Factors Influencing Icp, Scp and Energy Efficiency of Fuel Briquettes from Wood Processing Waste from Moramanga District, Alaotra Mangoro Region

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Factors Influencing Icp, Scp and Energy Efficiency of Fuel Briquettes from Wood Processing Waste from Moramanga District, Alaotra Mangoro Region Vol-6 Issue-1 2020 IJARIIE-ISSN(O)-2395-4396 FACTORS INFLUENCING ICP, SCP AND ENERGY EFFICIENCY OF FUEL BRIQUETTES FROM WOOD PROCESSING WASTE FROM MORAMANGA DISTRICT, ALAOTRA MANGORO REGION. I. AZIZ 1, J. L. RASOANAIVO 2, L.LEHIMENA3, A.O.RAVONINJATOVO 4, L. ANDRIANAIVO5, A.A. RATIARISON6 1 Senior lecturer, Physical chemistry Mention, Faculty of Science, Technology and Environment, University of Mahajanga, Madagascar 2Senior research scientist, Unité de Recherches : Biocarburant (bioéthanol, biodiesel), Energy Department, Centre National de Recherches Industrielle et Technologique (CNRIT) Madagascar 3 Senior lecturer, Plant physiology Mention, Faculty of Science, Technology and Environment University of Mahajanga Madagascar 4 Professor, Associate Research Director, Biomass Energy, Energy Department, National Centre for Industrial and Technological Research (CNRIT) Madagascar 5 Full Professor, Ecole Supérieure Polytechnique, University of Antananarivo Madagascar 6 Full Professor, Dynamics of Atmosphere, Climate and Oceans Laboratory (DyACO), Physics and Applications, Sciences and Technologies, University of Antananarivo Madagascar ABSTRACT The Moramanga district has long been known for its wealth of forest resources on the one hand and the existence of the state-owned company FANALAMANGA and several free zone enterprises working in the field of forest exploitation and export on the other. These companies generate a lot of wood processing waste every day: planing shavings, sawdust ... etc. which are left in the open air through the open spaces in the district's chief town. The purpose of this work is on the one hand to valorise these forest wastes for energy purposes by producing combustible briquettes based on planing shavings and sawdust and on the other hand to determine the Lower Calorific Value (LCV) and the Higher Calorific Value (HCV) of these combustible briquettes. The aim of this work is therefore to have an alternative fuel capable of substituting wood energy. Two important parameters were studied: the binder and the fine materials, varying their respective contents. The result of this research work showed that there is a correlation between the binder content and that of the fine materials used. The briquette based on planing chips with 5% binder is the most efficient as it has a high Lower Calorific Value (LCV: 6897.66 kcal/kg, a power of 745.7 W, an efficiency of 39.5% compared to wood energy and other fuel briquettes produced and studied. Keyword: wood processing waste, Moramanga district, energy recovery, fuel briquette, energy efficiency, wood energy. 1. INTRODUCTION Industrial activities generate significant amounts of waste that are both a nuisance to the environment and a loss of recyclable materials, yet they are resources that can still be recovered for various purposes. Their recovery by various biotechnological or technological processes is a solution of choice insofar as it not only contributes to the elimination of environmental pollution, but also makes it possible to produce substances with high added value and bioenergy. 11276 www.ijariie.com 518 Vol-6 Issue-1 2020 IJARIIE-ISSN(O)-2395-4396 The Moramanga district has long been known for its wealth of forest resources and for the existence of the state- owned company FANALAMANGA, which works in the field of forestry, as well as several free zone enterprises working in the field of forest product exports. These companies generate a lot of wood processing waste every day: planing shavings, sawdust, etc. which are left in the open almost everywhere and litter several places in the district's chief town. It is within this framework that the idea of this research work on the theme: "Optimisation of a mixture of organic matter and other mineral matter to make coal briquettes" was born. Several questions arise, among others: - Is it possible to produce environmentally friendly domestic fuel from these planing chips and sawdust in an appropriate mixture? - What is the ideal proportion of fuel briquette produced from these forest wastes? - Are these fuel briquettes based on planing chips and sawdust suitable as a substitute for wood energy? - What type of fuel briquette is most suitable as a substitute for charcoal or firewood? The aim of this research work is to make fuel briquettes based on planing chips and sawdust from a suitable mixture of organic and mineral material. 2. METHODOLOGIES 2.1. Study areas: District of Moramanga The Moramanga district was chosen as the study area because of the importance of forest resources in the area on the one hand and the existence of the state company FANALAMANGA and several free zone companies working in the timber and timber products sector on the other. This section provides information on the geographical characteristics, climate, demographic situation and forestry in the Alaotra Mangoro region. 2.1.1. Geographical location The town of Moramanga is an unavoidable stop on the National Road N°2. It is located in the Middle East region of Madagascar, in the south central part of the Alaotra Mangoro region. The Alaotra Mangoro Region is limited: - In the North-East by the districts of Mandritsara, Port Berge and Befandriana- North: Sofia Region - In the North-West by the District of Tsaratanana : Betsiboka Region - To the West by the Districts of Anjozorobe and Manjakandriana: Analamanga Region - In the South-West by the Districts of Andramasina and Ambatolampy: Analamanga and Vakinankaratra Regions - To the South by the District of Marolambo: Antsinanana Region - To the South-East by the Districts of Tanambao Manampotsy and Vatomandry: Antsinanana Region - To the East by the Districts of Brickaville and Toamasina II: Antsinanana Region - In the North by the Districts of Fenerive EST and Soanierana Ivongo: Analanjirofo Region. The region as a whole represents 41% of the area of the Autonomous Province of Toamasina of which it is part and the 5.21% of the whole island. It is subdivided into two : - the Alaotra including Ambatondrazaka, Amparafaravola and Andilamena. - the Mangoro including Moramanga and Anosibe An'Ala Table 1: geographical location of the town of Moramanga Country Madagascar Region Alaotra Mangoro Province Toamasina District Moramanga Contact details 18°57’ sud, 48°14’ Est Altitude 980 m This table informs the geographical parameters allowing to locate geographically the district of Moramanga 11276 www.ijariie.com 519 Vol-6 Issue-1 2020 IJARIIE-ISSN(O)-2395-4396 Figure 1: Location map of the town of Moramanga 2.1.2. State of forest cover in Madagascar and in the Alaotra Mangoro région : : 2.1.2.1. State of forest cover in Madagascar In reality, it is difficult to evaluate the forest cover according to the results of the National Forest Ecological Inventory (IEFN), based on satellite data in the national forest map on a scale of 1/100,000, Malagasy natural forests cover about 22% of the territory's surface area, i.e. 260,000 ha, of which 265,000 ha are reserved for plantations. The Malagasy forests are characterized by the presence of very varied fauna and flora and their densification estimated at 80% of the total forest which, in fact, is a unique ecological heritage in the world. This heritage is seriously threatened by the accelerated ecological degradation caused by deforestation and subsequent erosion. 2.2. Laboratory work to determine Calorific Value (ICP/SCP): 2.2.1. Determination of the physico-chemical properties of briquettes of sawdust and planing shavings with different binder contents (4%, 5%, 10%) and different fine material compositions Experimental work consists respectively of experimenting with sawdust briquettes and then with planing shavings briquettes. These tests include respectively: - The determination of the physical and chemical characteristics of sawdust and shavings briquettes with different binder and fine material compositions; - The determination of PCI (min, max) and PCS (min, max) of each composition in binder or fine material; 11276 www.ijariie.com 520 Vol-6 Issue-1 2020 IJARIIE-ISSN(O)-2395-4396 - Carrying out the various efficiency tests and the energy efficiency of each composition (binder, fine material) of sawdust and planing chips briquettes; - the evaluation of the efficiency and energy efficiency of sawdust and shavings briquettes of different composition (binder, fine) in relation to an improved furnace with a well-defined yield; 2.2.1.1. Determination of the physicochemical characteristics of sawdust and planning chip briquettes In order to determine the physico-chemical characteristics of sawdust briquettes and planning chips, our approach consists in calculating for each wood briquette and planning chip respectively: - the moisture content (H); - the ash content (Ce); - the volatile matter (Vm) content; - and by deduction the fixed carbon content (F.C). - the calculation of the Lower Calorific Value (LCV) and the PCS Our objective is to know the physicochemical characteristics of these briquettes in order to be able to dictate on the quality of the briquettes: a good fuel or not. a) Humidity (H): Dry the container in an oven at 105°C and cool in the desiccator, then weigh. 20g (weighed to the nearest 0.1 mg) of briquettes (sawdust, shavings) are placed in a tare box previously dried at 105°C, cooled and weighed. Spread the briquette (sawdust, shavings) evenly in the container, and place it in the oven heated to 105°C for 1 h to 1.5 h. Remove and place in the desiccator for 30 min and weigh to the nearest 0.1 mg. Calculation of the humidity from the loss of mass in relation to the initial mass. b) Volatile matter (VMI): Determine the volatile matter index or VMI, which is the percentage loss in mass, obtained under standard conditions, after pyrolysis heated in the absence of air, excluding the loss in mass due to evaporation at 550°C. c) Ash content (C): Combustion of a test sample in a muffle furnace at 850°C. The ash content is the amount of residue, relative to the mass of the test sample.
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