Skip Content
You are currently on the new version of our website. Access the old version .
SustainabilitySustainability
  • Editor’s Choice
  • Review
  • Open Access

26 April 2022

Food Additives from Fruit and Vegetable By-Products and Bio-Residues: A Comprehensive Review Focused on Sustainability

,
,
,
,
and
Centro de Investigação da Montanha (CIMO), Instituto Politécnico de Bragança, Campus de Santa Apolónia, 5300-253 Bragança, Portugal
*
Authors to whom correspondence should be addressed.
This article belongs to the Collection Food Additives and Sustainability

Abstract

Food waste is one of the fundamental issues when it comes to environmental impacts, and this type of waste results in the food’s loss itself, but also that of water, energy, fertilizers, and other resources used for its production. Many vegetable parts are removed from the final product before reaching retail (peels, roots, and seeds), and these raw materials are rich sources of highly valuable molecules such as phytochemicals, minerals, vitamins, and other compounds with health benefits (prevention of several diseases, improvement of the immune system, regulating gastrointestinal transit, and others). Therefore, substantial efforts have been made to find technological solutions to avoid food waste, namely through its reuse in the food chain, thus promoting the circular economy and sustainability. This review focuses on the biggest wastes generated by the food industry, the most common destinations, and case studies applying these by-products or biowaste in the food industry.

1. Introduction

Environmental problems, economic losses, inefficient use of resources (land, energy, water, chemicals, labor) are consequences of food loss and waste [1,2]. About a third of the world’s food production is lost or wasted per year, and around 22% of this loss is residue from fruits and vegetables (FV) [3,4], resulting in approximately $490 billion in losses per year. From the environmental point of view, it represents 8% of greenhouse gas emissions, 23% of fertilizer consumption, and 25% of fresh water used in agriculture and the use of arable land [5]. Food waste and loss was identified as one priority for the application of the European Circular Economic Strategy by the European Commission, in which food issues, such as safety and waste management, are among the major problems of the century [6].
In food waste processing, effluents and by-products are produced, products that, if treated incorrectly, can further negatively aggravate environmental impacts. Thus, the need for innovative solutions for the reuse of waste and by-products becomes a mandatory target of research [7]. The by-products and FV residues have the potential to be reused in secondary processes as a source of valuable compounds (oils, lipids, proteins, fibers, and phenolic and other bioactive compounds) [8].
Therefore, this review aims to describe the ways in which by-products are discarded and the potential reuse of residues from fruits and vegetables generated at different stages of the supply chain, and reports the main existing potential solutions to valorize the reuse of these raw materials.

2. Generation of Fruit and Vegetable Waste

2.1. Food Waste Definition

According to Directive 2008/98/EC of the European Parliament and of the Council, waste is defined as “any substance or objects that the holder disposes of or has the intention or obligation to dispose of”, and biowaste as “waste from biodegradable garden, food and kitchen residues from homes, restaurants, catering and retail units and similar residues from food processing units” [9]. In this review, biowaste will be portrayed as waste.
The absence of a definition of loss and food waste commonly accepted in the literature is an aspect that provides diversity in analyses and estimates. Consequently, it makes it difficult to unify the study of food loss and waste along the supply chain. Data from different sources can contain great heterogeneity and present a relevant range of values [5,10,11]. The Food and Agriculture Organization of the United Nations (FAO) understands that the negative variation in the quality and quantity of food is a loss or waste, and differentiates between the definition of food loss and food waste. Therefore, FAO considers: “food loss, as occurring along the food supply chain (harvest/slaughter/capture) until, but not including the retail level. Food waste, on the other hand, occurring in retail and consumption level (…), inedible parts are not considered as loss or food waste” [4].
In contrast, Food Use for Social Innovation by Optimizing Waste Prevention Strategies (FUSIONS) presents a broader definition of food waste: “is any food or inedible part of food removed from the supply chain to be recovered or disposed of” [12]. In comparison, the FUSIONS definition joins the FAO definition of food loss and waste, and adds inedible parts of food such as peels, logs, and others [3,12]. In this article, the concept used will be in accordance with FUSIONS due to the greater scope of the term.
The waste generated in the supply chain can be treated and converted into products with added value [5]. With vegetables, some by-products are peels, seeds, stems, leaves, roots, and pieces of food that derive from processing [13]. As wasted products have valuable compounds which can be extracted and used in different products, some researchers use the term “by-product” or “co-product” to identify wasted food, which have these molecules [5,14,15].

2.2. Waste in the Food Supply Chain

There are many indications that fruits and vegetables play a key role in the human diet. The presence of magnesium in these foods, for example, is associated with a reduced risk of type 2 diabetes [16]. Likewise, the intake of phenolic acids, carotenoids, and vitamin C are highly associated with the prevention of overall cancer and cardiovascular diseases due to the reduction of oxidative stress [17]. Furthermore, vegetables influence other aspects of the human body’s systems, such as improved appetite, enhanced flavor, and improved digestion. The advantages mentioned above are mainly explained by the composition of these foods, with many vitamins, fibers, minerals, and phytochemicals and a low caloric value (proteins and carbohydrates) [13,18].
The per capita consumption of vegetables in the world is 199 g/day, half than the recommendations of The World Health Organization (WHO) of 400 g/day and defined as the ideal content for significant health benefits. Data show Asia is the major consumer of vegetables, followed by Africa, North America, Oceania, Latin America and, finally, Europe. Regarding food waste, the continents follow the reverse order. Europe, North America, and Oceania, where the income is highest, are the most wasteful, followed by Asia, Africa, and Latin America, continents with limited sources of food [13]. India is one of the largest fruits and vegetable producers in the world, and over 30% of its production is lost due to difficulties in transport and storage that cause physical changes in food [19].
Agricultural and agro-industrial activity produce a large portion of waste and by-products [20]. The residues and by-products of fruits and vegetables (RBFV) occur mainly due to the fruits and vegetables being perishable and fragile to mechanical damages during processing. Moreover, there is also an unsuitable appearance, unwanted microorganisms in FV, and unnecessary parts in the final product [3].
Each stage of the supply chain (production, processing, packaging, handling, and transportation) contributes to the generation of these RBFV. In the first stage of the supply chain (production), there is a loss in the production itself, caused by mechanical damage to food, products left on the ground, climatic factors, insect and pest infestations, and deterioration of the harvest. Post-harvest, it is caused by improper handling and management, which makes it difficult to handle, store and transport the fresh product, in addition to deterioration over time [21]. In the intermediate stages of processing and distribution, the losses of the former are caused by the degradation and deterioration of the industrial process of transformation and the elimination of foods that are not suitable for processing. The causes of the distribution are due to low infrastructure, both in storing and packaging. In the last stage of the supply chain (consumption), the loss occurs due to the deterioration and non-consumption of the purchased food by the consumer, which is subsequently discarded in dumpsters along with other waste. In all stages of the chain, the qualitative and quantitative loss is present [4,11,13,22].
Waste in the consumption stage represents only 10% in developing countries, in which the harvesting and processing are the biggest stages of loss due to the lack of adequate infrastructures for storage and transport. In developed countries, due to stricter safety and quality standards, the greatest losses are in the harvest and consumption steps [5]. Figure 1 shows data regarding the loss of FV from world regions during each stage of the supply chain.
Figure 1. Fruits and vegetables loss during the supply chain in different regions.
Within the FV sector, the juice, vegetable, oil, potato starch, sugar and canned FV industries are among the main residue generators. FAO data estimate that 88 million tons of losses are generated by the European Union, with a growing trend. In North America, the value is almost double, about 170 million tons [5]. In the economic aspect, 750 billion dollars/year are lost in food waste [3]. Figure 2 exemplifies the estimated post-harvest loss of FV from other countries [22].
Figure 2. Fruits and vegetables loss post-harvest for other countries.
Several reports show that 38% of the used raw material in weight is equivalent to by-products, namely leaves, seeds, stems, branches, peels, waste from trim, pulps and bagasse [23,24]. Besides that, the amount of waste may be influenced by the countries’ infrastructure and cultural issues. Worldwide data referring to the quantity and type of by-products generated are few, mainly due to a difference in definitions and difficulty in collecting information in some stages along the supply chain [13].

2.3. Most-Representative Fruits and Vegetables Generating Waste

In Figure 3, the main by-products from different foods are shown, and Table 1 summarizes the data found in the literature about the annual production of vegetables and fruits, the percentage and amount of by-products only, as well as their destination.
Figure 3. Main by-products of fruits and vegetables.
Table 1. Production of fruits and vegetables and respective by-products generated.

2.3.1. Fruit Waste and By-Products

The main citrus fruits that have a global representation are orange (Citrus sinensis L.), lemon (Citrus limon L.), lime (Citrus aurantiifolia L.) and mandarin (Citrus reticulata L.), with an annual production of approximately 109.1 million tons. The peels, internal tissue and seeds are by-products generated by the industry. About 50% of the fruit becomes by-products during processing, and about 15 million tons of peel waste are generated per year [28,29].
Grape (Vitis sp.) bagasse is another residue composed of the peels, seeds and stems of the fruit, generated in the production of wine (about 80% of the total production of grapes) [15]. Furthermore, the by-products may come from the production of juices, jelly and raisins, but in smaller quantities [18].
Apple (Malus domestica) pomace, for instance, is a residue composed of the peels, seeds, stems and pulp of apples, produced by the fruit juice industry [15,27]. Mango (Mangifera indica L.) is one of the most important tropical fruits in the world, and the main by-products produced by mango are peels and seeds. This fruit can be consumed in juices, in jellies, frozen, dehydrated, concentrated, and in other forms [15,34].
Olive (Olea europaea) pomace is also a solid residue that contains peels, pulp, pieces of seeds and oil [41]. The pineapple (Ananas comosus L.) industry generates high amounts of waste, namely, skin, the crown, and the center of the fruit, that are discarded as low-value residues [42]. Banana, a widely consumed fruit, presents the peel as the main bio-residue, and only 12% of the plant is edible. This fruit is part of the Musaceae family and is identified as one of the most important fruits in the world [20].
Sugarcane production was estimated at 1949.3 million tons in 2019, Brazil being the largest producer, followed by India and China. The alcohol and sugar industries are the major users of this product and, consequently, the main producers of bagasse. Although bagasse corresponds to about 30% of the production and main by-product, other residues are generated, such as cane trash, molasses and press mud [36,43,44].
The pear (Pyrus spp.) is a fruit widely consumed worldwide, which had a production of 23 million tones in 2012. Furthermore, about 15–20% by mass are by-products (e.g., leaves and pomace) generated in the manufacture of pear derivatives, such as jams, puree and dried and fresh fruits [37,45].

2.3.2. Vegetable Waste and By-Products

Tomato (Lycopersicon esculentum L.), which is considered the second most important vegetable crop in the world [46], generates peels, seeds, and pulp as the main by-products [24]. The main tomato producers are China, India, the United States of America, Turkey, Egypt and Mexico. In the Asian continent, China loses 35% of its production after harvest, India 40%, and Turkey 20%. In the African continent, in which the major producers are Egypt, Nigeria and Tunisia, tomato production in 2012 was 17.94 million tons and production loss ranged from 20 to 30%. In Latin America, Mexico loses up to 20% of production, and Brazil 10% [13].
Another important food worldwide is potato (Solanum tuberosum L.), considered the most important vegetable crop in the world, and its most important by-product is the peel [46,47]. Chips and fries are the primary products of potato processing [14].
Onion (Allium cepa L.) is a crop of world importance, and its major producers are China, India and the United States. Onion losses in developed countries are found mainly in retail and consumption, varying from 5 to 30%. In developing countries, losses are around 50%, and are mostly from the beginning of the chain to retail [35].
Broccoli and cauliflower (Brassica oleraceae var. italica) produce the leaf and stem as by-products, in which about 37% of cauliflower is wasted along the production chain. An estimate of the production of broccoli and cauliflower showed that 50% of the waste could be used as animal feed, and the other half for bioconversion into new products [13].
Pea (Pisum sativum L.) is a leguminous plant with world-wide importance. In 2018, its production was around 13.5 million tones, with Canada, India, Russia and China being the main producing countries. The high protein content is a valuable feature for the industry and can be produced in wet or dry form. In processing, the pod is one of the main by-products that is usually rejected and burned [38,48].
Beetroot (Beta vulgaris L.) is a root vegetable from the Amaranthaceae family. Its main by-products are leaves, pulp and stems, which correspond to 15–30% of processing. They are typically discarded with no value added, such as with feed, fertilizer, or final disposal with no use whatsoever [49,50].Another vegetable with a global impact is cassava (Manihot esculenta Crantz), the fifth most widely used starch and the third most consumed in tropical areas, with estimated production in 2019 of approximately 303 million tons [51,52]. The main residues generated are leaves, stems, peels, wastewater and starch bagasse. As for producing cassava starch, almost the same value that is produced is generated of bagasse, for example, 1 ton of starch can generate maybe more than 900 kg of bagasse [53,54].
Carrot (Daucus carota L.) had an estimated production of 40 million tons in 2018 and is considered one of the 10 most important vegetables globally. Moreover, it is a high source of β-carotene. Regarding the by-products, they are mostly pomace and peels. In juice manufactures, these residues can represent about 12% by weight of the biomass [39,40].

2.4. Destination of the Generated By-Products/Biowaste

The destination of the generated biowaste and by-products can occur in different ways. The most common and cheaper destinations for dumping are places close to the production site and in sanitary landfills, waste incineration, animal feed and soil fertilization [26,32]. Besides these, other methods employed are composting and anaerobic fermentation [55]. However, the legislation in each region can make it difficult to dispose of waste, given that vegetables can suffer deterioration and generate problems in product quality and safety [18]. If the residue is edible and is in a condition to be eaten, the redistribution of food should be prioritized, followed by its redistribution as animal feed. If it is not edible and cannot be consumed for any other reason, the use of new recovery methods and technologies is important, even to valorize these raw materials [3].
Besides leachate, landfill deposition generates methane (CH2) and carbon dioxide (CO2) due to microbial decomposition, which are harmful to the environment [5,20]. The anaerobic degradation of organic matter corresponds to the emission of 800 million tons of CO2. North America, Europe and Asia are the main emitters of greenhouse gases in the atmosphere from landfills [56]. In Mexico, 44% of urban waste is fruits and vegetables disposed of in landfills and open dumps [57]. If properly disposed, the biogas produced in anaerobic degradation can generate energy and consequently valorize this waste, while also presenting potential to be used as a bio-fertilizer [58].
Regarding animal feeding, not all waste and by-products are eligible for animal feed since it is necessary to analyze the nutritional composition and possible presence of toxic compounds for the animals. Nevertheless, a low amount of water in the residue (less than 40% by mass) makes incineration viable. However, the incineration process releases highly toxic pollutants, while higher water contents favor the use of anaerobic fermentation [5,20,55]. Using landfills and incineration without energy harnessing are treatments that cause great environmental impacts and are not advantageous [3].
The disposal of FV residues and by-products using traditional methods, mentioned above, causes their devaluation. Waste recovery methods, such as the extraction of bioactive compounds and their conversion to generate biofuels and biomaterials, are strategies for a “cleaner” food production that are integrated with environment protection [5].

3. Valorization of By-Products/Biowaste

The “cleaner” food production that is integrated with the environment is based on the principle that losses must be reduced and reused/recycled, with the aim at valorizing these by-products and the waste produced, as well as executing innovative processes and developing products that work collaboratively with the environment, always aiming for quality, safety and efficiency [5,56].
Biorefinery comprises transforming the biomass from different sources into heat, energy and chemical compounds with added value. However, this process still presents high costs from an economic point of view. Variables such as composition, purity, stage of the supply chain, transportation and storage are aspects that must be studied and influence the final value of these products [56].
Economically, the transformation into energy generates less value (60–150 &/ton), together with animal feed (70–200 $/ton), followed by the use of biofuels (200–400 $/ton). The most profitable would be the transformation into bio-chemicals (1000 $/ton); however, the application of processes (extraction, purification, transport and storage) on a large scale are still a challenge for the industry [5].
RBFV are natural sources of carbohydrates, bioactive compounds, minerals and dietary fibers [24,32]. The interest in the valorization of these RBFV is increasing exponentially, for instance, through the use of food additives, functional foods, nutraceuticals, pharmaceuticals and others. Furthermore, there is a tendency to substitute synthetic components for natural ones, as they present less or no toxicity and, consequently, the development of a sustainable circular economy with less environmental impacts [21,23].
As these co-products and bio-residues are considered a waste for the food industry, they have a low economic value. This characteristic, added to the fact that many of these wastes have high biological activity and can be used to obtain bioactive compounds, make them an interesting alternative for several applications [59].
In the United States, in 2002, a US patent application 2002/0187239 proposed using nutritional constituents derived from by-products generated in the processing of coffee (coffee husk and undesirable parts); macadamia (internal and external husk); mango (peel and seed); yam (peel and seed); and papaya (peel and seed), which shows the opportunity to use secondary processes for the extraction of bioactive compounds. The extract from passion fruit peels, which has showed antioxidant and anti-inflammatory activity, besides other beneficial health effects, is another example of a patented by-product [32].
According to Ayala-Zavala et al. (2018), an increase in the amount of flavonoids, phenolic content, and consequently the antioxidant capacity in orange slices was verified with the addition of orange seed extract [3]. There is also the use of a tangerine extract from the leaves and peels of the fruit as a Kraft paper coating, showing improvement against oxidation reactions, improvement in protection against moisture and the potential for application as packaging and coating agents for foods to extend the shelf life [60].
The application of FV by-products in cereal is also used, such as olive, grape and carrot bagasse to enrich the phenolic compounds content in pasta, as well as tomato peel and apple bagasse to enrich dairy products, namely, cheese and yogurt, respectively [8].

4. Food Additives—Their Role in Modern Diets

Over time, human interactions with and preferences for food have changed from the need for survival to more nutritional aspects, such as quality, health effects and food safety. The increased consumer interest in these issues drives the food industry, together with the research community, to develop new methodologies and new foods [21,61].
Eating habits are influenced by several factors, such as demographic, socio-economic, cultural, political and environmental factors, which impact food processing, monitoring and conservation. Easy conservation, low environmental impact and the search for healthier foods are some of the biggest demands of the consumer. For healthy eating, there is a desire not only for foods that are not harmful but also to prevent diseases such as diabetes and heart problems [62].
According to the Codex Alimentarius, a food additive is defined as “any substance not normally consumed as food by itself and not normally used as a typical ingredient of the food, whether it has nutritive value, the intentional addition of which to food for a technological (including organoleptic) purpose in the manufacture, processing, preparation, treatment, packing, packaging, transport or holding of such food results, or may be reasonably expected to result (directly or indirectly), in it or its by-products becoming a component of or otherwise affecting the characteristics of such foods” [63].
Food additives are used for their diverse functions, including reducing food perishability and microbial degradation, giving color or flavor to foods, and their acidity, among others, ensuring their safety and improved characteristics, besides avoiding waste, and ensuring greater food variability for the population [64].
There are certain variables that influence the consumer’s perception of additives, which include cultural milestones about additives, published studies on related risks and public opinion in the media and social networks. The public uses what they know and their own experiences to relate to new market trends, since they have little accessibility to information. Additives, especially, are strongly influenced if there is a negative consumer perspective, which can totally change their acceptability [65].
The “E numbers”, codifications made for additives, when implemented in the 60s, were seen in the beginning from the consumer perspective as an advantage if it was present on the label, since it ensured that the food was safe for consumption. Currently, the situation is the opposite since the encoding represents something unknown [66].
Among the trends for the food industry, there is the use of the “clean label”, for which there is no concrete definition, but it can be described as a label that contains a short list of ingredients, excluding names that look like chemicals of the “E numbers” [67]. Although the public prefers foods that do not contain additives, if this is not possible, the consumer will choose foods containing natural additives rather than synthetic ones [68].
Another factor that is related to the insecurity of the consumption of synthetic additives is the research identifying these as hazardous compounds to health, associating them with their carcinogenic and mutagenic potential and allergenic properties. In addition, they are also seen as guilty due to the increased use of chemicals in the world and as responsible for altering the natural composition of foods [65].
Among the prohibited synthetic additives, there is the azodicarbonamide, banned in Australia and Europe, used as a bleaching agent in flours and presenting allergic properties. Besides that, when heated, it generates traces of semicabazide (SEM), on which studies were carried out pointing it out as genotoxic and in certain cases, as causing tumors [69]. Potassium bromate is also used in the bakery industry, generating greater elasticity for the dough and contributing to the growth of bread. However, this food additive was banned because studies initially showed nephrotoxic activity, besides being later able to generate neuropathological disorders and carcinoma in a renal cell of rats [70]. Butylated hydroxy anisole (BHA) and butylated hydroxytoluene (BHT) have been used for many years for their antioxidant and preservative capacity, besides maintaining the freshness of the food; however, it has been banned in several countries for its toxicity, presenting carcinogenicity in animals [71].
For the synthetic additives that are still commercialized, phosphates are widely used in the meat industry due to their preservative capacity, but studies have shown its relationship to kidney diseases and cardiovascular problems such as coronary calcification [72]. Potassium sorbate is used for its preservative property, inhibiting molds in dairy products. Although potassium sorbate is metabolized and oxidized to carbon dioxide and water, if consumed in amounts greater than 25 mg/kg, problems with its cytotoxicity and genotoxicity can occur, producing mutagenic compounds [73]. Sulfites are used to inhibit enzymatic and non-enzymatic browning reactions, besides being an antimicrobial and antioxidant agent, and this additive has a cytotoxic and carcinogenic effect in rats and humans [74]. The above-mentioned additives, as well as others, are seen by consumers as harmful, even though most of the toxicological data have proven their safety in recent years throughout several evaluations. Still, the consumers prefer natural additives or no additives at all on their plates, and thus, the use of by-products that enhance flavor, taste and appearance and may have a technological effect can help reduce the need for the “chemicals”.

Author Contributions

Conceptualization: S.A.H., M.C. and L.B.; writing original draft: J.M.U. and M.C.P.; writing–review and editing: S.A.H., M.C. and L.B.; supervision: S.A.H., M.C. and I.C.F.R.F. All authors have read and agreed to the published version of the manuscript.

Funding

This research received no external funding.

Institutional Review Board Statement

Not applicable.

Acknowledgments

The authors are grateful to the Foundation for Science and Technology (FCT, Portugal) for financial support through national funds FCT/MCTES to the CIMO (UIDB/00690/2020). M.C. Pedrosa thank FCT for her PhD grant (2021.04531.BD), S. Heleno and M. Carocho thank FCT for their individual employment program contract (CEECIND/03040/2017, CEEC-IND/00831/2018) and L. Barros also thanks FCT through the institutional scientific employment program contract for her contract.

Conflicts of Interest

The authors declare no conflict of interests.

References

  1. Augustin, M.A.; Sanguansri, L.; Fox, E.M.; Cobiac, L.; Cole, M.B. Recovery of wasted fruit and vegetables for improving sustainable diets. Trends Food Sci. Technol. 2020, 95, 75–85. [Google Scholar] [CrossRef]
  2. Ran, X.; Zhang, M.; Wang, Y.; Adhikari, B. Novel technologies applied for recovery and value addition of high value compounds from plant byproducts: A Review. Crit. Rev. Food Sci. Nutr. 2019, 3, 450–461. [Google Scholar] [CrossRef]
  3. Ayala-Zavala, J.F.; González-Aguilar, G.; Siddiqui, M.W. Plants Food By-Products: Industrial Relevance for Food Additives and Nutraceuticals. In Postharvest Biology and Technology; Apple Academic Press: New York, NY, USA, 2018; p. 382. [Google Scholar]
  4. Food and Agriculture Organization of the United Nations. The State of Food and Agriculture. Moving forward on Food Loss and Waste Reduction. 2019. Available online: https://www.fao.org/3/ca6030en/ca6030en.pdf (accessed on 15 July 2020).
  5. Esparza, I.; Jim, N.; Bimbela, F.; Ancín-Azpilicueta, C.; Gandía, L.M. Fruit and vegetable waste management: Conventional and emerging approaches. J. Environ. Manag. 2020, 265, 110510. [Google Scholar] [CrossRef] [PubMed]
  6. European Commission. An EU Action Plan for the Circular Economy. Available online: https://eur-lex.europa.eu/resource.html?uri=cellar:8a8ef5e8-99a0-11e5-b3b7-01aa75ed71a1.0012.02/DOC_1&format=PDF (accessed on 13 July 2020).
  7. Laufenberg, G.; Kunz, B.; Nystroem, M. Transformation of vegetable waste into value added products: (A) the upgrading concept; (B) practical implementations. Bioresour. Technol. 2003, 87, 167–198. [Google Scholar] [CrossRef]
  8. Dilucia, F.; Lacivita, V.; Conte, A.; Nobile, M.A.D. Sustainable Use of Fruit and Vegetable By-Products to Enhance Food Packaging Performance. Foods 2020, 9, 857. [Google Scholar] [CrossRef]
  9. European Food Safety Authority. Directive 2008/98/EC of the European Parliament and of the Council. Available online: https://eur-lex.europa.eu/legal-content/EN/TXT/PDF/?uri=CELEX:32008L0098andfrom=EN (accessed on 15 July 2020).
  10. Bellemare, M.F.; Çakir, M.; Peterson, H.H.; Novak, L.; Rudi, J. On the Measurement of Food Waste. Am. J. Agric. Econ. 2017, 99, 1148–1158. [Google Scholar] [CrossRef]
  11. Delgado, L.; Schuster, M.; Torero, M. The Reality of Food Losses: A New Measurement Methodology. Int. Food Policy Res. Inst. 2017, 01686, 40. [Google Scholar]
  12. Ostergren, K.; Gustavsson, J.; Bos-Brouwers, H.; Timmermans, T.; Hansen, J.; Moller, H.; Anderson, G.; O’Connor, C.; Soethoudt, H.; Quested, T.; et al. FUSIONS Definitional Framework for Food Waste—Full Report. Available online: https://www.eu-fusions.org/phocadownload/Publications/FUSIONS%20Definitional%20Framework%20for%20Food%20Waste%202014.pdf (accessed on 15 July 2020).
  13. Espinosa-Alonso, L.G.; Valdez-Morales, M.; Aparicio-Fernandez, X.; Medina-Godoy, S.; Guevara-Lara, F. Chapter 8—Vegetables By-Products. In Food Wastes and By-Products; Campos-Vega, R., Oohmah, B.D., Vergara-Castañeda, H.A., Eds.; Wiley Blackwell: Hoboken, NJ, USA, 2020; pp. 223–266. [Google Scholar]
  14. Galanakis, C.M. Recovery of high components from food wastes: Conventional, emerging technologies and commercialized applications. Trends Food Sci. Technol. 2012, 26, 68–87. [Google Scholar] [CrossRef]
  15. Schieber, A. Side Streams of Plant Food Processing as a Source of Valuable Compounds: Selected Examples. Annu. Rev. Sci. Technol. 2017, 8, 97–112. [Google Scholar] [CrossRef]
  16. Carter, P.; Gray, L.J.; Troughton, J.; Khunti, K.; Davies, M.J. Fruit and vegetable intake and incidence of type 2 diabetes mellitus: Systematic review and meta-analysis. BMJ 2010, 341, c4229. [Google Scholar] [CrossRef] [Green Version]
  17. Genkinger, J.M.; Plantz, E.A.; Hoffman, S.C.; Comstock, G.W.; Helzlsouer, K.J. Fruit, Vegetable, and Antioxidant Intake and All-Cause, Cancer, and Cardiovascular Disease Mortality in a Community-dwelling Population in Washington County, Maryland. Am. J. Epidemiol. 2004, 160, 1223–1233. [Google Scholar] [CrossRef] [PubMed]
  18. Djilas, S.; Jasna, C.; Cetkovic, G. By-products of fruits processing as a source of phytochemicals. Chem. Ind. Chem. Eng. Q. 2009, 15, 191–203. [Google Scholar] [CrossRef]
  19. Chakravarty, I.; Mandavgane, S.A. Valorization of fruit and vegetable waste for biofertilizer and biogas. J. Food Process Eng. 2020, 44, e13512. [Google Scholar] [CrossRef]
  20. Torres-León, C.; Ramírez-Guzman, N.; Londoño-Hernandez, L.; Martinez-Medina, G.A.; Díaz-Herrera, R.; Navarro-Macias, V.; Alvarez-Pérez, O.B.; Picazo, B.; Fillarreal-Vázquez, M.; Ascacio-Valdes, J.; et al. Food Waste and Byproducts: An Opportunity to Minimize Malnutrition and Hunger in Developing Countries. Front. Sustain. Food Syst. 2018, 2, 1–17. [Google Scholar] [CrossRef]
  21. Sharma, P.; Gaur, V.K.; Kim, S.H.; Pandey, A. Microbial strategies for bio-transforming food waste into resources. Bioresour. Technol. 2020, 299, 122580. [Google Scholar] [CrossRef]
  22. Parfitt, J.; Barthel, M.; MacNaughton, S. Food waste within food supply chains: Quantification and potential for change to 2050. Philos. Trans. R. Soc. B Biol. Sci. 2010, 365, 3065–3081. [Google Scholar] [CrossRef] [Green Version]
  23. Ramos, M.; Jiménez, A.; Garrigós, M.C. Il-based advanced techniques for the extraction of value-added compounds from natural sources and food by-products. TrAC Trends Anal. Chem. 2019, 119, 115616. [Google Scholar] [CrossRef]
  24. Kowalska, H.; Czajkowska, K.; Cichowska, J.; Lenart, A. What’s new in biopotential of fruit and vegetable by-products applied in the food processing industry. Trends Food Sci. Technol. 2017, 67, 150–159. [Google Scholar] [CrossRef]
  25. Silva, M.L.; Malcata, X.; Revel, G. Volatile Contents of Grape Marcs in Portugal. J. Food Compos. Anal. 1996, 9, 72–80. [Google Scholar] [CrossRef]
  26. Dyk, J.S.V.; Gama, R.; Morrison, D.; Swart, S.; Pletschke, B.I. Food processing waste: Problems, current management, and prospects for utilisation of the lignocellulose component through enzyme synergistic degradation. Renew. Sustain. Energy Rev. 2013, 26, 521–531. [Google Scholar]
  27. Walia, M.; Rawat, K.; Bhushan, S.; Padwad, Y.S.; Singh, B. Fatty acid composition, physicochemical properties, antioxidant, and cytotoxic activity of apple seed oil obtained from apple pomace. J. Sci. Food Agric. 2014, 94, 929–934. [Google Scholar] [CrossRef] [PubMed]
  28. Mamma, D.; Christakopoulos, P. Biotransformation of Citrus By-Products into Value Added Products. Waste Biomass Valorization 2014, 5, 529–549. [Google Scholar] [CrossRef]
  29. Ledesma-Escobar, C.A.; De Castro, M.D.L. Towards a comprehensive exploitation of citrus. Trends Food Sci. Technol. 2014, 39, 63–75. [Google Scholar] [CrossRef]
  30. Sampaio, S.L.; Petropoulos, S.A.; Alexopoulos, A.; Heleno, S.A.; Santos-Buelga, C.; Barros, L.; Ferreira, I.C.F.R. Potato peels as sources of functional compounds for the food industry: A review. Trends Food Sci. Technol. 2020, 103, 118–129. [Google Scholar] [CrossRef]
  31. Matharu, A.S.; Melo, E.M.; Houghton, J.A. Opportunity for high value-added chemicals from food supply chain wastes. Bioresour. Technol. 2016, 215, 123–130. [Google Scholar] [CrossRef] [PubMed]
  32. Gowe, C. Review on Potential Use of Fruit and Vegetables By-Products as a Valuable Source of Natural Food Additives. Food Sci. Qual. Manag. 2015, 45, 47–61. [Google Scholar]
  33. Oliveira, A.N.; Paula, D.A.; Oliveira, E.B.; Saraiva, S.H.; Stringheta, P.C.; Ramos, A.M. Optimization of pectin extraction from Ubá mango peel through surface response methodology. Int. J. Biol. Macromol. 2018, 113, 395–402. [Google Scholar] [CrossRef]
  34. Asif, A.; Farooq, U.; Akram, K.; Hayat, Z.; Sha, A.; Sarfraz, F.; Asim, M.; Sidhu, I.; Rehman, H. Therapeutic potentials of bioactive compounds from mango fruit wastes. Trends Food Sci. Technol. 2016, 53, 102–112. [Google Scholar] [CrossRef]
  35. Petropoulos, S.A.; Ntatsi, G.; Ferreira, I.C.F.R. Long-term storage of onion and the factors that affect its quality: A critical review. Food Rev. Int. 2017, 33, 62–83. [Google Scholar] [CrossRef]
  36. Mandal, A.; Chakrabarty, D. Isolation of nanocellulose from waste sugarcane bagasse (SCB) and its characterization. Carbohydr. Polym. 2011, 86, 1291–1299. [Google Scholar] [CrossRef]
  37. Chen, Y.W.; Hasanulbasori, M.A.; Chiat, P.F.; Lee, H.V. Pyrus pyrifolia fruit peel as sustainable source for spherical and porous network based nanocellulose synthesis via one-pot hydrolysis system. Int. J. Biol. Macromol. 2019, 123, 1305–1319. [Google Scholar] [CrossRef] [PubMed]
  38. Cui, W.; Ma, Z.; Li, X.; Hu, X. Structural rearrangement of native and processed pea starches following simulated digestion in vitro and fermentation characteristics of their resistant starch residues using human fecal inoculum. Int. J. Biol. Macromol. 2021, 172, 490–502. [Google Scholar] [CrossRef] [PubMed]
  39. Jayesree, N.; Hang, P.K.; Priyangaa, A.; Krishnamurthy, N.P.; Ramanan, R.N.; Turki, M.S.A.; Charis, M.G.; Ooi, C.W. Valorisation of carrot peel waste by water-induced hydrocolloidal complexation for extraction of carotene and pectin. Chemosphere 2021, 272, 129919. [Google Scholar] [CrossRef]
  40. Papoutsis, K.; Edelenbos, M. Postharvest environmentally and human-friendly pre-treatments to minimize carrot waste in the supply chain caused by physiological disorders and fungi. Trends Food Sci. Technol. 2021, 112, 88–98. [Google Scholar] [CrossRef]
  41. Mirabella, N.; Castellani, V.; Sala, S. Current options for the valorization of food manufacturing waste: A review. J. Clean. Prod. 2014, 65, 28–41. [Google Scholar] [CrossRef] [Green Version]
  42. Roda, A.; Marco, D.; Faveri, D.; Giacosa, S.; Dordoni, R.; Lambri, M. Effect of pre-treatments on the saccharification of pineapple waste as a potential source for vinegar production. J. Clean. Prod. 2016, 112, 4477–4484. [Google Scholar] [CrossRef]
  43. Meghana, M.; Shastri, Y. Sustainable valorization of sugar industry waste: Status, opportunities, and challenges. Bioresour. Technol. 2020, 303, 12292. [Google Scholar] [CrossRef]
  44. Agarwal, N.K.; Kumar, M.; Ghosh, P.; Kumar, S.S.; Singh, L.; Vijay, V.K.; Kumar, V. Anaerobic digestion of sugarcane bagasse for biogas production and digestate valorization. Chemosphere 2022, 295, 133893. [Google Scholar] [CrossRef]
  45. Kolniak-Ostek, J. Chemical composition and antioxidant capacity of different anatomical parts of pear (Pyrus communis L.). Food Chem. 2016, 203, 491–497. [Google Scholar] [CrossRef]
  46. Kalogeropoulos, N.; Chiou, A.; Pyriochou, V.; Peristeraki, A.; Karathanos, V.T. Bioactive phytochemicals in industrial tomatoes and their processing byproducts. LWT–Food Sci. Technol. 2012, 49, 213–216. [Google Scholar] [CrossRef]
  47. Schieber, A.; Stintzing, F.C.; Carle, R. By-products of plant food processing as a source of functional compounds—Recent developments. Trends Food Sci. Technol. 2001, 12, 401–413. [Google Scholar] [CrossRef]
  48. Li, H.; Shi, H.; He, Y.; Fei, X.; Peng, L. Preparation and characterization of carboxymethyl cellulose-based composite films reinforced by cellulose nanocrystals derived from pea hull waste for food packaging applications. Int. J. Biol. Macromol. 2020, 164, 4104–4112. [Google Scholar] [CrossRef] [PubMed]
  49. Lasta, H.F.B.; Lentz, L.; Rodrigues, L.G.G.; Mezzomo, N.; Vitali, L.; Ferreira, S.R.S. Pressurized liquid extraction applied for the recovery of phenolic compounds from beetroot waste. Biocatal. Agric. Biotechnol. 2019, 21, 101353. [Google Scholar] [CrossRef]
  50. Vulić, J.J.; Ćebović, T.N.; Čanadanović-Bruneta, J.M.; Ćetković, G.S.; Čanadanović, V.M.; Djilas, S.M.; Šaponjac, V.T.T. In vivo and in vitro antioxidant effects of beetroot pomace extracts. J. Funct. Foods 2014, 6, 168–175. [Google Scholar] [CrossRef]
  51. Florencia, V.; Lopez, O.V.; García, M.A. Exploitation of by-products from cassava and ahipa starch extraction as filler of thermoplastic corn starch. Compos. Part B 2020, 182, 107653. [Google Scholar] [CrossRef]
  52. Padi, R.K.; Chimphangoa, A.; Roskilly, A.P. Economic and environmental analysis of waste-based bioenergy integration into industrial cassava starch processes in Africa. Sustain. Prod. Consum. 2022, 31, 67–81. [Google Scholar] [CrossRef]
  53. Souza, C.B.; Jonathan, M.; Saad, S.M.I.; Schols, H.A.; Venema, K. Characterization and in vitro digestibility of by-products from Brazilian food industry Cassava bagasse, orange bagasse and passion fruit peel. Bioact. Carbohydr. Diet. Fibre 2018, 16, 90–99. [Google Scholar] [CrossRef]
  54. Oghenejoboh, K.M.; Orugba, H.O.; Oghenejoboh, U.M.; Agarry, S.E. Value added cassava waste management and environmental sustainability in Nigeria: A review. Environ. Chall. 2021, 4, 100127. [Google Scholar] [CrossRef]
  55. Russ, W.; Meyer-Pittroff, R. Utilizing Waste Products from the Food Production and Processing Industries Utilizing Waste Products from the Food Production and Processing Industries. Crit. Rev. Food Sci. Nutr. 2010, 44, 57–62. [Google Scholar] [CrossRef]
  56. Jiménez-Moreno, N.; Esparza, I.; Bimbela, F.; Gandía, L.M.; Ancín-Azpilicueta, C. Valorization of selected fruit and vegetable wastes as bioactive compounds: Opportunities and challenges. Crit. Rev. Environ. Sci. Technol. 2020, 50, 2061–2108. [Google Scholar] [CrossRef]
  57. Rodríguez-Valderrama, S.; Escamilla-Alvarado, C.; Rivas-García, P.; Magnin, J.P.; Alcalá-Rodríguez, M.; García-Reyes, R.B. Biorefinery concept comprising acid hydrolysis, dark fermentation, and anaerobic digestion for co-processing of fruit and vegetable wastes and corn stover. Environ. Sci. Pollut. Res. 2020, 27, 28585–28596. [Google Scholar] [CrossRef] [PubMed]
  58. Yazgin, O.; Keskin-Gundogdu, T. Production of Biogas and Astaxanthin from Fruit and Vegetable Wastes Using an Integrated System. Int. J. Second. Metab. 2020, 7, 35–46. [Google Scholar] [CrossRef]
  59. Andrade, M.A.; Lima, V.; Silva, A.S.; Vilarinho, F.; Castilho, M.C.; Khwaldia, K.; Ramos, F. Pomegranate and grape by-products and their active compounds: Are they a valuable source for food applications? Trends Food Sci. Technol. 2019, 86, 68–84. [Google Scholar] [CrossRef]
  60. Kasaai, M.R.; Moosavi, A. Treatment of Kraft paper with citrus wastes for food packaging applications: Water and oxygen barrier properties improvement. Food Packag. Shelf Life 2017, 12, 59–65. [Google Scholar] [CrossRef]
  61. Martins, N.; Ferreira, I.C.F.R. Wastes and by-products: Upcoming sources of carotenoids for biotechnological purposes and health-related applications. Trends Food Sci. Technol. 2017, 62, 33–48. [Google Scholar] [CrossRef]
  62. Señorans, F.J.; Ibáñez, E.; Cifuentes, A. New Trends in Food Processing. Crit. Rev. Food Sci. Nutr. 2003, 43, 507–526. [Google Scholar] [CrossRef]
  63. Food and Agriculture Organization of the United Nations; World Health Organization. Codex Alimentarius. General Standard for Food Additives. Codex Stan 192-1995. Available online: https://www.fao.org/fao-who-codexalimentarius/sh-proxy/en/?lnk=1&url=https%253A%252F%252Fworkspace.fao.org%252Fsites%252Fcodex%252FStandards%252FCXS%2B192-1995%252FCXS_192e.pdf (accessed on 30 March 2020).
  64. Bearth, A.; Cousin, M.; Siegrist, M. The consumer’s perception of artificial food additives: Influences on acceptance, risk, and benefit perceptions. Food Qual. Prefer. 2014, 38, 14–23. [Google Scholar] [CrossRef]
  65. Degreef, F. “What’s the deal with these strange substances in our food?” The representation of food additives by Belgian consumer organizations, 1960–1995. Food Foodways 2019, 27, 144–163. [Google Scholar] [CrossRef]
  66. Saltmarsh, M. Recent trends in the use of food additives in the United Kingdom. J. Sci. Food Agric. 2015, 95, 649–652. [Google Scholar] [CrossRef] [PubMed]
  67. Asioli, D.; Aschemann-Witzel, J.; Caputo, C.; Vecchio, R.; Annunziata, A.; Naes, T.; Varela, P. Making sense of the “clean label” trends: A review of consumer food choice behavior and discussion of industry implications. Food Res. Int. 2017, 99, 58–71. [Google Scholar] [CrossRef]
  68. Carocho, M.; Barreiro, M.F.; Morales, P.; Ferreira, I.C.F.R. Adding Molecules to Food, Pros and Cons: A Review on Synthetic and Natural Food Additives. Compr. Rev. Food Sci. Food Saf. 2014, 13, 377–399. [Google Scholar] [CrossRef] [PubMed]
  69. Ye, J.; Wang, X.; Sang, Y.; Liu, Q. Assessment of the Determination of Azodicarbonamide and Its Decomposition Product Semicarbazide: Investigation of Variation in Flour and Flour Products. J. Agric. Food Chem. 2011, 59, 9313–9318. [Google Scholar] [CrossRef] [PubMed]
  70. Ahmad, M.K.; Naqshbandi, A.; Fareed, M.; Mahmood, R. Oral administration of a nephrotoxic dose of potassium bromate, a food additive, alters renal redox and metabolic status and inhibits brush border membrane enzymes in rats. Food Chem. 2012, 134, 980–985. [Google Scholar] [CrossRef] [PubMed]
  71. Ito, N.; Fukushima, S.; Tsuda, H. Carcinogenity and modification of the carcinogenic response by BHA, BHT and other antioxidants. CRC Crit. Rev. Toxicol. 2008, 15, 109–150. [Google Scholar] [CrossRef] [PubMed]
  72. Ritz, E.; Hahn, K.; Ketteler, M.; Kuhlmann, M.K.; Mann, J. Phosphate Additives in Food—A Health Risk. Dtsch. Arztebl. Int. 2012, 109, 49–55. [Google Scholar]
  73. Dehghan, P.; Mohammadi, A.; Mohammadzadeh-Aghdash, H.; Dolatabadi, J.E.N. Pharmacokinetic and toxicological aspects of potassium sorbate food additive and its constituents. Trends Food Sci. Technol. 2018, 80, 123–130. [Google Scholar] [CrossRef]
  74. Suh, H.; Cho, Y.; Chung, M.; Kim, B.H. Preliminary data on sulphite intake from the Korean diet. J. Food Compos. Anal. 2007, 20, 212–219. [Google Scholar] [CrossRef]
  75. U.S. Food and Drug Administration. Use of the Term Natural on Food Labeling. Available online: https://www.fda.gov/food/food-labeling-nutrition/use-term-natural-food-labeling (accessed on 2 April 2020).
  76. Kumar, Y.; Yadav, D.N.; Ahmad, T.; Narsaiah, K. Recent Trends in the Use of Natural Antioxidants for Meat and Meat Products. Compr. Rev. Food Sci. Food Saf. 2015, 14, 796–812. [Google Scholar] [CrossRef] [Green Version]
  77. Baines, D. Defining the term “natural” in the context of food products. In Natural Food Additives, Ingredients, and Flavourings; Baines, D., Seal, R., Eds.; Woodhead Publishing: Cambridge, UK, 2012; pp. 1–22. [Google Scholar]
  78. Gokoglu, N. Novel natural food preservatives and applications in seafood preservation: A review. J. Sci. Food Agric. 2019, 99, 2068–2077. [Google Scholar] [CrossRef]
  79. Dávila-Aviña, J.E.; Zoellner, C.; Sólis-Soto; Rojas-Verde, G.; Garcia-Amezquita, L.E. Chapter 2: Economic and Environmental Benefits of Utilizing Plant Food By-Products. In Plant Food By-Products: Industrial Relevance for Food Additives and Nutraceutic; Ayala-Zavala, J.F., González-Aguilar, G., Siddiqui, M.W., Eds.; Apple Academic Press: Oakville, Australia, 2018; pp. 25–54. [Google Scholar]
  80. Faustino, M.; Veiga, M.; Sousa, P.; Costa, E.M.; Silva, S.; Pintado, M. Agro-Food Byproducts as a New Source of Natural Food Additives. Molecules 2019, 24, 1056. [Google Scholar] [CrossRef] [Green Version]
  81. Chantaro, P.; Devahastin, S.; Chiewchan, N. Production of antioxidant high dietary fiber powder from carrot peels. LWT-Food Sci. Technol. 2008, 41, 1987–1994. [Google Scholar] [CrossRef]
  82. Niu, B.; Shao, P.; Sun, P. Ultrasound-assisted emulsion electrosprayed particles for the stabilization of β-carotene and its nutritional supplement potential. Food Hydrocoll. 2020, 102, 105634. [Google Scholar] [CrossRef]
  83. Hernández-Carranza, P.; Ávila-Sosa, R.; Guerrero-Beltrán, J.A.; Navarro-Cruz, A.R.; Corona-Jiménez, E.; Ochoa-Velasco, C.E. Optimization of antioxidant compounds extraction from fruit by-products: Apple pomace, orange, and banana peel. J. Food Process. Preserv. 2016, 40, 103–115. [Google Scholar] [CrossRef]
  84. Osuna, M.B.; Romero, C.A.; Romero, A.M.; Judis, M.A.; Bertola, N.C. Proximal composition, sensorial properties and effect of ascorbic acid and α-tocopherol on oxidative stability of bread made with whole flours and vegetable oils. LWT-Food Sci. Technol. 2018, 98, 54–61. [Google Scholar] [CrossRef] [Green Version]
  85. Górnás, P. Unique variability of tocopherol composition in various seed oils recovered from by-products of apple industry: Rapid and simple determination of all four homologues (α, β, γ and δ) by RP-HPLC/FLD. Food Chem. 2015, 172, 129–134. [Google Scholar] [CrossRef]
  86. Wang, Y.; Li, F.; Zhuang, H.; Chen, X.; Li, L.; Qiao, W.; Zhang, J. Effects of plant polyphenols and α-tocopherol on lipid oxidation, residual nitrites, biogenic amines, and N-nitrosamines formation during ripening and storage of dry-cured bacon. LWT-Food Sci. Technol. 2015, 60, 199–206. [Google Scholar] [CrossRef]
  87. Okunowo, W.O.; Oyedeji, O.; Afolabi, L.O.; Matanmi, E. Essential Oil of Grape Fruit (Citrus paradisi) Peels and Its Antimicrobial Activities. Am. J. Plant Sci. 2013, 4, 1–9. [Google Scholar] [CrossRef] [Green Version]
  88. Dussault, D.; Vu, K.D.; Lacroix, M. In vitro evaluation of antimicrobial activities of various commercial essential oils, oleoresin and pure compounds against food pathogens and application in ham. Meat Sci. 2014, 96, 514–520. [Google Scholar] [CrossRef] [Green Version]
  89. Mandalari, G.; Bennett, R.N.; Bisignano, G.; Trombetta, D.; Saija, A.; Faulds, C.B.; Gasson, M.J.; Narbad, A. Antimicrobial activity of flavonoids extracted from bergamot (Citrus bergamia Risso) peel, a byproduct of the essential oil industry. J. Appl. Microbiol. 2007, 103, 2056–2064. [Google Scholar] [CrossRef]
  90. Xu, F.; Wang, C.; Wang, H.; Xiong, Q.; Wei, Y.; Shao, X. Antimicrobial action of flavonoids from Sedum aizoon L. against lactic acid bacteria in vitro and in refrigerated fresh pork meat. J. Func. Foods 2018, 40, 744–750. [Google Scholar] [CrossRef]
  91. Rodríguez-Carpena, J.G.; Morcuende, D.; Andrade, M.J.; Kylli, P.; Estévez, M. Avocado (Persea americana Mill.) Phenolics, In Vitro Antioxidant and Antimicrobial Activities, and Inhibition of Lipid and Protein Oxidation in Porcine Patties. J. Agric. Food Chem. 2011, 59, 5625–5635. [Google Scholar] [CrossRef] [PubMed]
  92. Rossi, R.C.; Rosa, S.R.; Weimer, P.; Moura, J.G.L.; Oliveira, V.R.; Castilhos, J. Assessment of compounds and cytotoxicity of Citrus deliciosa Tenore essential oils: From an underexploited by-product to a rich source of high-value bioactive compounds. Food Biosci. 2020, 38, 100779. [Google Scholar] [CrossRef]
  93. Yao, Y.; Ding, D.; Shao, H.; Peng, Q.; Huang, Y. Antibacterial Activity and Physical Properties of Fish Gelatin-Chitosan Edible Films Supplemented with D-Limonene. Int. J. Polym. Sci. 2017, 2017, 1837171. [Google Scholar] [CrossRef] [Green Version]
  94. Knoblich, M.; Anderson, B.; Latshaw, D. Analyses of tomato peel and seed byproducts and their use as a source of carotenoids. J. Sci. Food Agric. 2005, 85, 1166–1170. [Google Scholar] [CrossRef]
  95. Oliveira, D.M.; Minuceli, F.S.; Ribeiro, M.A.S.; Marques, D.R.; Testa, G.; Monteiro, A.R.G.; Moreira, J.N.; Clemente, E. Production Lycopene Dye São Caetano Melon (Momordica charantia L.) for Food Application. Chem. Eng. Trans. 2017, 57, 1951–1956. [Google Scholar]
  96. Crizel, T.M.; Hermes, V.S.; Rios, A.O.; Flôres, S.H. Evaluation of bioactive compounds, chemical and technological properties of fruits byproducts powder. J. Food Sci. Technol. 2016, 53, 4067–4075. [Google Scholar] [CrossRef] [Green Version]
  97. Backes, E.; Leichweis, M.G.; Pereira, C.; Carocho, M.; Barreira, J.C.M.; Genena, A.K.; Baraldi, I.J.; Barreiro, M.F.; Barros, L.; Ferreira, I.C.F.R. Ficus carica L. and Prunus spinosa L. extracts as new anthocyanin-based food colorants: A thorough study in confectionery products. Food Chem. 2020, 333, 127457. [Google Scholar] [CrossRef]
  98. Derrien, M.; Badr, A.; Gosselin, A.; Desjardins, Y.; Angers, P. Optimization of a green process for the extraction of lutein and chlorophyll from spinach by-products using response surface methodology (RSM). LWT-Food Sci. Technol. 2017, 79, 170–177. [Google Scholar] [CrossRef]
  99. Durmaz, Y.; Kilicli, M.; Toker, O.S.; Konar, N.; Palabiyik, I.; Tamturk, F. Using spray-dried microalgae in ice cream formulation as a natural colorant: Effect on physicochemical and functional properties. Algal Res. 2020, 47, 101811. [Google Scholar] [CrossRef]
  100. Rehman, S.; Nadeem, M.; Ahmad, F.; Mushtaq, Z. Biotechnological Production of Xylitol from Banana Peel and Its Impact on Physicochemical Properties of Rusks. J. Agric. Sci. Technol. 2013, 15, 747–756. [Google Scholar]
  101. Esfahlan, A.J.; Jamei, R.; Esfahlan, R.J. The importance of almond (Prunus amygdalus L.) and its by-products. Food Chem. 2010, 120, 349–360. [Google Scholar] [CrossRef]
  102. Santana, R.V.; Santos, D.C.; Santana, A.C.A.; Filho, J.G.O.; Almeida, A.B.; Lima, T.M.; Silva, F.G.; Egea, M.B. Quality parameters and sensorial profile of clarified “Cerrado” cashew juice supplemented with Saccharomyces boulardii and different sweeteners. LWT-Food Sci. Technol. 2020, 128, 109319. [Google Scholar] [CrossRef]
  103. Harini, K.; Ramya, K.; Sukumar, M. Extraction of nano celulose fibers from the banana peel and bract for production of acetyl and lauroyl cellulose. Carbohydr. Polym. 2018, 201, 329–339. [Google Scholar] [CrossRef] [PubMed]
  104. Zhao, Y.; Hou, Q.; Zhuang, X.; Wang, Y.; Zhou, G.; Zhang, W. Effect of regenerated cellulose fiber on the physicochemical properties and sensory characteristics of fat-reduced emulsified sausage. LWT-Food Sci. Technol. 2018, 97, 157–163. [Google Scholar] [CrossRef]
  105. Seixas, F.L.; Fukuda, D.L.; Turbiani, F.R.B.; Garcia, P.S.; Petkowics, C.L.O.; Jagadevan, S.; Gimenes, M.L. Extraction of pectin from passion fruit peel (Passiflora edulis f. flavicarpa) by microwave-induced heating. Food Hydrocoll. 2014, 38, 186–192. [Google Scholar] [CrossRef]
  106. Ismail, H.A.; Hameed, A.M.; Refaey, M.M.; Sayqal, A.; Aly, A.A. Rheological, physio-chemical, and organoleptic characteristics of ice cream enriched with Doum syrup and pomegranate peel. Arab. J. Chem. 2020, 13, 7346–7356. [Google Scholar] [CrossRef]
  107. Roldán, E.; Sánchez-Moreno, C.; Ancos, B.; Cano, M.P. Characterization of onion (Allium cepa L.) by-products as food ingredients with antioxidant and antibrowning properties. Food Chem. 2008, 108, 907–916. [Google Scholar] [CrossRef]
  108. Thorat, I.D.; Jagtap, D.D.; Mohapatra, D.; Joshi, D.C.; Sutar, R.F.; Kapdi, S.S. Antioxidants, their properties, uses in food products and their legal implications. Int. J. Food Stud. 2013, 2, 81–104. [Google Scholar] [CrossRef]
  109. Imran, M.; Ghorat, F.; Ul-Haq, I.; Ur-Rehman, H.; Aslam, F.; Heydari, M.; Shariati, M.A.; Okuskhanova, E.; Yessimbekov, Z.; Thiruvengadam, M.; et al. Lycopene as a Natural Antioxidant Used to Prevent Human Health Disorders. Antioxidants 2020, 9, 706. [Google Scholar] [CrossRef]
  110. Jiang, J.; Xiong, Y.L. Natural antioxidants as food and feed additives to promote health benefits and quality of meat products: A review. Meat Sci. 2016, 120, 107–117. [Google Scholar] [CrossRef] [Green Version]
  111. Maestri, D.M.; Nepote, V.; Lamarque, A.; Zygaglo, J.A. Natural Products as Antioxidants. Available online: https://citeseerx.ist.psu.edu/viewdoc/download?doi=10.1.1.621.3859&rep=rep1&type=pdf (accessed on 10 April 2022).
  112. Zhang, W.; Yu, S.; Zhang, T.; Jiang, B.; Mu, W. Recent advances in D-allulose: Physiological functionalities, applications, and biological production. Trends Food Sci. Technol. 2016, 54, 127–137. [Google Scholar] [CrossRef]
  113. Havelaar, A.H.; Brul, S.; Jong, A.; Jonge, R.; Zwietering, M.H.; Kuile, B.H. Future challenges to microbial food safety. Int. J. Food Microbiol. 2010, 139, 79–94. [Google Scholar] [CrossRef] [PubMed] [Green Version]
  114. Juneja, V.K.; Dweivedi, H.P.; Yan, X. Novel Natural Food Antimicrobials. Annu. Rev. Food Sci. Technol. 2012, 3, 381–403. [Google Scholar] [CrossRef]
  115. Chibane, L.B.; Degraeve, P.; Ferhout, H.; Bouajila, J.; Oulahal, N. Plant antimicrobial polyphenols as potential natural food preservatives. J. Sci. Food Agric. 2018, 99, 1457–1474. [Google Scholar] [CrossRef] [PubMed] [Green Version]
  116. Quinto, E.J.; Caro, I.; Villalobos-Delgado, L.H.; Mateo, J.; De-Mateo-Silleras, B.; Redondo-Del-Rio, R. Food Safety through Natural Antimicrobials. Antibiotics 2019, 8, 208. [Google Scholar] [CrossRef] [Green Version]
  117. Francis, F.J. Quality as Influenced by Color. Food Qual. Prefer. 1995, 6, 149–155. [Google Scholar] [CrossRef]
  118. Rodriguez-Amaya, D.B. Natural food pigments and colorants. Curr. Opin. Food Sci. 2016, 7, 20–26. [Google Scholar] [CrossRef]
  119. Leroux, J.; Langendorff, V.; Schick, G.; Vaishnav, V.; Mazoyer, J. Emulsion stabilizing properties of pectin. Food Hydrocoll. 2003, 17, 455–462. [Google Scholar] [CrossRef]
Publisher’s Note: MDPI stays neutral with regard to jurisdictional claims in published maps and institutional affiliations.

Article Metrics

Citations

Article Access Statistics

Multiple requests from the same IP address are counted as one view.