STUDY OF SOOT PARTICLES NANOSTRUCTURE EVOLUTION IN A LAMINAR PREMIXED FLAME BY RAMAN AND EPR SPECTROSCOPY
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1 STUDY OF SOOT PARTICLES NANOSTRUCTURE EVOLUTION IN A LAMINAR PREMIXED FLAME BY RAMAN AND EPR SPECTROSCOPY F. Picca*, M. Di Serio*, G. De Falco*, M. Commodo**, G. Vitiello*, G. D Errico***, P. Minutolo**, A. D Anna* francesca.picca@unina.it; commodo@irc.cnr.it * Dipartimento di Ingegneria Chimica, dei Materiali e della Produzione Industriale - Università degli Studi di Napoli Federico II, P.le Tecchio 80, 80125, Napoli, Italy ** Istituto di Ricerche sulla Combustione - CNR, P.le Tecchio 80, 80125, Napoli, Italy *** Dipartimento di Scienze Chimiche - Università degli Studi di Napoli Federico II, Complesso Monte S. Angelo, 80126, Napoli, Italy Abstract In this study the physicochemical evolution of soot particles in a laminar premixed flame has been investigated. The evolution of the particle size distribution as function of the different heights above the burner has been explored in conjunction with changes of particle chemical/physical properties retrieved by Raman and Electron Paramagnetic Resonance spectroscopy. In addition, the results obtained by Raman spectroscopy on flame formed soot particles were compared to those obtained by analyzing some standard carbon-based materials such as commercial carbon black, activated carbon, disordered graphite and highly oriented pyrolytic graphite. Introduction Soot formation results from the incomplete combustion of hydrocarbons. These carbonaceous particles have been the object of numerous studies over the decades in various research areas because of thei r negative effects on human health, climate change, and the environment [1,2]. Soot can be defined as a mixture of particles and aggregates composed prevalently by aromatic carbon compounds, thus mainly presenting sp 2 carbons. Despite the great efforts in understanding the mechanism of soot formation in combustion and several advances achieved in the last years, the complete understanding of this process has not reached yet. In fuel-rich flames, the incomplete oxidation of the fuel molecules results on the formation of gas-phase products, close to the flame front, which later recombine forming benzene, naphthalene and other larger polycyclic aromatic hydrocarbons (PAHs). In order to describe the soot formation process is fundamental to understand the structure of the PAH compounds acting as building blocks of the soot particles. Indeed, once formed, these aromatic structures begin to assemble into just-nucleated particles or clusters, whose size is usually of the order of few
2 nanometers, i.e., 2-3 nm [3]. Only at higher residence times, i.e., at increased height above the burner (HABs), the particle growth process due to coagulation/coalescence and surface mass addition lead to the formation of a second mode centered at larger diameters in the particle size distribution (PSD) [3, 4].The aim of this research has been to move a step forward in the understanding of this complex process, by analyzing the physicochemical transformation of soot particles during the aging process in the flame. In this work the initial evolution of carbon nanoparticles in a laminar premixed flame has been investigated in term of particle size by on-line differential mobility analysis (DMA), and in term of chemical/structural properties by Raman and Electron Paramagnetic Resonance spectroscopies. Experimental A premixed laminar ethylene-air flame was stabilized on a water cooled sintered bronze McKenna burner. Ethylene was chosen as fuel being one of the main products of the decomposition of any hydrocarbons. The cold gas stream velocity was 9.8 m/s and the carbon to oxygen (C/O) atomic ratio was set at 0.67, corresponding to a flame equivalence ratio Ф of PSDs, were measured online by a DMA system. To this purpose, flame products were sampled through an orifice (ID = 0.2 mm, thickness = 0.5 mm) into the turbulent flow dilution probe with 1 cm outer diameter, positioned horizontally, using N 2 as diluent ensuring a dilution ratio, DR, of 3*10 3. Such sampling procedure was adopted to prevent particle coagulation and to quench chemical reactions, thus preventing particle mass growth within the sampling line [4-6]. Off-line analyses were performed on the particles sampled with a tubular probe (similar to the one used for PSDs measurements) and were collected on quartz filters (Whatman QM-A Quartz Microfiber Filters, with diameter of 47 mm) placed on-line in a filter holder. Total sampling time for each filter was 7 hours. Particles collected on the Quartz filters were first analyzed by Raman spectroscopy using a Horiba XploRA Raman microscope system equipped with a 100 objective (NA0.9, Olympus). The laser source was a frequency doubled Nd:YAG laser (λ = 532 nm) and an infrared laser (λ = 785 nm). The power of the excitation laser beam, the exposure time and the other instrumental parameters were opportunely adjusted to avoid structural changes of the sample due to thermal decomposition and to ensure the best resolution. Spectra were obtained with a laser beam power of 1%, and an accumulation-exposure time of 5 cycles of 30 s each. For each sample, 10 spots were randomly selected and averaged to obtain statistically relevant Raman spectra. Finally, all the spectra were baseline corrected and normalized to the maximum of the G-peak, around 1600 cm 1. In addition, Raman spectra of commercially available carbon-based material have been also measured. These include: carbon black, activated carbon, disordered graphite and, highly oriented pyrolytic graphite, HOPG. EPR spectroscopy experiments of soot particles collected on the quartz filters were
3 carried out by means of X-band (9 GHz) Bruker Elexys E-500 spectrometer (Bruker, Rheinstetten, Germany), equipped with a super-high sensitivity probe head. Defined sections of quartz filters were coaxially inserted in a standard 8 mm quartz sample tube and the measurements were performed at 25 C. The instrumental settings were as follows: sweep width, 100 G; resolution, 1024 points; modulation frequency, 100 khz; modulation amplitude, 1.0 G. EPR spectra were recorded at an attenuation value of 15 db and 128 scans were accumulated to improve the signal-to-noise ratio. The g-factor values were evaluated by means an internal standard (Mg/MnO) [7] which was inserted in the quartz tube co-axially with the samples. Results Particle size distributions measured by DMA along the flame axis are reported in Fig.1. PSDs are plotted in terms of volume diameter, d P, [7]. PSD evolves from unimodal to bimodal by increasing the HABs. HAB=6mm 12 HAB=7mm 12 HAB=8mm HAB=9mm dn/dlnd, cm 3 HAB=10mm HAB=12mm HAB=14mm HAB=16mm d p, nm Figure 1. Evolution of the PSD as a function of HAB. Black dots represent the measurement data, red lines are the sum of the log-normal fits. Lognormal distribution functions are usually used to fit particles distributions: one function is sufficient to fit PSDs from 6 to 8 mm above the burner, while two lognormal functions are required to fit the PSDs at higher HABs, i.e. from 9 to 16 mm. Further information on the physicochemical evolution of soot particles in laminar
4 premixed flame were obtained by Raman spectroscopy. Indeed, Raman scattering is as a remarkable and powerful tool for gaining chemical, structural and electronic information of many carbon-based materials. The Raman spectra of soot collected at HABs, obtained by using two different excitation wavelengths, i.e., λ = 532 nm and λ = 785 nm are shown in Fig 2. Spectra are acquired in the first order Raman region of cm 1. All the measured spectra present the typical characteristics of any disordered carbonaceous materials for which a thorough description is reported elsewhere [8,9]. Briefly: two main bands are commonly present, one centred at about 1600 cm -1 named G band, the other centred at about 1350 cm -1 and named D band. Figure 2. Raman spectra at several heights above the burner. On the left, collected spectra at 532nm;on the right, collected spectra at 785nm. The data have been normalized on the G peak after subtracting the photoluminescence background The high sensitivity of the technique, in probing chemical/structural information of carbon materials, lies in the fact that the presence of defects in the sp 2 aromatic network allows the activation of the Raman D mode at ~1350 cm -1, prohibited in the perfect hexagonal lattice [8, 9] Conversely, the G band, at ~1600 cm -1, which is due to every sp 2 bond, is mostly insensitive to defects only presenting small changes in width and position of the maximum as function of the different carbon structures. It is worth noticing that although D and G bands represent the most prominent features in the first order spectrum of soot and other amorphous carbon materials, the presence of other Raman lines can be also taken into account [10] each characteristics of specific disorder origin in the carbon matrix [9-11]. However, because of the superposition of these lines, the Raman spectrum needs to be fitted with a multiple-line function to evidence each contribution. This will be part of future work. The major differences in the spectra changing HABs consist in changes in the relative intensity of the D and G peak and in the band position. In Fig 3 the trends of these parameters are reported in detail. Fig. 3a and Fig. 3b report the D-peak and G-peak position, respectively Pos(D) and Pos(G), obtained from the Raman spectra of soot collected at different HABs in comparison to that of standard carbon materials such as activated carbon (AC), carbon black (CB), defected graphite (DG) and HOPG.
5 Pos(D), cm -1 I(D)/I(G) HAB7 HAB8 HAB9 HAB10 HAB12 (a) Position 532 nm Position 785 nm 532 nm 785 nm HAB7 HAB8 HAB9 HAB10 HAB14 HAB16 (c) HAB12 HAB14 HAB16 AC CB AC CB DG HOPG DG Pos(G), cm -1 L a, nm Figure 3. Position D-peak, Pos(D), (a); Position G-peak, Pos(G), (b); I(D)/I(G) ratio (c) from the Raman spectra of soot particles collected at several HABs and other standard carbon materials. It is observable a decrease of the position of the two bands as the soot particle aging proceeds, almost approaching the values obtained for the AC and CB. For the G band this trend is consistent with graphitization process as also reported by Ferrari and Robertson [8] investigating amorphous carbon materials. The shift of D line is generally consequent to strain or doping in the lattice [12]. In the case of the particles here examined strain could be caused by the non-perfect planarity of the aromatic units. The trend of Fig. 3a is consistent with the increase of bending of the aromatic islands in the particles when particle aging proceeds at increasing HABs. Although not directly comparable to soot particles, the trend observed for the carbon standards follows the same tendency with the position of the D band of AC and BC shifted towards lower wavenumber (larger strain) respect to the graphite. Other source of strain/doping such as electrical charges and/or Oxygen atom are less likely. The change in the chemical/structural properties of the different soot particles can be also observed by considering the relative intensity of the D and G band, i.e., I(D)/I(G). It is well known that this ratio is related to the average size of the aromatic units or clusters forming the carbon materials, L a [8]. For graphite and nano-graphite the intensity ratio I(D)/I(G) has been shown to be inversely proportional to L a [13]. Such functional dependence has been successively verified HAB7 HAB7 HAB8 HAB9 HAB10 HAB12 HAB8 HAB9 (b) Position 532 nm Position 785 nm (d) HAB10 HAB14 HAB16 HAB12 AC CB HAB14 DG HOPG HAB16
6 up to a minimum L a, of about 2-3 nm, where I(D)/I(G) reaches a maximum value [9]. When L a further decreases, I(D)/I(G) decreases to zero. For flame-generated soot particles the low-l a regime, i.e., L a < 2-3 nm, usually applies [13], for which the following empirical expression has been found to correlate L a with the relative intensity of the Raman bands [8]: L a 2 (nm 2 ) = E L 4 (ev 4 ) I(D) I(G) (1) where E L is the energy of the incident photon. The results obtained for the different soot particles are reported in Fig. 3d, in which an increase of L a as function of HAB is observable. EPR spectra of soot collected at different HABs are reported in Figure 4. 7 mm 8 mm 10 mm 12 mm 14 mm Figure 4. EPR spectra of soot particles on quartz filters collected at different HABs. All spectra show a single peak at g-factor = (as reported in Table 1), typical of very persistent carbon-centered radicals with the single electron localized on a carbon atom, aliphatic or aromatic [14]. However, a closer inspection of Figure 4 indicates that the spectra at lower (7 and 8 mm) and higher (14 mm) HABs reveal a significantly broad signal. This evidence is associated to the presence and superposition of multiple paramagnetic species into the soot particles [14, 15]. This difference in these line shapes was quantitatively corroborated by the determination of signal amplitude, ΔB, which is also inversely related to the mean distance between the radical centres. In our case, EPR analysis shows that the ΔB value for the soot samples obtained at lower and higher HABs was significantly B/G
7 larger than those obtained at other HABs (see Table 1). Since soot is principally composed of carbon and the spectral width ΔB of soot resulting from electron spinspin interactions is usually ~2 G [16], the reported variations in ΔB values are a clear confirmation of the presence of multiple radical species, indicating different chemical and structural organization properties of soot particles produced at different HABs. Table 1. EPR spectral parameters of soot particles collected at different HABs. HAB g-factor B (G) 7 mm ± ± mm ± ± mm ± ± mm ± ± mm ± ± mm ± ± mm ± ± 0.2 Conclusions In this work, the physicochemical evolution of soot particles in a laminar remixed flame has been investigated. PSDs measurements coupled to Raman and EPR spectroscopy analysis have been performed. As the residence time in flame increases, the PSD change from unimodal to bimodal. In addition to the particle size, the soot evolution in flame also includes chemical/structural modifications. Indeed, the analysis of the measured Raman spectra shows that the two main peaks, the D and G bands, change in terms of relative intensity and band position. Using standard carbon materials as reference, the position and intensity of D and G were used as an index of a structural change. The results showed an evolution of the soot particles toward a more ordered structure during the growing process. Finally, the EPR data shows the presence and superposition of multiple paramagnetic species characteristics of carbon radicals. In addition, the reported variations in ΔB values indicate different chemical and structural organization properties of soot particles produced collected at different HABs. References [1] De Falco, G., Terlizzi, M., Sirignano, M., et al., Human peripheral blood mononuclear cells (PBMCs) from smokers release higher levels of IL-1-like cytokines after exposure to combustion-generated ultrafine particles, Scientific Reports, 7: 43016, (2017). [2] Bond, T.C., Doherty, S.J., Fahey, D.W., et al., Bounding the role of black carbon in the climate system: A scientific assessment, Journal of Geophysical Research: Atmospheres, 118: (2013).
8 [3] M. Commodo, G. De Falco, P. Minutolo, A. D'Anna, Structure and size of soot nanoparticles in laminar premixed flames at different equivalence ratios, Fuel, 216: (2018). [4] B. Zhao, Z. Yang, Z. Li, H. Wang, A.S. Wexler, M. Balthasar, M. Kraft, Measurement and numerical simulation of soot particle size distribution functions in a laminar premixed ethylene oxygen-argon flame, Combust. Flame, 133: (2003). [5] F. Carbone, M. Attoui, A. Gomez, Challenges of measuring nascent soot in flames as evidenced by high resolution differential mobility analysis, Aerosol Sci. Tech., 50: (2016). [6] Commodo, M., De Falco, G., Bruno, A., Borriello, C., Minutolo, P., D Anna, A., Physicochemical evolution of nascent soot particles in a laminar premixed flame: from nucleation to early growth, Combust. Flame 162: (2015). [7] Yordanov, N.D., Lubenova, S., Effect of dielectric constants, sample containers dimensions and frequency of magnetic field modulation on the quantitative EPR response, Analytica Chimica Acta, 403, (2000). [8] Ferrari, A.C., Robertson, J., Resonant Raman spectroscopy of disordered, amorphous, and diamondlike carbon, Phys. Rev. B, 64: (2001). [9] Sadezky, A., Muckenhuber, H., Grothe, H., Niessner, R., Pöschl U., Raman microspectroscopy of soot and related carbonaceous materials: Spectral analysis and structural information, Carbon, 43: [10] Herdman, J.D., Connelly, B.C., Smooke, et al., "A comparison of Raman signatures and laser-induced incandescence with direct numerical simulation of soot growth in non-premixed ethylene/air flames", Carbon, 49, (2011). [11] Commodo, M., De Falco, G., Minutolo, P., D'Anna, A., "Structure and size of soot nanoparticles in laminar premixed flames at different equivalence ratios, Fuel, 216: (2018). [12] Ferrari and Basko, Raman spectroscopy as a versatile tool for studying the properties of graphene, Nature Nanotechnology, 8: (2013) [13] Tuinstra,F. and Koenig, J.L, Raman spectrum of graphite, The Journal of chemical physics, 53: (1970). [14] Valavanidis, A., Iliopoulos, N., Gotsis, G., Fiotakis, K., Persistent free radicals, heavy metals and PAHs generated in particulate soot emissions and residue ash from controlled combustion of common types of plastic, J. Hazar. Mater., 156: (2008). [15] Herring, P., Khachatryan, L., Lomnicki, S., Dellinger, B., Paramagnetic centers in particulate formed from the oxidative pyrolysis of 1- methylnaphtalene in the presence of Fe(III)2O3 nanoparticles, Combust. Flame, 160: (2013). [16] Ingram, D.J.E., Free radicals as studied by electron spin resonance. London: Butterworths Scientific Publications, 210 (1958).
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