CLC number: X734.2
On-line Access: 2018-12-03
Received: 2018-07-01
Revision Accepted: 2018-09-14
Crosschecked: 2018-11-14
Cited: 0
Clicked: 3275
Yu-zhe Zhang, Ting-ting Bian, Yi Zhang, Xu-dong Zheng, Zhong-yu Li. Effective and green tire recycling through microwave pyrolysis[J]. Journal of Zhejiang University Science A, 2018, 19(12): 951-960.
@article{title="Effective and green tire recycling through microwave pyrolysis",
author="Yu-zhe Zhang, Ting-ting Bian, Yi Zhang, Xu-dong Zheng, Zhong-yu Li",
journal="Journal of Zhejiang University Science A",
volume="19",
number="12",
pages="951-960",
year="2018",
publisher="Zhejiang University Press & Springer",
doi="10.1631/jzus.A1800388"
}
%0 Journal Article
%T Effective and green tire recycling through microwave pyrolysis
%A Yu-zhe Zhang
%A Ting-ting Bian
%A Yi Zhang
%A Xu-dong Zheng
%A Zhong-yu Li
%J Journal of Zhejiang University SCIENCE A
%V 19
%N 12
%P 951-960
%@ 1673-565X
%D 2018
%I Zhejiang University Press & Springer
%DOI 10.1631/jzus.A1800388
TY - JOUR
T1 - Effective and green tire recycling through microwave pyrolysis
A1 - Yu-zhe Zhang
A1 - Ting-ting Bian
A1 - Yi Zhang
A1 - Xu-dong Zheng
A1 - Zhong-yu Li
J0 - Journal of Zhejiang University Science A
VL - 19
IS - 12
SP - 951
EP - 960
%@ 1673-565X
Y1 - 2018
PB - Zhejiang University Press & Springer
ER -
DOI - 10.1631/jzus.A1800388
Abstract: Waste tire rubber has become a severe environmental issue, which calls for a green method to recycle this rubber. microwave thermolysis serves as an ideal recycling process for used tires. By surveying the dielectric characteristics from 25 to 700 °C under microwave frequencies of 915 and 2466 MHz, the microwave absorption ability of waste tire rubbers was studied. At temperatures below 350 °C, the dielectric characteristics were relatively steady. Both the loss factor and relative dielectric constant (DC) increased sharply with the rise in temperature. The reason for this is the release of volatile substances, which increases the electrical conductivity. The performance of microwave absorption of tire rubber during thermolysis, and thus the efficiency of microwave tire rubber thermolysis, can be largely impacted by the specimen dimension. The calculation of the reflection loss (RL) of the tire rubber specimens suggests that when the waste tire rubber is 5 mm thick, the highest microwave absorption can be achieved at 915 MHz and 592.1 °C, with RL of −17.30 dB. The product after microwave pyrolysis of waste tire rubber comprises 35% carbon black, 40% oil, and 25% gas. Based on this investigation of the optimal condition of microwave absorption, a proper microwave pyrolysis recycling system was designed for waste tire. This system is efficient at recycling the waste tire rubber into valuable carbon black, oil, and gas products.
This is an interesting and technically-relevant paper presenting an alternative method for recycling waste tires.
[1]Ahmaruzzaman M, Gupta VK, 2011. Rice husk and its ash as low-cost adsorbents in water and wastewater treatment. Industrial & Engineering Chemistry Research, 50(24):13589-13613.
[2]Al-Harahsheh M, Kingman SW, 2004. Microwave-assisted leaching—a review. Hydrometallurgy, 73(3-4):189-203.
[3]Ariyadejwanich P, Tanthapanichakoon W, Nakagawa K, et al., 2003. Preparation and characterization of mesoporous activated carbon from waste tires. Carbon, 41(1):157-164.
[4]Asfaram A, Ghaedi M, Agarwal S, et al., 2015. Removal of basic dye Auramine-O by ZnS:Cu nanoparticles loaded on activated carbon: optimization of parameters using response surface methodology with central composite design. RSC Advances, 5(24):18438-18450.
[5]Bartoli M, Rosi L, Giovannelli A, et al., 2018. Microwave assisted pyrolysis of crop residues from Vitis vinifera. Journal of Analytical and Applied Pyrolysis, 130:305-313.
[6]Bignozzi MC, Sandrolini F, 2006. Tyre rubber waste recycling in self-compacting concrete. Cement and Concrete Research, 36(4):735-739.
[7]Caponero J, Tenório JAS, Levendis YA, et al., 2003. Emissions of batch combustion of waste tire chips: the afterburner effect. Energy & Fuels, 17(1):225-239.
[8]Caponero J, Tenório JAS, Levendis YA, et al., 2004. Emissions of batch combustion of waste tire chips: the hot flue-gas filtering effect. Energy & Fuels, 18(1):102-115.
[9]Caponero J, Tenório JAS, Levendis YA, et al., 2005. Emissions of batch combustion of waste tire chips: the pyrolysis effect. Combustion Science and Technology, 177(2):347-381.
[10]Casal MD, Canga CS, Díez MA, et al., 2005. Low-temperature pyrolysis of coals with different coking pressure characteristics. Journal of Analytical and Applied Pyrolysis, 74(1-2):96-103.
[11]Dai XW, Yin XL, Wu CZ, et al., 2001. Pyrolysis of waste tires in a circulating fluidized-bed reactor. Energy, 26(4):385-399.
[12]Devaraj M, Saravanan R, Deivasigamani R, et al., 2016. Fabrication of novel shape Cu and Cu/Cu2O nanoparticles modified electrode for the determination of dopamine and paracetamol. Journal of Molecular Liquids, 221:930-941.
[13]Fang SW, Gu WL, Dai MQ, et al., 2018. A study on microwave-assisted fast co-pyrolysis of chlorella and tire in the N2 and CO2 atmospheres. Bioresource Technology, 250:821-827.
[14]Ghaedi M, Hajjati S, Mahmudi Z, et al., 2015. Modeling of competitive ultrasonic assisted removal of the dyes– Methylene blue and Safranin-O using Fe3O4 nanoparticles. Chemical Engineering Journal, 268:28-37.
[15]Gupta VK, Saleh TA, 2013. Sorption of pollutants by porous carbon, carbon nanotubes and fullerene-an overview. Environmental Science and Pollution Research, 20(5):2828-2843.
[16]Gupta VK, Gupta B, Rastogi A, et al., 2011a. Pesticides removal from waste water by activated carbon prepared from waste rubber tire. Water Research, 45(13):4047-4055.
[17]Gupta VK, Jain R, Nayak A, et al., 2011b. Removal of the hazardous dye—tartrazine by photodegradation on titanium dioxide surface. Materials Science and Engineering: C, 31(5):1062-1067.
[18]Gupta VK, Kumar R, Nayak A, et al., 2013. Adsorptive removal of dyes from aqueous solution onto carbon nanotubes: a review. Advances in Colloid and Interface Science, 193-194:24-34.
[19]Gupta VK, Nayak A, Agarwal S, et al., 2014. Potential of activated carbon from waste rubber tire for the adsorption of phenolics: effect of pre-treatment conditions. Journal of Colloid and Interface Science, 417:420-430.
[20]Gupta VK, Nayak A, Agarwal S, 2015. Bioadsorbents for remediation of heavy metals: current status and their future prospects. Environmental Engineering Research, 20(1):1-18.
[21]Huang H, Tang L, 2009. Pyrolysis treatment of waste tire powder in a capacitively coupled RF plasma reactor. Energy Conversion and Management, 50(3):611-617.
[22]Jia Q, Che DF, Liu YH, et al., 2009. Effect of the cooling and reheating during coal pyrolysis on the conversion from char-N to NO/N2O. Fuel Processing Technology, 90(1):8-15.
[23]Karthikeyan S, Gupta VK, Boopathy R, et al., 2012. A new approach for the degradation of high concentration of aromatic amine by heterocatalytic Fenton oxidation: kinetic and spectroscopic studies. Journal of Molecular Liquids, 173:153-163.
[24]Kato T, Yoshikawa N, Taniguchi S, et al., 2011. Microwave magnetic field heating of a cobalt-based amorphous ribbon. Japanese Journal of Applied Physics, 50(3R):033001.
[25]Khani H, Rofouei MK, Arab P, et al., 2010. Multi-walled carbon nanotubes-ionic liquid-carbon paste electrode as a super selectivity sensor: application to potentiometric monitoring of mercury ion(II). Journal of Hazardous Materials, 183(1-3):402-409.
[26]Lee JM, Lee JS, Kim JR, et al., 1995. Pyrolysis of waste tires with partial oxidation in a fluidized-bed reactor. Energy, 20(10):969-976.
[27]Levendis YA, Atal A, Carlson J, et al., 1996. Comparative study on the combustion and emissions of waste tire crumb and pulverized coal. Environmental Science & Technology, 30(9):2742-2754.
[28]Metaxas R, 2000. Radio frequency and microwave heating: a perspective for the millennium. Power Engineering Journal, 14(2):51-60.
[29]Mittal A, Mittal J, Malviya A, et al., 2010. Removal and recovery of Chrysoidine Y from aqueous solutions by waste materials. Journal of Colloid and Interface Science, 344(2):497-507.
[30]Mohammadi N, Khani H, Gupta VK, et al., 2011. Adsorption process of methyl orange dye onto mesoporous carbon material–kinetic and thermodynamic studies. Journal of Colloid and Interface Science, 362(2):457-462.
[31]Mui ELK, Ko DCK, McKay G, 2004. Production of active carbons from waste tyres––a review. Carbon, 42(14):2789-2805.
[32]Nisar J, Ali G, Ullah N, et al., 2018. Pyrolysis of waste tire rubber: influence of temperature on pyrolysates yield. Journal of Environmental Chemical Engineering, 6(2):3469-3473.
[33]Peng ZW, Hwang JY, Mouris J, et al., 2010. Microwave penetration depth in materials with non-zero magnetic susceptibility. ISIJ International, 50(11):1590-1596.
[34]Peng ZW, Hwang JY, Mouris J, et al., 2011. Microwave absorption characteristics of conventionally heated nonstoichiometric ferrous oxide. Metallurgical and Materials Transactions A, 42(8):2259-2263.
[35]Peng ZW, Hwang JY, Kim BG, et al., 2012. Microwave absorption capability of high volatile bituminous coal during pyrolysis. Energy & Fuels, 26(8):5146-5151.
[36]Rajendran S, Khan MM, Gracia F, et al., 2016. Ce3+-ion-induced visible-light photocatalytic degradation and electrochemical activity of ZnO/CeO2 nanocomposite. Scientific Reports, 6:31641.
[37]Robati D, Mirza B, Rajabi M, et al., 2016. Removal of hazardous dyes-BR 12 and methyl orange using graphene oxide as an adsorbent from aqueous phase. Chemical Engineering Journal, 284:687-697.
[38]Sadhukhan AK, Gupta P, Saha RK, 2011. Modeling and experimental investigations on the pyrolysis of large coal particles. Energy & Fuels, 25(12):5573-5583.
[39]Saleh TA, Gupta VK, 2011. Functionalization of tungsten oxide into MWCNT and its application for sunlight-induced degradation of rhodamine B. Journal of Colloid and Interface Science, 362(2):337-344.
[40]Saleh TA, Gupta VK, 2012a. Photo-catalyzed degradation of hazardous dye methyl orange by use of a composite catalyst consisting of multi-walled carbon nanotubes and titanium dioxide. Journal of Colloid and Interface Science, 371(1):101-106.
[41]Saleh TA, Gupta VK, 2012b. Synthesis and characterization of alumina nano-particles polyamide membrane with enhanced flux rejection performance. Separation and Purification Technology, 89:245-251.
[42]Saleh TA, Gupta VK, 2014. Processing methods, characteristics and adsorption behavior of tire derived carbons: a review. Advances in Colloid and Interface Science, 211:93-101.
[43]Saravanan R, Thirumal E, Gupta VK, et al., 2013a. The photocatalytic activity of ZnO prepared by simple thermal decomposition method at various temperatures. Journal of Molecular Liquids, 177:394-401.
[44]Saravanan R, Gupta VK, Prakash T, et al., 2013b. Synthesis, characterization and photocatalytic activity of novel Hg doped ZnO nanorods prepared by thermal decomposition method. Journal of Molecular Liquids, 178:88-93.
[45]Saravanan R, Karthikeyan N, Gupta VK, et al., 2013c. ZnO/Ag nanocomposite: an efficient catalyst for degradation studies of textile effluents under visible light. Materials Science and Engineering: C, 33(4):2235-2244.
[46]Saravanan R, Joicy S, Gupta VK, et al., 2013d. Visible light induced degradation of methylene blue using CeO2/V2O5 and CeO2/CuO catalysts. Materials Science and Engineering: C, 33(8):4725-4731.
[47]Saravanan R, Khan MM, Gupta VK, et al., 2015a. ZnO/ Ag/CdO nanocomposite for visible light-induced photocatalytic degradation of industrial textile effluents. Journal of Colloid and Interface Science, 452:126-133.
[48]Saravanan R, Khan MM, Gupta VK, et al., 2015b. ZnO/ Ag/Mn2O3 nanocomposite for visible light-induced industrial textile effluent degradation, uric acid and ascorbic acid sensing and antimicrobial activity. RSC Advances, 5(44):34645-34651.
[49]Saravanan R, Sacari E, Gracia F, et al., 2016. Conducting PANI stimulated ZnO system for visible light photocatalytic degradation of coloured dyes. Journal of Molecular Liquids, 221:1029-1033.
[50]Shuang Y, Wu CN, Yan BH, et al., 2010. Heat transfer inside particles and devolatilization for coal pyrolysis to acetylene at ultrahigh temperatures. Energy & Fuels, 24(5):2991-2998.
[51]Sun X, 2006. Treatment of Electric Arc Furnace Dust by Microwave Heating. PhD Thesis, Michigan Technological University, Michigan, USA.
[52]Zeaiter J, Azizi F, Lameh M, et al., 2018. Waste tire pyrolysis using thermal solar energy: an integrated approach. Renewable Energy, 123:44-51.
[53]Zhou J, Yang YR, Ren XH, et al., 2006. Investigation of reinforcement of the modified carbon black from wasted tires by nuclear magnetic resonance. Journal of Zhejiang University SCIENCE A, 7(8):1440-1446.
[54]Zhu WK, Song WL, Lin WG, 2008. Effect of the coal particle size on pyrolysis and char reactivity for two types of coal and demineralized coal. Energy & Fuels, 22(4):2482-2487.
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