An Overview of the Classification, Production and Utilization of Biofuels for Internal Combustion Engine Applications

Biofuel, a cost-effective, safe, and environmentally benign fuel produced from renewable sources, has been accepted as a sustainable replacement and a panacea for the damaging effects of the exploration for and consumption of fossil-based fuels. The current work examines the classification, generation, and utilization of biofuels, particularly in internal combustion engine (ICE) applications. Biofuels are classified according to their physical state, technology maturity, the generation of feedstock, and the generation of products. The methods of production and the advantages of the application of biogas, bioalcohol, and hydrogen in spark ignition engines, as well as biodiesel, Fischer–Tropsch fuel, and dimethyl ether in compression ignition engines, in terms of engine performance and emission are highlighted. The generation of biofuels from waste helps in waste minimization, proper waste disposal, and sanitation. The utilization of biofuels in ICEs improves engine performance and mitigates the emission of poisonous gases. There is a need for appropriate policy frameworks to promote commercial production and seamless deployment of these biofuels for transportation applications with a view to guaranteeing energy security.


Introduction
Accessibility to clean, safe, and affordable energy has a strong correlation with the quality of life of an individual. With increasing population and urbanization in the 21st century, universal energy accessibility has become one of the greatest challenges in meeting sustainable development goals. The improved economic activities in developing and emerging economies have elicited a rapid upsurge in energy demand with an attendant increase in greenhouse gas (GHG) emissions and, consequently, exacerbated global warming [1]. The continued utilization and consumption of fossil-based (FB) fuels have resulted in the depletion of the finite fuel reserve, emission of dangerous gases, terrestrial and aquatic pollution, climate change, and irreparable environmental degradation. According to British Petroleum, both oil and gas could be exhausted within the next 50 years while coal reserves can only last for the next 115 years based on the current rate of exploitation [2,3]. With these scenarios, research on the development of affordable and sustainable renewable fuels has been escalated to meet the present global energy needs without compromising future sustainability.
Owing to their numerous advantages, including their renewability, environmental friendliness, feedstock availability, the flexibility of the production techniques, and their availability in solid, liquid, and gaseous states, biofuels have gained sustained popularity as an alternative to FB fuels. Other renewable energy systems like solar and wind do not pollute the environment, but they are incapable of sequestrating CO 2 emissions and  [5,7]. Developed by the authors.
Research has been conducted on the exploitation and utilization of renewable fuel, especially biofuel. Lee et al. [8] identified thermochemical and biochemical technologies as the leading pathways for converting waste to bioenergy. They stated that the transesterification process is the easiest and most cost-effective route to large-scale synthesis of biodiesel from waste. Investigations into further developing household and commercial production of biodiesel are still ongoing. Researchers have also reviewed perspectives on biofuels along with their history, status, and classifications for various applications [9][10][11]. There is a consensus of opinion on the need for more investigations to fill the identified research gaps on the production technologies and classification of biofuels and their utilization as alternative fuels in ICEs, bioelectricity, bioenergy, and other applications. This forms the motivation for this present effort. This study aims to provide an overview of biofuel as a form of renewable fuel in terms of the classifications of biofuels, as based on various defined parameters, their production, and the utilization of biodiesel and other renewable fuels for internal combustion application. Sequentially, after classifying biofuels, the generation and applications of biodiesel, biogas, bioalcohol, hydrogen, Fischer-Tropsch (F-T) fuel, and dimethyl ether (DME) as transportation fuels are presented. While focusing on biodiesel as an alternative renewable fuel, the effects of the use of some biofuels on the performance and emission characteristics of ICEs are also discussed. The current study is limited to describing the classification of biofuels, the transesterification process for biodiesel synthesis, and the application of bioalcohol (methanol, ethanol, and butanol), biogas, and hydrogen in spark ignition engines, as well as the use of biodiesel, F-T fuel, and DME in compression ignition (CI) engines. The required information for this review was sourced from recently published articles.

Biofuel as a Renewable Fuel
Since the early 1970s, when the word "biofuel" was first used, authors have defined the term as: (a) a fuel manufactured either from or by fresh, living micro-or macroorganisms [12]; (b) a fuel made directly or indirectly from biomass [13]; (c) a liquid fuel obtained from biomass, e.g., biodiesel produced from fats and oils, biogas generated from animal waste, etc. [14]; (d) a bio-based fuel naturally obtained from wood and wood chips or agricultural residues or chemically converted from biomass to charcoal, biodiesel, bioethanol, and biomethane [15]. Using these definitions, we can summarize that biofuel is generated from plants, animal waste, manure, sludge, etc., in either a solid, liquid, or gaseous form, and is capable of being converted to another variety of biofuel [16]. Major benefits and paybacks derivable from the deployment of biofuels as a form of renewable fuel include: 1.
Biofuels are renewable and are carbon-and CO 2 /GHG-neutral during the progression of the life cycle [17].

2.
Less GHG emissions are generated from the utilization of biofuels compared to FB fuels [18,19]. 3.
Biofuels are largely produced from locally available and accessible resources, applying safe production methods [22,23]. 5.
Production and utilization of biofuels enhance home-grown agricultural development and investment [24,25]. 6.
Biofuels provide improvements in the health and living conditions of people [24,25]. 7.
Biofuels create jobs and improvements in local livelihoods and reduce energy importations [26,27]. 8.
Economically, biofuel helps to stabilize energy prices, conserve foreign exchange, and generate employment at the macroeconomic level [28,29]. 9.
Household usage of biofuel does not trigger life-threatening health conditions, as opposed to FB fuels [30,31].
Notwithstanding these advantages, the high initial cost of production and storage of biofuels can be a deterrent for potential producers and users. There are justifiable concerns that the increased demand for biofuel will increase the cost of the relevant agricultural and woody raw materials, as well as other feedstocks [32,33]. Also, continuous demand for wood can lead to rapid deforestation, while huge parcels of land are required to cultivate special trees and other inedible oils for biofuel production. In specific terms, methane, a major component of biogas, is a major contributor to global climate change and continuous usage of biogas can exacerbate ozone layer depletion [34], while biodiesel, a form of biofuel, generates high NOx emission and contributes to higher engine wear compared to FB fuel [35]. Despite the obstacles, biofuel is a clean, sustainable, and affordable energy resource choice that can replace FB fuels and rescue humankind from the looming environmental disaster. The adaptation of biofuels as sustainable fuels in various sectors of the economy is one of the strategies for CO 2 reduction and carbon mitigation [36,37].

Classification of Biofuels
For this work, biofuels are categorized based on four parameters, namely physical state, technology maturity, generation of feedstock, and generation of products.

Classification Based on the Physical State
In principle, any renewable and biological substance can be utilized as fuel; thus, various raw materials can be considered as biofuels and can exist in the following three physical states.

Solid Biofuels
Generally, any solid biomass material can be described as solid biofuel. Solid biomass is principally any solid feedstock that can be converted into biofuel [38]. Examples of such solid biomass include lignocellulosic biomass and various types of solid waste [39]. Table 1 shows various categories of solid biofuel and their examples. Ideally, each of these raw solid biomasses can be used directly as solid biofuels or as feedstock for other forms of biofuel production.

Liquid Biofuels
Liquid biofuels refer to any renewable fuel in liquid form. They are mainly used as transport fuels. In 2019, liquid biofuel production increased to 96 Mtoe from 82.31 Mtoe and 8.57 Mtoe produced in 2016 and 1990, respectively [45,46]. Notable examples of liquid biofuels are biodiesel, biomethanol, bioethanol, biobutanol, biopropanol, bio-oil, jet fuel, etc. [47][48][49]. Some of the features and benefits that have escalated research and helped popularize the application of liquid biofuels include the following [50]: (i) their high combustibility, (ii) they are safer and easy to store, (iii) they are easy to transport with pipelines, (iv) they are safer to transport compared to petrol, (v) they are relatively inexpensive, (v) they have a high energy to mass ratio, (vi) their storage stability, and (vii) they are reasonably nonexplosive.

Gaseous Biofuels
Biogas/biomethane, biohydrogen, and biosyngas are the commonest examples of gaseous biofuels. They have a wide variety of applications, including for thermal, transport, and heat uses and electricity/power generation. Over the years, gaseous biofuels have been extensively studied and utilized due to the many benefits derivable from them, which include [51]: (i) higher reactivity, (ii) generation of less waste when applied, (iii) the fewer oxidants required, (iv) the simplicity of the reactors, and (v) ease of control.

Classification Based on Technology Maturity
According to the degree of technology maturity or status of the commercialization technologies, biofuels are often categorized as conventional biofuels and advanced biofuels, as shown in Figure 2.  [52]. Developed by the authors.

Conventional Biofuels
Conventional biofuels are produced through already commercially available technologies. Such technologies continue to be developed for economic viability and profitability. Examples of conventional biofuels include bioethanol, biodiesel, and biogas which are produced through fermentation, transesterification, and anaerobic digestion, respectively. These technologies have been developed, commercialized, and adapted for local or household deployment. Common feedstocks for conventional biofuels include sugarcane and sugar beet, corn, wheat, vegetable oil, animal fat, recovered household fat, waste frying oil, etc. The commercialization of these categories of renewable fuel is hampered by high production costs and unprofitable retail prices [53].

Advanced Biofuels
The conversion technologies for most advanced biofuels are still generally at the research and development, demonstration, or early commercial stages. Major examples include hydrotreated vegetable oil, lignocellulosic bioethanol, biomass-generated esters, microalgae biodiesel, and biohydrogen. Bearing in mind the challenges of shortages of feedstock, the interference of some feedstocks with the food chain, and the poor cost competitiveness associated with conventional biofuels, investment in and production of advanced biofuels from inedible feedstocks has become an encouraging alternative. However, the adaptation and commercialization of advanced biofuel are hampered by poor fuel economy [54]. Some inedible feedstocks, conversion technologies, and examples of advanced biofuels are shown in Figure 3.  [54]. Developed by the authors.

Classification Based on the Generation of Feedstock
Feedstocks for biofuel production are divided into three categories in terms of their generation: first-generation feedstock, second-generation feedstock, and third-generation feedstock. The choice of feedstock has a huge influence on the development and utilization of biofuel as a substitute for FB fuels. Feedstocks are chosen based on price, hydrocarbon content, and biodegradability. For example, edible feedstocks and those containing pure sugars are relatively expensive. Simple sugars are preferred as feedstocks because they are easy to decompose with microbes while lignocellulosic biomasses are selected based on their relative affordability.

First-Generation Feedstock
The first sets of raw materials that were converted to biofuels are referred to as firstgeneration feedstock (1GF). Major examples of 1GF include rapeseed oil, soybean oil, palm oil, sunflower oil, corn, sugarcane, wheat, and sugar beet. The extracted oils are converted to biodiesel through the transesterification process while ethanol, a form of bioalcohol, is produced from corn, sugarcane, etc., by direct fermentation [55]. A schematic illustration of ethanol production from corn is shown in Figure 4. Due to the low production cost, good cost/yield ratio, and a large number of carbohydrates in starch or saccharose form in corn and sugarcane, the use of these feedstocks has gained prominence and become an industrial standard [56]. However, the need for large tracts of arable land to cultivate the plants, deforestation, exploitation of natural ecosystems, bush burning, drastic changes to the ecosystem as a result of increased farming activities, the food vs. energy debate, and spikes in the prices of the edible oils used for biodiesel are major drawbacks of the use of this generation of feedstock. Also, the feedstock conversion processes are influenced by the physical attributes of the biomass. The products of 1GF generate a larger carbon footprint compared to other generations of biofuel. These shortcomings prompted researchers to look for microorganisms and other forms of feedstock to respond to the escalated requests for biodiesel and ethanol [57,58]. . Schematic illustration of ethanol production from first-generation feedstock. Adapted from [58]. Developed by the authors.

Second-Generation Feedstock
Lignocellulosic biomasses are generally referred to as second-generation feedstock (2GF) and are converted to bioethanol and biodiesel. The lignocellulosic biomasses are always pre-treated before conversion. For this purpose, four pre-treatment processes, namely, physical, biological, chemical, and combinatorial (physicochemical and biochemical), are commonly adopted. Apart from the pre-treatment processes, other procedures implemented for the transformation of lignocellulosic biomass to bioethanol include hydrolysis, fermentation, and distillation [59]. 2GF biofuels include cellulose, hemicellulose, and lignin. Cellulose and hemicellulose are polysaccharides and are converted to monomeric sugars by fractionalization while monomeric sugars are used for the production of bioethanol through microbial fermentation. Lignin is a complex aromatic polymer of polyphenols and not only forms a bond between hemicellulose and cellulose but also functions as an obstacle to the saccharification of hemicellulose and cellulose. Though lignocellulosic biomass does not affect food chains and is seen as an economically feasible feedstock for producing renewable fuels, its product also has several limitations. The conversion of 2GF to biofuel suffers from many technical challenges and lacks a mature conversion technology, which makes its conversion uneconomical and unsustainable [60].

Third-Generation Feedstock
Third-generation feedstock (3GF) originates from non-food sources. Algae, which are subdivided into macroalgae and microalgae, are a major example of 3GF. Table 2 shows the features of microalgae and macroalgae. Microalgae are microscopic unicellular photosynthetic microorganisms from which a larger amount of biomass can be generated than from terrestrial plants. They are usually over 400 µm in size, between 1 µm to 30 µm in diameter [61], and can convert algal biomass, waste, and CO 2 into diverse bioenergy products by photosynthesis. Microalgae grow rapidly with small quantities of water per kg of biomass, produce a large number of lipids and starch for biofuel synthesis, and are capable of sequestering CO 2 from flue gas [62,63]. Macroalgae are multicellular marine organisms with low concentrations of cellulose and lipid and high levels of structural polysaccharides but no lignin content [64]. Macroalgae, also called seaweed, are capable of growing to up to 60 m in length [65]. Microalgae are categorized according to their availability while macroalgae are grouped in terms of their photosynthetic pigmentations, as shown in Figure 5.
Algal biomass derives CO 2 from power plant emissions and uses CO 2 for its growth. The biomass is converted to CO 2 by photosynthesis, which emits oxygen into the atmosphere. The cultivation and utilization of algae as a feedstock for biofuel production is one of the strategies for achieving CO 2 mitigation. Algae are organisms that grow quickly in salty water, municipal wastewater, and coastline water and on land that is not useful for farming [66,67]. Algal biomass can be grown naturally or artificially. The strategies for artificial microalgae and macroalgae biomass production include open pond cultivation, photobioreactors (phototrophic reactors), and heterotrophic aerobic fermenters [68]. Algae has been widely used as a sustainable biofuel feedstock due to its fast rate of acclimatization to potentially challenging environments, the increased popularity of algae-based biofuels, and the derivation of other associated bio-products, including natural cosmetics, aquaculture, oils, pigments, pharmaceuticals, and nutritional supplements [69]. Energies 2021, 14, 5687 Figure 5. Classification of microalgae and macroalgae. Adapted from [33,72]. Developed by the authors.
Compared with other biomass feedstocks, algae feedstock is very competitive and offers many advantages, including the following: i.
The cultivation of algae consumes CO 2 , ensures carbon mitigation, and contributes to a carbon-neutral environment. The generation of 1 g algal biomass consumes 1.83 g CO 2 [73]; ii.
Conversion of CO 2 to algae-based biofuel; a ton of CO 2 can be converted to between 55 and 70 gallons of ethanol [74]; iii.
It does not compete with fresh water since algae can be cultivated in wastewater [75,76]; iv.
Non-utilization of physical and fertile land [76]; algae can be grown artificially without land [77]; v.
No competition with food security; eliminates the food vs. fuel debate [78]; vi.
Algae-based biofuel is substantially compatible with traditional gasoline engines and no engine modifications are required [80,81]; viii.
Algae biomass has high oil content and produces between 10 and 100 times more oil per acre compared with other traditional oil crops [83]; x.
Cultivation of algae does not involve the application of herbicides or pesticides [84]; xi.
Microalgal biomass can be utilized as food, animal feed, and fertilizer [70].
Despite these advantages, high production costs, highly technical infrastructure outlay, difficulties with integration into the existing system, and complex conversion techniques have restricted the sustainable commercial utilization of 3GF as feedstock [33,86].

Fourth-Generation Feedstock
The challenges thrown up by the other generations of feedstock have encouraged researchers to look for biofuel from other sources. Fourth-generation feedstock (4GF) is genetically engineered [87]. Though 4GF is still in the experimental laboratory stage, it is being developed from the modification of algae. In this way, algae are being metabolically modified to have higher oil contents, increased carbon capture capability, and enhanced cultivation, harvesting, and fermentation procedures. Also, metabolic engineering is being harnessed to fast-track the growth rate and boost the lipid content of some species of algal biomass [88,89]. Since the oil contents of algae are species-dependent, some strains of algaenamely, Botryococcus braunii, Chaetoceros calcitrans, the Chlorella species, Isochrysis galbana, Nannochloropsis, Schizochytrium limacinum, and the Scenedesmus species-are being analyzed for their applicability and suitability [90,91]. Some investigations have been carried out on the application of nanotechnology to increase the efficiency and cost-effective production of algae-based biofuel. A novel approach referred to as "nanofarming" has been tipped to be invaluable for the acceleration of oil extraction from algal biomass by "milking algae", and it allows for the continuous utilization of biomass for a long period, up to 70 days [92,93].

Classification Based on the Generation of Products
Ever since the commencement of the utilization of biofuels (peanut oil to power the Rudolf Diesel Engine in 1900 [94] and vegetable oil to run ICEs in 1930 [95]), various parameters have been used for their classification. Researchers have classified biofuels into various generations. Naik et al. [96] and Akhlaghi et al. [97] classified biofuels into firstand second-generation biofuels. According to them, examples of first-generation biofuels (1GB) are bioethanol, biodiesel, and biogas, while vegetable oils, animal fats, etc., form second-generation biofuels (2GB). Other researchers, however, have classified biofuels into three generations, namely, 1GB, 2GB, and third-generation biofuels (3GB), which are produced from food crops (edible feedstocks), non-food crops (inedible feedstocks), and aquatic materials (cultivated feedstocks), respectively [98][99][100]. However, Algayyim et al. [101] and Rodionova et al. [102] grouped biofuels into primary biofuels and secondary biofuels. According to them, primary biofuels are those biomasses used without modifications, including wood, wood chips, grass, etc., and which are usually burned to generate heat for cooking and warming, while secondary biofuels are classified into 1GB, 2GB, and 3GB and produced from grains, lignocellulosic biomass, and algae, respectively. For their part, Noraini et al. [103], Mahjoub et al. [104], and Chowdhury and Loganathan [105] categorized biofuels into natural biofuels, 1GB, 2GB, and 3GB, which are sourced from firewood and animal waste and edible, lignocellulosic, and algae feedstocks, respectively. Also, Ziolkowska [106] and Fasahati et al. [107] classified biofuels into conventional biofuels (1GB) and advanced biofuels. According to them, conventional biofuels are ethanol and biodiesel produced from high-sugar-content crops, like corn, cereal, and sugarcane and biodiesel generated from waste oil, animal fats, soybean, rapeseed, palm oil, etc., while advanced biofuels are made up of cellulosic ethanol (2GB), algae biofuel (3GB), and next-generation biofuel (4GB).
Hao et al. [108] identified 1GB as being produced from food feedstocks; 1.5GB as generated from non-food and oil-bearing crops; 2GB as sourced from cellulosic crops, waste cooking oil, and agricultural and forestry residues; and 3GB as made from algae. The majority of the recently published studies in the literature classify biofuels into 1G (biodiesel, bioethanol), 2G (bio-oil, biodiesel, bioalcohol, biohydrogen), 3G (biodiesel, biomethanol, bioethanol, jet fuel), and 4G (green biodiesel, biogasoline, green aviation fuels) [109][110][111][112][113]. Table 3 shows a summary of the classification of biofuels by various researchers. For this work, biofuels were categorized into five classifications: primary biofuels, 1GB, 2GB, 3GB, and 4GB. Table 4 shows the benefits and drawbacks of the adaptation and utilization of the primary biofuels and the four generations of biofuels.

Primary Biofuels
The main feature of primary biofuels, also known as natural biofuel [103] or zerogeneration biofuel, is that they are used the way they occur without any modifications, alterations, processing, or pre-treatment. Examples of primary biofuels include firewood, wood chips, pellets, animal waste, forest and crop residues, and landfill gas. Notable areas of application of primary biofuels include cooking, household heating, brick kilns, drying, roasting, and electricity generation. This type of biofuel is readily available and its utilization does not require any special skill or infrastructure. However, their utilization is crude, compromises air quality, and may negatively impact the health of the user [118,119].

First-Generation Biofuels
The need to get a sustainable and viable alternative to finite energy sources gave rise to the development of 1GB. Major examples include biodiesel, biogas, bioalcohols, biosyngas, biomethanol, and bioethanol. Major feedstocks for the production of 1GB include edible (food) crops like corn, wheat, palm oil, soybeans, edible vegetable oil [120], rapeseed, Karanja, Moringa oleifeara, Jatropha curcas [121], corn, cereals, sugar cane, wood, grains, straw, charcoal, household waste, and dried manure [122]. Though 1GB is biodegradable and offers great environmental and social benefits, the food vs. fuel trade-off and extensive area and time required to grow the inedible feedstock are some of its drawbacks [123]. Also, the high cost of feedstock, which was found to consume over 70% of the generation cost, is discouraging [124][125][126].

Second-Generation Biofuels
Second-generation biofuels (2GB), which were developed as a solution to some of the drawbacks associated with 1GB, can be produced from inedible feedstocks like waste cooking oil [127], waste animal fats [128], recovered oil [129], and lignocellulosic biomass, like grass, wood, sugarcane bagasse, agricultural residues, forest residues, and municipal solid waste [130,131], as well as from bioethanol, biodiesel, biosyngass, biomass to liquid biodiesel conversion, bio-oil, biohydrogen, bioalcohols, biodimethylfuran, and bio-Fischer-Tropsch [115,132]. The generation of 2GB does not affect the food chain and the cost of feedstocks is relatively low, but the production technologies are still complex and have not been commercialized yet [98,133].

Third-Generation Biofuels
The challenges associated with 1GB and the 2GB gave rise to the development of 3GB, particularly with regard to feedstock selection. Algae, which is the major feedstock for 3GB, does not interfere with the food chain and requires no land or freshwater for cultivation, either naturally or artificially [134]. Other feedstocks for 3GB include yeast, fungi, and cyanobacteria, while examples of 3GB include bioethanol, vegetable oil, biodiesel, biomethanol, and jet fuels. In recent years, 3GB has attracted more investment, particularly in algae cultivation and conversion technologies [135].
Fourth-Generation Biofuels 4GB are produced from genetically or metabolically engineered feedstock from algae. Unlike 2GB and 3GB, the production of this generation of biofuels ensures sustainable production and catches CO 2 emissions from oxygenated fuel combustion throughout the entire production progression [136]. The application of production technologies has drastically reduced the cost of production, making it economically competitive. Major examples of 4GB include hydrogenated renewable diesel, bio-gasoline, green aviation fuel, vegetable oil, and biodiesel. Table 4 shows the benefits and drawbacks of the adaptation and utilization of the primary biofuels and the four generations of biofuels.  The process requires high energy inputs [144,145] Compiled by the authors.

Transesterification as the Biofuel Conversion Technique
Transesterification is a technology for the synthesis of biodiesel. The process of transesterification is easy to implement, cost-effective, easy to commercialize, and can be carried out at the household level. Although biodiesel can be generated through pyrolysis, microemulsion, transesterification, dilution, and superfluid methods, the transesterification process appears to have gained prominence among biodiesel producers. Table 5 compares the benefits and drawbacks of some biodiesel generation techniques. Indonesia, the USA, and Brazil dominated global biodiesel production and consumption in 2019 (Table 6) [146]. Due to its properties, including biodegradability, lower toxic emissions, improved cetane number, and better lubricity, the global consumption of biodiesel is projected to continue to increase. The search for sustainable fuels to replace environmentally degrading FB fuels, depleting oil reserves, and the unpredictability of the global oil market are expected to drive the continuous increase in the production and consumption of biodiesel in the foreseeable future. Table 7 compares the four generations of biodiesel in terms of their feedstocks, processing methods, benefits, and challenges.   Transesterification is a chemical process in which renewable biological raw materials react chemically with alcohol with or without a catalyst. At the end of the reaction, a mixture of biodiesel, also commonly referred to as fatty acid methyl ester (FAME), and glycerol, an equally high-value co-product, is produced. A non-catalytic transesterification process is one in which no catalyst is involved in the conversion process. The non-catalytic transesterification process is believed to occur within a pressure range of 45 bar to 65 bar, a temperature range of 200 • C to 400 • C, and in the presence of alcohol [149]. Compared with the catalytic transesterification process, the supercritical transesterification process has been found to take place in a shorter time and is a simplified purification process, as removal of a catalyst is not needed. However, the non-catalytic transesterification process is limited to batch processes and requires high temperature and pressurized reaction vessels, so it has a high energy cost. A transesterification reaction can be catalyzed by homogeneous catalysts (NaOH, KOH), heterogeneous catalysts (CaO, Mg/Zr, Mg-Al), or a bio-based catalyst (enzyme), like lipase. Table 8 compares the merits and demerits of homogeneous, heterogeneous, and bio-based catalysts for the transesterification process. The biodiesel yield and oil conversion rate are influenced by various process parameters. These parametric conditions include the FFA value, reaction temperature, reaction time, alcohol to oil ratio, catalyst to oil ratio, catalyst type, catalyst concentration, catalyst particle size, and mixing or agitation rate [149]. For example, the choice of methanol as alcohol means the reaction temperature must be less than 60 • C. Also, if the FFA value of the feedstock is greater the 1 mgKOH/g, a two-step procedure consisting of acid-catalyzed esterification ( Figure 6) and alkaline-catalyzed transesterification reactions is adopted. Generally, under varying catalysts and feedstocks, the process parameters for optimal production of biodiesel agree with the established standards, particularly the ASTM D6751 and EN 14214 standards. Figure 7 depicts the combination of the three steps involved in transesterification.
The choice of alcohol determines the nomenclature of the resulting ester. Commonly used alcohols include methanol, ethanol, propanol, isopropanol, and butanol. Though methanol and ethanol are the most frequently used alcohols for biodiesel synthesis, methanol is often selected due to its physical and chemical benefits. Methanol dissolves easily in homogeneous catalysts, particularly NaOH, and reacts more easily with triglycerides than ethanol [153]. When bioethanol is used as the alcohol, completely bio-based biodiesel is produced. If methanol is used as the alcohol, the reaction gives FAME, while fatty acid ethyl ester results from the use of ethanol as the alcohol [154]. The number of steps involved in the transesterification process can be determined based on the amount of free fatty acids (FFAs). If the FFA value of the feedstock is above 1 mgKOH/g, transesterification is preceded by the esterification process. Esterification is a single-step process in which tetra oxo sulphate IV acid is used as a homogenous catalyst to bring the FFA value to less than 1 mgKOH/g. If the FFA value is lower than 1 mgKOH/g, a single-step transesterification process is adopted. Due to the low quality of some of the feedstocks, especially waste cooking oil, waste animal fats, recovered fats, and grease, pretreatment processes are required before transesterification [155,156].

Biofuel Production from Waste
Cost is one of the major factors inhibiting the adaptation of biofuels as sustainable transportation fuels. For example, the pump price of biodiesel is higher than that of fossilbased diesel fuel. The cost of feedstock is a major component of the cost of production. The cost of feedstock accounts for about 70-95%, 36-56%, and 49-56% of the overall production costs of biodiesel, bioethanol, and biogas, respectively [125,160,161]. The use of waste materials as feedstock is a viable cost-reduction strategy for biofuel production. The use of edible vegetable oils that have been previously used for frying in households and restaurants has become popular in recent years. These used vegetable oils are collected from users at the point of disposal. Consumption of WCO has serious health implications and its inappropriate disposal block drains and pollutes terrestrial and aquatic habitats.
In separate studies, Pugazhendhi et al. [21], Mohadesi et al. [162], and Naeem et al. [163] produced biodiesel from WCO with the transesterification process and reported biodiesel yields of 90%, 97.4%, and 98% respectively. The transesterification process was also used to convert waste beef tallow from tanneries and slaughterhouses [164], waste chicken fat chicken from chicken processing units [165], and swine fat from meat processing companies [166] to quality biodiesel at moderate operating conditions. Kitchen, garden, and food waste were used for bioethanol production through fermentation and the residue was subjected to AD for biogas production [167][168][169][170]. Waste activated sludge, waste peach pulp, and waste tires were also used as feedstocks in studies on the production of biohydrogen that explored fermentation and gasification technologies [171][172][173]. Other forms of waste have also been converted to biofuels for ICE applications. The conversion of this waste to biofuels is cost-effective and ensures waste minimization and appropriate waste disposal, sanitation, and waste management. Table 9 shows some of the recently investigations on the conversion of waste to biodiesel, biogas, bioethanol, and hydrogen.

Biofuel as Internal Combustion Engine Fuels
Transportation is one of the necessities of life and a major contributor to the socioeconomic growth of countries. The ease of the movement of goods and services is one of the measures of the quality of life of individuals. Governments across jurisdictions devote significant efforts and resources to ensure affordable and safe transportation services. The transportation sector consumes over 90% of the total FB fuel products and over 25% of global energy [174,175]. The proportion of the total energy used for on-road transport is projected to increase from the present 28% to 50% by 2030 and further to 80% by 2050 [176]. The total energy consumption in the transport sector was 110 million TJ in 2015 including passenger vehicles (cars and bikes), buses, air, passenger rail, and air freight. Heavy trucks, light trucks, and marine transport jointly consume 35% of the transportation sector energy, as shown in Figure 8    Currently, there are about 1.2 billion vehicles on the road and this number is projected to rise to 2 billion cars by 2035 and further to 2.5 billion cars by 2050 [180,181]. If these cars depend on FB fuels, the attendant environmental effects will be disastrous and the cost unimaginable. Biofuel, hydrogen, and electric vehicles (EVs) are the three options for low-carbon transport systems. Though hydrogen and EVs avoid land use and impact air quality, ICEs will still be in use in most developing countries for the foreseeable future [182].
Liquid and gaseous biofuels are used to power ICEs. However, liquid biofuels are preferred over gaseous biofuels for vehicle propulsion. This is because liquid biofuels have a higher energy density than gaseous fuels, thereby allowing vehicles to possess immense range. Table 10 shows the energy stored per liter for petrol or petroleum-based gasoline (PBG) fuel, PBD fuel, and some biofuels. Gaseous fuels require pressurized tanks and they must be larger for an equal quantity of stored energy compared to liquid fuels. Also, refueling is more straightforward, easier, and faster with liquid fuels than gaseous fuels. The use of a fuel as an ICE fuel depends on its properties. Table 11 shows some properties of diesel, gasoline, and some liquid and gaseous biofuels. The density is calculated as the mass per unit volume. The density of a fuel is determined by the mass of fuel entering the combustion chamber and the air/fuel ratio. A higher heating value (HHV) is the quantity of heat realized when a unit amount of fuel is completely combusted. HHV is obtained by cooling the products of combustion, leading to the formation of water vapor [184,185]. The HHV of fuel is directly proportional to the quantity of carbon in the fuel and the ratio of C-H to O 2 -N 2 . Conversely, the lower heating value (LHV) of a fuel is the energy content of the fuel. The distinction between the HHV and LHV is a measure of the heat content of the condensed water vapor formed during combustion. The density and heating values determine the energy available in the fuel, along with the volume and mass. The cetane number (CN) is a function of the amount of time lag between the fuel injection and auto-ignition [184]. The CN is used to classify PBD fuel and measures the ability of the fuel to self-ignite. Fuels with high CNs are good for CI engines because this ensures that the engine enjoys an excellent start and runs smoothly, particularly during cold weather. A low CN tends to result in incomplete combustion and exacerbates the emission of dangerous gases [186].
Kinematic viscosity is a property that influences the atomization properties, the size of the droplets and spray penetration, and the potential of atomized fuel. Fuels with high kinematic viscosity values suffer from poor fuel atomization during the spray and increased wear rate of the engine, pump parts, and injectors, which jointly result in poor combustion and increased emissions [187]. Ethanol and dimethyl ether have lower viscosity values and are more capable of making fine droplet sprays than PBD fuel. The flash point measures the temperature at which sufficient water vapor is released to generate the appropriate quantity of the water vapor-air mixture and relates to the safe handling and transportation of the fuel. A fuel with a flashpoint below 38 • C (100 • F) is considered flammable [188]. The latent heat of vaporization quantifies the degree of coolness experienced as a result of fuel evaporation. The stoichiometric air/fuel ratio (A/F) of a fuel is a measure of the hydrogen/carbon ratio of the fuel and the quantity of oxygen contained in the compound [189]. The research octane number (RON) is also used to classify PBG fuel and measures the ability of the fuel to self-ignite. High RONs are good for spark ignition (SI) engines [190]. The Reid vapor pressure is also a critical fuel fingerprint for measuring the behavior of fuel, particularly when the SI engine is appropriately carbureted and fueled. The ease with which the spark ignites the air/fuel mixture indicates the flammability limit of the fuel. Hydrogen fuel, a form of renewable fuel, is reputed to possess the highest flammability limit. Table 11. Physical and chemical properties of some transportation fuels [183,[191][192][193][194].

Utilization of Biofuels in Spark Ignition Engines
Generally, for a particular fuel to be suitable as a renewable alternative fuel for SI engine applications, it must meet the requirements for the octane number, flammability, combustion stability, the heating value of the air-fuel mixture, the laminar burning velocity, vapor pressure, the boiling curve, and volatility [195]. Against this backdrop, alternative fuels for SI engines can be categorized as either liquid biofuels or gaseous biofuels. Liquid biofuels include bioalcohol (methanol, ethanol, butanol) and gaseous biofuels include biogas and hydrogen. These are the preferred renewable alternatives to replace PBG fuel because of their advantages [174], which include: (i) higher octane numbers than PBG fuels; (ii) fewer olefins and aromatic-structured hydrocarbons than PBG fuels; (iii) lower sulfur content; (iv) higher flash points; (v) safer handling; (vi) better cold flow properties. Furthermore, bioethanol has a higher latent heat of vaporization compared to PBG fuels, and alcohol fuels (oxygenated fuels) have (i) high oxygen content; (ii) lower Reid vapor pressure, resulting in lower emission of volatile organic components during filling at gas stations; and (iii) a lower carbon-to-hydrogen ratio than gasoline fuels, resulting in lower carbon-based emissions. However, there are some drawbacks to the use of these renewable alternatives, including [174]: (i) for alcohol fuels, lower calorific values compared to PBG fuels, resulting in lower power output, (ii) cold starting problems as a result of the high latent heat of vaporization values of renewable fuels, (iii) the oxygenated nature of the alcohol-based fuels, which leads to the generation of more NOx, although NOx emission is reduced due to the high latent heat of vaporization values of renewable fuels.
Biogas, a form of gaseous biofuel, is produced by the digestion of waste. Digestion is a biochemical conversion process for the biological decomposition of waste bacteria either in the presence (aerobic) or absence (anaerobic) of oxygen. Anaerobic digestion (AD) is the preferred method of biogas production due to the following advantages [196]: (i) more efficient organic removal, (ii) the higher organic loading rate, (iii) lower nutrient requirements, (iv) reduced energy consumption, (v) better odor control, (vi) the digestate can be used as fertilizer, (vii) reduced costs for bedding materials, (viii) reduced pathogens associated with manure discharges, (ix) better operational flexibility, and (x) it can provide an extra source of revenue from the sales of the slurry. During AD, various species of bacteria and specialized microorganisms take part in the breakdown of the complex organic matter in the various forms of animal waste that serve as feedstock into smaller molecules to generate a methane-rich gas called biogas. The AD process takes place in an airtight reactor called a digester. The process reaction is as shown in Equation (1), while Table 12 shows the four major steps involved in AD.

Steps and pH Process Reaction Equations Microorganisms
Step 1: Hydrolysis pH = 5.5-6.0 Breakdown of large organic polymers (carbohydrates, fats, and proteins) in biomass into smaller molecules (amino acids, fatty acids, and simple sugars) to produce hydrogen and acetate (c 6 H 10 O 5 ) n + nH 2 O = n(C 6 H 12 O 6 ) Clostridium, Proteus, Vibrio, Bacillus, Peptococcus, Bacteroides, Staphylococcus Step 2: Acidogenesis pH = 6.0-7.0 Acidogenic microorganisms further break down the organic matter in the biomass into smaller molecules to generate an acidic environment. The fermentative bacteria generate NH 3  Step 3: Acetogenesis pH = 6.0-7.0 Acetogens catabolize the products of acidogenesis into acetic acid, CO 2 , and H 2 , which are later converted to methane (CH 4 ) by methanogens

Methanoplanus, Methanospirillum
Biogas is used to power SI engines either as raw biogas or enriched biogas. Raw biogas is approximately 60% CH 4 and roughly 40% CO 2 with H 2 S, N 2 , and H 2 in trace proportions [199]. Raw biogas suffers from lower flame velocities and calorific values when compared with gasoline fuel. SI engines fueled with raw biogas thus have poor combustion characteristics, lower thermal efficiency, higher specific fuel consumption, lower power output, and higher emissions of CO and HC because of the lower flame velocity, less adiabatic flame temperature, and lower calorific value of biogas compared to PBG fuels. To enhance the quality of the unrefined biogas, the CH 4 content of the biogas can be enriched and the CO 2 , H 2 S, and water content reduced or removed. The upgraded biogas is called biomethane and possesses acceptable specifications for ICEs [200]. Various technologies and techniques have been successfully employed, at household and commercial scales, to upgrade and enrich biogas, including physical and chemical absorption, gas filtration, low-temperature separation, and various methods of scrubbing [198][199][200][201][202][203].
The CH 4 content of enriched biogas can be as high as 95% [198]. Though enrichment of biogas imposes an additional cost on the fuel, biomethane is ultimately more valuable when factors relating to storage, pipeline gas transportation, and the superior performance and the reduced emissions characteristics of SI engines compared to raw biogas are taken into account. The application of biomethane as an SI engine fuel ensures clean combustion, which gives rise to low particulates and NOx and decreased infiltration of engine oil. To use biogas to power an SI engine, the carburetor must be replaced with a device for mixing air/biogas [204]. Generally, biogas is employed to power both light-and heavy-duty vehicles. A gasoline car can be converted to run on biogas as a secondary fuel by attaching a separate fuel supply structure and airtight storage cylinders for the biogas [205]. The use of biomethane is becoming remarkably widespread in Germany, Sweden, and the United Kingdom, where biogas generated from municipal waste and wastewater remediation plants is being employed as alternative fuel for buses and other on-road SI engines [206]. Biomethane utilization in the transport sector is projected to rise from about 1 billion m 3 in 2016 to 13 billion m 3 in 2050 [179].
Hydrogen, which has been used in the hydrocracking of petroleum products, ammonia production, the heat-treating and refining of metals, the catalytic hydrogenation of organic compounds, fertilizer production, glass purification, and other applications, has also found uses as an alternative fuel for SI engines as part of emission mitigation strategies. An estimated 120 million tons of hydrogen, equivalent to 14.4 EJ, are produced annually, with about 95% produced from fossil fuels (natural gas and coal) and the remaining 5% generated by the electrolysis process [207]. Various technologies have been deployed for the production of hydrogen to meet its growing demand. Photochemical, thermochemical, and electrochemical methods are the three main technologies that have been employed for the production of hydrogen from various sources [208]. Fuel hydrogen is also generated using biological routes, including direct and indirect bio-photolysis and dark fermentation and photofermentation with organisms like cyanobacteria and green algae [209]. Sharma and Ghoshal [210] surveyed various technologies for hydrogen fuel production, including steam methane reforming, gasification of coal, electrolysis of water, and technologies using biomass and nuclear energy. The application of hydrogen as a substitute fuel for SI engines has been reported by various researchers [211,212].
The utilization of hydrogen fuel to power SI engines has gained wide acceptance thanks to its benefits. The distinctive fingerprints of hydrogen, such as its low ignition energy, high diffusion coefficient, flammability, high flame velocity, and high octane number, make it a favorable candidate for SI engines [213]. The use of hydrogen ensures clean combustion, higher thermal efficiency, and zero emission of CO, CO 2 , HC, PM, and other carbon-based substances. SI engines fueled with hydrogen entail technical challenges, such as backfires, power drops, and high NOx emissions [174,214]. To evade these drawbacks, hydrogen can be blended with a quantity of CH 4 to ensure good knocking resistance, a richer air/fuel mixture, and better power performance [214].
Bioethanol is one of the most prominent biofuels because of its easy production method and the use of native and readily available raw materials as feedstocks. Currently, bioethanol accounts for about 65% of total biofuel production, with global production projected to increase from 100.2 billion liters in 2014 to about 134.5 billion liters by 2024 and the USA and Brazil leading the producing countries [215]. Bioethanol is produced through the fermentation of various raw materials including sugarcane molasses, sugar beet, sweet sorghum, rice, potato, sweet potato, barley, and fruit and vegetable waste. Fermentation is a biochemical process for the anaerobic conversion of the simple sugars obtained from hydrolysis of lignocellulosic biomass into bioethanol. The process of conversion of lignocellulosic biomass into simple sugars is a complicated procedure due to the existence of long-chain polysaccharide molecules, and it therefore demands acids or enzymes. The anaerobic catabolism of simple sugar by microorganisms yields alcohol, gas, or organic acid, as shown in Equation (2) [216].
There are three types of microorganisms frequently utilized for the conversion of lignocellulosic biomass to bioethanol: yeasts, bacteria, and fungi. Yeasts have proven to be the best microorganism for fermentation of biomass to bioethanol. In particular, the yeast Saccharomyces cerevisiae, operating at a temperature of 30 • C, pH 5.5, and with a fermentation time between 48 h and 65 h, resulting in an ethanol yield of 130.13 g/L [217], and the bacterium Zymomonas mobilis, operating at a temperature of 30 • C, pH 6.0, and with a fermentation time of 18 h, resulting in an ethanol yield of 99.78 g/L [218], have been used for commercial production of ethanol.
The homolactic and heterotactic fermentation processes, shown in Equations (3) and (4), respectively, are employed for the production of organic acids. (3) The produced ethanol is distilled and desiccated to high-octane, waterless alcohol. In addition to feedstocks such as sugar crops and starch crops, lignocellulosic biomass, like wood and cereals, can be converted to ethanol [219,220]. Table 13 shows the effects of some alternative fuels on the performance and emission behaviors of SI engines.   [235] C = cylinder, N = engine speed, NA = naturally aspirated, S = stroke, IMEP = indicated mean effective pressure, Vs = swept volume, r = crank radius, bTDC = before top dead center, ITE = indicated thermal efficiency, BP = brake power, BTE = brake thermal efficiency, BSFC = brake-specific fuel consumption, ↑ = increased, ↓ = reduced.

Utilization of Biofuels in Compression Ignition Engines
Compression ignition (CI) engines have better thermal efficiency than SI engines and have found applications in diverse areas, including transportation, construction, agriculture, and power generation. The need for renewable fuel to power CI engines results from the poor performance and hazardous emissions, particularly of CO, UHC, NOx (NO and NO 2 ), and PM, of CI engines fueled with PBD fuel. The selection of fuels for CI engines is based, primarily, on the cetane number of the fuel. A fuel candidate for CI engines must meet some important criteria, namely [195]: a good cetane number, appropriate boiling point, a narrow density and viscosity spread, and low aromatic compound content. Such fuel must ensure quality ignition, combustion without knock, and smooth running of the engine. Biodiesel, Fischer-Tropsch (F-T) fuel, and dimethyl ether (DME) are the preferred renewable fuels for CI engines because of their [174] higher cetane numbers and lower levels of olefins and aromatic-structured hydrocarbons compared to PBD fuels. Furthermore, biodiesel and F-T fuels have higher flash points than PBD fuels, but F-T and DME fuels have better cold flow properties than biodiesel.
Biodiesel and its blends have been used to power CI engines due to their characteristic oxygenated fingerprints, which support complete combustion. Though the combustion, performance, and emissions characteristics of biodiesel as a CI engine fuel have been studied, the determining factors that have engaged the interest of researchers are the improved performance and mitigated emissions characteristics of unretrofitted engines fueled with biodiesel. Over the years, biodiesel has been produced from various feedstocks, and the products have been tested and compared with PBD fuel using the BSFC, BTE, BP, and EGT as performance criteria and measurement of NOx, PM, UHC, and CO emission benchmarks. The ultimate goal is to make biodiesel-fueled CI engines consume less fuel, generate more power, and emit less hazardous gases [174,236]. Biodiesel, due to its increased oxygen content, has low calorific values and consequently emits more NOx emissions and suffers from power drops.
F-T diesel is produced through a catalytic chemical reaction where syngas derived from biomass are converted into hydrocarbons of various molecular weights. The H 2 and CO in the syngas are involved in the reaction according to Equation (5). The reaction takes place at a temperature range of 200-350 • C and pressure range of 390-660 psi. The Fischer-Tropsch process is a catalytic exothermic reaction that can take place in a fixed bed, fluidized bed, or slurry bed reactor in the presence of iron, cobalt, or nickel catalysts [209,210].
F-T diesel has a higher calorific value, higher cetane number, and lower density than PBD fuel. F-T diesel fuel contains more paraffinic compounds, has a lower C/H ratio, lower in-cylinder temperature, lower aromatic or sulfur content, and better combustion properties, resulting in lower NOx, UH, CO, and PM emissions in comparison with PBD fuel. F-T diesel has better cold flow properties and superior transportation and storage properties when compared with biodiesel. F-T diesel-fueled CI engines emit less NOx emissions and suffer from fewer power drops, making F-T diesel a better renewable fuel than biodiesel for CI engine applications [237].
Dimethyl ether (DME) a clean, colorless, non-toxic, and degradable gas, which was originally applied as an aerosol propellant and in LPG blending for cooking, has become a prominent alternative to FB fuels. Currently, there is large-scale production of DME in many countries, including the USA, Canada, Uzbekistan, Russia, Mexico, Brazil, Argentina, China, Japan, Sweden, India, and South Korea. According to the International DME Association, current global production is about 9 million tons per annum while the global market size, which was USD 5.6 billion in 2020, has been projected to reach USD 9.7 billion in 2027 [238,239]. DME can be produced from biomass, coal, municipal waste, natural gas, methanol, agricultural bio-products, and other bio-based feedstocks through either direct or indirect routes. In the indirect production route, methanol is hydrogenated from syngas and the product is purified and dehydrated. Direct synthesis of DME is achieved in a single-stage process directly from syngas in an exothermic reaction [207]. Inayat et al. [208] investigated the use of an empty fruit bunch as feedstock to synthesize DME in a production process that involved gasification, waster-gas shift reactions, and CO 2 removal. Partial oxidation, gasification, Boudouard, methanation, and methane-reforming reactions take place during the gasification stage. The schematic diagram of the production process is shown in Figure 10, while Equations (6)- (13) are the reaction equations [208].
As a result of its many applications, the global DME market, appraised at USD 4790 million in 2017, is projected to reach USD 9100 million in 2024 [238]. DME as a CI engine fuel discharges low NOx, SOx, and soot emissions and has outstanding combustion attributes [239]. The choice of DME (CH 3 OCH 3 ) as a sustainable fuel for CI engines is strengthened by its superior oxygen content, which allows better combustion and lower NOx, UHC, and smoke emissions, higher cetane numbers, and shorter ignition delays than PBD fuel. The emission of less smoke and PM can also be attributed to the lack of C-C bonds, as DME has only C-H and C-O bonds. DME-fueled CI engines offer the best emissions when compared with biodiesel and F-T diesel, but its utilization as a vehicle fuel and its adoption for vehicle fleets is hampered by the lack of production, storage, transport, and dispensing infrastructures. Also, DME has lower lubricity, resulting in increased wear of moving parts; lower viscosity, which can cause leakages in fuel pumps and fuel injectors; and higher flammability limits than PBD fuel [174,237,240]. Table 14 shows data on biodiesel-, F-T diesel-, and DME-fueled CI engines in terms of their performance and emission characteristics.  ↑ = increased, ↓ = reduced, DI = direct injection, EGT = exhaust gas temperature, VCR = variable compression ratio, SO = smoke opacity, C = cylinder, N = engine speed, NA = naturally aspirated, S = stroke, IMEP = indicated mean effective pressure, Vs = swept volume, r = crank radius, BP = brake power, BTE = brake thermal efficiency, BSFC = brake specific fuel consumption.

Prospects for Biofuel Conversion Techniques
The application of biofuel as an alternative to FB fuels faces many challenges associated with its conversion technologies. There are concerns about the use of water in the conversion process, conversion costs, energy requirements, the availability and maturity of conversion technologies, and the carbon neutrality of the conversion technologies, which all need to be considered and addressed [251]. For this to occur, there is a need for technical, economic, and life-cycle assessments of the various conversion technologies. The drawbacks associated with the production of 1GB and 2GB biofuels are partly being overcome by the conversion technologies of 3GB and 4GB biofuels, such as the use of the microalgae conversion processes [109].
Microalgae feedstock no doubt offers some advantages when compared to conventional crop plants. Microalgae, which are sophisticated microorganisms, can be cultivated with less effort, have multiple cultivation cycles, offer better photosynthetic performance, have short harvesting cycles (less than 10 days), and offer significant continuous and enhanced yields. The various methods of algae cultivation like open ponds and close photobioreactors, and the algae conversion technologies, like oil transesterification, ethanol fermentation, anaerobic digestion, etc., are still at the laboratory or pilot stages. Commercial and large-scale implementation is plagued with uncertainties that are yet to be addressed. Apart from the technical issues, like photobioreactor design, other economic and operational challenges need to be dealt with. Large-scale algae cultivation through photobioreactors, though practicable and effective, is still expensive and not commercially viable. The less expensive and less technically demanding open-pond algae cultivation is susceptible to evaporation and contamination by native algae species. For these reasons, algae harvesting and processing are not yet being undertaken at a scale that would make the large-scale generation of liquid biofuel from microalgae technically feasible and economically realistic [252,253].
The transformation of biomass into hydrocarbon fuels through aqueous phase reforming (APR) has been proposed [254,255]. Through APR, compounds like glycerol, sugars, and sugar alcohols can be obtained from biomass and converted into hydrogen and light alkanes. In these cases, the raw materials are in the liquid phase while the products are generated at lower temperatures compared to with gasification or pyrolysis, thereby averting costly and highly energy demanding vaporization processes. The conversion of sugars into paraffin molecules through fermentation by direct sugar-to-hydrocarbon technologies could offer a pathway to biofuel production on a commercial scale when fully developed and harnessed [256,257].
The use of combined technologies for biofuel production through renewable solar fuel generation, called helioculture, offers hope for better biofuel conversion technology in the future. This highly innovative conversion pathway produces ethanol or hydrocarbons directly and any upgrade of the technology will not be difficult to apply in practice. For example, the authors of [106] generated over 20,000 gallons of fuel per acre per annum (or 19,000 m 3 per square kilometer).

Implications
Biofuels have been widely accepted as alternative fuels for the transportation sector to enhance the performance of transport vehicles. The challenges associated with the application of FB fuels as ICE fuels include operational, performance, safety, cost, infrastructural, and availability challenges. The conversion of various categories of waste into useful fuels has become advantageous in terms of economic, sanitation, availability, and environmental considerations. The choice of feedstock, conversion technology, production infrastructure, and utilization platform cannot be restricted to fuel producers and engine manufacturers but must involve professionals from many disciplines, including finance, plant science, microbiology, chemical engineering, mechanical engineering, process engineering, environmental science, food science, agronomy, and more. Investigations into areas such as metabolic engineering, processing subsidizations, tax immunity, feedstock identification, equipment development, engine modifications, land use regulations, and the use of artificial intelligence, are needed to ensure the sustainable production and application of biofuels [258][259][260]. Political leaders from various jurisdictions, policymakers, funders, investment analysts, and other development partners must unite in making biofuel production and utilization worthwhile and sustainable.
The current review contributes to the body of knowledge by providing up-to-date information on the classification, production, and utilization of biofuels with a view to enhancing and enriching the available data. A new vista in the classification of biofuels is here unveiled to ensure more comprehensive knowledge and information sharing along the biofuel value chain. Deployments of biodiesel, biogas, F-T diesel, DME, and bioethanol to replace FB fuels in SI and CI engines have been highlighted from the perspectives of performance and emissions advantages. The outcomes of this investigation enable renewable fuel refiners, engine designers, emission specialists, environmentalists, and consumers to be better informed about the strategies available to boost the performance and emissions characteristics of ICEs through the application of biofuels.

Conclusions and Outlook
The application of renewable fuels offers benefits and advantages. Their utilization can improve the environmental condition and air quality since only a low amount or no GHGs are generated. Biofuels can also solve energy security and poverty issues by making energy available equally without undue discrimination and political victimization. They can make affordable energy available, stabilize energy prices, provide employment, and improve living conditions. Studies have shown that reductions in GHG emissions have led to reduced cases of health problems and contribute to healthy living and wellbeing. The production of some forms of biofuel, like biogas and biodiesel, contributes to proper waste disposal and conversion of waste to energy for household use, thereby reducing the cost of energy for heating and cooking in rural households. However, there are some limitations to the adaptation and utilization of biofuels and bioenergy as sustainable alternatives to FB fuels. The high initial cost, highly technical conversion technologies, and highly skilled personnel required limit the application of some categories of biofuel and bioenergy. Some of the technologies for the utilization of some categories of biofuels cannot be deployed domestically, thereby limiting their accessibility and utilization. The adap-tation of existing FB fuel distribution and transportation infrastructures needs time and financial resources and is unaffordable for individuals and households.
With the increased popularity of EVs, more innovative research along with technologies that allow the efficient use of biofuels as flexible hybrid fuels are needed to fully enjoy the benefits of biofuel as a transport vehicle fuel. The requirement to mitigate GHGs and other emissions presents an incentive and a giant motivation for the utilization of biofuels, but an appropriate infrastructure and policy framework needs to be in place to ensure gradual uptake. Given the right environment and context, and the political will of governments at various levels, biofuels can be strong drivers for a cleaner environment through waste minimization, proper waste disposal, effective waste conversion, and mitigation of climate change. However, adequate controls are required, as the extent to which biofuel can be deployed sustainably is constrained by the available land, infrastructure, technical know-how, and sustainable practices. Effective policies, education, awareness campaigns, and programs, along with more research and development initiatives, are needed to ensure that the lifecycle emissions from biofuel offer substantial savings compared to FB fuels. There is a need for sufficiently sustainable frameworks and techniques to ensure GHG emissions are not created in the processes of conversion and deployment in the biofuel value chain.