Biofilms were formed on poly(ethylene oxide) (PEO) cryogels by using bacteria cultured from xenobiotics polluted environments and their phenol biodegrading capability was studied. PEO cryogels were synthesized via UV irradiation cross linking of moderately frozen aqueous system. Two xenobiotics tolerant bacterial isolates KCM R5 and KCM RG5 were used to construct the biofilms on the cryogels.

Obtained PEO-biofilms were assessed for their ability to remove phenol at concentrations 300, 400, 600 and 1000 mg L-1 for 28 days. The biofilm PEO-KCM RG5 removed phenol up to 600mg L-1/24 h, whereas the biofilm PEO-KCM R5 was able to degrade up to 1000 mg L-1/24 h. The high content of free-water in the cryogels allowed reproduction of the used bacteria. The high content of free-water in the cryogels allowed reproduction of the used bacteria. Short initial adaptation of the PEO-bio�lms with 100 mg L-1/24 h phenol was crucial for protecting the bacterial cells from dead. The obtained results showed that the liquid debit through the bio�lms on the 28th day of the experiments was lower than at the beginning. The cryogels demonstrated non-toxicity, high biocompatibility with bacteria and excellent mechanical characteristics. After aggressive phenol treatment the PEO-biofilms remained compact, porous and

elastic. The investigated new biological materials demonstrate potential for application in the industrial wastewater treatment technologies

Bogdanov, Vladimir

Dimkov, Raycho

Golovinsky, Evgeny

Gorbovskaya, Alla

Petrov, Petar

Satchanska, Galina

Selenska-Pobell, Sonja

Topalova, Yana

Tsvetanov, Christo

English

New Bulgarian University Scholar Electronic Repository

Доклади на Българската академия на наукитеComptes rendus de l’Acade´mie bulgare des SciencesTome 62, No 8, 2009BIOLOGIEBiotechnologiePHENOL BIODEGRADATION BY TWO XENOBIOTICS-TOLERANT BACTERIA IMMOBILIZEDIN POLYETHYLENE OXIDE CRYOGELSGalina Satchanska∗,∗∗, Yana Topalova∗∗∗, Raycho Dimkov∗∗∗,Petar Petrov∗∗∗∗, Christo Tsvetanov∗∗∗∗, Sonja Selenska-Pobell∗∗∗∗∗,Alla Gorbovskaya∗∗∗∗∗∗, Vladimir Bogdanov∗∗∗∗∗∗,Evgeny Golovinsky∗(Submitted on April 24, 2009)AbstractBiofilms were formed on poly(ethylene oxide) (PEO) cryogels by using bac-teria cultured from xenobiotics polluted environments and their phenol biode-grading capability was studied. PEO cryogels were synthesized via UV irra-diation cross linking of moderately frozen aqueous system. Two xenobioticstolerant bacterial isolates KCM R5 and KCM RG5 were used to construct thebiofilms on the cryogels.Obtained PEO-biofilms were assessed for their ability to remove phenolat concentrations 300, 400, 600 and 1000 mg L−1 for 28 days. The biofilmPEO-KCM RG5 removed phenol up to 600 mg L−1/24 h, whereas the biofilmPEO-KCM R5 was able to degrade up to 1000 mg L−1/24 h. The high contentof free-water in the cryogels allowed reproduction of the used bacteria. Shortinitial adaptation of the PEO-biofilms with 100 mg L−1/24 h phenol was crucialfor protecting the bacterial cells from dead. The obtained results showed thatthe liquid debit through the biofilms on the 28th day of the experiments waslower than at the beginning. The cryogels demonstrated non-toxicity, highbiocompatibility with bacteria and excellent mechanical characteristics. Afteraggressive phenol treatment the PEO-biofilms remained compact, porous andelastic. The investigated new biological materials demonstrate potential forapplication in the industrial wastewater treatment technologies.Key words: polluted environments, xenobiotics, biodegradetion, bacteriaIntroduction. In the last decade widening and reorientation of immobilizedcells and enzymes application was recorded. It comes out the previous frames ofThis work was supported by grant VUH – No 302 financed by the National Science Fund,Ministry of Science and Education, Bulgaria.957food and pharmaceutical industry [1,2] and expands in wastewater treatment anddetoxification technologies.Among the monocyclic aromatic substances phenol and its derivatives aresome of the most dangerous environmental pollutants. Because of its long termapplication in chemical-, wood-, textile- and oil processing industry the abovementioned compounds persist in the environment in high concentrations.Many bacteria from various genera are capable of phenol degradation. Repre-sentatives of Pseudomonas [3–5], Acinetobacter [6], Alcaligenes [7], and Bacillus [8]are among them. Pseudomonades, especially their environmental isolates were re-ported as most numerous and active. The biodegradation of phenol in wastewaterby immobilized cells of Pseudomonas putida was described by Loh et al. [9].In recent years different organic carriers for bacterial immobilization wereinvestigated [10,11]. Among the synthetic polymers, poly(ethylene oxide) hydro-gels are excellent candidates because they are nontoxic biocompatible materialswhich meet all of the requirements of strength, absorbency, flexibility and adhe-siveness [12]. Firstly, PEO hydrogels have been obtained in situ by γ-irradiation ofdilute aqueous solutions [13], and two decades later, via methods based on chem-ical cross linking [14]. Hydrogels of high-molecular-weight poly(ethylene oxide)have also been synthesized in situ by applying a facile procedure that involves UVcrosslinking of PEO in aqueous solution. Moreover, when the UV cross linkingis performed in a frozen aqueous system, macroporous hydrogels (cryogels) withvery high yield of gel fraction and high crosslinking density are obtained [15,16].In the present study, macroporous PEO hydrogels were investigated as carri-ers of xenobiotics degrading bacteria and the obtained PEO-biofilms were inves-tigated for their ability for phenol biodegradation.Materials and methods. 1. Cryogels preparation. High molecularweight poly(ethylene oxide) (Union Carbide; MW = 2.106 g/mol) was dissolvedin distilled water (5 wt.%) and then a photo initiator (4-benzoylbenzyl) trimethy-lammonium chloride (Aldrich; 2 wt.% with respect to the polymer) was addedunder stirring at room temperature. The resulting homogeneous solution waspoured into Teflon dishes (50 mm diameter) forming a 2.5 mm thick layer, whichwas then kept in a freezer at a temperature of −20 ◦C for 2 h. The dishes werequickly placed in a thermostatic open chamber connected with a Julabo cryostatapparatus. The frozen system was irradiated with full spectrum UV-VIS light at−20 ◦C with a Dymax 5000-EC UV curing equipment with 400 W metal halideflood lamp for 2 min (dose – 11.4 J/cm2; input power – 93 mW/cm2).The PEO cryogels were extracted in distilled water for seven days, quicklyfrozen in liquid nitrogen and freeze dried in an Alpha 1-2 Freeze Drier (MartinChrist) at −55 ◦C and 0.02 mbar for 24 h. The gel fraction (GF) yield was calcu-lated by the following equation: GF yield [%] = (weight of dried sample/initialweight of polymer)× 100.2. Microbial strains and inoculants. The studied microbial isolates were958 G. Satchanska, Y. Topalova, R. Dimkov et al.cultured from polluted soil near the Pb-Zn smelter called KCM (strain KCM R5)and from groundwater collected near the pesticide producing factory AGRIA(KCM RG5). Both manufactories are situated at a distance of about 6 km fromthe town of Plovdiv, Bulgaria. The Pb-Zn smelter is the biggest one on the BalkanPeninsula. AGRIA factory is manufacturing more than 50 various pesticides.Most of them contain in their structure monocyclic aromatic rings.The bacterial isolates KCM R5 and KCM RG5 were initially cultured in ster-ile 200 ml synthetic mineral media according to Furukawa and Chakrabarty[17] containing per 1 L: 5.6 g K2HPO4 × 3H2O, 3.4 g KH2PO4, 2 g (NH4)2SO4,0.34 g MgCl2 × 6H2O, 0.001 g MnCl2 × 4H2O, 0.0006 g FeSO4 × 7H2O, 0.026 gCaCl2×2H2O and also 0.002 g Na2MoO4×2H2O. The substances K2HPO4×3H2Oand CaCl2 × 2H2O were added at the end in order to avoid precipitation. Themedium was autoclaved at 0.8–1 atm for 30 min. To the medium 0.1% sterileglucose and 100 mg L−1 phenol were added. The bacterial strains were cultivatedin Erlenmeyer flasks for 24 h/180 rpm/28 ◦C to reach OD of 0.300. The OD wasmeasured spectrophotometrically at λ = 450 nm using 10 mm cuvettes. After-wards the bacterial strains used were adapted to low phenol concentrations. Forthis in 300 mL sterile synthetic mineral medium 100 mg L−1 phenol and 20 ml ofthe pre-cultivated strains KCM R5 and KCM RG5 were added and incubated for72 h/180 rpm/28 ◦C until reaching an OD of 0.550.3. Cryogels adaptation and biofilms construction. PEO cryogels wereadapted for 24 h in 100 mL synthetic mineral medium without shaking. To eachone of the adapted bacterial cultures KCM R5 and KCM RG5 grown in a volumeof 300 mL an equal volume sterile mineral medium was added and the resultingmixture was then divided in three equal parts each of 200 mL. The bacterialcultures were transferred in vessels, tightly locked and shaken with the addedPEO-cryogels gently at 100 rpm for 48 h. The resulted PEO-biofilms were placedon the membrane filter of reusable bottle-Top Filter 47 mm, 500 mL (Nalgene,Rochester, USA). The locking ring was screwed up softly in order to avoid cuttingof the biofilm. The media run through the PEO-biofilms by its gravity forces.The biofilms were prepared in triplicates.4. Phenol removal. In order to clean the constructed PEO-biofilms fromresidual compounds 250 mL synthetic mineral medium with no phenol added wasrun through them for 24 h. The PEO-biofilms were then treated for 28 daysconsequently with sterile mineral medium containing increasing concentrations ofphenol as follows: 7 days with 300 mg L−1, 5 days with 400 mg L−1, 4 days with600 mg L−1 and 12 days with 1000 mg L−1. The phenol amount in the filteredliquid was measured every 24 h. The phenol concentration was determined col-orimetrically following the pyramidone based method [18]. In 12.375 mL distilledwater were added 0.125 mL filtrate sample, 0.250 mL ammonia chloride buffer,pH 9.3 (adjusted with ammonia), 0.125 mL 3.5% pyramidone and 0.375 ml am-monia persulfate, pH 7.0 (adjusted with ammonia). After mixing the reaction wasCompt. rend. Acad. bulg. Sci., 62, No 8, 2009 959kept at room temperature for 45 min. The absorption was measured spectropho-tometrically at λ = 540 nm against the control in which distilled water insteadof filtered liquid was added. The phenol amount was determined according to astandard curve.The efficiency of the phenol removal was calculated according to the formulaEfficiency in (X) hour (%) =Ci − CfCi× 100,where Ci is the initial phenol concentration in the filtration system, and Cf is thephenol concentration in the filtrate.Results and discussion. PEO cryogel of high gel fraction yield (93%)was synthesized via UV irradiation of moderately frozen semi-diluted solutionof PEO and photo initiator for extremely short time and subsequent thawingas described elsewhere [15,16]. The cryogel obtained was heterogeneous, super-macroporous material with large interconnected pores (50–100 µm) surroundedby dense thin walls (ca. 1–2 µm). Importantly, more that 80% of the water inthe cryogel is capillary-bound water that fills the space of the macro pores. Thefreeze-dried PEO cryogel possesses the original macro porous structure (Fig. 1)and, once immersed in the suspension, the liquid fills the channels (interconnectedpores) of the cryogel.The isolate KCM R5 was determined as Gram(−), motile and oval-shapedbacterium while the isolate KCM RG5 as a Gram(+), motile and a rod-shapedone. KCM R5 was affiliated with high extent of 16S rRNA gene similarity toPseudomonas rhodesiae and KCM RG5 – to Bacillus subtilis. KCM R5 andKCM RG5 demonstrated tolerance to heavy metals such as Pb, Mn and Cdand could grow in the presence of phenol, ortho-nitrophenol, 2,4-dinitrophenol,Fig. 1. SEM micrograph of PEO cryogels, ×10002,5-nitrophenol, pentachloro-phenol, and 2,4-dichloropheno-xiacetic acid as a sole carbonand energy source [19,20]. Themorphology of the isolates isshown in Fig. 2.Both isolates were im-mobilized in the cryogels ofpoly(ethylene oxide) and twoPEO-biofilms were obtained.Phenol biodegradation byconstructed PEO-biofilms wasstudied at 28 ◦C. According toPolymenakou and Stepha-nou [4] the optimal phenoldegradation at concentrations960 G. Satchanska, Y. Topalova, R. Dimkov et al.1 2Fig. 2. Morphology of the environment bacterial isolates KCM-R5 (1) and KCM-RG5 (2)of up to 500 mg L−1 was realized by a Pseudomonas sp. strain at 30 ◦C. Tsai andYuang [5] described maximum rates of phenol degradation at 30 ◦C and at pH 7and demonstrated that no considerable phenol depletion was performed at 10 ◦Cor 40 ◦C. In addition to the temperature they described also a pH influence onthe phenol biodegradation. Phenol biodegradation at a higher concentration of1000 mg L−1 was studied for another member of the genus Pseudomonadaceae [21].Only one case of phenol degradation at a higher concentration of 1600 mg L−1was described up to date. It concerned a strain of Alcaligenes faecalis and wasreported by [7]. In contrast to the bacterial strains studied in our work, this01020304050607080901001 2 3 4 5 6 7 8 9 10 11 12 13 14 15 16 17 18 19 20 21 22 23 24 25 26 27 28Time(days)Efficiency(%)Biofilm PEO-KCM R5Biofilm PEO-KCM Rg5Fig. 3. Efficiency of the phenol biodegradation by biofilms PEO-KCM R5 and PEO-KCM RG5.Biofilms were treated for 28 days with different phenol concentrations: 300 mg L−1 (1–7 day),400 mg L−1 (8–12 day), 600 mg L−1 (12–16 day) and 1000 mg L−1 (17–28 day)4 Compt. rend. Acad. bulg. Sci., 62, No 8, 2009 961bacterium was not isolated from an industrial area. Similar data about represen-tatives of the genera Pseudomonas and Bacillus are not yet reported.Our results showed that both biofilms removed phenol at almost equal amountat phenol concentration of 300, 400 and 600 mg L−1 for 24 h (17th day) reachingefficiency up to 100% (Fig. 3). When treating the PEO-biofilms with 1000 mgL−1/24 h phenol the biofilm PEO-KCM R5 kept its ability for phenol removalwhile the biofilm PEO-KCM RG5 loose it and did not restore it up to the end ofthe experiment. As it is shown in Fig. 3, the biodegradation efficiency of the PEO-KCM R5 biofilm remains high – 96–98%, in contrast to the biofilm PEO-KCMRG5 which efficiency was reduced to 5%.T a b l e 1Volumes of the liquid filtered through the biofilmsDayInfluent (mineral media +phenol (ml))Eﬄuent of biofilmPEO-KCM-R5 (ml)Eﬄuent of biofilmPEO-KCM-RG5 (ml)1st 250 212∗ 50∗2nd 250 224 453rd 250 148 394th 250 90 385th 250 56 916th 250 33 697th 250 24 588th 250 16 509th 250 17 4310th 250 15 3611th 250 15 3512th 250 14 3613th 250 14 3614th 250 14 3715th 250 12 3516th 250 12 3717th 250 12 3718th 250 10 2919th 250 10 2920th 250 10 2921st 250 12 3022nd 250 12 3023rd 250 19 3024th 250 19 3025th 250 14 2526th 250 14 2527th 250 14 2528th 250 7 15∗Data are average value of three replicates962 G. Satchanska, Y. Topalova, R. Dimkov et al.1 2Fig. 4. SEM micrograph of biofilms after phenol treatment (1) biofilm PEO-KCM R5 and (2)biofilm PEO-KCM RG5As it is evident from the results presented in Fig. 3 the first phenol portionof 1000 mg L−1/24 h caused immediate decrease of the phenol biodegradation bythe biofilm PEO-KCM RG5. This biofilm was not able to bear higher phenolconcentration than 600 mg L−1/24 h.It must be remarked that in the course of our experiments the volumes ofthe filtered liquid decreased up to 10 times in comparison to those of the initialdays (see Table 1). The probable reason for the volume decreasing is the intensivebacterial reproduction in the cryogels.SEM micrographs of two studied PEO-biofilms after 28 days of phenol treat-ment are shown in Fig. 4. Our results showed that biofilms remained compactand elastic, with no damages.Conclusions. PEO cryogels showed high biocompatibility with xenobioticsdegrading bacterial strains KCM R5 and KCM RG5. The biofilm PEO-KCMRG5 utilized phenol up to 600 mg L−1/24 h while the biofilm PEO-KCM R5 wasable to utilize phenol at 1000 mg L−1/24 h. In the course of our experiments thevolumes of the filtered liquid decreased up to 10 times compared to those of theinitial days. The long term phenol treatment does not influence the compactnessand mechanical strength of the constructed PEO biofilms.Acknowledgements. We thank Mrs. Elmira Daskalova from Sofia Univer-sity for her valuable technical assistance.REFERENCES[1] Ogbonna C., M. Matsumura, H. Kotaoka. Process Biochem., 26, 1991, 109–121.[2] Westrin B. A., A. Axelsson, G. Zacchi. J. Controlled Release, 30, 1994,189–199.Compt. rend. Acad. bulg. Sci., 62, No 8, 2009 963[3] Neumann G., R. Teras, L. Monson, M. Kavisaar, F. Schauer, H. Heip-ieper. Appl. Environ. Microbiol., 70, 2004, 1907–1912.[4] Polymenakou P., E. Stephanou. Biodegradation, 16, 2005, No 5, 403–413.[5] Tsai S., R. Juang. J. 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Bonchev Str., Bl. 211113 Sofia, Bulgaria∗∗New Bulgarian University21, Montevideo Str.1618 Sofia, Bulgaria∗∗∗Faculty of BiologySt. Kliment Ohridsky Sofia University8, Dragan Tsankov Blvd1164 Sofia, Bulgaria∗∗∗∗Institute of PolymersBulgarian Academy of SciencesAcad. G. Bonchev Str., Bl. 103A1113 Sofia, Bulgaria∗∗∗∗∗Forschungszentrum Dresden-Rossendorf01314 Dresden, Germany∗∗∗∗∗∗Saint Petersburg State University199034 Saint Petersburg, Russia964 G. Satchanska, Y. Topalova, R. Dimkov et al.

Microbiological and Enzymological Aspects of Phenol Biodegradation,

No 2, 252{259. Institute of Molecular Biology Bulgarian Academy of Sciences Acad.

Preparation Methods and Structure of Hydrogels,

Phenol Biodegradation by Two Xenobiotics-Tolerant Bacteria Immobilized in Polyethylene Oxide Cryogels

Phenol Biodegradation by Two Xenobiotics-Tolerant Bacteria Immobilized in Polyethylene Oxide Cryogels

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