Manuela Hidalgo

Dr. Manuela Hidalgo

orcid

Research Focus & Metrics

Academic Career Length

38Years (1989-Present)

(Calculated once Scilit publication data is synced: current year − year of first publication + 1)

Representative Publications

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1 March 2009 in TrAC Trends in Analytical Chemistry
Verified
Journal Article
Closed access
EMEva Marguí
Eva Marguí
Ignasi QueraltIgnasi Queralt
Ignasi Queralt
MHManuela Hidalgo
Manuela Hidalgo

1 September 2006 in Journal of Colloid and Interface Science
Verified
Journal Article
Closed access
AUAbdusalam Uheida
Abdusalam Uheida
MIMònica Iglesias
Mònica Iglesias
Clàudia FontàsClàudia Fontàs
Clàudia Fontàs
MHManuela Hidalgo
Manuela Hidalgo
VSVictoria Salvado
Victoria Salvado
MMMamoun Muhammed
Mamoun Muhammed


1 October 2004 in Analytica Chimica Acta
Verified
Journal Article
Closed access
EME. Marguı́
E. Marguı́
VSVictoria Salvado
Victoria Salvado
Ignasi QueraltIgnasi Queralt
Ignasi Queralt
MHManuela Hidalgo
Manuela Hidalgo

14 March 2013 in Journal of Analytical Atomic Spectrometry
Verified
Journal Article
Closed access
PDF file
KKKarina Kocot
Karina Kocot
BZBeata Zawisza
Beata Zawisza
EMEva Marguí
Eva Marguí
Ignasi QueraltIgnasi Queralt
Ignasi Queralt
MHManuela Hidalgo
Manuela Hidalgo
RSRafal Sitko
Rafal Sitko
In this paper the combination of dispersive micro solid-phase extraction (DMSPE), using multiwalled carbon nanotubes (MWCNTs) as solid sorbents, with total-reflection X-ray fluorescence spectrometry (TXRF) is proposed for preconcentration and determination of lead and cadmium ions in water samples. The proposed sample preparation is quite simple and economic. After the sorption processes of the metals on the MWCNTs, the aqueous sample is separated by centrifugation and the metal loaded MWCNTs are suspended using a small volume of an internal standard solution and analyzed directly by TXRF. Parameters affecting the extraction process (complexing agent, pH of the aqueous sample, amount of MWCNTs) and TXRF analysis (volume of the deposited suspension on the reflector, drying mode, and instrumental parameters) have been carefully evaluated to test the real capability of the developed methodology for the determination of Cd and Pb at trace levels. For both elements the linear range is observed up to 50 ng mL−1. Under optimized conditions detection limits are 1.0 ng mL−1 and 2.1 ng mL−1 for Cd(II) and Pb(II) ions, respectively. Both of the examined elements can be determined with quantitative recoveries (ca. 100%) and with an adequate precision (RSD = 6.0% and 10.5% for Cd(II) and Pb(II), respectively). Our results give insight into the possibilities of the combination of DMSPE and TXRF for trace metal determination in different types of environmental waters (sea, river and waste water).