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458 CHEMICAL PROBLEMS 2024 no. 4 (22) ISSN 2221-8688
UDC 628.4.037113.01:658.567.1:629
CHEMICAL CHARACTERIZATION OF ECO-FRIENDLY RECOVERY METHOD FOR
RUBBER FROM WASTE TIRES
R.J.N. AL - Jubouri, Fawzi Habeeb Jabrail*
Department of Chemistry, College of Science, University of Mosul, Mosul, Iraq *email: _ fawzijabrail@uomosul. edu. iq
Received 15.02.2024 Accepted 19.04.2024
Abstract: Recycling of waste tires is the goal of many studies, where the chemical dissolution method depends on the recovery of tire rubber (TR) and carbon black (CB) from the waste tires. Petroleum ether was used to dissolve tire powder and a black solution was produced which after refluxed at 140°C for two hours with a mixture of adsorbents including silicon dioxide (.SiO2) and aluminum oxide (Al2O3) and then filtered, will give clear rubber filtrate and CB precipitate and the used petroleum ether was totally regenerate. The rubber was recovered with a weight percentage of 24% (w/w), whereas CB was reclaimed with 20% (w/w) from the total waste tire used. The recovered rubber was characterized and its functional groups were studied by H-NMR and FTIR spectroscopy which shows the rubber is polyisoprene blended with polybutadiene. The XRD, FESEM, and thermal analyses (TGA, DTA, and DSC) show the recovered rubber is amorphous with an elastic nature, thermally stable with endothermic behavior, and contains some inorganic impurities. On the other hand, the BET (Brunauer-Emmett-Teller) analysis, of carbon black shows it is a mesoporous material with a high specific surface area (as = 149.44m2. g-1) and pores with a mean diameter (13.623 nm). The particle size, structure and surface chemistry of the reclaimed CB which was measured accordingly by XRD, BET, and FESEM and it was emphasized that the CB has excellent adsorption qualities. Keywords: Recycling of tires, rubber, petroleum ether, carbon black, Silicon dioxide, Aluminum oxide. DOI: 10.32737/2221-8688-2024-4-458-467
1. Introduction
The large growth in the use of automobiles produced a large amount of tire consumption, creating an extreme waste problem [1]. Because of chemical cross-linking, vulcanized rubber, unlike thermoplast polymers, cannot be recycled or reprocessed. The vulcanization process can form a cross-linked structure between the chains of the rubber, which resists environmental agents, shear modulus, and temperature applications [2]. In general, tires are made of natural rubber (NR) and synthetic rubber (SR). The three-dimensional network structure after vulcanization makes tires unable to biodegrade and difficult to photochemically decompose under environmental conditions [3]. Various rubber products ranging from healthcare, military, household, construction, and
automotive [4] result in a hard-to-decompose large amount of waste rubber, which causes environmental and economic problems. There are different methods for the treatment of scrap tires [5-9], but the main methods are tire retreading, heat energy utilization, rubber powder production, pyrolysis, etc. The cost of rubber powder production is high, and the requests are limited. The production of regenerated rubber is complicated and produces waste gas, causing great harm to the environment without proper treatment [10]. Heat energy utilization of scrap tires produces high calorific value and can be used, but it will cause secondary environmental pollution. Through the pyrolysis process, the waste rubber can decompose completely and produce oil, in
CHEMICAL PROBLEMS 2024 no. 4 (22)
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addition to gases that also cause secondary pollution to the environment.
The chemical recycling process of rubber is considered the most common and contains organic, inorganic, and many diverse chemical processes. In the organic process, the used reagents could cause the scission of S-S or C-S bonds of the vulcanized rubber. Chemical reagents such as butyl mercaptan, thiophenols, xylene, etc. cause cleavage of sulfur cross-links at 188°C and for 4 h [11, 12]. The chemical dissolution process can reclaim rubber from waste tires using hydrocarbon solvents [13]. The solvent molecules can penetrate among the rubber chains and cause swelling. Sometimes, the interactions that occur between solventpolymer and polymer-polymer could encourage
the rubber chains to cleave into small segments.
In the recent work, the chemical dissolution process was used mainly for the recovery of rubber and carbon black (CB) as side products from waste tires. It is noteworthy that petroleum ether was selected as a hydrocarbon reagent for rubber dissolution because of its high permeability between rubber chains; its low cost due to its availability from a high fraction of aliphatic hydrocarbon and boiling in the range of 100-140 °C, and its low toxicity and medium impact on the environment. The silicon dioxide (SiO2) mixed with aluminum oxide (Al2O3) was used as a good adsorbing agent for the separation of CB from the rubber-petroleum ether solution.
2. Experimental part
2.1. Materials
End-of-life automotive tires were collected from the local market, and washed with a soft detergent and warm water. The large tire pieces are cut into small pieces and then ground into small particles of 2.0-1.5 mm. Petroleum ether (90-140oC) from ROMIL Ltd. company was purchased, silicon dioxide and aluminum oxide were received from Aldrich Chemical Company, whereas methanol was supplied from Sharlau Chemicals, which was used as received.
2.2. Rubber Recovery
The chemical dissolution process was used for the reclaim of rubber using petroleum ether for the dissolution of crushed tires. Petroleum ether 100 ml was used for dissolving 10 g of the crushed tire (10 wt %) using a 250 ml conical flash, which was closed and fixed inside the water bath at 50°C for 3 days and shaken from time to time [14].
The steeped tire solution after filtration from undissolved solid materials was transferred into a 250 ml round bottom flask. Then, to the solution, 7g of silicon dioxide and 3 g of aluminum oxide were added as adsorbing agents for adsorbing CB and isolated from the rubber
solution. The mixture was heated to the boiling point of the solvent, around 140°C for two hours with gentle stirring. The hot solution was filtered, a pale yellow solution was collected, and then left to cool [15]. Methanol as a precipitator was added at 40% (V/V) to the pale yellow solution of rubber and then heated inside the water bath at 50°C. Finally, elastic material of a yellowish brown color was precipitating, and the precipitator methanol was collected and used in the next batch [15].
2.3. Carbon Black (CB) Recovery
After the hot filtration step of tire solution, the collected black precipitate in the filter paper, which is mainly CB, was collected with the undissolved solid rubber materials and treated chemically for purification in two steps, where the first was washed sequentially with different solvents, including hexane, acetone, ethanol, and methanol, by keeping the precipitate inside each solvent for 15 minutes inside a water bath at 50°C. Finally, it was washed with hot and followed with cold water, and then the precipitate CB was dried inside a vacuum oven at 100°C. In the second step, the precipitate was heated inside the tube furnace for one hour at 500°C ±10°C and then left to cool [16].
3. Results and Discussion
The chemical dissolution method was used for the recovery of rubber and CB from waste tires. The method is simple, safe, and cheap in comparison with the seriousness of pollution issues. The important point is that the method recovered both rubber and CB. Whereas, other methods, such as the incineration method or pyrolysis of the waste tires, are dangerous and have dangerous effects on the environment, they also lose rubber. Even the mechanical methods caused rrubber to be lost, and the crushed tires will be used only as filling or second materials in construction supplies.
3.1. FTIR of Waste Tire
The main functional groups of the main compounds (rubber and CB) in waste tires were determined by FTIR spectroscopy using JASCO V-630 (Portland), OR 97211, U.S. in the range of 400-4000 cm-1. The absorption frequencies of the fundamental functional groups of the pristine waste tire Figure 1A shows peaks at 1342 cm-1 and 1376 cm-1 for y(C-H)str of methane and methyl groups, respectively. The peaks at 1416 cm-1, 2846 cm-1 and 2914 cm-1 in Figure 1A, are for y(C-H)str of the methylene group of the rubber. The peaks at 1537cm-1 and 1170cm-1 are for y(C=o)str, y(C-O)str and 5(O-H)bend respectively of CB.
The band at 960 cm-1 in Figure 1A, is for y(C=C)str which belongs to the unsaturated bands of the rubber. FTIR wave numbers (Figure 1A) of the pristine material shows the absorption frequencies are belonging to functional groups of polyisoprene blend with polybutadiene.
3.2. Rubber and Carbon Black Recovery
Petroleum ether was used in the chemical dissolution method for the recovery of rubber from waste tires, with the help of 70% (w/w) SiO2 and 30% (w/w) Al2O3. Soaking the tire powder in a suitable solvent is important due to the compactness of the tires. Therefore, the tire powder was soaked for 72h inside petroleum ether at 50°C with gentle shaking, which afforded the potentiality for the solvent to penetrate among rubber chains [17]. The problem of the separation of CB from the rubber solution was solved by adding the adsorbing agent. Accordingly, a mixture of SiO2 and Al2O3 was used as adsorbing agents for the separation of CB and it showed a strong ability for adsorbing. The method showed a recovery of 24% (w/w) rubber and 17.4% (w/w) carbon black from the total waste tire powder used. The recovered materials were characterized using different analysis techniques.
3.3 Recovered Rubber Characterization 3.3.1. FTIR spectroscopy Recovered rubber was characterized by FTIR (Figure 1B). Where the peaks at 1452 cm-1, 2852 cm-1 and 2921 cm-1 represent the y(C-H)str of the methylene group. The peaks at 1308 cm-1 and 1376 cm-1 are of y(C-H)str of methine and methyl groups respectively. The bands at 968 cm-1 and 1605 cm-1 Figure 1B, belong to y(C=C)str of alkenes groups in rubber. The peak at 719cm-1 Figure 1B, is of y(C-C)str aliphatic of the rubber chains. Those peaks at 1016cm-1 and 1160cm-1 represent the S(C-H)str aliphatic and in the plane groups of the rubber. The mentioned bands confirm their return to polyisoprene and polybutadiene rubber.
3.3.2. *H NMR Spectroscopy
The reclaimed rubber structure was studied by NMR spectroscopy using Bruker Biospin, Avance III 500, which has variable temperature unit B-VT 3000, Germany, using deuterated chloroform solvent. The proton
Peak list: 'H-NMR (500 MHz, CDC13) S 5.27, 5.02, 3.56, 3.23, 2.48, 2.32, 2.06, 1.98, 1.93, 1.57, 1.49, 1.15, 0.79, 0.77, 0.76, 0.74, -0.03.
Multiplets [1H-NMR (500 MHz, Chloroform-d) S 5.27 (s, 1H), 5.02 (s, 4H), 3.56 (s, 1H), 2.48 (s, 16H), 2.32 (s, 42H), 2.16 (t, J = 7.6 Hz, 3H), 2.06 (s, 17H), 1.95 (d, J = 20.8 Hz, 20H), 1.57 (s, 16H), 1.15 (s, 77H), 0.83 - 0.69 (m, 16H), -0.03 (s, 14H)].
The proton resonance (s, 16 H) Figure 2, at 1.57 is for the (=CH-) methine group of recovered rubber. The proton resonance (d, J=20.8Hz, 20 H) at o = 1.95 ppm belongs to the proton which is next to a double bond i.e. an allylic group of the rubber [18]. The proton resonance (s, 4H) and (s, 1H) Figure 2, at o = 5.02 ppm and o = 5.27 ppm those chemical
resonance Figure 2 shows proton resonance (m, 16H) at chemical shift o = 0.69-0.83 ppm, which belongs to the (-CH3) methyl group present in reclaimed rubber. The proton resonance (s, 77H) at 1.15 ppm belongs to the (-CH2-) methylene group of the rubber.
shifts belong to (-C=C-) alkene group of the reclaimed rubber. The studied protons and their chemical shifts confirm their returned to polybutadiene and polyisoprene rubber.
3.3.3. XRD Analysis
The x-ray diffraction of the recovered rubber was measured using a Philips x-ray (PW-1730) with a cu-ka radiation target with a nickel filter, with 30Kv current and 30mA voltages. The XRD pattern in Figure 3 and Table 1 shows the recovered rather has intensive peaks with a long 20 axis, which belong to the remaining inorganic additive and some remaining adsorbing agent. Most rubbers have an amorphous nature with a low crystalline percentage.
Table 1: XRD Data of recovered rubber
Pos. [°2Th.] Height [cts] FWHM [°2Th.] d-spacing [A] Rel. Int. [%] Tip width [°2Th.]
25.501 1986.52 0.2952 3.49305 100 0.3542
38.0345 536.67 0.2952 2.36591 27.02 0.3542
38.7971 171.62 0.2952 2.32114 8.64 0.3542
48.2033 755.2 0.2952 1.88790 38.02 0.3542
54.1159 514.14 0.2952 1.69477 25.88 0.3542
55.3068 555.23 0.246 1.66107 27.95 0.2952
5.6 5.4 5.2 5.0 4.8 4.6 4.4 4.2 4.0 3.8 3.6 3.4 3.2 3.0 2.8 2.6 2.4 2.2 2.0 1.8 1.6 1.4 1.2 l.O 0.8 0.6 0.4 0.2 O.O
5 (ppm)
Fig. 2. 1H-NMR spectrum of recovered rubber, using petroleum ether
However, the adsorbing agent Al2O3 has 35°; 37.7°, 43.8°, 52.5°, 57.4° 66.5° and 68.1° the following intensive peaks which are similar [19]. In addition, the adsorbed agent SiO2 has to those found in Figure 3 and Table 1, 25.4°, one broad peak and a long 20 axis at 22.6° [20].
62.854 508.89 0.1476 1.47856 25.62 0.1771
69.0264 231.65 0.1968 1.36065 11.66 0.2362
70.4675 183.63 0.2952 1.33631 9.24 0.3542
75.2178 272.78 0.3 1.26223 13.73 0.36
Fig. 3. XRD pattern of the rubber reclaimed by petroleum ether
The peaks of the adsorbing agent are very close to those of Figure 3, which means the rubber is not pure and is recovered with some impurities.
3.3.4. Thermal Analysis Reclaimed rubber was studied thermally (TGA, DTA, and DSC) using TA instrument SDT Q600, UB, NY, 14260, USA. The heat rate was 80°C/min, and AL203 was the reference.
The TGA thermogram Figure 4 and Table 2 shows the weight loss (%) at the initial decomposition temperature (IDT) of 92°C was 0.6% while it is 83.2% at 601°C the final decomposition temperature (FDT). At maximum decomposition temperature (Tmax) the weight loss was 44.8% and at crystalline decomposition temperature (Tcr) the weight loss was 77.7%.
The peaks of the adsorbing agent are very close to those of Figure 3, which means the rubber is not pure and is recovered with some impurities.
3.3.4. Thermal Analysis
Reclaimed rubber was studied thermally (TGA, DTA, and DSC) using TA instrument SDT Q600, UB, NY, 14260, USA. The heat rate was 80°C/min, and AL203 was the reference.
The TGA thermogram Figure 4 and Table 2 shows the weight loss (%) at the initial decomposition temperature (IDT) of 92°C was 0.6% while it is 83.2% at 601°C the final decomposition temperature (FDT). At maximum decomposition temperature (Tmax) the weight loss was 44.8% and at crystalline decomposition temperature (Tcr) the weight loss was 77.7%.
Table 2. Thermal data of the reclaimed rubber
Sample TAG weight loss % DTA °C/mg DSC W/g
Recover rubber IDT FDT TMAX T T cr Docomp. rate °C.min/mg Tg°C AHf J/g
0.6 83.2 44.8 77.7 0.007453 <0 +6.368
92 °C 601°c 358°C 475°C 473°C 473°C
The TGA data in Figure 4 and Table 2 show the recovered rubber has almost the same data as the polybutadiene [21] and polyisoprene [22].
The DTA thermogram of the recovered rubber in Figure 4 and Table 2, shows maximum decomposition rate of the rubber was very low
0.007453°C.min/mg at 473°C. Finally, the DSC thermogram (Figure 4 and Table 2) shows the heat of fusion AHf = +6.368 J/g at 473°C is an endothermic and thermally stable material and these specifications are for polybutadiene and polyisoprene rubber [23].
Fig. 4. TGA, DTA and DSC thermograms of rubber reclaimed by petroleum ether
3.3.5. FESEM Analysis
The FESEM analysis of recovered rubber was studied using the TESCAN MIRA FESEM instrument, Brno, Czech Republic. The FESEM image (Figure 5) shows elastic surface morphology and its materials are homogeneous. The folds and ripples appear clearly on the
sample surface. Moreover, the FESEM image shows the reclaimed rubber has an amorphous surface with crystal deficiency. All the aforementioned features indicate that the recovered rubber is a blend of polybutadiene and polyisoprene [24].
Fig. 5. FESEM image of recovered rubber
3.4. CB Recovered
CB can be recovered as by a product material from waste tire solution. Where soaking the tire waste powder in petroleum ether gives a turbid solution, but after reflux and hot filtration, it will give a clear filtrate and a black precipitate. The black precipitate beside the undissolved rubber waste in petroleum ether is mainly composed of CB, an adsorbing agent, and traces of inorganic additives. The precipitate was washed with different organic and inorganic solvents and burned inside the furnace at 500°C
± 10°C for the removal of contaminants. Finally, the collected CB was characterized.
3.4.1. XRD Analysis.
The XRD pattern of the recovered CB (Figure 6A) shows the collected material is amorphous and has only one intense peak at 47.8° a long 20 axis representing the graphite structure of the CB [25]. The hump-like peak at 24.0° a long 20 axis represents the featured peak of amorphicity of CB [26]. Finally, an XRD study Figure 6A shows the recovered CB is pure material that has an amorphous nature and the
individual peak was for graphite oxide present with the CB sample.
3.4.2. BET Studies
The specific surface area of the reclaimed CB particles and their pore area and other physical parameters were studied by BET measurement using surface area and porosimetry analyzer type BELSORP MINI II, Japan. The Langmuir-specific surface area is (as=126.87 m2.g-1), whereas the BET-specific surface area is (as=149.44 m2.g-1). The pore area between the CB particles from the BJH plot is (rp=4.61nm) with a specific surface area of (176.12 m2.g-1). On the other hand, the pore
volume of CB from the BET plot is (0.5089 cm3 g-1) with a pore diameter of (13.623nm). In general, the collected data from BET analysis shows the recovered CB has a high specific surface area, which means its particles are mesoporous and these are important properties for CB to become an industrial material.
3.4.3. FESEM Analysis
The FESEM image of the recovered CB (Figure 6B) shows clusters of CB particles have spherical shapes and are interspersed with numerous holes. The CB particles Figure 6B shows smooth surfaces and particles with uniform sizes.
Fig. 6. XRD pattern (A) and FESEM image (B) of the recovered CB
4. Conclusions
The chemical dissolution process used for the recovery of rubber and CB from waste tires depends on petroleum ether and a mixture of active absorbing agents (SiO2 and Al2O3) and shows an effective rubber recovery process from a quantitative and qualitative viewpoint. Petroleum ether, the hydrocarbon solvent, was shown to be highly effective in the reclamation of rubber due to its success in dissolving the rubber chains. Moreover, the use of 10 wt% of waste tire powder in petroleum ether and adding 70 % (w/w) SiO2 and 30% (w/w) AhO3 could reclaim 24 % (w/w) rubber and 20 % (w/w) CB from the total waste tire sample. At the same time, the used chemical process could almost completely regenerate petroleum ether, the hydrocarbon solvent beside the precipitator methanol, and be used successively in other batches.
The analyses of the recovered materials
have shown that the reclaimed rubber is a mixture of polybutadiene and polyisoprene, has an amorphous nature, is not pure, but still contains some additives. Thermally, the recovered rubber is stable and has a homogeneous morphology and elastic surface. The analyses of the recovered CB contain spherical particles with an amorphous nature and a high specific surface area, besides, they are mesoporous, which are good industrial properties for CB. The previous characterizations of both reclaimed rubber and CB show they have chemical, physical, and mechanical specifications qualified for renewal of scrap tires, sheet rubber, steps, bleachers, and playgrounds. Whereas, the reclaimed CB was shown to have a good specific absorption area, and its mesoporous properties are useful for reuse in tire manufacturing.
References
1. Thitithammawong A., Hayichelaeh C., Nakason W., Jehvoh N. The use of reclaimed rubber from waste tires for production of dynamically cured natural rubber/reclaimed rubber/polypropylene blends: Effect of reclaimed rubber loading // Journal of Metals, Materials and Minerals, 2019, V. 29(2), p. 98-104.
2. Fazli A., Rodrigue D. Recycling waste tires into ground tire rubber (GTR)/rubber compounds: a review // Journal of Composites Science, 2020, V. 4(3), p. 103.
3. Abnisa F., Daud W.M. Optimization of fuel recovery through the stepwise co-pyrolysis of palm shell and scrap tire // Energy Conversion and Management, 2015, V. 99, p. 334-345.
4. Nuzaimah M., Sapuan S.M., Nadlene R., Jawaid M. Recycling of waste rubber as fillers: A review // InlOP Conference Series: Materials Science and Engineering, 2018, V. 368, p. 012016
5. Mohaved S.O., Ansarifar A., Nezhad S.K., Atharyfar S. A novel industrial technique for recycling ethylene-propylene-diene waste rubber // Polymer Degradation and Stability, 2015, V. 111, p. 114-123.
6. Mangili I., Lasagni M., Huang K., Isayev A.I. Modelling and optimization of ultrasonic devulcanization using the response surface methodology based on central composite face-centred design // Chemometrics and Intelligent Laboratory Systems, 2015, V. 144, p. 1-10.
7. Jiang G., Zhao S., Luo J., Wang Y., Yu W., Zhang C. Microbial desulfurization for NR ground rubber by Thiobacillus ferrooxidans // Journal of Applied Polymer Science, 2010, V. 116(5), p. 2768-2774.
8. Diaz R., Colomines G., Peuvrel-Disdier E., Deterre R. Thermo-mechanical recycling of rubber: Relationship between material properties and specific mechanical energy // Journal of Materials Processing Technology, 2018, V. 252, p. 454-468.
9. Ghorai S., Bhunia S., Roy M., De D. Mechanochemical devulcanization of natural rubber vulcanizate by dual function disulfide chemicals // Polymer degradation and
stability, 2016, V. 129, p. 34-46.
10. Han W., Han D., Chen H. Pyrolysis of waste tires: a review // Polymers, 2023, V. 15(7), 1604.
11. Abraham E., Cherian B.M., Elbi P.A., Pothen L.A., Thomas S. Recent advances in the recycling of rubber waste // Recent developments in polymer recycling, 2011, V. 47, 100.
12. Myhre M., Saiwari S., Dierkes W., Noordermeer J. Rubber recycling: chemistry, processing, and applications // Rubber chemistry and technology, 2012, V. 85(3), p. 408-449.
13. Sedransk K.L., Kaminski C.F., Hutchings L.R., Moggridge G.D. The metathetic degradation of polyisoprene and polybutadiene in block copolymers using Grubbs second generation catalyst // Polymer degradation and stability, 2011, V. 96(6), p. 1074-1080.
14. Sultan A.M., Jabrail F.H. Decalin dissolving method for recover of styrene-butadiene rubber from scrap tires // J. Environ. Sci., 2019, V. 15, p. 145-153.
15. Abdulrahman A.S., Jabrail F.H. Treatment of Scrap Tire for Rubber and Carbon Black Recovery // Recycling 2022, V. 7(3), 27.
16. Stickney P.B., Falb R.D. Carbon black-rubber interactions and bound rubber // Rubber Chemistry and Technology, 1964, V. 37(5), p. 1299-340.
17. Maria H.J., Lyczko N., Nzihou A., Mathew C., George S.C., Joseph K., Thomas S. Transport of organic solvents through natural rubber/nitrile rubber/organically modified montmorillonite nanocomposites // Journal of Materials Science, 2013, V. 48, p. 5373-86.
18. Bahani M., Laupretre F., Monnerie L. NMR and DSC investigations of the miscibility of blends of cis-1, 4-polyisoprene with polybutadienes of different microstructures // Journal of Polymer Science Part B: Polymer Physics, 1995, V. 33(2), p. 167-78.
19. Mohammed A.A., Khodair Z.T., Khadom A.A. Preparation and investigation of the structural properties of a-Al2O3 nanoparticles using the sol-gel method //
Chemical Data Collections, 2020, V. 29, 100531.
20. Dubey R.S., Rajesh Y.B., More M.A. Synthesis and characterization of SiO2 nanoparticles via sol-gel method for industrial applications // Materials Today: Proceedings, 2015, V. 2(4-5), p. 3575-9.
21. Jiang D.D., Levchik G.F., Levchik S.V., Wilkie C.A. Thermal decomposition of cross-linked polybutadiene and its copolymers // Polymer degradation and stability, 1999, V. 65(3), p. 387-94.
22. Chen F., Qian J. Studies on the thermal degradation of cis-1, 4-polyisoprene // Fuel. 2002, V. 81(16), p. 2071-7.
23. Li N., Zong X., Li H., He A., Zhang X. Aging behaviors of trans-1, 4-poly (isoprene-co-butadiene) copolymer rubber // Polymer Degradation and Stability, 2021, V. 183, 109456.
24. Ding Y., Wang J., Song S. Synthesis and characterization of linear polyisoprene supramolecular elastomers based on quadruple hydrogen bonding // Polymers, 2020, V. 12(1), 110.
25. Kun P., Wéber F., Balázsi C. Preparation and examination of multilayer graphene nanosheets by exfoliation of graphite in high efficient attritor mill // Central European Journal of Chemistry, 2011, p. 47-51.
26. Escamilla-Mejía J.C., Hidalgo-Carrillo J., Martín-Gómez J., López-Tenllado F.J., Estévez R., Marinas A., Urbano F.J. Biochars from Olive Stones as Carbonaceous Support in Pt/TiO2-Carbon Photocatalysts and Application in Hydrogen Production from Aqueous Glycerol Photoreforming // Nanomaterials, 2023, V. 13(9), 1511.
TULLANTI §iNL9RD9N REZiNiN T9KRAR EMALI Ü£ÜN EKOLOJi ÜSULUN
KiMYOVi XÜSUSiYY9TL9Ri
R.J.N. AL-Cuburi, F.H. Cabrayil*
Kimya §öbdsi, Elm Kolleci, Mosul Universiteti, Mosul, iraq *e-mail: fawzijabrail@uomosul. edu. iq
Xülasa: Tullanti takarlarin takrar emali bir 9ox tadqiqat9ilarin tadqiqat obyektidir. Bu tadqiqatlarda takar rezininin (TR) va texniki karbonun (TC) tullanti takarlardan barpasi kimyavi hallolmadan asilidir. §in tozunu hall etmak ü9ün neft efirindan istifada edilmi§ va alinmi§ qara mahlul 140°C-da iki saat arzinda tarkibinda silisium oksid (SiO2) va alüminium oksid (Al2O3) olan adsorbentlarla qaynadilmi§dir. Sonra mahlul süzülmü§ va naticada §affaf kau9ukun mahlulu va TC 9öküntüsü alinmi§dir, istifada edilmi§ neft efiri isa tamamila regenerasiya edilmi§dir. istifada olunan takarlarin ümumi miqdarina nazaran regenerasiya edilan kau9uk kütla faizi 24%, TC isa 20% ta§kil etmi§dir. Barpa edilmi§ rezin va onun funksional qruplari 1H-NMR va iQ spektroskopiya üsullari ila tadqiq olunmu§ va müayyan edilmi§dir ki, o polibutadien qari§iqli poliizoprendan ibaratdir. Rentgen difraksiya, FESEM va termiki analiz (TGA, DTA va DSC) üsullarinin naticalari göstarmi§dir ki, barpa olunan rezin elastikdir, termiki sabitdir va tarkibinda bazi qeyri-üzvi a§qarlar var. Digar tarafdan, texniki karbonun BET (Brunauer-Emmett-Teller) analizi göstarir ki, o, yüksak xüsusi sath sahasina (as = 149,44 m2.g-1) va orta diametra (13.623 nm) malik mezomasamali materialdir. Texniki karbonun hissaciklarinin öl9üsü, qurulu§u va sath kimyasi müvafiq olaraq rentgen difraksiya, FESEM va BET üsullari ila tadqiq olunaraq, yüksak adsorbsiya xassalarina malik oldugu müayyanla§dirilmi§dir.
A?ar sözlari: takarlarin takrar emali, rezin, neft efiri, karbon qarasi, silisium 4-oksid, alüminium oksidi.
ХИМИЧЕСКАЯ ХАРАКТЕРИСТИКА ЭКОЛОГИЧЕСКОГО МЕТОДА ПЕРЕРАБОТКИ РЕЗИНЫ ИЗ ОТХОДНЫХ ШИН
Р.Дж.Н. АЛ-Джубури, Ф.Х. Джабраил*
Кафедра химии, Научный колледж Мосульского университета, Мосул, Ирак *e-mail: fawzijabrail@,uomosul. edu. iq
Резюме: Переработка отработанных шин является целью многих исследований, в которых метод химического растворения зависит от извлечения шинной резины (ШР) и технического углерода (ТУ) из отработанных шин. Для растворения порошка шин использовался петролейный (нефтяной) эфир, и был получен черный раствор, который после кипячения с обратным холодильником при 140°C в течение двух часов со смесью адсорбентов, включающих диоксид кремния (SiO2) и оксид алюминия (Al2O3), был отфильтрован, в результате чего получили прозрачный фильтрат каучука и осадок ТУ, а использованный петролейный эфир полностью регенерировали. Каучук был регенерирован с массовым процентом 24% (по весу), а ТУ - с массовым процентом 20% (по весу) от общего количества использованных шин. Восстановленный каучук был охарактеризован, а его функциональные группы были изучены с помощью ^-ЯМР и ИК-спектроскопии, которые показали, что каучук представляет собой полиизопрен, смешанный с полибутадиеном. Исследования рентгеновской дифракции, FESEM и термический анализ (ТГА, ДТА и ДСК) показали, что восстановленный каучук является аморфным, эластичным по природе, термически стабильным с эндотермическим поведением, и содержит некоторые неорганические примеси. С другой стороны, BET (Brunauer-Emmett-Teller) анализ технического углерода показывает, что это мезопористый материал с высокой удельной поверхностью (as = 149,44 м2г-1) и порами со средним диаметром (13,623 нм). Размер частиц, структура и химия поверхности регенерированного ТУ были измерены соответственно с помощью XRD, BET и FESEM, и было выявлено, что он обладает превосходными адсорбционными свойствами. Ключевые слова: переработка шин, резина, петролейный эфир, технический углерод, диоксид кремния, оксид алюминия.
