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Rucha Deshpande et al Int. Journal of Engineering Research and Applications
ISSN : 2248-9622, Vol. 3, Issue 6, Nov-Dec 2013, pp.730-734

RESEARCH ARTICLE

www.ijera.com

OPEN ACCESS

Synthesis & Effectiveness Study Of Banana Peel Adsorbent &
Artificial Neural Network Modeling In Removal Of Cu (II) Ions
From Aqueous Solution
Shekhar Pandharipande *, Rucha Deshpande**
*(Associate Professor, Department of Chemical Engineering , RTM Nagpur University, Nagpur-33)
** (B.Tech ( Chemical Engineering) , RTM Nagpur University, Nagpur)
ABSTRACT
Release of poisonous and harmful gases in the open air and of untreated polluted water to fresh water bodies has
made the environmental conditions severe. Presence of excessive heavy metals like copper is found to damage
not only fishes but humans also through the food cycle. The present work aims to synthesize an effective
adsorbent from Banana peels, a material readily available by chemical treatment. The adsorbent synthesized is
employed in removal of copper ions from waste water & is observed to be effective in removal of 12% to
89.47% of copper for adsorbent dosage varied between 0.5gm to 2 gm. Conventional adsorption isotherms have
been estimated to describe the adsorption process & efforts have been made to develop Artificial Neural
Network models for the same. It can be concluded that there is a lot of potential in Banana peel adsorbent that
need to be tapped.
Keywords – Artificial Neural Network, Banana Peel Adsorbent, Copper Sulphate, Wastewater treatment, Percent adsorption

I.

INTRODUCTION

Today, the environment is mainly affected by
air and water pollution. Release of poisonous and
harmful gases in the open air and of untreated polluted
water to fresh water bodies has made the
environmental conditions severe. In order to sustain
the healthy surroundings, it is essential for all the
industries contributing to the pollution to treat the
generated wastes before discharging the effluent
streams. This includes discharge of pollutant gases
even from low ppm level to elevated heights.
Discharge of treated water to water bodies is essential
to ensure the safety of the marine life.
Presence of excessive heavy metals like
copper is found to damage the marine life since it
affects the gills, liver, nervous system of the fishes &
the problems are transferred to the humans through the
food cycle. Existence of copper in drinking water may
cause mucosal irritation, hepatic and renal damage,
capillary damage, gastrointestinal irritation and central
nervous problem in humans. Several research articles
have highlighted about the utilization of activated
carbon for the removal of the heavy metals from
wastewater [1]. The overall cost of the treatment
process increases as the adsorbent cost goes on
increasing. There is a need for development of
efficient, low cost, economical alternative to activated
carbon and other costly adsorbents.
The present work addresses to exploring the
possibility of synthesizing an effective adsorbent from
Banana peels, a material readily available [2]. The
peel is characterized by a heterogeneous, rough and
porous surface with crater like pores that helps to its
possible use as an adsorbent. The effectiveness of the
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adsorbent synthesized is determined in removal of
copper ions from waste water. Conventional
adsorption isotherms have been employed to describe
the adsorption process[3] & efforts have been made to
develop Artificial Neural Network models for the
same.
Artificial neural network is a paradigm in
itself that is inspired by the functioning of biological
neural networks. ANN is viewed as a black box
modeling tool & has been applied by researchers in
several chemical processes for various purposes such
as prediction of parameters, modeling of complex
nonlinear multivariable relationships, in fault
detection & diagnostics & in control, as among others.
There are several types of artificial neural network &
error back propagation (EBP) is common for modeling
applications. Each layer has a number of processing
elements called as neurons or nodes and it is decided
by the number of input & output parameters that are to
be correlated. The output from each neuron in the
input layer is altered by a multiplication factor or
weight and every node in the next layer receives the
summation of the product of the outputs of all the
nodes from the preceding layer. The resulting signal
received by the node is transformed further by using
functions like sigmoid & the resulting signal acts as an
input for the nodes in the next layer. Training of EBP
is essential & the algorithm suggested by Rummelhart
is popular for this purpose.

II.

MATERIALS AND METHODS

2.1 Banana peel as an adsorbent
In the present work chemically treated and
dried banana peel adsorbent has been synthesized and
730 | P a g e
Rucha Deshpande et al Int. Journal of Engineering Research and Applications
ISSN : 2248-9622, Vol. 3, Issue 6, Nov-Dec 2013, pp.730-734
is
employed
in
the
adsorption
studies
experimentations.
The banana peels are oven dried at 1000C and
screened to determine the particle size. The particulate
matter is treated with Sodium hydroxide pellets in hot
distilled water. Similar procedure is adopted with
oxalic acid. The treated peels are washed with hot
distilled water for the removal of the adhered
chemicals on the surface [4]. Dried banana peel
adsorbent samples are stored in air tight container for
further adsorption studies [5]. The details of
consolidated observation in the Banana peel adsorbent
synthesis are given in TABLE 1.
Table 1. Observations in the synthesis of Banana peel
adsorbent
S Initial
Final
Wate
Drying Perce
r. weight of weig
r
temper nt
n banana
ht of remo
ature
yield
o peels
peels
ved
(O C)
(gm)
(gm)
(gm)
180.3
6.8
100 14.86
1
153.5
2.2 Methodology
The first part of the present work deals with
the standardization of the digital colorimeter by
correlating the optical density of the samples of
aqueous solution and the known concentration of
copper sulphate. The ANN model is developed on the
data generated by conducting experiments in
determination of optical densities of the aqueous
solutions samples for known Cu(II) concentration. The
second part is related to the adsorption studies, using
the synthesized Banana peel adsorbent in removal of
Cu(II) from aqueous solution. This is carried out by
dosing a known volume and concentration of copper
sulphate solution with a known quantity of banana
peel adsorbent [6]. The solution is filtered after
ensuring that the equilibrium is reached the optical
density of the filtered solution is determined using a
digital colorimeter The optical density determined is
used for estimation of the concentration of the
solution by applying the ANN model developed. The
adsorption parameters like percent adsorption, amount
of adsorbate adsorbed per unit amount of adsorbent
are calculated with the help of equilibrium
concentrations of the Cu(II) estimated using the ANN
model.
The adsorption studies data generated is used
in developing ANN models to correlate the percentage
adsorption of Cu(II), equilibrium concentration of
adsorbate on adsorbent & amount of adsorbate
adsorbed per unit amount of adsorbent with the initial
concentration of Cu(II) in feed solution and adsorbent
dosing. In this study, elite-ANN© is used in
developing all ANN models [7].

III.

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RESULT AND DISCUSSION

3.1 Developing ANN model for standardization of
Digital colorimeter
The objective of this part of the present work
is to develop a ANN model for the standardization of
the digital colorimeter for the estimation of remaining
Cu(II) in aqueous solution after adsorption. The data
sets of input copper concentrations and the
corresponding optical densities obtained using digital
colorimeter is used to train the ANN model. Based on
the training the model predicts the concentration of the
solution after adsorption. There is one input parameter
as optical density and one output parameter as
concentration of Cu (II) ions (gm/ml).
Three different ANN models BS-30, BM-30, BC-30
having different topologies are developed for
standardization of colorimeter with 22 data points.
The details of the topology of ANN models
developed for the standardization of digital
colorimeter is given in TABLE 2. All the models
developed have good accuracy levels.
Table 2. Neural Network topology for standardization
of colorimeter
Number of Neurons
RMS
st
nd
rd
Mod Inp
E
1
2
3
Outp
el
traini
ut
Hidd hidd hidd
ut
ng
Lay
en
en
en
Laye
data
er
layer layer layer
r
Set
BS1
00
05
05
1
0.017
30
66
BM1
00
05
05
1
0.017
30
44
BC1
00
05
05
1
0.016
30
2
Number of Iterations= 30000;Input parameter: Optical
density of aqueous solution
Output parameter: Concentration of Cu(II) ions in
aqueous solution
Fig.1 shows a schematic for the typical neural network
architecture used in developing model BC-30.

Figure 1: Neural Network Architecture for ANN
model BC-30
Based on the values of RMSE, model BC-30
has been selected for the standardization of the
colorimeter for estimation of Cu(II) ions in aqueous

www.ijera.com

731 | P a g e
Rucha Deshpande et al Int. Journal of Engineering Research and Applications
ISSN : 2248-9622, Vol. 3, Issue 6, Nov-Dec 2013, pp.730-734
solution with the corresponding values of its optical
density.
Fig.2 & Fig. 3 show the graphs plotted between the
predicted values as obtained using ANN model BC-30
and the actual values of copper concentration in
aqueous solution samples for training and test data set
respectively.

www.ijera.com

Amount of adsorbate adsorbed per unit amount of
adsorbent = ((Initial concentration- Equilibrium
concentration) x Volume of solution)/ Amount of
adsorbent
TABLE 3 shows the details of the observations &
corresponding calculated values of percentage
adsorption of Cu (II) & amount of adsorbate adsorbed
per unit amount of adsorbent.

Concentration of Cu(II)
mg/ml

10
8
6
4

1th
Actual
output

2
0
1 4 7 10 13 16 19 22

Data point
number

Table 3: Adsorption terms calculated from equilibrium
Cu (II) concentration

1th
Predicte
d output

S
r,
N
o.

Concentration of Cu(II)
mg/ml

Figure 2 : Comparison of actual and predicted values
of Copper concentration for training data set using
model BC-30
6
5
4
3
2
1
0

1th
Actual
output
1th
Predicte
d
output

1

2

3

Data point
number

4

Figure 3: Comparison of actual and predicted value of
copper concentration for test data set using model
BC-30
From these graphs it can be seen that the
actual & predicted values are very close to each other.
ANN model BC-30 developed has higher accuracy of
prediction & is used for estimation of the equilibrium
concentration of Cu(II) ions in the solution samples
that are obtained during the adsorption studies. The
estimated values are further used for determining the
effectiveness of the synthesized adsorbent by
calculating adsorption terms such as percentage
adsorption and amount adsorbed per unit amount of
adsorbent.
Percentage adsorption of Cu(II) ions is evaluated as:
Percentage adsorption = (Initial concentrationEquilibrium concentration)/ Initial concentration x 100
[8]

www.ijera.com

1
2
3
4
5
6
7
8
9

Initial
copper
ion
concentr
ation
(mg/ml)

Adsor
bent
Dosa
ge

3.8175
3.8175
3.8175
4.581
4.581
4.581
6.108
6.108
6.108

0.5
1
2
0.5
1
2
0.5
1
1.2

(gm)

Copper
ion
concentr
ation
after
adsorpti
on
Ce
(mg/ml)

Perce
nt
adsor
ption

3.328
3.328
0.401
3.174
1.572
0.564
4.219
3.919
2.852

12.81
12.81
89.47
30.70
65.66
87.68
30.91
35.82
53.30

Amou
nt of
adsor
bate
adsor
bed
per
amou
nt of
adsor
bent
(mg/g
m)
24.45
12.22
42.69
70.32
75.20
50.21
94.40
54.70
67.83

3.2 Developing ANN models for adsorption studies
The objective of this part of present work is
to develop ANN model for adsorption studies
correlating the percentage adsorption of Cu (II) and
equilibrium concentrations of adsorbate, on adsorbent
& in aqueous solution for the known input parameters
such as initial concentration of Cu (II) & adsorbent
dosing. The data generated in adsorption studies of the
present work as given in TABLE 3 is used for this
purpose.
Three ANN models AS, AM and AC having
different topology as given in TABLE 4 are
developed. Fig. 4 shows a typical architecture of one
of the models AS developed.
All the ANN models developed in the present
work are using elite-ANN©. The snapshot of eliteANN© in run mode and the variation of error versus
iteration during training mode for developing “AM
model” are shown in Fig. 5 & Fig.6 respectively.

732 | P a g e
Rucha Deshpande et al Int. Journal of Engineering Research and Applications
ISSN : 2248-9622, Vol. 3, Issue 6, Nov-Dec 2013, pp.730-734

www.ijera.com

100
Series1

50

Series2

0
1 2 3 4 5 6 7 8 9

Figure 8: Comparison of actual and predicted values
of percentage adsorption
Figure 4: Neural Network architecture for ANN model
AM-50
ANN model AM-50 is selected because of its
lower RMSE value among the three models that are
developed & employed for estimating the equilibrium
concentration of the copper sulphate solution,
percentage adsorption and the amount of adsorbent
adsorbed per unit amount of the adsorbent.

100
50

Series1
Series2

0
1 2 3 4 5 6 7 8 9

Figure 9 : Comparison of actual and predicted values
of amount of adsorbent adsorbed per amount of
adsorbent adsorbed
The claim of accuracy is further substantiated
by calculation of the % relative error for each data
point for all the output parameters as given below:
% relative error = (actual value- predicted value)*
100/ (actual value)
Figure 5: Snapshot of elite-ANN© in run mode
5
0
Data points
-5

Figure 6: RMSE variation with iterations for training
data set for AM-50 model
Fig. 7, Fig. 8 & Fig. 9 show the graphs plotted for the
comparison of actual and predicted values of
equilibrium Cu(II) concentration, percent adsorption,
amount of adsorbate adsorbed per amount of
adsorbent respectively.
5
Series1

0
1 2 3 4 5 6 7 8 9

%
Relative
error

Figure 10 :% Relative error for equilibrium
concentration of Cu(II) between training data set and
that obtained by model AM-50
2
0
Data points
-2
-4
Figure 11: % Relative error for percent adsorbed of
Cu(II) between training data set and that obtained by
model AM-50

Series2

Figure 7: Comparison of actual and predicted values
of copper concentration after adsorption using model
AM-50

www.ijera.com

733 | P a g e
Rucha Deshpande et al Int. Journal of Engineering Research and Applications
ISSN : 2248-9622, Vol. 3, Issue 6, Nov-Dec 2013, pp.730-734

Table 4: Neural Network topology

Mod
el

In
p
ut
L
ay
er

Number of Neurons
1st
2nd
3rd
hid hid hidd
den de
en
laye
n
laye
r
lay
r
er

O
ut
pu
t
la
ye
r
3

RM
SE
trai
ning
data
Set

AS2
00
05
05
0.00
50
34
AM- 2
00
10
10
3
0.00
50
16
AC2
00
10
10
3
0.00
50
216
Number of Iterations= 50000
Input parameters: Initial Concentration
Cu(II) ions, adsorbent dosage
Output parameters: Equilibrium Conc. Of
Cu(II) ions, amount of adsorbate adsorbed
per unit amount of adsorbate adsorbed per
unit amount of adsorbent, % adsorption

and other costly adsorbents can be replaced with this
low cost effective adsorbent which is developed from
waste material. Further research can also be carried
out to study the effectiveness of Banana peel
adsorbent in removal of other metallic compounds
that are present in industrial waste water.

V.

REFERENCES
[1]

[2]

[3]

% relative error

0
Data points
-5

[5]

Figure 12: % Relative error for amount of Cu (II)
adsorbed er unit amount of adsorbent between training
data set and that obtained by model AM-50
[6]
As can be seen from Fig.10, Fig.11& Fig. 12;
the percent relative error for AM-50 ranges between 0
to 4%, 0 to 1.4%, 0 to 2.5% in estimation of
equilibrium concentration of Cu(II) ions, percent
adsorption and amount of adsorbate adsorbed per
amount of adsorbent respectively. Thus it can be said
that the ANN model AM-50 has high accuracy of
predictions & is acceptable.

[7]
[8]

IV.

CONCLUSION AND FUTURE SCOPE

The objective of the present work was to
explore the utilization of Banana peel adsorbent for
the removal of Copper (II) metal ions from aqueous
solution. Based on the adsorption studies it is
observed that the adsorbent was effective in removal
of 12% to 89.47% of copper for the adsorbent dosage
varying between 0.5gm to 2 gm [9]. The novel feature
of the present work is to develop ANN models in
adsorption studies having high accuracy levels.
There is a need for extending the laboratory
scale work to pilot plant scale so that activated carbon
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ACKNOWLEDGEMENTS

Authors are thankful to Director,L.I.T., for
providing infrastructural facilities and constant
encouragement.

[4]
5

www.ijera.com

[9]

D. Mohapatra, S. Mishra, N. Sutar Banana
and its byproduct utilization: an overview,
Journal of scientific and industrial research,
volume 69,pp 323-329,May 2010.[1]
G. Annadurai, R. Juang, , D. Lee, , Use of
cellulose based wastes for adsorption of dyes
from aqueous solutions, Journal of
hazardous materials, volume B92,pp 263274,2 . [2]
J. Memon, S.Memon ,
Bhanger , I
Muhammad Y. Khuhawar , Banana Peel: A
Green and Economical Sorbent for Cr(III)
Removal , Pak. J. Anal. Environ. Chem. Vol.
9, No. 1 (2008) 20 – 25[3].
W. Ngah wan, M. Hanafiah, , Removal of
heavy metal ions from wastewater by
chemically modified plant wastes as
adsorbents ,Bioresource technology, volume
99, pp 3935-3948, 2008.
A. Ashraf , A. Wajid, K. Mahmood , J.
Maah
J. Yusoff., Low cost biosorbent
banana peel (Musa sapientum) for the
removal of heavy metals , Scientific
Research and Essays Vol. 6(19), pp. 40554064, 8 September, 2011.[4]
M. Hossain, H. Ngo, W. Guo, and T.
Nguyen, Biosorption of cu (II) from water
by Banana peel based biosorbent:
experiments and models of adsorption and
desorption,
Journal
of
water
sustainability,volume 2,pp 87-104,March
2012.
S.Pandharipande, Y. Badhe, elite-ANN©.
2004; ROC No SW-1471 India.
S. Pandharipande, A. Deshmukh , Synthesis
, characterization and adsorption studies for
adsorbents synthesized from Aegel marmelos
shell for removal of Cr(VI) from aqueous
solution
, International journal of
Engineering research and applications, Vol.
2, Issue 4, July- August 2012, pp.1337-1341.
P. Velmurugan
, V. Rathina kumar, G.
Dhinakaran , Dye removal from aqueous
solution using low cost adsorbent ,
International journal of Environmental
sciences Volume 1 , No 7, 2011.

734 | P a g e

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Dv36730734

  • 1. Rucha Deshpande et al Int. Journal of Engineering Research and Applications ISSN : 2248-9622, Vol. 3, Issue 6, Nov-Dec 2013, pp.730-734 RESEARCH ARTICLE www.ijera.com OPEN ACCESS Synthesis & Effectiveness Study Of Banana Peel Adsorbent & Artificial Neural Network Modeling In Removal Of Cu (II) Ions From Aqueous Solution Shekhar Pandharipande *, Rucha Deshpande** *(Associate Professor, Department of Chemical Engineering , RTM Nagpur University, Nagpur-33) ** (B.Tech ( Chemical Engineering) , RTM Nagpur University, Nagpur) ABSTRACT Release of poisonous and harmful gases in the open air and of untreated polluted water to fresh water bodies has made the environmental conditions severe. Presence of excessive heavy metals like copper is found to damage not only fishes but humans also through the food cycle. The present work aims to synthesize an effective adsorbent from Banana peels, a material readily available by chemical treatment. The adsorbent synthesized is employed in removal of copper ions from waste water & is observed to be effective in removal of 12% to 89.47% of copper for adsorbent dosage varied between 0.5gm to 2 gm. Conventional adsorption isotherms have been estimated to describe the adsorption process & efforts have been made to develop Artificial Neural Network models for the same. It can be concluded that there is a lot of potential in Banana peel adsorbent that need to be tapped. Keywords – Artificial Neural Network, Banana Peel Adsorbent, Copper Sulphate, Wastewater treatment, Percent adsorption I. INTRODUCTION Today, the environment is mainly affected by air and water pollution. Release of poisonous and harmful gases in the open air and of untreated polluted water to fresh water bodies has made the environmental conditions severe. In order to sustain the healthy surroundings, it is essential for all the industries contributing to the pollution to treat the generated wastes before discharging the effluent streams. This includes discharge of pollutant gases even from low ppm level to elevated heights. Discharge of treated water to water bodies is essential to ensure the safety of the marine life. Presence of excessive heavy metals like copper is found to damage the marine life since it affects the gills, liver, nervous system of the fishes & the problems are transferred to the humans through the food cycle. Existence of copper in drinking water may cause mucosal irritation, hepatic and renal damage, capillary damage, gastrointestinal irritation and central nervous problem in humans. Several research articles have highlighted about the utilization of activated carbon for the removal of the heavy metals from wastewater [1]. The overall cost of the treatment process increases as the adsorbent cost goes on increasing. There is a need for development of efficient, low cost, economical alternative to activated carbon and other costly adsorbents. The present work addresses to exploring the possibility of synthesizing an effective adsorbent from Banana peels, a material readily available [2]. The peel is characterized by a heterogeneous, rough and porous surface with crater like pores that helps to its possible use as an adsorbent. The effectiveness of the www.ijera.com adsorbent synthesized is determined in removal of copper ions from waste water. Conventional adsorption isotherms have been employed to describe the adsorption process[3] & efforts have been made to develop Artificial Neural Network models for the same. Artificial neural network is a paradigm in itself that is inspired by the functioning of biological neural networks. ANN is viewed as a black box modeling tool & has been applied by researchers in several chemical processes for various purposes such as prediction of parameters, modeling of complex nonlinear multivariable relationships, in fault detection & diagnostics & in control, as among others. There are several types of artificial neural network & error back propagation (EBP) is common for modeling applications. Each layer has a number of processing elements called as neurons or nodes and it is decided by the number of input & output parameters that are to be correlated. The output from each neuron in the input layer is altered by a multiplication factor or weight and every node in the next layer receives the summation of the product of the outputs of all the nodes from the preceding layer. The resulting signal received by the node is transformed further by using functions like sigmoid & the resulting signal acts as an input for the nodes in the next layer. Training of EBP is essential & the algorithm suggested by Rummelhart is popular for this purpose. II. MATERIALS AND METHODS 2.1 Banana peel as an adsorbent In the present work chemically treated and dried banana peel adsorbent has been synthesized and 730 | P a g e
  • 2. Rucha Deshpande et al Int. Journal of Engineering Research and Applications ISSN : 2248-9622, Vol. 3, Issue 6, Nov-Dec 2013, pp.730-734 is employed in the adsorption studies experimentations. The banana peels are oven dried at 1000C and screened to determine the particle size. The particulate matter is treated with Sodium hydroxide pellets in hot distilled water. Similar procedure is adopted with oxalic acid. The treated peels are washed with hot distilled water for the removal of the adhered chemicals on the surface [4]. Dried banana peel adsorbent samples are stored in air tight container for further adsorption studies [5]. The details of consolidated observation in the Banana peel adsorbent synthesis are given in TABLE 1. Table 1. Observations in the synthesis of Banana peel adsorbent S Initial Final Wate Drying Perce r. weight of weig r temper nt n banana ht of remo ature yield o peels peels ved (O C) (gm) (gm) (gm) 180.3 6.8 100 14.86 1 153.5 2.2 Methodology The first part of the present work deals with the standardization of the digital colorimeter by correlating the optical density of the samples of aqueous solution and the known concentration of copper sulphate. The ANN model is developed on the data generated by conducting experiments in determination of optical densities of the aqueous solutions samples for known Cu(II) concentration. The second part is related to the adsorption studies, using the synthesized Banana peel adsorbent in removal of Cu(II) from aqueous solution. This is carried out by dosing a known volume and concentration of copper sulphate solution with a known quantity of banana peel adsorbent [6]. The solution is filtered after ensuring that the equilibrium is reached the optical density of the filtered solution is determined using a digital colorimeter The optical density determined is used for estimation of the concentration of the solution by applying the ANN model developed. The adsorption parameters like percent adsorption, amount of adsorbate adsorbed per unit amount of adsorbent are calculated with the help of equilibrium concentrations of the Cu(II) estimated using the ANN model. The adsorption studies data generated is used in developing ANN models to correlate the percentage adsorption of Cu(II), equilibrium concentration of adsorbate on adsorbent & amount of adsorbate adsorbed per unit amount of adsorbent with the initial concentration of Cu(II) in feed solution and adsorbent dosing. In this study, elite-ANN© is used in developing all ANN models [7]. III. www.ijera.com RESULT AND DISCUSSION 3.1 Developing ANN model for standardization of Digital colorimeter The objective of this part of the present work is to develop a ANN model for the standardization of the digital colorimeter for the estimation of remaining Cu(II) in aqueous solution after adsorption. The data sets of input copper concentrations and the corresponding optical densities obtained using digital colorimeter is used to train the ANN model. Based on the training the model predicts the concentration of the solution after adsorption. There is one input parameter as optical density and one output parameter as concentration of Cu (II) ions (gm/ml). Three different ANN models BS-30, BM-30, BC-30 having different topologies are developed for standardization of colorimeter with 22 data points. The details of the topology of ANN models developed for the standardization of digital colorimeter is given in TABLE 2. All the models developed have good accuracy levels. Table 2. Neural Network topology for standardization of colorimeter Number of Neurons RMS st nd rd Mod Inp E 1 2 3 Outp el traini ut Hidd hidd hidd ut ng Lay en en en Laye data er layer layer layer r Set BS1 00 05 05 1 0.017 30 66 BM1 00 05 05 1 0.017 30 44 BC1 00 05 05 1 0.016 30 2 Number of Iterations= 30000;Input parameter: Optical density of aqueous solution Output parameter: Concentration of Cu(II) ions in aqueous solution Fig.1 shows a schematic for the typical neural network architecture used in developing model BC-30. Figure 1: Neural Network Architecture for ANN model BC-30 Based on the values of RMSE, model BC-30 has been selected for the standardization of the colorimeter for estimation of Cu(II) ions in aqueous www.ijera.com 731 | P a g e
  • 3. Rucha Deshpande et al Int. Journal of Engineering Research and Applications ISSN : 2248-9622, Vol. 3, Issue 6, Nov-Dec 2013, pp.730-734 solution with the corresponding values of its optical density. Fig.2 & Fig. 3 show the graphs plotted between the predicted values as obtained using ANN model BC-30 and the actual values of copper concentration in aqueous solution samples for training and test data set respectively. www.ijera.com Amount of adsorbate adsorbed per unit amount of adsorbent = ((Initial concentration- Equilibrium concentration) x Volume of solution)/ Amount of adsorbent TABLE 3 shows the details of the observations & corresponding calculated values of percentage adsorption of Cu (II) & amount of adsorbate adsorbed per unit amount of adsorbent. Concentration of Cu(II) mg/ml 10 8 6 4 1th Actual output 2 0 1 4 7 10 13 16 19 22 Data point number Table 3: Adsorption terms calculated from equilibrium Cu (II) concentration 1th Predicte d output S r, N o. Concentration of Cu(II) mg/ml Figure 2 : Comparison of actual and predicted values of Copper concentration for training data set using model BC-30 6 5 4 3 2 1 0 1th Actual output 1th Predicte d output 1 2 3 Data point number 4 Figure 3: Comparison of actual and predicted value of copper concentration for test data set using model BC-30 From these graphs it can be seen that the actual & predicted values are very close to each other. ANN model BC-30 developed has higher accuracy of prediction & is used for estimation of the equilibrium concentration of Cu(II) ions in the solution samples that are obtained during the adsorption studies. The estimated values are further used for determining the effectiveness of the synthesized adsorbent by calculating adsorption terms such as percentage adsorption and amount adsorbed per unit amount of adsorbent. Percentage adsorption of Cu(II) ions is evaluated as: Percentage adsorption = (Initial concentrationEquilibrium concentration)/ Initial concentration x 100 [8] www.ijera.com 1 2 3 4 5 6 7 8 9 Initial copper ion concentr ation (mg/ml) Adsor bent Dosa ge 3.8175 3.8175 3.8175 4.581 4.581 4.581 6.108 6.108 6.108 0.5 1 2 0.5 1 2 0.5 1 1.2 (gm) Copper ion concentr ation after adsorpti on Ce (mg/ml) Perce nt adsor ption 3.328 3.328 0.401 3.174 1.572 0.564 4.219 3.919 2.852 12.81 12.81 89.47 30.70 65.66 87.68 30.91 35.82 53.30 Amou nt of adsor bate adsor bed per amou nt of adsor bent (mg/g m) 24.45 12.22 42.69 70.32 75.20 50.21 94.40 54.70 67.83 3.2 Developing ANN models for adsorption studies The objective of this part of present work is to develop ANN model for adsorption studies correlating the percentage adsorption of Cu (II) and equilibrium concentrations of adsorbate, on adsorbent & in aqueous solution for the known input parameters such as initial concentration of Cu (II) & adsorbent dosing. The data generated in adsorption studies of the present work as given in TABLE 3 is used for this purpose. Three ANN models AS, AM and AC having different topology as given in TABLE 4 are developed. Fig. 4 shows a typical architecture of one of the models AS developed. All the ANN models developed in the present work are using elite-ANN©. The snapshot of eliteANN© in run mode and the variation of error versus iteration during training mode for developing “AM model” are shown in Fig. 5 & Fig.6 respectively. 732 | P a g e
  • 4. Rucha Deshpande et al Int. Journal of Engineering Research and Applications ISSN : 2248-9622, Vol. 3, Issue 6, Nov-Dec 2013, pp.730-734 www.ijera.com 100 Series1 50 Series2 0 1 2 3 4 5 6 7 8 9 Figure 8: Comparison of actual and predicted values of percentage adsorption Figure 4: Neural Network architecture for ANN model AM-50 ANN model AM-50 is selected because of its lower RMSE value among the three models that are developed & employed for estimating the equilibrium concentration of the copper sulphate solution, percentage adsorption and the amount of adsorbent adsorbed per unit amount of the adsorbent. 100 50 Series1 Series2 0 1 2 3 4 5 6 7 8 9 Figure 9 : Comparison of actual and predicted values of amount of adsorbent adsorbed per amount of adsorbent adsorbed The claim of accuracy is further substantiated by calculation of the % relative error for each data point for all the output parameters as given below: % relative error = (actual value- predicted value)* 100/ (actual value) Figure 5: Snapshot of elite-ANN© in run mode 5 0 Data points -5 Figure 6: RMSE variation with iterations for training data set for AM-50 model Fig. 7, Fig. 8 & Fig. 9 show the graphs plotted for the comparison of actual and predicted values of equilibrium Cu(II) concentration, percent adsorption, amount of adsorbate adsorbed per amount of adsorbent respectively. 5 Series1 0 1 2 3 4 5 6 7 8 9 % Relative error Figure 10 :% Relative error for equilibrium concentration of Cu(II) between training data set and that obtained by model AM-50 2 0 Data points -2 -4 Figure 11: % Relative error for percent adsorbed of Cu(II) between training data set and that obtained by model AM-50 Series2 Figure 7: Comparison of actual and predicted values of copper concentration after adsorption using model AM-50 www.ijera.com 733 | P a g e
  • 5. Rucha Deshpande et al Int. Journal of Engineering Research and Applications ISSN : 2248-9622, Vol. 3, Issue 6, Nov-Dec 2013, pp.730-734 Table 4: Neural Network topology Mod el In p ut L ay er Number of Neurons 1st 2nd 3rd hid hid hidd den de en laye n laye r lay r er O ut pu t la ye r 3 RM SE trai ning data Set AS2 00 05 05 0.00 50 34 AM- 2 00 10 10 3 0.00 50 16 AC2 00 10 10 3 0.00 50 216 Number of Iterations= 50000 Input parameters: Initial Concentration Cu(II) ions, adsorbent dosage Output parameters: Equilibrium Conc. Of Cu(II) ions, amount of adsorbate adsorbed per unit amount of adsorbate adsorbed per unit amount of adsorbent, % adsorption and other costly adsorbents can be replaced with this low cost effective adsorbent which is developed from waste material. Further research can also be carried out to study the effectiveness of Banana peel adsorbent in removal of other metallic compounds that are present in industrial waste water. V. REFERENCES [1] [2] [3] % relative error 0 Data points -5 [5] Figure 12: % Relative error for amount of Cu (II) adsorbed er unit amount of adsorbent between training data set and that obtained by model AM-50 [6] As can be seen from Fig.10, Fig.11& Fig. 12; the percent relative error for AM-50 ranges between 0 to 4%, 0 to 1.4%, 0 to 2.5% in estimation of equilibrium concentration of Cu(II) ions, percent adsorption and amount of adsorbate adsorbed per amount of adsorbent respectively. Thus it can be said that the ANN model AM-50 has high accuracy of predictions & is acceptable. [7] [8] IV. CONCLUSION AND FUTURE SCOPE The objective of the present work was to explore the utilization of Banana peel adsorbent for the removal of Copper (II) metal ions from aqueous solution. Based on the adsorption studies it is observed that the adsorbent was effective in removal of 12% to 89.47% of copper for the adsorbent dosage varying between 0.5gm to 2 gm [9]. The novel feature of the present work is to develop ANN models in adsorption studies having high accuracy levels. There is a need for extending the laboratory scale work to pilot plant scale so that activated carbon www.ijera.com ACKNOWLEDGEMENTS Authors are thankful to Director,L.I.T., for providing infrastructural facilities and constant encouragement. [4] 5 www.ijera.com [9] D. Mohapatra, S. Mishra, N. Sutar Banana and its byproduct utilization: an overview, Journal of scientific and industrial research, volume 69,pp 323-329,May 2010.[1] G. Annadurai, R. Juang, , D. Lee, , Use of cellulose based wastes for adsorption of dyes from aqueous solutions, Journal of hazardous materials, volume B92,pp 263274,2 . [2] J. Memon, S.Memon , Bhanger , I Muhammad Y. Khuhawar , Banana Peel: A Green and Economical Sorbent for Cr(III) Removal , Pak. J. Anal. Environ. Chem. Vol. 9, No. 1 (2008) 20 – 25[3]. W. Ngah wan, M. Hanafiah, , Removal of heavy metal ions from wastewater by chemically modified plant wastes as adsorbents ,Bioresource technology, volume 99, pp 3935-3948, 2008. A. Ashraf , A. Wajid, K. Mahmood , J. Maah J. Yusoff., Low cost biosorbent banana peel (Musa sapientum) for the removal of heavy metals , Scientific Research and Essays Vol. 6(19), pp. 40554064, 8 September, 2011.[4] M. Hossain, H. Ngo, W. Guo, and T. Nguyen, Biosorption of cu (II) from water by Banana peel based biosorbent: experiments and models of adsorption and desorption, Journal of water sustainability,volume 2,pp 87-104,March 2012. S.Pandharipande, Y. Badhe, elite-ANN©. 2004; ROC No SW-1471 India. S. Pandharipande, A. Deshmukh , Synthesis , characterization and adsorption studies for adsorbents synthesized from Aegel marmelos shell for removal of Cr(VI) from aqueous solution , International journal of Engineering research and applications, Vol. 2, Issue 4, July- August 2012, pp.1337-1341. P. Velmurugan , V. Rathina kumar, G. Dhinakaran , Dye removal from aqueous solution using low cost adsorbent , International journal of Environmental sciences Volume 1 , No 7, 2011. 734 | P a g e