The short‐term and long‐term effects of Fe(II) on the performance of anammox granules

Fe(II) is one of the commonly used additives in wastewater treatment and proved to be beneficial for promoting microbial activity. In this study, the effects of Fe(II) on the specific anammox activity (SAA) and reactor performance were proved to be concentration‐dependent. In the short‐term experime...

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Veröffentlicht in:Water environment research 2021-09, Vol.93 (9), p.1651-1659
Hauptverfasser: Zhou, Biru, Chen, Guangjiao, Dong, Chifei, Jiang, Yushi, Chen, Haoyu, Ouyang, Tong, Li, Yu‐You, Zhang, Yanlong
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container_end_page 1659
container_issue 9
container_start_page 1651
container_title Water environment research
container_volume 93
creator Zhou, Biru
Chen, Guangjiao
Dong, Chifei
Jiang, Yushi
Chen, Haoyu
Ouyang, Tong
Li, Yu‐You
Zhang, Yanlong
description Fe(II) is one of the commonly used additives in wastewater treatment and proved to be beneficial for promoting microbial activity. In this study, the effects of Fe(II) on the specific anammox activity (SAA) and reactor performance were proved to be concentration‐dependent. In the short‐term experiment, low concentration of Fe(II) (5–80 mg/L) significantly enhanced the SAA, while high concentration of Fe(II) (120–300 mg/L) inhibited the SAA. It was confirmed that anammox can be domesticated after long‐term exposure to low Fe(II) concentration, and the SAA could be further enhanced by higher Fe(II) concentration in the following phases. In addition, as an important factor for anammox granulation and maintaining the SAA, the extracellular polymeric substance (EPS) was also affected by Fe(II) addition. In spite of the effects on SAA and EPS, Fe(II) was proved to be the key factor that enhances the N2O emission via abiotic pathway in the anammox reactor. Practitioner points Low Fe(II) concentrations enhanced SAA, while high concentrations inhibited SAA. Long‐term acclimatization by Fe(II) improved the tolerance of anammox to Fe(II). Fe(II) affects the amount and constituent of EPS and the performance of anammox granules. Accumulation of Fe(II) in the AAFEB reactor promoted the N2O emission. The effects of Fe(II) concentration on anammox granules in long‐term and short‐term experiments were revealed.
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In this study, the effects of Fe(II) on the specific anammox activity (SAA) and reactor performance were proved to be concentration‐dependent. In the short‐term experiment, low concentration of Fe(II) (5–80 mg/L) significantly enhanced the SAA, while high concentration of Fe(II) (120–300 mg/L) inhibited the SAA. It was confirmed that anammox can be domesticated after long‐term exposure to low Fe(II) concentration, and the SAA could be further enhanced by higher Fe(II) concentration in the following phases. In addition, as an important factor for anammox granulation and maintaining the SAA, the extracellular polymeric substance (EPS) was also affected by Fe(II) addition. In spite of the effects on SAA and EPS, Fe(II) was proved to be the key factor that enhances the N2O emission via abiotic pathway in the anammox reactor. Practitioner points Low Fe(II) concentrations enhanced SAA, while high concentrations inhibited SAA. Long‐term acclimatization by Fe(II) improved the tolerance of anammox to Fe(II). Fe(II) affects the amount and constituent of EPS and the performance of anammox granules. Accumulation of Fe(II) in the AAFEB reactor promoted the N2O emission. 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Long‐term acclimatization by Fe(II) improved the tolerance of anammox to Fe(II). Fe(II) affects the amount and constituent of EPS and the performance of anammox granules. Accumulation of Fe(II) in the AAFEB reactor promoted the N2O emission. 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In this study, the effects of Fe(II) on the specific anammox activity (SAA) and reactor performance were proved to be concentration‐dependent. In the short‐term experiment, low concentration of Fe(II) (5–80 mg/L) significantly enhanced the SAA, while high concentration of Fe(II) (120–300 mg/L) inhibited the SAA. It was confirmed that anammox can be domesticated after long‐term exposure to low Fe(II) concentration, and the SAA could be further enhanced by higher Fe(II) concentration in the following phases. In addition, as an important factor for anammox granulation and maintaining the SAA, the extracellular polymeric substance (EPS) was also affected by Fe(II) addition. In spite of the effects on SAA and EPS, Fe(II) was proved to be the key factor that enhances the N2O emission via abiotic pathway in the anammox reactor. Practitioner points Low Fe(II) concentrations enhanced SAA, while high concentrations inhibited SAA. Long‐term acclimatization by Fe(II) improved the tolerance of anammox to Fe(II). Fe(II) affects the amount and constituent of EPS and the performance of anammox granules. Accumulation of Fe(II) in the AAFEB reactor promoted the N2O emission. The effects of Fe(II) concentration on anammox granules in long‐term and short‐term experiments were revealed.</abstract><cop>HOBOKEN</cop><pub>Wiley</pub><pmid>33657245</pmid><doi>10.1002/wer.1549</doi><tpages>9</tpages><orcidid>https://orcid.org/0000-0002-9132-5585</orcidid><orcidid>https://orcid.org/0000-0002-3659-5005</orcidid></addata></record>
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subjects Acclimatization
Additives
Anammox granule
Biological activity
Emission
Engineering
Engineering, Environmental
Environmental Sciences
Environmental Sciences & Ecology
Extracellular
extracellular polymeric substance
ferrous iron
Granular materials
Granulation
Iron
Life Sciences & Biomedicine
Limnology
Marine & Freshwater Biology
Microbial activity
Microorganisms
N2O
Nitrous oxide
Physical Sciences
Reactors
Science & Technology
specific anammox activity
Technology
Wastewater treatment
Water Resources
title The short‐term and long‐term effects of Fe(II) on the performance of anammox granules
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