Next Article in Journal
The Impact of Must Nutrients and Yeast Strain on the Aromatic Quality of Wines for Cognac Distillation
Next Article in Special Issue
Table Olive Wastewater as a Potential Source of Biophenols for Valorization: A Mini Review
Previous Article in Journal
Staphylococcus spp. and Lactobacillus sakei Starters with High Level of Inoculation and an Extended Fermentation Step Improve Safety of Fermented Sausages
Previous Article in Special Issue
Purification and Characterization of Strong Simultaneous Enzyme Production of Protease and α-Amylase from an Extremophile-Bacillus sp. FW2 and Its Possibility in Food Waste Degradation
 
 
Font Type:
Arial Georgia Verdana
Font Size:
Aa Aa Aa
Line Spacing:
Column Width:
Background:
Review

Valorization of Brewers’ Spent Grains: Pretreatments and Fermentation, a Review

1
TIMR (Integrated Transformations of Renewable Matter), Université de Technologie de Compiègne, ESCOM, Centre de Recherche Royallieu, CS 60 319, CEDEX, 60 203 Compiègne, France
2
Laboratoire CTA, UR TVA, Centre d’Analyses et de Recherche, Faculté des Sciences, Université Saint-Joseph, Beyrouth 1104 2020, Lebanon
*
Authors to whom correspondence should be addressed.
Submission received: 23 December 2021 / Revised: 16 January 2022 / Accepted: 21 January 2022 / Published: 25 January 2022
(This article belongs to the Special Issue Valorization of Waste from Agro-Food, Food and Marine Industry)

Abstract

:
Brewers’ spent grains constitute a valuable byproduct of the beer industry. They are characterized by a rich nutritional composition consisting of around 70% lignocellulosic fibrous material, 20% proteins, 10% lipids, in addition to vitamins, minerals, amino acids, and phenolic compounds. These spent grains are produced in large amounts all through the year, are cheap, and lack economically feasible applications. Nowadays, 70% of these spent grains are used as animal feed, 10% are used for biogas production, and the remaining 20% are disposed in landfills. Due to the aforementioned facts, alternative uses of the brewers’ spent grains are highly sought-after. In fact, this nutrient-rich industrial by-product makes it a very good candidate for valorization through biotechnological processing, particularly microbial fermentation. After applying the needed pretreatments, using brewers’ spent grains as a substrate in submerged and solid-state fermentation of different microorganisms leads to the production of various value-added compounds such as organic acids, amino acids, volatile fatty acids, enzymes, vitamins, second-generation biofuels and other products.

1. Introduction

Beer is one of the oldest and most consumed alcoholic drinks worldwide. It is the third most popular beverage after water and tea [1]. The brewing process involves a set of treatment steps of the initial barely grains, including malting, milling, mashing, lautering, boiling, wort cooling, and fermenting. Like other manufacturing processes, industrial beer production predictably produces waste and by-products. After the mashing of barley starch, the insoluble solid fraction of the grains, known as Brewers’ spent grains (BSG), is filtered from the wort, which is the sweet liquor that will be fermented into beer [2]. BSG comprises the seed coat (testa), husk, and the pericarp layers that covered the original barley grains. In fact, BSG account for 85% of the total solid residues generated during the brewing process and 30% of the initial malt weight [3]. In 2018, around 1.94 billion hectoliters (hL) of beer were manufactured worldwide, out of which 406 million hL were produced in the European Union. According to the annual beer statistics report of 2019, Germany is the leading beer producing country, followed by Poland, United Kingdom, and Spain. It is noteworthy that for every 100 L of beer produced, around 20 kg of wet BSG are obtained as by-products [4,5].
This by-product is known to contain considerable amounts of valuable compounds that are unaltered during the brewery process [6]. However, the chemical composition of BSG depends on the type of barley grains, the harvesting time, the brewing technology, and the process parameters used [7]. Despite this variability, BSG mainly consist of lignocellulosic fibrous material and relatively high protein content corresponding to 70% and 20% of dry basis, respectively [8]. The fiber part is composed of around 28.35% hemicellulose, 16.25% cellulose, and 7.27% lignin, all of which provide resistance to the degradation of the BSG [6]. Various monosaccharides, oligosaccharides, and polysaccharides are present in BSG. The most abundant monosaccharides in BSG are glucose, xylose, and arabinose. The most common proteins present are hordeins, glutelins, globulins, and albumins. Moreover, 10% of BSG consist of lipids, of which triglycerides have a higher percentage, followed by free fatty acids [6,9]. BSG also contains amino acids, vitamins, minerals, and phenolic compounds. Particularly, phenylalanine, lysine, tryptophan, histidine, and methionine are the essential amino acids that are present in BSG, whereas alanine, glycine, proline, and serine are the non-essential ones. A wide range of vitamins have been reported in BSG; namely, biotin, choline, pantothenic acid, folic acid, niacin, riboflavin, thiamine, and pyridoxine. In addition, phosphorus, calcium, cobalt, potassium, copper, iron, magnesium, manganese, selenium, sulphur, and sodium are the minerals present in BSG. It is worth mentioning that ferulic acid and p-coumaric acid are the major phenolic compounds present in BSG [10].
Due to its high moisture content, which is around 80%, along with its richness in polysaccharides and proteins, BSG is highly prone to microbial contamination, and hence has a very short lifespan (between 7 and 10 days) [6]. These characteristics have various impacts on different levels. At the environmental level, BSG present a high risk if disposed without a required treatment. In fact, in a landfill, every ton of BSG releases around 514 kg CO2 greenhouse gases equivalent. Therefore, BSG lead to high waste generation and bad environmental effects [11]. At the level of spent grains, the aforementioned characteristics render the transportation of BSG expensive, their storage difficult, and limit their stability and exploitation [12]. Currently, 70% of the BSG are used in animal feed such as cattle, poultry, and chicken, while 10% are used for biogas production, and the remaining 20% are disposed in landfills [11]. Due to the interesting nutritional constituents of BSG, recent studies are suggesting incorporating it in some food products and hence in the human diet. A limited amount of BSG—around 5 to 10%-has been added to various food products, including bread, cakes, cookies, and egg pasta, in order to avoid affecting the final product properties such as the taste, color, and texture [3].
To overcome BSG aggregation-related issues, and to minimize the waste and pollution arising from the brewing industry, an alternative valorization route through biotechnological processing is highly sought-after. In addition to the nutritional value of the spent grains, their availability throughout the year at a very low cost—equivalent to 40.23 USD per ton of BSG—makes them a favorable raw material for various potential applications [13,14]. Particularly, microbial fermentation is a promising biovalorization method for this high-volume industrial byproduct [2]. For instance, it was reported that this cheap feedstock was used to naturally produce the valuable aromatic compound 2-phenylethanol through microbial fermentation mainly using yeasts, competing with the conventional, environmentally unfriendly, chemical synthesis routes [15]. A simplified scheme of the brewing process, BSG constituents, and their uses, is illustrated in Figure 1.
In this review, the biotechnological valorization of the BSG will be discussed. The various pretreatment methods applied for BSG to disrupt the natural resistance of the lignocellulose and to prepare the substrate for microbial activity—making it more accessible—were introduced. Then, submerged fermentation and solid-state fermentation methods were defined and discussed. The multiple value-added compounds produced via both types of fermentation were also described.

2. Pretreatment Methods of Brewers’ Spent Grains

As previously mentioned, BSG composition allows the formation of value-added products. However, due to the complicated natural plant cell wall composition, including cellulose, hemicellulose, and lignin, which interlock together to form a recalcitrant structure, the utilization of lignocellulosic materials in biorefinery processes require a pretreatment that disrupt their crystalline structure and allow their fractionation [16]. Effectively disrupting the rigid structure of lignocellulose releases and exposes the locked polysaccharides, after which they can be saccharified more easily by the action of the cellulolytic enzymes, hence maximizing the release of sugars upon enzymatic hydrolysis [17]. Therefore, breaking down the spent grains into their constituents will yield a number of value-added components including carbohydrates and proteins, which constitute a suitable medium or substrate for the fermentative production of various bioactive compounds [18]. Consequently, pretreatments will prepare the lignocellulosic substrate for microbial activity, making it more accessible to the microbial consortium [19]. These pretreatments will break cellulose into glucose and hemicellulose into mainly xylose and arabinose, which are the most abundant monosaccharides present in the hydrolyzed spent grains [20]. Prior to enzymatic hydrolysis, a pretreatment step is applied to the BSG. Pretreatments can be classified into chemical (e.g., alkaline, acid, organosolv pretreatments, and ionic liquids), physical (e.g., mechanical, hydrothermal, ultrasonic, and microwave radiation pretreatments), biological (using fungi or bacteria), and hybrid pretreatment methods such as physicochemical pretreatments [21]. A summary of the various types of pretreatments is presented in Figure 2.
Chemical pretreatments’ efficacy and the mode of action vary with the pH. One of the most commonly used pretreatments is the use of acidic solutions, such as sulfuric acid, using either low acid concentration, less than 5%, a high temperature, between 120 and 210 °C, and a pressure less than 10 atm, or a concentrated acid, less than 30%, a temperature less than 100 °C, and at atmospheric pressure [9]. Acidic pretreatments are based on the sensitivity of the glycosidic bonds between hemicellulose and cellulose to acid [22]; hence, they aim to enhance the efficiency of recovering cellulose and xylose [23]. On the other hand, other chemical pretreatments use alkaline reagents, such as sodium, calcium, and potassium hydroxides. The latter solutions work by removing lignin, and, to a lesser extent, hemicellulose from the lignocellulosic material of BSG, which facilitates the access of the enzymes to it. In fact, a saponification reaction occurs during this type of pretreatment, leading to the cleavage of intermolecular ester linkages between hemicelluloses and lignin. Alkaline reagents also act through a swelling mechanism, which increases the porosity and internal surface of the biomass [24]. The conditions of alkaline pretreatments are usually less severe compared to other types of pretreatments. They can be done at room temperature but to a longer pretreatment time compared to higher temperatures [25]. A study done on BSG reported that the enzymatic hydrolysis of acid and alkali pretreated BSG has doubled the hydrolysis compared to the untreated sample. Yet the nature of the solubilized sugars was different. The amount of reducing sugars (monosaccharides) obtained from the enzymatic hydrolysis of H2SO4 pretreated BSG was much higher (66% for 0.5 N H2SO4) than the one obtained from the hydrolysis of the NaOH pretreated sample (35% for 0.5 N NaOH) [26]. Alkaline pretreatments have various advantages including usage of cheap chemicals, mild reaction conditions, effective removal of lignin, and low inhibitor formation, and some disadvantages—namely, the long processing time, difficulties in neutralization of the mixture post-treatment, and alteration in lignin structure [27]. On the other hand, acidic pretreatments produce high glucose yield and solubilize hemicellulose, despite the high acid cost. Additionally, this pretreatment method leads to the formation of toxic byproducts such as hydroxymethylfurfural (HMF), furfural, and acetic acid [25,27]. In the presence of these inhibitors, an extra detoxification step is needed prior to enzymatic hydrolysis and fermentation [28]. Furthermore, alkaline hydrogen peroxide (AHP) pretreatment is another chemical pretreatment method. This method uses a combination of hydrogen peroxide and sodium hydroxide solutions at pH 11.5. It is effective for the delignification and solubilization of hemicellulose. AHP pretreatments are characterized by modest reaction conditions and low usage of alkali [24]. Additionally, organosolv pretreatment method uses various organic or aqueous solvent mixtures in order to solubilize hemicellulose and extract lignin. Actually, these solutions break down the internal bonds between lignin and hemicellulose. A wide range of organic solvents might be used in this method, some of which are methanol, ethanol, acetone, ethyl glycol, and organic acids. The optimal temperature of the organosolv pretreatment method is between 100 and 250 °C. A catalyst is usually added in this process to either improve the delignification rate or decrease the pretreatment temperature [22]. Finally, there is an increasing interest in the usage of ionic liquids (ILs) as pretreatment methods. In ILs pretreatments, both cations and anions play an important role in solubilizing cellulose and lignin. ILs are characterized by their low vapor pressure, non-toxicity, non-volatility, large thermal and chemical stability, and most importantly their recoverability and reusability [29].
On the other hand, various physical pretreatment methods could be applied in order to disrupt the lignocellulosic structure of BSG and release its valuable constituents, making it more accessible to enzymes. In fact, physical pretreatments are suitable for products that are destined for use in food [30], starting with mechanical pretreatments, such as milling and blending, which reduces the BSG into small fragments. Then, followed by enzymatic treatment, Beldman et al. reported that these two techniques yielded a 10% increase in the monosaccharides present in BSG derived from cellulose and hemicellulose hydrolysis, indicating an improve in the susceptibility to the enzymatic hydrolysis [26]. Another example of physical pretreatment methods is hydrothermal pretreatments. The deconstruction process in this method is referred to as autohydrolysis, since the water content of the BSG acts to disrupt the lignocellulosic structure and to hydrolyze the hemicellulose, prior to the subsequent enzymatic hydrolysis. Hydrothermal pretreatments do not use hazardous and costly chemicals, but they require harsh operating conditions, particularly a high temperature, ranging between 120 and 200 °C, to attain satisfactory degradation. The addition of a catalyst—namely, a diluted strong acid—was reported to improve the efficiency of this process and to permit the usage of a lower temperature [17]. It is noteworthy that several toxic byproducts are produced during this method. A study done by Gomes et al. reported that hydrothermolysis led to a 10% increase in methane production from BSG. Particularly, 467.6 NmL/g methane was produced by a pretreated sample (hydrothermolysis at 140 °C for 15 min) compared to 409.8 NmL/g produced by the unpretreated sample [19]. Finally, ultrasonic pretreatment holds potential for large-scale processes. It enables a major decrease in time and energy when compared to alkaline extraction [30]. Ultrasonic pretreatment occurs in liquid media, resulting in cavitation phenomena. In this phenomenon, microbubbles are formed, grow, and then at a critical size they aggressively collapse, converting sonic into mechanical energy. The latter cavitation effect produces high temperature and pressure, in addition to shear forces, which lead to the creation of the “hot-spot effect” in the liquid and the formation of free radicals. The preciously described phenomenon aids in decreasing the crystallinity of the cellulose and increasing the surface area of the BSG, making it more accessible to the enzymatic hydrolysis. BSG pretreatment, under the optimal ultrasonication conditions, led to a 2.1 fold increase in sugar yield, compared to the unpretreated BSG [31].
Moving to hybrid methods, physicochemical and microwave-assisted alkaline pretreatment methods will be discussed. Steam explosion [32], ammonia fiber explosion (AFEX) [33], CO2 explosion pretreatment [34], and liquid hot water (LHW) [35] are various examples of physicochemical pretreatments. They affect the physical parameters, as well as the chemical bonds and intermolecular interactions of the lignocellulosic materials [36]. Additionally, microwave-assisted alkali pretreatment is another hybrid approach. The application of microwave radiation in the presence of alkali solution (0.5 M NaOH) for 10 min at 160 °C, liberated 49% of the polysaccharides present in BSG [30].
Finally, biological pretreatments require microorganisms, mainly fungi or bacteria, for the treatment of lignocellulosic material and degradation of hemicellulose, lignin, and sometimes cellulose, depending on the microorganism used. Mainly white-rot fungi are involved in this type of pretreatment, due to the high sugar yield associated with enzymatic hydrolysis. Since they carry lignin degrading enzymes, white-rot usually degrades lignin. In fact, brown-rot degrades cellulose whereas white- and soft-rot fungi target lignin and cellulose. Biological pretreatment method is environmentally friendly, consumes less energy, involves mild conditions, and is not costly; however, it is very slow (low rate of hydrolysis) and requires careful control of growth conditions, as well as much space to perform the pretreatment [21,29].
As previously mentioned, pretreated susceptible spent grains are then subjected to enzymatic saccharification. A wide range of enzymes might be used in order to complete the hydrolysis, including xylanases, acetyl esterases, glucuronidases, β-xylosidases, feruloyl esterases, glucuronoyl esterases and α-L-arabinofuranosidases, which can be targeted toward specific products [37]. Enzymatic hydrolysis process displays some advantages, including mild process requirements, low energy consumption, high sugar yields, and no production of unwanted waste products [38]. Finally, it is noteworthy that no pretreatment has a 100% conversion rate [9].

3. Brewers’ Spent Grains Fermentation and Production of Value-Added Compounds

The production of high value-added bio-products using microorganisms, mainly bacteria and fungi, has been a trending headline in the biotechnological industry. Particularly, using biomass from agro-industrial waste materials as a substrate in these biotechnological applications, to produce microbial cell biomass and to grow different fungi without the need for extra nutrients, has been at the center of attention [8]. Due to the high nutritional value of BSG, mainly its high hemicellulose content ranging between 19 and 42% [19], this secondary raw material can produce through fermentation several value-added products, such as organic acids, amino acids, volatile fatty acids, enzymes, vitamins, second-generation biofuels and other products [23,39]. For instance, a study done by Marcus and Fox reported that BSG can be processed into various enzymes, including α-amylase, β-amylase, cellulases, glucanases, hemicellulases, etc., and to other products such as xylitol, bioethanol, and citric acid through fungal fermentation of BSG [40]. Other value-added products are reported in this review—namely, L-lactic acid, β-xylosidase and α-L-arabinofuranosidase, 2-phenylethanol (2-PE), gibberellic acid (GA3), using not only fungal fermentation but also bacterial fermentation of BSG. Additionally, it is noteworthy that recent studies have reported that this valuable by-product can be biovalorized into natural pigments, namely monascus red pigment, which has been used as a natural coloring agent and food additive in East Asia, hence broadening the applications and importance of this industrial nutrient-rich byproduct [41].
Two types of fermentation might be used in the valorization process of BSG. In the next section, both submerged and solid-state fermentation processes will be discussed along with the various value-added products that can be produced via both types of fermentation.

3.1. Submerged Fermentation

3.1.1. Introduction about Submerged Fermentation

Submerged fermentation (SmF) is the classical fermentation type that has been used since the 1940s [42]. In this technique, microorganisms grow in a liquid medium containing the needed nutrients. The quantity of water available for bacterial growth affects the development of biomass, the metabolic reactions, and the mass transfer processes [9]. The free-flowing liquid substrates can be either a synthetic media (broths), a waste, or industrial by-product substrate such as molasses. It is noteworthy that this technique is suitable for microorganisms that usually require high moisture content and for the production of secondary metabolites that need to be used in their liquid form since they are usually secreted in the fermentation broth [43]. Due to the numerous advantages of this technique, it is being used by many industries and facilities. Particularly, most of the enzyme-producing facilities use SmF due to better monitoring and ease of handling [44]. Additionally, this technique allows for the precise control of important growth parameters, including temperature, pH, dissolved oxygen, and substrate concentration [45]. SmF is also characterized by its simple downstream processing after fermentation, particularly easy purification of the products [43,46]. This type of fermentation is less susceptible to substrate inhibition compared to other types, hence leading to a high product yield [47]. Scale-up methods and bioreactors for this type of fermentation were well developed; thus, SmF can be used on an industrial-scale [48]. SmF supports the use of genetically modified organisms [43]. On the other hand, however, it has various disadvantages. For one, it is a time-consuming process where secondary metabolites require time to be produced. Also, it is an energy-consuming process, since SmF is prone to bacterial and fungal contamination, and requires energy for sterilization. It is a costly process when synthetic media is used as a substrate and expensive raw materials are added to it. Finally, substrates in SmF are utilized quite rapidly and need to be constantly supplemented with nutrients or replaced [49]. Like any other technique, SmF displays advantages and disadvantages, and its usage depends on the field of application and aim of the experiment [42].

3.1.2. Valorization of BSG Using Submerged Fermentation

As previously mentioned, BSG can be used as substrate for the fermentation process and yield various valuable compounds. In this part, the production of various value-added compounds through SmF will be discussed. SmF of BSG using Escherichia coli SL100 can produce ethanol. At first, BSG underwent a phosphoric acid pretreatment in order to recover part of the sugar content (retrieving 80% of the hemicellulose sugar content in BSG and 35.5% of the total glucose in BSG). The liquid fraction from the pretreatment was then fermented using an ethanologenic E. coli SL100, which is a strain capable of converting the spent grains’ xylose, arabinose, and glucose into ethanol and has a high inhibitor tolerance. SmF was carried out with 150 mL of prehydrolysate, for 92 h at pH 6.5, 37 °C, and 300 rpm. After 55 h, a maximal concentration of ethanol was produced which was equal to 16 g/L, corresponding to a yield of 0.4 g of ethanol per g of sugar in the medium [12].
Moreover, SmF of BSG using Aspergillus niger and Saccharomyces cerevisiae can produce citric acid. A. niger strain was isolated from spoiled orange and S. cerevisiae strain was isolated from palm wine samples. Fermentation was performed in 500 mL Erlenmeyer flasks containing 200 mL of the fermentation medium and 0.2 mL of methanol (to enhance the fungal production of citric acid) for 14 days at 30 °C and pH 4.5. The highest citric acid concentrations produced were 0.512%/v by A. niger after 96 h fermentation, and 0.312%/v by S. cerevisiae after 7 days fermentation [50]. Debaryomyces hansenii was also reported to produce ethanol via fermentation on BSG hydrolysates [51].
Additionally, SmF of BSG using Lactobacillus rhamnosus can produce L-lactic acid. Fermentation was carried out at 37 °C in 300 mL conical flask containing 100 mL immobilized lactic acid bacteria (L. rhamnosus NBRC14710), 70 mL of liquefied BSG that was enzymatically hydrolyzed, and Tween 80 (a growth factor for lactic acid bacteria). After 5 days, L. rhamnosus NBRC14710 produced 19.0 g/L L-lactic acid [52].
Furthermore, SmF of BSG using Bacillus sp. KR-8104 can produce α-amylase. Traditionally, SmF is used to produce α-amylase on an industrial scale. The fermentation occurred in 250 mL Erlenmeyer flask containing 50 mL medium (dextrin, yeast extract, meat extract, KH2PO4, and MgSO4·7H2O), 5% (w/v) BSG, and inoculated with a 2% (v/v) bacterial culture at 37 °C and 180 rpm. The maximum production of α-amylase was achieved when using a dextrin-free culture medium and it was around 25,255 U/L (Unit of α-amylase per L of fermented culture medium) [49].
In addition, SmF of BSG using Aspergillus fumigatus and Penicillium sp. can produce cellulase. 100 g of BSG were washed with 250 mL of distilled water, at room temperature and 220 rpm for 2 h. Then, the liquid part was recuperated using centrifugation whereas the solid part (washed BSG) was dried at 70 °C for 72 h. SmF occurred at 30 °C, 220 rpm, for 96 h in a flask containing 80 g/L washed BSG and culture medium (containing yeast extract, (NH4)NO3, KH2PO4, K2HPO4, and MgSO4) inoculated with a 3-day precultured fungi. The highest cellulase activity was 0.354 and 0.232 U/mL for A. fumigatus and Penicillium sp., respectively [53]. Subsequently, various value-added compounds including ethanol, citric acid, L-lactic acid, α-amylase, and cellulase, can be produced through fermentation, particularly SmF, of different microorganisms on BSG and its usage as a carbon and nutrient source for their growth.

3.2. Solid-State Fermentation

3.2.1. Introduction about Solid-State Fermentation

Solid-state fermentation (SSF) is one of the world’s oldest microbiological procedures for fermented food preservation and development. SSF, unlike SmF, is the controlled growth and/or cultivation of microorganisms in the absence of water or with a small amount of water for the manufacture of desired products of interest. The solid matrix can be a source of nutrients or simply support impregnated with the nutrients necessary for microbial development [54,55]. According to the history of fermentation technology, this method was largely ignored in developed countries after the 1940s at the expense of SmF technology. Following the development of penicillin in SmF and due to the importance of penicillin during the 2nd World War, SmF has become a model technology for the production of any substance via fermentation. As a result, researchers focused solely on the SmF, and the SSF was overlooked. The study of SSF systems has continued in isolated areas, and the transformation of steroids with the help of fungi cultures has been described between the years 1950 and 1960. The trend has continued, albeit slowly, and during the 1960s and 1970s, reports on the production of mycotoxins by the SSF became widely known [56]. The second major activity was the production of high-protein animal feed from agricultural waste. Since then, this process has been used extensively, and this trend has accelerated over the last decade [56,57].
Furthermore, SSF is a well-known and well-established bioprocess for improving nutritional profiles and producing enzymes, particularly used for biomass degradation. The bioreactors used in SSF processes, and classified based on design and operation, are tray bioreactors, packed-bed bioreactors, stirred-drum bioreactors and rotating drum bioreactors, gas-solid fluidized beds and various stirred-aerated bioreactors [58]. Choosing the right bioreactor for the SSF process requires an understanding of the microorganism’s morphology, as well as consideration of the process parameters (e.g., pH, temperature, support type, aeration, moisture, and water activity).
SSF has the potential to be a good bioprocess for the generation of microbial secondary metabolites from agricultural waste and industrial leftovers. Bagasse, bran, husks, whole pomace, seeds, peels, corn residue, BSG, and other waste products are produced in large amounts and are either underutilized or discarded. Recently, there has been a lot of focus on using the abovementioned materials, as they are readily available and low-cost renewable substrates able to generate a variety of valuable chemicals [59]. This approach has several advantages over SmF, including lower catabolite repression and substrate inhibition, superior enzyme harvests, environmentally friendly, low output waste, low energy consumption, prolonged product steadiness, no discharge of organic waste water, and low production costs [60,61,62]. In addition, the process is suitable for work with filamentous fungi. It consists of a simple fermentation process with no foam formation and easy to control of bacterial contamination [63].
Moreover, the disadvantages of this technique depend on the type of bioreactor used. Generally, it is hard to control the metabolite temperature during the process. As a result, the temperature will rise to the point where the intended microbial product will be destroyed or the growth and fermentation are entirely stopped [64]. In addition, steady aeration, growth, and kinetic study are still difficult to achieve [63].

3.2.2. Valorization of BSG Using Solid State-Fermentation

SSF is a valuable technique for the valorization of agro-industrial byproducts—namely, BSG—to produce value-added products [65]. Cellulase and xylanase enzymes can be produced through SSF of A. niger on BSG. SSF was carried out in 250 mL Erlenmeyer flask containing 2 g of BSG in an enriched medium (composed of (NH4)2SO4, NaNO3, KH2PO4, and yeast extract) with a solid to liquid ratio of 3.5:1 (w/v), and an 80% humidity. The medium was then sterilized and inoculated with A. niger CECT 2700 strain acquired from the Spanish collection of type culture. Fermentation occurred at 30 °C for 7 days without mixing. The highest cellulase activity was 6.23 U/g of dry substrate (gds) using BSG pretreated with boiling water, whereas the highest xylanase activity was 1400.80 U/gds obtained using BSG pretreated in an autoclave [66]. Another study reported the ability of A. fumigatus and Penicillium sp. to produce cellulase, using SSF. Cellulase was produced by fermenting 5 g of washed BSG inoculated with 4 mL of a 3-day fungi preculture, at 30 °C for 18 days, and with 73.6% humidity. The highest cellulase activity was 7.5 U/gds after 11 days for A. fumigatus, whereas Penicillium sp. produced 8.3 U/gds cellulase after 14 days [53].
In addition, SSF of BSG using Penicillium janczewskii can lead to the production of multiple xylanolytic enzymes, particularly xylanase, β-xylosidase and α-L-arabinofuranosidase. SSF was performed in 250 mL Erlenmeyer flasks containing 5 g of dried BSG and Vogel’s salt solution, with a 50% initial moisture, inoculated with 1 mL of P. janczewskii CRM 1348 suspension. SSF was carried out for 7 days at 28 °C. The maximum amounts of xylanase, β-xylosidase and α-L-arabinofuranosidase produced were 370 U/gds, 246.5 mU/gds, and 606.7 mU/gds, respectively [67].
Laccase enzyme can also be produced through the biovalorization of BSG using Trametes versicolor TV-6. 50 g of BSG mixed with 10 mL of distilled water were placed in a flask, autoclaved, and then cooled down. The medium was then inoculated with T. versicolor. SSF occurred for 14 days at 27 °C, with a 63% initial moisture content. The highest laccase activity was produced after 7 days fermentation and it was equal to 560 U/L [68].
2-PE is another value-added molecule that can be produced through SSF of BSG. The SSF using Pichia kudriavzevii CECT 13,184 was carried out for 96 h in 500 mL Erlenmeyer flasks containing 95 g of pretreated and inoculated BSG. The highest concentration of 2-PE appeared after 10 h fermentation and at 30 °C and 76% initial content moisture, it was equal to 6.5 mg2−PE/gds in the presence of 4% L-phenylalanine as precursor [69].
Ethanol is another alcohol that can be produced through SSF of BSG. SSF of pretreated (via diluted phosphoric acid) and enzymatically hydrolyzed BSG produced ethanol using S. cerevisiae for 72 h at 150 rpm and 40 °C. Actually, after 30 h fermentation, 5.1 g of ethanol were produced for every 100 g of BSG [12].
In addition, GA3 can be produced through SSF of BSG. Fermentation occurred in 500 mL flasks containing 50 g BSG in an enriched medium (containing glucose, FeSO4·7H2O, MgSO4, MnSO4·H2O, ZnSO4·7H2O, and at pH 5–5.5). The flasks were then autoclaved and inoculated using Fusarium fujikuroi IOC 4380, at a ratio equal to 15% to the mass of BSG. The highest GA3 production was achieved after 96 h of fermentation, at 28 °C and 80% moisture content, and was equal to 0.82 g per kg of BSG [70].
SSF of BSG using Aspergillus oryzae can also produce α-amylase. Fermentation occurred in 250 mL Erlenmeyer flasks containing 5 g of BSG and a salt solution (composed of NH4NO3, KH2PO4, NaCl, and MgSO4·7H2O). The substrate was then autoclaved and inoculated with A. oryzae NRRL 6270. After 96 h fermentation at 30 °C and 70% moisture content, the maximum amount of α-amylase produced by A. niger was 6870 U/gds [71].
Finally, as previously discussed, BSG is a cost-effective carbon and nitrogen source that can be used as a substrate for microbial growth [53]. Through SSF on BSG, different microorganisms were able to produce various value-added compounds including cellulase, xylanolytic enzymes, laccase, 2-PE, ethanol, GA3, and α-amylase.

4. BSG Supply Chain System

It was reported that around 3.4 and 4.5 million tons of BSG were produced from the brewing industry in Europe and the United States, respectively [14]. The huge quantities of BSG generated in the breweries, their low market value, their high moisture content associated with a difficulty in their storage, and their bad environmental effect made their disposal challenging [72]. The market price of BSG (40.23 USD/ton) is lower than the price of other cellulosic crops (between 50 and 150 USD/ton), which is mainly because BSG have high moisture content and are sold as is [14]. Formerly, large beer manufacturers used to install drying facilities to decrease the water content of the grains and make them more appealing for the farmers. However, most of the breweries are moving away from the drying process since it is expensive and energy-intensive [73]. A study done by Buffington suggested the usage of a “hub and spoke” model in order to integrate potential sellers and buyers of BSG. Therefore, the author proposed the creation of a network between different breweries and a bio-refinery (drying and storage of BSG), which will sell the BSG to biomass buyers that will manufacture them into the various useful products. Buffington assume that this proposition will increase the market price of BSG by 450% to reach 179.29 USD/ton [14]. More research should be done in order to develop the right supply chain structures for BSG and its economic market.

5. Conclusions

The increasing beer manufacturing nowadays leads to a corresponding increased accumulation of BSG that needs to be properly managed. BSG is the solid fraction remaining after wort removal [6]. It is nutritionally rich and composed of fibers, mainly hemicellulose, cellulose, and lignin, in addition to proteins, lipids, vitamins, and minerals [7]. However, due to the high moisture content and high polysaccharides and proteins contents, this byproduct is prone to microbial contamination within a few days of production; therefore, there is a need to find a suitable, economical, and environmentally friendly valorization method [2]. The biotechnological route of BSG valorization using SmF and SSF leads to the production of various value-added compounds [13]. To make the valorization process more efficient, a pretreatment step (e.g., chemical, physical, biological, hybrid, etc.) should precede the fermentation, in order to disrupt the natural recalcitrance of the lignocellulosic fibrous material of the BSG, exposing the polysaccharides, and making them more susceptible for enzymatic hydrolysis which aims to decompose them into fermentable sugars [74]. Finally, BSG can be processed into organic acids, amino acids, volatile fatty acids, vitamins, and second-generation biofuels [23] such as ethanol, citric acid, L-lactic acid, α-amylase, cellulase, xylanolytic enzymes, laccase, 2-PE and GA3.

Author Contributions

S.M.: Investigation, Writing—original draft, Writing—review & editing, Formal analysis. S.-J.S.: Writing—original draft, Writing—eview & editing. A.K., E.L. and R.G.M.: Formal analysis, Writing—review & editing. N.L. and M.K.: Conceptualization, Supervision, Writing—review & editing, Formal analysis. All authors have read and agreed to the published version of the manuscript.

Funding

This research was funded by the Ministry of Higher Education, Research and Innovation in France, and by The Research Council of the Saint Joseph University of Beirut, in Lebanon FS-165.

Institutional Review Board Statement

Not applicable.

Informed Consent Statement

Not applicable.

Data Availability Statement

Not applicable.

Conflicts of Interest

The authors declare no conflict of interest.

References

  1. Oliver, G.; Colicchio, T. The Oxford Companion to Beer; The Oxford University Press: New York, NY, USA, 2011. [Google Scholar]
  2. Patel, A.; Mikes, F.; Bühler, S.; Matsakas, L. Valorization of brewers’ spent grain for the production of lipids by oleaginous yeast. Molecules 2018, 23, 3052. [Google Scholar] [CrossRef] [PubMed] [Green Version]
  3. Parchami, M.; Ferreira, J.A.; Taherzadeh, M.J. Brewing process development by integration of edible filamentous fungi to upgrade the quality of brewer’s spent grain (BSG). BioResources 2021, 16, 1686. [Google Scholar] [CrossRef]
  4. Goberna, M.; Camacho, M.D.M.; Lopez-Abadia, J.A.; García, C. Co-digestion, biostimulation and bioaugmentation to enhance methanation of brewer’s spent grain. Waste Manag. Res. 2013, 31, 805–810. [Google Scholar] [CrossRef] [PubMed]
  5. The Brewers of Europe. European Beer Trends Statistics Report; The Brewers of Europe: Brussels, Belgium, 2019. [Google Scholar]
  6. Kavalopoulos, M.; Stoumpou, V.; Christofi, A.; Mai, S.; Barampouti, E.M.; Moustakas, K.; Malamis, D.; Loizidou, M. Sustainable valorisation pathways mitigating environmental pollution from brewers’ spent grains. Environ. Pollut. 2021, 270, 116069. [Google Scholar] [CrossRef] [PubMed]
  7. Aprodu, I.; Simion, A.B.; Banu, I. Valorisation of the Brewers’ Spent Grain Through Sourdough Bread Making. Int. J. Food Eng. 2017, 13, 20170195. [Google Scholar] [CrossRef]
  8. Cooray, S.T.; Chen, W.N. Valorization of brewer’s spent grain using fungi solid-state fermentation to enhance nutritional value. J. Funct. Foods 2018, 42, 85–94. [Google Scholar] [CrossRef]
  9. Chetrariu, A.; Dabija, A. Brewer’s spent grains: Possibilities of valorization, a review. Appl. Sci. 2020, 10, 5619. [Google Scholar] [CrossRef]
  10. Cooray, S.T.; Lee, J.J.L.; Chen, W.N. Evaluation of brewers’ spent grain as a novel media for yeast growth. AMB Express 2017, 7, 1–10. [Google Scholar] [CrossRef]
  11. San Martin, D.; Orive, M.; Iñarra, B.; Castelo, J.; Estévez, A.; Nazzaro, J.; Iloro, I.; Elortza, F.; Zufía, J. Brewers’ Spent Yeast and Grain Protein Hydrolysates as Second-Generation Feedstuff for Aquaculture Feed. Waste Biomass Valorization 2020, 11, 5307–5320. [Google Scholar] [CrossRef]
  12. Rojas-Chamorro, J.A.; Cara, C.; Romero, I.; Ruiz, E.; Romero-García, J.M.; Mussatto, S.I.; Castro, E. Ethanol Production from Brewers’ Spent Grain Pretreated by Dilute Phosphoric Acid. Energy Fuels 2018, 32, 5226–5233. [Google Scholar] [CrossRef]
  13. Teixeira, M.R.; Guarda, E.C.; Freitas, E.B.; Galinha, C.F.; Duque, A.F.; Reis, M.A.M. Valorization of raw brewers’ spent grain through the production of volatile fatty acids. New Biotechnol. 2020, 57, 4–10. [Google Scholar] [CrossRef] [PubMed]
  14. Buffington, J. The Economic Potential of Brewer’s Spent Grain (BSG) as a Biomass Feedstock. Adv. Chem. Eng. Sci. 2014, 4, 308–318. [Google Scholar] [CrossRef] [Green Version]
  15. Mitri, S.; Koubaa, M.; Maroun, R.G.; Rossignol, T.; Nicaud, J.-M.; Louka, N. Bioproduction of 2-Phenylethanol through Yeast Fermentation on Synthetic Media and on Agro-Industrial Waste and By-Products: A Review. Foods 2022, 11, 109. [Google Scholar] [CrossRef] [PubMed]
  16. Su, Y.; Du, R.; Guo, H.; Cao, M.; Wu, Q.; Su, R.; Qi, W.; He, Z. Fractional pretreatment of lignocellulose by alkaline hydrogen peroxide: Characterization of its major components. Food Bioprod. Process. 2015, 94, 322–330. [Google Scholar] [CrossRef]
  17. Wilkinson, S.; Smart, K.A.; Cook, D.J. Optimising the (Microwave) Hydrothermal Pretreatment of Brewers Spent Grains for Bioethanol Production. J. Fuels 2015, 2015. [Google Scholar] [CrossRef] [Green Version]
  18. Wang, H.; Tao, Y.; Temudo, M.; Bijl, H.; Kloek, J.; Ren, N.; van Lier, J.B.; de Kreuk, M. Biomethanation from enzymatically hydrolyzed brewer’s spent grain: Impact of rapid increase in loadings. Bioresour. Technol. 2015, 190, 167–174. [Google Scholar] [CrossRef]
  19. Gomes, M.M.; Rabelo, C.A.B.S.; Sakamoto, I.K.; Silva, E.L.; Varesche, M.B.A. Methane Production Using Brewery Spent Grain: Optimal Hydrothermolysis, Fermentation of Waste and Role of Microbial Populations. Waste Biomass Valorization 2021. [Google Scholar] [CrossRef]
  20. Mussatto, S.I. Brewer’s spent grain: A valuable feedstock for industrial applications. J. Sci. Food Agric. 2014, 97, 1264–1275. [Google Scholar] [CrossRef] [Green Version]
  21. Kisielewska, M.; Rusanowska, P.; Dudek, M.; Nowicka, A.; Krzywik, A.; Dębowski, M.; Joanna, K.; Zieliński, M. Evaluation of Ultrasound Pretreatment for Enhanced Anaerobic Digestion of Sida hermaphrodita. Bioenergy Res. 2020, 13, 824–832. [Google Scholar] [CrossRef] [Green Version]
  22. Baruah, J.; Nath, B.K.; Sharma, R.; Kumar, S.; Deka, R.C.; Baruah, D.C.; Kalita, E. Recent trends in the pretreatment of lignocellulosic biomass for value-added products. Front. Energy Res. 2018, 6, 141. [Google Scholar] [CrossRef]
  23. Dávila, J.A.; Rosenberg, M.; Cardona, C.A. A biorefinery approach for the production of xylitol, ethanol and polyhydroxybutyrate from brewer’s spent grain. AIMS Agric. Food 2016, 1, 52–66. [Google Scholar] [CrossRef]
  24. Wilkinson, S.; Smart, K.A.; Cook, D.J. Optimisation of alkaline reagent based chemical pre-treatment of Brewers spent grains for bioethanol production. Ind. Crop. Prod. 2014, 62, 219–227. [Google Scholar] [CrossRef]
  25. Brodeur, G.; Yau, E.; Badal, K.; Collier, J.; Ramachandran, K.B.; Ramakrishnan, S. Chemical and physicochemical pretreatment of lignocellulosic biomass: A review. Enzyme Res. 2011, 2011. [Google Scholar] [CrossRef] [PubMed]
  26. Beldman, G.; Hennekam, J.; Voragen, A.G.J. Enzymatic hydrolysis of beer brewers’ spent grain and the influence of pretreatments. Biotechnol. Bioeng. 1987, 30, 668–671. [Google Scholar] [CrossRef] [PubMed]
  27. Jȩdrzejczyk, M.; Soszka, E.; Czapnik, M.; Ruppert, A.M.; Grams, J. Physical and chemical pretreatment of lignocellulosic biomass. In Second and Third Generation of Feedstocks: The Evolution of Biofuels; Elsevier: Amsterdam, The Netherlands, 2019; pp. 143–196. ISBN 9780128151624. [Google Scholar]
  28. Wagner, E.; Pería, M.E.; Ortiz, G.E.; Rojas, N.L.; Ghiringhelli, P.D. Valorization of brewer’s spent grain by different strategies of structural destabilization and enzymatic saccharification. Ind. Crop. Prod. 2021, 163, 113329. [Google Scholar] [CrossRef]
  29. Aftab, M.N.; Iqbal, I.; Riaz, F.; Karadag, A.; Tabatabaei, M. Different Pretreatment Methods of Lignocellulosic Biomass for Use in Biofuel Production. In Biomass for Bioenergy-Recent Trends and Future Challenges; IntechOpen: London, UK, 2019. [Google Scholar]
  30. Lynch, K.M.; Steffen, E.J.; Arendt, E.K. Brewers’ spent grain: A review with an emphasis on food and health. J. Inst. Brew. 2016, 122, 553–568. [Google Scholar] [CrossRef]
  31. Hassan, S.S.; Ravindran, R.; Jaiswal, S.; Tiwari, B.K.; Williams, G.A.; Jaiswal, A.K. An evaluation of sonication pretreatment for enhancing saccharification of brewers’ spent grain. Waste Manag. 2020, 105, 240–247. [Google Scholar] [CrossRef]
  32. Yu, Z.; Zhang, B.; Yu, F.; Xu, G.; Song, A. A real explosion: The requirement of steam explosion pretreatment. Bioresour. Technol. 2012, 121, 335–341. [Google Scholar] [CrossRef] [PubMed]
  33. Menon, V.; Rao, M. Trends in bioconversion of lignocellulose: Biofuels, platform chemicals & biorefinery concept. Prog. Energy Combust. Sci. 2012, 38, 522–550. [Google Scholar] [CrossRef]
  34. Zheng, Y.; Lin, H.M.; Tsao, G.T. Pretreatment for cellulose hydrolysis by carbon dioxide explosion. Biotechnol. Prog. 1998, 14, 890–896. [Google Scholar] [CrossRef] [PubMed]
  35. Zhuang, X.; Wang, W.; Yu, Q.; Qi, W.; Wang, Q.; Tan, X.; Zhou, G.; Yuan, Z. Liquid hot water pretreatment of lignocellulosic biomass for bioethanol production accompanying with high valuable products. Bioresour. Technol. 2016, 199, 68–75. [Google Scholar] [CrossRef] [PubMed]
  36. Taylor, M.J.; Alabdrabalameer, H.A.; Skoulou, V. Choosing physical, physicochemical and chemical methods of pre-treating lignocellulosic wastes to repurpose into solid fuels. Sustainability 2019, 11, 3604. [Google Scholar] [CrossRef] [Green Version]
  37. Puligundla, P.; Mok, C. Recent advances in biotechnological valorization of brewers’ spent grain. Food Sci. Biotechnol. 2021, 30, 341–353. [Google Scholar] [CrossRef] [PubMed]
  38. Bensah, E.C.; Mensah, M. Chemical pretreatment methods for the production of cellulosic ethanol: Technologies and innovations. Int. J. Chem. Eng. 2013, 2, 887–898. [Google Scholar] [CrossRef]
  39. Guarda, E.C.; Oliveira, A.C.; Antunes, S.; Freitas, F.; Castro, P.M.L.; Duque, A.F.; Reis, M.A.M. A two-stage process for conversion of brewer’s spent grain into volatile fatty acids through acidogenic fermentation. Appl. Sci. 2021, 11, 3222. [Google Scholar] [CrossRef]
  40. Marcus, A.; Fox, G. Fungal biovalorization of a brewing industry byproduct, brewer’s spent grain: A review. Foods 2021, 10, 2159. [Google Scholar] [CrossRef] [PubMed]
  41. Silbir, S.; Goksungur, Y. Natural red pigment production by monascus purpureus in submerged fermentation systems using a food industry waste: Brewer’s spent grain. Foods 2019, 8, 161. [Google Scholar] [CrossRef] [Green Version]
  42. Hölker, U.; Lenz, J. Solid-state fermentation—Are there any biotechnological advantages? Curr. Opin. Microbiol. 2005, 8, 301–306. [Google Scholar] [CrossRef]
  43. Subramaniyam, R.; Vimala, R. Solid State and Submerged Fermentation for the Production of Bioactive Substances: A Comparative Study. Int. J. Sci. Nat. 2012, 3, 480–486. [Google Scholar]
  44. Singhania, R.R.; Sukumaran, R.K.; Patel, A.K.; Larroche, C.; Pandey, A. Advancement and comparative profiles in the production technologies using solid-state and submerged fermentation for microbial cellulases. Enzyme Microb. Technol. 2010, 46, 541–549. [Google Scholar] [CrossRef]
  45. Wolters, N.; Schabronath, C.; Schembecker, G.; Merz, J. Efficient conversion of pretreated brewer’s spent grain and wheat bran by submerged cultivation of Hericium erinaceus. Bioresour. Technol. 2016, 222, 123–129. [Google Scholar] [CrossRef] [PubMed]
  46. Srivastava, N.; Srivastava, M.; Ramteke, P.W.; Mishra, P.K. Solid-state fermentation strategy for microbial metabolites production: An overview. In New and Future Developments in Microbial Biotechnology and Bioengineering: Microbial Secondary Metabolites Biochemistry and Applications; Elsevier: Amsterdam, The Netherlands, 2019; ISBN 9780444635044. [Google Scholar]
  47. Soccol, C.R.; da Costa, E.S.F.; Letti, L.A.J.; Karp, S.G.; Woiciechowski, A.L.; de Souza Vandenberghe, L.P. Recent developments and innovations in solid state fermentation. Biotechnol. Res. Innov. 2017, 1, 52–71. [Google Scholar] [CrossRef]
  48. Doriya, K.; Jose, N.; Gowda, M.; Kumar, D.S. Solid-State Fermentation vs Submerged Fermentation for the Production of L-Asparaginase. In Advances in Food and Nutrition Research; Elsevier: Amsterdam, The Netherlands, 2016. [Google Scholar]
  49. Hashemi, M.; Razavi, S.H.; Shojaosadati, S.A.; Mousavi, S.M. The potential of brewer’s spent grain to improve the production of α-amylase by Bacillus sp. KR-8104 in submerged fermentation system. New Biotechnol. 2011, 28, 165–172. [Google Scholar] [CrossRef] [PubMed]
  50. Victor, A.; Titilayo, F.-O. Citric acid production from brewers spent grain by Aspergillus niger and Saccharomyces cerevisiae Enzymes from microorganisms isolated from insect gut View project Citric acid production from brewers spent grain by Aspergillus niger and Saccharomyces cere. Int. J. Res. Biosci. 2013, 2, 30–36. [Google Scholar]
  51. Rachwał, K.; Waśko, A.; Gustaw, K.; Polak-Berecka, M. Utilization of brewery wastes in food industry. PeerJ 2020, 8, e9427. [Google Scholar] [CrossRef]
  52. Shindo, S.; Tachibana, T. Production of L-lactic acid from spent grain, a by-product of beer production. J. Inst. Brew. 2004, 110, 347–351. [Google Scholar] [CrossRef]
  53. Casas-Godoy, L.; González-Escobar, J.L.; Mathis, A.G.; Barrera-Martínez, I. Revalorization of untreated Brewer’s spent grain: Novel and versatile feedstock to produce cellulases, lipases, and yeast biomass in a biorefinery approach. Biomass Convers. Biorefinery 2020, 1–12. [Google Scholar] [CrossRef]
  54. Singh, M.; Devi, S.; Rana, V.S.; Mishra, B.B.; Kumar, J.; Ahluwalia, V. Delivery of phytochemicals by liposome cargos: Recent progress, challenges and opportunities. J. Microencapsul. 2019, 36, 215–235. [Google Scholar] [CrossRef]
  55. Thomas, L.; Larroche, C.; Pandey, A. Current developments in solid-state fermentation. Biochem. Eng. J. 2013, 81, 146–161. [Google Scholar] [CrossRef]
  56. Pandey, A. Solid-state fermentation. Biochem. Eng. J. 2003, 13, 81–84. [Google Scholar] [CrossRef]
  57. Krishna, C. Solid-state fermentation systems—An overview. Crit. Rev. Biotechnol. 2005, 25, 1–30. [Google Scholar] [CrossRef] [PubMed]
  58. Rodríguez-Couto, S. Solid-State Fermentation for Laccases Production and Their Applications. In Current Developments in Biotechnology and Bioengineering; Elsevier: Amsterdam, The Netherlands, 2018; pp. 211–234. [Google Scholar]
  59. Lima-Pérez, J.; López-Pérez, M.; Viniegra-González, G.; Loera, O. Solid-state fermentation of Bacillus thuringiensis var kurstaki HD-73 maintains higher biomass and spore yields as compared to submerged fermentation using the same media. Bioprocess Biosyst. Eng. 2019, 42, 1527–1535. [Google Scholar] [CrossRef] [PubMed]
  60. Krishania, M.; Sindhu, R.; Binod, P.; Ahluwalia, V.; Kumar, V.; Sangwan, R.S.; Pandey, A. Design of Bioreactors in Solid-State Fermentation. In Current Developments in Biotechnology and Bioengineering; Elsevier: Amsterdam, The Netherlands, 2018; pp. 83–96. [Google Scholar]
  61. Agarwal, A.K.; Agarwal, R.A.; Gupta, T.; Gurjar, B.R. Biofuels: Technology, Challenges and Prospects. In Green Energy and Technology; Springer: Berlin, Germany, 2017. [Google Scholar]
  62. Salgado-Bautista, D.; Volke-Sepúlveda, T.; Figueroa-Martínez, F.; Carrasco-Navarro, U.; Chagolla-López, A.; Favela-Torres, E. Solid-state fermentation increases secretome complexity in Aspergillus brasiliensis. Fungal Biol. 2020, 124, 723–734. [Google Scholar] [CrossRef]
  63. Hyseni, B.; Aytekin, A.Ö.; Nikerel, E. Solid state fermentation for enzyme production for food industry. J. Microbiol. Biotechnol. Food Sci. 2018, 7, 615–622. [Google Scholar] [CrossRef]
  64. Costa, J.A.V.; Treichel, H.; Kumar, V.; Pandey, A. Advances in Solid-State Fermentation. In Current Developments in Biotechnology and Bioengineering; Elsevier: Amsterdam, The Netherlands, 2018; pp. 1–17. [Google Scholar]
  65. Kumar, A.; Kanwar, S. Lipase production in solid-state fermentation (SSF): Recent developments and biotechnological applications. Dyn. Biochem. Process Biotechnol. Mol. Biol. 2012, 6, 13–27. [Google Scholar]
  66. Moran-Aguilar, M.G.; Costa-Trigo, I.; Calderón-Santoyo, M.; Domínguez, J.M.; Aguilar-Uscanga, M.G. Production of cellulases and xylanases in solid-state fermentation by different strains of Aspergillus niger using sugarcane bagasse and brewery spent grain. Biochem. Eng. J. 2021, 6, 13–27. [Google Scholar] [CrossRef]
  67. Terrasan, C.R.F.; Carmona, E.C. Solid-state fermentation of brewer’s spent grain for xylanolytic enzymes production by penicillium janczewskii and analyses of the fermented substrate. Biosci. J. 2015, 31, 1826–1836. [Google Scholar] [CrossRef] [Green Version]
  68. Tišma, M.; Jurić, A.; Bucić-Kojić, A.; Panjičko, M.; Planinić, M. Biovalorization of brewers’ spent grain for the production of laccase and polyphenols. J. Inst. Brew. 2018, 124, 182–186. [Google Scholar] [CrossRef] [Green Version]
  69. Martínez-Avila, O.; Muñoz-Torrero, P.; Sánchez, A.; Font, X.; Barrena, R. Valorization of agro-industrial wastes by producing 2-phenylethanol via solid-state fermentation: Influence of substrate selection on the process. Waste Manag. 2021, 121, 403–411. [Google Scholar] [CrossRef]
  70. da Silva, L.R.I.; de Andrade, C.J.; de Oliveira, D.; Lerin, L.A. Solid-state fermentation in brewer’s spent grains by fusarium fujikuroi for gibberellic acid production. Biointerface Res. Appl. Chem. 2021, 11, 13042–13052. [Google Scholar] [CrossRef]
  71. Francis, F.; Sabu, A.; Madhavan Nampoothiri, K.; Szakacs, G.; Pandey, A. Synthesis of α-amylase by Aspergillus oryzae in solid-state fermentation. J. Basic Microbiol. 2002, 42, 320–326. [Google Scholar] [CrossRef]
  72. Assandri, D.; Pampuro, N.; Zara, G.; Cavallo, E.; Budroni, M. Suitability of composting process for the disposal and valorization of brewer’s spent grain. Agriculture 2021, 11, 2. [Google Scholar] [CrossRef]
  73. Landry, C. Beer for Bessie. Available online: https://www.perc.org/2002/12/01/beer-for-bessie/ (accessed on 10 December 2021).
  74. Panjičko, M.; Zupančič, G.D.; Zelić, B. Anaerobic biodegradation of raw and pre-treated brewery spent grain utilizing solid state anaerobic digestion. Acta Chim. Slov. 2015, 62, 818–827. [Google Scholar] [CrossRef] [PubMed] [Green Version]
Figure 1. Simplified scheme of the brewing process, focusing on the brewers’ spent grains, their composition and utilization [2,10,11].
Figure 1. Simplified scheme of the brewing process, focusing on the brewers’ spent grains, their composition and utilization [2,10,11].
Fermentation 08 00050 g001
Figure 2. Lignocellulosic biomass pretreatment methods [21,22].
Figure 2. Lignocellulosic biomass pretreatment methods [21,22].
Fermentation 08 00050 g002
Publisher’s Note: MDPI stays neutral with regard to jurisdictional claims in published maps and institutional affiliations.

Share and Cite

MDPI and ACS Style

Mitri, S.; Salameh, S.-J.; Khelfa, A.; Leonard, E.; Maroun, R.G.; Louka, N.; Koubaa, M. Valorization of Brewers’ Spent Grains: Pretreatments and Fermentation, a Review. Fermentation 2022, 8, 50. https://0-doi-org.brum.beds.ac.uk/10.3390/fermentation8020050

AMA Style

Mitri S, Salameh S-J, Khelfa A, Leonard E, Maroun RG, Louka N, Koubaa M. Valorization of Brewers’ Spent Grains: Pretreatments and Fermentation, a Review. Fermentation. 2022; 8(2):50. https://0-doi-org.brum.beds.ac.uk/10.3390/fermentation8020050

Chicago/Turabian Style

Mitri, Sara, Sarah-Joe Salameh, Anissa Khelfa, Estelle Leonard, Richard G. Maroun, Nicolas Louka, and Mohamed Koubaa. 2022. "Valorization of Brewers’ Spent Grains: Pretreatments and Fermentation, a Review" Fermentation 8, no. 2: 50. https://0-doi-org.brum.beds.ac.uk/10.3390/fermentation8020050

Note that from the first issue of 2016, this journal uses article numbers instead of page numbers. See further details here.

Article Metrics

Back to TopTop