“…In all of the experiments a 3-compartment electrodialytic cell design was used and an illustration of the set-up can be found elsewhere [30]. The experimental set-up consisted of a centre compartment containing the sediment suspensions and electrolyte liquids were circulated in two adjoining compartments.…”
Section: Methodsmentioning
confidence: 99%
“…Metal partitioning, determined by sequential extraction, is an indication of how available the metals are in the sediment and to what extent a metal will be mobilised by ion-exchange, dissolution of carbonates, reducing or oxidising conditions, or acidic (pH<2) conditions. It can be a useful tool for assessing the potential for removing metals from sediments by electrodialysis and higher removal rates have for instance been observed for the more available metals (exchangeable/reducible) in the sediment [7,30].…”
Section: Metal Availability In the Sedimentsmentioning
confidence: 99%
“…Current density and time have been shown to be the most important experimental variables influencing EDR [16,25,[28][29][30]. High current densities may however impede the removal and increase the energy consumption significantly.…”
Chemometrics was used to determine the influence of sediment properties and experimental settings for the electrodialytic removal (EDR) of Cu, Pb and Zn from six harbour sediments from Greenland and Norway. A Projection onto latent structures (PLS) model revealed that the most important sediment properties for achieving acidification (lag-phase, pH>4), necessary for desorbing and mobilising metals in the polluted sediments, were buffer capacity and grain size distribution. Higher stirring rate reduced the acidification time, stressing the importance of thorough mixing of the sediment suspension to achieve a fast and uniform acidification.PLS models were calculated to determine the influence of sediment properties on the removal of metals during EDR, which was observed to vary depending on the targeted metal and the stage of the remediation. In general, buffer capacity, grain size distribution, element composition and metal partitioning were important for remediation efficiency and are important parameters for determining optimal experimental settings. In the fast removal phase (final pH 2-4), organic matter as well as stirring rate had increasing importance indicating oxidation and release of metals at this stage. Understanding the influence of sediment properties is important for determining experimental settings in accordance with the phase of EDR.
“…In all of the experiments a 3-compartment electrodialytic cell design was used and an illustration of the set-up can be found elsewhere [30]. The experimental set-up consisted of a centre compartment containing the sediment suspensions and electrolyte liquids were circulated in two adjoining compartments.…”
Section: Methodsmentioning
confidence: 99%
“…Metal partitioning, determined by sequential extraction, is an indication of how available the metals are in the sediment and to what extent a metal will be mobilised by ion-exchange, dissolution of carbonates, reducing or oxidising conditions, or acidic (pH<2) conditions. It can be a useful tool for assessing the potential for removing metals from sediments by electrodialysis and higher removal rates have for instance been observed for the more available metals (exchangeable/reducible) in the sediment [7,30].…”
Section: Metal Availability In the Sedimentsmentioning
confidence: 99%
“…Current density and time have been shown to be the most important experimental variables influencing EDR [16,25,[28][29][30]. High current densities may however impede the removal and increase the energy consumption significantly.…”
Chemometrics was used to determine the influence of sediment properties and experimental settings for the electrodialytic removal (EDR) of Cu, Pb and Zn from six harbour sediments from Greenland and Norway. A Projection onto latent structures (PLS) model revealed that the most important sediment properties for achieving acidification (lag-phase, pH>4), necessary for desorbing and mobilising metals in the polluted sediments, were buffer capacity and grain size distribution. Higher stirring rate reduced the acidification time, stressing the importance of thorough mixing of the sediment suspension to achieve a fast and uniform acidification.PLS models were calculated to determine the influence of sediment properties on the removal of metals during EDR, which was observed to vary depending on the targeted metal and the stage of the remediation. In general, buffer capacity, grain size distribution, element composition and metal partitioning were important for remediation efficiency and are important parameters for determining optimal experimental settings. In the fast removal phase (final pH 2-4), organic matter as well as stirring rate had increasing importance indicating oxidation and release of metals at this stage. Understanding the influence of sediment properties is important for determining experimental settings in accordance with the phase of EDR.
“…Stirring has proven more efficient than a stationary set-up (Pedersen et al, 2003;Ottosen et al, 2012) and appears appropriate to apply for remediating dredged sediments. Other variables of importance to the efficiency of EDR include sediment, cell design, current density and time (Pedersen et al, 2015d;Pedersen et al, 2015e). The 2-compartment and 3-compartment cells used in the study were designed using the same materials and sizes; the 3-compartment cells consisted of two electrolyte compartment and between these a compartment containing the sediment suspension.…”
Section: Electrodialytic Remediation Experiments 231 Materials and mentioning
confidence: 99%
“…For this, different statistical tools may prove valuable and in a recent report the use of factorial design in optimizing the remediation of uranium polluted soils was reported (Radu et al, 2015). Another method is projections onto latent structures (PLS) which has been extensively used in chemical synthesis (Carlson and Carlson, 2005a) and also in studies of the influence of soil properties on PAH oxidation (Jonsson et al, 2007) and for identifying the most relevant variables for electrochemical treatment of sediments (Pedersen et al, 2015b;Pedersen et al, 2015c;Pedersen et al, 2015d).…”
Multivariate methodology was employed for finding optimum remediation conditions for electrodialytic remediation of harbour sediment from an Arctic location in Norway. The parts of the experimental domain in which both sediment- and technology-specific remediation objectives were met were identified. Objectives targeted were removal of the sediment-specific pollutants Cu and Pb, while minimising the effect on the sediment matrix by limiting the removal of naturally occurring metals while maintaining low energy consumption. Two different cell designs for electrochemical remediation were tested and final concentrations of Cu and Pb were below background levels in large parts of the experimental domain when operating at low current densities (<0.12 mA/cm(2)). However, energy consumption, remediation times and the effect on naturally occurring metals were different for the 2- and 3-compartment cells.
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