Tetrachloroethene metabolism of Dehalospirillum multivorans

Dehalospirillum multivorans is a strictly anaerobic bacterium that is able to dechlorinate tetrachloroethene (perchloroethylene; PCE) via trichloroethene (TCE) to cis-1,2-dichloroethene (DCE) as part of its energy metabolism. The present communication describes some features of the dechlorination reaction in growing cultures, cell suspensions, and cell extracts of D. multivorans. Cell suspensions catalyzed the reductive dechlorination of PCE with pyruvate as electron donor at specific rates of up to 150 nmol (chloride released) min^-1 (mg cell protein)^-1 (300 M PCE initially, pH 7.5, 25°C). The rate of dechlorination depended on the PCE concentration; concentrations higher than 300 M inhibited dehalogenation. The temperature optimum was between 25 and 30°C; the pH optimum at about 7.5. Dehalogenation was sensitive to potential alternative electron acceptors such as fumarate or sulfur; nitrate or sulfate had no significant effect on PCE reduction. Propyl iodide (50 M) almost completely inhibited the dehalogenation of PCE in cell suspensions. Cell extracts mediated the dehalogenation of PCE and of TCE with reduced methyl viologen as the electron donor at specific rates of up to 0.5 mol (chloride released) min^-1 (mg protein).^-1 An abiotic reductive dehalogenation could be excluded since cell extracts heated for 10 min at 95°C were inactive. The PCE dehalogenase was recovered in the soluble cell fraction after ultracentrifugation. The enzyme was not inactivated by oxygen.Abbreviations PCE Perchloroethylene or tetrachloroethene - TCE Trichloroethene - DCE cis-1,2-Dichloroethene - CHC Chlorinated hydrocarbon - MV Methyl viologen     

Lithotrophic growth ofSulfurospirillum deleyianum with sulfide as electron donor coupled to respiratory reduction of nitrate to ammonia

Sulfurospirillum deleyianum grew in batch culture under anoxic conditions with sulfide (up to 5 mM) as electron donor, nitrate as electron acceptor, and acetate as carbon source. Nitrate was reduced to ammonia via nitrite, a quantitatively liberated intermediate. Four moles of sulfide were oxidized to elemental sulfur per mole nitrate converted to ammonia. The molar growth yield per mole sulfide consumed, Y_m, was 1.5 ± 0.2 g mol^–1 for the reduction of nitrate to ammonia. By this type of metabolism, S. deleyianum connected the biogeochemical cycles of sulfur and nitrogen. The sulfur reductase activity in S. deleyianum was inducible, as the activity depended on the presence of sulfide or elemental sulfur during cultivation with nitrate or fumarate as electron acceptor. Hydrogenase activity was always high, indicating that the enzyme is constitutively expressed. The ammonia-forming nitrite reductase was an inducible enzyme, expressed when cells were cultivated with nitrate, nitrite, or elemental sulfur, but repressed after cultivation with fumarate. Received: 13 March 1995 / Accepted: 29 May 1995     

Data consistency,yield and maintenance coefficient for the growth of Candida lypoytica and Pseudomonas aeruginosa on n-hexadecane

Summary When more than the minimum number of variables are measured, and measurement error is taken into account, the results of parameter estimation depend on which of the measured variables are selected for this purpose. The reparameterization of Pirt's models for growth produces multiresponse models with common parameters. By using the covariate adjustment technique, a unit variate linear model with covariates is obtained. This allows a combined point and interval estimates of biomass energetic yield and maintenance coefficient to be obtained using standard multiple regression programmes. When this method was applied using form I and form II of the Pirt's models, good combined estimates were obtained and compared. Using data from the literature for Candida lipolytica produced reliable results. However, for Pseudomonas aeruginosa, which has been known to produce intermediate products, a modified Pirt's model is required for a good estimate of the biomass energetic yield.Nomenclature a Mole of ammonia per quantity of organic substrate containing 1 g atom carbon, g mole/g atom carbon - b Moles of oxygen per quantity of organic substrate containing 1 g atom carbon, g mole/g atom carbon - c Moles of water per quantity of organic substrate containing 1 g atom carbon, g mole/g atom carbon; no of covariates included in model - d Moles of carbon dioxide per quantity of organic substrate containing 1 g atom carbon, g mole/g atom carbon - e _i Error terms in Eqs. (6–8) - l Atomic ratio of oxygen to carbon in organic substrate, dimensionless - m Atomic ratio of hydrogen to carbon in organic substrate, dimensionless - m _e Rate of organic substrate consumption for maintenance, g equiv. of available electrons in biomass (h) or kcal/Kcal of biomass(h) - n Atomic ratio of oxygen to carbon in biomass, dimensionless - p Atomic ratio of hydrogen to carbon in biomass, dimensionless - Q _{CO 2} Rate of evolution of carbon dioxide, g moles/g dry wt (h) - Q _{O 2} Rate of oxygen consumption, g moles/g dry wt (h) - Q _s Rate of organic substrate consumption g/g dry wt (h) - q Atomic ratio of nitrogen to carbon in biomass, dimensionless - r Atom ratio of hydrogen to carbon in products, dimensionless; the number of parameters of interest - s Atomic ratio of oxygen to carbon in products, dimensionless - t Atomic ratio of nitrogen to carbon in products, dimensionless - r Mean of k responses in Eq. (10) - x _ki Kth response in the ith observation - y _c Biomass carbon yield (fraction of organic substrate carbon in biomass), dimensionless - z _i Covariate matrix - z Fraction of organic substrate carbon in products, dimensionless - a _i Parameters associated with covariates - _s Reductance degree of biomass, equivalents of available electrons per gram atom carbon - Reductance degree of organic substrate, equivalents of available electrons per gram atom carbon - Fraction of energy in organic substrate which is evolved as heat, dimensionless - Fraction of available electrons transferred to biomass; biomass energetic yield - True growth yield - Specific growth rate, h^-1 - _p Fraction of available electrons incorporated into products; product energetic yield - Correlation coefficient - Mass fraction carbon - ² Mean square error of model (10)     

Tetrachloroethene reductive dehalogenase of Dehalospirillum multivorans: substrate specificity of the native enzyme and its corrinoid cofactor

The substrate specificity of the tetrachloroethene reductive dehalogenase of Dehalospirillum multivoransand its corrinoid cofactor were studied. Besides reduced methyl viologen, titanium(III) citrate could serve as electron donor for reductive dehalogenation of tetrachloroethene (PCE) and trichloroethene to cis-1,2-dichloroethene. In addition to chlorinated ethenes, chlorinated propenes were reductively dechlorinated solely by the native enzyme. trans-1,3-Dichloropropene, 1,1,3-trichloropropene and 2,3-dichloropropene were reduced to a mixture of mono-chloropropenes, 1,1-dichloropropene, and 2-chloropropene, respectively. Other halogenated compounds that were rapidly reduced by the enzyme were also dehalogenated abiotically by the heat-inactivated enzyme and by commercially available cyanocobalamin. The rate of this abiotic reaction was dependent on the number and type of halogen substituents and on the type of catalyst. The corrinoid cofactor purified from the tetrachloroethene dehalogenase of D. multivorans exhibited an activity about 50-fold higher than that of cyanocobalamin (vitamin B(12)) with trichloroacetate as electron acceptor, indicating that the corrinoid cofactor of the PCE dehalogenase is not cyanocobalamin. Corrinoids catalyzed the rapid dehalogenation of trichloroacetic acid. The rate was proportional to the amount of, e.g. cyanocobalamin; therefore, the reductive dehalogenation assay can be used for the sensitive and rapid quantification of this cofactor.     

Properties of tetrachloroethene and trichloroethene dehalogenase of Dehalospirillum multivorans

Some properties of tetrachloroethene and trichloroethene dehalogenase of the recently isolated, tetrachloroethene-utilizing anaerobe, Dehalospirillum multivorans, were studied with extracts of cells grown on pyruvate plus fumarate. The dehalogenase catalyzed the oxidation of reduced methyl viologen with tetrachloroethene (PCE) or trichloroethene (TCE) as electron acceptor. All other artificial or physiological electron donors tested were ineffective. The PCE and TCE dehalogenase activity was insensitive towards oxygen in crude extracts. When extracts were incubated under anoxic conditions in the presence of titanium citrate as reducing agent, the dehalogenase was rapidly inactivated by propyl iodide (50 M). Inactivation did not occur in the absence of titanium citrate. The activity of propyl-iodide-treated extracts was restored almost immediately by illumination. The dehalogenase was inhibited by cyanide. The inhibition profile was almost the same under oxic and anoxic conditions independent of the presence or absence of titanium citrate. In addition, N₂O, nitrite, and ethylene diamine tetra-acetate (EDTA) were inhibitors of PCE and TCE dehalogenase. Carbon monoxide and azide had no influence on the dehalogenase activity. Trans-1,2-dichloroethene or 1,1-dichloroethene, both of which are isomers of the dechlorination product cis-1,2-dichloroethene, neither inhibited nor inactivated the dehalogenase. PCE and TCE dechlorination appeared to be mediated by the same enzyme since the inhibitors tested had nearly the same effects on the PCE and TCE dehalogenating activity. The data indicated the involvement of a corrinoid and possibly of an additional transition metal in reductive PCE and TCE dechlorination.Abbreviations PCE Tetrachloroethene - TCE Trichloroethene - DCE Dichloroethene - EDTA Ethylene diamine tetra-acetate - MV Methyl viologen - BV Benzyl viologen - PI Propyl iodide, 1-iodopropane - TC Titanium(III) citrate     

Dehalogenation of chlorinated aromatic compounds using a hybrid bioinorganic catalyst on cells of <Emphasis Type="Italic">Desulfovibrio desulfuricans</Emphasis>

A novel bioinorganic catalyst was obtained via reduction of Pd(II) to Pd⁰ on to the surface of cells of Desulfovibrio desulfuricans at the expense of H₂. Palladised biomass, supplied with formate or H₂ as an electron donor, catalysed the dehalogenation of 2-chlorophenol and polychlorinated biphenyls. In the example of 2,3,4,5-tetrachlorobiphenyl, the bioinorganic catalyst promoted a rate of chloride release of 9.33 ± 0.17 nmol min^–1 mg ^–1and only ~5% of this value was obtained using chemically reduced or commercially available Pd ⁰. In the case of 2,2,4,4,6,6-hexachlorobiphenyl the rate was more than four orders of magnitude faster than the degradation reported using a sulfidogenic culture. Negligible chloride release occurred from any of the chloroaromatic compounds using biomass alone, or from palladised biomass challenged with hexane carrier solvent only. Analysis of the spent solution showed that in addition to catalysis of reductive dehalogenation the new material was able to remove very effectively the organic residua, with neither any PCB nor any breakdown products identifiable by GC/MS.Revisions requested 8 September 2004; Revisions received 21 October 2004;     

Studies on hydrogenase activity and chlorobenzene respiration in <Emphasis Type="Italic">Dehalococcoides</Emphasis> sp. strain CBDB1

Hydrogen oxidation and electron transport were studied in the chlorobenzene-utilizing anaerobe Dehalococcoides sp. strain CBDB1. While Cu²⁺ and Hg²⁺ ions irreversibly inhibited hydrogenase activity in intact cells, Ni²⁺ ions inhibited reversibly. About 80% of the initial hydrogenase activity was inactivated within 30 s when the cells were exposed to air. In contrast, hydrogenase was active at a redox potential of +10 mV when this redox potential was established anoxically with a redox indicator. Viologen dyes served both as electron acceptor for hydrogenase and electron donor for the dehalogenase. A menaquinone analogue, 2,3-dimethyl 1,4-naphthoquinone, served neither as electron acceptor for the hydrogenase nor as electron donor for the dehalogenase. In addition, the menaquinone antagonist 2-n-heptyl-4-hydroxyquinoline-N-oxide had no effect on dechlorination catalyzed by cell suspensions or isolated membranes with hydrogen as electron donor, lending further support to the notion that menaquinone is not involved in electron transport. The ionophores tetrachlorosalicylanilide and carbonylcyanide m-chlorophenylhydrazone did not inhibit dechlorination by cell suspensions, indicating that strain CBDB1 does not require reverse electron transport. The ATP-synthase inhibitor N,N-dicyclohexylcarbodiimide inhibited the dechlorination reaction with cell suspensions; however, the latter effect was partially relieved by the addition of tetrachlorosalicylanilide. 1,2,3,4-Tetrachlorobenzene strongly inhibited dechlorination of other chlorobenzenes by cell suspensions with hydrogen as electron donor, but it did not interfere with either hydrogenase or dehalogenase activity.     

Molecular characterization of the enzymes involved in the degradation of a brominated aromatic herbicide

Dehalogenation is the key step in the degradation of halogenated aromatics, while reductive dehalogenation is originally thought to rarely occur in aerobes. In this study, an aerobic strain of Comamonas sp. 7D‐2 was shown to degrade the brominated aromatic herbicide bromoxynil completely and release two equivalents of bromides under aerobic conditions. The enzymes involved in the degradation of bromoxynil to 4‐carboxy‐2‐hydroxymuconate‐6‐semialdehyde, including nitrilase, reductive dehalogenase (BhbA), 4‐hydroxybenzoate 3‐monooxygenase and protocatechuate 4,5‐dioxygenase, were molecularly characterized. The novel dehalogenase BhbA was shown to be a complex of a respiration‐linked reductive dehalogenase (RdhA) domain and a NAD(P)H‐dependent oxidoreductase domain and to have key features of anaerobic respiratory RdhAs, including two predicted binding motifs for [4Fe‐4S] clusters and a close association with a hydrophobic membrane protein (BhbB). BhbB was confirmed to anchor BhbA to the membrane. BhbA was partially purified and found to use NAD(P)H as electron donors. Full‐length bhbA homologues were found almost exclusively in marine aerobic proteobacteria, suggesting that reductive dehalogenation occurs extensively in aerobes and that bhbA is horizontally transferred from marine microorganisms. The discovery of a functional reductive dehalogenase and ring‐cleavage oxygenases in an aerobe opens up possibilities for basic research as well as the potential application for bioremediation.     

pH-dependent photoreactions of the high- and low-potential forms of cytochrome b559 in spinach PS II-enriched membranes

Cytochrome b559 (Cyt b559) is a well-known intrinsic component of Photosystem II (PS II) reaction center in all photosynthetic oxygen-evolving organisms, but its physiological role remains unclear. This work reports the response of the two redox forms of Cyt b559 (i.e. the high- (HP) and low-potential (LP) forms) to inhibition of the donor or acceptor side of PS II. The photooxidation of HP Cyt b559 induced by red light at room temperature was pH-dependent under conditions in which electron flow from water was diminished. This photooxidation was observed only at pH values higher than 7.5. However, in the presence of 1 M CCCP, a limited oxidation of HP Cyt b559 was observed at acidic pH, At pH 8.5 and in the presence of the protonophore, this photooxidation of the HP form was accompanied by its partial transformation into the LP form. On the other hand, a partial photoreduction of LP Cyt b559 was induced by red light under aerobic conditions when electron transfer through the primary quinone acceptor Q_A was impaired by strong irradiation in the presence of DCMU. This photoreduction was enhanced at acidic pH values. To the best of our knowledge, this is the first time that both photoreduction and photooxidation of Cyt b559 is described under inhibitory conditions using the same kind of membrane preparations. A model accommodating these findings is proposed.Abbreviations CCCP carbonylcyanide 3-chlorophenylhydrazone - Cyt cytochrome - DCBQ 2,5-dichloro-p-benzoquinone - DCMU dichlorophenyldimethylurea - E _m midpoint redox potential - HP and LP high- and low-potential forms of Cyt b559 - P680 primary donor - I_A acceptor side inhibition - I_D donor side inhibition - Pheo pheophytin - PS II photosystem II - Q_A primary quinone acceptor of PS II - Q_B secondary quinone acceptor of PS II     

Application of material and energy balances in the interpretation of intermediate product build-up in batch growth of Pseudomonas aeruginosa on n-hexadecane

Summary This work is concerned with the application of material and energy balances in an attempt to understand the phenomenon of product build-up when Pseudomonas aeruginosa is grown on n-hexadecane in a batch fermentor. It is shown that the organism accumulates a polyactide, called poly-B-hydroxybutyrate (PHB) during early stages of growth and metabolizes it at later stages of growth. This explains the low carbon and available electron balances which have been observed.Nomenclature d Moles of carbon dioxide per quantity of organic substrate containing one g atom carbon, g mole/g atom carbon - m _e Rate of organic substrate consumption for maintenance, g equiv. of available electrons/g equiv. of available electrons in biomass (h) - Specific rate of evolution of carbon dioxide, g moles/g dry wt (h) - Specific rate of oxygen consumption, g mole/g dry wt (h) - s Organic substrate concentration, g/liter - t Time (h) - x Biomass concentration, g/liter - y _c Biomass carbon yield (fraction of organic substrate carbon in biomass), dimensionless - _b Reductance degree of biomass, equivalents of available electrons per g atom carbon - _s Reductance degree of substrate, equivalents of available electrons per g atom carbon - Fraction of energy in organic substrate which is evolved as heat, dimensionless - Fraction of energy in organic substrate which is coverted to biomass or biomass energetic yield, dimensionless - Specific growth rate, h^-1 - _b Weight fraction carbon in biomass, dimensionless - _s Weight fraction carbon in substrate, dimensionless     

Studies on tetrachloroethene respiration inDehalospirillum multivorans

Tetrachloroethene (PCE) respiration was studied in the tetrachloroethene-utilizing anaerobe,Dehalospirillum multivorans, with respect to localization of the catabolic enzymes, the electron carriers potentially involved in electron transport, and the response to ionophores and specific inhibitors. Hydrogenase and formate dehydrogenase were recovered in the periplasmic cell fraction and were membrane-associated. Electron-accepting tetrachloroethene dehalogenase was found in the cytoplasmic fraction. In the PCE dehalogenase assay, only artificial electron donors with a standard redox potential of <-360 mV were effective electron donors for PCE reduction. Besides these artificial reductants, ferredoxin isolated fromD. multivorans (E_o=-445 mV) could serve as electron donor for PCE reduction. However, the reaction rate with ferredoxin was only 1% of that with methyl viologen, whereas the pyruvate-ferredoxin oxidoreductase exhibited almost the same reaction rates with methyl viologen and ferredoxin as electron acceptors for pyruvate oxidation. Reduced menadione (2-methyl-1,4-naphthoquinone) did not serve as electron donor in the PCE dehalogenase reaction. 2-Heptyl-4-hydroxyquinoline-N-oxide (HOQNO) had no significant effect on PCE dechlorination in cell suspensions and in crude extracts. Whole cells catalyzed the reductive dechlorination of PCE with H₂ or formate as electron donors. The dechlorination in cell suspensions rather than in cell extracts was inhibited by the ionophores carbonylcyanide-p-(trifluoromethoxy)-phenylhydrazone (FCCP) and tetrachlorosalicylanilide (TCS), indicating that a membrane potential and/or a pH gradient may be required for the reaction in vivo.Abbreviations CTAB N-cetyl-trimethylammonium bromide - DCE cis-1,2-Dichloroethene - FCCP Carbonyl cyanide-p-(trifluoromethoxy)phenylhydrazone - Fd Ferredoxin - HOQNO 2-Heptyl-4-hydroxyquinoline-N-oxide - MV Methyl viologen - PCE Tetrachloroethene or perchloroethylene - Pyr Pyruvate - TCE Trichloroethene - TCS Tetrachlorosalicylanilide Dedicated to Prof. Achim Kröger on the occasion of his 60^th birthday, especially in honor of his excellent contributions to the elucidation of anaerobic respiration processes     

Purification and characterization of the tetrachloroethene reductive dehalogenase of strain PCE-S

The membrane-associated tetrachloroethene reductive dehalogenase from the tetrachloroethene-reducing anaerobe, strain PCE-S, was purified 165-fold to apparent homogeneity in the presence of the detergent Triton X-100. The purified dehalogenase catalyzed the reductive dechlorination of tetrachloroethene to trichloroethene and of trichloroethene to cis-1,2-dichloroethene with reduced methyl viologen as the electron donor, showing a specific activity of 650 nkat/mg protein. The apparent K _m values of the enzyme for tetrachloroethene, trichloroethene, and methyl viologen were 10 μM, 4 μM, and 0.3 mM, respectively. SDS-PAGE revealed a single protein band with an apparent molecular mass of 65 kDa. The apparent molecular mass of the native enzyme was 200 kDa as determined by gel filtration. Tetrachloroethene dehalogenase contained 0.7 ± 0.3 mol corrinoid, 1.0 ± 0.3 mol cobalt, 7.8 ± 0.5 mol iron, and 10.3 ± 2.0 mol acid-labile sulfur per mol subunit. The pH optimum was approximately 7.2, and the temperature optimum was approximately 50 °C. The dehalogenase was oxygen-sensitive with a half-life of approximately 50 min. The N-terminal amino acid sequence of the enzyme was determined, and no significant similarity was found to any part of the amino acid sequence of the tetrachloroethene (PCE) reductive dehalogenase from Dehalospirillum multivorans. Received: 4 December 1997 / Accepted: 10 February 1998     

Phenyl methyl ethers: novel electron donors for respiratory growth of<Emphasis Type="Italic"> Desulfitobacterium hafniense</Emphasis> and<Emphasis Type="Italic"> Desulfitobacterium</Emphasis> sp. strain PCE-S

Desulfitobacterium hafniense and Desulfitobacterium sp. strain PCE-S grew under anoxic conditions with a variety of phenyl methyl ethers as electron donors in combination with fumarate as electron acceptor. The phenyl methyl ethers were O-demethylated to the corresponding phenol compounds. O-demethylation was strictly dependent on the presence of fumarate; no O-demethylation occurred with CO₂ as electron acceptor. One mol phenyl methyl ether R-O-CH₃ was O-demethylated to R-OH per 3 mol fumarate reduced to succinate. The growth yields with vanillate or syringate plus fumarate were approximately 15 g cells (dry weight) per mol methyl moiety converted. D. hafniense utilized vanillate or syringate as an electron donor for reductive dehalogenation of 3-Cl-4-hydroxyphenylacetate, whereas strain PCE-S was not able to dechlorinate tetrachloroethene with phenyl methyl ethers. Crude extracts of both organisms showed O-demethylase activity in the O-demethylase assay with vanillate or syringate as substrates when the organism was grown on syringate plus fumarate. Besides the homoacetogenic bacteria, only growing cells of Desulfitobacterium frappieri PCP-1 have thus far been reported to be capable of phenyl methyl ether O-demethylation. This present study is the first report of Desulfitobacteria utilizing phenyl methyl ethers as electron donors for fumarate reduction and for growth.Abbreviations PCE Tetrachloroethene - TCE Trichloroethene - DCE cis-1,2-Dichloroethene - ClOHPA 3-Cl-4-Hydroxyphenylacetate - OHPA 4-Hydroxyphenylacetate - FH₄ Tetrahydrofolate     

Photoinactivation of the reactivation capacity of photosystem II in pea subchloroplast particles after a complete removal of manganese

After a complete removal of Mn from pea subchloroplast photosystem-II (PS II) preparations the electron phototransfer and oxygen evolution are restored upon addition of Mn²⁺ and Ca²⁺. Pre-illumination of the sample in the absence of Mn²⁺ leads to photoinhibition (PI) — irreversible loss of the capability of PS II to be reactivated by Mn²⁺. The effect of PI is considerably decreased in the presence of Mn²⁺ (4 Mn atoms per reaction center of PS II) and it is increased in the presence of ferricyanide or p-benzoquinone revealing the oxidative nature of the photoeffect. PI results in suppression of oxygen evolution, variable fluorescence, photoreduction of 2,6-dichlorophenol indophenol from either water or diphenylcarbazide. However, photooxidation of chlorophyll P₆₈₀, the primary electron donor of PS II as well as dark and photoinduced EPR signal II (ascribed to secondary electron donors D ₁ and Z) are preserved. PI is accompanied by photooxidation of 2–3 carotenoid molecules per PS II reaction center (RC) that is accelerated in the presence of ferricyanide and is inhibited upon addition of Mn²⁺ or diuron. The conclusion is made that PI in the absence of Mn leads to irreversible oxidative inactivation of electron transfer from water to RC of PS II which remains photochemically active. A loss of functional interaction of RC with the electron transport chain as a common feature for different types of PS II photoinhibition is discussed.Abbreviations A photoinduced absorbance changes - DPC diphenylcarbazide - DPIP 2,6-dichlorophenol indophenol - F _o constant fluorescence of chlorophyll - F photoinduced changes of Chl fluorescence yield - Mn manganese - P₆₈₀ the primary electron donor in PS II - PI photoinhibition - PS II photosystem II - Q the primary (quinone) electron acceptor in PS II - RC reaction center     

Effect of hydromechanical forces on the production of filamentous haemagglutinin and pertussis toxin ofBordetella pertussis

Summary The production ofBordetella pertussis extracytoplasmic filamentous haemagglutinin (FHA) and pertussis toxin (PT) in a bioreactor under stirring conditions was studied in order to investigate the effect of hydromechanical forces on yields of both antigens. It was shown that FHA loses its haemagglutinin activity when the power transmitted by the agitator and the aerator per unit volume increases, whereas PT production is not affected. The loss of FHA activity can be explained by the action of shear forces on the filamentous structure of this antigen.Nomenclature C^* dissolved oxygen saturation concentration - C₁ dissolved oxygen concentration - D impeller diameter - power transmitted by the agitator and the aerator per unit of liquid volume - E_m maximum local energy dissipation rate per unit of liquid volume - K_La volumetric oxygen transfer coefficient - N impeller speed - Pg power input in aerated system - qO₂m maximum specific oxygen consumption rate - R_e Reynold number (D²N /) - VVM volume of air per volume of fermentation broth per minute - Xm maximum of biomass concentration - o Kolmogorov-microscale - fermentation broth viscosity - fermentation broth kinematic viscosity - fermentation broth density - expt experiment     

Comparison of Energy and Growth Yields for Desulfitobacterium dehalogenans during Utilization of Chlorophenol and Various Traditional Electron Acceptors

Desulfitobacterium dehalogenans grew with formate as the electron donor and 3-chloro-4-hydroxyphenylacetate (3-Cl-4-OHPA) as the electron acceptor, yielding Y_X/formate, Y_X/2e⁻, and Y_X/ATP ranging from 3.2 to 11.3 g of biomass (dry weight)/mol, thus indicating that energy was conserved through reductive dechlorination. Pyruvate was utilized as the electron donor and acceptor, yielding stoichiometric amounts of acetate and lactate, respectively, and a Y_{X/reduced acceptor} of 13.0 g of biomass (dry weight)/mol. The supplementation of pyruvate-containing medium with additional electron acceptors, such as 3-Cl-4-OHPA, nitrate, fumarate, or sulfite, caused pyruvate to be replaced as the electron acceptor and nearly doubled the Y_X/ATP (Y_{X/acetate formed}). A comparison of the yields for 3-Cl-4-OHPA with those for other traditional electron acceptors indicates that the dehalogenation reaction led to the formation of similar amounts of energy equivalents. The various electron acceptors were used concomitantly with 3-Cl-4-OHPA in nonacclimated cultures, but the utilization rates and amounts utilized differed.     

Kinetic and equilibrium studies of the interactions of silver ions with poly(A)

The interaction of silver ions with poly(A) was studied by potentiometric titration, uv spectrophotometry, and stopped-flow spectroscopy. For 0 < r_b < 0.5, where r_b is moles of silver ion bound per mole of nucleotide base, there exists only one type of binding for poly(A). Using McGhee's theory, the binding parameters, such as intrinsic binding constant, number of sites per nucleotide, and cooperativity, were determined from the potentiometric titration data. Using the stopped-flow method, one relaxation time was observed in 0 < r₀ < 0.5, where r₀ is the moles of silver ions added per mole of nucleotide base. The concentration dependences of the relaxation time suggest that the binding of silver ions to poly(A) proceeds through the following mechanism: where M is free silver ions, P the free binding sites on poly(A), and C and C′ are two forms of the complex. The nature of the binding of silver ions to poly(A) is also discussed.