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Naji, M. |
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Motta, Antonella |
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Aletan, Dirar |
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Mohamed, Tarek |
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Ertürk, Emre |
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Taccardi, Nicola |
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Kononenko, Denys |
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Petrov, R. H. | Madrid |
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Alshaaer, Mazen | Brussels |
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Bih, L. |
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Casati, R. |
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Muller, Hermance |
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Kočí, Jan | Prague |
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Šuljagić, Marija |
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Kalteremidou, Kalliopi-Artemi | Brussels |
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Azam, Siraj |
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Ospanova, Alyiya |
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Blanpain, Bart |
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Ali, M. A. |
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Popa, V. |
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Rančić, M. |
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Ollier, Nadège |
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Azevedo, Nuno Monteiro |
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Landes, Michael |
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Rignanese, Gian-Marco |
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Kirkelund, Gunvor Marie
Technical University of Denmark
in Cooperation with on an Cooperation-Score of 37%
Topics
Publications (23/23 displayed)
- 2024Mapping circular economy practices for steel, cement, glass, brick, insulation, and wood – A review for climate mitigation modelingcitations
- 2022Influence of ash type and mixing methods on workability and compressive strength when using Greenlandic MSWI fly ash as cement replacement in mortar
- 2022Effects of Chlorides and Sulphates on Heavy Metal Leaching from Mortar with Raw and Electrodialytically Treated MSWI Fly Ashcitations
- 2021Impact of electrodialytic remediation of MSWI fly ash on hydration and mechanical properties of blends with Portland cementcitations
- 2020Screening of untreated municipal solid waste incineration fly ash for use in cement-based materials: chemical and physical propertiescitations
- 2019Characterization of sewage sludge ash and its effect on moisture physics of mortarcitations
- 2019Electrodialytically treated MSWI fly ash use in clay bricks
- 2019Screening Untreated Municipal Solid Waste Incineration Fly Ash for Use in Cement-Based Materials – Chemical and Physical Properties
- 2018Using polycarbobetaines for cu recovery from catholytes generated by electrodialytic treatment of sewage sludge ash
- 2017Colour, compressive strength and workability of mortars with an iron rich sewage sludge ashcitations
- 2016Wood ash used as partly sand and/or cement replacement in mortarcitations
- 2016Replacement of 5% of OPC by fly ash and APC residues from MSWI with electrodialytic pre-treatment
- 2015Ammonium citrate as enhancement for electrodialytic soil remediation and investigation of soil solution during the processcitations
- 2015Multivariate methods for evaluating the efficiency of electrodialytic removal of heavy metals from polluted harbour sedimentscitations
- 2014Electrodialytically treated MSWI APC residue as substitute for cement in mortar
- 2014The Aesthetical quality of SSA-containing mortar and concrete
- 2013Effect of pulse current on acidification and removal of Cu, Cd, and As during suspended electrodialytic soil remediationcitations
- 2012Electrodialytic remediation of suspended soil – Comparison of two different soil fractionscitations
- 2012Testing the possibility for reusing mswi bottom ash in Greenlandic road construction
- 2012Characterisation of MSWI bottom ash for potential use as subbase in Greenlandic road construction
- 2009Electrodialytic remediation of harbour sediment in suspension - Evaluation of effects induced by changes in stirring velocity and current density on heavy metal removal and pHcitations
- 2007Electrodialytic extraction of Cd and Cu from sediment from Sisimiut Harbour, Greenlandcitations
- 2005Acidification of Harbour sediment and removal of heavy metals induced by water splitting in electrodialytic remediation.citations
Places of action
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document
Using polycarbobetaines for cu recovery from catholytes generated by electrodialytic treatment of sewage sludge ash
Abstract
Electrodialytic remediation is a process that uses a low current density to remove heavy metals from different waste matrixes, such as sewage sludge ash (SSA). The SSA is suspended in water and separated from the anolyte and catholyte compartments by ion exchange membranes. The heavy metal cations are separated from the ash and electromigrate into the catholyte, where they can electrodeposite on the cathode. Despite this electrodeposition, the catholyte contains heavy metals after the remediation process. Newly developed water-soluble polycarbobetaines (PCBets) have shown potential for selective removal of metal ions and especially Cu in synthetic solutions. In this study, it was investigated for the first time if the PCBets can remove Cu from the catholytes generated by electrodialytic remediation. Four electrodialytic separation experiments were made, treating SSA in slurries at liquid to solid ratios 3.5-21. The Cu removal from the SSA was between 6-30 %, resulting in catholyte concentrations between 0.18-4.34 mg Cu/l. The Cu selective PCBet, PCEAC was added to the four different catholytes for Cu extraction after a pH adjustment to around 5 of the catholytes. The removal of Cu was almost negligible by the PCEAC, regardless of the initial Cu concentration. Thus, the samples were spiked with Cu to concentrations between 77 – 319 mg/l and then the removal of Cu was tested by the addition of PCEAC or PCEAMC from the catholyte solution, resulting in Cu removals up to 70 % and 40 % respectively. However, a significant co-adsorption of Al, Ca and Zn was also seen. Based on the results, there is a potential in combining the use of PCBets to electrodialytic treatment, however the metal concentration in the catholyte should be increased and the PCBets should be further developed to avoid co-adsorption.