In-situ Evaluation of Different CAM Plants as Plant Microbial Fuel Cells for Recovery Energy in Atacama Desert

1. Introduction

The effect of climate change, pollution, and the depletion of natural resources, with the high percentage of the population living in areas with water scarcity (over 2.4 billion inhabitants), has led to the search for new forms of sustainable energy, such as photovoltaic systems [1] The recent trends worldwide are focused on developing technologies and innovations that allow the supply of energy to the population without generating a negative impact on the territory and environment. The Sun is the primary source of energy that supplies most of the processes on Earth and the Sun a year is greater than the total of all existing fossil energy resources on the planet. Despite this, there are still problems with making the most of solar resources, such as (i) the discontinuity of the resource and (ii) the high level of radiation dispersion, which generates a non-uniformity of the resource because of the movement of the Earth around the Sun. The reference data of solar radiation, which are the solar constant and the spectral distribution, are established for the average sun-earth distance conditions. The solar constant is the energy that falls per unit area and per unit time on a surface normally oriented to the direction of propagation of solar radiation and located outside the Earth's atmosphere. This value varies slightly and is equivalent on average to 1367 W m^-2. [2,3] The radiation emitted by the Sun is distributed over a wide spectrum of wavelengths, with most of the radiated energy corresponding to the portion between 150 and 3000 nm, with a spectral distribution very similar to that produced by a black body at 5777 K. About half of this energy falls within the visible band, 390 to 770 nm. The rest corresponds almost entirely to infrared radiation, with a small percentage of ultraviolet radiation.

The Plant Microbial Fuel Cell (PMFC) uses plants and bacterial communities, principally the Geobacter genus, to generate electricity through natural processes that occur in the roots of plants. [4,5,6,7,8,9,10,11], One of the main challenges with the current state of technology is its power output. Even though the theoretical power output is estimated at 3.2 W m^-2 in systems [12] with plants as the sole organic matter source [13,14,15]. The power yield of the PMFC can reach 1000 GJ ha^-1year^-1 by considering a multidisciplinary European research consortium, and the hypothetical PMFC power yield of 21 GJ ha^-1 year^-1 is generally a traditional device [12]. When applied in an indigenous habitat, the power yield of PMFC is assessed to be limited to 1.6 MW km^-2 [16]. While wind turbines and solar panels could create 5 to 7.7 MW km^-2 and 4.5 to 7.5 MW km^-2 respectively, on a typical windy day under Western European conditions [9].

Plants produce organic material from sunlight and environmental CO₂ through photosynthesis. About 70% of the organic material ends up in the soil as dead root debris, mucilage, and exudates [17,18,19,20,21,22]. The organic material that fixes the plants in the soil can be oxidized by the rhizosphere bacterial community’s releases of CO₂, protons (H⁺), and electrons (e^-). These e^- are donated by bacteria when operating their metabolic processes. The H⁺ and dissolved O₂ are part of O₂ reduction reaction (ORR) mechanisms, generating electrical work during e^- reduction. [23,24]The PMFC device is considered a specific solar cell, transforming the biochemical energy to electricity under specific electrochemical work [16]. The materials used as electrodes have total relevance. Various materials, such as Cu, Ni, C (graphite), Ti, and among others, have been tested as anode materials because of their catalytic activity. [25,26] The Cu metal has the following characteristics, (i) it is known to be an antimicrobial material (Cu ions are toxic for the planktonic bacterial cells and prevent biofilm formation), (ii) the Cu conductivity is close to 900 times well than the polycrystalline graphite, (iii) decrease the internal resistance, and (iv) reduce the amount of required electrode material considerably [27,28,29,30]. The Cu corrosion products avert the creation of electrochemically active biofilms over the Cu anode electrode, especially during the start-up of the electrochemical period when biofilm formation still must take place, and the anode potential due to the missing reduction power of a fully established microbial biofilm may shift into the corrosion potential. [31,32] On the other hand, stainless steel AISI 316L materials are used as cathode electrodes with interesting performance [22,33]. The potential difference between the anode and cathode simplifies the movement of e^- by an external circuit to decrease an e^- acceptor such as O₂ at the cathode surface. [34,35] Using this renewable energy is an imperative need to develop agriculture even in the most desert-like climates with plants growing locally.

It is one of those rare studies to analyze the in-situ behavior of CAM plants for possible use as PMFC. This study is based on the extensive data obtained from the application of AISI 316 and Cu electrodes in different CAM plants that can grow at considering the following (i) high levels of solar radiation, (ii) tolerance to water stress, (ii) resistance to temperature variations present, and (iv) different open circuit potentials (OCP) behavior.

2. Materials and Methods

2.1. Open Circuit Potential (OCP) Monitoring.

The experimental procedure was designed to examine the potential (V) generation from in situ CAM plants in Calama located in Atacama Desert. The electrodes used were a Cu plate as an anode and an stainless steel AISI 316L plate as a cathode of 10 cm². The PMFC single chamber with electrodes thoughtfully positioned around the rhizosphere (1mm distance) represents a sophisticated bioelectrochemical marvel. It ingeniously taps into the dynamic metabolic interplay of soil-dwelling microorganisms amidst plant roots to orchestrate a remarkable feat: the generation of electricity. This ingenious setup capitalizes on the intrinsic synergy between plant biology, microbial consortia, and conductive materials to efficient electron transfers, culminating in electric current. The rhizosphere, the bustling realm where plant roots and the soil meet, becomes a nexus of activity. The roots exude is used as a spread for the resident microorganisms located in the rhizosphere. These electrons, tiny messengers of potential energy, traverse the conductive material of the anode electrodes, forging an intimate connection between the living world below and the inanimate electrode realm above. The study was designed considering 2 stations of study in the Atacama Desert climate. The CAM species were selected for their characteristics such as resistance to high levels of solar radiation, tolerance to water stress, and resistance to sudden variations in temperature. All experiments used a data logger AEMC model L452 for continuously collecting OCP potential fluctuations. The PMFC was monitored for periods of 8 days on average. The recording intervals of the sampled information are every 1 second for the variables potential (V), temperature (°C), relative humidity (RH, %), and radiation (Wm^-2) using the horizontal global radiation.

2.2. Electrodes Surface Characterization.

The morphological analysis of the cathode and anode electrode surface was characterized by scanning electron microscopy (SEM), using a Hitachi SU 500 microscope.

2.3. Meteorology Monitoring.

The experiment was carried out in Calama (Figure 1). This city is located at 2260 m.a.s.l. in the Atacama Desert (22° 28′ 0″ S, 68° 55′ 60″ W). It presents a Köppen climate rating of type BWk', which corresponds to a cold arid zone (Figure 1a) [36]. It offers an excellent quality of solar resources which shows an average per day of 7.22 kWh m^-2 of global horizontal irradiance (GHI), obtaining a total of 2,632 kWh m^-2 annually. This zone is characterized by annual precipitation that does not exceed 50 mm year^-1, which is reflected in clear skies throughout the year, as shown in Figure 1b) (satellite image taken by MODIS-Terra, instrument from space, August 23^rd, 2022) [37]. The atmospheric parameters involved in the study were evaluated with a meteorological station in the city. Ambient Temperature (Tamb) and relative Humidity (RH) were measured with a young thermometer and hygrometer models CS215-L11 and hmp60-L11, respectively. Global horizontal irradiance (GHI) was measured with a Kipp & Zonen CMP21 pyranometer. The resolution of each measured parameter was 1s and was recorded as an average value per minute.

2.4. Experimental Data Analysis.

The model L452 datalogger records data by voltage (V) with a voltage range of 1V and an internal impedance of 1 MΩ (ref). The experimental data, for each test, were conducted between 06/07/2020 and 19/08/2020, with a sampling resolution of 1 minute. The cumulative energy generated by the plants needs the following sequence.

The current generated during the experiments was calculated using Ohm's law, according to the following expression.

$$I_p=\frac{V_p}{R};$$

(1)

where $I_p$ is the current generated from the plants in A, $V_p$ is the potential generated for the plants of the experimental measurements in V, and R is the impedance resistance of the equipment in Ω, respectively.

The power generated by the plants is calculated according to Equation 2.

$$P_p=V_p\bullet I_p;$$

(2)

where $P_p$ is the power generated from the plants in W, $V_p$ is the potential of the experimental measurements in V, and $I_p$ is the current calculated using equation 1.

Finally, the accumulated energy recovery from the plant was obtained by calculating the area under the curve using the trapezoid method. according to the following expression.

$$E=\frac{(P_{p\_n}+P_{p\_n+1})\bullet (t_{n+1}-t_n)}{2};$$

(3)

where E is the energy generate for each plant during the experiment in Wh, $P_{p\_n}$ is the power in W calculated using equation 2, t is the time in minutes, and n is the number of samples, respectively [39,40].

2.5. CAM Species Plants as PMFC.

The species used were seven and are (i) Aloe perfoliate [41,42], (ii) Cereus jamacaru [43,44,45,46,47], (iii) Austrocylindropuntia subulate [48,49,50], (iv) Agave potatorum [51,52,53,54,55], (v) Malephora crocea [56,57], (vi) Kalanchoe daigremontiana [58,59,60,61,62,63] and (vii) Aloe arborescens [64,65,66]. The soil used was a commercial composed of forest residues such as pine bark and sawdust and seaweed residues, with apparent density 0.4-0.7, pH (Dilution 1:5) 5-8.5, Electrical Conductivity (EC) Dilution 1:5) < 3 dS/m, C/N relation < 50 for each PMFC. The condition monitoring as climatic conditions was not controlled, being subjected to high or extreme levels of solar radiation, high temperature, and humidity relative fluctuations. The water supply to the system was controlled by watering the plants with only 100 ml every 7 seven days (before installing the electrodes) to generate a medium with high water stress.

3. Results and Discussion

The behavior of the open circuit potential (OCP, V) of the different PMFC concerning meteorological variables, such as (i) solar radiation, (ii) atmospheric humidity, and (iii) ambient temperature during a specific period are represented in Figure 2, Figure 3 and Figure 4. Generally, the OCP performance of each PMFC presents a notable variability; however, they all present a cyclical behavior concerning the atmospheric variables analyzed in this study.

The species Cereus jamacaru and Kalanchoe daigremontiana represented in Figure 2c,f, respectively, show a notable cyclic behavior of the OCP concerning solar radiation, generating an OCP of 0.187 and 0.248V with a radiation level of 886.5 W m^-2 and relative humidity in 8 days of analysis. The same cyclic behavior, despite not being so evident, is exhibited by Austrocylindropuntia subulata represented in Figure 2a, but from the second day of measurement, presenting its maximum OCP about 0.240 V in the periods of maximum solar radiation and relative humidity of about 942 W m^-2 and 61% represented in Figure 3g. On the other hand, Aloe arborescens and Aloe perfolia represented in Figures 2g and 3b, show slight peaks in periods of higher solar radiation, generating a maximum OCP of 0.295V with solar radiation and an atmospheric humidity of 872 W m^-2 and 54%, however, A. arborescens presents a more stable output potential compared to Aloe perfolia and the other species concerning time. Contrary to the previous cases, Malephora crocea and Agave potatorum represented in Figure 3d,e, do not show a good performance, however, their maximum OCP was 0.250 and 0.167V, respectively.

Figure 3. Potential (blue line) vs Atmospheric Humidity (green line) (a) Austrocylindropuntia subulata, (b) Aloe perfoliata, (c) Cereus jamacaru, (d) Malephora crocea, (e) Agave potatorum, (f) Kalanchoe daigremontiana, and (g) Aloe arborescens.

Figure 3. Potential (blue line) vs Atmospheric Humidity (green line) (a) Austrocylindropuntia subulata, (b) Aloe perfoliata, (c) Cereus jamacaru, (d) Malephora crocea, (e) Agave potatorum, (f) Kalanchoe daigremontiana, and (g) Aloe arborescens.

The behavior of PMFC concerning ambient temperature shown in Figure 4, generally maintains behaviors that are inversely proportional to humidity and directly proportional to solar radiation, so that in most cases, results like those from the analysis of radiation and humidity will be obtained. The performance for each of the seven plant species, even though not all of them behaved in the same way, is an expected result since they are different plant species with the same photosynthetic path. These will consist of a different rate of fixation of organic matter through its exudation in the rhizosphere, which will lead to variations in the colonies of electrogenic microorganisms.

The meteorological variables must play a fundamental role in the performance of the PMFC, as was observed in the results, in general, the majority of the plant species present a cyclical behavior of the generation of electrical energy, being directly related to the cycle of solar radiation from which two assumptions can be deduced, the first being that the performance is influenced by photosynthetic activity, produced by the greater activity of the stomata, which generates greater secretion of organic matter to the rhizodeposits, which triggers a greater activity of the rhizobacteria (responsible for generating electrical energy) due to an increase in the electrical interactions of the cell membrane as they have a greater amount of resources to metabolize. As a second assumption regarding the correlation of cell potential concerning meteorological variables, it consists of the availability of molecular O₂ in the cathodic zone that can be generated at times of greater solar radiation, which triggers an increase in ambient temperature (see Figure 4), which generates greater evaporation. of the substrate reducing humidity and a decrease in relative humidity that is related to the possible contribution of moisture to the substrate. This effect would trigger an increase in the efficiency in the anodic zone, since the greater the availability of O₂, the greater the rate of reduction of O₂ in H₂O, due to the effect of the ORR, with the 4e^- consume predominating direct formation of H₂O, compared to the 2e^- consume, which is less efficient and generates H₂O₂, which is harmful to microorganisms, which would affect the generation of electrical energy by reducing the microbial population of the electrochemical system.

Figure 4. Potential (blue line) vs Ambient Temperature (orange line) (a) Austrocylindropuntia subulata, (b) Aloe perfoliata, (c) Cereus jamacaru, (d) Malephora crocea, (e) Agave potatorum, (f) Kalanchoe daigremontiana, and (g) Aloe arborescens.

Figure 4. Potential (blue line) vs Ambient Temperature (orange line) (a) Austrocylindropuntia subulata, (b) Aloe perfoliata, (c) Cereus jamacaru, (d) Malephora crocea, (e) Agave potatorum, (f) Kalanchoe daigremontiana, and (g) Aloe arborescens.

Figure 5, illustrates the energy recovery performance of each plant concerning the prevailing environmental parameters, including solar radiation, relative humidity, and temperature according to equations 1 to 3. These graphs visually represent the correlation between these factors and the amount of energy harnessed by the plants through their microbial fuel cell systems. By examining the trends depicted in Figure 5, we can gain valuable insights into how variations in solar radiation, relative humidity, and temperature influence the overall energy generation potential of the plant microbial fuel cells. The data presented in this figure plays a crucial role in understanding and optimizing the efficiency of these sustainable energy conversion systems in diverse environmental conditions.

The experiment using CAM plants in PMFC yielded promising results, showcasing the energy recovery capabilities of each plant. The accumulated energy recovery values, measured in mWh m^-2 of electrodes,: (i) Aloe perfoliata demonstrated an impressive energy generation of 5.9 mWh m^-2, (ii) Cereus jamacaru exhibited a respectable energy production of 2 mWh m^-2, (iii) Austrocylindropuntia subulata displayed a remarkable energy generation of 8.8 mWh m^-2, (iv) Agave potatorum demonstrated a noteworthy energy production of 7.8 mWh m^-2, (v) Malephora crocea showcased a considerable energy generation of 3.2 mWh m^-2, (vi) Kalanchoe daigremontiana displayed a significant energy production of 9.4 mWh m^-2, (vii) Aloe arborescens exhibited a commendable energy generation of 4.1 mWh m^-2. These energy recovery values demonstrate the potential of various CAM plants as efficient candidates for sustainable energy conversion in PMFC systems. The results offer valuable insights for optimizing and selecting suitable plant species to maximize energy generation in different environmental conditions, paving the way for eco-friendly and renewable energy solutions.

Plants have a characteristic that allows them to be grouped into three different types, depending on the environment in which they develop, they will have, to a greater or lesser extent, regulated something known as photorespiration, which is responsible for regulating the loss of water present in the plants. The photosynthetic pathways classifying into three classes: C3, C4, and CAM [56]. The plants in each class differ from each other. The efficiency of C4 plants in the photosynthesis process is higher than the other categories [21] reaching a maximum limit of 6% compared to C3 and 4.6% compared to CAM plants. They are the photosynthetic efficiency that defines the rate of conversion of solar energy into organic materials, thus allowing a greater proliferation of microorganisms. Understanding the photosynthetic pathways of plants is essential to choosing the right plant for the system. On the other hand, CAM plants that inhabit arid regions differ from C3 and C4 due to their ability to absorb CO₂ at night, leading to water conservation in their tissues. The CAM plants grow very slowly, resulting in lower biomass production than C3 and C4 plants. [67] Therefore, the choice of the type of plant will be even more relevant if it is to be used in places such as the north of Chile where radiation levels are very high, being around 1000-1300 W m^-2 highlighting with violet colors the sectors of the Chilean territory with the highest rates of solar radiation. The CAM plants have adaptations to dry, arid climates. They use the Crassulacean Acid Metabolism (CAM) pathway to minimize photorespiration. The characteristic of this metabolic pathway is that instead of separating the light-dependent reactions and the use of CO₂ in the Calvin cycle, CAM plants separate these processes (CO₂ fixation) in time, which means that; during the night these plants open their stomata so that the CO₂ diffuses through the leaves and thus the CO₂ is fixed in the oxaloacetate by PEP carboxylase, the same step in the metabolism of the C4 and which is subsequently converted into malate or another organic acid. This acid is later stored in the vacuoles until the next day. The result of this process allows CAM plants to carry out photosynthesis during the day without the need to open their stomata. This product has organic acids stored in its vacuoles that decompose to release CO₂ and enter it into the Calvin cycle. Having controlled the release of CO₂ maintains a high concentration around the rubisco [17,24,56,67].

During the cathodic sub-process, the main e^- acceptor is the dissolved O₂, which functions as a reductant and, in the presence of a suitable catalyst, can form H₂O. The process of e^- acceptance and subsequent O₂ reduction is known as the oxygen reduction reaction (ORR) mechanism. This process can occur by the 4e- transfer process or by a 2e^- transfer process, which will depend largely on factors such as the catalyst (cathode material) and the pH that will define the reaction path. Generally, there are two different pathways for the reaction of O₂ molecules; the first is the 4e^- pathway, where O₂ is reduced directly into two H₂O molecules in an acid medium or into four OH^- molecules in a basic medium [7,68] as seen in the following reactions:

$$O_2+4H^{+}+4e^{-}\to 2H_{2}O \left(Acid media\right)$$

(4)

$$O_2+2H_{2}O+4e^{-}\to 4O{H}^{-} \left(Alkaline or neutral media\right)$$

(5)

The second alternative for the reduction of the O₂ molecule is through the path of two e^-, this is considered an incomplete process which occurs in two steps where O₂ is reduced to H₂O₂ in acid soil, in the case of the reduction of the O₂ molecule in alkaline medium is reduced to OH^-, as shown below. [68]

$$O_2+2H^{+}+2e^{-}\to H_2{O}_2 \left(Acid media\right)$$

(6)

$$H^{+}+2e^{-}+H_2{O}_2\to 2H_{2}O \left(Acid media\right)$$

(7)

$$O_2+H_{2}O+2e^{-}\to OO{H}^{-}+O{H}^{-}\left(Alkaline media\right)$$

(8)

$$OO{H}^{-}+H_{2}O+2e^{-}\to 3O{H}^{-} \left(Alkaline media\right)$$

(9)

The plant's main function is to provide nutrients to bacteria through photosynthetic reactions and generate an ideal space for the proliferation of bacterial colonies [69]. An unhealthy plant will have a lower yield, which means that it will run out of nutrients to feed the bacterial colonies present in the rhizosphere [70]. The PMFC (Figure 6) is based on the bioelectrochemical activity of microorganisms with the ability to degrade organic material and nutrients into simpler molecules such as CO₂ (metabolic waste) and also release e^- and H⁺, these processes occur in areas with high microbial activity and ideally with low levels of O₂, because the electrogenic bacteria (e^- donors) are mostly anaerobic and/or facultative bacteria, for this reason in the anodic zone (where the anodic electrode is located) is where the processes occur in their entirety capture and transfer of electrons that occurs when bacterial colonies form a biofilm on the anode surface, becoming electron donors, which is known as the process of extracellular electron transfer [71].

The anode in contact with the ground is populated with an electrogenic bacteria community concentrating these on its surface. The bacteria community releases e- during the metabolic process of nutrients present in the substrate creating a current circuit during the reduction process over the cathode surface. The reaction involved during the anodic sub-process is the following [72,73].

$${CH}_3{COO}^{-}+4H_{2}O\to 2{HCO}_3^{-}+{9H}^{+}+{8e}^{-}$$

(10)

Figures 6, shows the anode electrode's morphological change during the electrochemical process before and after the bioprocess and contact this bacteria colony. Figure 6a indicates the electrode is pure Cu, and Figure 6c and 6e shows the result of an anodic subprocess where the dissolution of Cu is present as Cu → Cu²⁺ + 2e^- and the adhesion of nutrients such as Ca, Mg, C, K, and P and trace elements like Fe and Cu are evident over anodic electrode after bioprocess.

Figure 6. Surface morphology of the Cu anode electrode used for bioenergy recovery, a) Cu electrode before bioenergy recovery, c - e) Cu electrode after bioenergy recovery, b - d) XRD patterns of Cu electrode before bioenergy recovery with nutrient added over anode electrode.

Figure 6. Surface morphology of the Cu anode electrode used for bioenergy recovery, a) Cu electrode before bioenergy recovery, c - e) Cu electrode after bioenergy recovery, b - d) XRD patterns of Cu electrode before bioenergy recovery with nutrient added over anode electrode.

The natural electron acceptors are oxygen, nitrogen, and sulfur, among others. [16] The great influencing factor on the efficiency and electricity production by the plant, are the climatic conditions, salinity of the soil, relative humidity, sun exposure time, radiation, and mainly the type of bacteria present in the piliferous zone of the root.

The e^- transfer process occurs from proteins in the outer membrane via intracellular e^- carriers such as NAD⁺/NADH. This mechanism gives certain bacteria the ability to be the electrogenic process. The interaction that occurs between the e^- donor and the electrode is known as extracellular electron transfer and occurs in three steps: (i) microbial oxidation (metabolic process), (ii) transfer from the intracellular carrier, and (iii) uptake from extracellular, respectively. In the area near the anode, oxidation reactions occur due to microbial activity. [74]Microorganisms can oxidize e^- donors through a process called extracellular electron transfer. Therefore, this process involves both internal and external e^- transport of the cell. Of which three transfer mechanisms are (i) direct e^- transfer involving enzyme complexes associated or attached as a biofilm to the anode, (ii) indirect e^- transfer, when a soluble organic or inorganic compound is oxidized in the cell and subsequently diffuses toward the acceptor (anode electrode), and (iii) direct transfer of e- through a conductive matrix in the form of pilus, called nanowires, respectively.

4. Conclusions

Based on the analysis conducted, CAM plants emerge as a promising and sustainable alternative for utilization in PMFC, particularly in regions characterized by high solar radiation and arid or hyper-arid climates such as the Atacama Desert in Northem Chile. The performance of PMFC employing CAM plants underscores the significance of nutrient availability, specifically Ca, Mg, C, K, and P, as well as trace elements like Fe and Cu, in optimizing electricity generation efficiency.

Among the CAM plants studied, Kalanchoe daigremontiana exhibits exceptional performance metrics. It demonstrates the highest electrical energy generation, remarkable consistency in cell potential, and minimal variations. This plant achieves a maximum cell potential of 0.248 V and a minimum of 0.139 V, with a recurrence rate of approximately 89% within the voltage range of 0.200 to 0.250 V. These results position Kalanchoe daigremontiana as a first candidate for further exploration on a larger scale due to its noteworthy attributes, including low variability in the open circuit potential (OCP). This low variability corresponds to a remarkable energy production of about 9.4 mWh m^-2 of the electrode, further highlighting its viability for practical implementation. The energy estimate of energy generated by each CAM plant studied can be considered unique information which contributes to the scientific development of plant species adapted to desert climatic zones. However, while the potentials obtained from the metabolic processes of various CAM plant species exhibit relatively minor differences under the given conditions, determining the ultimate optimal species remains a challenge. Consequently, it becomes imperative to shift the focus of research toward the design and engineering of the electrochemical system itself. This approach aims to enhance energy recovery, thereby accommodating the extreme environmental conditions characteristic of the Atacama Desert, where this study was conducted.

Proposed avenues for further investigation involve the integration of soilless cultivation technologies within the context of the electrochemical system. This strategic approach is intended to provide insights into how CAM plants interact with the electrochemical environment when grown in controlled conditions, potentially yielding significant improvements in performance and energy output. In the context of the nutrient requirements for bacterial activity in the rhizosphere of these CAM plants within PMFC, it is important to acknowledge that the specific needs of bacteria can vary based on the particular bacterial species, the chosen plant species, and the composition of the soil. Furthermore, the availability of nutrients, including Ca, Mg, C, K, P, Fe, and Cu, is intrinsically linked to parameters such as pH, temperature, and humidity. These factors collectively influence the microbial metabolic processes and the subsequent electricity generation in the PMFC systems. CAM plants, particularly exemplified by Kalanchoe daigremontiana, hold great promise as a sustainable solution for PMFC electrochemical systems in challenging environmental conditions. The study underscores the critical role of nutrients and trace elements in optimizing PMFC performance. Moving forward, a shift towards system-level design and engineering, coupled with controlled cultivation techniques, will be crucial for advancing the practical application of this innovative technology in extreme environments.