Photochemical transformation of atrazine and formation of photointermediates under conditions relevant to sunlit surface waters: Laboratory measures and modelling

2013 ◽  
Vol 47 (16) ◽  
pp. 6211-6222 ◽  
Author(s):  
Giulia Marchetti ◽  
Marco Minella ◽  
Valter Maurino ◽  
Claudio Minero ◽  
Davide Vione
2016 ◽  
Vol 88 ◽  
pp. 235-244 ◽  
Author(s):  
P. Calza ◽  
D. Vione ◽  
F. Galli ◽  
D. Fabbri ◽  
F. Dal Bello ◽  
...  

2016 ◽  
Vol 566-567 ◽  
pp. 712-721 ◽  
Author(s):  
Angelica Bianco ◽  
Debora Fabbri ◽  
Marco Minella ◽  
Marcello Brigante ◽  
Gilles Mailhot ◽  
...  

2014 ◽  
Vol 53 ◽  
pp. 235-248 ◽  
Author(s):  
Elisa De Laurentiis ◽  
Carsten Prasse ◽  
Thomas A. Ternes ◽  
Marco Minella ◽  
Valter Maurino ◽  
...  

Chemosphere ◽  
2016 ◽  
Vol 145 ◽  
pp. 277-283 ◽  
Author(s):  
Davide Vione ◽  
Elisa De Laurentiis ◽  
Silvia Berto ◽  
Claudio Minero ◽  
Arzu Hatipoglu ◽  
...  

2013 ◽  
Vol 47 (16) ◽  
pp. 6109-6121 ◽  
Author(s):  
Giulia Ruggeri ◽  
Giovanni Ghigo ◽  
Valter Maurino ◽  
Claudio Minero ◽  
Davide Vione

1985 ◽  
Vol 6 (2) ◽  
pp. 52-58 ◽  
Author(s):  
Susan T. Bagley

AbstractThe genus Klebsiella is seemingly ubiquitous in terms of its habitat associations. Klebsiella is a common opportunistic pathogen for humans and other animals, as well as being resident or transient flora (particularly in the gastrointestinal tract). Other habitats include sewage, drinking water, soils, surface waters, industrial effluents, and vegetation. Until recently, almost all these Klebsiella have been identified as one species, ie, K. pneumoniae. However, phenotypic and genotypic studies have shown that “K. pneumoniae” actually consists of at least four species, all with distinct characteristics and habitats. General habitat associations of Klebsiella species are as follows: K. pneumoniae—humans, animals, sewage, and polluted waters and soils; K. oxytoca—frequent association with most habitats; K. terrigena— unpolluted surface waters and soils, drinking water, and vegetation; K. planticola—sewage, polluted surface waters, soils, and vegetation; and K. ozaenae/K. rhinoscleromatis—infrequently detected (primarily with humans).


Author(s):  
James S. Webber

INTRODUCTION“Acid rain” and “acid deposition” are terms no longer confined to the lexicon of atmospheric scientists and 1imnologists. Public awareness of and concern over this phenomenon, particularly as it affects acid-sensitive regions of North America, have increased dramatically in the last five years. Temperate ecosystems are suffering from decreased pH caused by acid deposition. Human health may be directly affected by respirable sulfates and by the increased solubility of toxic trace metals in acidified waters. Even man's monuments are deteriorating as airborne acids etch metal and stone features.Sulfates account for about two thirds of airborne acids with wet and dry deposition contributing equally to acids reaching surface waters or ground. The industrial Midwest is widely assumed to be the source of most sulfates reaching the acid-sensitive Northeast since S02 emitted as a byproduct of coal combustion in the Midwest dwarfs S02 emitted from all sources in the Northeast.


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