2002
DOI: 10.1016/s0043-1354(01)00506-1
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Fenton and photo-Fenton oxidation of textile effluents

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Cited by 384 publications
(194 citation statements)
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“…This is attributed to the lower pH (3.0) and higher temperature (30°C) in the previous study. Under these conditions, the rate of the Fenton reaction is known to be higher (Pérez et al 2002;Jung et al 2009). Modification with DMDHEU and GA reduced the ML during the exposure to Fenton reagent; the increasing WPGs of the treated veneers further reduced the ML (Figure 3a,b).…”
Section: Colour Change and MLmentioning
confidence: 99%
“…This is attributed to the lower pH (3.0) and higher temperature (30°C) in the previous study. Under these conditions, the rate of the Fenton reaction is known to be higher (Pérez et al 2002;Jung et al 2009). Modification with DMDHEU and GA reduced the ML during the exposure to Fenton reagent; the increasing WPGs of the treated veneers further reduced the ML (Figure 3a,b).…”
Section: Colour Change and MLmentioning
confidence: 99%
“…Among these new technologies, advanced oxidation processes (AOP) are potentially the most promising due to their high efficiency and versatility. Thus, a variety of classes of compounds can be completely mineralized by existing AOP, including compounds refractory to conventional biological treatment processes (Kiwi et al, 2000;Pérez et al, 2002;Pignatello et al, 2006).…”
Section: Introductionmentioning
confidence: 99%
“…Several applications of Fenton and Photo-fenton processes have been reported, such as treatment of textile wastewaters (Pérez et al, 2002), reduction of Polynuclear Aromatic Hydrocarbons (PAH) in water (Beltran et al, 1998), removal of Adsorbable Organic Halogens (AOX) from pharmaceutical wastewater (Holf et al, 1997), treatment of paper pulp manufacturing effluents (Pérez et al, 2002), and others.…”
Section: Introductionmentioning
confidence: 99%