Noguerol Arias Joan

Dr. Noguerol Arias Joan

orcid

Research Focus & Metrics

Academic Career Length

15Years (2012-Present)

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

Representative Publications

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5 June 2012 in Analytical Chemistry
Verified
Journal Article
Closed access
NJNoguerol Arias Joan
Noguerol Arias Joan
ARAngela Rodríguez-Abalde
Angela Rodríguez-Abalde
EREva Romero-Merino
Eva Romero-Merino
Xavier FlotatsXavier Flotats
Xavier Flotats

1 November 2013 in TrAC Trends in Analytical Chemistry
Verified
Journal Article
Closed access
FBFrancisco Raposo Bejines
Francisco Raposo Bejines
Rafael BorjaRafael Borja
Rafael Borja
JCJ.A. Cacho
J.A. Cacho
JMJ. Mumme
J. Mumme
Kaja OrupõldKaja Orupõld
Kaja Orupõld
VFV. Fernández-Cegrí
V. Fernández-Cegrí

1 September 2015 in Journal of Chromatography A
Verified
Journal Article
Open access
FBFrancisco Raposo Bejines
Francisco Raposo Bejines
Rafael BorjaRafael Borja
Rafael Borja
JCJesús A. Cacho
Jesús A. Cacho
JMJan Mumme
Jan Mumme
Angel F. MohedanoAngel F. Mohedano
Angel F. Mohedano
CSCecilia Sambusiti
Cecilia Sambusiti
The performance parameters of volatile fatty acids (VFAs) measurements were assessed for the first time by a multi-laboratory validation study among 13 laboratories. Two chromatographic techniques (GC and HPLC) and two quantification methods such as external and internal standard (ESTD/ISTD) were combined in three different methodologies GC/ESTD, HPLC/ESTD and GC/ISTD. Linearity evaluation of the calibration functions in a wide concentration range (10-1000mg/L) was carried out using different statistical parameters for the goodness of fit. Both chromatographic techniques were considered similarly accurate. The use of GC/ISTD, despite showing similar analytical performance to the other methodologies, can be considered useful for the harmonization of VFAs analytical methodology taking into account the normalization of slope values used for the calculation of VFAs concentrations. Acceptance criteria for VFAs performance parameters of the multi-laboratory validation study should be established as follows: (1) instrument precision (RSDINST≤1.5%); (2) linearity (R(2)≥0.998; RSDSENSITIVITY≤4%; REMAX≤8%; REAVER≤ 3%); (3) precision (RSD≤1.5%); (4) trueness (recovery of 97-103%); (5) LOD (≤3mg/L); and (6) LOQ (10mg/L).

1 August 2021 in Journal of Environmental Chemical Engineering
Verified
Journal Article
Closed access
Miriam CerrilloMiriam Cerrillo
Miriam Cerrillo
LBLaura Burgos
Laura Burgos
ESErnesto Serrano-Finetti
Ernesto Serrano-Finetti
VRVictor Riau
Victor Riau
NJNoguerol Arias Joan
Noguerol Arias Joan
ABAugust Bonmatí
August Bonmatí

1 March 2018 in Atmospheric Environment
Verified
Journal Article
Open access
MTMarta Torrellas
Marta Torrellas
LBLaura Burgos
Laura Burgos
LTLaura Tey
Laura Tey
NJNoguerol Arias Joan
Noguerol Arias Joan
VRVictor Riau
Victor Riau
August BonmatíAugust Bonmatí
August Bonmatí

15 November 2023 in Sustainability
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Journal Article
Open access
PDF file
MCMartina Cattaneo
Martina Cattaneo
CTCarlota Tayà
Carlota Tayà
LBLaura Burgos
Laura Burgos
LMLluis Morey
Lluis Morey
NJNoguerol Arias Joan
Noguerol Arias Joan
August BonmatíAugust Bonmatí
August Bonmatí
Emission quantification from the agricultural sector, and especially from livestock manure management, is relevant for assessing mitigation strategies and for inventory purposes. There are different direct techniques used to monitor emissions from quiescent surfaces. Common techniques include the closed static chamber and the open dynamic chamber. The aim of this study was to evaluate and compare different direct methods, two dynamic hoods and one static hood, for monitoring NH3 and greenhouse gas (GHG) emissions (N2O, CO2, and CH4) from different emission sources. These sources are ammonia solutions and different by-products of manure (compost, liquid fraction of digestate, and solid fraction of pig slurry). The use of dynamic hoods, despite their differences in size, operation, and applied air flux, presents comparable emission rates for all emissions and compounds assayed. These rates are always higher than those obtained using static hoods. Therefore, it can be concluded that the use of dynamic hoods is a valuable technique for refining the indirect estimation of emissions.