Introduction

Peroxides can be mainly divided into organic peroxides (OPs) and inorganic peroxides. Inorganic peroxides are generally oxidizing substances and are unreactive. By contrast, OPs are unstable and potentially explosive when exposed to thermal sources or even mechanical impact. Thus, the storage, transportation, manufacturing, and disposal of OPs can be dangerous. Under unexpected situations, OPs might cause accidents if the peroxy functional groups (–O–O–) in them decompose, because this produces an enormous amount of heat and pressure and engenders fires or explosions [1,2,3,4,5,6,7,8].

OPs are affected by their external environment, such as thermal sources or high temperatures, exposure to which may result in fire, explosion, toxic release, or other destruction that is detrimental to the environment [9] and additionally has costly social effects. The OP 1,1-bis(t-butylperoxy)-3,3,5-trimethylcyclohexane (TMCH) is used as a catalyst in polymerization reactions and as a cross-linking agent in the chemical industry. The CAS number of TMCH is 6731-36-8. Being intrinsically unstable and thermally reactive, this OP can trigger runaway reactions when mixed with acids, bases, or metal ions because the mixing process induces catalytic reactions [10,11,12,13,14,15,16]. Some metal ions adversely affect the thermal stability of TMCH. Metal ions are commonly present everywhere in manufacturing equipment such as rotating equipment, metal containers, and aging pipelines. Most storage containers, waste storage tanks, and pipelines are made of metal, such as copper or iron, which can age and rust, and using these for the storage and transport of TMCH may trigger a runaway reaction [17].

We investigated the thermal hazard characteristics and incompatible reactions of TMCH when it is mixed with various metal ion solutions, such as copper chloride (CuCl2) and ferric chloride (FeCl3), to determine how related thermal explosions could be prevented [18]. Thermokinetic parameters, including the apparent onset temperature (T 0), heat of decomposition (ΔΗ d), and maximum temperature (T max), were detected by differential scanning calorimetry (DSC) [19]. Through isoconversional kinetic analysis using nonisothermal experimental data, we obtained isothermal thermokinetic parameters including the isothermal time to maximum heating rate (TMR iso), highest or peak heat flow, reaction time, and apparent activation energy (E a) at different isothermal temperatures (60.0, 70.0, 80.0, and 90.0 °C). We conducted isothermal tests using thermal activity monitor III (TAM III) to identify the differences between the simulation and isothermal experimental results.

The results of this study can be used as a reference for the reactions caused by the mixing of TMCH and metals during the storage and transportation of TMCH. Inherently safer equipment could thus be designed for TMCH storage and transportation to avoid endangering the manufacturing system under adverse conditions [20,21,22].

Experimental

Sample preparations

To assess the reaction and determine the related thermokinetic parameters of TMCH when mixed with metal ions (copper and iron), we purchased 88.0 mass% TMCH from ACE Chemical Corporation, Taiwan, and stored it in a refrigerator at 4.0 °C. The chemical structural formula of TMCH is illustrated in Fig. 1. TMCH was mixed with commonly used and commercially available metal ion solutions. CuCl2 and FeCl3, diluted with distilled water to 5.0 mass%, were used in this study. The oxygen balance (OB %) of the organic peroxide and other compounds was calculated using [23,24,25,26]

$${\text{OB}}\% = \frac{ - 1600}{W} \times \left( {2X + \left( {\frac{Y}{2}} \right) + M - Z} \right)$$
(1)

where W is the molecular weight of the compound (in g mol−1) and M, X, Y, and Z are the numbers of metal, carbon, hydrogen, and oxygen atoms, respectively. Moreover, the sample mass of each experiments is listed in Tables 28.

Fig. 1
figure 1

Chemical structural formula of TMCH [1, 8]

DSC

The DSC apparatus used contained reference and target samples, a furnace, and a thermal resistance material. The outer wall of the entire body of the furnace was wrapped in an adiabatic shell to prevent heat loss and external temperature interference. The DSC apparatus combined with STARe software was used to measure the heating of the chemical substances during a warming scan, and the material’s endothermic and exothermic energy changes and basic thermal safety parameters were evaluated. The reference and target samples were heated in the same furnace simultaneously, leading to each sample having a different temperature and causing the target sample to release energy during thermal decomposition. Accordingly, the heat of decomposition in the cell was determined.

Programmable temperature control was used during the DSC tests, with various heating and cooling rates from 0.01 to 750.0 °C min−1 used and target sample temperatures from −150.0 to 700.0 °C detected. To ensure favorable equilibrium was attained during heating, we used heating rates β of 0.5, 1.0, 2.0, 4.0, and 8.0 °C min−1, and the temperature range considered was 30.0–300.0 °C. Each set of experiments was produced at least three times to ensure repeatability. The results of DSC were averaged to list the calorimetric data. The Kissinger formal model was applied to evaluate the kinetics. In addition, linear regression was employed to determine the apparent activation energy E a from the regression slope. We obtained various heating rates and peak temperatures using DSC:

$$\frac{{2.303 [\log \left( {\beta /T_{\hbox{max} }^{2} } \right)]}}{{1/T_{\hbox{max} } }} = \frac{{ - E_{\text{a}} }}{R}$$
(2)

Thermal simulation using isoconversional kinetic analysis

Differential isoconversional kinetic analysis was used to estimate the thermal stability of the TMCH–metal ion mixtures under the temperature conditions employed. We imported DSC experimental data and calculated kinetic parameters, such as TMR iso and E a, to predict the response mode under isothermal and nonisothermal conditions [27,28,29]. The relationship between conversion rate and absolute temperature was used to determine E a (α):

$$\frac{{{\text{d}}\alpha }}{{{\text{d}}t}} = A\left( \alpha \right)\exp \left[ { - \frac{{E_{\text{a}} \left( \alpha \right)}}{RT\left( t \right)}} \right]f\left( \alpha \right)$$
(3)
$$A^{'} \left( \alpha \right) = A\left( \alpha \right)f\left( \alpha \right)$$
(4)
$$\frac{{{\text{d}}\alpha }}{{{\text{d}}t}} = A^{'} \left( \alpha \right)\exp \left[ { - \frac{{E_{\text{a}} \left( \alpha \right)}}{RT\left( t \right)}} \right]$$
(5)
$$t_{\text{a}} = \mathop \smallint \limits_{0}^{t} {\text{d}}t = \mathop \smallint \limits_{{\partial_{0} }}^{\alpha } \frac{{\text{d}}\alpha }{{A^{'} \left( \alpha \right)\exp \left[ { - \frac{{E_{\text{a}} \left( \alpha \right)}}{RT\left( t \right)}} \right]}}$$
(6)
$$\ln \left( {\frac{{\text{d}}\alpha }{{\text{d}}t}} \right) = \ln \left( {A^{'} \left( \alpha \right)} \right) - \frac{{E_{\text{a}} \left( \alpha \right)}}{RT\left( t \right)}$$
(7)

where A is the frequency factor, f(α) is the reaction model, t is the reaction time, and T is the temperature.

Thermal activity monitor III

Isothermal calorimetry, TAM III, was used to explore the changes in the material’s thermal response under constant temperature; TAM III involves a continuous and highly thermally sensitive thermostat system and equipment for detecting the stability of the material. The liquid in the thermostat of TAM III was mineral oil, contained in a reactor with a total volume of 25.0 L. Because an external heating thermostat was used and the bottom of the microheater controlled the mineral oil temperature, a perfect isothermal effect was achieved. The temperatures used were 15.0–150.0 °C, and the maximum change in temperature over one day was less than 0.0001 °C. The decomposition of the sample was thus measured using TAM III under isothermal conditions [6]. TAM III Assistant™ software was further used to govern the thermostat and calculate thermokinetic parameters, which were then used to validate the simulation results of the differential isoconversional kinetic analysis.

TAM III was used to determine the thermal decomposition reactions of 88.0 mass% TMCH and 88.0 mass% TMCH mixed with either 5.0 mass% CuCl2 or FeCl3. The mass of the sample used in a cell was 100.0 mg of TMCH mixed with 10.0 mg of CuCl2 or FeCl3 at 60.0, 70.0, 80.0, or 90.0 °C. TMR was used as a safety index to evaluate the degree of hazard; therefore, we used TMR iso to evaluate the runaway hazard of TMCH [30].

Results and discussion

Thermal analysis of DSC tests

The oxygen balance (OB %) indicates whether a reactant molecule contains a surplus or insufficient amount of oxygen available for oxidation during combustion. The OB % of TMCH was −248.6, indicating low thermal hazard. The DSC results were measured by using a PerkinElmer DSC8500 with thermal analysis, determining the heat of decomposition and T 0 under different temperatures. The thermal characteristics of pure TMCH and TMCH mixed with 5.0 mass% CuCl2 or FeCl3 are presented in Tables 14. The average ΔΗ d values of pure TMCH, TMCH mixed with CuCl2, and TMCH mixed with FeCl3 were 1584.8, 898.9, and 1161.1 J g−1, respectively. ΔH d was not changed in any systematic way when M and β were altered in the pure TMCH DSC experiments. The highest ΔH d value was 1890.9 J g−1, obtained when β was 8.0 °C min−1 and M was only 0.4 mg.

Table 1 Hazard of TMCH mixed of CuCl2 or FeCl3 as assessed using React95 [31]
Table 2 Calorimetric data from DSC tests of TMCH 88.0 mass%
Table 3 Calorimetric data from DSC tests of TMCH 88.0 mass% mixed with 5.0 mass% CuCl2
Table 4 Calorimetric data from DSC tests of TMCH 88.0 mass% mixed with 5.0 mass% FeCl3

For mixed TMCH and CuCl2, ΔH d was also neither constant, nor did it change systematically. The ΔH d value at β = 0.5 °C min−1 was 1369.2 J g−1, but the ΔH d values at different β values in this set of experiments were scattered between 709.8 and 814.4 J g−1. For TMCH mixed with FeCl3, the calculated ΔH d values were distributed between 862.9 and 1374.7 J g−1, comparatively higher than the values for TMCH mixed with CuCl2. Compared with that of pure TMCH, the ΔΗ d value of TMCH mixed with CuCl2 or FeCl3 was lower and the T 0 value of TMCH mixed with CuCl2 or FeCl3 was lower. Only one exothermic peak was detected during the DSC tests of TMCH.

Figure 2 illustrates the DSC curves of pure TMCH when different heating rates were used. There is a consistent trend in the curves, with the height of the curve’s peak dramatically increased at high β. Because of the excellent consistency observed in the DSC experiments, the E a value of pure TMCH was calculated with a high degree of confidence. The DSC curves of TMCH mixed with CuCl2 or FeCl3 also illustrate one dominating exothermic peak, and the T 0 value of TMCH mixed with CuCl2 or FeCl3 was between 108.6 and 137.1 °C (Figs. 24). The results from various heating rates indicated that the faster the reaction was, the greater the intensity of heat omitted became, whereas the lower the heating rate was, the later the appearance of the exothermic peak became.

Fig. 2
figure 2

DSC curves of heat flow versus temperature for pure TMCH decomposition at heating rates of 0.5, 1.0, 2.0, 4.0, and 8.0 °C min−1

Fig. 3
figure 3

DSC curves of heat flow versus temperature for the decomposition of TMCH mixed with 5.0 mass% CuCl2 at heating rates of 0.5, 1.0, 2.0, 4.0, and 8.0 °C min−1

Fig. 4
figure 4

DSC curves of heat flow versus temperature for the decomposition of TMCH mixed with 5.0 mass% FeCl3 at heating rates of 0.5, 1.0, 2.0, 4.0, and 8.0 °C min−1

Figure 5 illustrates a plot of the natural logarithm of the heating rate versus the reciprocal of the absolute temperature for TMCH and the TMCH mixtures. Through the application of the Kissinger kinetic equation, the E a values of TMCH, TMCH mixed with CuCl2, and TMCH mixed with FeCl2 were determined to be 129.8, 127.1, and 143.1 kJ mol−1, respectively. The E a value was lowest for TMCH mixed with CuCl2, whereas the E a value of TMCH mixed with FeCl2 was substantially higher than those of the other two samples.

Fig. 5
figure 5

E a analysis graphs for TMCH, TMCH mixed with CuCl2, and FeCl2 at heating rates of 0.5, 1.0, 2.0, 4.0, and 8.0 °C min−1 using the Kissinger kinetic equation

Thermal simulation using isoconversional kinetic analysis

DSC can acquire the experimental parameters of pure TMCH or TMCH mixed with 5.0 mass% CuCl2 or FeCl3, such as the sample mass, reaction time, reaction temperature, and heat flow; such parameters can be used to execute isoconversional kinetic analysis. The relationship between heating rate and E a was determined through isoconversional kinetic analysis simulations. Using isoconversional kinetic analysis, E a of pure TMCH, TMCH mixed with CuCl2, and TMCH mixed with FeCl3 were obtained from a linear regression model for the natural logarithm of the heating rate versus the reciprocal of absolute temperature. The corresponding temperatures were obtained from the peak of heat flow of five different heating rates. According to the plots in Fig. 6, the E a values calculated using nonisothermal heating rates for pure TMCH, TMCH mixed with CuCl2, and TMCH mixed with FeCl3 were 137.9, 119.5, and 132.6 kJ mol−1, respectively. The linear regression model had an excellent fit, and Fig. 6 shows the high accuracy of the thermokinetic model of the three TMCH mixtures for varying heating rate. The E a value was substantially lower for TMCH mixed with CuCl2 than for the other two samples.

Fig. 6
figure 6

E a analysis graph of TMCH, TMCH mixed with CuCl2, and TMCH mixed with FeCl3 determined from isoconversional kinetic analysis with different nonisothermal heating rates of 0.5, 1.0, 2.0, 4.0, and 8.0 °C min−1

The results of E a analysis for TMCH and TMCH mixed with different metal ions are similar because they were calculated using the Kissinger kinetic equation. Of the three samples subjected to isoconversional kinetic analysis, TMCH mixed with CuCl2 exhibited the lowest E a value. Therefore, isoconversional kinetic analysis effectively simulated the exothermic reactions in pure TMCH, TMCH mixed with 5.0 mass% CuCl2, and TMCH mixed with 5.0 mass% FeCl3 under isothermal conditions (i.e., temperatures of 60.0, 70.0, 80.0, and 90.0 °C), and Figs. 79 display the corresponding curves of heat flow versus time for these samples, respectively. These figures indicate that for TMCH mixed with 5.0 mass% CuCl2 or 5.0 mass% FeCl3, the isothermal temperature was higher, the heat flow was enhanced, and the reaction was prematurely terminated; the maximum reaction time simulated was 15 h. The isothermal simulation results (Figs. 79) were effectively exhibited but not fitting perfectly. It is because the isothermal simulation data were calculated from nonisothermal conditions by DSC in which the sample mass was poured in 10.0 mg. However, the isothermal experiments (Figs. 1012) were carried out by TAM III in which the sample mass was high to 100.0 mg.

Fig. 7
figure 7

Differential isoconversional kinetic analysis simulation of isothermal curves for decomposition of pure TMCH at 60.0, 70.0, 80.0, and 90.0 °C

Fig. 8
figure 8

Differential isoconversional kinetic analysis simulation of isothermal curves for decomposition of TMCH mixed with 5.0 mass% CuCl2 at 60.0, 70.0, 80.0, and 90.0 °C

Fig. 9
figure 9

Differential isoconversional kinetic analysis simulation of isothermal curves for decomposition TMCH mixed with 5.0 mass% FeCl3 at 60.0, 70.0, 80.0, and 90.0 °C

Fig. 10
figure 10

TAM III thermal curves of heat flow versus time for decomposition of pure TMCH at 60.0, 70.0, 80.0, and 90.0 °C

Fig. 11
figure 11

TAM III thermal curves of heat flow versus time for decomposition of TMCH mixed with 5 mass% CuCl2 at 60, 70, 80, and 90 °C

Fig. 12
figure 12

TAM III thermal curves of heat flow versus time for decomposition of TMCH mixed with 5.0 mass% FeCl3 at 60.0, 70.0, 80.0, and 90.0 °C

Few exothermic reactions occurred in any sample when the temperature was 60.0 °C; however, small exothermic reactions occurred after 2 h at 70.0 °C. At 80.0 °C, nevertheless, substantial exothermic phenomena occurred in the TMCH and TMCH mixtures during the isothermal simulations. The heat flow was not large but was sufficient to cause heat accumulation if a storage container contained a large amount of chemicals. At 90.0 °C, the maximum heat flow was significantly higher and TMR iso was shorter than those at lower temperatures. The simulation results thus reveal that the maximum heat flow of TMCH mixed with metal ions was remarkably higher than that of pure TMCH. This phenomenon was more noticeable when the isothermal surroundings were at a higher temperature.

Isothermal analysis of TAM III tests

The results of heat flow versus time for pure TMCH or TMCH mixed with 5.0 mass% metal ions at different isothermal temperatures determined using TAM III are presented in Figs. 1012. The terminal reaction time decreased as the experimental temperature was increased. TMR iso decreased when the isothermal temperature was increased, down from 189.3 to 0.5 h for pure TMCH when the isothermal temperature was changed from 60.0 to 90.0 °C, as detailed in Tables 58. TMR iso since TMCH mixed with CuCl2 was dramatically reduced from 106.4 to 1.5 h, although the heat flow in the sample was greater than that in pure TMCH or TMCH mixed with FeCl3, as demonstrated in Figs. 1012. At 90.0 °C, the heat flow in TMCH mixed with CuCl2 was more unstable than that in pure TMCH or TMCH mixed with FeCl3. TMR iso of pure TMCH was shorter than that of TMCH mixed with CuCl2 at isothermal temperatures of 60.0, 70.0, 80.0, and 90.0 °C. However, the TMR iso duration observed for pure TMCH in the TAM III isothermal experiment was shorter than those observed in the other isothermal experiments at 80.0 and 90.0 °C.

Table 5 Scanning data of the thermal runaway decomposition of pure TMCH and TMCH mixed with metal ions at 60.0 °C using TAM III
Table 6 Scanning data of the thermal runaway decomposition of pure TMCH and TMCH mixed with metal ions at 70.0 °C using TAM III
Table 7 Scanning data of the thermal runaway decomposition of pure TMCH and TMCH mixed with metal ions at 80.0 °C using TAM III
Table 8 Scanning data of the thermal runaway decomposition of pure TMCH and TMCH mixed with metal ions at 90.0 °C using TAM III

When TMCH was mixed with FeCl3, TMR iso decreased remarkably from 131.7 to 2.3 h when the temperature was increased from 60.0 to 90.0 °C. Although these TMR iso durations were shorter than those for pure TMCH, the heat flow was still substantial. As illustrated in Figs. 11 and 12, the TMR iso duration of TMCH mixed with CuCl2 was shorter because the exothermic peak in the corresponding thermal curve was significantly sharper and higher than that in the curve for TMCH mixed with FeCl3. Both differential isoconversional kinetic analysis simulations and TAM III isothermal experiments indicated that the heat flow of TMCH mixed with CuCl2 was prominently higher when a higher temperature was used. The reaction time determined in the TAM III experiment was much longer than that calculated through differential isoconversional kinetic analysis simulations. However, the reactivity levels of TMCH mixed with FeCl3 demonstrated using simulations and experiments were similar, as illustrated by the exothermic peaks.

In summary, results from experiments and simulations under isothermal conditions matched reasonably well. Greater heat flow was discovered at higher temperatures, with TMR iso correspondingly shorter.

Conclusions

Although no obvious catalysis was observed in TMCH mixed with metal ions, the effect of high heat flow at high temperatures should not be ignored. DSC revealed that T 0 was decreased as the heating rate was increased when TMCH was mixed with CuCl2 or FeCl3, and that heat flow was reduced for TMCH mixed with CuCl2 in the nonisothermal tests compared with pure TMCH. The results differed when isothermal temperatures were used in experiments. TMCH mixed with metal ions accumulates heat and thus produces thermal energy. TMR iso was shortened at isothermal temperatures when CuCl2 or FeCl3 was added to TMCH. The E a value of pure TMCH was lower than that of TMCH mixed with FeCl3, indicating that reactions could occur readily in pure TMCH.

In addition to OP storage and transportation challenges, the chemical industry must handle waste stream treatments wherein mixtures are not completely recycled. This may result in incompatible reactions, leading to a thermal accident. In the future, OPs mixed with metal ions must be investigated using schematic and systematically approaches with analytical assessments as well as the identification of reaction mechanisms.