Received: 01 October 2019
Accepted: 19 February 2020
Published: 01 July 2020
DOI: https://doi.org/10.26850/1678-4618eqj.v45.3.2020.p28-36
Abstract: Non-edible fats are a common renewable feedstock for the biofuels production to avoid partially the use of edible feeds and fossil fuels. The aim of this work was the use of waste rendering fat to produce pyrolyzed and hydrogenated oils. The feedstock was hydrolyzed producing free fatty acids and glycerol + residues. The free fatty acids were pyrolyzed (with and without metal sulfides metal supported catalyst) or hydrotreated separately. An autoclave closed hermetically in nitrogen (pyrolysis) or hydrogen (hydrotreatment) atmosphere was used. Gaseous products were analyzed by GC‑FID/TCD. Liquid products were analyzed by Simulated Distillation (ASTM D2887) and FT-IR (attenuated total reflectance technique). For the pyrolysis, the main gaseous products were carbon dioxide, methane, ethane, and propane. For the hydrotreatment, the total amount of gases produced was much lower being the main product the carbon dioxide. For liquids, the hydrotreatment of the free fatty acids produced the respective hydrocarbons by decarboxylation reaction and the pyrolysis produced a mixture of compounds with lighter boiling ranges compared to the original free fatty acids. The use of a metal sulfide metal supported catalyst in the pyrolysis led to a higher amount of hydrogen production. but similar boiling range liquid products compared to the non-catalytic test.
Keywords: animal fat, pyrolysis, hydrodeoxygenation, hydrotreatment, free fatty acids.
1. Introduction
The petroleum location in unstable territories, the fossil fuel restrictions by law and the greenhouse carbon dioxide production led to a high need in biofuels production. Concretely, the revised Renewable Energy Directive (EU) 2018/2001, adopted in December 2018 by the European Parliament and by the Council of Ministers of the European Union, promotes the use of energy from renewable sources in the European Union. In addition, the European Union is avoiding the use of croplands for the biofuels production. In 2015 new rules came into effect to reduce the risk of indirect land use change (Renewable Energy Directive 2009/28/EC and the Fuel Quality Directive 2009/30/EC). Therefore, the use of wastes to produce biofuels can be considered as a necessary alternative for the biofuels production.
Three types of biofuels are considered worldwide: (i) first-generation biofuels (conventional ones such as fatty acids methyl esters – FAME), (ii) second-generation biofuels are produced from non-edible raw materials and can be produced by catalytic hydrotreatment and (iii) third-generation biofuels products from algae feedstock1. In the case of cold weather countries, the using of first-generation biofuels (biodiesel) can be a problem because they present a high freezing point or low energy density (due to its oxygen content). Second-generation biofuels are nowadays produced, in refineries, by catalytic hydro-processing to obtain hydrocarbons2-5. Particularly, non-edible feedstocks are being using in refineries.. Concretely, the use of waste animal fat1,7 is considered as a good option for the biofuels production. Third-generation biofuels can be considered as a key technology. However, this technology needs to be still improved and implemented (not yet used on an industrial scale)8.
Rendering fat (RF) is a non-edible waste feedstock which can be produced from the waste of slaughterhouses and carcasses of livestock and it is considered as a cheap material for green diesel production9. However, RF contains usually high phosphorous and metal contents which could affect the catalytic activity9. RF is produced in Czech Republic in a relatively large amount so it can be considered as an available and cheap feedstock in this zone-area10. The amount registered of rendering fat, sludge, meat and bone meals residues produced in Czech Republic (2018) were 36780 tons all together11. The lipid wastes generated by commercial enterprises in Czech Republic (2017) classified by groups were the next: Spent waxes and fats 1640 tons, waste fats and oils 21979 tons, edible fat, and oils 2971 tons and other greases and oil mixtures 374 tons12.
Biofuels of second generation can be obtained by hydrodeoxygenation (HDO) or by pyrolysis. The pyrolysis is an extensively studied pathway to convert triacylglycerols to hydrocarbons. However, the study of pyrolysis for free fatty acids has received lower attention13,14. The aim of this work was to evaluate the free fatty acids (from rendering fat) processing by catalytic and non-catalytic pyrolysis to fuels and chemicals using metal sulfide supported catalyst and compare these results with standard hydrodeoxygenation (HDO) process by using the same catalyst. NiW sulfide supported on SiO2-Al2O3 is a commercial catalyst. This material was used instead standard NiMo or CoMo (used standardly for HDO reactions) supported catalysts with the added aim of cracking the free fatty acids to shorter molecules producing gases, gasoline and diesel fractions which could be then be evaluated for being used for fuels or petrochemistry.
2. Experimental
2.1. Materials
Waste RF (from dead animals, pig (80 wt.%) also including chicken (14 wt.%) and cow (6 wt.%) residues) used in a previous work7 was analysed (metal and elemental C, H, N, S analyses) as shown in Tab. 1.
Oleic acid Lach-ner (Oleic acid min. 70% pure/1000 ml; CAS: 67701-08-0; EINECS: 266-932-7; Assay fatty acids (as oleic acid) min. 97%; Refractive index 1.460 - 1.463) was used as model molecule for pyrolysis.
Dimethyl disulfide (DMDS) ≥ 99.0% Sigma Aldrich was used for the commercial catalyst sulfidation. NiW/SiO2–Al2O3 reference material as catalyst with a 6.4 and 17.5 wt.% of Ni and W contents respectively (200 m2 g-1 of BET surface) was tested.
2.2. Tests
Experiments were performed in an autoclave 4575/76 with a “4848B” controller delivered by Parr Instruments Company. The scheme of the overall work-process is exposed in Fig. 1. The catalyst was activated using DMDS. 20 g of DMDS and 5 g of catalyst were used for each activation. DMDS and catalysts were introduced into the reactor-autoclave. Then, the reactor was flushed with nitrogen to remove air residues and finally flushed and pressurized to 5 MPa with hydrogen. Temperature was then increased from ambient temperature (24 °C) to 340 °C with a rate of 8.3 °C min-1. At this temperature (340 °C), the pressure was increased to 15 MPa (by H. flow) and the reactor was kept at these conditions for 1 h. The activation period was followed by the reactor external cooling by air flow (cooling rate approx. 4.5 °C min-1) to ambient temperature and stabilization for 1 h.
For hydrolysis of rendering fat, HDO and pyrolysis tests similar procedures were performed. Three types of tests were carried out:
A) For hydrolysis, two tests were performed, 50 g of rendering fat, 50 g of distilled water and 2 g of sulfuric acid were used. The reactor was under nitrogen atmosphere with no added pressure. Then, it was heated to 250 °C and maintained at this temperature during 1 h with 500 rpm of stirring rate. After reaction, the system was externally cooled by air flow (approx. 4.5 °C min−1) to room temperature and stabilized for 20 h. After that, the liquid was collected for analysis. After the hydrolysis the glycerol was considered as side product while free fatty acids were further processed in two ways: in a pyrolysis or in HDO reaction.
B) For pyrolysis, 18.4 g of free fatty acids (FFA) and 3.7 g of activated-sulfide NiW/SiO2-Al2O3 catalyst were used. The autoclave was tested in nitrogen with no added pressure at room temperature and then heated to 420 °C with a heating rate of 8.3°C min−1. Reaction was conducted stirring with a rate of 500 rpm. Then, the system was externally cooled. Afterwards, the gas was sampled at 30 °C and the autoclave depressurized. After that, the autoclave was opened, and the liquid collected for analysis. A blank probe, with 20 g of FFA and without the use of a catalyst and pyrolysis with oleic acid as a model molecule was also done, according to the above described procedure.
C) For HDO reaction, 20 g of FFA and 5 g of sulfide NiW/SiO2-Al2O3 commercial catalyst were placed in the autoclave. The reactor was then flushed with nitrogen and pressurized with hydrogen to 7 MPa. Then, the reactor was heated up to 365 °C. The system was maintained at 365 °C for 1 h and stirred with 500 rpm. The, the system was cooled, and gas sampled at 30 °C. Finally, the autoclave was depressurized and opened for collecting the liquid.
2.3. Products analyses
Liquid products of the reaction were characterized by simulated distillation (SimDist) using gas chromatography according to the ASTM D2887 and attenuated total reflectance FT-IR technique (ATR). Gaseous products were analysed by RGA-GC (Method Refinery Gas Analysis, Agilent).
3. Results and Discussion
First, the hydrolysis of the RF was performed. The hydrolysis of triglycerides (Triglyceride + 3 H2O ⇌ 3 Fatty Acids + Glycerol), in the presence of water, produces free fatty acids and glycerol (the sulfuric acid addition led to the acid hydrolysis). In this case, the hydrolysis reaction was carried out not only to produce free fatty acids and separate them from the glycerol but also to remove other possible water-soluble compounds included previously in the original rendering fat (not triglycerides).
Two tests with similar results (Tab. 2) were carried out. The simulated distillation of the FFA product presented about 90 wt.% of pure FFA (Fig. 2). After hydrolysis tests no gaseous samples (C1-C4 gases) were produced. Glycerol and organic phases were separated by centrifugation. The organic phase SIMDIS is shown in Fig. 2.
The main products in the organic phase were FFA as shown in Fig. 2 (boiling range 340 – 420 °C). The SIMDIS was calibrated and as shown in a previous work7, the boiling range of 50 – 220 °C is related to C5-C12 compounds, 220-340 °C to C12-C19, 340-420 °C is mainly related to the free fatty acids but also to C20 + compounds and > 420 °C is related mainly to mono, di and triglycerides. Then, these FFA were used as feedstock for pyrolysis.
Next, after obtaining the FFA, two tests were carried out with FFA. One test using sulfide commercial catalyst and one test without catalyst. Oleic acid was also used as model molecule to perform a pyrolysis test for comparing results with those obtained using FFA from RF.
The pyrolysis led to an effective conversion to liquid and gaseous products different than feedstock as shown in Fig. 3. The SimDis and RGA analyses together demonstrated that the pyrolysis was effective producing lighter products compared to the free fatty acids (FFA) due to a cracking process. As shown in Tab. 2, the use of a sulfide catalyst increased the light liquid production and decreased the number of gaseous products C1-C6. The amount of gases and liquids compared between FFA and oleic acid tests are different due to the presence of other FFA in the animal fat (not only oleic acid). HDO test clearly led to hydrocarbons (Fig. 3) especially to products C15-C18 according to calibrated RGA methodology peaks. This result is confirmed by ATR (Fig. 4) not showing signals for oxygenated compounds.
The gaseous products composition is shown in Fig. 5. The use of catalyst in nitrogen tests produced an increment in the hydrogen composition in gas products. Thus, the use of a sulfide catalyst led to a higher amount% of hydrogen in the product but a total less amount of gases as consequence of the higher production of carbon dioxide in nitrogen tests. In the case of the oleic acid, the amount% composition is similar to the FFA test without catalyst in nitrogen. So, the gasification activity was similar in selectivity but different in the total production of gases. The total production of gases could be favored by the other compounds present in the animal fat.
HDO test clearly showed four main increments of the amount distilled at 270, 286, 305 and 318 °C which are related to C15-C18 hydrocarbons, respectively. Two significative increments of amount distilled were also shown for catalytic FFA pyrolysis tests (C15 and C17 hydrocarbons zone) indicating that the use of the metal sulfide catalyst led to a higher amount of C15, C17 hydrocarbons. However, in pyrolysis no hydrogen was used so these hydrocarbons could be produced by the hydrogen produced by the initial FFA hydrogen loss originated during the test.
ATR absorbance spectra of liquid products in the frequency range between 690 and 4000 cm-1 are shown in Fig. 5. In general, for triglycerides and hydrogenated vegetable oils, the bands at 2925, 2965 cm−1 are related to the stretching vibrations of the CH. and CH. groups14. The absorption at 3100–3000 cm−1, 1603 cm−1, 1500 cm−1 and 900–700 cm−1 is typical for aromatic compounds14. The band at 1709 cm−1 can be attributed to the presence of free fatty acids and the band at 1746 cm-1 to the ester carbonyl functional group of the triglycerides which was only present in the feedstock14. Concretely, the band at 1746 cm-1 was only found for the feedstock confirming the hydrolysis of the animal fat to FFA. However, for the feedstock and hydrolysis products, the band at 1182 cm-1 can be attributed to the stretching vibration of the C-O ester groups indicating a non-complete hydrolysis being this result in agreement with SimDis (amounts distilled at higher temperatures than 420 °C). At 727 cm-1 was found a band attributed to the overlapping of the CH. rocking vibration and the out-of-plane vibration of cis-disubstituted olefins14. The shoulder at 2890-3009 cm−1 C-H (stretching vibration of the cis-double bond (=CH)) found for the feedstock was also present in the liquid products.
Although the pyrolysis and HDO reaction of oleic acid and rendering fat were already studied15-18, to the best of our knowledge, comparing with literature, a comparison between non-catalytic and catalytic pyrolysis of rendering-fat using sulfide catalyst was not found. In addition, the use of oleic acid led to know the possible differences by using real feedstock and this model molecule.
4. Conclusions
Several tests of hydrolysis, HDO and pyrolysis were performed obtaining good yields to free fatty acids (hydrolysis) and hydrocarbons (HDO). Pyrolysis tests of FFA were carried out with and without catalyst to see its influence. The use of catalyst led to an increment in hydrogen production, decrease in total gas production and to higher amounts of C15 and C17 hydrocarbons compared to non-catalytic pyrolysis. Lighter olefins, aromatics and hydrocarbons were produced after pyrolysis.
Acknowledgements
This publication is a result of the project CACTU, Reg. No. CZ.02.1.01/0.0/0.0/17_049/0008397, which has been co-financed by European Union from the European Regional Development Fund through the Operational Programme Research, Development and Education. This project has also been financially supported by the Ministry of Industry and Trade of the Czech Republic which has been providing institutional support for long-term conceptual development of research organization. The project CACTU has been integrated into the National Sustainability Programme I of the Ministry of Education, Youth and Sports of the Czech Republic (MEYS) through the project Development of the UniCRE Centre (LO1606). The result was achieved using the infrastructure of the project Efficient Use of Energy Resources Using Catalytic Processes (LM2015039) which has been financially supported by MEYS within the targeted support of large infrastructures.
References
[1] de Paz Carmona, H., de la Torre Alfaro, O., Alayón, A. B., Vázquez, M. A. R., Hernández, J. J. M., Co-processing of straight run gas oil with used cooking oil and animal fats, Fuel 254 (2019) 115583. https://doi.org/10.1016/j.fuel.2019.05.166.
[2] Bezergianni, S., Dimitriadis, A., Kikhtyanin, O., Kubička, D., Refinery co-processing of renewable feeds, Progress in Energy and Combustion Science 68 (2018) 29-64. https://doi.org/10.1016/j.pecs.2018.04.002.
[3] Kovács, S., Boda, L., Leveles, L., Thernesz, A., Hancsók, J., Catalytic hydrotreating of triglycerides for the production of bioparaffin mixture, Chemical Engineering Transactions 21 (2010) 1321-1326. https://doi.org/10.3303/CET1021221.
[4] Arun, N., Sharma, R. V., Dalai, A. K., Green diesel synthesis by hydrodeoxygenation of bio-based feedstocks: Strategies for catalyst design and development, Renewable and Sustainable Energy Reviews 48 (2015) 240-255. https://doi.org/10.1016/j.rser.2015.03.074.
[5] Dujjanutat, P., Kaewkannetra, P., Production of bio-hydrogenated kerosene by catalytic hydrocracking from refined bleached deodorised palm/ palm kernel oils, Renewable Energy 147 (1) (2020) 464-472. https://doi.org/10.1016/j.renene.2019.09.015.
[6] Chrysikou, L. P., Dagonikou, V., Dimitriadis, A., Bezergianni, S., Waste cooking oils exploitation targeting EU 2020 diesel fuel production: Environmental and economic benefits, Journal of Cleaner Production 219 (2019) 566-575. https://doi.org/10.1016/j.jclepro.2019.01.211.
[7] Hidalgo, J. M., Tišler, Z., Vráblík, A., Velvarská, R., Lederer, J., Acid-modified phonolite and foamed zeolite as supports for NiW catalysts for deoxygenation of waste rendering fat, Reaction Kinetics, Mechanisms and Catalysis 126 (2) (2019) 773-793. https://doi.org/10.1007/s11144-018-1510-1.
[8] Correa, D. F., Beyer, H. L., Fargione, J. E., Hill, J. D., Possingham, H. P., Thomas-Hall, S. R., Schenk, P. M., Towards the implementation of sustainable biofuel production systems, Renewable and Sustainable Energy Reviews 107 (2019) 250-263. https://doi.org/10.1016/j.rser.2019.03.005.
[9] Baladincz, P., Hancsók, J., Fuel from waste animal fats, Chemical Engineering Journal 282 (2015) 152-160. https://doi.org/10.1016/j.cej.2015.04.003.
[10] Víšek, L., Pokorný, M., Production of fatty acid esters (Biodiesel Oil) from waste animal fats, Chemicke Listy 107 (2013) 476-478.
[11] Statistics on the energy use of waste and alternative fuels (1989–2018), Results of statistical surveys. Ministry of Industry and Trade of the Czech Republic. Secondary energy sources Report, 2019 https://www.mpo.cz/cz/energetika/statistika/obnovitelne-zdroje-energie/statistika-energetickeho-vyuzivani-odpadu-a-alternativnich-paliv-1989-_-2018--245185/.
[12] Generation, Recovery and Disposal of Waste – 2017, Czech Statistical Office, 2018. https://www.czso.cz/csu/czso/generation-recovery-and-disposal-of-waste-2017.
[13] Toteva, V., Georgiev, A., Topalova, L., Oxidative desulphurization of light cycle oil: Monitoring by FTIR spectroscopy, Fuel Processing Technology 90 (7-8) (2009) 965-970. https://doi.org/10.1016/j.fuproc.2009.03.012.
[14] Vlachos, N., Skopelitis, Y., Psaroudaki, M., Konstantinidou, V., Chatzilazarou, A., Tegou, E., Applications of Fourier transform-infrared spectroscopy to edible oils, Analytica Chimica Acta 573-574 (2006) 459-465. https://doi.org/10.1016/j.aca.2006.05.034.
[15] Leon, M., Garcia, A. N., Marcilla, A., Martinez-Castellanos, I., Navarro, R., Catala, L., Thermochemical conversion of animal by-products and rendering products, Waste Management 73 (2018) 447-463. https://doi.org/10.1016/j.wasman.2017.08.010.
[16] Asomaning, J., Mussone, P., Bressler, D. C., Thermal deoxygenation and pyrolysis of oleic acid, Journal of Analytical and Applied Pyrolysis 105 (2014) 1-7. https://doi.org/10.1016/j.jaap.2013.09.005.
[17] Asomaning, J., Mussone, P., Bressler, D. C., Thermal cracking of free fatty acids in inert and light hydrocarbon gas atmospheres, Fuel 126 (2014) 250-255. https://doi.org/10.1016/j.fuel.2014.02.069.
[18] Asomaning, J., Mussone, P., Bressler, D. C., Pyrolysis of polyunsaturated fatty acids, Fuel Processing Technology 120 (2014) 89-95. https://doi.org/10.1016/j.fuproc.2013.12.007.