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Novel sulfonate-containing halogen-free flame-retardants: effect of ternary and quaternary sulfonates centered on adamantane on the properties of polycarbonate composites

Dong Yu Zhu, Jian Wei Guo*, Jia Xing Xian and Shu Qin Fu
School of Chemical Engineering and Light Industry, Guangdong University of Technology, Guangzhou 510006, China. E-mail: guojw@gdut.edu.cn

Received 12th June 2017 , Accepted 3rd July 2017

First published on 10th August 2017


Abstract

In order to find a more environmentally friendly flame retardant, we have designed a novel halogen-free flame-retardant (FR) system consisting of ternary and quaternary sulfonates centered on adamantane. They are named 1,3,5-tri(phenyl-4-sodium sulfonate)adamantane (AS3) and 1,3,5,7-tetrakis(phenyl-4-sodium sulfonate)adamantane (AS4), respectively. Both kinds of FRs were synthesized and compounded with polycarbonate (PC) to study their effects on the properties of PC composites. The results show that the new FR system can improve PC flame retardancy efficiently, and has mechanical strength advantages as well. The PC composites with only 0.1 wt% AS3 or 0.08 wt% AS4 can pass vertical burning tests (UL-94) V-0 level, with increasing the value of limiting oxygen index (LOI) to 31.2% or 32.3%. Moreover, they can maintain ideal mechanical properties compared to neat PC simultaneously. Finally, the flame retardant mechanism of this system was verified via thermal analysis, morphology and chemical structure analysis of the char residues.


1 Introduction

With the development of technology, polymer materials are used with an ever increasing magnitude instead of metal or ceramics in all kinds of areas. However, fire hazards associated with the use of these polymeric materials are usually present and can cause heavy loss of life and property.1–3 Therefore, it is vital to reduce the combustibility of the polymers by using flame retardants in the development and application of new materials.4 Polycarbonate (PC) is one of the fastest growing engineering plastics containing excellent physical properties including transparency, toughness, high heat distortion temperature, and beneficial mechanical properties.5 Generally, PC shows a V-2 rating in the UL-94 test and the oxygen index is about 25%, but it is still difficult to meet the needs of more stringent flame retardant performance in many practical applications.6–8

For the sake of safety, all kinds of flame retardants have been developed and used for PC. The halogen-containing flame-retardants that have high flame-resistant efficiency, however, have been gradually forbidden due to the generated toxicity and environmental problems. Because of this, the development of environmentally friendly halogen-free flame retardants has attracted the interests of more and more researchers from both the academic and industrial fields.9–15 However, the general non-halogenated flame retardants (FR) such as phosphorus-, silicon-, and nitrogen-containing FRs are usually not efficient enough to enable PC to pass V-0 rating in the UL 94 test until being incorporated with a relatively large amount.6,16–20 For example, among the above halogen-free FRs, phosphorus-containing compounds like triphenyl phosphate (TPP) and resorcinol bis(diphenyl phosphate) (RDP) are the most widely used FRs for PC and their blends, but generally, to enable PC passing UL94 V-0 test, the required additive amount should be as much as 5–15 wt%.21–25 As we known, the additive type flame retardants are generally incorporated into polymeric materials by physical means, a large amount of addition may bring in a variety of problems, such as poor transparency, leaching, and a reduction in mechanical properties.

According to the study,26–28 organosulfonates such as the commercially available potassium diphenylsulfone sulfonate (KSS) are highly effective FRs for PC. In general, very low additions (no less than 1 wt%) of certain metal salt sulfonates can provide a self-extinguishing performance to polycarbonate. However, the halogen-free flame retarding PC composites incorporated with current sulfonates FRs like KSS still have drawbacks. For example, higher flame retardancy is limited and the mechanical properties suffer a loss, which can be attributed to the poor interfacial adhesion between FR and the polymer matrix. Therefore, to design a series of novel efficient sulfonate FRs and to study the effect of their structure on the properties of PC composites is of great significance for promoting the development of this field.

In this paper, ternary and quaternary sulfonate centered on adamantane were designed as 1,3,5-tri(phenyl-4-sodium sulfonate)adamantane (AS3) and 1,3,5,7-tetrakis(phenyl-4-sodium sulfonate)adamantane (AS4), respectively. Owing to the various advantages of adamantane such as having stereo-regularity, multiple substitutability, excellent lipophilicity, good thermal and oxidative stabilities and high rigidity, the novel sulfonate flame retardant with high sulfur content is expected to be more efficient for flame retardancy and less negative to mechanical property. In this study, these two kinds of FRs were first synthesized and characterized, then the flammability of PC composites filled with the novel FR were investigated using a cone calorimeter, as well as the LOI and UL-94 tests. The effect of the two kinds of FR content on mechanical properties and thermal properties of PC/ASn (n = 3, 4) was also systematically studied. Finally, the flame retarding mechanism was deduced from the thermal degradation and the residual char morphology and chemical structure. Using this system, PC composites with only 0.08 wt% AS4 or 0.1 wt% AS3 can pass V-0 and have LOI value higher than 30, and can maintain ideal mechanical properties as well. In addition, it is found that the higher the sulfonate content in FR molecular structure, the better for flame retardant PC.

2 Experimental

2.1 Materials

Polycarbonate (PC, grade: 301-10) was supplied by Dow Chemical Company (American) with a melt index (GB 368283) of 20 g/10 min and a density of 0.918 g cm−3. PC was dried in the oven at 120 °C for 8 h prior to blending. Adamantane (99%) was purchased from Zhang jia gang Xikai Chemical Co., Ltd., China. Bromine (AR, 99.5%), Aluminium chloride (AR, 99%) and tert-butyl bromide (AR, 99%) were purchased from Aladdin. Chlorosulfonic acid (AR) was supplied by Xiya Reagent Co., Ltd., China. The potassium diphenylsulfone sulfonate (KSS) used here as a reference flame retardant was offered by Guangdong Ever Sun Corp., China. Benzene (AR) and dichloromethane (AR) purchased from Guangzhou Chemical Reagent Factory, were distilled in anhydrous calcium chloride before used. Other chemicals were all used without further purification.

2.2 Synthesis of ternary and quaternary sulfonate FR AS3 and AS4

The ASn (n = 3, 4) was synthesized through the reactions of Friedel-crafts arylation from 1-bromoadamantane,29 followed by substitution reaction, hydrolysis reaction and neutralization reaction according to the above reaction route as shown in Scheme 1.
image file: c7ra06504c-s1.tif
Scheme 1 Synthesis route and structures of flame retardants ASn (n = 3, 4).

A typical procedure for synthesis of 1,3,5-triphenyladamantane is as follows: 5.0 g 1-bromoadamantane (23 mmol), 6.5 g tert-butyl bromide (50 mmol), and 175 mL benzene was introduced into a 500 mL three-neck flask equipped with a reflux condenser, a calcium chloride drying tube and a magnetic stirrer. After being stirred for 10 min at 55 °C, 0.2 g aluminium chloride (1.9 mmol) was added slowly and the reaction solution was heated under vigorous reflux for another 10 minutes. Finally, the system was then poured into an ice water and ether mixture, the resultant undissolved substance was filtrated and extracted by chloroform, followed by recrystallization from benzene to get the final product of 1,3,5-triphenyladamantane.

The procedure for preparing 1,3,5,7-tetraphenyladmantane is very similar to that for 1,3,5-triphenyladamantane, except for using more catalyst of aluminium chloride (0.6 g) and reacting for a longer time of 60 min in the same case as shown above. In addition, after the reaction completed, the product is insoluble, so it should be obtained as the filter residue not the filtrate after soxhlet extraction from chloroform. Finally, 1,3,5,7-tetraphenyladmantane was gained after vacuum dried as white solid.

The reaction approaches for both 1,3,5-tri(phenyl-4-sulfochloride)adamantane and 1,3,5,7-tetrakis(phenyl-4-sulfochloride)adamantane are the same. Take 1,3,5-tri(phenyl-4-sulfochloride)adamantane for example, a typical procedure is as follows: 1.35 g 1,3,5-triphenyladamantane (3.72 mmol), 20 mL dry dichloromethane was added to a 100 mL three-neck flask equipped with a reflux condenser, a calcium chloride drying tube, a dropping funnel and a magnetic stirrer in an ice bath, and then to the reaction system was dropwise added 2.5 mL chlorosulfonic acid and 5 mL dichloromethane within 10 min. The temperature was slowly raised to 35 °C and kept stirring for 75 min. After cooling to room temperature, the organic layer was separated by centrifuge, and rotary evaporated to get a brown oil which was washed by water and then filtrated. Finally, 2.35 g (95.7%) solid product of 1,3,5-tri(phenyl-4-sulfochloride)adamantane was obtained after vacuum dried at 45 °C for 12 h.

The procedure for the final step is the same for both AS3 and AS4. To take AS3 for example, a typical method is as follows: 5.0 g 1,3,5-tri(phenyl-4-sulfochloride)adamantane and 300 mL deionized water was added to a 500 mL flask with a reflux condenser and a magnetic stirrer. The mixture was heated at 100 °C for 24 h to give a clear solution which was distilled under reduced pressure, and the residue was dried by vacuum oven at 45 °C for 12 h. Next, the resultant solid was dissolved in 50 mL of water and was neutralized by 10 wt% NaOH solution. After the water was thoroughly removed, the residue was bleached and vacuum dried to afford 5.0 g (98.4%) the product of AS3 as a white salt.

2.3 Preparation of flame retardant PC composites

PC and the flame retardants AS3 and AS4 were first dried overnight at 120 °C before compounding. The PC composites filled with 0.06–0.16 wt% AS3 or AS4 FR were prepared in a HL-200 internal mixer (Jilin University Science and Education Instrument factory, China) under 50 rpm for 8 min at the temperature of 245 °C, which were denoted as PC/AS3 (0.06%), PC/AS3 (0.08%), PC/AS3 (0.1%), PC/AS3 (0.12%), and PC/AS3 (0.16%), respectively. PC/AS4 were labeled in the same manner. The compounds were then broken into pieces and dried in a vacuum oven at 90 °C over 5 h. Afterwards, the composite pieces were injection molded or compression molded into standard sizes for different tests. Unfilled PC and the PC composites filled with flame retardant KSS of a suitable amount were also manufactured under the same conditions for comparison.

2.4 Characterization and measurements

2.4.1 Spectroscopic analysis. The Fourier transform infrared (FTIR) spectra were recorded with KBr on a Nicolet 6700 FTIR spectrometer from 400 to 4000 cm−1. The hydrogen nuclear magnetic resonance (1H-NMR) spectra were recorded on a Bruker AVANCE III HD400-MHz superconducting NMR spectrometer.
2.4.2 Flammability tests. Limiting oxygen index (LOI) measurements were carried out using a HP6115 type oxygen index test apparatus (Foshan, China) following an ASTM D2863-2008 standard procedure, and the dimensions of all samples were 80 mm × 10 mm × 4 mm. The LOI values were calculated based on the results of five tests.

The vertical burning tests (UL-94) were conducted on a ZRS-2 vertical horizontal burning apparatus (NEARBYMRO, Germany) according to ASTM D3801 standard, the dimensions of all samples were 125 mm × 13 mm × 3 mm. In the test, five sample bars suspended vertically over surgical cotton were ignited using a 50 W methane gas burner.

The cone calorimetry test was carried out by using a FTT 0007 cone calorimeter (Fire Testing Technology, UK) in accordance with the ISO 5660 standard procedures. Each specimen, with a dimension of 100 mm × 100 mm × 3 mm, was wrapped in aluminum foil and exposed horizontally to an external heat flux of 35 kW m−2. The recorded parameters included the time to ignition (TTI), heat release rate (HRR, kW m−2), peak value of the heat release rate (PHRR, kW m−2), specific extinction area (SEA), the peak value of smoke production rate (SPR), and CO production rate (COP).

2.4.3 Mechanical tests. The tensile and flexural tests were performed using a PHM-5 universal tester according to an ISO 844 and ASTM D790 standard procedure, respectively. Each batch included five specimens to yield averaged values.

2.5 Thermogravimetric analysis and thermal degradation kinetics

Thermogravimetric analysis (TGA) and thermal degradation kinetics were carried out with a NetzschSTA409 PC thermoanalyzer instrument (Netzsch, Germany). For the thermal analysis of FRs, each sample was heated from 50 to 800 °C at the rate of 20 °C min−1 under nitrogen atmosphere. To test the thermal degradation kinetics, each sample was heated from 50 to 800 °C at various rates of 5, 10, 15 and 20 °C min−1 under air atmosphere. The Flynn–Wall–Ozawa method was used to analyze the thermal degradation kinetics parameters.

2.6 Scanning electron microscopy (SEM)

The SEM observation was performed on a Hitachi S-3400N scanning electron microscope (Hitachi, Japan) to investigate the morphology of the char layer of samples after the LOI tests.

3 Results and discussion

3.1 Chemical structure characterization of FRs

The flame retardant AS3 and AS4 were synthesized via the reaction route presented in Scheme 1. The 1H NMR, IR spectra and elementary analysis data for each intermediate product were provided in the ESI (Fig. S1–S7). Fig. 1(a) shows the 1H NMR spectra of AS3 and AS4 with DMSO-d6 as a solvent, and Fig. 1(b) the IR spectra.
image file: c7ra06504c-f1.tif
Fig. 1 (a) 1H NMR spectra of AS3 and AS4 with DMSO-d6 as solvent, (b) FTIR spectra of AS3 and AS4.

The 1H NMR spectrum of AS3 is shown in Fig. 1(a), the multi-peaks at 1.932–2.070 ppm (m, 12H) correspond to the protons (b + c) of –CH2 in adamantyl. The peak at 2.447 ppm (s, 1H) is attributed to the (a) proton of –CH in adamantyl, and the peaks during 7.444–7.564 ppm (m, 12H) are due to (d + e + f + g) protons in the benzene ring.

As shown in the right side of Fig. 1(a) which is the 1H NMR spectrum of AS4, we can see the chemical shifts of H protons at the peak appearing at 2.06 (s, 12H) correspond to the H protons (a) in CH2 of tetra-substituted adamantyl, and the peaks at 7.515–7.551 (m, 16H) are assigned to H protons (b + c) in = C–H of benzene ring.

To confirm the successful synthesis of AS3 and AS4, FT-IR spectra were also recorded and presented in Fig. 1(b). AS3 shows almost the same absorption peaks with AS4. The peaks at 3022 cm−1, 1600 cm−1 and 1495 cm−1 should be attributed to the stretching vibrations of = C–H and C[double bond, length as m-dash]C in benzene rings, respectively, and the characteristic absorption peak of para-disubstituted benzene ring is observed at 825 cm−1. The peaks corresponding to stretching vibration and the deformative vibration of C–H and–CH2 in adamantane appear at 2923, 1446, 712 cm−1. The characteristic absorption of S[double bond, length as m-dash]O which belongs to the sulfonate group is observed at 1180 and 1041 cm−1. In addition, it can be also shown that a broad absorption peak appears at 3444 cm−1, which should correspond to the signal of absorbed water. Conclusively, the 1H NMR and the FTIR spectra confirm that AS3 and AS4 have been synthesized successfully.

3.2 Thermal analysis of FRs

The basic thermal properties of FRs are vital for their application in polymers.

Fig. 2 shows the thermal stability of the flame retardant AS3 and AS4 by thermogravimetric analysis under nitrogen atmosphere. Both AS3 and AS4 display the similar TG and DTG curves, but AS4 has a little higher degradation temperature. As shown in Fig. 2, about 10 wt% weight loss between 100 and 300 °C results from the evaporation of (i) absorbed moisture and (ii) crystal water. According to the weight loss percent of the corresponding part on the curves, the maximum weight loss between 480 °C and 550 °C should correspond to the released SO2 from the decomposition of the sulfonate groups, and the last stage of weight loss between 630 °C and 800 °C should be attributed to the pyrolysis of –ONa from benzene rings. The residues should be 1,3,5-triphenyladamantane or 1,3,5,7-tetraphenyladamantane and sodium ions. In general, proper decomposition temperature is very important for additive-type flame retardants to work for matrix materials. The maximum decomposition peak temperature which corresponds to the degradation of sulfonate is 527.7 °C for AS3 and 543.3 °C for AS4, that is much higher than the thermo-processing temperature of PC composites and matchable with the degradation temperature of PC (Tpeak = 534.2 °C) (see Fig. 7). It demonstrates that the novel FR system of AS3 and AS4 can well meet the demand for flame retardants of PC in regards to thermal property.


image file: c7ra06504c-f2.tif
Fig. 2 TG and DTG curves of AS3 and AS4 recorded in N2.

3.3 Flammability of PC composites

The flammability of PC/ASn (n = 3, 4) composites was systematically evaluated using LOI, UL-94 and cone calorimetry methods. The results of LOI and UL-94 tests for PC/ASn with different loadings and PC/KSS composites as the control samples are displayed in the above Fig. 3. As shown in Fig. 3, the LOI value of neat PC is 25.8%. After being added with the synthesized new FRs, we can see that both AS3 and AS4 improved the flammability of PC composites efficiently. According to the JISK 7201 industrial standard, with LOI >30%, PC/AS3 with AS3 content between 0.1–0.16 wt% and PC/AS4 with AS4 content 0.08–0.16 wt% within the range studied, can all be assigned to the first class flame retardant materials that are extremely hard to ignite. As to the UL-94 tests, it also can be clearly indicated from Fig. 3 that the UL-94 rating for neat PC is V-2. As to the flame retardant PC composites, only 0.1 wt% AS3 or even 0.08 wt% AS4 can enhance PC materials to pass V-0 rating. So the optimal FR addition amount can be 0.1 wt% for AS3 and 0.08 wt% for AS4. In contrast, the control samples, which are added with KSS as FR instead, under the same FR content, can only reach V-2 with the LOI value of 27.1% for PC/KSS (0.08 wt%) and 28.6% for PC/KSS (0.1 wt%), respectively. Thus the above results from both LOI and UL-94 manifest that our synthesized AS3 or AS4 indeed works well in flame-retarding of PC composites, and AS4 which has more sulfonate content in molecular structure is shown more efficient than AS3.
image file: c7ra06504c-f3.tif
Fig. 3 The LOI values and UL-94 results of flame retardant PC composites PC/AS3 and PC/AS4 with different FR contents. For the control sample of PC/KSS (0.08%) is 27.1%, V-2, and PC/KSS (0.1%) 28.6%, V-2.

Cone calorimetry, as one of the most important bench-scale methods for evaluating the flame retarding performance of materials in a real fire case,30 was further investigated in this work. The samples of PC/AS3 (0.1%), PC/AS4 (0.08%) and PC are tested by cone calorimeter and some of the important results are summarized in Table 1. The heat release rate (HRR), in particular the peak of HRR (pHRR) value, is proved to be the most useful parameter to evaluate fire safety. Fig. 4 shows the HRR plots for pure PC, PC/AS3 (0.1%), and PC/AS4 (0.08%) composites.

Table 1 Cone calorimetric data with a heat flux of 35 kW m−2
Sample PC PC/AS3 (0.10%) PC/AS4 (0.08%)
TTI/s 102 72 86
pHRR (kW m−2) 305.9 243.2 247.8
THR (MJ m−2) 61.0 53.3 59.4
SEA (m3 kg−1) 680.5 510.3 573.3
pkSPR (m3 s−1) 0.133 0.081 0.079
Mean COY (kg kg−1) 0.148 0.103 0.089



image file: c7ra06504c-f4.tif
Fig. 4 Heat release rate curves of PC, PC/AS3 (0.1%) and PC/AS4 (0.08%) composites.

It can be seen from Table 1 and Fig. 4 that neat PC shows a very sharp HRR curve at the time range of 100–400 s with a maximum of 305.9 kW m−2 at 125 s. In comparison, the HRR curves of PC/AS3 (0.1%) and PC/AS4 (0.08%) both become flatter, indicating the lower intensity of a fire. The peak HRR (PHRR) values decrease to 243.2 kW m−2 and 247.8 kW m−2 for PC/AS3 (0.1%) and PC/AS4 (0.08%), respectively. The total heat release (THR) value for neat PC is 61.0 MJ m−2, and it also decreases to 53.3 MJ m−2 and 59.4 MJ m−2 for PC/AS3 (0.1%) and PC/AS4 (0.08%), respectively. These results demonstrate that both AS3 and AS4 can effectively reduce the risk of fire hazard.

Smoke and toxic gas release performances are other very important parameters to determine flame-retardant material in fire safety judgment.31 As seen in Table 1, the SEA data which measures the total generated smoke quantity decreases from 680.5 m3 kg−1 for PC to 510.3 m3 kg−1 and 573.3 m3 kg−1 for PC/AS3 (0.1%) and PC/AS4 (0.08%), respectively. And the pkSPR is also decreased from 0.133 m3 s−1 to 0.081 m3 s−1 and 0.079 m3 s−1, respectively. The lower value of SEA and pkSPR indicates that AS3 and AS4 can both strongly cut down the smoke emission of PC composites. Fig. 5 shows the variation of CO production during the combustion process. The mean CO yield of PC is 0.148 kg kg−1. With addition of ASn (n = 3, 4) FR, the mean CO yield decreased to 0.103 kg kg−1 and 0.089 kg kg−1 for PC/AS3 (0.1%) and PC/AS4 (0.08%), respectively. Moreover, the first peak CO production is significantly decreased from 0.0077 kg kg−1 for neat PC to 0.0043 kg kg−1 and 0.0044 kg kg−1, respectively. This means that the AS3 or AS4 flame retardant system can efficiently suppress poisonous gas emission so as to increase the likelihood of survival at the beginning of a fire.


image file: c7ra06504c-f5.tif
Fig. 5 CO release rate curves of PC, PC/AS3 (0.1%) and PC/AS4 (0.08%) composites.

It is worthwhile to mention that the TTI of pure PC is 102 s, while it is decreased to 72 s and 86 s with addition of 0.1 wt% AS3 and 0.08 wt% AS4, respectively. The unexpected decrease in TTI of PC/ASn composites indicates that AS3 and AS4 may retard the combustion of PC matrix through accelerating the thermal decomposition of PC and quickly promoting the formation of char layers at relatively lower temperature.

From the LOI test, UL-94 test and cone calorimeter results which are discussed above, it is clear that the flame retardancy of PC is significantly enhanced by incorporation of AS3 or AS4 FRs.

3.4 Mechanical properties

As an additive-type flame retardant, the effect of its incorporation on the mechanical properties of matrix material is a matter of concern. Fig. 6 depicts the tensile and flexural properties of PC and its composites. As shown in Fig. 6(a), the tensile strength of virgin PC is 60.55 MPa. With increasing of AS3 content, the tensile strength of PC/AS3 composites increases first and then levels off after a slight decrease. As to PC/AS4, the tensile strength keeps gradually increasing and then levels off with additional AS4 content. With the addition of FR at the optimal content for flame retardancy, the tensile strength rises to 61.58 MPa and 61.88 MPa for PC/AS3 (0.1%) and PC/AS4 (0.08%), respectively. While the control samples of PC/KSS (0.1%) and PC/KSS (0.08%) have the tensile strength of 59.88 MPa and 60.1 MPa, respectively, which are both lower than that of neat PC. As to the flexural test, we see that the flexural strength of PC/AS3 is slightly decreasing and then increasing with the rise of AS3 content, while for PC/AS4, the flexural strength increases first and then decreases sharply. At the optimal addition of each FR for flame retardancy, the flexural strength of PC/AS3 (0.1%) is 84.87 MPa, slightly reduced by 1.8% compared to that of pure PC of 86.47 MPa, and PC/AS4 (0.08%) is 88.75 MPa, increased by 2.6% compared to that of PC. In contrast, the flexural strengths are only 76.88 MPa and 78.88 MPa for the control samples of PC/KSS (0.1%) and PC/KSS (0.08%), respectively, which is decreased by 11% than PC.
image file: c7ra06504c-f6.tif
Fig. 6 (a) Effect of the FR content on the mechanical strengths of PC/AS3 and PC/AS4 composites; (b) histogram of the mechanical strengths of PC, PC/AS3 (0.1%), PC/AS4 (0.08%) and the control samples of PC/KSS (0.1%) and PC/KSS (0.08%).

In conclusion, the novel FR system we proposed in this study can effectively alleviate the deterioration of FR to the mechanical strength of polymeric matrix, and can even improve it to a certain extent in some cases. The advantages of AS3 and AS4 FR over the current existing control FR for PC could be attributed to the low incorporated content and the high stiffness and lipid solubility of adamantly that make AS3 and AS4 of better compatibility with PC.

3.5 Flame retardant mechanism

3.5.1 Thermal decomposition properties of PC composites. In order to clearly understand the flame retardant mechanism of PC/AS3 and PC/AS4, the thermal stability of the flame retardant PC composites is investigated by TGA. Moreover, the Flynn–Wall–Ozawa method is used to analyze their thermal degradation kinetics.

Histogram of average activation energy of PC, PC/AS3 (0.1%), and PC/AS4 (0.08%) with the degradation conversion rate from 0 to 70% calculated by the Flynn–Wall–Ozawa method.

The thermal degradation and stability of polymers have substantial connection with their flame retardancy. Therefore, TG analysis was used to investigate the thermal degradation properties of PC and its composites. Fig. 7(a) shows the TG and DTG curves under air for the PC, PC/AS3 (0.1%), and PC/AS4 (0.08%) composites, respectively. Compared to PC, it is observed that both the TG and DTG curves of PC/AS3 (0.1%) and PC/AS4 (0.08%) shift forward to lower temperature successively. The corresponding data such as onset decomposition temperature (T5%), the temperature at maximum weight loss rate (Tpeak) are list in the insert table of Fig. 7(a). It is found that the T5%, Tpeak of PC are 485.2 °C and 534.2 °C, respectively. However, the T5%, Tpeak are 468.2 °C, 528.8 °C, and 470.4 °C, 521.9 °C for PC/AS3 (0.1%) and PC/AS4 (0.08%) respectively. This result is in accordance with the variation of TTI listed in Table 1 that the TTI of the PC/AS3 and PC/AS4 composites are shorter than that of virgin PC. It can be deduced that the sulfonate groups in AS3 or AS4 flame retardants accelerate the decomposition of PC and promote its char-forming so as to result in the decline of the degradation temperature as well as TTI. Therefore, the decreased thermal stability is essential rather than a drawback of the multi-sulfonate FR system.


image file: c7ra06504c-f7.tif
Fig. 7 (a) TG and DTG curves of PC, PC/AS3 (0.1%), PC/AS4 (0.08%) composites, (b).

Furthermore, to study the degradation behavior of the PC composites, the Flynn–Wall–Ozawa method is used to analyze their thermal degradation kinetics. According to this method, the degradation activation energy can be determined directly from the log[thin space (1/6-em)]β versus 1/T plot as follows.32

image file: c7ra06504c-t1.tif
where A is the pre-exponential factor, R is the gas constant, E is the activation energy, β is heating rate, T is the Kelvin temperature, and f(α) is the integrated form of the conversion dependence function. The TG curves for PC, PC/AS3 (0.1%), PC/AS4 (0.08%) composites recorded under various heating flow rates of 5, 10, 15 and 20 °C min−1 under air atmosphere are shown in Fig. S8–S10. The activation energy data of the three samples calculated by the Flynn–Wall–Ozawa method are listed in Tables S1–S3, and the average thermal degradation activation energies within the conversion rate from 0 to 70% are shown in Fig. 7(b). It can be seen clearly from Fig. 7(b) that the average activation energy of PC is 176.9 kJ mol−1. When AS3 or AS4 is added, the average activation energy decreases to 160.7 kJ mol−1 and 153.5 kJ mol−1 for PC/AS3 (0.1%) and PC/AS4 (0.08%), respectively. Comparatively, the average activation energy of PC/AS4 (0.08%) is lower than that of PC/AS3 (0.1%), which demonstrates stronger accelerating decomposition. This result further manifests that both AS3 and AS4 can accelerate PC decomposition. AS4, with more sulfonate content in its molecular structure is relatively stronger, which is consistent with TGA results as shown in Fig. 7(a). This could be due to the SO2 generated from sulfonate degradation which shows high catalysis ability for PC decomposition.

3.5.2 Morphology and structure analysis of char residue. In order to further understand the flame retarding mechanism of PC/ASn system, the morphology and chemical structure of residual char obtained from the sample after LOI test was investigated by SEM and FT-IR, respectively. As can be observed in Fig. 8, the residue char surface of PC is smooth but with macro-pores and crevices, which cannot provide a good barrier for the polymer. In comparison, the char layers of both PC/AS3 and PC/AS4 samples are continuous and expansionary with a multitude of expanded spheres. This intumescent char layer provides a good flame shield to stop the propagation of heat and mass to the underneath layer, and delays the volatilization of combustible gases, it also retards the penetration of oxygen, and the feedback of heat. Consequently, such a useful char layer as the flame barrier can make the corresponding PC composites achieve excellent fire retardation.
image file: c7ra06504c-f8.tif
Fig. 8 SEM photos of the residue char for (a) PC, (b) PC/AS3 (0.1%) and (c) PC/AS4 (0.08%) composites.

Fig. 9 shows the FT-IR spectra of virgin PC and the residual char of PC/AS3 (0.1%) and PC/AS4 (0.08%), respectively. We can see that the FT-IR spectra for residual char of PC/AS3 and PC/AS4 are almost the same, but are of many differences compared to that of the virgin PC. The absorption peak in 3439 cm−1 and 1400 cm−1 represents the stretching and plane bending vibration of –OH groups, respectively. The characteristic peaks in 1630 cm−1 and 1597 cm−1 are attributed to the –C[double bond, length as m-dash]C– in the benzene ring. The above information in FT-IR spectra of residue char for PC/ASn (n = 3, 4) composites indicate that some aromatic alcohol compounds are produced in the residual char of PC/AS3 or PC/AS4 after combustion.


image file: c7ra06504c-f9.tif
Fig. 9 FT-IR spectra of virgin PC, and the residual char of PC/AS3 (0.1%) and PC/AS4 (0.08%).

From the FT-IR results in combination with the above char morphology and TG analysis of PC and its composites, we can obtain the flame retarding mechanism as follows: the flame retardant AS3 or AS4 first decomposes in case of fire and produces SO2 that serves as a kind of catalyst to accelerate the decomposition of PC. Subsequently, some compounds containing aromatic alcohol are then generated and further cross-linked automatically to promote intumescent char formation, so that the unburned PC is protected with high flame retardancy.

4 Conclusions

Two flame retardants (AS3 and AS4) with multi-sulfonate centered on adamantane have been synthesized successfully and characterized by 1H NMR and FTIR spectra. The TGA results of AS3 and AS4 demonstrate that the novel flame retardants have matchable thermal stability with PC matrix. Both the ternary sulfonate AS3 and the quaternary sulfonate AS4 exhibit high flame retardant ability to PC. Only 0.1 wt% AS3 or 0.08 wt% AS4 can provide PC composites with UL-94 V-0 rating and improve the LOI value from 25.8% to 31.2% and 32.3% for PC/AS3 (0.1%) and PC/AS4 (0.08%), respectively. Moreover, the results from cone calorimetry show that HRR, THR and COY of both PC/AS3 and PC/AS4 are reduced compared to the neat PC. In addition, they can maintain good mechanical strength, especially for PC/AS4 which displays increased mechanical strength in most cases. Finally, we obtain the flame retarding mechanism of this new PC/ASn system is that AS3 and AS4 have a high catalytic effect to accelerate PC thermal degradation and protective char formation. This novel sulfonate flame retardant system provide a new green solution for decreasing the deterioration of the mechanical performance and enhancing the flame retardancy simultaneously.

Acknowledgements

The authors would like to thank Sun Yat-sen University for plastic processing equipments, Kingfa Sci. and Tech. Co., Ltd. for supporting cone calorimetry tests. In addition, we thank James Wilk who is a English teacher in University of Massachusetts-Amherst for helping us to check the English writing of the revised manuscript. Funding: This work was supported by the National Natural Science Foundation of China [grant numbers 21476051, 21506038 and 21676058], the Nature Science Foundation of Guangdong Province [grant number 2014A030310307], and the Science and Technology Project of Guangdong Province [grant numbers 2013B010403028 and 2016A050502057].

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Footnote

Electronic supplementary information (ESI) available. See DOI: 10.1039/c7ra06504c

This journal is © The Royal Society of Chemistry 2017