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Agricultural waste as food, feed and functional products

International Journal of Agriculture and Food Science · 2026 · Vol. 8(4) · pp. 248–257
Bharti KapilaNeha Babbar

Abstract

Agricultural and agro-industrial activities generate substantial quantities of residues, including husks, peels, bagasse, pomace, and animal by-products. These materials are often treated as waste and disposed of through inefficient or environmentally harmful practices, resulting in the loss of valuable nutrients and bioactive compounds. However, these residues are rich sources of dietary fiber, proteins, phytochemicals, and other functional biomolecules that can be effectively converted into value-added food, feed, and functional products. This review provides a comprehensive overview of current approaches for the valorization of agricultural and agro-industrial wastes, with particular emphasis on applications in food and animal feed systems. Both conventional and emerging extraction technologies are discussed, including enzyme-assisted extraction, ultrasound-assisted extraction, microwave-assisted extraction, and supercritical fluid extraction. These techniques demonstrate significant potential for recovering high-value compounds from low-cost raw materials. In addition, recent advancements such as encapsulation, nanoemulsion systems, and fermentation-based strategies are highlighted for improving the stability and bioavailability of recovered bioactives. The utilization of agro-residues in animal feed production, particularly through solid-state fermentation, is also discussed as a sustainable approach to enhance protein content and reduce anti-nutritional factors. The review further addresses key challenges, including raw material collection, process scalability, economic feasibility, and consumer acceptance. Future prospects are explored with an emphasis on integrated biorefinery approaches and supportive policy frameworks. Overall, this review underscores the potential of agricultural waste valorization in promoting sustainable food systems, reducing environmental impact, and improving resource efficiency.

Full Text

Tables and figures are in the full-text PDF.

Introduction

The main driver of the world economy, agriculture provides the basis for industrial growth, energy production, and food security. But it is also the main cause of environmental stress, waste, and greenhouse gas emissions. With an estimated nearly 1.33 billion metric tonnes of waste produced yearly, including over 1.12 billion metric tonnes from industrial activity, Canada, for instance, has been said to produce the most rubbish globally. Around 4532 trillion British thermal units (TBtu) of biomass were produced in the US in 2020, which accounted for 4.9% of all primary energy use. Of this, 430 TBtu came from biomass derived from municipal trash, 2000 TBtu from biofuels, and 2101 TBtu from wood and biomass obtained from wood. Germany is the top producer of biofuel in Europe, whereas the Indonesia, Brazil, and United States are among the top producers worldwide [1] . These figures demonstrate the scope of agricultural production as well as the major obstacles associated with resource use and waste management. While the portion of crop which is not consumable, like peels, shells, stalks, husks, and press cakes, are classified as agricultural wastes, the consumable fractions of crops provide humans with direct supplies of nutrition and energy. These leftovers are produced in enormous amounts and frequently have significant levels of biological oxygen demand (BOD), suspended solids and chemical oxygen demand (COD). In addition to polluting soil and water, improper disposal practices like open dumping, uncontrolled landfilling, and burning also significantly increase greenhouse gas emissions [2] . The most of agricultural and agro-industrial wastes are still underutilized despite their abundance, which damages the environment and costs money.

Agro-industrial residues are rich sources of nutrients, dietary fibers, bioactive compounds, and functional biomolecules, which can be converted into wide range of value-added products. These materials find potential applications across several sectors, including environmental remediation, food, feed, energy, and pharmaceuticals. Research has demonstrated diverse uses of agricultural wastes such as biofuel production [3] , synthesis of nanomaterials [4] , removal of dyes and heavy metals from wastewater [5] , development of bioconstruction materials [6] , and production of bioalcohols [7] . Despite these promising applications, many of these inventions remain scattered and underexploited, highlighting the vast untapped potential of waste valorization. In this context, the present review aims to provide a comprehensive overview of the conversion of agricultural wastes into useful products, with particular focus on food, feed and functional application. It brings together existing knowledge, discuss technology approaches for waste transformation, and examines selected case studies that illustrate practical pathways toward sustainable and efficient utilization. The review aims to further the conversation on sustainable agriculture, the circular bioeconomy, and the creation of value-added goods that benefit society and the environment by highlighting the potential of agro-residues as renewable resources. Food waste and loss are urgent worldwide problems that have significant results on environment, the economy, and the society. Annually, around 1.3 billion tons of food roughly one-third of the world's production are lost or wasted, using up nearly 30% of agricultural area and significantly increasing greenhouse gas emissions. Wastage of food happens at the levels of consumer and retailers and is mostly caused by lifestyle decisions and purchasing habits, whereas food that has gone bad is described as a decline in the quality and amount of food throughout production, postharvest handling, and processing [8] . Each region generates waste at a different scale and stage. While developing nations frequently suffer losses at early supply chain stages due to inadequate facilities, countries with high-income, such those in Europe and North America, generate more waste at the consumer stage (175-200 kg per capita year) [9] . Approximately 931 million tons of food waste were reported worldwide in 2019, with the largest contributors being households (61%), food services (26%), and retail (13%) [10] . Animal-derived by-products (manure, offal, dairy whey), crop residues (stalks, straw, bagasse, culls), and processing wastes (peels, pomace, bran, seeds, pulp) are all examples of agricultural and food wastes [11,12,13] . Therefore, the expansion of resource efficiency, value added food products, and the circular economy all depend on the valorization of agricultural waste.

Important by products

Agricultural waste includes crop remains, animal corpses, plastic trash, fertilizer and pesticide runoff, agro-industrial waste, crop residues, livestock waste, and food waste. Agricultural waste is produced by a variety of farming operations and must be appropriately managed to lessen its adverse environmental consequences. Recently, agroindustrial residues from root crops and food-processing industries have drawn attention because of their rich organic matter and suitability for microbial valorisation [14] . Wheat straws are the dry stem that remains after wheat grain is harvested is known as wheat straw. The husk of rice is the insulating outer layer of rice grains that is destroyed during milling. The milling process produces rice husks, which build up in significant amounts in rice-producing areas. Sugarcane bagasse which is fibrous waste left after sugarcane juice is extracted. In regions where sugarcane is processed, bagasse which is created during the sugar extraction process is commonly accessible. Organic waste like leaves are produced by the natural shedding or harvesting of plant leaves. In gardening and farming, leaf debris often builds up in specific seasons, such the fall. Recent studies highlight that fruits, vegetables, and root crops account for nearly half of global food waste and are especially rich in carbohydrates, cellulose, soluble sugars, and organic acids, making them highly suitable substrates for microbial bioprocessing. Other wastes like cassava processing generates significant residues, particularly cassava wastewater (manihot wastewater), which contains high organic loads and requires careful management due to the presence of toxic compounds such as cyanide. Consequently, stringent treatment is necessary before its discharge into the environment [15,16,17] . Owing to their high carbohydrate content, these residues are increasingly being explored as promising substrates for microbial fermentation processes [18] . Orange peel is a particularly valuable agro-industrial residue, as it contains proteins, carbohydrates, lipids, lignin, polyphenols, and natural pigments, which enable its conversion into valueadded products such as bioplastics, functional polymers, organic acids, and various microbial metabolites. [19] . Orange peel has been used as the sole carbon source for the cultivation of Aspergillus niger, resulting in the production of 558 mg/mL of xylo-oligosaccharides under optimized fermentation conditions, thereby demonstrating its potential as a carbohydrate-rich substrate [20] . An organized summary of the loses in the form of important agro wastes, their key impacts is shown in Table 1. Recent studies indicate that fruits, vegetables, and root crop residues account for nearly half of global food waste and are rich in carbohydrates, cellulose, soluble sugars, minerals, and organic acids, making them highly suitable substrates for bioprocessing applications [33] . Interestingly, non-edible fractions such as peels and seeds often contain higher concentrations of bioactive compounds than the edible portions, highlighting the need for systematic compositional evaluation prior to their utilization [34,35] . Therefore, compounds like nutraceuticals, bioactives, antioxidants, polysaccharides, biopolymers, single cell proteins, biopeptides, antibiotics, industrial enzymes, bionanocomposites, activated carbon, chitosan, organic acids, pigments, sugars, and xanthan gum are few of the high-value compounds that can be recovered from byproducts and food wastes [31,32] . In addition, the biorefinery approach are widely applied to citrus waste streams to identify optimal valorization pathways such as the production of pectin, xylo-oligosaccharides, and organic acids based on raw material availability, seasonal variation, and overall process sustainability [36] . The replacement of chemicals, fuels, and materials derived from fossil fuels depends on the sustainable use of renewable resources. Green chemical and biotechnological methods, such as cascade processing of agricultural, forestry, and aquatic biomass, integrated biorefining, industrial symbiosis, and specialty product extraction, are used can be used accomplish this [37,38] . The concept is diagrammatically shown in Figure 1 depicting the valorisation pathways of agricultural and food wastes."

Techniques used for extraction of valuable substances from by products

Instead of being produced from petroleum-based chemicals, biobased compounds, phytochemicals, and natural bio1polymers can be recovered directly through extraction from agricultural and food wastes [39] . These priceless substances can be categorized as high-value goods and used as nutraceuticals, cosmetics, medicines, and food additives [40] . In order to fully exploit the byproducts, efficient valorization necessitates choosing extraction techniques that optimize recovery while reducing waste [38] . The characteristics of the food matrix and the target bioactive chemicals have a huge impact on the effectiveness of extraction procedures [40] . Furthermore, the efficiency of recovering specific bioactive compounds is greatly affected by the cellular structure of the by-product [41] . As reported by Soquetta [42] , extraction methods can be broadly classified into nonconventional and conventional approaches. Conventional techniques, such as such soxhlet extraction, solvent extraction, maceration, and hydrodistillation commonly rely on organic solvents including athanol, methanol, and acetone, along with controlled temperature and agitation conditions [42] . To ensure maximum recovery while preserving the stability of bioactive compounds, key operational parameters such as temperature, extraction time, pH, particle size, solid-toliquid ratio, and stirring speed must be carefully optimized. Although conventional extraction techniques are commonly employed, they suffer from several limitations, such as long extraction times, high solvent requirements, generation of toxic waste, and the need for additional purification steps to remove solvent residues and impurities [43] . To address these limitations, modern or unconventional extraction methods have been developed as faster, cleaner, and more efficient alternatives. These include enzyme assisted extraction, pressurized liquid, pressured liquid extraction, supercritical fluid extraction, microwave-assisted extraction, ultrasoundassisted extraction, and pulsed electric field-assisted extraction. Compared with traditional approaches, these techniques generally provide higher extraction efficiency, reduce solvent consumption, short processing times, and lower energy requirements [44,45] . Deep eutectic solvents (DESs) and their bio-based counterparts, known as natural deep eutectic solvents (NADESs), have emerged from the need of cost-effective and environmentally friendly extraction media. These novel solvents are particularly attractive for food waste valorization due to their low toxicity, biodegradability, and strong ability to dissolve a wide range of biomass components. DESs and NADESs have been successfully applied to extract valuable compounds from diverse sources, including lignocellulosic materials, bark, wood, algae, dairy and beverage wastes, and residues from vegetable oil processing [46,47] . The flexibility of this approach is further demonstrated by the efficient recovery of phenolic compounds from pear, tomato, olive, and onion wastes using a simple, inexpensive, and eco-friendly NADES composed of lactic acid, glucose, and water. The use of such solvents enhance the sustainability of food waste extraction and enables the food industry to obtain high-quality International Journal of Agriculture and Food Science https://www.agriculturaljournals.com functional ingredients [46] . Given the significance potential of food and agricultural wastes as source of value-added compounds, many studies have focused on refining extraction techniques to maximize recovery while minimizing environmental impact. These techniques enhance extraction efficiency and selectively align with green chemistry principles, making them particularly suitable for valorization of food and agricultural by-products [48] . Selected case studies illustrating the recovery of valuable compounds from agro-food wastes, along with the extraction methods and key outcomes, are summarized in Table 2. Ultrasound assisted extraction creates during sonic cavitation, ultrasound vibrations rupture plant tissue, facilitating the quicker release of extractable components. Bioactive substances are extracted by ultrasound from food waste and byproducts of fruits and vegetables. Microwave assisted extraction enhances molecular motion by increasing the solvent's ability to disrupt hydrogen bonds within the sample matrix, allowing the target compounds to dissolve more efficiently into the extraction fluid. Pressurized liquid extraction uses high temperatures (40-200 °C) and pressures (3.3-20.3 MPa), making molecules more soluble and desirable. Further Enzyme assisted extraction ensures that the cytoplasmic content moves through the extraction fluid, like water, by taking advantage of enzymes' ability to degrade the cell wall compartment. As this technique employs water as the extraction solvent rather than organic solvents, it is widely recognized as an environmentally benign and sustainable approach. Coffee husk Supercritical CO2 extraction 373 K, 300 bar, solvent-to-material ratio 197 kg CO2/kg Caffeine: 59% yield, 77% purity [56] Pumpkin seeds Ultrasound-assisted threephase partitioning (NH4)2SO4 30 g/100 mL, t-butanol:slurry 1:1, pH 5, duty cycle 60%, 118 W, 20 min Oil (39.79%), protein (14.30%), polysaccharides (1.97%); fatty acid composition detailed [57] Bioactive chemicals with anti-inflammatory, anticancer, antibacterial, antioxidant, and cardio metabolic health effects can be found in abundance in agricultural and food wastes [59,60] . Because of their strong antioxidant potential, polyphenols especially those found in skins, seeds, pulp, or pomace are among the most significant phytochemicals [61] . Although consumer demand for natural antioxidants is rising, their direct use in food is frequently restricted due to their salts, poor solubility, light, sensitivity to oxygen, heat, enzymes, and pH, which lowers bioavailability and bioactivity, and chemical degradation during processing and gastrointestinal transit [59,60] . Although consumer demand for natural antioxidants is rising, their direct use in food is frequently restricted due to their sensitivity to oxygen, poor solubility, pH, light, heat, enzymes, and salts, which lowers bioavailability and bioactivity, and chemical degradation during processing and gastrointestinal transit [61,62] . Although consumer demand for natural antioxidants is steadily increasing, their direct incorporation into foods is often limited due to sensitivity to oxygen, pH variations, light, heat, enzymes, and salts, as well as poor solubility. These factors can reduce their bioavailability and bioactivity, and promote chemical degradation during food processing and gastrointestinal digestion [62] . In this context, biotechnological approaches such as fermentation provide sustainable and effective routes for the valorization of food wastes by enhancing both the concentration and bioavailability of bioactive compounds. Fermentation involves the anaerobic breakdown of organic substrates and can be carried out as submerged, liquid, and solid state processes. Among these, solid state and submerged fermentation are most commonly employed for bioactive recovery. [63,64] . Fermentation not only improves the nutritional and functional properties of the resulting products but also requires lower energy input, reduced cost, and generated minimal waste. Various strategies adopted to enhance the stability and Fruit peels (citrus, apple) Spray drying (nano/microencapsulation) Retained polyphenols, improved antioxidant stability and solubility [59] Grape pomace Nanoemulsion (protein-lipid matrices) Enhanced polyphenol bioaccessibility and dispersibility [60] Tomato pomace Coacervation / Microfluidics emulsions Lycopene stability, increased bioavailability [61, 62] Mango peel W/O/W emulsions High encapsulation efficiency (98.65%), improved storage stability [65] Berry wastes (strawberry, blueberry) Freeze-drying with cyclodextrin Protected anthocyanins, improved solubility [59] Onion / garlic wastes Alginate nanoparticles Increased phenolic stability, controlled release [61] Vegetable pomace (carrot, beet) Liposome nanoencapsulation Enhanced β-carotene and phenolic bioavailability [62] Seed wastes (pumpkin, sesame) Protein-polysaccharide coacervation Increased antioxidant retention [59, 60] Agro-industrial wastes Fermentation (solid-state, submerged, liquid)

Increased phenolics, flavonoids, antioxidant activity, and bioaccessibility [43, 66] Ongoing concerns regarding the safety and acceptability of synthetic food additives have encouraged the food industry to explore natural alternatives derived from low-cost sources of proteins, colorants, flavouring agents, antioxidants, dietary fibers and antimicrobials [62,67] . By valorizing food and agro-industrial wastes as natural ingredients, industries can reduce waste management costs, create additional revenue streams, and develop products that are both nutritionally enhanced and commercially attractive. By reducing antinutritional elements, biotechnological methods can also provide byproducts that can be used to create balanced food compositions. The majority of small traders continue to dispose of waste incorrectly, even if some local communities find innovative ways to use residues. The Environmental Protection Agency (EPA) prioritizes using excess for human consumption, then animal feed, industrial applications, and composting or incineration in order to remedy this [43] . In addition to providing nutrients and bioactive chemicals, using food wastes as natural additives necessitates consideration of sensory qualities and consumer acceptability. For example, pineapple or white chocolate-flavoredss jelly samples enhanced with chicken foot collagen were rated favorably by tasters [68] . However, despite their attractive labeling, cookies enhanced with blueberry pomace were not as popular as the reference vanilla cookies [69] . Additionally, there are financial, nutritional, and environmental advantages to valuing food waste. In order to support programs like the Zero Hunger Challenge and UN Sustainable Development Goals, industries are increasingly pursuing "zero-waste" techniques, turning leftover biomass into raw materials for new goods [43] . For instance, the GEA Pro-Enrich project uses energy-efficient and economical techniques to extract pigments, dietary fibers, antioxidants, and functional proteins from fruit and vegetable residues, such as tomato, citrus, olive, and rapeseed byproducts, for use in adhesives, pet food, cosmetics, and dietary supplements [70] .. Representative case studies on the application of food waste-derived additives in different food products, along with their functional components and outcomes, are compiled in Table 4. Chicken feet Jelly (pineapple, white chocolate) Collagen Good sensory acceptance; consumers willing to consume [68] Blueberry pomace Cookies Antioxidant fiber Acceptable labeling; lower preference than reference cookie [69] Tomato residues, citrus peels, olive pomace, rapeseed meal Dietary supplements, pet food, cosmetics, adhesives Functional proteins, phenolics, dietary fibers, pigments High-quality extracts for multiple industrial applications [70] Fruit and vegetable byproducts (general) Various food products Bioactive compounds, natural colorants, antioxidants Supports zero-waste and functional food development [43] Agro By products as Animal Feed Cereal husks, fruit and vegetable peels, pulp, and bagasse are examples of agro-industrial wastes that could be used as substrates to create animal diets with added nutrients. Conventional feed products, which give animals vital macronutrients and energy, include blended raw residues, green/dry fodder (hay, silage, pasture), and formulated compound feeds. Nevertheless, these residues frequently contain anti-nutritional factors (ANFs) that restrict the availability and digestion of nutrients, including hydrogen cyanide, caffeine, polyphenols, oxalates, phytates, tannins and saponins. In addition, food and processing wastes typically possess high moisture content and readily degradable organic matter, which make them highly susceptible to rapid microbial spoilage and contamination [71] . Poor segregation practices can result in the presence of plastics, metals, chemical residues, and pathogenic microorganisms, thereby raising significant safety concerns for their use in animal feed. Furthermore, improper storage conditions may promote the formation of mycotoxins particularly aflatoxins which pose serious health risks to livestock [72] . To get around these restrictions, microbial valorization especially through Solid-State Fermentation (SSF) offers a safe and affordable solution. To convert solid organic wastes into value-added products like protein-rich feed, enzymes, bio-pigments, biofertilizers, and biofuels, SSF uses GRAS microorganisms, such as filamentous fungi (like Aspergillus niger and Rhizopus oryzae), yeasts (like Saccharomyces cerevisiae), and bacteria (like Bacillus spp. and Lactobacillus spp.) [73,74,75] . By increasing digestibility, decreasing ANFs, and increasing protein content, SSF improves the nutritional quality of agro-industrial residues. The biotransformation approach helps address protein deficiencies in livestock diets by enabling the production of safe, low cost feed alternatives. Cereal residues from sorghum, oats, corns, millet, and barley are widely valorized, while cereal by-products such as wheat bran, rice bran, and middlings are commonly used as feed concentrates or dietary supplements, particularly in regions such as North America and Europe [76] . The selection of suitable substrates for solid-sate fermentation (SSF) depends on factors such as their availability, lignocellulosic composition, carbohydrate content, and solid organic nature. Recent advances in microbial biotechnology and bioupgrading have further improve feed quality by promoting protein enrichment, redicing anti-nutritional factors and generating functional feed ingredients [73,77] . Despite these benefits, improper disposal of agro-industrial wastes remain a significant challenge, underscoring the importance of adopting SSF and related bioprocessing strategies for sustainable animal nutrition. Utilizing entire organisms or their constituent parts, bioprocessing integrates expertise from chemical engineering, microbiology, biochemistry, and related disciplines to transform raw materials into valuable products with added value (Muenz, 2021). It produces a variety of goods, such as vitamins, animal feed, biofuels, biosurfactants, and antibiotics. In addition to production, bioprocessing provides a number of "green" benefits, such as (i) using biomass rather than fossil fuels, (ii) using renewable resources sustainably, (iii) replacing depleted fossil energy, and (iv) lowering greenhouse gas emissions from petroleum-based industries [78] . Food wastes typically contain high moisture levels and readily biodegradable organic matter, making them highly susceptible to rapid microbial spoilage if left untreated [79,80] . Inadequate segregation during collection and handling may introduce contaminants such as plastics, metals, chemical residues, and pathogenic microorganisms, thereby necessitating thorough pretreatment before their use in animal feed [81] . Moreover, improper storage conditions significantly increase the risk of mycotoxin contamination particularly aflatoxins which pose serious threats to livestock health and therefore require strict monitoring and control measures [82] . Notwithstanding these advantages, it is expensive and technically difficult to produce bioproducts from biomass. Agro-industrial wastes that are high in sugar and starch act as the main fermentation substrates in the near run. Lignocellulosic agricultural leftovers are a plentiful, affordable, and readily processed source of feedstock for long-term sustainability. Solid-State Fermentation (SSF) is a viable and cost-effective biotechnological approach for the valorization of agro-inductrial residues, enabling the production of detoxified lingocellulosic materials, biofuels, animal feed and biopulp. By increasing protein content, improving essential nutrient availability, and reducing antinutritional factors (ANFs), SSF significantly enhances the nutritional quality of lignocellulosic wastes, making them suitable as safe and economical animal feed. Recent advances in bioupgrading and biodetoxification technologies have further strengthened the potential of SSF as a sustainable strategy for improving animal nutition. By increasing protein content, improving essential nutrient availability, and reducing anti-nutritional factors (ANFs), solid-state fermentation (SSF) enhances the nutritional quality of agro-industrial residues and enables the production of safe and low-cost animal feed. Recent advances in bioupgrading and biodetoxification technologies have further improved feed quality, strengthening the role of SSF as a promising strategy for sustainable animal nutrition. The first and most critical step in SSF is the selection of appropriate microbial strains and substrates. Due to the nature and large particle size of many agro-industrial wastes, substrates are commonly chopped, ground, or crushed to increase surface area, facilitate microbial colonization, and improve nutrient availability [83] . To support microbial growth and product formation, many residues, including the peels of cassava, yam, and plantains, are nutritionally lacking and need to be supplemented with external nutrients, especially nitrogen sources (such as ammonium nitrate, ammonium sulfate, peptone, sodium nitrate, yeast extract, and urea) and trace elements [84,85,86] . Studies indicate that supplementation with only microelements or nitrogen sources is insufficient, emphasizing the need for a balanced nutrient composition [87] . Filamentous fungus (like Aspergillus and Rhizopus), yeasts (like Saccharomyces), and bacteria (like Bacillus and Lactobacillus) are among the microorganisms utilized in SSF. Because they are more resilient in solid media than in liquid ones, fungus spores are favored [88][89][90][91] .

Conclusion

Agricultural and agro-industrial wastes represent a valuable yet underutilized resource with significant potential for the development of food, feed, and functional products. Advances in extraction technologies and bioprocessing approaches, particularly solid-state fermentation, have enabled the efficient recovery and enhancement of bioactive compounds from these residues. The integration of such strategies supports sustainable resource utilization, reduces environmental impact, and contributes to the circular bioeconomy. However, challenges related to scalability, economic feasibility, and consumer acceptance must be addressed to ensure wider industrial adoption. Future efforts should focus on developing cost-effective, integrated biorefinery systems and supportive policies to fully realize the potential of agricultural waste valorization.

Acknowledgement

AcknowledgementThe authors would like to acknowledge the contributions and collaboration of their co-authors in the preparation of this review .

References

  1. Tiseo I. Leading producers of biofuels worldwide in 2020, by country. Statista [Internet]. 2021 [cited 2025 Sep 14]. Available from: https://www.statista.com
  2. Yılbaşı Z. Biofuels, E-Fuels, and Waste-Derived Fuels: Advances, Challenges, and Future Directions. Sustainability. 2025 Jul 4;17(13):6145.
  3. Kumar JA, Sathish S, Prabu D, Renita AA, Saravanan A, Deivayanai VC, et al. Agricultural waste biomass for sustainable bioenergy production: Feedstock, characterization and pre-treatment methodologies. Chemosphere. 2023 Aug 1;331:138680.
  4. Hamad HN, Idrus S. Recent developments in the application of bio-waste-derived adsorbents for the removal of methylene blue from wastewater: a review. Polymers. 2022 Feb 17;14(4):783.
  5. Madurwar MV, Ralegaonkar RV, Mandavgane SA. Application of agro-waste for sustainable construction materials: A review. Construction and Building Materials. 2013 Jan 1;38:872-878.
  6. Borah D, Edachery B, Rout J, Nooruddin T. Production and characterization of bio-alcohols from agricultural wastes. In: Emerging Trends and Techniques in Biofuel Production from Agricultural Waste. Singapore: Springer Nature Singapore; 2024 Feb 24. p. 147-174.
  7. Food and Agriculture Organization of the United Nations (FAO). The state of food and agriculture 2019: Moving forward on food loss and waste reduction. FAO; 2019.
  8. Kannah RY, Merrylin J, Devi TP, Kavitha S, Sivashanmugam P, Kumar G, et al. Food waste valorization: Biofuels and value added product recovery. Bioresource Technology Reports. 2020 Sep 1;11:100524.
  9. United Nations Environment Programme (UNEP). Food waste index report. UNEP; 2021.
  10. Obi FO, Ugwuishiwu BO, Nwakaire JN. Agricultural waste concept, generation, utilization and management. Nigerian Journal of Technology. 2016 Oct 11;35(4):957-964.
  11. Baiano A. Recovery of biomolecules from food wastes-A review. Molecules. 2014 Sep 17;19(9):14821-14842.
  12. Plazzotta S, Manzocco L. Food waste valorization. In: Saving Food. Academic Press; 2019 Jan 1. p. 279-313.
  13. da Silva MD, Cano JP, Garcia-Cruz CH. Cassava hydrolysates used as substrates for the production of second-generation ethanol by Saccharomyces cerevisiae ATCC 26602 immobilized in sodium alginate spheres. Research, Society and Development. 2024 Mar 24;13(3):e9613345355.
  14. de Oliveira Schmidt VK, de Vasconscelos GM, Vicente R, de Souza Carvalho J, Della-Flora IK, Degang L, et al. Cassava wastewater valorization for the production of biosurfactants: surfactin, rhamnolipids, and mannosileritritol lipids. World Journal of Microbiology and Biotechnology. 2023 Feb;39(2):65.
  15. CONAB Companhia Nacional de Abastecimento. Análise Mensal: Mandioca-Setembro de 2023. Brasília, Brazil: Companhia Nacional de Abastecimento; 2023.
  16. Takahashi M. Cultivo da mandioca. Curitiba, Brazil: SENAR AR/PR; 2023.
  17. do Amaral Minussi G, Dos Santos AA, Scapini T, Bonatto C, Fenner ED, Dresch AP, dos Santos BC, et al. Transforming orange waste with yeasts: Bioprocess prospects. Revista Brasileira de Ciências Ambientais. 2024 Apr 10;59:e1859.
  18. Silva SD, Mafra AK, Pelissari FM, Rodrigues de Lemos L, Molina G. Biotechnology in Agro-Industry: Valorization of Agricultural Wastes, By-Products and Sustainable Practices. Microorganisms. 2025 Jul 31;13(8):1789.
  19. Chen C, Chaudhary A, Mathys A. Nutritional and environmental losses embedded in global food waste. Resources, Conservation and Recycling. 2020;160:104912.
  20. Ravindran R, Jaiswal AK. Exploitation of food industry waste for high-value products. Trends in Biotechnology. 2016 Jan 1;34(1):58-69.
  21. Conrad Z, Blackstone NT. Identifying the links between consumer food waste, nutrition, and environmental sustainability: a narrative review. Nutrition Reviews. 2021 Mar 1;79(3):301-314.
  22. Melikoglu M, Lin CS, Webb C. Analysing global food waste problem: pinpointing the facts and estimating the energy content. Central European Journal of Engineering. 2013 Jun;3(2):157-164.
  23. Paritosh K, Kushwaha SK, Yadav M, Pareek N, Chawade A, Vivekanand V. Food waste to energy: An overview of sustainable approaches for food waste management and nutrient recycling. Biomed Research International. 2017;2017:1-19.
  24. Song G, Li M, Semakula HM, Zhang S. Food consumption and waste and the embedded carbon, water and ecological footprints of households in China. Science of the Total Environment. 2015 Oct 1;529:191197.
  25. Food and Agriculture Organization of the United Nations (FAO). Food wastage footprint: Impacts on natural resources. FAO; 2013.
  26. Seberini A. Economic, social and environmental world impacts of food waste on society and zero waste as a global approach to their elimination. In: SHS Web of Conferences. EDP Sciences; 2020. p. 03010.
  27. Venkat K. The climate change and economic impacts of food waste in the United States. International Journal on Food System Dynamics. 2011 Feb 27;2(4):431-446.
  28. Chapagain A, James K. Accounting for the impact of food waste on water resources and climate change. In: Food Industry Wastes. 2013 Nov. p. 217-236.
  29. Kavitha S, Kannah RY, Kumar G, Gunasekaran M, Banu JR. Introduction: sources and characterization of food waste and food industry wastes. In: Food Waste to Valuable Resources. Academic Press; 2020 Jan 1. p. 113.
  30. Xiong X, Tsang IK, Bolan NS, Ok YS, Igalavithana AD, Kirkham MB, et al. Value-added chemicals from food supply chain wastes: State-of-the-art review and future prospects. Chemical Engineering Journal. 2019 Nov 1;375:121983.
  31. Takahashi M. Cultivo da mandioca. Curitiba, Brazil: SENAR AR/PR; 2023.
  32. Michael-Igolima U, Abbey SJ, Ifelebuegu AO, Eyo EU. Modified orange peel waste as a sustainable material for adsorption of contaminants. Materials. 2023 Jan 27;16(3):1092.
  33. Ortiz-Sanchez M, Omarini AB, González-Aguirre JA, Baglioni M, Zygadlo JA, Breccia J, et al. Valorization routes of citrus waste in the orange value chain through the biorefinery concept: The Argentina case study. Chemical Engineering and Processing. 2023 Jul 1;189:109407.
  34. Lin CS, Koutinas AA, Stamatelatou K, Mubofu EB, Matharu AS, Kopsahelis N, et al. Current and future trends in food waste valorization for the production of chemicals, materials and fuels: a global perspective. Biofuels, Bioproducts and Biorefining. 2014 Sep;8(5):686-715.
  35. Baiano A. Recovery of biomolecules from food wastes-A review. Molecules. 2014 Sep 17;19(9):14821-14842.
  36. Kover A, Kraljić D, Marinaro R, Rene ER. Processes for the valorization of food and agricultural wastes to value-added products: Recent practices and perspectives. Systems Microbiology and Biomanufacturing. 2022 Jan;2(1):50-66.
  37. Nayak A, Bhushan B. An overview of the recent trends on the waste valorization techniques for food wastes. Journal of Environmental Management. 2019 Mar 1;233:352-370.
  38. Gençdağ E, Görgüç A, Yılmaz FM. Recent advances in the recovery techniques of plant-based proteins from agro-industrial by-products. Food Reviews International. 2021 May 19;37(4):447-468.
  39. Soquetta MB, Terra LD, Bastos CP. Green technologies for the extraction of bioactive compounds in fruits and vegetables. CyTA-Journal of Food. 2018 Jan 1;16(1):400-412.
  40. Torres-Valenzuela LS, Ballesteros-Gómez A, Rubio S. Green solvents for the extraction of high added-value compounds from agri-food waste. Food Engineering Reviews. 2020 Mar;12(1):83-100.
  41. Galanakis CM. Recovery of high added-value components from food wastes: Conventional, emerging technologies and commercialized applications. Trends in Food Science & Technology. 2012 Aug 1;26(2):6887.
  42. Zia S, Khan MR, Shabbir MA, Aslam Maan A, Khan MK, Nadeem M, et al. An inclusive overview of International Journal of Agriculture and Food Science https://www.agriculturaljournals.com advanced thermal and nonthermal extraction techniques for bioactive compounds in food and food-related matrices. Food Reviews International. 2022 Aug 18;38(6):1166-1196.
  43. Jablonský M, Škulcová A, Malvis A, Šima J. Extraction of value-added components from food industry based and agro-forest biowastes by deep eutectic solvents. Journal of Biotechnology. 2018 Sep 20;282:46-66.
  44. Florindo C, Oliveira MM, Branco LC, Marrucho IM. Carbohydrates-based deep eutectic solvents: Thermophysical properties and rice straw dissolution. Journal of Molecular Liquids. 2017 Dec 1;247:441-447.
  45. Azmir J, Zaidul IS, Rahman MM, Sharif KM, Mohamed A, Sahena F, et al. Techniques for extraction of bioactive compounds from plant materials: A review. Journal of Food Engineering. 2013 Aug 1;117(4):426436.
  46. Carbone K, Amoriello T, Iadecola R. Exploitation of kiwi juice pomace for the recovery of natural antioxidants through microwave-assisted extraction. Agriculture. 2020 Sep 26;10(10):435.
  47. Cardullo N, Leanza M, Muccilli V, Tringali C. Valorization of agri-food waste from pistachio hard shells: Extraction of polyphenols as natural antioxidants. Resources. 2021 May 8;10(5):45.
  48. Yılmaz T, Kumcuoglu S, Tavman S. Ultrasoundassisted extraction of lycopene and β-carotene from tomato-processing wastes. Italian Journal of Food Science. 2017;29(1).
  49. Civan M, Kumcuoglu S. Green ultrasound-assisted extraction of carotenoid and capsaicinoid from the pulp of hot pepper paste based on the bio-refinery concept. LWT. 2019 Oct 1;113:108320.
  50. Lasta HF, Lentz L, Rodrigues LG, Mezzomo N, Vitali L, Ferreira SR. Pressurized liquid extraction applied for the recovery of phenolic compounds from beetroot waste. Biocatalysis and Agricultural Biotechnology. 2019 Sep 1;21:101353.
  51. da Rocha CB, Noreña CP. Microwave-assisted extraction and ultrasound-assisted extraction of bioactive compounds from grape pomace. International Journal of Food Engineering. 2020 Feb 25;16(12):20190191.
  52. Görgüç A, Bircan C, Yılmaz FM. Sesame bran as an unexploited by-product: Effect of enzyme and ultrasound-assisted extraction on the recovery of protein and antioxidant compounds. Food Chemistry. 2019 Jun 15;283:637-645.
  53. Tello J, Viguera M, Calvo L. Extraction of caffeine from Robusta coffee (Coffea canephora var. Robusta) husks using supercritical carbon dioxide. The Journal of Supercritical Fluids. 2011 Nov 1;59:53-60.
  54. Wang H, Chen K, Cheng J, Jiang L, Yu D, Dai Y, Wang L. Ultrasound-assisted three phase partitioning for simultaneous extraction of oil, protein and polysaccharide from pumpkin seeds. LWT. 2021 Nov 1;151:112200.
  55. Jafari SM, Capanoglu E. Extraction, processing and encapsulation of food bioactive compounds. Food Chemistry. 2022 Jul 1;381:132117.
  56. McClements DJ, Öztürk B. Utilization of nanotechnology to improve the application and bioavailability of phytochemicals derived from waste streams. Journal of Agricultural and Food Chemistry. 2021 Jul 26;70(23):6884-6900.
  57. Valdés García A, Garrigós Selva MD. Microencapsulation of natural antioxidant compounds obtained from biomass wastes: A review. In: Materials Science Forum. Trans Tech Publications Ltd; 2016 Nov 20. p. 112-126.
  58. Thakur J, Borah A. Microcapsules of bioactive compounds from fruits and vegetables waste and their utilization: A review. Pharma Innovation. 2021;10(5):151-157.
  59. Zhu Z, Gavahian M, Barba FJ, Roselló-Soto E, Kovačević DB, Putnik P, et al. Valorization of waste and by-products from food industries through the use of innovative technologies. In: Agri-food Industry Strategies for Healthy Diets and Sustainability. Academic Press; 2020 Jan 1. p. 249-266.
  60. Sadh PK, Kumar S, Chawla P, Duhan JS. Fermentation: a boon for production of bioactive compounds by processing of food industries wastes (by-products). Molecules. 2018 Oct 8;23(10):2560.
  61. Hadj Saadoun J, Bertani G, Levante A, Vezzosi F, Ricci A, Bernini V, et al. Fermentation of agri-food waste: A promising route for the production of aroma compounds. Foods. 2021 Mar 26;10(4):707.
  62. Velderrain-Rodríguez GR, Acevedo-Fani A, GonzálezAguilar GA, Martín-Belloso O. Encapsulation and stability of a phenolic-rich extract from mango peel within water-in-oil-in-water emulsions. Journal of Functional Foods. 2019 May 1;56:65-73.
  63. Martí-Quijal FJ, Khubber S, Remize F, Tomasevic I, Roselló-Soto E, Barba FJ. Obtaining antioxidants and natural preservatives from food by-products through fermentation: A review. Fermentation. 2021 Jul 7;7(3):106.
  64. Gowe C. Review on potential use of fruit and vegetables by-products as a valuable source of natural food additives. Food Science and Quality Management. 2015;45:47-61.
  65. de Almeida PF, de Araújo MG, Santana JC. Collagen extraction from chicken feet for jelly production. Acta Scientiarum Technology. 2012;34(3):345-351.
  66. Curutchet A, Cozzano S, Tárrega A, Arcia P. Blueberry pomace as a source of antioxidant fibre in cookies: Consumer's expectations and critical attributes for developing a new product. Food Science and Technology International. 2019 Dec;25(8):642-648.
  67. Garcia-Garcia G, Stone J, Rahimifard S. Opportunities for waste valorisation in the food industry-A case study with four UK food manufacturers. Journal of Cleaner Production. 2019 Feb 20;211:1339-1356.
  68. Kour R, Singh S, Sharma HB, Naik TS, Shehata N, Ali W, et al. Persistence and remote sensing of agri-food wastes in the environment: Current state and perspectives. Chemosphere. 2023 Mar 1;317:137822.
  69. Deka TJ, Osman AI, Baruah DC, Rooney DW. Assessment of bioenergy and syngas generation in India based on estimation of agricultural residues. Energy Reports. 2023 Dec 1;9:3771-3786.
  70. Yafetto L, Odamtten GT, Birikorang E, Adu S. Protein enhancement of yam (Dioscorea rotundata) peels with single-or co-inoculation of Aspergillus niger and Trichoderma viride under solid-state fermentation. Ghana Journal of Science. 2020;61(2):27-37.
  71. Pandey A, Soccol CR, Mitchell D. New developments in solid state fermentation: I-bioprocesses and products. Process Biochemistry. 2000 Jul 1;35(10):1153-1169.
  72. Abu Yazid N, Barrena R, Komilis D, Sánchez A. Solidstate fermentation as a novel paradigm for organic waste valorization: A review. Sustainability. 2017 Feb 8;9(2):224.
  73. Nambi VE, Chandrasekar V, Karthikeyan S. Value addition of grains using solid state fermentation. Nutrition and Food Science International Journal. 2017;3(4):555619.
  74. Aruna TE, Aworh OC, Raji AO, Olagunju AI. Protein enrichment of yam peels by fermentation with Saccharomyces cerevisiae (BY4743). Annals of Agricultural Sciences. 2017 Jun 1;62(1):33-37.
  75. Yang ST. Bioprocessing-from biotechnology to biorefinery. In: Bioprocessing for Value-Added Products from Renewable Resources. Elsevier; 2007 Jan 1. p. 1-24.
  76. Kohli K, Prajapati R, Sharma BK. Bio-based chemicals from renewable biomass for integrated biorefineries. Energies. 2019 Jan 13;12(2):233.
  77. Muniasamy R, Venkatachalam P, Rangarajan V, Samal S, Rathnasamy S. A comprehensive perspective on sustainable bioprocessing through extractive fermentation: Challenges and prospects. Reviews in Environmental Science and Biotechnology. 2023 Sep;22(3):715-737.
  78. Solarte-Toro JC, Cardona Alzate CA. Sustainability of biorefineries: Challenges and perspectives. Energies. 2023 Apr 28;16(9):3786.
  79. Prado-Acebo I, Cubero-Cardoso J, Lu-Chau TA, Eibes G. Integral multi-valorization of agro-industrial wastes: A review. Waste Management. 2024 Jun 30;183:42-52.
  80. Mitchell DA, Berovic M, Krieger N. Biochemical engineering aspects of solid state bioprocessing. In: New Products and New Areas of Bioprocess Engineering. 2001 Jan 30. p. 61-138.
  81. Ravindra P. Value-added food: Single cell protein. Biotechnology Advances. 2000 Oct 1;18(6):459-479.
  82. Muenz RA. Brief overview of bioprocessing. Lab Manager [Internet]. 2021. Available from: https://www.labmanager.com
  83. Yafetto L, Odamtten GT, Birikorang E, Adu S. Protein enhancement of yam peels with Aspergillus niger and Trichoderma viride under solid-state fermentation. Ghana Journal of Science. 2020;61(2):27-37.
  84. Patil SR, Dayanand A. Optimization of process for the production of fungal pectinases from deseeded sunflower head in submerged and solid-state conditions. Bioresource Technology. 2006 Dec 1;97(18):23402344.
  85. Pandey A, Soccol CR, Mitchell D. New developments in solid state fermentation: I-bioprocesses and products. Process Biochemistry. 2000 Jul 1;35(10):1153-1169.
  86. Oboh G. Nutrient enrichment of cassava peels using a mixed culture of Saccharomyces cerevisiae and Lactobacillus spp. Electronic Journal of Biotechnology. 2006 Jan;9(1).
  87. Canonico L, Comitini F, Oro L, Ciani M. Sequential fermentation with selected immobilized nonSaccharomyces yeast for reduction of ethanol content in wine. Frontiers in Microbiology. 2016 Mar 11;7:278.
  88. Ashok A, Doriya K, Rao DR, Kumar DS. Design of solid state bioreactor for industrial applications: An overview to conventional bioreactors. Biocatalysis and Agricultural Biotechnology. 2017 Jan 1;9:11-18.
  89. Adzitey F. Animal and meat production in Ghana-An overview. Journal of World's Poultry Research. 2013;3(1):1-4.
  90. Yan G, Feng Y, Long S, Zeng X, Sun Y, Tang X, et al. Challenges with biomass waste valorisation. In: Waste Valorisation: Waste Streams in a Circular Economy. 2020 Nov 16. p. 183-202.
  91. Aruna TE, Aworh OC, Raji AO, Olagunju AI. Protein enrichment of yam peels by fermentation with Saccharomyces cerevisiae. Annals of Agricultural Sciences. 2017;62(1):33-37.
  92. Das P, Ghosh K. Improvement of nutritive value of sesame oil cake in formulated diets for rohu after bioprocessing through solid state fermentation. International Journal of Aquatic Biology. 2015 Feb 19;3(2):89-101.
  93. Adu SK, Yafetto L, Ofosuhene A, Offei-Affedzie T, Adu S, Ntibe TN. Biotechnological potential of agroindustrial wastes for protein enrichment by solid-state fermentation using Aspergillus niger. Studies in Fungi. 2018 Jul 9;3(1):176-186.
  94. Anukam KC, Reid G. African traditional fermented foods and probiotics. Journal of Medicinal Food. 2009 Dec 1;12(6):1177-1184.
  95. Capanoglu E, Nemli E, Tomas-Barberan F. Novel approaches in the valorization of agricultural wastes and their applications. Journal of Agricultural and Food Chemistry. 2022 Feb 23;70(23):6787-6804.
Agricultural and Biological ResearchPhytochemicals and Antioxidant ActivitiesFood and Agricultural Sciencessupercritical fluid extractionmicrowave-assisted extractionultrasound-assisted extractionencapsulationsolid-state fermentationagricultural waste valorizationbiorefineryanimal feedsustainable food systemsbioactive compounds
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