Degradation of phenanthrene by <Emphasis Type="Italic">Burkholderia</Emphasis> sp. C3: initial 1,2- and 3,4-dioxygenation and <Emphasis Type="Italic">meta</Emphasis>- and <Emphasis Type="Italic">ortho</Emphasis>-cleavage of naphthalene-1,2-diol

Burkholderia sp. C3 was isolated from a polycyclic aromatic hydrocarbon (PAH)-contaminated site in Hilo, Hawaii, USA, and studied for its degradation of phenanthrene as a sole carbon source. The initial 3,4-C dioxygenation was faster than 1,2-C dioxygenation in the first 3-day culture. However, 1-hydroxy-2-naphthoic acid derived from 3,4-C dioxygenation degraded much slower than 2-hydroxy-1-naphthoic acid derived from 1,2-C dioxygenation. Slow degradation of 1-hydroxy-2-naphthoic acid relative to 2-hydroxy-1-naphthoic acid may trigger 1,2-C dioxygenation faster after 3 days of culture. High concentrations of 5,6-␣and 7,8-benzocoumarins indicated that meta-cleavage was the major degradation mechanism of phenanthrene-1,2- and -3,4-diols. Separate cultures with 2-hydroxy-1-naphthoic acid and 1-hydroxy-2-naphthoic acid showed that the degradation rate of the former to naphthalene-1,2-diol was much faster than that of the latter. The two upper metabolic pathways of phenanthrene are converged into naphthalene-1,2-diol that is further metabolized to 2-carboxycinnamic acid and 2-hydroxybenzalpyruvic acid by ortho- and meta-cleavages, respectively. Transformation of naphthalene-1,2-diol to 2-carboxycinnamic acid by this strain represents the first observation of ortho-cleavage of two rings-PAH-diols by a Gram-negative species.     

Effects of organic compounds on the degradation ofp-nitrophenol in lake and industrial wastewater by inoculated bacteria

Many microorganisms fail to degrade pollutants when introduced in different natural environments. This is a problem in selecting inocula for bioremediation of polluted sites. Thus, a study was conducted to determine the success of four inoculants to degradep-nitrophenol (PNP) in lake and industrial wastewater and the effects of organic compounds on the degradation of high and low concentrations of PNP in these environments.Corynebacterium strain Z4 when inoculated into the lake and wastewater samples containing 20 µg/ml of PNP degraded 90% of PNP in one day. Addition of 100 µg/ml of glucose as a second substrate did not enhance the degradation of PNP and the bacterium utilized the two substrates simultaneously. Glucose used at the same concentration (100 µg/ml), inhibited degradation of 20 µg of PNP in wastewater byPseudomonas strain MS. However, glucose increased the extent of degradation of PNP byPseudomonas strain GR. Phenol also enhanced the degradation of PNP in wastewater byPseudomonas strain GR, but had no effect on the degradation of PNP byCorynebacterium strain Z4.Addition of 100 µg/ml of glucose as a second substrate into the lake water samples containing low concentration of PNP (26 ng/ml) enhanced the degradation of PNP and the growth ofCorynebacterium strain Z4. In the presence of glucose, it grew from 2×10⁴ to 4×10⁴ cells/ml in 3 days and degraded 70% of PNP as compared to samples without glucose in which the bacterium declined in cell number from 2×10⁴ to 8×10³ cells/ml and degraded only 30% PNP. The results suggest that in inoculation to enhance biodegradation, depending on the inoculant, second organic substrate many play an important role in controlling the rate and extent of biodegradation of organic compounds.Abbreviations PNP p-nitrophenol     

Growth-substrate dependent dechlorination of 1,2-dichloroethane by a homoacetogenic bacterium

A rod shaped, gram positive, non sporulating Acetobacterium strain was isolated that dechlorinated 1,2-dichloroethane (1,2-DCA) to ethene at a dechlorination rate of up to 2 nmol Cl^- min^-1 mg^-1 of protein in the exponential growth phase with formate (40 mM) as the substrate. Although with other growth substrates such as pyruvate, lactate, H₂/CO₂, and ethanol higher biomass productions were obtained,the dechlorination rate with these substrates was more than 10-fold lower compared with formate growing cells. Neither cell extracts nor autoclaved cells of the isolatedAcetobacterium strain mediated the dechlorination of 1,2-DCA at significant rates. The addition of 1,2-DCA to the media did not result in increased cell production. No significant differences in corrinoid concentrations could be measured in cells growing on several growth-substrates. However, these measurements indicated that differences in corrinoid structure might cause the different dechlorination activity. The Acetobacterium sp. strain gradually lost its dechlorination ability during about 10 transfers in pure culture, probably due to undefined nutritional requirements. 16S rDNA analysis of the isolate revealed a 99.7% similarity with Acetobacterium wieringae. However, the type strains of A. wieringae and A. woodii did not dechlorinate 1,2-DCA.     

花生茎叶酚性成分研究

运用大孔树脂对花生茎叶提取液进行富集,不同浓度乙醇洗脱,硅胶、RP-18、Sephadex LH-20等多种材料进一步分离纯化,研究花生茎叶化学成分,并通过理化方法和光谱分析对化合物进行结构鉴定。结果表明:从花生茎叶大孔树脂10%乙醇洗脱部位中分离并鉴定了10个化合物,分别为邻苯二甲酸二异丁酯(1)、水杨酸(2)、儿茶酚(3)、对羟基苯甲酸(4)、(反)-3,4-二羟基苯丙烯酸(5)、对羟基苯酚(6)、邻苯二甲酸二丁酯(7)、3,4-二羟基苯乙醇(8)、对羟基苯乙醇(9)、3,4-二羟基苯甲酸(10)。除化合物1、2和4外,其余均为首次从该植物中分离得到。     

Purification and characterization of an alcohol dehydrogenase from 1,2-propanediol-grownDesulfovibrio strain HDv

The sulfate-reducing bacterimDesulfovibrio strain HDv (DSM 6830) grew faster on (S)- and on (R, S)-1,2-propanediol (μ_max 0.053 h⁻) than on (R)-propanediol (0.017 h⁻¹) and ethanol (0.027 h⁻¹). From (R, S)-1,2-propanediol-grown cells, an alcohol dehydrogenase was purified. The enzyme was oxygen-labile, NAD-dependent, and decameric; the subunit mol. mass was 48 kDa. The N-terminal amino acid sequence indicated similarity to alcohol dehydrogenases belonging to family III of NAD-dependent alcohol dehydrogenases, the first 21 N-terminal amino acids being identical to those of theDesulfovibrio gigas alcohol dehydrogenase. Best substrates were ethanol and propanol (K _m of 0.48 and 0.33 mM, respectively). (R, S)-1,2-Propanediol was a relatively poor substrate for the enzyme, but activities in cell extracts were high enough to account for the growth rate. The enzyme showed a preference for (S)-1,2-propanediol over (R)-1,2-propanediol. Antibodies raised against the alcohol dehydrogenase ofD. gigas showed cross-reactivity with the alcohol dehydrogenase ofDesulfovibrio strain HDv and with cell extracts of six other ethanol-grown sulfate-reducing bacteria.     

Biosynthesis and cytoplasmic accumulation of a chlorinated catechol pigment during 3-chlorobenzoate aerobic co-metabolism in Pseudomonas fluorescens

A strain of Pseudomonas fluorescens was capable of co-metabolizing 3-chlorobenzoic acid with the production of a chlorinated catechol black pigment. A peroxidase and another enzymatic activity referred to as a polyphenol oxidase were found to be involved in the oxidation of 4-chlorocatechol to 4-chloro-1,2-benzoquinone, i.e. in the production of highly reactive substrates for pigment formation. Therefore, P. fluorescens cells were seen to take an active part not only in 3-chlorobenzoate mineralization but also in overall pigment production. pH was found to be a key parameter in the regulation of the activity of P. fluorescens oxidoreductive enzymes. Ultrastructural investigations showed that electron dense granules of pigment were distributed throughout the cytoplasm of Pseudomonas fluorescens cells grown in presence of 3-chlorobenzoate, as confirmed also by Thiéry cytochemical investigations.In these cells, an extensive contraction of the cytoplasm as well as a significant damage to the cell wall after two days of incubation, suggested that pigment production caused a premature death of the cells accompanied by the leakage of the cell content. Pigment production seemed to occur mostly in the cytoplasmic context where the electron dense material accumulates until it is released in the medium after the cell lysis.Abbreviations 3-CBA 3-chlorobenzoic acid - BA benzoic acid - 4-CC 4-chlorocatechol - 3-CC 3-chlorocatechol - MBTH 3-methyl-2-benzothiazolinone hydrazone - l-DOPA l-3,4-dihydroxyphenyl-alanine - SPB sodium phosphate buffer     

Dioxygenase activity and relative behaviour of Pseudomonas strains from soil in the presence of different aromatic compounds

Ten different Pseudomonas strains isolated from contaminated soils were tested for expression of active dioxygenases. Of these, two different clusters, related to strain origin were observed. The first included two P. fluorescens strains and two P. aeruginosa strains isolated from soils polluted with polyaromatic hydrocarbons and the second two P. cepacia strains and four P. chlororaphis strains from soils with polyphenols. All the isolates showed catechol 1,2-dioxygenase basal activity, while other dioxygenases (catechol 2,3-dioxygenase, protocatechuate 2,3-, 3,4- and 4,5-dioxygenases) were detected only after growth in the presence of suitable inducers (benzoate, catechol, salicylate, phenol). Significant induction of catechol 1,2-dioxygenase, the major activity of the tested strains, was also observed when combining starvation with the presence of high molecular weight aromatic hydrocarbons with recalcitrant structures (fluoranthene, chrysene, benzanthracene, pyrene).     

Specific detection of an oil-degrading bacterium, Corynebacterium sp. IC10, in sand microcosms by PCR using species-specific primers based on 16S rRNA gene sequences

A species-specific PCR technique to detect an oil-degrading bacterium, Corynebacterium sp. IC10, released into sand microcosms is described. PCR primers, specific to strain IC10, were designed based on 16S rRNA gene sequences and tested against both closely and distantly related bacterial strains using four primer combinations involving two forward and two reverse primers. Two sets of them were specific to the strain IC10 and Corynebacterium variabilis and one set was selected for further analysis. The PCR amplification was able to detect 1 pg template DNA of strain IC10 and 1.2×10⁴ c.f.u. of IC10 ml wet sand^–1 in the presence of 3×10⁸ Escherichia coli cells. In non-sterile sand microcosms seeded with the strain IC10, the sensitivity of detection decreased to 9.6×10⁵ c.f.u. ml wet sand^–1. The detection sensitivity thus depends on the complexity of background heterogeneous DNA of environmental samples. The assay is suitable for detection of Corynebacterium sp. IC10 in laboratory microcosms, however, cross reaction with non-oil degrading coryneforms may prohibit its use in uncharacterized systems.     

Microbial Metabolism of Quinoline by Comamonas sp.

An aerobic bacterial strain which can use quinoline as the sole carbon and energy source has been isolated from activated sludge and identified as Comamonas sp. The microbial metabolism of quinoline by this strain has been investigated. A pH 8 and a temperature of 30 °C were the optimum degradation conditions of quinoline. Five intermediates including 2-oxo-1,2-dihydroquinoline, 5-hydroxy-6-(2-carboxyethenyl)-1H-2-pyridone, 6-hydroxy-2-oxo-1,2-dihydroquinoline, 5,6-dihydroxy-2-oxo-1,2-dihydroquinoline, and 8-hydroxy-2-oxo-1,2-dihydroquinoline were found during quinoline biodegradation. The presence of these intermediates suggested that at least two pathways were involved for quinoline degradation by Comamonas sp. and a reasonable degradation route was proposed to account for the intermediates observed. This revised version was published online in July 2006 with corrections to the Cover Date.     

Arrest of cell cycle by inhibition of ribonucleotide reductase induces accumulation of NAD+ by Mn2+-supplemented growth of Corynebacterium ammoniagenes

Cell division of the wild type strain Corynebacterium (formerly Brevibacterium) ammoniagenes ATCC 6872 which requires 1 M Mn²⁺ for balanced growth was inhibited by addition of 20 mM hydroxyurea (HU) or 10 mM p-methoxyphenol (MP) to a Mn²⁺-supplemented fermentation medium at an appropriate time. Scanning electron microscopy (SEM) showed a restricted elongation characteristic of arrest of the cell cycle in coryneform bacteria. The cultures treated with HU or MP had, respectively, a fourfold or sixfold enhanced accumulation of NAD⁺ by a salvage biosynthetic pathway. An assay of nucleotide-permeable cells for ribonucleotide reductase activity using [³H-CDP] as substrate revealed a pre-early and complete decline of DNA precursor biosynthesis not found in the untreated control. Overproduction of NAD⁺ is an alternative to the conventional fermentation process using Mn²⁺ deficiency. A simple model is presented to discuss the metabolic regulation of the new process based on the presence of a manganese ribonucleotide reductase (Mn-RNR) in the producing strain.     

Molecular genetics and evolutionary relationship of PCB-degrading bacteria

Biphenyl-utilizing soil bacteria are ubiquitously distributed in the natural environment. They cometabolize a variety of polychlorinated biphenyl (PCB) congeners to chlorobenzoic acids through a 2,3-dioxygenase pathway, or alternatively through a 3,4-dioxygenase system. Thebph genes coding for the metabolism of biphenyl have been cloned from several pseudomonads. The biochemistry and molecular genetics of PCB degradation are reviewed and discussed from the viewpoint of an evolutionary relationship.Abbreviations BP biphenyl - bph BP/PCB-degradative gene - 23DHBP 2,3-dihydroxybiphenyl - HPDA 2-hydroxy-6-oxo-6-phenylhexa 2,4-dienoic acid - KF707 P. pseudoalcaligenes strain KF707 - LB400 Pseudomonas sp. strain LB400 - PCB polychlorinated biphenyls - Q1 P. paucimobilis strain Q1tod; toluene catabolic gene     

Degradation of polychlorinated phenols by Streptomyces rochei 303

The strain Streptomyces rochei 303 (VKM Ac-1284D) is capable of utilizing 2-chloro-,2,4-,2,6-dichloro- and 2,4,6-trichlorophenols as the sole source of carbon. Its resting cells completely dechlorinated and degraded 2-, 3-chloro-; 2,4-, 2,6-, 2,3-, 2,5-, 3,4-, 3,5-dichloro-; 2,4-, 2,6-dibromo-; 2,4,6-, 2,4,5-, 2,3,4-, 2,3,5-, 2,3,6-trichlorophenols; 2,3,5,6-tetrachloro- and pentachlorophenol. During chlorophenol degradation, a stoichiometric amount of chloride ions was released and chlorohydroquinols were formed as intermediates. In cell-free extracts of S. rochei, the activity of hydroxyquinol 1,2-dioxygenase was found. The enzyme was induced with chlorophenols. Of all so far described strains degrading polychlorophenols, S. rochei 303 utilized a wider range of chlorinated phenols as the sole sourse of carbon and energy.Abbreviations CP chlorophenol - DCP dichlorophenol - TCP trichlorophenol - TeCP tetrachlorophenol - PCP pentachlorophenol - DBrP dibromophenol - CHQ chlorohydroquinol - DCHQ dichlorohydroquinol - HHQ hydroxyhydroquinol - CHHQ chlorohydroxyhydroquinol - CC chlorocatechol - TLC thin layer chromatography - GC/MC chromato-mass-spectrometry - HPLC high-performance liquid chromatography     

A novel enantioselective epoxide hydrolase for (R)-phenyl glycidyl ether to generate (R)-3-phenoxy-1,2-propanediol

Bacillus sp. Z018, a novel strain producing epoxide hydrolase, was isolated from soil. The epoxide hydrolase catalyzed the stereospecific hydrolysis of (R)-phenyl glycidyl ether to generate (R)-3-phenoxy-1,2-propanediol. Epoxide hydrolase from Bacillus sp. Z018 was inducible, and (R)-phenyl glycidyl ether was able to act as an inducer. The fermentation conditions for epoxide hydrolase were 35°C, pH 7.5 with glucose and NH₄Cl as the best carbon and nitrogen source, respectively. Under optimized conditions, the biotransformation yield of 45.8% and the enantiomeric excess of 96.3% were obtained for the product (R)-3-phenoxy-1,2-propanediol.     

Conversion of α1,2-mannosidase E-I from Candida albicans to α1,2-mannosidase E-II by limited proteolysis

Previous studies demonstrated the presence in Candida albicans ATCC 26555 of two soluble α1,2-mannosidases: E-I and E-II. In contrast, in the C. albicans CAI-4 mutant only E-I was detected and it could be processed by a membrane-bound proteolytic activity from the ATCC 26555 strain, generating an active 43 kDa polypeptide. Here, α1,2-mannosidase E-I from strain ATCC 26555 was purified by conventional methods of protein isolation and affinity chromatography in Concanavalin A-Sepharose 4B. Analytical electrophoresis of the purified enzyme revealed two polypeptides of 52 and 23 kDa, the former being responsible for enzyme activity as revealed by zymogram analysis. Time course proteolysis with an aspartyl protease from Aspergillus saitoi, converted α1,2-mannosidase E-I into an active polypeptide of 43 kDa which trimmed Man₉GlcNAc₂, generating Man₈GlcNAc₂ isomer B and mannose. Trimming was inhibited preferentially by 1-deoxymannojirimycin. Both, the molecular mass and the enzyme properties of the proteolytic product were identical to those described for α1,2-mannosidase E-II therefore supporting the notion that E-I is the precursor of E-II.     

Sarcomelicope alkaloids as leads for the discovery of new antitumor acronycine derivatives

The acridone alkaloid acronycine first isolated from Acronychia baueri Schott (Rutaceae) in 1948, was later shown to exhibit a promising activity against a broad spectrum of solid tumors. Nevertheless, clinical trials only gave poor results, probably due to the moderate potency and low water solubility of this alkaloid. Early studies on structure-activity relationships in the series concluded that the 1,2-double bond was an essential structural requirement to observe cytotoxic activity. It is the reason why the isolation in our laboratory of the unstable acronycine epoxide from several New-Caledonian Sarcomelicope species led to the hypothesis of bioactivation of acronycine by transformation of the 1,2-double bond into the corresponding oxirane in vivo. Consequently, there was interest in the search for acronycine derivatives modified in the pyran ring and having improved stability, but a similar reactivity toward nucleophilic agents as acronycine epoxide. Accordingly, we synthesized a series of cis- and trans-1,2-dihydroxy-1,2-dihydroacronycine diesters which exhibited interesting antitumor properties with a broadened spectrum of activity and increased potency when compared with acronycine. (±)-Cis-1,2-diacetoxy-1,2-dihydroacronycine was of particular interest, due to its marked activity in vivo against the resistant solid tumor C 38 colon carcinoma. The demonstration that acronycine should interact with DNA by some noncovalent process able to stabilize the double helix against thermal denaturation prompted us to develop benzo[b]acronycine analogues possessing an additional aromatic ring linearly fused on the natural alkaloid basic skeleton. When tested against a panel of cancer cell lines in vitro, cis-1,2-dihydroxy-1,2-dihydrobenzo[b]acronycine diesters exhibited cytotoxic activities within the same range of potency as the most active drugs currently used in cancer chemotherapy. In vivo, cis-1,2-diacetoxy-1,2-dihydrobenzo[b]acronycine (S23906-1), selected for further preclinical development, demonstated a marked antitumor activity in human orthotopic models of lung, ovarian and colon cancers xenografted in nude mice. This revised version was published online in June 2006 with corrections to the Cover Date.     

Degradation of low rank coal by Trichoderma atroviride ES11

A new isolate of Trichoderma atroviride has been shown to grow on low rank coal as the sole carbon source. T. atroviride ES11 degrades ∼82% of particulate coal (10 g l⁻¹) over a period of 21 days with 50% reduction in 6 days. Glucose (5 g l⁻¹) as a supplemented carbon source enhanced the coal solubilisation efficiency of T. atroviride ES11, while 10 and 20 g l⁻¹ glucose decrease coal solubilisation efficiency. Addition of nitrogen [1 g l⁻¹ (NH₄)₂SO₄] to the medium also increased the coal solubilisation efficiency of T. atroviride ES11. Assay results from coal-free and coal-supplemented cultures suggested that several intracellular enzymes are possibly involved in coal depolymerisation processes some of which are constitutive (phenol hydroxylase) and others that were activated or induced in the presence of coal (2,3-dihydrobiphenyl-2,3-diol dehydrogenase, 3,4-dihydro phenanthrene-3,4-diol dehydrogenase, 1,2-dihydro-1,2-dihydroxynaphthalene dehydrogenase, 1,2-dihydro-1,2-dihydroxyanthracene dehydrogenase). GC-MS analysis of chloroform extracts obtained from coal degrading T. atroviride ES11 cultures showed the formation of only a limited number of specific compounds (4-hydroxyphenylethanol, 1,2-benzenediol, 2-octenoic acid), strongly suggesting that the intimate association between coal particles and fungal mycelia results in rapid and near-quantitative transfer of coal depolymerisation products into the cell. An erratum to this article can be found at     

A Glutathione S-Transferase with Activity towards cis-1,2-Dichloroepoxyethane Is Involved in Isoprene Utilization by Rhodococcus sp. Strain AD45

Rhodococcus sp. strain AD45 was isolated from an enrichment culture on isoprene (2-methyl-1,3-butadiene). Isoprene-grown cells of strain AD45 oxidized isoprene to 3,4-epoxy-3-methyl-1-butene, cis-1,2-dichloroethene to cis-1,2-dichloroepoxyethane, and trans-1,2-dichloroethene to trans-1,2-dichloroepoxyethane. Isoprene-grown cells also degraded cis-1,2-dichloroepoxyethane and trans-1,2-dichloroepoxyethane. All organic chlorine was liberated as chloride during degradation of cis-1,2-dichloroepoxyethane. A glutathione (GSH)-dependent activity towards 3,4-epoxy-3-methyl-1-butene, epoxypropane, cis-1,2-dichloroepoxyethane, and trans-1,2-dichloroepoxyethane was detected in cell extracts of cultures grown on isoprene and 3,4-epoxy-3-methyl-1-butene. The epoxide-degrading activity of strain AD45 was irreversibly lost upon incubation of cells with 1,2-epoxyhexane. A conjugate of GSH and 1,2-epoxyhexane was detected in cell extracts of cells exposed to 1,2-epoxyhexane, indicating that GSH is the physiological cofactor of the epoxide-transforming activity. The results indicate that a GSH S-transferase is involved in the metabolism of isoprene and that the enzyme can detoxify reactive epoxides produced by monooxygenation of chlorinated ethenes.     

Co-metabolism of di- and trichlorobenzoates in a 2-chlorobenzoate-degrading bacterial culture: Effect of the position and number of halo-substituents

The degradative properties towards chlorobenzoates by a 2-chlorobenzoate-degrading mixed culture (2MC) were investigated. Although 2MC did not grow on 2,3,5-; 2,3,6- and 2,4,6-trichlorobenzoates, it was able to completely oxidise 2,3,5-trichlorobenzoate and 2,5-dichlorobenzoate. This was degraded through the intermediate formation of 4-chlorocatechol and 3-cis,cis-chloromuconate, suggesting a dioxygenation in 1,2 position. 4-Chlorobenzoate; 3,4- and 2,6-dichlorobenzoate; 2,4,6- and 2,3,6-trichlorobenzoate did not undergo any co-metabolic transformation, the only 2,4-dichlorobenzoate was scarcely transformed into a dichlorinated phenol as end-product. 2MC was constituted of three prominent species: Stenotrophomonas maltophilia, Cupriavidus necator and Flavobacterium sp. Ring-hydroxylating dioxygenase genes (BenA) were retrieved in S. maltophilia and C. necator, indicating the presence of a “modified ortho pathway” in the culture. On the basis of its degradative properties, 2MC could be a good candidate for use in the removal of ortho- and/or meta-chlorobenzoates that are the major end-products of PCB co-metabolism.     

Loss of sulfide adaptation ability in a thermophilic Oscillatoria

A spontaneous variant incapable of anoxygenic photosynthesis was derived from a fully competent strain of Oscillatoria amphigramulata which was originally isolated from a high sulfide-containing hot spring of New Zealand. Although the variant (Oa-2) acquired a slight ability to photosynthesize in the presence of 0.3–0.4 mM sulfide, this was only after a 24 h exposure to sulfide and represented oxygenic photosynthesis only. Unlike the parent strain, the incompetent variant never grew in the presence of sulfide >0.05 mM, nor was there any relief of the inhibition by DCMU [3-(3,4-dichlorophenyl)-1,1-dimethylurea] of CO₂ photoincorporation when sulfide was present. The variant strain has retained all of these characteristics over a 4 year period with monthyl transfers in non-sulfide medium. The wild type, under identical conditions, has retained all of its competence with respect to sulfide.Abbreviations DCMU 3-(3,4-dichlorophenyl)-1,1-dimethylurea     

Induction of phenoloxidase in cell suspension cultures of Mucuna pruriens L.

The effects of limitating nitrogen-containing compounds in the medium and of adding the amino-acid analogues p-fluorophenylalanine and ethionine on both phenoloxidase activity and the accumulation of L-3,4-dihydroxyphenylalanine (L-DOPA) are reported for cell suspension cultures of Mucuna pruriens. Nitrogen limitation of the cultures, or the addition of p-fluorophenylalanine or ethionine to the culture medium resulted in an increased phenoloxidase activity. There appeared to be an inverse relationship between phenoloxidase activity and the acccumulation of L-tyrosine into L-DOPA by alginate-entrapped cells occurred at a higher rate when phenoloxidase activity was increased.Abbreviations pFPA p-fluorophenylalanine - L-DOPA L-3,4-dihydroxyphenylalanine