2010
DOI: 10.1016/j.biotechadv.2010.08.007
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Advances in aerobic granule formation and granule stability in the course of storage and reactor operation

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Cited by 276 publications
(87 citation statements)
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“…First, irregular granules (138 ± 6 and 49 ± 8 lm of length and width, respectively) were observed after 2 weeks of operation in the first run. No single mechanism is responsible for formation of aerobic granules-this process is strongly influenced by different parameters and factors, like substrate composition, organic loading rate, feeding strategy (feast and famine periods), reactor design, hydrodynamics, settling time, exchange ratio and aeration intensity (Lee et al 2010). However, a critical parameter seems to be short settling time required to retain particles with good settleability.…”
Section: Resultsmentioning
confidence: 99%
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“…First, irregular granules (138 ± 6 and 49 ± 8 lm of length and width, respectively) were observed after 2 weeks of operation in the first run. No single mechanism is responsible for formation of aerobic granules-this process is strongly influenced by different parameters and factors, like substrate composition, organic loading rate, feeding strategy (feast and famine periods), reactor design, hydrodynamics, settling time, exchange ratio and aeration intensity (Lee et al 2010). However, a critical parameter seems to be short settling time required to retain particles with good settleability.…”
Section: Resultsmentioning
confidence: 99%
“…Therefore, it can be successfully used not only for nitrogen and phosphorus removal Wei et al 2014), but also for industrial wastewater treatment (Bumbac et al 2015) and toxic organic compound degradation (Zhu et al 2014). Community structure in aerobic granules is one of the most interesting topics for researchers (de Kreuk and van Loosdrecht 2004;de Kreuk et al 2007;Lee et al 2010;Weissbrodt et al 2013).…”
Section: Introductionmentioning
confidence: 99%
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“…Another positive effect of bacteria on microalgae is enhanced harvesting efficiency (de Bashan et al 2002). Bacteria are the most efficient self-aggregation microorganisms and can form bioaggregates with other microorganisms, resulting in the production of activated sludge, biofilms, aerobic granules, and anaerobic granules (Lee et al 2010;More et al 2014). Bioaggregates usually have good settling capability and are easily separated from treated wastewater.…”
Section: Introductionmentioning
confidence: 99%
“…Aerobic granules are densely packed structures of microbial communities that settle significantly faster than activated sludge flocs (de Kreuk and van Loosdrecht 2004; Lee et al 2010;Morgenroth et al 1997) and can contain a wide variety of microbial groups important to wastewater treatment, including acidifying, nitrifying, denitrifying bacteria and other aerobic heterotrophs (Tijhuis et al 1994). Aerobic granules have been used for nitrogen (N) removal in both sequencing batch airlift reactors (SBARs) (Beun et al 2001) and sequencing batch reactors (SBRs) (Jang et al 2003), and can perform simultaneous nitrification, denitrification and phosphorus removal (Yilmaz et al 2008).…”
Section: Introductionmentioning
confidence: 99%