10 research outputs found

    Increasing hexokinase 1 expression improves mitochondrial and glycolytic functional deficits seen in sporadic Alzheimer’s disease astrocytes

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    Abnormalities in cellular metabolism are seen early in Alzheimer’s disease (AD). Astrocyte support for neuronal function has a high metabolic demand, and astrocyte glucose metabolism plays a key role in encoding memory. This indicates that astrocyte metabolic dysfunction might be an early event in the development of AD. In this paper we interrogate glycolytic and mitochondrial functional changes and mitochondrial structural alterations in patients’ astrocytes derived with a highly efficient direct conversion protocol. In astrocytes derived from patients with sporadic (sAD) and familial AD (fAD) we identified reductions in extracellular lactate, total cellular ATP and an increase in mitochondrial reactive oxygen species. sAD and fAD astrocytes displayed significant reductions in mitochondrial spare respiratory capacity, have altered mitochondrial membrane potential and a stressed mitochondrial network. A reduction in glycolytic reserve and glycolytic capacity is seen. Interestingly, glycolytic reserve, mitochondrial spare respiratory capacity and extracellular lactate levels correlated positively with neuropsychological tests of episodic memory affected early in AD. We identified a deficit in the glycolytic enzyme hexokinase 1 (HK1), and correcting this deficit improved the metabolic phenotype in sAD not fAD astrocytes. Importantly, the amount of HK1 at the mitochondria was shown to be reduced in sAD astrocytes, and not in fAD astrocytes. Overexpression of HK1 in sAD astrocytes increases mitochondrial HK1 levels. In fAD astrocytes HK1 levels were unaltered at the mitochondria after overexpression. This study highlights a clear metabolic deficit in AD patient-derived astrocytes and indicates how HK1, with its roles in both oxidative phosphorylation and glycolysis, contributes to this

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

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    none32noneP. Bruno; M. Caselli; P. R. Dambruoso; B. E. Daresta; G. de Gennaro; C. M. Placentino; M. Tutino; D. Baldacci; M.Stracquadanio; L. Tositti; S. Zappoli; D. Gullotto; V. Librando; Z.Minniti; G. Perrini; G. Trincali; S. Becagli; A. Mannini; R. Udisti; E.Bolzacchini; L. Ferrero; C. Lo Porto; M. G. Perrone; C. Paradisi;A. Tapparo; P. Barbieri; L. Capriglia; F.Cozzi; E. Maran; E.Reisenhofer; V. Sicardi. P.Fermo; A. PiazzalungaP. Bruno; M. Caselli; P. R. Dambruoso; B. E. Daresta; G. de Gennaro; C. M. Placentino; M. Tutino; D. Baldacci; M.Stracquadanio; L. Tositti; S. Zappoli; D. Gullotto; V. Librando; Z.Minniti; G. Perrini; G. Trincali; S. Becagli; A. Mannini; R. Udisti; E.Bolzacchini; L. Ferrero; C. Lo Porto; M. G. Perrone; C. Paradisi;A. Tapparo; P. Barbieri; L. Capriglia; F.Cozzi; E. Maran; E.Reisenhofer; V. Sicardi. P.Fermo; A. Piazzalung

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

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    In order to studying the concentration and the chemical characterization of atmospheric particulate in the different season in all the Italian territory, inside the SITECOS project (PRIN 2004), a gravimetric sampling campaigns have been conducted. The PM10 and PM2.5 samplings were placed at the same time in different sites along the Italian peninsula. The sampling sites were: Bari, Taranto, Pollino (m.1800, remote site), Catania, Sesto Fiorentino, Florence, Arezzo, Grosseto, Capannori-LU, Prato, Montale-PT (rural site), Bologna and Monte Cimone (m.2100, remote site on Italian Apennines), Padua, Milan, San Colombano (m.2300, remote site on Italian Alps), Trieste and San Rocco a Muggia (TS). Daily PM2.5 and PM10 samples have been collected, to do a \u201csampling bank \u201c, available for a further chemical / physical / toxicological characterization of atmospheric particulate Samples have been chemically characterized according to their main species: PAHs, inorganic ions and EC/OC in the PM2.5 samples; elements in the PM10 samples. In the Padana plain (Milan, Bologna, Padua) the PM concentration is uniform and a strong seasonal trend is observed, with the highest values in winter time and the lowest values in summer while PM concentration in S. Colombano and Monte Cimone sites show an opposite seasonality, with the highest values in summer and the lowest ones in winter. These data show a slight evolution during the winter\u2019s day because of the height of the dispersion layer, in connection with microclimatic parameters; for example in Milan city during acute cases of pollution, the height is no more that 300m (Ferrero et al., 2006). Remote sites of S. Colombano and Monte Cimone in the winter time are above the boundary layer while during summer period they are on it. In the center of Italy PM seasonality concentration is less important while in the South Italy and in Sicily there is any seasonal trend. The reasons are, in part, linked to the different meteoclimatic features present in the Italian peninsula. Chemical composition data show a significant differences. In the North of Italy there is a strong seasonality of ionic component; in particular, during the winter, the Nitrate concentration is higher than the Sulfate one while the situation is opposed in summer. Ammonium does not show a strong seasonality, but it remains pretty constant; the same applies to Carbon. In the South of Italy cities, SO , NO 3 - and NH 4 + , primary component of inorganic ions, they do not show a seasonality with a Sulfate concentration that is always higher than Nitrates. In the center of Italy the seasonality is less marked thanks to the inorganic ions. Sulfate and Nitrate are similar from a percentage point of view. Also PAHs (expressed in weight/weight, quality of particulate), in the Padana plain, shows a strong seasonality, with a high percentage in the winter season and a lower one in summer (Ravindra et al., 2006). Over the year concentrations are constant in South of Italy, while in the center area, the seasonality is less strong. The vehicles traffic source is estimated to be one of the main PM source in the Padana plain, while in the South of Italy there are other sources like photochemistry reactivity, Saharan Dust events, etc. These results show a different role of PM sources along the Italian peninsula and they carry fundamental information for a correct management of the complex problem on a national scale. Ferrero, L., Lazzati, Z., Lo Porto, C., Perrone, M.G., Petraccone, S., Sangiorgi, G., Bolzacchini, E., (2006) Vertical distribution of particulate matter in the urban atmosphere of Milan. Poster. International Aerosol Conference 2006. Ravindra, K., Bencs, L., Wauters, E., Hoog, J., Deutsch, F., Roekens, E., Bleux, N., Berghmans, P., Van Grieken, R., (2006) Seasonal and sitespecific variation in vapour and aerosol phase PAHs over Flanders (Belgium) and their relation with anthropogenic activities. Atmospheric Environment 40 (2006) 771-785

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

    No full text
    In order to studying the concentration and the chemical characterization of atmospheric particulate in the different season in all the Italian territory, inside the SITECOS project (PRIN 2004), a gravimetric sampling campaigns have been conducted. The PM10 and PM2.5 samplings were placed at the same time in different sites along the Italian peninsula. The sampling sites were: Bari, Taranto, Pollino (m.1800, remote site), Catania, Sesto Fiorentino, Florence, Arezzo, Grosseto, Capannori-LU, Prato, Montale-PT (rural site), Bologna and Monte Cimone (m.2100, remote site on Italian Apennines), Padua, Milan, San Colombano (m.2300, remote site on Italian Alps), Trieste and San Rocco a Muggia (TS). Daily PM2.5 and PM10 samples have been collected, to do a \u201csampling bank \u201c, available for a further chemical / physical / toxicological characterization of atmospheric particulate Samples have been chemically characterized according to their main species: PAHs, inorganic ions and EC/OC in the PM2.5 samples; elements in the PM10 samples. In the Padana plain (Milan, Bologna, Padua) the PM concentration is uniform and a strong seasonal trend is observed, with the highest values in winter time and the lowest values in summer while PM concentration in S. Colombano and Monte Cimone sites show an opposite seasonality, with the highest values in summer and the lowest ones in winter. These data show a slight evolution during the winter\u2019s day because of the height of the dispersion layer, in connection with microclimatic parameters; for example in Milan city during acute cases of pollution, the height is no more that 300m (Ferrero et al., 2006). Remote sites of S. Colombano and Monte Cimone in the winter time are above the boundary layer while during summer period they are on it. In the center of Italy PM seasonality concentration is less important while in the South Italy and in Sicily there is any seasonal trend. The reasons are, in part, linked to the different meteoclimatic features present in the Italian peninsula. Chemical composition data show a significant differences. In the North of Italy there is a strong seasonality of ionic component; in particular, during the winter, the Nitrate concentration is higher than the Sulfate one while the situation is opposed in summer. Ammonium does not show a strong seasonality, but it remains pretty constant; the same applies to Carbon. In the South of Italy cities, SO , NO 3 - and NH 4 + , primary component of inorganic ions, they do not show a seasonality with a Sulfate concentration that is always higher than Nitrates. In the center of Italy the seasonality is less marked thanks to the inorganic ions. Sulfate and Nitrate are similar from a percentage point of view. Also PAHs (expressed in weight/weight, quality of particulate), in the Padana plain, shows a strong seasonality, with a high percentage in the winter season and a lower one in summer (Ravindra et al., 2006). Over the year concentrations are constant in South of Italy, while in the center area, the seasonality is less strong. The vehicles traffic source is estimated to be one of the main PM source in the Padana plain, while in the South of Italy there are other sources like photochemistry reactivity, Saharan Dust events, etc. These results show a different role of PM sources along the Italian peninsula and they carry fundamental information for a correct management of the complex problem on a national scale. Ferrero, L., Lazzati, Z., Lo Porto, C., Perrone, M.G., Petraccone, S., Sangiorgi, G., Bolzacchini, E., (2006) Vertical distribution of particulate matter in the urban atmosphere of Milan. Poster. International Aerosol Conference 2006. Ravindra, K., Bencs, L., Wauters, E., Hoog, J., Deutsch, F., Roekens, E., Bleux, N., Berghmans, P., Van Grieken, R., (2006) Seasonal and sitespecific variation in vapour and aerosol phase PAHs over Flanders (Belgium) and their relation with anthropogenic activities. Atmospheric Environment 40 (2006) 771-785
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