Landfill leachate contains a variety of contaminating substances organic and inorganic, dissolved and at suspension, such as humic and fulvic acids, xenobiotics, metals (Hg 2+ , Pb 2+ , Cd 2+ , Cu 2+ , Zn 2+ , Cr 3+ /Cr 6+) and ammoniacal nitrogen, which give it characteristics of low biodegradability, high organic load and toxicity. In the face of concern about the damages that this composition may cause to the environment and to animal and plant, the use and combination of new treatment technologies has a high research interest. In the first part of this work, interfering factors in the removal of dissolved organic carbon (DOC) of leachate by the photo-Fenton process, the coupling of treatments were evaluated. Firstly, the isolated application of the photo-Fenton process was employed, evaluating the influence of the concentration of Fe 2+ (25, 50, 100 and 200 mg L-1) on DOC removal efficiency, obtaining better results in the presence of 100 mg L-1 of Fe 2+. However, a long treatment time (20 h) and high consumption of hydrogen peroxide was required. Then, the influence of two coagulant ions (Al 3+ and Fe 3+) was evaluated as well as different dosages in the removal of the apparent color, turbidity and DOC by the coagulation-flocculation process in the leachate matrix at pH 3. It was defined as the best coagulant and dosage, 240 mg L-1 of Fe 3+ , which resulted in 60, 80 and 11%, respectively, of apparent color, turbidity and DOC removals. The influence of the matrix composition (SO 4 2and Clions and presence of color and turbidity) in the photo-Fenton process was also evaluated. For this, the isolated or combined precipitation of the SO 4 2and Clions with Ba 2+ and Ag + , respectively, as well as the application of a coagulation-flocculation pretreatment using Fe 3+ in the leachate were carried out. It was observed that the photo-Fenton process in the absence of inorganic ions resulted in a kinetic 2.4 times better, consuming half of the amount of oxidant when compared to the treatment of the raw leachate, with greater interference of sulfate ions. On the other hand, applying coagulation-flocculation pretreatment using Fe 3+ and in sequence photo-Fenton process, resulted in a similar efficiency in the treatment of raw leachate (70-77% DOC removal), with only 17% of the time and 7% of the consumption of H 2 O 2. In a second step, a protocol was evaluated for the treatment of landfill leachate by the integration of coagulation flocculation, filtration stage for the elimination of suspended material and solar photo-Fenton process at pH close to neutrality. The coagulation-flocculation process was applied at natural pH of the raw leachate (7.9), evaluating different concentrations of the coagulating agents-Fe 3+ or Al 3+ and salts of different anions (Cl-, NO 3 and SO 4 2-). Improved turbidity removal efficiency (66%) was obtained using 4.4 mmol Al 3+ L-1 (119 mg Al 3+ L-1) as nitrate salt. Afterwards, the photo-Fenton process was applied to the supernatant aiming to the degradation of residual DOC, being evaluated...