“…Advantages of PLS include simultaneous modelling of several responses, coping with collinearity between variables, coping with noise in the X and Y matrices, coping with moderate amounts of missing data (<20%) and since it is based on projections, it is possible to have more variables than objects [30,31]. The use of PLS in studies of pollution has been scarce and besides limited use for optimisation of remediation [33][34][35], it has been employed for identifying important factors for formation of toxic compounds in waste combustion [36,37].…”
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“…Advantages of PLS include simultaneous modelling of several responses, coping with collinearity between variables, coping with noise in the X and Y matrices, coping with moderate amounts of missing data (<20%) and since it is based on projections, it is possible to have more variables than objects [30,31]. The use of PLS in studies of pollution has been scarce and besides limited use for optimisation of remediation [33][34][35], it has been employed for identifying important factors for formation of toxic compounds in waste combustion [36,37].…”
Users may download and print one copy of any publication from the public portal for the purpose of private study or research. You may not further distribute the material or use it for any profit-making activity or commercial gain You may freely distribute the URL identifying the publication in the public portal If you believe that this document breaches copyright please contact us providing details, and we will remove access to the work immediately and investigate your claim.
“…Current density = Current (mA)/Area of inner circumference of electrodialytic cell (cm 2 ) 3 Experiments previously reported in [11] 4 Experiments previously reported in [10] 5 Experiments previously reported in [9] 6 Experiments previously reported in [7] The power consumption in Wh (E) was calculated as:…”
Section: Experimental Designmentioning
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%
“…It has however been employed for identifying important factors for formation of toxic PCB during waste combustion [5] and to assess the influence of soil properties on the chemical oxidation of PAH in soil [6]. In addition, our group has previously demonstrated the use of PLS models for evaluating the experimental variables for sediment-specific electrodialytic remediation (EDR) [7][8][9][10], as well as a tool for predicting experimental settings in new sediment [11].…”
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.
“…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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