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Bacterial communities

Bowman JP, Jimenez L, Rosario 1, et al. 1993. Characterization of the methanotrophic bacterial community present in a trichloroethylene-contaminated subsurface groundwater site. Appl Environ Microbiol 59 2380-2387. [Pg.255]

Liu S-Y, Z Zheng, R Zhang, J-M Bollag (1989) Sorption and metabolism of metolachlor by a bacterial community. Appl Environ Microbiol 55 733-740. [Pg.85]

Degradation of contaminants may occur with bacteria that have been isolated from pristine environments without established exposure to the contaminants, and exhibit no dependence on substrate concentration. For example, organisms from a previously unexposed forest soil were able to degrade 2,4,6-trichlorophenol at concentrations up to 5000 ppm, and terminal restriction fragment length polymorphism analysis revealed that at concentrations up to 500 ppm, the bacterial community was unaltered (Sanchez et al. 2004). [Pg.216]

Holben WE, JK Jansson, BK Chelm, JM Tiedje (1988) DNA probe method for the detection of specific microorganisms in the soil bacterial community. Appl Environ Microbiol 54 703-711. [Pg.232]

Timonen S, KS Jorgensen, K Haahtela, R Sen (1998) Bacterial community structure at defined locations of Pinus sylvestris-Suillus bovinus and Pinus sylvestris-Paxillus involutus mycorrhizospheres in dry pine forest humus and nursery peat. Can J Microbiol 44 499-513. [Pg.618]

Arino S, R Marchal, J-P Vandecasteele (1998) Involvement of a rhamnolipid-producing strain of Pseudomonas aeruginosa in the degradation of polycyclic aromatic hydrocarbons by a bacterial community. J Appl Microbiol 84 769-776. [Pg.654]

Vinas M, 1 Sabate, Ml Espuny, AM Solanas (2005) Bacterial community dynamics and polycyclic aromatic hdrocarbon degradation during bioremediation of heavily creosote-contaminated soil. Appl Environ Microbiol 71 7008-7018. [Pg.658]

L. Marilley and M. Aragno, Phylogenetic diversity of bacterial communities differing in degree of proximity of Lolium perenne and Trifolium repens roots. Applied Soil Ecology 73 127 (1999). [Pg.195]

S. U. Saratchandra, G. Burch, and N. R. Cox, Growth patterns of bacterial communities in the rhizoplane and rhizosphere of white clover (Trifolium repens L.) and... [Pg.321]

K. Bronstad, K. Dronen, L. Ovreas, and V. Torsvick, Phenotypic diversity and antibiotic resistance in soil bacterial communities, J. Ind. Microbiol. 77 253 (1996). [Pg.403]

Diaz-Ravina, M. and Baath, E., Development of metal tolerance in soil bacterial communities exposed to experimentally increased metal levels, Appl Environ Microbiol, 62 (8), 2970-2977, 1996. [Pg.425]

Baker, C.J.O., Fulthorpe, R.R., and Gilbride, K.A., An assessment of variability of pulp mill wastewater treatment system bacterial communities using molecular methods, Wat. Qual. Res. J. (Canadian), 38, 227-242, 2003. [Pg.909]

Zarda, B. Hahn, D. Chatzinotas, A. Schonhuber, W. Neef, A. Amann, R. I. Zeyer, J. Analysis of bacterial community structure in bulk soil by in situ hybridization. Arch. Microbiol. 1997,168,185-192. [Pg.17]

Soil Bacterial Community in Association with Land Degradation...317... [Pg.2]

Mummey DL, Stahl PD (2004) Analysis of soil whole- and inner-microaggregate bacterial communities. Microb Ecol 48 41-50... [Pg.35]

Whiteley AS, Bailey MJ (2000) Bacterial community structure and physiological state within an industrial phenol bioremediation system. Appl Environ Microbiol 66 2400-2407... [Pg.197]

The qCC>2 is often used as an indicator of whether the microbial biomass is under stress. In general, factors that decrease the size of the microbial biomass tend to increase qC02. That is, factors that cause stress to the microbial community tend to reduce its size. Other factors could also contribute to an increased qC02. For example, bacterial communities are less efficient at converting substrate C into cellular C than fungi (Sakamoto and Oba 1994) so a change in the composition of microbial biomass can alter qC02 values. [Pg.218]

Ros M, Pascuala JA, Garciaa C, Hemandeza MT, Insam H (2006) Hydrolase activities, microbial biomass and bacterial community in a soil after long-term amendment with different composts. Soil Biol Biochem 38 3443-3452 Rovira P, Vallejo VR (2002) Labile and recalcitrant pools of carbon and nitrogen in organic matter decomposing at different depths in soil an acid hydrolysis approach. Geoderma 107 109-141... [Pg.229]

Kozdroj J, van Elsas JD (2000) Response of the bacterial community to root exudates in soil polluted with heavy metals assessed by molecular and cultural approaches. Soil Biol Biochem 32 1405-1417... [Pg.314]

Reber HH (1992) Simultaneous estimates of the diversity and the degradative capability of heavy-metal-affected soil bacterial communities. Biol Fertil Soils 13 181-186... [Pg.314]

Antibiotic resistance profiles of the bacterial communities reflected the effects of deforestation and the land degradation (Fig. 2). The degradation was significant (p=0.05) as a source of variation for the numbers of soil bacterial cells resistant to lasalocid, penicillin, spectinomycin and trimethoprim, and marginally significant (0.50 Significant differences between two average values were observed for some antibiotics. When compared with the BG soil bacterial community, the DEF soil bacterial community had more bacterial cells resistant to dapson, kanamycin, lasalocid, nafcillin, penicillin, spectinomycin, streptomycin and trimethoprim. [Pg.326]

Changes in Antibiotic Resistance Profile of Soil Bacterial Community 331... [Pg.331]


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