Potassium permanganate (KMnO4)/sodium sulfite (Na2SO3) rapidly disintegrates waste activated sludge by reactive Mn(III) species and shapes microbial community structure

2020 ◽  
Vol 394 ◽  
pp. 124920 ◽  
Author(s):  
Wei Li ◽  
Yu Lou ◽  
Anran Fang ◽  
Kun Feng ◽  
Defeng Xing
Keyword(s):  
Community Structure ◽  
Microbial Community ◽  
Activated Sludge ◽  
Potassium Permanganate ◽  
Microbial Community Structure ◽  
Sodium Sulfite ◽  
Waste Activated Sludge

scholarly journals Microbial Community Structure and Enumeration of Bacillus species in Activated Sludge

2017 ◽  
Vol 15 (6) ◽  
pp. 233-240 ◽  
Author(s):  
Masashi Hatamoto ◽  
Tomoyo Kaneko ◽  
Yuya Takimoto ◽  
Tsukasa Ito ◽  
Naoki Miyazato ◽  
...  
Keyword(s):  
Community Structure ◽  
Microbial Community ◽  
Activated Sludge ◽  
Microbial Community Structure

scholarly journals Bioaugmentation of Activated Sludge by an Indigenous 3-Chloroaniline-Degrading Comamonas testosteroni Strain, I2gfp

2000 ◽  
Vol 66 (7) ◽  
pp. 2906-2913 ◽  
Author(s):  
Nico Boon ◽  
Johan Goris ◽  
Paul De Vos ◽  
Willy Verstraete ◽  
Eva M. Top
Keyword(s):  
Community Structure ◽  
Microbial Community ◽  
Activated Sludge ◽  
Microbial Community Structure ◽  
Denaturing Gradient Gel Electrophoresis ◽  
Dynamic Change ◽  
16S Rrna Genes ◽  
Rrna Genes ◽  
Adaptation Period ◽  
Comamonas Testosteroni

ABSTRACT A strain identified as Comamonas testosteroni I2 was isolated from activated sludge and found to be able to mineralize 3-chloroaniline (3-CA). During the mineralization, a yellow intermediate accumulated temporarily, due to the distalmeta-cleavage of chlorocatechol. This strain was tested for its ability to clean wastewater containing 3-CA upon inoculation into activated sludge. To monitor its survival, the strain was chromosomally marked with the gfp gene and designated I2gfp. After inoculation into a lab-scale semicontinuous activated-sludge (SCAS) system, the inoculated strain maintained itself in the sludge for at least 45 days and was present in the sludge flocs. After an initial adaptation period of 6 days, complete degradation of 3-CA was obtained during 2 weeks, while no degradation at all occurred in the noninoculated control reactor. Upon further operation of the SCAS system, only 50% 3-CA removal was observed. Denaturing gradient gel electrophoresis (DGGE) of 16S rRNA genes revealed a dynamic change in the microbial community structure of the activated sludge. The DGGE patterns of the noninoculated and the inoculated reactors evolved after 7 days to different clusters, which suggests an effect of strain inoculation on the microbial community structure. The results indicate that bioaugmentation, even with a strain originating from that ecosystem and able to effectively grow on a selective substrate, is not permanent and will probably require regular resupplementation.

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