Food Waste Malaysia

September 12, 2017 | Author: Ayesha Ralliya | Category: Municipal Solid Waste, Waste, Waste Management, Recycling, Compost
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Food Waste Management in Malaysia: P a g e | 36

An International Journal J. Ind. Res. & Technology 2(1), 36-39, 2012 HATAM Publishers

Journal of Industrial Research & Technology (ISSN 2229-9467)

Journal homepage: http://www.hgpub.com/index.php/jirt

Food Waste Management in Malaysia- Current situation and future management options Azlina Abdul Hamid*,1, Anees Ahmad2, Mahamad Hakimi Ibrahim 1, Nik Norulaini Nik Abdul Rahman3 1

Division of Environmental Technology, School of Industrial Technology, Universiti Sains Malaysia, 11800 Penang, Malaysia. 2 Division of Analytical and Environmental Chemistry, Department of Chemistry, A.M.U. Aligarh, 202002, India. 3 Division of Biology, School of Distance Education, Universiti Sains Malaysia, 11800 Penang, Malaysia. *Corresponding author, Phone:+60-102060336, Fax: 60-4-6573678, E-mail: [email protected]

ARTICLE INFORMATION Article history Received January 10, 2012 Revised February 20, 2012 Accepted March 05, 2012 Available online April 30, 2012

Keywords Food waste; Management; Municipal solid waste; Waste prevention; Food waste composition

1.

ABSTRACT The high amount of food waste generated is the main cause to most issues related to landfills such as foul odor, toxic leachate, emission of greenhouse gases and vermin infestation. Although food waste issue is as critical as municipal solid waste issue, the condition is such that municipal solid waste management systems in Malaysia are also very poorly conducted. Thus, the aim of this paper is to discuss the possible options of food waste management systems that are suitable for implementation in Malaysia.

Introduction The problem of food waste (FW) is a global issue nowadays and even the developed countries are much concerned to find its appropriate management solution along with the municipal solid waste (MSW). Countries such as Korea and Japan separate FW from MSW due to food waste degradation, insufficient areas for landfills, problems with transportation of FW to disposal sites and problems arising from landfill and incineration (Kim and Kim, 2010). Malaysia on the other hand, is trying its best to solve the basic problem of municipal solid waste management only and finding the most environmentally friendly solutions which are acceptable by the public. The FW is treated as part of MSW and a separate FW management system does not exist in Malaysia. Thus together with efforts to solve MSW issues, Malaysia should also consider finding solutions for FW matter as

© 2011 HATAM: Publishers. All rights Reserved. MSW is highly related to FW as it constitutes approximately 60% of MSW (Kathrivale, et al. 2003, Saeed, et al. 2009, Hassan, et al. 2001). In 2005, municipal solid waste generated was 7.34 million tons and is predicted to increase to 10.9 million tons in 2020 (Alias, 2010). Food waste content is about 60% of the MSW, thus the estimated amount of food waste generated in 2005 is 4.404 million tons and is estimated to increase to 6.54 million tons in 2020. The high amount of food waste generated is the main cause to most issues related to landfills such as foul odor, toxic leachate, emission of greenhouse gases and vermin infestation (Lee, et al. 2007). Although food waste issue is as critical as municipal solid waste issue, the condition is such that municipal solid waste management systems in Malaysia are also very poorly conducted (Hassan, et al. 1999). Thus, the aim of this paper is to discuss the possible options

Journal of Industrial Research & Technology, Volume 2, Issue 1, April 2012

Food Waste Management in Malaysia: P a g e | 37 of food waste management systems that are suitable for implementation in Malaysia.

Waste Prevention

2. Current food waste situation in Malaysia Municipal solid waste generated daily in Malaysia range from 0.8-0.9 kg per household in general and about 1.62 kg per household in densely populated cities such as Kuala Lumpur with food waste constituting approximately 60% of the total solid waste (Saeed, et al. 2009, Kathrivale, et al. 2003). Kathrivale, et al. (2003) also stated that 8590% of total solid waste are organic wastes. Table 1 shows the composition of Malaysian food waste.

Reuse Recycling Recovery Safe Disposal Figure 1 : Hierarchy of waste management option (Cox, et al. 2010)

Table 1: Composition (%) of food waste on wet weight basis. Components Malaysian food Japanese food waste (Ohkouchi waste & Inoue, 2007) Moisture 78.09 77.5 Ash 1.42 1.68 Total Sugar 10.36 9.85 Carbohydrate 8.05 7.79 Protein 3.50 3.99 Fats 5.22 5.41 Fiber (cellulose, lignin, hemicelluloses) 4.64 4.72 Note: Malaysian food waste data is taken from a laboratory work by the author to study food waste composition from a household in Malaysia. The above data is not regarded as representative of the whole countries’ food waste composition but only used as a sample reference. Table 2 :Food waste recycling methods Food waste recycling Description options Anaerobic digestion/ Food waste is collected and fermented to Co-digestion produce methane gas which is collected as renewable energy (Knipe, 2005) Composting Home composting (food waste digesters) or in-vessel composting facility whereby the compost product can be used as fertilizers or soil amendment (Knipe, 2005, Kim and Kim, 2010). Dry or wet feed Facility that processes and converts food wastes into safe animal feeds (Kim and Kim, 2010). The data given shows chemical content in Malaysian food waste compared to Japanese food waste content. Nevertheless, this data is not representative of all Malaysian food wastes as there is no actual study on food waste composition collected from households or disposed at landfills. A study by Afizah (2006) shows that moisture content of municipal solid waste collected from Pulau Burung landfill contains 54.1% moisture and Kathrivale, et al. (2003) study showed moisture content of 55%. Nevertheless, home food waste moisture content is higher as shown in Table 1 and is in agreement to the food waste tested in Japan (Ohkouchi and Inoue, 2007). This increase in

Examples of countries applying recycling options Germany, Great Britain.

Great Britain, Korea.

Korea

moisture could be due to the water from washing of plates and pots that were inevitably introduced to the waste mixture. Food waste in Malaysia is not segregated at source nor separated from other solid wastes at landfill sites before disposal. At present there are 289 landfills in Malaysia and only 7 out of total landfills are sanitary landfills (Syed Ali, 2009). Solid wastes are not normally recycled by Malaysians either by composting or by other recycling methods. Separation of wastes such as papers, plastics, glass, rubber, ferrous and non-ferrous metals are usually done by garbage collection worker and scavengers at disposal sites (Hassan, et al. 2000).

Journal of Industrial Research & Technology, Volume 2, Issue 1, April 2012

Food Waste Management in Malaysia: P a g e | 38 Food wastes with other organic wastes such as garden waste and timber products are dumped directly into landfills without any treatment whatsoever. Nevertheless, a positive turn of events recently shows that Malaysian government is concerned about the ever rising solid waste issues in the country. The government will enforce Malaysians to separate solid waste at home according to category by giving free garbage bins by the year 2013. Datuk Nadzri Yahya, the Director General of the Department of Solid Waste Management, said that the Prime Minister, Datuk Seri Najib Razak demanded during the last cabinet meeting that Solid Waste Management Act and Public Cleansing 2007 to be executed as soon as early next year. For the execution of this act, 2 separate garbage bins will be provided for every household that is one for organic solid waste and one for recyclable waste material (Alzahrin, 2010). 3. Types of food waste management in the world Food waste issue, although has always been frequently regarded as main contributor to greenhouse gasses, only recently received much attention even in developed countries. In order to assess management options, that option must have detailed health, safety, environmental, social, economic and operational risk to determine whether the waste management strategies are suitable for implementation (Knipe, 2005). There are many types of food waste management. Basically, all waste management methods should follow the hierarchy shown in Figure 1. Waste prevention is set as the top priority because that is the source of waste generation. Reuse of waste includes using second hand goods but in the case of food waste, not many foods in its original form can be reused due to edibility issue. Recycling of food waste in Malaysia is rarely conducted. But the importance of recycling is at the third priority. Examples of food recycling methods that some countries have applied are as shown in Table 2. Recovery level usually includes energy recovery from certain types of waste management for example incineration. The final option for waste management is safe disposal at an organized landfill system. 4. Food waste management option for Malaysia Suitability of food waste management is highly dependent on the costs of setting up and running the system. Based on the hierarchy shown in Figure 1, normally the most expensive part of waste management is to set up highly advanced facility for recycling, recovery and safe disposal. The least cost used is for the first priority and the second priority that is waste prevention and reuse respectively.

Nevertheless, this is the most difficult part to implement as it involves more human participation compared to the other three. Human attitude and behavior has always been the most difficult part to make a change to as shown in a study by group of researchers in United Kingdom on people’s waste prevention habits (Cox, et al. 2010). In order to produce change, steps to tackle this matter through education, campaigns and policies must be conducted continuously. The effect of waste prevention is enormous on the generation rate of food waste (Cox, et al. 2010). Thus, this is the ultimate step that Malaysians must take in order to reduce food waste generation as a whole. One of the prominent recycling methods of food waste and municipal solid waste is by incineration and has been successfully applied in countries such as Japan. In Malaysia, however, the previous Blue Valley project to build a mega-incinerator in Broga, Pahang has led to many serious objections from the residents in that area and most environmentallyconcerned non-government organization (The Sun, 2007). The government has finally decided to cancel the project (The Star, 2007). Recently, there have been articles in the newspaper that the government is planning to build mini-incinerators all over Malaysia such as in Melaka and Johor (Bernama, 2009). These new projects are bound to receive continuous protests as incineration ash by-product is highly toxic to the environment (Balifokus, 2006). Besides the hazardous ash by-product of incineration, the setup and running costs of such incinerator are also very expensive. The previously cancelled incinerator project costs 425 million US dollar. Other potential food waste processing facility includes anaerobic digestion, dry or wet animal feeds and in-vessel composting (Table 2). The government should be opened to these technologies as the by-products are relatively safe, can be used as soil amendment or safe to be disposed at landfills as well as useful for energy recovery (Kim and Kim, 2010). The private sector should also take this opportunity to enter this field as not only it helps in recycling the abundant of food waste but also producing revenue from sale of biogas, animal feeds and agriculture compost. There are also some other options that can be taken into consideration for example producing energy products from food waste. Currently, there are proven and applied technologies to produce methane (Han and Shin, 2004) and hydrogen (Kim et al. 2009). Other potential technologies include producing oil (Minowa et al. 1995), lactic acid (Sakai et al. 2000) and plastic (Sakai et al. 2004). Although most of these technologies are only available in lab scale, future interests and investment should be channeled to develop such beneficial technology into pilot scale project.

5. Conclusion Journal of Industrial Research & Technology, Volume 2, Issue 1, April 2012

Food Waste Management in Malaysia: P a g e | 39 Several food waste management options for Malaysia have been discussed. The most important part of waste management is to apply waste prevention and reuse to all Malaysians. Although this is undoubtedly the most difficult, the Malaysian government and non-government organizations should consider prompt implementation of this option due to its current and long term future benefits. Acknowledgement The authors would like to thank Institute of Postgraduate Studies for providing scholarships and grants in order to fulfill completion of the first author’s Master’s degree program. References Afizah, A. (2006) Composting of organic waste from municipal solid waste using aerated static pile method. In Master's Thesis. Universiti Sains Malaysia, Penang. Alias, A. Y. (2010) Amal kitar semula. Berita Harian (January 27), Shah Alam. Alzahrin, A. (2010) Penghuni wajib asingkan sampah: Kerajaan bekal tong sampah percuma mulai 2013. Berita Harian (Mei 21), Kuala Lumpur. Balifokus (2006) Policy Brief on Zero Waste: A proposal for a POPs-free alternative to managing municipal discards in Indonesia, Malaysia and the Philippines. Consumers' Association of Penang, Ecological Waste Coalition, Global Alliance for Incinerator Alternatives. International POPs Elimination Project. http://www.ipen.org (March). Bernama (2009) Two incinerators may be built in Melaka and Johor: Lajim Ukin. News Straits Times, Kuala Lumpur (November 3). Cox, J., Giorgi, S., Sharp, V., Strange, K., Wilson, D. C., and Blakely, N. (2010) Household waste prevention - a review of evidence. Waste Management and Research, 28, 193-219. Han, S. K. and Shin, H.S. (2004) Performance of an innovative two-stage process converting food waste to hydrogen and methane. Journal of Air & Waste Management Association, 54: 242249. Hassan, M. N., Zakaria, Z., and Rahman, R. A. (1999) Managing costs of urban pollution in Malaysia: The case of solid waste. Paper presented In MPPJ Seminar Petaling Jaya, Selangor, Malaysia. Hassan, M. N., Rakmi A. R., Chong, T. L., Zakaria, Z., and Awang, M. (2000) Waste Recycling in Malaysia: problems and prospects. Waste Management and Research, 18, 320-328. Hassan, M. N., Chong, T. L., Rahman, M., Salleh, M. N., Zakaria, Z. and Awang. M. (2001) Solid waste management in Southeast Asian countries with special attention to Malaysia.

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