Design, construction and experimental evaluation of the products of a low cost briquette machine for rural communities in nigeria
Table Of Contents
- TITLE PAGE . . . . . . . . ii
DECLARAION . . . . . . . . iii
CERTIFICATION . . . . . . . . iv
DEDICATION . . . . . . . . v
ACKNOWLEDGEMENT . . . . . . . vi
NOMENCLATURE . . . . . . . . viii
ABSTRACT . . . . . . . . . xii
TABLE OF CONTENTS . . . . . . . xiii
Chapter ONE
INTRODUCTION
- 1.0Introduction . . . . . . . . 1
- 1.1Problem Statement . . . . . . . 2
- 1.2Agricultural and wood Residues . . . . . 3
1.
- 2.1Particle board and straw board production . . . . 4
1.
- 2.2Biogas production by anaerobic decay of organic materials . . 4
1.
- 2.3Gasification . . . . . . . . 5
1.
- 2.4Biomass Combustion . . . . . . . 6
1.
- 2.5Briquetting . . . . . . . . 7
1.
- 2.6Ruminant Feeding . . . . . . . 7
1.
- 2.7Construction of village level grain storage structure . . . 7
1.
- 2.8Regulation and reduction of geothermal temperature . . 8
- 1.3Justification of Research . . . . . . 8
- 1.4Existing Briquetting Techniques . . . . . 10
xiv
1.
- 4.1Wu-Presser . . . . . . . . 10
1.
- 4.2Earth Rams . . . . . . . . 10
1.
- 4.3Tube-Presses . . . . . . . . 11
1.
- 4.4Screw Presser . . . . . . . . 12
1.
- 4.5Hydraulic Press . . . . . . . 12
1.
- 4.6Piston Press . . . . . . . . 13
1.
- 4.7Pelletizer . . . . . . . . 13
1.
- 4.8Heat Die Extrusion Screw Press . . . . . 14
- 1.5Objectives of study . . . . . . . 15
Chapter TWO
LITERATURE REVIEW
- 2.0Literature Review . . . . . . . 16
- 2.1Research and Development Efforts in the Use of Agricultural Residues
as Energy Source for Cooking Purpose Using Low Cost Technique . 16
- 2.2Review of Previous Research Work on Briquette making Raw Materials 22
- 2.3Review of Previous Research Work on Residue Energy Potential . 24
- 2.4Review of Previous Studies on Binding of Briquettes . . 25
- 2.5Review of Research Work on Calorific Values of Some Briquettes . 27
Chapter THREE
SYSTEM DESIGN AND IMPLEMENTATION
- 3.0Machine Design and Construction Processes. . . . 30
- 3.1Material . . . . . . . . 30
- 3.2Design Considerations . . . . . . 30
- 3.3Description of Parts and Functions . . . . . 31
3.
- 3.1The Main Frame and Mould . . . . . . 31
xv
3.3.
- 1.1Function . . . . . . . . 31
3.
- 3.2The Base Ram. . . . . . . . 32
3.3.
- 2.1Function . . . . . . . . 32
3.
- 3.3The Connecting Link Mechanism and Power Screw . . . 32
3.3.
- 3.1Function . . . . . . . . 32
- 3.4Design Analysis . . . . . . . 32
3.
- 4.1The Handle . . . . . . . . 32
3.
- 4.2The Thread Shaft (Square Thread) . . . . . 33
3.
- 4.3Bearings . . . . . . . . 35
3.
- 4.4Nut . . . . . . . . . 36
3.
- 4.5The Cover Plate . . . . . . . 36
3.
- 4.6Coupling Bolt for Installation . . . . . . 37
- 3.5Design Calculations . . . . . . . 38
- 3.6Construction of Machine . . . . . . 45
- 3.7Pallets (Aluminum Foil) . . . . . . 50
- 3.8Coupling of Components . . . . . . 50
- 3.9Method of Operating the Briquette Press . . . . 51
3.
- 9.1Filling Mould with Material . . . . . . 51
3.
- 9.2Compression Stroke . . . . . . . 52
3.
- 9.3Ejection Stroke . . . . . . . 52
3.
- 9.4Maintenance and Repair . . . . . . 53
- 3.10Briquette Production . . . . . . . 53
3.
- 10.1Material . . . . . . . . 53
3.
- 10.2The Binder: Cassava Flour . . . . . 53
xvi
3.
- 10.3Preparation and Production of Briquettes from Residues . . 54
Chapter FOUR
SYSTEM TESTING AND EVALUATION
- 4.0Tests and Results . . . . . . . 56
- 4.1Tests . . . . . . . . . 56
- 4.2Determination of Calorific Value . . . . . 56
4.
- 2.1Equipments used for the Calorific value test . . . . 56
4.
- 2.2Test Procedure Carried Out . . . . . . 56
- 4.3The Water Boiling Test (WBT) . . . . . 59
4.
- 3.1Introduction . . . . . . . . 59
4.
- 3.2Equipments used in the Boiling Water Test . . . . 60
4.
- 3.3Variables . . . . . . . . 60
4.3.
- 3.1Fuel Samples . . . . . . . . 60
4.3.
- 3.2Stove . . . . . . . . . 61
4.3.
- 3.3Pot . . . . . . . . . 61
4.3.
- 3.4Lid . . . . . . . . . 61
4.3.
- 3.5Power Control . . . . . . . . 62
4.3.
- 3.6Environment . . . . . . . . 62
4.
- 4.Experimental Phases Process . . . . . . 62
4.
- 4.1Phase 1: High Power (Cold start) . . . . . 62
4.
- 4.2Phase 2: High Power (Hot start) . . . . . 63
4.
- 4.3Phase 3: Low Power (Simmering) . . . . . 64
- 4.5Analysis . . . . . . . . 64
4.
- 5.1Definition of terms . . . . . . . 64
xvii
4.
- 5.2Statistical Analysis . . . . . . . 65
4.
- 5.3Analysis of Variance (ANOVA) . . . . . 66
- 4.6Calorific value of fuel samples . . . . . 67
4.
- 6.1Average Thermal Efficiency (ï¨ in %) for Fuel Samples . . 68
4.
- 6.2Average Burning Rate for Fuel Samples . . . . 68
4.
- 6.3Average Specific Consumption for Fuel samples . . . 69
4.
- 6.4Boiling Time . . . . . . . . 70
Chapter FIVE
SUMMARY, CONCLUSION AND RECOMMENDATIONS
- 5.0Discussion of Results . . . . . . . 75
- 5.1Introduction . . . . . . . . 75
- 5.2Performance of the Briquetting Screw Press . . . . 75
- 5.3Performance of Fuel Samples . . . . . . 76
5.
- 3.1Rice Straw Briquettes . . . . . . . 76
5.
- 3.2Rice Husk Briquettes . . . . . . . 77
5.
- 3.3Saw Dust Briquettes . . . . . . . 78
5.
- 3.450% Rice Husk + 50%Saw Dust Briquettes . . . . 79
CHAPTER SIX
- 6.0Summary, Conclusion and Recommendation. . . . 81
- 6.1Summary . . . . . . . . 81
- 6.2Conclusion . . . . . . . . 82
- 6.3Recommendation . . . . . . . 83
REFERENCES . . . . . . . . 84
APPENDICES . . . . . . . . 88
WORKING DRAWINGS . . . . . . . 114
xviii
Thesis Abstract
The decreasing availability of fuel wood, coupled with the ever rising prices of kerosene
and cooking gas in Nigeria draws attention to consider alternative sources of energy for
domestic and cottage level industrial use in the country. This research work was conducted
to design and construct a low cost briquette machine for rural communities in Nigeria. It
involved the modification of the existing CINVA RAM press and evaluation of the
products produced. Selected agricultural residues (i.e. rice straw and rice husk), saw dust
residue of softwood and a combination of 50% rice husk + 50% saw dust by weight with
30% optimum cassava starch by weight as binder were used to produce briquettes.
Performance characteristics were evaluated for the briquettes produced based on average
fuel efficiency, burning rate and specific fuel consumption. Calorific value of 16,577KJ/Kg
was obtained for rice straw briquette, 14,396KJ/Kg for rice husk briquette, 15,547KJ/Kg
for sawdust briquette, 17,529KJ/Kg for 50% rice husk + 50% saw dust briquette and
12,378KJ/Kg for firewood (Parkia biglobosa). The average fuel efficiency, burning rate
and specific fuel consumption values of 10.68%, 1.10Kg/hr, 0.3g/g, 22.42%, 0.83Kg/hr,
0.13g/g, 15.40%, 1.03Kg/hr, 0.26g/g, 18.52%, 0.93Kg/hr, 0.16g/g and 12.29%, 1.62Kg/hr,
0.36g/g were obtained for rice straw briquette, rice husk briquette, saw dust briquette, 50%
rice husk + 50% saw dust briquette and firewood respectively. Statistical analysis using the
least square differences in comparison to each of the fuel samples average performances
showed that rice husk briquette had the most outstanding thermal performance.
Thesis Overview
<p>
</p><p>INTRODUCTION<br>Approximately 2000 million people world wide; most rural people and many urban<br>as well, all depend on wood fuels as their main or sole source of energy to cook their food<br>and keep warm. Nine-tenths of all the wood harvested annually is used for energy; “it<br>accounts for over two-thirds of total energy consumption in 24 tropical countries of which<br>16 are least-developed countries” (Rodas, 1981).<br>The demand for fuel wood is expected to have risen to about 213.4×103 metric<br>tones, while the supply would have decreased to about 28.4×103 metric tones by the year<br>2030 (Adegbulugbe, 1994).<br>In Nigeria, the Energy Commission of Nigeria (ECN) recently (2005) reported that<br>Nigeria’s fossil led economy is under severe pressure and gave data of potential renewable<br>energy for utilization including crop residue as shown in table 1.1 below.<br>Table 1.1: Nigeria’s renewable energy resources<br>Energy Source Capacity<br>Hydropower, large scale 10,000MW<br>Hydropower, small scale 734MW<br>Fuel wood 13,071,464 hectares (forest land)<br>Animal waste 61 million tones/yr<br>Crop Residue 83 million tones/yr<br>Solar Radiation 3.5 – 7.0 kW/m2-day<br>Wind 2-4 m/s (annual average)<br>Source: ECN (2005)<br>2<br>1.1 Statement of Problem<br>As wood fuel supplies diminish, the people who depend on wood fuels are<br>suffering increase in physical or economic burdens in maintaining even a minimal daily<br>fuel supply. The use of firewood and misuse of the existing energy resources (agricultural<br>residues) is creating human and environmental crisis in developing countries which is<br>resulting in deforestation. Traditionally, wood in form of fuel wood, twigs and charcoal<br>has been the major source of renewable in Nigeria, accounting for about 51% of the total<br>annual energy consumption; the other sources of energy include natural gas (5.2%),<br>hydroelectricity (3.1%), and petroleum products (41.3%) (Akinbami, 2001).<br>In many developed and developing countries, the forest covers at least 25% of the<br>total land area, the minimum level required by international standard. The first indicative<br>forest inventory project completed in Nigeria in 1977 put reserved forest at approximately<br>10% of the total land area. Between 1976 and 1990, deforestation proceeded at an average<br>rate of 400,000 ha. per annum, in 1981-1985 at 3.48% while in 1986-1990 it was 3.57%<br>including some forest reserves. The FAO concluded that if this rate was maintained, the<br>remaining forest in Nigeria would disappear by the year 2020. The degradation and<br>depletion of the forest reserve base has major effects on other sectors of the economy. The<br>disappearance of forest cover leads to erosion, soil degradation and unfavorable<br>hydrological changes (Government of Nigeria, 1997).<br>The decreasing availability of fuel wood, coupled with the ever rising prices of<br>kerosene and cooking gas in Nigeria, draw attention to the need to consider alternative<br>sources of energy for domestic and cottage level industrial use in the country<br>(Olorunnisola, 2007). Such energy sources should be renewable and should be accessible<br>3<br>to the poor. As rightly noted by Stout and Best (2001), a transition to a sustainable energy<br>system is urgently needed in the developing countries such as Nigeria. This should, of<br>necessity, be characterized by a departure from the present subsistence energy level usage<br>which is based on decreasing firewood resources, to a situation where human and farming<br>activities would be based on sustainable and diversified energy forms.<br>The realization that deforestation and wood fuel shortages are likely to become<br>pressing problems in many countries has turned attention to other types of biomass fuel.<br>Agricultural residues are, in principle, one of the most important of these. They arise in<br>large volumes and in the rural areas which are often subject to some of the worst pressures<br>of wood shortage (Eriksson and Prior 1990). If one or more efficient method of using the<br>abundant agricultural and wood residues could be developed on a large scale the energy<br>situation could be sustainable and the deforestation problem could be controlled.<br>The lack of capital among most house holds in the rural communities makes it<br>difficult to move from either firewood or charcoal, to a more advanced energy sources<br>where small initial capital investment can be used. Hence, the substitute of these fuels<br>requires a minimal capital investment, be as cheap and accessible as charcoal and<br>firewood. At the same time be environmentally sustainable.<br>1.2 Agricultural and wood residues<br>Large quantities of agricultural and wood residues are generated yearly in<br>developing countries but they are neither managed nor utilized efficiently. Agricultural<br>residues which are freely available are often discarded or burned as wastes. They occur in<br>large amounts and have the potential to be an important industrial input for fuel production<br>in briquette forms, particle board and straw board for furniture making, biogas fuel,<br>4<br>gasification, biomass combustion, ruminant feeding, absorbent for industrial effluents<br>treatment, grain storage structure and regulation/reduction of geothermal temperature.<br>The procedures for manufacturing these products are described briefly below;<br>1.2.1 Particle board and straw board production.<br>Wood residues resulting from furniture making industries or stalks like cotton<br>stalks after harvesting cotton are either grounded into particles for particle board or steam<br>heated to breakdown the residues into fibers for medium density fiberboard, then dried to<br>lower moisture content. After the fiber is dried, it is blended with wax, a synthetic resin<br>such as urea formaldehyde, and other addictives, and formed into mats. The mats are<br>processed in large presses that use heat and pressure to cure the resin and form the products<br>into sheets or boards. Primary finishing steps of particle and medium density fiber board<br>include cooling or hot stacking, grinding, trimming/cutting and sanding. Secondary steps<br>include fooling, painting, laminating and edge finishing. Straw boards are made from straw<br>and bagasses, which undergo the same production procedure as particle board production.<br>They are used for making doors, furniture and cabinets (Gary and Rajiva, 2001).<br>1.2.2 Biogas production by anaerobic decay of organic materials.<br>Anaerobic reactors are generally used for the production of methane biogas, from<br>manure (human and animal waste) and agricultural residues. They utilize mixed<br>methanogenic bacterial cultures which are characterized by defined optimal temperature<br>ranges for growth. These mixed cultures allow digesters to be operated over a wide range<br>i.e. above 0oC up to 60oC. When functioning well, the bacteria convert about 90% of the<br>feedstock energy content into biogas containing about 55% methane, which is a readily<br>5<br>useable energy source for cooking and lighting. Fig.1 below shows the route path of biogas<br>energy production.<br>Figure 1: Biogas energy route Source: Elizabeth, et al, (1999)<br>1.2.3 Gasification.<br>Gasification is the process involving the burning of biomass fuels (human, animal<br>and agricultural wastes) at very high temperatures with a limited supply of oxygen so that<br>the burning process is only partially completed (Elizabeth et al, 1999). High temperatures<br>and a controlled environment lead to virtually all the raw materials being converted to gas.<br>This takes place in two stages. In the first stage, the biomass is partially combusted to form<br>producer gas and charcoal. In the second stage, the carbon dioxide (CO2) and water (H2O)<br>produced in the first stage is chemically reduced by the charcoal, forming carbon<br>monoxide (CO) and hydrogen (H2). The composition of the gas is 18% to 20% H2 gas<br>equal portion of CO, 2% to 3% methane (CH4), 8% to 10% CO2 and the rest nitrogen.<br>These stages are spatially in the gasifiers. Gasifiers require temperature of about 800oC and<br>is carried out in closed-top or open top gasifiers. These gasifiers can be operated at<br>Anaerobic<br>Digestion<br>Methane<br>Digester Sludge Heating and<br>lighting<br>Manure/Soil Mechanical power<br>Conditioner<br>Animal waste<br>Human/municipal<br>wastes<br>Agricultural or<br>crop wastes<br>Industrial<br>Carbonaceous<br>waste<br>Electrical power<br>6<br>atmospheric pressure or higher. The producer gas can be burned directly in processes<br>which normally use oil fired boilers. It can be burned in ovens, kilns and driers to replace<br>fuels otherwise, used in this equipment. The gas can also be cleaned and used to run an<br>engine for generating electricity.<br>Figure 2: Gasification process. Source: Vannbush, (2006)<br>1.2.4 Biomass Combustion.<br>Biomass fuel (agricultural residue) is burned in a furnace or boiler. The heat is used<br>to produce high pressure steam. This steam is introduced into a steam turbine where it<br>flows over a series of aerodynamic turbine blades, causing the turbine to rotate. The<br>turbine shares a common shaft with an electric generator so as the steam flows it causes the<br>turbine to rotate, the electric generator is turned and electricity is produced. Also it can be<br>used to produce hot water for goods processing.<br>7<br>1.2.5 Briquetting.<br>This involves the densification process of loose organic materials, such as rice<br>husk, sawdust and coffee husk aiming at improving handling and combustion<br>characteristics. There are two principal methods of briquetting, with or without a binder.<br>The binder technology is used where low pressure presses are employed to produce<br>briquette. Binders are added to this process to improve mechanical strength and also allow<br>dry materials to be briquetted using low pressure techniques as simple block presses or<br>extrusion presses. The binderless technology is a high pressure technique which produces<br>briquettes from fine dry particle size materials without a binder being added. Three types<br>of press are commonly used. Piston press, pelletizers and screw extrusion presses.<br>Briquettes are burned the same way as wood and can be used directly in open fires,<br>gasifiers, boilers, furnaces and kilns.<br>1.2.6 Ruminant Feeding.<br>Fibrous agricultural residues such as rice straw, sugarcane tops, cassava leaf,<br>soyabean-straw, peanut vines and sweet potato vines are important component of the feed<br>base for ruminant livestock particularly in areas where land grazing is limited and pasture<br>growth is seasonal (Dixon, 1985).<br>1.2.7 Construction of village level grain storage structure.<br>Agricultural residues could be used to construct village level grain storage<br>structure, called rhumbu which may be thatched, mud or underground pit. Thatched<br>rhumbus are commonly found in the north-Eastern parts of Nigeria. They are cylindrical in<br>shape with floors made of wooden grass stems or fibers and overhanging conical roof<br>made with straws or grass. The structure normally is supported on low wooden structure or<br>8<br>by stones. The wall is provided with tension rings in two or three positions using local rope<br>material. Mud rhumbus are found in Zaria and Sokoto towns in Nigeria. They are circular<br>in cross section and supported on stone pieces or pillars which are about 25-50cm above<br>the ground. The floor is made of wood and plastered with mud; the roof is conical and<br>made of thatch. Underground pits are found in the Sahel part of the Sudan savanna Zone<br>where water table is low. The pit is either round or square is 2-3m deep and 1.5-3m in<br>diameter or square. The pit is lined with straw mat (Zare) with corn husk padding or<br>insulation is provided at the bottom of the pit, it is covered with a polyethylene or metal<br>sheet, then a layer of husk and finally with layers of laterite (Olumeko and Igbeka, 1996).<br>1.2.8 Regulation and reduction of geothermal temperature.<br>In animal structures agricultural residues such as groundnut shells, maize husk or<br>sawdust of 6mm particles are spread on the floors of poultry houses, horse stables and<br>goat/sheep pens to serve as an absorbent material to keep the structure dry and the animals<br>away from cold floors.<br>1.3 Justification of Research<br>The abundantly available agricultural and wood residues can efficiently be used for<br>resolving energy problems to a significant extent by adopting proper measures.<br>Olorunnisola (2002) states that of the various types of biomass processing technologies<br>that are being considered, and for which there are currently potentially viable local markets<br>for in the country, which include biomass combustion, gasification and<br>briquetting/pelletizing it is evident that none of these alternatives can compete with the low<br>capital investment that is required; with the briquetting technology. Several kinds of<br>agricultural residues can be utilized properly by densifying loose residues to produce a<br>9<br>compact product of different sizes. Briquetting is essentially a mechanical process<br>requiring investment in equipment and training to ensure a product of reasonable quality<br>that will perform the task for which it is intended. Russell, (1997) considered that<br>briquetting is often seen as a relatively high-cost high-pressure technology, and that it is<br>possible to use a low-cost low-pressure technique to produce acceptable briquettes.<br>For rural communities the most suitable briquetting methods are those which are based<br>on available waste and building materials. The manufacturing should be done in locally<br>made hand operated presses and the briquettes held together mainly by a binder.<br>ï‚· Briquette making saves trees and prevents problems like soil erosion and<br>desertification by providing an alternative to burning wood for heating and<br>cooking.<br>ï‚· Briquetting substitutes agricultural waste like hulls, husk, corn stocks, grass, leaves<br>and other garbages for a valuable resource.<br>ï‚· Briquetting engenders many micro enterprise opportunities making the presses<br>from locally available materials, supplying materials, supplying materials and<br>making the briquettes, selling and delivering the briquettes.<br>ï‚· The availability of briquette as an alternative fuel to replace firewood can also<br>improve the living conditions of the rural women and children, who spend most of<br>their time collecting firewood instead of engaging in other income generating<br>activities or attending school.<br>10<br>1.4 Existing Briquetting Techniques<br>1.4.1 Wu-Presser<br>The Wu-presser was developed by the Washington University. It is constructed<br>from either metal or wooden parts as shown in figure 3 below.<br>Figure 3: The Wu-presser Source: Legacy Foundation (2003)<br>The Wu-presser presses briquettes in three steps shown in the illustration above. Each step<br>will press with increasing pressure. This takes advantage of the non-linear force to distance<br>property of briquetting pressing.<br>1.4.2 Earth Rams<br>Presses currently in use for making stabilized earth blocks might be modified to<br>make briquettes. The Combustaram, similar to the CINVA-Ram and Tersaram, is<br>commercially available or can be manufactured locally, see figure 4 below. The lever arm<br>is put in the open position, feed stock is poured into the molds and the lever is then quickly<br>pushed up, over the top of the press, and down. This movement positions the lever over the<br>top of the press and compresses the briquettes on the downward stroke.<br>11<br>Figure 4: Combustaram Source: Davies (1985)<br>The lever is then moved back to the original position and again pushed down, thus forcing<br>the briquettes out of the molds. Finished briquettes are set in the sun to dry. The process<br>requires at least two workers.<br>1.4.3 Tube-Presses<br>Metal or plastic pipe provides a good briquetting mould since it produces<br>cylindrical briquettes. The tube press, illustration shown in Figure 5 below,<br>Figure 5: Tube Press Source: Davies (1985)<br>Moulding Box<br>Roller Fulcrum<br>for Ejection<br>Adjustable piston<br>guide<br>Handle Latch<br>Toggle Linkage<br>Tube with<br>feed stock<br>Press<br>Removable Base<br>Plate<br>Hole to<br>push<br>finished<br>briquette<br>through<br>Close fitting ram<br>for hand<br>compression<br>Tube partially<br>filled with<br>briquetting<br>feedstock<br>Frame<br>Piston<br>12<br>consist of a tube mounted vertically on a platform and a close fitting ram used for<br>compaction. The basic design can be varied considerably, as the figure indicates. Feed<br>stock is poured into the tube and compressed with the ram. The tube is then positioned<br>over a hole (or a slide is removed) below the tube exposing a hole and the briquette is<br>pushed through. Briquettes are then dried in the sun before storage and use.<br>1.4.4 Screw Presser<br>The screw presser makes briquettes in upright cylinders. The raw material is<br>compressed by lowering a metal disc which is moved vertically by a screw that is turned<br>by hand. The screw press is most commonly made of metal as shown in figure 6 below.<br>Figure 6: Screw presser in use. Source: Olle and Olof (2006)<br>1.4.5 Hydraulic Press<br>These machines operate by hydraulic pressure acting upon a piston that extrudes<br>the material through a longitudinal die. The machine operates rather slowly which<br>minimizes the wave rates. However, they operate at much lower pressures and the<br>briquette quality is of lower density. They are typically used for low outputs of 40kg/hr but<br>can be made to achieve up to 80kg/hr.<br>13<br>1.4.6 Piston Press<br>These machine works best with dry (15% moisture content maximum) cellulose<br>material, which is fed into a compression chamber. A reciprocating piston then forces the<br>material through a tapered die to form a long briquette as shown in figure 7 below.<br>Typically flywheel drive machines produce between 300kg and 500kg of briquettes per<br>hour.<br>Figure 7: Piston Press Source: Bhattacharya et al, (1984)<br>The machine can achieve a service life of between 500 hours and 1000 hours using<br>relatively clean material such as sawdust. Use of agricultural wastes containing high levels<br>of silica (sand) will reduce the operating hours considerably. The initial cost of this type of<br>machine is high and the briquettes are prone to breaking.<br>1.4.7 Pelletizer<br>Pellet presses have dies with small diameter (usually about 30mm). The machine<br>has a number of dies arranged as holes bored in a thick steel disk or ring. The material is<br>forced into the dies by means of a ram, perpendicular to the centerline of the dies. The<br>14<br>main force applied results in shear stresses in the material which often is favorable to the<br>final quality of the material. The pellets are cut to lengths normally about one or two times<br>the diameter (Eriksson and Prior, 1990). Pelletizers can produce up to 1000kg of pellets<br>per hour but require high initial capital investment and high energy input.<br>1.4.8 Heat Die Extrusion Screw Press<br>The heat die extrusion screw press is an industrial machine for producing briquettes<br>(see figure 8 below). It consists basically of an electric motor, a hopper, a die heater and<br>muff, and the screw which densifies the raw material.<br>Figure 8: Heated die extrusion screw press Source: Bhattacharya et al, 1984<br>The electric motor drives the briquetting screw, which is housed inside the die,<br>through a V-belt and pulley arrangement. Biomass raw material is fed to the screw through<br>the hopper. The electric die-heater softens the lignin in the raw material as it passes<br>through the die which acts as a binding material. A smoke trapping system traps and<br>removes the smoke from the vicinity during the briquetting process. Besides the cost of the<br>Electric Motor<br>Die Heater<br>Hopper<br>Muff<br>15<br>investment, the machine has a cost for the electricity consumed. Another cost is the screw<br>that gets worn and has to be replaced frequently.<br>1.5 Objectives of study<br>The objective of this project is to:<br>ï‚· Design and construct a simple, low cost briquette machine which can be used in<br>rural communities.<br>ï‚· Test the design briquette machine using selected agricultural residues (sawdust, rice<br>husk, rice straw) with cassava starch as binder.<br>ï‚· Evaluate the calorific value of briquetted residues.<br>ï‚· Compare calorific value and performance with firewood.<br>16</p><p><b>GET TH</b></p>
<br><p></p>