Research Article
SimultaneousElectrochemicalDetectionofPbandCdbyCarbon
Paste Electrodes Modified by Activated Clay
Niraka Blaise,
1
HambateGomdjeVal´ ery ,
1
Raja Maallah,
2
Mohamed Oubaouz,
2
Bakary Tigana Djonse Justin,
1
Edwin Andrew Ofudje ,
3
and Abdelilah Chtaini
2
1
National Advanced School of Engineering, University of Maroua, P.O. Box 46, Maroua, Cameroon
2
Team of Molecular Electrochemistry and Inorganic Materials, Faculty of Sciences and Technology,
Sultan Moulay Slimane University of Beni Mellal, Beni Mellal, Morocco
3
Department of Chemical Sciences, Mountain Top University, Prayer City, Ogun State, Nigeria
CorrespondenceshouldbeaddressedtoHambateGomdjeVal´ ery;valeryhambate@gmail.comandEdwinAndrewOfudje;
eaofudje@mtu.edu.ng
Received 9 October 2021; Accepted 6 December 2021; Published 19 January 2022
AcademicEditor:JaroonJakmunee
Copyright©2022NirakaBlaiseetal.isisanopenaccessarticledistributedundertheCreativeCommonsAttributionLicense,
which permits unrestricted use, distribution, and reproduction in any medium, provided the original work is properly cited.
Calcinated and acidified clay modified carbon graphite electrode was deployed in the simultaneous evaluation of traces of Pb
2+
andCd
2+
insolution.After5minutesofaccumulationinthecircuit,thesensitivityoftheelectrodewasevaluatedinasolutionof
Na
2
SO
4
(0.1M) by square wave voltammetry on the one hand with Pb (II) and on the other hand with Cd (II). Several ex-
perimentalconditionssuchasthecompositionofthecarbonclaypaste,theeffectofpreconcentrationtime,thesweepingspeed,
concentration effect, media pH, and interference ionic response to the electrochemical response of the working electrode were
examined.Itwasobservedthat,after5minutesofpreconcentration,detectionlimitsof0.15513 μmol·L
−1
and 0.24227 μmol·L
−1
were obtained for Pb
2+
andCd
2+
in the electrolyte solution and 0.08438 μmol·L
−1
and 0.46522 μmol·L
−1
, respectively, when tap
waterwasused.edetectionwaseffectivebysquarewavevoltammetrywithamoreintensecurrentdensitywithrespecttolead.
1.Introduction
Heavy metals are used in many areas of life, but excessive
anduncontrolledusecanbeharmfultotheenvironmentand
to human health [1]. e presence of these heavy metals in
aquatic environments results from natural and anthropo-
genicactivities[2].Excessiveanduncontrolleduseofheavy
metals can increase their concentration even in drinking
water and could be harmful to living organisms. Prolonged
exposure even to low doses of lead (Pb
2+
) and cadmium
(Cd
2+
) ions by inhalation or ingestion can cause acute and
chronic nuisances such as decrease in hemoglobin level,
headache, nausea, dizziness, vomiting, constipation or di-
arrhea, breathing difficulties, haematuria, gastrointestinal
haemorrhage,acutehepaticfailure,cardiovasculardisorder,
neurotoxic effect (in children), abdominal cramps, and
impact on the immune system [3, 4].
isrequiresincreasedandreal-timemonitoringwitha
view to either reducing their presence in drinking water or
completeremoval.Severaltechniquesforanalyzingtracesof
heavymetalsinwaterhavebeenused,amongotherswhich
are IC (ion chromatography), ICP-AES (atomic emission
spectroscopy coupled with inductive plasma), AAS (atomic
absorption spectroscopy), and ICP-MS (mass spectroscopy
coupled with an inductive plasma) [5–7]. ese techniques
certainlygiveconvincingresults,butAAS,forexample,isa
destructivemethod,limitedjusttochemicalelementsinthe
atomicstate;inaddition,theelementtobeanalyzedmustbe
knowninadvance,anditsconcentrationmustbeatthetrace
scale at the risk of damaging the machine [8]. In addition,
ICP-MSandICP-AEShavethedrawbackofpretreatingthe
samples before analysis and with very expensive equipment
maintenance cost [9, 10]. Under another prism, the rapid
reaction,thegreatsensitivity,andtheportabilityrelatingto
Hindawi
Journal of Analytical Methods in Chemistry
Volume 2022, Article ID 6900839, 9 pages
https://doi.org/10.1155/2022/6900839