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Despite the abundance of nitrogen in the atmospheric and soil air, only a limited amount of reserved soil inorganic nitrogen in the forms of nitrate and ammonium is accessible to plants[18]. The limitation of nitrogen shortages in the soil was augmented for centuries through crop rotations with leguminous crops and the use of organic fertilizers like seaweeds, wood ash, and animal manures. Crop rotation mainly relies on biological nitrogen fixation where leguminous crops (with the aid of microorganisms) in rotation and free-living cyanobacteria help in converting atmospheric nitrogen to plant-available forms[4]. Apart from biological nitrogen fixation, another natural process of nitrogen fixation which is uncertain is lightning. It produces nitrate through the reaction of a nitrogen atom and an oxygen atom facilitated by an electric discharge in the atmosphere[6]. The highest and most important process of nitrogen fixation is the conversion of dinitrogen into ammonium on a large and industrial scale (Haber-Bosch process)[19]. These bring about the synthesis of mineral fertilizers which significantly increases crop production by 400%[20]. Artificially, a promising and alternative method of nitrogen fixation to the Haber-Bosch process is recently attracting much attention. This is photocatalytic nitrogen fixation using nanostructured materials[12,16]. Each of these processes has its advantages and disadvantages which will be reviewed in detail.
Natural processes of atmospheric nitrogen conversion
Biological processes
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Biological nitrogen fixation (BNF) is a process whereby free-living and symbiotic bacteria convert atmospheric dinitrogen to ammonia in the global nitrogen cycle. The process accounts for almost two-thirds of the total natural fixed dinitrogen on the earth's surface and is facilitated by the action of the nitrogenase catalytic/enzymatic complex[21]. The microorganisms and the enzymatic routes that convert dinitrogen to different oxidative states are still not fully understood. Thus, to understand the various microorganisms and the enzymatic reactions, the major microbial processes and the major reactions responsible for the BNF were highlighted based on the present perspective.
Biological nitrogen fixation is a kind of ammonification reaction that is achieved with the help of archaea and bacteria[22]. The reaction requires a large amount of energy (16 ATP molecules) as shown in Eqns (1) and (2) below:
$\rm N_{2(g)} + 8H^+ + 8e^- + 16ATP \to 2NH_{4}^+ + 16ADP + 16Pi $ (1) $\rm 2NH_{4}^+ + 2e^- \to 2NH_{3} + H_{2} $ (2) Among the microorganisms in the soil, only a few can use dinitrogen molecules, while others require a combined form of nitrogen[23]. The ammonium produced through the ammonification process is assimilated into biomass or utilized aerobically/anaerobically by ammonia-oxidizing microbes[24]. The ammonification process first produces ammonia in the soil. The ammonia then reacts with soil water to produce NH4+ ready for plant uptake[25,26]. Further to the BNF, the ammonia produced is also transformed into nitrite and nitrate[27]. The chemical reaction occurs via three steps (Eqns 3–5). The first step involves the action of monooxygenase (enzyme ammonia) on ammonia, catalyzing the oxidation of ammonia to hydroxylamine[28]. The second step is the conversion of hydroxylamine to nitrite with the aid of hydroxylamine oxidoreductase. The third step is the transformation of nitrite to nitrate in the presence of nitrite-oxidizing bacteria[29]. These processes are very important to plants because they produce more available nitrogen for plant uptake.
$\rm NH_{3} + O_{2} + 2H^+ + 2e^- \to NH_{2}OH + H_{2}O $ (3) $\rm NH_{2}OH + H_{2}O \to NO_{2}^- + 5H^+ + 4e^- $ (4) $\rm NO_{2}^- + 1/2O_{2} \to NO_{3}^- $ (5) The major drawback of BNF is that it only occurs in the nodules of the root of leguminous crops and/or by a few free-living archaea/bacteria in waterlogged/paddy conditions[30]. Even in leguminous crops, in the absence of root nodules or inefficiency of the nodulation, no nitrogen will be fixed. Also, the free-living bacteria that fix atmospheric nitrogen mostly do so in waterlogged/paddy conditions. Only a few crops of high value such as rice and cocoyam can grow in waterlogged conditions. Therefore, BNF cannot be depended upon for nitrogen fixation to meet the demands of the crops and to also feed the ever-increasing world population.
Atmospheric lightning
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Lightning is a process of electric discharge with aural and visual effects accompanied by a lightning flash that occurs mostly during a thunderstorm. Although the process occurs in a relatively short period, it has intense chemical reactions which radically changed the chemical composition of the air in and around the discharge zone[31]. The electric discharge breaks the dinitrogen gas (N2) triple bond and combines them with oxygen to produce nitrogen dioxide (NO2) and nitrogen oxide (NO), or reacts with hydrogen to form ammonia as shown in Eqns (6)–(8)[32]. The oxides and ammonia further dissolve in precipitation (snow and rain) to yield nitrates (NO3−) and ammonium (NH4+) respectively which are deposited into the soil for plant assimilation.
$\rm N_{2(g)} + O_{2(g)} \to 2NO_{(g)} $ (6) $\rm N_{2(g)} + 2O_{2(g)} \to 2NO_{2(g)} $ (7) $\rm N_{2(g)} + 3H_{2(g)} \to 2NH_{3(g)} $ (8) However, despite the many occurrences of lightning flashes around the globe, the process is not a reliable means of nitrogen compound production for plants, as it is highly uncertain and only produces 5 ± 3 Tg per annum NOx globally (5%–8% of fixed nitrogen)[6,33]. Therefore, lightning cannot be considered an alternative method of nitrogen fixation for sustainable crop production.
Artificial processes of atmospheric nitrogen conversion
Chemical processes
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The Haber-Bosch process is a chemical fixation of nitrogen which involves reacting dinitrogen gas (N2) with hydrogen gas (H2) at very high temperatures (650–750 K) and high pressures (50–200 bar) in the presence of a Fe-based catalyst to produce ammonia (Eqns 9–14)[34,35]. The NH3 produced through this process is the key chemical component in the fertilizer industries with yearly production exceeding 150 million tons worldwide[36]. In addition, due to the high gravimetric density of hydrogen (17.75 wt%), ammonia is also used as a clean energy carrier for the chemical storage of energy[23].
$ \rm N_2(g) \to N_2\;(adsorbed) $ (9) $\rm N_2\;(adsorbed) \to 2N\;(adsorbed) $ (10) $ \rm H_2(g) \to H_2\;(adsorbed) $ (11) $ \rm H_2\;(adsorbed) \to 2H\;(adsorbed) $ (12) $ \rm N\;(adsorbed) + 3H\;(adsorbed) \to NH_3\;(adsorbed) $ (13) $ \rm NH_3\;(adsorbed) \to NH_3(g) $ (14) In the Haber-Bosch method, the most significant and rate-determining step is the formation of atomically adsorbed nitrogen species through the dissociation of dinitrogen (Eqn 9), followed by hydrogen production which consumed the highest energy in the whole process. It involves steam methane reforming (SMR) at a high temperature of 800–1,000 °C (Eqn 15), and the purification of the effluents to remove CO and maximize H2 yield through water gas shift (WGS) exothermic reaction at 350–550 °C (Eqn 16)[37].
$\rm CH_4 + H_2O \to CO + 3H_2 $ (15) $ \rm CO + H_2O \to CO_2 + H_2 $ (16) There is no doubt that the discovery and industrial conversion of nitrogen through the Haber-Bosch process has transformed global crop production, however, the consequences attached to the development are of global concern. The purification of hydrogen in hydrogen production resulted in a massive release of carbon dioxide which contributes to around 3% of global greenhouse gas emissions[7]. Also, the process consumes a substantial amount of energy which is approximately 1%–2% of the annual global energy generation[12,38], and it only takes place at very high temperatures and pressure. Therefore, there is a need for the development of a sustainable and environmentally friendly method for nitrogen fixation.
Photocatalytic processes
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Apart from the Haber-Bosch process, another artificial method of nitrogen fixation that is attracting much attention is photocatalytic nitrogen fixation to produce ammonia[12] and/or nitrate[16]. The process utilizes abundant solar energy, N2, and H2O under atmospheric pressure and ambient temperature in the presence of a photocatalyst. It is considered a substitute for the Haber-Bosch process[39,40], as it is the most eco-friendly approach for ammonia and nitrate synthesis[16,41]. The process involves light absorption by a photocatalyst (mostly nanostructured materials), usually a semiconductor with relatively low band gap energy, leading to electron excitation from the valence band moving to the conduction band, leaving behind positively charged holes in the lower valence band. In the presence of a trap, interfacial charge carrier transfer takes place which subsequently leads to the redox reaction where N2 is reduced to NH3 (Eqns 17–20).
$ \rm 2N_{2} + 6H_{2}O \xrightarrow{Photocatalyst} 4NH_{3} + 3O_{2} $ (17) $\rm Photocatalyst \xrightarrow{Light\;absorption} H^+ + e^- $ (18) $ \rm 2H_2O \xrightarrow{\;\;\;\;\;\;\;\;\;\;} 4H^+ 4e^{-1} + O_2$ (19) $ \rm N_2 + 6H^+ + 6e^-\xrightarrow{\;\;\;\;\;\;\;\;\;\;} 2NH_3 $ (20) The electrons in the conduction band have the potential to reduce N2 to NH3 utilizing the protons generated at the valence band where oxidation of H2O is taking place. Thermodynamically, the reaction possesses a Gibbs free energy of +339 kJ·mol−1 (endothermic reaction)[12].
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Band gap energy can be described as the distance of electron travels between the valence band and the conduction band. It is the minimum amount of energy that an electron required to be excited from the valence band up to the conduction (free of its bound state) where it can participate in a reaction. The band gap energy is the key determinant of the photocatalytic performance of a nanostructured photocatalyst. For a material to catalyze with efficient photocatalytic properties, the band gap energy must not be smaller than 3 eV. This is to allow the catalyst to utilize the visible region (42% to 43%) of the solar energy. While 3 eV is the maximum band gap for efficient photocatalysis, the minimum band gap should not be less than 1.23 eV. This is because water splitting cannot occur if a photocatalyst has a band gap of less than 1.23 eV[100]. Table 1 gives some photocatalysts with their band gap energies. An effective photocatalyst mostly possesses bandgaps greater than 2 eV. Hence, it is imperative to target a material that has a band gap of 2–3 eV for effective and efficient photocatalytic nitrogen fixation.
Table 1. Photocatalyst for photocatalytic nitrogen fixation.
Photocatalyst Band gap
energy (eV)Yield (NH3) Ref. Bi2O2CO3 2.65 1,175.78 μmol·L−1·g−1·h−1 Feng et al.[101] I-g-C3H4 2.68 200.8 mg·L−1·g−1 Hu et al.[102] La2TiO5 4.07 158.13 μmol·g−1·h−1 Song et al.[103] C-BiOI 1.81 311 μmol·g−1·h−1 Zeng et al.[92] g-C3H4 2.74 150 mg·L−1·h−1·g−1 Hu et al.[104] FeS2/Fe-Pal 1.30 147 μmol·g−1·h−1 Ye et al.[105] In2O3/In2S3 2.77 40.04 μmol·g−1·h−1 Xu et al.[106] Ag/B-g-C3H4 2.82 5.19 mg·h−1·g−1 Yao et al.[107] N-g-C3H4 2.60 531.24 μmol·L−1·g−1·h−1 Liu et al.[108] Bi2S3 1.48 51.04 μmol·g−1·h−1 Lan et al.[109] Bi2S3@PCN-2 1.61 3,880 μg·h−1·g−1 Chen et al.[110] W18O49/g-C3N4 2.83 64.8 μmol·gcat−1·h−1 Huang et al.[111] TCN/ZnS/ZnIn2S4 2.59 136.56 μmol·L−1 Sun et al.[112] Redox potential of a photocatalyst
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The redox potential of a photocatalyst gauges its inclination to engage in reduction or oxidation reactions, involving the acceptance or donation of electrons, respectively. In the realm of photocatalytic processes, the efficacy of redox reactions hinges significantly on two key factors: the reduction potential of nitrogen molecules[113] and the energy band positioning within the photocatalyst[114]. For successful photocatalytic nitrogen fixation, a photocatalyst must possess a conduction band situated above the reduction potential required for N2 hydrogenation (0.55 V), while concurrently, its valence band should be positioned below the oxygen evolution potential (0.81 V)[113]. This highlights the pivotal role played by the bandgap energy when selecting a suitable material for photocatalytic nitrogen fixation.
Kinetic limitations
N2 adsorption and activation
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The critical and rate-controlling step in the fixation of N2 lies in the process of adsorption and activation of nitrogen molecule. N2 molecules, known for their chemical stability and low coordination, present a formidable challenge in terms of surface adsorption on a catalyst. Delving into the electronic configuration of nitrogen atoms (as depicted in Fig. 2), five valence electrons residing in the 2s and 2p orbitals are found, with three of them remaining unpaired. Upon bonding, these atomic orbitals undergo hybridization, giving rise to four bonding orbitals housing two σ orbitals and two π orbitals, along with four anti-bonding orbitals comprising two σ* orbitals and two π* orbitals[48]. This delineates a substantial energy gap of 10.82 eV between the highest occupied molecular orbital and the lowest unoccupied molecular orbital, leading to a high ionization energy of 15.58 eV[115]. Consequently, the N≡N triple bond exhibits remarkable stability, demanding the input of a substantial 945 kJ·mol−1 of energy for cleavage to occur[49]. It is this robust bond energy that imposes a formidable barrier to the adsorption and activation of N2 in the fixation process.
Drawing inspiration from the realm of biological nitrogen fixation, which finds its muse in natural nitrogenase, photocatalytic nitrogen fixation has witnessed the development of photocatalysts employing various transition metals (such as Fe, Mo, V, Bi) for the chemical fixation of atmospheric N2. This achievement hinges upon the potent interaction between these metals and the 2p orbital of nitrogen, enabling N2 to become chemically adsorbed on the catalyst's surface. This interaction, in turn, forges a pathway for the transfer of electrons from the catalyst to N2, thereby facilitating N2 activation. These donated electrons find their way into the anti-bonding π* orbitals of N2, causing an elongation of the bond length and a corresponding reduction in bond energy, ultimately leading to the cleavage of the N≡N bond. This intricate dance of electrons culminates in the adsorption and activation of N2. Consequently, the selection of a catalyst with a pronounced affinity for coordinating with nitrogen assumes paramount importance in the pursuit of efficient N2 fixation.
Electrons and hole separation and mitigation of charge recombination
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In the realm of photocatalytic processes, a significant energy gap between the brimming valence band (VB) and the unoccupied conduction band (CB) dictates that electrons can migrate only when furnished with ample energy. When light energy permeates a nanomaterial, an electron can absorb a photon of equivalent or higher energy than the material's band gap energy. This absorption elevates an electron from the VB to the CB, concurrently generating a vacancy or 'hole' in the VB. This pivotal mechanism, driven by light, underpins the separation of electrons and holes, a prerequisite step in the photocatalytic reaction cascade. These photogenerated entities subsequently traverse to the nanomaterial's surface, where they instigate reduction reactions with adsorbed nitrogen molecules. One of the most formidable challenges confronting many photocatalytic reactions is the propensity for photogenerated electrons and holes to recombine, dissipating energy and thereby diminishing reaction rates. Consequently, this recombination phenomenon erodes photocatalytic efficiency[116,117]. Hence, a pressing need arises to stymie recombination and bolster photocatalytic reaction efficiency.
Recent endeavors have seen a surge in studies aimed at extending the lifespan of photogenerated carriers, thus mitigating recombination and enhancing reaction efficiency. These strategies encompass the use of co-catalysts[118,119], modifications involving functional groups[120], surface engineering[103], the formation of heterojunctions[121,122], and doping techniques[103]. A comprehensive exploration of these methods will follow in the subsequent section.
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Data sharing not applicable to this article as no datasets were generated or analyzed during the current study.
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About this article
Cite this article
Yahaya SM, Abdu N, Aliyu IA, Mukhtar B. 2024. Revolutionizing nitrogen fixation: communicating the potentials of nanostructured photocatalysts for sustainable ammonia/nitrate synthesis. Circular Agricultural Systems 4: e015 doi: 10.48130/cas-0024-0014
Revolutionizing nitrogen fixation: communicating the potentials of nanostructured photocatalysts for sustainable ammonia/nitrate synthesis
- Received: 14 May 2024
- Revised: 23 July 2024
- Accepted: 08 August 2024
- Published online: 20 September 2024
Abstract: Photocatalytic nitrogen fixation (PNF) using nanostructured materials is a promising approach that is likely to rival the most expensive and high-energy-demanding Harber-Bosch method of ammonia synthesis. This is because the process is deemed the most sustainable method of nitrogen fixation, through the direct production of ammonia and/or nitrate from water and atmospheric nitrogen with the aid of sunlight; and the system has zero emission of carbon dioxide. The PNF process is receiving much attention making it among the hot research topics in recent years. There is, however, a knowledge gap between the photocatalytic processes and the nanostructured photocatalyst. In this review, therefore, recent breakthroughs and achievements in the photocatalytic reaction processes were discussed. In addition, the nanostructured photocatalysts used in nitrogen fixation were discussed in detail. This includes the importance of the nanomaterials in photocatalysis, the types used in photocatalytic nitrogen fixation, and the synthesis methods of the nanomaterials. Also, limitations that affect the photocatalytic reaction processes as well as the ways of overcoming them such as the creation of oxygen, sulphur, and nitrogen vacancies, doping techniques, formation of heterojunctions, and the use of cocatalysts were all discussed in detail. From the aforementioned discussions, PNF could be seen as the most eco-friendly and sustainable method of nitrogen fixation. However, understanding the mechanisms of PNF is very critical to identifying and designing an efficient photocatalytic system.
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Key words:
- Photocatalysis /
- Nitrogen fixation /
- Nanostructured materials /
- Ammonium /
- Nitrate