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187 results on '"Tositti, L"'

14. The nationwide dataset of PM chemical speciation of Italy: lighting-up the influence of local geographical differences on urban PM

Author

Pietrodangelo, A., Becagli, S., Bigi, A., Bove, M. C., Brattich, E., Caggiano, R., Calzolai, G., Canepari, S., Cappelletti, D., Cesari, D., Colombi, C., Contini, D., DE GENNARO, G., Ferrero, L., Gianelle, V., Iacobellis, S., Ielpo, P., Lucarelli, F., Masiol, M., Nava, S., Perrino, C., Perrone, M. G., Prati, P., Riccio, A., Tositti, L., Traversi, R., Venturini, E., and Vecchi, R.

Subjects
Settore GEO/08 - Geochimica e Vulcanologia
Published
2020

22. Aerosol concentration at two heights (2550 and 650 m a.s.l.) in SE Spain

Author

Gómez Cascales, P. J., García Orza, José Antonio, Ferro García, Mª Ángeles, Expósito Suárez, Víctor Manuel, Milena Pérez, Abel, Martínez Martínez, Bruna Raquel, Chham, Essaid, Piñero García, Francisco, Casquero Vera, Juan Andrés, Cazorla, Alberto, Alados Arboledas, Lucas, Olmo, F. J., Brattich, Erika, Tositti, L., Camacho, Antonia, Hernández-Ceballos, M. A., and Martiny, Nadege

Subjects
Concentration, Meteorology, Dust, Aerosol, Pollution
Abstract

Ponencia presentada en: XXXV Jornadas Científicas de la AME y el XIX Encuentro Hispano Luso de Meteorología celebrado en León, del 5 al 7 de marzo de 2018. The simultaneous aerosol sampling at two heights in southern Spain may provide valuable information on the vertical structure of the dust transport from North Africa to the Iberian Peninsula. It also allows the characterization of the ambient air at two sites with distinct anthropogenic impact. This work presents the results obtained from the first field campaign of the FRESA project (Impact of dust-laden African air masses and of stratospheric air masses in the Iberian Peninsula. Role of the Atlas Mountains), performed in the period July-November 2017 at El Albergue Universitario in Sierra Nevada (2550 m a.s.l.) and the city of Granada (650 m a.s.l.). The two sites were instrumented with a low-volume sampler with PM10 inlet for daily sampling and mass and chemical composition characterization, a high-volume sampler for total suspended particles (TSP) for weekly sampling and radionuclide activity determination, and with a GRIMM 365 optical particle counter that provides continuously the aerosol size distribution.

Published
2018

23. Indagine ambientale per la rilevazione di inquinanti atmosferici mediante modelli a recettore del distretto monfalconese (Procedimento nr. 1213/13 R.N.R.I. Procura della Repubblica di Gorizia)

Author

Tositti L., Brattich E., and Tositti L., Brattich E.

Subjects
PM10, sorgenti di emissione, speciazione chimica, modelli a recettore
Abstract

Risultati di una campagna di monitoraggio di gas e particolato atmosferico nell'area di Monfalcone - Studio del profilo delle sorgenti di emissione del distretto

Published
2016

28. Aerosol atmosferico alla stazioneWMO-GAW di Mt. Cimone (2165 m asl)

Author

Brattich E., Tositti L., Riccio A., Garcia-Orza J. A., and Brattich, E., Tositti, L., Riccio, A., Garcia-Orza, J.A.

Subjects
Monte Cimone, radionuclidi naturali, aerosol atmosferico, back-trajectorie
Abstract

Mt. Cimone (44°11′N, 10°42′E) è il picco più elevato degli Appenninisettentrionali, ed ospita una stazione globale WMO-GAW rappresentativa dellecondizioni di troposfera libera nella regione sud-europea/mediterranea, attualmenteidentificata come hot-spot in termini sia di cambiamento climatico che di qualitàdell’aria. A partire dal 1998 e fino al 2011, dati di aerosol atmosferico infrazione PM10 sono stati raccolti alla stazione tramite un campionatore ad altovolume. Dopo il campionamento, i filtri sono stati sottoposti a gravimetria e aspettrometria-γ ad alta risoluzione per la determinazione della massa sospesa e di7Be e 210Pb, radionuclidi naturali di origine contrastante (infatti il primo èoriginato in stratosfera/alta troposfera da reazioni nucleari di spallazione, mentreil secondo deriva dal decadimento di 222Rn di provenienza crostale). A Mt. Cimone, ilPM10 esibisce una forte fluttuazione stagionale con un minimo invernale ed un massimoestivo. L’influenza delle aree sorgente di PM10 viene discussa per confronto condati simultanei raccolti in stazioni di pianura a nord e a sud della catenaappenninica. In genere, il PM10 mostra un gradiente verticale negativo con la quota,con Mt. Cimone che rappresenta il valore medio minimo. Il confronto delle serietemporali di PM10 con quelle di densità numeriche di particelle fini e grossolane el’impiego di una tecnica statistica basata sulle retrotraiettorie rivelanol’influenza dei trasporti da regioni sorgente quali il Nord Africa, la PianuraPadana ed il continente europeo inclusa l’area balcanica. L’andamento stagionalee le aree sorgente di 210Pb, che con il PM10 ha in comune gran parte del terminesorgente (la crosta terrestre), sono risultati in gran parte confrontabili. Perentrambe le serie temporali, ed in analogia a quanto riscontrato per PM10 e PM2.5 inaltre stazioni remote europee, è stato identificato un trend in diminuzione la cuiorigine è attualmente oggetto di indagine da parte degli autori.

Published
2014

32. The effect on woods of a sterilisation process based on gamma rays

Author

Cancelliere, R, Mazzuca, C, Micheli, L, Carbone, M, Lettieri, R, Boancini, L, Prati, S, Sciutto, G, Mazzeo, R, Tositti, L, Ricci, G, Mostacci, D, Palleschi, A, and Palleschi, G

Subjects
Settore CHIM/03 - Chimica Generale e Inorganica, Settore CHIM/01 - Chimica Analitica, Settore CHIM/12 - Chimica dell'Ambiente e dei Beni Culturali, Settore CHIM/02 - Chimica Fisica
Published
2015

33. La composizione chimica del Particolato Atmosferico nella penisola Italiana, similitudini e analogie

Author

BOLZACCHINI, EZIO, FERRERO, LUCA, PERRONE, MARIA GRAZIA, PIAZZALUNGA, ANDREA, Lo Porto, C, de Gennaro, G, Bruno, P, Caselli, M, Dambruoso, PR, Daresta, BE, Placentino, CM, Tutino, M, Amodio, M, Baldacci, D, Stracquadanio, M, Tositti, L, Zappoli, S, Gullotto, D, Librando, V, Minniti, Z, Perrini, G, Trincali, G, Becagli, S, Mannini, A, Udisti, R, Paradisi, A, Tapparo, A, Barbieri, P, Capriglia, L, Cozzi, F, Maran, E, Reisenhofer, E, Sicardi, V, Fermo, P, Bolzacchini, E, Ferrero, L, Lo Porto, C, Perrone, M, de Gennaro, G, Bruno, P, Caselli, M, Dambruoso, P, Daresta, B, Placentino, C, Tutino, M, Amodio, M, Baldacci, D, Stracquadanio, M, Tositti, L, Zappoli, S, Gullotto, D, Librando, V, Minniti, Z, Perrini, G, Trincali, G, Becagli, S, Mannini, A, Udisti, R, Paradisi, A, Tapparo, A, Barbieri, P, Capriglia, L, Cozzi, F, Maran, E, Reisenhofer, E, Sicardi, V, Fermo, P, and Piazzalunga, A

Subjects
composizione chimica, particolato atmosferico, CHIM/12 - CHIMICA DELL'AMBIENTE E DEI BENI CULTURALI
Published
2006

36. Studio integrato sul territorio nazionale per la caratterizzazione ed il controllo di inquinanti atmosferici (SITECOS)

Author

Bruno, P, Caselli, M, Dambruoso, PR, Daresta, BE, De Gennaro, G, Placentino CM, Tutino, M, Baldacci, D, Sandrini, S, Tositti, L, Gullotto, D, Librando, V, Minniti, Z, Perrini, G, Tringali, G, Innocenti, M, Udisti, R, Grammatica, P, Marotta, R, Papa, E, Riccio, A, Campanella, L, Cardarelli, E, Dragone, R, Paradisi, C, Tapparo, A, Canepa, C, Rabezzana, R, Tonachini, G, Pierluigi, B, Capriglia, L, Cozzi, F, Maran, E, Reisenhofer, E, Sicardi, V, Benassi, A, Gianelle, V, Caramuscio, P, Giovannini, M., BOLZACCHINI, EZIO, FERRERO, LUCA, PERRONE, MARIA GRAZIA, Morselli, L, Bruno, P, Caselli, M, Dambruoso, P, Daresta, B, De Gennaro, G, Placentino, C, Tutino, M, Baldacci, D, Sandrini, S, Tositti, L, Gullotto, D, Librando, V, Minniti, Z, Perrini, G, Tringali, G, Innocenti, M, Udisti, R, Grammatica, P, Marotta, R, Papa, E, Bolzacchini, E, Ferrero, L, Perrone, M, Riccio, A, Campanella, L, Cardarelli, E, Dragone, R, Paradisi, C, Tapparo, A, Canepa, C, Rabezzana, R, Tonachini, G, Pierluigi, B, Capriglia, L, Cozzi, F, Maran, E, Reisenhofer, E, Sicardi, V, Benassi, A, Gianelle, V, Caramuscio, P, and Giovannini, M

Subjects
CHIM/12 - CHIMICA DELL'AMBIENTE E DEI BENI CULTURALI, inquinamento atmosferico, aree urbane, siti remoti, progetto SITECOS
Published
2005

41. Intercomparison of sampling and measurement of Be-7 in air at four high-altitude locations in Europe

Author

Tositti, L., Hübener, S., Kanter, H.-J., Ringer, W., Sandrini, S., and Tobler, L.

Subjects
Be-7, Gamma-spectrometry, Intercomparison, Aerosol
Abstract

For several years Be-7 measurements have been conducted at high-altitude stations in Austria (Sonnblick, 3106 m), Switzerland (Jungfraujoch, 3580 m), Germany (Zugspitze, 2962 m), and Italy (Mt. Cimone 2165 m) with the aim to support a study on vertical ozone transport in the Alps (VOTALP project). Aerosol samples, collected on filtering media with high volume samplers, are analysed for Be-7 by high-resolution gamma-spectrometry. Prior to evalution of the Be-7 time series of the four stations, both sampling and measurement procedures were cheked for comparibility. The results of an intercomparison exercise performed within the mentioned project are reported.

Published
2004

43. A climatology of 7Be at four high-altitude stations at the Alps and the Northern Apennines

Author

Gerasopoulos, E., Zanis, P., Stohl, A., Zerefos, C. S., Papastefanou, C., Ringer, W., Tobler, L., Hübener, S., Gäggeler, H. W., Kanter, H. J., Tositti, L., and Sandrini, S.

Subjects
7Be, Climatology, Surface ozone, Alps, Stratospheric intrusions
Abstract

The 7Be activity concentrations measured from 1996 to 1998 at four high-altitude stations, Jungfraujoch—Switzerland, Zugspitze—Germany, Sonnblick—Austria and Mt. Cimone—Italy, were analyzed in combination with a set of, meteorological and atmospheric parameters such as the tropopause height, relative and specific humidity and also in conjunction with 3D back-trajectories in order to investigate the climatological features of 7Be. A frequency distribution analysis on 7Be activity concentrations revealed the existence of two concentration classes around 1.5 and 6 mBq m−3 and a transition class between the two modes of the distribution at 3–4 mBq m−3. Cross-correlation analysis performed between 7Be and a number of meteorological and atmospheric parameters at the first three stations showed a strong negative correlation with relative humidity (−0.56, −0.51, −0.41) indicating the importance of wet scavenging as a controlling mechanism. Also, the positive correlation with the height of 3-days back-trajectories and tropopause height (+0.49/+0.43, +0.59/+0.36, +0.44/+0.38) shows that downward transport from the upper or middle to lower troposphere within anticyclonic conditions plays also an important role. Trajectory statistics showed that low 7Be concentrations typically originate from lower-altitude subtropical ocean areas, while high concentrations arrive from the north and high altitudes, as is characteristic for stratospheric intrusions. Although the 7Be activity concentrations are highly episodic, the monthly means indicate an annual cycle with a late-summer maximum at all stations. The correlation coefficients calculated for monthly means of the 7Be and atmospheric data suggest that the main predictor controlling the seasonality of the 7Be concentrations is tropopause height (+0.76, +0.56, +0.60), reflecting more vertical transport from upper tropospheric levels into the lower troposphere during the warm season than during the cold season.

Published
2001

45. Tracking of Airborne Radionuclides from the Damaged Fukushima Dai-Ichi Nuclear Reactors by European Networks

Author

Masson, O., Baeza, A., Bieringer, J., Brudecki, K., Bucci, S., Cappai, M., Carvalho, F.P., Connan, O., Cosma, C., Dalheimer, A., Didier, D., Depuydt, G., De Geer, L.E., De Vismes, A., Gini, L., Groppi, F., Gudnason, K., Gurriaran, R., Hainz, D., Halldórsson, Ó., Hammond, D., Hanley, O., Holeý, K., Homoki, Zs., Ioannidou, A., Isajenko, K., Jankovic, M., Katzlberger, C., Kettunen, M., Kierepko, R., Kontro, R., Kwakman, P.J.M., Lecomte, M., Leon Vintro, L., Leppänen, A.-P., Lind, B., Lujaniene, G., Mc Ginnity, P., Mahon, C. Mc, Malá, H., Manenti, S., Manolopoulou, M., Mattila, A., Mauring, A., Mietelski, J.W., Møller, B., Nielsen, Sven Poul, Nikolic, J., Overwater, R.M.W., Pálsson, S. E., Papastefanou, C., Penev, I., Pham, M.K., Povinec, P.P., Ramebäck, H., Reis, M.C., Ringer, W., Rodriguez, A., Rulík, P., Saey, P.R.J., Samsonov, V., Schlosser, C., Sgorbati, G., Silobritiene, B. V., Söderström, C., Sogni, R., Solier, L., Sonck, M., Steinhauser, G., Steinkopff, T., Steinmann, P., Stoulos, S., Sýkora, I., Todorovic, D., Tooloutalaie, N., Tositti, L., Tschiersch, J., Ugron, A., Vagena, E., Vargas, A., Wershofen, H., Zhukova, O., Masson, O., Baeza, A., Bieringer, J., Brudecki, K., Bucci, S., Cappai, M., Carvalho, F.P., Connan, O., Cosma, C., Dalheimer, A., Didier, D., Depuydt, G., De Geer, L.E., De Vismes, A., Gini, L., Groppi, F., Gudnason, K., Gurriaran, R., Hainz, D., Halldórsson, Ó., Hammond, D., Hanley, O., Holeý, K., Homoki, Zs., Ioannidou, A., Isajenko, K., Jankovic, M., Katzlberger, C., Kettunen, M., Kierepko, R., Kontro, R., Kwakman, P.J.M., Lecomte, M., Leon Vintro, L., Leppänen, A.-P., Lind, B., Lujaniene, G., Mc Ginnity, P., Mahon, C. Mc, Malá, H., Manenti, S., Manolopoulou, M., Mattila, A., Mauring, A., Mietelski, J.W., Møller, B., Nielsen, Sven Poul, Nikolic, J., Overwater, R.M.W., Pálsson, S. E., Papastefanou, C., Penev, I., Pham, M.K., Povinec, P.P., Ramebäck, H., Reis, M.C., Ringer, W., Rodriguez, A., Rulík, P., Saey, P.R.J., Samsonov, V., Schlosser, C., Sgorbati, G., Silobritiene, B. V., Söderström, C., Sogni, R., Solier, L., Sonck, M., Steinhauser, G., Steinkopff, T., Steinmann, P., Stoulos, S., Sýkora, I., Todorovic, D., Tooloutalaie, N., Tositti, L., Tschiersch, J., Ugron, A., Vagena, E., Vargas, A., Wershofen, H., and Zhukova, O.

Abstract

Radioactive emissions into the atmosphere from the damaged reactors of the Fukushima Dai-ichi nuclear power plant (NPP) started on March 12th, 2011. Among the various radionuclides released, iodine-131 (131I) and cesium isotopes (137Cs and 134Cs) were transported across the Pacific toward the North American continent and reached Europe despite dispersion and washout along the route of the contaminated air masses. In Europe, the first signs of the releases were detected 7 days later while the first peak of activity level was observed between March 28th and March 30th. Time variations over a 20-day period and spatial variations across more than 150 sampling locations in Europe made it possible to characterize the contaminated air masses. After the Chernobyl accident, only a few measurements of the gaseous 131I fraction were conducted compared to the number of measurements for the particulate fraction. Several studies had already pointed out the importance of the gaseous 131I and the large underestimation of the total 131I airborne activity level, and subsequent calculations of inhalation dose, if neglected. The measurements made across Europe following the releases from the Fukushima NPP reactors have provided a significant amount of new data on the ratio of the gaseous 131I fraction to total 131I, both on a spatial scale and its temporal variation. It can be pointed out that during the Fukushima event, the 134Cs to 137Cs ratio proved to be different from that observed after the Chernobyl accident. The data set provided in this paper is the most comprehensive survey of the main relevant airborne radionuclides from the Fukushima reactors, measured across Europe. A rough estimate of the total 131I inventory that has passed over Europe during this period was

Published
2011

46. Tracking of Airborne Radionuclides from the Damaged Fukushima Dai-Ichi Nuclear Reactors by European Networks

Author

Masson, Olivier, Baeza, A., Bieringer, Jacqueline, Brudecki, K., Bucci, S., Cappai, M., Carvalho, F. P., Connan, O., Cosma, C., Dalheimer, Axel, Didier, D., Depuydt, G., De Geer, L. E., De Vismes, Anne, Gini, L., Groppi, F., Gudnason, K., Gurriaran, R., Hainz, D., Halldorsson, O., Hammond, D., Hanley, O., Holey, K., Homoki, Zsolt, Ioannidou, A., Isajenko, Krzysztof A., Janković, Marija M., Katzlberger, Christian, Kettunen, M., Kierepko, Renata, Kontro, R., Kwakman, P. J. M., Lecomte, M., Vintro, L. Leon, Leppanen, A-P, Lind, B., Lujaniene, G., Mc Ginnity, P., Mc Mahon, C., Mala, Helena, Manenti, S., Manolopoulou, M., Mattila, A., Mauring, A., Mietelski, Jerzy W., Moller, Bredo, Nielsen, S. P., Krneta-Nikolić, Jelena D., Overwater, R. M. W., Palsson, S. E., Papastefanou, C., Penev, I., Pham, M. K., Povinec, Pavel Peter, Rameback, H., Reis, M. C., Ringer, Wolfgang, Rodriguez, A., Rulik, Petr, Saey, P. R. J., Samsonov, V., Schlosser, C., Sgorbati, G., Silobritiene, B. V., Soderstrom, C., Sogni, R., Solier, L., Sonck, M., Steinhauser, Georg, Steinkopff, Thomas, Steinmann, P., Stoulos, S., Sykora, Ivan, Todorović, Dragana, Tooloutalaie, N., Tositti, L., Tschiersch, Jochen, Ugron, A., Vagena, E., Vargas, A., Wershofen, Herbert, Zhukova, O., Masson, Olivier, Baeza, A., Bieringer, Jacqueline, Brudecki, K., Bucci, S., Cappai, M., Carvalho, F. P., Connan, O., Cosma, C., Dalheimer, Axel, Didier, D., Depuydt, G., De Geer, L. E., De Vismes, Anne, Gini, L., Groppi, F., Gudnason, K., Gurriaran, R., Hainz, D., Halldorsson, O., Hammond, D., Hanley, O., Holey, K., Homoki, Zsolt, Ioannidou, A., Isajenko, Krzysztof A., Janković, Marija M., Katzlberger, Christian, Kettunen, M., Kierepko, Renata, Kontro, R., Kwakman, P. J. M., Lecomte, M., Vintro, L. Leon, Leppanen, A-P, Lind, B., Lujaniene, G., Mc Ginnity, P., Mc Mahon, C., Mala, Helena, Manenti, S., Manolopoulou, M., Mattila, A., Mauring, A., Mietelski, Jerzy W., Moller, Bredo, Nielsen, S. P., Krneta-Nikolić, Jelena D., Overwater, R. M. W., Palsson, S. E., Papastefanou, C., Penev, I., Pham, M. K., Povinec, Pavel Peter, Rameback, H., Reis, M. C., Ringer, Wolfgang, Rodriguez, A., Rulik, Petr, Saey, P. R. J., Samsonov, V., Schlosser, C., Sgorbati, G., Silobritiene, B. V., Soderstrom, C., Sogni, R., Solier, L., Sonck, M., Steinhauser, Georg, Steinkopff, Thomas, Steinmann, P., Stoulos, S., Sykora, Ivan, Todorović, Dragana, Tooloutalaie, N., Tositti, L., Tschiersch, Jochen, Ugron, A., Vagena, E., Vargas, A., Wershofen, Herbert, and Zhukova, O.

Abstract

Radioactive emissions into the atmosphere from the damaged reactors of the Fukushima Dai-ichi nuclear power plant (NPP) started on March 12th, 2011. Among the various radionuclides released, iodine-131 ((131)I) and cesium isotopes ((137)Cs and (134)Cs) were transported across the Pacific toward the North American continent and reached Europe despite dispersion and washout along the route of the contaminated air masses. In Europe, the first signs of the releases were detected 7 days later while the first peak of activity level was observed between March 28th and March 30th. Time variations over a 20-day period and spatial variations across more than 150 sampling locations in Europe made it possible to characterize the contaminated air masses. After the Chernobyl accident, only a few measurements of the gaseous (131)I fraction were conducted compared to the number of measurements for the particulate fraction. Several studies had already pointed out the importance of the gaseous (131)I and the large underestimation of the total (131)I airborne activity level, and subsequent calculations of inhalation dose, if neglected. The measurements made across Europe following the releases from the Fukushima NPP reactors have provided a significant amount of new data on the ratio of the gaseous (131)I fraction to total (131)I, both on a spatial scale and its temporal variation. It can be pointed out that during the Fukushima event, the (134)Cs to (137)Cs ratio proved to be different from that observed after the Chernobyl accident. The data set provided in this paper is the most comprehensive survey of the main relevant airborne radionuclides from the Fukushima reactors, measured across Europe. A rough estimate of the total (131)I inventory that has passed over Europe during this period was LT 1% of the released amount. According to the measurements, airborne activity levels remain of no concern for public health in Europe.

Published
2011

48. Concentration and the chemical characterization of PM10 and PM2.5 in all the Italian territory

Author

Bolzacchini, E, Ferrero, L, Lo Porto, C, Perrone, M, de Gennaro, G, Bruno, P, Caselli, M, Dambruoso, P, Daresta, B, Placentino, C, Tutino, M, Amodio, M, Baldacci, D, Stracquadanio, M, Tositti, L, Zappoli, S, Gullotto, D, Librando, V, Minniti, Z, Perrini, G, Trincali, G, Becagli, S, Mannini, A, Udisti, R, Paradisi, A, Tapparo, A, Barbieri, P, Capriglia, L, Cozzi, F, Maran, E, Reisenhofer, E, Sicardi, V, Fermo, P, Piazzalunga, A, BOLZACCHINI, EZIO, FERRERO, LUCA, PERRONE, MARIA GRAZIA, PIAZZALUNGA, ANDREA, Dambruoso, P. R, Daresta, B. E, Placentino, C. M, Bolzacchini, E, Ferrero, L, Lo Porto, C, Perrone, M, de Gennaro, G, Bruno, P, Caselli, M, Dambruoso, P, Daresta, B, Placentino, C, Tutino, M, Amodio, M, Baldacci, D, Stracquadanio, M, Tositti, L, Zappoli, S, Gullotto, D, Librando, V, Minniti, Z, Perrini, G, Trincali, G, Becagli, S, Mannini, A, Udisti, R, Paradisi, A, Tapparo, A, Barbieri, P, Capriglia, L, Cozzi, F, Maran, E, Reisenhofer, E, Sicardi, V, Fermo, P, Piazzalunga, A, BOLZACCHINI, EZIO, FERRERO, LUCA, PERRONE, MARIA GRAZIA, PIAZZALUNGA, ANDREA, Dambruoso, P. R, Daresta, B. E, and Placentino, C. M

Published
2007

49. La composizione chimica del Particolato Atmosferico nella penisola Italiana, similitudini e analogie

Author

Bolzacchini, E, Ferrero, L, Lo Porto, C, Perrone, M, de Gennaro, G, Bruno, P, Caselli, M, Dambruoso, P, Daresta, B, Placentino, C, Tutino, M, Amodio, M, Baldacci, D, Stracquadanio, M, Tositti, L, Zappoli, S, Gullotto, D, Librando, V, Minniti, Z, Perrini, G, Trincali, G, Becagli, S, Mannini, A, Udisti, R, Paradisi, A, Tapparo, A, Barbieri, P, Capriglia, L, Cozzi, F, Maran, E, Reisenhofer, E, Sicardi, V, Fermo, P, Piazzalunga, A, BOLZACCHINI, EZIO, FERRERO, LUCA, PERRONE, MARIA GRAZIA, PIAZZALUNGA, ANDREA, Dambruoso, PR, Daresta, BE, Placentino, CM, Bolzacchini, E, Ferrero, L, Lo Porto, C, Perrone, M, de Gennaro, G, Bruno, P, Caselli, M, Dambruoso, P, Daresta, B, Placentino, C, Tutino, M, Amodio, M, Baldacci, D, Stracquadanio, M, Tositti, L, Zappoli, S, Gullotto, D, Librando, V, Minniti, Z, Perrini, G, Trincali, G, Becagli, S, Mannini, A, Udisti, R, Paradisi, A, Tapparo, A, Barbieri, P, Capriglia, L, Cozzi, F, Maran, E, Reisenhofer, E, Sicardi, V, Fermo, P, Piazzalunga, A, BOLZACCHINI, EZIO, FERRERO, LUCA, PERRONE, MARIA GRAZIA, PIAZZALUNGA, ANDREA, Dambruoso, PR, Daresta, BE, and Placentino, CM

Published
2006

50. Studio integrato sul territorio nazionale per la caratterizzazione ed il controllo di inquinanti atmosferici (SITECOS)

Author

Morselli, L, Bruno, P, Caselli, M, Dambruoso, P, Daresta, B, De Gennaro, G, Placentino, C, Tutino, M, Baldacci, D, Sandrini, S, Tositti, L, Gullotto, D, Librando, V, Minniti, Z, Perrini, G, Tringali, G, Innocenti, M, Udisti, R, Grammatica, P, Marotta, R, Papa, E, Bolzacchini, E, Ferrero, L, Perrone, M, Riccio, A, Campanella, L, Cardarelli, E, Dragone, R, Paradisi, C, Tapparo, A, Canepa, C, Rabezzana, R, Tonachini, G, Pierluigi, B, Capriglia, L, Cozzi, F, Maran, E, Reisenhofer, E, Sicardi, V, Benassi, A, Gianelle, V, Caramuscio, P, Giovannini, M, Dambruoso, PR, Daresta, BE, Placentino CM, Giovannini, M., BOLZACCHINI, EZIO, FERRERO, LUCA, PERRONE, MARIA GRAZIA, Morselli, L, Bruno, P, Caselli, M, Dambruoso, P, Daresta, B, De Gennaro, G, Placentino, C, Tutino, M, Baldacci, D, Sandrini, S, Tositti, L, Gullotto, D, Librando, V, Minniti, Z, Perrini, G, Tringali, G, Innocenti, M, Udisti, R, Grammatica, P, Marotta, R, Papa, E, Bolzacchini, E, Ferrero, L, Perrone, M, Riccio, A, Campanella, L, Cardarelli, E, Dragone, R, Paradisi, C, Tapparo, A, Canepa, C, Rabezzana, R, Tonachini, G, Pierluigi, B, Capriglia, L, Cozzi, F, Maran, E, Reisenhofer, E, Sicardi, V, Benassi, A, Gianelle, V, Caramuscio, P, Giovannini, M, Dambruoso, PR, Daresta, BE, Placentino CM, Giovannini, M., BOLZACCHINI, EZIO, FERRERO, LUCA, and PERRONE, MARIA GRAZIA

Published
2005

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