Sonolytic, photolytic, and photocatalytic decomposition of atrazine in thepresence of polyoxometalates

Citation
A. Hiskia et al., Sonolytic, photolytic, and photocatalytic decomposition of atrazine in thepresence of polyoxometalates, ENV SCI TEC, 35(11), 2001, pp. 2358-2364
Citations number
46
Categorie Soggetti
Environment/Ecology,"Environmental Engineering & Energy
Journal title
ENVIRONMENTAL SCIENCE & TECHNOLOGY
ISSN journal
0013936X → ACNP
Volume
35
Issue
11
Year of publication
2001
Pages
2358 - 2364
Database
ISI
SICI code
0013-936X(20010601)35:11<2358:SPAPDO>2.0.ZU;2-U
Abstract
Aqueous solutions of atrazine [2-chloro-4-(isopropylamino)-6-(ethylamino)-s -triazine] (CIET) decompose upon illumination with a low-pressure Hg-arc la mp (254 nm). However, no decomposition takes place with lambda > 300 nm. On the other hand, addition of polyoxometalates (POM), PW12O403- or SiW12O404 - into a solution of atrazine photodecomposes the substrate within a few mi nutes (cutoff flter 320 nm). Ultrasound (US) treatment also decomposes aque ous solutions of atrazine within a few minutes. Both methods, sonolysis and photolysis with POM, give common intermediates, namely, 2-hydroxy-4-(isopr opylamino)-6-(ethylamino)-s-triazine (OIET), 2-chloro-4-(isopropylamino)-6- amino-s-triazine (CIAT), 2-cholro-4-amino-6-(ethylamino)-striazine (CAET), 2-hydroxy-4,6-diamino-s-triazine (OAAT), and 2-hydroxy-4-hydroxy-6-amino-s- triazine (OOAT) among others. The final products for both methods, US and p hotolysis with POM, were cyanuric acid (OOOT), NO3-, Cl-, CO2 and H2O. OOOT showed no signs of decomposition by sonication and/or photolysis with POM. It also resisted degradation upon photolysis with plain UV light (254 nm). However, it has been reported to decompose upon photolysis with lambda > 2 00 nm. Combination of US and photolysis with POM produces only a cumulative effect.