3.3.2.3 Advanced Technology for Biomass Conversion
Current advanced technology for biomass conversion includes BIGCC (biomass integrated gasification combined cycle) systems, co-firing (coal including gas), combined heat and power (CHP), transesterification, and cellulosic biomass conversion [93].
3.3.2.3.1 Biomass Integrated Gasification Combined Cycle (BIGCC)
The BIGCC is the most effective and advanced technique for transforming biomass energy into biofuel from all biomass, such as urban waste, wood residues, and agro-food byproducts [94]. The BIGCC plant designed in a planned design focused on electricity and energy balances. With the rise of both pressure and temperature ratios and the increased firing of biomass, the efficiencies rise to an optimal firing category degree [95].
3.3.2.3.2 Co-firing
One of the easiest and cheapest options for increasing green energies is the co-firing bioresource from the coal energy sector [96]. Co-firing possesses benefits, including, but not limited to, reducing fossil fuel consumption, traditional plant usage, fuel flexibility, higher quality biomass use, and pollutant emission reduction [96]. For the co-firing of biomass with coal, three distinct approaches established; direct co-firing, indirect co-firing, and parallel are co-firing [96]. In combustion or gasification-based systems, coal with biomass as an alternative fuel is a feasible technical choice to eliminate harmful emissions [58].
3.3.2.3.3 Combined Heat and Power (CHP)
Combined heat and power (CHP) generation improves the overall performance of power systems. Its efficiency is higher than the general way of conversion. Biomass-fuel-based CHP is a substitute for combining efficient power systems with sustainable, climatic conditions-neutral gasoline [97]. Issues affecting CHP systems’ production include uncertainties, challenges in assuming the structure surrounding the infrastructure, extensive system borders, and displacement consequences [97].
3.3.2.3.4 Transesterification
Transesterification is described as the chemical conversion technique of alcohol triglycerides into alkyl esters using a catalyst [98]. In the presence of catalysts such as potassium hydroxide, a transesterification process is performed to produce biodiesel and alcohol from different kinds of biomass sources, such as cooking oils, milk waste rich in lipid sources [99, 100]. The wet-transesterification process is more economical than the conventional system for treating wet biomass (sewage sludge) without a drying process [26].
3.3.2.3.5 Cellulosic Biomass Conversion
As a substrate, biomass rich in cellulose such as lignocellulose and micro and macroalgae is used to process ethanol. Two steps are included in the transformation of biomass into ethanol: (i) pre-treatment and saccharification; (ii) fermentation [101]. Low yields and high costs for the pre-treatment and hydrolysis of cellulose are the significant barriers of existing technology in developing ethanol from biomass.
3.3.2.3.5.1 Pre-treatment and Saccharification
Acid and alkaline pre-treatment are the chemical compounds that have the potential to hydrolyze lignocellulosic biomass efficiently [92]. Alkaline pre-treatments raise the crystallinity of cellulose rather than the acidic pretreatment. Both pre-treatments release phenolic content; the maximum is with acid pre-treatments [102]. Combined pre-treatment with hydrothermal treatment and Fenton treatment efficiently facilitates the enzymatic hydrolysis of lignocellulosic biomass [103]. Mild O2-aided alkaline pre-treatment enhances structures fractional quality and enzymatic hydrolysis of biomass. Compared to traditional alkaline pre-treatment, more than 80% lignin and 92% cellulose at 80 °C and with 1% dilute NaOH extracted via O2-aided alkaline pre-treatment [104]. Xu et al. [105] demonstrated that choline chloride has significant efficacy in the pre-treatment of lignocellulosic biomass. Acidic hydrothermal pre-treatment with O2 effect on redox environment results in increased intensity, lower recovery of pre-treatment solids, lower recovery of glucans, better elimination of hemicellulose, pseudo-lignin production, improved total conversion of glucans, and increased concentrations of many microbial inhibitors [106]. The most successful pre-treatment process providing the shortest pre-treatment period relative to anoxia and alkali pre-treatment was ultrasonic pre-treatment for releasing microbial cells from WAS (waste-activated sludge) flocs and subsequent phagotrophic algae development. Ultrasonic pre-treatment was accomplished predominantly by breaking physical attracting forces, while the liberation of microbial cells was performed by breaking ionic bonds in alkali pre-treatment [107]. They were also stated that during algae formation, re-flocation of released microbial cells was observed in ultrasonic pre-treatment but was less resistant to floc reform in alkali pre-treatment.
Microwave-assisted (MW) pre-treatment compared to ultrasound is superior for removing hemicellulose [108]. A hydrolysate without any inhibitors and maximum reducing sugar at low solid loading is obtained even under moderate MW pre-treatment conditions. They have revealed that these factors had no significant effect on the ultrasound-pretreated agave. Compared to pre-treatment with traditional heating, pre-treatment assisted with MW decrease the method’s time and temperature. Enzymatic pre-treatment with protease, viscozyme, and enzyme blend pre-treatment at 55 °C shows maximum saccharification. Preliminary economic evaluation findings revealed that the essential enzymes’ expense makes enzymatic pre-treatment not yet commercially feasible [109]. The generation of low-cost enzymes, however, could promote the use of enzymes in microalgae pre-treatment. The cheapest method for cellulose saccharification and co-fermentation of all reducing sugars, including pentose and hexose sugars with engineered microorganisms, was also in proceedings for the effective ethanol development of efficient pre-treatment technologies [31].
3.3.2.3.5.2 Fermentation
Separate hydrolysis and fermentation (SHF), a two-step method for the processing of butanol, whereas saccharification and fermentation (SSF), a one-step process carried with rice straw [110]. They have claimed that an SSF was more effective than an SHF, notably due to the time reduction from improved productivity. Wirawan et al. [111] showed ethanol production by continuous separate hydrolysis and co-fermentation (SHcF) and simultaneous saccharification and co-fermentation (SScF) from alkaline pretreated sugarcane bagasse using Zymomonas mobilis (PVA immobilized cells) and Pichia stipitis (suspended cells). The ethanol yield and productivity of the SScF fermentation is higher than the SHcF process. S. cerevisiae an C. tropicalis produced ethanol from xylose and glucose without intrusion from H2O2-pretreated corn stover (CS) through SScF [112].
Consolidated bioprocessing (CBP) is a combination process of hydrolysis and fermentation. In modern times, using CBP to transform lignocellulosic biomass into suitable substances has gained considerable research attention to increasing the development of alternative fuels using a cost-effective method [113]. The co-culture of C. saccharoperbutylacetonicum with the fungus Phlebia sp. MG-60-P2 under anaerobic conditions in consolidated bioprocessing synergistically derived butanol from lignocellulosic materials and enhanced saccharification [114]. In another study, Singh et al. [115] have extracted docosahexaenoic acids and bioethanol from rice straw biomass by integrated consolidated thermoanaerobic and marine thraustochytrid bioprocessing. A semi-continuous cycling system possessing self-cycling fermentation (SCF) is used to detect the beginning of the stationary phase; once half of the broth volume has been seen, it is immediately collected then supplemented with a freshly prepared broth to begin the next stage [116, 117]. SCF can improve the yield and efficiency of products. Applying SCF to ethanol production improves efficiency dramatically and enhances the cellulosic ethanol industry [116].
3.3.3 Biofuel as Renewable Energy for the Future
3.3.3.1 Solid Fuel
Carbon,