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Mele, C. Fish Industry Waste and Electrochemical Energy Systems. Encyclopedia. Available online: https://encyclopedia.pub/entry/16722 (accessed on 27 July 2024).
Mele C. Fish Industry Waste and Electrochemical Energy Systems. Encyclopedia. Available at: https://encyclopedia.pub/entry/16722. Accessed July 27, 2024.
Mele, Claudio. "Fish Industry Waste and Electrochemical Energy Systems" Encyclopedia, https://encyclopedia.pub/entry/16722 (accessed July 27, 2024).
Mele, C. (2021, December 03). Fish Industry Waste and Electrochemical Energy Systems. In Encyclopedia. https://encyclopedia.pub/entry/16722
Mele, Claudio. "Fish Industry Waste and Electrochemical Energy Systems." Encyclopedia. Web. 03 December, 2021.
Fish Industry Waste and Electrochemical Energy Systems
Edit

Fish industry waste is attracting growing interest for the production of environmentally friendly materials for several different applications, due to the potential for reduced environmental impact and increased socioeconomic benefits. Recently, the application of fish industry waste for the synthesis of value-added materials and energy storage systems represents a feasible route to strengthen the overall sustainability of energy storage product lines. 

fish industry waste activated carbon battery supercapacitors protein batteries carbon electrodes porous carbon fish waste valorization circular economy sustainability

1. Introduction

The energy crisis, climate change, increased energy consumption and growing awareness of environmental protection needs have imposed the challenge of sustainable development, pushing industrial and academic research toward efficient, clean, ecological and high-performance materials and equipment for energy storage and conversion [1]. The energy produced by renewable resources needs to be stored by electrochemical energy storage devices from which it can be extracted at a later time to perform necessary tasks [2]. These devices are required to have increasingly improved energy and power density. Moreover, electrochemical energy storage technology is crucial for the sustainable development of wearable electronics [3]. Therefore, it is essential to find high-performing, low-cost and environmentally friendly materials. Additionally, the developed materials should be able to be produced at a large-scale for usage in various industries [4][5][6][7][8].
One of the most invaluable, renewable and sustainable resources for the synthesis of high-performance materials for energy storage is biomass [9]. The term biomass indicates all renewable organic materials deriving from plants, algae, trees, crops, wood wastes, agricultural and forestry wastes, animal and poultry wastes, fishery and aquaculture waste and food processing waste [10][11]. In 2016, the total biomass waste in the world was approximately 550 gigatons of carbon, and is increasing every year [12]. This waste is either burnt or left in the ocean which leads to environmental pollution and the emission of greenhouse gas [13][14]. Biomass is exploited for energy production through thermochemical processes, including combustion, gasification and pyrolysis, and biochemical processes, including fermentation and anaerobic digestion [10][15][16].
Thanks to biomass’ recyclability, abundance and low cost, the application of biomass as a precursor to produce green carbon materials for energy storage is economically and technically sustainable [3][17][18][19]. Nowadays, many porous and nanostructured carbons derived from biomass present high conductivity, high tensile strength, low density and large aspect ratios, leading to enhanced energy storage capacity [20][21][22]. These carbon-based materials can be used in hydrogen storage [23], energy storage devices [24][25] carbon capture and storage [26][27], photovoltaics [28][29], dye degradation [30] and environmental remediation applications [31][32]. Essentially, the utilization of biomass not only helps to find inexpensive high-potential materials for different industries but also prevents or alleviates environmental pollution, providing opportunities for biomass-based industries [3][4][33][34].
Transformation of biomass into carbon-based materials can be done through carbonization, pyrolysis and activation techniques, producing enriched materials with high surface areas, vast pore volumes and small pore sizes [35][36][37][38][39]. Instrumental and methodological details regarding different synthetic strategies for biomass-derived carbon can be found in [40][41][42]. Due to a better electrolyte seepage and higher charge storage capabilities compared to conventional materials, porous and high-surface carbon materials are suitable as electrode materials for batteries and supercapacitors [43][44][45][46][47]. As a result, the research on preparation techniques and activator typologies has led to the concept of engineered biochar, wherein the physicochemical properties, performance and environmental benefits of pristine biochar can be tailored for specific applications [35][48]. For example, it is possible to derive a porous carbon with precise micropore size and large specific surface area (up to 3000 m2/g) [4][33][49]. Additionally, chitin and chitosan, obtained from fish and crustacean shells, have been demonstrated to be effective as material for supercapacitors, LIBs, polymer electrolyte-based fuel cells and LSBs as polysulfide trapping agents [50][51][52].
Biowaste materials obtained from the fish industry have drawn significant attention as a novel raw material for various purposes. Around 50–75% of fish and seafood by-products, including viscera, skin, bones, scales, flesh, fins and shells are wasted during fish processing [53][54]. This waste occurs in huge quantities, considering that, in 2019, worldwide production of fish was estimated to be around 177.8 million metric tons (a number that will continually increase in the future) [55]. Of this amount, around 7.2–12 million tons are wasted yearly [56]. These waste products are discarded into the environment, in disposal areas or in the sea, with huge economic loss and detrimental effects on aquatic ecosystems, producing greenhouse gases and stench [57][58][59]. Fish waste disposal in the ocean increases organic matter content, leading to oxygen level reduction at the bottom of the ocean and endangering the lives of other oceanic inhabitants [60][61][62]. Discarding fish waste is a serious challenge that needs to be promptly overcome [53]. Consequently, the valorization of fish byproducts would be a great achievement, not only for the environment, but also for the fish and aquaculture industries [63][64].
Recent studies in literature reveal that fish industry waste can successfully be used as a low-cost precursor for the production of sustainable energy storage materials, since it is a rich source of carbon, nitrogen, oxygen, hydrogen and sulfur [60][65][66]. Moreover, biomass derived from fish waste includes a valuable amount of collagen, crude protein and amino acids, which are a great choice for preparing 3D and N-doped nanoporous carbon materials [39][67]. Fish scales, for example, contain organic and inorganic materials (collagen fibers and calcium-deficient hydroxyapatite, respectively) [68]. The organic parts of fish scales can be converted to carbon matrices; the inorganic parts may be a natural template to induce a chain porous structure after carbonization and activation [9][69][70][71]. Additionally, fins and fish skins contain valuable amounts of collagen fibers, including different amounts of carbon, oxygen, nitrogen, hydrogen and sulfur. Finally, the annual generation of around 0.5 million tons of crab shells makes crab shells another valuable source of material for energy storage devices. This amount of waste is much higher than the material produced for LIBs (about ten thousand tons for both anodes and cathodes) [72].
The increasing interest toward the valorization of fish waste into sustainable materials for electrochemical storage systems is highlighted by the growing number of scientific publications on this topic during the last decade and, in particular, in the last three years, as reported in Figure 1.
Figure 1. Distribution of scientific publications per year on sustainable materials derived from fish waste for electrochemical storage systems (Scopus database).

2. Applications in Lithium–Ion Batteries (LIBs)

To date, the most developed electrochemical energy storage devices are lithium-ion batteries (LIBs), which are currently applied in various fields including smartphones, laptops and electric vehicles, owing to their relatively high energy density and long cycle life [73][74][75]. Nevertheless, commercial graphite anodes cannot satisfy the increasing demand of the high energy density in LIBs. Predictions have claimed that the demand for lithium will be tripled by the year 2025 [76]. Another limitation is represented by the massive anode volume changes during Li+ insertion and extraction, which leads to the pulverization of the lithium–alloy particles and fast capacity drop during charge-discharge cycles [77]. To overcome these limitations, research on alternatives for graphite anodes has focused on nanoporous carbons (NPCs). NPCs have drawn interest because of their potentially higher specific capacity and stability and their well-organized porous structure. These can prepare rapid ion diffusion channels, which is advantageous when attempting to obtain high Li+ storage capacity [35]. A variety of NPCs have been investigated, such as carbon nanofibers [78][79] carbon nanocages [80][81], nitrogen-enriched nanocarbons [82][83], etc. Their porous structures can reduce the diffusion length of Li-ions, while their high specific surface area offers abundant active sites for Li+ storage reactions [84].
Recent literature demonstrates that fish waste can successfully be used as a sustainable source for nanoporous carbon materials; it is enriched with elements such as nitrogen, oxygen, hydrogen and sulfur, and characterized by cost-effectiveness and thermal stability. Depending on the type of fish industry waste, different routes have been reported in recent studies for obtaining porous carbon electrodes for Li-ion batteries, as schematically reported in Figure 2.
Figure 2. Schematic representation of the possible routes for obtaining porous carbon electrodes for Li-ion batteries from fish waste.
Crustacean shells are effective biotemplates for preparing nanostructured anodes for rechargeable Li-ion batteries, as demonstrated by Yao et al. [72]. They obtained hollow carbon nanofibers from crab shells encapsulating sulfur and silicon. The processing route involved several steps, as schematized in Figure 2. After air calcination of the crab shells, the organic components were removed and CaCO3 templates containing twisted hollow nanometric channels were obtained, with diameters close to those of commonly anodized aluminum oxide templates. The CaCO3 framework was coated with a thin layer of carbon via heat treatment in nitrogen. Then, the obtained active electrodes were inserted into the nanochannels, where they were treated by sulfur and silicon through thermal infusion and chemical vapor deposition, respectively. After dissolving the CaCO3 framework by acid treatment, the researchers obtained hollow carbon nanofiber arrays encapsulating sulfur or silicon. The hollow nanostructures provided sufficient space for the volume expansion of sulfur/silicon during the discharge/charge processes and the thin walls of the hollow carbon nanofibers allowed rapid lithium-ion transport from the electrolyte to sulfur/silicon. As reported in Table 1, the Li-ion battery prepared with this crab shell-templated carbon/silicon anode showed high specific capacity (1580 mAh/g at 1C) and high cycling performance [72].
The mechanism responsible for the excellent electrochemical performance of fish waste-derived porous carbon materials in LIBs occurs due to their uniform interconnected porous structure, which is beneficial for the rapid penetration of electrolytes, fast Li+ diffusion and the provision of active sites for the storage of Li+ ions [85]. The electrochemical properties of electrode materials can be improved by heteroatom doping, which induces defects and increases available active sites [86]. Nitrogen-doped porous carbons derived from crawfish shells were prepared by Wang et al. [87] by modifying the initial calcination treatment in a nitrogen atmosphere, followed by acid treatment to eliminate CaCO3. Then, N-doped porous carbon underwent a thermal treatment with cobalt acetate tetrahydrate to become nano-filled with nanometric cobalt oxide (Co3O4) nanoparticles. The N-doped porous carbon and Co3O4-N-doped porous carbon were used to prepare a working electrode via a slurry coating procedure with high electrochemical lithium storage performance. N-doped porous carbon had a capacity of about 400 mAh/g after 100 cycles, which was greater than that of commercial graphite (372 mAh/g). This demonstrated that N-doped porous carbon could potentially replace graphite in industrial production. More interestingly, as reported in Table 1, the N-doped PC-Co3O4 nanocomposite with 10 nm Co-based nanofiller presented a high reversible capacity of 1060 mAh/g after 100 cycles, acceptable rate capability, superior cyclic performance and excellent primary Coulombic efficiency (86.7%) [39][67].
In addition to the use of prawn shells (PSC), prawn meat (PMC) was used by Lian et al. [85] to prepare porous carbon materials to be applied as anodes in lithium-ion batteries. After calcination under an inert atmosphere, the obtained carbon structure was washed, centrifuged, dried and then combined with polyvinylidene fluoride (PVDF), acetylene black (AC) and N-methyl-2-pyrrolidone solvent. The initial discharge/charge capacities of PSC and PMC materials for the first 3 cycles at the current density of 30 mA/g were 1803/910 and 1200/694 mAh/g with the coulombic efficiency of 50.4% and 57.8%, respectively (see Table 1). Solid electrolyte interface formation was cited as the reason for the low initial coulombic efficiencies. For PSC and PMC, coulombic efficiency reached 91% and 93% after the first cycle and 94% and 95% after the third cycle, respectively [85]. The best performance was obtained by PSC due to the presence of a more uniform nanoporous structure compared to PMC and a higher level of N-doping.
The steps for the preparation of porous carbons from fish scales are schematized in Figure 2. As reported by Selvamani et al. [22], after air calcination, activation in alkaline solution and heat treatment, the obtained carbon was characterized by a high specific surface area and excellent electrochemical behavior, even under high charge/discharge situations. The galvanostatic charge/discharge curves at the current density of 75 mA/g demonstrated an initial discharge capacity around 541 mAh/g in ionic liquid electrolyte. After 75 cycles, the coulombic efficiency was 94% with a reversible capacity of 509 mAh/g. At the current densities of 400 and 4000 mAh/g, the reversible capacities were 390 mAh/g and 179 mAh/g, respectively. In addition to the aforementioned properties, the electrode was stable before and after cycling [22].
Very recently, it was demonstrated that collagen extracted by fish waste could be used to obtain porous materials for LIB electrodes, as schematized in Figure 2. Odoom-Wubah et al. [60] extracted collagen from Tilapia fish with an alkaline treatment followed by an acid treatment. The marine collagen was impregnated by Palladium nitrate followed by a heat treatment in nitrogen and then used in combination with polyvinylidene fluoride (PVDF), N-methyl-2-pyrrolidone and carbon black as an anode material for Li, Na and Mg half-cells. Results of electrochemical measurements revealed that the reversible capacities for Li, Na and Mg-based cells were 270 (Table 1), 120 (Table 2) and 100 mAh/g, respectively [60]. The proof of concept of extracted porous carbon from marine collagen was demonstrated, but further studies are still required to optimize the preparation and performance.
In Table 1 the performance of porous carbon-based materials obtained from fish industry waste for LIBs is compared with those of commercial graphite-based anodes for LIB in terms of specific capacity and cycle life. This latter indicates the number of charge/discharge cycles of the battery until the end of its lifetime. For LIBs, the cycle life is significantly dependent on the depth of discharge, which is an indication of the amount of storage capacity of the battery. It is typically in a range between 300 and 500 cycles for commercial LIBs, even if some manufactures have claimed 1000 cycles [88].
Table 1. Performance of porous carbon-based materials obtained from fish industry waste for Li-ion batteries.
Fish Waste Source Application Current Density
(mA/g)
or C-Rate
Initial Discharge Capacity (mAh/g) Reversible Specific Capacity
(mAh/g)
Capacity
Retention
References
Crab Shell Si-encapsulated nanostructured anode C/10-1C   3060 @C/10
1580 @1C
95% @200 cycles [72]
Crawfish shell nanoCo3O4 doped anode 100 1223 1060 98% @100 cycles [87]
Prawn shells anode 50–1000 1735 950 @50 mA/g
300 @1000 mA/g
84% @90 cycles [85]
Prawn meat anode 50–1000 1132 420 @50 mA/g
100 @1000 mA/g
40% @90 cycles [85]
Prawn Shells anode 0.1 740 732 99% @150 cycles [89]
Fish scales N-doped nanoporous anode 75
400
4000
541
418
214
509
390
179
94% @75 cycles
93% @75 cycles
84% @75 cycles
[22]
Collagen from Tilapia waste nanoPd doped anode 1C 600 270 @1C 100% @20 cycles [60]
Crab Shell anode 50 1758 703 @50 mA/g 83% @200 cycles [90]
  Commercial graphite-based anodes     372
theoretical
300–500 cycles [91][92]

3. Applications in Sodium-Ion Batteries (NIBs)

Li-ion batteries cannot meet the growing needs of the energy storage market because Li is an expensive, limited and unequally distributed resource [73][93]. Sodium-ion rechargeable batteries are attracting great attention due to their similarity to LIBs and the use of sodium ions (Na+) as the charge carriers [94]. Though sodium cannot compete with lithium’s energy density, that shortcoming is compensated due to its availability and price [95]. Therefore, compared to more widespread LIB, Na-ion batteries (NIB) have lower cost and do not use scarce resources [96]. However, sodium has two disadvantages. First, its weight is three times higher than lithium; even if only 5% of the overall battery weight is related to lithium, NIBs are heavier. In addition, the Na+ ion has a larger ionic radius than the Li+ ion, leading to more sluggish diffusion kinetics and more significant volumetric changes during repeated charging/discharging cycles. Therefore, Na-ion batteries are less powerful, primarily due to the low ability of the graphite anodes to absorb sodium. A possible solution for achieving higher storage capacities could be the replacement of the graphite anodes commonly used today with electrodes of graphene or hard carbon [97]. The latter is a disordered, mainly sp2, non-graphitic carbonaceous material consisting of single layers of carbon atoms that are arranged in a planar hexagonal network, but irregular and disordered along the c-axis [98][99]. These carbon-based materials can be obtained from biomass [47][100][101].
Table 2. Performance of porous carbon-based materials obtained from fish industry waste for Na-ion batteries.
Fish Waste Source Application Current Density
(mA/g) or C-Rate
Initial Discharge Capacity (mAh/g) Reversible Specific Capacity
(mAh/g)
Capacity Retention Ref.
Prawn Shells Na-ion batteries anode 100 370 325 @1C 100% @200 cycles [89]
Fish collagen (Tilapia) nanoPd doped anode for Na-battery 1C 60 NIB: 120 @1C 40% @20 cycles [60]
Crab Shell anode 50 mA/g 1211 283 62% @300 cycles [90]
  Commercial graphite-based anodes 25 250 184 @C/10 100 cycles [102][103]
Recent studies have reported the suitability of porous carbon-based materials obtained from fish industry waste as electrodes for NIB batteries. Previous investigations demonstrated that by a low cost, simple and environmentally friendly approach, nitrogen-doped hierarchically porous carbon material obtained from prawn shells could be obtained. The mechanisms underlying their great suitability for replacing common carbon electrodes is due to their porous structure, high inherent nitrogen content and the presence of macro, meso- and micropores that facilitate the storage and transport channels for Li and Na ions. Detailed investigation on this subject was conducted by Elizabeth et al. [89], who obtained a porous N-doped structure from prawn shells using a protocol similar to that reported in Figure 2. Experimental results revealed that, due to the high Nitrogen content in porous carbon material, electrical conductivity and active sites for Li/Na storage were increased, which led to an improved electrochemical performance. Galvanostatic charge/discharge tests showed that the initial capacity at the current density of 0.1 A/g was 1013 mAh/g, which was three times more than the capacity of conventional graphite carbon material. The formation of solid-electrolyte interphase and the irreversible trapping of Li in the pores were responsible for the heavy capacity fade at the beginning. Cyclic charge/discharge tests were conducted on the porous carbon as an anode material for sodium-ion batteries. In the first cycle, the charge specific capacity was around 660 mAh/g and the discharge capacity was 370 mAh/g with coulombic efficiency of 56%. This low coulombic efficiency was due to the irreversible capacity loss because of the solid-electrolyte interphase formation and Na trapping in the porous structure. At the current density of 0.4 A/g, the electrode reversible capacity was 234 mAh/g after 150 cycles, which was superior in comparison to other biomass-derived carbon materials used in the literature. This was ascribed to the hierarchical porous structure and N-doping of carbon. Moreover, TEM results also confirmed that, after 200 cycles, the porous structure showed little damage, which was an indication of the high structural stability of the electrode material [89].
In addition to the porous carbon derived from crustacean shells, suitable electrode materials can be obtained from fish waste, as demonstrated by Odoom-Wubah et al. [60], who extracted collagen from Tilapia waste (according to a procedure described in the previous paragraph) to obtain an anode material for NIB, achieving a specific capacity of 120 mAh/g. Other investigations have been performed in order to apply sustainable anodic materials obtained from fish collagen to Magnesium-ion batteries (MIBs) [60], or from seafood-derived chitin for Potassium-ion batteries (KIBs) [104], respectively. Reversible capacities of 105 mAh/g [60] and 154 mAh/g [104] were obtained for MIBs and KIBs, respectively.

References

  1. Yu, J.; Fu, N.; Zhao, J.; Liu, R.; Li, F.; Du, Y.; Yang, Z. High Specific Capacitance Electrode Material for Supercapacitors Based on Resin-Derived Nitrogen-Doped Porous Carbons. ACS Omega 2019, 4, 15904–15911.
  2. Anthony, L.S.; Vasudevan, M.; Perumal, V.; Ovinis, M.; Raja, P.B.; Edison, T.N.J.I. Bioresource-derived polymer composites for energy storage applications: Brief review. J. Environ. Chem. Eng. 2021, 9, 105832.
  3. Dos Reis, G.S.; Larsson, S.H.; de Oliveira, H.P.; Thyrel, M.; Claudio Lima, E. Sustainable biomass activated carbons as electrodes for battery and supercapacitors—A mini-review. Nanomaterials 2020, 10, 1398.
  4. Senthil, C.; Lee, C.W. Biomass-derived biochar materials as sustainable energy sources for electrochemical energy storage devices. Renew. Sustain. Energy Rev. 2021, 137, 110464.
  5. Ryu, H.; Yoon, H.J.; Kim, S.W. Hybrid Energy Harvesters: Toward Sustainable Energy Harvesting. Adv. Mater. 2019, 31, 1–19.
  6. Winter, M.; Barnett, B.; Xu, K. Before Li Ion Batteries. Chem. Rev. 2018, 118, 11433–11456.
  7. Liu, Z.; Yu, Q.; Zhao, Y.; He, R.; Xu, M.; Feng, S.; Li, S.; Zhou, L.; Mai, L. Silicon oxides: A promising family of anode materials for lithium-ion batteries. Chem. Soc. Rev. 2019, 48, 285–309.
  8. Mele, C.; Bilotta, A.; Bocchetta, P.; Bozzini, B. Characterization of the particulate anode of a laboratory flow Zn–air fuel cell. J. Appl. Electrochem. 2017, 47, 877–888.
  9. Gao, M.; Shih, C.C.; Pan, S.Y.; Chueh, C.C.; Chen, W.C. Advances and challenges of green materials for electronics and energy storage applications: From design to end-of-life recovery. J. Mater. Chem. A 2018, 6, 20546–20563.
  10. Demirbaş, A. Biomass resource facilities and biomass conversion processing for fuels and chemicals. Energy Convers. Manag. 2001, 42, 1357–1378.
  11. Gurría, P.; Ronzon, T.; Tamosiunas, S.; López, R.; García Condado, S.; Guillén, J.; Cazzaniga, N.E.; Jonsson, R.; Banja, M.; Fiore, G. Biomass Flows in the European Union; European Commission Joint Research Center: Seville, Spain, 2017.
  12. Bar-On, Y.M.; Phillips, R.; Milo, R. The biomass distribution on Earth. Proc. Natl. Acad. Sci. USA 2018, 115, 6506–6511.
  13. Malmgren, A.; Riley, G. Biomass Power Generation; Elsevier Ltd.: Amsterdam, The Netherlands, 2012; Volume 5, ISBN 9780080878737.
  14. Lionetto, F.; Esposito Corcione, C. An Overview of the Sorption Studies of Contaminants on Poly (Ethylene Terephthalate) Microplastics in the Marine Environment. J. Mar. Sci. Eng. 2021, 9, 445.
  15. Caputo, A.C.; Palumbo, M.; Pelagagge, P.M.; Scacchia, F. Economics of biomass energy utilization in combustion and gasification plants: Effects of logistic variables. Biomass Bioenergy 2005, 28, 35–51.
  16. McKendry, P. Energy production from biomass (part 2): Conversion technologies. Bioresour. Technol. 2002, 83, 47–54.
  17. Yaman, S. Pyrolysis of biomass to produce fuels and chemical feedstocks. Energy Convers. Manag. 2004, 45, 651–671.
  18. Titirici, M.M.; Antonietti, M. Chemistry and materials options of sustainable carbon materials made by hydrothermal carbonization. Chem. Soc. Rev. 2010, 39, 103–116.
  19. Dutta, S.; Bhaumik, A.; Wu, K.C.W. Hierarchically porous carbon derived from polymers and biomass: Effect of interconnected pores on energy applications. Energy Environ. Sci. 2014, 7, 3574–3592.
  20. Gao, Z.; Zhang, Y.; Song, N.; Li, X. Biomass-derived renewable carbon materials for electrochemical energy storage. Mater. Res. Lett. 2017, 5, 69–88.
  21. Titirici, M.M.; White, R.J.; Brun, N.; Budarin, V.L.; Su, D.S.; Del Monte, F.; Clark, J.H.; MacLachlan, M.J. Sustainable carbon materials. Chem. Soc. Rev. 2015, 44, 250–290.
  22. Selvamani, V.; Ravikumar, R.; Suryanarayanan, V.; Velayutham, D.; Gopukumar, S. Fish scale derived nitrogen doped hierarchical porous carbon—A high rate performing anode for lithium ion cell. Electrochim. Acta 2015, 182, 1–10.
  23. Blankenship, T.S.; Balahmar, N.; Mokaya, R. Oxygen-rich microporous carbons with exceptional hydrogen storage capacity. Nat. Commun. 2017, 8, 1633.
  24. Senthil, C.; Vediappan, K.; Nanthagopal, M.; Seop Kang, H.; Santhoshkumar, P.; Gnanamuthu, R.; Lee, C.W. Thermochemical conversion of eggshell as biological waste and its application as a functional material for lithium-ion batteries. Chem. Eng. J. 2019, 372, 765–773.
  25. Poochai, C.; Srikhaow, A.; Lohitkarn, J.; Kongthong, T.; Tuantranont, S.; Tuantranont, S.; Primpray, V.; Maeboonruan, N.; Wisitsoraat, A.; Sriprachuabwong, C. Waste coffee grounds derived nanoporous carbon incorporated with carbon nanotubes composites for electrochemical double-layer capacitors in organic electrolyte. J. Energy Storage 2021, 43, 103169.
  26. Balahmar, N.; Mitchell, A.C.; Mokaya, R. Generalized Mechanochemical Synthesis of Biomass-Derived Sustainable Carbons for High Performance CO2 Storage. Adv. Energy Mater. 2015, 5, 1–9.
  27. Sevilla, M.; Al-Jumialy, A.S.M.; Fuertes, A.B.; Mokaya, R. Optimization of the Pore Structure of Biomass-Based Carbons in Relation to Their Use for CO2 Capture under Low- and High-Pressure Regimes. ACS Appl. Mater. Interfaces 2018, 10, 1623–1633.
  28. Wang, L.; Shi, Y.; Wang, Y.; Zhang, H.; Zhou, H.; Wei, Y.; Tao, S.; Ma, T. Composite catalyst of rosin carbon/Fe3O4: Highly efficient counter electrode for dye-sensitized solar cells. Chem. Commun. 2014, 50, 1701–1703.
  29. Jing, H.; Shi, Y.; Wu, D.; Liang, S.; Song, X.; An, Y.; Hao, C. Well-defined heteroatom-rich porous carbon electrocatalyst derived from biowaste for high-performance counter electrode in dye-sensitized solar cells. Electrochim. Acta 2018, 281, 646–653.
  30. Li, L.; Sun, F.; Gao, J.; Wang, L.; Pi, X.; Zhao, G. Broadening the pore size of coal-based activated carbon: Via a washing-free chem-physical activation method for high-capacity dye adsorption. RSC Adv. 2018, 8, 14488–14499.
  31. Tian, W.; Zhang, H.; Sun, H.; Tadé, M.O.; Wang, S. One-step synthesis of flour-derived functional nanocarbons with hierarchical pores for versatile environmental applications. Chem. Eng. J. 2018, 347, 432–439.
  32. Tang, J.; Zhu, W.; Kookana, R.; Katayama, A. Characteristics of biochar and its application in remediation of contaminated soil. J. Biosci. Bioeng. 2013, 116, 653–659.
  33. Deng, J.; Li, M.; Wang, Y. Biomass-derived carbon: Synthesis and applications in energy storage and conversion. Green Chem. 2016, 18, 4824–4854.
  34. Wang, Z.; Shen, D.; Wu, C.; Gu, S. State-of-the-art on the production and application of carbon nanomaterials from biomass. Green Chem. 2018, 20, 5031–5057.
  35. Yuan, X.; Dissanayake, P.D.; Gao, B.; Liu, W.-J.; Lee, K.B.; Ok, Y.S. Review on upgrading organic waste to value-added carbon materials for energy and environmental applications. J. Environ. Manag. 2021, 296, 113128.
  36. Powell, M.D.; LaCoste, J.D.; Fetrow, C.J.; Fei, L.; Wei, S. Bio-derived nanomaterials for energy storage and conversion. Nano Sel. 2021, 2, 1682–1706.
  37. Bhat, V.S.; Jayeoye, T.J.; Rujiralai, T.; Sirimahachai, U.; Chong, K.F.; Hegde, G. Influence of surface properties on electro-chemical supercapacitors utilizing Callerya atropurpurea pod derived porous nanocarbons: Structure property relationship between porous structures to energy storage devices. Nano Sel. 2020, 1, 226–243.
  38. Zhao, J.; Cui, Y.; Zhang, J.; Wu, J.; Yue, Y.; Qian, G. Fabrication of a Sustainable Closed Loop for Waste-Derived Materials in Electrochemical Applications. Ind. Eng. Chem. Res. 2021, 60, 11637–11648.
  39. Joseph, S.; Saianand, G.; Benzigar, M.R.; Ramadass, K.; Singh, G.; Gopalan, A.I.; Yang, J.H.; Mori, T.; Al-Muhtaseb, A.H.; Yi, J.; et al. Recent Advances in Functionalized Nanoporous Carbons Derived from Waste Resources and Their Applications in Energy and Environment. Adv. Sustain. Syst. 2021, 5, 1–30.
  40. Upare, D.P.; Yoon, S.; Lee, C.W. Nano-structured porous carbon materials for catalysis and energy storage. Korean J. Chem. Eng. 2011, 28, 731–743.
  41. Wang, D.W.; Li, F.; Liu, M.; Lu, G.Q.; Cheng, H.M. 3D aperiodic hierarchical porous graphitic carbon material for high-rate electrochemical capacitive energy storage. Angew. Chem. Int. Ed. 2008, 47, 373–376.
  42. Kubo, S.; White, R.J.; Tauer, K.; Titirici, M.M. Flexible coral-like carbon nanoarchitectures via a dual block copolymer-latex templating approach. Chem. Mater. 2013, 25, 4781–4790.
  43. Larcher, D.; Tarascon, J.-M. Towards greener and more sustainable batteries for electrical energy storage. Nat. Chem. 2015, 7, 19–29.
  44. Zhang, L.; Liu, Z.; Cui, G.; Chen, L. Biomass-derived materials for electrochemical energy storages. Prog. Polym. Sci. 2015, 43, 136–164.
  45. Xu, G.; Han, J.; Ding, B.; Nie, P.; Pan, J.; Dou, H.; Li, H.; Zhang, X. Biomass-derived porous carbon materials with sulfur and nitrogen dual-doping for energy storage. Green Chem. 2015, 17, 1668–1674.
  46. Kigozi, M.; Kali, R.; Bello, A.; Padya, B.; Kalu-Uka, G.M.; Wasswa, J.; Jain, P.K.; Onwualu, P.A.; Dzade, N.Y. Modified activation process for supercapacitor electrode materials from african maize cob. Materials 2020, 13, 5412.
  47. Januszewicz, K.; Cymann-Sachajdak, A.; Kazimierski, P.; Klein, M.; Łuczak, J.; Wilamowska-Zawłocka, M. Chestnut-derived activated carbon as a prospective material for energy storage. Materials 2020, 13, 4658.
  48. Liu, W.-J.; Jiang, H.; Yu, H.-Q. Emerging applications of biochar-based materials for energy storage and conversion. Energy Environ. Sci. 2019, 12, 1751–1779.
  49. Simon, P.; Gogotsi, Y.; Dunn, B. Where Do Batteries End and Supercapacitors Begin? Science 2014, 343, 1210–1211.
  50. Vinodh, R.; Sasikumar, Y.; Kim, H.-J.; Atchudan, R.; Yi, M. Chitin and Chitosan Based Biopolymer Derived Electrode Materials for Supercapacitor Applications: A Critical Review. J. Ind. Eng. Chem. 2021, 104, 155–171.
  51. Peter, S.; Lyczko, N.; Gopakumar, D.; Maria, H.J.; Nzihou, A.; Thomas, S. Chitin and chitosan based composites for energy and environmental applications: A Review. Waste Biomass Valoriz. 2020, 12, 4777–4804.
  52. Ikram, R.; Mohamed Jan, B.; Abdul Qadir, M.; Sidek, A.; Stylianakis, M.M.; Kenanakis, G. Recent Advances in Chitin and Chitosan/Graphene-Based Bio-Nanocomposites for Energetic Applications. Polymers 2021, 13, 3266.
  53. Lionetto, F.; Esposito Corcione, C. Recent applications of biopolymers derived from fish industry waste in food packaging. Polymers 2021, 13, 2337.
  54. Mishra, P.K.; Gautam, R.K.; Kumar, V.; Kakatkar, A.S.; Chatterjee, S. Synthesis of Biodegradable Films Using Gamma Irradiation from Fish Waste. Waste Biomass Valoriz. 2020, 12, 2247–2257.
  55. Shahbandeh, M. Fish Production Worldwide 2002–2019. Available online: https://www.statista.com/statistics/264577/total-world-fish-production-since-2002/ (accessed on 4 November 2020).
  56. Qin, D.; Bi, S.; You, X.; Wang, M.; Cong, X.; Yuan, C.; Yu, M.; Cheng, X.; Chen, X.-G. Development and application of fish scale wastes as versatile natural biomaterials. Chem. Eng. J. 2022, 428, 131102.
  57. Yuvaraj, D.; Bharathiraja, B.; Rithika, J.; Dhanasree, S.; Ezhilarasi, V.; Lavanya, A.; Praveenkumar, R. Production of biofuels from fish wastes: An overview. Biofuels 2019, 10, 301–307.
  58. Cadavid-Rodríguez, L.S.; Vargas-Muñoz, M.A.; Plácido, J. Biomethane from fish waste as a source of renewable energy for artisanal fishing communities. Sustain. Energy Technol. Assess. 2019, 34, 110–115.
  59. Rai, A.K.; Swapna, H.C.; Bhaskar, N.; Halami, P.M.; Sachindra, N.M. Effect of fermentation ensilaging on recovery of oil from fresh water fish viscera. Enzyme Microb. Technol. 2010, 46, 9–13.
  60. Odoom-Wubah, T.; Rubio, S.; Tirado, J.L.; Ortiz, G.F.; Akoi, B.J.; Huang, J.; Li, Q. Waste Pd/Fish-Collagen as anode for energy storage. Renew. Sustain. Energy Rev. 2020, 131, 9968.
  61. Putro, S.P.; Sharani, J.; Adhy, S. Biomonitoring of the Application of Monoculture and Integrated Multi-Trophic Aquaculture (IMTA) Using Macrobenthic Structures at Tembelas Island, Kepulauan Riau Province, Indonesia. J. Mar. Sci. Eng. 2020, 8, 942.
  62. Kang, Y.; Kim, H.-J.; Moon, C.-H. Eutrophication Driven by Aquaculture Fish Farms Controls Phytoplankton and Dinoflagellate Cyst Abundance in the Southern Coastal Waters of Korea. J. Mar. Sci. Eng. 2021, 9, 362.
  63. Sotelo, C.G.; Blanco, M.; Ramos, P.; Vázquez, J.A.; Perez-Martin, R.I. Sustainable Sources from Aquatic Organisms for Cosmeceuticals Ingredients. Cosmetics 2021, 8, 48.
  64. Blanco, M.; Sotelo, C.G.; Pérez-Martín, R.I. New strategy to cope with common fishery policy landing obligation: Collagen extraction from skins and bones of undersized hake (Merluccius merluccius). Polymers 2019, 11, 1485.
  65. Tang, X.; Liu, D.; Wang, Y.-J.; Cui, L.; Ignaszak, A.; Yu, Y.; Zhang, J. Research advances in biomass-derived nanostructured carbons and their composite materials for electrochemical energy technologies. Prog. Mater. Sci. 2020, 118, 100770.
  66. Ling, H.Y.; Chen, H.; Wu, Z.; Hencz, L.; Qian, S.; Liu, X.; Liu, T.; Zhang, S. Sustainable bio-derived materials for addressing critical problems of next-generation high-capacity lithium-ion batteries. Mater. Chem. Front. 2021, 5, 5932–5953.
  67. Fu, M.; Chen, W.; Zhu, X.; Yang, B.; Liu, Q. Crab shell derived multi-hierarchical carbon materials as a typical recycling of waste for high performance supercapacitors. Carbon 2019, 141, 748–757.
  68. Niu, J.; Shao, R.; Liu, M.; Zan, Y.; Dou, M.; Liu, J.; Zhang, Z.; Huang, Y.; Wang, F. Porous carbons derived from collagen-enriched biomass: Tailored design, synthesis, and application in electrochemical energy storage and conversion. Adv. Funct. Mater. 2019, 29, 1905095.
  69. Chen, W.; Zhang, H.; Huang, Y.; Wang, W. A fish scale based hierarchical lamellar porous carbon material obtained using a natural template for high performance electrochemical capacitors. J. Mater. Chem. 2010, 20, 4773–4775.
  70. Liu, J.; Poh, C.K.; Zhan, D.; Lai, L.; Lim, S.H.; Wang, L.; Liu, X.; Gopal Sahoo, N.; Li, C.; Shen, Z.; et al. Improved synthesis of graphene flakes from the multiple electrochemical exfoliation of graphite rod. Nano Energy 2013, 2, 377–386.
  71. Gao, M.; Su, C.C.; He, M.; Glossmann, T.; Hintennach, A.; Feng, Z.; Huang, Y.; Zhang, Z. A high performance lithium-sulfur battery enabled by a fish-scale porous carbon/sulfur composite and symmetric fluorinated diethoxyethane electrolyte. J. Mater. Chem. A 2017, 5, 6725–6733.
  72. Yao, H.; Zheng, G.; Li, W.; McDowell, M.T.; Seh, Z.; Liu, N.; Lu, Z.; Cui, Y. Crab shells as sustainable templates from nature for nanostructured battery electrodes. Nano Lett. 2013, 13, 3385–3390.
  73. Pendashteh, A.; Orayech, B.; Ajuria, J.; Jáuregui, M.; Saurel, D. Exploring Vinyl Polymers as Soft Carbon Precursors for M-Ion (M = Na, Li) Batteries and Hybrid Capacitors. Energies 2020, 13, 4189.
  74. Ali, M.U.; Zafar, A.; Nengroo, S.H.; Hussain, S.; Junaid Alvi, M.; Kim, H.-J. Towards a smarter battery management system for electric vehicle applications: A critical review of lithium-ion battery state of charge estimation. Energies 2019, 12, 446.
  75. Bozzini, B.; Mele, C.; Veneziano, A.; Sodini, N.; Lanzafame, G.; Taurino, A.; Mancini, L. Morphological evolution of Zn-sponge electrodes monitored by in situ X-ray computed microtomography. ACS Appl. Energy Mater. 2020, 3, 4931–4940.
  76. Lavagna, L.; Meligrana, G.; Gerbaldi, C.; Tagliaferro, A.; Bartoli, M. Graphene and lithium-based battery electrodes: A review of recent literature. Energies 2020, 13, 4867.
  77. Goriparti, S.; Miele, E.; De Angelis, F.; Di Fabrizio, E.; Zaccaria, R.P.; Capiglia, C. Review on recent progress of nanostructured anode materials for Li-ion batteries. J. Power Sources 2014, 257, 421–443.
  78. Lee, J.-P.; Choi, S.; Cho, S.; Song, W.-J.; Park, S. Fabrication of Carbon Nanofibers Decorated with Various Kinds of Metal Oxides for Battery Applications. Energies 2021, 14, 1353.
  79. Verma, S.; Sinha-Ray, S.; Sinha-Ray, S. Electrospun CNF Supported Ceramics as Electrochemical Catalysts for Water Splitting and Fuel Cell: A Review. Polymers 2020, 12, 238.
  80. Lu, J.; Wang, D.; Liu, J.; Qian, G.; Chen, Y.; Wang, Z. Hollow double-layer carbon nanocage confined Si nanoparticles for high performance lithium-ion batteries. Nanoscale Adv. 2020, 2, 3222–3230.
  81. Sun, Y.; Zhu, D.; Liang, Z.; Zhao, Y.; Tian, W.; Ren, X.; Wang, J.; Li, X.; Gao, Y.; Wen, W. Facile renewable synthesis of nitrogen/oxygen co-doped graphene-like carbon nanocages as general lithium-ion and potassium-ion batteries anode. Carbon 2020, 167, 685–695.
  82. Chen, C.; Huang, Y.; Lu, M.; Zhang, J.; Li, T. Tuning morphology, defects and functional group types in hard carbon via phosphorus doped for rapid sodium storage. Carbon 2021, 183, 415–427.
  83. Wang, H.; Hu, J.; Yang, Y.; Wu, Q.; Li, Y. Fabrication of high-performance lithium ion battery anode materials from polysilsesquioxane nanotubes. J. Alloys Compd. 2021, 859, 157801.
  84. Liu, H.J.; Wang, X.M.; Cui, W.J.; Dou, Y.Q.; Zhao, D.Y.; Xia, Y.Y. Highly ordered mesoporous carbon nanofiber arrays from a crab shell biological template and its application in supercapacitors and fuel cells. J. Mater. Chem. 2010, 20, 4223–4230.
  85. Lian, X.; Li, Q.; Zhao, Y.; Liu, S.; Liu, H.; Zhang, H. The electrochemical properties of porous carbon derived from the prawn as anode for lithium ion batteries. Int. J. Electrochem. Sci. 2018, 13, 2474–2482.
  86. Liu, Y.; Huang, B.; Lin, X.; Xie, Z. Biomass-derived hierarchical porous carbons: Boosting the energy density of supercapacitors via an ionothermal approach. J. Mater. Chem. A 2017, 5, 13009–13018.
  87. Wang, L.; Zheng, Y.; Wang, X.; Chen, S.; Xu, F.; Zuo, L.; Wu, J.; Sun, L.; Li, Z.; Hou, H. Nitrogen-doped porous carbon/Co3O4 nanocomposites as anode materials for lithium-ion batteries. ACS Appl. Mater. Interfaces 2014, 6, 7117–7125.
  88. Qadrdan, M.; Jenkins, N.; Wu, J. Smart grid and energy storage. In McEvoy’s Handbook of Photovoltaics; Elsevier: Amsterdam, The Netherlands, 2018; pp. 915–928.
  89. Elizabeth, I.; Singh, B.P.; Trikha, S.; Gopukumar, S. Bio-derived hierarchically macro-meso-micro porous carbon anode for lithium/sodium ion batteries. J. Power Sources 2016, 329, 412–421.
  90. Wang, X.-T.; Yu, H.-Y.; Liang, H.-J.; Gu, Z.-Y.; Nie, P.; Wang, H.; Guo, J.-Z.; Ang, E.H.; Wu, X.-L. Waste Utilization of Crab Shell: 3D Hierarchically Porous Carbon Towards High-Performance Na/Li Storage. New J. Chem. 2021, 45, 19439–19445.
  91. Asenbauer, J.; Eisenmann, T.; Kuenzel, M.; Kazzazi, A.; Chen, Z.; Bresser, D. The success story of graphite as a lithium-ion anode material–fundamentals, remaining challenges, and recent developments including silicon (oxide) composites. Sustain. Energy Fuels 2020, 4, 5387–5416.
  92. Bresser, D.; Paillard, E.; Passerini, S. Advances in Batteries for Medium- and Large-Scale Energy Storage; Woodhead Publishing Series in Energy; Elservier: Amsterdam, The Netherlands, 2014.
  93. Wentker, M.; Greenwood, M.; Leker, J. A bottom-up approach to lithium-ion battery cost modeling with a focus on cathode active materials. Energies 2019, 12, 504.
  94. Zhao, Q.; Lu, Y.; Chen, J. Advanced organic electrode materials for rechargeable sodium-ion batteries. Adv. Energy Mater. 2017, 7, 1601792.
  95. Darjazi, H.; Staffolani, A.; Sbrascini, L.; Bottoni, L.; Tossici, R.; Nobili, F. Sustainable Anodes for Lithium-and Sodium-Ion Batteries Based on Coffee Ground-Derived Hard Carbon and Green Binders. Energies 2020, 13, 6216.
  96. Peters, J.F.; Peña Cruz, A.; Weil, M. Exploring the economic potential of sodium-ion batteries. Batteries 2019, 5, 10.
  97. Zhang, W.; Zhang, F.; Ming, F.; Alshareef, H.N. Sodium-ion battery anodes: Status and future trends. Energy Chem. 2019, 1, 100012.
  98. Dou, X.; Hasa, I.; Saurel, D.; Vaalma, C.; Wu, L.; Buchholz, D.; Bresser, D.; Komaba, S.; Passerini, S. Hard carbons for sodium-ion batteries: Structure, analysis, sustainability, and electrochemistry. Mater. Today 2019, 23, 87–104.
  99. Velez, V.; Ramos-Sánchez, G.; Lopez, B.; Lartundo-Rojas, L.; González, I.; Sierra, L. Synthesis of novel hard mesoporous carbons and their applications as anodes for Li and Na ion batteries. Carbon 2019, 147, 214–226.
  100. del Saavedra Rios, C.M.; Simonin, L.; de Geyer, A.; Ghimbeu, C.M.; Dupont, C. Unraveling the Properties of Biomass-Derived Hard Carbons upon Thermal Treatment for a Practical Application in Na-Ion Batteries. Energies 2020, 13, 3513.
  101. Luo, X.; Chen, S.; Hu, T.; Chen, Y.; Li, F. Renewable biomass-derived carbons for electrochemical capacitor applications. SusMat 2021, 1, 211–240.
  102. Dahbi, M.; Nakano, T.; Yabuuchi, N.; Ishikawa, T.; Kubota, K.; Fukunishi, M.; Shibahara, S.; Son, J.-Y.; Cui, Y.-T.; Oji, H. Sodium carboxymethyl cellulose as a potential binder for hard-carbon negative electrodes in sodium-ion batteries. Electrochem. Commun. 2014, 44, 66–69.
  103. Abraham, K.M. How Comparable Are Sodium-Ion Batteries to Lithium-Ion Counterparts? ACS Energy Lett. 2020, 5, 3544–3547.
  104. Chen, C.; Wang, Z.; Zhang, B.; Miao, L.; Cai, J.; Peng, L.; Huang, Y.; Jiang, J.; Huang, Y.; Zhang, L. Nitrogen-rich hard carbon as a highly durable anode for high-power potassium-ion batteries. Energy Storage Mater. 2017, 8, 161–168.
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