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Haloalkalophilic cellulose-degrading bacteria isolated from an alkaline saline soil.

Cellulose is the main component of plants and the most abundant polysaccharide on earth (1). Its characteristics have been investigated intensively (2). The microorganisms involved in its breakdown are important in ecological terms, i.e. their importance in the global carbon cycle, and in economic terms, i.e. their role in biofuel production (3).

Cellulose is a polysaccharide composed of anhydroglucose units, which are held together by [beta]-1,4 glucosidic bonds. In addition, the P configuration allows long cellulose chains to be formed linearly, which are not isolated, but bonded together by intramolecular hydrogen bonds forming a crystalline supramolecular structure resistant to hydrolysis (4).

The enzymatic hydrolysis of cellulose involves the sequential functioning and synergistic action of a group of cellulases, which have different binding sites, due to the complex nature of the cellulose molecule (1). Cellulases belong to a large family of glycosyl hydrolases (GH) and are common in some bacteria, fungi, plants and animals (6). These enzymes include cellobiohydrolases (EC 3.2.1.91), endo-1,4-[beta]-glucanases (3.2.1.4), [beta]-glucosidases (EC 3.2.1.21), endo-1,4-[beta]-xylanases (EC 3.2.1.8), [beta]-xylosidases (EC 3.2.1.37), [alpha]-L-arabinofuranosidases (EC 3.2.1.55), acetyl xylan esterase (EC 3.1.1.6), [beta]-glucuronidase (EC 3.2.1.131), pectatelyase (EC 4.2.2.2) and endo-[beta]-1,4-D-mannanase (EC 3.2.1.78).

Cellulases are enzymes produced by a variety of bacteria and fungi under aerobic, anaerobic, mesophilic or thermophilic conditions. However, only some of them produce extracellular cellulase enzymes capable of hydrolyzing cellulose in extreme pH conditions (6). For instance, [beta]-1,4-endoglucanase is produced by the bacteria Cellulomonas pachnodae found in the intestines of Pachnoda marginata larvae. These larvae are found in acidic environment with pH ranging from pH 4.8 to 6.07 and an alkalophilic Bacillus produces an endoglucanase with a pH range of 7.0 to 12.0 (8). An alkaline Nocardiopsis is another genus that produces an endo [beta]-1-4 D-glucanase (9). These enzymes have great economic potential in many industrial processes, i.e. agriculture, food, feed and drinks, detergents, textile, leather, pulp and paper (10).

Microorganisms that produce cellulases in extreme alkaline conditions or extremoenzymes have rarely been studied. Jones et al., 11 for instance found cellulolytic activity in genus Cellulomonas with optimal growth between pH 9.0 and 10.0. In a previous study, soil of former lake Texcoco with pH 9.8 and electrolytic conductivity (EC) 32.7 dS [m.sup.-1] showed cellulolytic activity. Emission of [sup.14]C[O.sub.2] occurred when the hemicellulose fraction of 14C labelled-maize was applied to the soil (12). It is unknown, however, which microorganisms were involved in this process. Consequently, the objective of this study was to isolate, identify and characterize microorganisms involved in the degradation of cellulose in this extreme alkaline saline environment.

MATERIALS AND METHODS

Site description

Lake Texcoco is located to the north-east of Mexico city at 2240 m above sea level, with an average annual temperature of 16[degrees]C and precipitation of 705 mm (13). A soil sample was taken from the 5 to 20 cm layer (19[degrees]26'45" N, 97[degrees]56'16" W). The alkaline saline soil had pH 9.5 and electrolytic conductivity (EC) 115 dS [m.sup.-1]. Sampled soil was taken to the laboratory on ice immediately. Isolated strain

A soil extract used was prepared by adding 10 g soil to 25 ml distilled water and the solution was centrifuged at 6,000 rpm for 10 min. The microorganisms that degrade cellulose were isolated on Petri dishes with Congo red agar medium (14) that contained ([l.sup.-1]): soil extract, 250 ml; MgS[O.sub.4] x 7[H.sub.2]0, 0.25 g; [K.sub.2]HP[O.sub.4], 0.5 g; Congo red, 0.18 g; gelatine, 1.8 g; carboxymethylcellulose (CMC), 2.0 g; agar 20 g. An aliquot of 100 [micro]l soil suspension was diluted ([10.sup.-1] to [10.sup.-6]) and incubated on the culture medium mentioned above at 30[degrees]C for 24 to 48 h in triplicate.

DNA extraction, PCR amplification and phylogenetic analysis

The extraction of genomic DNA for molecular characterization of each of the isolates was done using the QIAcube automatic system with the DNeasy Blood & Tissue Kit (Qiagen, Valencia, USA). Its integrity was assessed by visualization on agarose gel electrophoresis in 0.8%. Different aliquots of genomic DNA were stored at -20[degrees]C until processing. Amplification of DNA from each of the strains was done using the amplification protocol described by Rusznyak et al., (15). The PCR reaction used a 25 [micro]l mixture with ([micro]l): Buffer, 2.5, 25 mM; Mg[Cl.sub.2] 1.5; Oligonucleotides, 1.25, 60 mM; dNTPs, 0.5; genomic DNA, 1; Taq Polymerase, 0.125; BSA (bovine serum albumin), 7.5; [H.sub.2]O, 9.125; Dimethylsulfoxide, 1.5. The primers used were 27F (5'-AGAGTTTGATCM TGGCTCAG-3') and 1492R (5'-TACGGYTAC CTTGTTACGACTT-3'). The samples were placed in a thermocycler under the following conditions: initial heating at 94[degrees]C for 4 min (initial denaturation), 35 cycles of heating at 94[degrees]C for 1 min to denature, 1 min at 57[degrees]C for alignment and 2 min at 72[degrees]C for polymerization, and a final polymerization step at end of 72[degrees]C for 10 min. Finally, the reaction was kept at 4[degrees]C until the amplification reaction. The size of the amplicons was approximately 1465 bp.

The PCR product was purified and sequenced by MACROGEN (http://dna.macrogen.com/eng/). The sequences obtained were compared with reference 16S rRNA gene sequences retrieved from GenBank/EMBL by means of a BLAST search (16). Multiple alignments with sequences of the most closely related bacteria and calculations of sequence similarity were done using CLUSTAL X (17). Maximum likelihood phylogenetic analysis was performed using the online program PhyML 3.0 (http://www.atgcmontpellier.fr/phyml/) (18); with the data sets using the general time reversible model substitution model (19).

Enzyme assays

Strains were inoculated an Ar culture medium. The optical density of the medium was adjusted to 0.05 units in a Spectrophotometer 3000 SmartSpecTM flow, Catalogue Number 170-2501 at 600 nm. Cultures were incubated at 30[degrees]C and 120 rpm for 60 days. Cellulose activity of the above mentioned isolates was confirmed by measuring the amount of reducing sugars in Ar culture medium (22). One ml aliquot was taken approximately every 5 days for 2 months, centrifuged at 13,000 rpm for 3 min. A500 [micro]l aliquot of the supernatant was taken and added to 500 pl glycine buffer with 1% low viscosity CMC. The samples were incubated at 25[degrees]C, 37[degrees]C, 50[degrees]C, 70 [degrees]C and 90[degrees]C at pH 9, and at pH 7, 8, 9, 10 and 11 at 50[degrees]C for 5 min. The temperatures were varied around the optimum, which was 50[degrees]C, and around the optimum pH of 9.0 (20). The mixture was boiled for 5 min and then cooled on ice for 5 min. The sample was read in a spectrophotometer at 540 nm to measure the reduced sugars. The amount of reducing sugars was calculated using a standard glucose curve (21). A milliunit is considered the amount of enzyme needed to obtain 2.5 micromoles of reducing sugar per min and divided by thousand.

RESULTS AND DISCUSSION

Fifty isolates were obtained with the Congo red agar culture medium with CMC. Only seven strains (1r, 3r, 5r, 6r, 7r, 8r, and 16r) showed hydrolytic activity on Congo red agar medium with CMC as C source (Table 1). These strains showed a hydrolysis area ranging from 0.8 to 5.0 cm and an HC value (area compensation colony diameter) from 1.6 to 10.0; similar as those reported by Lu et al., (22). These results demonstrated that all strains have hydrolytic capacity in this medium and a possible production of extracellular enzymes or cellulases within 10 days.

The seven microorganisms that showed hydrolytic activity on Congo red agar media were isolated and characterized based on their 16S rRNA gene sequence. All seven isolates belonged to the phylum Actinobacteria (Table 1). Arthrobacter globiformis (strain 5r) is a well studied marine bacteria with resistance to low temperatures (23), although it is not clear if it can degrade cellulose. Nesterenkonia halotolerans (strain 16r) was first isolated from a hypersaline soil, but little is known about its metabolic pathways (24). Different strains belonging to the genus Streptomyces are known to contain cellulases (25), but it is not clear if S. aurantiacus (strains 3r and 6r) shows cellulolytic activity. Cellulomonas cellasea (strain 7r) is known to possess cellulolytic activity (26). Little information exists about C. bogoriensis (strain 1r) (11,21). It was described by Jones et al., (11) as 'an alkaliphilic, slightly halotolerant, chemo-organotrophic, Gram-positive, rod-shaped bacterium ' and was isolated from the sediment of the littoral zone of Lake Bogoria, Kenya'. They stated that its optimal growth occurred between pH 9.0 and 10.0. Nocardiopsis dassonvillei (strain 8r) belongs to the genus Nocardiopsis, a widespread group, which is versatile and pathogenic that produces a wide range of bioactive metabolites (28-29). It is known to show cellulolytic activity (30).

Cellulose alone can not be degraded completely by physical methods and microbial enzymes are required for its complete mineralization; such as those produced by cellulolytic microorganisms isolated in this study. While there are many reports on the isolation of cellulose degrading microorganisms from different ecosystems (31), few studies have isolated or identified cellulolytic bacteria from saline-alkaline soils. Grant et al.,32 reported on a wide range of halophilic bacteria isolated from saline environments, such as seas with dissolved salts (> 30%). They found phylotypes belonging to the genus Marinococcus and Sporosarcina, and strains of Bacillus salinicoccus (33,34-35). Ramirez et al., (36) reported on halo-alkaliphilic bacteria in different geographical regions of Mexico belonging to the genera Bacillus and Halomonas.

In previous studies of Valenzuela-Encinas et al.,37 and Soto-Padilla et al. (38), phylotypes were identified in the alkaline saline Texcoco soil belonging to the genera Kocuria, Micrococcus, Salinicoccus, Kurthia, Gracilibacillus, Bacillus, Halomonas, Arthrobacter, Nesterenkonia, Cellulomonas, Streptomyces and Nocardiopsis; all belonging to the order Actinomycetales or Firmicutes. Some strains belonging to these genera are known to show cellulolytic activity. In the study reported here, some of the above-mentioned genera, i.e. Arthrobacter, Nesterenkonia, Cellulomonas, Streptomyces and Nocardiopsis, were isolated.

Of the seven strains that showed hydrolytic activity on Congo red, only two showed cellulolytic enzyme activity. Their cellulolytic activity was further investigated using the DNS method.

Strain 1r had a 99.7% similarity with Cellulomonas bogoriensis and strain 8r 99.69% with Nocardiopsis dassonvillei (Figure 1). These two strains were tested at different pH (7 to 11) and temperatures (from 25 to 90[degrees]C) (Figures 2, 3, 4, 5). Strain 1r (Cellulomonas bogoriensis) had a maximum activity of 177 mU [ml.sup.-1] at pH 9 and 37[degrees]C and a minimum of activity 19.6 mU [ml.sup.-1] at pH 8 and 50[degrees]C. Strain 8r (Nocardiopsis dassonvillei) showed a maximum activity of 136 mU ml'1 at pH 9 and 37[degrees]C and a minimum of activity 14.6 mU [ml.sup.-1] at pH 7 and 50[degrees]C.

The use of a second quantitative method, i.e. the DNS technique, allowed to confirm the presence of microorganisms with cellulolytic activity producing extracellular enzymes (39-40). Of the seven strains that showed hydrolytic activity on Congo red, only two showed cellulolytic enzyme activity, i.e. strains 1r and 8r. The maximum cellulolytic activity of 177 mU [ml.sup.-1] for C. bogoriensis and 136 mU [ml.sup.-1] for N. dassonvillei was higher than values reported by Amore et al.,4 ranging from 30 to 110 mU ml--1 for cellulolytic microorganisms in an industrial waste based compost, but lower than values reported for cellulolytic microorganisms in a lower stalks-vegetable waste co-composting system (22). The strains 1r and 8r grew also on xylan and lignin and showed xylanase and ligninase activity (Data not shown). This study suggests that saline alkaline soil may be a source of new strains of cellulolytic bacteria, and these two species might play an important role in cellulose degradation in extreme saline environments.

CONCLUSION

Seven strains were isolated from the saline-alkaline soil that showed hydrolytic activity on Congo red agar. These strains belonged to the genera Cellulomonas, Nocardiopsis, Streptomyces, Arthrobacter and Nesterenkonia, all of them Actinomycetes. Two of those seven strains, one with 99.7% similarity with Cellulomonas bogoriensis and one with 99.69% similarity with Nocardiopsis dassonvillei showed cellulolytic activity as evidenced by the production of reducing sugars. The C. bogoriensis strain had a maximum cellulolytic activity of 177 mU [ml.sup.-1] at pH 9 and 37[degrees]C, and the N. dassonvillei strain 136 mU [ml.sup.-1]. Suggest that saline alkaline soil may be a source of novel strains and extremoenzymes of cellulolytic bacteria.

ACKNOWLEDGEMENTS

We thank 'Comision Nacional de Agua' for access to the former lake Texcoco. This work was funded by the 'Instituto de Ciencia y Tecnologia del Distrito Federal' project ICyTDF/295/2009. M.P. L.-R., K.B. S.-L., Y S.-G., VM. R.-V received grant-aided support from 'Consejo Nacional de Ciencia y Tecnologia' (CONACyT, Mexico).

REFERENCES

(1.) Lee, S.H., Doherty, T. V., Linhardt, R.J., Dordick, J.S. Ionic liquid-mediated selective extraction of lignin from wood leading to enhanced enzymatic cellulose hydrolysis. Biotechnol Bioeng., 2009; 102:1368-1376.

(2.) Shu-Huei, Y, Hao-Ying, H., Jen-Chieh, P., Deh-Wei, T., Chwen-Ming, S., Min-Lang, T., Yi-Chin, T., Fwu-Long, M. Active films from water-soluble chitosan/cellulose composites incorporating releasable caffeic acid for inhibition of lipid oxidation in fish oil emulsions. Food Hydrocolloids, 2013; 32:9-19.

(3.) den Haan, R., Kroukamp, H., Mert, M., Bloom, M., Gorgens, J.F., van Zyl, W.H. Engineering Saccharomyces cerevisiae for next generation ethanol production. J Chem Technol Biotechnol., 2013; 88:983-991.

(4.) Wang, X., Peng, Z., Sun, X., Liu, D., Chen, S., Li, F., Xia, H., Lu, T. The FPase properties and morphology changes of a cellulolytic bacterium, Sporocytophaga sp. JL-01, on decomposing filter paper cellulose. J Gen Appl Microbiol., 2012; 58:429-436.

(5.) Wang, L.W., Huan, X., Zhou. Y., Ma, Q., Chen, Y Simultaneous cloning and expression of two cellulase genes from Bacillus subtilis newly isolated from Golden Takin (Budorcas taxicolor Bedfordi). Biochem BiophysRes Comun., 2009; 383:397-400.

(6.) Oren, A. Industrial and environmental applications of halophilic microorganisms. Environ Technol., 2010; 31:825-834.

(7.) Cazemier, A.E., Verdoes, J.C., van Ooyen, A.J., Op den Camp, H.M. Molecular and biochemical characterization of two xylanase-encoding genes from Cellulomonas pachnodae. Appl Environ Microbiol, 1999; 65:4099-4107.

(8.) Sanchez-Torres, J., Perez, P., Santamaria, R.I. A cellulase gene from a new alkalophilic Bacillus sp. (strain N186-1). Its cloning, nucleotide sequence and expression in Escherichia coli. Appl Microbiol Biotechnol., 1996; 46:149-155.

(9.) Moreira, K.E., Walther, T.C., Aguilar, P.S., Walter, P. Pil1 controls eisosome biogenesis. Mol Biol Cell, 2009; 20:809-818.

(10.) Morozkina, E.V, Slutskaya, E.S., Fedorova, T. V, Tugay, T.I., Golubeva, L.I., Koroleva, L.I. Extremophilic microorganisms: Biochemical adaptation and biotechnological application (review). Appl Biochem Microbiol., 2010; 46:114.

(11.) Jones, B.E., Grant, W.D., Duckworth, A.W., Schumann, P., Weiss, N., Stackebrandt, E. Cellulomonas bogoriensis sp. nov., an alkaliphilic cellulomonas. Int J Syst Evol Microbiol., 2005; 55:1711-1714.

(12.) Luna-Guido, M.L., Vega-Estrada, J., Ponce-Mendoza, A., Hernandez-Hernandez, H., Montes-Horcasitas, M.C., Vaca-Mier, M., Dendooven, L. Mineralization of 14C-labelled maize in alkaline saline soils. Plant Soil, 2003; 250:29-38.

(13.) Dendooven, L., Alcantara-Hernandez, R.J., Valenzuela-Encinas, C., Luna-Guido, M., Perez-Guevara, F., Marsch, R. Dynamics of carbon and nitrogen in an 'extreme' alkaline saline soil: A review. Soil Biol Biochem., 2010; 42:865-877.

(14.) Xin, H., Itoh, T., Zhou, P., Suzuki, K., Nakase, T. Natronobacterium nitratireducens sp. nov., a haloalkaliphilic archaeon isolated from a soda lake in China. Int J Syst Evol Microbiol., 2001; 51:1825-1829.

(15.) Rusznyak, A., Vladar, P., Molnar, P., Reskone, M.N., Kiss, G., Marialigeti, K., Sabry, S.A., Ghanem, N.B., Abu-Ella, G.A., Schumann, P., Stackebrandt, E., Kroppenstedt, R.M. Cultivable bacterial composition and BIOLOG catabolic diversity of biofilm communities developed on Phragmites australis. Aquat Bot., 2008; 88:211-218.

(16.) Chun, J., Lee, J.H., Jung, Y, Kim, M., Kim, S., Kim, B.K., Lim, YW. EzTaxon: a web-based tool for the identification of prokaryotes based on 16S ribosomal RNA gene sequences. Int J Syst Evol Microbiol, 2007; 57:2259-2261.

(17.) Larkin, M.A., Blackshields, G., Brown, N.P., Chenna, R., McGettingan, P.A., McWilliam, H., Valentin, I.M., Wallace, A., Wilm, R., Lopez, J.D., Thompson, T.J., Higgins, D.G. Clustal W and clustal X version 2.0. Bioinformatics, 2007; 23:2947-2948.

(18.) Guindon, S., Dufayard, J.F., Lefort, V., Anisimova, M., Hordijk, W., Gascuel, O. New algorithms and methods to estimate maximum-likelihood phylogenies: Assessing the performance of PhyML 3.0. System Biol., 2010; 59:307-321.

(19.) Tavare, S. Some probabilistic and stadistical problems on the analysis of DNA sequences. LecMath Life Sci, 1986; 17: 57-86.

(20.) Martinez-Trujillo, A., Perez-Avalos, O., Ponce-Noyola, T. Enzymatic properties of a purified xylanase from mutant PN-120 of Cellulomonas flavigena. Enzyme Microbial Technol., 2003; 32:401-406.

(21.) Miller, G.L. Use of dinitrosalicylic acid reagent for determination of reducing sugar. Anal Chem., 1959; 31:426-428.

(22.) Lu, W.J., Wang, H.T., Yang, S.J., Wang, Z.C., Nie, Y.F. Isolation and characterization of mesophilic cellulose-degrading bacteria from flower stalks-vegetable waste co-composting system. J Gen Appl Microbiol., 2005; 51:353360.

(23.) Nath, I.V.A., Bharathi, P.A.L. Diversity in transcripts and translational pattern of stress proteins in marine extremophiles. Extremophiles, 2011; 15:129-153.

(24.) Li, W.J., Chen, H.H., Zhang, Y.Q., Schumann, P., Stackebrandt, E., Xu, L.H., Jiang, C.L. Nesterenkonia halotolerans sp. nov. and Nesterenkonia xinjiangensis sp. nov., actinobacteria from saline soils in the west of China. Int J Syst Evol Microbiol., 2004; 54:837841.

(25.) Hsu, C.L., Chang, K.S., Lai, M.Z., Chang, T.C., Chang, Y.H., Jang, H.D. Pretreatment and hydrolysis of cellulosic agricultural wastes with a cellulase-producing Streptomyces for bioethanol production. Biomass Bioenerg., 2011; 35:1878-1884.

(26.) Rajoka, M.I., Malik, K.A. Enhanced production of cellulases by Cellulomonas strains grown on different cellulosic residues. Folia Microbiol., 1997; 42:59-64.

(27.) Shaw, A., Saldajeno, M.L., Kolkman, M.A.B., Jones, B.E., Bott, R. Structure determination and analysis of a bacterial chymotrypsin from Cellulomonas bogoriensis. Acta Crystallogr FStructBiol Cryst Commun., 2007; 63:266-269.

(28.) Li, H.W., Zhi, X.Y., Yao, J.C., Zhou, Y, Tang, S.K., Klenk, H.P., Zhao, J., Li, W.J. Comparative genomic analysis of the genus Nocardiopsis provides new insights into its genetic mechanisms of environmental adaptability. PLoS ONE, 2013; 8:e61528.

(29.) Sun, H., Lapidus, A., Nolan, M., Lucas, S., Del Rio, T.G., Tice, H., Cheng, J.F., Tapia, R., Han, C., Goodwin, L., Pitluck, S., Pagani, I., Ivanova, N., Mavromatis, K., Mikhailova, N., Pati, A., Chen, A., Palaniappan, K., Land, M., Hauser, L., Chang, Y.J., Jeffries, C.D., Djao, O.D.N., Rohde, M., Sikorski, J., Goker, M., Woyke, T., Bristow, J., Eisen, J.A., Markowitz, V., Hugenholtz, P., Kyrpides, N.C., Klenk, H.P. Complete genome sequence of Nocardiopsis dassonvillei type strain (IMRU 509(T)). Stand Genomic Sci., 2010; 3:325-336.

(30.) Anderson, I., Abt, B., Lykidis, A., Klenk, H.P., Kyrpides, N., Ivanova, N. Genomics of aerobic cellulose utilization systems in actinobacteria. PLoS ONE, 2012; 7:e39331.

(31.) Mb,a, M.F., Davies, G.J., Drancourt, M., Henrissat, B. Genome analyses highlight the different biological roles of cellulases. Nature Rev Microbiol, 2012; 10:227-234.

(32.) Grant, W.D., Gemmel, R.T., GcGenity, T.J.: Halophiles. In: Extremophiles: Microbial life in extreme environments (Horikoshi K, Grant WD, ed). New York: Wiley-Liss Inc., 1998; pp 93-132.

(33.) DasSarma, S., Arora, P.: Halophiles. In: Encyclopedia of life sciences, vol. 8. London: Nature Publishing Group, 2002; pp 458-466.

(34.) Quesada, E., Ventosa, A., Rodriguez-Valera, F., Ramos-Cormenzana, A. Types and properties of some bacteria isolated from hypersaline soils. J Appl Microbiol, 1982; 53:155-161.

(35.) Rodriguez-Valera, F. Characteristics and microbial ecology of hypersaline environments. Halophilic Bacteria, 1988; 1:3-30.

(36.) Ramirez, N., Serrano, J.A., Sandoval, H. Extremophile microorganisms. Halophile actinomycetes in Mexico. Review. Redalyc., 2006; 37:56-71.

(37.) Valenzuela-Encinas, C., Neria-Gonzalez, I., Alcantara-Hernandez, R.J., Enriquez-Aragon, A., Estrada Alvarado, I., Hernandez-Rodriguez, C., Dendooven, L., Marsch, R. Phylogenetic analysis of the archaeal community in an alkaline-saline soil of the former lake Texcoco (Mexico). Extremophiles, 2007; 12:247-254.

(38.) Soto-Padilla, M.Y., Valenzuela-Encinas, C., Dendooven, L., Marsch, R., GortaresMoroyoqui, P., Estrada-Alvarado, M.I. Isolation and phylogenic identification of soil haloalkaliphilic strains in the former Texcoco lake. Inter J Environ Heal, 2013; R 1:1-9.

(39.) Lv, W., Yu, Z. Isolation and characterization of two thermophilic cellulolytic strains of Clostridium thermocellum from a compost sample. J Appl Microbiol., 2013; 114:10011007.

(40.) Mangunwardoyo,, W., Aprilismulan, A., Oetari, A., Sjamsuridzal, W. Screening cellulose activity of yeast isolated from soil, sediment and water river from Taman Nasional Gunung Halimun, West Java, Indonesia. Malay s J Microbiol., 2011; 7:210-216.

(41.) Amore, A., Pepe, O., Ventorino, V, Birolo, L., Giangrande, C., Faraco, V Industrial waste based compost as a source of novel cellulolytic strains and enzymes. FEMS Microbiol Lett., 2013; 339:93-101.

Maria Patricia Lopez-Ramirez [1], Katia Berenice Sanchez-Lopez [1], Yohanna Sarria-Guzman [1], Juan Manuel Bello-Lopez [1], Veronica Lorena CanoGarcia [1], Victor Manuel Ruiz-Valdiviezo [2] *, Luc Dendooven [1]

[1] Laboratory of Soil Ecology, ABACUS, Cinvestav, Av. I.P.N. 2508 C.P. 07360, Mexico D. F., Mexico.

[2] Laboratory of Biotechnology, Instituto Tecnologico de Tuxtla-Gutierrez, Tuxtla-Gutierrez, Chiapas, Mexico.

(Received: 10 May 2015; accepted: 26 July 2015)

* To whom all correspondence should be addressed. Tel: +52 55 57473319; Fax: +52 55 57473313; E-mail:bioqvic@hotmail.com

Caption: Fig. 1. Phylogenetic analysis based on 16S rRNA gene sequences of strains with cellulolytic activity (access numbers are in parenthesis). Percentages in the branching points with only values with > 50% shown

Caption: Fig. 2. Cellulolytic activity (mU [ml.sup.-1]) and microbial growth (O.D.) of strain 1r Cellulomonas bogoriensis at five different temperatures and pH 9.0 incubated for 60 days

Caption: Fig. 3. Cellulolytic activity (mU [ml.sup.-1]) and microbial growth (O.D.) of strain 1r Cellulomonas bogoriensis at different pH and 50[degrees]C incubated for 60 days

Caption: Fig. 4. Cellulolytic activity (mU [ml.sup.-1]) and microbial growth (O.D.) of strain 8r Nocardiopsis dassonvillei at five different temperatures and pH 9.0 incubated for 60 days

Caption: Fig. 5. Cellulolytic activity (mU [ml.sup.-1]) and microbial growth (O.D.) of strain 8r Nocardiopsis dassonvillei at different pH and 50[degrees]C incubated for 60 days
Table 1. Identification of the isolated cellulolytic strains based on
the gene sequence encoding for 16S rRNA and hydrolysis halos around
the colony isolates of 7 estimated by the ratio of size of maximum
clearing zone and hydrolytic capacity (HC) value for 10 days.

Strain   Micro-organism               %        Maximum     Maximum
                                      Simi-    clearing    HC value
                                      litude   zone
                                               size (cm)

1r       Cellulomonas bogoriensis     99.70    3.1         6.2
3r       Streptomyces aurantiacus     99.41    3.7         7.4
5r       Arthrobacter globiformis     98.75    1.3         2.6
6r       Streptomyces aurantiacus     99.31    2.8         5.6
7r       Cellulomonas cellasea        99.10    1.3         2.6
8r       Nocardiopsis dassonvillei    99.69    5.0         10.0
16r      Nesterenkonia halotolerans   98.68    0.8         1.6
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Author:Lopez-Ramirez, Maria Patricia; Sanchez-Lopez, Katia Berenice; Sarria-Guzman, Yohanna; Bello-Lopez, J
Publication:Journal of Pure and Applied Microbiology
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Date:Dec 1, 2015
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