Ettore Guerriero

Dr. Ettore Guerriero

CNR-IIA (Istituto sull'Inquinamento Atmosferico), Monterotondo, Italy
orcid

Research Focus & Metrics

Academic Career Length

30Years (1997-Present)

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

Representative Publications

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1 December 2015 in Computers & Operations Research
Verified
Journal Article
Closed access
MGMichel Gendreau
Michel Gendreau
GGGianpaolo Ghiani
Gianpaolo Ghiani
EGEmanuela Guerriero
Emanuela Guerriero

30 January 1997 in Environmental Science & Technology
Verified
Journal Article
Closed access
Carlo CrescenziCarlo Crescenzi
Carlo Crescenzi
ACAntonio Di Corcia
Antonio Di Corcia
Ettore GuerrieroEttore Guerriero
Ettore Guerriero
RSRoberto Samperi
Roberto Samperi

1 November 2008 in Computers & Operations Research
Verified
Journal Article
Closed access
PBPatrizia Beraldi
Patrizia Beraldi
GGGianpaolo Ghiani
Gianpaolo Ghiani
AGAntonio Grieco
Antonio Grieco
EGEmanuela Guerriero
Emanuela Guerriero

22 June 2023 in Science of The Total Environment
Verified
Journal Article
Open access
BMBenedetta Giannelli Moneta
Benedetta Giannelli Moneta
MFMaria Luisa Feo
Maria Luisa Feo
MTMarco Torre
Marco Torre
PTPatrizio Tratzi
Patrizio Tratzi
SASara Elsa Aita
Sara Elsa Aita
VPValerio Paolini
Valerio Paolini
Wastewater treatment plants are known to be relevant input sources of per- and polyfluoroalkyl substances (PFAS) in the aquatic environment. This study aimed to investigate the occurrence, fate, and seasonal variability of twenty-five PFAS in four municipal wastewater treatment plants (WWTP A, B, C, and D) surrounding the city of Milan (Northern, Italy). Composite 24-h wastewater samples were collected in July and October 2021 and May and February 2022 from influents and effluents of the four WWTPs. PFAS were detected at concentrations ranging between 24.1 and 66.9 μg L-1 for influent and 13.4 and 107 μg L-1 for effluent wastewater samples. Perfluoropentanoic acid was the most abundant (1.91-30.0 μg L-1) in influent samples, whereas perfluorobutane sulfonic acid predominated (0.80-66.1 μg L-1) in effluent samples. In sludge, PFOA was detected in plant A at concentrations in the range of 96.6-165 ng kg-1 dw in primary sludge samples and 98.6-440 ng kg-1 dw in secondary treatment sludge samples. The removal efficiency of total PFAS varied between 6 % and 96 %. However, an increase of PFAS concentrations was observed from influents to effluents for plant D (during July and October), plant A (during October and May), and plant C (during May) indicating that biotransformation of PFAS precursors can occur during biological treatments. This was supported by the observed increase in concentrations of PFOA from primary to secondary treatment sludge samples in plant A. Moreover, the plant operating at shorter hydraulic retention times (plant D) showed lower removal efficiency (<45 %). Seasonal variation of PFAS in influent and effluent appears rather low and more likely due to pulse release instead of seasonal factors.

29 May 1997 in Environmental Science & Technology
Verified
Journal Article
Closed access
ACAntonio Di Corcia
Antonio Di Corcia
Carlo CrescenziCarlo Crescenzi
Carlo Crescenzi
Ettore GuerrieroEttore Guerriero
Ettore Guerriero
RSRoberto Samperi
Roberto Samperi

1 December 2014 in Urban Climate
Verified
Journal Article
Closed access
ACAngelo Cecinato
Angelo Cecinato
Ettore GuerrieroEttore Guerriero
Ettore Guerriero
CBCatia Balducci
Catia Balducci
VMValeria Muto
Valeria Muto