<?xml version="1.0" encoding="UTF-8"?><?xml-stylesheet type="text/xsl" href="static/style.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>2026-09-18T21:59:58Z</responseDate><request verb="GetRecord" identifier="oai:openscholar.dut.ac.za:10321/3822" metadataPrefix="oai_dc">https://openscholar.dut.ac.za/server/oai/request</request><GetRecord><record><header><identifier>oai:openscholar.dut.ac.za:10321/3822</identifier><datestamp>2025-04-03T01:02:14Z</datestamp><setSpec>com_10321_5</setSpec><setSpec>col_10321_6</setSpec></header><metadata><oai_dc:dc xmlns:oai_dc="http://www.openarchives.org/OAI/2.0/oai_dc/" xmlns:dc="http://purl.org/dc/elements/1.1/" xmlns:xsi="http://www.w3.org/2001/XMLSchema-instance" xmlns:doc="http://www.lyncode.com/xoai" xsi:schemaLocation="http://www.openarchives.org/OAI/2.0/oai_dc/ http://www.openarchives.org/OAI/2.0/oai_dc.xsd">
   <dc:title>Optimization of extraction techniques for the isolation and pre-concentration of pharmaceuticals in aquatic environments</dc:title>
   <dc:creator>Sigonya, Sisonke</dc:creator>
   <dc:contributor>Mdluli, Phumlane Selby</dc:contributor>
   <dc:contributor>Chimuka, Luke</dc:contributor>
   <dc:subject>Extraction (Chemistry)</dc:subject>
   <dc:subject>Medical wastes</dc:subject>
   <dc:subject>Emerging contaminants in water</dc:subject>
   <dc:subject>Waste disposal in rivers, lakes, etc.</dc:subject>
   <dc:description>Dissertation submitted in fulfilment of the requirements for the degree Master of Applied Science: Chemistry, Durban University of Technology, 2021.</dc:description>
   <dc:description>The occurrence of pharmaceuticals in South African aquatic environments has been reported&#xd;
in several studies. However, most of these reports focused on the occurrence of organic&#xd;
compounds in wastewater and surface water. There are very few studies reporting the presence&#xd;
and concentration of these compounds in seawater and coastal areas. Further, most studies have&#xd;
looked at only on one season. This study focussed on the optimisation of a SPE extraction&#xd;
method using Bond Elut Plexa cartridges for the identification and quantification three nonsteroidal anti-inflammatory drugs (NSAIDs), three antiretroviral drugs (ARVs) and a lipid&#xd;
regulator in coastal area of Durban city, South Africa covering four seasons. The optimised&#xd;
SPE conditions were as follows: 500 mL sample volume and at pH 5.8, 5 and 5 mL as&#xd;
conditioning and elution volumes, respectively. The flow rate ranging from 5 to 10 mL/min 10&#xd;
and 5 mL/min as sample and elution flow rates. The extracted compounds were qualitatively&#xd;
and quantitatively detected by a high-performance liquid phase chromatographic instrument&#xd;
coupled to a photodiode array detector (HPLC-PDA). The recoveries ranged from 62 -102%&#xd;
with RSD values of 0.56 to 4.68% respectively for the determination of emtricitabine,&#xd;
tenofovir, naproxen, diclofenac, ibuprofen, efavirenz, and gemfibrozil. The analytical method&#xd;
was validated by spiking estuarine water samples with 5 µg L-1&#xd;
of a mixture containing the&#xd;
target pharmaceuticals and the matrix detection limits (MDL) were established to be 0.62- 1.78&#xd;
µg L-1&#xd;
for the target compounds. The optimized method was applied to seasonal monitoring of&#xd;
pharmaceuticals at chosen study sites from winter and spring of 2019 and summer and autumn&#xd;
of 2020.The sum of emerging pollutants (ƩEP) were calculated based on each study site. The&#xd;
influent of the Kingsburgh WWTP (EFK) had the highest ƩEP of 144.88 µg L-1&#xd;
in winter&#xd;
between the two wastewater treatment plants area in this study. The Northern WWTP influent&#xd;
(INN) had a total ƩEP of 117.11 µg L-1&#xd;
in autumn, the Kingsburgh WWTP effluent (EFK) had&#xd;
a concentration 63.8 µg L-1&#xd;
in autumn and a concentration 63.8 µg L-1&#xd;
in summer and the Northern (EFN) had a total ƩEP of 43.97 µg L-1&#xd;
in winter. A comparison between UMgeni&#xd;
(UR) and Kingsburgh river (KR) showed that the KR had the highest concentration of total&#xd;
ƩEP of 22.66 µg L-1&#xd;
and UR with the total ƩEP of 18.3 µg L-1&#xd;
both in winter and spring,&#xd;
respectively. The seawater EPs Blue Lagoon (BL) had the highest ƩEP of 46.75 µg L-1&#xd;
in&#xd;
spring, subsequently Warner Beach bottom (WBB), Glen Ashley (GA) and Warner Beach top&#xd;
(WBT) with concentrations of 24.96 µg L-1&#xd;
in summer, 13.29 µg L-1 in spring and 6.94 µg L-1&#xd;
in autumn, respectively. Estuarine EPs had concentrations of 37.9 µg L-1&#xd;
and 20.97 µg L-1 for Warner beach estuary (WE) and UMgeni estuary (UE) in winter. WBE having the highest&#xd;
concentration between the two. This showed a significant variation on the presence of these&#xd;
pharmaceuticals in different season.</dc:description>
   <dc:description>M</dc:description>
   <dc:date>2022-01-27T12:30:32Z</dc:date>
   <dc:date>2022-01-27T12:30:32Z</dc:date>
   <dc:date>2021</dc:date>
   <dc:type>Thesis</dc:type>
   <dc:identifier>https://hdl.handle.net/10321/3822</dc:identifier>
   <dc:identifier>https://doi.org/10.51415/10321/3822</dc:identifier>
   <dc:language>en</dc:language>
   <dc:format>109 p</dc:format>
   <dc:format>application/pdf</dc:format>
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