Lisette R.
Warren
a,
Aaron
Rowell
a,
Patrick
McMaster
b,
Colin R.
Pulham
a and
Carole A.
Morrison
*a
aEaSTCHEM School of Chemistry, University of Edinburgh, The King's Buildings, David Brewster Road, Edinburgh, EH9 3FJ, UK. E-mail: c.morrison@ed.ac.uk
bDOSG-ST1, NH4, MoD Abbey Wood, Bristol, BS34 8JH, UK
First published on 24th August 2023
We present a first-principles computational study to understand the action of lead and copper-based ballistic modifiers in the combustion of double-base propellants (DBPs). We show that lead oxide clusters are easily broken down upon addition of small amounts of carbon and the resulting graphitic matrix, dispersed with weakly bound and exposed Pb sites, acts as a Lewis acid to bind small molecule Lewis bases such as NO2 and CH2O that form in the combustion flame. This accounts for super-rate burning, where the fuel burn rate is enhanced. We also show how carbon availability accounts for the plateau- and mesa-rate burning effects, where the fuel burn rate is suppressed. In contrast, cluster integrity on binding carbon to copper oxide is retained, and interaction with NO2 and CH2O is essentially negligible. Carbon binds more strongly to copper oxide, however, and we therefore propose that when carbon levels start to fall this results in the lead oxide clusters being starved of carbon, which leads to plateau and mesa burning. Taken together, the calculations support a general model that accounts for the super-, plateau- and mesa-rate ballistic modifier burning effects.
r = apn | (1) |
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Fig. 1 Burning rate-pressure relation (a) for non-catalysed and catalysed DBP (Copyright AIAA, 1974),9 and (b) influence by lead and copper oxide ballistic modifiers (Copyright Springer, 1995).10 |
The first ballistic modifiers that were identified were lead oxides and aliphatic lead salts,11 and further addition of either carbon black or the use of aromatic lead salts was found to advantageously produce a larger plateau zone that extended to higher operating pressures.12 To date, only lead-based compounds have been found to support all three burn-rate effects.13 The further addition of copper salts pushes super-rate burning to higher pressures that inevitably results in a pronounced mesa burning effect, as shown in Fig. 1(b);10,14 the combined use of lead- and copper-based ballistic modifiers are considered as industry-standard formulations for DBPs.
The role of the ballistic modifier on the DBP combustion mechanism outlined above has recently been reviewed,13 and the literature consensus points towards involvement at the solid/gas boundary (known as the burning surface) of the propellant.6,15,16 Several theories attempt to account for both the super-rate and plateau-burning mechanisms, with the most comprehensive being the carbon-soot theory. This postulates that the lead salts decompose below the burning surface17 and alter the alkoxyl radical decomposition pathway of the DBP to favour the formation of carbon-soot at the burning surface.9,13,15,16,18 The resulting carbon matrix incorporates dispersed Pb particles (of lead or lead oxide),15,19 and is attributed to supporting super-rate burning.13,16,18 The subsequent loss of the carbon matrix with increasing pressure dampens the catalytic effect and is therefore thought to induce the plateau-burning effect.13,16,18
The continued dependence on lead additives in DBP formulations is problematic as this highly toxic element presents hazards in its use and disposal, and impending European Union regulations (REACH – registration, evaluation, authorisation and restriction of chemicals)20 will soon ban their use. As no current alternative exists, the aims of this study are to use computational modelling to understand how lead and copper, present in the form of metal oxide clusters, interact with carbon and small molecules such as CH2O and NO2 that are known to form in the combustion flame. The results from the simulations allow us to build upon the carbon-soot theory, to offer atomistic interpretations that account for the onset of the super-, plateau- and mesa-burn rate effects.
The paper is organised as follows. In the first instance, a library of lead oxide clusters has been generated via ab initio random structure searching (AIRSS), to present a plausible range of structures that could form at the burning surface of a DBP combustion flame. The influence of adding increasing amounts of carbon atoms to the clusters is then reported, alongside an investigation into the binding and activation of CH2O and NO2. An analogous investigation is also reported for the stable copper oxide cluster Cu5O5, to establish how it differs from lead oxide. We then propose a catalytic burn rate profile that accounts for the unique ability of lead-based ballistic modifiers to create super-, plateau- and mesa-burn rate effects.
For all CASTEP calculations, the ultrasoft pseudopotentials23 were generated “on the fly”, with Γ-point Brillouin zone sampling. For the first round of structure searching, convergence criteria were set at 0.05 eV Å−1, 0.1 GPa, 0.05 Å and 5 × 10−4 eV per atom for force, stress, ionic displacement and energy, respectively. The cut-off energy was set to 400 eV. Higher level optimisation calculations (energy cut-off 800 eV, optimisation criteria 0.01 eV Å−1, 0.02 GPa, 0.005 Å, and 5 × 10−6 eV per atom, for force, stress, ionic displacement and energy, respectively) were then run for the lowest energy structures. For all calculations, the PBE GGA functional24 was applied, along with the TS dispersion correction scheme.25
Local force constants were calculated using LMODEA,26–28 following geometry optimization and frequency calculation performed in Gaussian16 using the SDD/def2-TZV basis set and PBE0 functional with Grimme D3BJ dispersion.29–31 The resulting optimisations were analysed in Multiwfn to obtain the HOMO–LUMO gaps and orbital contributions to the LUMO,32 using Stout-Politzer population analysis for the latter. The relative stability of the clusters was determined from their binding energy per atom, defined as:
![]() | (2) |
The same model chemistry was used for the CH2O and NO2 binding study, according to the following equation:
Binding energy (ΔG) = E(AB) − E(A) − E(B) | (3) |
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Fig. 2 Relative energies of Pb4O4 clusters obtained by AIRSS/DFT vs. number of structures generated. Colour scheme: Pb (dark grey), O (red). |
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Fig. 3 Global minimum energy structures of Pb4O4–6 series found by AIRSS/DFT. Colour scheme: Pb (dark grey), O (red). |
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Fig. 4 Energy landscape of Pb4O4C12 clusters found by AIRSS/DFT. Colour scheme: Pb (dark grey). C (gold), O (red). |
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Fig. 5 Low energy structures Pb4O4–6 clusters, and representative structures obtained by AIRSS/DFT upon subsequent addition of carbon atoms. Colour scheme: Pb (dark grey), C (gold), O (red). |
While the amount of carbon included in these models is small compared to experimental levels,19,38 it sets a level of expectation that the addition of more carbon would likely create graphitic-type structures. It is also evident from Fig. 5 that the formation of graphitic carbon structures results in the destruction of the metal oxide cluster, and the metal atoms are more exposed compared to the carbon-free structures. Pb⋯Pb bond distances typically increase from ca. 3.5 to 4–8 Å upon addition of twelve carbon atoms (see ESI†). This finding is in agreement with a solid-state modelling study of PbO, where oxygen abstraction was observed upon contact with an amorphous carbon layer.39
The strengths of the individual bonds within the clusters can be gauged through local (mass independent) force constants for each bond type (Fig. 6 and ESI†).26–28 This plot explains the general observations obtained in the AIRSS/DFT study, where oxygen extraction to create strong terminal C–O bonds, alongside strong C–C bonds, provides the thermodynamic driver for the reaction. Overall, weak Pb–O bonds are replaced by longer Pb–C bonds of comparable strength (1.0 ± 0.4 mDyn Å−1), thus further exposing the metal atom sites.
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Fig. 7 Representative low energy structures for Cu5O5C0–12 clusters obtained by AIRSS/DFT. Colour scheme: Cu (blue), C (gold), O (red). |
In common with lead oxide, the addition of three carbon atoms resulted in oxygen abstraction from the copper oxide cluster (Fig. 7). Results diverge thereafter: whereas lead oxide clusters support the formation of graphitic carbon nets, for copper oxide further addition of carbon results in the formation of more carbon wires through further oxygen abstraction. Whilst graphitic-type structures were obtained upon addition of nine and twelve carbon atoms, carbon growth was generally observed to occur on the cluster surface. This is in contrast to the lead oxide clusters (Fig. 5) where graphitic carbon forms inside the cluster. Consequently Cu⋯Cu distances are largely unchanged by the build-up of the carbon structures (see ESI†).
Analysis of local force constants for the individual bond types found for the 26 low energy structures for Cu5O5C12 are given in Fig. 8(a), and show that the thermodynamic drivers for carbon insertion are still C–O and C–C bond formation. In Fig. 8(b) the local force constants for the Pb–C and Cu–C bonds have been plotted for direct comparison. From this it is clear that the Cu–C bonds formed are, on average, stronger than Pb–C (1.6 ± 0.5 mDyn Å−1vs. 1.0 ± 0.4 mDyn Å−1).
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Fig. 8 (a) Plots of bond length vs. local force constants for the 26 most stable Cu5O5C12 clusters and (b) replotting of data for Cu–C and Pb–C bonds, for direct comparison. |
The empty p-orbital character in the LUMOs for Pb4O4 and Pb4O4C12 shows that both have the potential to act as Lewis acids to bind small (Lewis base) molecules such as CH2O and NO2 (Fig. 9). This is balanced, however, against the location of prominent lone pairs on the lead atoms that originate from the HOMOs of the clusters, as shown by electron localisation function plots (ELFs), which are probability functions for pairs of electrons. These plots also show how cluster degradation exposes the Pb sites for small molecule binding. Small contributions from the Cu d-orbitals can be observed in the LUMO of Cu5O5, while the LUMO of Cu5O5C12 is dominated by empty orbitals on C and O atoms on the outside of the cluster. The ELF plots show electron pairs are located over the carbon, oxygen framework.
In total, three cluster types have been considered for the binding of small molecules to lead oxide clusters: the parent Pb4O4–6 structures from our cluster library, along with representative carbon-wire clusters obtained for Pb4O4C9, and carbon-net clusters obtained for Pb4O4C12. For the binding study of copper oxide, the only carbon-bound system investigated was the wire-type, as the net-type structures were consistently greater than 150 kJ mol−1 higher in energy. In this way, a range of models are explored to probe the structural response to varying levels of available carbon. Results are presented in Fig. 10, with further details in the ESI.†
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Fig. 10 Binding energies for NO2 (top) and CH2O (bottom) to lead oxide clusters (blue) and copper oxide clusters (red) with varying carbon content for Pb4O4 and Cu5O5. |
The binding strength of NO2 and CH2O to the lead oxide clusters progressively decreases as the amount of carbon present falls. This is particularly significant for NO2, where some binding sites in Pb4O4C12 even result in N–O bond cleavage (see ESI†). No favourable binding sites for NO2 could be found for Pb4O4 (although some were observed for Pb4O5 and Pb4O6, see ESI†). For CH2O, binding to Pb4O4C12 results in favourable adsorption, while binding to Pb4O4–6 is weak; this agrees with previous reports.44,45 Reactions between lead oxide and formaldehyde have been previously reported.46,47 The carbon-wire cluster Pb4O4C9 shows intermediate binding energies for both NO2 and CH2O. Taken together these results suggest that carbon activates the lead oxide clusters for small molecule binding by destroying the cluster integrity to expose more open metal sites, and that the effect is dependent on the quantity of carbon present. Local-mode analysis confirms that the C–O and N–O bonds weaken on binding to any of the lead oxide clusters (see ESI†).
Fig. 10 also shows that the binding energies for both NO2 and CH2O to Cu5O5 are weak and largely invariant with carbon content. For CH2O the most energetically favourable binding sites were across Cu–O bonds; copper oxide has previously been reported to oxidise formaldehyde.48,49 For NO2, as carbon is introduced to the structures, a preference for NO2 binding to carbon sites is found compared to Cu binding.
Applying this activity profile to the simulations we have performed, these results suggest that super-rate burning occurs due to high levels of carbon-activated lead oxide clusters catalysing exothermic reactions with small molecules such as NO2 and CH2O. This results in a rapid rise in temperature of the combustion flame. It is known that lead oxide alone is a poor ballistic modifier, requiring the addition of carbon-soot to the formulation to support the onset of super-rate burning.38 Moreover, it is also well known that aromatic lead salts, such as lead salicylate, produce longer plateau-burning responses which extend to larger pressures, compared to aliphatic lead salts such as lead stearate.11,12,14,52,53 This long-standing observation can now be attributed to the presence of pre-formed stable aromatic carbon structures to activate lead oxide. Super-rate burning stops when carbon levels fall. The variation in NO2 and CH2O binding strengths to lead oxide with varying carbon content shown in Fig. 10 follows a similar profile to loss of catalytic activity in Fig. 11(a), and we therefore propose that this is the reason for the onset of the plateau in the burning profile. Lastly, we attribute the weak nature of the Pb−C bonds, compared to e.g. Cu−C (Fig. 8(b)) for the mesa-burn rate effect, as the carbon and lead part company and are lost from the flame. Thus the three burn-rate effects can all be accounted for by the build-up and loss of carbon, and its consequent effect on activating and deactivating lead oxide for small molecule binding.
This model for ballistic modifier behaviour also highlights some important observations that go some way towards explaining why the task of finding lead-free ballistic modifiers capable of supporting all three burn-rate effects has proven to be such a difficult task. Firstly, it explains why super-rate burning is relatively straightforward to achieve, as any additional effect from the ballistic modifier will simply boost the underlying propellant burn rate. Plateau- and mesa-burning, however, only occur due to a delicate balance of competing effects. Fig. 11(c) illustrates that the mesa-effect is lost if sudden modifier deactivation does not occur, while Fig. 11(d) makes the point that a true plateau-effect is only achieved if the rate of loss of modifier activity matches the rise in propellant burn rate.
This context also provides a platform to account for the variation in DBP burn rate when copper oxide is added as a second ballistic modifier (Fig. 1). Firstly, the super-rate burning effect is enhanced. This can be directly attributed to an increase in the amount of carbon present, an effect previously noted in the literature where the highest carbon content combustion flames were reported for a Pb/Cu ballistic modifier combination.10 Secondly, the loss of a plateau-effect and an early onset mesa-effect can now be interpreted as due to a much more rapid loss of carbon from the activated lead oxide clusters. Given that this work has highlighted the stronger nature of Cu−C bonds compared to Pb−C, we therefore propose that copper oxide provides a stronger thermodynamic sink for carbon as levels drop, effectively starving the lead oxide clusters of carbon, resulting in rapid deactivation for small molecule binding.
We have also derived a general activity profile for ballistic modifiers that builds on the carbon-soot theory and accounts for the super-, plateau- and mesa-rate burning effects. It also goes some way towards explaining why plateau- and mesa-rate burning are hard effects to achieve, and therefore why the search for lead-free alternatives has proven so challenging. We hope that these new insights hasten the search for non-toxic alternatives to lead-based ballistic modifiers for DBPs.
Footnote |
† Electronic supplementary information (ESI) available. See DOI: https://doi.org/10.1039/d3cp03197g |
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