2019
DOI: 10.1016/j.jwpe.2019.100804
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Hybrid anaerobic-aerobic biological treatment for real textile wastewater

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Cited by 115 publications
(31 citation statements)
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“…Several physicochemical and biological technologies have been used to treat swine wastewater, namely, electrocoagulation ( Mores et al, 2016 ), electrochemical ( Huang et al, 2016 , 2018 ) and biological methods such as anaerobic-aerobic ( Aziza et al, 2019 ; Shoukat et al, 2019 ), moving bed biofilm reactor (MBBR; Yang et al, 2015 ), and membrane bioreactor (MBR; Guglielmi and Andreottola, 2011 ; Guadie et al, 2014 ). However, these technologies have limitations such as high initial investment cost, consumption of large quantities of chemicals, requiring large footprint, complex operation and control of parameters, and low nitrogen and phosphorous removal efficiencies.…”
Section: Introductionmentioning
confidence: 99%
“…Several physicochemical and biological technologies have been used to treat swine wastewater, namely, electrocoagulation ( Mores et al, 2016 ), electrochemical ( Huang et al, 2016 , 2018 ) and biological methods such as anaerobic-aerobic ( Aziza et al, 2019 ; Shoukat et al, 2019 ), moving bed biofilm reactor (MBBR; Yang et al, 2015 ), and membrane bioreactor (MBR; Guglielmi and Andreottola, 2011 ; Guadie et al, 2014 ). However, these technologies have limitations such as high initial investment cost, consumption of large quantities of chemicals, requiring large footprint, complex operation and control of parameters, and low nitrogen and phosphorous removal efficiencies.…”
Section: Introductionmentioning
confidence: 99%
“…Immobilization, co-contaminant influence on dye biodegradation, genetic modification of algae and cyanobacteria, graphene oxide addition and lipid production [137][138][139][140][141] Activated sludge, anaerobic sludge Granule formation (anaerobic core with aerobic shell), metagenomic analysis in anaerobic MBR, addition of resuscitation-promoting factors, integration of anaerobic and aerobic reactors, addition of halotolerant yeast and magnetic field [142][143][144][145][146][147][148][149][150] Biofilm Application of new biocarriers, co-substrate addition, kinetic analysis and process optimization in moving bed biofilm reactor, biomass acclimatization and optimization of anoxic/aerobic sequencing batch moving bed bioreactors [151][152][153][154][155] As seen from Table 2, there are numerous existing tried and tested methods to accomplish dye removal. Only in 2019, Deng et al [156] reviewed 42 papers on textile wastewater treatment technologies organized by physico-chemical, biological, and combined processes.…”
Section: Current Development Referencesmentioning
confidence: 99%
“…The aromatic amines produced as a result of azo bonds cleavage in the anaerobic step are further degraded in the aerobic one ( Figure 2 ) [ 232 ]. The combined anaerobic–aerobic treatment most often uses mixed bacterial cultures such as activated sludge [ 149 , 204 , 205 , 207 ], anaerobic granular sludge [ 150 , 153 ], anaerobic–aerobic granular sludge [ 142 , 206 ], immobilized activated sludge [ 151 ], or biofilm [ 111 , 153 , 155 ]. The sequencing of anaerobic–anoxic–aerobic conditions is easy to obtain in the sequence batch reactors (SBRs, [ 204 , 205 ])—the decolorization efficiency reached 100% by up to 94% of COD removal.…”
Section: Biological Processesmentioning
confidence: 99%
“…Lastly, a combined anaerobic–aerobic biological treatment process was developed to treat textile wastewater (Shoukat, Khan, & Jamal, 2019). The combined system is composed of both anaerobic and aerobic sequencing batch reactors and obtained satisfying removal efficiency: 99.5% of COD, 78.4% of color, and 99.3% of total Kjeldahl nitrogen removal at 54 hs of hydraulic retention time.…”
Section: Combined Processesmentioning
confidence: 99%