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Evaluation of Plastic Waste Management in Thailand Using Material ...

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The amounts <strong>of</strong> plastic waste disposed at landfills will <strong>in</strong>crease <strong>in</strong> 2016 due to the <strong>in</strong>crease<br />

<strong>of</strong> biodegradable plastic consumption. The recycl<strong>in</strong>g bus<strong>in</strong>ess <strong>of</strong> bio-plastics is not<br />

pr<strong>of</strong>itable because low plastics are conta<strong>in</strong>ed <strong>in</strong> bio-products, and they are not used to<br />

recover energy <strong>in</strong> the <strong>in</strong>c<strong>in</strong>eration due to GHG emissions from <strong>in</strong>c<strong>in</strong>erators. The available<br />

way to used bio-plastic wastes is the compost<strong>in</strong>g <strong>in</strong> order to produce chemical fertilizers<br />

for the agriculture works (Treewijitkasam, 2013).<br />

Increas<strong>in</strong>g <strong>of</strong> recycl<strong>in</strong>g rate will make the amount <strong>of</strong> improper disposed wastes decrease <strong>in</strong><br />

2016. Approximately 3% <strong>of</strong> improper disposed wastes <strong>in</strong> MSW will be expanded and<br />

stocked <strong>in</strong> the environment. The total stock <strong>in</strong> the environment will be 0.34 million tonnes,<br />

while the total stock <strong>of</strong> the scenario 2B will be 4.39 million tonnes <strong>in</strong> 2016 as same as the<br />

scenario 2A.<br />

The highest amount <strong>of</strong> stocked plastics was shown <strong>in</strong> the plastic consumption process<br />

amounted to 1.8 million tonnes. This stock is from the long-live products and<br />

reused/secondary plastic products. This amount <strong>of</strong> stocked plastics will be highest <strong>in</strong> the<br />

next five or ten years if the waste reduction and reuse policy stimulates people to use longlived<br />

products for over five or ten years.<br />

In conclusion, the total <strong>in</strong>put, stock and output <strong>of</strong> scenario 2A and scenario 2B were<br />

presented <strong>in</strong> the similar amounts. Scenario 2A will stimulate people to reduce and reuse<br />

plastic wastes by 10% with <strong>in</strong> 2016. The amount <strong>of</strong> MPW for landfill<strong>in</strong>g <strong>of</strong> scenario 2A <strong>in</strong><br />

2016 will decrease from 37% <strong>in</strong> 2010 to 30% <strong>in</strong> 2016. Otherwise, the percentage <strong>of</strong> MPW<br />

for landfill<strong>in</strong>g <strong>of</strong> scenario 2B will be equal to 40% <strong>in</strong> 2016. F<strong>in</strong>ally, approximately 8% and<br />

3% <strong>of</strong> MPW <strong>of</strong> scenario 2A and 2B will be disposed <strong>in</strong> open environment.<br />

4.3.1.3 Scenario 3: Increase <strong>in</strong> waste to energy options<br />

In the scenario 3, the changes and impacts <strong>of</strong> as alternative energy development plan <strong>in</strong><br />

2012-2021 was were predicted. The goals <strong>of</strong> this plan <strong>in</strong>clude the energy recovery rate and<br />

alternative fuel used will <strong>in</strong>crease by recovery 160 MW <strong>of</strong> energy with<strong>in</strong> 2021. This plan<br />

promotes to use wastes as fuels <strong>in</strong> order to recovery energy such as biogas from anaerobic<br />

digestion, municipal <strong>in</strong>c<strong>in</strong>eration, and alternative fuel production (coal, crude oil, RDF,<br />

and carbon black) (DEDE, 2013). The amounts <strong>of</strong> plastic production and plastic waste<br />

generation <strong>in</strong> 2016 were same as the scenario 1. The calculation <strong>of</strong> each flow <strong>in</strong> the<br />

scenario 3 is shown <strong>in</strong> Table E-9 <strong>in</strong> Appendix E. Figure 4.31 shows the material flow <strong>of</strong><br />

plastics <strong>in</strong> <strong>Thailand</strong> <strong>in</strong> 2016; the scenario 3.<br />

This scenario assumed that 10% <strong>of</strong> municipal plastic wastes <strong>in</strong> 2016 will not collected to<br />

dispose as well as the scenario 2, but whole <strong>in</strong>dustrial plastic wastes will be collected and<br />

disposed properly. The concept <strong>of</strong> this scenario <strong>in</strong>cludes the <strong>in</strong>creases <strong>of</strong> municipal and<br />

<strong>in</strong>dustrial <strong>in</strong>c<strong>in</strong>eration and oil recovery. 10% <strong>of</strong> municipal plastic wastes will be burnt at<br />

both <strong>of</strong> municipal and <strong>in</strong>dustrial <strong>in</strong>c<strong>in</strong>erators.<br />

The amount <strong>of</strong> municipal plastic wastes for <strong>in</strong>c<strong>in</strong>eration will be 0.24 million tonnes <strong>in</strong> 2016<br />

out <strong>of</strong> which 2,371 tonnes is thermosett<strong>in</strong>g wastes. Almost <strong>in</strong>dustrial plastic wastes<br />

(87.6%) will be combusted at the <strong>in</strong>dustrial <strong>in</strong>c<strong>in</strong>erators, and 0.3 million tonnes <strong>of</strong> RDF<br />

production from landfill sites will be burnt <strong>in</strong> the cement kiln.<br />

77

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