1. Introduction
The global energy landscape is undergoing a profound transformation driven by escalating energy demand, climate instability, and mounting environmental degradation. Conventional fossil-fuel–dependent systems are increasingly incompatible with international sustainability targets, necessitating the rapid development of clean, efficient, and scalable energy storage technologies (Lionetto et al., 2021; Winter et al., 2018). At the same time, modern applications—including electric vehicles, grid-level storage, and portable electronics—require electrochemical energy systems with higher energy density, longer cycle life, and improved safety (Ryu et al., 2019; Thackeray et al., 2012). These dual pressures have intensified interest in alternative electrode materials that are not only high-performing but also environmentally sustainable.
Among emerging solutions, biomass and biowaste have gained significant attention as renewable and low-cost precursors for next-generation energy storage materials (Demirbaş, 2001; Gao et al., 2018). Biomass encompasses a vast array of organic residues originating from plants, animals, and industrial processing streams, with global production reaching hundreds of gigatons annually (Bar-On et al., 2018). Despite this abundance, a substantial fraction of biomass is discarded or incinerated, contributing to greenhouse gas emissions and ecological degradation (Malmgren & Riley, 2012). Valorizing these residues into functional materials aligns closely with circular economy principles by simultaneously reducing waste burdens and offsetting reliance on finite raw materials (Larcher & Tarascon, 2015).
A particularly compelling yet underutilized biomass source is biowaste generated by the aquatic and fish processing industries. Large volumes of fish scales, skins, bones, fins, and shells are discarded globally, accounting for approximately 50–75% of total seafood biomass and amounting to 7.2–12 million tons of waste per year (Qin et al., 2022; Sotelo et al., 2021). Improper disposal of these residues contributes to oxygen depletion in marine ecosystems and poses serious ecological risks (Lionetto & Esposito Corcione, 2021; Yaman, 2004). However, from a materials science perspective, fishery waste is uniquely valuable due to its intrinsic enrichment in carbon, nitrogen, oxygen, sulfur, and hydrogen—elements that are critical for electrochemical functionality (Selvamani et al., 2015; Tang et al., 2020).
Through thermochemical processes such as pyrolysis, carbonization, and chemical activation, fish-derived residues can be transformed into heteroatom-doped nanoporous carbons with tailored pore structures and exceptionally high surface areas, in some cases exceeding 3000 m² g⁻¹ (Deng et al., 2016; Sevilla et al., 2018). These properties are particularly advantageous for electrochemical energy storage, where ion transport kinetics, electrode–electrolyte interactions, and structural stability dictate performance (Simon et al., 2014). Experimental studies have demonstrated that carbons derived from fish scales, crab shells, and shrimp shells exhibit superior lithium and sodium storage capacities compared to conventional graphite anodes (Selvamani et al., 2015; Wang et al., 2018).
In parallel, lignocellulosic agricultural residues—including almond shells, walnut shells, fruit stones, and crop stalks—represent another abundant and sustainable class of biomass precursors (Benítez et al., 2018; Zhang et al., 2015). Unlike food-based carbon sources, these non-edible residues do not compete with human nutrition or agricultural land use (Yuan et al., 2021). Their inherent cellulose, hemicellulose, and lignin content enables the formation of robust carbon frameworks with tunable micro- and mesoporosity (Dutta et al., 2014; Titirici & Antonietti, 2010). Such structures are particularly well suited for hosting electrochemically active species in advanced battery systems.
Lithium-ion batteries (LIBs), which dominate the current energy storage market, rely heavily on commercial graphite anodes with a theoretical capacity limited to 372 mAh g⁻¹ (Zhang et al., 2015). These materials also suffer from structural degradation and limited rate performance under high-demand conditions (Senthil & Lee, 2021). Biomass-derived carbons, by contrast, offer hierarchical pore networks and abundant defect sites that facilitate rapid ion diffusion and enhance reversible capacity (Long et al., 2017). Fish-waste-derived carbons, in particular, have demonstrated capacities far exceeding that of graphite, highlighting their promise as sustainable anode alternatives.
Beyond LIBs, lithium–sulfur (Li–S) batteries represent a next-generation technology with a theoretical specific capacity of 1675 mAh g⁻¹, substantially higher than conventional lithium-ion systems (Akridge et al., 2004; Bresser et al., 2013). Despite this advantage, Li–S batteries are hindered by the polysulfide shuttle effect, which leads to rapid capacity fading and poor cycle life (Nelson et al., 2012; Zhang, 2013). Biomass-derived porous carbons—particularly those derived from almond shells, cherry pits, olive stones, and agricultural residues—have proven effective as sulfur hosts that physically confine polysulfides and enhance electrochemical stability (Benítez et al., 2018; Moreno et al., 2014; Wu et al., 2016).
Supercapacitors further benefit from biowaste valorization due to their reliance on high surface area and surface chemistry rather than bulk crystallinity (Simon et al., 2014). Engineered biochars derived from both fishery and agricultural waste have demonstrated excellent capacitance retention and power density, especially when naturally doped with nitrogen or sulfur (Dos Reis et al., 2020). Moreover, protein-rich animal wastes such as fish scales and feathers have enabled the development of unconventional energy systems, including protein batteries and metal-free electrocatalysts for fuel cells (Guo et al., 2017; Hussain et al., 2020).
While individual experimental studies strongly support the promise of biowaste-derived materials, performance metrics vary widely depending on feedstock composition, synthesis conditions, and electrochemical configuration. To date, a quantitative synthesis of these results remains limited. Systematic review and meta-analysis offer a powerful framework for consolidating dispersed experimental evidence, identifying performance trends, and evaluating the statistical robustness of reported capacities and efficiencies (Anthony et al., 2021). By integrating data across fishery and agricultural biomass sources, this study provides a comprehensive and statistically grounded assessment of biowaste-derived carbons in electrochemical energy storage systems.




