Metal-Organic Framework-101 (MIL-101): Synthesis, Kinetics, Thermodynamics, and Equilibrium Isotherms of Remazol Deep Black RGB Adsorption
Hindawi
Journal of Chemistry
Volume 2018, Article ID 8616921, 14 pages
https://doi.org/10.1155/2018/8616921
Research Article
Metal-Organic Framework-101 (MIL-101): Synthesis, Kinetics,
Thermodynamics, and Equilibrium Isotherms of Remazol
Deep Black RGB Adsorption
Vo Thi Thanh Chau,1 Huynh Thi MinhThanh,2 Pham Dinh Du,3 Tran Thanh Tam Toan,4
Tran Ngoc Tuyen,4 Tran Xuan Mau ,4 and Dinh Quang Khieu 4
1
Tran Quoc Tuan High School, Quảng Ngãi 570000, Vietnam
Department of Chemistry, Qui Nhon University, Bı̀nh Ðịnh 590000, Vietnam
3
Faculty of Natural Sciences, Thu Dau Mot University, Thủ Dầu Một 820000, Vietnam
4
University of Sciences, Hue University, Hue 530000, Vietnam
2
Correspondence should be addressed to Dinh Quang Khieu;
Received 7 January 2018; Revised 11 April 2018; Accepted 14 May 2018; Published 24 June 2018
Academic Editor: Hossein Kazemian
Copyright © 2018 Vo Thi Thanh Chau 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.
In the present paper, the synthesis of metal-organic framework-101 (MIL-101) and Remazol Deep Black RGB (RDB) adsorption on
MIL-101 were demonstrated. The kinetics of RDB adsorption on MIL-101 was studied using Weber’s intraparticle diffusion model and
the pseudo-first- and pseudo-second-order kinetic models. Particularly, the statistical method of piecewise linear regression and multinonlinear regression was employed to analyse the adsorption data according to the previously mentioned kinetic models. The results
indicated that the adsorption process followed the three-step pseudo-first-order kinetic equation, which was consistent with the results
of the intraparticle diffusion model with three linear segments. This model best described the experimental data. In addition, the
adsorption isotherm data were studied using five adsorption models, namely, Langmuir, Freundlich, Redlich–Peterson, Toth, and Sips
in nonlinear forms, and the Langmuir model is the most appropriate for the experimental data. The values of energies of activation of
adsorption were calculated, and they revealed that the adsorption process was of endothermic chemical nature. A statistical comparison using Akaike information criterion to estimate the goodness of fit of the kinetic and isotherm models was presented.
1. Introduction
It is well known that wastewater from textile industries, pulp
mills, and dyestuff manufacturing has been a potential threat
to environment [1, 2]. Various treatment processes such as
physical separation, chemical oxidation, and biological degradation have been widely investigated to remove dyes from
wastewaters [3]. Among these processes, adsorption technology is considered as one of the most competitive methods
because it does not require high operating temperature and
has a simple operation as well as low cost, and several coloring
materials can be removed simultaneously [4].
MIL-101 has demonstrated good performance in storage
and adsorption of gas such as hydrogen storage [5], adsorption of CO2 and CH4 [6], and long-chain alkanes [7].
However, there are very few reports studying the adsorption
of dyes from aqueous solutions [8–10]. MOFs in general and
MIL-101 in particular exhibit high efficiency for adsorption of
dyes from aqueous solutions due to their unique structures
such as large surface areas, ordered porosity, and high density
of adsorption sites (anion and cation). MIL-101 demonstrates
excellent adsorption properties for dyes, such as methyl orange (MO), xylenol orange (XO), and uranine. For expanding
applications of MIL-101, studying the adsorption of this
material for Remazol Deep Black RGB (denoted as RDB) used
widely in dye industry will be a concern of this work.
Azo dyes with an azo group are widely used in many textile
industries due to their low cost, high solubility, and stability.
These dyes and their intermediate products are toxic, carcinogenic, and mutagenic to aquatic life. Remazol Deep Black
RGB is a common diazo reactive dye, widely used in textile
industries [11]. It is stable and hard to degrade biologically due
2
Journal of Chemistry
OH
NaO3SOCH2CH2O2S
NH2
N=N
N=N
NaO3S
SO3Na
SO2CH2CH2OSO3Na
Scheme 1: Molecular structure of RDB.
to the presence of aromatic rings. Thus, RDB removal from
textile wastewater has drawn much attention among researchers.
Several techniques including adsorption, electrochemistry, and
biosorption for RDB treatment have been reported. Soloman
et al. [11] applied the electrochemical treatment to hydrolyze
Remazol Black. They demonstrated that the performance of
the batch recirculation system was better than other reactor
configurations studied in terms of capacity utilization and energy
consumption. Brazilian pine-fruit shells (Araucaria angustifolia)
in their natural form were used as an adsorbent for the removal
of RDB dye from aqueous effluents [12]. A biosorption process
to discard azo dyes by fungi (Aspergillus flavus) was investigated
in batch reactors [13]. Ninety percent of the dye in a 100 mg/L
solution was removed. Recently, Thanh et al. [14] reported
that iron doping to ZIF-8 significantly enhances RDB adsorption
capacity. Fe–ZIF-8 also exhibits photocatalytic degradation of
RDB under visible light [15].
Batch adsorption studies focus on two main trends: (i)
designing and optimizing experiments with the evaluation of
the influence of the experimental variables—this approach
enables to estimate the magnitude of the influence of the
factors affecting the process and their interactions [16]—and
(ii) kinetics, thermodynamics, and equilibrium isotherm
adsorption studies [14, 17]. For the latter, several models are
used to study adsorption kinetics and isotherms. The parameters in these models are calculated with linear or nonlinear
regression approaches. However, the number of parameters in
each mode is different. For example, the Langmuir isotherm
model contains two parameters, while the Redlich–Peterson
isotherm model has three parameters. It is obvious that the
greater the number of model parameters, the lower the relative
errors (REs) or the sum of squared errors (SSEs). Therefore, the
model compatibility needs to be evaluated including SSEs or
REs and the number of model parameters as well as the experimental points. However, in the majority of current publications, the goodness of fit for models is estimated based on
only the REs or SSEs. To the best of our knowledge, the research
on this issue is limited.
In the present study, MIL-101 was employed as an adsorbent for removing RDB dye. The effects of initial concentration, adsorbent particle size, agitation speed, temperature,
and pH on the adsorption behavior of RDB onto MIL-101 were
investigated. The adsorption kinetic and isothermal studies and
the goodness of fit for models were addressed.
2. Experimental
2.1. Materials. Chromium (III) nitrate nona (...truncated)