Salvatore Barreca

Dr. Salvatore Barreca

ARPA Lombardia, UOC Lab Milano, Sede Lab Monza & Brianza, Via Solferino 16, I-20900 Monza, MB, Italy
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Research Focus & Metrics

Academic Career Length

14Years (2013-Present)

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

Representative Publications

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1 February 2018 in Marine Pollution Bulletin
Verified
Journal Article
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DSDario Savoca
Dario Savoca
MAMarco Arculeo
Marco Arculeo
Salvatore BarrecaSalvatore Barreca
Salvatore Barreca
SBSilvestre Buscemi
Silvestre Buscemi
SCSanto Caracappa
Santo Caracappa
Andrea PaceAndrea Pace
Andrea Pace

1 May 2014 in Journal of Photochemistry and Photobiology A: Chemistry
Verified
Journal Article
Closed access
Salvatore BarrecaSalvatore Barreca
Salvatore Barreca
JCJulia Janeth Velez Colmenares
Julia Janeth Velez Colmenares
Andrea PaceAndrea Pace
Andrea Pace
SOSantino Orecchio
Santino Orecchio
CPCesar Pulgarin
Cesar Pulgarin

27 June 2013 in Environmental Geochemistry and Health
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Journal Article
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SOSantino Orecchio
Santino Orecchio
RIRoberta Indelicato
Roberta Indelicato
Salvatore BarrecaSalvatore Barreca
Salvatore Barreca
In this work, phthalic acid esters (PAEs): dimethyl phthalate (DMP), diethyl phthalate (DEP), di-n-butyl phthalate, benzyl butyl phthalate, bis(2-ethylhexyl) phthalate, and di-n-octyl phthalate in indoor dust (used as passive sampler) were investigated. The settled dust samples were collected from thirteen indoor environments from Palermo city. A fast and simple method using Soxhlet and GC–MS analysis has been optimized to identify and quantify the phthalates. Total phthalates concentrations in indoor dusts ranged from 269 to 4,831 mg/kg d.w. (d.w. = dry weight). The data show a linear correlation between total PAEs concentration and a single compound content, with the exclusion of the two most volatile components (DMP and DEP) that are present in appreciable amounts only in two samples. These results suggest that most of the PAEs identified in the samples of settled dust originate from the same type of material. This evidence indicates that, in a specific indoor environment, generally is not present only one compound but a mixture having over time comparable percentages of PAEs. Consequently, for routine analyses of a specific indoor environment, only a smaller number of compounds could be determined to value the contamination of that environment. We also note differences in phthalate concentrations between buildings from different construction periods; the total concentration of PAEs was higher in ancient homes compared to those constructed later. This is due to a trend to reduce or remove certain hazardous compounds from building materials and consumer goods. A linear correlation between total PAEs concentration and age of the building was observed (R = 0.71).


28 August 2018 in Journal of Chemistry
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Journal Article
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Salvatore BarrecaSalvatore Barreca
Salvatore Barreca
MBMaddalena Busetto
Maddalena Busetto
MVMatteo Vitelli
Matteo Vitelli
LCLuisa Colzani
Luisa Colzani
LCLaura Clerici
Laura Clerici
PDPierluisa Dellavedova
Pierluisa Dellavedova
In this research paper, we report a method able to detect perfluorinated compound at pg·L−1 levels in superficial and underground water samples. An online solid phase extraction HPLC-MS/MS method was developed for the analysis of 12 perfluoroalkyl acids (PFASs). The method is based on injection of 5000 µL of water sample in SPE online WAX column followed by chromatography separation and mass spectrometry determination. SPE online elution was performed by water + 0.05% NH4OH and methanol + 0.05% NH4OH, while separation of target compounds was achieved within 10 min by Gemini chromatographic column operating from 1 to 12 pH range and using a mixture of water-methanol + 0.05% NH4OH. Sub ng·L−1 method detection limits (from 0.2 to 5 ng·L−1), linearity (from 0.2 to 250 ng·L−1), accuracy (from 80 to 120%), and precision (RSD less than 15% at LOQs levels) were achieved. The method is capable of measuring PFAS at trace levels, but above all it can reach the limit of 200 pg·L−1 required by European regulation for PFOS determination in surface and underground waters. The method was validated for quantitative analysis of PFASs in real water samples.