Removal of tetracycline from aqueous solution using Fe-doped zeolite
International Journal of Industrial Chemistry
https://doi.org/10.1007/s40090-019-0191-6
RESEARCH
Removal of tetracycline from aqueous solution using Fe‑doped zeolite
M. H. Jannat Abadi1 · S. M. M. Nouri2
· R. Zhiani3,4 · H. D. Heydarzadeh2 · A. Motavalizadehkakhky5
Received: 1 October 2018 / Accepted: 27 June 2019
© The Author(s) 2019
Abstract
Tetracycline is one of the most widely used antibiotics that causes contamination of aqueous environments and has raised
serious concern during the past few years. In this work, adsorption of tetracycline on a modified zeolite was studied through
a batch system. Synthetic zeolite 13X was modified using Fe(III). The results show that the removal efficiency of tetracycline by modified zeolite has considerably increased. Different experiments were carried out in order to analyze the effect
of parameters such as pH, initial concentration of tetracycline, time, etc. The results indicate that tetracycline adsorption on
the zeolite strongly depends on the pH of the solution due to amphoteric functional groups of tetracycline and maximum
adsorption capacity of tetracycline by modified zeolite with a pH of approximately 6. The Langmuir isotherm shows good
agreement with the experimental data suggesting monolayer adsorption. Maximum adsorption capacity of the modified
zeolite reached at the experiments is almost 200 mg/g. XRD, XRF and FTIR results confirm the existence of the Fe phase
in the zeolite texture. Amide groups of TC were responsible for the complexation with Fe3+. Also, tetracycline removal was
studied in a continuous column to simulate an industrial waste water process.
Keywords Tetracycline removal · Adsorption · Modified zeolite · Fe-doped sorbent
Introduction
Tetracyclines (TC) are a broad spectrum class of antibiotics
and are widely used for veterinary and human health purposes [1]. A large portion of antibiotics is transmitted from
the body to excretion without modification. Excessive use
of antibiotics, improper disposal, and lack of policy regulations pose a serious environmental and health concern [2].
Constant exposure to antibiotics in the environment not
only disturbs natural ecological processes but can also be
* S. M. M. Nouri
1
Chemical Engineering Department, Islamic Azad University,
Neyshabur Branch, Neyshabur, Iran
2
Chemical Engineering Department, Hakim Sabzevari
University, Sabzevar 9617976487, Iran
3
Young Researchers and Elite Club, Islamic Azad University,
Neyshabur Branch, Neyshabur, Iran
4
Chemistry Department, New Materials Technology
and Processing Research Center, Islamic Azad University,
Neyshabur Branch, Neyshabur, Iran
5
Chemistry Department, Islamic Azad University, Neyshabur
Branch, Neyshabur, Iran
fatal to humans in the form of multi-antibiotic resistant bacteria. These bacteria are present in environmental sources
(e.g., water, soil, and sediments) and can readily transfer
their resistance to pathogenic bacteria via horizontal gene
transfer, resulting in a global antibiotic resistance problem
[3].
In the last two decades, progress has been made to
address the antibiotic contamination problems in many environmental sources using various remediation technologies.
Several physical and chemical degradation methods such as
chemical oxidation, adsorption, membrane filtration, ozonation, photo-fenton, and bio-degradation methods such as
activated sludge, membrane reactor, and fixed bed reactor
treatment have been applied to many antibiotics including
TC with the purpose of degrading them in environmental
sources. However, these remediation technologies are highly
condition-based (e.g., pH, and molar ratio) and potentially
expensive based on the concentration of the contaminant
present in the environmental source (antibiotic) that needs
to be degraded [4–9].
Removal of antibiotics by adsorption is one of the inexpensive methods with small technical difficulties. Many
adsorbents have been widely used to remove tetracycline
from wastewater such as carbon nanotubes [10], graphene
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International Journal of Industrial Chemistry
oxide [11], activated carbon [12, 13], zeolites [14–16] and
metal oxides [17]. Synthetic zeolite 13X is a common adsorbent which is composed of silicon-oxygen and aluminumoxygen tetrahedron connected by oxygen atoms. The uniform pore structure and high surface area make it an ideal
sorbent. The cation exchange capacity is relatively high,
which enhances the effect of surface modification on the
adsorbent capacity of the sorbent [18, 19]. Fe oxides are
widely spread in ecosystems, and iron modified zeolites have
been used for organic and heavy metal removal from wastewaters [20–23]. They show high affinity to TC compounds
due to the surface complexation process [24, 25]. Iron ion
could form a bridge between the zeolite and tetracycline
molecule and enhance the adsorption process [26, 27].
The purpose of this work is to remove tetracycline using
synthetic zeolite 13X. The synthetic zeolite has been modified with trivalent iron. The effect of different operating
parameters such as pH, time, adsorbent dosage, etc. has been
investigated.
Materials and methods
The zeolite used in this work is Na-13X which was purchased from IranZeolite. Tetracycline hydrochloride was
purchased from Aldrich, F
eCl3·6H2O and NaOH from Merck
Inc.
In order to prepare the treated zeolite, 3 g of zeolite was
impregnated in 50 cc solution of 40 mmol F
eCl3. The solution was stirred at room temperature for 24 h, separated
and washed several times with deionized water and dried at
105 °C overnight. The obtained samples were powdered and
used for the adsorption experiments.
For the adsorption experiments, 50 ml of tetracycline
solution with different concentrations and specified amounts
of sorbent were mixed using a shaker for 24 h to make sure it
reaches the equilibrium state. After separation by centrifuge,
the supernatant solution was collected for concentration
measurement using UV–Vis spectroscopy at 357 nm wavelength. The pH of the solutions was adjusted using 0.1 M
NaOH and HCl. To investigate the effect of pH, experiments
were carried out in the pH range of 2–9. For all the experiments, temperature was set to 30 °C. For the kinetic experiments, 75 mg of modified zeolite was added to 50 ml of
tetracycline solution (200 ppm). Each 15 min, 1 ml of the
solution was separated using a 0.22 μm membrane filter and
the tetracycline concentration was measured.
Table 1 XRF results for raw
and modified zeolites
13
FESEM (TESCAN MIRA III), XRD (Philips PW 1730),
XRF (Philips PW 1410), BET (BELSORP MINI II) and
FTIR (Thermo AVATAR) analyses were performed for
characterization of the sorbents. The XRD analysis was
performed using the Philips PW 1730 instrument at an
angle between 10 and 80 degrees. A glass tube with 20 mm
diameter and 130 mm height was used for removal of tetracycline at continuous conditions. The tetracycline solution (200 ppm) was delivered using a perist (...truncated)