Journal of Environmental Treatment Techniques

2020, Volume 8, Issue 3, Pages: 936-946

J. Environ. Treat. Tech.

ISSN: 2309-1185

Journal web link: http://www.jett.dormaj.com

Nano Bioremediation of Textile Dye Effluent

using Magnetite Nanoparticles Encapsulated

Alginate Beads

A. Lincy *, P. Jegathambal , Martin Mkandawire , Stephanie MacQuarrie

Water Institute, Karunya Institute of Technology and Sciences, Coimbatore, India

Department of Chemistry, Cape Breton University, Nova Scotia, Canada

Received: 02/05/2020

Accepted: 12/06/2020

Published: 20/09/2020

Abstract

Due to increase in urbanization and industrialization, both water consumption and wastewater generation are high. It is a great

challenge to treat and provide safe water to the society. The conventional treatment methods are energy and cost intensive. These

limitations can be subsided by the application of nanotechnology that shows better efficiency in terms of treatment of wastewater.

The use of nanoparticles increases the adsorption of dye and removal efficiency due to their smaller size and increased Surface to

Volume (S/V) ratio. In this paper, magnetite nanoparticles were synthesized using Reverse Co-Precipitation method and their textile

dye removal efficiency using adsorption was studied in treatment of blue dye water. The synthesized magnetite nanoparticles were

qualitatively and quantitively characterized by Fourier Transform Infrared Spectroscopy (FTIR), Field Emission Scanning Electron

Microscopy (FESEM), UV-Vis Spectroscopy and Cyclic Voltammetry (CV). The observed continuous absorption spectral band

by FTIR and UV-Vis spectrum confirmed the formation of magnetite nanoparticles. The magnetite nanoparticles observed in

FESEM exhibited spherical shape with size of 60-100nm. The specific capacitance of the magnetics nanoparticles observed through

CV was 1828.5mA/g. The dye adsorption potential of magnetite nanoparticles was studied by conducting experiments on the

encapsulated alginate magnetic nanoparticles beads by varying operational parameters like contact time, pH, adsorbent dosage and

dye concentration. From the results, 82.4% removal of azo blue dye was observed with the initial dye concentration of 25 ppm.

Finally, the operational parameters were optimized based on maximum removal of blue dye.

Keywords: Nanotechnology, Magnetite, Beads, Adsorption, Blue dye

Introduction¹

the penetration of sunlight and oxygen which is more

essential for the survival of more aquatic forms. Textile

industries utilize substantial volume of water and chemicals

for wet-processing of textiles. There are nearly 8,000

chemical products associated with the dyeing process. So,

viable techno economical solutions are needed for treating

such types of wastewater. The eco-friendly and

economically adoptable wastewater remediation using

nanotechnology is one of the current areas of focus. Nano

bioremediation is a new emerging technique which employs

nanoparticles to clean up the environment and it removes the

pollutants and dyes efficiently. Numerous researches across

the globe are ongoing in green nanotechnology related to the

synthesis of nanoparticles using microorganisms. The

alternatives for conventional method of synthesis have been

modified with various biological entities and are being

Water is the basic necessity on earth for the human and

providing the clean water to society is of prime importance

for their better well-being. Water is highly contaminated due

to pollution, high population, amplification of industry and

textile effluents which lead to life time undermining

sicknesses[1]. The water consuming industries like paper

and pulp manufacturing, plastics, dyeing of cloth and

tanneries discharge a large amount of wastewater into the

soil and aquatic ecosystem. Few dyes are toxic in nature and

their presence in industrial effluents is of major

environmental concern because they are usually very

recalcitrant to microbial degradation. In some situations, the

dye solution will undergo anaerobic degradation and it will

form carcinogenic compounds that will end up in the food

chain [16]. Moreover, highly dyed wastewaters will block

Corresponding author: P. Jegathambal, Water Institute, Karunya Institute of Technology and Sciences, Coimbatore, India. E-

mail: jegatha@karunya.edu.

Journal of Environmental Treatment Techniques

2020, Volume 8, Issue 3, Pages: 936-946

employed in synthesis of nanoparticles [15]. The chemical

and biological substances can be detected and removed by

using nanoparticles, nanomembrane and nanocomposite

materials. To increase the adsorption capacity of

nanoparticles, biochar can be incorporated that improves the

surface area. The biochar can be prepared from any waste

source and it is of low costs, that can be used for wastewater

treatment and for soil amendment applications. It can be

prepared through pyrolysis process in an oxygen limited

environment. It has high porosity and stability and enables

the diffusion and adsorption of ions. The pH of biochar is

about 3.5-7, which has surface negative charge that prevents

biofouling on the surface of biochar [19].

There are numerous reasons to choose different Nano

Materials (NMs) to be used in bioremediation; for example,

when the material is reduced to nanoscale, surface area per

unit mass of a material increases; and a larger amount of the

material will come into contact with surrounding materials

that affects the reactivity. NMs show quantum confinement

effect and therefore it requires only less activation energy

that makes the chemical reactions feasible. The shape and

size of metallic and nonmetallic NMs are of great concern

while applying for contaminant removal. Various single

metal NPs, bimetallic NPs, carbon base NMs can be used

because (i) NPs can easily diffuse or penetrate into a

contamination zone because of their small size (ii) because

of their small size, they exhibit higher reactivity to redox-

amenable contaminants. [14]. Transition metal and metal

oxide-based cathode catalyst are economical and easy to

synthesize, thereby enhancing the performance of Microbial

Fuel Cells (MFC) [20].

fast reaction kinetics and magnetism ability for easy

recovery [2]. In recent days, numerous researches in

magnetite nanoparticles are ongoing in the field of

chemistry, medicine and social science, geology and

corrosion sciences (Figure 1). They are used for various

applications like sensors, superparamagnetic relaxometry

(SPMR), and MRI. The ferrofluid behaviour can be studied

and improved by conducting experiments related to fluid

stability, control of surfactants, particle sizes, materials, and

physical behaviour [3]. Due to colloidal nature of

nanoparticle, synthesis of nanoparticles to get

monodisperse uniform sized magnetic grains of approximate

size is a great challenge. Another important challenge is to

choose a simple technique which gives reproducible results

without any purification procedure. Generally, magnetite

nanoparticles can be prepared by various methods such as

co-precipitation, sol gel method, pechini method, emulsion

method, hydrothermal, solvothermal, biological method,

solid state synthesis and thermal decomposition method.

Nanoparticles with homogeneous composition and narrow

size distribution can also be synthesized by various

techniques

ultracentrifugation,

size-exclusion

chromatography, magnetic filtration etc.. Though there are

several methods available for synthesis, the most preferred

method used for the preparation of magnetite nanoparticles

is coprecipitation method.

2.2 Coprecipitation method

The simplest and efficient method to prepare magnetite

3 4 2 3

(either Fe O or γFe O NPs) is through co-precipitation

techniques. They are synthesized by taking the mixture of

ferrous and ferric salts in the ratio of 1:2 in aqueous medium.

The stoichiometric equation for formation of Fe

by the following:

is given

Fe²⁺+ 8OH + 2 Fe³⁺→ Fe

O + 4H O

3 4 2

(1)

According to thermodynamics, complete precipitation of

3 4

Fe O is expected to occur at pH between 8 and 14, with a

molar composition of 2:1 (Fe /Fe ) in a non-oxidizing

oxygen environment. In the presence of oxygen, Magnetite

can be converted into maghemite (γFe O ).

2 3

+2H⁺→ γFe +Fe²⁺+H

(2)

The main advantage is that a huge quantity of

nanoparticles can be obtained by using coprecipitation

process. Since the growth of crystals is controlled by

kinetics, the particle size distribution is a limiting factor.

Magnetite NPs are synthesized in two stages that occur in

coprecipitation process: In first stage, the species

concentration has to reach critical supersaturation thereby

causing a short burst of nucleation and because of that

minimum growth of the nuclei followed by solute diffusion

at the surface of the crystal is observed. In order to prepare

uniform size iron oxide nanoparticles, these above two

stages should be segregated; i.e., growth period can be

obtained during nucleation [4]. Though co-precipitation

Figure 1: Application of NMs in bioremediation

Synthesis of magnetite nanoparticles

.1 Nano iron and its Derivatives in Bioremediation

Iron nanoparticles, also called as nano zero-valent iron

(

nZVI). namely Magnetite (Fe

) and Maghemite (γ-

2 3

O ) are effectively used in environmental remediation

due to their high pollutant removal capacity. It also exhibits

Journal of Environmental Treatment Techniques

2020, Volume 8, Issue 3, Pages: 936-946

technique is simple and efficient, it has certain limitations,

such as insufficient dispersion, broad and uncontrollable

particle size distribution, difficulty of mass production [5].

To overcome these flaws, PCA–PEG–PCA polymers can be

surface potential (Tomohiro et.al) [11]. A novel synthetic

magnetite nanoparticles (nFe O ) was synthesized using co-

3 4

precipitation method at room temperature in controlled

atmosphere. The adsorption properties for As and Cu were

studied and compared to those of a commercial analogous

3 4

used to synthesize the uniform-sized Fe O particles to

modify the classical coprecipitation technique and high

magnetic response of Fe NPs. The size of the Fe NPs

3 4

material (nFe O ) at a pH value of 5. The degree of removal

of inorganic pollutants was found to be in the pH range of

3.0 to 8.0. In another study, ferrous chloride tetrahydrate and

ferric chloride hexahydrate were used as precursors to

synthesize magnetite NPs. The synthesized particles showed

a magnetite crystal structure with grain size of around 12

produced by this copolymer was found to be 5–10 nm and it

was smaller than the traditional method of preparation of

magnetite. The purpose of PCA–PEG–PCA was to provide

steric repulsion and improve the quality of the dispersion of

particles [6]. The magnetite nanoparticle prepared by this

method has good biocompatibility, good economic aspects,

and good magnetic quality (Zohre et.al) [6]. In another

−1

(±0.2) nm. The surface area was found to be 100.52 m g

and average pore size of the synthesized magnetite (nFe O )

nanoparticles were 24.40 nm. On the other hand, the BET

surface area and average pore size of the commercial Fe

method, ferrous (Fe ) and ferric (Fe ) ions were used along

with a base such as NaOH (or) NH .H O in an aqueous

solution. Using thermal decomposition of alkaline solution

3 4

particles were 6.81 m /gand 14.96 nm, respectively (Iconaru

et.al) [12]. A new method was proposed to prepare magnetic

of Fe chelate in the presence of hydrazine and by sono-

chemical decomposition of hydrolyzed Fe(II) salt followed

by thermal treatment, the magnetite nanoparticles were

synthesized. The disadvantage of these aqueous solution

synthesis is that pH value of the reaction mixture in both the

synthesis and purification steps was to be adjusted and the

process produced smaller (<20 nm) monodisperse

nanoparticles. Organic solution-phase decomposition of the

iron precursor at high temperature has also been widely used

to synthesis magnetite NPs. Recent advanced studies have

chitosan/Fe

composite nanoparticles by insitu in

microreactors which consists of tiny water pools with water-

in-oil emulsion. Once, the emulsion solution containing

chitosan and ferrous salt was added into NaOH base

3 4

solution, Fe O and chitosan nanoparticles were precipitated

from the system. The magnetic iron oxide nanoparticles

produced by this method were encapsulated with chitosan

nanoparticles. The magnetic chitosan nanoparticles size

produced by this method was found to be between 10 to 80

nm according to the different molecular weight of chitosan

(Jia et.al) [13].

In this study, three different magnetite NPs were

synthesized using co-precipitation method. After analyzing

the characteristics of the synthesized NPs, the adsorption

studies were carried out to evaluate the performance of

synthesized adsorbents in removal of textile dyeing effluent

by converting them into encapsulated alginate bead.

demonstrated that high quality monodisperse Fe

nanoparticle can be synthesized by direct decomposition of

Fe (CO) followed by oxidation. For the first time, the

synthesis of monodisperse Fe nanoparticles with sizes

below 20 nm has been reported in this article [7].

2 3

The synthesized Fe

adsorption. The Fe

have been widely used for dye

nanoparticles was preferred as

adsorbent material for dye removal by a simple magnetic

separation process. The optimum adsorption was achieved at

initial concentration of about 100 mg /L for procion dye and

for pH 6 and dosage of0.8 g L and contact time 30 minutes

and its adsorption capacity was found to be 30.503 mg/ g

Materials and methods

.1 Chemicals and Materials

3 4

All the reagents used for the synthesis Fe O were of

analytical grade and used without further purification. Ferric

chloride [FeCl ], ferrous sulphate [FeSO4. 7 H O], sodium

hydroxide [NaOH] were purchased from Merck.

(Podeji et.al) [8]. The usage of ferrous sulphate as choice of

iron precursor and ammonium hydroxide to be used as

precipitating agent [9]. The experiment was carried out

without any surfactant.

.2 Synthesis and Characterization of Magnetite

Nanoparticles

.2.1 Synthesis of Fe

In this study, Fe

The carboxylic group is naturally found in animal fats

and it can be used as the coating agent for the magnetite.

Oleic acid has been reported as a good surfactant for water

proof properties and the hexanoic acid was selected to study

the effect on the chain length of coating agent and compared

with oleic acid. The magnetite nanoparticles synthesized was

found to be about 10–40 nm and they showed different

electrical and magnetic properties (Petcharoen et.al) [10].

The high crystalline magnetite nanoparticles were

synthesized using facile single-step coprecipitation method

without any organic solvents. The particle size varied with

the coexisting anions and the surface potential of anions-

adsorbed precipitates. The coexisting anions led to the

3 4

O nanoparticles were synthesized in

four different routes. The protocol for preparation of

magnetite nanoparticles was as follows:

.2.1.1 Synthesis of Magnetite Nanoparticles using

Ferrous sulphate

Iron oxide nanoparticles were prepared using ferrous

sulphate by Reverse Co-precipitation method. In a 250mL

beaker, distilled water of about 50mL was taken, followed

by addition of Ammonium hydroxide solution of about

3 4

formation of finer Fe O nanoparticles in the increased order,

corresponding to the stability of iron complex and the

0mL (25% solution. The pH of the base solution was found

to be 13. In a separate 250mL beaker, iron salt precursor

Journal of Environmental Treatment Techniques

2020, Volume 8, Issue 3, Pages: 936-946

(

Ferrous sulphate) of concentration 0.8M was prepared. The

micropipette. The electrolyte solution was prepared by

dissolving 28.055g of KOH pellets in 500mL water. The

applied potential in working electrode, was varied in both

forward and reverse direction and the current was observed

for the variation. This technique consists of both linear and

a cyclic variation of electrode potential between the working

and reference electrodes within a potential window by

measuring the flowing current between working and counter

electrodes. The potentio dynamic electrochemical

measurement was done by repeating the cycle. The gives the

plot of Current Vs Applied potential. Thus, the redox

potential and electrochemical reaction rates can be obtained

through CV results. In this study, the specific capacitance of

the synthesized magnetite nanoparticles and nanocomposites

was carried out. Specific capacitance can be calculated by

.8M ferrous sulphate solution was added to NH OH base

solution. The solution was allowed to mix for 1 hour and

washed immediately. Finally, the obtained black solution

was washed repeatedly with deionized water and kept for

drying at 50 º c overnight.

.2.1.2 Synthesis of Magnetite nanoparticles using Ferrous

sulphate + Biochar

Iron oxide nanoparticles were prepared using ferric

chloride and ferrous sulphate by Reverse Co-precipitation

method. Biochar was prepared from sugarcane bagasse by

adopting the following steps: The sugarcane waste was

collected and was cut into small pieces. After washing with

distilled water for 4-5 times, the sample was kept for drying.

After drying, it was grinded well and made it as fine powder.

Sugarcane bagasse was kept in muffle furnace at 450 º c and

made it into biochar under pyrolysis.

To the prepared 0.8M ferrous sulphate solution as given

in 3.B.1.1, 2g of biochar was added and stirred for 15 mins

and after that ultrasonic mixing was done for about 10 mins.

The 0.8M ferrous sulphate solution with biochar was added

using the formula as follows, Specific Capacitance = I

2× Scan rate/ Mass of sample; where, I - Anodic current and

– Cathodic current.

The FTIR spectrum is mainly used to find the functional

– IC /

groups present in the sample. It gives the information about

sample absorption of light at each wavelength. The range of

Infrared region is 12800 ~ 10 cm and it can be divided into

-1

three regions such as near-IR region (12800 - 4000 cm ),

-1

to NH

OH base solution. The solution was allowed to mix

for 1 hour and washed immediately. Finally, black solution

was obtained and it was washed repeatedly with deionized

water and kept for drying at 50 º c overnight.

mid-IR region (4000 - 200 cm ) and far-IR region (50 - 1000

-1

cm ). To do FTIR analysis, 1% of sample powder was

mixed with 99% KBr and were made into pellet by 5mpa/

torr with 3mm diameter. The infrared absorption

spectroscopy will analyze the sample in region between

.2.1.3 Synthesis of Magnetite nanoparticles using Ferrous

sulphate + Graphite + Biochar

4000-400cm because organic compounds and inorganic

ions have absorption radiation in this range. The functional

groups present in magnetite nanoparticles can be interpreted

from FTIR analysis.

Iron oxide nanoparticles were prepared using ferrous

sulphate, biochar and graphite by reverse co-precipitation

method. To the prepared 0.8M ferrous sulphate solution, 5g

of biochar and 5g of graphite were added and stirred for 15

mins and after that ultrasonic mixing was done for about 10

The UV- Vis spectroscopy which was used to

characterize the sample works on the principle of Beer-

Lambert law. In this light of wavelength between 300-

800nm was allowed to pass and the absorbance of the analyte

at certain wavelength and appropriate peak are detected. It

can be used to characterize transition metals and organic

compounds.

mins. The prepared mixture was added to NH OH base

solution. The solution was allowed to mix for 1 hour and

washed immediately. Finally, the obtained black solution

was washed repeatedly with deionized water and kept for

drying at 50 º c overnight.

.3 Characterization of Prepared Magnetite

The characterization of prepared

3.4 Beads Preparation

magnetite

Magnetite nanoparticles prepared by reverse co-

precipitation method was encapsulated in the form of beads

using sodium alginate. The steps for the preparation of beads

were as follows: About 2g of sample was added into 2%

sodium alginate solution and allowed to stir for about 1hr

until it becomes like a gel. About 3% calcium chloride

solution was prepared separately in a beaker. The prepared

sodium alginate mixture with sample was transferred to

separating funnel and allowed to fall into the calcium

chloride solution drop by drop till the beads were formed.

The beads were left in calcium chloride solution under

stirring for 24hrs. The beads were washed with distilled

water for 3-4 times and stored in refrigerator (Figure 2).

nanoparticles was done using UV-Vis Spectroscopy (UV-

Vis), Cyclic Voltammetry (CV), Fourier Infrared

Spectroscopy (FTIR) and Field Scanning Electron

Microscope (FESEM).

Cyclic Voltammetry (CV) was used to study the redox

process in the cell. The electrocatalytic behaviour of

Magnetite nanoparticles prepared from different source of

materials was studied using cyclic voltametric technique.

The electrochemical setup consists of three electrode setups.

It consists of Glassy Carbon electrode (GCE) as working

electrode in 0.1M KOH solution as electrolyte with Platinum

(Pt) as reference electrode and Silver Chloride (AgCl) as

counter electrode. CV were recorded in a three-electrode

system. Working electrode was prepared by dispersing 1mg

of sample in 10µl of ethanol in a vial. The prepared sample

was drop casted on the Glassy Carbon electrode using

Journal of Environmental Treatment Techniques

2020, Volume 8, Issue 3, Pages: 936-946

Results and discussion

.1 Characterization techniques

The crystallographic information of the prepared

magnetite nanoparticles were characterized by using Cyclic

Voltammetry (CV), Fourier Transform Infrared

Spectroscopy (FTIR), Field Emission Scanning Electron

Microscope (FESEM) and UV- Vis.

.1.1 Cyclic voltammetry

The voltage range was from +0.5V to -0.5V and scan

rate was 10mV/ S was used in CV experiments. From these

above values, it was concluded that Ferrous Sulphate+

Graphite+ Biochar composite had higher specific

capacitance value, leading to the higher removal efficiency

(Table 1).

Table 1: Specific capacitance of nano-biochar composite

(a)

Ferrous

Sulphate+

Biochar

Ferrous

sulphate

Sulphate+

Graphite+

Biochar

Scan rate

mV/S)

(

F/g)

(

F/g)

(

F/g)

0.765

0.117

1.828

.1.2 UV-Visible spectrophotometer

The transition metals have unique colour characteristics

and they respond to corresponding peaks. When the samples

were analysed in UV-Vis (Figure 3), organic compounds

differed by their bond structure and functional group. From

UV- Vis spectroscopy, we infer that peak around 200-

00nm was due to presence of carbon in the sample. Peak

around 400- 480nm confers the formation of β Fe O

formation. The Magnetite nanoparticle display SPR band at

09 nm [19].

(b)

Figure 3: UV spectra of the NPs prepared using Ferrous Sulphate

(c)

Figure: 2: Prepared Magnetite Beads a) using Ferrous Sulphate b)

using Ferrous Sulphate + Biochar and c) using Ferrous Sulphate +

Biochar + Graphite

.1.3 Fourier transform infrared spectroscopy (ftir)

The FTIR spectrum confirmed the presence of magnetite

nanoparticles in the spectral range between 400 and 4000

-1

cm . The peak at 3433 cm corresponds to stretching

vibration of hydroxyl (O-H) group on the surface. 1745 cm

Journal of Environmental Treatment Techniques

2020, Volume 8, Issue 3, Pages: 936-946

corresponds to carbonyl stretching vibration, peak at 1444

cm corresponds to CH

cm corresponds to Fe-O bond stretching vibration. The

bands in the peak range between 400 and 750 cm

corresponds to the stretching vibration of Fe-O band excited

from γFe (Table 2). The observed vibration bands at low

bending vibrations. The peak at

161 cm corresponds to C-N bending vibrations and 588

frequencies indicates the formation of magnetite

nanoparticles [17].

Table 2: UV-Vis Spectrum - NPs using Ferrous Sulphate

Peak

Position

Spectrum

Description

Carbon peak

Remnants of collective

oscillation of SPR

band

UV- Vis

Figure 5: Ferrous Sulphate + Biochar + Graphite

Formation of

Magnetite

Excited peak of Fe-O

Table 5: FTIR Spectrum - using Ferrous Sulphate

Spectrum Peak Position Description

433

OH- Stretching vibration

Carbonyl stretching

vibration

Table 4: UV-Vis Spectrum – NPs using Ferrous Sulphate

Biochar

Spectrum Peak Position Description

1745

444

161

CH bending vibrations

Aliphatic C-N bending

vibrations

FTIR

Carbon peak

Remnants of collective

oscillation of SPR band

Fe-O stretches

Fe-O bond stretching

vibration

UV- Vis

338

Excited peak of Fe-O

Table 4: UV-Vis Spectrum - NPs using Ferrous Sulphate+

Biochar + Graphite

Spectrum Peak Position Description

UV- Vis

212

Carbon peak

Formation of Magnetite

Excited peak of Fe-O

Figure 6: FTIR Spectra of Ferrous Sulphate

Table 6: FTIR Spectrum - using Ferrous Sulphate

Biochar

Spectrum Peak Position Description

414

618

OH- Stretching vibration

NH stretching vibration

Fe-O bond stretching

vibration

FTIR

Fe-O Stretches

Figure 3: Ferrous Sulphate + Biochar

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2020, Volume 8, Issue 3, Pages: 936-946

Figure 7: FTIR Spectra of Ferrous Sulphate + Biochar

Figure 8: FTIR Spectra of Ferrous Sulphate + Biochar + Graphite

Table 7: FTIR Spectrum – using Ferrous Sulphate

+Biochar + Graphite

Spectrum Peak Position Description

431

764

OH -Stretching vibration

C-OO Symmetric

Fe-O bond stretching

vibration

FTIR

Fe-O stretching of

Magnetite

Fe -O stretches

The presence of magnetite nanoparticles was confirmed

from FTIR spectrum in the range between 400 and 4000

cm and at low frequencies (Figure 7). The peak at 3414 cm

Particle size: 60-100

corresponds to stretching vibration of hydroxyl (O-H)

group on the surface; 1618 cm corresponds to NH

stretching vibration; peak at 615 cm corresponds to Fe-O

bond stretching vibration and peak at 472 cm corresponds

to Fe-O stretches. The bands in the peak range between 400-

Figure 9: FESEM image of synthesized magnetic nanoparticles

50 cm corresponds to the stretching vibration of Fe-O

band excited from γFe (Table 2-7).

The peak at 3431 cm corresponds to stretching

vibration of hydroxyl (O-H) group on the surface. 1764

cm corresponds to C-OO Symmetric vibrations, peak at

-1

28cm corresponds to Fe-O bond stretching vibration, peak

-1 -1

at 534 cm and 460 cm corresponds to Fe-O bond

stretching vibration [18].

(

.1.4 Field Emission Scanning Electron Microscopy

FESEM)

The FESEM analysis depicts topographical and

elemental information at magnification 10x to 3,00,000x

with unlimited depth of field (DOP). Comparing to SEM,

FESEM gives clearer and higher resolution images. The

picture quality was three to six times better than SEM.

FESEM provides advanced coating and structure uniformity

determination. FESEM can examine even small surface very

clearly.

Figure 10: EDAX of Prepared Magnetite Sample

From FESEM images (Figure 9), it was observed that the

size of nanoparticles synthesized was about 60-100 nm. The

particles were well dispersed and were in spherical shape.

Journal of Environmental Treatment Techniques

2020, Volume 8, Issue 3, Pages: 936-946

Similar size and shape (Figure 11) were obtained in the work

carried on magnetite nanoparticles out by Rabel et al. [17].

Sodium alginate is a natural polysaccharide extracted

from brown seaweeds. This linear polymer was made up of

beta-D-mannuronate (M) and it has cellulose like structure

and alpha-L-guluronate (G) units were linked by beta-1,4

and alpha-1,4 glycosidic bonds. Here alginate beads were

used as a carrier material and it shows the possibility of

selective adsorption of organic molecules, depending on

their electrical charge which occurs due to chemical

interaction with the negatively charged carboxylate groups

on alginate. It undergoes a sol–gel transition in the presence

of multivalent cations because of the presence of carboxylate

groups in polymer and specifically with calcium ions. Due

to the presence of carboxylate groups on this polysaccharide,

they are negatively charged in neutral and alkaline media and

they exhibit greater affinity to cations. Because of presence

of various ligands such as hydroxyl and carboxyl functional

groups on its backbone, magnetite alginate beads were

considered as a potential adsorbent material for the removal

of textile blue dyes.

Figure 11: FESEM image of magnetite nanoparticles [17]

From EDAX result of ironoxide - Biochar- graphite

sample as given in Figure 10 and Table 8, the presence of

carbon, iron and oxygen in the synthesized sample

confirmed the the formation of magnetite nanoparticles.

Time Vs Removal Efficiency

Table 8: EDAX Result of Prepared Magnetite

Element

Carbon

Oxygen

Iron

Magnesium

Aluminium

Chlorine

Atomic Weight percentage

78.69

16.74

4.48

0.03

0.05

0.01

Time (hrs)

.2 Batch Adsorption Study

The stock solution was prepared by dissolving 0.01g of

Ferrous

Ferrous+Biochar

Ferrous+Biochar+ Graphite

blue dye in 100mL of distilled water. The adsorbent material

magnetite nanoparticles were incorporated into alginate

beads in order to increase the removal efficiency and to avoid

agglomeration effect. Batch adsorption equilibrium

experiments were performed by taking 100mL of dye water

and 25g of adsorbent in each 250mL conical flask. Two

different types of adsorbents were taken to carry out the

experiment. The performance of both iron oxide-biochar

encapsulated beads and iron oxide - biochar - graphite

encapsulated beads in removing the textile dye was

evaluation using adsorption experiments. After adsorption,

the adsorbents was separated by filtration and the filtrate dye

solutions were analyzed by measuring absorbance at 648nm

respectively for blue dye in UV- Visible Spectrophotometer.

To select the efficient adsorbent among three, the batch

experiments were conducted to study the colour removal

efficiency at different time interval (contact time). The

percentage of removal can be calculated by using the

equation: %Removal efficiency = Original absorbance –

Final absorbance / Original absorbance * 100

Figure 12: Removal efficiency of different adsorbents

During adsorption, the dye molecules migrate from the

bulk solution to the surface area of the nanoparticles

encapsulated in the beads, through external mass transfer

(

film diffusion), which is referred as instantaneous

adsorption stage. Then due to intra-particle diffusion,

gradual adsorption takes place but is rate limiting one. Thus,

the textile blue dye molecules get transported to the external

surface of the magnetite beads through film diffusion

process. Through the process of chemical adsorption on the

functional groups of the beads, chromophore group of textile

dye (N=N) was broken and resulted in removal of dye.

This experiment was conducted using three above

mentioned adsorbents. The contact time was varied for

1hrs. It was noticed that the rate of blue dye removal was

very slow at the beginning of film diffusion. After that, the

rate of adsorption gradually increased. From batch study, it

was observed that the removal of textile blue dye increased

Journal of Environmental Treatment Techniques

2020, Volume 8, Issue 3, Pages: 936-946

with increase in contact time till it reached the saturation.

The maximum dye removal efficiency was achieved after 20

hours of contact time, by Ferrous sulphate beads, Ferrous

sulphate+ Biochar beads and Ferrous sulphate + Biochar-

Graphite beads were 34.02%, 48.54% and 55.88% for

respectively (Figure 12). There was gradual increase in

adsorption capacity from 15 hours to 20hours. Due to low

adsorbent dosage (5 gm in 100 ppm dye solution), the

removal efficiency was less. From above values, it was

concluded that, iron oxide+ biochar+ graphite composite

showed higher removal and the performance of the same was

observed at other operational parameters.

prepared such as 25ppm, 50ppm, 75ppm, 100ppm, 125ppm

and 150ppm. The equilibrium time was fixed as 3hrs as it

was observed from contact time study. The pH was set as 8

as it was observed from pH study. The adsorption capacity

of textile blue dye decreases with increasing blue dye

concentration. This was due to the fact that at higher

concentration, the ratio of the initial number of MB

molecules to the surface area was very low and results in low

adsorption capacity. At lower dye concentration, surface

molecules get completely adsorbed on the dye molecules and

results in higher adsorption. The adsorption was independent

of initial concentration (Figure 15).

.2.1 Effect of pH

The effect of pH (2-11) on the adsorption of MB onto

Removal Efficiency (%) Vs Time (min)

magnetite beads was carried out. Ten different pH of dye was

prepared such as 2,3,4,5,6,7,8,9,10 and11. The equilibrium

time was fixed as 3hrs as it was observed from contact time

study. In this, pH- 8 shows highest removal. pH of original

textile blue dye was about 6-6.5. At low pH, surface charge

was negatively charged, H ions compete effectively with

dye cations causing a decrease in the amount of adsorbed dye

in acidic pH (Figure 13).

100

200

300

400

Time (min)

Figure 14: Effect of Contact time plot

pH Vs Removal Efficiency

Figure 13: Effect of pH plot

Dye Concentration Vs Removal

Efficiency

.2.2 Effect of Contact time

From Figure. 14, it was observed that the efficiency of

removal of dye by the nanocomposite adsorbent was 55.88%

after 21 hours, when the quantity was 5 gm. To achieve the

same efficiency at the reduced contact time, the experiments

were conducted for about 3 hours by increasing the

adsorbent concentration to 25 gm. From the results, it was

observed that the adsorption process was over after 6hrs and

the removal efficiency started reducing from 4rth hour. The

maximum removal efficiency of 55.22% was achieved at

Dye Concentration(ppm)

Figure 15: Effect of Dye Concentration Plot

100

150

200

.2.4 Effect of Adsorbent Dosage

The effect of adsorbent dosage (10–50gms) on the

adsorption of MB onto Magnetite beads was carried out.

Five different adsorbent dosage was chosen such as 10, 20,

0, 40 and 50gm. The equilibrium time was fixed as 3hrs as

it was observed from contact time study. The pH was set as

as it was observed from pH study. The dye concentration

hrs, for Ferrous sulphate + Biochar- Graphite beads for

00ppm of dye for 25g of Magnetite. So, the equilibrium

time was optimized as 3hours to carry out the other

experiments.

was set as 25ppm as it was observed from Dye concentration

study. The adsorption capacity of blue dye increases with

increasing adsorbent dosage. This is due to the fact that at

higher adsorbent, the available number of active sites will be

.2.3 Effect of Dye Concentration

The effect of initial Methylene blue dye concentration

(25–150ppm) on the adsorption of MB onto magnetite beads

was carried out. Six different concentration of dye was

Journal of Environmental Treatment Techniques

2020, Volume 8, Issue 3, Pages: 936-946

more and it leads to more uptake of dye molecules (Figure

Authors’ contribution

6.).

All authors of this study have a complete contribution

for data collection, data analyses and manuscript writing.

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