Abstract
Municipal solid waste (MSW) in Malaysia contains excessive moisture, which complicates recycling segregation and makes the use of advanced technology, such as solid waste combustion, inappropriate and harmful. Furthermore, MSW pre-treatment to reduce moisture content is uncommon in Malaysia. Biodrying is a cost-effective and environmentally beneficial technology since the fundamental principle relies on internal energy generated by the decomposition of organic waste. The process of biodrying could be a useful alternative for MSW management, allowing for the production of derived fuel. This chapter focuses on the potential of biodrying to reduce excessive moisture content for MSW, particularly in Malaysia. Through nine sub-chapters, this book chapter provides an overview of the fundamentals of solid waste biodrying as well as the potential of solid waste biodrying systems in Malaysia. The first chapter provides a succinct overview of the concerns and challenges of solid waste management in the world and Malaysia. In Chap. 2, a concise explanation of the drying technology is described. The solid waste biodrying treatment system is covered in Chap. 3, followed by the design of the biodrying reactor in Chap. 4. In Chap. 4, there is also a more detailed description of the case study that is being conducted at Universiti Kebangsaan Malaysia. The factors that influence the biodrying process are discussed in Chap. 5. Chapter 6 presents the direct observation of fieldwork at solid waste biodrying plants in Malaysia and abroad. The importance of biodrying from various perspectives is elaborated in Chap. 7, and the potential use of solid waste biodrying in solid waste management in Malaysia is discussed in Chap. 8. Finally, Chap. 9 concludes the importance of a solid waste biodrying system in the future.
Access this chapter
Tax calculation will be finalised at checkout
Purchases are for personal use only
Abbreviations
- ASTM:
-
American Society for Testing and Materials
- EEB:
-
European Environmental Bureau
- GDP:
-
Gross domestic product
- MHLG:
-
Ministry of Housing and Local Government
- MSW:
-
Municipal solid waste
- MYR:
-
Malaysian Ringgit
- NSP:
-
National Strategic Plan
- NSWMD:
-
National Solid Waste Management Department
- PU:
-
Polyurethane
- PVC:
-
Polyvinyl chloride
- RDF:
-
Refuse derived fuel
- SMSW:
-
Synthetic municipal solid waste
- SWCorp:
-
Solid Waste Corporation
- TNB:
-
Tenaga Nasional Berhad
- UKM:
-
Universiti Kebangsaan Malaysia
- WtE:
-
Waste to energy
References
Wilson, D. C., & Velis, C. A. (2015). Waste management—Still a global challenge in the 21st century: An evidence-based call for action. Waste Management & Research, 33, 1049–1051.
Kaza, S., Yao, L., Bhada-Tata, P., & Van Woerden, F. (2018). What A Waste 2.0: A global snapshot of solid waste management to 2050 (urban development series). World Bank.
Map of Peninsular and East Malaysia. Retrieved August 3, 2021, from http://en.wikipedia.org/wiki/Malaysia
The Malay Mail. (2021, March 11). SWCorp data shows trashpile averaged slightly over 200,000 tonnes a month since MCO 1.0, mostly from food and plastics. Retrieved August 20, 2021, from https://www.malaymail.com/news/malaysia/2021/03/11/swcorp-data-shows-trashpile-averaged-slightly-over-200000-tonnes-a-month-si/1956803
World Bank—GDP. (2019b). Retrieved May 5, 2019, from https://data.worldbank.org/indicator/NY.GDP.MKTP.CD
Kathirvale, S., Yunus, M., Sopian, K., & Samsuddin, A. (2004). Energy potential from municipal solid waste in Malaysia. Renewable Energy, 29, 559–567.
Ciuta, S., Apostol, T., & Rusu, V. (2015). Urban and rural MSW stream characterization for separate collection improvement. Sustainability, 7, 916–931.
Rada, E. (2014). Energy from municipal solid waste. WIT Transactions on Ecology and the Environment, 190, 945–958.
Rada, E. (2013). Effects of MSW selective collection on waste-to-energy strategies. WIT Transactions on Ecology and the Environment, 176, 215–223.
Consonni, S., Giugliano, M., Massarutto, A., Ragazzi, M., & Saccani, C. (2011). Material and energy recovery in integrated waste management systems: Project overview and main results. Waste Management, 31, 2057–2065.
Cioranu, S. I., & Badea, A. (2013). Different strategies for MSW management in two Romanian cities: Selective collection versus bio-drying. UPB Scientific Bulletin, Series D, 75, 151–158.
World Bank—Population. (2019a). Retrieved May 5, 2019, from https://data.worldbank.org/indicator/SP.POP.TOTL?locations=MY
SWCorp. (2019). Compendium solid waste Malaysia (2nd ed.). Solid Waste Management and Public Cleaning Corporation (SWCorp) of Ministry of Urban Wellbeing, Housing and Local Government of Malaysia.
Sakawi, Z. (2011). Municipal solid waste management in Malaysia: Solution for sustainable waste management. Journal of Applied Sciences in Environmental Sanitation, 6, 29–38.
SWCorp Malaysia. (2021, May 12). Kadar Kitar Semula Kebangsaan 2020. Retrieved August 10, 2021, from https://www.instagram.com/p/COwor4vsBHZ/?utm_medium=copy_link
Periathamby, A., Hamid, F. S., & Khidzir, K. (2009). Evolution of solid waste management in Malaysia: Impacts and implications of the solid waste bill, 2007. Journal of Material Cycles and Waste Management, 11, 96–103.
Compendium of Environment Statistics, Malaysia 2020. (2020, November 27). Retrieved August 20, 2021, from https://www.dosm.gov.my/v1/index.php?r=column/cthemeByCat&cat=162&bul_id=TjM1ZlFxb3VOakdmMnozVms5dUlKZz09&menu_id=NWVEZGhEVlNMeitaMHNzK2htRU05dz09
Ab Jalil, N., Basri, H., Basri, N. E. A., & Abushammala, M. F. (2015). The potential of biodrying as pre-treatment for municipal solid waste in Malaysia. Journal of Advanced Review on Scientific Research, 7, 1–13.
Michel Devadoss, P. S., Agamuthu, P., Mehran, S. B., et al. (2021). Implications of municipal solid waste management on greenhouse gas emissions in Malaysia and the way forward. Waste Management, 119, 135–144.
Mujumdar, A. S. (2007). An overview of innovation in industrial drying: Current status and R & D needs. In Drying of porous materials (pp. 3–18). Springer.
Ståhl, M., Granström, K., Berghel, J., & Renström, R. (2004). Industrial processes for biomass drying and their effects on the quality properties of wood pellets. Biomass and Bioenergy, 27(6), 621–628.
Bala, B., & Janjai, S. (2012). Solar drying technology: Potentials and developments. In Energy, environment and sustainable development (pp. 69–98). Springer.
Zaman, B., Oktiawan, W., Hadiwidodo, M., Sutrisno, E., & Purwono, P. (2020). Calorific and greenhouse gas emission in municipal solid waste treatment using biodrying. Global Journal of Environmental Science and Management, 7(1), 33–46.
Pirasteh, G., Saidur, R., Rahman, S., & Rahim, N. (2014). A review on development of solar drying applications. Renewable and Sustainable Energy Reviews, 31(133–148).
Sai, P. S. T. (2013). Drying of solids in a rotary dryer. Drying Technology, 31(2), 213–223.
Walton, D. (2000). The morphology of spray-dried particles a qualitative view. Drying Technology, 18(9), 1943–1986.
Patel, A. D., Agrawal, A., & Dave, R. H. (2014). Investigation of the effects of process variables on derived properties of spray dried solid-dispersions using polymer based response surface model and ensemble artificial neural network models. European Journal of Pharmaceutics and Biopharmaceutics, 86(3), 404–417.
Suhimi, N. M., & Mohammad, A. W. (2012). Optimization of the gelatin spray drying process using the surface grease method. Sains Malaysiana, 41(8), 983–991.
Gailin, L., & Nail, S. (1993). Freeze drying: A practical overview. Bioprocess Technology, 18, 317–367.
Jangam, S. V. (2011). An overview of recent developments and some R & D challenges related to drying of foods. Drying Technology, 29(12), 1343–1357.
Naryono, E., & Soemarno, S. (2013). Design of household organic waste sorting, drying and burning systems. The Indonesian Green Technology Journal, 2(1), 27–36.
Cossu, R., & Raga, R. (2008). Test methods for assessing the biological stability of biodegradable waste. Waste Management, 28(2), 381–388.
Ibbetson, C. (2006). UK market development of solid recovered fuel from MBT plants. Regen Fuels.
Pires, A., Martinho, G., & Chang, N.-B. (2011). Solid waste management in European countries: A review of systems analysis techniques. Journal of Environmental Management, 92(4), 1033–1050.
Stegmann, R. (2005). Mechanical biological pretreatment of municipal solid waste. In Proceedings of the Sardinia ’05, International Waste Management and Landfill Symposium.
Adani, F., Baido, D., Calcaterra, E., & Genevini, P. (2002). The influence of biomass temperature on biostabilization–biodrying of municipal solid waste. Bioresource Technology, 83(3), 173–179.
Rada, E. C., Ragazzi, M., & Panaitescu, V. (2009). Msw bio-drying: An alternative way for energy recovery optimization and landfilling minimization. UPB Scientific Bulletin, Series D, 71(4), 113–120.
Sugni, M., Calcaterra, E., & Adani, F. (2005). Biostabilization–biodrying of municipal solid waste by inverting air-flow. Bioresource Technology, 96(12), 1331–1337.
Tambone, F., Scaglia, B., Scotti, S., & Adani, F. (2011). Effects of biodrying process on municipal solid waste properties. Bioresource Technology, 102(16), 7443–7450.
Cai, L., Chen, T.-B., Gao, D., Zheng, G.-D., Liu, H.-T., & Pan, T.-H. (2013). Influence of forced air volume on water evaporation during sewage sludge bio-drying. Water Research, 47(13), 4767–4773.
Zhang, D., He, P., Shao, L., Jin, T., & Han, J. (2008). Biodrying of municipal solid waste with high water content by combined hydrolytic-aerobic technology. Journal of Environmental Sciences, 20(12), 1534–1540.
Negoi, R. M., Ragazzi, M., Apostol, T., Rada, E. C., & Marculescu, C. (2009). Bio-drying of Romanian municipal solid waste: An analysis of its viability. UPB Scientific Bulletin, Series C, 71, 193–204.
Zawadzka, A., Krzystek, L., & Ledakowicz, S. (2009). Autothermal drying of organic fraction of municipal solid waste. Environment Protection Engineering, 35(3), 123–133.
Villegas, M., & Huiliñir, C. (2014). Biodrying of sewage sludge: Kinetics of volatile solids degradation under different initial moisture contents and air-flow rates. Bioresource Technology, 174, 33–41.
Winkler, M.-K., Bennenbroek, M., Horstink, F., Van Loosdrecht, M., & Van De Pol, G.-J. (2013). The biodrying concept: An innovative technology creating energy from sewage sludge. Bioresource Technology, 147, 124–129.
Perazzini, H., Freire, F. B., Freire, F. B., & Freire, J. T. (2016). Thermal treatment of solid wastes using drying technologies: A review. Drying Technology, 34(1), 39–52.
Dufour, P. (2006). Control engineering in drying technology: Review and trends. Drying Technology, 24(7), 889–904.
Jewell, W. J., Dondero, N. C., van Soest, P. J., Cummings, R. T., Vegara, W. W., & Linkenheil, R. (1984). High temperature stabilization and moisture removal from animal wastes for by-product recovery. In Final report for the Cooperative State Research Service. SEA/CR 616–15-168 (p. 169). USDA.
Velis, C., Longhurst, P. J., Drew, G. H., Smith, R., & Pollard, S. J. (2009). Biodrying for mechanical–biological treatment of wastes: A review of process science and engineering. Bioresource Technology, 100(11), 2747–2761.
Frei, K. M., Cameron, D., & Stuart, P. R. (2004). Novel drying process using forced aeration through a porous biomass matrix. Drying Technology, 22(5), 1191–1215.
Nurul Ain Ab Jalil. (2016). Pre-treatment of municipal solid waste in Malaysia using biodrying method. Doctoral Thesis. Universiti Kebangsaan Malaysia.
Park, J. R., & Lee, D. H. (2021). Effect of aeration strategy on moisture removal in bio-drying process with auto-controlled aeration system. Drying Technology, 1–15.
Sadaka, S., VanDevender, K., Costello, T., Sharara, M. (2011). Partial composting for biodrying organic materials. Agricultural and Natural Resources, University of Arkansas.
Tom, A. P., Pawels, R., & Haridas, A. (2016). Biodrying process: A sustainable Technology for Treatment of municipal solid waste with high moisture content. Waste Management, 49, 64–72.
Ngamket, K., Wangyao, K., & Towprayoon, S. (2020). Comparative biodrying performance of municipal solid waste in the reactor under greenhouse and non-greenhouse conditions. Journal of Environmental Treatment Techniques, 9(1), 211–217.
Finstein, M., & Hogan, J. (1993). Integration of composting process microbiology, facility structure and decision-making. Science and Engineering of Composting, 1–23.
Lee, C. C., & Lin, S. (2000). Handbook of environmental engineering calculations. McGraw-Hill Professional.
Yasuhara, A., Amano, Y., & Shibamoto, T. (2010). Investigation of the self heating and spontaneous ignition of refuse-derived fuel (Rdf) during storage. Waste Management, 30(7), 1161–1164.
Garg, A., Smith, R., Hill, D., Longhurst, P., Pollard, S., & Simms, N. (2009). An integrated appraisal of energy recovery options in the United Kingdom using solid recovered fuel derived from municipal solid waste. Waste Management, 29(8), 2289–2297.
Gómez, R. B., Lima, F. V., & Ferrer, A. S. (2006). The use of respiration indices in the composting process: A review. Waste Management & Research, 24(1), 37–47.
Scaglia, B., Acutis, M., & Adani, F. (2011). Precision determination for the dynamic respirometric index (Dri) method used for biological stability evaluation on municipal solid waste and derived products. Waste Management, 31(1), 2–9.
Tiquia, S., & Tam, N. (2000). Fate of nitrogen during composting of chicken litter. Environmental Pollution, 110(3), 535–541.
Tchobanoglous, G., Theisen, H., & Vigil, S. (1993). Integrated solid waste management: Engineering principles and management issues. McGraw-Hill.
Zhu, N., Deng, C., Xiong, Y., & Qian, H. (2004). Performance characteristics of three aeration systems in the swine manure composting. Bioresource Technology, 95(3), 319–326.
Latifah, A., Basri, H., & Basri, N. E. A. (2010). A multi-criteria approach for selecting the best solid waste management technology. Sains Malaysiana, 39(3), 417–422.
Mohamad, S. H., & Jaafar, H. I. (2012). Development of renewable energy resources from an islamic perspective. 3rd National Conference of Fiqh Science and Technology 2012.
Mckendry, P. (2002). Energy production from biomass (part 1): Overview of biomass. Bioresource Technology, 83(1), 37–46.
Zaman, B., Oktiawan, W., Hadiwidodo, M., Sutrisno, E., & Purwono, P. (2021). Calorific and greenhouse gas emission in municipal solid waste treatment using biodrying. Global Journal of Environmental Science and Management, 7(1), 33–46.
United Nations. (2009). Climate change conference, Copenhagen. United Nations.
Hasnah, A., Dody, D., Noraziah, A., Maznah, I., & Sarifah, Y. (2012). Masyarakat Dan Amalan Pengurusan Sisa Pepejal Ke Arah Kelestarian Komuniti: Kes Isi Rumah Wanita Di Bandar Baru Bangi [Community Sustainability and Solid Waste Management Practice: A Case Study of Women Household in Bandar Baru Bangi], Malaysia. GEOGRAFIA Malaysia Journal of Society and Space, 8(54), 64–75.
Wzorek, M. (2021). Solar drying of granulated waste blends for dry biofuel production. Environmental Science and Pollution Research, 28, 34290–34299.
Author information
Authors and Affiliations
Corresponding author
Editor information
Editors and Affiliations
Glossary
- Biodrying
-
Is a pre-treatment method for solid waste that combines biological and mechanical principles. It is a sort of natural biological solid waste treatment that uses internal heat to eliminate moisture. When compared to the use of high-cost, cutting-edge treatment technologies, natural biological treatment is an effective treatment method that is also environmentally friendly. Furthermore, biodrying waste can be used as an energy source. The potential for heat recovery from solid waste is facilitated and improved by biodrying of plants, which creates refuse-derived fuel (RDF) as the major product by eliminating excess moisture.
- Calorific Value
-
Is defined as the amount of heat produced by the complete combustion of a unit volume of a substance. Kilojoule per kilogram (kJ/kg) is the unit of calorific value. It is also known as a parameter used to define the energetic content of materials; it is also known as gross calorific value (GCV) or high heating value (HHV). It is significant because it provides the value of fuel or food in numbers that can be calculated using a formula. Because humans consume fuels and food on a daily basis, it is critical to track their consumption, which is also important in health and financial aspects.
- Composting
-
Is the natural process of microorganism ‘rotting’ or decomposing organic materials under controlled settings. After composting, raw organic materials such as crop residues, animal wastes, food waste, some municipal wastes, and suitable industrial wastes improve their suitability for application to the soil as a fertilising resource. Controlled biological decomposition of organic solid waste materials can occur under aerobic or anaerobic conditions. Composting can be accomplished in windrows, static piles and enclosed vessels.
- Conduction Drying
-
Is a method that heats the air using a heat source, such as an electric heater. Heat is transferred from the heater to the air through physical contact between the two. In an indirect heat-transfer dryer, wet materials are not in direct contact with heating media. A blower or fan is then used to convey the warm air to the drying area. The heat in the air is then used to speed up the drying process, which entails evaporating any water (or other liquid) that remains on the part after it has been cleaned and rinsed.
- Convection Drying
-
Is the use of convective transfer in the drying process. During convective drying, the ambient air is frequently heated. This air will circulate around the damp material. This contact between the heated air and the material results in a heat and mass exchange between the two media.
- Dissolved Air Flotation (DAF)
-
Has recently been understood as one of the most efficient and reliable methods for removing suspended solids (TSS), biochemical oxygen demand (BOD5), fats, oils and grease (FOG), phosphorus (P) and nutrients from wastewaters. Contaminants are eliminated by pumping air under pressure into a recycled stream of clarified DAF effluent to create a dissolved air-in-water solution. In an internal contact chamber, dissolved air escapes from the solution in the form of micron-sized bubbles that adhere to the contaminants, and this recycle stream is combined and mixed with incoming wastewater. Bubbles and contaminants rise to the surface and form a floating bed of material, which a surface skimmer removes into an internal hopper for further processing.
- Dynamic Respiration Index
-
Is used in a respirometer system to determine the current rate of aerobic microbial activity of solid recovered fuels. The current rate of aerobic microbial activity is determined by measuring the oxygen uptake rate by microorganisms to biodegrade easily degradable organic matter in the sample itself under defined continuous airflow and adiabatic conditions.
- Freeze-Drying
-
Is also known as lyophilisation is a water removal process that is commonly used to preserve perishable materials in order to extend their shelf life and/or prepare them for transport. Freeze-drying is the process of freezing a substance, then lowering the pressure and increasing the heat to allow the frozen water to vaporise (sublimate). The three steps of freeze-drying are freezing, primary drying (sublimation) and secondary drying (adsorption). Freeze drying can reduce drying times by up to 30%.
- Green Technology
-
Is the development and usage of products, equipment and systems that help to protect the natural environment and resources while minimising and reducing the negative effects of human activity. It can also refer to clean energy production, which is the use of alternative fuels and technologies that are less destructive to the environment than fossil fuels. Green technology’s goal is to protect the environment, repair past environmental damage, conserve natural resources, and preserve the Earth’s natural resources. Green technology has also grown into a thriving industry that is attracting massive amounts of investment capital.
- Hydrolytic
-
Literally means water reaction. It is a chemical mechanism in which a molecule is broken into two pieces by adding a molecule of water. The most common hydrolytic occurs when a salt containing a weak acid or a weak base (or both) is dissolved in water.
- Perforated Baffle
-
Is typically a straight pipe with a lot of small holes. As a result, vapour condensate can easily pass through this perforation.
- Rotary Dryer
-
Is used to remove excess water from organic materials in order to make them more usable. Rotary dryers elevate materials and circulate them through heated air, allowing moisture to evaporate and making organic materials viable. The feed materials in all rotary dryers pass through a spinning cylinder known as a drum. It is a cylindrical shell made of steel plates that is slightly inclined. In some circumstances, a negative internal pressure (vacuum) is used to prevent dust from escaping.
- Solar Drying
-
Is a system that makes use of solar energy to heat air and dry any substance that is loaded. Solar dryers can be classified as either direct or indirect. The former entails directly exposing the material to sunlight. In the latter, the material is dried by circulating hot air over it without being directly exposed to the sun. The benefits of any solar dryer would be determined by the type and amount of material to be dried.
- Spray Drying
-
Is one of the most energy-intensive drying methods; it is nevertheless necessary for the manufacturing of dairy and food product powders. Spray drying works by atomising the input liquid into small droplets, which are then subjected to a stream of hot air and converted into powder particles. Atomisation is a distinguishing feature of the spray drying process and is crucial in determining the finished product’s quality. It involves creating a large number of droplets from a liquid stream, greatly increasing the liquid’s surface area and allowing for a faster drying rate. A variety of simultaneous heat and mass transfer processes occur when the atomised droplets come into contact with the heated air currents entering the chamber. Heat is transferred to the product in order to evaporate moisture, and mass is transferred to the surrounding gas as a vapour.
- Sun Drying
-
Is the process to leave material outside in the sun and wind for approximately 7–10 days, depending on the temperature and humidity for good dehydration. In terms of drying temperature, the most important thing is to dry the material in bright, sunny and dry weather. The greatest part about sun drying is that it is a low-cost and low-investment process. However, there are a few drawbacks to sun drying; for example, the temperature cannot be controlled and may occasionally become overheated. Furthermore, sun drying is a labour-intensive method that involves a large number of people in the process. Furthermore, the sun drying process is slightly risky due to its reliance on the unpredictability of weather conditions.
- The Bulking Agent
-
Is a carbon-based substance that gives your compost pile structure (or bulk). Wood chips, wood shavings, sawdust, dry leaves, shredded landscape waste, shredded paper, shredded cardboard and animal bedding are all common examples. Inside the compost heap, a good bulking agent provides free air space. This traps air and oxygen, allowing the microorganisms in compost to work without having to introduce extra air on a frequent basis. A good bulking agent is a dry material that effectively balances the high moisture content of the food waste.
- Thermophilic Bacteria
-
Thrive at higher temperatures, while mesophilic bacteria thrive at lower temperatures. This means that thermophilic bacteria thrive at temperatures ranging from 45 to 122 °C, while mesophilic bacteria thrive at temperatures ranging from 20 to 45 °C. Mesophilic bacteria are thought to be the best soil decomposers. In addition, they contribute to food contamination and degradation. Thermophiles can be found in a variety of harsh environments, including direct sunlight-exposed soil, silage, compost heaps, volcanic environments, hot springs, deep-sea hydrothermal vents and so on. Thermophiles include archaea and bacteria. These organisms have strong structures that can withstand high temperatures.
- Waste
-
Is defined as any substance that is discarded after its primary use or that is worthless, defective and useless. The primary aim of waste management is to reduce the harmful effects of hazardous waste on the environment and human health. If waste is harmful or toxic, it could potentially be a source of disease and death, not just for humans, but for everything that supports life, such as water, air, soil and food.
Rights and permissions
Copyright information
© 2022 The Author(s), under exclusive license to Springer Nature Switzerland AG
About this chapter
Cite this chapter
Jalil, N.A. et al. (2022). Biodrying of Municipal Solid Waste: A Case Study in Malaysia. In: Wang, L.K., Wang, MH.S., Hung, YT. (eds) Solid Waste Engineering and Management. Handbook of Environmental Engineering, vol 25. Springer, Cham. https://doi.org/10.1007/978-3-030-96989-9_7
Download citation
DOI: https://doi.org/10.1007/978-3-030-96989-9_7
Published:
Publisher Name: Springer, Cham
Print ISBN: 978-3-030-96988-2
Online ISBN: 978-3-030-96989-9
eBook Packages: EngineeringEngineering (R0)