Nutrient-enhanced survival of and phenanthrene mineralization by alginate-encapsulated and freePseudomonas sp. UG14Lr cells in creosote-contaminated soil slurries

The effects of nutrient amendment and alginate encapsulation on survival of and phenanthrene mineralization by the bioluminescentPseudomonas sp. UG14Lr in creosote-contaminated soil slurries were examined. UG14Lr was inoculated into creosote-contaminated soil slurries either as a free cell suspension or encapsulated in alginate beads prepared with montmorillonite clay and skim milk. Additional treatments were free-cell-inoculated slurries amended with sterile alginate beads, free-cell-inoculated and uninoculated slurries amended with skim milk only, and uninoculated, unamended slurries. Mineralization was determined by measuring¹⁴CO₂ released from radiolabelled phenanthrene. Survival was measured by selective plating and bioluminescence. Inclusion of skim milk was found to enhance both survival of and phenanthrene mineralization by free and encapsulated UG14Lr cells.     

Plasmid transfer between strains of Pseudomonas putida, and their survival, within a pilot scale percolating-filter sewage treatment system

Abstract: The effect of Pseudomonas aeruginosa UG2 biosurfactants or UG2 inocula on phenanthrene mineralization in uninoculated nonsterile soil slurries and slurries inoculated with the phenanthrene-mineralizing Pseudomonas sp. UG14r was investigated. In sandy loam and silt loam slurries amended with phenanthrene, inoculation with UG14r alone or in co-culture with UG2Lr reduced the lag period before onset of phenanthrene mineralization by 1 week. The total amount mineralized after 5 weeks was lower or not significantly different from the uninoculated control slurries. Inoculation with P. aeruginosa UG2Lr alone did not improve phenanthrene mineralization. In creosote-contaminated soil slurries, no lag period in phenanthrene mineralization was observed in any treatment. After 4 weeks, the greatest extent of mineralization was observed in creosote-contaminated soil slurries inoculated with the UG14r-UG2Lr co-culture and UG14r alone. In sandy loam and silt loam soil slurries inoculated with Pseudomonas sp. UG14r, addition of UG2 rhamnolipid biosurfactants (100 to 400 mg rhamnose equivalents (RE) · l⁻¹ slurry) inhibited phenanthrene mineralization by 10 to 15%. Mineralization was also inhibited in uninoculated sandy loam slurries. In creosote-contaminated soil slurries inoculated with Pseudomonas sp. UG14r, biosurfactants at 250 mg RE · l⁻¹ slurry enhanced mineralization whereas 400 mg RE · l⁻¹ had no effect, compared to unamended slurries. In uninoculated creosote-contaminated soil slurries, UG2 biosurfactants at 250 and 400 mg RE · l⁻¹ slurry enhanced mineralization, compared to unamended slurries.     

Survival of free and alginate-encapsulated Pseudomonas aeruginosa UG2Lr in soil treated with disinfectants

Pseudomonas aeruginosa UG2Lr, a rifampicin-resistant strain possessing the luxAB on a chromosomal Tn5 insert, was inoculated into soil microcosms as either free cells or encapsulated in dry alginate beads. A 100-fold increase in cell number g^-1 dry soil was observed in microcosms inoculated with alginate-encapsulated UG2Lr after 3 weeks incubation at 22°C compared to microcosms inoculated with free cells. After 98 d, microcosms inoculated with free UG2Lr cells contained 10⁴ cfu g^-1 dry soil compared to 10⁷ cfu g^-1 dry soil in microcosms inoculated with alginate-encapsulated UG2Lr cells. The effects of disinfectants on both the free and alginate-encapsulated UG2Lr cells were also examined. 1·0% (w/g dry soil) calcium hypochlorite, formaldehyde and Spectrum Clear Bath, were added to microcosms each week for 4 weeks. Formaldehyde killed both free and alginate-encapsulated UG2Lr cells within 14 d after only two amendments. Calcium hypochlorite reduced free UG2Lr cell numbers 10-fold 2 d after initial application; however, the introduced population recovered and was unaffected by subsequent treatments at 7, 14 and 21 d. Alginate-encapsulated UG2Lr cells were not affected by calcium hypochlorite treatment. Spectrum Clear Bath did not kill either free or alginate-encapsulated UG2Lr cells in soil. Alginate encapsulation improved survival of introduced bacteria in soil except in the presence of formaldehyde. Killing genetically-engineered bacteria in soil may be difficult unless a powerful disinfectant such as formaldehyde is used or the genetically-engineered micro-organism is allowed to become non-viable over time.     

Phenanthrene mineralization by Pseudomonas sp. UG14

A phenanthrene-mineralizing Pseudomonas sp., designated UG14, was isolated from creosote-contaminated soil. It contained two plasmids, of approximately 77 kb and 76 kb, the smaller of which contained DNA sequences that hybridized with probes specific for ndoB and xylE, genes involved in catabolism of aromatic hydrocarbons. At initial phenanthrene concentrations of 10, 50, 200 and 1000 mg/l broth, 27%, 19%, 7.7% and 3.3%, respectively, of the [9-¹⁴C]phenanthrene was recovered as ¹⁴CO₂ after 36 days' incubation at 30°C. Most ¹⁴C-label was converted to a water-soluble metabolite tentatively identified as 1-hydroxy-2-naphthoic acid. Rhamnolipid biosurfactants produced by P. aeruginosa UG2 enhanced mineralization of 50 mg phenanthrene/l by Pseudomonas sp. UG14. With the biosurfactant at 0, 25 and 250 mg rhamnose equivalents/l, 6.5%, 8.2% and 9.8%, respectively, of the phenanthrene was mineralized after 35 days.M.A. Providenti, H. Lee and J.T. Trevors are with the Department of Environmental Biology, University of Guelph, Guelph, Ontario, N1G 2W1, Canada; C.W. Greer is with the National Research Council Canada, Biotechnology Research Institute, 6100 Royalmount Ave, Montreal, Quebec, H4P 2R2, Canada.     

Transport and survival of alginate-encapsulated and free lux-lac marked Pseudomonas aeruginosa UG2Lr cells in soil

Transport and survival of alginate-encapsulated and unencapsulated Pseudomonas aeruginosa UG2Lr through soil microcosms was examined. Bacterial cells encapsulated in alginate beads or mixed with soil were introduced into soil microcosms. Microbial cell survival and cell transport were monitored by destructive sampling and selective plating of the microcosms over a 9-week period. Survival rates were greatest when using encapsulated P. aeruginosa UG2Lr cells. Water flow increased microbial cell dispersal from the site of inoculation. After 3 weeks, encapsulated and free cells showed similar distribution patterns. However, after 9 weeks microbial cell distribution was more extensive throughout the soil in the encapsulated treatments under all conditions. Therefore, alginate encapsulation is a suitable method to enhance survival and distribution of microbial inocula in the soil environment.     

Effect of corn plant on survival and phenanthrene degradation capacity of Pseudomonas sp. UG14LR in two soils

A study was undertaken to assess if corn (Zea mays L.) can enhance phenanthrene degradation in two soils inoculated with Pseudomonas sp. UG14Lr. Corn increased the number of UG14Lr cells in both soils, especially in the acidic soiL Phenanthrene was degraded to a greater extent in UG14Lr-inoculated or corn-planted soils than uninoculated and unplanted soils. The spiked phenanthrene was completely removed within 70 days in all the treatments in slightly alkaline soil. However, in acidic soil, complete phenanthrene removal was found only in the corn-planted treatments. The shoot and root lengths of corn grown in UG14Lr-inoculated soils were not different from those in non-inoculated soil between the treatments. The results showed that in unplanted soil, low pH adversely affected the survival and phenanthrene degradation ability of UG14Lr. Planting of corn significantly enhanced the survival of UG14Lr cells in both the bulk and rhizospheric soil, and this in turn significantly improved phenanthrene degradation in acidic soil. Re-inoculation of UG14Lr in the acidic soil increased the number of UG14Lr cells and enhanced phenanthrene degradation in unplanted soil. However, in corn-planted acidic soils, re-inoculation of UG14Lr did not further enhance the already active phenanthrene degradation occurring in both the bulk or rhizospheric soils.     

Enhanced mineralization of pentachlorophenol by κ-carrageenan-encapsulated Pseudomonas sp. UG30

A pentachlorophenol(PCP)-degrading Pseudomonas sp. strain UG30 was encapsulated in κ-carrageenan for use in PCP degradation. Free and encapsulated cells were compared for their ability to dechlorinate and mineralize 100–800 μg/ml sodium pentachlorophenate in broth. Dechlorination was measured with a chloride ion electrode, and mineralization was measured by ¹⁴CO₂ evolution from radiolabelled [U-¹⁴C]PCP. Free and encapsulated Pseudomonas sp. UG30 cells mineralized up to 200 μg/ml and 600 μg/ml PCP, respectively, after 21 days. Encapsulation of UG30 cells provided a protective effect, allowing dechlorination and mineralization of high levels of PCP to occur. Received: 3 May 1996 / Received revision: 4 September 1996 / Accepted: 13 September 1996     

Phenanthrene stimulates the degradation of pyrene and fluoranthene by <Emphasis Type="Italic">Burkholderia</Emphasis> sp. VUN10013

Pyrene and fluoranthene, when supplied as the sole carbon source, were not degraded by Burkholderia sp. VUN10013. However, when added in a mixture with phenanthrene, both pyrene and fluoranthene were degraded in liquid broth and soil. The amounts of pyrene and fluoranthene in liquid media (initial concentrations of 50 mg l⁻¹ each) decreased to 42.1% and 41.1%, respectively, after 21 days. The amounts of pyrene and fluoranthene in soil (initial concentrations of 75 mg kg⁻¹ dry soil each) decreased to 25.8% and 12.1%, respectively, after 60 days. None of the high molecular weight (HMW) polycylic aromatic hydrocarbons (PAHs) tested adversely affected phenanthrene degradation by this bacterial strain and the amount of phenanthrene decreased rapidly within 3 and 15 days of incubation in liquid broth and soil, respectively. Anthracene also stimulated the degradation of pyrene or fluoranthene by Burkholderia sp. VUN10013, but to a lesser extent than phenanthrene. The extent of anthracene degradation decreased in the presence of these HMW PAHs.     

Survival of κ-carrageenan-encapsulated and unencapsulated Pseudomonas aeruginosa UG2Lr cells in forest soil monitored by polymerase chain reaction and spread plating

Abstract A method was developed for direct extraction, purification and amplification of DNA from forest soil. Eighty-two % of the DNA in Pseudomonas aeruginosa UG2Lr introduced into soil was recovered. The detection limit for the strain was approximately 800 cfu g⁻¹ of dry soil based on the polymerase chain reaction (PCR). Survival of κ-carrageenan-encapsulated and unencapsulated UG2Lr was monitored by antibiotic selective and bioluminescence-based nonselective plating and PCR-amplification of a tnsA fragment. After freeze-thaw treatment of soil samples, the unencapsulated UG2Lr declined from an initial population density of 1 × 10⁹ cfu g⁻¹ of dry soil to below the detection threshold of both selective (14 cfu g⁻¹ of dry soil) and nonselective (1 × 10³ cfu g⁻¹ of dry soil) plating. However, presence of nonculturable UG2Lr cells in the soil was revealed by PCR and resuscitation of the bacteria. Population density of the encapsulated UG2Lr increased from 2.7 × 10⁶ to 2.9 × 10⁸ cfu g⁻¹ of dry soil after a 3-week incubation at 22°C and declined to 6.3 × 10⁶ cfu g⁻¹ of dry soil after the freeze-thaw treatment.     

Pilot Scale Bioremediation of Creosote-Contaminated Soil—Efficacy of Enhanced Natural Attenuation and Bioaugmentation Strategies

In this study, the efficacy of bioremediation strategies (enhanced natural attenuation with nitrate and phosphate addition [ENA] and bioaugmentation) for the remediation of creosote-contaminated soil (7767 ± 1286 mg kg^?1 of the 16 EPA priority PAHs) was investigated at pilot scale. Bioaugmentation of creosote-contaminated soil with freshly grown or freeze dried Mycobacterium sp. strain 1B (a PAH degrading microorganism) was applied following bench scale studies that indicated that the indigenous soil microflora had a limited PAH metabolic activity. After 182 days, the total PAH concentration in creosote-contaminated soil was reduced from 7767 ± 1286 mg kg^?1 to 5579 ± 321 mg kg^?1, 2250 ± 71 mg kg^?1, 2050 ± 354 mg kg^?1 and 1950 ± 70 mg kg^?1 in natural attenuation (no additions) and ENA biopiles and biopiles augmented with freshly grown or freeze dried Mycobacterium sp. strain 1B respectively. In ENA and bioaugmentation biopiles, between 82% and 99% of three-ring compounds (acenaphthene, anthracene, fluorene, phenanthrene) were removed while four-ring PAH removal ranged from 33 to 81%. However, the extent of PAH degradation did not vary significantly between the ENA treatment and biopiles augmented with Mycobacterium sp. strain 1B. Four-ring PAH removal followed the order fluoranthene > pyrene > benz[a]anthracene > chrysene. The high residual concentration of some four-ring PAHs may be attributable to bioavailability issues rather than a lack of microbial catabolic activity. Comparable results between ENA and bioaugmentation at pilot scale were surprising given the limited degradative capacity of the microbial consortia enriched from the creosote-contaminated soil.     

Simultaneous mineralization of glyphosate and diuron by a consortium of three bacteria as free- and/or immobilized-cells formulations

A bacterial consortium able to mineralize two herbicides, glyphosate (Pseudomonas 4ASW) and diuron (Arthrobacter sp. N4 and Delftia acidovorans), was cultivated in both a synthetic culture medium without phosphate and a sediment extract medium. In the aim at optimizing glyphosate and diuron mineralization, all the combinations, i.e., free and/or immobilized cells in Ca-alginate beads were tested. With the synthetic medium, the simultaneous mineralization of glyphosate and diuron required at least the immobilization of Pseudomonas 4ASW. Conversely, with the sediment extract medium, only the mineralization of diuron was observed, most probably, because of both nutrient deficiency and phosphate in the sediment extract medium.     

Effects of Soil Water Content on Biodegradation of Phenanthrene in a Mixture of Organic Contaminants

Phenanthrene biodegradation was investigated at different soil water contents [0.11, 0.22, 0.33, 0.44 g H₂O (g soil)^?1] to determine the effects of water availability on biodegradation rate. A subsurface horizon of Kennebec silty loam soil was used in this study. [9-¹⁴C] phenanthrene was dissolved in a mixture of organic contaminants that consisted of 76% decane, 6% ρ-xylene, 6% phenanthrene, 6% pristane, and 6% naphthalene, and then added to the soil. The highest rate of mineralization, in which 0.23% of the [9-¹⁴C] phenanthrene degraded to ¹⁴CO₂ after 66 days of incubation, was observed at the soil water content of 0.44 g H₂O/g dry soil. Most of the ¹⁴C remained in the soil as the parent compound or as nonextractable compounds by acetonitrile at the highest water content. Concentrations of nonextractable compounds increased with water content, but residual extractable phenanthrene decreased significantly with increasing water content, which presumably indicates that bio-transformation occurred. The mineralization analysis of radiolabeled 9th carbon in phenanthrene underestimated phenanthrene biodegradation. The strong adsorption and low solubility of phenanthrene contributed to the low mineralization of phenanthrene 9th carbon. The other components were subject to higher biological and abiotic dissipation processes with increasing soil water content.     

Application of immobilized tannase from <Emphasis Type="Italic">Aspergillus niger</Emphasis> for the removal of tannin from myrobalan juice

Microbial diversity of soil and water samples collected from pyrochemicals exposed areas of Virdhunagar district (Tamil Nadu, India) was studied. Soil and water samples from cultivable area, waste land and city area of the same region were also studied for a comparative acount. There is a remarkable reduction in total heterotrophic bacterial population (THB) in pyrochemicals exposed soil and water samples (42 × 10⁴ CFU/g and 5.6 × 10⁴ CFU/ml respectively), compared to the THB of cultivable area soil and water samples (98 × 10⁷ CFU/g and 38.6 × 10⁷ CFU/ml). The generic composition the THB of the pyrochemicals exposed samples too exhibited considerable change compared to other samples. Pseudomonas sp. was the predominant one (41.6%) followed by Achromobacter sp. (25%) in pyrochemical exposed soil and Pseudomonas sp. was the predominant one (25%) in pyrochemical exposed water samples followed by Bacillus sp. (25%) and Micrococcus sp. (16.6%). It was observed that Cornybacterium sp. and Micrococcus sp. were absent completely in pyrochemical exposed soil and Achromobacter sp. was missing in the pyrochemical exposed water samples, which were present in the other samples. The outcome of this study clearly demonstrates that pollutants such as chemicals used in pyrotechniques affect the microbial biodiversity and suitable measures have to be taken to control the pollution level and to save biodiversity.     

Dehalogenation of a mixture of chloroaromatics by immobilized Pseudomonas sp. US1 ex cells

Summary Pseudomonas sp. US1 ex entrapped in calcium alginate could dehalogenate a mixture of isomeric monochlorobenzoates and 2,4-dichlorophenoxyacetic acid. Rates of dehalogenation by the immobilized cells were found to be comparable to those of free cells. Conditions for optimum dehalogenation of chloroaromatics by immobilized cells and their reusability were investigated. Preliminary attempts were made to set up a continuous system for dehalogenation of chloroaromatics using a fluidized bed column reactor. Offprint requests to: V. Modi     

Biosorption of Malathion by immobilized cells of Bacillus sp. S14

Abstract

Biosorption is potentially an attractive technology for the treatment of wastewater by removing pesticide molecules from dilute solutions. This study investigated the feasibility of an isolated Bacillus sp. S₁₄ immobilized in calcium alginate that was used as a biosorbent for Malathion removal from aqueous solutions in batch mode. The highest value of Malathion uptake by isolated Bacillus sp. S14 (1.33g L^?1, dry basis) immobilized in 3% calcium alginate was 64.4% at 25°C and pH7.0 when the initial Malathion concentration was 50 mg L^?1. Equilibrium was attained at 8h. The sorption data conformed well to the Fruendlich isotherm model.     

Survival of lux-lac-marked biosurfactant-producing Pseudomonas aeruginosa UG2L in soil monitored by nonselective plating and PCR.

Two reporter systems, lacZY and luxAB, were stably integrated into the chromosome of Pseudomonas aeruginosa UG2, a biosurfactant-producing strain. Growth and rhamnolipid production of the UG2 wild-type and reporter gene-bearing UG2L strains were similar in liquid culture. A spontaneous rifampin-resistant detecting UG2Lr, allowed antibiotic selection. Phenotypic characteristics were compared for usefulness in detecting UG2Lr colonies: morphology, fluorescent pigment production, light emission (lux), X-Gal (5-bromo-4-chloro-3-indolyl-beta-D-galactopyranoside) cleavage (lac), and rifampin resistance. Survival patterns of UG2, UG2L, and UG2Lr strains were similar in sandy loam soil microcosms over 12 12 weeks. The lac marker was not suitable for monitoring P. aeruginosa UG2Lr in soil since 20 to 42% of cultured, aerobic, heterotrophic soil microorganisms formed blue, lactose-positive colonies. The lux genes provided a stable and unequivocal reporter system, as effective as conventional antibiotic plating, for tracking microorganisms nonselectively at 10(3) CFU/g of soil. Three months after inoculation into oil-contaminated and uncontaminated soil microcosms, UG2Lr cells were recovered at 10(7) and 10(4) cells per g (dry weight) of soil, respectively. Detection by PCR amplification of part of the luxA gene confirmed a decrease in UG2Lr cell numbers in uncontaminated soil. In combination, antibiotic resistance, bioluminescence, and PCR analyses provided sensitive detection and quantitative enumeration of P. aeruginosa UG2Lr in soil.     

Application of Colorimetric Assays to Assess Viability, Growth and Metabolism of Hydrogel-Encapsulated Cells

The applicability of the colorimetric 3-(4,5-dimethylthiozol-2-yl)-2,5-diphenyltetrazolium bromide (MTT) and lactate dehydrogenase (LDH) assays to measure cell growth and viability in hydrogel encapsulation systems was investigated using HepG2 liver cells encapsulated in alginate matrices. The MTT assay was effective in measuring viable cell density in alginate-encapsulated cell systems, demonstrating less variance and higher throughput capability than hemocytometry. The LDH assay was effective in measuring dead cell density in monolayer cultures and in alginate-encapsulated cells simply by measuring the LDH concentration secreted into the medium. Further validation of these assays was shown in two additional cell lines (rat muscle and mouse embryonic fibroblasts). The MTT and LDH assays are particularly significant in the rapid evaluation of in vitro cell encapsulation device design.     

Degradation of p-nitrophenol and pentachlorophenol mixtures by Sphingomonas sp. UG30 in soil perfusion bioreactors

The degradation of mixtures of pentachlorophenol (PCP) and p-nitrophenol (PNP) were evaluated in pure cultures of Sphingomonas sp. UG30, statically incubated soils (60% water-holding capacity) and soil perfusion bioreactors where encapsulated cells of UG30 were used as a soil inoculant. In pure-culture studies, conditions were optimized for mineralization of PCP and PNP mixtures at concentrations of 30 mg l⁻¹ each. Optimum in vitro mineralization of PCP and PNP mixtures by UG30 was facilitated using ammonium phosphate as a nitrogen source, while inhibition was observed with ammonium nitrate. The bioreactor system used columns containing soil treated with mixtures of 100, 225 or 500 mg kg⁻¹ of PCP and PNP. Rapid dissipation of both substrates was observed at the 100 mg kg⁻¹ level. Inoculation with UG30 enhanced PCP degradation at the 100 mg kg⁻¹ level in bioreactors but not in static soil microcosms. At higher PCP and PNP concentrations (225 mg kg⁻¹), occasional complete degradation of PNP was observed, and PCP degradation was about 80% compared to about 25% in statically incubated soils after 20 days at 22°C. There was no additional degradation of the PCP and PNP mixtures attributable to inoculation with encapsulated cells of UG30 in either soil system at concentrations of 225 or 500 mg kg⁻¹. Journal of Industrial Microbiology & Biotechnology (2000) 25, 93–99. Received 25 February 2000/ Accepted in revised form 07 June 2000     

Degradation of phenol by polymer entrapped microorganisms

Summary A Pseudomonas sp. which was isolated from phenol-containing soil was immobilized in alginate and polyacrylamide-hydrazide (PAAH) and cultivated in a special airlift fermenter.The immobilized Pseudomonas sp. was able to degrade phenol at initial concentrations up to 2 g/l in less than 2 days, although the free cells did not grow at this concentration.The immobilization materials act as a protective cover against phenol, PAAH being more effective than alginate. The degradation activity as well as the outgrowth of bacteria can be manipulated by the concentration of the immobilization material, the temperature and the nitrogen content in the medium.The cells grew predominantly in microcolonies in the outer area of the beads when nitrogen was available as 1.0g NH₄NO₃/l and 0.5g (NH₄)₂SO₄/l.Prof. Dr. A. Fiechter dedicated to his 60th birthday     

Plant regeneration from alginate-encapsulated shoot tips of Phylianthus amarus schum and thonn, a medicinally important plant species

Summary A method was developed for plant regeneration from alginate-encapsulated shoot tips of Phyllanthus amarus. Shoot tips excised from in vitro proliferated shoots were encapsulated in calcium alginate beads. The best gel complexation was achieved using 3% sodium alginate and 75 mM CaCl₂·2H₂O. Maximum percentage response for conversion of encapsulated shoot tips into plantlets was 90% after 5 wk of culture on Murashige and Skoog (MS) medium without plant growth regulator. The regrowth ability of encapsulated shoot tips was affected by the concentration of sodium alginate, storage duration, and the presence or absence of MS nutrients in calcium alginate beads. Plantlets with well-developed shoot and roots were transferred to pots containing an autoclaved mixture of soilrite and peat moss (1∶1). The conversion of encapsulated shoot tips into plantlets also occurred when calcium alginate beads were directly sown in autoclaved soilrite moistened with 1/4-MS salts. Encapsulation of vegetative propagules in calcium alginate beads can be used as an alternative to synthetic seeds derived from somatic embryos.