Rubio-Rincón Francisco, Lopez-Vazquez Carlos, Welles Laurens, van den Brand Tessa, Abbas Ben, van Loosdrecht Mark, Brdjanovic Damir
Sanitary Engineering Chair Group, Department of Environmental Engineering and Water Technology, UNESCO-IHE Institute for Water Education, Westvest 7, 2611AX, Delft, The Netherlands.
Department of Biotechnology, Delft University of Technology, Van der Maasweg 9, 2629 HZ, Delft, The Netherlands.
Appl Microbiol Biotechnol. 2017 Aug;101(15):6229-6240. doi: 10.1007/s00253-017-8340-3. Epub 2017 May 25.
The concentration of sulphate present in wastewater can vary from 10 to 500 mg SO/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, NO and NO). 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 °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.
废水中硫酸盐的浓度可在10至500毫克SO/L之间变化。在厌氧条件下,硫酸盐还原菌(SRB)会将硫酸盐还原为硫化物。废水处理厂(WWTPs)中不希望产生硫化物。先前的研究表明,电子受体(如O、NO和NO)的存在会抑制SRB。然而,这些研究中使用的接触时间和浓度远高于污水处理厂中的实际情况。由于硫化物会影响生物脱氮和除磷过程,本研究旨在了解生物营养物去除(BNR)系统中常见的不同电子受体如何影响SRB的增殖。为此,在序批式反应器中富集了SRB培养物(约占细菌总数的88%)。富集后,将SRB暴露于BNR系统中观察到的典型电子受体浓度下2小时。使用三种不同类型的电子供体(乙酸盐、丙酸盐和乳酸盐)评估它们的活性。无论使用何种碳源,氧气都是最具抑制作用的电子受体。在暴露于氧气并投喂乙酸盐后,观察到硫酸盐还原活性有1.75小时的失活时间。一旦硫酸盐还原活性恢复,仅恢复了原始活性的60%。建议SRB的增殖最有可能发生在厌氧部分高于15%且污泥停留时间高于20天(温度为20°C)的BNR工厂中。这些结果可用于实施控制硫酸盐还原菌生长的策略,这些细菌可能会与聚磷菌竞争有机碳。