Besides n icotinamide, other commercially important compounds such as nicotinic acid and p-aminobenzoic acid have been shown to be produced by resting cells of Nocardia sp. and R. rhodochrous 1 1 K9, 1 30, As chemical syntheses of these compounds are very complex and require harsh conditions, their production by biotechnological route that uses only mild conditions is very attractive. Recently, Lonza has announced that a biological process based on the enzymat ic convers ion of 3 -cyanopyridine by the R. rhodochrous cells with nitrile hydratase wilI be used in a 3000 tpa nicotinamide plant in Guanzhou, South China. This technology has been licensed from Nitto Chemical Industries, Japan, and the plant is due to come on-stream very soon 1 37 •
Acrylic Acid and Methacrylic Acid Acrylic acid and methacrylic acid are commercially
important starting materials for the synthesis of various polymers, They are traditionally manufactured by gasphase oxidation of propylene and isobutylene in the presence of oxide catalysts at a high temperature l3X , Severe problems with the catalysts such as coking, inactivation, etc. and polymerization of the products at high temperatures are some of the draw-backs in the chemical syntheses. So for the production of these acids the use of nitrile-metabolizing organisms as biocatalysts, which require only mild conditions as opposed to traditional chemical methods, is attractive 13K. Nocardia rhodochrous
LL l OO-2 1 has been found to convert acrylonitrile to acrylic acid but is unable to metabolize the acrylic acid further9. S imilarly, R. rhodochrous 1 1 n i trilase induced by E-caprolactam is also shown to be a very powerful biocatalyst of value for the industrial scale production of acryl ic acid and methacrylic acid w ith a h igh molar conversion and without any by-product formation 1 3K. Processes for the preparation of ammonium acrylate and ammon ium methacryl ate from acry lon i t r i le or methacrylonitri1e, respectively, using R. rhodochrous nitrilase with low Km for acrylonitrile have been patented '39, '40.
Hydroxamic Acids Hydroxamic acids (HA), which form very stable che
lates with a number of metal ions, are also constituents of growth factors, food additives, antibiotics, antibiotic antagonists, tumor inhibitors, antifungal agents, cell division factors and enzyme inhibitors and are used as reagents in analytical chemistry for metal determinations73. u-Aminohydroxamic acid derivatives have medical applications, since they are potent inhibitors of several matrix metalloproteases, the zinc endopeptidase enzymes involved in the t issue remodel l ing73 , Some of the polymerizable unsaturated HA and mid-chain or longchain HA are used for wastewater treatment and nuclear technology to eliminate metal ions73, ' 4 1 . '43. The longchain HA are also efficient surfactants '44 . As the chemical methods for the manufacture of these highly useful compounds have the drawbacks of requiring many solvents, sometimes high temperatures, n itrogen atmosphere and cumbersome steps, use of biocatalysts for producing these molecules facil i tates some otherwise difficult reactions under mild conditions73, '44 . Recently, the amidases from the organism, Rhodococcus sp. R3 1 2 have been reported to have the exceptional capability of catalyzing the biosynthesis of the HA compounds under mild conditions in reaction media devoid of organic solvents 73. 1 44 . The Rhodococcus sp. R3 1 2 wide-spectrum amidase can synthesize short-chain C2-C
3 HA, while the
Rhodococcus sp. R3 1 2 adipamidase catalyzes the synthesis of C
4-CK HA and the Candida parapsilosis l ipase/
acyl transferase produces the hydrophobic long-chain HA144.
Optically Active Compounds Use of nitrile-hydrolyzing enzymes offers a potential
method for enantioselective conversion of racemic u-
942 J SCI IND RES VOL.58 DECEMBER 1 999
hydroxy or a-amino ni triles to stereospecific (0- or Lisomer) a-hydroxy or a-amino acids (or amides) under mild conditions. Using these organisms, lactic acid has been produced from lactonitrile which can be easily and economically made by reacting acetaldehyde and hydrogen cyanidel,�. Nitto Chemical Industry patented a process for microbial manufacture of optically active (0- or L-) lactic acid (e.e., 1 00%) from racemic lactonitri le by several microorganisms including Enterobacter Sp. 145. Lactic acid has the potential of becoming a very large volume commodity chemical intermediate for use as feedstock for b iodegradable polymers, oxygenated chemicals, plant growth regulators, environmentally friendly 'green ' solvents and speciality chemical intermediates l 4n. Of even greater commercial interest is the synthesis of other expensive, optically pure D- or L-acids from corresponding racemic ni triles. Rhodococcus sp. R3 1 2 has converted OL-aminonitriles to L-amino acids in 50% yield, the remainder being o-aminoamidel . Aminopropionitrile has been stereospecifically converted to L-a lan i n e by u s i ng immob i l ized ce l l s of an Acinetobacter sp. 102. Optically active aminoacids have been produced from a-aminonitriles by the cells of R. rhodochrous PA-34 having n itrilase2�. The non-steroidal, anti- inflammatory compounds such as (S)-( +)ibuprofen, naproxen and ketoprofen can be made from corresponding ni triles by enantiomer selective transformation by Acinetobacter sp. AK226, Agrobacterium tumefaciens d3, Rhodococcus sp. C3II, R. erythropolis MP50, R. equi A4, respectively l 03, 1 1 1 . l l i . A process using ultrafiltration membrane bioreactor or immobilzation on porus cellulose beads has been described for the production of (S)-( + )-ibuprofen 147, 14X . Simi larly, optically pure 2-ary lhydroxy propionic acids having herbicidal activity have been prepared from the corresponding racemic nitriles by Brevibacterium imperiale CBS49874)(�).
Adipic Acid and Caprolactam Interestingly, Novo Industri AlS, Denmark, using
n itrilase, nitrile hydratase and amidase prepared precursors of nylon-6 and nylon-6,6, adipic acid and caprolactam by converting adiponitrile into either the corresponding cyanoamides or cyanocarboxylic acids, etc . , that can be further converted to precursors by chemical synthesis�5. Another enzymatic process for adipic acid production from adiponitrile using mutants of Rhodococcus sp. R3 I 2, which have h igher adiponitrile-metabolizing capabi lity has also been reportedn7, 14�- 1 5 1 . Novo Industri AIS h as been cons ider ing the b i ocon vers i on of
adiponitrile to produce adipic acid and caprolactam on a commercial scale for nylon manufacture.
Biodegradation of Nitrile-containing Industrial Effluents
A very important aspect of biotechnological potential of nitrile metabol ism is the biodegradation of nitrile-containing industrial effluents. Manufacturing of n itriles on a large scale world-wide is usual ly associated with the formation of a large amount of toxic effluents. These effluents pose a great danger to the environment and microbial degradation is the most convenient and cost-effective technology for their detoxification.
A) Acrylonitrile Plant Wastewater Acrylon itrile (ACN) is manufactured conventional ly
by ammoxidation process where propylene is oxidized in the presence of ammonia and air (oxygen). This generates two major ACN effluent streams: I ) wastewater-I in the quench column after stripping volatile organics, designated as K01 1 (EPA hazardous waste code) wastewater, contains very high amounts of organics, cyan ides, total dissolved solids (TDS) mostly as ammonium sulphate l 52, 2) wastewater-II, the stripper column bottom after recovery of crude acetonitrile, designated as KO 1 3, is relatively dilute with lower amount of organics and cyanideJ52. The ACN wastewater typical ly contains cyanides, acrolein, acrylonitrile, acetonitri le, ammonia and other reaction products along with heavy organic material 1 53 . Since the ACN wastewater contains cyanide mostly in the form of inorganic cyanide, many chemical oxidation methods such as alkaline chlorination, etc. can be used for the removal 154 , 1 55. Due to its high toxicity, acclimation of biological systems to degrade ACN wastewater has general ly been only partially successful . Kato and Yamamural56 failed to adapt an ordinary activated sludge system to degrade even dilute concentrat ions of ACN wastewater. However, by augmentation of a nitrile-degrading Nocardia to the activated sludge, the system degraded 1 0-50 mg/L cyanide. Similarly, Fuj i i and Oshimil57 also treated the wastewater by activated sludge having Alcaligenes or Achromobacter that degrade nitriles and cyanide. Mimura and coworkers l 5x h ave reported the appl ication of Corynebacterium nitrophilus having the abi lity to degrade acetonitrile, hydrocarbons, carboxylic acids, alcohols and ketones, for biotreatment. Ramakrishna and coworkersl 5� have studied the activated carbon powder-activated sludge (PAC-AS) process for the treatment of ACN plant waste-
I
RAMAKRISHNA et al. : MICROBIAL METABOLISM OF NITRILES 943
water, which has shown advantageous effects such as enhanced COD reduction and specific respiration rate of the activated sludge. However, with prolonged operation the advantages diminished as irreversible adsorption of non-biodegradable components inhibited the in situ regenerati on of carbon surface . Knowles and Wyattl60- 162 developed and patented a novel biological process for the degradation of ACN wastewater using a mixed cul ture of Alcaligenes, Pseudomonas, Flavobacterium, Acinetobacter spp and Bacillus megaterium capable of degrading the main wastewater constituents. An integrated process for the treatment of KO I I and KO 1 3 ACN wastewaters i s proposed by Zimpro Passavant Environmental Systems, Inc. USA'52. The treatment includes, first step pretreatment by wet air oxidation, then a second step passage through evaporator/crystall izer to remove ammonium sulphate and a third step biophysical powdered activated carbon treatment (PACT). Mishra and coworkers 163 have also successfully treated the ACN wastewater by a wet air oxidation process followed by biotreatment. Indian Petrochemicals Corporation Ltd (IPCL) have studied various processes and found a physicochemical treatment fol lowed by b iotreatment to be commercially feasible 'M, ' 65 . For biotreatment, a mixed microbial culture containing Acetobacter, Acinetobacter, Arthrobacter, Aeromonas, Bacillus, Flavobacterium and Pseudomonas has been developed with advantageous properties l ike better COD and cyanide degradation, settleabil ity, shock resistance, growth and higher specific respiration ratel64. The efficiency of this process improved significantly by using polypropylene pads or active carbon powder as biomass support material resulting in a very stable performance under shock loading conditions '64 and the know-how is currently being translated in to a commercial scale biotreatment plant.
B) Wastewater from A diponitrile and Nylon Manufacture
Adiponitrile is manufactured commerc ially by several processes, such as the DuPont Process based on catalytic addition of HCN to butadiene and the Monsanto process based on electrodimerization of acrylonitrile'. Though not much information is avai lable on the biotreatment of adiponitrile and £-caprolactam manufacture effluents, biodegradation of adiponitrile and acrylonitrile by organisms l ike Rhodococcus sp. R3 1 2 1 , Arthrobacter Sp. 166, 1 67, Klebsiella pneumoniae '6x, etc . is well documented. B iodegradation of £-caprolactam and related compounds 'fi9 and nylon-6 wastewater contain-
ing £-caprolactam by Pseudomonas aeruginosa MCM B-407 170 has been reported.
Miscellaneous Uses The crude oi l produced from shale deposits contains
h igh levels of undesirable n itrogen and sulphur compounds. As a result, the upgradation of shale oil is generally carried out by costly hydrotreatment at h igh temperatures and pressures. A b iotechnological process using P aeruginosa and P fluorescence, which selectively degraded the shale oil n i triles, has been described for the upgradation of shale oi ls '7 1 . Such biotech process potentially reduces the cost of shale oi l upgradation .
The nitrile-metabolizing organi sms can also be used for the detoxification of food products containing toxic cyanoglucosides such as cassava roots, a staple food in developing countries 1 72 . Rhodococcus sp. R3 1 2 with an endocellular �-glucosidase, a nitrile hydratase and an amidase ha s been u sed to remove the tox i c cyanoglucosides and a-hydroxy n i triles in cassava pulpl72 .
Another interesting appl ication of the n i trile-metabol izing organisms is the enzymatic decontamination of aqueous polymer emulsions (latexes) of n i trile rubbers containing acrylonitri le ' 7, by means of whole cells and cellular lysates of Brevibacterium imperiale CBS 49874, Corynebacterium nitrophilus ATCC 2 1 4 1 9 or Novo's biocatalyst SP 409.
A significant use of n i trile metabolizing organisms has been the development of herbicide resistant plants for the crop i mprovement. Genes from Klebsiella ozaenae or Myrothecium verruca ria that degrade the herbicides, dichlorobenil, bromoxynil and cyanamide, respectively, have been used to develop transgenic tobacco or tomato plants resistant to the herbicides75,Kl . These transgenic plants may soon be available in the market.
Conclusions A wide variety of microorganisms are reported to have
the capabil i ty to metabolize different types of n i triles. The microbial degradation of nitriles proceeds through two distinct enzymatic pathways: n itrilase catalyzes the direct hydrolysis of n i triles to carboxylic acids and ammonia, while n itrile hydratase catalyzes the hydration of n itriles to amides fol lowed by their conversion to the carboxylic acids plus ammonia by amidase.
Nitrilases are multimeric, sulphydryl enzymes that do not have any metal cofactors or prosthetic groups, while
944 J SCI IND RES VOL.58 DECEMBER 1 999
nitrile hydratases, the most studied among the nitrile hydrolyzing enzymes, are metal loenzymes having iron or cobalt. Recent studies have shown novel ligand structures of metal binding sites, the unique photoactivation of ferric nitrile hydratase and the mechanism of hyper induction of these enzymes. The versati le biocatalytic nature and applications of nitri le converting enzymes are now increasingly recognised for the production of several pharmaceuticals and fine chemicals . Also, microbial nitrile hydrolysis has been shown as a potential method for the preparation of optically active nitriles, amides and carboxylic acids, not generally feasible by chemical routes . A commercial process involving the mult i-ki loton scale synthesis of acry lamide using Rhodococcus rhodochrous Jl nitrile hydratase is the best example of a ful ly developed industrial application of this biotechnology. Similarly, for nicotinamide also commercial scale biotechnological process is being established.
The nitrile metabolizing microorganisms by virtue of their capability to eliminate the highly toxic nitrile compounds play a very significant role in al leviating environmental pollution by way of bioremediation of environmental matrices contaminated with toxic nitrile compounds . The genes from the nitrile herbicide degrading organisms have been used to develop transgenic tobacco or tomato plants with herbicide resistance. Though recent developments broadened the scope of potential application of these versatile biocatalysts in chemical synthesis and bioremediation, further application-oriented studies are required to ful ly harness their biotechnological potential .
Acknowledgements The authors thank the management of Indian Petro
chemicals Corporation Ltd, for their continued support and permission for publication of this article.
References I Jallageas J C, Arnaud A & Galzy P, Adv Biochem Eng , 14
( 1 980) I . 2 Legras J L, Chuzel G, Arnaud A & Galzy P, World J
Microbiol Biotechnol, 6 ( 1 990) 83. 3 Mckinney RJ & DeVito SC, in Kirk-Othmer Encyclopedia of
Chemical Technology 4th ed, Suppl Vol . edited by J I Kroschwitz & M Howe-Grant (Wiley, New York ) 1 996, pp. 437-459.
4 Pollak P, Romeder G, Hagedorn F & Gelbke H-P, in Ullman s Encyclopedia of Industrial Chemistry 5th edition, Vol A I 7, edited by B Elvers , S Hawkins & G Schulz (Verlag Chemic, Gennany) 1 99 1 , pp. 363-376.
5 Verschueren K, Handbook of Environmental Data on Organic Chemicals (van Nostrand Reinhold Co, New York) 1 977.
6 DeVito SC, in Designing Safer Chemicals: Green CIII'II/is/I),
for Pollution Prevention, ACS Symp Ser 640, edited by S C DeVito & R L Garrett (American Chemidcal Society, Washington) 1 996, pp. 1 94-223.
7 Knowles C J & Bunch A W, Adv Microb PIIysiol , 27 ( 1 9X6) 73.
8 Harris R E, Bunch A W & Knowles C J, Sci /Jrog ( O x ford ) , 71 ( 1 987) 293.
9 Thompson L A, Knowles C J, Linton E A & Wyatt J M, Chem Bri/, ( 1 988) 900.
1 0 Nagasawa T & Yamada H , Trends Bio/ecllnol , 7 ( 1 989) 1 53 . I I Finnegan I , Toerien S , Abbot L, Smit F & Raubenheimer HG,
Appl Microbiol Bio/echnol, 36 ( 1 99 1 ) 1 42. 1 2 Selly M K & Conn E E, i n Methods in Enzymology Vol XVI I
Part B , edited b y N I H Tabor (Academic Press, New York) 197 1 , pp. 239-244.
1 3 Kuwahara M & Yanase H, Agric Bioi Chem, 49 ( I nS) 1 25 .
14 Hardy R W F, Burns R C & Parshall GW, in Inorgallic Biochemis/I)I, Vol 2, edited by K Eichkorn (Elsevier, Amsterdam) 1 97 1 , pp. 746-793.
1 5 Kobayashi M & Shimizu S , FEMS Microbiol Lelt, 120 ( 1 994) 2 1 7.
1 6 Robinson W G & Hook R H , J Biol Chem, 239 ( 1 964) 4257. 1 7 Hook R H & Robinson W G , J Biol Chem, 239 ( 1 964) 4263. 1 8 Harper D B , Biochem Soc TrailS, 4 ( 1 976) 502. 1 9 Bandyopadhyay A K , Nagasawa T, Asano Y, Fuj ishiro K,
Tani Y & Yamada H, Appl Environ Microbial , 51 ( 1 986) 302.
20 Nagasawa T, Kobayashi M & Yamada H , A rch Micmbiol , 150 ( 1 988) 89.
2 1 Kobayashi M, Nagasawa T & Yamada H , Eur J Biochem, 182 ( 1 989)349.
22 Kobayashi M, Yanaka N, Nagasawa T & Yamada H, J Bacterial, 172 ( 1 990) 4807.
23 Kobayashi M, Yanaka N, Nagasawa T & Yamada H, FEMS Microbiol Lett , 77 ( 1 99 1 ) 1 2 1 .
24 Nagasawa T, Nakamura T & Yamada H, Arch Microbial , 155 ( 1 990) 1 3.
25 Levy-Schil S, Sou brier F, Crutz-Le Coq A-M, Faucher D, Crouzet J & Petre D, Gene, 1 6 1 ( 1 995) 1 5.
26 Mauger J, Nagasawa T & Yamada H, A rch Micmbiol , 155 ( 1 990) I .
27 Nagasawa T, Mauger J & Yamada H, Eur J Biochem , 1 94 ( 1 990) 765.
28 Yamamoto K , Fugimatsu I & Komatsu K I, J Ferment Bioeng, 73 ( 1 992) 425.
29 Bhalla TC, Miura A, Wakamoto A, Ohaba Y & Furuhashi K, Appl Microbial Biotechnol , 37 ( 1 992) 1 84.
30 Kobayashi M, Yanaka N, Nagasawa T & Yamada H, Biochemistry, 31 ( 1 992) 9000.
3 1 Stevenson D E, Feng R, Dumas F, Grolean D , M ihoc A & Storer A, Bioleelinol App/ Bioeliem, 1 5 ( J 992) 283.
32 Stevenson DE, Feng R & Storer A C, FEBS Lett , 277 ( 1 990) 1 1 2.
33 Novo C, Tata R, Clemente A & Brown PR, FEBS Lett , 367 ( 1 995) 275.
' 1
.. .
RAMAKRISHNA et at. : MICROBIAL METABOLISM OF NITRILES 945
34 Mimura A, Kawamoto T & Yamaga K, J Ferme11l Tecl1l10l ,
47 ( 1 969) 63 ! . 35 Sugiura Y, Kuwahara J, Nagasawa T & Yamada H , J Alii
Chem Soc, 109 ( 1 987) 5848. 36 Nelson M l , lin H, Turner 1 M , Grovc G, Scarrow R C, Brennan
B A & Que L, J Am Chem Soc, 1 13 ( 1 99 1 ) 7072. 37 Jin H, Turner I M, Nelson M J, Gerbil R .I, Doan P E &
Hoffman B M, J Am Chem Soc, 115 ( 1 993) 5290. 38 Doan P E, Nelson M J, lin H & Hoffman B M, .I Am Gem
Soc, 1 18 ( 1 996) 70 1 4. 39 Scarrow R C, Brennan B A, Cummings 1 G, Jin H, Duong D l ,
Kindt 1 T & Nelson M l, Biochemist!".'; 3 5 ( 1 996) 1 0078.
40 Ellison 1 1, Neinstedt A, Shoner S C, Barnhart D, Cowen 1 A & Kovacs 1 A, .I Am Chell1 Soc , 120 ( 1 998) 569 1 .
4 1 Huang W, lia J, Cummings 1 , Nelson M , S<.:hneider G & Lindquist Y, Structure. 5 ( 1 997) 69 1 .
42 Honda 1 , Nagamune T, Tetrani Y, Hirata A, Sasabe H & Endo I , Ann NY Acad Sci USA , 672 ( 1 992) 29.
43 Nagamune T, Kurata H, Hirata M, Honda 1, Koike H, Ikeuchi M, Inoue Y, Hirata A & Endo I , Biochelll Biophys Res COmmlln, 1 68 ( 1 990) 437.
44 Nagamune T, Kurata H, Hirata M, Honda J, Hirata A & Endo I , Photochem Photobiol, 51 ( 1 990) 89.
45 Odaka M, Noguchi T, Nagashima S, Yohada M, Yabuki S, Hoshino M , Inoue Y & Endo I, Biochem Biophys Res COmI/lUII, 221 ( 1 996) 1 46.
46 Tsujimura M, Dohmae N, Odaka M, Chijimatsu M , Takio K, Yohada M, Nagashima S & Endo I , J Biochelll, 272 ( 1 997) 29454.
47 Tsujimura M, Odaka M , Nagashima S, Yohada M & Endo I, J Biochem, 119 ( 1 996) 407.
48 Noguchi T, Honda 1 , Nagamune T, Sasabe H, Inoue Y & Endo I, FEBS Lett, 358 ( 1 995) 9.
49 Noguchi T, Hoshino M, Tsujimura M, Odaka M, Inoue Y & Endo I, Biochemistry, 35 ( 1 996) 1 6777.
50 Odaka M, Fuj i K , Hoshino M , Noguchi T, Tsuj i mura M, Nagashima S, Honda J, Nagamune T, Sasabe H, Inoue Y & Endo I, J Am Chem Soc, 119 ( 1 997) 3785.
5 1 Nagasawa T & Yamada H, Biochem Biophys Res Commun,
147 ( 1 987) 70 ! . 5 2 Nagasawa T & Yamada H , in Biocatalysis, edited b y D A
Abramowicz (van Nostrand Reinhold, New York ) 1 990, pp. 277-3 1 8.
5 3 Yamada H & Kobayashi M , Biosci Biotechnol Biochem, 60 ( 1 996) 1 39 ! .
54 Kobayashi M & Shimizu S , Nature Biotechnol, 1 6 ( 1 998) 733. 55 Kobayashi M, Nishiyama M , Nagasawa T, Horinouchi S,
Beppu T & Yamada H , Biochim Biophys Acta, 1 129 ( 1 99 1 ) 23.
56 Brennan B A, Alms G, Nelson M J, Durney L T & Scarrow R C, J Am Chem Soc, 118 ( 1 996) 9 1 94.
57 Brennan B A, Cummings 1 G, Chase D B, Turner I M, Nelson M 1, Biochemistry, 35 ( 1 996) 1 0068.
58 Fallon R D, Stieglitz B & Turner I, Appl Microbiol Biotechnol, 47 ( 1 997) 1 56.
59 Payne M S, Wu S , Fallon R, Tudor G, Stieglitz B, Turner 1 & Nelson M , Biochemistry , 36 ( 1 997) 5447.
60 Kobayashi M, Suzuki T, Fujita T, Masuda M & Shimizu S, Proc Natl Acad Sci USA, 92 ( 1 995) 7 1 4.
6 1 Maier-Greiner U H , Obennaier-Skrobranek B M M , Estennaier L M, Kammerloher W, Freund C, Wulfing C, Burkert U I . Matern D H , Breur M, Eulitz M, Kufrevioglu 0 I & Hartmann G R, Proc Natl Acad Sci USA , 88 ( 1 99 1 ) 4260.
62 Nawaz M S, Khan A A . Seng 1 E, Leakey 1 E, Siitoneu P H & Cerniglia C E, Appl Enviroll Microbiol , 60 ( 1 994)
3343. 63 Nawaz M S, Khan A A, Bhattacharyya D, Siitoneu P H &
Cerniglia C E, J Bacteriol, 1 78 ( 1 996) 2397 . 64 Ciskainik L M, Wi lczek 1 M & Fallon R D, Appl I:'nvimn
Microbiol , 6] ( 1 995 ) 998.
65 Kieny-L'Homme M P, Arnaud A & Galzy P, J Gell Apl)1 Microhiol, 27 ( 1 98 1 ) 307.
66 Mayaux 1 F. Cerbelaud E, Sou brier F, Faucher D & Petre D, J Bacteriol , 172 ( 1 990) 6764.
67 Moreau 1 L , Bernet N. Arnaud A & Galzy P, Call J MiclVhiol.
39 ( 1 993) 524. 68 Chan KwoChion CKN, Duran R, Arnaud A & Galzy P, AJlJlI
Microbiol Biotech/wI, 36 ( 1 99 1 ) 205. 69 Soubrier F, Levy-Schil S, Mayaux 1 F, Petre D, Arnaud A &
Crouzet 1, Gene 116 ( 1 992) 99. 70 Mayaux J F, Cerbelaud E, Soubrier F, Yeh P, Blanche F &
Petre D, J Bacterial, 173 ( 1 99 1 ) 6694. 7 1 Kobayashi M , Komeda T, Nagasawa T, Yamada H & Shimizu
S, Biosci Biotechno/ Biochell1 , 57 ( 1 993) 1 949. 72 Kobayashi M, Fuj iwara M, Goda H, Komeda H & Shimizu S ,
Proc Natl Acad Sci USA , 94 ( 1 997) 1 1 986. 73 Fournand D, Bigey F & Arnaud A , Appl Environ MiclVbiol,
64 ( 1 998) 2844. 74 Stalker D M & McBride K E, J Bacteriol , 169 ( 1 987) 955. 75 Stalker D M, McBride K E & Malyj L D, Science , 242 ( 1 988)
4 1 9. 76 Kobayashi M, Komeda H, Yanaka N, Nagasawa T & Yamada
H, J Bioi Chem, 267( 1 992) 20746. 77 Kobayashi M, lzu H, Nagasawa T & Yamada H, Proc Natl
A cad Sci USA , 90 ( 1 993) 247. 78 Beppu T, Yamada H, Nagasawa T, Horinouchi S, Nishiyama
M , Eur Pat, EP 444639, 1 99 1 79 Beppu T, Yamada H, Nagasawa T, Horinouchi S & Nishiyama
M, Eur Pat, EP 445 646, 1 99 1 . 80 Mizunashi W, Nishiyama M, Horinouchi S & Beppu T, Appl
Microbiol Biotechnol, 49 ( 1 998) 568. 8 1 Wu S, Fallon R D & Payne M S , Appl Microbiol Biotechnol ,
48 ( 1 997) 704 82 Yamaki T, Oikawa T, I to K & Nakamura T, J Ferment Bioeng,
83 ( 1 997) 474. 8 3 Maier-Greiner U H , Klaus C B A, Estermaier L M & Hartmann
G R, Angw Chem, 30 ( 1 99 1 ) 1 3 1 4. 84 Crosby J, Moilliet J, Parratt J S , & Turner N, J Chem Soc
Perkin Trans "f, ( 1 994) 1 679. 85 Yamada H & Nagasawa T, Ann N Y Acad Sci Enzyme Eng , 10
( 1 990) 1 42. 86 Yamada H & Nagasawa T, Eur Pat, EP 307 926, 1 989. 87 Yamada H, Nagasawa T, Nakamura T, Eur Pat, EP 444 640,
1 99 1 . 88 Nakayama K , Ogawa Y, Honda H , Ohata T & Ozawa T, Eur
Pat, EP 3 1 9 344 , 1 989. 89 Vaughan P A, Knowles C J & Cheetham P S, Enzyme
Microb Technol. 11 ( 1 989) 8 1 5 .
946 J SCI IND RES VOL.58 DECEMBER 1 999
90 Eyal J & Charles M, J Ind Microbial , 5 ( 1 990) 7 1 . 9 1 Klempier N, d e Raadt A , Faber K & Griengel H, Tetrahedron
Leu, 32 ( 1 99 1 ) 34 1 . 92 de Raadt A, Griengl H, Klempier N & Stutz AE, J Org
Chem, 58 ( 1 993) 3 1 79. 93 de Raadt A, Klempier N, Faber K & Griengl H, J Chem Soc
Perkill Trails I . ( 1 992) 1 37. 94 Meth-Cohn 0 & Wang M X, J Chem Soc Perkill Trans I ,
( 1 997) 1 099. 95 Godtfredsen SE, Ingvorsen K, Yde B & Anderson 0, in
Biocatalysts in Organic Syntheses, edited by J Tramper, H C van der Plas & P Linko (Elsevier, Amsterdam) 1 985, pp. 3- 1 8.
96 Kobayashi M, Yanaka N, Nagasawa T & Yamada H, Tetrahedroll, 46 ( 1 990) 5587.
97 Cohen M A, Sawden J & Turner N, Tetrahedron Lell , 31 ( 1 990) 7223.
98 Cohen M A, Parralt J S, Turner N J & Crosby J, Tetrahedron Asymmetry, 3 ( 1 992) 1 543 .
99 Fallon R D & Wysong E B, US Pat, 5552 305. 1996 1 00 Fukuda Y, Harada T & Izumi Y, J Ferment Technol, 973 51
( 1 973) 393. 1 0 1 Jallageas J C, Arnaud A & Galzy P, US Pat, 4366250 1 982. 1 02 Macadam A M & Knowles C J, Biotechnol Lett, 7( 1 985) 865. 1 03 Yamamoto K, & Komatsu K, Agric BioI Chem, 55 ( 1 99 1 )
1 459. 1 04 Yamamoto K, Ueno K, Otsubo K, Kawakami K & Komatsu
K, Appl Enviroll Microbial, 56 ( 1 990) 3 1 25. 1 05 Yamamoto K, Oishi K, Fujimatsu I & Komatsu K, Appl
Environ Microbial, 57 ( 1 99 1 ) 3028. 1 06 Layh N, Stolz A, Forster S, Effenberger F & Knackmuss H
J, Arch Microbiol, 158 ( 1 992) 405. 1 07 Gradley M L & Knowles C J, Biotec/lIlol LeU, 16 ( 1 994) 4 1 . 1 08 Kakeya H , Sakai N , Sugai T & Ohta H , Tetrahedron Lett , 32
( 1 99 1 ) 1 343. 1 09 Bianchi D, B osnetti P, Cesti G, Franzosi G & Spezia S,
Biotechnol Leu , 13 ( 1 99 1 ) 24 1 . 1 1 0 Gill igan T, Yamada H & Nagasawa T, Appl Microbiol
Biotechnol, 39 ( 1 993) 720. I I I Bauer R, Herrlinger B , Layh N, Stolz A & Knackmuss H J,
Appl Microbial Biotechllol , 42 ( 1 994) I . 1 1 2 Layh N, Stolz A, Bohme J, Effenberger F & Knackmuss
HJ , J Bioteclznol, 33 ( 1 994) 1 75. 1 1 3 Layh N, Knackmuss H J & Stolz A, Biotec/1I101 Lell , 17
( 1 995) 1 87. 1 1 4 Martinkova L, Stolz A & Knackmuss H J, Biotechnol Lell,
18 ( 1 996) 1 073. 1 1 5 Effenberger F & Graef B W, J Biotechllol , 60 ( 1 998) 1 65. 1 1 6 Matsutomo S, Inoue A, Kumagi K, Mutai R & Mitsuda S, Biosci
Biotechllol Biochem, 59 ( 1 995) 20. 1 1 7 Hashimoto Y, Kobayashi E, Endo T, Ni shiyama M &
Horinouchi S, Biosci Biotechnol Bioclzem, 60 ( 1 996) 1 279. 1 1 8 B lakely A J, Colby J, Wil l iams E & O'Rei l ly C, FEMS
Microbiol Leu , 129( 1 995) 57. 1 1 9 Bauer R, Knackmuss H J & Stolz A, Appl Micr�hiol
Biotechnol, 49 ( 1 998) 89. 1 20 Crosby J, Parralt J S & Turner N, Tetrahedron Asymmetry,
3 ( 1 992) 1 547. 1 2 1 Beard T, Cohen M A, Parratt JS & Turner N, Tetrahedroll
Asymmetry, 4 ( 1 993) 1 085.
1 22 Matoishi K, Sano A, Imai N, Yamazaki T, Yokoyama M, Sugai T & Ohata H, Tetrahedron Asymmetry, 9 ( 1 998) 1 097.
1 23 Kerridge A, Parratt J S, Roberts S M, Thiel F, Turner N J & Willetts A J, Bioorg Med Chem, 2 ( 1 994) 447.
1 24 Maddrell S J, Turner N J, Kerridge A, Willets A J & Crosby J, Tetrahedron Leu, 37 ( 1 996) 600 I .
1 25 van den Tweel W J J, van Dooren T J G M , de Jonge P H, Kaptein B, Duchateau A L L & Kamphuis J , Appl Microhiol Biotechllol , 39 ( 1 993) 296.
1 26 Wiser M, Heinzmann K & Kiener A, Appl Microbial Biotechnol , 48 ( 1 997) 1 74.
1 27 Layh N & Willets A, Biotechnol Letl, 20 ( 1 998) 329. 1 28 Anton D, Fallon R D, Linn W, Stieglitz B & Witterholt V, In
ternational Pat, WO 92/05275 , 1 992 1 29 Stieglitz B, Linn W J, Jobst W, Fried K M, Fallon R D,
Ingvorsen K & Yde B, International Pat, WO 9210 1 062, 1992
1 30 Endo T, Yamagami T & Tamura K, US Pat , 5326702, 1 994. 1 3 1 Yamamoto K, Otsubo K & Oishi K , US Pat, 5283 1 93, 1 994. 1 32 Favre-Bulle 0, Pierrard J, David C, Morel P & Horbez D, In-
ternational Pat, WO 981 1 8,941 , 1 998. 1 34 Kobayashi M, Nagasawa T & Yamada H, Trends Biotechnol ,
10 ( 1 992) 27. 1 35 Nagasawa T, Mathew C D, Mauger J & Yamada H, Appl
Environ Microbiol, 54 ( 1 988) 1 766. 1 36 Mathew C D, Nagasawa T, Kobayashi M & Yamada H, Appl
Environ Microbial, 54 ( 1 988) 1 30. 1 37 ElIr Chem News 1996, 66 ( 1 743) 1 9. 1 38 Nagasawa T, Nakamura T & Yamada H, Appl Microbial
Biotechnol, 34 ( 1 990) 322. 1 39 Armitage Y C, Hughes J & Webster N A, International Pat,
WO 9512 1 805, 1 995. 1 40 Symes K C & Hughes J , International Pat, WO 95/2 1 827,
1 995 1 4 1 Heitner H I & Ryles R G, Eur Pat, E P 05 1 4648B I , 1 992. 1 42 Rothenberg A S & Ryles R G, Eur Pat, EP, 0641 584A2,
1 995 1 43 Lewellyn M E, Intemational Pat, WO 96/ 1 427 1 , 1 996. 1 44 Fournand D, Arnaud A & Galzy P, J Malec Calal B: Enzy
matic, 4 ( 1 998) 77. 145 Yamagami T, Kobayashi E & Endo T, Eur Pat, EP 473328 ,
1 992. 1 46 Datta R, Tsai S P. Bonsignore P, Moon S H & Franl J R, FEMS
Microbial Rev, 16 ( 1 995) 22 1 . 1 47 Takagi M , Oishi K , Ishimura F & Fuj imatsu I, J Ferlllelll
Bioeng, 78 ( 1 994) 54. 1 48 Takagi M, Shirokaze J-I, Oishi K , Otsubo K, Yamamoto K,
Yoshida N, Fujimatsu I, J Ferment Bioeng , 78 ( 1 994) 1 9 1 . 1 49 Moreau J L , Arnaud A & Galzy P, Microhiol Res, 149
( 1 994) 47. 1 50 Moreau J L. Azza S. Arnaud A & Galzy P, J Basic
Microbial, 33 ( 1 993) 323. 1 5 1 Moreau J L, Bigey F, Azza S , Arnaud A & Galzy P,
BiocCltalysis, 10 ( 1 994) 325. 1 52 Copa W M, Lehmann R W, & Vollstedt T J , in Chemical o.ri
dation, Vol 2 (Academic Press, New York) 1 994, pp. 328-355. 1 53 Sittig M, Pollution Control in the Organic ChelllicaI Indl/stl)"
Pollution Technol Review No 9 (Noyes Data Corp, New Jersey) 1 974.
RAMAKRISHNA et at. : MICROBIAL METABOLISM OF NITRILES 947
1 54 Grosse D W, in Encyclopedia of Environmental Technology Vol 4, edited by P N Cherimisinoff (Gulf Publication, Houston) 1 990, pp. 54 1 -6 1 1 .
1 55 Desai J D & Ramakrishna C , J Sci inc! Res , 57 ( 1 998) 44 1 . 1 56 Kato A H & Yamamura K K , US Pat, 3 940 332, 1 976. 1 57 Fujii Y & Oshmi T, US Pat, 3 756 947, 1 973. 1 5 8 Mimura A, Kawamoto T & Yamaga K, Hakko Kagaku Zasshi,
48 ( 1 970) 68; Chem Abst, 73, 6989. 1 59 Ramakrishna C, Kar D & Desai J D, J Ferment Bioeng, 67
( 1 989)430. 1 60 Knowles C 1 & Wyatt 1 M, Eur Pat, EP 0274 856, 1 988. 1 6 1 Wyatt 1 M & Knowles C 1 , Biodegradation , 6 ( 1 995)93. 1 62 Wyatt 1 M & Knowles C 1 , 1111 Biodeteriorat Biodegrad, 35
( 1 995) 227. 1 63 Mishra V S, Padiyar V, loshi 1 B, Mahajani V V & Desai
10, Trans inst Chem Eng (UK) , 73 ( 1 995) 243. 1 64 Ramakrishna C & Desai 1 D, Report on Treatability of A CN
Wastewater II, I nternal Report, Rese arch Centre, Indian Petrochem Corp Ltd, Baroda, India, 1 997.
1 65 Patel P S , Ramakrishna C & Desai 1 D, Indian Pat, App1 438! BOM!96 1 996.
1 66 Yamada H , Asano Y, Hino T & Tani Y, J Ferment Technol , 57 ( 1 979) 8.
1 67 Ramakrishna C & Desai 1 D, ' indian J Exptl Bioi, 3 1 ( 1 993) 1 73 .
168 Nawaz M S, Franklin W, Campbell W L , Heinze T M & Cerniglia C R ,Arch Microbiol, 156 ( 1 99 1 )23 1 .
1 69 Shama G & Wase D A 1 , fnt Biodeterioral Bull , 1 7 ( 1 9S I ) I . 1 70 Kulkarni R S & Kanekar P P, Curr Microbiol , 37 ( 1 998) 1 9 1 .
1 7 1 Aislabie 1 & Atlas R M , Appl EHviroll Microbiol , 54 ( 1 988) 2 1 97.
1 72 Legras 1 L , lory M, Arnaud A & Galzy P, Appl Microbiol Biotechnol, 33 ( 1 990) 529.
1 7 3 Battistel E, Bernardi A & Maestri P, Biolechnol Lell , 19 ( 1 997) 1 3 1 .
1 74 Col l ins P A & Knowles C J , J Cell MicmiJiol , l29 ( 1 983) 7 1 1 .
1 75 Goldlust A & Bohak Z , Biolechllol Appl Biochem, 1 1 ( 1 989) 58 1 .
1 76 Asano Y. Fujishiro K , Tani Y & Yamada H , A/Vic Bioi Chelll, 46 ( 1 982) 1 1 65.
1 77 Toutniex D, Thiery A. Mastracci M, Arnaud A & Galzy P, Alltollie vall Leeuwellhoek. 52 ( 1 986) 1 73.
1 78 Tani Y. Kurihara M & Nishise H , Agric Bioi Chelll, 53 ( 1 989) 3 1 5 I .
1 79 Nagasawa T. Nanba H , Ryuno K , Takeuchi K & Yamada H, Eur J Biochem, 162 ( 1 987) 69 1 .
1 80 Hjort C M , Godtfredsen S E & Emborg C, J Chem Tee/lIlol Biolechnol, 48 ( 1 990) 2 1 7.
1 8 1 Kaakeh M R , Legras 1 L, Duran R, Chan K wo Chion Ch K N, Arnaud A & Galzy P, Zelltral Mikrobiol , 146 ( 1 99 1 ) 89.
1 82 Endo T & Watanabe I, FEBS Lell , 243 ( 1 989) 6 1 . 1 83 Asano Y, Yasuda T, Tani Y & Yamada H , Agric Bioi Chem,
46 ( 1 982) 1 1 83. 1 84 Thiery A. Mastracci M, Arnaud A, Galzy P & Nicholas M,
J Basic Microbiol, 26 ( 1 986) 299. 1 85 Clarke PH , J Cell Microbiol, 71 ( 1 972) 24 1 .
1 86 Kagayama T & Ohe T, Agric Bioi Chem, 54 ( 1 990) 2565.