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i n t e r n a t i o n a l j o u r n a l o f h y d r o g e n e n e r g y 3 4 ( 2 0 0 9 ) 7 4 7 5 – 7 4 8 2
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Optimization of biohydrogen production by Clostridiumbutyricum EB6 from palm oil mill effluent using responsesurface methodology
Mei-Ling Chonga,*, Nor’ Aini Abdul Rahmana, Raha Abdul Rahimb, Suraini Abdul Aziza,Yoshihito Shiraic, Mohd Ali Hassana
aDepartment of Bioprocess Technology, Faculty of Biotechnology and Biomolecular Sciences, Universiti Putra Malaysia, 43400 Serdang,
Selangor, MalaysiabDepartment of Cell and Molecular Biology, Faculty of Biotechnology and Biomolecular Sciences, Universiti Putra Malaysia, 43400 Serdang,
Selangor, MalaysiacGraduate School of Life Sciences and System Engineering, Kyushu Institute of Technology, 808-0196 Hibikino 2-4, Wakamatsu-ku,
Kitakyushu-shi, Fukuoka, Japan
a r t i c l e i n f o
Article history:
Received 13 July 2008
Received in revised form
17 May 2009
Accepted 17 May 2009
Available online 23 June 2009
Keywords:
Biohydrogen
Clostridium butyricum EB6
Response surface methodology
POME
* Corresponding author. Tel.: þ603 89467590;E-mail address: [email protected]
0360-3199/$ – see front matter ª 2009 Interndoi:10.1016/j.ijhydene.2009.05.088
a b s t r a c t
Clostridium butyricum EB6 successfully produced hydrogen gas from palm oil mill effluent
(POME). In this study, central composite design and response surface methodology were
applied to determine the optimum conditions for hydrogen production (Pc) and maximum
hydrogen production rate (Rmax) from POME. Experimental results showed that the pH,
temperature and chemical oxygen demand (COD) of POME affected both the hydrogen
production and production rate, both individually and interactively. The optimum condi-
tions for hydrogen production (Pc) were pH 5.69, 36 �C, and 92 g COD/l; with an estimated Pc
value of 306 ml H2/g carbohydrate. The optimum conditions for maximum hydrogen
production rate (Rmax) were pH 6.52, 41 �C and 60 g COD/l; with an estimated Rmax value of
914 ml H2/h. An overlay study was performed to obtain an overall model optimization. The
optimized conditions for the overall model were pH 6.05, 36 �C and 94 g COD/l. The
hydrogen content in the biogas produced ranged from 60% to 75%.
ª 2009 International Association for Hydrogen Energy. Published by Elsevier Ltd. All rights
reserved.
1. Introduction be produced by expensive methods, such as electrolysis and
Hydrogen gas is a clean and ideal alternative energy for the
future, therefore hydrogen gas production and utilization
have been highly investigated [1,2]. Hydrogen has a high
energy yield of 122 kJ/g, which is 2.75 times greater than
hydrocarbon fuels. This characteristic has made it a prom-
ising alternative fuel. However, there are major challenges
with using hydrogen gas as a fuel. Not only it is difficult to
transport and store, but also unavailable in nature and must
fax: þ603 89467593.m (M.-L. Chong).ational Association for H
steam reformation. For these reasons, biological hydrogen gas
production has sparked great interest, as it is less energy
intensive and can be combined with wastewater treatment
processes [3] via dark fermentation and photofermentation
[4]. The fermentation feedstocks most studied have been
municipal solid waste [5], food processing industry waste [6,7]
and dairy waste [8].
In Malaysia, palm oil extraction generates about 50 million
tons of palm oil mill effluent (POME) annually. POME contains
ydrogen Energy. Published by Elsevier Ltd. All rights reserved.
i n t e r n a t i o n a l j o u r n a l o f h y d r o g e n e n e r g y 3 4 ( 2 0 0 9 ) 7 4 7 5 – 7 4 8 27476
high chemical oxygen demand (COD) due to the lignocellulose
and hemicelluloses components of the material [9]. In our
previous study, we developed a closed-tank anaerobic system
to investigate COD removal efficiency [10]. During the acido-
genesis process, organic substances are converted into acid
and hydrogen gas. If the degradation is continued to the
methanogenesis process, methane gas is the end-product.
Previous research has showed hydrogen production using
POME sludge as the inoculum is promising [11]. Single strain
cultivation, using locally isolated Clostridium butyricum EB6,
was successfully carried out in POME.
Hydrogen gas production from waste has been extensively
studied. Researchers reported that hydrogen gas production
was dependent on the pH, organic loading rate and tempera-
ture [12–14]. Results indicated that pH was crucial to hydrogen
gas production, due to its effect on the hydrogenase enzyme
[15] and its metabolism [16]. The reported optimum pH varied
with the substrate used, but it was always within the range of
pH 4.5–7.0 [17]. Temperature effect on the maximum substrate
utilization rates has also been studied in clostridia [13].
Results of previous studies have shown that the substrate
concentration significantly affected the hydrogen gas
production and the metabolic product distribution [18].
The response surface methodology (RSM) has been
proposed to study the influence of identified parameters and
their individual and interactive effects. This study used a well-
designed strategy, based on RSM theory, to perform a number
of planned experiments and analyze the responses statisti-
cally [19]. The objective of the current study was to identify the
individual and interactive effects of pH, temperature and COD
of POME on hydrogen gas production using C. butyricum EB6.
2. Materials and methods
2.1. Microorganism and culture medium
The bacterium used in this study was C. butyricum EB6.
Previous studies have proved that this strain is capable of
producing hydrogen gas via fermentation [20]. The bacterium
was preserved in 20% glycerol at �20 �C. Bacterium stability
was routinely examined under a microscope. The Hungate
tube cultivation technique was adapted to culture C. butyricum
EB6 in an aerobic environment.
2.2. Cultivation medium and reactor set-up
For inoculum preparation, a stock culture (10 ml in Hungate
tube) was heat-shocked at 90 �C for 90 s. After the culture
cooled, it was transferred to a 250 ml modified serum bottle
with 100 ml of reinforced clostridial medium. Reinforced
clostridial medium consists of (g/l): meat extract, 10; peptone,
5; yeast extract, 3; Dþ glucose, 5; starch, 1; sodium chloride, 5;
sodium acetate, 3; L-cystenium chloride, 0.5; agar, 0.5. The pH
of the medium was initially adjusted to 6.5 and sparged with
nitrogen before sterilization. The inoculum was then incu-
bated at 37 �C for 18 h without shaking. Hydrogen production
experiments were conducted in a 3L fermenter (B. Braun,
Germary). 1000 ml of fresh POME were added to the fermenter
at varying pH, temperature and COD levels. Prior to their use,
all media were sparged with nitrogen for 20 min to ensure
anaerobic conditions. The pH of the medium was controlled
using 1 N NaOH. The agitation rate was constant (200 rpm) for
all experiments.
2.3. Experimental design
Optimization of hydrogen production using POME was carried
out using a central composite design. The pH, temperature
and COD of POME were selected as independent variables with
the range of 5.3–6.7, 32–42 �C and 60–100 g COD/l, respectively.
These ranges were selected based on previous research
[11,13,14,21]. The variable, Xi, was coded as xi according to
equation (1) such that X0 corresponded to the central value:
xi ¼Xi � X�i
DXi; where i ¼ 1; 2;3;/k; (1)
where xi is the dimensionless coded value of an independent
variable, Xi is the actual value of an independent variable for
the ith test, Xi* is the actual value of an independent variable
at the center point and DXi is the step change.
The experimental design was analyzed using response
surface methodology (RSM); a collection of mathematical and
statistical techniques used to model and analyze problems in
which a response of interest is influenced by several variables.
The objective is to optimize this response [19]. The general
form of the second degree polynomial equation is:
Yi ¼ bo þXk
i¼1
bixi þXk
i¼1
biix2i þ
Xk
i¼1
Xk
j¼1
bijxixj (2)
where Yi is the predicted response, xixj are input variables
which influence the response variable Y, bo is the offset term,
bi is the ith linear coefficient, bii is the ith quadratic coefficient
and bij is the ijth interaction coefficient. The secondary order
polynomial coefficients were calculated using Design Expert
software version 7.0.0 (Stat-Ease Inc.).
2.4. Analytical method
The exit gas was analyzed using a Shimadzu GC-8A gas
chromatograph (GC) with a thermal conductivity detector.
The carrier gas was nitrogen and the column was packed with
Porapak Q (80/100 mesh). Temperatures at the stainless steel
column and injection/detector point were 50 �C and 100 �C,
respectively. A standard hydrogen curve was plotted using
standard hydrogen gas. Total carbohydrate in POME was
analyzed using phenol sulfuric acid method (standard method
by APHA)
2.5. Kinetic modeling
The cumulated hydrogen production in the batch experi-
ments followed the modified Gompertz equation [22] (equa-
tion (3)).
H ¼ P exp
�� exp
�Rmaxe
Pðl� tÞ þ 1
��(3)
H is the cumulative hydrogen production (ml), l the lag time
(h), P is the hydrogen production potential (ml), Rmax is the
Table 1 – Experimental results for Pc and Rmax for thecomposite design.
Run Actual value Pc (ml H2/gcarbohydrate)
Rmax (mlH2/h)
X1:pH
X2:temperature
X3:COD
1 6.0 37 80 297.9 780
2 5.3 42 60 206.2 230
3 6.0 37 80 296.0 885
4 6.0 37 80 310.6 754
5 6.0 37 120 279.0 839
6 6.0 37 80 284.0 910
7 6.0 37 80 283.2 885
8 5.3 32 100 262.4 421
9 6.0 37 40 200.2 635
10 6.7 32 60 195.5 383
11 6.7 42 100 170.6 646
12 5.3 42 100 227.3 269
13 5.3 32 60 216.4 150
14 6.0 37 80 297.9 783
15 7.4 37 80 160.8 383
16 6.7 42 60 125.1 929
17 6.7 32 100 212.4 550
18 6.0 27 80 168.0 171
19a 4.7 37 80 – –
20a 6.0 47 80 – –
Pc (ml H2/g carbohydrate)¼Hydrogen production.
Rmax (ml H2/h)¼Hydrogen production rate.
a Experiments were excluded from the design as it is an extreme
condition for biohydrogen production from POME using Clostridium
butyricum EB6.
1000
0
2000
3000
4000
5000
6000
Tot
al a
ccum
ulat
edhy
drog
en g
as (
ml)
0 2 4 6 8 10 12 14 16 18 20
Time (hour)
0
10
20
30
40
50
60
70
80
a
c
Fig. 1 – Batch hydrogen fermentation of Clostridium butyricum E
Profile of hydrogen production (ml), (b) Profile of biogas producti
total carbohydrate.
i n t e r n a t i o n a l j o u r n a l o f h y d r o g e n e n e r g y 3 4 ( 2 0 0 9 ) 7 4 7 5 – 7 4 8 2 7477
maximum hydrogen production rate (ml/h) and e is
2.718281828. The P, Rmax and l values for each batch were
estimated using the nonlinear estimation function in STA-
TISTICA (version 6).
Hydrogen gas production was calculated using gas
sampled from the bioreactor headspace and the gas compo-
sition was measured. The total volume of biogas produced at
each time interval is given by equation (4).
VH;i ¼ VH;i�1 þ CH;i
�VG;i � VG;i�1
�þ VH
�CH;i � CH;i�1
�(4)
VH,i and VH,i � 1 are cumulative hydrogen gas volumes at the
current (i) and previous (i� 1) time intervals, VG,i and VG,i � 1
the total biogas volumes in the current and previous time
intervals, CH,i and CH,i � 1 the fraction of hydrogen gas in the
headspace of the bottle measured using gas chromatography
in the current and previous intervals, and VH the total volume
of headspace in the reactor [23].
3. Results and discussion
In all experiments, the biogas produced contained hydrogen
(60–75%) and carbon dioxide (25–40%). No methane gas was
detected. All cumulative hydrogen production data fitted
equation (3) well, with R2> 0.99.
3.1. Overall performance of hydrogen productionfrom POME
The experimental results of all eighteen runs are summarized
in Table 1. Fig. 1 illustrates the biohydrogen production profile
for Run #4 at pH 6.0, 37 �C and 80 g COD/l. Fig. 1a and b repre-
sents hydrogen production and total biogas production, fitted
1000
0
2000
3000
4000
5000
6000
Tot
al b
ioga
s (m
l)
0 2 4 6 8 10 12 14 16 18 20
Time (hour)
12
14
16
18
20
22
24
26
28
Tot
alca
rboh
ydra
te (
g/L
)
b
d
B6 from POME at pH 6.0, 37 8C and 80 g COD/l (Run #4). (a)
on (ml), (c) Profile of hydrogen percentage, and (d) Profile of
Table 2 – ANOVA on model for Pc and Rmax.
Pc (ml H2/gcarbohydrate)
Rmax (ml H2/h)
Model probability <0.0001 <0.0001
Model F-value 27.29 32.34
R2 0.9685 0.9733
Adjusted R2 0.9330 0.9432
Adequate precision 14.2381 15.9990
Standard deviation 14.7828 65.3260
Lack of fit probability 0.0877 0.5363
Lack of fit F-value 3.92 0.82
3235
3740
42
60
7080
90
100
190
220
250
280
310
Hyd
roge
n pr
oduc
tion
(ml/g
car
bohy
drat
e)H
ydro
gen
prod
ucti
on(m
l/g c
arbo
hydr
ate)
Hyd
roge
n pr
oduc
tion
(ml/g
car
bohy
drat
e)
Temperature (deg C)
Temperature (deg C)
COD (g COD/L)
5.30
5.656.00
6.356.70
32
3537
40
42
160
198
235
273
310
pH
6.70100
213
236
259
281
304c
b
a
i n t e r n a t i o n a l j o u r n a l o f h y d r o g e n e n e r g y 3 4 ( 2 0 0 9 ) 7 4 7 5 – 7 4 8 27478
to the modified Gompertz equation. The kinetic parameters
for total accumulated hydrogen gas (ml) were P: 3790 ml, Rmax:
885.8 ml H2/h and l: 7.14 h.
As shown in Fig. 1c, the percentage of hydrogen gas in the
bioreactor increased with time. Initially, there was a 7 h lag
phase, after which, the gas production increased greatly. The
total carbohydrate degradation began after the 4 h. During the
stationary phase of hydrogen gas production, 48% of total
carbohydrate in POME remained, suggesting that C. butyricum
cannot utilize all remaining carbohydrates. POME naturally
contains high amounts of cellulosic and lignocellulosic
material. C. butyricum in nature produces xylanase [24]. The
hemicellulose in POME can be readily utilized by C. butyricum
EB6, leaving behind unutilized cellulose.
3.1.1. Effects of pH, temperature and COD on Pc
(hydrogen production)In order to evaluate the effects of pH, temperature and COD on
Pc, the design matrix of experimental conditions with their
corresponding Pc values (Table 1) was subjected to regression
analysis. The mathematical model relating the production of
biohydrogen to the independent process variables of pH,
temperature and COD is given in the quadratic regression as
follows:
Pc ¼ 292:9� 23:1x1 � 22:7x2 þ 17:9x3 � 8:4x1x2 � 0:6x1x3
þ 0:5x2x3 � 24:5x21 � 45:6x2
2 � 14:8x23; (5)
where, Pc is the hydrogen production (ml H2/g carbohydrate),
and x1, x2 and x3 are coded values of independent variables.
The multiple correlation efficient, R2 and adjusted R2 were
evaluated. The adjusted R2 measures the amount of variation
about the mean explained by the model. It is adjusted for the
Table 3 – Summary of model terms.
Term p-value
Pc (ml H2/g carbohydrate) Rmax (ml H2/h)
X1-pH 0.0017 <0.0001
X2-temp 0.0019 0.0172
X3-COD 0.0013 0.0502
X1X2 0.1485 0.0048
X1X3 0.9125 0.0500
X2X3 0.9309 0.0061
X12 0.0005 <0.0001
X22 <0.0001 <0.0001
X32 0.0011 0.0862
COD (g COD/L)pH
5.305.65
6.006.35
6070
80
90
Fig. 2 – Three dimension surface graphs of the model for Pc
at the optimum point for each variable: (a) fixed pH at 6.0
(b) fixed COD at 80 g/l (c) temperature 37 8C.
number of model parameters relative to the number of points
in the design. The adjusted R2 of 93.3% for Pc is attributed to
the independent variables. The R2 for Pc is 96.85%, which
indicates a good agreement between experimental and pre-
dicted values.
Table 4 – Summary of optimize conditions for Pc and Rmax and experimental value.
Pc (ml H2/gcarbohydrate)
Rmax
(ml H2/h)Overall modeloptimization
Experimental value Experimental value
Optimum
condition
Low value Optimum
pH 5.69 6.52 6.05 5.5 6.05
Temperature
(�C)
36 41 36 32 36
COD (g/L) 92 60 94 94 94
Predicted value 306 914 Pc¼ 298, Rmax¼ 850 Pc¼ 254 (Std dev¼�12.65)a,
Rmax¼ 460 (Std dev¼�11.93)aPc¼ 290 (Std dev¼�5.66)a,
Rmax¼ 802 (Std dev¼�33.94)a
a Std dev¼ standard deviation.
Pre
dict
ed V
alue
s
120 140 160 180 200 220 240 260 280 300 320120
160
200
240
280
320
0 100 200 300 400 500 600 700 800 900 1000
Observed Values
0
200
400
600
800
1000
a
b
Fig. 3 – Relationship between predicted values and
observed values: (a) hydrogen production (ml H2/g
carbohydrate) and (b) hydrogen production rate (ml H2/h).
i n t e r n a t i o n a l j o u r n a l o f h y d r o g e n e n e r g y 3 4 ( 2 0 0 9 ) 7 4 7 5 – 7 4 8 2 7479
The ANOVA study is documented in Table 2. The F-value
for a term compares a term’s variance with the residual
variance. The ANOVA result showed the computed F-value
was 27.29, which was much greater than the F0.05,9,8 (3.39),
which implied the model is significant at high confidence level
of 95%. The probability> F of <0.0001 means there was less
than a 0.01% chance that a model F-value could occur due to
noise. Lack of fit measures the variation of the data around the
fitted model. The lack of fit F-value compares the lack of fit
variance with pure error variance. If the model does not fit the
data well, this value will be significant; if the variances are
close to the same, the ratio will be close to one and it is less
likely that lack of fit is significant. The computed lack of fit F-
value of 3.92 was less than the F0.05,3,5 (5.41), therefore, the lack
of fit test was insignificant. The model fit the data well, with
a p-value of 0.0877; there was only 8.77% chance that this lack
of fit F-value could occur due to noise.
The p-values for the linear, interactive and quadratic terms
are shown in Table 3. The confidence level was set at 95%
(a¼ 0.05). The linear and quadratic coefficients of the three
variables showed a significant effect with p-values lower than
0.002. In short, all three variables influenced the Pc. This result
was comparable to results from previous research using
ananaerobic culture [25] and Enterobacter aerogenes [26]. The
coefficients for interactive effects were very high. However,
we could not overrule their effect on biohydrogen production
from POME by C. butyricum EB6 because of their individual
effect.
Fig. 2 illustrates the three-dimensional response surfaces
based on equation (5), by keeping one variable constant at its
center point, and leaving two variables within the experi-
mental range. As shown in Fig. 2, the response surface of Pc
displayed a clear optimum point which fell inside of the
boundary range. From the examination of the contour plot
with fixed COD (Fig. 2b) compared to the others (Fig. 2a and c),
there was a slight elongation sloping downward. The
hydrogen production, Pc, was slightly more sensitive to
changes in temperature than to pH. The contour plot with
respect to temperature to COD (fixed pH) and pH to COD (fixed
temperature) showed a round ridge running around the center
point, suggesting low correlation levels. This is confirmed by
the p-value of both being >0.05. The maximum predicted
response value for Pc, as estimated by equation (5), is 306 ml
H2/g carbohydrate with a pH of 5.69, temperature of 36 �C and
92 g COD/l (Table 4). Fig. 3a shows that actual experimental
values were close to the predicted using equation (5).
In many studies, the pH, temperature and substrate
concentration significantly affected the hydrogen gas
production during acidogenesis of the anaerobic digestion of
waste [27]. The optimum conditions found from this study
were similar to previously published results obtained with
mixed culture, mainly clostria sp.
3.1.2. Effect of pH, temperature and COD on Rmax
Similarly, the data for Rmax was analyzed based on ANOVA
and response surface to study the pH, temperature and COD.
The mathematical model relating to the production of bio-
hydrogen, with the independent process variables of pH,
temperature and COD, was given in the quadratic regression
as follows:
Rmax ¼ 829:37þ 184:95x1 þ 66:057x2 þ 37:63x3 þ 89:25x1x2
� 53:25x1x3 � 85:25x2x3 � 209:26x21 � 136:76x2
2 � 25:69x23
(6)
The R2 for Rmax is 97.33%, which indicated a good agreement
between experimental and predicted values. The ANOVA
32
3537
4042
6070
80
90
100
470
565
850
Hyd
roge
n pr
oduc
tion
rat
e (m
l/h)
Hyd
roge
n pr
oduc
tion
rat
e (m
l/h)
Hyd
roge
n pr
oduc
tion
rat
e (m
l/h)
5.30
5.65
6.00
6.35
6.70
3235
37
40
42
270
427.5
585
742.5
900
pH
pH5.30
5.65
6.00
6.35
6.70
6070
80
90
100
310
452.5
595
737.5
880
755
660
Temperature (deg C)
Temperature (deg C)
COD (g COD/L)
COD (g COD/L)
a
b
c
Fig. 4 – Three dimension surface graphs of the model for Rmax (a) fixed pH at 6.0 (b) fixed COD at 80 g/l 37 8C (c) fixed
temperature.
i n t e r n a t i o n a l j o u r n a l o f h y d r o g e n e n e r g y 3 4 ( 2 0 0 9 ) 7 4 7 5 – 7 4 8 27480
(Table 2) showed that the F-value for the model was 32.34,
greater than the tabulated F-value. This indicated that the
model term was significant, with p-value< 0.000. The pre-
dicted lack of fit F-value of 0.82 was less than the F0.05,3,5 (5.41),
showing the lack of fit test was insignificant. The model fit the
data well and the lack of fit p-value of 0.5363 shows there was
53.63% chance that a lack of fit F-value could occur due to
noise.
Fig. 5 – Overlay plot of hydrogen production and hydrogen
production rate in response to temperature and pH with
the COD fixed at 94 g COD/l. The optimum area is shaded in
grey.
i n t e r n a t i o n a l j o u r n a l o f h y d r o g e n e n e r g y 3 4 ( 2 0 0 9 ) 7 4 7 5 – 7 4 8 2 7481
The p-values of the linear, interactive and quadratic terms,
shown in Table 3 with 95% confidence, showed that almost all
the terms were significant, except the quadratic terms for
COD. However, the effect of quadratic terms for COD cannot
be completely eliminated, because the p-value was within the
90% confidence range.
Fig. 4 illustrates the three-dimensional response surfaces
based on equation (6), by keeping one variable constant at its
center point, and leaving two variables within the experi-
mental range. As shown in Fig. 4, the response surface of Rmax
showed a clear optimum point which fell inside of the
boundary range. From the examination of the contour plot,
there was an elongation diagonally in both directions. This
showed that the interactions of temperature to COD (Fig. 4a),
Table 5 – Comparison of biohydrogen production with cited lit
Microorganism Substrate pH Temperature (�C) Subst
C. butyricum POME 6.05 36
Mixed culture Glucose 6 35
Mixed culture Glucose 5.5 36
C. butyricum Sucrose 5.5 37
Mixed culture Sucrose 5.5 37
Mixed culture POME 5.5 60
a g COD/l.
b ml H2/g carbohydrate.
c mol H2/mol glucose.
d mol H2/mol sucrose.
e ml H2/g COD/l.
f ml H2/L-medium.
temperature to pH (Fig. 4b) and COD to pH (Fig. 4c) were
significant. This was confirmed by the ANOVA result, with the
p-value lower than 0.05. The maximum predicted response
value for Pc, estimated by equation (6), was 914.08 ml H2/h
with the corresponding variables of pH 6.52, 41 �C and COD
60 g/l (Table 4). The experimental values were close to value
predicted using equation (6) (Fig. 3b). The hydrogen produc-
tion rates from this study were comparable to those found in
literature [28]. Additionally, this study confirmed that the RSM
approach is appropriate for optimizing the hydrogen produc-
tion from POME by C. butyricum EB6.
3.2. Process optimization
Hydrogen production (Pc) and hydrogen production rate (Rmax)
were each optimized at pH, temperature and COD of POME.
We aimed to then determine the correct combination of
variables to allow both responses to be optimized simulta-
neously. The best compromise can be determined visually by
superimposing overlaying responses on a contour plot [29].
Fig. 5 illustrates the overlay plot of temperature and pH. The
optimum region (shaded region) was identified for hydrogen
production (Pc) and hydrogen production rate (Rmax). The
optimum condition for the overall model was at pH 6.05, 36 �C
and 94 g COD/l. In order to validate the model, one point
within the optimum region and one point outside the region
were chosen. Experiments were performed to compare the
experimental result with its corresponding predicted value
(Table 4). The first experiment corresponded to the lower
value of pH (5.5) and temperature (30 �C), yielding Pc at 254 ml
H2/g carbohydrate and Rmax at 460 ml H2/h. The second
experiment corresponded to the optimum value of pH (6.0)
and temperature (36 �C), yielding Pc at 290 ml H2/g carbohy-
drate and Rmax at 802 ml H2/h. The accuracy of the optimum
conditions was checked by calculating the standard deviation
for each response. The experiment results were close to the
model prediction. Table 5 shows the comparison of hydrogen
gas production and the production rate with previously pub-
lished results. Hydrogen gas production and hydrogen
production rate results were found to be comparable with the
published data.
erature.
rate concentration Pc Rmax (ml H2/h) Reference
94a 315.8b 885.8 This work
10 1.43c 198.6 [26]
7 2.1c nv [17]
20 2.91d 160 [30]
7.5a 46.6e 74.7 [14]
nv 4708f 454 [11]
i n t e r n a t i o n a l j o u r n a l o f h y d r o g e n e n e r g y 3 4 ( 2 0 0 9 ) 7 4 7 5 – 7 4 8 27482
4. Conclusion
C. butyricum EB6 produced hydrogen gas from POME. The
optimized conditions were determined for hydrogen produc-
tion (Pc) and hydrogen production rate (Rmax), using variables
of pH, temperature and COD. It was found that pH, tempera-
ture and COD greatly influenced the hydrogen gas production,
as determined by ANOVA of these variables. The optimized
conditions for hydrogen production from POME using C.
butyricum were pH 6.05, 36 �C and 94 g COD/l, with the esti-
mated hydrogen production (Pc) at 298 ml H2/g-carbohydrate
and hydrogen production rate (Rmax) at 849.5 ml H2/h.
Acknowledgments
The authors are grateful for financial support from the
Ministry of Science, Technology and Innovation, Malaysia;
University Putra Malaysia; Kyushu Institute of Technology
(KIT) and Japan Society for Promotion of Science (JSPS).
r e f e r e n c e s
[1] Penner SS. Steps toward the hydrogen economy. Energy2006;31:33–43.
[2] Solomon Barry D, Banerjaee A. A global survey of hydrogenenergy research, development and policy. Energy Policy 2006;34:781–92.
[3] Nath K, Das D. Hydrogen from biomass. Curr Sci 2003;85:265–71.[4] Kapdan IK, Kargi F. Biohydrogen production from waste
materials. Enzyme Microb Technol 2006;38:569–82.[5] Lay JJ, Lee YJ, Noike T. Feasibiligy of biological hydrogen
production from organic fraction of municipal solid waste.Water Res 1999;33:2579–86.
[6] Van Ginkel SW, Oh SE, Logan BE. Biohydrogen gas productionfrom food processing and domestic wastewaters. IntJ Hydrogen Energy 2005;30:1535–42.
[7] Shin HS, Youn JH. Conversion of food waste into hydrogen bythermophilic acidogenesis. Biodegradation 2005;16:33–44.
[8] Collet C, Adler N, Schwitzguebel JP, Peringer P. Hydrogenproduction by Clostridium thermolacticum during continuousfermentation of lactose. Int J Hydrogen Energy 2004;29:1479–85.
[9] Sumathi S, Chai SP, Mohamed AR. Utilization of oil palm asa source of renewable energy in Malaysia. Renew SustainEnergy Rev 2008;12:2404–21.
[10] Yacob S, Shirai Y, Hassan MA, Wakisaka M, Subash S. Start-upoperation of semi-commercial closed anaerobic digester forpalm oil mill effluent treatment. Proc Biochem 2006;41:962–4.
[11] Atif AAY, Fakhru’l-Razi A, Ngan MA, Morimoto M, Iyuke SE,Veziroglu NT. Fed batch production of hydrogen from palmoil mill effluent using anaerobic microflora. Int J HydrogenEnergy 2005;30:1393–7.
[12] Kim IS, Hwang MH, Jang NJ, Hyun SH, Lee ST. Effect of low pHon the activity of hydrogen utilizing methanogen inbiohydrogen process. Int J Hydrogen Energy 2004;29:1133–40.
[13] Zhang YF, Shen JQ. Effect of temperature and ironconcentration on the growth and hydrogen production ofmixed bacteria. Int J Hydrogen Energy 2006;31:441–6.
[14] Van Ginkel S, Sung SW, Lay JJ. Biohydrogen production asa function of pH and substrate concentration. Environ SciTechnol 2001;35:4726–30.
[15] Dabrock B, Bahl H, Gottschalk G. Parameters affectingsolvent production by Clostridium pasterurianum. ApplEnviron Microbiol 1992;58:1233–9.
[16] Lay JJ. Modeling and optimization of anaerobic digestedsludge converting starch to hydrogen. Biotechnol Bioeng2000;68:269–78.
[17] Fang HHP, Liu H. Effect of pH on hydrogen production fromglucose by a mixed culture. Bioresour Technol 2002;82:87–93.
[18] He GQ, Kong Q, Ding LX. Response surface methodology foroptimizing the fermentation medium of Clostridiumbutyricum. Lett Appl Microbiol 2004;39:363–8.
[19] Montgomery DC. Design and analysis of experiments. US:John Wiley; 2005.
[20] Chong ML, Raha AR, Shirai Y, Hassan MA. Biohydrogenproduction by Clostridium butyricum EB6 from palm oil milleffluent. Int J Hydrogen Energy 2009;34:764–71.
[21] O-Thong S, Prasertsan P, Intrasungkha N, Dhamwichukorn S,Birkeland NK. Optimization of simultaneous thermophilicfermentative hydrogen production and COD reduction frompalm oil mill effluent by thermoanaerobacterium-richsludge. Int J Hydrogen Energy 2008;33:1221–31.
[22] Lay JJ, Li YY, Noike T. The influences of pH and moisturecontent on the methane production in high solids sludgedigestion. Water Res 1997;31:1518–24.
[23] Logan BE, Oh SE, Van Ginkel SW. Biological hydrogenproduction measured in batch anaerobic respirometers.Environ Sci Technol 2002;36:2530–55.
[24] Marichamy S, Mattiasson B. Rapid production of cellulase-free xylanases by solventogenic clostridia from rumen.Enzyme Microb Technol 2005;37:497–504.
[25] Jo JH, Lee DS, Park D, Choe WS, Park MP. Optimization of keyprocess variables for enhanced hydrogen production byEnterbacter aerogenes using statistical methods. BioresourTechnol 2008;99:2061–6.
[26] Mizuno O, Dinsdale R, Hawkes FR, Hawkes DL, Noike T.Enhancement of hydrogen production from glucose bynitrogen gas sparging. Bioresour Technol 2000;73:59–65.
[27] Wang G, Mu Y, Yu HQ. Response surface analysis to evaluatethe influence of pH, temperature and substrateconcentration on the acidogenesis of sucrose-richwastewater. Biochem Eng J 2005;23:175–84.
[28] Mu Y, Wang G, Yu HQ. Response surface methodologicalanalysis on biohydrogen production by enriched anaerobiccultures. Enzyme Microb Technol 2006;38:905–13.
[29] Zinatizadeh AAL, Mohamed AR, Abdullah AZ, Mashitah MD,Hasnain Isa M, Najafpour GD. Process modeling and analysisof palm oil mill effluent treatment in an up-flow anaerobicsludge fixed film bioreactor using response surfacemethodology (RSM). Water Res 2006;40:3193–208.
[30] Chen WM, Tseng ZJ, Lee KS, Chang JS. Fermentativehydrogen production with Clostridium butyricum CGS5isolated from anaerobic sewage sludge. Int J HydrogenEnergy 2005;30:1063–70.