Stable and high-rate anaerobic co-digestion of food waste and cow manure: Optimisation of start-up conditions

2020 ◽  
Vol 307 ◽  
pp. 123195 ◽  
Author(s):  
Bao-Shan Xing ◽  
Sifan Cao ◽  
Yule Han ◽  
Junwei Wen ◽  
Kaidi Zhang ◽  
...  
Keyword(s):  
2020 ◽  
Vol 168 ◽  
pp. 115099 ◽  
Author(s):  
Bao-Shan Xing ◽  
Yule Han ◽  
Xiaochang C. Wang ◽  
Jing Ma ◽  
Sifan Cao ◽  
...  

2020 ◽  
Vol 315 ◽  
pp. 123830 ◽  
Author(s):  
Bao-Shan Xing ◽  
Yule Han ◽  
Xiaochang C. Wang ◽  
Sifan Cao ◽  
Junwei Wen ◽  
...  

1992 ◽  
Vol 26 (3-4) ◽  
pp. 601-605 ◽  
Author(s):  
H.-S. Shin ◽  
K.-H. Lim ◽  
H.-S. Park

Aerobic upflow sludge blanket(AUSB) process is a new biological wastewater treatment method applying the concept of the self-immobilization to activated sludge. Two sets of AUSB system with different mixing velocities of 3 rpm(R1) and 6 rpm(R2) were operated for high-rate treatment of synthetic wastewater. The COD removal efficiency in R2 was higher than R1 at the same loading rate up to 7 kg/m3·day. However, in R1, the sludge bulking was observed at the end of the experiment. The chocolate colored granules were formed about 5 days after the start-up. The morphological study on the granular sludge consortia was made with both scanning electron and optical microscopes. The granules were 0.5-2.5 mm in diameter and mainly consisted of bacteria with pili-like appendages and filamentous bacteria, which were thought to be Sphaerotilus natans and Beggiatoa. In R1, the long multicellular filaments causing bulking were prevalent in the granule, while in R2 overgrowth of filamentous bacteria was prevented with appropriate shear stress resulting in higher MLSS density. Experimental results indicated that granulation could be controlled by physical stress on granular sludge.


2020 ◽  
Vol 314 ◽  
pp. 123751 ◽  
Author(s):  
Ee Yang Lim ◽  
Hailin Tian ◽  
Yangyang Chen ◽  
Kewei Ni ◽  
Jingxin Zhang ◽  
...  

1990 ◽  
Vol 22 (1-2) ◽  
pp. 17-24 ◽  
Author(s):  
G. Albagnac

Recognition of the advantages of anaerobic wastewater treatment induced the development of high rate processes, i.e. reactors designed to allow an efficient treatment of even diluted streams. The performance of these advanced reactors is mainly dependent on the retention within the reactor of high bacterial concentrations. The prevailing mechanism is either the formation of bacterial aggregates with good settling characteristics, the development of methanogenic biolayers at the surface of inert carriers or both. During the past decade information on the biology of methanogenic ecosystems became available at an increasing rate. From a practical point of view it can be stated that the biological conversion of organic compounds to methane is reasonably well understood. However the current knowledge on the aggregation and adhesion of methanogenic consortia remains very limited. In most cases reactor start-up procedures are rather long and appear to be more empirical than rational. This paper is a brief presentation on the current knowledge of methanogenic aggregates and biofilms. The fundamental aspects of bacterial adhesion and the modelling of anaerobic biofilms growth are presented elsewhere.


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