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PVC plasticizer from trimethylolpropane trioleate: synthesis, properties, and application

Abstract

A new oleic acid derivative plasticizer, epoxidized trimethylolpropane trioleate (EPO), has been synthesized and its application in PVC formulations compared with di(2-ethylhexyl) 1,2-cyclohexanoate (DOCH/DEHCH), a commercial phthalate-free plasticizer of petrochemical origin. EPO and their blends with DOCH were added to PVC resin (50 PHR) and the plasticized PVC has been characterized by thermal and mechanical measurements. EPO demonstrated good compatibility with the PVC resin improving the thermal stability and elongation at break. Due to EPO high molar mass, a slight increase in the glass transition temperature and hardness was observed as the content of EPO in the plasticizer blend increased. The results indicate that EPO is a potential plasticizer for PVC when pure and, by replacing 50% of DOCH, the PVC compound shows similar properties to pure DOCH, but better elongation at break and thermal stability.

Keywords:
plasticizers; PVC; renewable sources; epoxidized trimethylpropane trioleate; dioctyl cyclohexanoate

1. Introduction

Poly(vinyl chloride), PVC, is the most widely used thermoplastic in commercial and household applications, such as toys, medical supplies, packaging materials, and others[11 Hosney, H., Nadiem, B., Ashour, I., Mustafa, I., & El‐Shibiny, A. (2018). Epoxidized vegetable oil and bio‐based materials as PVC plasticizer. Journal of Applied Polymer Science, 135(20), 46270. http://dx.doi.org/10.1002/app.46270.
http://dx.doi.org/10.1002/app.46270...
]. This range of uses is due to the large number of additives that can be incorporated into PVC, originating from rigid to flexible or translucent to opaque products[22 Shah, B. L., & Shertukde, V. V. (2003). Effect of plasticizers on mechanical, electrical, permanence, and thermal properties of poly (vinyl chloride). Journal of Applied Polymer Science, 90(12), 3278-3284. http://dx.doi.org/10.1002/app.13049.
http://dx.doi.org/10.1002/app.13049...
].The most used additives in PVC are plasticizers. These compounds can efficiently interact with the polymer due to the existence of the polarized C-Cl bond in PVC, which allows the association between the plasticizer and polymer chain during the product's lifetime[33 Unar, I. N., Soomro, S. A., & Aziz, S. (2010). Effect of various additives on the physical properties of polyvinylchloride resin. Pakistan Journal of Analytical & Environmental Chemistry, 11(2), 44-50. Retrieved in 2020, December 17, from http://pjaec.pk/index.php/pjaec/article/view/107/117
http://pjaec.pk/index.php/pjaec/article/...
,44 Daniels, P. H. (2009). A brief overview of theories of pvc plasticization and methods used to evaluate pvc‐plasticizer interaction. Journal of Vinyl & Additive Technology, 15(4), 219-223. http://dx.doi.org/10.1002/vnl.20211.
http://dx.doi.org/10.1002/vnl.20211...
].

Many plasticizers used in PVC are derived from petroleum and have phthalates in their structure. Some studies show that these compounds, containing a phthalate fraction, are very toxic and can cause disturbances in the human reproductive system[55 Latini, G., De Felice, C., & Verrotti, A. (2004). Plasticizers, infant nutrition and reproductive health. Reproductive Toxicology (Elmsford, N.Y.), 19(1), 27-33. http://dx.doi.org/10.1016/j.reprotox.2004.05.011. PMid:15336709.
http://dx.doi.org/10.1016/j.reprotox.200...

6 Tan, J., Zhang, S., Lu, T., Li, R., Zhong, T., & Zhu, X. (2019). Design and synthesis of ethoxylated esters derived from waste frying oil as anti-ultraviolet and efficient primary plasticizers for poly (vinyl chloride). Journal of Cleaner Production, 229, 1274-1282. http://dx.doi.org/10.1016/j.jclepro.2019.04.395.
http://dx.doi.org/10.1016/j.jclepro.2019...

7 Radke, E. G., Galizia, A., Thayer, K. A., & Cooper, G. S. (2019). Phthalate exposure and metabolic effects: a systematic review of the human epidemiological evidence. Environment International, 132, 104768. http://dx.doi.org/10.1016/j.envint.2019.04.040. PMid:31196577.
http://dx.doi.org/10.1016/j.envint.2019....
-88 Tickner, J. A., Schettler, T., Guidotti, T., McCally, M., & Rossi, M. (2001). Health risks posed by use of Di‐2‐ethylhexyl phthalate (DEHP) in PVC medical devices: a critical review. American Journal of Industrial Medicine, 39(1), 100-111. http://dx.doi.org/10.1002/1097-0274(200101)39:1<100::AID-AJIM10>3.0.CO;2-Q. PMid:11148020.
http://dx.doi.org/10.1002/1097-0274(2001...
]. The restriction of the use of phthalates, in particular dioctyl phthalate (DOP), as a plasticizer is increasing. In the United States, for example, the Environmental Protection Agency (EPA) has already banned its use in toys that go in children's mouths. Currently, there are many alternative plasticizers to DOP, one of which are secondary alcohol esters of cyclohexanecarboxylic acids, that have been used to prepare flexible PVC compounds with enhanced low temperature flexibility, low toxicity, and improved resistance to outdoor aging[99 Bui, T. T., Giovanoulis, G., Cousins, A. P., Magnér, J., Cousins, I. T., & de Wit, C. A. (2016). Human exposure, hazard and risk of alternative plasticizers to phthalate esters. The Science of the Total Environment, 541, 451-467. http://dx.doi.org/10.1016/j.scitotenv.2015.09.036. PMid:26410720.
http://dx.doi.org/10.1016/j.scitotenv.20...
,1010 Colle, K. S., Stanat, J. E. R., Reinoso, J. J., & Godwin, S. (2010). US Patent No. 20100305250A1. USA: USPTO. Retrieved in 2020, December 17, from https://patents.google.com/patent/US20100305250A1/en
https://patents.google.com/patent/US2010...
].

Among the commercial non-toxic plasticizers used, di(2-ethylhexyl) 1,2-cyclohexanoate (DOCH) stands out as a highly efficient and phthalate-free primary plasticizer[1111 Ou, Y., Ding, X., & Zhang, L. (2014). Synthesis and application of an alternative plasticizer Di (2‐Ethylhexyl)‐1, 2‐cyclohexane dicarboxylate. Journal of Applied Polymer Science, 131(2), n/a. http://dx.doi.org/10.1002/app.39763.
http://dx.doi.org/10.1002/app.39763...

12 Hou, L., Fan, C., Liu, C., Qu, Q., Wang, C., & Shi, Y. (2018). Evaluation of repeated exposure systemic toxicity test of PVC with new plasticizer on rats via dual parenteral routes. Regenerative Biomaterials, 5(1), 9-14. http://dx.doi.org/10.1093/rb/rbx020. PMid:29423263.
http://dx.doi.org/10.1093/rb/rbx020...
-1313 Hab, S. A., Talpur, F. N., Baig, J. A., Afridi, H. I., Surhio, M. A., & Talpur, M. K. (2018). Leaching and exposure of phthalates from medical devices; health impacts and regulations. Environmental Contaminants Reviews, 1(2), 13-21. http://dx.doi.org/10.26480/ecr.02.2018.13.21.
http://dx.doi.org/10.26480/ecr.02.2018.1...
]. Schilling and Kelly[1414 Schilling, C. L. 3rd, & Kelly, K. K. (2018). U.S. Patent US:.2018/0105673 A1. Kingsport: U.S. Patent and Trademark Office.] found that DOCH is more compatible with PVC in formulations with high contents of plasticizer (100 PHR or more) and, the blend of DOCH with other plasticizers showed a better performance in the range of 60-120 PHR. However, with the increasing restrictions of environmental policies and the imminent depletion of oil, more and more people are opting to replace fossil plasticizers with ones from renewable sources[1515 Mizik, T., & Gyarmati, G. (2021). Economic and sustainability of biodiesel production: a systematic literature review. Cleanroom Technology, 3(1), 19-36. http://dx.doi.org/10.3390/cleantechnol3010002.
http://dx.doi.org/10.3390/cleantechnol30...
].

Vegetable oil-based plasticizers have a high potential to replace petrochemical plasticizers. Among the vegetable plasticizers, epoxidized soybean oil (ESO) stands out, being among the green plasticizers recognized by the Food and Drugs Administration of the United States[1616 Jamarani, R., Erythropel, H. C., Nicell, J. A., Leask, R. L., & Marić, M. (2018). How green is your plasticizer? Polymers, 10(8), 834. http://dx.doi.org/10.3390/polym10080834. PMid:30960759.
http://dx.doi.org/10.3390/polym10080834...
].

Epoxidized soybean oil (ESO) is known as an additive in plasticized PVC since it functions both as a plasticizer and stabilizer. Therefore, Karmalm et al.[1717 Karmalm, P., Hjertberg, T., Jansson, A., Dahl, R., & Ankner, K. (2009). Network formation by epoxidised soybean oil in plastisol poly (vinyl chloride). Polymer Degradation & Stability, 94(11), 1986-1990. http://dx.doi.org/10.1016/j.polymdegradstab.2009.07.029.
http://dx.doi.org/10.1016/j.polymdegrads...
] studied ESO as a primary PVC plasticizer in the formation of plastisols and noticed that after aging the material became stiff and opaque, due to the formation of a cross-linking network between ESO and PVC. However, using a suspension PVC resin,it was not observed, concluding that the crosslinking reaction was catalyzed by some component of the PVC plastisol preparation, which was avoided by the addition of stabilizers.

Mao et al.[1818 Mao, D., Chaudhary, B. I., Sun, B., Shen, C.-Y., Yuan, D., Dai, G.-C., Li, B., & Cogen, J. M. (2015). Absorption and migration of bio‐based epoxidized soybean oil and its mixtures with tri (2‐ethylhexyl) trimellitate in poly (vinylchloride). Journal of Applied Polymer Science, 132(19), n/a. http://dx.doi.org/10.1002/app.41966.
http://dx.doi.org/10.1002/app.41966...
] studied the ability of ESO, tri(2-ethylhexyl) trimellitate, and their blends as plasticizers for PVC. Both were efficient in plasticizing the polymer and, as expected, plasticizer migration decreased with increasing ESO content. In addition, PVC compounds with higher ESO content showed lower Shore D hardness. Given this, ESO can fully or partially replace the fossil plasticizer.

Epoxidized soybean oil and its methyl esters were tested as plasticizers for PVC by Chaudhary et al.[1919 Chaudhary, B. I., Nguyen, B. D., Smith, P., Sunday, N., Luong, M., & Zamanskiy, A. (2015). Bis (2‐ethylhexyl) succinate in mixtures with epoxidized soybean oil as bio‐based plasticizers for poly (vinylchloride). Polymer Engineering and Science, 55(3), 634-640. http://dx.doi.org/10.1002/pen.23934.
http://dx.doi.org/10.1002/pen.23934...
]. The authors showed that ESO, even having a high molar mass, proved compatible with PVC, plasticizing it efficiently. This study shows that soybean oil and its derivatives can be used as sustainable plasticizers for PVC and meets the requirements for coating wires and cables, among others.

When PVC is used in food packaging, the migration of plasticizers is of increasing concern in terms of toxicity and environmental pollution. Therefore, Coltro et al.[2020 Coltro, L., Pitta, J. B., da Costa, P. A., Fávaro Perez, M. Â., de Araújo, V. A., & Rodrigues, R. (2014). Migration of conventional and new plasticizers from PVC films into food simulants: a comparative study. Food Control, 44, 118-129. http://dx.doi.org/10.1016/j.foodcont.2014.03.058.
http://dx.doi.org/10.1016/j.foodcont.201...
] studied the migration of several plasticizers from the PVC matrix, including ESO. The authors used olive oil as a simulant for fatty foods and it was proven that ESO showed the highest rate of exudation. Choi et al.[2121 Choi, M. S., Rehman, S. U., Kim, H., Han, S. B., Lee, J., Hong, J., & Yoo, H. H. (2018). Migration of epoxidized soybean oil from polyvinyl chloride/polyvinylidene chloride food packaging wraps into food simulants. Environmental Science and Pollution Research International, 25(5), 5033-5039. http://dx.doi.org/10.1007/s11356-017-0951-9. PMid:29273993.
http://dx.doi.org/10.1007/s11356-017-095...
] also evaluated the migration of ESO simulating fatty food environment using n-heptane. The samples with ESO showed a high exudation rate, around 35%. These results demonstrate that the migration of plasticizers should be constant.

Besides, the search for new plasticizers from ESO or other green sources has been gaining space in recent years[2222 Jia, P., Xia, H., Tang, K., & Zhou, Y. (2018). Plasticizers derived from biomass resources: a short review. Polymers, 10(12), 1303. http://dx.doi.org/10.3390/polym10121303. PMid:30961228.
http://dx.doi.org/10.3390/polym10121303...
]. Jia et al.[2323 Jia, P., Zhang, M., Hu, L., & Zhou, Y. (2016). Green plasticizers derived from soybean oil for poly (vinyl chloride) as a renewable resource material. Korean Journal of Chemical Engineering, 33(3), 1080-1087. http://dx.doi.org/10.1007/s11814-015-0213-9.
http://dx.doi.org/10.1007/s11814-015-021...
] synthesized new polyol esters using soybean oil, with glycerol or pentaerythritol, of which two were acetylated and two were additionally epoxidized. The pentaerythritol-derived esters showed the best performance as a PVC plasticizer. Zheng et al. performed the transesterification of methyl esters from waste cooking oil with 2-ethylhexanol[2424 Zheng, T., Wu, Z., Xie, Q., Fang, J., Hu, Y., Lu, M., Xia, F., Nie, Y., & Ji, J. (2018). Structural modification of waste cooking oil methyl esters as cleaner plasticizer to substitute toxic dioctyl phthalate. Journal of Cleaner Production, 186, 1021-1030. http://dx.doi.org/10.1016/j.jclepro.2018.03.175.
http://dx.doi.org/10.1016/j.jclepro.2018...
]. These epoxidized esters were tested as plasticizers and the obtained PVC compounds showed improved mechanical and thermal performance, and the migration resistance was reduced. In addition, 2-ethylhexyl epoxidized esters from cooking oil proved to be an effective alternative to dioctyl phthalate, replacing about 40% of the total plasticizer.

In 2015, Kandula et al.[2525 Kandula, S., Stolp, L., Grass, M., Woldt, B., & Kodali, D. (2017). Functionalization of soy fatty acid alkyl esters as bio plasticizers. Journal of Vinyl & Additive Technology, 23(2), 93-105. http://dx.doi.org/10.1002/vnl.21486.
http://dx.doi.org/10.1002/vnl.21486...
] added several functional groups such as epoxy, acetoxy, methoxy, thiirane, and aziridine to soybean oil and evaluated it as a PVC plasticizer. The high viscosity and darker color of the aziridine and thiirane derivatives limited their usefulness, while the physical properties of the other derivatives were acceptable. Methoxy and acetoxy plasticizers of soybean fatty acid esters (methyl and n-butyl) showed good PVC compatibility, high efficiency, and gelling properties comparable to the properties of the commercial plasticizer, di-isononyl phthalate.

Owing to environmental concerns and the impending depletion of petroleum, this study developed a new green, phthalate-free plasticizer. This bio plasticizer was synthesized from the epoxidation of a vegetable triester, trimethylolpropane trioleate. The difference to a triglyceride is the absence of hydrogen-β, which increases the thermal stability in relation to soybean oil derivatives[2626 Moreira, D. R., Chaves, P. O. B., Ferreira, E. N., Arruda, T. B. M. G., Rodrigues, F. E. A., Câmara, J. F. No., Petzhold, C. L., Maier, M. E., & Ricardo, N. M. P. S. (2020). Moringa polyesters as eco-friendly lubricants and its blends with naphthalenic lubricant. Industrial Crops and Products, 158, 112937. http://dx.doi.org/10.1016/j.indcrop.2020.112937.
http://dx.doi.org/10.1016/j.indcrop.2020...
]. In addition, epoxy groups were added for better compatibility of the bioplasticizer with PVC. This product was tested as a plasticizer, either pure or mixed with DOCH at different concentrations (10 - 50 PHR), and the plasticizer efficiency was investigated through the mechanical and thermal properties.

2. Materials and Methods

2.1 Materials

PVC was purchased from Braskem (Norvic® SP1000) having a volumetric density of 0.52 ± 0.03 g.cm-3. Di(2-ethylhexyl)-1,2-cyclohexane dicarboxylate (DOCH) was purchased from Elekeiroz® (EKFLEX® 8815), with a density of 0.952 g.cm-3 and a molar mass of 396 g.mol-1. Trimethylolpropane trioleate (Emulchem OTMP) was purchased from Chemax® with a molar mass of 924 g.mol-1. Formic acid and 30% hydrogen peroxide were purchased from Synth and Nuclear, respectively. External lubricant (Stearic Acid, Gotalube), thermal stabilizer (Ca-Zn, Gotalube GL-4522®), and optical brightener (Hostalux KCD®) were donated by the Federal Institute of Rio Grande do Sul (IFRS).

2.2 Epoxidized Trimethylolpropane Trioleate Synthesis (EPO)

Trimethylolpropane trioleate, OTMP, (30.92 g, 0.10 mol double bond) was mixed with formic acid (7.55 mL, 0.2 mol) in a round-bottomed tritubulated flask under mechanical stirring followed by the addition of an aqueous solution of 30% hydrogen peroxide (204 mL, 2 mol) drop by drop for one hour (maintaining a molar ratio of 1:20:2 double bond/hydrogen peroxide/formic acid). This addition was performed at room temperature, and the reaction proceeded for 4 h at 65 ºC. Thereafter 100 mL of a saturated solution of sodium bisulfite was added and the mixture was stirred for 15 min. The mixture was placed in a separation funnel and washed with 130 mL diethyl ether. The organic phase was separated and washed with 200 mL deionized water and 200 mL brine, and the pH of the solution should be around 7. The aqueous solution was discarded, the organic phase dried with anhydrous sodium sulfate, filtered, and concentrated in a rotary evaporator. The isolated product was characterized by 1H-NMR, TGA, GPC, and Brookfield Viscosity. Yield: 55%

OTMP= 1H NMR (400 MHz, CDCl3) δ (ppm): 5.33 (He, m, 5.97H), 4.01 (Ha, s, 6H), 2.29 (Hb, t, 6.10H), 1.99 (Hd and Hf, m, 11H), 1.60 (Hc, m, 6.28H), 1.29 (CH2, m, 60H), 0.87 (CH3, t, 12H). (Figure S1 – Supplementary Material).

EPO = 1H NMR (400 MHz, CDCl3) δ (ppm): 3.99 (Ha, s, 6H), 2.87 (He, m, 5.76H), 2.28 (Hb, t, 6.57H), 1.59 (Hd,f, m, 6.24H), 1.47 (Hc, m, 20.97 H), 1.30 - 1.25 (CH2, m, 40H), 0.86 (CH3, t, 12H). (Figure S2 – Supplementary Material).

2.3 PVC compound preparation

100g of PVC resin (sp1000) was mixed in an intensive mixer, developed by IFRS, with external lubricant (Stearic Acid, 0.5 PHR), thermal stabilizer (Ca-Zn, 3 PHR), and an optical brightener (Hostalux, 0.2 PHR) until a temperature of 80 ºC was reached, by shearing with 7200 rpm. At this temperature, the plasticizers EPO and/or DOCH (50 PHR) were added, the temperature was increased to 95 ± 1 ºC, and kept stirring for 30 minutes to obtain the dry blend. After this time, the dry blend obtained was calendered in calender with dimensions 149 x 92 x 59 cm (H x W x D, MH150C, MH Equipaments®) and two horizontal stainless steel rolls (Ø 11 x 23 cm, 25 rpm) at 130 ºC, forming rectangular films with 22 x 33 cm length versus width, and 1 mm thickness. The films were cut into 11x11 cm squares, stacked, and pressed at 150 °C with 8 tons of pressure for 20 min. The pressed squares were cut according to type IV specimen [ASTM D638-02], with 4 ± 1 mm thick and 11 cm in total length, and stored at 25 °C. The samples were labeled 50DOCH, 4010, 2525, 1040, and 50EPO according to Table 1.

Table 1
Plasticizer content in each formulation (PHR).

2.4 Characterization of EPO and PVC compounds

2.4.1 1H NMR measurements

1H NMR spectra were performed in equipment Bruker 400 MHz. Samples were dissolved in deuterated chloroform (CDCl3), using the chloroform signal at 7.26 ppm for calibration.

2.4.2 Infrared spectroscopy (FTIR)

The Infrared spectra (IR) were recorded on a Perkin-Elmer spectrometer model Frontier in the ATR (attenuated total reflectance) mode, the spectra expressed by the wavenumber ratio (cm-1) being the sample analyzed from 6000 to 400 cm-1.

2.4.3 Gel Permeation Chromatography (GPC)

Analyzes were performed on Viscotek chromatograph with GPCmax module (VE2001) equipped with detector TDA402 and Shodex columns (806M, 805L, 804L, and 803L). The samples were solubilized in THF and filtered with a Chromafil Xtra PVDF - 45/25 filter with a pore size of 0.45 μm before injection. For calibration standard monodisperse polystyrene samples were used.

2.4.4 Brookfield viscosity

The viscosity of the solutions was measured at 60°C on a DVII + PRO digital viscometer (Brookfield) and the results were expressed as dynamic viscosity (cP).

2.4.5 Mechanical dynamic analysis

According to ASTM E1640, the DMA analysis was performed on a Perkin Elmer DMA 8000 equipment at a heating rate of 2 °C.min-1 using a strain amplitude of 0.010 mm and a frequency of 1 Hz.

2.4.6 Hardness Test (Shore A)

Based on ASTM D2240-15, the test was performed in a standard laboratory atmosphere at a temperature of 23 ± 2 ºC and relative humidity of 50 ± 10% using a Shore A durometer (Woltest®, 0-100 Shore A). The samples were at least 5.0 mm thick and the analysis was performed at five different positions, 5 mm apart. The durometer readings were taken after ten seconds of penetration of the durometer tip into the sample.

2.4.7 Tensile properties

To determine the tensile properties of PVC samples the universal testing machine (DL2000, EMIC, Brazil) was used, the test was based on ASTM D638-14 at a speed of 50 mm.min-1 with a load cell of 500 Kgf. Five samples were conditioned in a standard laboratory atmosphere. A 25 mm strain gauge was used, and the samples were 6 mm wide in the working area and 5 ± 1 mm thick.

2.4.8 Thermogravimetric analyzer

TGA measurements were performed in a Perkin Elmer TGA 4000, based on ASTM E1131-08. The analysis parameters used were a heating ramp from 30 °C to 900 °C at a heating rate of 20 °C.min-1 under an inert atmosphere (nitrogen). The initial mass of the samples was 9.500 mg ± 1 mg.

2.4.9 Migration testing

To evaluate the migration of polymeric matrix plasticizers tests were performed in n-heptane according to ASTM D1239-14[2727 American Society for Testing and Materials – ASTM. (2014). ASTM D1239–14: Standard Test Method for Resistance of Plastic Films to Extraction by Chemicals. West Conshohocken: ASTM.] and resolution n°105 of ANVISA (National Health Surveillance Agency, Brazil)[2828 Brasil. Ministério da Saúde. Agência Nacional de Vigilância Sanitária – ANVISA. Resolução nº 105, de 19 de maio de 1999 (1999, 20 maio). Aprova os Regulamentos Técnicos: Disposições Gerais para Embalagens e Equipamentos Plásticos em contato com Alimentos. Diário Oficial da República Federativa do Brasil, Brasília.]. This test consists of weighing the materials and after submerging seven (7) days in the n-heptane, and after this time the samples are weighed again.

3 Results and Discussion

3.1 EPO synthesis

Since the 1950s, conventional epoxidation, also called Prilezhaev epoxidation, can be used to epoxidize vegetable oils. This conventional epoxidation method uses peracids, with performic, peracetic, and m-chloroperbenzoic being the most common[2929 Danov, S. M., Kazantsev, O. A., Esipovich, A. L., Belousov, A. S., Rogozhin, A. E., & Kanakov, E. A. (2017). Recent advances in the field of selective epoxidation of vegetable oils and their derivatives: a review and perspective. Catalysis Science & Technology, 7(17), 3659-3675. http://dx.doi.org/10.1039/C7CY00988G.
http://dx.doi.org/10.1039/C7CY00988G...
]. Even though benzoic peracids have high activity in epoxidation, they are characterized by high cost and difficulty in separating the oil and the aqueous phase. Among the other two peracids, performic acid is preferable to peracetic acid, because the latter requires the addition of a strong and corrosive acid as a catalyst (e.g. HNO3, HCl, H2SO4) and higher temperatures, which can cause hydrolysis of the oxirane ring formed[3030 Köckritz, A., & Martin, A. (2008). Oxidation of unsaturated fatty acid derivatives and vegetable oils. European Journal of Lipid Science and Technology, 110(9), 812-824. http://dx.doi.org/10.1002/ejlt.200800042.
http://dx.doi.org/10.1002/ejlt.200800042...
,3131 Noor Armylisas, A. H., Siti Hazirah, M. F., Yeong, S. K., & Hazimah, A. H. (2017). Modification of olefinic double bonds of unsaturated fatty acids and other vegetable oil derivatives via epoxidation: a review. Grasas y Aceites, 68(1), 174. http://dx.doi.org/10.3989/gya.0684161.
http://dx.doi.org/10.3989/gya.0684161...
].

Therefore, when performing reactions on larger scales, it is preferable to use the in situ generated performic acid and for this reason, this method was chosen for the epoxidation of trimethylolpropane trioleate (OTMP) to obtain EPO from the epoxidized product as shown in Figure 1.

Figure 1
Epoxidation of OTMP to obtain EPO.

3.2 NMR analysis

The following signals are observed in the OTMP spectrum (Figure 2A): at 5.3 ppm for oleate fraction of vinyl hydrogens; at 4.0 ppm, the methylene hydrogens CH2-O; at 2.3 ppm, the methylene hydrogens CH2-CO; at 2.0 ppm, allylic methylene hydrogens CH2-CH = CH, at 1.6 ppm, the methylene hydrogens CH2-CH2-CO, at 1.3 ppm, the aliphatic methylene hydrogens and 0.9 ppm methyl hydrogens -CH3. The lower intensity signals at 3.5 and 2.8 ppm refer to hydrogens derived from linoleate present in the starting reagent[3232 Cheong, M., Hasan, Z. A. A., & Idris, Z. (2019). Characterisation of epoxidised trimethylolpropane trioleate: NMR and thermogravimetric analysis. Journal of Oil Palm Research, 31(1), 146-158. http://dx.doi.org/10.21894/jopr.2018.0066.
http://dx.doi.org/10.21894/jopr.2018.006...
].

Figure 2
1H-NMR spectra of (A) OTMP and (B) EPO (400 MHz, CDCl3)[11 Hosney, H., Nadiem, B., Ashour, I., Mustafa, I., & El‐Shibiny, A. (2018). Epoxidized vegetable oil and bio‐based materials as PVC plasticizer. Journal of Applied Polymer Science, 135(20), 46270. http://dx.doi.org/10.1002/app.46270.
http://dx.doi.org/10.1002/app.46270...
].

The EPO NMR spectrum (Figure 2B) was confirmed the complete consumption of the double bonds (signal disappearance at 5.0 and 2.0 ppm) and the appearance of the signal at 2.9 ppm, corresponding to the hydrogens of the oxirane ring and at 1.5 ppm of the methylene hydrogens adjacent to the oxirane.

The product was obtained with a conversion of 100% of the double bonds and approximately 81% epoxy selectivity (calculated by Equation 1 using the integration obtained through 1H NMR spectrum), giving a functionality of 2.3 epoxy groups.mol-1. As it is known from literature[3333 Monteavaro, L. L., da Silva, E. O., Costa, A. P. O., Samios, D., Gerbase, A. E., & Petzhold, C. L. (2005). Polyurethane networks from formiated soy polyols: synthesis and mechanical characterization. Journal of the American Oil Chemists’ Society, 82(5), 365-371. http://dx.doi.org/10.1007/s11746-005-1079-0.
http://dx.doi.org/10.1007/s11746-005-107...
] excess formic acid and long reaction times can lead to opening reactions of the epoxy group resulting in OH/formiate groups.

S e l e c t i v i t y = H e p o x i d e H d o u b l e b o n d * 100 (1)

3.3 FTIR analysis

The FTIR spectra of OTMP and EPO are shown in Figure 3. In the OTMP spectrum was observed the double bond signal at 3014 cm-1 (=C-H stretch due to cis unsaturated fatty acid), which disappears in EPO IR-spectrum and a new absorption band at 810 cm-1 attributed to the C-O-C asymmetric bending of the epoxy group is observed[3434 Suzuki, A. H., Botelho, B. G., Oliveira, L. S., & Franca, A. S. (2018). Sustainable synthesis of epoxidized waste cooking oil and its application as a plasticizer for polyvinyl chloride films. European Polymer Journal, 99, 142-149. http://dx.doi.org/10.1016/j.eurpolymj.2017.12.014.
http://dx.doi.org/10.1016/j.eurpolymj.20...
].

Figure 3
FTIR spectra of OTMP and EPO.

3.4 GPC and brookfield analysis

Table 2 shows the number average molar mass and Brookfield viscosity of the OTMP, EPO, and the commercial PVC plasticizer, DOCH. The number average molar mass was determined by GPC using a calibration curve with standard monodisperse polystyrene samples and THF as eluent. Therefore, the obtained Mn is a relative value and depends on the hydrodynamic volume of the molecule in solution. The compounds based on trimethylolpropane esters showed higher viscosity and higher molar mass than DOCH. Although EPO and OTMP have similar molar masses, EPO showed a higher viscosity than OTMP, probably due to the presence of stronger intermolecular interactions due to the presence of epoxy groups. However, etherification and esterification of the epoxide groups of EPO generating compounds with higher molar mass cannot be ruled out as observed in GPC curves of the plasticizers in Figure S3 (Supplementary Material).

Table 2
Number average molar mass and Brookfield viscosity of PVC plasticizers.

3.5 TGA analysis

TGA/DTG curves of the plasticizers performed under an inert atmosphere are presented in Figure 4, and initial decomposition Tonset, and maximum degradation rate temperature (Tmax) are summarized in Table 3. The compounds derived from vegetable oil (OTMP and EPO) showed higher thermal stability than DOCH, which presents a degradation process with Tonset at 204 ºC and Tmax at 315 ºC. While OTMP presented only one process of weight loss with Tonset at 342 ºC and Tmax at 441 ºC, EPO degraded in two processes: from 200 to 400 oC, due to the elimination of formiate groups attached to the opened oxirane rings corresponding to 11% weight loss and from 400 to 500 oC, relative to the main carbon chains degradation. As expected, the epoxidation of double bonds increases the thermal stability of the compounds[3535 Kim, J. R., & Sharma, S. (2012). The development and comparison of bio-thermoset plastics from epoxidized plant oils. Industrial Crops and Products, 36(1), 485-499. http://dx.doi.org/10.1016/j.indcrop.2011.10.036.
http://dx.doi.org/10.1016/j.indcrop.2011...
,3636 Borugadda, V. B., & Goud, V. V. (2016). Physicochemical and rheological characterization of waste cooking oil epoxide and their blends. Waste and Biomass Valorization, 7(1), 23-30. http://dx.doi.org/10.1007/s12649-015-9434-8.
http://dx.doi.org/10.1007/s12649-015-943...
]. None of the three compounds presented residue.

Figure 4
TGA and DTG curves of the plasticizers DOCH, OTMP, and EPO (N2, 20oC.min-1).
Table 3
Thermal degradation temperatures of DOCH, OTMP, and EPO.

3.6 Characterization of PVC compounds

Characterization was performed on the specimens produced according to the formulation in Table 1. It was not possible to obtain a specimen as pure PVC, because degradation occurs during calendering, and the OTMP cannot plasticize PVC.

3.6.1 DSC analysis

An essential parameter of the plasticizer efficiency is the reduction of the glass transition temperature (Tg) compared to pure PVC. The Tg of the PVC resin used is 86°C (determined by DSC in Figure S4 - Supplementary Material). The DSC heating curve of pure EPO showed a melting peak around -10 °C (Figure 5) which was not observed in the plasticized PVC, indicating compatibility between the PVC and the plasticizer. As observed in Table 4, the addition of EPO to PVC decreased the glass transition temperature by about 30 ºC compared to resin, as there is a weakening of intermolecular interactions and an increase in the free volume between the PVC chains resulting in higher overall mobility of the main chain[3737 Chen, J., Liu, Z., Nie, X., & Jiang, J. (2018). Synthesis and application of a novel environmental C26 diglycidyl ester plasticizer based on castor oil for poly (vinyl chloride). Journal of Materials Science, 53(12), 8909-8920. http://dx.doi.org/10.1007/s10853-018-2206-7.
http://dx.doi.org/10.1007/s10853-018-220...

38 Tong, H., & Hai, J. (2019). Sustainable synthesis of bio‐based hyperbranched ester and its application for preparing soft polyvinyl chloride materials. Polymer International, 68(3), 456-463. http://dx.doi.org/10.1002/pi.5730.
http://dx.doi.org/10.1002/pi.5730...

39 Bocqué, M., Voirin, C., Lapinte, V., Caillol, S., & Robin, J. J. (2016). Petro‐based and bio‐based plasticizers: chemical structures to plasticizing properties. Journal of Polymer Science, Part A: Polymer Science, 54(1), 11-33. http://dx.doi.org/10.1002/pola.27917.
http://dx.doi.org/10.1002/pola.27917...
-4040 Ang, D. T. C., Khong, Y. K., & Gan, S. N. (2016). Palm oil‐based compound as environmentally friendly plasticizer for poly (vinyl chloride). Journal of Vinyl & Additive Technology, 22(1), 80-87. http://dx.doi.org/10.1002/vnl.21434.
http://dx.doi.org/10.1002/vnl.21434...
].

Figure 5
DSC heating curves of EPO and PVC 50EPO (20 °C/min, N2 atmosphere).
Table 4
Properties of PVC compounds.

The polar ester and epoxy groups of the plasticizers interact with the polar part of the PVC polymer chain, spacing out the PVC molecules reducing their friction, and increasing the compatibility[11 Hosney, H., Nadiem, B., Ashour, I., Mustafa, I., & El‐Shibiny, A. (2018). Epoxidized vegetable oil and bio‐based materials as PVC plasticizer. Journal of Applied Polymer Science, 135(20), 46270. http://dx.doi.org/10.1002/app.46270.
http://dx.doi.org/10.1002/app.46270...
]. Furthermore, the long non-polar alkyl chain can increase the free volume between polymer molecules, resulting in a reduction of Tg[4141 Tan, J., Liu, B., Fu, Q., Wang, L., Xin, J., & Zhu, X. (2019). Role of the oxethyl unit in the structure of vegetable oil-based plasticizer for PVC: an efficient strategy to enhance compatibility and plasticization. Polymers, 11(5), 779. http://dx.doi.org/10.3390/polym11050779. PMid:31052451.
http://dx.doi.org/10.3390/polym11050779...
].

3.6.2 Mechanical properties

The compatibility and plasticized effect of EPO in PVC were investigated by DMA measurements. The Tg of the PVC compounds was obtained by the maximum peak of the tan δ. Figure 6 shows tan δ versus temperature curves of plasticized PVC with DOCH and EPO mixtures. All compounds presented only one symmetrical tan δ peak, indicating that the materials are uniform, in other words, the plasticizers are compatible with PVC[66 Tan, J., Zhang, S., Lu, T., Li, R., Zhong, T., & Zhu, X. (2019). Design and synthesis of ethoxylated esters derived from waste frying oil as anti-ultraviolet and efficient primary plasticizers for poly (vinyl chloride). Journal of Cleaner Production, 229, 1274-1282. http://dx.doi.org/10.1016/j.jclepro.2019.04.395.
http://dx.doi.org/10.1016/j.jclepro.2019...
,4242 Jia, P., Zhang, M., Hu, L., Feng, G., Bo, C., & Zhou, Y. (2015). Synthesis and application of environmental castor oil based polyol ester plasticizers for poly (vinyl chloride). ACS Sustainable Chemistry & Engineering, 3(9), 2187-2193. http://dx.doi.org/10.1021/acssuschemeng.5b00449.
http://dx.doi.org/10.1021/acssuschemeng....
].

Figure 6
Tan δ versus temperature for PVC compounds.

Therefore, the sample 50DOCH presents a lower glass temperature than EPO plasticized samples, since EPO has a molar mass three times higher than DOCH. Similar results were observed by Omrani et al.[4343 Omrani, I., Ahmadi, A., Farhadian, A., Shendi, H. K., Babanejad, N., & Nabid, M. R. (2016). Synthesis of a bio-based plasticizer from oleic acid and its evaluation in PVC formulations. Polymer Testing, 56, 237-244. http://dx.doi.org/10.1016/j.polymertesting.2016.10.027.
http://dx.doi.org/10.1016/j.polymertesti...
] using a bio-based plasticizer from oleic acid.

However, in the work of Ma et al.[4444 Ma, Y., Song, F., Hu, Y., Kong, Q., Liu, C., Rahman, M. A., Zhou, Y., & Jia, P. (2020). Highly branched and nontoxic plasticizers based on natural cashew shell oil by a facile and sustainable way. Journal of Cleaner Production, 252, 119597. http://dx.doi.org/10.1016/j.jclepro.2019.119597.
http://dx.doi.org/10.1016/j.jclepro.2019...
], the addition of a compound with a high molar mass causes an increase in the free volume of the molecule and, consequently, a decrease in the glass transition temperature. This effect was related to the dendritic structure of the molecule, which promotes the separation of PVC molecules. Tan et al.[4141 Tan, J., Liu, B., Fu, Q., Wang, L., Xin, J., & Zhu, X. (2019). Role of the oxethyl unit in the structure of vegetable oil-based plasticizer for PVC: an efficient strategy to enhance compatibility and plasticization. Polymers, 11(5), 779. http://dx.doi.org/10.3390/polym11050779. PMid:31052451.
http://dx.doi.org/10.3390/polym11050779...
] also observed that the incorporation of flexible oxyethyl units in the plasticizer can efficiently reduce the Tg of the plasticized PVC, although the higher molar mass.

The storage modulus of the PVC compounds (Figure 7) increases as the amount of EPO increases, indicating greater resistance to deformation. These data corroborate with the high Tg and Shore A hardness values (Table 4), because the higher the energy storage, the lower the free volume, which leads to increased stiffness of the PVC compound. Similar results were reported by Feng et al.[4545 Feng, G., Ma, Y., Zhang, M., Jia, P., Liu, C., & Zhou, Y. (2019). Synthesis of bio-base plasticizer using waste cooking oil and its performance testing in soft poly (vinyl chloride) films. Journal of Bioresources and Bioprodcts, 4(2), 99-110. http://dx.doi.org/10.21967/jbb.v4i2.214.
http://dx.doi.org/10.21967/jbb.v4i2.214...
] when using cooking oil modified with an alkyl diacid as a bio plasticizer.

Figure 7
Storage modulus versus temperature of PVC compounds.

The efficiency of the plasticizer can also be described by hardness measurements because it is associated with the free volume in the PVC matrix[4646 Schiller, M. (2015). PVC additives: performance, chemistry, developments, and sustainability. Munich: Carl Hanser Verlag. http://dx.doi.org/10.3139/9781569905449.
http://dx.doi.org/10.3139/9781569905449...
]. The lower the hardness of the material, the higher the mobility of the PVC chains, consequently, the better is the plasticization efficiency. The addition of EPO to the PVC matrix has slightly increased the hardness of the material regarding the formulation with the commercial DOCH (Table 4), which should be associated with its higher molar mass in comparison with DOCH. Omrani et al. also obtained similar Shore A hardness for PVC plasticized with a bio-based plasticizer synthesized from the oleic acid and thioglycolic acid[4242 Jia, P., Zhang, M., Hu, L., Feng, G., Bo, C., & Zhou, Y. (2015). Synthesis and application of environmental castor oil based polyol ester plasticizers for poly (vinyl chloride). ACS Sustainable Chemistry & Engineering, 3(9), 2187-2193. http://dx.doi.org/10.1021/acssuschemeng.5b00449.
http://dx.doi.org/10.1021/acssuschemeng....
].

Mehta et al.[4747 Mehta, B., Kathalewar, M., & Sabnis, A. (2014). Diester based on castor oil fatty acid as plasticizer for poly (vinyl chloride). Journal of Applied Polymer Science, 131(11), 40354. http://dx.doi.org/10.1002/app.40354.
http://dx.doi.org/10.1002/app.40354...
] prepared PVC plasticized with a blend containing 26 PHR of DOP and 26 PHR of an epoxy acylated ricinoleic acid binary alcohol ether ester and obtained a compound with a hardness of 95 Shore A. This value is much higher when compared with the hardness of 50EPO (89 Shore A), using 50 PHR of vegetable triester.

Table 5 shows the mechanical properties of PVC compounds. The addition of EPO increases the elastic modulus and the elongation at break of the material; however, no significant variation of tensile strength was observed indicating that EPO is a potential plasticizer to substitute the petrochemical DOCH.

Table 5
Mechanical properties of PVC compounds.

The elongation at break reached the highest value (24% higher than 50DOCH) when equal weight proportions of DOCH and EPO are presented (2525). Similar results were observed for the plasticizing effect of epoxy soybean oil compared with dioctyl phthalate petrochemical plasticizer[4848 Feng, G., Hu, L., Ma, Y., Jia, P., Hu, Y., Zhang, M., Liu, C., & Zhou, Y. (2018). An efficient bio-based plasticizer for poly (vinyl chloride) from waste cooking oil and citric acid: synthesis and evaluation in PVC films. Journal of Cleaner Production, 189, 334-343. http://dx.doi.org/10.1016/j.jclepro.2018.04.085.
http://dx.doi.org/10.1016/j.jclepro.2018...
]. Feng et al. also obtained a much higher elongation at break using a natural origin plasticizer[4545 Feng, G., Ma, Y., Zhang, M., Jia, P., Liu, C., & Zhou, Y. (2019). Synthesis of bio-base plasticizer using waste cooking oil and its performance testing in soft poly (vinyl chloride) films. Journal of Bioresources and Bioprodcts, 4(2), 99-110. http://dx.doi.org/10.21967/jbb.v4i2.214.
http://dx.doi.org/10.21967/jbb.v4i2.214...
].

3.6.3 TGA analysis

The thermal stability of the PVC compounds was investigated by thermogravimetric analysis (TGA) as showed in Figure 8. The thermal data as initial decomposition and 50% loss weight temperatures (Tonset and T50) and, the maximum degradation rate temperature corresponding to each process (TM1 and TM2) were summarized in Table 6.

Figure 8
TGA and DTG curves of PVC compounds (N2, 20 °C.min-1).
Table 6
TGA data of PVC resin and compounds.

All PVC compounds showed the characteristic two-loss weight processes. The first one corresponds to the PVC dehydrochlorination and the second to the formation of aromatic and allyl compounds followed by degradation of hydrocarbons chains. After the hydrogen chloride loss and breakage of double bonds, cross-linking occurs between polymer chains originating carbon black, which explains the residue of 4 to 6% regarding the initial weight of the PVC resin[4949 Yu, J., Sun, L., Ma, C., Qiao, Y., & Yao, H. (2016). Thermal degradation of PVC: a review. Waste Management (New York, N.Y.), 48, 300-314. http://dx.doi.org/10.1016/j.wasman.2015.11.041. PMid:26687228.
http://dx.doi.org/10.1016/j.wasman.2015....
,5050 Marongiu, A., Faravelli, T., Bozzano, G., Dente, M., & Ranzi, E. (2003). Thermal degradation of poly (vinyl chloride). Journal of Analytical and Applied Pyrolysis, 70(2), 519-553. http://dx.doi.org/10.1016/S0165-2370(03)00024-X.
http://dx.doi.org/10.1016/S0165-2370(03)...
].

While for the formulation with commercial plasticizer DOCH (50DOCH) the thermal stability decreased, all specimens formulated with EPO improved the thermal stability. The initial degradation temperature, T50, and TM1 increase as the content of EPO increases. Comparing pure PVC resin with 50EPO, an increase of 40 ºC in the Tonset was observed, better than the results obtained for plasticizers based on epoxidized soybean oil[4545 Feng, G., Ma, Y., Zhang, M., Jia, P., Liu, C., & Zhou, Y. (2019). Synthesis of bio-base plasticizer using waste cooking oil and its performance testing in soft poly (vinyl chloride) films. Journal of Bioresources and Bioprodcts, 4(2), 99-110. http://dx.doi.org/10.21967/jbb.v4i2.214.
http://dx.doi.org/10.21967/jbb.v4i2.214...
,4848 Feng, G., Hu, L., Ma, Y., Jia, P., Hu, Y., Zhang, M., Liu, C., & Zhou, Y. (2018). An efficient bio-based plasticizer for poly (vinyl chloride) from waste cooking oil and citric acid: synthesis and evaluation in PVC films. Journal of Cleaner Production, 189, 334-343. http://dx.doi.org/10.1016/j.jclepro.2018.04.085.
http://dx.doi.org/10.1016/j.jclepro.2018...
]. Only TM2 remains very close to PVC resin confirming that the plasticizer acts directly on the loss of hydrochloric acid from PVC. As described in the literature the epoxy groups can absorb hydrogen chloride degraded by light and heat, preventing the continuous decomposition of PVC and prolonging its lifetime[11 Hosney, H., Nadiem, B., Ashour, I., Mustafa, I., & El‐Shibiny, A. (2018). Epoxidized vegetable oil and bio‐based materials as PVC plasticizer. Journal of Applied Polymer Science, 135(20), 46270. http://dx.doi.org/10.1002/app.46270.
http://dx.doi.org/10.1002/app.46270...
].

3.6.4 Migration test

The migration stability of the EPO plasticizer in PVC blends was preliminarily investigated by leaching test using n-heptane, which is a good solvent for the bio plasticizers and a fatty food simulant[2727 American Society for Testing and Materials – ASTM. (2014). ASTM D1239–14: Standard Test Method for Resistance of Plastic Films to Extraction by Chemicals. West Conshohocken: ASTM.,2828 Brasil. Ministério da Saúde. Agência Nacional de Vigilância Sanitária – ANVISA. Resolução nº 105, de 19 de maio de 1999 (1999, 20 maio). Aprova os Regulamentos Técnicos: Disposições Gerais para Embalagens e Equipamentos Plásticos em contato com Alimentos. Diário Oficial da República Federativa do Brasil, Brasília.]. The plasticizers presented lower leaching resistance in n-heptane (weight loss higher than 10%) since they are organic compounds. Unsurprisingly the extraction of a high molar mass plasticizer EPO was lower than the low molar mass plasticizer DOCH, improving the resistance to exudation[5151 Wang, Y., Nie, X., & Li, X. (2016). Synthesis and characterization of novel pentaerythritol ester as PVC plasticizer. Journal of Applied Polymer Science, 133(47), 44227. http://dx.doi.org/10.1002/app.44227.
http://dx.doi.org/10.1002/app.44227...
]. The weight loss results (average value among five samples) were 19% for 50DOCH, 13% for 50EPO, and 10% for 2525.

4. Conclusions

Epoxidized trimethylolpropane trioleate (EPO), an acid oleic derivate, was easily synthesized and used as PVC environment-friendly plasticizer in substitution to commercial di(2-ethylhexyl) 1,2-cyclohexanoate (DOCH). Blends of DOCH/EPO (50 PHR) were added to PVC and their properties investigated. The presence of the epoxidized renewable source compound had a direct influence on the degradation temperature of PVC, making the polymer matrix more stable for all formulations compared to the commercial plasticizer DOCH.

EPO demonstrated good compatibility with PVC, which is evidenced by the presence of only one tan δ peak in the DMA analysis and the improvement of mechanical characteristics of PVC compounds. Thus, the tensile strength, Young modulus, and elongation at break increase achieving the best effect for a mixture containing equal amounts of DOCH/EPO.

Therefore, it can be stated that EPO is a potential bio plasticizer that can replace DOCH, a plasticizer of fossil origin, and by replacing DOCH with 50% EPO significantly improved the mechanical and thermal properties of the PVC compound.

5. Acknowledgments

The authors acknowledge CAPES and DAAD for the financial support in the partnership program PROBRAL (project nr. 88887.144057/2017-00). L. Souza thanks CAPES and Federal Institute of Rio Grande do Sul (IFRS-Campus Farroupilha).

References

  • 1
    Hosney, H., Nadiem, B., Ashour, I., Mustafa, I., & El‐Shibiny, A. (2018). Epoxidized vegetable oil and bio‐based materials as PVC plasticizer. Journal of Applied Polymer Science, 135(20), 46270. http://dx.doi.org/10.1002/app.46270
    » http://dx.doi.org/10.1002/app.46270
  • 2
    Shah, B. L., & Shertukde, V. V. (2003). Effect of plasticizers on mechanical, electrical, permanence, and thermal properties of poly (vinyl chloride). Journal of Applied Polymer Science, 90(12), 3278-3284. http://dx.doi.org/10.1002/app.13049
    » http://dx.doi.org/10.1002/app.13049
  • 3
    Unar, I. N., Soomro, S. A., & Aziz, S. (2010). Effect of various additives on the physical properties of polyvinylchloride resin. Pakistan Journal of Analytical & Environmental Chemistry, 11(2), 44-50. Retrieved in 2020, December 17, from http://pjaec.pk/index.php/pjaec/article/view/107/117
    » http://pjaec.pk/index.php/pjaec/article/view/107/117
  • 4
    Daniels, P. H. (2009). A brief overview of theories of pvc plasticization and methods used to evaluate pvc‐plasticizer interaction. Journal of Vinyl & Additive Technology, 15(4), 219-223. http://dx.doi.org/10.1002/vnl.20211
    » http://dx.doi.org/10.1002/vnl.20211
  • 5
    Latini, G., De Felice, C., & Verrotti, A. (2004). Plasticizers, infant nutrition and reproductive health. Reproductive Toxicology (Elmsford, N.Y.), 19(1), 27-33. http://dx.doi.org/10.1016/j.reprotox.2004.05.011 PMid:15336709.
    » http://dx.doi.org/10.1016/j.reprotox.2004.05.011
  • 6
    Tan, J., Zhang, S., Lu, T., Li, R., Zhong, T., & Zhu, X. (2019). Design and synthesis of ethoxylated esters derived from waste frying oil as anti-ultraviolet and efficient primary plasticizers for poly (vinyl chloride). Journal of Cleaner Production, 229, 1274-1282. http://dx.doi.org/10.1016/j.jclepro.2019.04.395
    » http://dx.doi.org/10.1016/j.jclepro.2019.04.395
  • 7
    Radke, E. G., Galizia, A., Thayer, K. A., & Cooper, G. S. (2019). Phthalate exposure and metabolic effects: a systematic review of the human epidemiological evidence. Environment International, 132, 104768. http://dx.doi.org/10.1016/j.envint.2019.04.040 PMid:31196577.
    » http://dx.doi.org/10.1016/j.envint.2019.04.040
  • 8
    Tickner, J. A., Schettler, T., Guidotti, T., McCally, M., & Rossi, M. (2001). Health risks posed by use of Di‐2‐ethylhexyl phthalate (DEHP) in PVC medical devices: a critical review. American Journal of Industrial Medicine, 39(1), 100-111. http://dx.doi.org/10.1002/1097-0274(200101)39:1<100::AID-AJIM10>3.0.CO;2-Q PMid:11148020.
    » http://dx.doi.org/10.1002/1097-0274(200101)39:1<100::AID-AJIM10>3.0.CO;2-Q
  • 9
    Bui, T. T., Giovanoulis, G., Cousins, A. P., Magnér, J., Cousins, I. T., & de Wit, C. A. (2016). Human exposure, hazard and risk of alternative plasticizers to phthalate esters. The Science of the Total Environment, 541, 451-467. http://dx.doi.org/10.1016/j.scitotenv.2015.09.036 PMid:26410720.
    » http://dx.doi.org/10.1016/j.scitotenv.2015.09.036
  • 10
    Colle, K. S., Stanat, J. E. R., Reinoso, J. J., & Godwin, S. (2010). US Patent No. 20100305250A1. USA: USPTO. Retrieved in 2020, December 17, from https://patents.google.com/patent/US20100305250A1/en
    » https://patents.google.com/patent/US20100305250A1/en
  • 11
    Ou, Y., Ding, X., & Zhang, L. (2014). Synthesis and application of an alternative plasticizer Di (2‐Ethylhexyl)‐1, 2‐cyclohexane dicarboxylate. Journal of Applied Polymer Science, 131(2), n/a. http://dx.doi.org/10.1002/app.39763
    » http://dx.doi.org/10.1002/app.39763
  • 12
    Hou, L., Fan, C., Liu, C., Qu, Q., Wang, C., & Shi, Y. (2018). Evaluation of repeated exposure systemic toxicity test of PVC with new plasticizer on rats via dual parenteral routes. Regenerative Biomaterials, 5(1), 9-14. http://dx.doi.org/10.1093/rb/rbx020 PMid:29423263.
    » http://dx.doi.org/10.1093/rb/rbx020
  • 13
    Hab, S. A., Talpur, F. N., Baig, J. A., Afridi, H. I., Surhio, M. A., & Talpur, M. K. (2018). Leaching and exposure of phthalates from medical devices; health impacts and regulations. Environmental Contaminants Reviews, 1(2), 13-21. http://dx.doi.org/10.26480/ecr.02.2018.13.21
    » http://dx.doi.org/10.26480/ecr.02.2018.13.21
  • 14
    Schilling, C. L. 3rd, & Kelly, K. K. (2018). U.S. Patent US:.2018/0105673 A1. Kingsport: U.S. Patent and Trademark Office.
  • 15
    Mizik, T., & Gyarmati, G. (2021). Economic and sustainability of biodiesel production: a systematic literature review. Cleanroom Technology, 3(1), 19-36. http://dx.doi.org/10.3390/cleantechnol3010002
    » http://dx.doi.org/10.3390/cleantechnol3010002
  • 16
    Jamarani, R., Erythropel, H. C., Nicell, J. A., Leask, R. L., & Marić, M. (2018). How green is your plasticizer? Polymers, 10(8), 834. http://dx.doi.org/10.3390/polym10080834 PMid:30960759.
    » http://dx.doi.org/10.3390/polym10080834
  • 17
    Karmalm, P., Hjertberg, T., Jansson, A., Dahl, R., & Ankner, K. (2009). Network formation by epoxidised soybean oil in plastisol poly (vinyl chloride). Polymer Degradation & Stability, 94(11), 1986-1990. http://dx.doi.org/10.1016/j.polymdegradstab.2009.07.029
    » http://dx.doi.org/10.1016/j.polymdegradstab.2009.07.029
  • 18
    Mao, D., Chaudhary, B. I., Sun, B., Shen, C.-Y., Yuan, D., Dai, G.-C., Li, B., & Cogen, J. M. (2015). Absorption and migration of bio‐based epoxidized soybean oil and its mixtures with tri (2‐ethylhexyl) trimellitate in poly (vinylchloride). Journal of Applied Polymer Science, 132(19), n/a. http://dx.doi.org/10.1002/app.41966
    » http://dx.doi.org/10.1002/app.41966
  • 19
    Chaudhary, B. I., Nguyen, B. D., Smith, P., Sunday, N., Luong, M., & Zamanskiy, A. (2015). Bis (2‐ethylhexyl) succinate in mixtures with epoxidized soybean oil as bio‐based plasticizers for poly (vinylchloride). Polymer Engineering and Science, 55(3), 634-640. http://dx.doi.org/10.1002/pen.23934
    » http://dx.doi.org/10.1002/pen.23934
  • 20
    Coltro, L., Pitta, J. B., da Costa, P. A., Fávaro Perez, M. Â., de Araújo, V. A., & Rodrigues, R. (2014). Migration of conventional and new plasticizers from PVC films into food simulants: a comparative study. Food Control, 44, 118-129. http://dx.doi.org/10.1016/j.foodcont.2014.03.058
    » http://dx.doi.org/10.1016/j.foodcont.2014.03.058
  • 21
    Choi, M. S., Rehman, S. U., Kim, H., Han, S. B., Lee, J., Hong, J., & Yoo, H. H. (2018). Migration of epoxidized soybean oil from polyvinyl chloride/polyvinylidene chloride food packaging wraps into food simulants. Environmental Science and Pollution Research International, 25(5), 5033-5039. http://dx.doi.org/10.1007/s11356-017-0951-9 PMid:29273993.
    » http://dx.doi.org/10.1007/s11356-017-0951-9
  • 22
    Jia, P., Xia, H., Tang, K., & Zhou, Y. (2018). Plasticizers derived from biomass resources: a short review. Polymers, 10(12), 1303. http://dx.doi.org/10.3390/polym10121303 PMid:30961228.
    » http://dx.doi.org/10.3390/polym10121303
  • 23
    Jia, P., Zhang, M., Hu, L., & Zhou, Y. (2016). Green plasticizers derived from soybean oil for poly (vinyl chloride) as a renewable resource material. Korean Journal of Chemical Engineering, 33(3), 1080-1087. http://dx.doi.org/10.1007/s11814-015-0213-9
    » http://dx.doi.org/10.1007/s11814-015-0213-9
  • 24
    Zheng, T., Wu, Z., Xie, Q., Fang, J., Hu, Y., Lu, M., Xia, F., Nie, Y., & Ji, J. (2018). Structural modification of waste cooking oil methyl esters as cleaner plasticizer to substitute toxic dioctyl phthalate. Journal of Cleaner Production, 186, 1021-1030. http://dx.doi.org/10.1016/j.jclepro.2018.03.175
    » http://dx.doi.org/10.1016/j.jclepro.2018.03.175
  • 25
    Kandula, S., Stolp, L., Grass, M., Woldt, B., & Kodali, D. (2017). Functionalization of soy fatty acid alkyl esters as bio plasticizers. Journal of Vinyl & Additive Technology, 23(2), 93-105. http://dx.doi.org/10.1002/vnl.21486
    » http://dx.doi.org/10.1002/vnl.21486
  • 26
    Moreira, D. R., Chaves, P. O. B., Ferreira, E. N., Arruda, T. B. M. G., Rodrigues, F. E. A., Câmara, J. F. No., Petzhold, C. L., Maier, M. E., & Ricardo, N. M. P. S. (2020). Moringa polyesters as eco-friendly lubricants and its blends with naphthalenic lubricant. Industrial Crops and Products, 158, 112937. http://dx.doi.org/10.1016/j.indcrop.2020.112937
    » http://dx.doi.org/10.1016/j.indcrop.2020.112937
  • 27
    American Society for Testing and Materials – ASTM. (2014). ASTM D1239–14: Standard Test Method for Resistance of Plastic Films to Extraction by Chemicals. West Conshohocken: ASTM.
  • 28
    Brasil. Ministério da Saúde. Agência Nacional de Vigilância Sanitária – ANVISA. Resolução nº 105, de 19 de maio de 1999 (1999, 20 maio). Aprova os Regulamentos Técnicos: Disposições Gerais para Embalagens e Equipamentos Plásticos em contato com Alimentos. Diário Oficial da República Federativa do Brasil, Brasília.
  • 29
    Danov, S. M., Kazantsev, O. A., Esipovich, A. L., Belousov, A. S., Rogozhin, A. E., & Kanakov, E. A. (2017). Recent advances in the field of selective epoxidation of vegetable oils and their derivatives: a review and perspective. Catalysis Science & Technology, 7(17), 3659-3675. http://dx.doi.org/10.1039/C7CY00988G
    » http://dx.doi.org/10.1039/C7CY00988G
  • 30
    Köckritz, A., & Martin, A. (2008). Oxidation of unsaturated fatty acid derivatives and vegetable oils. European Journal of Lipid Science and Technology, 110(9), 812-824. http://dx.doi.org/10.1002/ejlt.200800042
    » http://dx.doi.org/10.1002/ejlt.200800042
  • 31
    Noor Armylisas, A. H., Siti Hazirah, M. F., Yeong, S. K., & Hazimah, A. H. (2017). Modification of olefinic double bonds of unsaturated fatty acids and other vegetable oil derivatives via epoxidation: a review. Grasas y Aceites, 68(1), 174. http://dx.doi.org/10.3989/gya.0684161
    » http://dx.doi.org/10.3989/gya.0684161
  • 32
    Cheong, M., Hasan, Z. A. A., & Idris, Z. (2019). Characterisation of epoxidised trimethylolpropane trioleate: NMR and thermogravimetric analysis. Journal of Oil Palm Research, 31(1), 146-158. http://dx.doi.org/10.21894/jopr.2018.0066
    » http://dx.doi.org/10.21894/jopr.2018.0066
  • 33
    Monteavaro, L. L., da Silva, E. O., Costa, A. P. O., Samios, D., Gerbase, A. E., & Petzhold, C. L. (2005). Polyurethane networks from formiated soy polyols: synthesis and mechanical characterization. Journal of the American Oil Chemists’ Society, 82(5), 365-371. http://dx.doi.org/10.1007/s11746-005-1079-0
    » http://dx.doi.org/10.1007/s11746-005-1079-0
  • 34
    Suzuki, A. H., Botelho, B. G., Oliveira, L. S., & Franca, A. S. (2018). Sustainable synthesis of epoxidized waste cooking oil and its application as a plasticizer for polyvinyl chloride films. European Polymer Journal, 99, 142-149. http://dx.doi.org/10.1016/j.eurpolymj.2017.12.014
    » http://dx.doi.org/10.1016/j.eurpolymj.2017.12.014
  • 35
    Kim, J. R., & Sharma, S. (2012). The development and comparison of bio-thermoset plastics from epoxidized plant oils. Industrial Crops and Products, 36(1), 485-499. http://dx.doi.org/10.1016/j.indcrop.2011.10.036
    » http://dx.doi.org/10.1016/j.indcrop.2011.10.036
  • 36
    Borugadda, V. B., & Goud, V. V. (2016). Physicochemical and rheological characterization of waste cooking oil epoxide and their blends. Waste and Biomass Valorization, 7(1), 23-30. http://dx.doi.org/10.1007/s12649-015-9434-8
    » http://dx.doi.org/10.1007/s12649-015-9434-8
  • 37
    Chen, J., Liu, Z., Nie, X., & Jiang, J. (2018). Synthesis and application of a novel environmental C26 diglycidyl ester plasticizer based on castor oil for poly (vinyl chloride). Journal of Materials Science, 53(12), 8909-8920. http://dx.doi.org/10.1007/s10853-018-2206-7
    » http://dx.doi.org/10.1007/s10853-018-2206-7
  • 38
    Tong, H., & Hai, J. (2019). Sustainable synthesis of bio‐based hyperbranched ester and its application for preparing soft polyvinyl chloride materials. Polymer International, 68(3), 456-463. http://dx.doi.org/10.1002/pi.5730
    » http://dx.doi.org/10.1002/pi.5730
  • 39
    Bocqué, M., Voirin, C., Lapinte, V., Caillol, S., & Robin, J. J. (2016). Petro‐based and bio‐based plasticizers: chemical structures to plasticizing properties. Journal of Polymer Science, Part A: Polymer Science, 54(1), 11-33. http://dx.doi.org/10.1002/pola.27917
    » http://dx.doi.org/10.1002/pola.27917
  • 40
    Ang, D. T. C., Khong, Y. K., & Gan, S. N. (2016). Palm oil‐based compound as environmentally friendly plasticizer for poly (vinyl chloride). Journal of Vinyl & Additive Technology, 22(1), 80-87. http://dx.doi.org/10.1002/vnl.21434
    » http://dx.doi.org/10.1002/vnl.21434
  • 41
    Tan, J., Liu, B., Fu, Q., Wang, L., Xin, J., & Zhu, X. (2019). Role of the oxethyl unit in the structure of vegetable oil-based plasticizer for PVC: an efficient strategy to enhance compatibility and plasticization. Polymers, 11(5), 779. http://dx.doi.org/10.3390/polym11050779 PMid:31052451.
    » http://dx.doi.org/10.3390/polym11050779
  • 42
    Jia, P., Zhang, M., Hu, L., Feng, G., Bo, C., & Zhou, Y. (2015). Synthesis and application of environmental castor oil based polyol ester plasticizers for poly (vinyl chloride). ACS Sustainable Chemistry & Engineering, 3(9), 2187-2193. http://dx.doi.org/10.1021/acssuschemeng.5b00449
    » http://dx.doi.org/10.1021/acssuschemeng.5b00449
  • 43
    Omrani, I., Ahmadi, A., Farhadian, A., Shendi, H. K., Babanejad, N., & Nabid, M. R. (2016). Synthesis of a bio-based plasticizer from oleic acid and its evaluation in PVC formulations. Polymer Testing, 56, 237-244. http://dx.doi.org/10.1016/j.polymertesting.2016.10.027
    » http://dx.doi.org/10.1016/j.polymertesting.2016.10.027
  • 44
    Ma, Y., Song, F., Hu, Y., Kong, Q., Liu, C., Rahman, M. A., Zhou, Y., & Jia, P. (2020). Highly branched and nontoxic plasticizers based on natural cashew shell oil by a facile and sustainable way. Journal of Cleaner Production, 252, 119597. http://dx.doi.org/10.1016/j.jclepro.2019.119597
    » http://dx.doi.org/10.1016/j.jclepro.2019.119597
  • 45
    Feng, G., Ma, Y., Zhang, M., Jia, P., Liu, C., & Zhou, Y. (2019). Synthesis of bio-base plasticizer using waste cooking oil and its performance testing in soft poly (vinyl chloride) films. Journal of Bioresources and Bioprodcts, 4(2), 99-110. http://dx.doi.org/10.21967/jbb.v4i2.214
    » http://dx.doi.org/10.21967/jbb.v4i2.214
  • 46
    Schiller, M. (2015). PVC additives: performance, chemistry, developments, and sustainability. Munich: Carl Hanser Verlag. http://dx.doi.org/10.3139/9781569905449
    » http://dx.doi.org/10.3139/9781569905449
  • 47
    Mehta, B., Kathalewar, M., & Sabnis, A. (2014). Diester based on castor oil fatty acid as plasticizer for poly (vinyl chloride). Journal of Applied Polymer Science, 131(11), 40354. http://dx.doi.org/10.1002/app.40354
    » http://dx.doi.org/10.1002/app.40354
  • 48
    Feng, G., Hu, L., Ma, Y., Jia, P., Hu, Y., Zhang, M., Liu, C., & Zhou, Y. (2018). An efficient bio-based plasticizer for poly (vinyl chloride) from waste cooking oil and citric acid: synthesis and evaluation in PVC films. Journal of Cleaner Production, 189, 334-343. http://dx.doi.org/10.1016/j.jclepro.2018.04.085
    » http://dx.doi.org/10.1016/j.jclepro.2018.04.085
  • 49
    Yu, J., Sun, L., Ma, C., Qiao, Y., & Yao, H. (2016). Thermal degradation of PVC: a review. Waste Management (New York, N.Y.), 48, 300-314. http://dx.doi.org/10.1016/j.wasman.2015.11.041 PMid:26687228.
    » http://dx.doi.org/10.1016/j.wasman.2015.11.041
  • 50
    Marongiu, A., Faravelli, T., Bozzano, G., Dente, M., & Ranzi, E. (2003). Thermal degradation of poly (vinyl chloride). Journal of Analytical and Applied Pyrolysis, 70(2), 519-553. http://dx.doi.org/10.1016/S0165-2370(03)00024-X
    » http://dx.doi.org/10.1016/S0165-2370(03)00024-X
  • 51
    Wang, Y., Nie, X., & Li, X. (2016). Synthesis and characterization of novel pentaerythritol ester as PVC plasticizer. Journal of Applied Polymer Science, 133(47), 44227. http://dx.doi.org/10.1002/app.44227
    » http://dx.doi.org/10.1002/app.44227

Publication Dates

  • Publication in this collection
    11 Oct 2021
  • Date of issue
    2021

History

  • Received
    17 Dec 2020
  • Reviewed
    15 June 2021
  • Accepted
    09 Aug 2021
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