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Abstract

Plastics are one of the most widely used materials, and, in most cases, they are designed to have long life spans. Since plastic and packaging waste pollute the environment for many years, their disposal is of great importance for the environment and human health. In this paper, a system was developed to store liquid fuel from plastic and organic waste mixes without solidification, which then can be used as fuel in motor vehicles and construction machinery. For this purpose, polyethylene terephthalate (PET), polyvinyl chloride (PVC), and organic wastes and clay, zeolite, and MCS23-code materials (50% magnetite- %25 calcium oxide- %25 sodium chloride) were heated in a closed medium at temperatures ranging from 300 to400 oC and subsequently re-condensed. The study conducted twenty tests, involving various types and rates of plastic and organic materials, as well as different rates of catalysts. Among these tests, the highest liquid fuel yield (67.47%) was achieved in Test 9, where 50% PVC-50% PET waste, 75 g of clinoptilolite, and 500 g of MCS23 waste were collectively used. Notably, Test 12 exhibited the highest density value (79.8 kg/m3), while the best viscosity value (2.794 mm2/s) was observed in Test 2. Across all samples, flash point values were found to be below 40oC. The most favorable yield point value was recorded in Test 2 (-6oC). The samples displayed ash content within the range of 0 to0.01% (m/m)] and combustion heat values of 35.000> J/g which fall within the standard range. The incorporation of MCS23 with clinoptilolite additives is believed to have a significant impact on obtaining high-yield products with improved fuel properties.
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Bibliography

  1. Allende S., Brodie G. & Jacob M.V. (2022) Energy recovery from sugarcane bagasse under varying microwave-assisted pyrolysis conditions, Bioresource Technology Reports, 20, 101283, ISSN 2589-014X, DOI: 10.1016/j.biteb.2022.101283
  2. Damodharan D., Kumar B.R., Gopal K., De Poures M.V. & Sethuramasamyraja B., (2019). Utilization of waste plastic oil in diesel engines: a review. Reviews in Environmental Science and Bio/Technology. 18, pp. 681-697. DOI: 10.1007/s11157-019-09516-x
  3. DIN, DIN 51900-2, 2003. Petroleum products – Petroleum products – Determination of Heat of Combustion – Bomb Calorimetry Method, Berlin. DOI: 10.31030/9447973
  4. Dorado C., Mullen C.A. & Boateng A.A., (2014). Origin of carbon in aromatic and olefin products derived from HZSM-5catalyzed co-pyrolysis of cellulose and plastics via isotopic labeling. Applied CatalysisB: Environmental. 162, pp. 338-345. DOI: 10.1016/j.apcatb.2014.07.006
  5. Erşen T, & Pehlivan D, 2011. High density polyethylene – Co-pyrolysis of wood blends. Gazi Üniversitesi Mühendislik Mimarlık Fakültesi Dergisi. 26, pp. 607-612.
  6. Kalargaris I., Tian G. & Gu S., (2017). The utilisation of oils produced from plastic waste at different pyrolysis temperatures in a DI diesel engine. Energy. 131, pp. 179-185. DOI: 10.1016/j.energy.2017.05.024
  7. Kaminsky W. & Kim J.S., (1999). Pyrolysis of mixed plastics into aromatics. Journal of Analytical and Applied Pyrolysis. 51, pp. 127-134. DOI: 10.1016/S01652370(99)00012-1
  8. Kaminsky W., Predel M. & Sadiki A., (2004). Feedstock recycling of polymers by pyrolysis in a fluidised bed. Polymer Degradation and Stability. 85, pp. 1045-1050, 146. DOI: 10.1016/j.polymdegradstab.2003.05.002
  9. Kirov N.Y. & Peck M.A. (1970). Characteristics of chars from fluid-bed coal carbonization, Fuel, 49( 4), pp. 375-394. DOI: 10.1016/S0016-2361(70)80003-5.
  10. Krishnamurthy S., Shah Y.T. & Stiegalt G.J. (1980). Pyrolysis of coal liquids, Fuel, 59(11), pp. 738-746. DOI: 10.1016/0016-2361(80)90247-1
  11. Lee D-J., (2022). Gasification of municipal solid waste (MSW) as a cleaner final disposal route: A mini-review. Bioresource Technology. 344, 126217. DOI: 10.1016/j.biortech.2021.126217
  12. Liu B., Han Z., Li J. & Yan B. (2022). Comprehensive evaluation of municipal solid waste power generation and carbon emission potential in Tianjin based on Grey Relation Analysis and Long Short Term Memory. Process Safety and Environmental Protection, 168, pp. 918-927. DOI: 10.1016/j.psep.2022.10.065
  13. Liu Q., Sheng Y. & Wang Z. (2023). Co-pyrolysis with pine sawdust reduces the environmental risks of copper and zinc in dredged sediment and improves its adsorption capacity for cadmium. Journal of Environmental Management, 334, 117502, DOI: 10.1016/j.jenvman.2023.117502
  14. Mazumdar B.K. & Chatterjee N.N. (1973). Mechanism of coal pyrolysis in relation to industrial practice. Fuel, 52(1), pp. 11-19. DOI: 10.1016/0016-2361(73)90005-7
  15. Ma J., Feng S., Zhang Z., Wang Z., Kong W., Yuan P., Shen B. & Mu L. (2022). Pyrolysis characteristics of biodried products derived from municipal organic wastes: Synergistic effect of bulking agents and modification of biodegradation, Environmental Research. 206, 112300., DOI: 10.1016/j.envres.2021.112300
  16. Miranda R., Pakdel H., Roy C. & Vasile C., (2001). Vacuum pyrolysis of commingled plastics containing PVC II. Product analysis. Polymer Degradation and Stability. 73, pp.47-67. DOI: 10.1016/S0141-3910(01)00066-0
  17. Öngen A., Karabag N., Yiğit H.S., Özcan H.K., Elmaslar Ö.E. & Aydın S., (2019). An Assessment of Pyrolysis Process for the Treatment of Agricultural and Forest Wastes. Recyclıng And Reuse Approaches For Better Sustaınabılıty. pp. 97110. DOI: 10.1007/978-3-319-95888-0_9
  18. Öngen A., Özcan H.K. & Elmaslar Ozbas E. (2016). Gasification of biomass and treatment sludge in a fixed bed gasifier. Internatıonal Journal of Hydrogen Energy, vol.41(19), 8146-8153. DOI: 10.1016/j.ijhydene.2015.11.159
  19. Öngen A., Özcan H.K., Elmaslar Özbaş, E. & Pangaliyev Y. (2019). Gasification of waste tires in a circulating fixed-bed reactor within the scope of waste to energy. Clean Technologies and Environmental Policy,.21,pp. 1281-1291. DOI: 10.1007/s10098-019-01705-0
  20. Özcan H.K., Öngen A. & Pangaliyev Y., (2016). An Experimental Study of Recoverable Products from Waste Tire Pyrolysis. Global Nest Journal. 3, pp. 582-590. DOI: 10.30955/gnj.001907
  21. Pan R. & Debenest G., (2022). Numerical investigation of a novel smoldering-driven reactor for plastic waste pyrolysis. Energy Conversion and Management, 257, 115439.DOI: 10.1016/j.enconman.2022.115439.
  22. Pan R., Martins M.F. & Debenest G., (2022). Optimization of oil production through ex-situ catalytic pyrolysis of waste polyethylene with activated carbon. Energy, 248, 123514. DOI: 10.1016/j.energy.2022.123514
  23. Pan R., Lougou B. G., Shuai Y. & Debenest G. (2023). A multidimensional numeric study on smoldering-driven pyrolysis of waste polypropylene. Process Safety and Environmental Protection, 172, pp. 305-316. DOI: 10.1016/j.psep.2023.02.018
  24. Papari S., Bamdad H. & Berruti F. (2021). Pyrolytic conversion of plastic waste to value-added products and fuels: A Review. Materials. 14(10), 2586. DOI: 10.3390/ma14102586
  25. Pinto F., Costa P., Gülyurtlu I. & Cabrita I. (1999). Pyrolysis of plastic wastes. 1. Effect of plastic waste composition on product yield. Journal of Analytical and Applied Pyrolysis. 51, pp. 39-55. DOI: 10.1016/S0165-2370(99)00007-8
  26. Saliba M., Frantzi S. & Beukering P. (2022). Shipping spills and plastic pollution: A review of maritime governance in the North Sea. Marine Pollution Bulletin, 181, 113939, DOI: 10.1016/j.marpolbul.2022.113939
  27. Schafer H.N.S. (1979). Pyrolysis of brown coals. 2. Decomposition of acidic groups on heating in the range 100–900 °C. Fuel, 58(9), pp. 673-679. DOI: 10.1016/0016-2361(79)90222-9
  28. Sharma B.K., Moser B.R., Vermillion K.E., Doll K.M. & Rajagopalan N. (2014). Production, characterization and fuel properties of alternative diesel fuel from pyrolysis of waste plastic grocery bags. Fuel Processing Technology. 122, pp. 79-90. DOI: 10.1016/j.fuproc.2014.01.019
  29. Sogancioglu M., Ahmetli G. & Yel E. (2017). A Comparative Study on Waste Plastic Pyrolysis Liquid Products Quantity and Energy Recovery Potential. Energy Procedia, 118, pp.221-226. DOI: 10.1016/j.egypro.2017.07.020
  30. TS, TS 1233 ISO 3016, (1997). Petroleum products-Determination of pour point, Ankara. https://intweb.tse.org.tr/Standard/Standard/Standard.aspx?081118051115108051104119110104055047105102120088111043113104073081055057051113111083082048090121
  31. TS, TS 1451 EN ISO 3104, (1999). Petroleum products-Transparent and opaque liquids-Kinematic viscosity determination and calculation of dynamic viscosity, Ankara. https://intweb.tse.org.tr/Standard/Standard/Standard.aspx?081118051115108051104119110104055047105102120088111043113104073083077102090084083076053089099056
  32. TS, TS 6147 EN ISO 12937, (2002). Petroleum products- Water determination- Calometric Karl fischer titration method, Ankara. https://intweb.tse.org.tr/Standard/Standard/Standard.aspx?081118051115108051104119110104055047105102120088111043113104073081107087097053098049101074085051
  33. TS, TS EN ISO 12185, (2007). Crude oil and petroleum products- Density determination - oscillating u-Tube method, Ankara. https://intweb.tse.org.tr/Standard/Standard/Standard.aspx?081118051115108051104119110104055047105102120088111043113104073087088047079051101109088047113066
  34. TS, TS EN ISO 2719, (2016). Petroleum products and lubricants - Determination of flash point - Pensky Martens closed cup method, Ankara. https://intweb.tse.org.tr/Standard/Standard/Standard.aspx?081118051115108051104119110104055047105102120088111043113104073082090086090075081118122084111048
  35. TS, TS EN ISO 6245, (2006). Petroleum products – Ash determination, Ankara. https://intweb.tse.org.tr/Standard/Standard/Standard.aspx?081118051115108051104119110104055047105102120088111043113104073084090047056119107056057109067090)
  36. Williams P.T. & Williams E.A. (1999). Interaction of Plastics in Mixed-Plastics Pyrolysis. Energy & Fuels.13, pp. 188-196. DOI:10.1021/ef980163x
  37. Williams P.T. & Slaney E. (2007). Analysis of products from the pyrolysis and liquefaction of single plastics and waste plastic mixtures. Resources, Conservation and Recycling. 51, pp. 754-769. DOI: 10.1016/j.resconrec.2006.12.002
  38. Varank G., Öngen A., Guvenc S. Y., Ozcan H. K., Ozbas E. & Guven E.C. (2022). Modeling and optimization of syngas production from biomass gasification. International Journal of Envıronmental Science and Technology, 19(4), pp. 3345-3358. DOI: 10.1007/s13762-021-03374-3
  39. Vinti G., Bauza V., Clasen T., Tudor T., Zurbrügg C. & Vaccari M. (2023). Health risks of solid waste management practices in rural Ghana: A semi-quantitative approach toward a solid waste safety plan. Environmental Research, 216(3), 114728. DOI: 10.1016/j.envres.2022.114728
  40. Zhang C., Hu M., Maio F., Sprecher B., Yang X. & Tukker A. (2022). An overview of the waste hierarchy framework for analyzing the circularity in construction and demolition waste management in Europe. Science of The Total Environment, 803, 149892. DOI: 10.1016/j.scitotenv.2021.149892 .
  41. Zhang J., Jin J., Wang M., Naidu R., Liu Y., Man Y.B., Liang X., Wong M.H., Christie P., Zhang Y., Song C. & Shan S. (2020). Co-pyrolysis of sewage sludge and rice husk/ bamboo sawdust for biochar with high aromaticity and low metal mobility. Environmental Research, 191, 110034. DOI: 10.1016/j.envres.2020.110034
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Authors and Affiliations

Mehmet Can Sarıkap
1
Fatma Hoş Çebi
2
ORCID: ORCID

  1. İstanbul University-Cerrahpaşa, Turkey
  2. Karadeniz Technical University, Turkey
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Abstract

In the last decade a growing interest was observed in low-cost adsorbents for heavy metal ions. Clinoptilolite is a mineral sorbent extracted in Poland that is used to remove heavy metal ions from diluted solutions. The experiments in this study were carried out in a laboratory column for multicomponent water solutions of heavy metal ions, i.e. Cu(II), Zn(II) and Ni(II). A mathematical model to calculate the metals' concentration of water solution at the column outlet and the concentration of adsorbed substances in the adsorbent was proposed. It enables determination of breakthrough curves for different process conditions and column dimensions. The model of process dynamics in the column took into account the specificity of sorption described by the Elovich equation (for chemical sorption and ion exchange). Identification of the column dynamics consisted in finding model coefficients β, KE and Deff and comparing the calculated values with experimental data. Searching for coefficients which identify the column operation can involve the use of optimisation methods to find the area of feasible solutions in order to obtain a global extremum. For that purpose our own procedure of genetic algorithm is applied in the study.

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Authors and Affiliations

Elwira Tomczak
Władysław Kamiński
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Abstract

The subject of this work was the investigation of zeolite as a sorbent of toxic gases. In Nizny Hrabovec in the Slovak republic, two layers of zeolite with the active component clinoptilolite can be found. The study presented here investigated the ability of this natural zeolite to reduce polycyclic aromatic hydrocarbons (PAH) and NO emissions from engine exhaust. Exhaust gases from combustion engines include toxic components such as carbon monoxide, nitrogen oxides and hydrocarbons. Polycyclic aromatic hydrocarbons (PAH) are a component of hydrocarbons causing harmful influence on life forms. The experiments focused on the potential reduction of these toxic gases based on the sorption and catalytic properties of natural zeolite. Also observed was the influence of chemical adjustment including incorporation of certain metal elements. Chemical analysis by mutually independent technologies served to observe the sorption of PAH with carcinogenic properties on the natural zeolite tested. The experiments showed that chemical modification improved the sorption and catalytic properties of natural zeolite. The PAH were analysed in an extract of the contaminated, thermally-activated natural zeolite and modified zeolite after washing with ammonium chloride, cobalt chloride and copper sulphate. The study also presents results of NO measurements obtained by testing the filter-sorptive automobile system.

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Authors and Affiliations

Jozef Mačala
Iveta Pandová
Taťána Gondová
Katarína Dubayová

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