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33
Proc. of the Intl. Conf. on Advances in Applied science and Environmental Technology - ASET 2015.
Copyright © Institute of Research Engineers and Doctors, USA .All rights reserved.
ISBN: 978-1-63248-040-8 doi: 10.15224/ 978-1-63248-040-8- 38
An Evaluation of the Adsorptive Properties of
Coconut Husk for Oil Spill Cleanup
Augustine Osamor Ifelebuegu and Zenebu Momoh
Abstract-The removal of vegetable oil and diesel fuel from
seawater using waste coconut coir was investigated by
batch adsorption experiments at varying sorbent doses and
temperatures. Maximum adsorption capacities of 7231 and
6530 mg/g were achieved for the adsorption of vegetable
oil and diesel fuel, respectively. The water adsorbency was
relatively high at 6540 mg/g which is a limitation in its
potential field application for oil spill cleanup. The
maximum adsorption capacities improved significantly by
up to 22% with a corresponding reduction in water
adsorbency when coconut husk was impregnated with
human hair. The adsorption kinetics followed a pseudo
second order kinetic model and fitted to the Freundlich
adsorption isotherm model. The sorption capacity was
found to decrease with increasing temperatures. This work
demonstrated that with adequate modifications to improve
its hydrophobicity, coconut coir can potentially provide a
low cost environmentally friendly adsorbent for oil spill
cleanup.
Keywords—coconut coir, Adsorption capacity, oil spill
I. Introduction
Massive oil spills have often occurred as a result of
exploration, production, storage and transportation of oil
catalysed by the high demand for oil by the growing world
population. When oil spill occurs, it has an adverse impact on
the environment, economy, humans and biota [1, 2], hence, the
need for prompt cleanup after a spillage. One of the effective
ways of achieving this is mechanical recovery by adsorbents.
Adsorbents are insoluble materials or mixtures of materials
applied to recover liquids by the mechanisms of absorption or
adsorption. In absorption, molecules of the adsorbate penetrate
the adsorbent while in adsorption, the molecules of the
adsorbate bind to the outer surface of the adsorbent without
penetrating into it [3, 4]. Studies have shown that adsorption
of oil by adsorbents is closely connected to their functional
properties and surface morphology. Adsorbents can adsorb oil
because of their ability to selectively remove resinous, sulphur
containing compounds, unsaturated and polycyclic materials
as well as organic residues of sulphuric acid and solvents from
oil [5]. Important functional groups responsible for oil uptake
include O-H, N-H, C-O and C=O groups [3]. The influence of
surface morphology on adsorption can be seen in excellent
adsorbents like kapok and populous seeds whose hollow
structures coated with wax provide a large surface area for
adsorption [6, 7, 8].
Authors: A. O Ifelebuegu, Z. Momoh Coventry University
United Kingdom
A.Ifelebuegu@coventry.ac.uk
Adsorbents are of three main types namely; natural inorganic
sorbents, natural organic sorbents and synthetic sorbents.
Synthetic adsorbents are commonly used as commercial
adsorbents for oil spill cleanup as they are hydrophobic and
oleophilic. However, their cost and non-biodegradable nature
has necessitated the search for alternatives that are cost
effective, abundant in nature and eco-friendly. The use of
coconut coir is investigated in this study with a view to
evaluating their suitability as potential substitutes for synthetic
adsorbents in booms, for oil spill cleanup.
Coconut coir is an agricultural waste obtained from the fibrous
mesocarp layer of the coconut (Cocos nucifera L.) fruit [9]. It
contains 38% cellulose, 28 % hemicellulose and 32.8% lignin.
Functional groups such as -OH and fibre carbonaceous CxOH
present on its surface are dissociated at specific pH values and
facilitate the uptake of positively charged metal ions from
aqueous solution. Its lignin content plays a vital role its
capacity to adsorb organic substances from aqueous solutions
[10].
II. Materials and Methods
A. Materials
The coconut husk used in this experiment was purchased from
the local store in Coventry. It was then pulverised, washed and
dried in the oven. Human hair used was also collected from a
local barbing salon. The human hair was of African origin, it
was washed with detergent and hot water and dried prior to
use. Samples of the dried adsorbents are shown in figures 1 a
& b. The vegetable oil was purchased from Sainsbury
Supermarket, the diesel fuel from Esso, Coventry, UK.
Artificial sea water was prepared as has been previously
described in Kester et al. 1967 [11].
a b
Figure 1(a) coconut coir (b) Human hair
34
Proc. of the Intl. Conf. on Advances in Applied science and Environmental Technology - ASET 2015.
Copyright © Institute of Research Engineers and Doctors, USA .All rights reserved.
ISBN: 978-1-63248-040-8 doi: 10.15224/ 978-1-63248-040-8- 38
B. Batch Experiments
Adsorption experiments were conducted in seawater. 20 g of
vegetable oil and diesel fuel were poured into separate 500 ml
conical flask with 200 ml of sea water. Varying amounts of the
sorbents were added with a 60 mins contact time following the
ASTM F 726-99 standard methods for testing oil spill sorbents
[12]. Water adsorbency was also measured following the same
method. Oil concentrations were measured based on US-EPA
method 1664 [13]. Oil adsorption capacities (mg/g) were
obtained from the following equation:
(1)
Where Xo is the total mass of wet sorbent after oil adsorption
and Xs is the mass of the adsorbent before adsorption. All
experiments were conducted at room temperature (25oC ±
20C) and carried out in triplicate with the average value and
standard deviation (SD) calculated. Sample data with SD
greater than 10% were rejected with a re-run of the test carried
out.
III. Results and Discussions
A. Effect of Contact Time on Adsorption
Capacity of Coconut Coir
The effects of contact time on the adsorption capacity of
coconut coir for vegetable oil and diesel fuel and are
illustrated in Figure 2. It can be seen that there was a rapid
increase in the retention of vegetable oil and diesel fuel in the
first 5 minutes and thereafter proceeded at a slower rate and
finally attained equilibrium at about 60 minutes. The initial
high retention rate of the adsorbates can be attributed to the
existence of bare active sites on coconut coir. As portions of
these sites got occupied with molecules of diesel fuel and
vegetable with increasing contact time, the adsorption rate
became slower until the 60th minute when there was no more
significant adsorption due to the saturation of the surfaces of
coconut husk and hence an equilibrium between adsorption
and desorption processes [8].
Figure 2. Adsorption Rate of coconut coir in vegetable oil and
diesel fuel at temperature 25oC ± 20C. The bars represent
standard deviation of the mean.
B. Oil/Water Adsorbency of Coconut
Coir
The oil and water adsorbency for coconut husk and varying
combination of coconut husk and human hair are shown in the
figure 3. It can be seen that coconut husk has a comparatively
good oil adsorption properties but also has a high water
adsorbency which could be a limiting factor in potential field
application. It can also be seen that the oil adsorbency
increased significantly with decreased water adsorbency when
modified by blending it with human hair. The increased oil
adsorbency and lower water adsorbency of the coconut coir
impregnated with human hair are due to the higher
oleophilicity and hydrophobicity of human hair. A ratio of
adsorbency to water adsorbency greater than one is often
considered a good characteristic for oil adsorbents. This ratio
was greater than one fpr vegetable oil adsorption to coconut
coir but less than one for diesel fuel. It was however,
significantly improved above one for both vegetable oil and
diesel fuel when coconut coir was impregnated with human
hair. Table 1 shows the reported adsorption capacity for other
similar adsorbents and how coconut husk compares. It can be
seen it compares favorably with some alternative adsorbents.
A drawback to its use in oil spill cleanup is its high water
absorbency which can be significantly reduced with increase
in oil adsorbency by modification, to increase its oleophilicity
and hydrophobicity.
Figure 3. Adsorption capacities of coconut coir and coconut
coil human hair blends, in vegetable oil and diesel fuel at 25oC
± 20C. The bars represent standard deviation of the mean.
Table 1: Types of adsorbents, adsorbates and their
adsorption capacities
Types of
adsorbent
Adsorbate
Adsorption
capacity
(mg/g)
Reference
Activated sugar
bagasse
Machine oil
20,000
[15]
Acetylated banana
Machine oil
18,012
[16]
35
Proc. of the Intl. Conf. on Advances in Applied science and Environmental Technology - ASET 2015.
Copyright © Institute of Research Engineers and Doctors, USA .All rights reserved.
ISBN: 978-1-63248-040-8 doi: 10.15224/ 978-1-63248-040-8- 38
Polypropylene
(commercial
sorbent)
Crude oil
9100-10,000
[17]
Organoclay
Diesel
7200
[18]
Treated sludge
Crude oil
2000
[10]
Modified oil palm
leaves
Vegetable
oil
646
[19]
Human hair
Vegetable
oil
Crude oil
Diesel fuel
9300
8100
7917
[20]
Coconut coir
Vegetable
oil
Diesel fuel
7231
6530
This study
Coconut coir and
human hair (3:1)
Vegetable
oil
Diesel fuel
8333
7705
This study
Coconut coir and
human hair (1:1)
Vegetable
oil
Diesel fuel
8814
7916
This study
C. Adsorption Kinetics and Isotherms
The adsorption kinetics was investigated for coconut coir by
using the pseudo-first order and pseudo-second order
adsorption models as proposed by Lagergren, 1898 [21] and
can be expressed linearly as:
Log (Ce-Ct) = Log Ce- k1 (2)
2.303
t/Ct = 1/k2*C 2+t/Ce (3)
Pseudo-first order plot of Log (Ce-Ct) against t should give a
linear relationship from which k1 in (min-1) can be calculated
from the slope of the graph. A plot of t/Ct will give a rate
constant k2 (mg g-1min-1) for pseudo-second order kinetics.
Table 2 presents the constant values and correlation
coefficients R2 of both pseudo-first order and pseudo-second
order kinetic models for adsorption of vegetable oil and diesel
fuel onto coconut coir. The kinetic plots showed a good fit of
sorption equilibrium data with respect to pseudo-second order
on the basis of the correlation coefficient. This suggests the
possibility of chemisorption as the rate controlling step.
Table 2. Result obtained from pseudo first order and pseudo
second order kinetic modeling of the adsorption of diesel and
vegetable oil by coconut coir
Pseudo-first order
Pseudo-second
order
R2
K1
R2
K2
Diesel oil
0.349
0.024
0.984
0.034
Vegetable oil
0.591
0.024
0.983
0.005
The equilibrium data obtained in the isotherm study was
analysed using the Langmuir and Freundlich adsorption
isotherm models. The linear form of the Langmuir isotherm is
expressed in equation 4 as:
where:
X – the mass of adsorbate
M – the mass of adsorbent
Ce – the concentration of solute remaining at equilibrium in
mg/l
a, b – the constants. a is coefficient and b is the amount of
adsorbate needed to form a complete monolayer on the
adsorbent surface and so increases with molecular size. A plot
of (1/(X/M)) against (1/Ce) gave a straight line.
Also the linearised form of the Fruendlich isotherm is
expressed in equation 5:
where:
X – the mass of adsorbate
M – the mass of adsorbent
Ce – the concentration of solute remaining at equilibrium in
mg/l
kf and n – constants derived from the adsorption isotherm by
plotting (X/M) against Ce on log-log paper which produces a
straight line with a slope 1/n while the y intercept is kf.
The results of the isotherm study showed a good fit of the
Freundlich model, indicating that sorption of the oils onto
coconut coir occurred on heterogeneous sites with non-
uniform distribution of energy level rather than on
homogenous sites.
D. Effect of Ttemperature on Adsorption
of Crude Oil by Coconut Coir
The effect of temperature on the uptake efficiency of crude oil
by coconut coir was investigated at varying temperatures of
18, 28, 38 and 480C.The results of the adsorption capacities at
varying temperatures is illustrated in figure 4. It can be seen
that the oil retention efficiency by coconut husk decreased
with increasing temperatures. The decrease in adsorption of oil
from aqueous media as the temperature of the media increases
may be due to the fact that its solubility in water increases, its
viscosity decreases making it drain off sorbent’s surface
easily. In addition, its Brownian motion increases, hence
increasing the energy required to bind the oil to the surface of
the coconut coir [22, 23].
36
Proc. of the Intl. Conf. on Advances in Applied science and Environmental Technology - ASET 2015.
Copyright © Institute of Research Engineers and Doctors, USA .All rights reserved.
ISBN: 978-1-63248-040-8 doi: 10.15224/ 978-1-63248-040-8- 38
Figure 4. Effect of temperature on the sorption capacity of
coconut coir. The bars represent standard deviation of the
mean.
IV. Conclusion
The adsorption capacity of coconut coir was evaluated to
determine its applicability as an oil spill adsorbent. Adsorption
capacities of 7231 and 6530 mg/g were achieved for pure
coconut coir for the adsorption of vegetable oil and diesel fuel,
respectively. The ratio of oil adsorbency to water adsorbency
was greater than 1 for vegetable oil and less than 1 for diesel
fuel. With the impregnation of coconut coir with human hair,
water adsorbency was reduced and adsorption capacities for
vegetable oil and diesel fuel increased to 8814 and 7916 mg/g,
respectively. The adsorption capacities for both vegetable and
diesel fuel were inversely related to temperature. The
adsorption kinetic followed a pseudo-second order kinetic
model. With the modification of coconut coir to reduce its
water adsorbency, it could potentially be used as a low- cost
adsorbent for the cleanup of oil spills in oily water.
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Proc. of the Intl. Conf. on Advances in Applied science and Environmental Technology - ASET 2015.
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ISBN: 978-1-63248-040-8 doi: 10.15224/ 978-1-63248-040-8- 38
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