Next Article in Journal / Special Issue
Breaking the Mold: Towards Rapid and Cost-Effective Microbial Contamination Detection in Paints and Cosmetics Using ATP-Bioluminescence
Previous Article in Journal
Biogenic Amine Formation in Artisan Galotyri PDO Acid-Curd Cheeses Fermented with Greek Indigenous Starter and Adjunct Lactic Acid Bacteria Strain Combinations: Effects of Cold (4 °C) Ripening and Biotic Factors Compromising Cheese Safety
Previous Article in Special Issue
PluMu—A Mu-like Bacteriophage Infecting Actinobacillus pleuropneumoniae
 
 
Font Type:
Arial Georgia Verdana
Font Size:
Aa Aa Aa
Line Spacing:
Column Width:
Background:
Article

Green Macroalgae Hydrolysate for Biofuel Production: Potential of Ulva rigida

1
National Top School of Chemistry Rennes (ENSCR), CNRS, Institut des Sciences Chimiques de Rennes (ISCR)—UMR 6226, University of Rennes, 35000 Rennes, France
2
Unilasalle-Ecole des Métiers de l’Environnement, Cyclann, Campus de Ker Lann, 35170 Bruz, France
3
Centre D’étude et de Valorisation des Algues, Presqu’ile de Pen Lan BP3, 22610 Pleubian, France
*
Authors to whom correspondence should be addressed.
Appl. Microbiol. 2024, 4(2), 563-581; https://doi.org/10.3390/applmicrobiol4020039
Submission received: 8 February 2024 / Revised: 1 March 2024 / Accepted: 4 March 2024 / Published: 22 March 2024

Abstract

:
In this study, the green macroalgae Ulva rigida, which contains 34.9% carbohydrates, underwent treatment with commercial hydrolytic enzymes. This treatment yielded a hydrolysate that contained 23 ± 0.6 g·L−1 of glucose, which was subsequently fermented with Saccharomyces cerevisiae. The fermentation process resulted in an ethanol concentration of 9.55 ± 0.20 g·L−1. The optimal conditions for ethanol production by S. cerevisiae were identified as follows: non-sterilized conditions, an absence of enrichment, and using an inoculum size of 118 mg·L−1. Under these conditions, the fermentation of the green macroalgal hydrolysate achieved a remarkable conversion efficiency of 80.78%. The ethanol o/t ratio, namely the ratios of the experimental to theoretical ethanol produced, for Scheffersomyces stipitis, Candida guilliermondii, Kluyveromyces marxianus, and S. cerevisiae after 48 h of fermentation were 52.25, 63.20, 70.49, and 82.87%, respectively. Furthermore, S. cerevisiae exhibited the best outcomes in terms of ethanol production (9.35 g·L−1) and conversion efficiency (80.78%) after 24 h (optimal time) of fermentation.

1. Introduction

Over the past few years, research has shifted towards high-tech alternate fuels in response to the ongoing consumption of fossil fuels, which has resulted in the depletion of these resources [1]. The role of fossil fuels is very important in energy sectors and the global economy [2,3], covering about 80–88% of the basic requirements [4,5]. This resource is recognized as non-sustainable as it contributes to the accumulation of greenhouse gases in the atmosphere, leading to global warming [6,7].
The depletion of fossil fuels not only raises their costs but also plays a role in global climate changes, contributing to increased carbon dioxide (CO2) emissions [8]. This has spurred the necessity for alternate energy sources, prompting the development of biofuels in a bio-economical context [9,10]. Bioethanol has been considered to be an ideal candidate and a clean alternative fuel compared to fossil fuels [11,12]. It can be produced from many different biomass feedstocks, like date syrup [13], sugar cane, or corn starch (first-generation ethanol, 1G) [14,15]. However, due to the competition with feed production, the use of these resources for bioethanol production is limited. Indeed, using land plants for the manufacturing of alternative energy becomes a problem due to competition for food resources and the resulting higher price of cereals. Besides competition with food and feed, the increased use of biomass also has effects on land use and water availability [16,17]. These limitations have led to the development of alternative feedstocks, such as lignocellulosic biomass: wood, agricultural, or forest residue (second-generation ethanol, 2G) [18]. But current technologies for lignocellulose fermentation need to overcome the cost of the complicated procedures required to release simple sugars from recalcitrant polysaccharides [19,20]. Moreover, the increasing need for energy consumption is anticipated to continue as the world population is predicted to increase. To fulfill the normal expanding demand for bioethanol, there is, therefore, a necessity to find alternative biomass sources.
Algal biomass has recently gained extensive world attention as a source of “third-generation biofuels” [21,22,23,24,25,26], due to its abundance, high photosynthetic efficiency, and production rate without the drawbacks of first- and second-generation biofuels. Initially, microalgae production with a high lipid content was conceived; however, this third biofuel generation presents some challenges in terms of production costs since it is under development. Within the third biofuel generation, a new concept can be proposed based on the use of seaweeds (macroalgae) as a promising 3G biomass material for 1G/2G “sugar-to-ethanol” processes [27,28].
Macroalgae are known to synthesize a great variety of polysaccharides, such as agar, carrageenan, or alginates, but also alkali-soluble hemicellulosic (β-(1,4)-D-glucuronan) and (β-(1,4)-D-glucoxylan) and amorphous α-cellulose with xylose residues [29,30]. It has also been reported that green algae of the Ulva type could produce ulvan, a sulfated polysaccharide mainly composed of glucuronic acid and sulfated rhamnose [31,32]. The oligosaccharides from Ulva latuca represent an important added-value income of algae biorefineries [33]. Furthermore, macroalgae have earned interest due to the absence of lignin in the cell wall, which facilitates the depolymerization of these polysaccharides [34]. After hydrolysis, a wide range of simple sugars, such as glucose, galactose, xylose, arabinose, and rhamnose, are provided [2,35]. Sugars from macroalgae could be obtained via hydrothermal systems [36]. Then, monosaccharides can serve as a substrate for bioethanol production. Macroalgae hydrolysates have already been studied with brown species such as Sargassum spp. [37] and Laminaria digitata [38], red species such as Gelidium amansii [39] and Palmaria palmata [40], and green species such as Ulva lactuca [41].
The production yields of macroalgae per unit area are significantly higher than those for terrestrial biomass [42]. Marine algae present relatively high photon conversion efficiency, enabling rapid biomass synthesis by assimilating abundant resources in nature such as sunlight, CO2, and inorganic nutrients [43,44]. Notably, this biomass also requires no agricultural input such as fertilizer, pesticides, and water. In addition, it can be cultivated both on seawater and on-shore [45], so one does not necessarily encroach on agricultural land required for food crops. Indeed, seaweed crops can be integrated into municipal, agricultural, or industrial wastewaters [46], as well as within buildings [47], or in innovative ring-shaped systems for growth improvement [48]. However, it is noteworthy that open ponds are the most widely used system for large-scale outdoor seaweed cultivation; this preference is attributed to their cost-effectiveness, simplicity in construction, and ease of operation [49]. Naturally occurring algae are very low in density and relatively poor in carbohydrates, so mass culturing in controlled environments could be an interesting solution to ensure reliable high productivity. Faced with thermal stress or nutrient starvation, seaweed species can alter their metabolic pathways towards the formation and accumulation of intracellular compounds such as carbohydrates or lipids to endure unfavorable environmental conditions [50]. In a previous study, it was reported that Ulva sp. could accumulate high carbohydrates under nitrogen starvation [51]. Therefore, controlling crop conditions emerges as a pivotal factor in enhancing carbohydrate content and, consequently, in optimizing bioethanol production.
The green macroalga Ulva sp. (Chlorophyceae) is a common seaweed abundantly found worldwide that also thrives in eutrophicated coastal waters, providing a potential aquatic energy crop due to its high potential growth rate and relatively high carbohydrate content (36%) [52,53]. Recently, the research in [54] proposed an integrated process based on the production of ethanol and greenhouse gas consumption from macroalgae Saccharina japonica.
Nevertheless, bioethanol production does not only depend on sugar availability, but also on the choice of an adequate microorganism [55,56]. Among all microorganisms utilized for bioethanol production, S. cerevisiae is the most common yeast strain studied for ethanol conversion of brown, red, and green algal hydrolysate biomass [21,40,57]. This strain has a high ethanol tolerance, but also high yields and rates of fermentation. So, this yeast strain was selected as the reference for ethanol production in this study. However, other yeast strains could be used. For example, Pichia stipitis could be interesting for xylose fermentation [58,59] and Kluyveromyces marxianus is able to ferment mixed sugars comprising glucose, galactose, xylose, arabinose, and mannose from green macroalgae [40,60]. Due to its broad substrate spectrum (glucose, galactose, xylose, mannitol, and rhamnose), Candida guilliermondii is also an interesting strain for waste valorization in ethanol [40,61,62].
Therefore, the present study seeks to establish an effective and optimized approach for bioethanol production from the green macroalgae U. rigida using S. cerevisiae at first. After the characterization of the studied algae, different hydrolysate conditioning were tested, such as mineral and nitrogen enrichment as well as sterilization methods. The presence of endogenous species and their impact on bioethanol production was also investigated. Furthermore, the impact of varying inoculum sizes and yeast strains was examined to enhance the efficiency of the process.

2. Materials and Methods

2.1. Macroalgae and Determination of Their Composition

U. rigida was provided from the Algaplus company in Portugal (Ref. Algaplus U1. 2915.F; Ref. CEVA 2015-NV-381, Ílhavo, Portugal). Seaweed was cultivated in commercial outdoor open ponds, agitated by air injection under nitrogen starvation conditions for 21 days, by interrupting water renewal to increase the carbohydrate fraction. During cultivation, an increase from 7 to 24% dry matter (DM) of glucose content was observed due to intracellular production of starch under stress conditions. The seaweed samples underwent several processing steps; they were frozen, then subsequently thawed. Once thawed, the seaweed was milled using an URSCHEL machine (Urschel, Tiel, The Netherlands), resulting in fragments of about 2 cm in size. Dry matter was determined according to the gravimetric method by drying the macroalgae at 103 °C until all moisture had evaporated. Measurement of ash was made according to the reference standard NF V 18-101. Fibers were determined according to the Association of Official Analytical Chemist (AOAC) enzymatic–gravimetric method of [63]. Total Kjeldahl nitrogen (TNK) was measured using the normalized, regulation 152/2009 and a conversion factor of 6.5 was used (N × 6.5) to estimate the protein content [64].
A turbidimetric method was used for measuring total sulfates. A solution of barium chlorides and gelatin were added to a solution of sulfates in an acid medium, leading to a precipitate of the barium sulfate formed by the association of one mole of Ba2+ ions and one mole of SO42− [65].

2.2. Microorganisms and Inoculum Preparation

The yeast S. cerevisiae CLIB 95 was obtained from the CIRM (Centre National de Ressources Microbiennes, Marseille, France). Scheffersomyces stipitis 3651, Candida guilliermondii 11947, and Kluyveromyces marxianus 11954 were obtained from DSMZ in Germany. Stock cultures were maintained on Petri dishes and the medium composition was (in g·L−1): glucose, 10; peptone, 5; yeast extract, 3; malt extract, 3; and agar, 15. Cultures were maintained at 28 °C for 24 h and then stored at 4 °C. The inoculum preparation was well described by [66].

2.3. Endogenous Biomass Identification

Endogenous strains were isolated from algal hydrolysate as follows: after 48 h of incubation at 180 rpm and 28 °C, 1 mL of hydrolysate was resuspended in 9 mL KCl sterilized (150 mM), then diluted in cascade and seeded in a Sabouraud medium. Characterization of the isolated strain was realized by matrix-assisted laser desorption ionization–time of flight mass spectrometry (MALDI-TOF) Labocea (Fougères, France) [67].

2.4. Preparation of Algal Hydrolysates

The hydrolysis of algae was carried out in a pilot (Brouillon process) with 34.45 kg of defrosted Ulva biomass (20.8% dry matter). The biomass was added into 120 L concentration vessel containing water to obtain a 10% dry matter suspension and heated at 60 °C. The pH was adjusted at 5.5 by the addition of HCl (1 M). The gelatinization step was achieved by stirring and heating the biomass at 100 °C for 30 min. After cooling at room temperature, amylase enzyme was added in the reaction medium at 2.9% level based on the dry weight (DW) of starch, and then kept at 85 °C for 2 h to carry out the liquefaction step. Amyloglucosidase enzyme was added at 11.6% level based on the DW of starch and they were heated at 65 °C for 2 h under stirring to achieve the scarification step. Enzymes were deactivated by heating the mixture at 100 °C for 30 min. After they were cooled at 60 °C, the suspension was then transferred into a 100 L reactor. The pH was then adjusted to 0.88 using sulfuric acid 96%. To allow hydrolysis of co-extracted ulvans, the mixture was heated at 70 °C for 6 h, before being cooled at 40 °C to limit viscosity of the reaction mixture. pH was then adjusted to 5.0 by adding Na2CO3. Finally, the hydrolysate residues smaller than 11 µm sieve was recovered by filtration (Sweco Separator, Sweco, Nivelles, Belgium). The hydrolysate was autoclaved at 120 °C for 15 min, and the analysis of the biochemical composition of autoclaved and non-autoclaved hydrolysates was outsourced to the laboratory Agrobio (Vezin-le-Coquet, Brittany, France). Hydrolysate enrichment was carried out with NH4Cl (1.07 g·L−1) or peptone (5 g·L−1).

2.5. Synthetic Medium

A synthetic medium was used as a model for the comparison to the hydrolysate-based medium. Its composition was a simple sugar (glucose) and salts at levels close to those found in the green algae U. rigida (NaCl, 0.25 M and SO42−, 0.21 M). This medium was enriched with peptone (5 g·L−1) (source of nitrogen) and with mineral supplementation as described by [66].

2.6. Ethanol Fermentation

A rotating shaker (New Brunswick, INNOVA 40, Shirley, NJ, USA) was used for ethanol production assays at 180 rpm, 28 °C. The volume of the culture media was 250 mL and the culture time was 48 h. Inoculation levels were 0.1% or 1% (v/v). Samples were regularly withdrawn and centrifuged at 3000 rpm, 4 °C and 5 min. All experiments were duplicated. Fermentation efficiency corresponded to the ratio of the ethanol produced over the ethanol theoretically produced ratio ((Ethanol) o/t).
( E t h a n o l ) t h e o r = 2 × ( g l u c o s e ) × M e t h a n o l M g l u c o s e ;   E t h a n o l o / t = ( e t h a n o l ) o b s e r v e d ( e t h a n o l ) t h e o r
E f f i c i e n c y = P r a t i c a l   y i e l d   o f   e t h a n o l T h e o r e t i c a l   y i e l d × 100

2.7. Analytical Methods

Analysis of total sugars and free sugars was determined using HPLC with an apolar column C18 after degradation of the polysaccharides by acidic methanolysis. Free sugar content was determined by the HPLC method with a column Rezex pb2+. The HPLC involving an ion exclusion column HPX-87H (300 × 7.8 mm; Bio-Rad, Hercules, CA, USA) was used to measure the various metabolites produced by yeast including ethanol and glycerol. The analytical conditions were well described by Djelal et al. [66]. Assay of cell growth in the samples was measured with a spectrophotometer (SECOMAM, Ales, France) at 600 nm; this assay was performed twice, just directly after the levy and then samples were centrifuged at 3000 rpm, 4 °C and 5 min; the difference between the two assays represented the cell growth. The pH was adjusted at 6 (pH meter 315i, WTW, Frankfurt, Germany) by the addition of sterile KOH 2 mol·L⁻1. The salts founded in algae were analyzed with Dionex DX 120 (ThermoFisher Scientific, Waltham, MA, USA) equipped with a conductivity detector and Anion exchange column AS19 (4 × 250 mm) as the stationary phase. KOH was used at the mobile phase and the flow rate was set at 1 mL·min⁻1. Analyses were carried out with a gradient elution mode. A simplified schematic representation for Section 2 is presented in Appendix A.

3. Results and Discussion

3.1. Global Composition of Ulva sp.

U. rigida composition was analyzed for its nitrogen and carbohydrate contents to obtain information regarding its potential as biomass for ethanol production. The global chemical composition of U. rigida is summarized in Table 1. Ulva contained an important quantity of fibers compared to other macroalgae; the fiber content reached 34.9% showing its relevance for bioenergy production [68]. The carbohydrate content of green macroalgae was 25–50% dry weight. This result is consistent with the findings of [69], who reported a carbohydrate content of 27.9 ± 0.4% in U. rigida.
Green algae contain glucans and sulfated polysaccharides (e.g., ulvan) as the major carbohydrate fraction. Ulvan is a water-soluble polysaccharide, constituted of repeated disaccharide units composed of sulfated rhamnose, glucuronic acid, iduronic acid, and xylose (Table 2). The composition of ulvan varies from one green algae to another. For example, ulvans from Ulva fasciata (U. fasciata) are mainly composed of rhamnose, xylose, and glucuronic acid [70,71]; whereas those from Ulva armoricana are mainly composed of rhamnose, glucuronic acid, and iduronic acid [32,72].
The protein content was 5.68%, which is not high compared to other green algae, for example U. fasciata, which presents a protein content of 14.4% [73]. The variation in the reported composition of Ulva species may be related to several environmental factors, such as water temperature, salinity, light, and nutrients which influence their ability to stimulate or inhibit the biosynthesis of several compounds [74].
Additionally, this macroalgae showed a high amount of ash (31.9%), which is in accordance with the usual values known for green algae ranging from 11% to 34% on a dry weight basis [69,75]. These results demonstrate that the macroalgae U. rigida are potentially good sources of polysaccharides and proteins.

3.2. Fermentation of Algal Hydrolysate with S. cerevisiae

The fermentation of the algal hydrolysate of U. rigida by S. cerevisiae with 0.1% (v/v) inoculation size was studied. The kinetics of the concentrations of glucose, ethanol, glycerol, and acetic acid during the fermentation are shown in Figure 1. Glucose was fermented in 48 h by S. cerevisiae and 9.55 g·L−1 of ethanol was produced. The concentration of glycerol and acetic acid produced increased during the fermentation and reached 1.3 and 0.36 g·L−1 at the end of the fermentation.
The results obtained in the algal hydrolysate and the synthetic model medium are compared in Figure 2, showing that S. cerevisiae produces close yields of glycerol and acetic acid but more yields of ethanol with higher efficiency (experimental ethanol yield/ theoretical ethanol yield) in the algal hydrolysate than those in the synthetic medium. The ethanol yields and the efficiency were 0.44 g·g−1 (0.57 C/C) reducing sugar and 85.33%, respectively, in the algal hydrolysate, whereas 0.38 g·g−1 and 74.35% were obtained in the synthetic medium. Therefore, algal hydrolysate is a performant source of carbon and nitrogen to produce bioethanol.
If compared to the related literature, it appears that the ethanol yield found (0.44 g·g−1 reducing sugar) was superior to those from Eucheuma cottonii and Sargassum sagamianum hydrolysates (0.33 and 0.39 g·g−1 reducing sugar) [76,77]; meanwhile, it was close to some other results. Indeed, 0.43 g·g−1 was obtained during the fermentation of the red algae Gracilaria verrucosa [78].
Lee et al. [79] obtained ethanol yields of 0.43–0.44 g·g−1 reducing sugar. An ethanol yield of 0.47 g·g−1 reducing sugar was obtained during the fermentation of the algal hydrolysate of the green algae U. fasciata, corresponding to 93.81% conversion efficiency [80]. Choi et al. [81] used the glucose contained in the hydrolysate of Ulva pertusa Kjellman for bioethanol production by S. cerevisae and the concentration of ethanol was approximately 90% of the maximum theoretical ethanol yield. It can be noticed from the ethanol yield and efficiency obtained, that algal hydrolysate of U. rigida has a great potential as a raw biomass for bioethanol production.

3.3. Optimization of the Fermentation with S. cerevisiae

3.3.1. Effect of Medium Enrichment

For comparative purposes, two types of enrichment were tested; a mineral one, NH₄CL with mineral supplementation as described by [65], and an organic one, peptone. The corresponding results recorded during S. cerevisiae culture (0.1% v/v inoculum) are summarized in Table 3.
S. cerevisiae showed the same fermentation time of glucose (48 h) in the presence or absence of enrichment, even with a mineral or organic nitrogen source. Adding nitrogen had no impact on the rate of ethanol production which was 0.20 g·L−1·h−1 in all cases. Ethanol and glycerol yields were not improved by nitrogen supplementation. S. cerevisiae showed the same trend of growth regardless of the type of enrichment.
The high content of proteins and minerals in algae should account for the absence of the impact of mineral and nitrogen additional sources on S. cerevisiae growth; in fact, algae are sources of proteins [82]. The amount of proteins that can be found in the raw material may increase after hydrolysis, Hou et al. [38], who studied Laminaria digitata, found that the protein content in the solid residues after fermentation was enriched 2.7 fold, and they found that amino acids contained in peptone were also abundant in this macroalgae. Moreover, the authors of [73] found that the enrichment of culture medium with yeast extract and peptone during fermentation of U. fasciata had no impact on ethanol yields, which was supported by the high protein content of the seaweed U. fasciata, 14.4 ± 2.2% on dry basis. Therefore, the use of an additional source of nitrogen in the fermentation of algal hydrolysates is not needed. Consequently, the hydrolysate obtained after the enzymatic saccharification could be fermented directly without the addition of nitrogen sources and minerals.

3.3.2. Inoculum Size Effect

The amount of inoculum used is one of the main factors that influence fermentation, specific consumption, and production rate. The 0.1 and 1% (v/v) inoculum sizes were investigated to determine whether they could affect ethanol fermentation. Glucose was totally consumed (100%) in 24 h of fermentation in the case of 1% inoculation, whereas for the 0.1% inoculation level this percentage decreased to 58% (Table 4). Maximum ethanol productivity (0.40 g·L−1·h−1) was also obtained with 1% inoculation, leading to 9.64 g·L−1 of ethanol produced, while these results were divided by two in the case of 0.1% inoculation.
On the contrary, inoculum size did not influence ethanol yield, which was 56.19 and 55.20% (c/c) for 0.1 and 1% (v/v) inoculation levels, respectively. In terms of ratio, (Ethanol) o/t and ethanol yield 0.1 and 1% v/v inoculation showed very similar results. Many studies [83,84] have reported that the size of the inoculum enhanced the rate of 2,3-butanediol formation but not its product on carbon substrate yield. Glucose consumption rate also increased with the inoculation level; it rose from 0.54 to 0.95 g·L−1·h−1; the productivity was also influenced by the quantity of inoculated cells. However, a study of the optimization of the fermentation of glucose by Bacillus licheniformis, probably carried out using a factorial design [85], demonstrated that an increase in the size of the inoculum also had a positive effect on the yield on butanediol production. In the present work, raising the inoculation level increased the production rate, but not the amount of ethanol yield. High ethanol productivity is an economically relevant factor for an industrial purpose and hence the 1% inoculation level was selected and considered thereafter.

3.3.3. Sterilization Effect

In many microbial processes, sterilization costs impact significantly the total production cost [86]. Ethanol production under non-sterilized conditions has gained high attention for energy saving considerations. The impact of this parameter was therefore examined. S. cerevisiae was cultured in sterilized (autoclaved at 120 °C for 15 min) and non-sterilized hydrolysate with 1% (v/v) inoculum size, at pH 5. Indeed, only a very slight decrease in lipid, carbohydrate, and calcium was observed, showing the stability of the hydrolysates under the considered sterilization conditions. Ethanol o/t ratio, the ratio of the experimental to the theoretical ethanol produced, was found to be 82.7% in the sterilized medium and 80.7% in the non-sterilized medium. This slight difference was potentially caused by the small number of endogenous bacteria present in the medium due to the unsterilized conditions, which can also be the reason for the difference in growth observed in Figure 3a. Maillard reactions could be processed by the autoclave, leading to negative effects, such as the generation of undesired furfural compounds, other nutritional elements, and the degradation of sugars [87]. The glucose concentrations before and after the sterilization process were 22.75 g·L−1 and 22.65 g·L−1, respectively, showing no sugar loss and hence indicating the absence of significant impact of the Maillard reactions between glucose and nitrogen sources as often observed during culture media sterilization (Figure 3b). Regarding the ethanol concentration, it was also not significantly affected by the sterilization (Figure 3c); indeed, the ethanol concentrations were 9.99 g·L−1 and 9.59 g·L−1 in the sterilized and non-sterilized medium, respectively. It agrees with other findings [88] that demonstrated the feasibility and the potential of the non-sterile fermentation process of oil mill wastewater. Ethanol production in non-sterile fermentation by S. cerevisiae was successfully achieved in their study; no significant statistical differences were observed for both biomass and ethanol production between sterile and non-sterile cultures. Contrarily, most of the related studies found an impact of sterilization on the fermentation performances. Glucose concentration decreased by 5% after autoclaving during ethanol production by Zymomonas mobilis. This loss was attributed to the Maillard reactions between glucose and the nitrogen sources, leading to an increase in the ethanol yield for the non-autoclaved process, from 70 to 73 g·L−1 compared with the autoclaved process (fermentation at pH = 4.5); the rate of glucose utilization in the non-sterilized media was also found to be higher compared to autoclaved media [89]. The impact of the sterilization on the composition of the hydrolysate was examined, showing its negligible impact (Table 5). From non-sterile and not seeded algal hydrolysate, bacteria were isolated and identified as Pseudomonas putida, an aerobic strict, Gram-negative bacterium. This resistant microorganism could be largely encountered in soil and water. However, its impact could be neglected, since in the absence of inoculation, only 5% (result not shown) of the glucose present in the hydrolysate was consumed after 48 h. Consequently, the presence of this resistant bacterium did not significantly impact ethanol fermentation. The absence of sterilization constitutes a significant advantage to the process for its subsequent implementation on an industrial scale [89,90].

3.4. Comparison with Three Other Yeast Strains

The hydrolysate was subjected to fermentation without sterilization or enrichment and for an inoculum size of 1% (v/v). Batch cultures were carried out using four different yeasts: S. cerevisiae, K. marxianus, P. stipites, and C. guilliermondii. These yeasts have proven their relevance for ethanol fermentation from various biomasses [77,91,92]. Fermentation of the algal hydrolysate using the four yeasts was compared to synthetic medium to demonstrate the potentiality of the algal hydrolysate in the production of ethanol. The glucose consumption from algal hydrolysate varied according to the evaluated yeast. Glucose was completely consumed after 24 h by S. cerevisiae and K. marxianus; meanwhile, after 48 h, C. guilliermondii consumed 74.95% of the glucose present in the hydrolysate, and P. stipitis showed a slow consumption, only 22% of the available glucose (Figure 4a). Because of the differences in glucose consumption, bioethanol production varied for each yeast (Figure 4b), and the four yeasts can be classified according to the level of ethanol production as follows: S. cerevisiae > K. marxianus > C. guilliermondii and P. stipitis. S. cerevisiae exhibited the highest and fastest growth, because of its higher and faster consumption of sugars compared to the other strains; despite its low glucose consumption, the growth observed for P. stipitis was like that observed for C. guillermondii and K. marxianus (Figure 4c). For S. cerevisiae and K. marxianus, after 22 h of fermentation, all the glucose was depleted and ethanol production ceased after 28 h of culture, while growth continued until the end of fermentation (48 h). This can be caused by the richness of proteins and vitamins of the algal hydrolysate. As regards the ethanol o/t ratio, the results were found to be maximal with S. cerevisiae with a value of 82.87% after 48 h of fermentation; meanwhile, K. marxianus and C. guillermondii showed 70.49 and 63.20%, respectively, and only 52.25% for P. stipitis (Table 6).
Moreover and unlike the other strains, P. stipitis displayed a very low ethanol production rate and glucose consumption rate in the algal hydrolysate if compared to the other strains; this should be related to the sensibility of this strain to the aeration conditions and its need for a micro-oxygenation of the medium, essentially given by a high agitation [93]. Studies [94,95] have shown that oxygen concentration is an important factor for P. stipitis to ferment glucose and xylose into ethanol. Under anaerobic conditions, P. stipitis cells suffered a decrease in ethanol yield and fermentation rate [96]. The algal hydrolysate of U. rigida contains glucose as the main sugar, and P. stipitis is recognized for its higher ethanol productivity growing on glucose than on xylose [97]; for that, it was chosen for this study. But the aeration conditions applied for the fermentation were not appropriate for ethanol production by P. stipitis.
In addition, a decrease in the performances was observed for P. stipitis in the algal hydrolysate if compared to the synthetic medium; the glucose consumption rate decreased from 0.10 to 0.03 g·L−1·h−1 and ethanol production rate was divided by four. On the other hand, a faster fermentation in the hydrolysate compared to the synthetic model medium was observed for the other strains. Rouhollah et al. [98] tested the fermentation of sugars by P. stipitis, S. Cerevisiae and K. marxianus, and observed that P. stipitis ferments glucose more slowly (30 times of fermentation) than the two other yeasts. However, in the present study, P. stipitis showed similar rates of production (approximately 0.12 g·L−1·h−1) and consumption (0.42 g·L−1·h−1) in the synthetic model medium compared to the other strains. The fermentation process was therefore affected by the composition of the algal hydrolysate; nutrients such as trace elements or vitamins can be required for P. stipitis to achieve rapid fermentation, or the presence of some inhibitors have decreased the rate of production of ethanol and consumption of glucose by P. stipitis.
Based on ethanol yields, namely ethanol produced over glucose consumed (expressed in carbon/carbon), the results were as follows: S. cerevisiae (55% C/C) > K. marxianus (47%) > C. guilliermondii (42% C/C) > P. stipitis (35%) (Figure 5). From this, S. cerevisiae appeared to be the most promising candidate for the valorization of glucose contained in algal hydrolysates. It should be noted that during fermentation acetic acid and glycerol were secreted by the yeasts. For acetic acid yields, S. cerevisiae was found to be the highest producer with (3% C/C), whereas P. stipitis did not produce this acid. Contrarily, this latter species produced the highest yields of glycerol, 8% C/C; while S. cerevisiae, K. marxianus, and C. guilliermondii produced 6, 3, and 1% C/C, respectively. This high glycerol yield showed an attempt to adapt their metabolism to the algal hydrolysate.
S. cerevisiae, C. guilliermondii, and K. marxianus were therefore able to ferment algal hydrolysate and produce ethanol, as well as P. stipitis but at a lower production rate. S. cerevisiae showed relevant results, in agreement with the related literature. Indeed, some studies [99] have reported that S. cerevisiae was able to produce 7.2 g·L−1 of ethanol by fermenting Ulva pertusa hydrolysate. Furthermore, some research [100] recorded high levels of ethanol produced by a wild S. cerevisiae strain growing on Sargassum spp. hydrolysate based on glucose as substrate. To save time, the fermentation was stopped at 24 h and despite this, S. cerevisiae, the most studied for ethanol conversion of cellulosic and lignocellulosic biomass [101,102], still gave the best results in terms of ethanol produced (9.35 g·L−1) and conversion efficiency (80.78%).

3.5. Comparison of Ethanol Yields for Different Green Algal Feedstocks

The culture performances achieved with S. cerevisiae (1% v/v inoculum, non-sterilized, and non-enriched hydrolysate) were compared to the performances reported for various algal feedstocks (Table 7). The ethanol yield obtained in this study (0.41 g·g−1) exceeded the values reported for the green seaweed U. rigida by [103] and [52], which were 0.37 g·g−1 and 0.33 g·g−1, respectively. Similarly, it outperformed the red seaweed Kappaphycus alvarezii (0.39 g·g−1) despite using the same S. cerevisiae strain, enriching the algal hydrolysate, and employing a higher inoculum size [104]. This result was in agreement with other findings [105] during the fermentation of the green algae Chaetomorpha linum (0.41 g·g−1). However, it was lower than those of other studies [78]. The potential of algal biomass appears therefore highly promising; nonetheless, it is imperative to assess the current state of the resource, considering the imperative to avoid any alteration to the biodiversity of the encompassing ecosystem.
Khambhaty and colleagues [104] estimated the ethanol production from the red algae Kappaphycus alvarezii at 2.3 kg/1000 kg fresh weight; the percentage of ethanol reached 2.46%. In the present study, ethanol production from the green algae U. rigida was estimated at 90 kg/1000 kg dry weight corresponding to an ethanol content of 1.04%.
This comparison showed that the results of the present study were comparable to those reported in the literature; therefore, the green algae U. rigida holds potential as a feedstock for bioethanol production.
Ethanol production under non-sterilized conditions has gained the attention of many researchers since it can save 30–40% energy consumption in cooking starch and sterilization during ethanol production, which also simplifies the process [89]. In addition, nitrogen, trace elements, and vitamins are needed to achieve rapid fermentation and high levels of ethanol, but they increase production costs, especially on an industrial scale. In this study, fermentation experiments were carried out without sterilization or enrichment; so, the combination of the energy saving of the non-sterilized and non-enriched process on the one hand and the efficiency of ethanol production by S. cerevisiae on the other hand is promising for future implementation on a larger scale.

4. Conclusions

Algal seaweed exhibits significant potential as one of the most important renewable energy sources. This present study successfully demonstrated that the green algae U. rigida serves as an attractive biomass material that can be readily converted into ethanol. Following enzymatic hydrolysis, we evaluated fermentation parameters. The results indicate that the optimal conditions for the fermentation of the green macroalgal hydrolysate, resulting in an 80.78% conversion efficiency, were as follows: using S. cerevisiae under non-sterilized conditions, without enrichment, and with an inoculum size of 1% (v/v). Among the strains studied, S. cerevisiae appeared to be the most promising for fermenting algal hydrolysates.

Author Contributions

Conceptualization, A.C., W.S. and M.B.; methodology, A.C., W.S. and M.B.; validation, H.D., A.A. and R.P.; formal analysis, W.S. and M.B.; investigation, W.S., A.C. and M.B.; writing—original draft preparation, W.S., A.C. and M.B.; writing—review and editing, A.S., H.D. and A.A.; supervision, H.D., A.A. and R.P.; funding acquisition, R.P. and A.A. All authors have read and agreed to the published version of the manuscript.

Funding

This research was funded by the Agence Nationale de la Recherche (ANR) (Project ANR-14-CE05-0043– Green AlgOhol, Programme Grands Défis Sociétaux 2014).

Data Availability Statement

Data are contained within the article.

Acknowledgments

The authors extend their gratitude to M.-A. Hairan from Unilasalle-EME, Rennes, France, for her valuable assistance in editing the English language.

Conflicts of Interest

The authors declare no conflicts of interest.

Appendix A

Figure A1. Simplified design for the protocol used to produce ethanol.
Figure A1. Simplified design for the protocol used to produce ethanol.
Applmicrobiol 04 00039 g0a1

References

  1. Ruangrit, K.; Chaipoot, S.; Phongphisutthinant, R.; Kamopas, W.; Jeerapan, I.; Pekkoh, J.; Srinuanpan, S. Environmental-Friendly Pretreatment and Process Optimization of Macroalgal Biomass for Effective Ethanol Production as an Alternative Fuel Using Saccharomyces cerevisiae. Biocatal. Agric. Biotechnol. 2021, 31, 101919. [Google Scholar] [CrossRef]
  2. Farobie, O.; Amrullah, A.; Anis, L.A.; Hartulistiyoso, E.; Syaftika, N.; Saefurahman, G.; Bayu, A. Valorization of Brown Macroalgae sargassum Plagiophyllum for Biogas Production under Different Salinity Conditions. Bioresour. Technol. Rep. 2023, 22, 101403. [Google Scholar] [CrossRef]
  3. Ullah, K.; Ahmad, M.; Sofia; Sharma, V.K.; Lu, P.M.; Harvey, A.; Zafar, M.; Sultana, S. Assessing the Potential of Algal Biomass Opportunities for Bioenergy Industry: A Review. Fuel 2015, 143, 414–423. [Google Scholar] [CrossRef]
  4. Demirbas, A.; Fatih Demirbas, M. Importance of Algae Oil as a Source of Biodiesel. Energy Convers. Manag. 2011, 52, 163–170. [Google Scholar] [CrossRef]
  5. Gielen, D.; Boshell, F.; Saygin, D.; Bazilian, M.D.; Wagner, N.; Gorini, R. The Role of Renewable Energy in the Global Energy Transformation. Energy Strategy Rev. 2019, 24, 38–50. [Google Scholar] [CrossRef]
  6. Arias, A.; Feijoo, G.; Moreira, M.T. Macroalgae Biorefineries as a Sustainable Resource in the Extraction of Value-Added Compounds. Algal Res. 2023, 69, 102954. [Google Scholar] [CrossRef]
  7. Bai, F.; Yan, W.; Zhang, S.; Yu, D.; Bai, L. Immobilized Lipase of Reconstructed Oil Bodies and Its Potential Application in Biodiesel Production. Fuel 2014, 128, 340–346. [Google Scholar] [CrossRef]
  8. Shah, I.H.; Manzoor, M.A.; Jinhui, W.; Li, X.; Hameed, M.K.; Rehaman, A.; Li, P.; Zhang, Y.; Niu, Q.; Chang, L. Comprehensive Review: Effects of Climate Change and Greenhouse Gases Emission Relevance to Environmental Stress on Horticultural Crops and Management. J. Environ. Manag. 2024, 351, 119978. [Google Scholar] [CrossRef]
  9. Antar, M.; Lyu, D.; Nazari, M.; Shah, A.; Zhou, X.; Smith, D.L. Biomass for a Sustainable Bioeconomy: An Overview of World Biomass Production and Utilization. Renew. Sustain. Energy Rev. 2021, 139, 110691. [Google Scholar] [CrossRef]
  10. Malla, F.A.; Bandh, S.A.; Wani, S.A.; Hoang, A.T.; Sofi, N.A. Biofuels: Potential Alternatives to Fossil Fuels. In Biofuels in Circular Economy; Bandh, S.A., Malla, F.A., Eds.; Springer Nature: Singapore, 2022; pp. 1–15. ISBN 978-981-19583-7-3. [Google Scholar]
  11. Wang, P.; Lü, X. Chapter 1—General Introduction to Biofuels and Bioethanol. In Advances in 2nd Generation of Bioethanol Production; Lü, X., Ed.; Woodhead Publishing Series in Energy; Woodhead Publishing: Salzton, UK, 2021; pp. 1–7. ISBN 978-0-12-818862-0. [Google Scholar]
  12. Loulergue, P.; Balannec, B.; Fouchard-Le Graët, L.; Cabrol, A.; Sayed, W.; Djelal, H.; Amrane, A.; Szymczyk, A. Air-Gap Membrane Distillation for the Separation of Bioethanol from Algal-Based Fermentation Broth. Sep. Purif. Technol. 2019, 213, 255–263. [Google Scholar] [CrossRef]
  13. Chniti, S.; Djelal, H.; Hassouna, M.; Amrane, A. Residue of Dates from the Food Industry as a New Cheap Feedstock for Ethanol Production. Biomass Bioenergy 2014, 69, 66–70. [Google Scholar] [CrossRef]
  14. Yue, Z.; Ma, D.; Peng, S.; Zhao, X.; Chen, T.; Wang, J. Integrated Utilization of Algal Biomass and Corn Stover for Biofuel Production. Fuel 2016, 168, 1–6. [Google Scholar] [CrossRef]
  15. Cripwell, R.A.; Favaro, L.; Viljoen-Bloom, M.; van Zyl, W.H. Consolidated Bioprocessing of Raw Starch to Ethanol by Saccharomyces Cerevisiae: Achievements and Challenges. Biotechnol. Adv. 2020, 42, 107579. [Google Scholar] [CrossRef]
  16. Barboza-Rodríguez, R.; Rodríguez-Jasso, R.M.; Rosero-Chasoy, G.; Rosales Aguado, M.L.; Ruiz, H.A. Photobioreactor Configurations in Cultivating Microalgae Biomass for Biorefinery. Bioresour. Technol. 2024, 394, 130208. [Google Scholar] [CrossRef]
  17. Renzaho, A.M.N.; Kamara, J.K.; Toole, M. Biofuel Production and Its Impact on Food Security in Low and Middle Income Countries: Implications for the Post-2015 Sustainable Development Goals. Renew. Sustain. Energy Rev. 2017, 78, 503–516. [Google Scholar] [CrossRef]
  18. Malode, S.J.; Prabhu, K.K.; Mascarenhas, R.J.; Shetti, N.P.; Aminabhavi, T.M. Recent Advances and Viability in Biofuel Production. Energy Convers. Manag. X 2021, 10, 100070. [Google Scholar] [CrossRef]
  19. Bušić, A.; Marđetko, N.; Kundas, S.; Morzak, G.; Belskaya, H.; Ivančić Šantek, M.; Komes, D.; Novak, S.; Šantek, B. Bioethanol Production from Renewable Raw Materials and Its Separation and Purification: A Review. Food Technol. Biotechnol. 2018, 56, 289–311. [Google Scholar] [CrossRef]
  20. Jatoi, A.S.; Abbasi, S.A.; Hashmi, Z.; Shah, A.K.; Alam, M.S.; Bhatti, Z.A.; Maitlo, G.; Hussain, S.; Khandro, G.A.; Usto, M.A.; et al. Recent Trends and Future Perspectives of Lignocellulose Biomass for Biofuel Production: A Comprehensive Review. Biomass Conv. Bioref. 2023, 13, 6457–6469. [Google Scholar] [CrossRef]
  21. Zhang, K.; Zhang, F.; Wu, Y.-R. Emerging Technologies for Conversion of Sustainable Algal Biomass into Value-Added Products: A State-of-the-Art Review. Sci. Total Environ. 2021, 784, 147024. [Google Scholar] [CrossRef] [PubMed]
  22. Li, L.; Ge, Y.; Xiao, M. Towards Biofuel Generation III+: A Sustainable Industrial Symbiosis Design of Co-Producing Algal and Cellulosic Biofuels. J. Clean. Prod. 2021, 306, 127144. [Google Scholar] [CrossRef]
  23. Das, P.; Chandramohan, V.P.; Mathimani, T.; Pugazhendhi, A. Recent Advances in Thermochemical Methods for the Conversion of Algal Biomass to Energy. Sci. Total Environ. 2021, 766, 144608. [Google Scholar] [CrossRef] [PubMed]
  24. Eloka-Eboka, A.C.; Maroa, S.; Behera, S. 16—Algal Biofuels—Technologies, Scope, Opportunities, Challenges, and Applications. In Sustainable Biofuels; Ray, R.C., Ed.; Applied Biotechnology Reviews; Academic Press: Cambridge, MA, USA, 2021; pp. 449–470. ISBN 978-0-12-820297-5. [Google Scholar]
  25. Kumar, M.; Sun, Y.; Rathour, R.; Pandey, A.; Thakur, I.S.; Tsang, D.C.W. Algae as Potential Feedstock for the Production of Biofuels and Value-Added Products: Opportunities and Challenges. Sci. Total Environ. 2020, 716, 137116. [Google Scholar] [CrossRef] [PubMed]
  26. Sasaki, Y.; Yoshikuni, Y. Metabolic Engineering for Valorization of Macroalgae Biomass. Metab. Eng. 2022, 71, 42–61. [Google Scholar] [CrossRef] [PubMed]
  27. Zhang, W.; Zhang, J.; Cui, H. The Isolation and Performance Studies of an Alginate Degrading and Ethanol Producing Strain. Chem. Biochem. Eng. Q. 2014, 28, 391–398. [Google Scholar] [CrossRef]
  28. Wong, K.H.; Tan, I.S.; Foo, H.C.Y.; Chin, L.M.; Cheah, J.R.N.; Sia, J.K.; Tong, K.T.X.; Lam, M.K. Third-Generation Bioethanol and L-Lactic Acid Production from Red Macroalgae Cellulosic Residue: Prospects of Industry 5.0 Algae. Energy Convers. Manag. 2022, 253, 115155. [Google Scholar] [CrossRef]
  29. Broda, M.; Yelle, D.J.; Serwańska, K. Bioethanol Production from Lignocellulosic Biomass—Challenges and Solutions. Molecules 2022, 27, 8717. [Google Scholar] [CrossRef]
  30. Stiger, V.; Bourgougnon, N.; Deslandes, E. Carbohydrates from Seaweeds. In Seaweed in Health and Disease Prevention; Academic Press: Cambridge, MA, USA, 2016; pp. 223–274. ISBN 978-0-12-802772-1. [Google Scholar]
  31. Guidara, M.; Yaich, H.; Amor, I.B.; Fakhfakh, J.; Gargouri, J.; Lassoued, S.; Blecker, C.; Richel, A.; Attia, H.; Garna, H. Effect of Extraction Procedures on the Chemical Structure, Antitumor and Anticoagulant Properties of Ulvan from Ulva Lactuca of Tunisia Coast. Carbohydr. Polym. 2021, 253, 117283. [Google Scholar] [CrossRef]
  32. Li, C.; Tang, T.; Du, Y.; Jiang, L.; Yao, Z.; Ning, L.; Zhu, B. Ulvan and Ulva Oligosaccharides: A Systematic Review of Structure, Preparation, Biological Activities and Applications. Bioresour. Bioprocess. 2023, 10, 66. [Google Scholar] [CrossRef]
  33. Andrade, C.; Martins, P.L.; Duarte, L.C.; Oliveira, A.C.; Carvalheiro, F. Development of an Innovative Macroalgae Biorefinery: Oligosaccharides as Pivotal Compounds. Fuel 2022, 320, 123780. [Google Scholar] [CrossRef]
  34. Wahlström, N.; Edlund, U.; Pavia, H.; Toth, G.; Jaworski, A.; Pell, A.J.; Choong, F.X.; Shirani, H.; Nilsson, K.P.R.; Richter-Dahlfors, A. Cellulose from the Green Macroalgae Ulva Lactuca: Isolation, Characterization, Optotracing, and Production of Cellulose Nanofibrils. Cellulose 2020, 27, 3707–3725. [Google Scholar] [CrossRef]
  35. Tan, I.S.; Lam, M.K.; Foo, H.C.Y.; Lim, S.; Lee, K.T. Advances of Macroalgae Biomass for the Third Generation of Bioethanol Production. Chin. J. Chem. Eng. 2020, 28, 502–517. [Google Scholar] [CrossRef]
  36. Morales-Contreras, B.E.; Flórez-Fernández, N.; Dolores Torres, M.; Domínguez, H.; Rodríguez-Jasso, R.M.; Ruiz, H.A. Hydrothermal Systems to Obtain High Value-Added Compounds from Macroalgae for Bioeconomy and Biorefineries. Bioresour. Technol. 2022, 343, 126017. [Google Scholar] [CrossRef] [PubMed]
  37. Kazemi Shariat Panahi, H.; Dehhaghi, M.; Aghbashlo, M.; Karimi, K.; Tabatabaei, M. Shifting Fuel Feedstock from Oil Wells to Sea: Iran Outlook and Potential for Biofuel Production from Brown Macroalgae (Ochrophyta; Phaeophyceae). Renew. Sustain. Energy Rev. 2019, 112, 626–642. [Google Scholar] [CrossRef]
  38. Hou, X.; Hansen, J.H.; Bjerre, A.-B. Integrated Bioethanol and Protein Production from Brown Seaweed Laminaria digit. Bioresour. Technol. 2015, 197, 310–317. [Google Scholar] [CrossRef] [PubMed]
  39. Cho, H.Y.; Ra, C.-H.; Kim, S.-K. Ethanol Production from the Seaweed, Gelidium amansii Using Specific Sugar Acclimated Yeasts. J. Microbiol. Biotechnol. 2014, 24, 264–269. [Google Scholar] [CrossRef] [PubMed]
  40. Kostas, E.T.; White, D.A.; Du, C.; Cook, D.J. Selection of Yeast Strains for Bioethanol Production from UK Seaweeds. J. Appl. Phycol. 2016, 28, 1427–1441. [Google Scholar] [CrossRef]
  41. Lara, A.; Rodríguez-Jasso, R.M.; Loredo-Treviño, A.; Aguilar, C.N.; Meyer, A.S.; Ruiz, H.A. Chapter 17—Enzymes in the Third Generation Biorefinery for Macroalgae Biomass. In Biomass, Biofuels, Biochemicals; Singh, S.P., Pandey, A., Singhania, R.R., Larroche, C., Li, Z., Eds.; Elsevier: Amsterdam, The Netherlands, 2020; pp. 363–396. ISBN 978-0-12-819820-9. [Google Scholar]
  42. Zhang, R.; Wang, Q.; Shen, H.; Yang, Y.; Liu, P.; Dong, Y. Environmental Benefits of Macroalgae Products: A Case Study of Agar Based on Life Cycle Assessment. Algal Res. 2024, 78, 103384. [Google Scholar] [CrossRef]
  43. Sudhakar, M.P.; Kumar, B.R.; Mathimani, T.; Arunkumar, K. A Review on Bioenergy and Bioactive Compounds from Microalgae and Macroalgae-Sustainable Energy Perspective. J. Clean. Prod. 2019, 228, 1320–1333. [Google Scholar] [CrossRef]
  44. Sun, H.; Zhao, W.; Mao, X.; Li, Y.; Wu, T.; Chen, F. High-Value Biomass from Microalgae Production Platforms: Strategies and Progress Based on Carbon Metabolism and Energy Conversion. Biotechnol. Biofuels 2018, 11, 227. [Google Scholar] [CrossRef]
  45. Kostas, E.T.; Adams, J.M.M.; Ruiz, H.A.; Durán-Jiménez, G.; Lye, G.J. Macroalgal Biorefinery Concepts for the Circular Bioeconomy: A Review on Biotechnological Developments and Future Perspectives. Renew. Sustain. Energy Rev. 2021, 151, 111553. [Google Scholar] [CrossRef]
  46. Lawton, R.J.; Cole, A.J.; Roberts, D.A.; Paul, N.A.; de Nys, R. The Industrial Ecology of Freshwater Macroalgae for Biomass Applications. Algal Res. 2017, 24, 486–491. [Google Scholar] [CrossRef]
  47. Chemodanov, A.; Robin, A.; Golberg, A. Design of Marine Macroalgae Photobioreactor Integrated into Building to Support Seagriculture for Biorefinery and Bioeconomy. Bioresour. Technol. 2017, 241, 1084–1093. [Google Scholar] [CrossRef] [PubMed]
  48. Sebök, S.; Herppich, W.B.; Hanelt, D. Development of an Innovative Ring-Shaped Cultivation System for a Land-Based Cultivation of Marine Macroalgae. Aquac. Eng. 2017, 77, 33–41. [Google Scholar] [CrossRef]
  49. Dahiya, A. Chapter 13—Algae Biomass Cultivation for Advanced Biofuel Production. In Bioenergy, 2nd ed.; Dahiya, A., Ed.; Academic Press: Cambridge, MA, USA, 2020; pp. 245–266. ISBN 978-0-12-815497-7. [Google Scholar]
  50. Elsayed, K.N.M.; Kolesnikova, T.A.; Noke, A.; Klöck, G. Imaging the Accumulated Intracellular Microalgal Lipids as a Response to Temperature Stress. 3 Biotech 2017, 7, 41. [Google Scholar] [CrossRef] [PubMed]
  51. Traugott, H.; Zollmann, M.; Cohen, H.; Chemodanov, A.; Liberzon, A.; Golberg, A. Aeration and Nitrogen Modulated Growth Rate and Chemical Composition of Green Macroalgae Ulva sp. Cultured in a Photobioreactor. Algal Res. 2020, 47, 101808. [Google Scholar] [CrossRef]
  52. Korzen, L.; Pulidindi, I.N.; Israel, A.; Abelson, A.; Gedanken, A. Single Step Production of Bioethanol from the Seaweed Ulva rigida Using Sonication. RSC Adv. 2015, 5, 16223–16229. [Google Scholar] [CrossRef]
  53. Korzen, L.; Israel, A. Growth, Protein and Carbohydrate Contents in Ulva Rigida and Gracilaria Bursa-Pastoris Integrated with an Offshore Fish Farm. J. Appl. Phycol. 2015, 28, 1835–1845. [Google Scholar] [CrossRef]
  54. Dickson, R.; Liu, J.J. A Strategy for Advanced Biofuel Production and Emission Utilization from Macroalgal Biorefinery Using Superstructure Optimization. Energy 2021, 221, 119883. [Google Scholar] [CrossRef]
  55. Su, T.; Zhao, D.; Khodadadi, M.; Len, C. Lignocellulosic Biomass for Bioethanol: Recent Advances, Technology Trends, and Barriers to Industrial Development. Curr. Opin. Green Sustain. Chem. 2020, 24, 56–60. [Google Scholar] [CrossRef]
  56. Kechkar, M.; Sayed, W.; Cabrol, A.; Aziza, M.; Ahmed Zaid, T.; Amrane, A.; Djelal, H. Isolation and Identification of Yeast Strains from Sugarcane Molasses Dates and Figs for Ethanol Production Under Conditions Simulating Algal Hydrolysate. Braz. J. Chem. Eng. 2019, 36, 157–169. [Google Scholar] [CrossRef]
  57. Dave, N.; Selvaraj, R.; Varadavenkatesan, T.; Vinayagam, R. A Critical Review on Production of Bioethanol from Macroalgal Biomass. Algal Res. 2019, 42, 101606. [Google Scholar] [CrossRef]
  58. Polprasert, S.; Choopakar, O.; Elefsiniotis, P. Bioethanol Production from Pretreated Palm Empty Fruit Bunch (PEFB) Using Sequential Enzymatic Hydrolysis and Yeast Fermentation. Biomass Bioenergy 2021, 149, 106088. [Google Scholar] [CrossRef]
  59. Phaiboonsilpa, N.; Chysirichote, T.; Champreda, V.; Laosiripojana, N. Fermentation of Xylose, Arabinose, Glucose, Their Mixtures and Sugarcane Bagasse Hydrolyzate by Yeast Pichia stipitis for Ethanol Production. Energy Rep. 2020, 6, 710–713. [Google Scholar] [CrossRef]
  60. Sayed, W.; Cabrol, A.; Abdallah, R.; Taha, S.; Amrane, A.; Djelal, H. Enhancement of Ethanol Production from Synthetic Medium Model of Hydrolysate of Macroalgae. Renew. Energy 2018, 124, 3–10. [Google Scholar] [CrossRef]
  61. Acourene, A.; Ammouche, A. Optimization of Ethanol, Citric Acid, and α-Amylase Production from Date Wastes by Strains of Saccharomyces cerevisiae, Aspergillus niger, and Candida guilliermondii. J. Ind. Microbiol. Biotechnol. 2012, 39, 759–766. [Google Scholar] [CrossRef]
  62. Cunha-Pereira, F.d.; Hickert, L.R.; Rech, R.; Dillon, A.P.; Ayub, M.A.Z.; Cunha-Pereira, F.d.; Hickert, L.R.; Rech, R.; Dillon, A.P.; Ayub, M.A.Z. Fermentation of Hexoses and Pentoses from Hydrolyzed Soybean Hull into Ethanol and Xylitol by Candida guilliermondii BL 13. Brazilian J. Chem. Eng. 2017, 34, 927–936. [Google Scholar] [CrossRef]
  63. Prosky, L.; Asp, N.G.; Schweizer, T.F.; DeVries, J.W.; Furda, I. Determination of Insoluble, Soluble, and Total Dietary Fiber in Foods and Food Products: Interlaboratory Study. J. Assoc. Off. Anal. Chem. 1988, 71, 1017–1023. [Google Scholar] [CrossRef]
  64. Sáez-Plaza, P.; Navas, M.J.; Wybraniec, S.; Michałowski, T.; Garcia Asuero, A. An Overview of the Kjeldahl Method of Nitro-gen Determination. Part II. Sample Preparation, Working Scale, Instrumental Finish, and Quality Control. Crit. Rev. Anal. Chem. 2013, 43, 224–272. [Google Scholar] [CrossRef]
  65. Anechiţei, L.; Cojocaru, T.; Munteanu, G.; Bulgariu, L. Simple Methods for Quantitative Determination of Sulphate Ions from Aqueous Media with Industrial Applications. Bull. Polytech. Inst. Jassy Constructions. Archit. Sect. 2019, 65, 27–37. [Google Scholar]
  66. Djelal, H.; Larher, F.; Martin, G.; Amrane, A. Effect of the Dissolved Oxygen on the Bioproduction of Glycerol and Ethanol by Hansenula anomala Growing under Salt Stress Conditions. J. Biotechnol. 2006, 125, 95–103. [Google Scholar] [CrossRef] [PubMed]
  67. Clark, A.E.; Kaleta, E.J.; Arora, A.; Wolk, D.M. Matrix-Assisted Laser Desorption Ionization–Time of Flight Mass Spectrometry: A Fundamental Shift in the Routine Practice of Clinical Microbiology. Clin. Microbiol. Rev. 2013, 26, 547–603. [Google Scholar] [CrossRef]
  68. Schultz-Jensen, N.; Thygesen, A.; Leipold, F.; Thomsen, S.T.; Roslander, C.; Lilholt, H.; Bjerre, A.B. Pretreatment of the Macroalgae Chaetomorpha linum for the Production of Bioethanol—Comparison of Five Pretreatment Technologies. Bioresour. Technol. 2013, 140, 36–42. [Google Scholar] [CrossRef]
  69. Nova, P.; Pimenta-Martins, A.; Maricato, É.; Nunes, C.; Abreu, H.; Coimbra, M.A.; Freitas, A.C.; Gomes, A.M. Chemical Composition and Antioxidant Potential of Five Algae Cultivated in Fully Controlled Closed Systems. Molecules 2023, 28, 4588. [Google Scholar] [CrossRef] [PubMed]
  70. Kidgell, J.T.; Magnusson, M.; de Nys, R.; Glasson, C.R.K. Ulvan: A Systematic Review of Extraction, Composition and Function. Algal Res. 2019, 39, 101422. [Google Scholar] [CrossRef]
  71. Paulert, R.; Ebbinghaus, D.; Urlass, C.; Moerschbacher, B.M. Priming of the Oxidative Burst in Rice and Wheat Cell Cultures by Ulvan, a Polysaccharide from Green Macroalgae, and Enhanced Resistance against Powdery Mildew in Wheat and Barley Plants. Plant Pathol. 2010, 59, 634–642. [Google Scholar] [CrossRef]
  72. Paradossi, G.; Cavalieri, F.; Chiessi, E. A Conformational Study on the Algal Polysaccharide Ulvan. Macromolecules 2002, 35, 6404–6411. [Google Scholar] [CrossRef]
  73. Trivedi, N.; Gupta, V.; Reddy, C.R.K.; Jha, B. Enzymatic Hydrolysis and Production of Bioethanol from Common Macrophytic Green Alga Ulva fasciata Delile. Bioresour. Technol. 2013, 150, 106–112. [Google Scholar] [CrossRef] [PubMed]
  74. Toth, G.B.; Harrysson, H.; Wahlström, N.; Olsson, J.; Oerbekke, A.; Steinhagen, S.; Kinnby, A.; White, J.; Albers, E.; Edlund, U.; et al. Effects of Irradiance, Temperature, Nutrients, and pCO2 on the Growth and Biochemical Composition of Cultivated Ulva fenestrata. J. Appl. Phycol. 2020, 32, 3243–3254. [Google Scholar] [CrossRef]
  75. Bird, M.I.; Wurster, C.M.; de Paula Silva, P.H.; Bass, A.M.; de Nys, R. Algal Biochar—Production and Properties. Bioresour. Technol. 2011, 102, 1886–1891. [Google Scholar] [CrossRef]
  76. Tan, I.S.; Lam, M.K.; Lee, K.T. Hydrolysis of Macroalgae Using Heterogeneous Catalyst for Bioethanol Production. Carbohydr. Polym. 2013, 94, 561–566. [Google Scholar] [CrossRef]
  77. Yeon, J.-H.; Lee, S.-E.; Choi, W.Y.; Kang, D.H.; Lee, H.-Y.; Jung, K.-H. Repeated-Batch Operation of Surface-Aerated Fermentor for Bioethanol Production from the Hydrolysate of Seaweed Sargassum sagamianum. J. Microbiol. Biotechnol. 2011, 21, 323–331. [Google Scholar] [CrossRef]
  78. Kumar, S.; Gupta, R.; Kumar, G.; Sahoo, D.; Kuhad, R.C. Bioethanol Production from Gracilaria verrucosa, a Red Alga, in a Biorefinery Approach. Bioresour. Technol. 2013, 135, 150–156. [Google Scholar] [CrossRef]
  79. Lee, S.-E.; Lee, J.-E.; Shin, G.-Y.; Choi, W.Y.; Kang, D.H.; Lee, H.-Y.; Jung, K.-H. Development of a Practical and Cost-Effective Medium for Bioethanol Production from the Seaweed Hydrolysate in Surface-Aerated Fermentor by Repeated-Batch Operation. J. Microbiol. Biotechnol. 2012, 22, 107–113. [Google Scholar] [CrossRef]
  80. Trivedi, N.; Reddy, C.R.K.; Radulovich, R.; Jha, B. Solid State Fermentation (SSF)-Derived Cellulase for Saccharification of the Green Seaweed Ulva for Bioethanol Production. Algal Res. 2015, 9, 48–54. [Google Scholar] [CrossRef]
  81. Choi, W.Y.; Han, J.G.; Lee, C.G.; Song, C.H.; Kim, J.S.; Seo, Y.C.; Lee, S.E.; Jung, K.H.; Kang, D.H.; Heo, S.J.; et al. Bioethanol Production from Ulva Pertusa Kjellman by High-Temperature Liquefaction. Chem. Biochem. Eng. Q. 2012, 26, 15–21. [Google Scholar]
  82. Valente, L.M.P.; Gouveia, A.; Rema, P.; Matos, J.; Gomes, E.F.; Pinto, I.S. Evaluation of Three Seaweeds Gracilaria Bursa-Pastoris, Ulva rigida and Gracilaria cornea as Dietary Ingredients in European Sea Bass (Dicentrarchus labrax) Juveniles. Aquaculture 2006, 252, 85–91. [Google Scholar] [CrossRef]
  83. Garg, S.K.; Jain, A. Fermentative Production of 2,3-Butanediol: A Review. Bioresour. Technol. 1995, 51, 103–109. [Google Scholar] [CrossRef]
  84. Grover, B.P.; Garg, S.K.; Verma, J. Production of 2,3-Butanediol from Wood Hydrolysate by Klebsiella pneumoniae. World J. Microbiol. Biotechnol. 1990, 6, 328–332. [Google Scholar] [CrossRef]
  85. Perego, P.; Converti, A.; Del Borghi, M. Effects of Temperature, Inoculum Size and Starch Hydrolyzate Concentration on Butanediol Production by Bacillus licheniformis. Bioresour. Technol. 2003, 89, 125–131. [Google Scholar] [CrossRef] [PubMed]
  86. Maiorella, B.L.; Blanch, H.W.; Wilke, C.R. Economic Evaluation of Alternative Ethanol Fermentation Processes. Biotechnol. Bioeng. 1984, 26, 1003–1025. [Google Scholar] [CrossRef] [PubMed]
  87. Sakai, K.; Ezaki, Y. Open L-Lactic Acid Fermentation of Food Refuse Using Thermophilic Bacillus coagulans and Fluorescence in Situ Hybridization Analysis of Microflora. J. Biosci. Bioeng. 2006, 101, 457–463. [Google Scholar] [CrossRef]
  88. Sarris, D.; Giannakis, M.; Philippoussis, A.; Komaitis, M.; Koutinas, A.A.; Papanikolaou, S. Conversions of Olive Mill Wastewater-Based Media by Saccharomyces cerevisiae through Sterile and Non-Sterile Bioprocesses. J. Chem. Technol. Biotechnol. 2013, 88, 958–969. [Google Scholar] [CrossRef]
  89. Tao, F.; Miao, J.Y.; Shi, G.Y.; Zhang, K.C. Ethanol Fermentation by an Acid-Tolerant Zymomonas mobilis under Non-Sterilized Condition. Process Biochem. 2005, 40, 183–187. [Google Scholar] [CrossRef]
  90. Lin, Y.; Tanaka, S. Ethanol Fermentation from Biomass Resources: Current State and Prospects. Appl. Microbiol. Biotechnol. 2006, 69, 627–642. [Google Scholar] [CrossRef]
  91. Wu, W.-H.; Hung, W.-C.; Lo, K.-Y.; Chen, Y.-H.; Wan, H.-P.; Cheng, K.-C. Bioethanol Production from Taro Waste Using Thermo-Tolerant Yeast Kluyveromyces marxianus K21. Bioresour. Technol. 2016, 201, 27–32. [Google Scholar] [CrossRef]
  92. Schirmer-Michel, Â.C.; Flôres, S.H.; Hertz, P.F.; Matos, G.S.; Ayub, M.A.Z. Production of Ethanol from Soybean Hull Hydrolysate by Osmotolerant Candida guilliermondii NRRL Y-2075. Bioresour. Technol. 2008, 99, 2898–2904. [Google Scholar] [CrossRef]
  93. Silva, V.F.; Arruda, P.V.; Felipe, M.G.; Gonçalves, A.R.; Rocha, G.J. Fermentation of Cellulosic Hydrolysates Obtained by Enzymatic Saccharification of Sugarcane Bagasse Pretreated by Hydrothermal Processing. J. Ind. Microbiol. Biotechnol. 2011, 38, 809–817. [Google Scholar] [CrossRef] [PubMed]
  94. Grootjen, D.R.J.; Meijlink, L.H.H.M.; van der Lans, R.G.J.M.; Luyben, K.C.A.M. Cofermentation of Glucose and Xylose with Immobilized Pichia stipitis and Saccharomyces cerevisiae. Enzym. Microb. Technol. 1990, 12, 860–864. [Google Scholar] [CrossRef]
  95. Hahn-Hägerdal, B.; Jeppsson, H.; Skoog, K.; Prior, B.A. Biochemistry and Physiology of Xylose Fermentation by Yeasts. Enzym. Microb. Technol. 1994, 16, 933–943. [Google Scholar] [CrossRef]
  96. Ligthelm, M.E.; Prior, B.A.; Preez, J.C. du The Oxygen Requirements of Yeasts for the Fermentation of D-Xylose and d-Glucose to Ethanol. Appl. Microbiol. Biotechnol. 1988, 28, 63–68. [Google Scholar] [CrossRef]
  97. Skoog, K.; Hahn-Hägerdal, B. Effect of Oxygenation on Xylose Fermentation by Pichia stipitis. Appl. Environ. Microbiol. 1990, 56, 3389–3394. [Google Scholar] [CrossRef] [PubMed]
  98. Rouhollah, H.; Iraj, N.; Giti, E.; Sorah, A. Mixed Sugar Fermentation by Pichia stipitis, Sacharomyces cerevisiaea, and an Isolated Xylose fermenting Kluyveromyces marxianus and Their Cocultures. Afr. J. Biotechnol. 2007, 6, 9. [Google Scholar]
  99. Yanagisawa, M.; Nakamura, K.; Ariga, O.; Nakasaki, K. Production of High Concentrations of Bioethanol from Seaweeds That Contain Easily Hydrolyzable Polysaccharides. Process Biochem. 2011, 46, 2111–2116. [Google Scholar] [CrossRef]
  100. Borines, M.G.; de Leon, R.L.; Cuello, J.L. Bioethanol Production from the macroalgae Sargassum spp. Bioresour. Technol. 2013, 138, 22–29. [Google Scholar] [CrossRef] [PubMed]
  101. Kuhad, R.C.; Mehta, G.; Gupta, R.; Sharma, K.K. Fed Batch Enzymatic Saccharification of Newspaper Cellulosics Improves the Sugar Content in the Hydrolysates and Eventually the Ethanol Fermentation by Saccharomyces cerevisiae. Biomass Bioenergy 2010, 34, 1189–1194. [Google Scholar] [CrossRef]
  102. Mishra, A.; Sharma, A.K.; Sharma, S.; Bagai, R.; Mathur, A.S.; Gupta, R.P.; Tuli, D.K. Lignocellulosic Ethanol Production Employing Immobilized Saccharomyces cerevisiae in Packed Bed Reactor. Renew. Energy 2016, 98, 57–63. [Google Scholar] [CrossRef]
  103. El Harchi, M.; Fakihi Kachkach, F.Z.; El Mtili, N. Optimization of Thermal Acid Hydrolysis for Bioethanol Production from Ulva Rigida with Yeast Pachysolen tannophilus. S. Afr. J. Bot. 2018, 115, 161–169. [Google Scholar] [CrossRef]
  104. Khambhaty, Y.; Mody, K.; Gandhi, M.R.; Thampy, S.; Maiti, P.; Brahmbhatt, H.; Eswaran, K.; Ghosh, P.K. Kappaphycus alvarezii as a Source of Bioethanol. Bioresour. Technol. 2012, 103, 180–185. [Google Scholar] [CrossRef]
  105. Ben Yahmed, N.; Jmel, M.A.; Ben Alaya, M.; Bouallagui, H.; Marzouki, M.N.; Smaali, I. A Biorefinery Concept Using the Green Macroalgae Chaetomorpha linum for the Coproduction of Bioethanol and Biogas. Energy Convers. Manag. 2016, 119, 257–265. [Google Scholar] [CrossRef]
  106. Zhang, W.; Mao, Y.; Liu, Z.; Wang, M. Ethanol Production from Colpomenia sinuosa by an Alginate Fermentation Strain Meyerozyma guilliermondii. Indian J. Microbiol. 2022, 62, 112–122. [Google Scholar] [CrossRef]
  107. Wu, F.-C.; Wu, J.-Y.; Liao, Y.-J.; Wang, M.-Y.; Shih, I.-L. Sequential Acid and Enzymatic Hydrolysis in Situ and Bioethanol Production from Gracilaria Biomass. Bioresour. Technol. 2014, 156, 123–131. [Google Scholar] [CrossRef] [PubMed]
Figure 1. Glucose consumption, ethanol, acetic acid, and glycerol production during 48 h of fermentation of algal hydrolysate by S. cerevisiae.
Figure 1. Glucose consumption, ethanol, acetic acid, and glycerol production during 48 h of fermentation of algal hydrolysate by S. cerevisiae.
Applmicrobiol 04 00039 g001
Figure 2. Glycerol, acetic acid, and ethanol yields (g·g−1), after 48 h of fermentation by S. cerevisiae in the algal hydrolysate (Applmicrobiol 04 00039 i001 ) and the synthetic medium (Applmicrobiol 04 00039 i002).
Figure 2. Glycerol, acetic acid, and ethanol yields (g·g−1), after 48 h of fermentation by S. cerevisiae in the algal hydrolysate (Applmicrobiol 04 00039 i001 ) and the synthetic medium (Applmicrobiol 04 00039 i002).
Applmicrobiol 04 00039 g002
Figure 3. Growth rate (a), glucose consumption (b), and ethanol production (c) for S. cerevisiae with the non-sterilized and the sterilized algal hydrolysate.
Figure 3. Growth rate (a), glucose consumption (b), and ethanol production (c) for S. cerevisiae with the non-sterilized and the sterilized algal hydrolysate.
Applmicrobiol 04 00039 g003
Figure 4. Glucose consumption (a), ethanol production (b), and cell density (c) for P. stipitis, C. guilliermondii, K. marxianus, and S. cerevisiae during fermentation of algal hydrolysate without sterilization or enrichment and for an inoculum size of 1% (v/v).
Figure 4. Glucose consumption (a), ethanol production (b), and cell density (c) for P. stipitis, C. guilliermondii, K. marxianus, and S. cerevisiae during fermentation of algal hydrolysate without sterilization or enrichment and for an inoculum size of 1% (v/v).
Applmicrobiol 04 00039 g004
Figure 5. Glycerol, acetic acid, and ethanol yields obtained with the various yeasts at 48 h of fermentation.
Figure 5. Glycerol, acetic acid, and ethanol yields obtained with the various yeasts at 48 h of fermentation.
Applmicrobiol 04 00039 g005
Table 1. Chemical composition of cultivated U. rigida.
Table 1. Chemical composition of cultivated U. rigida.
Proximate CompositionRelative % (Dry Weight Basis/Brut)
Dry matter94.9 ± 0.05
Fibers34.90 ± 0.05
Protein5.68 ± 0.05
Ash31.9 ± 0.05
N Kjeldahl0.91 ± 0.05
Total sulfates7.8 ± 0.05
Table 2. Carbohydrate chemical composition of U. rigida.
Table 2. Carbohydrate chemical composition of U. rigida.
Carbohydrate ContentGlucoseRhamnoseXyloseIduronic AcidGlucuronic Acid
Relative % (dry weight basis/brut)25.6 ± 0.056.5 ± 0.052.1 ± 0.050.6 ± 0.052.8 ± 0.05
Table 3. Effect of minerals, ammonium chloride, and peptone on fermentation of algal hydrolysate by S. cerevisiae, after 48 h of fermentation.
Table 3. Effect of minerals, ammonium chloride, and peptone on fermentation of algal hydrolysate by S. cerevisiae, after 48 h of fermentation.
ConditionsCell Density
(600 nm)
Ethanol (g·L−1)Productivity (g·L−1·h−1)Glycerol Yield (%) (c/c)Ethanol
Yields
(%) (c/c)
Efficiency
(%)
Without nutrients, ammonium chloride and peptone9.35 ±0.059.55 ± 0.050.20 ± 0.055.87 ± 0.0556.83 ± 0.0585.33 ± 0.05
With nutrients and ammonium chloride9.10 ±0.059.41 ± 0.050.20 ± 0.056.87 ± 0.0555.92 ± 0.0583.96 ± 0.05
With peptone9.30 ±0.059.40 ± 0.050.20 ± 0.056.03 ± 0.0555.79 ± 0.0583.76 ± 0.05
Table 4. Inoculum size effect on fermentation by S. cerevisiae over 24 h of fermentation.
Table 4. Inoculum size effect on fermentation by S. cerevisiae over 24 h of fermentation.
Inoculum Size % (v/v)Ethanol (g·L−1)Sugar Consumed
%
Productivity g·L−1·h−1Glucose Consumption Rate g·L−1·h−1Y Ethanol
(%) (c/c)
(Ethanol)o/t
Ratio (%)
0.15.54 ± 0.0558 ± 0.050.23 ± 0.050.54 ± 0.0556.19 ± 0.0584.38 ± 0.05
19.64 ± 0.05100 ± 0.050.40 ± 0.050.95 ± 0.0555.20 ± 0.0582.89 ± 0.05
Table 5. Chemical composition of autoclaved and non-autoclaved hydrolysates.
Table 5. Chemical composition of autoclaved and non-autoclaved hydrolysates.
Composition % (Dry Weight/Dry Weight)
AshMoistureLipidsTotal
Nitrogen
CarbohydratesCalcium
(mg/100 g)
Hydrolysate5.63 ± 0.0588.8 ± 0.050.3 ± 0.050.4 ± 0.054.9 ± 0.0555.2 ± 0.05
Autoclaved hydrolysate5.52 ± 0.0589.2 ± 0.050.1 ± 0.050.4 ± 0.054.8 ± 0.0554.0 ± 0.05
Table 6. Comparison of the results obtained during yeasts’ growth on synthetic medium and algal hydrolysate at 48 h of fermentation.
Table 6. Comparison of the results obtained during yeasts’ growth on synthetic medium and algal hydrolysate at 48 h of fermentation.
Glucose Consumption Rate at 48 h (g·L−1·h−1)Ethanol Production Rate (g·L−1·h−1)(Ethanol) o/t Ratio
HydrolysateSynthetic MediumHydrolysateSynthetic MediumHydrolysateSynthetic Medium
K. marxianus0.49 ± 0.050.43 ± 0.050.18 ± 0.050.14 ± 0.0570.49 ± 0.0564.10 ± 0.05
P. stipitis0.10 ± 0.050.41 ± 0.050.03 ± 0.050.10 ± 0.0552.25 ± 0.0549.37 ± 0.05
C. guilliermondii0.35 ± 0.050.43 ± 0.050.11 ± 0.050.09 ± 0.0563.20 ± 0.0542.97 ± 0.05
S. cerevisiae0.47 ± 0.050.42 ± 0.050.20 ± 0.050.16 ± 0.0582.87 ± 0.0574.35 ± 0.05
Table 7. Comparison of ethanol yields obtained during S. cerevisiae growth on various algae.
Table 7. Comparison of ethanol yields obtained during S. cerevisiae growth on various algae.
AlgaeFermenting StrainEnrichmentSize of InoculumEthanol Yield References
U. rigidaS. cerevisiae CLIB 95Without enrichment1% v/v
(0.12 g)
0.54% (c/c)
(0.41 g·g−1 reducing sugar)
Present study
U. rigidaPachysolen tannophilus-5%0.37 g·g−1[103]
Colpomenia sinuosaMeyerozyma guilliermondii,-10%0.26 g·g−1[106]
Kappaphycus alvareziiS. cerevisiae (NCIM 3455)With nitrogen source5% v/v0.39 g·g−1[104]
Chaetomorpha linumS. cerevisiae (Baker’s yeast)Yeast extract
Peptone medium
10% v/v0.41 g·g−1[105]
U. rigidaS. cerevisiae
(beaker)
-0.5 g333.3 mg·g−1[52]
Gracilaria sp.S. cerevisiae2 g·L−1 yeast extract10% v/v0.47 g·g−1[107]
Gracilaria verrucosaS. cerevisiae3 g·L−1 yeast extract and 0.25 g·L−1 (NH4)2HPO4 6% v/v0.43 g·g-−1[78]
Disclaimer/Publisher’s Note: The statements, opinions and data contained in all publications are solely those of the individual author(s) and contributor(s) and not of MDPI and/or the editor(s). MDPI and/or the editor(s) disclaim responsibility for any injury to people or property resulting from any ideas, methods, instructions or products referred to in the content.

Share and Cite

MDPI and ACS Style

Sayed, W.; Cabrol, A.; Salma, A.; Amrane, A.; Benoit, M.; Pierre, R.; Djelal, H. Green Macroalgae Hydrolysate for Biofuel Production: Potential of Ulva rigida. Appl. Microbiol. 2024, 4, 563-581. https://doi.org/10.3390/applmicrobiol4020039

AMA Style

Sayed W, Cabrol A, Salma A, Amrane A, Benoit M, Pierre R, Djelal H. Green Macroalgae Hydrolysate for Biofuel Production: Potential of Ulva rigida. Applied Microbiology. 2024; 4(2):563-581. https://doi.org/10.3390/applmicrobiol4020039

Chicago/Turabian Style

Sayed, Walaa, Audrey Cabrol, Alaa Salma, Abdeltif Amrane, Maud Benoit, Ronan Pierre, and Hayet Djelal. 2024. "Green Macroalgae Hydrolysate for Biofuel Production: Potential of Ulva rigida" Applied Microbiology 4, no. 2: 563-581. https://doi.org/10.3390/applmicrobiol4020039

Article Metrics

Back to TopTop