Microbial Fuel Cells (MFC) are a device or arrangements that provide bioactive
conditions for converting substrates to electricity energy via microbial catalyzed-redox
reactions (Du et al., 2007). The typical MFC
consists of two chambers, representing an anode and a cathode, where the anode
accepts electrons as a result of oxidation of the organic components and the
cathode, in aerated condition, allows the reaction of electrons in the chamber.
The two chambers are separated by placing a proton exchange membrane (PEM) allows
cation, principally proton, transport toward the cathode. Microorganisms cultivated
in the anodic chamber of MFCs are partially distributed (Du
et al., 2007), while the rest are attached to the electrode (Bond
and Lovely, 2003). Once the substrate are consumed and oxidized by the microbial
via metabolism process, electrons will be generated and transfer to the anode
surface. The electrons were transferred from anode to cathode by the way of
external circuit with loading. On the other hand, the associated protons are
transferred through PEM into the cathode by the internal electrolysis solution.
MFC yields currents that caused by the transport of electrons and ions. These
currents are limited by the following factors: (1) electrons activation in anode
and cathode surfaces caused by oxidation and reduction process, (2) electron
transfer from microbial cells to the anode and (3) internal resistances of the
circuit and anions passing through the PEM (Fu et al.,
2009). Therefore, concerning the above factors, this study was conducted
to observe the change of electrochemical parameters at different level of COD.
Various overvoltage loses based on fuel cell j-v behavior was represented using
fuel cell polarization model. The changes of OCV during the experiment, that
was only considered during the start-up and recovering of the MFCs voltage
after maximum current operation (Fu et al., 2009;
Wen et al., 2009) also was investigated. In the
present study, microbial communities obtained from POME sludge, was cultured
and tested in both POME and synthetic wastewater.
MATERIALS AND METHODS
Cultivation of POME sludge and biomass assay: The sludge culture was
obtained from anaerobic digester pond at Sri Ulu Langat Palm Oil Mill in Dengkil,
Selangor, Malaysia. It was cultivated in the Modified Wolfes Medium (Atlas,
2004) containing (g L-1): glucose 1.0; NaH2PO4.H2O
2.76; Na2HPO4 4.26; NH4Cl 0.31 and KCl 0.13,
10 mL Wolfes vitamin solution and 10 mL Wolfes mineral solution.
The cultivation was carried out in 2000 mL Duran bottle with 1000 mL of sludge
together with 1000 mL of wastewater from the collection site. The sludge mixture
was purged with Nitrogen gas to remove the oxygen and to keep the culture in
anaerobic condition. The mixture was continuously stirred with magnetic stirrer
to keep the culture active and the original POME sludge and wastewater that
contain high COD level (30000-50000 mg L-1) was removed in this stage.
The feeding of glucose only was started after the formation bubble appeared
on the surface had stopped intent to remove original high level of COD. The
stock culture was feed with modified Wolfes medium in room temperature
with temperature range of 28-30°C, for at least 2 times to obtain a stable
culture communities and controlled COD level in the sludge. Subsequently, the
culture was harvested by dewatering the sludge and transfer into the chamber
for MFCs experiment start-up.
Configuration of dual-chamber MFC: Two 500 mL MFCs were constructed by 0.8 cm thickness transparent poly-acrylic plastic and the dimension of each chamber has 8.2 (L), 9.0 (W) and 10.4 (H) cm. Plain carbon paper was used as electrodes for both anode and cathode, with size 9.0 (L), 5.0 (W) and 0.240 (T) cm. The electrodes were installed at the opposite end to each other or 7.3 cm apart. One of the electrodes was assigned as anode where the anaerobic culture was located, while the other one was assigned as a cathode. The electrode at cathode was coated with 0.5 mg cm-2 50% Pt/C catalyst to increase the reduction of oxygen. The culture medium in anode compartment, the Modified Wolfe Medium, plays a role as anode electrolyte. The cathode chamber was filled with only 50 mM PBS (in g L-1: NaH2PO4.H2O 2.76; Na2HPO4 4.26; NH4Cl 0.31 and KCl 0.13) and continuous air-sparged by aquarium pump. A proton-exchange membrane (Nafion 117) that clamped between the two compartments was used to separate the electrolytes while allowing transfer of H+ion through the membrane. Prior to use in the MFC system, membrane was treated by boiling in 30% H2O2, 0.5 M H2SO4 and washed in running deionized water for about 1 h. The assembled MFC chambers were filled with deionized water overnight before operation.
Analysis of power generation and treatment efficiency from MFC operation:
The two MFCs were operated at controlled temperature 35°C, in the water
bath. Half of total volume of MFC was added with POME sludge and topped up mixed
with Modified Wolfes Medium for total operating volume of 450 mL. For
long time operation, the readings of MFC voltage were registered every 15 min
using a true-rms digital multimeter (Fluke 289, USA), that was clipped on the
carbon paper by titanium binders. It was then connected to PC via USB-IR cable
interface. Different levels of COD by varying glucose concentrations were studied
to examine the effect on the open circuit voltage (OCV). The cells electromotive
force, OCV, without taking into account internal losses, is defined as the difference
in chemical potentials or thermodynamic state between the two electrodes (Logan
et al., 2006). The glucose concentration of 10.0 g L-1
was mixed into the culture medium to make final COD concentration of 10000 mg
L-1. Finally, the medium using fresh POME was also used and were
prepared with distilled water in ratio 1:10. When the time interval of taking
voltage reading had changed to 1 min, the performance of MFC and COD value were
registered every day. The readings of voltage were recorded at variable resistance
points and taken after 10 min to obtain the pseudo-steady state value. The adjustable
resistance value was varied from 1.0 M ohm to 1.0 K ohm and power density were
calculated according formula PD (mW m-2) = IDxV,
where ID is current density (mA m-2) which can be calculated
by ID = V/(RextxA) based on external resistance (Ω)
and projected surface area A (m2). Polarization curves were constructed
by plotting the value of cell voltage and power density against current density.
COD was determined by standard method using 10 mL COD vial supplied with digester
reagent COD range of 0- 1, 500 mg-COD L-1 (Hach, USA).
RESULTS AND DISCUSSION
MFC startup and OCV: Prior to start the experiments, the POME sludge
was settled and filtered with to remove bigger suspended solid from the sludge.
Amounts of 200 mL filtered sludge were taken and pour directly into the MFCs
chamber before starting up. The Open Circuit Voltage (OCV) was recorded with
the absence of current for some time (Fu et al.,
2009), increased gradually from zero. From the observation, the systems
only took less than 3 h to approach 0.8 V and the current remained zero during
this change. Since, the startup experiment has caused contact of biomass with
the electrode, the resulting transient dynamics of OCV responses occurred and
can be regarded as a general exponential curve during initial run. For the OCV
reading taking after phase of start up, the OCV was registered from the maximum
current to zero current which is shown under same plot with the start up OCV.
The transition of OCV responses is dependent upon the value of time constant
(RC), which is known as the product of internal resistance and capacitance in
MFC. The voltage, as function of both RC and time, is described in Eq.
1 (Floyd, 2004):
where V is the voltage reading, Vf is the OCV at the steady state, RC is the time constant and t is the time duration. To obtain the time as a constant, Eq. 1 can be further rearranged by linear relationship into Eq. 2:
By using the linearization curve fitting method, RC can be determined from
Fig. 1a, b and the results are summarized
in Table 1. The value of RC was 3.36 h for 3 750 mg-COD L-1
(10% POME) and 1.95 h for 10000 mg-COD L-1. High RC value occurred
at low COD have indicated that the potential generated was unstable at the anode
surface. However, the RC results from different level of COD have also shown
that the bacteria community tends to produce strong potential at the anode with
high range of COD supply and lower RC value. The time constant, RC represents
the characteristic of electronic circuit, which defined the necessary of time
space to reach 63.2% of the final steady state.
||Summary on RC value, steady state OCV at initial, maximum
power density and COD removal efficiency that achieved in different initial
|*Occurred at day 2 of experiment
The time constant and power
could be varied simultaneously as the internal resistance is reduced.
As the COD increased from 3750 to 10000 mg L-1, the respective initial OCV (Vf,o) also showed the increments from 0.0728 to 0.4112. Most Vf value were close to the higher value for several day and then, gradually fall to lower value toward the last day of operation. The Vf for MFC with COD 10000 mg L-1, was found fluctuated and unstable as show in Fig. 1b. However, the Vf was found more stable with COD 3 750 mg L-1.
||OCV with RC value determination curve based on Eq.
2 at different initial COD level (a) 10% POME (3 750 mg L-1);
(b) synthetic wastewater (10000 mg L-1)
Effect of power output on COD concentration: The MFC runs with 10% POME
supplied with different glucose concentrations was investigated to study the
effect of initial COD level on electricity generated. For every 10.0 g L-1
of glucose concentrations, COD value contributed into the system will be of
about 10000 mg L-1. Fresh POME used in this study was diluted beforehand
with distilled water in the ratio of 1:10. The initial MFC stabilized was at
OCV of 0.8-0.9 V. However, when the resistance was applied to the MFC at certain
resistance points, it caused the voltage to drop. The voltage had experienced
a sudden drop of voltage to 0.68 V when a 90 KΩ resistance was applied
and during that time, the scurrent density (current per electrode area) started
to increase from 0 to 0.07 mA m-2. In this experiment, various level
of resistance was applied, from 1 kΩ to 1 MΩ with the aims to observe
the effects of voltage and current density changes. Each of them took 10 min
or more to approach new pseudo-steady state and each data was taken at 1 min
interval. The time course of the current and power density generated by varying
COD concentration at different consecutive day are shown in Fig.
To test the effect on biomass activity, the MFCs experiments were run at different
COD and the power densities were noted everyday.
||Voltage and power performance curve for initial COD of (a)
10% POME (3 750 mg L-1) and (b) Synthetic wastewater (10000 mg
L-1) (other days data are not show)
Since the plot of voltage and current density against different resistance
are known from the previous polarization experiments, power curve could be obtained.
From the polarization curve, three zones can be divided into (1) activation
loses, (2) ohmic loses and (3) mass transport losses, where each is subjected
to the kinetics, overall resistance and ion transportation, respectively. The
MFC performance was determined by ohmic losses based on power density and polarization
curve. The power density was likely to increase at the beginning of the experiment
but decreased after day 3. The optimal power densities of MFC at 10000 and 3750
mg-COD L-1 (10% POME), was determined to be 3.115 and 1.780 mW m-2,
COD removal and treatment: The efficiency of MFC was observed by the power generation performance and removal of COD from the synthetic and real wastewater. After day 3 operations, the efficiency of total COD removal was 72.2% for the POME and 89.9% for the synthetic wastewater. Figure 3 shows COD removal at different initial glucose concentration begins from day 1 until day 13. The removal efficiencies were increase constantly from day 1 and reach maximum at day 10. The RC value, steady state OCV at initial, maximum power density and COD removal efficiency that achieved in different initial COD level was summarized in Table 1.
Polarization and power density at different COD condition: The maximum
current and power density were monitored every day during experiments. The value
of maximum current and power density that uses synthetic wastewater as starter
culture were observed. It was found that the values tend to increase from day
1 until day 2, before the value was decreasing after fresh wastewater was replaced.
||COD removal using POME sludge culture at different initial
||Maximum power densities and the current densities at Pmax
for POME and synthetic wastewater at different day of experiments
||Maximum current density & power density for COD 10% POME
and 10 000 mg L-1 at different day of experiment (others day
data are not shown)
From day 3 to day 8, the current and power density were found slightly decrease
due to the accumulation of metabolite product such as the accumulation of ion
H+ depressed microbial activities. The maximum value was constantly dropped after day 2 and finally maintain
to constant for the next consecutive days as shown in Fig. 4
and the results are summarized in Table 2.
MFC modeling: The mathematical expression for MFC could be written using
conventional fuel cell model (Wen et al., 2009):
where V is cell voltage when operating of fuel cell; Eo is predicted theoretical open circuitvoltage; ηact, ηomic and ηconc are voltage loses due to reaction kinetic, ohmic resistance and mass transport, respectively. The net fuel cell j-V behavior can be written in detail as:
||Averaged performance of MFC simulated from polarization model
using parameter as mention in Table 3
||Averaged electrochemical parameters subtracting from polarization
model based on Eq. 4)
|*Value at pmax
where ηact = b log ID, represents activation losses from both electrodes in MFC based on natural logarithm of Tafel equation η omic = RID, ohmic resistance losses based on current density ID and resistance R; ηconc = γexp(ωD) is combined fuel cell concentration loss, where γis a empirical constant and ω is fitting constant.
The experimental data was subjected to numerical simulation and was evaluate
to obtain a best fit of electrochemical parameters. The simulation code was
developed in MATLAB (version R2008a) using sum square error method (Mahreni,
2009). The regression value, R2 indicated best fit between experimental
and simulation data were set closed to 0.95.
The simulated results were show Fig. 2 (in different day and initial COD level) and Fig. 5 (averaged polarization curve) using electrochemical parameter from Table 3. The electrochemical parameters summaries in Table 3 indicated the effect of current limitation and total losses was eliminated at high COD level except ω value and increased power density. Figure 5 shows averaged power density that could achieve at different level of COD. Meanwhile, Fig. 6 shows current limitation due to voltage losses. Both curves show the concentration loss in MFC was dominant followed by ohmic and electrodes active loss.
||Voltage losses analysis based on polarization model for initial
COD level (a) 10 % POME (3 750 mg L-1) (b) synthetic wastewater
(10 000 mg L-1)
The RC obtained from OCV of MFC has shown getting lower value with higher COD concentration. The MFC needed longer time to reach its new steady stage OCV that recover from the maximum current operation. However, with the increment of lower initial COD level (3750 mg L-1) to high COD level (10000 mg L-1), maximum power density and COD removal were gradually increased. The COD removal efficiency has shown that the removal of 72.2% for higher COD concentration was obtained and for lower COD concentration, the removal was 89.9%. It means that the MFC work more efficient at lower COD concentration and produce higher power density at lower COD concentration. At 3750 and 10000 mg-COD L-1, optimal maximum power density (present current density) were 3.155 mW m-2 (9.322 mA m-2) and 1.780 mW m-2 (3.996 mA m-2), respectively. The results shown that power densities and COD removals were proportionally increase with increment of initial COD level in MFC. However, the relationship between RC values was inversely proportionally regarding to initial COD levels. Most of electrochemical parameters simulated from polarization model were decreased from 15-55% indicated the total losses was eliminated at high initial COD level. From the results, concentration loss was major loss in MFC followed by ohmic and electrodes active loss.
The authors would like to express their gratitude to the Ministry of Science, Technology and Innovation of Malaysia (GUP grant: GUP-BTT-07-30/187) and Malaysian Toray Science Foundation (Grant no. 09/G48) for the financial support to this study.