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
First published on 10th August 2017
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.
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.
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.
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).
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 CC 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 SO 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.
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.
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.
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 |
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.
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.
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.
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.
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 logβ versus 1/T plot as follows.32
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 –CC– 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.
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.
Footnote |
† Electronic supplementary information (ESI) available. See DOI: 10.1039/c7ra06504c |
This journal is © The Royal Society of Chemistry 2017 |