“…For this reason, the use of some triazine pesticides has been banned in some countries or their permitted levels in drinking water is very low, so that analytical procedures for quantitative determination of several triazines, as well as their degradation products, at low levels are often requested. In this sense, several analytical techniques have been developed, like HPLC (Katsumata et al, 2006), CG-MS, capillary electrophoresis (Frías et al, 2004), solid-phase micro-extraction coupling with GC, LC, ion mobility spectrometry (Garcia Galan et al, 2010;Mohammadi et al, 2009;Sanchez Ortega et al, 2009;Quintana et al, 2001) and with HPLC (Zhou et al, 230 2009;See et al, 2010), immunosensors (Bahnd et al, 2005) and multi-biosensor based on immobilized Photosystem II (Touloupakisa et al, 2005;Dong et al, 2009), micellar electrokinetic chromatography (Zhang et al, 2008), tandem techniques (Beale et al, 2009;Tsang et al,2009;Lacina et al, 2010) cyclic voltammetry (Fuchiwaki et al, 2009;Zapardiel et al, 2000) and differential-pulse polarography (Ignjatovic et al, 1993;Kubo et al, 2008;Vaz et al, 1996) on solid electrodes, photosynthetic electron transport (PET) electrochemical biosensors (Campàs, et al, 2008;Preuss & Hall, 1995), PET colorimetric detection (Brewster & Lightfield, 1993;Shao et al, 2002) and adsorptive stripping voltammetry in dispersed media (Pedredo et al, 1995). In the last years, the environmental pollution by pesticides has become in a serious problem especially in aquatic ecosystems, due to their heavy use in agriculture and to their persistence.…”