Thermochemical conversion technologies that utilizes briquettes include combustion, gasification, and pyrolysis. However, combustion is the most developed and widely applied process used for such utilization because of its low costs and high reliability [ 25 ]. Additionally, co-combustion of biomass with fossil fuel is considered as one of the attractive short-term options for biomass utilization in the power generation industry. As shown by Andrić et al. [ 26 ], the addition of about 20% biomass to the mass of the combustion mixture in a biomass co-combustion power plant can reduce CO2 emissions by 11%–25%. Christoforou and Fokaides [ 25 ] noted that the co-combustion mix of less than 50% of coal is achievable but that is dependent on the co-combustion technology, the type of combustion boiler, and the plant configuration. A summary and comparison of the main observation and conclusions from several studies that reported the use of these conversion technologies can be found elsewhere [ 27 ].
Of all energy sources, biomass is the third largest energy resource in the world [ 9 ]. It is also the most dominant source of cooking and heating energy for three-quarters of all people in developing countries, and accounts for about 14% of the total global energy use [ 10 12 ]. In most of these countries, more than 80% contributes to national energy consumption [ 13 14 ]. In Ethiopia for instance, traditional biomass burning supplies more than 92% of its energy consumption [ 15 ], over 64% in Ghana [ 16 ], 70% in Kenya [ 17 ], 78% in Nigeria [ 18 ], 60% in Bangladesh [ 19 ], and 7% to electricity in Brazil [ 20 21 ]. The threats posed by the continuous consumption of fossil fuels and inefficient use and disposal of biomass can be curbed by effective utilization of biomass waste when converted to briquettes through densification [ 22 ]. Studies showed that the combustion properties were increased by 20% after the biomass was molded into solid briquettes and the emissions of greenhouse gas, NOx, and SOwere only one-ninth, one-fifth, and one-tenth that of coal [ 23 ]. Briquettes are used domestically and industrially for heat and power generation. The use of renewable energy from biomass is one of the few proven, cost-effective, and available technologies that can decrease COemissions [ 24 ].
The demand for energy has been on the increase mostly attributed to the growth in human population as well as a significant rise in the commercial and industrial activities witnessed across the globe. Fossil fuels such as petroleum products, coal, natural gas, etc., are the most important energy sources, which supply about 80% of the global primary energy requirement [ 1 ]. The depletion of fossil fuel, which is non-renewable, has been a global issue; nevertheless, it is the growing utilization that is currently presenting a new and major challenge. According to Tursi [ 2 ], the increasing usage of fossil fuels for industrial and post-industrial development has attracted growth in wealth, but so also higher levels of pollution and the consequent degeneration of public health. In 2018, the global carbon dioxide (CO) emissions from fuel combustion reached 32.8 billion tonnes [ 3 ]. The rise of carbon dioxide concentrations will continue unless emissions are drastically reduced. A recent report noted that the earth is set to warm up to 3.2 °C by 2100 unless efforts to cut emission are tripled [ 4 ]. The desire for the average rise in temperature to be sustained well below 2 °C requires a total decarbonization of energy generation away from fossil fuels [ 5 ]. Interestingly, fossil fuels are not the only constituents of environmental degradation. Inefficient use and disposal of biomass as well as inadequate proper cooking technologies also persist. Anenberg et al. [ 6 ] reported that 3 billion people rely on fuelwood, coal, charcoal, or animal waste for cooking and heating. Most of these people are predominantly found in developing countries. They get exposed to high indoor concentrations of health-damaging pollutants including particulate matter and carbon monoxide due to incomplete combustion [ 7 8 ]. Furthermore, one-third of the global population lives without access to healthy, clean, and sustainable cooking fuel or technologies [ 5 ].
These resources are used as fuel, directly or indirectly, avoiding needless burning, burying, or storage [ 44 46 ], but can also cause extensive environmental pollution when used inefficiently [ 20 47 ]. In comparison to other renewable energy options, several studies noted that biomass is abundant in supply from various sources and its energy has the key advantages of being nearly carbon neutral [ 48 50 ]. The carbon neutrality of biomass resources is dependent on the net COequivalent greenhouse gases (GHGs) emitted across the entire life cycle processes considered [ 51 ], which also involves the emissions generated during the manufacturing and transport phases. The COreleased through its burning, utilization, and exploitation processes does not cause an increase in atmospheric CO, but instead leads to a faster transfer of COinto the atmosphere that is reused by plants to produce biomass again [ 2 ]. This environmentally friendly attribute of biomass makes it an ideal renewable and sustainable source for briquette production. Studies have explored several types of biomass materials with some in combination with non-biomass materials used in briquetting ( Table 1 ).
According to Bajwa et al. [ 37 ], biomass resources can be grouped in terms of properties (‘woody’ and ‘non-woody’ biomasses) or sourcing (agricultural residue and harvested natural materials). The ISO 17225-1: [ 38 ] classified biomass feedstock resources into four specific groups, namely woody, herbaceous, fruit, and aquatic biomass. Other classification includes animal and human waste and biomass mixtures [ 2 ]. In developing countries, large amounts of biomass residues are generated annually as by-products of the commercial forestry, agricultural, and industrial sectors [ 39 40 ]. In 2008, about 134 million tons (Mt) of rice husks were produced globally from 671 million tons (Mt) of rice production and approximately 135 million tons (Mt) of corn cobs from 797 million tons (Mt) of corn production [ 41 ]. Similarly, for the year 2010-2011, agricultural and forest biomass feedstock was found to be 242 million tons (Mt) and it is estimated to increase to 281 million tons (Mt) in 2030–31 due to the growing production of the agricultural crops [ 42 ]. The supply of biomass from various sources around the globe is approximately 220 billion tons per year [ 43 ].
Common examples of inorganic binders include clay, lime, cement, plaster, and sodium silicate. On the other hand, the organic binders are sub-grouped into biomass binder (e.g., cassava paste, wastepaper pulp, molasses, cow dung, and starch), tar, pitch and petroleum bitumen binder, lignosulphonate binder, and polymer binder [ 97 99 ]. A combination of the two or more binders from both the organic and inorganic binders forms the compound binder. Different types of briquette may require different binder, but the strength, thermal stability, combustion performance, and cost of briquette is influenced by the quality of binder [ 100 ]. There are some advantages that one type of binder may have over the other because of its material components. Briquettes made with inorganic binders have higher compressive strength, compaction ratio, and hydrophobic nature compared to those made with an organic binder. However, such briquettes display an increase in ash content, burn out temperature, and reduced calorific value [ 72 102 ]. For effective fuel production, the binder must be plastic and elastic as its use is known to improve density, durability, and resistance to shearing [ 103 ].
Binders can be added during mixing of the feedstock or after carbonization of the feedstock before densification. Some biomass material will not agglomerate except with the addition of binder especially if a low-pressure compaction technique is employed. Binder addition to biomass feedstock is a co-processing practice, which aids in densification or increase the mechanical or thermal properties of the product [ 37 ]. Binder addition helps to reduce wear on production equipment. It forms a bridge to enhance strong inter-particle bonding with biomass components [ 90 ]. The amount of binder to be added depends on the binding properties of the raw material and the binding agent [ 95 ]. There are three types of binders used for briquette production, namely inorganic binders, organic binders, and compound binders [ 96 ].
Size reduction is a very important process prior to biomass briquetting. Studies have noted that it partially breaks down the lignin content of biomass and increases the total surface area leading to greater inter-particle bonding [ 88 89 ]. Size reduction in biomass also increases the bulk density, which improves the flow of biomass during densification [ 90 ]. There are several size reduction methods, which include chopping, chipping, hammer milling, crushing, shredding, and grinding. Size-reduced biomass was classified as chopped (50–250 mm), chipped (8–50 mm), or grinded (<8 mm) [ 85 ]. Another means of reducing the size of biomass before densification is through the use of sieve either by oscillatory screen method [ 91 ] or by vibratory screen method [ 92 ]. The status of the biomass feedstock determines which method or combined methods that needs to be adopted. Tumuluru and Heikkila [ 93 ] reported a two-stage grinding process of woody and herbaceous biomass materials. The first stage entails the grinder breaking the biomass bundles into a larger size material enhancing its movement in the conveyors, while the second stage involves a further grinding to a smaller size to make the biomass suitable for biochemical and thermochemical conversion processes. Common equipment used to reduce the size of biomass for briquette densification include hammer mill, knife mill, linear knife grids, and disk attrition. However, hammer mills are considered the most suitable [ 86 ], whereas the cutting mill is the next most preferred [ 94
Feedstock drying is essential particularly if the feed is wet, however some materials like coffee husk, groundnut shells, and rice husk usually may not require drying. Drying of feedstock increases its efficiency but should not be excessively dried. Allowing a small amount of moisture helps in binding the biomass particles. According to Solano et al. [ 85 ], drying can be done naturally by exposing the feedstock to favorable environmental conditions to reduce its moisture contents without supplying any heat externally. Another way is forced drying by industrial process that reduces the moisture content of biomass fuel down to a specified range (5% to 15%) suitable to start densification. For biomass that has to be forced dried, Grover and Mishra [ 86 ] noted the use of direct driers in which hot air or flue gases are intimately mixed with material and indirect ones where heat is transferred to materials through a metallic surface. In the indirect driers, material is not mixed with the hot air. Purohit and Chaturvedi [ 87 ] noted that the drying process is the most energy-intensive process and accounts for about 70% of the total energy used in the biomass densification process.
The densification of biomass materials into briquettes usually starts with sorting and cleaning of the feedstock. This procedure is also called sieving, which is done to remove all unwanted materials ensuring that all the feedstock is of the required size [ 83 ]. As reported in [ 37 ], screening equipment such as sieves and magnetic conveyors are used to remove impurities such as soil, dirt, metal, and plastic strings, etc., to achieve the maximum cleanliness of the feedstocks. These unwanted materials are generated during the collection and storage of residues. Washing the materials with water or mild solvents is another means of cleaning out impurities generated through alkali oxide, chemicals, and fertilizer application in agricultural farms. Said et al. [ 84 ] observed that washing can improve the combustion properties of biomass
During the densification of corn stover and switchgrass, Kaliyan and Morey [ 109 ] used scanning electron microscopes (SEMs) to understand the formation of solid-type bridges. Results from the SEM images showed that the bonding between particles was created mainly through solid bridges. The solid bridges between particles were made by natural binders in the biomass expressed during the densification process. Ultraviolet auto-fluorescence images of briquettes and pellets further confirmed that the solid bridges were made mainly by natural binders such as lignin and protein. It was found that activating the natural binders using moisture and temperature in the range of glass transition is important to make durable inter-particle bonding. Tumuluru et al. [ 9 ] suggested that more studies at a micro level using techniques like SEM and transmission electron microscope (TEM) will be useful in understanding intra-particle cavities, material properties, and process variable interactions on the quality attributes of densified biomass
The production process of briquettes essentially involves the acquisition of the biomass feedstock, processing it, and eventual densification ( Figure 1 ). Densification is done by applying pressure, heat, and binding agent on the residues to produce the briquettes [ 141 ]. The output of the densification process is briquette ( Figure 2 ), which is referred to as a compressed block of organic waste material [ 83 ] used for domestic and industrial purposes in both rural and urban areas [ 141 ]. Briquettes are made of different qualities and dimensions depending on the raw materials, mold, and technologies applied during production [ 83 95 ]. Briquettes vary a lot in size and form, but usually they are of a cylindrical shape with a diameter of between 25 and 100 mm and lengths ranging from 10 to 400 mm [ 142 ]. Square, rectangular, and polygonal briquettes also exist. Densified biomass such as briquettes have several advantages, which includes, but are not limited to, increased energy density, ease of handling, transport and storage, improved combustibility, lower particle emission, low volatility, and uniform size, density, and quality [ 143 145 ].
Cellulose, a linear polymer, is a complex carbohydrate (or polysaccharide) with a high molecular weight and a maximum of 10,000 monomeric units of D-glucose, linked by β-1,4-glycosidic bonds. Cellulose is an abundant source of carbon in biomass [ 165 ]. Carbon enables combustion of briquettes and a higher carbon content is commonly related to a higher calorific value [ 166 ]. Hemicellulose consists of heterogeneous branched polysaccharides and is strongly linked to the surface of cellulose microfibrils. It is amorphous in nature and has adhesive properties, with a high tendency to toughen when it is dehydrated [ 2 ]. Lignin, contained in plant cell wall, denotes a complex amorphous aromatic polymer with a three-dimensional network, composed of phenylpropane units linked together. In the feed material, lignin serves as an in-situ binder enabling the binding process at high temperatures when it softens [ 144 ], making it possible to produce more durable briquettes [ 55 ]. Additionally, it yields more energy when burned than cellulose [ 9 ].
Temperature affects both biomass feedstock and the die of the briquetting machine before and during the briquetting process. It aids in the release of components such as lignin, cellulose, and hemicellulose where the lignin act as binders. Yank et al. [ 147 ] noted that high temperature and pressure are widely agreed to enhance binding mechanisms but require important energy input. Grover and Mishra [ 86 ] advised that the preheating temperature should not exceed 300 °C to prevent biomass materials decomposition while that of the die in a screw press extruder should be kept at about 280–290 °C. Okot et al. [ 149 ] investigated maize cobs briquettes densified at varying temperatures of 20–80 °C. The study concluded that densification at temperature of 80 °C could produce briquettes with high density and durability/mechanical strength required to meet quality certification standards. As part of the process parameters in briquetting of pine needles, Mandal et al. [ 150 ] used a temperature range of 60–150 °C. Results from the study showed that a temperature of 150°C was found to be optimum to produce briquette. Optimum temperature value within the range of 65–100 °C for feedstock preheating was proposed by Kaliyan and Morey [ 144 ] but added that temperatures higher than 100 °C and up to 300 °C can be used if desired. According to Grover and Mishra [ 86 ], die temperature exceeding what is required will decrease the friction between feedstock and die wall enabling densification at lower pressure to produce low-quality briquettes. Conversely, low temperature will result in higher pressure and power consumption. It also leads to lower production rate, but higher-quality briquettes.
Biomass can be densified under a high compaction pressure or a low compaction pressure. Generally, the feedstock type, moisture content, and particle size and shape determine the amount of pressure to be applied. Densification under low compaction pressure requires a binding agent to enable interparticle bonding. High-pressure densification utilizes the natural binding components such as starch, protein, lignin, and pectin, which are squeezed out of the particles of the biomass materials, to facilitate inter-particle bonding. According to Dinesha et al. [ 42 ], the outcome of pressure application is plastic and elastic deformations and filling of voids, forming higher density briquettes. Compaction pressure influences density, compressive strength, and durability of briquettes. Kpalo et al. [ 70 ] varied pressure from 5.1 to 15.3 MPa to produce briquettes made from wastepaper andmixtures at different ratios. The study reported that pressure at 15.3 MPa produced the highest densities for each ratio of briquettes, while the pressure at 5.1 MPa produced the lowest densities. Additionally, in measuring the shear strength of biomass briquettes, Chin and Siddiqui [ 146 ] raised the densification pressure from 1 to 10 MPa and found that the shear strength of briquettes increased from 27.5 to 95.7 N (sawdust), 1.2 to 4.6 N (rice husk), 1.3 to 6.7 N (peanut shell), 10 to 73.3 N (coconut fiber), and 10 to 36.2 N (palm fiber). Kaliyan and Morey [ 144 ] noted that high pressure helps the densification of biomass and suggests a range of 100–150 MPa, or higher. However, studies have shown that low compaction pressure can produce low-cost briquettes that are durable [ 73 148 ].
Different types of manual presses exist for the densification of biomass materials. Some come in the form of piston or screw presses but are operated with bare hands and hardly uses electricity. According to Maninder et al. [ 47 ], manual presses are designed for the purpose of briquette making or adapted from existing implements used for other purposes. Manual clay brick making press is a good example with which briquettes can be made from both carbonized and non-carbonized biomass feedstock. Another common example of manual press is the WU-Presser ( Figure 6 ) developed by the Washington University, USA [ 174 ]. The press is made from both metal and wood with the latter being the most common. These machines operate with very minimal pressure and binder addition to feedstock is required. Manual presses are characterized by low capital costs, low operating costs, and low levels of skill required to operate the technology. However, they have a low production capacity of about 5 kg/h or 50 kg in a 10-hour day [ 142 ].
Roller presses are considered the global standard technology to produce pillow-shaped briquettes using diverse types of biomass. The roller press works on the principle of pressure and agglomeration ( Figure 5 ). It consists of dual cylindrical rollers of the same diameter, rotating horizontally in opposite directions on parallel axes [ 172 ]. The two rollers are arranged in such a way that a small gap exists between them and the distance from each other depends on factors such as the biomass type, the particle size, the moisture content, and the addition of binders. During operation, the raw material is fed into the press and forced through the gap between the rollers on one side. It is then pressed into a die forming the densified product, which comes out on the opposite side. The smooth production of briquettes using this technology requires high-quality rollers with smooth surfaces on which the briquettes are shaped. The type of roller or die used determines the shape of the densified biomass [ 172 ] and typical bulk densities range from 450 to 550 kg/m 173 ].
The hydraulic piston press operates like the mechanical piston press. However, the energy to the piston is exerted by a cylinder operated by a hydraulic system. Eriksson and Prior [ 104 ] noted that the briquetting pressures with hydraulic presses are considerably low and this is because of limitations in pressure in the hydraulic system, which is normally limited to 30 MPa. The piston head can exert a higher pressure when it is of a smaller diameter than the hydraulic cylinder, but the gearing up of pressure in commercial applications is modest. The typical production capacities of these machines are in the range of 50–400 kg/h and can tolerate higher moisture contents than the usually accepted 15% for mechanical piston presses. It usually produces briquettes with a bulk density lower than 1000 kg/m³ because pressure is limited [ 9 ]. In general, briquettes produced have a uniform shape and size, typically using 40 × 40-mm cylinders [ 105 ], and the quality of the product here is much higher compared to mechanical presses. Additionally, a hydraulic press can sometimes be an alternative to a mechanical press, and typical materials suitable for this machine are paper, cardboard, manure, etc. [ 104 ].
The mechanical piston press consists of a ram (piston) and a die and it is driven by an electric motor ( Figure 4 ). Biomass feedstock is punched into a die by a reciprocating ram with a very high compaction pressure to obtain a briquette. According to Tumuluru et al. [ 9 ], this machine develops a compression force of approximately 196.1 MPa and is typically used for large-scale production, ranging 200–2500 kg/h. The achieved briquette densities are generally in the range between 1000 and 1200 kg/m 85 ]. The capacity of a mechanical piston press is defined by the volume of material that can be fed in front of the piston before each stroke and the number of strokes per unit of time. Capacity by weight is then dependent on the density of the material before compression. The moisture limit of feedstock in most cases is 15%; nonetheless, the ideal operating region is 8%–12%. A lower limit of 5% is acceptable as anything less will cause friction and thus increase energy demand [ 104 ]. Materials that can be densified include agricultural waste, coal dust, saw dust and shavings, tree bark, etc. In comparison to the screw press, it has long life of wearing parts and a low power consumption rate. It also requires a higher level of maintenance and the briquettes produced are of lower quality. Additionally, it generally gives a better return on investment (ROI) than the hydraulic piston press [ 9 ].
A screw press consists of screw extruder and a die ( Figure 3 ). Three types of screw presses are recognized, and they include conical screw presses; cylindrical screw presses with heated dies; and those without externally heated dies. In the screw extruder, the biomass is continuously fed into a screw, which forces the material into a heated cylindrical die to the point where lignin flow occurred [ 104 ]. The technology is based on the pressure of a special screw that pushes raw material within a chamber that becomes progressively narrower [ 85 ]. The pressure is built up along the screw rather than in a single zone as in the piston machines. Binder is hardly required in a screw press densification; however, it could be necessary if the required temperature (200–250 °C) to dissolve lignin is not achieved, or when biomass has been carbonized, which destroys lignin content. The screw press may enjoy lower capital costs, but higher maintenance cost than the piston presses due to substantial wear on the screws, which must be reconstructed regularly. Its specific energy demand is also higher. Screw extruders were initially built and used for briquetting sawdust; however, field data verify that the machine also work well when briquetting rice husks, apart from the high wear problems [ 104 ]. Screw press briquettes have a concentric hole, which gives better combustion characteristics due to a larger specific area. They are also homogeneous with a high combustion rate and do not disintegrate easily. Briquette densities from these machines usually range between 1000 to 1400 kg/m 86 ].
The briquetting technology is new in African nations, but advanced in Asia, America, and Europe [ 167 ]. Certain advantages of using biomass have led to the development of such advanced technologies for energy and fuels conversion [ 168 ]. According to Wilaipon [ 169 ], the technology can, based on compaction, be divided into high-pressure compaction and low-pressure compaction. Eriksson and Prior [ 104 ] classified compaction pressures as low (5 MPa), intermediate (5–100 MPa), and high (100 MPa and above). High-pressure compaction technology uses a heating device while the other uses a binder. However, based on equipment used, Ahmed et al. [ 141 ] categorized the technology into piston press technology and screw press technology. There are several types of briquetting machines available for densification and compaction of biomass. Their mode of operation varies from one principle to another. Several studies have identified these machines to include the screw press extruder, roller press, piston press (which can either be mechanical or hydraulic), and manual press [ 9 171 ]. Table 3 shows a comparison of these machines based on certain parameters while their utilization in briquette production from the literature is presented in Table 4
In another study by Feng et al. [ 185 ], findings revealed that NPV was sensitive to change in the price of briquette and cost of raw materials. For instance, percentage change from −10% to +10% in the price of briquettes resulted in the fluctuation of the NPV from4.93 million to14.70 million. It also revealed that a 10% increase in the cost of raw material reduces the NPV and vice versa. The study concluded that the risk of lower NPV from briquette price reduction is less compared to the increase in the cost of raw material. Similarly, a varied percentage change from −20% to +20% in the price of briquette and cost of cornstalk influenced the economic performance of a biomass briquette fuel system [ 186 ]. The percentage change in briquette price caused the NPV, IRR, and PBP to range from −0.40 million to3.06 million, from −2% to 60%, and 2.8 to 25 years, respectively, while the change in cost of corn stalk led the economic indices to range from0.68 million to2.02 million, from 24% to 47%, and 3.5 to 6.5 years, respectively. The sensitivity analysis is geared towards determining how diverse values of an independent variable will impact a dependent variable given a set of assumptions and ultimately to determine the profitability of the proposed project.
A Sensitivity analysis is used to include uncertainty in a project’s economic assessment to generalize the results for diverse situations where input factors and costs are different [ 188 ]. In a recent study by Sahoo et al. [ 189 ], a sensitivity analysis was conducted to determine the impact of key input parameter on the minimum selling price (MSP) of woodchips briquettes (WCB), torrefied-woodchips briquettes (TWCB), and biochar. The MSPs per oven-dry metric ton (ODMT) of WCB, TWCB, and biochar were162,274, and1044, respectively. The study varied ±20% change in input parameters for the financial model and results showed variation in the relationship between changes in the models’ input variables and their impact on MSP. Moisture content was found to be the most sensitive input for WCB, and its MSP was decreased by 10% or increased by 12.5% by using woodchips at 29% or 43% moisture. Furthermore, about 4%–8% change in the MSP was obtained by a 20% variation in the capital cost.
is the ratio of the equivalent worth of benefits to the equivalent worth of costs. A project can be accepted if the BCR is equal or greater than 1 [ 181 ]. The economic analysis in [ 175 ] found that briquettes produced from cassava rhizome charcoal with either molasses or starch gel binder in proportion of 7:3 were found best with highest BCR of 2.01 and 2.15, respectively. BCR for cashew shell, grass, and rice husk briquettes were 2.8, 2.93, and 1.51, respectively [ 183 ]. The values for BCR obtained in these studies indicates acceptability. To conclude that a project like briquetting plant or technology is feasible and profitable, all economic indicators used for economic analysis are expected to be positive
is the maximum interest that could be paid for the resources used if a project is to recover all cost expended and still break even [ 183 ]. In conducting an economic assessment of a briquetting project with an expected 15 years economic life, Hu et al. [ 186 ] reported an IRR of 36% and a payback period of 4.4 years. Onchieku [ 180 ] also reported 68%, 76%, and 100% on different scenarios when carrying out a cost-benefit analysis of charcoal briquette production over two years. The discount factor in this case was 15%. According to Walekhwa et al. [ 182 ], an investment is said to be profitable when the value of IRR is higher than the discount rate.
is calculated while accounting for the time-value of money and used also to measure the level of risk. Sengar et al. [ 183 ] reported that cashew shell and grass briquettes took 0.68 and 0.63 years, respectively, as the project’s payback period. However, the same project took 2.5 year for rice husk briquettes, which is slightly above the two-year period reported by Hamid et al. [ 74 ] for the production of rubber seed kernel (RSK) and palm oil shell (POS) briquettes. In other studies, the payback period for durian peel and rice straw briquettes was 1.3 years [ 187 ] while peat briquettes production was between five and six years [ 184 ]. The payback period of a project is usually compared with its economic life. The lesser the number of years to recover the investment, the better for the project
Żarski [ 177 ] reported that total cost of producing 1 ton of briquette from cereal and oil-rape straw amounted to62.43, with cost of raw materials, depreciation, and cost of electricity taking the largest share. Similarly, the total cost of producing 1 ton of fuel briquettes from sawdust was84.45, which is more than 35% higher than in the case of production of briquettes from straw. In analyzing the cost of smokeless charcoal briquette produced from agricultural and forest residues, Tippayawong et al. [ 178 ] reported0.42 as the total cost of a kilogram of the briquette. The cost of the raw char accounted for around 70% of the total cost, however an estimated 22.4% was also reported as profit. These studies agree with [ 22 176 ] that the purchasing price of biomass account for the largest proportion in briquettes price. Additionally, Gill et al. [ 53 ] reported that the total cost of making briquettes from chopped rice straw only was0.041 per kilogram and0.00281 per mega joule of energy, while that of briquettes from chopped rice straw with 10% and 20% cotton stalks was0.050 and0.051 per kilogram, respectively, and0.0033 per mega joule of energy. The study concluded that it is economically viable to produce briquettes from chopped rice straw with and without cotton stalk as a binder. Srivastava et al. [ 68 ] produced and evaluated briquettes using four types of vegetable market wastes (VMW) without the use of external binder. Results showed that the total cost of briquettes, including the cost of raw material, ranged from24.68 to28.90 per ton. The study noted that the cost is comparable to the cost of wood available at market rate and thus concluded that the briquetting of VMW may be a viable option for obtaining useful energy instead of being allowed to rot creating environmental problems
The costs of processing equipment, briquetting machine and accessories, land, and building where necessary, are basically what constitutes the capital cost of a biomass briquetting system. The costs associated with mounting such equipment and machinery on site refer to the installation cost. The cost of labor, raw material, electricity, oil and lubricant for machinery, transportation, and other related inputs that enhance the smooth running of the briquetting plant essentially forms the operation cost. Finally, the repair and maintenance cost are basically comprised of expenditure made on the appropriate maintenance of the briquetting plant and machinery on a daily, weekly, monthly, or as deemed necessary basis. This involves repair or outright replacement of damaged parts, oil cleaning, and tightening of loose screws. Several studies have reported the application of these costs to arrive at the total production cost of briquettes.
For countries in the developing world, residue availability does not present a problem, however the optimization of the chemical and mechanical treatments needed for most of the innumerable feedstocks remains a challenge. With reference to the rural communities where power is hardly enough, an appropriate means of pre-processing will be the type that will require minimum energy input. Most technologies that produce high-quality briquettes, as reviewed, are expensive and requiring high energy input. Production of briquettes on a large scale will require significant capital investment. This presents an obstacle to further expand biomass densification. To attract more investment in areas that lacks adequate financial capacity and high energy input, efforts should be geared towards the development of more user-friendly and cost and energy effective technologies at various scales. Finally, the market for briquette and their extensive utilization as substitutes to conventional biomass (fuelwood) and fossil fuel exists. However, to bring its full potential to bear, the challenges presented above should be addressed.
The world today is experiencing a rise in population growth and this also comes with increasing energy demand. Records have shown that there is a lot of pressure on fossil fuel, which is diminishing at a fast rate and whose growing utilization has consequential effects leading to climate change. To forestall future energy crisis and mitigate climate change, it has become imperative to source for alternative energy supply. Biomass presents an opportunity to reduce our dependence on fossil fuels. The challenge with biomass is that it is usually low in bulk and energy density, which poses a problem of handling, transportation, and storage. This problem is however curbed by briquetting, which also improves the biomass density, burn time, and the calorific value. This paper reviewed studies on technical and economic aspects of biomass briquetting. The review revealed that type of biomass material (feedstock), pre-processing, briquetting process parameter, and technology determine the quality of briquettes. Briquetting can be done with a low-pressure or high-pressure technique. However, the technology utilizing high compaction pressure and temperature is significant in producing more durable and high energy density briquettes. Currently, the machines available for briquetting include the screw press extruder, roller press, and the piston press (mechanical or hydraulic). Additionally, successful briquetting requires financing and it is necessary to evaluate its economic viability since the products are meant to serve as alternatives to existing fuels. This evaluation is achieved by analyzing the various costs involved including economic indicators such as NPV, PBP, IRR, and BCR. In the end, it is in the overall interest of both producer and the end users for the cost of briquettes to be cheaper and more efficient than the cost of the fuels they are likely to substitute. Biomass briquettes can be used in both rural and urban areas for domestic heating applications. They can also be utilized in industrial applications for heating and energy production such as gasification. Since high-pressure technology and supporting conditions are not easily available in many local communities especially in the developing countries, more efforts should be directed towards improving the quality of fuel briquettes produced at lower pressures and temperature. Appropriate briquetting machine capable of producing such quality briquettes and at low costs suitable for local communities needs to be developed.
What are briquettes?
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Briquettes are compressed blocks of coal or charcoal that burn under fire. They are an excellent way to utilise the smashed pieces of charcoal usually thrown away and the cow dung that causes pollution if not properly disposed of.
Briquettes burn longer than charcoal and, therefore, will reduce the amount of charcoal a household uses.
Briquettes help to conserve the environment because they burn for an average of two hours-and-a-half compared to the 45 minutes of charcoal.
Briquettes dry in less than three days during the dry season and take twice as long during the wet season. Those made from charcoal dust and paper dry faster than those made from charcoal dust and soil.
How to use briquettes
When using briquettes, light your charcoal stove with a little charcoal. When the charcoal has lit up, you add the briquettes.
While cooking, even when the small charcoal you use gets finished, the briquettes will remain hot and you can cook with them.
With these three simple steps, you can save money. Briquette-making can also be a money venture for both you and your children.
Benefits of briquettes
Briquettes are a clean cooking fuel. They keep the environment safe and healthy to use since they are smokeless.
Briquettes made of cow dung and charcoal dust burn for over four hours, compared to 45 minutes for regular charcoal.
Briquettes neither smell nor 4Briquettes produce less smoke compared to charcoal and leave no soot on pots.
Experiments have proved that briquettes reduce household carbon monoxide pollution.
Briquette production is a profitable business for the youth since materials used to make them are locally available.
Marketing briquettes
You can sell five charcoal briquettes for sh1,000 and can make around 1,000 briquettes in three hours.
You will need half a bag of charcoal dust (sh6,000) and three wheelbarrows of cow dung (sh10,000) to make 1,000 briquettes.
Potential customers need information on the multiple benefits of fuel briquettes to realise high sales.
Make some and give them to people for free so they understand that they burn hotter and for longer than normal charcoal.
Easy step-by-step guide
STEP 1: Sieve charcoal dust to free it from any impurity.
STEP 2: Crush charcoal dust into fine powder.
STEP 3: Mix cow dung with charcoal dust and little water in a ratio of 1:3:0.5 (cow dung to charcoal dust to water).
STEP 4: Put the material inside the briquette mould, hit 2 or 3 times and remove.
STEP 5: Manual grinding and compacting of fuel briquettes is tedious and compromises the density of the product, leading to breakages during transportation.
STEP 6: Remove the briquettes and dry in a solar dryer or under a well-ventilated place where they stay for four days before being packaged.
Drying fuel briquettes on the ground slows down the process as some pieces receive low amounts of sunlight. Spreading briquettes on roof tops speeds up the drying process, but results in breakages.
These two forms of drying also expose briquettes to rain. The drying period depends on the raw material used, size of briquettes and the weather.
What you will need
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