Please use this identifier to cite or link to this item: http://hdl.handle.net/10397/90097
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dc.contributorDepartment of Civil and Environmental Engineeringen_US
dc.creatorLi, RHen_US
dc.creatorCui, JLen_US
dc.creatorLi, XDen_US
dc.creatorLi, XYen_US
dc.date.accessioned2021-05-18T08:20:52Z-
dc.date.available2021-05-18T08:20:52Z-
dc.identifier.issn0013-936Xen_US
dc.identifier.urihttp://hdl.handle.net/10397/90097-
dc.language.isoenen_US
dc.publisherAmerican Chemical Societyen_US
dc.rights© 2018 American Chemical Societyen_US
dc.rightsThis document is the Accepted Manuscript version of a Published Work that appeared in final form in Environmental Science & Technology, copyright © American Chemical Society after peer review and technical editing by the publisher. To access the final edited and published work see http://pubs.acs.org/doi/abs/10.1021/acs.est.8b03355en_US
dc.titlePhosphorus removal and recovery from wastewater using Fe-Dosing bioreactor and cofermentation : investigation by X-ray absorption near-edge structure spectroscopyen_US
dc.typeJournal/Magazine Articleen_US
dc.identifier.spage14119en_US
dc.identifier.epage14128en_US
dc.identifier.volume52en_US
dc.identifier.issue24en_US
dc.identifier.doi10.1021/acs.est.8b03355en_US
dcterms.abstractA new phosphorus (P) removal and recovery process that integrates an FeCl 3 -dosing, membrane bioreactor (MBR), and side-stream cofermentation was developed for wastewater treatment. The Fe and P species and their transformation mechanisms via aerobic and anaerobic conditions were investigated with X-ray absorption near edge structure (XANES) spectroscopy. In the new treatment system, 98.4% of the total P in domestic wastewater was removed and retained in activated sludge in the MBR. During the subsequent acidogenic cofermentation with food waste, P in the MBR sludge was released and eventually recovered as vivianite, achieving an overall P recovery efficiency of 61.9% from wastewater. The main pathways for P removal and recovery with iron dosing and acidogenic fermentation were determined by XANES analysis. The results showed that Fe-enhanced P removal with the MBR was mainly achieved by precipitation as ferric phosphate (24.2%) and adsorption onto hydrous iron oxides (60.3%). During anaerobic fermentation, transition from Fe(III)-P to Fe(II)-P complex occurred in the sludge, leading to Fe(II) dissolution and P release. The pH decrease and microbial Fe reduction were crucial conditions for effective P extraction from the MBR sludge. The efficiency of P recovery increased with an increase in the fermentation time and organic load and a decrease of pH in the solution.en_US
dcterms.accessRightsopen accessen_US
dcterms.bibliographicCitationEnvironmental science & technology, 18 Dec. 2018, v. 52, no. 24, p. 14119-14128en_US
dcterms.isPartOfEnvironmental science & technologyen_US
dcterms.issued2018-12-18-
dc.identifier.scopus2-s2.0-85058759010-
dc.identifier.pmid30452241-
dc.identifier.eissn1520-5851en_US
dc.description.validate202105 bchyen_US
dc.description.oaAccepted Manuscripten_US
dc.identifier.FolderNumbera0683-n14-
dc.description.fundingSourceRGCen_US
dc.description.fundingSourceOthersen_US
dc.description.fundingTextWe gratefully acknowledge the funding for this research provided by Grant Nos. 17204914, C7044-14G, and T21-711/ 16R from the Research Grants Council (RGC) of the Hong Kong SAR Government, the Grant KQJSCX20160226190815 from Shenzhen Municipal Science and Technology Innovation Council of Shenzhen Government, China, and the Grant Nos. 51678333 and 41603093 from National Natural Science Foundation of China.en_US
dc.description.pubStatusPublisheden_US
dc.description.oaCategoryGreen (AAM)en_US
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