Many microorganisms, especially bacteria, produce biosurfactants when grown on water-immiscible substrates. Biosurfactants are more effective, selective, environmentally friendly, and stable than many synthetic surfactants. Most common biosurfactants are glycolipids in which carbohydrates are attached to a long-chain aliphatic acid, while others, like lipopeptides, lipoproteins, and heteropolysaccharides, are more complex. Rapid and reliable methods for screening and selection of biosurfactant-producing microorganisms and evaluation of their activity have been developed. Genes involved in rhamnolipid synthesis (rhlAB) and regulation (rhlI and rhlR) in Pseudomonas aeruginosa are characterized, and expression of rhlAB in heterologous hosts is discussed. Genes for surfactin production (sfp, srfA, and comA) in Bacillus spp. are also characterized. Fermentative production of biosurfactants depends primarily on the microbial strain, source of carbon and nitrogen, pH, temperature, and concentration of oxygen and metal ions. Addition of water-immiscible substrates to media and nitrogen and iron limitations in the media result in an overproduction of some biosurfactants. Other important advances are the use of water-soluble substrates and agroindustrial wastes for production, development of continuous recovery processes, and production through biotransformation. Commercialization of biosurfactants in the cosmetic, food, health care, pulp- and paper-processing, coal, ceramic, and metal industries has been proposed. However, the most promising applications are cleaning of oil-contaminated tankers, oil spill management, transportation of heavy crude oil, enhanced oil recovery, recovery of crude oil from sludge, and bioremediation of sites contaminated with hydrocarbons, heavy metals, and other pollutants. Perspectives for future research and applications are also discussed.

Microbial production of surfactants and their commercial potential.

Starting from known properties of non-specific salt effects on the surface tension at an air–water interface, we propose the first general, detailed qualitative molecular mechanism for the origins of ion-specific (Hofmeister) effects on the surface potential difference at an air–water interface; this mechanism suggests a simple model for the behaviour of water at all interfaces (including water–solute interfaces), regardless of whether the non-aqueous component is neutral or charged, polar or non-polar Specifically, water near an isolated interface is conceptually divided into three layers, each layer being 1 water-molecule thick We propose that the solute determines the behaviour of the adjacent first interfacial water layer ( I 1 ); that the bulk solution determines the behaviour of the third interfacial water layer ( I 3 ), and that both I 1 and I 3 compete for hydrogen-bonding interactions with the intervening water layer ( I 2 ), which can be thought of as a transition layer The model requires that a polar kosmotrope (polar water-structure maker) interact with I 1 more strongly than would bulk water in its place; that a chaotrope (water-structure breaker) interact with I 1 somewhat less strongly than would bulk water in its place; and that a non-polar kosmotrope (non-polar water-structure maker) interact with I 1 much less strongly than would bulk water in its place We introduce two simple new postulates to describe the behaviour of I 1 water molecules in aqueous solution The first, the ‘relative competition’ postulate, states that an I 1 water molecule, in maximizing its free energy (—δG), will favour those of its highly directional polar (hydrogen-bonding) interactions with its immediate neighbours for which the maximum pairwise enthalpy of interaction (—δ H ) is greatest; that is, it will favour the strongest interactions We describe such behaviour as ‘compliant’, since an I 1 water molecule will continually adjust its position to maximize these strong interactions Its behaviour towards its remaining immediate neighbours, with whom it interacts relatively weakly (but still favourably), we describe as ‘recalcitrant’, since it will be unable to adjust its position to maximize simultaneously these interactions The second, the ‘charge transfer’ postulate, states that the strong polar kosmotrope–water interaction has at least a small amount of covalent character, resulting in significant transfer of charge from polar kosmotropes to water–especially of negative charge from Lewis bases (both neutral and anionic); and that the water-structuring effect of polar kosmotropes is caused not only by the tight binding (partial immobilization) of the immediately adjacent ( I 1 ) water molecules, but also by an attempt to distribute among several water molecules the charge transferred from the solute When extensive, cumulative charge transfer to solvent occurs, as with macromolecular polyphosphates, the solvation layer (the layer of solvent whose behaviour is determined by the solute) can become up to 5- or 6-water-molecules thick We then use the ‘relative competition’ postulate, which lends itself to simple diagramming, in conjunction with the ‘charge transfer’ postulate to provide a new, startlingly simple and direct qualitative explanation for the heat of dilution of neutral polar solutes and the temperature dependence of relative viscosity of neutral polar solutes in aqueous solution This explanation also requires the new and intriguing general conclusion that as the temperature of aqueous solutions is lowered towards o °C, solutes tend to acquire a non-uniform distribution in the solution, becoming increasingly likely to cluster 2 water molecules away from other solutes and surfaces (the driving force for this process being the conversion of transition layer water to bulk water) The implications of these conclusions for understanding the mechanism of action of general (gaseous) anaesthetics and other important interfacial phenomena are then addressed

https://www.cambridge.org/core/services/aop-cambridge-core/content/view/S0033583500005369

The Hofmeister effect and the behaviour of water at interfaces.

Nitroaromatic compounds are released into the biosphere almost exclusively from anthropogenic sources. Some compounds are produced by incomplete combustion of fossil fuels; others are used as synthetic intermediates, dyes, pesticides, and explosives. Recent research revealed a number of microbial systems capable of transforming or biodegrading nitroaromatic compounds. Anaerobic bacteria can reduce the nitro group via nitroso and hydroxylamino intermediates to the corresponding amines. Isolates of Desulfovibrio spp. can use nitroaromatic compounds as their source of nitrogen. They can also reduce 2,4,6-trinitrotoluene to 2,4,6-triaminotoluene. Several strains of Clostridium can catalyze a similar reduction and also seem to be able to degrade the molecule to small aliphatic acids. Anaerobic systems have been demonstrated to destroy munitions and pesticides in soil. Fungi can extensively degrade or mineralize a variety of nitroaromatic compounds. For example, Phanerochaete chrysosporium mineralizes 2,4-dinitrotoluene and 2,4,6-trinitrotoluene and shows promise as the basis for bioremediation strategies. The anaerobic bacteria and the fungi mentioned above mostly transform nitroaromatic compounds via fortuitous reactions. In contrast, a number of nitroaromatic compounds can serve as growth substrates for aerobic bacteria. Removal or productive metabolism of nitro groups can be accomplished by four different strategies. (a) Some bacteria can reduce the aromatic ring of dinitro and trinitro compounds by the addition of a hydride ion to form a hydride-Meisenheimer complex, which subsequently rearomatizes with the elimination of nitrite. (b) Monooxygenase enzymes can add a single oxygen atom and eliminate the nitro group from nitrophenols. (c) Dioxygenase enzymes can insert two hydroxyl groups into the aromatic ring and precipitate the spontaneous elimination of the nitro group from a variety of nitroaromatic compounds. (d) Reduction of the nitro group to the corresponding hydroxylamine is the initial reaction in the productive metabolism of nitrobenzene, 4-nitrotoluene, and 4-nitrobenzoate. The hydroxylamines undergo enzyme-catalyzed rearrangements to hydroxylated compounds that are substrates for ring-fission reactions. Potential applications of the above reactions include not only the biodegradation of environmental contaminants, but also biocatalysis and synthesis of valuable organic molecules.

Biodegradation of Nitroaromatic Compounds

Heme-containing peroxidases secreted by fungi are a fascinating group of biocatalysts with various ecological and biotechnological implications. For example, they are involved in the biodegradation of lignocelluloses and lignins and participate in the bioconversion of other diverse recalcitrant compounds as well as in the natural turnover of humic substances and organohalogens. The current review focuses on the most recently discovered and novel types of heme-dependent peroxidases, aromatic peroxygenases (APOs), and dye-decolorizing peroxidases (DyPs), which catalyze remarkable reactions such as peroxide-driven oxygen transfer and cleavage of anthraquinone derivatives, respectively, and represent own separate peroxidase superfamilies. Furthermore, several aspects of the “classic” fungal heme-containing peroxidases, i.e., lignin, manganese, and versatile peroxidases (LiP, MnP, and VP), phenol-oxidizing peroxidases as well as chloroperoxidase (CPO), are discussed against the background of recent scientific developments.

New and classic families of secreted fungal heme peroxidases

Halogenated organic molecules can also arise as natural products in which the carbon -halogen bonds are generated enzymatically. To date, more than 4500 halogenated natural products have been discovered, 2 though it is likely to be a substantially incomplete inventory. Enzymatic incorporation of halogens during natural product assembly alters physical properties, including electronic and steric effects that can be consequential for determining the affinity and selectivity of interactions with biological targets. Many of the genes encoding such halogen-incorporating enzymes are embedded in specific biosynthetic gene clusters, enabling coordinate regulation to activate these secondary metabolite pathways. Biological halogenation occurs on a diverse array of organic scaffolds, from terpenes to polyketides to nonribosomal peptides. Within these scaffolds, halogen atoms are incorporated on aliphatic carbons, olefinic centers, and a wide variety of aromatic and heterocyclic rings. A recent inventory of halogen-containing natural products indicated 2300 organochlorines, 2100 organobromines, 120 organoiodines, and 30 organofluorines. 2 The larger representation of chlorinated and brominated metabolites probably reflects the abundance of chloride and bromide ions in microenvironments of terrestrial and marine producer organisms. A brief list of some chlorinated, brominated, and iodinated metabolites is noted below. Among the chlorinated natural products of therapeutic interest are vancomycin ( 1), rebeccamycin ( 2), chlortetracycline (3), and chloramphenicol ( 4; Figure 1A).3-6 The natural products1-3 carry chlorine groups on aromatic rings while chloramphenicol has a 2,2-dichloroacetyl group. As shown in Figure 1B, the cyanobacterial metabolite barbamide (5) has a trichloromethyl substituent and syringomycin E ( 6), produced by the phytotoxicPseudomonas syringae , is monochlorinated on the terminal methyl of a threonyl residue. 7,8 In the biocontrol agents pyrrolnitrin ( 7) and pyoluteorin (8; Figure 1C), also produced by Pseudomonas strains, pyrrole rings are monoand dichlorinated, respectively.9,10 Brominated metabolites are typically produced by marine microorganisms, and three such molecules are shown in Figure 2. The bromoterpene snyderol comes in three isomeric forms (9-11; R, â, and γ), reflecting three modes of quenching an intermediate carbocation. 11,12 Convolutamine A (12) has a tribromoanisole ring presumably reflecting three tandem bromination steps during maturation. 13 The terpenoid product laurallene ( 13) has two C-Br bonds, most notably the terminal bromoallene group. 14

Nature's Inventory of Halogenation Catalysts: Oxidative Strategies Predominate

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Biohalogenation : principles, basic roles, and applications

Peroxide oxidation of primary alcohols to aldehydes by chloroperoxidase catalysis.

Epoxidation of alkenes by chloroperoxidase catalysis.

The wax ester compositions produced by the action of Acinetobacter sp. HO1-N on n-alkanes (C16 through C20) were analyzed using capillary gas chromatography/mass spectrometry (GC/MS). The wax esters contained, surprisingly, a large percentage of mono-and diunsaturated components. The acyl and alkoxy segments are reported for each wax ester component. Also, the positions of the carbon-carbon double bonds in the wax esters produced from the C16 and C20 n-alkanes are reported. These microbial-produced wax ester mixtures bear a close chemical similarity to those of sperm whale and jojoba oils.

John Geigert

Papers

Biohalogenation : principles, basic roles, and applications

Peroxide oxidation of primary alcohols to aldehydes by chloroperoxidase catalysis.

Epoxidation of alkenes by chloroperoxidase catalysis.

Saturated and Unsaturated Wax Esters Produced by Acinetobacter sp. HO1-N Grown on C16-C20n-Alkanes

Isolation and characterization of a novel nonheme chloroperoxidase