Véronique Lenoble

Dr. Véronique Lenoble

Université de Toulon, MIO, UMR CNRS 7294, CS 60584 83041 TOULON CEDEX 9
orcid

Research Focus & Metrics

Academic Career Length

25Years (2002-Present)

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

Representative Publications

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1 November 2002 in Journal of Colloid and Interface Science
Verified
Journal Article
Closed access
Véronique LenobleVéronique Lenoble
Véronique Lenoble
OBOmar Bouras
Omar Bouras
VDVéronique Deluchat
Véronique Deluchat
BSBernard Serpaud
Bernard Serpaud
JBJean-Claude Bollinger
Jean-Claude Bollinger

4 November 2003 in Talanta
Verified
Journal Article
Closed access
Véronique LenobleVéronique Lenoble
Véronique Lenoble
VDVéronique Deluchat
Véronique Deluchat
BSBernard Serpaud
Bernard Serpaud
JBJean-Claude Bollinger
Jean-Claude Bollinger

1 October 2011 in Marine Pollution Bulletin
Verified
Journal Article
Closed access
ETErwan Tessier
Erwan Tessier
CGCédric Garnier
Cédric Garnier
JMJean-Ulrich Mullot
Jean-Ulrich Mullot
Véronique LenobleVéronique Lenoble
Véronique Lenoble
MAMireille Arnaud
Mireille Arnaud
SMStéphane MOUNIER
Stéphane MOUNIER

6 February 2020 in Environmental Science and Pollution Research
Verified
Journal Article
Open access
PDF file
Laura CutroneoLaura Cutroneo
Laura Cutroneo
ARAnna Reboa
Anna Reboa
Giovanni BesioGiovanni Besio
Giovanni Besio
FBFranco Borgogno
Franco Borgogno
LCLaura Canesi
Laura Canesi
MCMarco Capello
Marco Capello
The European Interreg Italy–France 2014–2020 Maritime Project SPlasH! (Stop to Plastics in H2O!) focused on the study of microplastics (MPs) in the marine port environment to evaluate their presence, abundance, and mechanisms of diffusion to the open sea. In the framework of this project, a worldwide review of 74 studies was carried out, providing an overview of MP investigation techniques, focusing on sampling strategies, laboratory methodologies, and identification of MPs collected in seawater, and specifically evaluating their applicability to the marine port environment. Nets were the most commonly used device for MP surface sampling, but their use can be difficult in narrow spaces within the port basins, and they must be coupled to discrete sampling devices to cover all port basins. In the laboratory, density separation (NaCl, ZnCl2, NaI, sodium lauryl sulfate (SLS)), filtration (polycarbonate, polyamide, glass, cellulose, ANOPORE inorganic membrane filters), sieving, visual sorting, and digestion methods (acidic, enzymatic, alkaline, oxidative) were used to separate MPs from seawater. Digestion becomes essential with water samples with great inorganic and organic loads as deriving from a port. Although many studies are based only on visual MP identification under a microscope, analytical identification techniques unequivocally determine the particle nature and the identity of the plastic polymers and are necessary to validate the visual sorting of MPs. Fourier-transform infrared spectroscopy (FTIR) is the most used analytical identification technique.

1 June 2004 in Science of The Total Environment
Verified
Journal Article
Closed access
Véronique LenobleVéronique Lenoble
Véronique Lenoble
CLChristelle Laclautre
Christelle Laclautre
BSBernard Serpaud
Bernard Serpaud
VDVéronique Deluchat
Véronique Deluchat
JBJean-Claude Bollinger
Jean-Claude Bollinger

1 August 2005 in Journal of Hazardous Materials
Verified
Journal Article
Closed access
Véronique LenobleVéronique Lenoble
Véronique Lenoble
CLChristelle Laclautre
Christelle Laclautre
VDVéronique Deluchat
Véronique Deluchat
BSBernard Serpaud
Bernard Serpaud
JBJean-Claude Bollinger
Jean-Claude Bollinger