<?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>2026-09-24T17:58:39Z</responseDate><request verb="GetRecord" identifier="oai:univendspace.univen.ac.za:11602/2474" metadataPrefix="dim">https://univendspace.univen.ac.za/server/oai/request</request><GetRecord><record><header><identifier>oai:univendspace.univen.ac.za:11602/2474</identifier><datestamp>2024-09-10T14:38:30Z</datestamp><setSpec>com_11602_1928</setSpec><setSpec>com_11602_1914</setSpec><setSpec>com_11602_1897</setSpec><setSpec>com_11602_737</setSpec><setSpec>col_11602_2140</setSpec><setSpec>col_11602_738</setSpec></header><metadata><dim:dim xmlns:dim="http://www.dspace.org/xmlns/dspace/dim" xmlns:xsi="http://www.w3.org/2001/XMLSchema-instance" xmlns:doc="http://www.lyncode.com/xoai" xsi:schemaLocation="http://www.dspace.org/xmlns/dspace/dim http://www.dspace.org/schema/dim.xsd">
   <dim:field mdschema="dc" element="contributor" qualifier="advisor">Gitari, W. M.</dim:field>
   <dim:field mdschema="dc" element="contributor" qualifier="advisor">Mudzielwana, R.</dim:field>
   <dim:field mdschema="dc" element="contributor" qualifier="advisor">Ngure, V.</dim:field>
   <dim:field mdschema="dc" element="contributor" qualifier="author">Sathekge, Salphinah Ntombikayise</dim:field>
   <dim:field mdschema="dc" element="date">2022</dim:field>
   <dim:field mdschema="dc" element="date" qualifier="accessioned">2023-05-29T06:28:15Z</dim:field>
   <dim:field mdschema="dc" element="date" qualifier="available">2023-05-29T06:28:15Z</dim:field>
   <dim:field mdschema="dc" element="date" qualifier="issued">2023-05-19</dim:field>
   <dim:field mdschema="dc" element="identifier" qualifier="citation">Sathekge, S. N. (2022) Assessment of co-occurrence of cyanotoxins, toxic metals and anionic surfactants in irrigation water, agricultural soils and food crops. University of Venda. South Africa.&amp;lt;http://hdl.handle.net/11602/2474&amp;gt;.</dim:field>
   <dim:field mdschema="dc" element="identifier" qualifier="uri">http://hdl.handle.net/11602/2474</dim:field>
   <dim:field mdschema="dc" element="identifier" qualifier="vancouvercitation" lang="en_ZA">Sathekge SN. Assessment of co-occurrence of cyanotoxins, toxic metals and anionic surfactants in irrigation water, agricultural soils and food crops. []. , 2023 [cited yyyy month dd]. Available from: http://hdl.handle.net/11602/2474</dim:field>
   <dim:field mdschema="dc" element="identifier" qualifier="apacitation" lang="en_ZA">Sathekge, S. N. (2023). &amp;lt;i&amp;gt;Assessment of co-occurrence of cyanotoxins, toxic metals and anionic surfactants in irrigation water, agricultural soils and food crops&amp;lt;/i&amp;gt;. (). . Retrieved from http://hdl.handle.net/11602/2474</dim:field>
   <dim:field mdschema="dc" element="identifier" qualifier="chicagocitation" lang="en_ZA">Sathekge, Salphinah Ntombikayise. &amp;lt;i&amp;gt;&amp;quot;Assessment of co-occurrence of cyanotoxins, toxic metals and anionic surfactants in irrigation water, agricultural soils and food crops.&amp;quot;&amp;lt;/i&amp;gt; ., , 2023. http://hdl.handle.net/11602/2474</dim:field>
   <dim:field mdschema="dc" element="identifier" qualifier="ris" lang="en_ZA">&#xd;
TY  - Dissertation&#xd;
AU  - Sathekge, Salphinah Ntombikayise&#xd;
AB  - Globally, the occurrence of cyanobacterial blooms in freshwater ecosystems has become a concern.&#xd;
Cyanobacteria produces secondary metabolites, known as cyanotoxins that cause acute and chronic&#xd;
poisoning in animals and humans. History of mining, industrial activities and poor maintenance of&#xd;
wastewater treatment infrastructure are the main causes of the hyper-eutrophic conditions affecting&#xd;
most dams in South Africa. The co-occurrence of multiple stressors in agricultural waters and soils&#xd;
potentially pose a human and animal risk if contaminated water and plants are ingested.&#xd;
The study investigated the co-existence of cyanotoxins, anionic surfactants and metal species in&#xd;
irrigation water, agricultural soils and food crops and determine the health risks associated with&#xd;
consuming cyanotoxins contaminated plants in the Crocodile (West) Marico Water Management&#xd;
Area, which covers parts of Gauteng and Northwest Provinces. Lastly, the study assessed the&#xd;
applicability of passive sampling technology in monitoring of cyanotoxins using DIAON HP20&#xd;
resins as an adsorbent. Water, food crops and soil samples were collected from Roodeplaat and&#xd;
Hartbeespoort dam sites in irrigation canals and cropping fields in June 2019, September 2019,&#xd;
February 2020, and March 2021. Seven sites were selected for sampling of water for cyanotoxins,&#xd;
anionic surfactants and toxic metals, while 4 farmland sites were selected for agricultural soils and&#xd;
food crops in Roodeplaat and Hartbeespoort sites. Physicochemical parameters of the irrigation&#xd;
water (pH, temperature, EC, TDS, DO), chlorophyll-a and dissolved nutrients were also monitored&#xd;
using Spectrophotometer and Spectro-Quant® Merck Pharo 100 with the photo-metric test kits&#xd;
from Merck, respectively. The levels of Microcystins (MCs), anionic surfactants, and metals were&#xd;
detected and quantified using the ELISA method, anionic surfactant portable photometer and&#xd;
inductively coupled plasma mass spectrometry (ICP- MS), respectively. The results are presented&#xd;
for each chapters below.&#xd;
The results for chapter 1 revealed the co-existence of cyanotoxins, metal species and anionic&#xd;
surfactants in the irrigation water, and agricultural soils, across sampling sites, throughout sampling&#xd;
period. The microcystins in irrigation water ranged from 0.00 to 15.57 μg/L. Total anionic&#xd;
surfactants in irrigation water and agricultural soil ranged from 0.01 to 3.49 mg/L and 1.81 to 5.46&#xd;
mg/kg, respectively. Among all the physicochemical parameters only pH (p = 0.624), TDS (p = -&#xd;
0.466), EC (p = - 0.445), and turbidity (p = 0.521) correlated with MCs. Moreover, total anionic&#xd;
surfactant showed to have positive moderate relationship with levels of MCs in irrigation water (p =&#xd;
0.342). Metal species in irrigation water were decreased in the following order: Al &amp;gt; Mn &amp;gt; Fe &amp;gt; B &amp;gt;&#xd;
Zn &amp;gt; Ni &amp;gt; Cu &amp;gt; Pb &amp;gt; Cr &amp;gt; As and were all below the maximum DWAF acceptable limit, implying&#xd;
that the water was safe for irrigation use. Metal species in other soil sampling sites such as&#xd;
16534.61 – 33285 mg/kg (Fe), 111.25 – 723.4 mg/kg (Cr),4.44 – 23.93 mg/kg (Pb), 0.80 – 9.70&#xd;
mg/kg (As), 22.11 – 33.95 mg/kg (Cu), and 33.70 – 85.885 mg/kg (Ni) were above the maximum&#xd;
limit set by DEA, USEPA, and FAO/WHO for agricultural use. Thus, soils from Roodeplaat and&#xd;
Hartbeespoort farmland sites are contaminated by the mentioned metals.&#xd;
The findings from the second chapter of results revealed the bio-accumulation of microcystins and&#xd;
metals in food crops. The estimated daily intake (EDI) for MCs in all food crops for both adults and&#xd;
children were below 0.04 μg/kg DW acceptable value set by World Health Organisation, implying&#xd;
that the crops were safe for human consumption by adult and children population. Metal species&#xd;
levels accumulated in plant samples collected from different sampling sites, showed that 0.21 to&#xd;
10.80 mg/kg (Cr), 19.64 to 734.00 mg/kg (Fe), 5.45 to 76.80 mg/kg (Zn), 0.01 to 0.20 mg/kg (As),&#xd;
0.96 to 60.40 mg/kg (Cu), and 0.10 to 0.70 mg/kg (Pb) were above the EU and FAO/WHO&#xd;
guideline standards. Spearman correlation between metals in plants and water showed that only Pb&#xd;
(p = 0.874) and As (p = 0.809) in irrigation water had a positive moderate association with metals in&#xd;
plants collected from the sampling sites. The estimated daily intake (EDI) of metals via&#xd;
consumption of the crops were found to be below the maximum tolerable daily intake (MTDI)&#xd;
proposed for each metal. The translocation factors (TF) showed that only Cu and Cd were rapidly&#xd;
transported to the plant’s edible parts from the soil. Moreover, target hazard quotient (THQ) for&#xd;
each metal were below 1, indicating that consuming the food crops wont cause carcinogenic effect&#xd;
to the adult population, while hazard index (HI) for other sites was found to be &amp;gt;1 for crop plants,&#xd;
thus plants from these sites pose a health hazards to adult population. In addition, the target cancer&#xd;
risk (TCR) value for Cr and Ni in crops from other sampling sites were above the maximum&#xd;
threshold implying that there is a potential cancer risk to adult population over a long-term.&#xd;
In addition, findings from the third chapter showed that SPATT was applicable in monitoring and&#xd;
detecting MCs across all sampling sites and sampling months. The MCs levels in grab and SPATT&#xd;
bags ranged from 0.14 to 13.03 μg/L and 0.99 to 2.28 ng/g resin throughout the sampling sites and&#xd;
months, respectively. Thus, showing the persistence of MCs in canals and farm dams of Roodeplaat&#xd;
and Hartbeespoort. A spearman correlation revealed that pH (p = 0.776), Turbidity (p = 0.699) and&#xd;
DO (p = 0.829) had a significant positive association with total toxins in grab samples, while total&#xd;
dissolved MCs in SPATT samples showed negative moderate relationship with TDS (p = - 0.615)&#xd;
and EC (p = - 0.602). Total toxin concentrations in SPATT bags and Grab samples did not show&#xd;
any correlation this is because SPATT bags detect and collect microcystins within water column&#xd;
overtime, unlike point (Grab sampling), hence, there is no relationship between the two-sampling&#xd;
method. Overall results showed that SPATT bags with DIAON HP20 resin as an adsorbent proved&#xd;
to be applicable in monitoring and detecting microcystins in the irrigation water of Roodeplaat and&#xd;
Hartbeespoort sites.&#xd;
DA  - 2023-05-19&#xd;
DB  - ResearchSpace&#xd;
DP  - Univen&#xd;
KW  - Cyanobacteria&#xd;
KW  - Cyanotoxins&#xd;
KW  - Toxic metals&#xd;
KW  - Aniomic surfactants&#xd;
KW  - Irrigation water&#xd;
KW  - Agricultural soils&#xd;
KW  - Food crops&#xd;
KW  - Solid phase adsorption toxin tracking (SPATT)&#xd;
LK  - https://univendspace.univen.ac.za&#xd;
PY  - 2023&#xd;
T1  - Assessment of co-occurrence of cyanotoxins, toxic metals and anionic surfactants in irrigation water, agricultural soils and food crops&#xd;
TI  - Assessment of co-occurrence of cyanotoxins, toxic metals and anionic surfactants in irrigation water, agricultural soils and food crops&#xd;
UR  - http://hdl.handle.net/11602/2474&#xd;
ER  - &#xd;
</dim:field>
   <dim:field mdschema="dc" element="description" lang="en_ZA">Department of Geography and Environmental Sciences</dim:field>
   <dim:field mdschema="dc" element="description">Department of Geography and Environmental Sciences</dim:field>
   <dim:field mdschema="dc" element="description" qualifier="abstract" lang="en_ZA">Globally, the occurrence of cyanobacterial blooms in freshwater ecosystems has become a concern.&#xd;
Cyanobacteria produces secondary metabolites, known as cyanotoxins that cause acute and chronic&#xd;
poisoning in animals and humans. History of mining, industrial activities and poor maintenance of&#xd;
wastewater treatment infrastructure are the main causes of the hyper-eutrophic conditions affecting&#xd;
most dams in South Africa. The co-occurrence of multiple stressors in agricultural waters and soils&#xd;
potentially pose a human and animal risk if contaminated water and plants are ingested.&#xd;
The study investigated the co-existence of cyanotoxins, anionic surfactants and metal species in&#xd;
irrigation water, agricultural soils and food crops and determine the health risks associated with&#xd;
consuming cyanotoxins contaminated plants in the Crocodile (West) Marico Water Management&#xd;
Area, which covers parts of Gauteng and Northwest Provinces. Lastly, the study assessed the&#xd;
applicability of passive sampling technology in monitoring of cyanotoxins using DIAON HP20&#xd;
resins as an adsorbent. Water, food crops and soil samples were collected from Roodeplaat and&#xd;
Hartbeespoort dam sites in irrigation canals and cropping fields in June 2019, September 2019,&#xd;
February 2020, and March 2021. Seven sites were selected for sampling of water for cyanotoxins,&#xd;
anionic surfactants and toxic metals, while 4 farmland sites were selected for agricultural soils and&#xd;
food crops in Roodeplaat and Hartbeespoort sites. Physicochemical parameters of the irrigation&#xd;
water (pH, temperature, EC, TDS, DO), chlorophyll-a and dissolved nutrients were also monitored&#xd;
using Spectrophotometer and Spectro-Quant® Merck Pharo 100 with the photo-metric test kits&#xd;
from Merck, respectively. The levels of Microcystins (MCs), anionic surfactants, and metals were&#xd;
detected and quantified using the ELISA method, anionic surfactant portable photometer and&#xd;
inductively coupled plasma mass spectrometry (ICP- MS), respectively. The results are presented&#xd;
for each chapters below.&#xd;
The results for chapter 1 revealed the co-existence of cyanotoxins, metal species and anionic&#xd;
surfactants in the irrigation water, and agricultural soils, across sampling sites, throughout sampling&#xd;
period. The microcystins in irrigation water ranged from 0.00 to 15.57 μg/L. Total anionic&#xd;
surfactants in irrigation water and agricultural soil ranged from 0.01 to 3.49 mg/L and 1.81 to 5.46&#xd;
mg/kg, respectively. Among all the physicochemical parameters only pH (p = 0.624), TDS (p = -&#xd;
0.466), EC (p = - 0.445), and turbidity (p = 0.521) correlated with MCs. Moreover, total anionic&#xd;
surfactant showed to have positive moderate relationship with levels of MCs in irrigation water (p =&#xd;
0.342). Metal species in irrigation water were decreased in the following order: Al &amp;gt; Mn &amp;gt; Fe &amp;gt; B &amp;gt;&#xd;
Zn &amp;gt; Ni &amp;gt; Cu &amp;gt; Pb &amp;gt; Cr &amp;gt; As and were all below the maximum DWAF acceptable limit, implying&#xd;
that the water was safe for irrigation use. Metal species in other soil sampling sites such as&#xd;
16534.61 – 33285 mg/kg (Fe), 111.25 – 723.4 mg/kg (Cr),4.44 – 23.93 mg/kg (Pb), 0.80 – 9.70&#xd;
mg/kg (As), 22.11 – 33.95 mg/kg (Cu), and 33.70 – 85.885 mg/kg (Ni) were above the maximum&#xd;
limit set by DEA, USEPA, and FAO/WHO for agricultural use. Thus, soils from Roodeplaat and&#xd;
Hartbeespoort farmland sites are contaminated by the mentioned metals.&#xd;
The findings from the second chapter of results revealed the bio-accumulation of microcystins and&#xd;
metals in food crops. The estimated daily intake (EDI) for MCs in all food crops for both adults and&#xd;
children were below 0.04 μg/kg DW acceptable value set by World Health Organisation, implying&#xd;
that the crops were safe for human consumption by adult and children population. Metal species&#xd;
levels accumulated in plant samples collected from different sampling sites, showed that 0.21 to&#xd;
10.80 mg/kg (Cr), 19.64 to 734.00 mg/kg (Fe), 5.45 to 76.80 mg/kg (Zn), 0.01 to 0.20 mg/kg (As),&#xd;
0.96 to 60.40 mg/kg (Cu), and 0.10 to 0.70 mg/kg (Pb) were above the EU and FAO/WHO&#xd;
guideline standards. Spearman correlation between metals in plants and water showed that only Pb&#xd;
(p = 0.874) and As (p = 0.809) in irrigation water had a positive moderate association with metals in&#xd;
plants collected from the sampling sites. The estimated daily intake (EDI) of metals via&#xd;
consumption of the crops were found to be below the maximum tolerable daily intake (MTDI)&#xd;
proposed for each metal. The translocation factors (TF) showed that only Cu and Cd were rapidly&#xd;
transported to the plant’s edible parts from the soil. Moreover, target hazard quotient (THQ) for&#xd;
each metal were below 1, indicating that consuming the food crops wont cause carcinogenic effect&#xd;
to the adult population, while hazard index (HI) for other sites was found to be &amp;gt;1 for crop plants,&#xd;
thus plants from these sites pose a health hazards to adult population. In addition, the target cancer&#xd;
risk (TCR) value for Cr and Ni in crops from other sampling sites were above the maximum&#xd;
threshold implying that there is a potential cancer risk to adult population over a long-term.&#xd;
In addition, findings from the third chapter showed that SPATT was applicable in monitoring and&#xd;
detecting MCs across all sampling sites and sampling months. The MCs levels in grab and SPATT&#xd;
bags ranged from 0.14 to 13.03 μg/L and 0.99 to 2.28 ng/g resin throughout the sampling sites and&#xd;
months, respectively. Thus, showing the persistence of MCs in canals and farm dams of Roodeplaat&#xd;
and Hartbeespoort. A spearman correlation revealed that pH (p = 0.776), Turbidity (p = 0.699) and&#xd;
DO (p = 0.829) had a significant positive association with total toxins in grab samples, while total&#xd;
dissolved MCs in SPATT samples showed negative moderate relationship with TDS (p = - 0.615)&#xd;
and EC (p = - 0.602). Total toxin concentrations in SPATT bags and Grab samples did not show&#xd;
any correlation this is because SPATT bags detect and collect microcystins within water column&#xd;
overtime, unlike point (Grab sampling), hence, there is no relationship between the two-sampling&#xd;
method. Overall results showed that SPATT bags with DIAON HP20 resin as an adsorbent proved&#xd;
to be applicable in monitoring and detecting microcystins in the irrigation water of Roodeplaat and&#xd;
Hartbeespoort sites.</dim:field>
   <dim:field mdschema="dc" element="description" qualifier="sponsorship" lang="en_ZA">NRF</dim:field>
   <dim:field mdschema="dc" element="format" qualifier="extent">1 online resources (xiv, 170 leaves) : color illustrations, color maps</dim:field>
   <dim:field mdschema="dc" element="language" qualifier="iso" lang="en_ZA">en</dim:field>
   <dim:field mdschema="dc" element="rights">University of Venda</dim:field>
   <dim:field mdschema="dc" element="subject" lang="en_ZA">Cyanobacteria</dim:field>
   <dim:field mdschema="dc" element="subject" lang="en_ZA">UCTD</dim:field>
   <dim:field mdschema="dc" element="subject" lang="en_ZA">Cyanotoxins</dim:field>
   <dim:field mdschema="dc" element="subject" lang="en_ZA">Toxic metals</dim:field>
   <dim:field mdschema="dc" element="subject" lang="en_ZA">Aniomic surfactants</dim:field>
   <dim:field mdschema="dc" element="subject" lang="en_ZA">Irrigation water</dim:field>
   <dim:field mdschema="dc" element="subject" lang="en_ZA">Agricultural soils</dim:field>
   <dim:field mdschema="dc" element="subject" lang="en_ZA">Food crops</dim:field>
   <dim:field mdschema="dc" element="subject" lang="en_ZA">Solid phase adsorption toxin tracking (SPATT)</dim:field>
   <dim:field mdschema="dc" element="subject" qualifier="ddc">571.950968</dim:field>
   <dim:field mdschema="dc" element="subject" qualifier="lcsh">Cyanobacteria -- South Africa</dim:field>
   <dim:field mdschema="dc" element="subject" qualifier="lcsh">Cyanobacteria toxin -- South Africa</dim:field>
   <dim:field mdschema="dc" element="subject" qualifier="lcsh">Irrigation water -- South Africa</dim:field>
   <dim:field mdschema="dc" element="subject" qualifier="lcsh">Food crops -- South Africa</dim:field>
   <dim:field mdschema="dc" element="title" lang="en_ZA">Assessment of co-occurrence of cyanotoxins, toxic metals and anionic surfactants in irrigation water, agricultural soils and food crops</dim:field>
   <dim:field mdschema="dc" element="type" lang="en_ZA">Dissertation</dim:field>
   <dim:field mdschema="others" element="access-status">open.access</dim:field>
</dim:dim></metadata></record></GetRecord></OAI-PMH>