Aerobic biodegradation of emerging azole contaminants by return activated sludge and enrichment cultures

2021 ◽  
pp. 126151
Author(s):  
Kalyani V. Jog ◽  
Kendra Z. Hess ◽  
Jim A. Field ◽  
Mark J. Krzmarzick ◽  
Reyes Sierra-Alvarez
2013 ◽  
Vol 20 (1) ◽  
pp. 199-208 ◽  
Author(s):  
Marketa Julinova ◽  
Jan Kupec ◽  
Roman Slavik ◽  
Maria Vaskova

Abstract A synthetic polymer, polyvinylpyrrolidone (PVP - E 1201) primarily finds applications in the pharmaceutical and food industries due to its resistance and zero toxicity to organisms. After ingestion, the substance passes through the organism unchanged. Consequently, it enters the systems of municipal wastewater treatment plants (WWTP) without decomposing biologically during the waste treatment process, nor does it attach (through sorption) to particles of activated sludge to any significant extent, therefore, it passes through the system of a WWTP, which may cause the substance to accumulate in the natural environment. For this reason the paper investigates the potential to initiate aerobic biodegradation of PVP in the presence of activated sludge from a municipal wastewater treatment plant. The following agents were selected as the initiators of the biodegradation process - co-substrates: acrylamide, N-acethylphenylalanine and 1-methyl-2-pyrrolidone, a substance with a similar structure to PVP monomer. The biodegradability of PVP in the presence of co-substrates was evaluated on the basis of biological oxygen demand (BOD) as determined via a MicroOxymax O2/CO2/CH4 respirometer. The total substrate concentration in the suspension equaled 400 mg·dm-3, with the ratio between PVP and the cosubstrate being 1:1, while the concentration of the dry activated sludge was 500 mg·dm-3. Even though there was no occurrence of a significant increase in the biodegradation of PVP alone in the presence of a co-substrate, acrylamide appeared to be the most effective type of co-substrate. Nevertheless, a recorded decrease in the slope of biodegradation curves over time may indicate that a process of primary decomposition was underway, which involves the production of metabolites that inhibit activated sludge microorganisms. The resulting products are not identified at this stage of experimentation.


2015 ◽  
Vol 57 (11) ◽  
pp. 4982-4993 ◽  
Author(s):  
Xiang fei Lü ◽  
Hong rui Ma ◽  
Kai Du ◽  
Ran Zhao ◽  
Xia Zhao ◽  
...  

2009 ◽  
Vol 60 (4) ◽  
pp. 983-994 ◽  
Author(s):  
M. A. Hoque ◽  
V. Aravinthan ◽  
N. M. Pradhan

A comparison of four different established models along with parameter estimation was carried out in order to explain the aerobic biodegradation of acetate in an activated sludge system. These models were investigated using experimental OUR data from batch experiments of three different concentration studies. Model calibration reveals that ASM1 model is not suitable to explain the observed experimental OUR during the famine phase implying storage compounds could play an important role during that stage. Besides, the model corresponds to the accumulation concept and is not well fitted for all concentrations studies though it includes the storage phenomena. Both the ASM3 model and the model for simultaneous storage and growth on substrate can well describe the acetate biodegradation process, however the OUR data alone is not sufficient to justify the suitability of those models. Simulated profiles using the model outputs demonstrate that storage is overestimated while ammonia degradation is underestimated in ASM3 compared to simultaneous growth and storage model. The current study also gives reasonable outcomes related to parameter estimation as compared with previous study which is statistically interpreted in this paper.


2002 ◽  
Vol 36 (21) ◽  
pp. 4585-4592 ◽  
Author(s):  
Roberto Frontera-Suau ◽  
F. Daniel Bost ◽  
Thomas J. McDonald ◽  
Pamela J. Morris

2011 ◽  
Vol 46 (1) ◽  
pp. 284-289 ◽  
Author(s):  
Zeinab Salehi ◽  
Hidemi Yoshikawa ◽  
Ryo Mineta ◽  
Yoshinori Kawase

1999 ◽  
Vol 29 (2) ◽  
pp. 197-204 ◽  
Author(s):  
Christian Zipper ◽  
Thomas Fleischmann ◽  
Hans-Peter E. Kohler

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