1. Introduction
Hydrogen peroxide has been a well-established and widely used propellant since the beginning of the rocket propulsion era. Its earliest documented applications include systems such as the Walter HWK 109-500 thruster, which was employed as a liquid-propellant assist rocket for various aircraft, and the H
2O
2-based turbopumps that fueled the German V2 rocket during World War II [
1]. Over the following 80 years, from the 1940s to the present day, the highly concentrated aqueous solution commonly known as High Test Peroxide (HTP) has been selected for various spacecraft and rocket propulsion systems owing to some of its unique chemico-physical characteristics. These include high density, which implies high specific impulse, reducing the volume and dry mass of the relative tanks [
2]. Its liquid nature (at ambient pressure and room temperature) and chemical stability make it easy to store, and are coupled with low procurement costs and relatively low toxicity, also dictated by low vapor pressure at room temperature [
1]. In addition, its high specific heat makes it suitable for regenerative cooling applications [
2]. This is paired with satisfactory propulsive performance for numerous applications, and with the ability to feed different types of propulsion systems. Specifically, hydrogen peroxide can be employed for monopropellant thrusters, as an oxidizer in liquid bipropellant systems, including quasi-hypergolic and hypergolic configurations, and in hybrid rocket engines. It can also be used as a gas generator to drive turbo pumps in more complex propulsion architectures. This versatility provides significant flexibility, enabling it to meet a wide range of mission requirements. The working principle shared by all of the above-mentioned technologies is the exothermic decomposition of hydrogen peroxide, which follows the reaction scheme shown in Equation (
1) [
1].
This mechanism generates an oxygen-rich gas and releases a large amount of heat, equal to 97.98 kJ/mol of pure H
2O
2 decomposed. Among the possible applications, the resulting flow can be used as a propellant for hybrid rockets, such as the ILR-33 AMBER [
3], Nammo’s Nucleus sounding rocket [
4], and DLR/HyImpulse mini-launcher [
5], as well as a Reaction Control System (RCS), as was the case for missions such as Mercury, SYNCOM II/III, and COMSAT [
6]. The exothermic decomposition of hydrogen peroxide can be activated by exposing the aqueous mixture to high temperatures or through interaction with chemical elements or molecules, resulting in thermal or catalytic decomposition, respectively. The latter is typically preferred because, by choosing suitable catalysts, the activation energy of the phenomenon can be lowered [
1], facilitating the reaction and making it more controllable, repeatable, and reliable.
The development of catalysts for propulsion applications has always been one of the most active areas of research related to hydrogen peroxide-based systems. The main challenge is to develop materials capable of ensuring satisfactory performance in a reliable manner, while at the same time guaranteeing resistance to chemical degradation and mechanical strength. This is crucial considering applications that require an extended lifetime and a high number of thermomechanical cycles. One of the first and historically most widespread technological solutions involved the use of silver mesh. However, the low melting temperatures typical of materials containing this element constitute a critical disadvantage, as they limit the maximum concentration of H
2O
2 that can be employed [
7]. Indeed, higher HTP concentrations imply higher temperatures of the decomposition products, which can reach up to 1000 °C for 99% HTP [
1]. Furthermore, silver gauze typically exhibits degraded performance at low operating temperatures, complicating the startup of the catalytic component. To overcome these problems, advanced catalysts based on chemical compounds such as platinum, palladium, lead oxides [
8], manganese oxides [
9], and alkali permanganates [
10] have been developed over the years, often coupled with ceramic substrates such as alumina. These technologies are not immune to issues such as poisoning (by stabilizers and impurities), thermomechanical degradation, powdering, and the creation of excessive pressure drops across the catalytic bed [
9]. However, their use generally guarantees significantly higher propulsive performance than that obtained with classic silver gauze [
8,
11], and they are therefore preferred.
As mentioned above, one of the key aspects to be analyzed for the successful use of catalysts is their durability and the degradation phenomena induced by thermomechanical and chemical stresses during successive decomposition cycles. Several studies have addressed this issue, attempting to characterize various types of substrates, chemical compounds, and manufacturing methods. In [
11], Palmer et al. performed an extensive study regarding 33 different types of catalyst, sorted among three main categories depending on their substrate: metallic foam-based, ceramic-based, and metallic gauze-based. Each sample was characterized by different catalytic compounds selected among the most common ones, ranging from platinum, to manganese oxide and palladium. Experimental tests measured decomposition capabilities and assessed structural and catalytic degradation induced by successive decomposition cycles. Results show that fatigue survivability, mechanical integrity, and durability are critical aspects and that, despite the numerous combinations evaluated, only a very limited number of catalysts can guarantee acceptable catalytic performance for possible applications in space propulsion [
11]. Torre et al. [
12] analyzed the durability and resistance to poisoning of 20 samples composed of a spherical alumina substrate coated with various catalytic chemical compounds: platinum, palladium, manganese oxides, ruthenium oxides, and silver. The phenomenon of poisoning can be caused by stabilizing substances present in hydrogen peroxide to prevent its self-decomposition, such as pyrophosphate ions [
11]. These chemical elements can interact with the catalytic bed, inhibiting its action and lowering its catalytic performance. The catalysts were subjected to numerous decomposition cycles, studying their behavior over time. Even in this case, a trend of degradation and consequent inactivation of some batches was observed, both with the Pd/Al
2O
3 formulation (ALTA ID LR-63) and with the Ag/Al
2O
3 (ALTA ID LR-121), as well as for Mn
xO
y/Al
2O
3 (ALTA ID LR-161) catalysts. All other samples, on the other hand, showed high resistance to degradation and poisoning [
12]. However, it should be noted that, in addition to the different chemical composition and manufacturing techniques used for the catalysts examined in this work, the concentration of hydrogen peroxide used is relatively low (30% wt). For applications in monopropellant/hybrid thrusters, where the HTP used is typically concentrated between 85% and 98%, the thermo-mechanical and chemical stresses are greater, which could reduce the durability of the catalysts studied. A progressive degradation of catalysts was also noted in [
13,
14], where the performance and endurance of four platinum catalysts on a ceramic base were evaluated. In firing tests carried out with 90% HTP, a deterioration in catalytic capacity was observed for samples on compact carriers, while for those made on porous carriers, the loss of performance was due to thermomechanical wear, which caused an increasing pressure drop. The combined analysis of all the above-mentioned experimental results found in the literature highlights the importance of catalyst degradation in the decomposition of high-concentration hydrogen peroxide. Although the phenomenon of catalyst degradation is well known and widely studied in the relevant scientific literature, to the best of the authors’ knowledge, no methods have currently been proposed for the regeneration of catalysts used in firing tests.
This work contributes to ongoing research in this area by investigating the behavior of a palladium-coated alumina pellets. Their durability is assessed through a sequence of hybrid firing tests performed on a 10 N-class mini-thruster for CubeSat applications, previously investigated in earlier studies [
15]. The progressive degradation of the catalytic decomposition performance is analyzed and its underlying causes are identified. A regeneration technique is then proposed, and the decomposition capability of the regenerated pellets is evaluated and compared with the original behavior. This study therefore aims to evaluate the performance degradation of commercial catalysts under relevant operating conditions, a critical aspect for ensuring effectiveness and reliability in future space applications. The lifetime of catalytic elements is a key limiting factor for re-ignition capability driven by mission requirements and directly influences propulsion system design choices. Furthermore, identifying low-cost regeneration techniques supports the implementation of university-level experimental campaigns based on this class of catalysts, reducing both material consumption and procurement costs for ground-based testings.
4. Results and Discussion
In this chapter, the results concerning the performance of the catalysts under investigation throughout their lifetime are presented. The possible causes of the degradation of catalytic activity are then analyzed, and a solution to the problem through a regeneration process is proposed. Finally, the performance of the catalysts in their initial state is compared with that observed after regeneration following the first failure.
4.1. Evolution of Catalyst Performance
With the aim of monitoring step by step the level of catalyst consumption, the decomposition efficiency was calculated using Equation (
2) during the hybrid combustion phase of each firing test. This analysis has been implemented in order to assess whether a possible degradation has an impact on the combustion efficiency. The cumulative amount of decomposed HTP in previous tests was also monitored. Indeed, since the tests are performed under different operating conditions and a wide variety of testing scenarios is considered for these catalysts, evaluating the consumption by parameterizing it solely in terms of pressures and mass flow rates over time may be of limited relevance. It is instead more meaningful to determine how much HTP can be decomposed with high efficiency over a wide range of operating conditions.
In the first set of tests prior to failure (Tests 1-B1 to 3-B1), the catalysts operated at pressures up to 17 bar, with mass flow rates reaching values of 11 g/s during the impulse phase, while in the hybrid phase the flow rate stabilized at slightly less than 3 g/s.
Table 4 reports the main results of interest concerning the catalytic and combustion performance in the conducted tests, together with the cumulative amount of HTP decomposed prior to the test in the hybrid configuration.
The efficiency observed in Test 1-B1 is remarkably high, demonstrating that the fresh catalyst, as originally designed, exhibits very good catalytic capabilities.
Figure 5 illustrates the behavior during the hybrid phase in terms of measured values of pressure and temperature in the catalytic chamber. In addition to a stable pressure level, a temperature measured at mid-length of the catalytic chamber approaching 900 K is observed, while the adiabatic decomposition temperature is about 1000 K. The fact that the gas temperature is already so high at mid-chamber indicates that, under these conditions, a shorter length than the full catalytic chamber is sufficient to achieve complete decomposition. In general, this may have an impact in terms of catalyst consumption. Indeed, a very hot gaseous phase flowing through the catalyst, in addition to causing significant pressure losses, tends to accelerate catalyst degradation due to enhanced thermomechanical loads. Therefore, during the design phase, it would be preferable to tailor the catalytic chamber to the expected mass flow rate and pressure levels, so as to achieve complete decomposition only near the end of the catalytic chamber. It is also true that it is not possible to change the catalytic chamber for each operating condition; for this reason, such issues inevitably arise, causing rapid degradation phenomena.
It can be observed that the decomposition efficiency decreases as the tests progress, while at the same time it does not appear to have a significant impact on the combustion efficiency. Indeed, in the first two tests, although the decomposition efficiency drops by 16%, the combustion performance does not show any noticeable degradation. This behavior is reasonable, since even when the decreases, the hydrogen peroxide injected into the combustion chamber is already in the gaseous state (with temperatures in the catalytic chamber always exceeding 700 K). Therefore, no heat losses associated with phase change occur in the combustion chamber. Instead, the fraction not decomposed in the catalytic chamber undergoes thermal decomposition due to the high temperatures in the combustion chamber. An asterisk is reported for Test 3, since, owing to the use of ABS as fuel and the incomplete knowledge of its thermophysical properties, the theoretical characteristic velocity adopted for the efficiency calculation may not be fully reliable.
Test 4-B1 was performed after a total of 255.61 g of hydrogen peroxide had been decomposed. Despite exhibiting a residual catalytic activity, with the temperature in the catalytic chamber never exceeding 450 K, the catalysts were unable to induce fuel pyrolysis and to ensure flame ignition and stabilization.
Following this, the catalysts were analyzed and several activities were carried out to explain the underlying mechanisms responsible for the observed degradation and how the problem could be addressed. This is discussed in the following sections.
4.2. Degradation Assessment
The catalysts extracted from the catalytic chamber after the test failure were visually inspected and appeared slightly discolored compared to the intense black color typical of unused pellets. Some pellets appeared to be in good condition to the naked eye. They were considered for the subsequent analyses, in order to verify whether they exhibited a level of degradation sufficient to compromise their decomposition capability.
A comparison between the appearance of a spent catalyst, shown in
Figure 6, and a new pellet, shown in
Figure 2, highlights the difference in color.
Subsequently, in order to assess the ineffectiveness of the catalyst when in this condition, static tests were carried out by comparing two fresh pellets with two spent pellets of the type shown in
Figure 6.
In two separate experiments, two pellets were placed in a glass column containing 7 g of hydrogen peroxide (90% wt), with a thermocouple positioned 5 cm above the liquid surface.
Figure 7 reports the temperature profiles obtained during these experiments. For fresh catalysts, temperature reached approximately 100 °C and the hydrogen peroxide was almost completely consumed after about two minutes. Instead, in the case of spent catalysts no significant reaction was observed, with the temperature remaining at ambient level and no appreciable hydrogen peroxide consumption, except for the formation of a few small gas bubbles.
4.3. Degradation Causes and Regeneration
As mentioned, visual inspections of the catalytic pellets after propulsion experiments highlighted a significant modification of their color, switching from black to dark brown (
Figure 8, left). Such variation in color is diagnostic of a significant modification of the oxidation state of the palladium nanoparticles on the Al
2O
3 surface. The treatment in NaBH
4 restored the color of the pellets, highlighting the reduction of the formed oxides to metallic palladium.
Temperature Programmed Reduction (TPR) experiments were carried out to obtain further insights into the modification of the oxidation state of the palladium nanoparticles after treatment in NaBH
4.
Figure 9a displays the behavior of the Thermal Conductivity Detector (TCD) signal during stabilization at 30 °C. While the spent catalyst exhibits a monotonic decreasing profile, the regenerated catalyst shows a distinct peak, suggesting that a fraction of palladium oxides was still present on the catalyst surface after NaBH
4 treatment. Nonetheless, those oxides are easily reduced at low temperatures (30 °C). Many literature case-studies displayed that classical Pd/Al
2O
3 catalysts are easily reduced at T < 20 °C [
32,
33,
34]. Such reduction peaks require specific instruments with integrated cooling units for accurate detection. Moreover, an additional contribution to the hydrogen consumption can be attributed to the formation of
-PdH because of the interaction of H
2 with metallic Pd. The obtained thermograms for both the spent and regenerated catalysts are displayed in
Figure 9b. Both catalysts exhibited a sharp negative peak at T = 60 °C, which is attributed to the desorption of hydrogen from
-PdH species [
35]. In case of the regenerated catalyst, no additional peaks were observed. On the contrary, the spent catalyst revealed broad reduction peaks at different temperatures, namely at 175 °C, 315 °C, 380 °C and 750 °C. High temperature reduction peaks have been scarcely observed in the open literature for Pd/Al
2O
3 catalysts without promoters. Among the first, Lieske and Voelter [
36] explored the reduction behavior of Pd/Al
2O
3 catalysts after treatment at high temperatures (600 and 900 °C) under oxygen atmosphere. Their results revealed the formation of high temperature reduction peaks, which were attributed to the formation of palladium oxide surface complexes [PdO]
sc with strong interactions with the alumina support. Given the presence of oxygen and hydrogen peroxide, which is also a strong oxidating agent, and the high temperatures in the catalytic chamber, a similar oxidation behavior is presumed during propulsion, yielding catalyst deactivation. Similar thermograms were observed in our previous study in the low temperature hydrogen peroxide decomposition on 3D printed Pd/Al
2O
3 catalysts [
37]. In that case, the highest reduction peak was at 380 °C. The exposure of the catalyst to propulsion conditions yielded to the formation of stronger palladium oxides, which are more difficult to reduce in hydrogen atmosphere. Nonetheless, the TPR profile of the regenerated catalyst did not show significant peaks, proving that the strong palladium oxides are reduced by NaBH
4 at low temperatures. The analysis of TPR experiments during both the stabilization of the TCD signal and the temperature gave meaningful information on the primary causes of catalyst deactivation and highlighted the role of NaBH
4 in the regeneration experiment. The presence of oxygen and concentrated hydrogen peroxide in the catalytic chamber causes the formation of palladium oxide surface complexes which are difficult to reduce. Such oxides are responsible for a steep decline in the catalytic activity. The treatment with NaBH
4 allows the reconversion of palladium oxides into metallic palladium. However, the reduction is not completed since reduction peaks are observed during signal stabilization in the regenerated catalyst (
Figure 9a). Further investigations will aim at improving the regeneration of the palladium oxides to restore completely the catalytic activity by e.g., increasing the reduction temperature, increasing the NaBH
4 concentration or changing the reducing agent.
4.4. Performance of Regenerated Catalysts and Comparisons
After regenerating the catalysts, a test was carried out under the same operating conditions as the failed one (see Test 4-B1Fail in
Table 3) and was designated as Test 4-B1Reg. For completeness, and in order to enable a direct comparison among fresh, spent, and regenerated catalysts, an additional test was also performed using the same type of catalyst but never previously used, referred to as Test 4-BFresh.
Figure 10 shows some of the pressure signals obtained during step 2 of the pulse train reported in
Table 2. It can be observed that, under identical operating conditions, the pressure peak achieved during the pulsed phase differs significantly among the three analyzed cases. Since the pressure level is indicative of the amount of hot gas generated in the catalytic chamber, the results obtained in the propulsion environment also clearly suggest that the regeneration process, although effective, is not complete but only partial.
This conclusion is further supported by the analysis of the pressure gradient recorded during the pulsed phase, which is indicative of the rate of pressure variation and thus of the catalyst reactivity when it comes into contact with hydrogen peroxide. As shown in
Figure 11, the fresh catalyst reaches a peak of about 80 bar/s, which is approximately twice that exhibited by the regenerated catalyst.
Nevertheless, although regeneration is only partial, it is sufficient for this type of application to ensure ignition and flame sustaining. For this reason, the pressure curves during the continuous phase in hybrid configuration were analyzed in order to further assess the possible impact of the catalyst on combustion efficiency.
Figure 12 reports the pressure signals recorded in the catalytic chamber and in the combustion chamber for both the fresh and the spent catalyst cases. It can be observed that the pressure levels are practically identical, which already suggests that, during operation in hybrid configuration, the engine behaved in the same manner under identical operating conditions. In both cases, the efficiencies were also evaluated in order to obtain a quantitative estimate (see
Table 5).
Based on the value of the decomposition efficiency, it appears that the regenerated catalyst returned to conditions slightly better than those observed after the first Test 1-B1. It will be important to determine how many times this regeneration procedure can be repeated before it ultimately becomes ineffective.
5. Conclusions
This work investigated the evolution of the decomposition performance of a batch of palladium-coated alumina pellets subjected to a sequence of hybrid firing tests using a 10 N-class mini-thruster exmploying 90% HTP and HDPE/ABS as propellants. During the first three tests, continuous monitoring of the main propulsive parameters revealed a progressive degradation of the catalytic activity. In the fourth test, this degradation resulted in the inability to ignite the polymeric fuel grain, leading to the failure of the firing test.
The degraded pellets were subsequently analyzed through visual inspection, static HTP decomposition measurements, and Temperature Programmed Reduction (TPR) experiments. These analyses identified surface oxidation of palladium as the primary cause of the observed loss in catalytic performance. On the basis of these findings, a regeneration technique based on sodium borohydride (NaBH4) treatment was developed. This approach enables the reduction of palladium oxides back to their metallic state, thereby restoring the decomposition capability of the catalyst. The treatment resulted in partial regeneration of the pellets, which were then subjected to an additional firing test to characterize their behavior. By comparing the experimental results obtained from the regenerated pellets with those from both a new batch and the degraded batch, the effectiveness of the proposed treatment was assessed. Despite the partial nature of the regeneration, the treated pellets exhibited performance only slightly lower than that of new catalysts and were fully sufficient to ensure reliable ignition of the fuel grain and successful completion of the firing test.
This work has provided some insights into the degradation mechanisms at work during repeated firing tests of small-scale hybrid thrusters operating with hydrogen peroxide, highlighting how the surface oxidation of palladium pellets severely limits their catalytic activity over time, making them practically inactive after a limited number of consecutive firing tests. Furthermore, the experimental results reported demonstrate that the proposed regeneration technique is capable of partially recovering the decomposition performance of palladium-coated alumina pellets affected by surface oxidation. providing significantly better decomposition properties than spent pellets, although slightly lower than new pellets. This shows that sodium borohydride treatment can be considered as a promising technique that deserves further study and development. It could be exploited to lower costs for ground-based testing, facilitating the experimental activities of research groups, especially in universities and in the early stages of hybrid rocket propulsion system R&D. Future work will focus on further optimization of the oxide reduction process, assessment of the long-term behavior of regenerated catalysts, and evaluation of the maximum number of feasible regeneration cycles. The possibility of developing regeneration systems for use in orbit may also be evaluated through dedicated feasibility studies.