Zerin N H, Rasul M G, Jahirul M I, Sayem A S M
Fuel and Energy Research Group, School of Engineering and Technology, Central Queensland University, North Rockhampton, Queensland 4702, Australia.
Fuel and Energy Research Group, School of Engineering and Technology, Central Queensland University, North Rockhampton, Queensland 4702, Australia.
Sci Total Environ. 2023 Dec 20;905:166981. doi: 10.1016/j.scitotenv.2023.166981. Epub 2023 Sep 12.
The number of end-of-life waste tyres has increased enormously worldwide, which is one of the non-biodegradable Municipal Solid Waste (MSW) piling up in an open space for a long time. Every year, various types of tyres are released in the environment from different vehicles, such as trucks, buses, cars, motorcycles, and bicycles, which negatively impact the environment. Nowadays, waste tyres are treated in several ways, whereas thermochemical conversion is one of them, including combustion, gasification, incineration, and pyrolysis. Many literatures revealed that pyrolysis is a more environmentally friendly process than others since it can convert waste tyres into crude oil, char, and syngas without emitting harmful gases. In this study, the pyrolysis of tyres and the chemical activation of tyres are reviewed in terms of their kinetic behaviour. According to the literature, the most influential factors of the pyrolysis process are reactors, temperature, heating rate, residence time, feedstock size and catalyst. As the main ingredient of the tyre is rubber, tyre pyrolysis starts from 300 °C and completely decomposed nearly 550 °C. It can be found from literature that Pyrolysed tyre can produce 30-65% oil, 25-45% char and 5-20 % gas. It is also explained how the properties of active carbon (AC) are affected by activating conditions, including activation temperature, agent, the ratio of reagent mixture and others. Generally, pyrolytic char has surface area between 20 and 80 m/g, whereas tyre-derived activated carbon's (TDAC) surface area varied from 90 to 970 m/g. For large surface area and porous structure, TDAC has large application in purification and energy storage sector. The individuality of this article is to depict the entire pathway of AC production from waste tyres. The findings of this literature review help to improve technologies for producing activated carbon from waste tyres pyrolysed char.
在全球范围内,报废轮胎的数量急剧增加,这些不可生物降解的城市固体废弃物长期堆积在露天场地。每年,各类车辆(如卡车、公交车、汽车、摩托车和自行车)都会向环境中排放不同类型的轮胎,这对环境产生了负面影响。如今,报废轮胎有多种处理方式,热化学转化便是其中之一,包括燃烧、气化、焚烧和热解。许多文献表明,热解是一种比其他方式更环保的过程,因为它能将报废轮胎转化为原油、焦炭和合成气,且不排放有害气体。在本研究中,从动力学行为方面对轮胎的热解和化学活化进行了综述。根据文献,热解过程中最具影响力的因素是反应器、温度、加热速率、停留时间、原料尺寸和催化剂。由于轮胎的主要成分是橡胶,轮胎热解从300℃开始,在近550℃时完全分解。从文献中可以发现,热解后的轮胎可产生30 - 65%的油、25 - 45%的焦炭和5 - 2%的气体。还阐述了活化条件(包括活化温度、试剂、试剂混合物比例等)如何影响活性炭(AC)的性能。一般来说,热解焦炭的表面积在20至80平方米/克之间,而轮胎衍生活性炭(TDAC)的表面积在90至970平方米/克之间。由于具有大表面积和多孔结构,TDAC在净化和储能领域有广泛应用。本文的独特之处在于描绘了从废旧轮胎生产活性炭的整个过程。这篇文献综述的结果有助于改进从废旧轮胎热解焦炭生产活性炭的技术。