Briquetting of Dry Sugarcane Leaves by Using Press Mud, Cow Dung, and Buffalo Dung as Binders

Chemical Engineering Department, D. Y. Patil College of Engineering and Technology, Kasaba Bavada, Kolhapur 416006, India Chemical Engineering Department, KLE Dr. M. S. Sheshgiri College of Engineering and Technology, Belagavi 590008, India Chemical Engineering Department, Universiti Teknologi PETRONAS, Bandar Seri Iskandar, Perak, Malaysia Centre for Systems Engineering, Institute of Autonomous Systems, Universiti Teknologi PETRONAS, Bandar Seri Iskandar, Perak, Malaysia Faculty of Mechanics and Mathematics, Department of Mathematical and Computer Modelling, Al-Farabi Kazakh National University, Almaty, Kazakhstan Department of Energy Engineering, Graduate School of the Environment and Energy,Science and Research Branch, Islamic Azad University, Tehran, Iran


Introduction
Energy is an important parameter in a civilian's life. Today, the lifestyle of civilians is largely dependent on energy and the amount of energy required by the population and industrial sector is increasing. e requirement for energy will always be higher than the energy supply. To fulfil the requirement for energy, there is thus a need to generate energy from various renewable resources [1]. To fulfil its demand for energy, India is largely dependent on oil and natural gas. Of total oil demand, 70% is imported, which affects the economy of the country [2]. Further, the use of oil and natural gas as a source of energy results in environmental pollution. Renewable sources are therefore an urgent solution for both pollution and economic problems. Examples of renewable sources are biomass, nuclear, hydro, tidal, geothermal, solar, and wind energy [3].

Source of Energy Biomass.
Biomass, an organic matter or biological material derived from living organisms, is the best alternative to oil and natural gas. It can be transformed into solid, liquid, and gaseous biofuels that generate energy on burning [4]. Biomasses in different forms are available in large quantities in developing countries. Biomass accounts for 11.5% of energy demand and is expected to increase to between 15% and 50% by 2050 [5,6]. e cost of energy produced from biomass is relatively low [7]. e world's biomass energy potential in 2020 is presented in Table 1 [8].
Human waste, food processing, animal waste, agricultural waste, and forestry are examples of biomass [9]. In total, 320 million tonnes of agricultural waste such as dry sugarcane leaves, bagasse, rice straw, rice husks, wheat straw, and corncobs are produced by India. is residue is often burnt in an open atmosphere, creating smoke and fly ash problems. Approximately 100 million tonnes of agricultural waste are burnt in open fields, creating air pollution [10]. Burning this agricultural waste results in a huge loss of energy. However, the great task is converting this biomass into briquettes to generate energy [11][12][13].

Dry Sugarcane Leaves.
Sugarcane plants are the best examples of how nature has provided us with renewable biomass to generate energy. Research has examined how such plants can be a substitute for coal, oil, and natural gas. For example, converting the waste of sugarcane plants into solid fuel such as briquettes could be the best solution to deforestation, which is a hot topic [14]. A large amount of sugarcane is produced globally, especially in India [15]. In 2015, 1877105 thousand metric tonnes of sugarcane were produced globally. India ranked in second place with 341200 thousand metric tonnes after Brazil (739267 thousand metric tonnes) with China in third (125536 thousand metric tonnes). e top 10 sugarcaneproducing countries are presented in Table 2 [14,16] and the top three sugarcane-producing states in India are Uttar Pradesh, Maharashtra, and Karnataka (132427.6842, 69648.0768, and 35732 thousand metric tonnes, respectively). e top 10 sugarcane-producing states in India are presented in Table 3 [17]. e modification of the agricultural sector has produced a huge amount of waste, which has the potential to produce low-cost energy compared with oil and natural gas [18][19][20][21]. A large amount of agricultural waste is produced after cleaning sugarcane stems.
is agricultural waste mostly consists of leaves and tops, which remain unused in the sugar production process [22]. Approximately 279 million metric tonnes of residue such as dry leaves and bagasse are generated by the sugarcane industry [15]. Although 3500 kg of dry sugarcane leaves is produced from one hectare of sugarcane crops and the gross calorific content of dry sugarcane leaves is 16919.667 kJ/kg, converting dry sugarcane leaves into biofuels has hardly been explored [23]. Dry sugarcane leaves are the major source of energy that could be used to make briquettes.

Briquetting.
e technique of compacting loose biomass is known as briquetting [12,14]. Techniques include high-pressure and low-pressure briquetting.
ese are classified depending on the method applied to make briquettes, such as using a piston press, screw press, pellet mill, and hydraulic press. e types of binders used to make dry sugarcane leaf briquettes are starch, protein, fibre, fat/oil, lignin, cattle dung, press mud, molasses, and pulp and paper. e objective of the present study was to explore different binders for making dry sugarcane leaf briquettes and examine the expediency of briquettes by determining their physical parameters and proximate analysis.

Material.
Dry sugarcane leaves of species 86032, which were used to make the briquettes, were collected from an agricultural field in Kolhapur, Maharashtra, India. Breed 86032 is cultivated in large quantities in Maharashtra and across India. e cow dung and buffalo dung binders used to make the briquettes were collected from a local dairy farm in western Maharashtra and the press mud binder was collected from a sugar manufacturer in western Maharashtra.   e following instruments were used to analyse the dry sugarcane leaves, cow dung, buffalo dung, press mud, and briquettes. A digital balance (model: SJ, Vibra, Mumbai, India) was used to weigh the required amount of briquettes. A hot air oven (model no.: Digital 1874, Lab Hosp, Mumbai, India) was used to measure the moisture content of the sample. A muffle furnace (model no.: 591010, Shital Scientific Ind., Mumbai, India) was used to determine the volatile matter and ash content. e gross calorific value (GCV) was measured using a bomb calorimeter (model: BCA, Dynamic Engineering, Mumbai, India). A tumbling machine (Shital-Gayatree Enterprise, Rajkot, India) was used to measure the tumbling resistance (TR). Split tensile strength (STS) was measured using a hydraulic press (model no.: TUE-C400, Fine Spavy Associates Pvt. Ltd., Miraj, India).

Experimental Setup.
A hydraulic press or universal testing machine (model no.: UTM-86/08/003, Superfine Testing Equipment, Kolhapur, India) was used to make the briquettes. A cutting machine (Arihant Fabrication and Engineering, Minache, Kolhapur, India) was used to cut the dry sugarcane leaves. A digital weight balance (model no.: PNM101, Padmini Industries, Sangli) was used to measure the required amount of the sample. e dry sugarcane leaves and binders were placed in a die of 0.15 m inner diameter and 0.13 m height. e sample was compressed with a block of 0.147 m diameter and a height of 0.075 m. e die and block were held between two plates of 0.117 m in diameter on the universal testing machine.

Experimental Procedure for Making Dry Sugarcane
Leaf Briquettes from Different Binders. First, 0.2 kg of dry sugarcane leaves was weighed by using an electronic weighing balance. e dry sugarcane leaves were mixed with 1 kg of the binder (cow dung, buffalo dung, and press mud binders separately). e mixture was placed in the die and the block was adjusted over the sample. e load was gradually applied to the sample. At a high load, the original moisture present in the sample came out along with some of the binder. is load was 22 kN for the cow dung binder, 11 kN for the buffalo dung binder, and 12 kN for the press mud binder. After the removal of the sample from the die, the briquette was disintegrated. Further experiments were carried out at a lower load (20 kN for the cow dung binder, 9 kN for the buffalo dung binder, and 10 kN for the press mud binder). e experiments were conducted for the following weight ratios of dry sugarcane leaves to binders: 1 : 0.5, 1 : 1, 1 : 1.5, 1 : 2, 1 : 2.5, 1 : 3, 1 : 3.5, 1 : 4, 1 : 4.5, and 1 : 5. e optimum weight ratio was chosen depending on the briquette formation. e optimum weight ratio of the dry sugarcane leaves to the cow dung binder was 1 : 3.5, to the buffalo dung binder was 1 : 4, and to the press mud binder was 1 : 2. ese were the ratios at which suitable briquette formation took place. e optimum weight ratio samples were applied with different loads. A suitable briquette formation took place for the cow dung binder at 18 kN, the buffalo dung binder at 9 kN, and the press mud binder at 10 kN. Before the optimum load, no briquette formation occurred. en, the sample was tested by adding water (1 ml and 2 ml). When the water was added to the sample, moisture came out along with some of the binder and the briquette was disintegrated after it was removed from the die. e dry sugarcane leaf briquettes with the cow dung binder (DSL/CD), buffalo dung binder (DSL/BD), and press mud binder (DSL/PM) were analysed based on the optimum weight ratios and optimum load.

Physical Parameters
(1) Bulk density (BD): the BD of the briquettes was determined by using a standard procedure. An empty container with a known volume was weighed. e container was then filled with the sample and weighed. e BD was calculated using the following equation [24]: where W 2 is the weight of the container + sample, W 1 is empty weight of the container, and V is the volume of the container. (2) Relaxed density (RD) or BD of the briquettes by geometric measurements: if the briquettes are cylindrical, their density can be calculated from their geometry. e RD was calculated using the following formula [24]: where D is the diameter of the briquette and H is the height of the briquette. (3) BD of briquettes by using the water displacement method: the briquettes were coated with an adhesive tape (cellux self-adhesive tape) to prevent any water penetration when submerged in water. e weights of the briquettes were measured before and after coating with the tape. e coated briquette was submerged in water and the volume of the water displaced was measured. e BD of the briquettes was obtained using the following formula: International Journal of Chemical Engineering bulk density kg/m 3 � (weight of coated briquette − weight of briquette) volume of water displaced . (3) (4) Degree of densification (DD): the DD is the bounding ability of biomass. It increases in the density of dry sugarcane leaves and binders due to briquetting. It was calculated using the following equation [25]: degree of densification � (density of briquette − density of dry sugarcane leaves) density of dry sugarcane leaves .
(5) Compression ratio (CR): the CR is the ratio of the density of a briquette to the density of dry sugarcane leaves. As the briquetting load increases, the CR increases in a similar manner to the BD [25]. (6) STS: STS is the maximum load at which the failure of a briquette takes place. A briquette was held between two parallel flat plates. A gradually increasing load was applied using a hydraulic press (model no.: TUE-C400, Fine Spavy Associates Pvt. Ltd., Miraj, India) until the failure of the briquette took place. e load at which the failure of the briquette took place was noted. STS was calculated using the following formula [26]: where P is the load at which cracking occurs, D is the briquette diameter, and L is the briquette length. (7) TR test: the TR is the resistance to the stress or force of a briquette. e weight of the briquette was measured and placed in the metallic cylinder of 0.2 m inner diameter and 0.24 m length. e opening on the top of the cylinder was closed. e cylinder was rotated in the tumbling machine (Shital-Gayatree Enterprise, Rajkot, India) at 70 rpm for 5 minutes. e weight of the briquette after the tumbling test was noted and the TR was calculated using the following equation [25]: where W 3 is the weight of the briquette before the tumbling test and W 4 is the weight of the briquette after the tumbling test.
tumbling resistance(%) � 100 − % weight loss. (7) (8) Shatter resistance (SR) test: the hardness of a briquette is determined using an SR test. e weight of the briquette before the SR test was measured. e sample was then dropped on a concrete floor from a 1 m height. e procedure was repeated for 10 drops. e weight of the briquette after 10 drops was measured. e SR of the briquette was calculated using the equations given below [25]: where W 5 is the weight of the briquette before the shatter test and W 6 is the weight of the briquette after the shatter test.

Proximate Analysis
(1) Moisture content: the moisture content was measured by using a standard method (ASTM). e weight of the briquette before drying was measured and then the briquette was placed in an oven (model no.: Digital 1874, Lab Hosp, Mumbai, India) at 378 K for 240 to 300 minutes until a constant weight was reached. e weight of the sample after drying was noted.
is method of measuring the moisture content is called the oven drying method. e moisture content of the sample was calculated using the following equation [25]: where W 7 is the weight of the crucible, W 8 is the weight of the crucible + sample before drying, and W 9 is the weight of the crucible + sample after drying. (2) Volatile matter: the dried briquette left from the procedure described in Section 2.4.1 was used to calculate the volatile matter. e crucible with the dried sample was covered with a lid. en, it was placed in a muffle furnace (model no.: 591010, Shital Scientific Ind., Mumbai, India) at 873 K for 10 minutes according to the standard method (ASTM). e crucible was removed from the furnace and cooled in air and then in desiccators. e weight of the crucible was noted. e percentage of the volatile matter was calculated using the following formula [25]: 4 International Journal of Chemical Engineering volatile matter(%) � where W 10 is the weight of the crucible, W 11 is the weight of the crucible + sample, W 12 is the weight of the crucible + sample in the muffle furnace, and W 13 is the weight of the crucible + sample after heating. (3) Ash content: the residual sample from the volatile matter content was heated without a lid in a muffle furnace at 973 K for 240 to 300 minutes until a constant weight was reached. e crucible was removed from the furnace and cooled in air and then in desiccators. e percentage of the ash content was calculated following ASTM standards. e weight of the crucible was recorded. e percentage of the ash content was calculated using the following formula [25]: where W 14 is the weight of the crucible, W 15 is the weight of the crucible + sample, and W 16 is the weight of the crucible + ash. (4) Fixed carbon content: the percentage of the fixed carbon content was determined using the following equation [25]: fixed carbon(%) � 100 − %(ash content + volatile matter + moisture content).
(5) GCV: the GCV was measured by using a standard procedure (ASTM). e complete combustion of the sample was carried out in an adiabatic bomb calorimeter (model: BCA, Dynamic Engineering, Mumbai, India) at 25 atm of oxygen. To measure the water equivalent of the apparatus, a powder of 0.01 kg of pure and dry benzoic acid was burnt in a bomb calorimeter under the same conditions. Altogether, 6324 calories/gm of the calorific value of benzoic acid was taken. e GCV was determined using the following formula: where X is the mass of the sample briquette taken in the crucible.

Energy Density Ratio (EDR).
e EDR measures the energy content per unit volume of a briquette. e BD and GCV were used to calculate the EDR [13]: energy density ratio � energy content of briquette kJ/m 3 energy content of dry sugarcane leaves kJ/m 3 .

Results and Discussion
e physical analysis and proximate analysis were carried out after one week of briquette production. e briquettes were sun-dried at a temperature between 305 and 310 K and a humidity between 62% and 69%. high-quality briquette should have a high BD, which will burn for longer periods, have a high content energy per volume, and be easy to handle and store [27]. Due to the high load application, a solid bridge may be developed between particles. van der Waals forces developed with the help of moisture also aggregate the particles. Lignin, which is present in dry sugarcane leaves and the buffalo dung binder, acts as a binding agent and helps the binding process. At a high load, lignin comes from the biomass particles and helps form a solid bridge between them [28]. Because of this process, the BD of DSL/BD is high. As the amount of the binder in the briquettes increases, the BD increases. It also depends on the load applied for briquetting [29]. e proportion of the buffalo dung binder present in the dry sugarcane briquette is 18.12%. e load applied to make a briquette is 9 kN. e BDs of DSL/BD and DSL/CD are higher than that of wheat straw bale briquettes, reported to be 100 kg/m 3 to 120 kg/m 3 [29]. Figure 2 shows that as the load increases, the height of a briquette decreases.

RD or BD of the Briquettes by Geometric Measurements.
is decrease in height reduces the volume of the briquette. erefore, the RD decreases [30]. e volumes of DSL/CD and DSC/BD were found to be 0.00257 m 3 and 0.002629 m 3 , respectively. e RD was found to be low for DSL/CD, 169.40 kg/m 3 , and high for DSL/BD, 174.95 kg/m 3 . e RD for DSL/PM was 171.31 kg/ m 3 . e RDs of DSL/CD, DSL/BD, and DSL/PM were higher than those of cotton stalk, sunflower stalk, and ground nutshell briquettes, reported to be 94.58 kg/m 3 , 111.78 kg/ m 3 , and 90.127 kg/m 3 , respectively [30].

BD of Briquettes Using the Water Displacement
Method.
e BD when using the water displacement method depends on the size and shape of a particulate solid. When a solid is submerged in water, the volume of water displaced is the same as the volume of the solid particle [31,32]. As the volume of DSL/BD was more, the BD when using the water displacement method of DSL/BD had the highest value, whereas the equivalent BDs of DSL/CD, DSL/ BD, and DSL/PM were 3.28 kg/m 3 , 3.46 kg/m 3 , and 1.923 kg/ m 3 , respectively, as shown in Figure 3. A high-quality briquette should have a higher BD when using the water displacement method [33].

DD of the Briquettes.
e DD is the ratio of the difference in the density of a briquette and the raw material to the density of the raw material. To calculate the DD, the BDs of the briquettes and dry sugarcane leaves were used. Figure 4 shows that the DD of DSL/CD was 0.033, that of DSL/BD was 0.1315, and that of DSL/PM was 0.00156. e DD is the bounding ability of biomass, and it depends on the load applied and particle size [25,34]. e highest DD was found to be for DSL/BD.

CR of the Briquettes.
e CR is the ratio of the density of a briquette to the density of the raw material. e BDs of the briquettes and dry sugarcane leaves were considered to calculate the CR. e highest CR of 1.131 was found for DSL/ BD and the lowest CR of 1.0015 was found for DSL/PM; the CR for DSL/CD was 1.033, as shown in Figure 5. As the briquetting load increased, the CR increased in a similar manner to the BD. A high CR is good for packing briquettes. e CRs recorded for the other briquettes were 3.80 for rice husk briquettes and 4.2 for groundnut briquettes [35,36].

STS of the Briquettes.
e STSs of DSL/CD, DSL/BD, and DSL/PM were found to be 7.164 kN/m 2 , 5.59 kN/m 2 , and 6.98 kN/m 2 , respectively, as shown in Figure 6. e cellulosic and hemicellulosic fibres present in the cow dung binder were 1.10% and 13.10%, respectively, higher than those of the buffalo dung and press mud binders. During the compression load, fibres become twisted or entrapped and fold over each other to interlock. is interlocking increases the resistance to the STS test [37]. e STS of the briquettes increased with an increasing binder percentage and dry sugarcane leaf percentage, which itself is a high-density material [38]. With an increasing load during briquette making, the STS of the briquettes increased due to plastic deformation. e load applied to make the briquettes with the cow dung binder was 18 kN, higher than the load used to make the DSL/BD and DSL/PM briquettes. STS may also depend on the physical properties of biomass. High STS was observed for DSL/CD, which is good for transporting and storing briquettes [39].

TR of the Briquettes.
e TR is the resistance to the stress or force of a briquette. Figure 7 shows that the TR for DSL/CD was 87.84%, that for DSL/BD was 84.13%, and that for DSL/PM was 86.66%. e maximum TR was thus for DSL/CD. A high-quality briquette should have a high TR for ease of handling, transportation, and storage. e increase in the TR was due to the binder percentage in the briquettes and application of a high load during briquette making [40]. e percentage of the binder and load applied to make DSL/ CD were 20.55% and 18 kN, higher than those of DSL/BD and DSL/PM.

SR of the Briquettes.
e hardness of the briquette was determined by using the SR test to measure its resistance to impact. e DSL/CD showed some resistance to impact and DSL/BD and DSL/PM disintegrated after the drops, as shown in Table 4. e SR is useful for loading and unloading the briquettes from trucks as well as storing in silos and bins [28]. e increase in the TR is due to the binder percentage in the briquettes and application of a high load during briquette making [41,42]. e percentage of the binder and load applied to make DSL/CD were 20.55% and 18 kN, higher than those of DSL/BD and DSL/PM.

Proximate Analysis of the Briquettes with Different Binders.
e values of the fixed carbon, volatile matter, and ash content of the briquettes depend on the composition of the dry sugarcane leaves and binders. A change was observed by mixing heterogeneous materials [43].

Moisture Content of the Briquettes.
e briquettes were difficult to handle after their removal from the die. ey were sun-dried for one week at a temperature between 305 and 310 K and a humidity between 62% and 69%. After  International Journal of Chemical Engineering drying, the briquettes were easy to handle. e moisture content of the briquettes was observed to be 25.61% for DSL/ CD, 33.89% for DSL/BD, and 6.52% for DSL/PM, as shown in Figure 8. is percentage of moisture should be reduced to less than 18% before combustion to generate the maximum heat [44]. In the briquette-making process, water is a natural binding agent present in binders. is helps develop the van der Waals forces between the particles to bind them together. However, higher moisture content briquettes are difficult to handle. erefore, a suitable moisture content in a briquette is important for easy handling and making the briquette stable. It has been reported that an increase in the calorific value of a briquette can be because of a lower moisture content [45]. e lower moisture content in the briquettes was caused by removing the moisture from the mixture by compression during briquette making [46]. e lowest moisture content was observed to be for DSL/PM.

Ash Content of the Briquettes.
e impurity left after combustion is called ash. e ash content of the briquettes increased by increasing the percentage of the binder in the briquette. A low ash content increases the calorific value of the briquette, ensures suitable thermal and biological conversion, and lowers the corrosion of equipment [47]. e ash content also affects the oxygen diffusion and heat transfer of the briquette [48]. Figure 9 shows that the ash contents of DSL/CD, DSL/BD, and DSL/PM were 10.99%, 9.86%, and 18.88%, respectively. e ash content was found to be low for DSL/BD because the original ash content of the buffalo dung binder was 4.23% lower than that of the cow dung and press mud binders. e binder percentage in the briquettes was 18.12% lower than those of DSL/CD and DSL/PM. e ash contents for DSL/BD and DSL/CD were lower than those of sugarcane leaf and rice straw briquettes, recorded as 12.85% [43].

Fixed Carbon Content of the Briquettes.
e fixed carbon content is the solid fuel (coal) available for combustion after the vaporisation of the volatile matter. A higher value of the fixed carbon content has a positive effect on the calorific value. It adds to heat generation during briquette burning [49]. Figure 10 shows that the fixed carbon content was 2.93% for DSL/CD, 7.96% for DSL/BD, and 6.87% for DSL/PM. e fixed carbon contents of DSL/BD and DSL/ PM were more than that of coconut leaf briquettes, which was found to be 4.72%. is value is encouraging, as it can lengthen the energy release [50].

Volatile Matter Content of the Briquettes.
e volatile matter contents of DSL/CD, DSL/BD, and DSL/PM were found to be 60.47%, 48.29%, and 67.73%, respectively, as shown in Figure 11. is is equivalent to the components of carbon, hydrogen, and oxygen, which can result in easy ignition and increase the flame length. A low volatile matter content results in incomplete combustion, which results in smoke and harmful gas emissions. e volatile matter recorded for rice husk briquettes was 68.20%, that for sawdust charcoal briquettes was 71%, and that for rice straw/sugarcane leaf briquettes was 74.67% [50][51][52]. DSL/CD and DSL/PM met the requirement of the volatile matter content of the briquettes. Most of the briquettes are converted into vapor and burn as gas in the combustion chamber [51]. e maximum volatile matter content was found to be 67.73% in the briquettes with the press mud binder (DSL/PM).

GCV of the Briquettes.
e GCV is the heat generated by combustion when the water produced is allowed to return to the liquid state. e GCV is an important property of highquality briquettes. e GCV depends on the composition and GCV values of the raw material [53] as well as the moisture content of the briquette [45]. At a high compression load, the dry sugarcane leaf briquettes reported good heat content [44]. e maximum GCV (16262.308 kJ/kg) was for DSL/CD. e minimum GCV was found to be 15257.428 kJ/kg for DSL/PM. e GCV of DSL/BD was 16232.999 kJ/kg, as shown in Figure 12. e GCVs of DSL/CD, DSL/BD, and DSL/PM were found to be higher than those of rice husk briquettes, ground nut shell briquettes, cowpea briquettes, and soybean briquettes, which were measured as 15175 kJ/kg, 12600 kJ/kg [54], 14372.93 kJ/kg, and 12953 kJ/kg, respectively [55,56]. e GCVs of DSL/CD, DSL/BD, and DSL/PM are much higher for domestic and industrial applications. e maximum GCV briquette burns without difficulty and is superior to the low GCV [55].

NCV of the Briquettes.
e NCV is the heat generated by combustion when the water produced remains in vapour form. e NCV is an important property of a briquette. It is contingent on its GCV, moisture content, and hydrogen content. Nitrogen, oxygen, and the ash content have less effect on the NCV [53]. A maximum NCV briquette burns without difficulty and is superior to a low NCV [55]. e maximum NCV was found to be 15362.103 kJ/kg for DSL/CD. e minimum NCV was found to be 13473.766 kJ/kg for DSL/BD. e NCV was 13972.019 kJ/kg for DSL/PM, as shown in Figure 13. A high-quality briquette should have a higher NCV.

EDR of the Briquettes.
e EDR is the energy content of a briquette fuel per unit volume to the energy content of the raw biomass per unit volume [25]. To calculate the EDR, the GCV and BD were used. Figure 14 shows that the highest EDR was found to be 0.9296 for DSL/CD and the lowest EDR was found to be 0.8478 for DSL/BD. e EDR was 0.9003 for DSL/PM.

Comparison of DSL/CD, DSL/BD, and DSL/PM for Selecting the Best Binder.
is research aimed to find the best binder for making high-quality dry sugarcane leaf briquettes. Table 5 compares the physical parameters, proximate e GCV and NCV are the main properties of briquettes. e higher the values of the GCV and NCV are, the higher the quality of the briquettes is. e GCV and NCV of DSL/CD were found to be 16262.31 kJ/kg and 15362.1 kJ/kg, respectively, higher than those of DSL/BD and DSL/PM. e STS, TR, SR, and EDR of DSL/CD were found to be 7.164 kN/m 2 , 87.84%, 12.75%, and 0.9296, respectively, higher than those of DSL/BD and DSL/PM. erefore, it can be suggested that cow dung was the better binder for making high-quality dry sugarcane leaf briquettes compared with the buffalo dung and press mud binders.

Conclusions
Dry sugarcane leaves are produced in huge quantities and usually burnt directly in an open atmosphere, creating environmental pollution. Dry sugarcane leaves have a GCV of 16919.667 kJ/kg, which can be converted into briquettes or otherwise be wasted. ese briquettes are a good choice for generating energy for households and industrial applications. From the above results, the following conclusions can be drawn: (1) e proximate analysis and physical properties of the briquettes estimated in this study show that cow dung is a better binder for making high-quality dry sugarcane leaf briquettes compared with the buffalo dung and press mud binders. e dry sugarcane leaf briquettes with the cow dung binder satisfy the main parameters required for high-quality briquettes. e highest values of the GCV, NCV, STS, TR, SR, and EDR were found to be 16262.31 kJ/kg, 15362.1 kJ/kg, 7.164 kN/m 2 , 87.84%, 12.75%, and 0.9296, respectively. (2) We provided evidence that there is no need to add water during briquette making. Briquettes can be made using the moisture naturally present in dry sugarcane leaves and binders. (3) A dry sugarcane leaf briquette has great potential to fulfil demand for energy. (4) Dry sugarcane leaf briquettes can be short-term quick-fix solution for the energy problems faced by India.

Data Availability
e data used to support the findings of this study are included within the article.