Effects of electron acceptors on sulphate reduction activity in activated sludge processes

被引:22
作者
Rubio-Rincon, Francisco [1 ,2 ]
Lopez-Vazquez, Carlos [1 ]
Welles, Laurens [1 ,2 ]
van den Brand, Tessa [3 ]
Abbas, Ben [2 ]
van Loosdrecht, Mark [2 ]
Brdjanovic, Damir [1 ,2 ]
机构
[1] UNESCO IHE Inst Water Educ, Sanit Engn Chair Grp, Dept Environm Engn & Water Technol, Westvest 7, NL-2611 AX Delft, Netherlands
[2] Delft Univ Technol, Dept Biotechnol, Van der Maasweg 9, NL-2629 HZ Delft, Netherlands
[3] KWR Watercycle Res Inst, Groningenhaven 7, NL-3433 PE Nieuwegein, Netherlands
关键词
Sulphate reduction activity; Sulphate-reducing bacteria; Biological nutrients removal; Wastewater treatment; Electron acceptor inhibition; REDUCING BACTERIA; AUTOTROPHIC DENITRIFICATION; BIOLOGICAL REMOVAL; SULFIDE TOXICITY; NITRATE; SULFUR; PHOSPHORUS; KINETICS; NITRITE; GROWTH;
D O I
10.1007/s00253-017-8340-3
中图分类号
Q81 [生物工程学(生物技术)]; Q93 [微生物学];
学科分类号
071005 ; 0836 ; 090102 ; 100705 ;
摘要
The concentration of sulphate present in wastewater can vary from 10 to 500 mg SO4 (2-)/L. During anaerobic conditions, sulphate is reduced to sulphide by sulphate-reducing bacteria (SRB). Sulphide generation is undesired in wastewater treatment plants (WWTPs). Previous research indicated that SRB are inhibited by the presence of electron acceptors (such as O-2, NO3 and NO2). However, the contact times and concentrations used in those studies are by far higher than occur in WWTPs. Since sulphide can influence the biological nitrogen and phosphorus removal processes, this research aimed to understand how the different electron acceptors commonly present in biological nutrient removal (BNR) systems can affect the proliferation of SRB. For this purpose, a culture of SRB was enriched in a sequencing batch reactor (approx. 88% of the total bacteria population). Once enriched, the SRB were exposed for 2 h to typical concentrations of electron acceptors like those observed in BNR systems. Their activity was assessed using three different types of electron donors (acetate, propionate and lactate). Oxygen was the most inhibiting electron acceptor regardless the carbon source used. After exposure to oxygen and when feeding acetate, an inactivation time in the sulphate reduction activity was observed for 1.75 h. Once the sulphate reduction activity resumed, only 60% of the original activity was recovered. It is suggested that the proliferation of SRB is most likely to occur in BNR plants with an anaerobic fraction higher than 15% and operating at sludge retention times higher than 20 days (at a temperature of 20 A degrees C). These results can be used to implement strategies to control the growth of sulphate reducers that might compete for organic carbon with phosphate-accumulating organisms.
引用
收藏
页码:6229 / 6240
页数:12
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