Treatment of Sulfonated Azo Dye Reactive Red 198 by UV/H<sub>2</sub>O<sub>2</sub>

Ribeiro, Jefferson P.; Oliveira, Juliene T.; Oliveira, André G.; Sousa, Francisco W.; Abdala Neto, Eliezer F.; Vidal, Carla B.; de Keukeleire, Denis; Santos, André B. dos; Nascimento, Ronaldo F.

doi:https://doi.org/10.1155/2014/619815

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Research Article | Open Access

Volume 2014 | Article ID 619815 | https://doi.org/10.1155/2014/619815

Treatment of Sulfonated Azo Dye Reactive Red 198 by UV/H₂O₂

Jefferson P. Ribeiro,¹Juliene T. Oliveira,²André G. Oliveira,²Francisco W. Sousa,¹Eliezer F. Abdala Neto,¹Carla B. Vidal,¹Denis de Keukeleire,³André B. dos Santos,¹and Ronaldo F. Nascimento²

Academic Editor: Vijay K. Thakur

Received07 Jul 2014

Accepted08 Aug 2014

Published08 Sept 2014

Abstract

UV/H₂O₂ system was tested on the color removal of sulfonated azo dye Reactive Red 198 (RR), which is widely used in textile process. The effects of hydrogen peroxide concentration, temperature, pH, and the in-line addition of hydrogen peroxide on high color and chemical oxygen demand (COD) removals were investigated. The kinetic of dye decolorization was also determined. The results showed that 2% H₂O₂ decreased the process efficiency, while 1% H₂O₂ solution led to a better performance of the system. Despite the fact that the pH increase had small effect on color removal, it affects positively COD removals. The same behavior was found for temperature increase. A high temperature resulted in a slight decrease in color removal and a sharp decrease for COD removal. In addition the H₂O₂ in-line provided a small improvement in both color and COD removals. UV/1% H₂O₂ treatment was the most efficient, the good performance was linked to higher amount of hydroxyl radicals formed.

1. Introduction

The contamination of natural waters has been identified as one of the biggest problems in modern society. The textile industry has been a particular focus because it is associated with the use of inputs (dyes, detergents, and fabric softeners) and the generation of large volumes of effluent due to the overuse of water [1, 2].

Textile effluents are often highly colored due to the presence of dyes that are not fixed onto the fiber during the dyeing process, and these effluents contain large amounts of suspended solids. In addition, textile effluents have highly fluctuating pH values, elevated temperatures, high chemical oxygen demands (CODs), and considerable concentrations of toxic metal ions (Cr, Ni, and Cu) [3]. It has been estimated that approximately 1–15% of textile dyes used are lost during the dyeing process and are released in effluents [4, 5].

The release of effluents into aquatic ecosystems may decrease the water transparency and solar radiation penetration, thus decreasing photosynthetic activity and gases solubility, causing irreversible damage to the flora and fauna [6].

The different pollutants produced by the textile industry can be treated by physical-chemical and/or biological processes, which, like other technological processes for wastewater treatment, have advantages and disadvantages. Biological processes are widely used for the treatment of textile wastewaters, usually in combination with a physical-chemical posttreatment. However, these processes usually demand high hydraulic retention times (HRT) and transfer part of the dyes to a different phase, leading to other environmental consequences (sludge) [7, 8]. Moreover, trace amounts of dioxins and furans can be formed as byproducts of incomplete oxidation [9]. Because of these limitations as well as the low efficiencies that can be found with many dye classes, new technologies for the treatment of effluents from textile industry have been developed.

Advanced oxidation processes (AOPs) are highly effective at destroying organic compounds that are difficult to degrade. They function by generating hydroxyl radicals that act as a very reactive oxidizing agent and can quickly and nonselectively cleave chemical bonds, leading to partial or complete mineralization of the contaminant. Examples of AOPs include Fe/H₂O₂, UV/O₃, O₃/H₂O₂, O₃/UV/H₂O₂, UV/TiO₂, and UV/H₂O₂, and the use of this technology on textile wastewater is well documented [10–14].

A combined process using UV and H₂O₂ is one of the AOPs that have been successfully applied to the treatment of various aqueous pollutants [15]. Oxidation processes are associated with very reactive species, such as hydroxyl radicals, which are generated by the direct photolysis of H₂O₂ under UV irradiation [16]: This study investigated the use of UV/H₂O₂ system on degradation of the sulfonated azo dye Reactive Red 198 (RR), Figure 1. The kinetics of dye decolorization were determined as well as the effects of hydrogen peroxide concentration, temperature, pH, and the in-line addition of hydrogen peroxide on dye removal.

2. Materials and Methods

2.1. Reagents

Reactive Red 198 (RR) (CAS 145017-98-7) was supplied by DyStar and was used to test the dye degradation capacities: hydrogen peroxide (30% w/w) (SYNTH), sodium hydroxide (NaOH) (VETEC), and sulfuric acid (H₂SO₄) (SYNTH). All solutions were prepared with deionized water (Milli-Q Academic-Millipore).

The molecular weight of Reactive Red is approximately 968.2 g/mol. The chemical oxygen demand (COD) of a solution containing 1 g/L of this dye is 2381.30 mg O₂/L. The UV-VIS absorption spectrum at a concentration of 1 g/L (purity disregarded) showed a strong absorption peak at 520 nm (black line), characterized by the presence of azo group (–N=N–) bound to aromatic rings, as shown in Figure 2.

2.2. UV/H₂O₂ AOP Reactor

The dye degradation study was performed in an irradiation chamber (95 cm long, 2.8 cm internal diameter, and useful volume 710 mL) composed of a quartz tube and an ultraviolet (UV) source, a 30 W UV-C PHILIPS TUV-T5 low-pressure mercury vapor lamp with an intensity of 100 μW/cm² (Figure 3).

The UV source was positioned inside the quartz tube; the dye solution was on the outside of the tube; hence, there was no direct contact between the UV source and the dye to be irradiated. A stainless steel reflective dome was placed over the experimental set-up to shield the rest of the laboratory from the UV radiation. The experiments were conducted in a glass jar covered with aluminum foil on a hot plate with magnetic stirring. Recirculation of the dye solution to be treated was performed using a peristaltic pump (GILSON, model Miniplus 3).

Three degradation systems were used: UV, H₂O₂, and UV/H₂O₂. All experiments were performed with a total volume of 2 L of the dye solution. The dye was dissolved in water and heated to a predetermined temperature, and then known amounts of hydrogen peroxide and NaOH or H₂SO₄ (to adjust the pH) were added to the solution. All experiments were performed at a flow rate of 25 mL/min and a hydraulic retention time (HRT) of 28.4 minutes. The decolorization rate and the effects of temperature, pH, amount of hydrogen peroxide, and in-line addition of hydrogen peroxide were studied. All experiments were performed in duplicate.

2.2.1. Effect of the Hydrogen Peroxide Concentration

The effect of the hydrogen peroxide concentration on dye removal was evaluated using five different concentrations: 0.3, 0.5, 0.7, 1, and 2% (w/v). The dye concentration used was 1.03 mM. In this part of the study, the experiments were performed using three degradation systems: UV, H₂O₂, and UV/H₂O₂. The total irradiation time was 240 minutes and the initial pH was 10. Determinations of residual H₂O₂, pH, conductivity, color, and COD were performed every 60 minutes.

2.2.2. Effect of the Initial pH

After the investigation of the effect of the hydrogen peroxide concentration, experiments were performed with initial pH values of 3, 6, 8, and 10. This study was run using the UV/H₂O₂ system, hydrogen peroxide concentration of 1% (w/v), dye concentration of 1.03 mM, and temperature of 25°C.

2.2.3. Effect of Temperature

After the evaluation of hydrogen peroxide concentration and initial pH influence on color and COD removals, experiments were performed to elucidate the influence of temperature. For this test, four temperatures were evaluated: 25, 45, 60, and 80°C. This study was performed using the UV/H₂O₂ system, hydrogen peroxide concentration of 1% (w/v), and dye concentration of 1.03 mM.

2.2.4. Effect of the In-Line Addition of Hydrogen Peroxide

The last part of the experiment consisted of an evaluation of in-line hydrogen peroxide addition in the AOP reactor. Therefore, small amounts of H₂O₂ were added to the UV/H₂O₂ system by using a peristaltic pump (GILSON, model Miniplus 3), in which the initial pH was 10, hydrogen peroxide concentration of 1% (w/v), dye concentration 1.03 mM, and temperature of 60°C. It is worth mentioning that we added in-line the same volume of hydrogen peroxide used for the experiments 2.2.4, in which this compound was kept in a container with the dye and other chemicals.

2.3. Physical and Chemical Analyses

Dye characterization was performed by analyzing color, amount of residual peroxide, pH, conductivity, and COD. The pH was measured with a digital pH meter (TECNAL microprocessor; model TEC-5). Hydrogen peroxide concentration was determined using a volumetric titration method. Conductivity was measured with a SCIENTIFIC THERMO (Orion 5 Star) conductivity meter.

The color was determined using a spectrophotometer (Thermo-Nicolet Evolution 100) and scans were performed every 60 minutes. The samples were diluted (1 : 5) in ultrapure water and then centrifuged at 13000 rpm for 2 minutes (Eppendorf, MiniSpin). Dye removal efficiency was estimated from the absorbance measurements according to where and are final and initial concentration of Reactive Red 198, respectively. COD was determined photometrically (Thermo-Evolution Nicolet 100) according to standard methods (APHA, 2005). The residual concentration of hydrogen peroxide (H₂O₂) is important because it affects the COD by consuming K₂Cr₂O₇ [17]: This interference can be corrected taking into account the COD of a hydrogen peroxide solution. After determining the residual hydrogen peroxide concentrations, corrections were made according to Lin and Lo [18] who reported that 1 g/L of hydrogen peroxide corresponds to COD of 270 mg/L.

3. Results and Discussion

3.1. Effect of the Hydrogen Peroxide Concentration

The effect of the oxidant concentration (H₂O₂) was assessed in the H₂O₂, UV/ H₂O₂, and UV degradation systems. During UV/ H₂O₂ treatment, it was observed that increasing the concentration of hydrogen peroxide from 0.3 to 1% an increase in color removal was observed (Figure 4). However, a negative effect was found when the hydrogen peroxide concentration was 2%. A negative effect of hydrogen peroxide on the decolorization rates was also verified on Chang et al. [19]. The color removal in the presence of only hydrogen peroxide (1%) or UV was negligible. Elmorsi et al. [20] also observed this effect in their study, demonstrating that the combination of UV and H₂O₂ is necessary.

Table 1 presents the changes in the physical-chemical properties for each condition studied. The conductivity results generally show increases for all treatments (Table 1) which are most likely either due to the addition of hydrogen peroxide at the beginning of the experiment or due to the formation of ions in the solution after dye bond cleavage. For instance, some authors have observed the formation of , , and Cl⁻ during the mineralization of Reactive Red 198 [21].

The analyses confirmed a pH decrease for all treatments (Table 1), most likely due to the formation of acidic substances by hydroxyl radicals during dye removal. Similar results were found by Kowalska et al. [22]. For instance, Mahmoodi et al. [21] reported the formation of organic carboxylic acids during the photocatalytic degradation of triazinic ring-containing azo dye (Reactive Red 198) by using immobilized TiO₂ photoreactor. The results for the residual peroxide concentration (Table 1) showed a gradual decrease in this concentration for all treatments, most likely due to the formation of hydroxyl radicals from hydrogen peroxide cleavage.

COD removal varied from 14.83% to 78.41% and the UV/1% H₂O₂ treatment was the most efficient (Figure 5). The good performance was linked to higher amount of hydroxyl radicals formed. However, no improvement in either color or COD removals was found when the H₂O₂ concentration increased from 1 to 2% (Figure 5). Therefore, UV/1% H₂O₂ was selected for the subsequent studies.

According to Kalsoom et al. when low-pressure mercury vapor lamps and low concentrations of peroxide are used in AOP system, the amount of UV absorption during the generation of hydroxyl radicals is insignificant [23]. Published studies showed that increasing the concentration of hydrogen peroxide leads to a subsequent increase in the hydroxyl radical production. Excess hydrogen peroxide in the reaction may decrease the process efficiency since this compound is able to scavenge hydroxyl radicals to form water and hydroperoxyl radicals (), thus initiating other reactions that affect the oxidation process [19]:

3.2. Effect of the Initial pH

According to the results shown in Figure 6, pH had no influence on the color removal capacity. Elmorsi et al. [20] also found no differences in color removal varying the pH from 2 to 9, which is in agreement with our observations. Under a technological perspective this is an important characteristic and an advantage of the UV/H₂O₂ AOP system because there is no need of pH corrections in the treatment plant and usually the pH of textile wastewaters is alkaline.

Table 2 displays the results of the physical-chemical analyses highlighting an increase in the conductivity after treatment. However, it was observed that at higher pH values, there was a greater variation between initial and final conductivities. This was likely due to further molecular fragmentations leading to ionized reaction products.

The residual peroxide concentrations decreased for all treatments, but it is worth noting that, at basic pH values, there is a higher rate of peroxide decomposition (Table 2), as previously reported [24]. UV radiation, which promotes the formation of hydroxyl radicals, also favors the rate of peroxide decomposition. Legrini et al. [25] indicated that, at alkaline pH, the rate of photolysis of H₂O₂ increases, likely due to anion formation, which has a higher molar absorption coefficient (240 M⁻¹ cm⁻¹ at 254 nm) than hydrogen peroxide (18.6 M⁻¹ cm⁻¹ at the same wavelength). Some authors have reported that the rate of H₂O₂ decomposition (see (8)) increases as the pH value approaches to pKa value (11.7) [25]. The hydroxyl radical is deactivated approximately 100 times faster in the presence of the anion than in the presence of H₂O₂ (see (9) and (10)) [19]. Consider the following: Contrary to the color removal, COD removal showed a pH dependence (initial values of 3, 6, 8, and 10), which increases with the pH increase. The highest COD removal was found at an initial pH of 10, which resulted in a reduction of 78.81% (Figure 7). This likely indicates that COD removal was not affected by the formation of the hydroperoxyl anion () or maybe the dye oxidation by the hydroxyl radicals was not taking place initially in the chromophore, which is responsible for the observed color, but in the auxochromes. Therefore, further experiments to determine the oxidation pathways should be required.

3.3. Effect of Temperature

It is well known that usually textile wastewater is discharged at high temperatures. Hence, a study of the effect of temperature on dye removal was performed. The results presented in Figure 8 indicate that there was a small increase in the rate of decolorization by the temperature increase. However, the temperature of 80°C negatively impacted the process.

The results for COD removal are shown in Figure 9 and a slight improvement was observed by the temperature increase. However, 80°C decreased COD removal, as negatively affecting color removal. The highest COD removal was found at 60°C, which corresponded to 87.05%.

Another important point verified was the increase in the decomposition rate of hydrogen peroxide as the temperature increases (Table 3). For this parameter, 80°C was the best temperature. However, it seems that the species formed upon hydrogen peroxide oxidation were not involved either in color or in COD removals, as there was a decrease in the rates when the temperature changed from 60°C to 80°C.

The pH did not vary significantly between the treatments but there was an increase in conductivity with the temperature increase (Table 3).

3.4. Kinetic Modeling

The radicals in aqueous solution may be produced by UV irradiation and hydrogen peroxide (see (1)). To develop the kinetic model, we use (1) and (4)–(7) and compile the reaction steps: The reaction of hydroxyl radical with corresponds to the reactions of the hydroxyl radical with other scavenger such as chloride, nitrate, sulfate, and carbonate. The corresponding kinetic equation of decolorization for RR is Considering the and radicals major species in decolorization, For state-steady approximation, it follows that As a consequence of state-steady concentration and from (14)–(17), the concentration of hydroxyl radical can be described by (21): where is the initial quantum yield of hydrogen peroxide disappearance, equal to 0.5, and is the radiation intensity absorbed by H₂O₂.

Also, In (19), is the incident UV light intensity, is the optical path length of system, and and are the molar extinction coefficient for and RR, respectively. Considering the RR and having a high absorbance in the early stages of the process, And , it can be written as And then (22) can be changed into (13): In the present study, the results, Figure 10, show that the decolorization of dye RR corresponds to zero order kinetics; thus , and the overall rate expression simplifies: The results in Table 4 reveal that increases with increasing concentration of H₂O₂ and decreases above at 1%.

3.5. Effect of the In-Line Addition of Hydrogen Peroxide

The effect of the in-line peroxide addition was studied to determine if this operational strategy would benefit the process. The decolorization process was not significantly affected, although it should be noted that after 180 minutes of treatment, there was a slight improvement (Figure 11) compared to the conventional hydrogen peroxide feeding. A small but higher effect of hydrogen peroxide in-line addition was found for COD removal (Figure 12).

The results of the physical-chemical analyses are presented in Table 5. There was an increase in the conductivity for the two operational strategies tested and a significant pH variation during in-line addition of H₂O₂.

The gradual addition of hydrogen peroxide may positively influence the mineralization process. This behavior can be explained by the fact that H₂O₂ in excess in solution, even under optimal operational conditions, is able to act as a hydroxyl radical () scavenger. Additionally, intermediates can compete with the target molecules of the radicals. Nonetheless, an economic evaluation should be done to verify if a new line is composed of a different pump (including energy costs) as well as a separate container for stock solution, mixer, and so forth, would be compensated by the efficiency increase.

4. Conclusions

High color and COD removals were achieved by treating the sulfonated azo dye Reactive Red 198 by the UV/H₂O₂ advanced oxidation process, even when low radiation times were used. 1% H₂O₂ solution showed to be the best concentration, in which 2% H₂O₂ decreased the process efficiency. The pH increase had a small effect on color removal but impacted positively COD removals. The same behavior was found for temperature increase, but changing from 60°C to 80°C resulted in a slight decrease for color removal and a sharp decrease for COD removal. In-line addition provided a small improvement in both color and COD removals. Therefore, the UV/H₂O₂ AOP system seems to be an interesting option for textile wastewaters and the most important parameters for color and COD removals are irradiation time and hydrogen peroxide concentration.

Conflict of Interests

The authors declare no conflict of interests in the research.

Acknowledgments

The authors would like to thank the Brazilian agencies CNPq, CAPES, and FUNCAP for the scholarship and financial support.

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Copyright © 2014 Jefferson P. Ribeiro et al. This is an open access article distributed under the Creative Commons Attribution License, which permits unrestricted use, distribution, and reproduction in any medium, provided the original work is properly cited.

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