Set of policies ordered by global biofuel producers.
Abstract
Fossil fuels oil, coal, and gas are valuable resources that are depleting day by day around the world and also imparting a negative impact on the environment. Biofuel because of its dynamic properties; its market values; and being sustainable, renewable, biodegradable, economic, non-pollutant, and abundant is an alternate source of energy. Each country can produce it independently, and because of these valuable properties biofuels have become superior over fossil fuels. This chapter gives a concise preface to biofuels and its impact on the environment. It includes definitions; classifications; impact on environment; implications; types of production techniques like chemical, biochemical, physical, and thermochemical techniques; types of resources like lignocellulosic-biomass, feedstock energy crops, algae, micro-algae, all kinds of solid wastes; and biofuels of prime importance like solid biofuels (biochar, solid biomass), gaseous biofuels (biogas, bio-syngas, and bio-hydrogen), and the most important liquid biofuels (bioethanol, biodiesel, and bio-oil). Due to increasing global warming and climate-changing conditions, in the near future biofuel being an environment-friendly resource of energy will be a substantial part of the world’s energy demand, with no or zero polluting agents.
Keywords
- biofuels
- biodiesel
- renewable energy resources
- global warming solutions
- alternate of fossil fuels
- energy investment
- future fuels
- biodiesel
- ethanol
- oils
- TAGs
- biogas
- green-diesel
- algae
- macroalgae
- plants
- wood
1. Introduction
Biofuels: a term that has broad implications in regard to the world’s needs, biofuels have been a part of human life for a long time ever since the first person burned wood to get heat. Over time, he found the value of heat and started cooking by burning wood. So, the biofuels have an extended history than humanity’s record and civilizations because these were present in the form of grass and wood before when we human beings found and used the fire.
With the progression of human civilizations, biofuels took an important place in the human’s life. For example, CH4 gas also known as domestic gas or biogas was used to warm water to take a bath in the 10th BC [1]; CH3CH2OH or bioethanol was used in a combustion engine in 1826 [2]; Sadi’s Carnot engines used biodiesel also known as Rudolph’s diesel [3]; and for the very first time, peanut oil was used in the busses and trucks in 1896 [4]. Many other such applications developed and changed people’s lives around the world [5].
In contrast with fossil fuels natural gas, coal, and oil, biofuels have some advantages:
These are renewable [6]
Resources of biofuels are abundant [6]
Biofuels do not play any role in ozone layer depletion as these are neutral to greenhouse gases [7]
Sulphur oxide emissions are zero or negligible [8]
They result in fewer nitrous oxide emissions [9]
Biofuels are friendly to the environment [10]
These are easy to produce [11]
All biofuels are biodegradable [12]
All kinds of biofuels are sustainable [13]
Biofuels production procedures are safe [14]
Biofuels also have some economic benefits:
These fuels will lead to rural and agricultural development [15]
These fuels enhance supply range [16]
They lead to reduced dependence of energy on imports [14, 17]
They improve rural economy [16].
To increase and promote the biofuel industry, several countries have planned many rules and objectives. Here, documents issued in the European Union, USA, Brazil, Thailand, India, and China are mentioned in Table 1.
Country | Target or mandate | References |
---|---|---|
EU | Mandate: minimum of 10% of transport fuel from renewable fuels by 2020 | [19] |
United States | Mandate: 36 billion gallons of biofuel by 2022 | [19] |
Brazil | Mandate: biodiesel use set at 10% by 2020 | [19] |
India | Indicative: 20% blending for both ethanol and biodiesel by 2017 | [19] |
China | Target: solid biofuels (10,000 t/year), biogas (billion m3/year), nonfood bioethanol (10,000 t/year), biodiesel (10,000 t/year) by 2020 | [19] |
China | Target: 12.7 Bnl ethanol and 2.3 Bnl biodiesel consumption in 2020 15% of fuel consumption to be non-fossil fuel by 2020 |
[19] |
Thailand | Ethanol: E20 mandatory since 2008 Biodiesel: B2 mandatory since 2008 and B5 since 2012 |
[19] |
2. Biofuel
2.1 Definitions
The term fossil fuels was used for fuels like natural gas, coal, and oil gotten from the decomposition of different plants and a variety of animals that remain buried underneath the earth’s deepest layer for many years [14]. Over time, the word “biofuel” started being used. Till now, there are many distinctive definitions for the word “biofuel.” Some of these statements are
Bio-fuels are obtained from or with the help of microorganisms [14].
Biofuels are those fuels that are obtained from biomass, petroleum, natural gas, and firewood [20].
We derive these from different biological and plant materials [21].
Bio-fuels are the products obtainable from natural resources, which include timber, peat or bagasse, or transformed chemically from biomass to synthesize ethanol, charcoal, bio-oil, and biogas [4, 22].
These fuels are extractable from biomass feedstock or waste materials [15].
Bio-fuels include liquid, solid, and gaseous fuels obtained from organic material like plants and animals [19].
These are also known as the renewable fuels like biodiesel, bio-hydrogen, charcoal, bioethanol, and biogas obtained from biomass gotten from the organic waste materials and are reliable for transportation [10, 19, 23].
Liquid biofuels: these include biodiesel extracted from fats and oils, bioethanol extracted from lignocellulosic material, sugar and starch, etc. [18].
According to the above definitions, “biofuel” can be defined as any kind of fuel that is produced by or from any renewable living organisms.
2.2 Significance
“Biofuels” or “bio-fuels” are significant in many ways such as:
Biofuel is employed to supply heat, energy, light, and power.
Biofuel is also claimed as a living fuel, that is produced from different living micro/macro-organisms: (the “bio” springs from the Greek word “bios,” means “life”); these are the ways in which these fuels differ from all other fuels like fossil fuels having hydrogen and carbon.
Biofuels are renewable, therefore the living organism can reproduce it in a relatively short time. While fossil fuels took many years and are non-renewable (this property of biofuels made it significant over fossil fuel).
Biofuels might be obtained from plant structure, water algae, micro-algae, manure, animal waste, sludge, etc.
Biofuel could be a solid, gas, or liquid.
One type of biofuel is interconvert able to another type of fuel.
2.3 Classification
As we know there are many definitions of “biofuels”; similarly there are many classifications of biofuels according to different eras and research groups. According to the very first classification based on commercialization position of the biofuel production and resources, these are usually classified into two groups: one is conventional biofuels and the other is advanced biofuels (Figure 1). Commercialization can be ranked accordingly: research < demonstration < early commercial < commercial. The conventional or traditional bio-fuels contain such biofuels that are based on biodiesel gotten from the trans-esterification process; bioethanol obtained from starch and bio-methane or biogas from animal waste obtained via anaerobic digestion process. With regard to advanced bio-fuels, an early commercial-stage biofuel is a hydrologically treated oil. The demonstration level and research level stages contain lignocellulosic or cellulosic bioethanol, BtL (biomass-to-liquid) biodiesel, bio-hydrogen, and biodiesel obtained from micro-algae. We know that advanced biodiesel is not dominant at commercial level but because of its environmental and economic demand, it will be dominate in the market and will be fully commercialized in more advanced form in near future. Based on feedstock resource availability and synthetic techniques, many researchers classify this biofuels into two groups like 1st-generation and 2nd-generation biofuels [24, 25]. This classification is shown in Figure 2. Biofuels of 1st generation contain biodiesel, biogas, and bioethanol [24, 26]. The unsaturated and saturated edible plant-oils obtained from the corn, soybean, sunflower, canola-seeds, and some oils containing fruits like palm, olives, and coconut are categorized under liquid bio-fuels [25, 26]. It also has been stated in different researches that the solid biofuels like agricultural waste material, dried manure, and fire-wood are also part of the 1st-generation biofuels. The lipid-derived bio-fuels obtained from the waste of vegetable-oils, insects, animal fats, and oil-producing microbes are categorized under biofuels of 2nd generation [25]. At present biofuels of 1st generation are fully commercialized, while 2nd-generation biofuels are still under developmental stages [24].
Biofuel’s generations according to many other studies are classified in 1st, 2nd, and 3rd-generation biofuels [10, 27] mentioned in Figure 3. Biodiesel, biogas, bio-alcohols, bio-syngas, and vegetable oil, which are commonly known as biofuels of 1st generation and obtained from edible crops: wheat, soybeans, vegetable oil, starch, corn, sugar, and grains, [28], are also contained within ryegrass, straw, wood, domestic refuse, switchgrass, grass cake, charcoal, grass cuttings, and dried manure [29]. The biofuels of 2nd generation includes biodiesel-FT(Fischer Tropsch), dimethyl ether, bioethanol, bio-syngas, biodiesel BTL(biomass-liquid) are synthesized from feedstock (lignocellulosic-biomass), nonfood material like cereal straw, wood grass, forest residues, sugar-cane, bagasse, energy crops (vegetative plants and short lifecycle forests) and domestics waste material [10, 30, 31].
The biofuels derived from feedstocks that are aquatically cultivated like cyanobacteria, algae, and micro-algae are 3rd-generation biofuels; these include biodiesel, bio-methane, bio-butanol, aviation fuels, bioethanol, jet fuels, gasoline, and vegetable oil [10, 32].
In another classification, biofuels are categorized into two groups: (i) primary biofuels included many solid biofuels without modifications like wood, grass, and wood slices that are burned for heating purposes and to cook different foods directly and (ii) secondary type biofuels have three generations of biofuels shown in Figure 4 [33, 34].
According to some studies, biofuels are categorized into four groups: (i) natural bio-fuels are derived from simple organic materials like firewood, plants, vegetables, landfill gas, and animal waste and are used for heating, cooking, brick kiln, and production of electricity; (ii) the biofuels of 1st generation are obtained from eating able feedstocks, mostly palm, wheat, corn, soybean, maize, rapeseed, sugarcane, sugar beet, and oil crops [34]; (iii) the lignolytic feedstocks contain jatropha, miscanthus, sterculia, ceiba foetida, switchgrass, pentandra, and poplar are included in the 2nd-generation biofuels; (iv) algae feedstocks are the main source of 2nd generation biofuels Figure 5 shows its classification [34].
With the advancement of research, oil-containing (jatropha) crops and nonfood (cassava) crops were known as one and a half- or 1.5-generation bio-fuels. Then biofuels took a new place in the classification tree and were re-classified into four groups: (1G) 1st-generation, (1.5G) 1.5-generation, (2G) 2nd-generation, and (3G) 3rd-generation of biofuels as shown in Figure 6. Some researchers grouped these bio-fuels as 1st, 2nd, 3rd, and 4th generations of biofuels [3, 35, 36, 37, 38, 39, 40]. Figure 7 shows all the four groups and the uses of biofuels and types of feedstocks that were used to produce these four generations of bio-fuels are represented in Table 2. Some important merits versus demerits are also briefly described in Table 3. With the advancement of biofuels production and kind, we can classify these into the five different groups: 0th, 1st, 2nd, 3rd, and 4th generations of biofuels, as shown in Figure 8.
Biofuels | Examples | Feedstocks |
---|---|---|
1st generation | Bio-alcohols, vegetable oil, biodiesel, bio-methanol, bio-syngas, biogas | Sugar, starch, animal fats, soybean, soya, rapeseed, mustard, sunflower, maize, sugarcane, sugar beet, sorghum, potato, palm oil, coconut, canola, plant, cassava, castor, jatropha, sewage waste |
2nd bio-alcohols, bio-oil, biodiesel, bio-DMF, generation | Bio-methanol, bio-Fischer-Tropsch diesel, bio-hydrogen | Nonfood crops, wheat straw, corn, wood, switchgrass, cereal straw, sugarcane bagasse, reed canary grass, forest residues, energy crops, municipal solid wastes, alfalfa, agave, jatropha |
3rd generation | Bioethanol, vegetable oil, biodiesel, bio-methanol, jet fuels | Microbial species, algae, yeast, fungi, cyanobacteria |
4th generation | Green diesel, bio-gasoline, green aviation fuel | Vegetable oil, biodiesel |
Biofuel | Merits | Demerits |
---|---|---|
1st generation | Biodegradable | 1. Competition of land use |
Energy security | 2. Blending with conventional fuel | |
Feedstock can be easily produced by already existing infrastructure and technology | 3. Highest carbon footprint compared with other generations of biofuel | |
Environmental and social benefits | 4. Requires large amount of inputs in terms of fertilizer, water and land area thereby reducing net energy ratio | |
Feedstocks available at large quantities | 5. Contributes to higher food prices owing to competition with food | |
6. Might potentially have negative impacts on biodiversity | ||
2nd generation | 1. No competition with food | 1. Even though requires less compared to 1st-generation biofuels, the land required for production of 2nd-generation feedstock is substantial |
2. Use of whole plant instead of only seeds or grains, and use of residues means more energy produced per hectare of land | 2. The use of agriculture and forest residue degrades soil quality and also induces soil erosion | |
3. Marginal lands can be used for planting of advanced feedstock such as |
3. Complex processes are required | |
4. Higher yield and lower land requirement | 4. Low conversion as compared with petroleum fuel | |
5. Available feedstocks in large quantities | 5. Conversion technologies are under development | |
6. Feedstock can be easily produced by already existing infrastructure and technology | 6. Lack of technological and research breakthrough | |
7. Low cost for feedstock | 7. Lack of efficient technologies for commercial applications | |
8. Energy security | ||
9. Production of high-value added products | ||
10. Close to meeting the claimed environmental benefits | ||
3rd generation | 1. No food or land competition | 1. Difficult to harvest and process |
2. Produces more energy per acre than conventional crops | 2. High processing cost | |
3. Algae can be grown using land and water unsuitable for food production | 3. Lack of technological and research breakthrough | |
4. High oil yield | 4. Not yet commercially feasible | |
5. No toxic content | 5. Production technology is under development | |
6. Energy security | 6. Requires new technologies from the production of feedstock to processing into final biofuel product | |
7. Bioengineered algae are renewable | ||
8. Low and sometimes no cost for feedstock | ||
9. Improves performance of 1st- and 2nd-generation biofuels when employed in integrated biofuels | ||
4th generation | 1. 4th-generation biofuel is argued to be carbon negative rather than simply carbon neutral, as it “locks” away more carbon than it produces | 1. Lack of study on its practical performance in terms of technical and economic aspects |
2. Synthetic raw materials to produce biofuels is a possibility | 2. High cost | |
3. Energy security | 3. Still in research and development stage | |
4. Requires new technologies from the production of feedstock to processing into final biofuel product |
The 1st to 4th types of biofuels are like the above-described generations. The biofuels of the 0th-generation biofuels are naturally existing bio-fuels like raw feedstocks and can be used directly with no processing, special treatment, or modifications.
3. Gaseous bio-fuel synthesis techniques
Global warming and adverse climatic condition are propelling the researchers to bring a revolution with sustainable and renewable energy resources to reduce reliance on fossil fuels, which are depleting constantly. In this scenario, gaseous biofuels are environment friendly, will make vital contribution and will be a substantial part of the world’s energy demand. The most valuable gaseous biofuels are bio-gas and bio-hydrogen.
3.1 Biogas (bio-methane)
A renewable, most sustainable and versatile energy source is biogas [41]. Shortly, biogas will make a remarkable impact to meet the energy demand. Biogas or bio-methane production resources are easily available at low cost and some even at no-cost like animal waste, domestic waste, animal feedstock waste, and municipal-organic, industrial effluent, for example, fat-separator wastes, glycerin, and food processing effluents waste material and residues of cereal crops [42, 43]. Biogas is the best replacement for fossil fuels [44]. It is safe to use in vehicles, generators, and combustion engines just like natural gas or fossil fuel gas.
The percentage of methane content in biogas defines its flammability and energy capacity. Production of biogas is mainly accomplished from the digestion of anaerobic biomass. It has 50–75% CH4 (methane), 25–50% CO2 (carbon dioxide), sulfur traces, water, hydrogen sulfide, oxygen, hydrogen, and ammonia. Production of biogas in methane treatment-plant that upgrades methane has similar properties just like natural gas and contains about 95% methane. To generate heat and electricity in co-generation units, de-sulfurized and dried bio-gas is safe to use [44]. With recent research, algae, water algae, and micro-algae are of prime importance for the production of bio-gas with outstanding results [42].
Anaerobic production of biogas is mainly divided into four steps: (a) hydrolysis, (b) acidification (also called acido-genesis), (c) de-hydrogenation/aceto-genesis, and (d) methanation [41]. As different anaerobic bacteria are used for biogas production, anaerobic conditions, pH, nutrient, and temperature are provided according to the demand for biogas production.
3.2 Bio-hydrogen
Bio-hydrogen is just simple hydrogen produced from the biochemical or thermochemical conversion of biomass like feedstock, residues of crops, cereal crops, agricultural grasses residues, livestock waste, forest biomass, waste-oil, algae, and micro-algae biomass, and industrial effluents [45, 46].
Hydrogen is a low-molecular mass gas having a higher heating value (HHV) of combustion products. The important thing that makes it perfect for the environment is that during chemical combustion after releasing energy, only water (H2O) is the product. It has no harmful effect on the environment and global warming condition. Greenhouse gases are not produced during bio-hydrogen combustion. Bio-hydrogen production technologies are still under development [47, 48]. There are two techniques for bio-hydrogen production: (a) thermochemical (b) bio-chemical as shown in Figure 8 [49].
3.2.1 Thermochemical method
Thermochemical process of bio-hydrogen production is further subdivided into two different methods like (a) gasification and (b) pyrolysis. Mainly, gasification is a common method to produce bio-hydrogen gas. In this method, carbon-rich material is converted into bio-hydrogen thermochemically with/without catalyst at high temperature [50]. Energy is not released directly in the form of heat of combustion; rather it is converted in the form of bond energy as a lightweight fuel.
3.2.2 Bio-chemical method
The biochemical process of bio-hydrogen production is further subdivided into three different methods like (a) bio-photolysis, (b) dark fermentation, and (c) photo-fermentation. Nitrogenase, Fe-hydrogenase, and Ni-Fe-hydrogenase have commonly been used enzymes in the bio-chemical production method to convert biomass to bio-hydrogen [51, 52]. The bio-photolysis process is catalyzed by Fe-hydrogenase. This could be an indirect or direct process.
In the photo-fermentation process, a nitrogenase enzyme is used. By using water and nitrogen-deficient organic acids in the presence of light and nitrogenase enzyme, photosynthetic bacteria produce bio-hydrogen gas [53]. Dark fermentation is carried out by anaerobic bacteria by using carbohydrate-containing sources during the catabolism process of which carbohydrate-containing substrate bio-hydrogen gas is liberated [51].
4. Liquid bio-fuels
Liquid biofuel mainly includes biodiesel, which is of prime importance. Many techniques are in practice to produce the biodiesel.
4.1 Biodiesel
FAME (fatty_acid_methyl_ester) is a chemical name for biodiesel. It is a renewable bio-fuel and derived from the recycled greases, animal fats, and vegetable oils [54]. This fuel is just like petroleum-based diesel fuel and with very little to no reforms, it is safe to use in diesel engines also known as the compression ignition engine. Because of some important factors, biodiesel is superior over conventional diesel; for example, it does not contain sulfur residues, has lower life-cycle GHG emissions, and has lower particulate matter. Because of the high viscosity of vegetable oils, these can create problems; so we cannot use them directly. Vegetable oil has low volatility and its viscosity is 11–17× greater than the conventional diesel fuel; hence it forms deposits inside the fuel-injector of diesel engines because it does not burn completely [55]. The viscosity of vegetable oil can be reduced by following different methods. The most common production techniques are four in number (i) micro-emulsion, (ii) thermal-cracking also known as pyrolysis, (iii) dilution, and (iv) transesterification [56]. Transesterification is the preferable technique and it produces good-quality fuel. It is a chemical reaction between fat and oil by using alcohol mediums in the presence of a catalyst, which results in the formation of glycerol and esters [36].
4.2 Biodiesel: intensification techniques
As the use of fossil-fuel has influenced both human lives and the environment. Therefore, Biodiesel has revealed an optimistic effect to resolve environmental issues and helping to achieve energy requirements as a renewable energy resource [57]. Nonedible plants such as
4.2.1 Microwave-based method
A microwave-assisted technique reduces the processing time and also saves energy because the electromagnetic field is the main source of energy in this technique [60]. As to enhance the biofuel production and reaction rate in a very short period via a harmless and suitable method at optimum temperature, this microwave technique is of prime importance and is widely accepted as a chemical reaction tool [45]. In the transesterification method, catalysts like alkali convert the crude oil into fatty-acid-alkyl-esters (biodiesel) by using the monohydric-alcohol substrate. For biodiesel commercialization, the major issue is the operating cost.
To resolve this issue, a microwave-assisted technique as shown in Figure 9 is the finest method to increase biodiesel yield and reduce reaction time; the transesterification method is an energy-saving and fast method for biodiesel production than the conventional method. This microwave method can make the separation process easier and also speed up the rate of reaction by providing specific heat during trans esterification reaction [46]. An increase of dipolar rotation phenomenon can reduce the activation energy when microwave electromagnetics interact with reaction components (triglycerides, alcohol) [61].
4.2.1.1 Factors influencing the reaction rate
The transesterification process is ruled by the amount and by type of alcohol. Methanol is one of the most preferable reactants that are used in both techniques of transesterification like microwave-based and conventional methods. Methanol is mostly used to achieve maximum production of biodiesel by using non-edible oils as those shown in Table 4. Methanol allows easier methyl ester formation and separation of glycerol simultaneously compared to other alcohols like ethanol [62]. So, this is because, in the catabolism of methane anoin ethoxide (C2H5O–) have low reactivity compared to methoxide (methanolysis) [63]. The sensitivity of ethanol causes the formation of soap in the non-edible oil.
Microwave-assisted base-catalyzed transesterification reaction | ||||||||
---|---|---|---|---|---|---|---|---|
Feedstock | Alcohol:Oil ratio | Catalyst (wt%) | Temp. (°C) | Time (min) | Power (W) | Conversion (%) | References | |
Waste cooking oil | Methanol 6:1 | CH3ONa0.75% | – | 3 | 750 | 97.9 | [42] | |
Methanol 6:1 | NaOH 0.75% | – | 3 | 750 | 96.2 | [42] | ||
Methanol 6:1 | NaOH 1% | 64 | 5 | 600 | 93.36 | [44] | ||
Methanol 6:1 | KOH 2% | 78 | 5 | 300 | 95 | [57] | ||
Methanol 6:1 | SrO 1.85% | Around 80°C | 3 | 1000 | 93 | [42] | ||
Jatropha oil | Methanol 30:1 | NaOH 4% | 55 | 7 | 1200 | 86.3 | [43] | |
Methanol 7.5:1 | KOH 1.5% | 65 | 2 | 1200 | 97.4 | [58] | ||
Cottonseed oil | Methanol 6:1 | KOH 1.5% | 60 | 7 | 21% | 92.4 | [76] | |
Karanja oil | Methanol 33.4 wt% | KOH 1.33% | – | 2.5 | 180 | 89.9 | 0.3 | [59] |
Palm oil | Ethanol 4:1 | KOH 1.5% | – | 5 | 70 | 97.4 | [60] | |
Methanol 20:1 | K2CO3 3% | ≈alcohol B.P | 180 | 1000 | 85.63 | [38] | ||
2-propanol 20:1 | K2CO3 3% | 180 | 1000 | 49.51 | [38] | |||
Methanol 18:1 | CaO 15% | – | 4 | 900 | 96.7 | [45] | ||
Macauba oil | Ethanol 9:1 | Novozyme 435 2.5% | 30 | 15 | – | 45.2 | [46] | |
Ethanol 9:1 | Lipozyme IM 5% | 40 | 5 | – | 35.8 | [46] |
Vitally, methanol has more ability to absorb the microwave spectrum than ethanol under microwave irradiation. The electromagnetic energy storage in material measures the capacity of substances to insulate charges from each other in dielectric constant. The material becomes polarized easily in the electric field at high dielectric constant due to decrease in the dielectric constant through the growing straight chain in the R-OH. Methanol is more favorable for biodiesel production via microwave technique due to its smallest path between the hydroxyl and hydrocarbons group and a remarkable nucleophilic property.
Ethanol produced from renewable biomass is an appropriate product for the production of biodiesel; there are five types of alcohol in the transesterification process [64]. The obtained values show the ascending conversion order such as iso-propyl-alcohol < 2,butyl-alcohol < iso-propenyl-alcohol < iso-butyl-alcohol < methanol. So, we concluded that methanol is one of the efficient absorbers compared to the iso-butyl and iso-propenyl alcohol in a microwave field. Though microwave technique is very efficient for a transesterification reaction, there is a barrier with the immiscibility of oils with alcohols, which direct the minor triglycerides to biodiesel conversion.
Hence, to achieve a better yield, increasing the reaction rate and catalysts solubility of alcohol is of prime importance [65]. These catalysts can catalyze the reaction both heterogeneously as well as homogeneously. Under microwave operating reaction requirement of a catalyst excluded about tenfold as compared to the conventional heating method in transesterification [62, 66]. Different catalysts such as alkaline (NaOH, KOH, CH3ONa, CH3OK) and acidic (H2SO4, HCl, H3PO4) are used in biodiesel production because of their highest performance [67].
Therefore, at the molecular scale of the microwave method, there is the inability for the suspended heterogeneous constituent part; so in this case, homogenous catalysts are more preferable. The catalysts ions help to increase the molecular interaction of solvents because of their strong electric field. So it is concluded that the rate of reaction of acidic catalysis is slower 4000 times than the basic catalysis reactions, therefore, acidic catalysis reactions are less common because of their acidic nature rather than the basic nature [68, 69]. Catalysts like sodium-methoxides and potassium are better and preferable for a large-scale production process [70].
In another case, water causes the saponification and the formation of fatty acids in the strong basic medium [71]. In methoxide solutions, these catalysts do not liberate H2O during the transesterification process and behave like weak Lewis-bases. Negligible ester dissolution in glycerol and fewer yield losses are observable under methoxide catalysis transesterification reactions. In another way, sodium and potassium hydroxides are inexpensive catalysts.
Homogeneous catalyst’s drawbacks of homogeneous catalysts are controlled by using heterogeneous catalysts. Heterogeneous catalysts are reusable and recyclable due to inexpensive production costs with very good performance rate to avoid undesired saponification reactions [72]. It is reported that heterogeneous acid base-catalyzed reaction can act as an intermediate in both transesterification and esterification processes and they provide easier separation and cleaner products at the same time. SRO, Al2O3/50% KOH, CaO, BaO, SiO2/50% H2SO4 etc. are the best solid catalysts for the production of biodiesel [73, 74, 75].
In the conventional method, at the higher temperature crude oil viscosity decreases with an increase of reaction rate exhibiting positive influence and reaction time reduction in both microwave and conventional methods [77]. In microwave reaction system, rapid heat transfer is achievable by molecular interactions of ionic and dipolar compounds via electromagnetic field that dramatically accelerates the reaction rate and also produces heat energy by volumetric distribution compared to conventional method where heat is transferred via radiation. However, reaction yield increases with increasing irradiation power [78].
4.2.2 Ultrasonic sound waves-based method
While using solid and liquid mediums for the process of intensification ultrasonic method is preferable [79]. Mechanical energy is required for continuous mixing and initiation of reaction in transesterification process. Ultrasonic sound wave energy of higher frequencies can be used [80]. It speeds up the reaction and also enhances the biodiesel yield. Cavitation is a phenomenon that creates chemical and physical effects on the reaction [81]. Ultrasonic cycles generate and also increase the size of cavitation bubbles from ten to a hundred times bigger [82]. High temperature (5000°C) and pressure (500 atm) occur due to collusion of bubbles in less than a microsecond and lead to the vigorous mixing and rapid heating in the system between the two immiscible reactants shown in Figure 10. There are cycles of expansion and compression because of introducing ultrasonic waves to liquid. A positive pressure push liquid molecules closer in the compression cycle and negative pressure pull apart in expansion cycles [83]. Collision between the molecules generate radicals (H+ and OH–) promoting reaction rate between the reactants [84]. Hielscher Ultrasonic GmbH ultrasonic reactor (frequency: 18–20 kHz) for biodiesel production was introduced in 2000 [81, 85] and used low frequencies (28–40 kHz) for transesterification of vegetable oils. However, at 28 kHz there was a high yield production and reaction time was shortened considerably at 40 kHz [86].
Production of biodiesel from the oil of the Schleicher Triguga plant is influenced by ultrasonic irradiation [87]. The esterification reaction using H2SO4 catalyst reduced the acid value from 21.65 to 0.84 mg/g in the first step (reaction time: 20 min at 40°C). While a during a second step of transesterification reaction, a catalyst Ba(OH)2 is used (80 min at 50°C) with the 96.8% conversion of triglyceride. So, in conventional methods, ultrasonic waves accelerate the transfer of mass in heterogeneous nature catalyzed reactions [88]. Tables 5 and 6 show the comparison of the ultrasonic-assisted method as well as a method of conventional stirring for the transesterification reactions. In several studies, RSO (rubber seed oil) and non-edible oil is reported as acid pre-treated by using the ultrasonic method [89]. To harvest 98% of FFA conversion this reaction took only 30 min, while some researchers reports 60, and 90 min [90, 91, 92, 93]. In mechanical stirring, observed FFA conversion was only 75%.
Methods | Feedstock | Catalyst | Optimum reaction condition | Yield/conversion (Wt %) | References |
---|---|---|---|---|---|
MS | Waste cooking oil | KOH | Cat. 1 wt%, MeOH/oil 6:1, T 70°C, t 1 h | Y 98.2 | [46] |
MS | Used frying | NaOH | Cat. 1.1 wt%, MeOH/oil 7:1, T 70°C, t 0.33 h | Y 88.8 | [47] |
MS | Waste cooking oil | H2SO4 | Cat. 4 wt%, MeOH/oil 20:1, T 95°C, t 20 h | C>90 | [48] |
MS | Rubber seed oil (42.5% FFA) | H2SO4 | Cat. 10.74 wt%, MeOH/oil 10:1, T 65°C, t 60 min | FFA conversion 98.6% | [41] |
MS | Rubber seed oil (40.14% FFA) | H2SO4 | Cat. 7.5 wt%, MeOH/oil 23:1, T 50°C, t 30 min | FFA conversion 75% | [56] |
UM | Rubber seed oil (40.14% FFA) | H2SO4 | Cat. 7.5 wt%, MeOH/oil 23:1, T 50°C, t 30 min | FFA conversion 98% | [56] |
UM | Soybean oil | KOH | Cat. 1.5–2.2 wt%, MeOH/oil 6:1, T 40°C, t 0.25 h | Y 99.4 | [47] |
UM | Waste cooking oil | KOH | Cat. 1 wt%, MeOH/oil 4:1, T 27–32°C, t 0.016 h | Y 99 | [48] |
UM | Oleic acid | H2SO4 | Cat. 5 wt%, Ethanol/acid 3:1, T 60°C, t 2 h | C>90 | [49] |
Method | Feedstock | Catalyst | Optimum reaction condition | Yield/conversion (Wt %) | References |
---|---|---|---|---|---|
MS | Palm oil | KF/Ca-Al hydrotalcite | Cat. 4 wt%, MeOH/oil 12:1, T 65°C, t 5 h | Y 97.98 | [51] |
MS | Palm kernel | CaO | Cat. 6 wt%, Alcohol/oil 30:1, T 60°C, t 3 h | Y 98 | [52] |
MS | Palm oil | CaO/Al2O3 | Cat. 6 wt%, MeOH/Oil 12:1, T 65°C, t 5 h | Y 98.64 | [53] |
MS | Soybean oil | 15-KOH/CaO | Cat. 4 wt%, MeOH/oil 16:1, T 65°C, t 1 h | Y 97.1 | [50] |
MS | Soybean oil | Calcined sodium silicate | Cat. 3 wt%, MeOH/oil 7.5:1, T 60°C, t 1 h | Y>95 | [57] |
MS | Soybean oil | K2CO3/MgO | Cat. 1 wt%, MeOH/oil 6:1, T 70°C, t 2 h | Y 99 | [58] |
MS | Jatropha oil | Mg-Al hydrotalcite | Cat. 1 wt%, MeOH/oil 4:1, T 45°C, t 1.5 h | Y 95.2 | [47] |
MS | Waste cooking oil | K3PO4 | Cat. 4 wt%, MeOH/oil 6:1, T 60°C, t 2 h | Y 97.30 | [60] |
MS | Waste cooking oil | MgO/TiO2 | Cat. 10 wt%, MeOH/oil 50:1, T 170°C, t 6 h | Y 91.6 | [45] |
4.2.3 Bio-gasoline and green diesel: thermochemical upgraded processes
4.2.3.1 Hydro-deoxygenation catalytic process
For cracking of long-chain gas oils into small-chain petroleum product distillates, olefin hydrocarbons saturation, and removal of heteroatoms, catalytic hydro-processing is the most preferable petrochemical method. Hydro-deoxygenation of vegetable oil occurs at a temperature of 300–450°C, with lowest space velocity and hydrogen pressure above 3 MPa. Vegetable oils are converted into saturated long-chain hydrocarbons with boiling points (180–360°C) [94]. HDO technology has been established by many commercial companies like HP-Innovations, UOP-Honeywell, Nest Oil-Corporation, Valero Energy-Corporation, and ConocoPhillips in green-diesel synthesis process. They successfully introduced the substantial potential of catalytic hydro-processing.
4.2.3.2 Factors affecting green-diesel production
Hydrogen consumption, properties, and rate of an exergonic reaction in liquid biofuels are greatly influenced by the feedstock [95]. It is stated that higher unsaturated and long carbon chain lipid containing feedstock cause undesirable aromatization, oligomerization, cyclization, and dimerization of unsaturated long-chain carbon compounds intermediates inhibits the catalytic activities [96]. In the hydro-processing technique, temperature range depends on the product of interest. Temperature is the most important factor to harvest the hydrocarbons in diesel range; so for this purpose, many researchers have done many experiments to optimize the temperature range for the production of hydrocarbon chains within the diesel range. For long-chain hydrocarbons, for thermal cracking process to yield lower carbon chains, best temperature is above 400°C.
5. Conclusion
With the increasing demand for energy, continually depleting fossil fuels and energy resources, and a substantial environmental risk because of the consumption of fossil fuels, there is a demand for alternative resource. These factors are not ignorable; keeping in mind this situation, many researchers have introduced biofuels as an alternative, sustainable, and renewable source of energy. These are producible at a very low cost by using organic raw material, feedstock, domestic waste, animal waste, plant waste, energy crops, seed oils, biological organisms, micro-algae, water algae, macro-algae, etc.; biofuels can be produced through different chemical and biochemical techniques and many advancements are being introduced day by day with new researches. Biofuels are the future of this universe due to their environment-friendly nature.
References
- 1.
Guo M, Song W, Buhain J. Bioenergy and biofuels: History, status, and perspective. Renewable and Sustainable Energy Reviews. 2015; 42 :712-725 - 2.
Demirbas MF, Balat M, Balat H. Potential contribution of biomass to the sustainable energy development. Energy Conversion and Management. 2009; 50 (7):1746-1760 - 3.
Sadeghinezhad E, Kazi SN, Sadeghinejad F, Badarudin A, Mehrali M, Sadri R, et al. A comprehensive literature review of bio-fuel performance in internal combustion engine and relevant costs involvement. Renewable and Sustainable Energy Reviews. 2014; 30 :29-44 - 4.
Cruz CH, Souza GM, Cortez LA. Biofuels for transport. In: Chapter 11 in Future Energy. Second ed. London, UK: Elsevier Ltd; 2014. pp. 215-244 - 5.
Demain AL, Báez-Vásquez MA. Chapter 14: Biofuels of the present and the future. In: Suib SLBT-N and FD in C. Amsterdam, The Netherlands: Elsevier; 2013. pp. 325-370 - 6.
Zhang Y, Ghaly AE, Li B. Determination of the exergy of four wheat straws. American Journal of Biochemistry and Biotechnology. 2013; 9 (3):338-347 - 7.
Major P. Availability and physical properties of residues from major agricultural crops for energy conversion through thermochemical processes. American Journal of Agricultural and Biological Science. 2012; 7 (3):312-321 - 8.
Zhang Y, Yu X, Li B, Zhang H, Liang J, Li Y. Exergy characteristics of woody biomass. Energy Sources, Part A: Recovery, Utilization, and Environmental Effects. 2016; 38 (16):2438-2446 - 9.
Zhang Y, Wang Q , Li B, Li H, Zhao W. Is there a general relationship between the exergy and HHV for rice residues? Renewable Energy. 2018; 117 :37-45 - 10.
Suganya T, Varman M, Masjuki HH, Renganathan S. Macroalgae and microalgae as a potential source for commercial applications along with biofuels production: A biorefinery approach. Renewable and Sustainable Energy Reviews. 2016; 55 :909-941 - 11.
Zhang Y, Chen P, Liu S, Fan L, Zhou N, Min M, et al. Microwave-assisted pyrolysis of biomass for bio-oil production. In: Pyrolysis. Croatia: IntechOpen; 2017 - 12.
Chew TL, Bhatia S. Catalytic processes towards the production of biofuels in a palm oil and oil palm biomass-based biorefinery. Bioresource Technology. 2008; 99 (17):7911-7922 - 13.
Zhang Y, Zhao W, Li B, Li H. Understanding the sustainability of fuel from the viewpoint of exergy. European Journal of Sustainable Development Research. 2018; 2 (1):09 - 14.
Alaswad A, Dassisti M, Prescott T, Olabi AG. Technologies and developments of third generation biofuel production. Renewable and Sustainable Energy Reviews. 2015; 51 :1446-1460 - 15.
Pradhan A, Mbohwa C. Development of biofuels in South Africa: Challenges and opportunities. Renewable and Sustainable Energy Reviews. 2014; 39 :1089-1100 - 16.
Ghobadian B. Liquid biofuels potential and outlook in Iran. Renewable and Sustainable Energy Reviews. 2012; 16 (7):4379-4384 - 17.
Russo D, Dassisti M, Lawlor V, Olabi AG. State of the art of biofuels from pure plant oil. Renewable and Sustainable Energy Reviews. 2012; 16 (6):4056-4070 - 18.
Schulte LA, Ontl TA, Larsen GD. Biofuels and Biodiversity, Wildlife Habitat Restoration. Encyclopedia of Biodiversity. Second ed. 2013. pp. 540-551 - 19.
Pandey A, Larroche C, Gnansounou E, Khanal SK, Dussap CG, Ricke S, editors. Biomass, Biofuels, Biochemicals: Biofuels: Alternative Feedstocks and Conversion Processes for the Production of Liquid and Gaseous Biofuels. Elsevier GN-GEN Laboratories, Academic Press; 2019. p. 6 - 20.
Robertson BA, Doran PJ. Biofuels and Biodiversity: The Implications of Energy Sprawl. In: Encyclopedia of Biodiversity. Second ed. Waltham, MA: Academic Press; 2013. pp. 528-539 - 21.
Delshad AB, Raymond L, Sawicki V, Wegener DT. Public attitudes toward political and technological options for biofuels. Energy Policy. 2010; 38 (7):3414-3425 - 22.
Demirbas MF, Balat M, Balat H. Biowastes-to-biofuels. Energy Conversion and Management. 2011; 52 (4):1815-1828 - 23.
Saladini F, Patrizi N, Pulselli FM, Marchettini N, Bastianoni S. Guidelines for emergy evaluation of first, second and third generation biofuels. Renewable and Sustainable Energy Reviews. 2016; 66 :221-227 - 24.
Naik SN, Goud VV, Rout PK, Dalai AK. Production of first and second generation biofuels: A comprehensive review. Renewable and Sustainable Energy Reviews. 2010; 14 (2):578-597 - 25.
Akhlaghi S, Gedde UW, Hedenqvist MS, Braña MT, Bellander M. Deterioration of automotive rubbers in liquid biofuels: A review. Renewable and Sustainable Energy Reviews. 2015; 43 :1238-1248 - 26.
Ruan R, Zhang Y, Chen P, Liu S, Fan L, Zhou N, et al. Biofuels: Introduction. In: Biofuels: Alternative Feedstocks and Conversion Processes for the Production of Liquid and Gaseous Biofuels. Elsevier GN-GEN Laboratories, Academic Press; 2019. pp. 3-43 - 27.
Luna C, Luna D, Bautista FM, Estevez R, Calero J, Posadillo A, et al. Application of enzymatic extracts from a CALB standard strain as biocatalyst within the context of conventional biodiesel production optimization. Molecules. 2017; 22 (11):2025 - 28.
Joshi G, Pandey JK, Rana S, Rawat DS. Challenges and opportunities for the application of biofuel. Renewable and Sustainable Energy Reviews. 2017; 79 :850-866 - 29.
Gupta VK, Potumarthi R, O’Donovan A, Kubicek CP, Sharma GD, Tuohy MG. Bioenergy research: An overview on technological developments and bioresources. In: Bioenergy Research: Advances and Applications. Waltham, MA: Elsevier; 2014. pp. 23-47 - 30.
Franco CJ, Zapata S, Dyner I. Simulation for assessing the liberalization of biofuels. Renewable and Sustainable Energy Reviews. 2015; 41 :298-307 - 31.
Scaife MA, Merkx-Jacques A, Woodhall DL, Armenta RE. Algal biofuels in Canada: Status and potential. Renewable and Sustainable Energy Reviews. 2015; 44 :620-642 - 32.
Algayyim SJ, Wandel AP, Yusaf T, Hamawand I. Production and application of ABE as a biofuel. Renewable and Sustainable Energy Reviews. 2018; 82 :1195-1214 - 33.
Noraini MY, Ong HC, Badrul MJ, Chong WT. A review on potential enzymatic reaction for biofuel production from algae. Renewable and Sustainable Energy Reviews. 2014; 39 :24-34 - 34.
Hao H, Liu Z, Zhao F, Ren J, Chang S, Rong K, et al. Biofuel for vehicle use in China: Current status, future potential and policy implications. Renewable and Sustainable Energy Reviews. 2018; 82 :645-653 - 35.
Li X, Luo X, Jin Y, Li J, Zhang H, Zhang A, et al. Heterogeneous sulfur-free hydrodeoxygenation catalysts for selectively upgrading the renewable bio-oils to second generation biofuels. Renewable and Sustainable Energy Reviews. 2018; 82 :3762-3797 - 36.
Lee KT, Lim S, Pang YL, Ong HC, Chong WT. Integration of reactive extraction with supercritical fluids for process intensification of biodiesel production: Prospects and recent advances. Progress in Energy and Combustion Science. 2014; 45 :54-78 - 37.
Fokaides PA, Christoforou E. Life cycle sustainability assessment of biofuels. In: Handbook of Biofuels Production. Duxford, UK: Woodhead Publishing; 2016. pp. 41-60 - 38.
Acheampong M, Ertem FC, Kappler B, Neubauer P. In pursuit of Sustainable Development Goal (SDG) number 7: Will biofuels be reliable? Renewable and Sustainable Energy Reviews. 2017; 75 :927-937 - 39.
Renzaho AM, Kamara JK, Toole M. Biofuel production and its impact on food security in low and middle income countries: Implications for the post-2015 sustainable development goals. Renewable and Sustainable Energy Reviews. 2017; 78 :503-516 - 40.
Taghizadeh-Alisaraei A, Hosseini SH, Ghobadian B, Motevali A. Biofuel production from citrus wastes: A feasibility study in Iran. Renewable and Sustainable Energy Reviews. 2017; 69 :1100-1112 - 41.
Peter W. Biogas production: Current state and perspectives. Applied Microbiology and Biotechnology. 2010; 85 :849-860 - 42.
Montingelli ME, Tedesco S, Olabi AG. Biogas production from algal biomass: A review. Renewable and Sustainable Energy Reviews. 2015; 43 :961-972 - 43.
Christy PM, Gopinath LR, Divya D. A review on anaerobic decomposition and enhancement of biogas production through enzymes and microorganisms. Renewable and Sustainable Energy Reviews. 2014; 34 :167-173 - 44.
Wellinger A, Murphy JD, Baxter D, editors. The Biogas Handbook: Science, Production and Applications. Woodhead, EU Science Hub: Elsevier; 2013 - 45.
Amore KM, Leadbeater NE. Microwave-promoted esterification reactions: Optimization and scale-up. Macromolecular Rapid Communications. 2007; 28 (4):473-477 - 46.
Motasemi F, Ani FN. A review on microwave-assisted production of biodiesel. Renewable and Sustainable Energy Reviews. 2012; 16 (7):4719-4733 - 47.
Balat H, Kırtay E. Hydrogen from biomass—Present scenario and future prospects. International Journal of Hydrogen Energy. 2010; 35 (14):7416-7426 - 48.
Udomsirichakorn J, Salam PA. Review of hydrogen-enriched gas production from steam gasification of biomass: The prospect of CaO-based chemical looping gasification. Renewable and Sustainable Energy Reviews. 2014; 30 :565-579 - 49.
Saxena RC, Seal D, Kumar S, Goyal HB. Thermo-chemical routes for hydrogen rich gas from biomass: A review. Renewable and Sustainable Energy Reviews. 2008; 12 (7):1909-1927 - 50.
Moghadam RA, Yusup S, Azlina W, Nehzati S, Tavasoli A. Investigation on syngas production via biomass conversion through the integration of pyrolysis and air–steam gasification processes. Energy Conversion and Management. 2014; 87 :670-675 - 51.
Hallenbeck PC, Benemann JR. Biological hydrogen production; fundamentals and limiting processes. International Journal of Hydrogen Energy. 2002; 27 (11-12):1185-1193 - 52.
Peters JW, Schut GJ, Boyd ES, Mulder DW, Shepard EM, Broderick JB, et al. [FeFe]-and [NiFe]-hydrogenase diversity, mechanism, and maturation. Biochimica et Biophysica Acta (BBA)-Molecular Cell Research. 2015; 1853 (6):1350-1369 - 53.
Manish S, Banerjee R. Comparison of biohydrogen production processes. International Journal of Hydrogen Energy. 2008; 33 (1):279-286 - 54.
Banković-Ilić IB, Stamenković OS, Veljković VB. Biodiesel production from non-edible plant oils. Renewable and Sustainable Energy Reviews. 2012; 16 (6):3621-3647 - 55.
Demirbas A. Biodiesel production from vegetable oils via catalytic and non-catalytic supercritical methanol transesterification methods. Progress in Energy and Combustion Science. 2005; 31 (5-6):466-487 - 56.
Agarwal M, Chauhan G, Chaurasia SP, Singh K. Study of catalytic behavior of KOH as homogeneous and heterogeneous catalyst for biodiesel production. Journal of the Taiwan Institute of Chemical Engineers. 2012; 43 (1):89-94 - 57.
Bokhari A, Chuah LF, Yusup S, Klemeš JJ, Akbar MM, Kamil RN. Cleaner production of rubber seed oil methyl ester using a hydrodynamic cavitation: Optimisation and parametric study. Journal of Cleaner Production. 2016; 136 :31-41 - 58.
Bokhari A, Chuah LF, Yusup S, Ahmad J, Shamsuddin MR, Teng MK. Microwave-assisted methyl esters synthesis of Kapok ( Ceiba pentandra ) seed oil: Parametric and optimization study. Biofuel Research Journal. 2015;2 (3):281-287 - 59.
Asif S, Ahmad M, Bokhari A, Chuah LF, Klemeš JJ, Akbar MM, et al. Methyl ester synthesis of Pistacia khinjuk seed oil by ultrasonic-assisted cavitation system. Industrial Crops and Products. 2017;108 :336-347 - 60.
Thostenson ET, Chou TW. Microwave processing: Fundamentals and applications. Composites Part A: Applied Science and Manufacturing. 1999; 30 (9):1055-1071 - 61.
Perreux L, Loupy A. A tentative rationalization of microwave effects in organic synthesis according to the reaction medium, and mechanistic considerations. Tetrahedron. 2001; 57 (45):9199-9223 - 62.
Sajjadi B, Aziz AA, Ibrahim S. Investigation, modelling and reviewing the effective parameters in microwave-assisted transesterification. Renewable and Sustainable Energy Reviews. 2014; 37 :762-777 - 63.
Kanitkar A, Balasubramanian S, Lima M, Boldor D. A critical comparison of methyl and ethyl esters production from soybean and rice bran oil in the presence of microwaves. Bioresource Technology. 2011; 102 (17):7896-7902 - 64.
Muley PD, Boldor D. Investigation of microwave dielectric properties of biodiesel components. Bioresource Technology. 2013; 127 :165-174 - 65.
Mazo PC, Rios LA. Esterification and transesterification assisted by microwaves of crude palm oil: Homogeneous catalysis. Latin American Applied Research. 2010; 40 (4):337-342 - 66.
Borugadda VB, Goud VV. Biodiesel production from renewable feedstocks: Status and opportunities. Renewable and Sustainable Energy Reviews. 2012; 16 (7):4763-4784 - 67.
Lam MK, Lee KT, Mohamed AR. Homogeneous, heterogeneous and enzymatic catalysis for transesterification of high free fatty acid oil (waste cooking oil) to biodiesel: A review. Biotechnology Advances. 2010; 28 (4):500-518 - 68.
Fukuda H, Kondo A, Noda H. Biodiesel fuel production by transesterification of oils. Journal of Bioscience and Bioengineering. 2001; 92 (5):405-416 - 69.
Vyas AP, Verma JL, Subrahmanyam N. A review on FAME production processes. Fuel. 2010; 89 (1):1-9 - 70.
Atadashi IM, Aroua MK, Aziz AA, Sulaiman NM. The effects of catalysts in biodiesel production: A review. Journal of Industrial and Engineering Chemistry. 2013; 19 (1):14-26 - 71.
Singh A, He B, Thompson J, Van Gerpen J. Process optimization of biodiesel production using alkaline catalysts. Applied Engineering in Agriculture. 2006; 22 (4):597-600 - 72.
Gude VG, Patil P, Martinez-Guerra E, Deng S, Nirmalakhandan N. Microwave energy potential for biodiesel production. Sustainable Chemical Processes. 2013; 1 (1):5 - 73.
Encinar JM, González JF, Martínez G, Sánchez N, Pardal A. Soybean oil transesterification by the use of a microwave flow system. Fuel. 2012; 95 :386-393 - 74.
Azcan N, Danisman A. Alkali catalyzed transesterification of cottonseed oil by microwave irradiation. Fuel. 2007; 86 (17-18):2639-2644 - 75.
Zu Y, Zhang S, Fu Y, Liu W, Liu Z, Luo M, et al. Rapid microwave-assisted transesterification for the preparation of fatty acid methyl esters from the oil of yellow horn ( Xanthoceras sorbifolia Bunge.). European Food Research and Technology. 2009;229 (1):43-49 - 76.
Wang Y, Ou S, Liu P, Xue F, Tang S. Comparison of two different processes to synthesize biodiesel by waste cooking oil. Journal of Molecular Catalysis A: Chemical. 2006; 252 (1-2):107-112 - 77.
Leung DY, Guo Y. Transesterification of neat and used frying oil: Optimization for biodiesel production. Fuel Processing Technology. 2006; 87 (10):883-890 - 78.
Chen KS, Lin YC, Hsu KH, Wang HK. Improving biodiesel yields from waste cooking oil by using sodium methoxide and a microwave heating system. Energy. 2012; 38 (1):151-156 - 79.
Patil PD, Reddy H, Muppaneni T, Mannarswamy A, Schuab T, Holguin FO, et al. Power dissipation in microwave-enhanced in situ transesterification of algal biomass to biodiesel. Green Chemistry. 2012; 14 (3):809-818 - 80.
Mulet A, Carcel J, Benedito J, Rosselló C, Simal S. Ultrasonic mass transfer enhancement in food processing. Transport Phenomena in Food Processing. 2003; 18 :265-278 - 81.
Stavarache C, Vinatoru M, Nishimura R, Maeda Y. Fatty acids methyl esters from vegetable oil by means of ultrasonic energy. Ultrasonics sonochemistry. 2005; 12 (5):367-372 - 82.
Chowdhury P, Viraraghavan T. Sonochemical degradation of chlorinated organic compounds, phenolic compounds and organic dyes–a review. Science of the Total Environment. 2009; 407 (8):2474-2492 - 83.
Vajnhandl S, Le Marechal AM. Ultrasound in textile dyeing and the decolouration/mineralization of textile dyes. Dyes and Pigments. 2005; 65 (2):89-101 - 84.
Pang YL, Abdullah AZ, Bhatia S. Review on sonochemical methods in the presence of catalysts and chemical additives for treatment of organic pollutants in wastewater. Desalination. 2011; 277 (1-3):1-4 - 85.
Suslick KS. Sonochemistry. Science. 1990; 247 (4949):1439-1445 - 86.
Serrano-Ruiz JC, editor. Advanced Biofuels: Using Catalytic Routes for the Conversion of Biomass Platform Molecules. Apple Academic, CRC Press; 2015; 27 :120-125 - 87.
Sarve A, Varma MN, Sonawane SS. Optimization and kinetic studies on biodiesel production from kusum ( Schleichera triguga ) oil using response surface methodology. Journal of Oleo Science. 2015;64 (9):987-997 - 88.
Sharma YC, Singh B. An ideal feedstock, kusum ( Schleichera triguga ) for preparation of biodiesel: Optimization of parameters. Fuel. 2010;89 (7):1470-1474 - 89.
Trinh H, Yusup S, Uemura Y. Optimization and kinetic study of ultrasonic assisted esterification process from rubber seed oil. Bioresource Technology. 2018; 247 :51-57 - 90.
Ahmad J, Yusup S, Bokhari A, Kamil RN. Study of fuel properties of rubber seed oil based biodiesel. Energy Conversion and Management. 2014; 78 :266-275 - 91.
Chuah LF, Bokhari A, Yusup S, Klemeš JJ, Abdullah B, Akbar MM. Optimisation and kinetic studies of acid esterification of high free fatty acid rubber seed oil. Arabian Journal for Science and Engineering. 2016; 41 (7):2515-2526 - 92.
Mootabadi H, Salamatinia B, Bhatia S, Abdullah AZ. Ultrasonic-assisted biodiesel production process from palm oil using alkaline earth metal oxides as the heterogeneous catalysts. Fuel. 2010; 89 (8):1818-1825 - 93.
Yadav AK, Khan ME, Pal A, Singh B. Ultrasonic-assisted optimization of biodiesel production from Karabi oil using heterogeneous catalyst. Biofuels. 2018; 9 (1):101-112 - 94.
Srifa A, Faungnawakij K, Itthibenchapong V, Assabumrungrat S. Roles of monometallic catalysts in hydrodeoxygenation of palm oil to green diesel. Chemical Engineering Journal. 2015; 278 :249-258 - 95.
Vouitsis I, Geivanidis S, Samaras Z. Liquid biofuels in Greece—Current status in production and research. Journal of Renewable and Sustainable Energy. 2014; 6 (2):022703 - 96.
Liu Y, Sotelo-Boyás R, Murata K, Minowa T, Sakanishi K. Hydrotreatment of vegetable oils to produce bio-hydrogenated diesel and liquefied petroleum gas fuel over catalysts containing sulfided Ni–Mo and solid acids. Energy & Fuels. 2011; 25 (10):4675-4685