Sequential study on reactive blue 29 dye removal from aqueous solution by peroxy acid and single wall carbon nanotubes: experiment and theory
© Jahangiri-Rad et al.; licensee BioMed Central Ltd. 2013
Received: 9 December 2012
Accepted: 11 December 2012
Published: 5 January 2013
The majority of anthraquinone dye released to the environment come from antrapogenic sources. Several techniques are available for dyes' removal. In this study removal of reactive blue 29 (RB29) by an advanced oxidation process sequenced with single wall carbon nanotubes was investigated. Advanced oxidation process was optimized over a period of 60 minutes by changing the ratio of acetic acid to hydrogen peroxide, the compounds which form peroxy acid. Reduction of 20.2% -56.4% of reactive blue 29 was observed when the ratio of hydrogen peroxide/acetic acid/dye changed from 344/344/1 to 344/344/0.08 at different times (60, 120 and 180 min). The optimum ratio of acetic acid/hydrogen peroxide/dye was found to be 344/344/0.16 over 60 min. The resultant then was introduced for further removal by single wall carbon nanotubes(SWCNTs) as adsorbent. The adsorption of reactive blue 29 onto SWCNTs was also investigated. Langmuir, Freundlich and BET isotherms were determined and the results revealed that the adsorption of RB29 onto SWCNTs was well explained by BET model and changed to Freundlich isotherm when SWCNTs was used after the application of peroxy acid. Kinetic study showed that the equilibrium time for adsorption of RB 29 on to SWCNT is 4 h. Experiments were carried out to investigate adsorption kinetics, adsorbent capacity and the effect of solution pH on the removal of reactive blue29. The pseudo-second order kinetic equation could best describe the sorption kinetics. The most efficient pH for color removal (amongst pH=3, 5 and 8) was pH= 5. Further studies are needed to identify the peroxy acid degradation intermediates and to investigate their effects on SWCNTs.
Dyes are color organic compounds which can colorize other substances. Dyes are extensively used in the textile, leather, paper and other industries. The complex aromatic structure of dyes make them more stable and difficult to be removed from water bodies . Textile manufacturing is one of the largest industrial producer of wastewater characterized by highly fluctuating pH,high chemical oxygen demand (COD), strong color and biotoxicity . It has been estimated that approximately 50% of applied reactive dyes is wasted because of dye hydrolysis in the alkaline dye bath at concentrations in the range of 10-200mg/L . As the regulations world wide have become more stringent, stricter,the effluent of textile and related industries have to be treated before discharging in to the environment. This has resulted in a highly demand for environmentally friendly technologies. Numerous approaches including electrochemical oxidation , ozone treatment [5, 6], biological treatment , membrane filtration , and adsorption  have been applied to remove organic compounds. Promising results have been achieved using advanced oxidation processes(AOPs) for effluent from dye industries in recent years . These processes are based on the production of highly reactive radicals, especially hydroxyl reactive radicals which promote destruction of the target pollutant until mineralization .
Moreover, adsorption technology with no chemical degradation is attractive due to it's unique Effectiveness, efficiency and economy . Carbon nanotubes are increasing used in researchs as new adsorbents. They are an alternative for the removal of organic and inorganic contaminants from water because theyhave large specific surface area, small size and hollow, layered structure . According to the grapheme layer, CNTs are classified into sigle wall (SWCNTs) and multi-wall (MWCNTs). Carbon nanotubes are unique and one-dimensional macromolecules which exhibit considerably thermal and chemical stability . More recently, Long and Yang, reported that MWCNTs could be more efficient for the removal of dioxin than activated carbon . Cai et al., prepared a CNT-packed cartridge for the solid-phase extraction of compounds such as bisphenol A and 4-c-nonylphenol in environmental water samples . CNTs have been proven to possess great potential as superior adsorbents for removing many kinds of organic and inorganic including 1,2-dichlorobenzene , trihalomethanes  and cationic dyes . Therefore, CNTs might be ideal sorbents for the removal of dyes from water.
Composite textile wastewater is characterized mainly by measurements of biochemical oxygen demand (BOD), chemical oxygen demand(COD), suspended solids (SS) and dissolved solids (DS). According to other studies, COD values of composite wastewater are extremely high compared to other parameters. In most cases BOD/COD ratio of the composite textile is around 0.25 that implies the wastewater containing large amount of non biodegradable organic matter.
Materials and methods
Characterization of SWCNTs
Single–wall carbon nanotubes were subjected to energy dispersive spectrometer for surface distribution of elemental composition and scanning electron microscopy (SEM). Size and morphology of SWCTs were reported by transmission electron microscopy (TEM). The specific surface area of SWCNTs were measured by BET method. The outer and inner diameter of SWCNTs were 1–2 nm and 0.8-1. 1 nm, respectively. The length of SWCNTs was 10 μm with specific surface area of 700 m2/g. The purity of selected single-wall carbon nanotubes was 95%.
Peroxy acid oxidation
Peroxy acid oxidation experiment were conducted using 250 mL pyramid glass bottles with the addition of 100 mL reactive blue29 (30 mg/L)solution. Predetermined volumes of acetic acid (50%) and hydrogen peroxide (30%) were added to each bottle in order to keep the mole ratio of hydrogen peroxide/acetic acid/dye in 344/344/1 and lower. In other studies degradation of organic matter were investigated by peroxy acid and the range of hydrogen peroxide/peroxy acid/pollutant was kept in the same range [24, 25]. The samples then were put on the illuminated refrigerated incubator shaker (Innova 4340) and shaken at 150 rpm, the temperature kept at 3180c. The samples were shaken for a chosen reaction time after which the solusion was quenched by adding 1 mL of sodium solfite (1M).
Estimated reaction rates for reactive blue 29
Batch adsorption experiments
Batch adsorption experiment were conducted after the optimum conditions for advanced oxidation process were found. The pH of the solutions were adjusted to 5 by adding NaoH 0.1N. Different suspensions of SWCNTs (4, 6, 7 and 8 mg) were added to each bottle. The solutions were then put again on shaker and equilibrated at 3180c for 24 h.
Where: Ci and Ce are the initial and equilibrium concentrations, respectively in mg/L, and m is the amount of SWCNTs in mg/L. In order to conduct adsorption experiment of RB29 solely, reactive blue (30 mg/L) was equilibrated by different suspensions of SWCNTs (0.13, 0.1, 0.08, 0.06, 0.04 and 0.02 g/L) at pH=5 and temperature of 318°C for 24 h. At the end of the equilibrium period, the suspensions were centrifuged at 4000 rpm for 10 min and the supernatant was sent for analysis of the dye concentration. The adsorption of RB29.
The advanced oxidation process was conducted for initial dye concentration of 30 mg/L after optimum mole ratio of hydrogen peroxide/acetic acid/reactive blue 29 was found. The resultant was then shaken with SWCNT(0.08 g/L) for 2 h. Total color removal efficiency was finally calculated. The Langmuir, Freundlich and BET isotherms were determined to investigate the adsorption behavior of dye remained in the solution onto SWCNTs after AOP process.
Advanced oxidation process by peroxy acid
Constants of Freundlich,Langmuir and BET isotherm for RB29
Constants of Freundlich, Langmuir and BET isotherms for RB29 after peroxy acid process
Effect of contact times
where C is the intercept and ki is the intraparticle diffusion rate constant (mg/g min1/2), which can be evaluated from the slope of the linear plot of qt versus t1/2.
Pseudo-first second order and intraparticle diffusion model parameters
Pseudo-first order model:ln(qe-qt)=−0.01 t + 5.22
Pseudo-second order model:t/qt=0.003t+0.16
Intraparticle diffusion model:qt=11.6 t ½+88.21
k i(mg/g. min 1/2)
Effect of pH
Adsorption isotherm is a dynamic concept when the rate at which molecules adsorb on to the surface is equal to the rate at which they desorb. The equilibrium adsorption isotherm‘s shape is of great importance to provide information about the adsorbents’ surface structure. The data obtained indicated that adsorption of RB29 onto SWCNTs first well explained by BET isotherm with R2=0.987 which shows that dye molecules form multilayer on SWCNTs t. Then Freundich isotherm fitted the experimental data better than BET and Langmuir with R2=0.958 when SWCNTs were used in sequence with peroxy acid. The Freundlich isotherm model assumes that different sites with several adsorption energies are involved. It is generally known that values of n in the range of 2–10 shows good, 1–2 approximately difficult, and < 1 shows poor adsorption property. SWCNT stated good behavior (n>2) in this experiment. The slope 1/n ranging betwwen 0 and 1 is a measure of adsorption intensity or surface heterogeneity. As this value reaches zero, the surface becomes more heterogeneous. In this study 1/n was < 0.3 indicating the heterogeneity of the surface. R2 values of the pseudo-first and second-order models exceeded 0.95 (Table 1), but due to the higher R2 values obtained from pseudo-second order, this model represented better adsorption kinetics . Typically, various mechanisms control the adsorption kinetics, the most limiting are the diffusion which include external diffusion, boundary layer diffusion and intraparticle diffusion . When the line of intraparticle diffusion model passes through the origin(C=0), the intra particle diffusion will be the sole rate control step . The regression in our study was linear, but it did not pass through the origin (Table 4), suggesting that adsorption of dye on to SWCNTs involved intraparticle diffusion, but that was not the only rate-controlling step.
Effect of initial pH
Effect of initial pH is shown in Figure 7. It was observed that dyes adsorbed increased when pH increased from 3 to 5, perhaps suggesting that one of the contributions of SWCNTs adsorption toward cationic dyes resulted from attraction between positively charged reactive blue dye and negatively charged adsorbent surface. As pH increased from 5 to 7, dyes adsorbed decreased. This phenomenon might be resulted from competition between RB 29 dye an OH- on the same SWCNTs sites.
Combination study of peroxy acid and SWCNTs
The optimum ratio of hydrogen peroxide/acetic acid/dye was found to be 344/344/0.16 in 60 min owing to the higher R2 (0.959) calculated for reaction rate (Table 1). This conclusion is based on the future design of the remediation strategy where cost plays a role. In another study conducted by N’guessan, the optimum v/v ratio of peroxide/acetic acid/organic pollutant was determined as 3/5/7 ml . The disappearance of RB29 by peroxy acid seemed to be dependent on the acetic acid as hydroxyl radical formation catalyst and hydrogen peroxide as hydroxyl radicals source. Maximum color removal by combination of peroxy acid and SWCNTs (0.08 g/L) was 66.3%. By comparing the results obtained from adsorption isotherms it is clear that degradation intermediates have direct effects on adsorption of RB29 by SWCNTs because the adsorption isotherm changed (BET in the first stage to Freundlich from in the second). Two assumptions can be made: (a) intermediates compete with RB29 for the adsorption onto SWCNTs or(b) intermediates might inhibit or induce the adsorption of RB29 onto SWCNTs. Mechanism of SWCNTs towards RB29 and AOPs degradation intermediates maybe derivedfrom two reasons. One reason might be based on Van der Waals interactions occurring between carbon atoms and aromatic backbones of the dye and intermediates. The other might be due to the electrostatic attraction between the dye and intermediates onto SWCNTs surface . In another study performed on adsorption of Reactive Blue 4 dye from water solutions by SWCNTs, the same result was obtained, and the authors concluded that Reactive Blue 4 textile dye could be adsorbed on SWCNT through an electrostatic interaction . Both AOP process by peroxy acid and adsorption onto SWCNTs have high affinity for reactive blue29 dye removal. The Freundlich isotherm with R2=0.958 well fitted to the data obtained from combination experiment. Maximum color removal was 66.3% in combination process by peroxy acid and SWCNTs (0.08 g/L) as adsorbent. Further research works on testing the effects of intermediates on adsorption of reactive blue29 onto SWCNTs are needed in order to optimize the application of SWCNTs in water treatment.
Advanced oxidation process and single-wall carbon nanotubes for effective reactive blue dye 29 have been used. Both AOP proces by peroxy acid and adsorption onto SWCNTs have high affinity for RB29 dye removal. The optimum mole ratio of hydrogen peroxide/acetic acid/dye was found to be 344/344/0.16 in 60 min. The adsorption capacity of the adsorbent towards RB29 was illustrated by experimental adsorption isotherms at room temperature. BET isotherm well fitted the data when SWCNT was applied. Experiments were carried out to investigate adsorption kinetics,adsorption capacity of the adsorbent and the effect of solution pH on the removal of reactive blue29. The pseudo-second order kinetic equation could best describe the sorption kinetics. The most efficient pH for color removal was pH= 5.
This study was funded by Tehran University of Medical Sciences, Department of Environmental Health Engineering (2009–2010). The authors would like to thank the laboratory staff of the Department for their collaboration in this research.
- Crinic G: Recent developments in polysaccharide-based materials used as adsorbents in wastewater treatments. Prog Poly Sci. 2005, 30 (1): 38-70. 10.1016/j.progpolymsci.2004.11.002.View ArticleGoogle Scholar
- Walker GM, Weatherley LR: COD removal from textile industry effluent:pilot plant studies. Chem Eng J. 2001, 84 (2): 125-131. 10.1016/S1385-8947(01)00197-8.View ArticleGoogle Scholar
- Arsland-Alaton I, Gursoy BH, Smidth JE: Advanced oxidation of acid and reactive dyes:effects of Fenton treatment on aerobic,anoxic and anaerobic processes. Dyes Pigments. 2008, 78 (2): 117-130. 10.1016/j.dyepig.2007.11.001.View ArticleGoogle Scholar
- Ehrampoush MH, Moussavi GR, Ghaneian MT, Rahimi S, Ahmadian M: Removal of methylene blue dye from textile simulated sample using tubular reactorandTiO2/UV-C photocatalytic process. Iran J Environ Health Sci Eng. 2011, 8 (1): 35-40.Google Scholar
- Keisuk I, Mohammad ED, Shane AS: Ozonation and advanced oxidation treatment of emerging organic pollutants in water and wastewater. J Environ Sci Health A Tox Hazard Subst Environ Eng. 2008, 30 (1): 21-26.Google Scholar
- Mehmet FS, Hasan ZS: Ozone treatment of textile effluents and dyes: effect ofapplied ozone dose, pH and dye concentration. J Chem Technol Biotechnol. 2002, 77: 842-850. 10.1002/jctb.644.View ArticleGoogle Scholar
- Kornatos M, Lyberatos G: Biological treatment of wastewater from a dye manufacturing company using a trickling filter. J Hazard Mater. 2006, 136 (1): 95-102. 10.1016/j.jhazmat.2005.11.018.View ArticleGoogle Scholar
- Capar G, Yetis U, Yilmaz L: Membrane based strategies for the pre-treatment of dye bath wastewater. J Hazard Mater. 2006, 1359 (1–3): 423-430.View ArticleGoogle Scholar
- De-lisi R, Lazzara G, Milioto S, Murator N: Adsorption of dye on clay and sand. Use of cyclodextrins as solubility enhancement agents. Chemosphere. 2007, 69 (11): 1703-1712. 10.1016/j.chemosphere.2007.06.008.View ArticleGoogle Scholar
- Sadik WA, Sadek OM, EL-Demerash AM: The Use of heterogeneous advanced oxidation processes to degrade neutral Red Dye in aqueous solution. J Macromol Sci D. 2004, 43 (6): 1675-1686.Google Scholar
- Ollis D: Comparative aspects of advanced oxidation process. Emerging technologies in waste management. 1993, Washington DC: ACS symposium series 518, 18-34.Google Scholar
- Bach RD, Canepa C, Winter JE, Blanchette PE: The Mechanism of Acid Catalyzed Epoxidation of Alkenes with Peroxyacids. J Org Chem. 1997, 62: 5191-5197. 10.1021/jo950930e.View ArticleGoogle Scholar
- Levitt JS, N'Guessan AL, Rapp KL, Nyman MC: Remedation of a-methylnaphtalene- contaminated sediments using peroxy acids. Water Res. 2003, 37 (12): 3016-3022. 10.1016/S0043-1354(03)00116-7.View ArticleGoogle Scholar
- Belgin G, Berkant KA, Muat G, Arif H: Oxidative degradation of reactive blue4 by different advanced oxidation process. J Hazard Mater. 2009, 168 (1): 129-136. 10.1016/j.jhazmat.2009.02.011.View ArticleGoogle Scholar
- Crinic G: Non conventional low cost adsorbents for dye removal:a review. Biosource Technol. 2006, 97: 1061-1085. 10.1016/j.biortech.2005.05.001.View ArticleGoogle Scholar
- Lu CS, Chiu HS: Adsorption of zinc with purified carbon nanotubes. Chem Eng Sci. 2006, 61: 138-145.Google Scholar
- Venkata KK, Deng S, Mitchell C, Geoffery B: Application of carbon nanotube technology for removal of contaminants in drinking water.A review. Sci Total Environ. 2009, 408 (1): 1-13. 10.1016/j.scitotenv.2009.09.027.View ArticleGoogle Scholar
- Long RQ, Yang C: Carbon nanotubes as superior sorbent for dioxin removal. J Am Chem Soc. 2001, 123: 2058-2059. 10.1021/ja003830l.View ArticleGoogle Scholar
- Cai Y, Jiang G, Liu J, Zhou Q: Multiwalled carbon nanotubes as a solid-phase extraction adsorbent for the determination of bisphenol a, 4-n-nonylphenol, and 4-tert-octylphenol. Anal Chem. 2003, 75: 2517-2521. 10.1021/ac0263566.View ArticleGoogle Scholar
- Peng X, Li Y, Luan Z, Di Z, Wang H, Tian B, Jia Z: Adsorption of 1,2- dichlorobenzene from water to carbon nanotubes. Chem Phys Lett. 2003, 376: 154-158. 10.1016/S0009-2614(03)00960-6.View ArticleGoogle Scholar
- Lu C, Chung YL, Chang KF: Adsorption of trihalomethanes from water with carbon nanotubes. Water Res. 2005, 39: 1183-1189. 10.1016/j.watres.2004.12.033.View ArticleGoogle Scholar
- Gong GL, Wang B, Guang Z, Yang CP, Cheng-Gang N, Qiu-Ya N, Wen-Jin Z, Yi L: Removal of cationic dyes from aqueous solution using magnetic multi wall carbon nanotubes. J Hazard Mater. 2009, 164 (2–3): 1517-1522.View ArticleGoogle Scholar
- Gilbert E, Hoffmann S: Ozonation of ethylenediaminetetra acetic acid(EDTA) in aqueous solution. Water Res. 1990, 24: 39-44. 10.1016/0043-1354(90)90062-B.View ArticleGoogle Scholar
- Scott-Alderman N: The proxy acid treatment process:an investigation of process mechanics. 2011, USA: Proquest,Umi Dissertation PublishingGoogle Scholar
- N’Guessan AL, Cariqnan T, Nyman MC: Remediation of benzo pyrene in contaminated sediments. Chemosphere. 2004, 38 (5): 1554-1560.Google Scholar
- Wu CH: Studies of the equilibrium and thermodynamics of the adsorption of Cu2+ onto as-produced and modified carbon nanotubes. J Colloid Interface Sci. 2007, 311: 338-346. 10.1016/j.jcis.2007.02.077.View ArticleGoogle Scholar
- Kavitha D, Namasivayam C: Experimental and kinetic studies on methylene blue adsorption by coir pith carbon. Bioresour Technol. 2007, 98: 14-21. 10.1016/j.biortech.2005.12.008.View ArticleGoogle Scholar
- Ehrampoush MH, Ghanizadeh G, Ghaneian MT: Equilibrium and kinetics study of reactive red 123 dye removal from aqueous solution by asdorption on eggshell. Iran J Environ Health Sci Eng. 2011, 89 (2): 101-108.Google Scholar
- Guibal E, McCarrick P, Tobin J: Comparison of the sorption of anionic dyes on activated carbon from dilute solution. Sep Sci Technol. 2003, 38: 3049-3073. 10.1081/SS-120022586.View ArticleGoogle Scholar
- Kanan K, Sundaram MM: Comparison of the sorption of methylene blue by adsorption on various carbons. Dyes pigment. 2001, 51: 25-40. 10.1016/S0143-7208(01)00056-0.View ArticleGoogle Scholar
- Machado FM, Bergmann CP, Lima EC, Royer B, De Souza FE, Jauris IM, Calvete T, Mehmet and FS, Hasan ZS: Ozone treatment of textile effluents and dyes: effect of applied ozone dose, pH and dye concentration. J Chem Technol Biotechnol. 2002, 77: 842-850. 10.1002/jctb.644. View ArticleGoogle Scholar
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