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                                                                                                                                                                 DOI: 10.3303/CET2294103 
 
 
 
 
 
 
 
 
 
 
 
 
 
 
 
 
 
 
 
 
 
 
 
 
 
 
 
 
 
 
 
 
 
 
 
 
 
 
 
 
 
 
 
 
 
 
 
 
 
 
 
 
 
 
 
 
 
 
 
 
 
 
 
 
 
 
 
 
 
 
Paper Received: 16  April  2022; Revised: 09  June  2022; Accepted: 16  June  2022 
Please cite this article as: Sakai Y., Nielsen C.M., Sato Y., Kato S., Kansha Y., 2022, Evaluation of the Dependence of Microbial Fuel Cells on 
Soil Composition and Water Content, Chemical Engineering Transactions, 94, 619-624  DOI:10.3303/CET2294103 
  

A publication of 

 
 CHEMICAL ENGINEERING TRANSACTIONS  

 

VOL. 94, 2022 The Italian Association 
of Chemical Engineering 
Online at www.cetjournal.it 

Guest Editors: Petar S. Varbanov, Yee Van Fan, Jiří J. Klemeš, Sandro Nižetić 
Copyright © 2022, AIDIC Servizi S.r.l. 
ISBN 978-88-95608-93-8; ISSN 2283-9216 

Evaluation of the Dependence of Microbial Fuel Cells on Soil 
Composition and Water Content 

Yuka Sakai, Christina M. Nielsen, Yuki Sato, Shoma Kato, Yasuki Kansha* 
Organization for Programs on Environmental Sciences, Graduate School of Arts and Sciences, The University of Tokyo, 3-
8-1 Komaba, Meguro-ku, Tokyo 153-8902, Japan 
kansha@global.c.u-tokyo.ac.jp 

In recent years, microbial fuel cells (MFCs), which utilize microorganisms in the soil, have been attracting 
attention as a new environmental power generation technology. Fuel cells (FCs), which have already been put 
to practical use in power generators and automobiles, use hydrogen as fuel and generate electric current using 
hydrogen's electrons. On the other hand, MFCs have the same principle as fuel cells but use organic materials 
as fuel. Microorganisms break down the organic materials to extract electrons. Various organic materials can 
be used as fuel, including sugars, carbohydrates, alcohols, agricultural wastewater, and sewage sludge. To 
expand the application of this technology, it is essential to study the use of freshwater with low conductivity and 
the optimal conditions of the soil environment. In this study, we focused on the moisture content of the soil to 
improve the efficiency of microbial fuel cells in freshwater. Soils with different moisture contents were prepared 
and used in microbial fuel cells to quantitatively evaluate the effect of moisture content on microbial power 
generation. Under conditions of MFC moisture content up to 82 %, the open-circuit voltage tended to increase 
with increasing moisture content; when MFC was kept stationary for five days, the highest power generation 
was observed at 86 % moisture content in the high moisture content region, and power generation tended to 
decrease as moisture content increased to 91 %. When MFCs with similar moisture content were mixed once a 
day, the amount of electricity generated grew higher when the moisture content was 91 % than when the 
moisture content was 86 %. 

1. Introduction 
The market size of energy harvesting technologies (Mateu and Moll, 2005) is growing. More research is being 
conducted on the effective use of novel light energy materials and dilute energy (Wang et al., 2018). Various 
methods have been developed for autonomous power supply technologies that support the IoT society, 
including technologies that use small temperature changes near room temperature, pressure, and 
microorganisms. Materials and systems that can flexibly adapt to the location of use are under construction. 
Among these, sunlight is moving toward higher efficiency, and next-generation solar panels (Hashemi et al., 
2020) and piezoelectric elements have become widely used (Liu et al., 2018). Research on unused thermal 
energy has been developing (Petsagkourakis et al., 2018), such as the use of changes in magnetic moments 
(Kansha and Ishizuka, 2019). Microbial fuel cells (MFCs) (Logan et al., 2006), which utilize microorganisms in 
the soil (Rabaey and Verstraete, 2005) as well as energy harvesting technologies (Rabaey and Verstraete, 
2005), have recently gained attention as a promising technology that can simultaneously purify soil and water 
quality. MFCs are based on the same principle as fuel cells (FCs). FCs are fueled by hydrogen and use electrons 
in the hydrogen to generate electric current, whereas MFCs are driven by organic matter and powered by 
microorganisms (Ferriday and Middleton, 2021). Electricity is generated using electrons released outside the 
cells as the microorganisms break down the organic matter (Logan et al., 2006). A schematic diagram of the 
interior of an MFC is shown in Figure 1. Electrons generated by the metabolism of electricity-generating 
microorganisms and reaching the anode electrode are consumed by reduction reactions at the cathode 
electrode via an external resistance. Organic materials such as sugars, carbohydrates, alcohols, agricultural 
wastewater, and domestic wastewater can be used as fuel in various states. MFCs are relatively inexpensive to 
produce and maintain because they use power-generating microorganisms such as Schwanella bacteria in soil, 

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which are ubiquitous. It can also be used in severely contaminated sites and is being studied as a technology 
used in various areas (Jatoi et al., 2021). In particular, its practical application in water treatment is increasing. 
Research is also underway to simultaneously generate electricity and treat wastewater using organic matter 
contained in wastewater and sludge and recover resources in wastewater (Ichihashi et al., 2012).  
Various styles of MFCs have been fabricated and studied, including one- and two-layer MFCs for the liquid 
phase, sediment microbial fuel cells (SMFCs) that use soil, and plant microbial fuel cells (PMFCs) that 
simultaneously grow plants. Among these, SMFCs can use not only sewage sludge but also a wide range of 
soils, such as those near rice paddies, estuaries, and lakeshores, and are being considered an effective method 
of generation technology, such as independent environmental power sources in non-electrified area (Srivastava 
et al., 2021). To increase power generation, it is desirable to have high nutrient and anaerobic conditions to 
make the power-generating microorganisms highly active. Sludge and sewage, highly nutritious for power-
generating microorganisms, are effective when used in cells (Xu et al., 2019).  
However, supposing the application of SMFCs is to be expanded as a power source in un-electrified areas. It is 
necessary to build SMFCs systems with high power generation capacity, even in freshwater with low conductivity 
and little organic matter. Adding organic matter and salts to improve conductivity for activating microorganisms, 
not for environmental cleaning, is an ecological burden (Abbas and Rafatullah, 2021). It has been confirmed 
that microorganisms can be activated if only the anode side is highly anaerobic, even when no organic matter 
is provided (Logan et al., 2021). On the other hand, the cathode side must be in a shape that facilitates oxygen 
supply. In SMFCs, if the moisture content of the soil is low, the anaerobic condition on the anode side is 
insufficient, and the electrical conductivity is low (Abbas and Rafatullah, 2021), resulting in lower mobility of 
hydrogen ions and lower power generation. If the moisture content is too high, the percentage of the electrolyte 
decreases. Depending on the cell conditions, the distance between the electrodes opens up, reducing the 
mobility of hydrogen ions and making it challenging to obtain electricity (Abbas and Rafatullah, 2021). Due to 
the complexity of the system, the relationship between soil water content and electricity production in SMFCs 
has only been discussed qualitatively.  
In this study, SMFCs with different soil moisture contents were fabricated using the same organic soil with 
uniform nutrient conditions, focusing on the effect of moisture content on the high nature of SMFCs. We 
quantitatively evaluated the impact of soil moisture content on power generation and provided a basis for 
constructing promising SMFCs even under freshwater and relatively low organic matter conditions. 

 
Figure 1: Schematic diagram of an MFC. Bacteria metabolize glucose in the anode chamber, and the electrons 
produced move from the anode to the cathode chamber, where they reduce oxygen. (Logan et al., 2006) 

2. Experimental Methods 
2.1 Preparation of SMFCs 

Wood chip-based organic soil was used for the preparation of SMFCs. First, to check the amount of water in 
the untreated soil, three 200 mL beakers were filled with 50 g of soil at a high fill rate. These beakers were 
placed in a thermostatic bath at 120 °C and recorded every 10 min until the change in mass was small (about 
300 min) (Figure 2). A 35 % decrease in mass was observed in all beakers after 300 min compared to untreated 
soil. When the soil was left in the thermostatic chamber, therefore an extended period, the soil mass gradually 
decreased. Imitating the conditions of the SMFCs to be made, we prepared 30 g of soil in a 200 mL beaker 
without compressing the soil and heat treated it at a lower fill rate, which resulted in an average mass loss of 47 

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%. It is believed that heat treatment at a lower fill rate sufficiently reduced the amount of water in the soil. In all 
studies, the dry reference moisture content of the untreated soil was assumed to be 47 %, and SMFCs were 
prepared with distilled water added for conditioning soils of different moisture contents. The soil weight used for 
all cells was adjusted to be the same for comparison for each study. Figure 3(a) shows a schematic of the 
SMFCs used in the experiment. A beaker (100-200 mL) was used with a 5 mm thick carbon felt electrode on 
the anode side and a 12 mm thick carbon felt electrode on the cathode side. The cell was prepared with 5 g of 
untreated soil (47 % moisture content) below the anode and 20 g between the anode and cathode, with 
anaerobic conditions on the anode side and aerobic conditions on the cathode side.  

2.2 Study to optimize the water content of the microbial fuel cell 

Four cells were prepared for each of the three types of SMFCs with different water content: 
 Group A was a cell with no distilled water added (47 % water content). 
 Group B was a cell with 25 g distilled water added (73 % water content). 
 Group C was a cell with 50 g distilled water added (82 % water content). 
Distilled water for moisture content adjustment was added evenly to the soil above and below the anodes to 
ensure that the water was evenly distributed throughout the cell (Figure 3a). The SMFCs were stored in 
desiccators under high humidity conditions, and the open-circuit voltage was measured as one of the methods 
to evaluate the performance of MFCs (Winfield et al., 2013). This method is predominantly used to check the 
power generation state until a specific voltage is reached due to increased microorganisms (Sanchez et al., 
2022). To evaluate the performance of each SMFCs, their stable open-circuit voltage values within 5 s were 
recorded once a day for 16 consecutive days with a digital multimeter (Linkman LDM81B). The results were 
used to investigate the relationship between the moisture content and the open-circuit voltage of the SMFC.  

2.3 The relationship between the water content of the microbial fuel cell and the amount of electricity 
generated 

SMFCs with water content was adjusted to 86 %, and 91 % were prepared. When the SMFCs were left for an 
extended period with a moisture content of 86 % or higher, the heavier soil was divided near the anode and the 
lighter soil near the cathode. A layer with shallow soil content and almost exclusively water was formed in the 
middle, as shown in Figure 3b. The effect of soil content on power production was investigated in two cells. The 
soil was left separated on the anode and cathode sides at each moisture content, and on the other, the soil was 
mixed once daily so that it would not be separated. Samples that were left separated were labeled "separated" 
and samples mixed daily to prevent separation were labeled "mixed. 
Current potential measurements were performed on these SMFCs using an Automatic Polarization System 
(Hokuto Denko Corp., HSV-110), with the anode side as the working pole and the cathode side as the pole 
counter electrode (Wang and Jiang, 2019). The voltage was swept from open-circuit voltage to 0 V at 10 mV/s. 
The Linear Sweep Voltammetry (LSV) results were used to determine the maximum value of power for each 
SMFC using equation (1) from the voltage and current values (Table 1). 

𝑃 = 𝐼 ∗ 𝑉 = 𝐼2 ∗ 𝑅 = 𝑉
2

𝑅   (1) 

 

Figure 2: Water lost by mass overtime during the first heat drying test 

 

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(a)                                                     (b) 

Figure 3: Schematic of the SMFCs layout used for the voltage test. Soil volume refers to dry base soil only. 
Water was distributed evenly throughout the cells. 

3.  Results and discussion 
3.1 Change over time of open-circuit voltage of MFC 

Figure 4 shows the change over time in the open-circuit voltage. The dashed line shows the measurement 
results for each cell, and the solid line shows the average of the results for each moisture content. The cells 
were stored in desiccators, but the cathode side was opened at the top to become aerobic, so the water in the 
soil tended to decrease slowly. Therefore, on days 7 and 14, evaporated water was added up to the specified 
amount. When compared in terms of average voltage, group C, with 82 % water content, had the highes showed 
little change in voltage to which no distilled water was added little change in voltage. Group B showed little 
change in voltage but only slightly higher than Group A. Group B, with 73 % moisture content, showed the 
highest average voltage. In contrast, Group C, with 82 % moisture content, showed the lowest average voltage. 
Group B, with 73 % moisture content, showed almost no increase in open-circuit voltage values after 16 days 
of measurements, confirming that 73 % moisture content is insufficient for SMFCs. It is considered that a higher 
moisture content facilitates the movement of electrons produced by microorganisms to the anode side and, at 
the same time, facilitates the diffusion of hydrogen ions produced, which reach the cathode side at a higher rate, 
resulting in a particular potential difference (Rossi et al., 2019). On the other hand, if the soil moisture content 
is low, the anode side does not become sufficiently anaerobic, making it difficult for microbial activity to increase.  
In addition, the measurement of electrical conductivity (EC) of soil is greatly affected by moisture, so it is 
necessary to make sure that all the objects being measured have the same specific moisture content (Abbas 
and Rafatullah, 2021). The lack of moisture content makes it difficult for the generated electrons to move to the 
anode side and, at the same time, prevents the migration of the generated hydrogen ions. Therefore, it is thought 
to be why a potential difference could not be observed. In this study, the voltage value tended to increase as 
the water content in the soil increased. However, if the water content increased significantly, the concentration 
of hydrogen ions generated by the power-generating microorganisms would decrease, and the arrival rate at 
the cathode side would also decrease. For Group C, with 82 % water content, a significant increase in open-
circuit voltage was observed immediately after the start. Since the water was spread over the entire soil, the 
generated hydrogen reached the cathode side, and the reduction reaction on the cathode side was considered 
to have progressed. However, the open-circuit voltage reversed for two of the four cells and temporarily 
observed an inversion of the open-circuit voltage. Voltage output has been reported to be stabilized by providing 
external resistance or by increasing the concentration of organic matter in the cell (Oh and Logan, 2007). Also, 
if the anode side is not sufficiently anaerobic or otherwise inactive for the bacteria, the amount of electricity 
generated will be insufficient, and voltage reversal will occur (Winfield et al., 2013). In the present case, the 
concentration of easily degradable organic matter was low, and the measurements were taken at open voltage. 
In addition, the anode side was not deep enough, so bacterial activity was not stable, and a voltage reversal 
was observed. The anode side must be more anaerobic to suppress a voltage reversal phenomenon. Therefore, 
power generation was examined using conditions where soil moisture content exceeded 82 %. 

3.2 MFC power generation in high moisture content region 

Table 1 shows the amount of electricity generated by each cell of SMFCs prepared with 86 % and 91 % moisture 
content five days after the start of the experiment. As the moisture content increases, the soil tends to separate 

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Figure 4: Initial daily voltage readings over 16 days. Samples from group A (blue) had a 47 % moisture content, 
group B (red) had a 73 % moisture content, and group C (green) had an 82 % moisture content.  

on the anode side and the cathode side after a long period of standing. Therefore, we prepared four types of 
cells, one in which the soil was left separated at each moisture content (separated) and one in which the soil 
was mixed once a day (mixed). This study showed that the 91 % water content separation generated the least 
power, 22.5 μW, and the mixed generated the most power, 30.5 μW. When comparing the power generation of 
the 86 % separation and 91 % separation left for 5 days, the 86 % separation showed a tendency to generate 
about 12 % more power. However, for the 86 % mixing and 91 % mixing, which were mixed once each day, the 
91 % mixing generated about 7 % more power. Comparing separation and mixing, the mixed mixture generated 
more power for the 86 % and 91 % moisture content cases, with a 13 % increase for the 86 % moisture content 
case and a 36 % increase for the 91 % moisture content case. Since all SMFCs were fabricated in the same 
vessel, the separation with 91 % water content has the anode located further away from the water surface. It 
is more anaerobic, and microorganisms are activated, resulting in higher power generation than the separation 
with 86 % water content (Rossi et al., 2019). It has also been reported that the addition of silica colloids to low-
conductivity paddy soil forms a network of silica colloids in the cells, which reduces soil resistance, resulting in 
increased ion mobility and a 10-fold increase in power generation (Garay et al., 2013). Mixing the separated 
solids and liquid may have contributed to the increase in power generation as the fine soil acted as a silica 
colloid. Therefore, in the 91 % mixed, microbial power generation increased due to increased anaerobic activity 
on the anode side. In the case of separation, on the other hand, the mobility of hydrogen ions is considered to 
be lower as the distance between the electrodes increases because there is less fine soil between the 
electrodes. 

Table 1 Relationship between fuel cell condition and power generation at 86 % and 91 % moisture content 

 86 % separated 86 % mixed 91 % separated 91 % mixed 

Power / µW 25.3 28.6 22.5 30.5 
 
Furthermore, forming an almost water layer in the middle of the SMFCs increases the resistance (Garay et al., 
2013). It reduces the probability of the generated hydrogen ions reaching the cathode side, which may have 
resulted in the 91 % water content separation producing less electricity than the 86 % water content. Although 
microorganisms are more active in regions of high water content and anaerobic activity, the relationship is 
thought to be reduced mobility due to increased solid-liquid separation. Therefore, it is believed that more power 
can be obtained by mixing solid-liquid when the percentage of the liquid phase is high. 

4. Conclusions 
In SMFCs, the open-circuit voltage and the amount of electricity generated tended to increase as the moisture 
content increased for conditions up to 82 %. The electricity generated was higher when the SMFCs were left to 
stand at 86 % moisture content than at 91 % moisture content. However, when the SMFCs were mixed, the 
amount of electricity generated was higher at 91 % moisture content, indicating that in systems with high 

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moisture content and solid-liquid separation, the amount of electricity generated tends to increase when the 
SMFCs are mixed. The results suggest that highly nutrient-rich soils, such as those contaminated with organic 
matter, and soils with relatively low organic matter, can quickly improve power generation by adjusting water 
content and mixing. For SMFCs with high water content and solid-liquid separation, various external vibrations 
from walking or vehicle driving can be amplified and incorporated into the solid-liquid mixing system in the 
battery, resulting in a location-independent, high-performance SMFC. So, the proposed system is a highly 
promising.  

References 

Abbas S. Z., Rafatullah M., 2021. Recent advances in soil microbial fuel cells for soil contaminants remediation. 
Chemosphere, 272, 129691. 

Ferriday T.B., Middleton P.H., 2021. Alkaline fuel cell technology - A review. International Journal of Hydrogen 
Energy, 46, 18489-18510. 

Garay A.D., Berna A., Bernad I. O., Nuńez A. E., 2013. Silica Colloid Formation Enhances Performance of 
Sediment Microbial Fuel Cells in a Low Conductivity Soil. Environmental Science and Technology, 47, 2117-
2122. 

Hashemi S.A., Ramakrishna S., Aberle A.G., 2020. Recent progress in flexible–wearable solar cells for self-
powered electronic devices. Energy and Environmental Science, 13, 685-743. 

Ichihashi O., Hirooka K., 2012. Removal and recovery of phosphorus as struvite from swine wastewater using 
a microbial fuel cell. Bioresource Technology 114, 303-307. 

Jatoi A.S., Akhter F., Mazari S.A., Sabzoi N., Aziz S., Soomro S.A., Mubarak N.M., Baloch H., Memon A.Q., 
Ahmed S., 2021. Advanced microbial fuel cell for water wastewater treatment—a review. Environmental 
Science and Pollution Research, 28, 5005–5019. 

Kansha Y., Ishizuka M., 2019. Design of energy harvesting wireless sensors using magnetic phase transition. 
Energy, 180, 1001-1007. 

Liu H., Zhong J., Lee C., Lee S.W., Lin L., 2018. A comprehensive review on piezoelectric energy harvesting 
technology: Materials, mechanisms, and applications. Applied Physics Reviews, 5, 041306 1-35. 

Logan B.E., Hamelers B., Rozendal R.A., Schroder U., Keller J., Freguia S., Aelterman P., Verstraete W., 
Rabaey K., 2006. Microbial Fuel Cells: Methodology and Technology. Environmental Science and 
Technology, 40, 17, 5181-5192. 

Mateu L., Moll F., 2005. Review of Energy Harvesting Techniques and Applications for Microelectronics. 
Proceedings of SPIE, 5837, 359-373. 

Oh S.E., Logan B.E., 2007. Voltage reversal during microbial fuel cell stack operation. Journal of Power Sources 
167, 11–17. 

Petsagkourakis I., Tybrandt K., Crispin X., Ohkubo I., Satoh N., Mori T., 2018. Thermoelectric materials and 
applications for energy harvesting power generation. Science and Technology of Advanced Materials, 19, 
836-862. 

Rabaey K., Verstraete W., 2005. Microbial fuel cells: novel biotechnology for energy generation. TRENDS in 
Biotechnology, 23, 6, 291-298. 

Rossi R., Cario B. P., Santoro C., Yang W., Saikaly P. E., Logan B. E., 2019. Evaluation of Electrode and 
Solution Area-Based Resistances Enables Quantitative Comparisons of Factors Impacting Microbial Fuel 
Cell Performance. Environmental Science and Technology, 53, 3977-3986. 

Sanchez C., Dessì P., Duffy M., Lens N.L.P., 2022. Gauging sediment microbial fuel cells using open-circuit 
auxiliary electrodes. Journal of Power Sources, 527, 231216. 

Srivastava P., Patil S.A., Yadav A.K., 2021. A comprehensive review on emerging constructed wetland coupled 
microbial fuel cell technology: Potential applications and challenges. Bioresource Technology, 320, 124376. 

Wang C., Jiang H., 2019. Real-time monitoring of sediment bulking through a multi-anode sediment microbial 
fuel cell as reliable biosensor. Science of the Total Environment, 697, 134009. 

Wang H., Jasima A., Chena X., 2018. Energy harvesting technologies in roadway and bridge for different 
applications – A comprehensive review. Applied Energy, 212, 1083. 

Winfield J., Greenman J., Huson D., Ieropoulos I., 2013. Comparing terracotta and earthenware for multiple 
functionalities in microbial fuel cells. Bioprocess Biosyst. Eng., 36, 1913–1921. 

Xu F., Ouyang D., Rene E. R., Ng H. Y., Guo L., Zhu. Y., Zhou. L, Yuan Q., Miao M., Wang Q., Kong Q., 2019. 
Electricity production enhancement in a constructed wetland-microbial fuel cell system for treating saline 
wastewater. Bioresource Technology, 288, 121462.

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