<?xml version="1.0" encoding="UTF-8"?><?xml-stylesheet type="text/xsl" href="static/CINECAstyle.xsl"?><OAI-PMH xmlns="http://www.openarchives.org/OAI/2.0/" xmlns:xsi="http://www.w3.org/2001/XMLSchema-instance" xsi:schemaLocation="http://www.openarchives.org/OAI/2.0/ http://www.openarchives.org/OAI/2.0/OAI-PMH.xsd"><responseDate>2026-09-23T11:40:21Z</responseDate><request verb="GetRecord" identifier="oai:iris.unica.it:11584/266321" metadataPrefix="oai_dc">https://iris.unica.it/oai/request</request><GetRecord><record><header><identifier>oai:iris.unica.it:11584/266321</identifier><datestamp>2022-10-20T09:32:47Z</datestamp><setSpec>com_11584_207615</setSpec><setSpec>com_11584_111066</setSpec><setSpec>col_11584_265854</setSpec></header><metadata><oai_dc:dc xmlns:oai_dc="http://www.openarchives.org/OAI/2.0/oai_dc/" xmlns:doc="http://www.lyncode.com/xoai" xmlns:xsi="http://www.w3.org/2001/XMLSchema-instance" xmlns:dc="http://purl.org/dc/elements/1.1/" xsi:schemaLocation="http://www.openarchives.org/OAI/2.0/oai_dc/ http://www.openarchives.org/OAI/2.0/oai_dc.xsd">
<dc:title>Use of electrokinetic and reactive barriers to treat heavy metals-contaminated soils</dc:title>
<dc:creator>SPIGA, DANIELA</dc:creator>
<dc:subject>Electrokinetic remediation</dc:subject>
<dc:subject>arsenate</dc:subject>
<dc:subject>chromate</dc:subject>
<dc:subject>reactive barrier</dc:subject>
<dc:subject>transformed red mud</dc:subject>
<dc:subject>Settore ICAR/03 - Ingegneria Sanitaria-Ambientale</dc:subject>
<dc:description>The combined use of electrokinetic (EK) and reactive barrier (RB) of transformed red mud (TRM) (a&#xd;
by-product of bauxite refinement for alumina production) for the remediation of low permeability&#xd;
contaminated soils by chromium and arsenic was investigated. The combination of EK with RB is a&#xd;
possible way in order to enhance EK removal of Cr and As that are reported to be among the more&#xd;
difficult elements to remove by electrokinetics.&#xd;
The goal and the novelty of the research consisted of evaluating the synergic interaction between&#xd;
the EK system and the RB and to compare the efficiency of such combined treatment with usual,&#xd;
unenhanced EK remediation process. From the joint application of EK and a TRM reactive barrier&#xd;
the following advantages were expected:&#xd;
-- the acid neutralizing capacity of the TRM RB should suppress acidification of the&#xd;
contaminated soil promoting the desorption of oxyanions under the influence of the&#xd;
alkalinity produced at the cathode and, in turn, enhancing their electromigration towards&#xd;
the anodic zone and the TRM RB;&#xd;
--        hydrogen ions generated at the anode during the EK process should provide the acidity&#xd;
required to increase the capacity of the nearby TRM RB to adsorb oxyanions.&#xd;
In the second part of the research, an in situ electrokinetic fence was compared with the&#xd;
performance of different permeable reactive barriers made of TRM, sodium-treated zeolite,&#xd;
magnesium oxide and biochar. The aim of the study was to compare the efficiency of each barrier&#xd;
system on the containment of the copper in order to withstand the spread of contaminant&#xd;
through the soil due to diffusion or hydraulic gradient.&#xd;
&#xd;
------------------------------------------------------------------------------------------------------------------------&#xd;
L'uso combinato dell’elettrocinesi (EK) e delle barriere reattive (RB) costituite da fanghi rossi&#xd;
trasformati (TRM) (residuo industriale del processo di produzione dell’allumina) è stato studiato&#xd;
per la bonifica di suoli caratterizzati da bassa permeabilità contaminati da cromo e arsenico.&#xd;
L’applicazione combinata di EK e RB consentirebbe di migliorare la rimozione elettrocinetica di Cr&#xd;
e As che sono segnalati essere tra gli elementi più difficili da rimuovere utilizzando l’elettrocinesi.&#xd;
L'obiettivo e la novità della ricerca è stato quello di valutare l'interazione sinergica tra il sistema&#xd;
elettrocinetico e la barriera reattiva, confrontando l'efficacia di tale trattamento combinato con il&#xd;
classico processo di bonifica elettrocinetica. Dall'applicazione congiunta erano previsti i seguenti&#xd;
vantaggi:&#xd;
-- la capacità di neutralizzazione acida dei TRM, sopprimendo l'acidificazione del suolo&#xd;
contaminato, promuoverebbe il desorbimento dei contaminanti anionici sotto l'influenza&#xd;
dell’alcalinità prodotta al catodo, migliorando la loro elettromigrazione verso la zona&#xd;
anodica dove è inserita la barriera reattiva;&#xd;
-- gli ioni idrogeno generati all'anodo durante il processo elettrocinetico fornirebbero l'acidità&#xd;
necessaria per aumentare la capacità di adsorbimento della TRM RB.&#xd;
Nella seconda parte della ricerca, la prestazione di una barriera elettrocinetica è stata confrontata&#xd;
con quella di barriere permeabili reattive costituite da TRM, Na-zeolite, ossido di magnesio e&#xd;
biochar. Lo scopo dello studio era di confrontare l'efficienza di ogni “sistema barriera” per il&#xd;
contenimento del rame, al fine di contrastare la diffusione</dc:description>
<dc:date>2011-03-25</dc:date>
<dc:type>info:eu-repo/semantics/doctoralThesis</dc:type>
<dc:identifier>http://hdl.handle.net/11584/266321</dc:identifier>
<dc:language>eng</dc:language>
<dc:relation>numberofpages:212</dc:relation>
<dc:rights>info:eu-repo/semantics/openAccess</dc:rights>
<dc:publisher>Università degli Studi di Cagliari</dc:publisher>
<dc:rights>license:Non specificato</dc:rights>
</oai_dc:dc></metadata></record></GetRecord></OAI-PMH>