Effect of alginate encapsulation and selected disinfectants on survival of and phenanthrene mineralization byPseudomonas sp UG14Lr in creosote-contaminated soil

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.

Enhancing cell survival of atrazine degrading Rhodococcus erythropolis NI86/21 cells encapsulated in alginate beads

AIMS

To develop a method to produce beads with encapsulated Rhodococcus erythropolis NI86/21 with high cell density, extended shelf life, ease of handling and good atrazine degradation capabilities in both liquid and in agricultural soil.

METHODS AND RESULTS

Our findings show that the supplementary recovery step in nutrient broth media shortly after cell encapsulation facilitates cell survival in both wet and dry beads upon extended storage at 4 degrees C. Air drying has little or no impact on encapsulated R. erythropolis cell's ability to degrade atrazine in liquid or soil. Bead storage for periods extending up to 12 months at 4 degrees C did not affect the capacity of R. erythropolis encapsulated cells to degrade atrazine in either BMN or nonsterile soil extracts. Bentonite-amended beads formulated with 1% skim milk and exposed to the supplementary growth step, outperformed all other bead formats. These beads provided adequate numbers of vigorous R. erythropolis cells in either liquid or soil media to degrade atrazine.

CONCLUSIONS

Supplementary growth in nutrient broth media immediately following cell encapsulation greatly enhances R. erythropolis cells survival in both wet and dry beads upon extended storage at 4 degrees C. Wet and dried beads have similar capacity for atrazine degradation, and their usefulness and appeal in agronomic practise will only be known after bioassay evaluation and successful demonstration at field scale using incurred residues.

SIGNIFICANCE AND IMPACT OF THE STUDY

R. erythropolis NI86/21 encapsulated cells have the potential to reduce residual atrazine in soil, thereby minimizing the likelihood of off-site transport to ground or river water and reduce the loss of crops because of phytotoxicity of residual herbicide. Owing to their ease of handling, storage and possible compatibilities with pre-existing mechanical equipment, dried bead formats are ideally suited for agricultural and remediational applications.

Atrazine degradation by encapsulated Rhodococcus erythropolis NI86/21

AIMS

To develop an encapsulation procedure for Rhodococcus erythropolis NI86/21 and demonstrate its use as a slow-release inoculant for reducing atrazine levels in aquatic and terrestrial environments.

METHODS AND RESULTS

Alginate encapsulation procedures were developed for the atrazine-degrading bacteria R. erythropolis NI86/21. Several bead amendments, including bentonite, powdered activated carbon (PAC) and skimmed milk (SM), were evaluated for slow release of R. erythropolis NI86/21 and efficacy of atrazine degradation. All bead types demonstrated a capacity to degrade atrazine in basal minimal nutrient buffer whilst continually releasing viable bacterial cells. We found that the addition of bentonite hastened cell release whilst SM sustained cell viability in bead formulations. Reducing the percentage of SM to 1% (w/v) resulted in faster rates of atrazine degradation in both liquid and soil, and was found to prolong cell survival upon bead storage. Limited oxygen transfer affects the capacity of the encapsulated R. erythropolis cells to degrade atrazine.

CONCLUSIONS

Degradation studies have demonstrated the efficacy of R. erythropolis encapsulated cells to degrade atrazine in amended liquid and soil. However, in their current formulation, the wet alginate-based beads are impractical for field application because of their poor cell viability during storage.

SIGNIFICANCE AND IMPACT OF THE STUDY

R. erythropolis NI86/21-encapsulated cells have the potential to reduce atrazine residues in a number of soil and water environments, possibly ensuring the continued registration and use of atrazine in agriculture by minimizing or eliminating nontarget effects.

Biodegradation of gasoline by gellan gum-encapsulated bacterial cells

Encapsulated cell bioaugmentation is a novel alternative solution to in situ bioremediation of contaminated aquifers. This study was conducted to evaluate the feasibility of such a remediation strategy based on the performance of encapsulated cells in the biodegradation of gasoline, a major groundwater contaminant. An enriched bacterial consortium, isolated from a gasoline-polluted site, was encapsulated in gellan gum microbeads (16-53 microm diameter). The capacity of the encapsulated cells to degrade gasoline under aerobic conditions was evaluated in comparison with free (non-encapsulated) cells. Encapsulated cells (2.6 mg(cells) x g(-1) bead) degraded over 90% gasoline hydrocarbons (initial concentration 50-600 mg x L(-1)) within 5-10 days at 10 degrees C. Equivalent levels of free cells removed comparable amounts of gasoline (initial concentration 50-400 mg x L(-1)) within the same period but required up to 30 days to degrade the highest level of gasoline tested (600 mg x L(-1)). Free cells exhibited a lag phase in biodegradation, which increased from 1 to 5 days with an increase in gasoline concentration (200-600 x mg L(-1)). Encapsulation provided cells with a protective barrier against toxic hydrocarbons, eliminating the adaptation period required by free cells. The reduction of encapsulated cell mass loading from 2.6 to 1.0 mg(cells) x g(-1) bead caused a substantial decrease in the extent of biodegradation within a 30-day incubation period. Encapsulated cells dispersed within the porous soil matrix of saturated soil microcosms demonstrated a reduced performance in the removal of gasoline (initial concentrations of 400 and 600 mg x L(-1)), removing 30-50% gasoline hydrocarbons compared to 40-60% by free cells within 21 days of incubation. The results of this study suggest that gellan gum-encapsulated bacterial cells have the potential to be used for biodegradation of gasoline hydrocarbons in aqueous systems.