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. 2020 Mar 2;5(10):5480–5486. doi: 10.1021/acsomega.0c00119

Synthesis of a Novel Bio-Oil-Based Hyperbranched Ester Plasticizer and Its Effects on Poly(vinyl chloride) Soft Films

Jie Chen †,‡,*, Xiaoan Nie †, Jianchun Jiang †
PMCID: PMC7081639  PMID: 32201840

Abstract

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A novel hyperbranched ester plasticizer (SOHE) was synthesized from soybean oil. FTIR, 1H NMR, and 13C NMR spectroscopies were used to analyze the chemical structure of SOHE. SOHE was added into poly(vinyl chloride) (PVC). Thermal, mechanical, and dynamic mechanical properties of PVC samples were studied with thermal gravimetric analysis, dynamic mechanical analysis, and tensile tests. The results of SOHE substitution of petroleum-based dioctyl phthalate (DOP) in soft PVC samples were studied. The results indicated that PVC blends mixed with the obtained plasticizer showed higher thermal stability and flexibility. When DOP was completely replaced with SOHE, the Ti, T10, and T50 of the films were raised to 267.5, 275.3, and 338.0 °C, respectively. The plasticizing mechanism was also investigated. The volatility resistance and extraction were studied, which results indicated that the migration stability of PVC samples was significantly enhanced with the increasing amount of SOHE.

1. Introduction

To obtain the desired flexible PVC products, more than 80% plasticizers are used in PVC processing as additives, which could be applied to medical devices, pipes, coatings, films, and so on.1−4 The commercial plasticizer DOP is the usual main plasticizer, which is limited by the law due to its high risk of biological effects and toxicity on humans.5 Furthermore, because of easy diffusion to surroundings from PVC resin, phthalates have an environmental impact, which also reduce the durable performance of PVC products.3,6−8 In addition, research on environmentally friendly alternative plasticizers has been triggered by environmental concerns.9−12

Soybean oil is a renewable low-cost and commonly used agricultural resource. From it, we can derive epoxidized soybean oil (ESO), polyesters, and modified polyurethane, which can be widely used in industries. It is reported that ESO is generally used as a reactive modifier, diluent, and plasticizer or stabilizer for PVC.13−15 However, ESO presents poor migration stability for use in large doses, which is usually used in lower amounts as a secondary plasticizer.

Highly branched esters have improved plasticizer migration compared to DOP, which also have lower toxicity.16 Kwak et al. developed bio-based alkyl terminal hyperbranched polyglycerols and highly branched polycaprolactone/glycidol copolymeric plasticizers.16,17 The prepared PVC films showed excellent flexibility and solvent extraction resistance, showing potential in replacing DOP.16 Hai et al. did work on synthesis of castor oil-based hyperbranched esters,18 which have improved plasticizing effects, volatility resistance, and solvent extraction resistance. However, there are unreacted double bonds in the obtained hyperbranched ester plasticizer, which might reduce the compatibility of plasticizers and PVC.16,17

We provided a novel soybean oil-based plasticizer, a hyperbranched ester plasticizer (SOHE), in this work (Figure 1). This plasticizer was blended into PVC as the main plasticizer or a secondary plasticizer for DOP. A wide range of PVC sample properties, such as thermal properties, dynamic mechanical properties, mechanical properties before and after aging, and migration properties, was investigated. According to our study, SOHE could prove to be a promising candidate for an alternative renewable plasticizer.

Figure 1.

Figure 1

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Synthesis routes of SOHE.

2. Results and Discussion

2.1. Characterization

In Figure 2, the chemical structure of SOHE was analyzed with FTIR and compared with SOL and SOH. In the spectrum of SOL, the peak at 3442 cm–1 corresponded to an absorption peak of O–H. The strong absorption at 1737 cm–1 was attributed to a carbonyl group. Furthermore, the absorption peak at 3456 cm–1 in the curve of SOH appears to be stronger than that of SOL, which indicated that more O–H groups appeared in SOH. For SOHE, the characteristic absorption peak around 3456 cm–1 had disappeared. The peaks of carbonyl groups at 1742 cm–1 appeared to be stronger than those of SOH and SOL. These illustrated that the ester groups were obtained. The results implied that the soybean oil-based polyol SOH had been converted into ester by esterification, and the hyperbranched ester was prepared.

Figure 2.

Figure 2

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FTIR spectra of SOL, SOH, and SOHE.

Figure 3 shows the 1H NMR spectra of SOL, SOH, and SOHE. As seen from Figure 3a, the peak at 0.89 ppm (peak 1) was assigned to protons of methyl groups. The peak at 1.32 ppm (peak 2) and peaks at around 1.40–3.00 ppm (peaks 8, 5, and 9) corresponded to protons of methylene. The peaks at 3.00–4.50 ppm (peaks 10, 6, 7, 3, 4, and 12) corresponded to the protons of methylene groups of glyceride with the methyne connected to hydroxyl groups and methoxy groups. In Figure 3b, the peaks at 2.08–4.21 ppm (peaks 3, 3′, and 3″) corresponding to the protons of the methylene and methyne linked with hydroxyl were stronger than those of SOL, which indicated that the polyol was produced. Figure 3c shows the 1H NMR of SOHE. The chemical shift at 2.04 ppm (peak 1′) was attributed to protons of methyl groups linked with carbonyl groups. The new peak at 5.26 ppm (peak 11′) corresponded to the protons of methyne groups connected to carbonyl. These results suggested that the hyperbranched ester was prepared.

Figure 3.

Figure 3

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1H NMR spectra of (a) SOL, (b) SOH, and (c) SOHE.

2.2. Thermal Stability

Figure 4 displays the TGA spectrum of SOHE and DOP heated in nitrogen at the rate of 10 °C/min. In Table 2, the initial decomposition temperature (Ti), 10% and 50% mass loss temperatures (T10 and T50), and weight loss are summarized. It can be seen that SOHE had increases of 137.3, 104.8, and 129.6 °C compared with DOP in Ti, T10, and T50, respectively. It can be summarized that the plasticizer SOHE shows better thermal stability.

Figure 4.

Figure 4

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TGA curves of SOHE and DOP.

Table 2. Formulation of the PVC Samples.

component (phr) F1 F2 F3 F4 F5
total plasticizer content 40.0 40.0 40.0 40.0 40.0
SOHE content 0.0 10.0 20.0 30.0 40.0
DOP content 40.0 30.0 20.0 10.0 0.0
thermal-stabilizer content 2.0 2.0 2.0 2.0 2.0
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Figure 5 shows the results of PVC samples with different contents of SOHE. The degradation data of Ti, T10, and T50 and weight loss data at different times are summarized in Table 1. There are two main degradation steps in the degradation curve of PVC samples.19,20 It can be seen in the first stage that the largest weight loss of 69.7% is at 200–350 °C. Furthermore, the second step has the largest weight loss of 21.6% at 400–500 °C. The Ti, T10, and T50 of the PVC sample plasticized with DOP (F1) were 226.0, 239.2, and 291.7 °C. The Ti, T10, and T50 were enhanced when DOP was replaced with SOHE, and the Ti, T10, and T50 reached 263.3, 266.8, and 314.3 °C, respectively, when 75% DOP was substituted with SOHE. The Ti, T10, and T50 reached 275.4, 281.8, and 321.8 °C when DOP was fully replaced with SOHE. It can be observed that the thermal stability of PVC samples was increased when the content 0f SOHE increased. The reason can be explained with the fact that the carbonyl groups and long alkane chains with high heat resistance are contained in the chemical structure of SOHE. The results show that the addition of SOHE can more effectively improve the thermal stability of the PVC matrix than DOP.

Figure 5.

Figure 5

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TGA curves of the PVC samples with different plasticizers.

Table 1. Thermal Properties of PVC Samples with Different Plasticizers.

          weight loss (wt %)
sample Tg (°C) Ti (°C) T10 (°C) T50 (°C) 200–350 (°C) 400–500 (°C)
DOP   224.3 223.1 263.3    
SOHE   361.6 327.9 392.9    
F1 41.46 226.0 239.2 291.7 69.7 16.1
F2 45.68 260.7 256.9 304.4 66.6 17.4
F3 46.82 259.2 259.3 304.3 64.9 19.4
F4 51.57 263.3 266.8 314.3 62.5 20.8
F5 61.89 275.4 281.8 321.8 59.8 21.6
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2.3. Dynamic Mechanical Analysis

A DMA instrument was used to evaluate the dynamic mechanical property. Figure 6 shows the loss factor of the PVC samples. All the curves show a single peak of tan δ, which indicate that the blends are completely intersoluble and homogeneous materials.21 The glass transition temperature (Tg) is the temperature at the maximum of the tan δ curve, which is an important metric of plasticizing efficiency. As shown in Table 1, the Tg values for F1–F5 are 41.46, 45.68, 46.82, 51.57, and 61.89 °C, respectively. However, the Tg of plasticized PVC samples was much less than the value of 92.3 °C for pure PVC. When 25% and 50% DOP was replaced with SOHE, the Tg was slightly higher than that of pure DOP. With the addition of SOHE, tan δ peaks moved to higher temperatures, and the corresponding Tg values increased.22 This might be due to the chemical structure of SOHE.23,24 Compared with DOP, SOHE has the higher molecular weight, which makes the plasticizing effect reduced when DOP is substituted with SOHE. However, the damping capability increased with the addition of SOHE, leading to taller and narrower peaks than those of sample F1. In addition, the plasticizing mechanism can be explained according to the molecular features of PVC and plasticizers. As indicated in Figure 7, the ester polar groups of SOHE interact with the α hydrogen of PVC chains to form hydrogen bonds, which decreased the interaction of PVC–PVC sites and increased the space between polymer molecules. Furthermore, more free volume in the polymer will be created by the motion of long alkyl chains of SOHE. The interaction promoted the random motion of PVC to make plasticized PVC chains easy to proceed and show flexibility.

Figure 6.

Figure 6

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DMA curves for the PVC samples.

Figure 7.

Figure 7

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Intermolecular force interaction between SOHE and PVC molecules.

2.4. Mechanical Properties

The results of tensile strength and elongation at break of PVC samples before and after heat aging are demonstrated in Figure 8. Compared with F1, PVC plasticized with SOHE (films F2 and F3) had an increased elongation at break and lower tensile strength. Because more dendritic structures with ester carbonyl polar groups and flexible long alkane chains present synergistic plasticizing effects on PVC, SOHE had a remarkable effect on the flexibility when partly replacing DOP.25,26 However, the elongation at break decreased and the tensile strength increased when the concentration of SOHE increased to 75 and 100%, respectively. This is mainly because of the high molecular weight of SOHE. These results suggest that SOHE can be used as a secondary plasticizer, endowing the PVC matrix with better flexibility. On the other hand, sample F0 showed the max change of mechanical properties after heat aging. The PVC films plasticized with SOHE as a partial or whole replacement plasticizer for DOP (films F2–F5) did not show much difference in the mechanical properties after aging. The above results suggested that SOHE could improve the thermal stabilities and flexibility of PVC materials.

Figure 8.

Figure 8

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Mechanical properties of the PVC samples before and after heat aging.

2.5. Extraction and Volatility Resistance

To increase the safety and extend the service life of PVC samples, the volatile resistance and solvent extraction resistance of the plasticizer should be raised. In this work, the extraction resistance of SOHE in petroleum ether and volatility were investigated.

As displayed in Figure 9, the weight loss of F2–F5 ranged from 6.3 to 7.9% of their initial weight. The weight loss of F1 is 11.8% of its initial weight loss. This result suggested that SOHE is superior to DOP in solvent extraction resistance. The change of weight loss of PVC samples in the volatilization test is similar to that of the extraction test. The weight loss of F3 was lower than 1.1% in the experiment of volatilization. However, F1 lost approximately 2.0% of its initial weight. It can be seen that SOHE has excellent heat resistance, which makes it more stable than DOP in volatilization experiments. The excellent solvent extraction resistance and volatile resistance of SOHE can be attributed to the high branching degree, large relative molecular mass, and high ester content of SOHE. Compared with DOP, the stronger intermolecular interaction force prevents SOHE migration from PVC blends. It can endow PVC products with long-term stability and safety.

Figure 9.

Figure 9

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Weight losses of PVC samples after extraction and volatilization experiments.

3. Conclusions

SOHE was synthesized, and we evaluated its effects on mechanical properties, thermal stabilities, and migration stabilities of PVC samples. When SOHE partially or completely substituted commercial plasticizer DOP in soft PVC samples, the effects were investigated. The DMA results suggested that, with the increasing amount of SOHE, the compatibility between the plasticizers and PVC enhanced. TGA was used to examine the thermal stability. The TGA results suggested that SOHE could endow PVC samples with increased thermal stability. When SOHE completely substituted DOP, Ti, T10, and T50 increased to 267.5, 275.3, and 338.0 °C, respectively. The tensile results suggested that SOHE had an enhanced plasticizing effect compared with that of DOP. In addition, PVC samples had better migration stability with the substitution of SOHE into DOP. Consequently, this soybean oil-based plasticizer has the potential to be a secondary environmental plastic material.

4. Experimental Section

4.1. Materials

Epoxidized soybean oil (98.0%), glycol dimethyl ether (99.5%), methanol (99.5%), glycidyl (98.0%), acetone (99.0%), anhydrous magnesium sulfate (99.5%), acetic anhydride (98.0%), ethyl acetate (98.0%), sodium bicarbonate (99.5%), zinc stearate, and calcium stearate were obtained from Aladdin Chemical Reagent Co., Ltd.(Shanghai, China). PVC (S-1000) was purchased from the Sinopec Qilu Co., Ltd., (Zibo, China).

4.2. Preparation of the Soybean Oil-Based Hyperbranched Polyalcohol (SOL)

To a flask equipped with a magnetic stirrer, reflux condenser, and thermometer, epoxidized soybean oil (50 g), methanol (50 g), and four-fluorine boric acid (0.75 g) were mixed at 45 °C for 2 h. Then, the raw product was dissolved in ethyl acetate and distilled water. The oil phase was separated from the water phase. Then, the oil phase was washed with sodium bicarbonate solution and distilled water to neutral. The solvent and water were removed by distillation under vacuum. The SOL was obtained, and the yield was 83.64%.

4.3. Preparation of the Soybean Oil-Based Hyperbranched Polymer (SOH)

SOL (69 g) and tetrafluoroboric acid (0.38 g) were dissolved in dimethoxyethane and mixed in a flask under a nitrogen atmosphere. After the mixture was heated to 75 °C, 56 g of glycidol was dropwise added. Then, the mixture was stirred at 100 °C for 4 h. The raw product was dissolved in methanol and acetone. SOH was obtained after vacuum distillation. The yield of SOH was 61.03%.

4.4. Preparation of the Soybean Oil-Based Hyperbranched Ester Plasticizer (SOHE)

To a flask equipped with a magnetic stirrer, thermometer, and reflux condenser, SOH (194 g) and acetic anhydride (234 g) were charged. The mixture was heated at 120 °C for 3.5 h. After cooling to room temperature, the raw product was soluble in ethyl acetate and distilled water to neutral. The water was removed through distillation under vacuum. The yield of SOHE was 85.60%. Figure 1 displays the synthetic route of the bio-based plasticizer hyperbranched ester.

4.5. Preparation of Plasticized PVC Test Specimens

PVC, thermal stabilizers (Ca salts/Zn salts = 3/1), and plasticizers were compounded in a mixer for 5 min at room temperature. Then, the compound was mixed by double-roller blending rolls (Zhenggong Co., China) at 165 °C for 5 min. Then, the PVC samples with a thickness of 3 mm were obtained. The formulations were displayed in Table 2.

4.6. Characterizations

1H NMR spectra in deuterated chloroform (CDCl3) were recorded on a Bruker ARX 300 spectrometer (Bruker Co., Germany) at 23 °C. Fourier transform infrared (FTIR) spectroscopy was carried out by an attenuated total reflectance method using a Nicolet IS10 spectrometer (Thermo Fisher Scientific Inc., U.S.A.). Dynamic mechanical analysis (DMA) was done in a dual cantilever mode with a frequency of 1 Hz by a DMA Q800 instrument (TA Instruments, New Castle, DE). The heating rate was of 3 °C/min. The testing temperature was swept from −60 to 80 °C. Replicated tests were performed for each specimen to ensure the reproducibility of data. Thermogravimetric analysis (TGA) was conducted in a 409PC thermogravimetric analyzer (Netzsch Co., Germany). Each specimen was scanned from 30 to 600 °C under a nitrogen atmosphere. The heating rate was 10 °C/min. According to ISO 527-2:1993, tensile properties were carried out by a SANS CMT-4303 universal testing machine (Shenzhen Xinsansi Jiliang Instrument Co., China) with a cross-head speed at 10 mm/min. To obtain an average value, five specimens were prepared for each group. Prior to tensile testing, all specimens were conditioned at 23 °C for one day. According to ASTMD 1239-98, the extraction tests were carried out. The PVC specimens were sank into petroleum ether at 50 ± 5% relative humidity and 23 ± 1 °C. The extracted specimens were rinsed using flowing water and wiped up after 24 h. Then, the specimens were dried at 30 °C for 24 h in a convection oven (Shanghai Suopu Instrument Co., China). The changes of weight loss before and after sinking were measured. To obtain an average value, three specimens were tested. The activated carbon method (ISO 176:2005) was carried out to determine the volatility. The specimens were placed on the bottom of a metal container. Approximately 120 cm3 of activated carbon was spread over these specimens. The container was placed in the convection oven (Shanghai Suopu Instrument Co., China) for 24 h at a temperature of 70 ± 1 °C. The container was removed and cooled in a desiccator. The specimens were reweighed. The changes of weight loss were measured.

Acknowledgments

The authors are grateful for the Fundamental Research Funds for the Central Non-Profit Research Institution of CAF (no. CAFYBB2018QA002).

The authors declare no competing financial interest.

References

  1. Chen J.; Liu Z.; Nie X.; Jiang J. Synthesis and application of a novel environmental C26 diglycidyl ester plasticizer based on castor oil for poly(vinyl chloride). J. Mater. Sci. 2018, 53, 8909–8920. 10.1007/s10853-018-2206-7. [DOI] [Google Scholar]
  2. Hines C. J.; Hopf N. B.; Deddens J. A.; Silva M. J.; Calafat A. M. Occupational exposure to diisononyl phthalate (DiNP) in polyvinyl chloride processing operations. Int. Arch. Occup. Environ. Health 2012, 85, 317–325. 10.1007/s00420-011-0674-z. [DOI] [PubMed] [Google Scholar]
  3. Chiellini F.; Ferri M.; Morelli A.; Dipaola L.; Latini G. Perspectives on alternatives to phthalate plasticized poly(vinyl chloride) in medical devices applications. Prog. Polym. Sci. 2013, 38, 1067–1088. 10.1016/j.progpolymsci.2013.03.001. [DOI] [Google Scholar]
  4. Chiellini F.; Ferri M.; Latini G. Physical-chemical assessment of di-(2-ethylhexyl)-phthalate leakage from poly(vinyl chloride) endotracheal tubes after application in high risk newborns. Int. J. Pharm. 2011, 409, 57–61. 10.1016/j.ijpharm.2011.02.024. [DOI] [PubMed] [Google Scholar]
  5. Papageorgiou G. Z.; Tsanaktsis V.; Papageorgiou D. G.; Exarhopoulos S.; Papageorgiou M.; Bikiaris D. N. Evaluation of polyesters from renewable resources as alternatives to the current fossil-based polymers. Phase transitions of poly(butylene 2,5-furan-dicarboxylate). Polymer 2014, 55, 3846–3858. 10.1016/j.polymer.2014.06.025. [DOI] [Google Scholar]
  6. Sampson J.; De Korte D. DEHP-plasticised PVC: relevance to blood services. Transfus. Med. 2015, 21, 73–83. 10.1111/j.1365-3148.2010.01056.x. [DOI] [PubMed] [Google Scholar]
  7. Lithner D.; Larsson A.; Dave G. Environmental and health hazard ranking and assessment of plastic polymers based on chemical composition. Sci. Total Environ. 2011, 409, 3309–3324. 10.1016/j.scitotenv.2011.04.038. [DOI] [PubMed] [Google Scholar]
  8. Drake P. L.; Rojas M.; Reh C. M.; Mueller C. A.; Jenkins F. M. Occupational exposure to airborne mercury during gold mining operations near El Callao, Venezuela. Int. Arch. Occup. Environ. Health 2001, 74, 206–212. 10.1007/s004200000206. [DOI] [PubMed] [Google Scholar]
  9. Papageorgiou G. Z.; Tsanaktsis V.; Papageorgiou D. G.; Chrissafis K.; Exarhopoulos S.; Bikiaris D. N. Furan-based polyesters from renewable resources: Crystallization and thermal degradation behavior of poly(hexamethylene 2,5-furan-dicarboxylate). Eur. Polym. J. 2015, 67, 383–396. 10.1016/j.eurpolymj.2014.08.031. [DOI] [Google Scholar]
  10. Chen J.; Liu Z.; Nie X.; Zhou Y.; Jiang J.; Murray R. E. Plasticizers derived from cardanol: synthesis and plasticization properties for polyvinyl chloride(PVC). J. Polym. Res. 2018, 25, 128. 10.1007/s10965-018-1524-4. [DOI] [Google Scholar]
  11. Fernandez S. S.; Kunchandy S.; Ghosh S. Linseed Oil Plasticizer Based Natural Rubber/Expandable Graphite Vulcanizates: Synthesis and Characterizations. J. Polym. Environ. 2015, 23, 526–533. 10.1007/s10924-015-0721-z. [DOI] [Google Scholar]
  12. Noel A.; Borguet Y. P.; Wooley K. L. Self-Reporting Degradable Fluorescent Grafted Copolymer Micelles Derived from Biorenewable Resources. ACS Macro Lett. 2015, 4, 645–650. 10.1021/acsmacrolett.5b00227. [DOI] [PMC free article] [PubMed] [Google Scholar]
  13. Chen J.; Li X.; Wang Y.; Huang J.; Li K.; Nie X.; Jiang J. Synthesis and application of environmental soybean oil based epoxidized glycidyl ester plasticizer for poly(vinyl chloride). Eur. J. Lipid Sci. Technol. 2016, 119, 1600216. 10.1002/ejlt.201600216. [DOI] [Google Scholar]
  14. Demertzis P. G.; Riganakos K. A.; Akrida-Demertzi K. Study of compatibility of PVC and polyester-type plasticizer blends by inverse gas chromatography. Eur. Polym. J. 1990, 26, 137–140. 10.1016/0014-3057(90)90177-6. [DOI] [Google Scholar]
  15. Fertier L.; Koleilat H.; Stemmelen M.; Giani O.; Joly-Duhamel C.; Lapinte V.; Robin J. J. The use of renewable feedstock in UV-curable materials – A new age for polymers and green chemistry. Prog. Polym. Sci. 2013, 38, 932–962. 10.1016/j.progpolymsci.2012.12.002. [DOI] [Google Scholar]
  16. Lee K. W.; Chung J. W.; Kwak S. Y. Synthesis and characterization of bio-based alkyl terminal hyperbranched polyglycerols: a detailed study of their plasticization effect and migration resistance. Green Chem. 2016, 18, 999–1009. 10.1039/C5GC02402A. [DOI] [Google Scholar]
  17. Lee K. W.; Chung J. W.; Kwak S. Y. Highly Branched Polycaprolactone/Glycidol Copolymeric Green Plasticizer by One-Pot Solvent-Free Polymerization. ACS Sustainable Chem. Eng. 2018, 6, 9006–9017. 10.1021/acssuschemeng.8b01356. [DOI] [Google Scholar]
  18. Tong H.; Hai J. Sustainable synthesis of bio-based hyperbranched ester and its application for preparing soft polyvinyl chloride materials. Polym. Int. 2019, 456. 10.1002/pi.5730. [DOI] [Google Scholar]
  19. Chen J.; Li X.; Wang Y.; Li K.; Huang J.; Jiang J.; Nie X. Synthesis and application of a novel environmental plasticizer based on cardanol for poly (vinyl chloride). J. Taiwan Inst. Chem. Eng. 2016, 65, 488–497. 10.1016/j.jtice.2016.05.025. [DOI] [Google Scholar]
  20. Jiménez A.; Berenguer V.; López J.; Sánchez A. Thermal degradation study of poly (vinyl chloride): kinetic analysis of thermogravimetric data. J. Appl. Polym. Sci. 1993, 50, 1565–1573. 10.1002/app.1993.070500910. [DOI] [Google Scholar]
  21. Greco A.; Brunetti D.; Renna G.; Mele G.; Maffezzoli A. Plasticizer for poly (vinyl chloride) from cardanol as a renewable resource material. Polym. Degrad. Stab. 2010, 95, 2169–2174. 10.1016/j.polymdegradstab.2010.06.001. [DOI] [Google Scholar]
  22. Lai H.; Wang Z.; Wu P.; Chaudhary B. I.; Sengupta S. S.; Cogen J. M.; Li B. Structure and Diffusion Behavior of Trioctyl Trimellitate (TOTM) in PVC Film Studied by ATR-IR Spectroscopy. Ind. Eng. Chem. Res. 2012, 51, 9365–9375. 10.1021/ie300007m. [DOI] [Google Scholar]
  23. Soudais Y.; Moga L.; Blazek J.; Lemort F. Coupled DTA–TGA–FT-IR investigation of pyrolytic decomposition of EVA, PVC and cellulose. J. Anal. Appl. Pyrolysis 2007, 78, 46–57. 10.1016/j.jaap.2006.04.005. [DOI] [Google Scholar]
  24. Linde E.; Gedde U. W. Plasticizer migration from PVC cable insulation - The challenges of extrapolation methods. Polym. Degrad. Stab. 2014, 101, 24–31. 10.1016/j.polymdegradstab.2014.01.021. [DOI] [Google Scholar]
  25. Yahya M. Z. A.; Arof A. K. Effect of oleic acid plasticizer on chitosan–lithium acetate solid polymer electrolytes. Eur. Polym. J. 2003, 39, 897–902. 10.1016/S0014-3057(02)00355-5. [DOI] [Google Scholar]
  26. Lavorgna M.; Piscitelli F.; Mangiacapra P.; Buonocore G. G. Study of the combined effect of both clay and glycerol plasticizer on the properties of chitosan films. Carbohydr. Polym. 2010, 82, 291–298. 10.1016/j.carbpol.2010.04.054. [DOI] [Google Scholar]

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