Evaluation of Separator Performance in a Vermiculture Based
Microbial Fuel Cell Assembly (VBMFC) with Eudrilus Eugeniae
Kristopher Ray S. Pamintuan
1,2,
Catherine Jill D. Brillas
1
, Ronalyn R. Inagan
1
1
School of Chemical, Biological, and Materials Engineering and Sciences, Mapua University, Muralla St., Intramuros,
Manila, Philippines 1002
2
Center for Renewable Bioenergy Research, Mapua University, Muralla St., Intramuros, Manila, Philippines 1002
Keywords: Vermiculture, microbial fuel cells, Eudrilus eugeniae, waste management
Abstract: Vermiculture-based Microbial Fuel Cells (VBMFC) generate electricity by using earthworms as catalysts that
speed up the degradation of bulk organic substrates, leaving simpler compounds for exoelectrogenic
bacteria to feast on. In this type of set-up, renewable electricity is generated while simultaneously reducing
the volume of solid waste. Eudrilus eugeniae, commonly known as African nightcrawler, was used as the
model earthworm for this study. The worms were fed with a total of 1.854 kg of watermelon peels. These
peels act as the substrate for the bacteria to metabolize and generate electricity. The main objective of the
study is to determine what type of separator would yield a higher power output. Results show that the
control system (no separator) produced the highest maximum voltage of 40.5 mV. On the other hand,
VBMFCs with clay membranes had the highest average voltage of 9.68 mV. Polarization curves were used
to measure the optimal current, maximum power density, and internal resistance of the three systems. The
control system had the largest optimum current density of 1.23 mA/m2 and the highest maximum power
density of 0.056 mW/m2. On the other hand, vessel that had cotton cloth as separator had a better current
density and maximum power density than the vessel with clay membrane, which offered the most
resistance. Overall, the absence of a separator seems to benefit power generation, as well as helping to offset
the cost of construction as the membrane separator often is the most expensive part of the set-up.
1. INTRODUCTION
The energy demand in the world right now continues
to increase and it prompts an increased usage of
fossil fuels, consequently trigerring environmental
pollution. The dependence on fossil fuels, such as oil
and gas, is not sustainable in view of the fact that it
is limited, its supply is decreasing, and it poses
negative effects on the environment. As a result of
this, many researches are focused on alternative,
renewable, and also carbon neutral energy sources
which are necessary for the sustainability of the
environment and economy [1].
The global community recognized that solid
waste management is an issue that requires serious
attention. The aggressive pursuit for economic
growth, by developing countries like the Philippines,
has resulted in the manufacture, distribution and use
of products and generation of wastes that contributes
to enhanced environmental degradation [2]. In the
past years, the Microbial Fuel Cell (MFC)
technology has gained the attention of the scientific
community due to its attractive quality of being able
to cleam wastewater while generating electricity [3].
MFC are devices in which bacteria generate
electrical power by oxidizing simple compounds
such as dissolved organic matter in wastewater. This
technology depicts a new and promising approach
for power generation. MFCs not only clean
wastewater, but they also transform organics in the
wastewater into energy that can be useful. With the
world’s finite supply of fossil fuels and the impact of
fossil fuels on climate change, the ability of MFC
technology to generate renewable and also carbon
neutral energy has cause huge interest globally.
MFCs have been broadly seen as a standout amongst
the most promising alternative sources of renewable
energy [4].
The success of MFCs do not come without
limitations. For one, it mainly relies on wastewater
for its source of energy. To solve solid waste
management issues, the MFC needs to be modified
to accommodate soil-based decomposition. With
that, the concept of a Vermiculture-based Microbial
Ray S. Pamintuan, K., Jill D. Brillas, C. and R. Inagan, R.
Evaluation of Separator Performance in a Vermiculture Based Microbial Fuel Cell Assembly (VBMFC) with Eudr ilus Eugeniae.
DOI: 10.5220/0008656700410045
In Proceedings of the International Conference on Future Environment Pollution and Prevention (ICFEPP 2019), pages 41-45
ISBN: 978-989-758-394-0
Copyright
c
2019 by SCITEPRESS Science and Technology Publications, Lda. All rights reserved
41
Fuel Cell (VBMFC) was born. In this set-up, solid
biodegradable waste is fed to earthworms, much like
in vermiculture. The worm castings then become a
prime nutrient source for bacteria to consume and
generate electricity with carefully-placed electrodes.
Desirable qualities for a VBMFC would be high
power generation, low internal resistance, and low
cost, much like in MFCs. Earthworm selection is
also to be considered. Commonly, Red wigglers
(Eisenia fetida) are thought to be the most adaptable
of all the vermicomposting worms, but comparing it
with other worms in terms of selected parameters
(e.g. size, time of maturity, incubation time, ideal
working temperature, etc.), the African nightcrawler
seems more capable. In laboratory tests, E. eugeniae
outperformed E. fetida at in tests
utilizing cattle manure as the feedstock. Also, some
assert that E. eugeniae also slightly sensitive to
handling and disturbance. It appears that it is not
usual for E. eugeniae to start roving after disturbance
or even clear reasons at all. That being said, E.
eugeniae appear to be the most popular choice
among vermicomposters due to its quick growth and
bigger size compared to E. fetida [5].
There are still some ongoing studies on ways to
collect electricity from different variants of MFC
like Plant-Microbial Fuel Cells (PMFCs) [6] and
Constructed-Wetland Microbial Fuel Cells
(CWMFCs). However, there are no studies that
explore VBMFCs for their power generation and
waste management capabilities. In terms of its
operation, it is similar to an MFC but differs on the
substrate. Conventionally, MFCs include a
membrane separator to segregate charges in the
anode and cathode compartments. However,
commercially available membranes are costly, and it
is generally attractive for MFC technology to be
low-cost. Thus, alternative materials are to be
sought. The objective of this study is to determine
the performance of cotton cloth and clay as
membrane separators in VBMFC using E. euginae
as decomposer. In addition, polarization curves will
be used to measure the optimal current, maximum
power, and internal resistance of the VBMFCs.
2 METHODOLOGY
2.1 VBMFC Design
The VBMFC assembly is shown in Figure 1.
Polycarbonate plastic was cut and assembled into a
rectangular vessel measuring 12 inches by 6 inches
with a height of 8 inches. The edges were then
sealed with hot glue and duct tape. Two carbon fiber
sheets measuring 6 inches by 8 inches each were
attached to the inner opposite sides of the vessel to
act as electrodes. Alligator clips were latched into
the top part of the carbon fiber to attach them to
copper wires. The other ends of the connecting wire
were connected to an external 2000 ohms resistor to
continuously polarize the set-up. The experimental
separators were attached as seen in Fig. 1. Two types
of separators were tested against a control: clay and
cotton cloth. Both types of separators were cut to the
size of the set-up cross-section and attached to the
containers. Moist loam soil was used to fill the
container. Triplicates were prepared for every
experimental set-up.
2.2 Experimental Set-up
E. euginae was obtained from a vermiculture farm in
Manila, Philippines. 50 adult worms were placed in
the anodic compartment for set-ups with separators,
and were scattered in the control set-ups (without
separator). Since the worms are sensitive to light, all
set-ups were covered with dark-colored cloth to
maintain a dark environment without suffocating the
worms. Good moisture was maintained by daily
spraying of distilled water, taking care not to flood
the set-ups.
The worms were fed starting on their second day
on the containers with fresh watermelon peels. They
were fed ad libitum, although care was exercised to
not let the watermelon peels decompose before they
were consumed. 5-g portions of peels were added in
every container until it is consumed.
Figure 1. Vermicultue-based microbial fuel cell
(VBMFC) assembly
2.3 Data Acquisition and Analysis
The voltage of the VBMFC set-ups were manually
measured everyday against a 2000-ohm resistance,
for 25 days, using a digital multimeter (RS Pro
RS14). From the gathered data, power can be
ICFEPP 2019 - International conference on Future Environment Pollution and Prevention
42
determined ( ) as well as power density
( ). All parameters were plotted against
time to analyse their evolution as the assembly
matures. Polarization curves were generated at the
end of the experimental period.
3. RESULTS AND DISCUSSION
3.1 Voltage of VBMFCs
As seen on Fig. 2, the maximum average voltage for
the control was obtained on day 23 with a value of
0.405 V and the lowest average voltage on day 8
with a value of 0.001 V. For the cotton separator, the
maximum average voltage was obtained on day 17
with a value of 0.025 V and the lowest average
voltage on days 2 and 5 with a value of 0.001 V.
Lastly, for the clay separator set-up, the maximum
average voltage was obtained on day 18 with a value
of 0.0255 V and the lowest average voltage on days
2, 5 and 12 with a value of 0.001 V. These are
summarized in Table 1.
The maximum voltage of the control system is
significantly higher than the experimental cotton and
clay separators . In terms of the average
voltage, there is no significant difference between
the values from the control and the clay separator,
although both are significantly larger than that of the
cotton separator. For voltage readings, it can be seen
that using a clay separator or no separation at all is
more advantageous than using cotton.
There are some factors that may hinder the
VBMFC from generating its maximum potential
voltage, one of which is resistances, both inherent
and induced. In the operation of the VBMFCs, the
junctions between the electrodes and the connecting
wires are often sources of resistance from rusting.
Another factor to consider is the adaptation of
bacteria to the working environment and the
formation and destruction of exoelectrogenic biofilm
in the electrodes due to the constant movement of
earthworms.
3.2 Polarization
The constructed polarization curves are shown in
Fig. 3.
The control system had the highest optimum
current density of 1.227 mA/m
2
amongst the other
systems. Control system is a Single Chamber MFC
(SC-MFC) which does not incorporate the use of
membranes. In Ohms law, current is inversely
proportional to resistance. Therefore, higher current
occurs at lower internal resistances [7] .
(a)
(b)
(c)
Figure 2: Average voltage measured from the constructed
VBMFCs: control (a), cotton separator; (b), and clay
separator (c)
In another context, the control system had the
highest Maximum Power Point (MPP) obtained at
0.0560 mW/m
2
. The maximum output power of the
fuel cell is proportional to the square of the open-
circuit voltage and is inversely proportional to its
Evaluation of Separator Performance in a Vermiculture Based Microbial Fuel Cell Assembly (VBMFC) with Eudrilus Eugeniae
43
internal resistance. When the load resistance is equal
to the internal resistance, the output power of the
fuel cell is at the maximum. Thus, monitoring the
internal resistance of the microbial fuel cell
effectively is not only the necessary condition for
realizing the maximum power output, but also a key
action to ensure the health and performance of the
microbial fuel cell.
Table 1. Maximum and average voltage of
VBMFC
System
V
max
(mV)
V
ave
(mV)
Control
40.5
8.89
Cotton cloth membrane
25
5.36
Clay membrane
25.5
9.68
Table 2. Maximum Power and Optimum
Current Density of VBMFC
Syste
m
Int
ernal
Resista
nce (Ω)
Maximum
power
density
(mW/m
2
)
Contro
l
12
40
0.0560
Cotton
cloth
28
74
0.0030
Clay
54
93
0.0009
On the other hand, the vessel with cotton cloth as
membrane had a better current density and
maximum power than the vessel with clay
membrane. These dual chamber MFC corporates
membranes that allows internal ionic fluxes but
prevents mixing of anodic reducing solution and
cathodic oxidant. This membrane, however, is one
of the principal cost factors in an MFC plant and
increases the cell’s internal resistance [8]. Other
factors that contributes to lesser conductivity and
power are ohmic losses, activation losses and
microbial losses. Ohmic losses can be reduced by
minimizing the electrode spacing, using a membrane
with a low resistivity and checking thoroughly all
contacts. Low activation losses can be achieved by
increasing the electrode surface area, improving
electrode catalysis, increasing the operating
temperature, and through the establishment of an
enriched biofilm on the electrode.
4. CONCLUSIONS
This study has shown that electricity generation is
possible in a VBMFC, albeit its magnitude is still
small compared to other sources of energy. The set-
ups with no membrane separators exhibited the
highest voltage, current density, and power density,
along with the lowest internal resistance. With
regard to the two experimental separators, cotton
cloth exhibited less internal resistance and thus
would lead to higher power density compared to the
clay separator. All of these were confirmed by
polarization studies. The elimination of the
membrane separator would cut down significantly
on the building cost of VBMFCs.
(a)
(b)
Figure 3: Polarization curves of VBMFCs with
cotton separator (a), and clay separator (b)
It is therefore recommended for future studies to
further develop the VBMFC technology through
optimizations for electrode materials, substrate, type
of earthworm, and configurations.
ICFEPP 2019 - International conference on Future Environment Pollution and Prevention
44
REFERENCES
[1] M. S. Guney and Y. Tepe, “Classification and
assessment of energy storage systems,”
Renewable and Sustainable Energy Reviews, vol.
75. pp. 11871197, 2017.
[2] N. Hussain, S. Das, L. Goswami, P. Das, B.
Sahariah, and S. S. Bhattacharya, “Intensification
of vermitechnology for kitchen vegetable waste
and paddy straw employing earthworm
consortium: Assessment of maturity time,
microbial community structure, and economic
benefit,” J. Clean. Prod., vol. 182, pp. 414426,
2018.
[3] C. Santoro, C. Arbizzani, B. Erable, and I.
Ieropoulos, “Microbial fuel cells: From
fundamentals to applications. A review,” J.
Power Sources, vol. 356, pp. 225244, 2017.
[4] B. E. Logan et al., “Microbial fuel cells:
Methodology and technology,” Environmental
Science and Technology, vol. 40, no. 17. pp.
51815192, 2006.
[5] A. J. Reinecke and S. A. Viljoen, “Effects of
worm density on growth and cocoon production
of the african nightcrawler Eudrilus eugeniae
(Oligochaeta),” Eur. J. Soil Biol., vol. 29, no. 1,
pp. 2934, 1993.
[6] K. R. S. Pamintuan, J. A. A. Clomera, K. V.
Garcia, G. R. Ravara, and E. J. G. Salamat,
“Stacking of aquatic plant-microbial fuel cells
growing water spinach (Ipomoea aquatica) and
water lettuce (Pistia stratiotes),” IOP Conf. Ser.
Earth Environ. Sci., vol. 191, 2018.
[7] L. P. Fan and J. J. Li, “Overviews on internal
resistance and its detection of microbial fuel
cells,” vol. 10, 2016.
[8] A. G. Capodaglio et al., Microbial Fuel Cells
for Direct Electrical Energy Recovery from
Urban Wastewaters,” vol. 2013, 2013.
Evaluation of Separator Performance in a Vermiculture Based Microbial Fuel Cell Assembly (VBMFC) with Eudrilus Eugeniae
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