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Ionic response of algal-bacterial granular sludge system during biological phosphorus removal from wastewater

Biological phosphorus removal (BPR) from wastewater can be generally realized through alternative non-aeration and aeration operation to create anaerobic and aerobic conditions respectively for P release and uptake/accumulation by polyphosphate accumulating organisms (PAOs), with P removal finally a...

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Published in:Chemosphere (Oxford) 2021-02, Vol.264 (Pt 2), p.128534, Article 128534
Main Authors: Wang, Jixiang, Lei, Zhongfang, Tian, Caixing, Liu, Sen, Wang, Qian, Shimizu, Kazuya, Zhang, Zhenya, Adachi, Yasuhisa, Lee, Duu-Jong
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cited_by cdi_FETCH-LOGICAL-c443t-429d7939d94553d64873f9068545802e310a642a25a9e3ebd920382ec8c90d883
cites cdi_FETCH-LOGICAL-c443t-429d7939d94553d64873f9068545802e310a642a25a9e3ebd920382ec8c90d883
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container_issue Pt 2
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container_title Chemosphere (Oxford)
container_volume 264
creator Wang, Jixiang
Lei, Zhongfang
Tian, Caixing
Liu, Sen
Wang, Qian
Shimizu, Kazuya
Zhang, Zhenya
Adachi, Yasuhisa
Lee, Duu-Jong
description Biological phosphorus removal (BPR) from wastewater can be generally realized through alternative non-aeration and aeration operation to create anaerobic and aerobic conditions respectively for P release and uptake/accumulation by polyphosphate accumulating organisms (PAOs), with P removal finally achieved by controlled discharge of P-rich sludge. In this study, the response of algal-bacterial aerobic granular sludge (AB-AGS) during BPR to main ions including Ac− (acetate), Cl−, SO42−, NH4+, K+, Mg2+, Ca2+ and Na+ in wastewater was investigated with conventional bacterial AGS (B-AGS) as control and acetate as the sole carbon source. Results show that BPR process mainly involved the changes of Ac−, K+, Mg2+, and Ca2+ rather than Cl−, SO42−, NH4+ and Na+. The mole ratio of ΔP/ΔAc kept almost unchanged during the non-aeration (P release) phase in both B-AGS and AB-AGS systems (ΔPB-AGS/ΔAcB-AGS > ΔPAB-AGS/ΔAcAB-AGS), and it was negatively influenced by the light in AB-AGS systems, in which 62% of acetate was not utilized for P release at the high illuminance of 81 k lux. During the entire non-aeration/aeration period, both ΔK/ΔP and ΔMg/ΔP remained constant, while ΔKAB-AGS/ΔPAB-AGS > ΔKB-AGS/ΔPB-AGS and ΔMgAB-AGS/ΔPAB-AGS ≈ ΔMgB-AGS/ΔPB-AGS. The presence of algae seemed not beneficial for PAOs to remove P, while more K+ and P uptake by algae in AB-AGS suggest its great potential for manufacturing biofertilizer. [Display omitted] •P release/uptake involved acetate, K+, Mg2+, and Ca2+ changes rather than others.•ΔP/ΔAc decreased in AB-AGS at high light density with >62% acetate not for PAOs.•ΔK/ΔP and ΔMg/ΔP ratios kept stable while were affected by illumination intensity.•Co-existing algae might mainly contribute to P removal at high light density.
doi_str_mv 10.1016/j.chemosphere.2020.128534
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In this study, the response of algal-bacterial aerobic granular sludge (AB-AGS) during BPR to main ions including Ac− (acetate), Cl−, SO42−, NH4+, K+, Mg2+, Ca2+ and Na+ in wastewater was investigated with conventional bacterial AGS (B-AGS) as control and acetate as the sole carbon source. Results show that BPR process mainly involved the changes of Ac−, K+, Mg2+, and Ca2+ rather than Cl−, SO42−, NH4+ and Na+. The mole ratio of ΔP/ΔAc kept almost unchanged during the non-aeration (P release) phase in both B-AGS and AB-AGS systems (ΔPB-AGS/ΔAcB-AGS &gt; ΔPAB-AGS/ΔAcAB-AGS), and it was negatively influenced by the light in AB-AGS systems, in which 62% of acetate was not utilized for P release at the high illuminance of 81 k lux. During the entire non-aeration/aeration period, both ΔK/ΔP and ΔMg/ΔP remained constant, while ΔKAB-AGS/ΔPAB-AGS &gt; ΔKB-AGS/ΔPB-AGS and ΔMgAB-AGS/ΔPAB-AGS ≈ ΔMgB-AGS/ΔPB-AGS. 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subjects Acetate
Algal-bacterial aerobic granular sludge
Anion
Biological Products
Bioreactors
Cation
Nitrogen
Phosphorus
Phosphorus release
Sewage
Waste Disposal, Fluid
Waste Water
title Ionic response of algal-bacterial granular sludge system during biological phosphorus removal from wastewater
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