1 Introduction

Agriculture has become an important resource to contribute to reducing poverty and improving the life standard of the world population with the encouragement of Food and Agricultural Organization (FAO) since 1945 [1]. Cereals (such as wheat, corn, rice, oats) are used as a traditional food source (such as flour) as well as in the preparation of new generation foods for nutrition [2]. Food by-products (husks and straws) rich in lignocellulose are generated during the processing of these cereals in food industries. Among them, 11 million tons of oats are grown worldwide, and oat husk containing high sugar content (2.75–3.3 million tons) are produced by the processing of oats [3, 4]. Lignocellulosic materials, including agricultural wastes and by-products, serve as a cheap and abundant feedstock. The discharge of these agricultural residues/by-products to the environment without treatment can pose a serious problem regarding environmental pollution due to their rich content (lignin, cellulose, hemicellulose, protein and starch) [5]. However, lignocellulosic compounds can be converted into a wide variety of value-added products (biogas, bioethanol, acetone, butanol, enzyme, etc.) by microbial fermentation [6,7,8,9]. The use of lignocellulosic substrates in bioprocesses not only provides alternative substrates but also helps to solve pollution problems by their disposal [9, 10]. Recovery of lignocellulosic materials to the biorefinery requires a pretreatment step to remove the lignin barrier and recover the cellulose and hemicellulose fractions [11].

Pretreatment, i.e., conversion to fermentable sugar production, is one of the most important steps in converting lignocellulosic materials into valuable microbial products. Pretreatment strategies can be carried out by using the different methods such as physical, chemical, enzymatic or biological, or a combination of these [12]. Among the pretreatment methods, organosolv pretreatment can be considered advantageous as it can split lignocellulose into three high purity streams, namely, rich in glucan-, lignin-, and hemicellulose compounds fractions (Scheme 1) [5, 13, 14]. Although ionic liquids and deep eutectic solvents have been also used to obtain cellulose and lignin from lignocellulosic material, various types of cellulose (Avicel, microcrystalline cellulose (MCC), pre-hydrolysis sulfate pulp, α-cellulose) are obtained. These differences change the characterization of cellulose as well as their molecular weight and morphology. On the other hand, this method does not guarantee high lignin extractability from lignocellulosic biomass [15]. Additionally, this technology suffers from high operating costs and the large amounts of water used. During biomass conversion, some degradation compounds considered toxic to microbial growth might be released from polysaccharides (e.g., furfural) and lignin (e.g., ferulic acid) [16]. Alternatively, the organosolv process can be considered as a promising method with its low chemical cost, easy recovery of solvents used at the end of the process, and providing high-quality glucan and lignin recovery [13]. The fractions of the organosolv treatment can be utilized for second-generation ethanol production and biomass production through filamentous fungi or baker’s yeast, and the integration of these streams to plant also brings a net profit to the related production facility [17]. Filamentous fungal biomass, which can be obtained from a variety of substrates, can be normally used as an animal feed or food source with its high protein, essential amino acids, polyunsaturated fatty acids, vitamins, chitin/chitosan, and minerals contents [18]. Altogether, the potential of filamentous fungi as an alternative protein source needs to be investigated for the use of substrates such as glucan and hemicellulose fractions obtained by organosolv.

Scheme 1
scheme 1

Schematic representation of organosolv treatment of oat husk

Sulfuric acid is mostly used to acidify the solvent in organosolv treatments [5, 14, 19,20,21]. However, its use in applications is limited due to its toxic, corrosive, dangerous, and inhibitory properties [22, 23]. Compared to sulfuric acid, phosphoric acid is advantageous to use because it has low corrosion effects, is less hazardous, and is low cost [24, 25]. More environmentally friendly organic acids (such as acetic acid, formic acid, and oxalic acid) can also be performed as catalyst [26, 27]. Among them, oxalic acid is of biological origin, which attracts attention due to its strong acidity and good complexing ability. Oxalic acid can not only be produced through microbial fermentation but also easily degraded compared to sulfuric acid [28]. Moreover, oxalic acid has the advantage of exhibiting less inhibitors and higher catalytic activity [29, 30]. In a previous study conducted by Chopda et al. [5], ethanol acidified with sulfuric acid was studied as a solvent in organosolv treatment to obtain high purity lignin and glucan fractions from oat husk. As a continuation of this study, it was aimed to determine the potential effects of different catalysts (oxalic acid as an organic acid and phosphoric acid as a mineral acid) as an alternative to conventional sulfuric acid. In addition, the effects of the initial amount of substrate, solid-to-liquid ratio, and the amount of washing solutions used on glucan and lignin yields were investigated by using organic oxalic acid. Then, fungal biomass production was evaluated through Aspergillus oryzae and Neurospora intermedia cultivated in the organosolv fractions which give the highest glucan yield, so that fungal biomass could be evaluated in feed/food applications. Furthermore, the products obtained by organosolv treatment have been elaborated on how these can be evaluated in biorefinery.

2 Materials and methods

2.1 Substrate

The oat husk (1 cm length and 0.2 cm thickness) obtained from Lantmännen Agroethanol AB (Norköping, Sweden) was used as substrate for organosolv pretreatment. The glucan and lignin contents of oat husk were 24.78 ± 0.88 and 21.59 ± 0.35% (g/g), respectively [5].

2.2 Pretreatment

The oat husk was pretreated in acidified ethanol solution (50%, v/v) using 150-mL tubular stainless-steel reactors (Swagelok, El Paso, TX, USA). The effects of acid catalyst (sulfuric acid, phosphoric acid, and oxalic acid), initial amount of the substrate, and solid-to-liquid ratio (S/L; 1:2, 1:1, and 2:1, w/v) were studied. The reactors were placed in an oil bath (Bridge Mounted Circulator SE-Z, Julabo, Seelbach, Germany) and incubated for 90 min at 210 °C under static conditions [5]. Experiments were conducted using one factor strategy at a time.

After the incubation in the oil bath, the reactors were transferred to a container with ice and allowed to cool. The pretreated substrate from the cooled reactors was poured into a sieve (0.25 mm2 pore size) to separate it into solid (glucan-rich) and liquid (solvent, lignin-rich, and hemicellulose-rich) phases (Scheme 1). The solid phase was washed with 28.3 mL of solvent/g of dry sample. This solvent was collected and then mixed with liquor. To precipitation of lignin, 56.6 mL of water/g of dry sample was added to the liquor [5, 14]. Then, the liquor was filtered by using a vacuum filtration to separate lignin-rich fraction and hemicellulose-rich fraction (Scheme 1). In addition, the effects of the amount of solvent and water (reducing water washing 50%, reducing solvent washing 50%, and reducing both water washing 50% and solvent washing 50%) used for glucan and lignin recovery were also examined. All fractions were kept in the refrigerator at 4 °C until use. All cultivations were carried out in duplicate.

2.3 Enzymatic hydrolysis

Fractions rich in glucan and rich in hemicellulose compounds obtained in the best conditions were mixed and then evaporated using a rotary evaporator (LABO ROTA 20, Heidolph, Schwabach, Germany) at 110 °C, 40 rpm, and at a vacuum pressure of 100 mPa. The enzyme cocktail Cellic® Ctec3 (Novozymes, Denmark), with an activity of 222 filter paper units (FPU)/mL, was used at an enzyme loading of 10 FPU/g glucan [5, 14]. The enzymatic hydrolysis experiments were carried out in 250-mL sterile Erlenmeyer flasks containing 100 mL of the mixture adjusted to pH 5.2, which were incubated at 50 °C for 48 h using a shaking water bath at 125 rpm. Hydrolysed substrates were used for fungal cultivation at the end of the enzymatic hydrolysis.

2.4 Fungal cultivation

In this work, Aspergillus oryzae var. oryzae CBS 819.72 and Neurospora intermedia CBS 131.92 were used for fungal cultivation. The fungal strains were maintained on PDA (Potato Dextrose Agar; 4 g/L potato extract, 20 g/L glucose, and 15 g/L agar) medium agar. The agar plates were inoculated with 100 µL spore solution which was evenly distributed onto the agar surface with another L-shape spreader. Then, the inoculated plates were incubated at 30 °C for 3 days and then stored at 4 °C until use.

Fungal cultivations were performed by using 250 mL wide-neck Erlenmeyer flasks containing 100 mL of hydrolysed substrates. Each flask was inoculated with 2 mL of spore solution (1.69 × 107 and 6.30 × 105 spores/mL for A. oryzae and N. intermedia, respectively), and incubated at 35 °C with orbital shaking at 125 rpm for 120 h using a water bath. At the end of the cultivation, the broth was poured into a sieve (1 mm2 pore size) and the retained fungal biomass was washed with distilled water. All cultivations were carried out in duplicate.

2.5 Analytical methods

The total solids (TS), dissolved solids (DS), and ash contents were determined according to Sluiter et al. [31]. The recovery and purity of the lignin-rich and glucan-rich fractions were also analyzed according to previous work [5]. The nitrogen content of the substrate and biomass was analyzed by using the Kjeldahl method, and the crude protein of the biomass was calculated by a factor of 6.25 [32]. The COD levels were determined using a COD Kit (Nanocolor® COD 15,000, Düren, Germany).

The HPLC system (Waters 2695, Milford, MA, USA) equipped with a refractive index detector (Waters 2414, Milford, MA, USA) was used for determining the sugars, acids, and alcohols. The determination of acids, alcohols, and glucose was carried out by using an analytical ion exchange column based on hydrogen ions (Aminex HPX-87H, Bio-Rad, Hercules, CA, USA) operating at 60 °C with 0.6 mL/min of 5 mM H2SO4 as the eluent.

2.6 Statistical analysis

The software Minitab17® was used for the statistical analysis of the obtained results with ANOVA (analysis of variance). Pairwise comparisons among groups of data were also carried out using the Tukey test. Significant differences were considered at p-value < 0.05 within a 95% confidence interval. All error bars and intervals presented represent two times the standard deviation.

3 Results and discussion

The oat husk was separated through acid-catalyzed ethanol organosolv pretreatment into three high-quality streams which are glucan-rich, lignin-rich, and hemicellulose compounds-rich fractions. First, the effects of phosphoric acid and oxalic acid as catalysts were investigated due to their lower corrosion and toxicity activities than sulfuric acid. Then, oxalic acid was used in all subsequent pretreatment experiments because it is an effective catalyst for glucan purity and recovery and also is known as safe organic acid. The other pretreatment factors such as acid concentration, initial amount of substrate, solid-to-liquid ratio, and amount of washing solutions (water and solvent) on lignin/glucan purity and recovery were investigated. A mixture of evaporated fractions rich in glucan and hemicellulose compounds obtained in the best pretreatment condition was evaluated for fungal biomass production.

3.1 Effects of catalyst type and concentration

In order to evaluate the effects of catalysts (sulfuric acid, phosphoric acid, and oxalic acid) in ethanol organosolv pretreatment of oat husk, such parameters of 36.36 initial substrate amount, 1:2 solid-to-liquid ratio, 210 °C, and 90 min were used [5]. All three different acids were treated with solvent such that their initial pH values were adjusted to 3.00 (Fig. 1a, b) or their acid concentrations (0.0001428 g acid/g sample) were the same (Fig. 1c, d). Different types of acid catalysts (pH 3.0) had no significant effect on lignin purity, lignin recovery, and glucan purity (Fig. 1a, b). Similarly, Mondylaksita et al. [14] reported that different acids (sulfuric acid and acetic acid) as catalysts did not affect the lignin purity in their organosolv treatment; however, acetic acid could be considered as a more efficient catalyst regarding the lignin recovery. In this study, it was also determined that there was a statistically significant increase in glucan recovery with phosphoric acid and oxalic acid compared to sulfuric acid (p = 0.014, Fig. 1b). Dicarboxylic organic acids can hydrolyse polymers of β-(1, 4)-glycosidic bonds more than sulfuric acid at equivalent solution pH [33, 34]. Similarly, oxalic acid was found to be more effective than sulfuric acid in the hydrolysis of substrates such as beech and bamboo [35, 36].

Fig. 1
figure 1

Effect of the catalyst type (sulfuric, phosphoric, and oxalic acid) on the yields of lignin purity and recovery and glucan purity and recovery. a and b represent the initial pH of the solvents as 3.0 (at different acid concentrations); c and d represent the initial pH of the solvents as 3.0, 3.5, and 3.2 (at same final acid concentrations) for sulfuric, phosphoric, and oxalic acid, respectively. All experiments were performed in duplicate, and error bars indicate sample standard deviations. Different letters indicate significant (P < 0.05) differences

The initial amount of acid is one of the parameters affecting the efficiency of the organosolv pretreatment [19, 37]. Hence, in this study, the solvents were reprepared with the same amount of acid and the pH values of the solvents varied according to the amount of acid (pH values of sulfuric, phosphoric acid oxalic acids were 3.00, 3.50, and 3.22, respectively). Solvents prepared using the same amount of acid (phosphoric or oxalic acid) had a negative effect on lignin purity, although it did not make any change on lignin recovery (Fig. 1c). Similarly, concentrations only had a slight effect on the amount of lignin and pulp at values of 0.02–2 N H2SO4 for pretreating wheat straw [37]. On the other hand, it was determined that these solvents had a partially positive effect (p = 0.053) on glucan purity and recovery (Fig. 1d). The glucan fraction of the biomass may be partially hydrolysed at high acid concentrations. It was recommended that the final pH of the organosolv liquor could not be less than about 3.5 to prevent cellulose hydrolysis [38]. Yawalata and Paszner [39] also suggested that a pH between 3.8 and 4.2 could be optimal for organosolv treatment of soft wood pulping. In this study, it was found that the pH value of the solvent could be 3.5 for phosphoric acid and 3.2 for oxalic acid to obtain high glucan recovery from oat husk.

3.2 Effects of initial substrate amount and solid-to-liquid ratio

In organosolv treatment, many parameters such as solvent type and concentration, solid-to-liquid ratio, incubation time, and temperature can affect the glucan yield [13]. In addition, the use of high substrate concentration affects product quality such as surface area, pore size, and polymerization degree (DP) [40]. For oat husk’s organosolv pretreatment, two different initial substrate amounts (36.36 g vs. 18.18 g [5]) were applied using S/L of 1:2 and oxalic acid as catalyst. Reducing the initial substrate amount by half resulted in an increase in lignin and glucan recoveries by 46% and 23%, respectively (Fig. 2a, b). Here, the increased yield is likely to be achieved by increasing the amount of acid per gram substrate. In relation to this result, there was a statistically decrease in glucan recovery since the amount of acid per gram of substrate was significantly reduced with increasing of solid contents (S/L; 1:2, 1:1, 2:1) (Fig. 2d). Similar reductions in glucan yield occurred when the total amount of solvent and substrate in the reactor was made up to 50 mL (at different S/L values) (Fig. 2f). The optimum S/L ratio to recovery and purity of glucan or lignin may vary depending on the substrate used; for example, different S/L values have been suggested such as 1:2 for oat husk [5], 1:5 for cornstalk [17], 1:10 for oil palm empty fruit bunch [14], and 1:20 for horticulture [41]. In this study, the optimum parameters for oxalic acid-catalyzed glucan recovery from oat husk were 18.18 g initial substrate and 1:2 solid–liquid ratio. Organosolv treatment was continued with these optimum conditions in determining the effects of the amount of washing solution.

Fig. 2
figure 2

The yields of lignin purity and recovery and glucan purity and recovery at varying parameters: a and b represent the effects of initial amount of substrate (36.36 g and 18.18), c and d represent the effects of solid-to-liquid ratios (1:2, 1:1, and 2:1), e and f represent the effects of solid-to-liquid ratios (1:2, 1:1, and 2:1) with different initial amounts of substrate. All experiments were performed in duplicate, and error bars indicate sample standard deviations. Different letters indicate significant (P < 0.05) differences

3.3 Effects of washing amount

Solvents used in organosolv treatment processes should be removed from the system. Extraction and separation techniques are used for this, but this distillation process also affects the operating cost [42, 43]. Although the solvent can be recovered to a large extent at the end of the process, it is not economically viable for the business [41]. In addition to solvent, a large amount of water is required for the precipitation of lignin [44]. The effects of these washing solutions (water and solvent) on the purity and recovery of glucan and lignin were investigated by reducing the amount of water, solvent, and both solutions by 50%, separately. The reduction of washing solutions (water or solvent) had no adverse effect on lignin purity (72.7–79.4%, p = 0.076), while lignin recoveries were reduced from 64.4 to 27.1% (p = 0.002) (Fig. 3a). Although it was determined that the reducing amount of solvent or water by 50% reduced the glucan purity by 11.3–23.1% (Fig. 3b), these reductions were not statistically significant (p = 0.059). Similarly, the amount of washing solution had no effect on glucan recovery (p = 0.125, Fig. 3b). Since reductions in the amount of washing (water or solvent) do not affect glucan recovery, bioprocesses using glucan will therefore not be affected. To this end, Bulkan et al. [17] reported that a company producing ethanol and fungal biomass from glucan can have a 3.32-fold increase in net present value in 20 years, by reducing the amount of solvent and water in pulp washing. On the other hand, since reducing the amount of washing affects the recovery of lignin, it may also affect the usage areas of lignin and the sale price of lignin.

Fig. 3
figure 3

Effects of amount of washing solutions (A. without reduction, B. reducing water washing by 50%, C. reducing solvent washing by 50%, reducing both water and solvent washing by 50%) on a lignin purity and recovery and b glucan purity and recovery. All experiments were performed in duplicate, and error bars indicate sample standard deviations. Different letters indicate significant (P < 0.05) differences

3.4 Fungal cultivation

A mixture of fractions rich in glucan and hemicellulose compounds obtained under optimum conditions for high glucan purity and recovery was evaporated and then digested using 10 FPU of Cellic® Ctec3 enzyme per gram of glucan, for 48 h. After the enzymatic hydrolysis, this hydrolysed mixture was evaluated for fungal cultivation by A. oryzae and N. intermedia. At the end of the cultivation, biomass production and glucose consumption were not observed in the medium in which N. intermedia was inoculated. On the other hand, 4.62 (g/kg) biomass containing 10.3% protein was obtained through A. oryzae cultivation (Fig. 4a). In addition, glucose was consumed by 93.3% and 97.2% after 96 and 120 h of incubation, respectively (Fig. 4b). In contrast, Marhendraswari et al. [45] reported that the growth ability with glucose consumption of Rhizopus delemar in the substrate obtained by organosolv treatment was very slow, but the efficiency of fungal biomass was increased with additional nutrients (yeast, minerals, and trace elements). Although nutritional supplementation is not required for the cultivation of Aspergillus yielding 0.55 g biomass/g glucose, it may be necessary for the cultivation of Neurospora. However, nitrogen sources could improve amino acids, purines, pyrimidines, and enzyme cofactors syntheses for required to microbial growth [46]. Sar et al. [47] also reported that the addition of sodium nitrate as a nitrogen supplementation could reduce incubation time from 96 to 48 h and increase the protein content of biomass from 15.9 to 29.5%, whereas the supplementation did not affect the total amount of A. oryzae biomass from olive oil mill wastewater. Therefore, some additional nitrogen sources can be evaluated to shorten the incubation time and increase the amount of protein of A. oryzae.

Fig. 4
figure 4

A. oryzae cultivation on the mixture of glucan and hemicellulose compounds rich fractions obtained from organosolv pretreatment; a fungal biomass production and b consumption of glucose and other metabolites. All experiments were performed in duplicate, and error bars indicate sample standard deviations

The composition of organosolv-treated substrate was given in Table 1. After the fungal cultivation, the levels of total solids and COD were removed by 53.8% and 68.0%, respectively. Similarly, COD levels was successfully reduced when A. oryzae was cultivated on different substrates such as fish industry side-streams, olive oil mill wastewater, vinasse, and starch plant wastewater. [47,48,49,50].

Table 1 Characterization of initial substrate (the mixture of glucan and hemicellulose compounds rich fractions) and the remaining stream following cultivation of A. oryzae and biomass separation

3.5 Biorefinery of organosolv treated fractions

A total of 247.8 kg of glucan and 215.9 kg of lignin can be theoretically obtained from 1 ton of oat husk considering the glucan and lignin contents of oat husk. According to the organosolv results obtained in this study, 244.7 to 247.8 kg of glucan (with a purity between 49 and 64%) and 58.5 to 139 kg of lignin (with a purity between 72 and 79%) can be obtained depending on the amount of washing solutions. Then, the mixture of glucan and hemicellulose rich fractions was used for the cultivation of A. oryzae and theoretically yielded 105.4 kg of dried biomass from 1 ton of oat husk. The obtained biomass can be evaluated as an animal feed additive or as a high-quality feed or food by increasing the protein content. It can be mixed with different nitrogen-rich substrates (e.g., thin stillage, fish industry wastes [17, 32, 48]) to increase the protein content of the biomass, and then the mixture streams integrated into fungal biomass production facilities. Besides the potential for biomass production, organosolv fractions can also be used to produce some value-added products (Fig. 5) and contribute to the integrated production facilities [13, 17, 51, 52]. Furthermore, the use of ethanol as a solvent facilitates the possibility of process integration in ethanol plants, and the recovery of ethanol from organosolv treatment benefits the existing equipment in the ethanol plant [5, 17].

Fig. 5
figure 5

Potential uses of fractions (glucan, hemicellulose, and lignin) obtained after organosolv pretreatment in biorefinery

Lignin is also an attractive material to produce biofuels, carbon fibers, thermoplastic compounds, bio-based binding agent, and polyurethane foams (reviewed in [13, 53, 54]). On the other hand, lignin can be commercially sold and costs between 0.6 and 1.0 dollars per kilogram depending on its purity [17]. Conversion of lignin to biofuels/biochemicals or its commercial sale will provide additional income or energy savings for the facility.

4 Conclusions

In this study, the use of oxalic acid as a catalyst in the organosolv process was effective in glucan purity and recovery, and it was also evaluated as an alternative to conventional sulfuric acid as it is known as a safe organic acid. Initial substrate amount and solid-to-liquid ratio were found to be critical parameters on yields of glucan recovery. On the other hand, reducing the amount of washing solutions (water and solvent) affected the lignin recovery efficiency but not the glucan recovery efficiency. With glucan recovery, it was determined that 244.7 kg of glucan and then 105.4 kg of fungal biomass could be obtained per ton by treating the oat husk with organosolv pretreatment. The results showed that the organosolv fractions could be potentially used in biorefinery to produce fungal biomass. Further research including large-scale reactor and techno-economic analysis may also be carried out.