Rhamnolipid stimulates uptake of hydrophobic compounds by Pseudomonas aeruginosa

The biodegradation of hexadecane by five biosurfactant-producing bacterial strains (Pseudomonas aeruginosa UG2, Acinetobacter calcoaceticus RAG1, Rhodococcus erythropolis DSM 43066, R. erythropolis ATCC 19558, and strain BCG112) was determined in the presence and absence of exogenously added biosurfactants. The degradation of hexadecane by P. aeruginosa was stimulated only by the rhamnolipid biosurfactant produced by the same organism. This rhamnolipid did not stimulate the biodegradation of hexadecane by the four other strains to the same extent, nor was degradation of hexadecane by these strains stimulated by addition of their own biosurfactants. This suggests that P. aeruginosa has a mode of hexadecane uptake different from those of the other organisms. Rhamnolipid also enhanced the rate of epoxidation of the aliphatic hydrocarbon alpha,omega-tetradecadiene by a cell suspension of P. aeruginosa. Furthermore, the uptake of the hydrophobic probe 1-naphthylphenylamine by cells of P. aeruginosa was enhanced by rhamnolipid, as indicated by stopped-flow fluorescence experiments. Rhamnolipid did not stimulate the uptake rate of this probe in de-energized cells. These results indicate that an energy-dependent system is present in P. aeruginosa strain UG2 that mediates fast uptake of hydrophobic compounds in the presence of rhamnolipid.     

The enhancement by surfactants of hexadecane degradation by Pseudomonas aeruginosa varies with substrate availability.

The rhamnolipid biosurfactant produced by Pseudomonas aeruginosa influences various processes related to hydrocarbon degradation. However, degradation can only be enhanced by the surfactant when it stimulates a process that is rate limiting under the applied conditions. Therefore we determined how rhamnolipid influences hexadecane degradation by P. aeruginosa UG2 under conditions differing in hexadecane availability. The rate of hexadecane degradation in shake flask cultures was lower for hexadecane entrapped in a matrix with 6 nm pores (silica 60) or in quartz sand than for hexadecane immobilized in matrices with pore sizes larger than 300 nm or for hexadecane present as a separate liquid phase. This indicates that the availability of hexadecane decreased with decreasing pore size under these conditions. The rate-limiting step for hexadecane entrapped in silica 60 was the mass transfer of substrate from the matrix to the bulk liquid phase, whereas for hexadecane present as a second liquid phase it was the uptake of the substrate by the cells. Hexadecane degradation in batch incubations was accelerated by the addition of rhamnolipid or other surfactants in all experiments except in those where hexadecane was entrapped in silica 60, indicating that the surfactants stimulated uptake of hexadecane by the cells. Since rhamnolipid stimulated the degradation rate in batch experiments to a greater extent than any of the other 14 surfactants tested, hexadecane uptake was apparently more enhanced by rhamnolipid than by the other surfactants. Although rhamnolipid did not stimulate the release of hexadecane from silica 60 under conditions of intense agitation, it significantly enhanced this rate during column experiments in the absence of strain UG2. The results demonstrate that rhamnolipid enhances degradation by stimulating release of entrapped substrate in column studies under conditions of low agitation and by stimulating uptake of substrate by the cells, especially when degradation is not limited by release of substrate from the matrices.     

Role of rhamnolipid biosurfactants in the uptake and mineralization of hexadecane in Pseudomonas aeruginosa

A study was undertaken to investigate the mechanisms for biosurfactant-enhanced hexadecane uptake into Pseudomonas aeruginosa. Two strains of Ps. aeruginosa were studied, one producing rhamnolipids (PG201) and the other rhamnolipid deficient (UO299). Rhamnolipids produced by PG201 acted to increase the solubility of n-hexadecane in the culture medium (from 1.84 to 22.76 microg l(-1). Rates of(l4)C-n-hexadecane uptake and mineralization were higher in PG201 than in UO299. However, the degree of difference was lower than expected. Additional studies were carried out on the cell surface properties of the two strains. During growth on n-hexadecane, the cell surface hydrophobicity of both PG201 (50.5%) and UO299 (33.7%) increased compared with that observed in water-soluble growth substrates (7-8%). Studies were also carried out to ascertain any energy requirements for the transport of n-hexadecane into Ps. aeruginosa cells. The addition of CCCP (an inhibitor of cytochrome oxidase which thereby blocks oxidative phosphorylation) at a range of concentrations caused a marked decrease in n-hexadecane uptake, indicating that n-hexadecane uptake in Ps. aeruginosa is an energy-dependent process. These studies support the hypothesis of alkane transport into microbial cells by direct contact with larger alkane droplets and by pseudosolubilization. Also, it appears that both mechanisms occur simultaneously.     

Hydrocarbon assimilation and biosurfactant production in Pseudomonas aeruginosa mutants.

We isolated transposon Tn5-GM-induced mutants of Pseudomonas aeruginosa PG201 that were unable to grow in minimal media containing hexadecane as a carbon source. Some of these mutants lacked extracellular rhamnolipids, as shown by measuring the surface and interfacial tensions of the cell culture supernatants. Furthermore, the concentrated culture media of the mutant strains were tested for the presence of rhamnolipids by thin-layer chromatography and for rhamnolipid activities, including hemolysis and growth inhibition of Bacillus subtilis. Mutant 65E12 was unable to produce extracellular rhamnolipids under any of the conditions tested, lacked the capacity to take up 14C-labeled hexadecane, and did not grow in media containing individual alkanes with chain lengths ranging from C12 to C19. However, growth on these alkanes and uptake of [14C]hexadecane were restored when small amounts of purified rhamnolipids were added to the cultures. Mutant 59C7 was unable to grow in media containing hexadecane, nor was it able to take up [14C]hexadecane. The addition of small amounts of rhamnolipids restored growth on alkanes and [14C]hexadecane uptake. In glucose-containing media, however, mutant 59C7 produced rhamnolipids at levels about twice as high as those of the wild-type strain. These results show that rhamnolipids play a major role in hexadecane uptake and utilization by P. aeruginosa.     

Cloning and heterologous expression of a gene encoding an alkane-induced extracellular protein involved in alkane assimilation from Pseudomonas aeruginosa.

Pseudomonas aeruginosa PG201 produces a 16-kDa extracellular protein in media containing n-hexadecane as a carbon source but not in media containing glycerol or glucose. This protein was purified, and the N-terminal amino acid sequence was determined. The amino acid composition of the protein was found to be very similar to that of the so-called protein-like activator for n-alkane oxidation (PA) from P. aeruginosa S7B1. This extracellular protein was previously characterized (K. Hisatsuka, T. Nakahara, Y. Minoda, and K. Yamada, Agric. Biol. Chem. 41:445-450, 1977) and found to stimulate the growth of P. aeruginosa on n-hexadecane and to possess emulsifying activity. To study the role(s) of the PA protein and to make it accessible for possible future applications, we have cloned the PA-encoding (pra) gene and determined its nucleotide sequence. This analysis revealed a protein-coding region of 162 amino acids, with the first 25 residues being reminiscent of those of a typical bacterial signal sequence. The pra gene was inactivated by insertional mutagenesis, and the resulting strain was found to lack extracellular PA protein and to be retarded in its growth in n-hexadecane-containing media. These results are consistent with the growth stimulatory role of the PA protein. The pra gene was expressed in Escherichia coli, and substantial amounts of the recombinant protein were found in the extracellular growth medium. The recombinant protein was purified by metal chelate affinity chromatography. The ability to produce secreted PA protein by E. coli provides a simple and safe means to analyze its function(s) in alkane assimilation in the future.     

Rhamnolipid (biosurfactant) effects on cell aggregation and biodegradation of residual hexadecane under saturated flow conditions.

The objective of this research was to evaluate the effect of low concentrations of a rhamnolipid biosurfactant on the in situ biodegradation of hydrocarbon entrapped in a porous matrix. Experiments were performed with sand-packed columns under saturated flow conditions with hexadecane as a model hydrocarbon. Application of biosurfactant concentrations greater than the CMC (the concentration at which the surfactant molecules spontaneously form micelles or vesicles [0.03 mM]) resulted primarily in the mobilization of hexadecane entrapped within the sand matrix. In contrast, application of biosurfactant concentrations less than the CMC enhanced the in situ mineralization of entrapped hexadecane; however, this effect was dependent on the choice of bacterial isolate. The two Pseudomonas isolates tested, R4 and ATCC 15524, were used because they exhibit different patterns of biodegradation of hexadecane, and they also differed in their physical response to rhamnolipid addition. ATCC 15524 cells formed extensive multicell aggregates in the presence of rhamnolipid while R4 cells were unaffected. This behavior did not affect the ability of the biosurfactant to enhance the biodegradation of hexadecane in well-mixed soil slurry systems but had a large affect on the extent of entrapped hexadecane biodegradation in the sand-packed-column system that was used in this study.     

Imaging and analysis of Pseudomonas aeruginosa swarming and rhamnolipid production

Many bacteria spread over surfaces by "swarming" in groups. A problem for scientists who study swarming is the acquisition of statistically significant data that distinguish two observations or detail the temporal patterns and two-dimensional heterogeneities that occur. It is currently difficult to quantify differences between observed swarm phenotypes. Here, we present a method for acquisition of temporal surface motility data using time-lapse fluorescence and bioluminescence imaging. We specifically demonstrate three applications of our technique with the bacterium Pseudomonas aeruginosa. First, we quantify the temporal distribution of P. aeruginosa cells tagged with green fluorescent protein (GFP) and the surfactant rhamnolipid stained with the lipid dye Nile red. Second, we distinguish swarming of P. aeruginosa and Salmonella enterica serovar Typhimurium in a coswarming experiment. Lastly, we quantify differences in swarming and rhamnolipid production of several P. aeruginosa strains. While the best swarming strains produced the most rhamnolipid on surfaces, planktonic culture rhamnolipid production did not correlate with surface growth rhamnolipid production.     

Effect of a Pseudomonas rhamnolipid biosurfactant on cell hydrophobicity and biodegradation of octadecane.

In this study, the effect of a purified rhamnolipid biosurfactant on the hydrophobicity of octadecane-degrading cells was investigated to determine whether differences in rates of octadecane biodegradation resulting from the addition of rhamnolipid to four strains of Pseudomonas aeruginosa could be related to measured differences in hydrophobicity. Cell hydrophobicity was determined by a modified bacterial adherence to hydrocarbon (BATH) assay. Bacterial adherence to hydrocarbon quantitates the preference of cell surfaces for the aqueous phase or the aqueous-hexadecane interface in a two-phase system of water and hexadecane. On the basis of octadecane biodegradation in the absence of rhamnolipid, the four bacterial strains were divided into two groups: the fast degraders (ATCC 15442 and ATCC 27853), which had high cell hydrophobicities (74 and 55% adherence to hexadecane, respectively), and the slow degraders (ATCC 9027 and NRRL 3198), which had low cell hydrophobicities (27 and 40%, respectively). Although in all cases rhamnolipid increased the aqueous dispersion of octadecane at least 10(4)-fold, at low rhamnolipid concentrations (0.6 mM), biodegradation by all four strains was initially inhibited for at least 100 h relative to controls. At high rhamnolipid concentrations (6 mM), biodegradation by the fast degraders was slightly inhibited relative to controls, but the biodegradation by the slow degraders was enhanced relative to controls. Measurement of cell hydrophobicity showed that rhamnolipids increased the cell hydrophobicity of the slow degraders but had no effect on the cell hydrophobicity of the fast degraders. The rate at which the cells became hydrophobic was found to depend on the rhamnolipid concentration and was directly related to the rate of octadecane biodegradation.(ABSTRACT TRUNCATED AT 250 WORDS)     

Rhamnolipid Stimulates Uptake of Hydrophobic Compounds by Pseudomonas aeruginosa

The biodegradation of hexadecane by five biosurfactant-producing bacterial strains (Pseudomonas aeruginosa UG2, Acinetobacter calcoaceticus RAG1, Rhodococcus erythropolis DSM 43066, R. erythropolis ATCC 19558, and strain BCG112) was determined in the presence and absence of exogenously added biosurfactants. The degradation of hexadecane by P. aeruginosa was stimulated only by the rhamnolipid biosurfactant produced by the same organism. This rhamnolipid did not stimulate the biodegradation of hexadecane by the four other strains to the same extent, nor was degradation of hexadecane by these strains stimulated by addition of their own biosurfactants. This suggests that P. aeruginosa has a mode of hexadecane uptake different from those of the other organisms. Rhamnolipid also enhanced the rate of epoxidation of the aliphatic hydrocarbon α,ω-tetradecadiene by a cell suspension of P. aeruginosa. Furthermore, the uptake of the hydrophobic probe 1-naphthylphenylamine by cells of P. aeruginosa was enhanced by rhamnolipid, as indicated by stopped-flow fluorescence experiments. Rhamnolipid did not stimulate the uptake rate of this probe in de-energized cells. These results indicate that an energy-dependent system is present in P. aeruginosa strain UG2 that mediates fast uptake of hydrophobic compounds in the presence of rhamnolipid.     

Production of Pseudomonas aeruginosa Rhamnolipid Biosurfactants in Heterologous Hosts

The high-level production of rhamnolipid biosurfactants is a unique feature of Pseudomonas aeruginosa and is strictly regulated in response to environmental conditions. The final step in rhamnolipid biosynthesis is catalyzed by the rhlAB genes encoding a rhamnosyltransferase. The expression of the cloned rhlAB genes was studied in heterologous hosts, either under the control of the rhlR and rhlI rhamnolipid regulatory elements or under the control of the tac promoter. A recombinant P. fluorescens strain harboring multiple plasmid-encoded copies of the rhamnolipid gene cluster produced rhamnolipids (0.25 g liter(sup-1)) when grown under nitrogen-limiting conditions. The highest yields (0.6 g liter(sup-1)) and productivities (24 mg liter(sup-1) h(sup-1)) were obtained in a recombinant Pseudomonas putida strain, KT2442, harboring promoterless rhlAB genes fused to the tac promoter on a plasmid. Active rhamnosyltransferase was synthesized, but no rhamnolipids were produced, by recombinant Escherichia coli upon induction of rhlAB gene expression.     

Rhamnolipid-induced removal of lipopolysaccharide from Pseudomonas aeruginosa: effect on cell surface properties and interaction with hydrophobic substrates

Little is known about the interaction of biosurfactants with bacterial cells. Recent work in the area of biodegradation suggests that there are two mechanisms by which biosurfactants enhance the biodegradation of slightly soluble organic compounds. First, biosurfactants can solubilize hydrophobic compounds within micelle structures, effectively increasing the apparent aqueous solubility of the organic compound and its availability for uptake by a cell. Second, biosurfactants can cause the cell surface to become more hydrophobic, thereby increasing the association of the cell with the slightly soluble substrate. Since the second mechanism requires very low levels of added biosurfactant, it is the more intriguing of the two mechanisms from the perspective of enhancing the biodegradation process. This is because, in practical terms, addition of low levels of biosurfactants will be more cost-effective for bioremediation. To successfully optimize the use of biosurfactants in the bioremediation process, their effect on cell surfaces must be understood. We report here that rhamnolipid biosurfactant causes the cell surface of Pseudomonas spp. to become hydrophobic through release of lipopolysaccharide (LPS). In this study, two Pseudomonas aeruginosa strains were grown on glucose and hexadecane to investigate the chemical and structural changes that occur in the presence of a rhamnolipid biosurfactant. Results showed that rhamnolipids caused an overall loss in cellular fatty acid content. Loss of fatty acids was due to release of LPS from the outer membrane, as demonstrated by 2-keto-3-deoxyoctonic acid and sodium dodecyl sulfate-polyacrylamide gel electrophoresis analysis and further confirmed by scanning electron microscopy. The amount of LPS loss was found to be dependent on rhamnolipid concentration, but significant loss occurred even at concentrations less than the critical micelle concentration. We conclude that rhamnolipid-induced LPS release is the probable mechanism of enhanced cell surface hydrophobicity.     

Improved production of biosurfactant with newly isolated Pseudomonas aeruginosa S2

An indigenous strain Pseudomonas aeruginosa S2 (P. aeruginosa S2), isolated from diesel-contaminated soil, produced extracellular surface-active material identified as rhamnolipid. Due to its excellent surface activity, rhamnolipid is known to be well-suited for stimulating the bioremediation efficiency of oil contaminated sites. To improve production yield of rhamnolipid with P. aeruginosa S2, various carbon and nitrogen sources were screened to select favorable ones leading to better biosurfactant production yield. It was found that using 4% glucose could attain better rhamnolipid yield, while 50 mM NH4NO3 appeared to be the most preferable nitrogen source. Meanwhile, the effect of carbon to nitrogen ratio (C/N ratio) on rhamnolipid yield was also investigated, and the optimal C/N ratio was identified as approximately 11.4. Moreover, response surface methodology (RSM) was applied to optimize the trace element concentration for rhamnolipid production. Results from two-level design indicate that concentrations of MgSO4 and FeSO4 were the most significant factors affecting rhamnolipid production. Using steepest ascent method and RSM analysis, an optimal medium composition was determined, giving a rhamnolipid production yield of 2.37 g/L in 100 h at 37 degrees C and 200 rpm agitation. Scale-up production of rhamnolipid in a well-controlled 5 L jar fermentor using the optimal medium and operating condition (at 37 degrees C and pH 6.8) further elevated the biosurfactant production yield to 5.31 g/L (in 97 h), which is over 2-fold higher than the best results obtained from shake-flask tests.     

Green fluorescent protein as a molecular marker in microbiology

Molecular markers such as: lacZ (b-galactosidase), xylE (catechol 2,3-dioxygenase), lux (bacterial luciferase), luc (insect luciferase), phoA (alkaline phosphatase), gusA and gurA (beta-glucuronidase), gfp (green fluorescent protein), bla (beta-lactamase) and other antibiotic resistance markers, heavy metals resistance genes are commonly used in environmental microorganisms research (Errampaii et al., 1998; Kohler et al., 1999). Most of these markers require one or more substrates, complex media and/or expensive equipment for detection. The gfp gene is widely used as a marker because of its very useful properties such as high stability, minimal toxicity, non-invasive detection and the ability to generate the green light without addition of external cofactors and without application of expensive equipment. Various applications of that reporter gene were showed starting from monitoring of microorganism's survival in complex biological systems such as activated sludge to biodegradation of chemical compounds in soil. GFP allowed the detection, determination of spatial location and enumeration of bacterial cells from diverse environmental samples such as biofilm and water. The gfp as a biomarker was very useful in monitoring of gene expression and protein localisation in bacterial cells, too. The techniques with using gfp marker promise to supply a better understanding of environmental processes. It can make possible to use that knowledge in designing more effective and more efficient methods of biodegradation of toxic compounds from different environments.     

Engineering bacteria for production of rhamnolipid as an agent for enhanced oil recovery

Rhamnolipid as a potent natural biosurfactant has a wide range of potential applications, including enhanced oil recovery (EOR), biodegradation, and bioremediation. Rhamnolipid is composed of rhamnose sugar molecule and beta-hydroxyalkanoic acid. The rhamnosyltransferase 1 complex (RhlAB) is the key enzyme responsible for transferring the rhamnose moiety to the beta-hydroxyalkanoic acid moiety to biosynthesize rhamnolipid. Through transposome-mediated chromosome integration, the RhlAB gene was inserted into the chromosome of the Pseudomonas aeruginosa PAO1-rhlA(-) and Escherichia coli BL21 (DE3), neither of which could produce rhamnolipid. After chromosome integration of the RhlAB gene, the constitute strains P. aeruginosa PEER02 and E. coli TnERAB did produce rhamnolipid. The HPLC/MS spectrum showed that the structure of purified rhamnolipid from P. aeruginosa PEER02 was similar to that from other P. aeruginosa strains, but with different percentage for each of the several congeners. The main congener (near 60%) of purified rhamnolipid from E. coli TnERAB was 3-(3-hydroxydecanoyloxy) decanoate (C(10)-C(10)) with mono-rhamnose. The surfactant performance of rhamnolipid was evaluated by measurement of interfacial tension (IFT) and oil recovery via sand-pack flooding tests. As expected, pH and salt concentration of the rhamnolipid solution significantly affected the IFT properties. With just 250 mg/L rhamnolipid (from P. aeruginosa PEER02 with soybean oil as substrate) in citrate-Na(2)HPO(4), pH 5, 2% NaCl, 42% of oil otherwise trapped was recovered from a sand pack. This result suggests rhamnolipid might be considered for EOR applications.     

Effect of Rhamnolipid (Biosurfactant) Structure on Solubilization and Biodegradation of n-Alkanes

A study to quantify the effect of rhamnolipid biosurfactant structure on the degradation of alkanes by a variety of Pseudomonas isolates was conducted. Two dirhamnolipids were studied, a methyl ester form (dR-Me) and an acid form (dR-A). These rhamnolipids have different properties with respect to interfacial tension, solubility, and charge. For example, the interfacial tension between hexadecane and water was decreased to <0.1 dyne/cm by the dR-Me but was only decreased to 5 dyne/cm by the dR-A. Solubilization and biodegradation of two alkanes in different physical states, liquid and solid, were determined at dirhamnolipid concentrations ranging from 0.01 to 0.1 mM (7 to 70 mg/liter). The dR-Me markedly enhanced hexadecane (liquid) and octadecane (solid) degradation by seven different Pseudomonas strains. For an eighth strain tested, which exhibited extremely high cell surface hydrophobicity, hexadecane degradation was enhanced but octadecane degradation was inhibited. The dR-A also enhanced hexadecane degradation by all degraders but did so more modestly than the dR-Me. For octadecane, the dR-A only enhanced degradation by strains with low cell surface hydrophobicity.     

Rhamnolipid production by Pseudomonas aeruginosa immobilised in polyvinyl alcohol beads

A marine bacterium, Pseudomonas aeruginosa BYK-2 (KCTC 18012P), was immobilised by entrapment in 10% (w/v) polyvinyl alcohol beads and optimized for the continuous production of rhamnolipid. The relative activity of rhamnolipid production was maintained at 80 approximately 90% of the initial production during 15 cycles in a repeated batch culture. Continuous culture was performed in a 1.8 1 airlift bioreactor, yielding 0.1 g rhamnolipid h(-1) at a dilution rate of 0.0 18 h(-1), 25 degrees C, initial pH 7, and 0.5 vvm aeration rate with a 1.21 working volume.     

Pseudomonas aeruginosa biosurfactant production in continuous culture with glucose as carbon source.

Rsan-ver, a strain of Pseudomonas aeruginosa isolated at this department, was used for the development of a continuous process for biosurfactant production. The active compounds were identified as rhamnolipids. A final medium for production was designed in continuous culture by means of medium shifts, since the formation of surface-active compounds was decisively influenced by the composition and concentration of the medium components. In the presence of yeast extract, biosurfactant production was poor. For the nitrogen-source nitrate, which was superior to ammonium, an optimum carbon-to-nitrogen ratio of ca. 18 existed. The iron concentration needed to be minimized to 27.5 micrograms of FeSO4 X 7H2O per g of glucose. A carbon-to-phosphate ratio below 16 yielded the maximum production of rhamnolipids. The final productivity dilution rate diagram indicated that biosurfactant production was correlated to low growth rates (dilution rate below 0.15 h-1). With a medium containing 18.2 g of glucose liter-1, a biosurfactant concentration (expressed as rhamnolipids) of up to 1.5 g liter-1 was obtained in the cell-free culture liquid.