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
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.