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REVIEW article

Front. Phys., 27 January 2022
Sec. Optics and Photonics
This article is part of the Research Topic State-of-the-Art Laser Spectroscopy and its Applications : Volume II View all 51 articles

Application of Molecular Emissions in Laser-Induced Breakdown Spectroscopy: A Review

Fanghao Xu,Fanghao Xu1,2Shixiang MaShixiang Ma1Chunjiang ZhaoChunjiang Zhao1Daming Dong
Daming Dong1*
  • 1National Research Center of Intelligent Equipment for Agriculture, Beijing Academy of Agriculture and Forestry Sciences, Beijing, China
  • 2College of Mechanical and Electrical Engineering, Gansu Agricultural University, Lanzhou, China

Laser-induced breakdown spectroscopy (LIBS) with advantages of rapid, in situ, and little sample pretreatment has been used in various fields. However, LIBS technology remains challenging in the detection of halogens, isotopes, and samples with similar elements. Therefore, molecular emission was proposed to improve the detection ability of LIBS. In this review, we introduced molecular emissions formed by organic elements, oxidizable elements, and halogens. Then, molecular emission in different experiment parameters, such as the acquisition window, laser characters (laser energy, laser wavelength, and pulse duration), and ambient atmospheres, were discussed. In the end, we highlight the application of molecular emissions on element content determination, material type classification, and combustion and explosion process monitoring.

1 Introduction

Laser-induced breakdown spectroscopy (LIBS) is an ideal spectroscopic technique for material component analysis. The advantages of a rapid, in situ, real-time and remote analysis, and simple sample preparation [13] extend LIBS to detection in various environments, such as the space [4, 5], ocean [6, 7], nuclear reactors [8, 9], mines [10, 11], and in the metallurgical [12, 13] and industrial fields [14, 15]. These studies are based on the atomic emissions in the spectra. However, atomic emissions still have several drawbacks, including 1) the matrix effect [16,] and self-absorption [17, 18] blocking accuracy for quantitation and 2) its unsuitability for the classification of matters with similar elemental compositions. To overcome these drawbacks, researchers have focused on molecular emission in recent years [19]. Moreover, molecular emission can monitor burning and exploding processes.

In recent years, molecular emission was mentioned in LIBS reviews of specific targets, such as organics [20], explosives [21], and combustion [22]. The formation mechanism and experimental parameters for molecular emission were not discussed. The purpose of this review was to summarize the application of laser-induced molecular emission in quantitative classification and process monitoring. To make the molecular emission application well-founded, we summarized the molecular emission formation and how the experimental parameters influenced molecular emissions before the application. And, the framework of this review is shown in Figure 1.

FIGURE 1
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FIGURE 1. Framework of this review.

2 Molecular Emissions in LIBS

The characteristic molecular emission line radiates from the plasma induced by high irradiance (typically about 1010 W/cm2) and short pulse duration (typically <10 ns) laser, which is the same condition as that for atomic and ionic emissions. Different from the atomic and ionic emissions, however, there are two routes for molecular emissions: 1) recombination of the atomic and ionic species in the plasma and/or 2) direct emission by the molecular fragments separate from the matrix. For recombination routes, the species in the plasma contain molecular fragments and atomic and ionic species induced from the sample and surroundings, and the process can be described as plasma chemistry [20].

The molecular emission can be divided into organic element molecular emissions, oxide molecular emissions, and halogen element molecular emissions by the composition of the molecular radical. The band system and formation routes are listed in Table 1.

TABLE 1
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TABLE 1. Molecular emissions used in this review.

Organic Element Molecular Emissions

Carbon (C), hydrogen (H), nitrogen (N), and oxygen (O) are the main organic elements and can combine to form diatomic molecular radicals, such as CN (cyanogen), C2 (carbon dimer), CH (methylidyne), OH (hydroxyl) and NH (amidogen), and so on.

CN molecular emissions can easily occur during laser ablation of carbonic matter in the air. This mainly comes from the recombination of the carbon and nitrogen atoms in the plasma [23].

C2 molecular emissions can also occur from the carbonic matter. However, they always require the presence of a carbon–carbon bond (C-C) or carbon–carbon double bond (C=C) in the matrix. This mainly comes from molecular fragments [24].

CH molecular emissions are common from the core of the combustion zone. CH emission can be directly released and formed by carbon and hydrogen species [25].

OH molecular emission can radiate from plasma that includes high amount of H and O species. Such as laser ablation materials containing high mount water (H2O) and hydroxide radical. And the OH molecular emission is generally low [26].

NH molecular emissions can radiate from the plasma with nitrogen and hydrogen species. These molecular emissions are commonly released in high hydrogen (H) content materials induced by laser in the air and occur more commonly in the femtosecond-induced plasma [27].

Oxide Molecular Emissions

Metals and non-metals induced by lasers can combine with O to form oxide molecular emissions, such as aluminum monoxide (AlO), strontium monoxide (SrO), carbon monoxide (CO), boron monoxide (BO), and silicon monoxide (SiO).

AlO molecular emission can occur when aluminum alloy undergoes laser ablation in ambient air [28], combining Al and O in the plasma. SrO, CO, BO, and SiO molecular emissions are similar to the AlO molecular emission.

Halogen Molecular Emissions

Halogen is difficult to detect in LIBS due to the weak emission, which overlaps with the matrix, and because of their ultraviolet spectral region. The emissions of diatomic molecules of halogens, such as fluorine (F), chlorine (Cl), bromine (Br), and iodine (I), combined with alkali earth elements substantially increases the sensitivity for halogen detection. Alkali earth-halogen molecular emissions mainly recombined in the plasma [29].

3 Experimental Parameters for Molecular Emission

The same matters can radiate different molecular emissions due to the fact that plasma chemistry can be strongly influenced by experimental parameters [30], such as the timeline, laser characteristics (laser energy, pulse duration, and laser wavelength), and ambient air, which are the main influence factors. And, most studies were about CN and C2 molecular emissions. The CN emission is obtained by recombination, while the C2 emission is principally fragmented directly from the matrix. In this part, we will discuss the influence though CN and C2 molecular emissions. The formation route of CN and C2 molecular emissions is shown in Figure 2.

FIGURE 2
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FIGURE 2. Formation routes of CN and C2 molecular emissions. Laser ablate sample, atomizing carbon-atom and nitrogen-atom, fragmenting CN and C2 species from the sample, and atomizing nitrogen-atom and oxygen-atom from ambient gas. Species from the sample and surroundings combining new molecular species in the plasma.

Timeline of Molecular Emission

Spectral lines emitted from the plasma are changed continuously because of the electron density and temperature decrease during the expansion. Over the duration of the plasma’s persistence, the prevailing emitting species changes from ions to atoms, and to molecules in the ns LIB spectrum [31]. Furthermore, the lifetimes of the molecular emissions from the laser-induced plasma are much longer and later than the ionic and atomic emissions [32]. The molecular emission signal acquisition windows are in delay time 0.5–5 μs and gate width 0.5–1 F06Ds in experiments, generally [3335]. For CN molecular emissions, Fernandez-Bravo et al. [30] obtained precise time-resolved CN emissions. The results showed that CN emissions exhibited large behavior differences among organic compounds.

Laser Characteristics for Molecular Emission

In the LIBS system, the laser used to ablate the sample can be described by three characteristics: laser energy, pulse duration, and laser wavelength. As mentioned before that molecular species is produced at the timeline where the plasma temperature is low, the excitation of the molecular emission can be enhanced by reducing the heating effect of the laser with the materials.

When the laser energy reaches the ablation threshold of the material and vaporized it, the remaining energy is used to excite the vaporized materials to the upper state, and then the plasma is generated. Serrano et al. [36] showed that with a laser energy of increasing strength, greater energy will be used to atomize the material after reaching the ablation threshold, resulting in less molecular species in the plasma. And, they represented the atomization by the intensity ratio of CN/C2. Thus, to achieve more molecular fragments in the plume, it is helpful to have the laser energy close to the sample ablation threshold.

The other two characteristics, pulse duration and laser wavelength, depend on the native properties of lasers. Research studies have indicated that a shorter pulse duration and ultraviolet (UV) wavelength of the laser pulse can improve the spectral quality of molecular emission.

For the duration of the laser pulse, Junjuri et al. [37] concluded that femtosecond (fs) lasers are more suitable for the excitation of molecular emission than nanosecond (ns) lasers owing to shorter interacting time between the laser and materials. Rao et al. [33] showed that fs lasers can induce molecular emission earlier than ns counterparts, and the emission intensity can be stronger [38]. The reused Figure 3 shows that CN and C2 molecular emissions in ns and fs laser–induced spectra [34]. The intensity of ionic and atomic emissions is higher in the ns laser–induced spectrum, but molecular emissions are higher in the fs laser–induced spectrum. De Lucia et al. [39] discovered that the fs laser can reduce the disturbance due to inducing less species from the ambient atmosphere. Further, Shaik et al. [40] concluded that fs lasers can introduce less substrate interferences in molecular emissions.

FIGURE 3
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FIGURE 3. (A) Nanosecond LIBS signal obtained from TNT on an aluminum substrate. The detection gate delay and width values were 1 and 2 µs, respectively. (B) Femtosecond LIBS signal obtained from TNT on an aluminum substrate, over the complete detection wavelength range. The detection gate delay and width values were 100 ns and 1 µs, respectively [34].

For the wavelength of the laser pulse, the most commonly used wavelengths are the infrared (IR) laser pulses (1,064 nm) and the second harmonic, visible (Vis) laser pulses (532 nm) of the Nd:YAG laser. The short wavelength can interact with the sample more efficiently. Baudelet et al. ablated organic materials with UV pulses (266 nm) delivered by a quadrupled Nd:YAG laser, comparing the plasmas induced by the 4 ns IR laser with energy from 1–5 mJ [41]. The results demonstrated that ns UV pulses with a low fluence can produce native molecular fragments efficiently and a minimized recombination with ambient air [42]. The middle-infrared (M-IR) laser pulse (10.591 μm, 3.16 J) is also used in molecular emission studies [43, 44].

Ambient Atmospheres for Molecular Emission

The N and O atoms in the air (approximately 80% N2 and 20% O2) are also excited by the laser and participate in the plasma chemistry. To make more accurate use of molecular emission, it is necessary to study the atmosphere condition. Mousavi et al. [23] studied the molecular emissions of CN and C2 in ambient nitrogen (N2), air, oxygen (O2), and argon (Ar) atmospheres by the ns laser pulse. The results showed that the intensity of the CN and C2 molecular emissions decreased owing to the increased O2 content. In the N2 environment, the CN molecular emission intensity increased owing to the recombination of C and N. In the inert gas, Ar atmosphere, the vibrational temperatures of both CN and C2 had the highest values. Researchers have also studied CN and C2 in helium (He) and carbon dioxide (CO2) atmospheres [45, 46].

In addition, molecular emission is influenced by different pressures of the surrounding atmosphere. Delgado et al. [47] investigated the molecular emissions at high vacuum (<10−1 mbar) to high pressure (1,000 mbar). The results showed that emissions were dominated by ionic and atomic emissions at high vacuum. The C2 and CN emissions increased rapidly when the pressure was increased in the range between 10–100 mbar. While the pressure surpassed 100 mbar, the C2 and CN emissions decreased. The authors attributed this observation to there being less species collision in the plasma at a low pressure, leading to less reaction in the plasma.

4 Application of Molecular Emission

Quantitative Analysis by Molecular Emission

LIBS analysis through atomic and ionic emissions provides insufficient results when the self-absorption appearance and/or disturbed by other elements. In this part, we will discuss the role of molecular emissions in quantitative analysis [48].

4.1.1 Molecular Emission for Quantitative Analysis

Ionic and atomic emissions are rarely used for the quantitative analysis of high-content samples because of the strong self-absorption effect. The molecular emission from LIBS can be a promising solution. Zhu et al. [49] collected the BO molecular emissions from a mixture of H3BO3 and C6H12O6⋅H2O in the powder form. The root mean square error of prediction (RMSEP) and the mean prediction error (MPE) for the genetic algorithm and partial least square regression combination model (GA-PLSR) were 0.8667 wt.% and 10.9685% by BO molecular emissions, respectively. There was much better linearity in the molecular emission than the atomic emission of B I (249.68, 249.77, 208.88, and 208.96 nm), owing to the much lower self-absorption effect. However, the intensity of molecular emissions is much lower, which means that there is still room for further improvement in the calibration of the molecular emission. Guo et al. [50] assisted LIBS with laser-induced radical fluorescence (LIBS-LIRF) to establish calibration of BO molecular emissions. The results showed that the enhancement factors are 29.35 for vibrational ground state excitation (LIRFG) and 22.61 for vibrational excited state excitation separately (LIRFE). The LIRFG had better sensitivity, with a limit of detection (LoD) of 0.0993 wt.%, while the LIRFE was more accurate, with a root mean square error of cross validation (RMSECV) of 0.2514 wt.%. The enhancement factors and quantitative results are shown in Figure 4. Zhang et al. [51] used LIBS assisted with laser-induced molecular fluorescence (LIBS-LIMF) to establish the calibration of the silicon content by silicon monoxide (SiO) molecular emission in micro-alloyed steel. The determination coefficient R2 = 0.988, LoD = 187 μg/g, and RMSECV of 0.046 wt.%. In addition, CaOH emission can be used to detect the Ca content in underwater conditions. The results showed a LoD = 2.46 ppm with good linearity in a range from 5 to 2000 ppm [52].

FIGURE 4
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FIGURE 4. Spectral comparisons of (A) LIBS and LIRFG and (B) LIBS and LIRFE. Calibration curves of BO in (C) LIRFG and (D) LIRFE. [50].

4.1.2 Molecular Isotopic Emission for Quantitative Analysis

LIBS has been used in nuclear isotope safeguard inspection [8, 9, 53], but the tiny shifts between the isotopic atomic or ionic emissions can only be detected by high-resolution detectors and/or in low-pressure environments. Laser ablation molecular isotopic spectrometry (LAMIS) has been proposed as an efficient isotope detection method owing to the larger isotopic shifts. For example, the boron isotopic (11B–10B) shift in atomic emission is 2 picometer (pm). However, for 10BO and 11BO, the isotopic shifts extend from 0.74 nm to 5–8 nm. A partial least square (PLS) regression was used to further analyze the isotopic abundance approximately from 1 to 100% content of 11B, R2 = 0.9993 [54]. Furthermore, researchers at the Lawrence Berkeley National Laboratory detected the isotopes of hydrogen (H), boron (B), carbon (C), and oxygen (O) with LAMIS in reference [55]. Mao et al. [56] performed the isotopic analysis of solid Sr-containing samples (86Sr, 87Sr, and 88Sr) in ambient air at normal pressure. The results showed that the radial spectra of SrO and strontium fluoride (SrF) molecular emissions provided a well-resolved spectrogram for the naturally occurring Sr isotopes. Chirinos et al. [57] detected 13C from a graphite sample at a distance of 36 m by fs filaments - laser ablation molecular isotopic spectrometry (F-2-LAMIS) with a standardless quantification approach. The authors concluded that F-2-LAMIS can be a method to remote sense isotopes in the field.

In addition, the second laser enhance technology has been used in LAMIS. Brown et al. [58] utilized middle-infrared (Mid-IR) laser pulses (10.6 μm) for the second pulse, referred to as double-pulse LAMIS (DP-LAMIS) to determine the relative abundance of 11B and 10B. The results showed R2 > 0.960 and LoD <2.3%. Akpovo et al. [59] combined LIBS and molecular laser-induced fluorescence (MLIF) to selectively enhance the BO molecular emission (253–271 nm). The LoD was 1.88% by PLS regression, which was better than the single pulse result of 2.45%.

4.1.3 Halogen Molecular Emission for Quantitative Analysis

The emission of halogen elements (such as F, Cl, Br, and I) is weak in LIBS because they require a high excitation energy and cannot reach a good quantitative accuracy. Alkali earth-halogen molecular emission can be another choice to detect the halogen elements.

Dietz et al. [60] quantified the Cl content, a harmful element present in cement-based materials, by calcium-monochloride (CaCl) molecular emission. The results showed an LoD = 0.075 wt.%, which was below the critical threshold of 0.2 wt.% of chlorides related to the cement in reinforced concrete. Álvarez et al. [61] investigated the fluorite (CaF2) mass-content from 2.3 to 60% by calcium fluoride (CaF) molecular emissions in powdered ore samples. Further, CaF molecular emission was used to studied Cu matrix samples containing different F concentrations (between 50 and 600 μg/g) with variable amounts of Ca in the copper ore [62]. The results showed good linear relationships between the CaF molecular emission and F content. This methodology was extended in Ca-free samples by nebulizing a Ca-containing solution on the surface to form CaF molecular emission [63]. The LoD was 50 μg/g, similar to the Ca-containing samples. For other researchers, Tang et al. [64] used strontium fluoride (SrF) molecular emissions to detect the fluorine (F) content. The results showed that LoD = 5 ppm, R2 = 0.9933, and RMSECV = 0.0049 wt.%. In water condition [65], LoDs of F and Cl elements detected by CaF and CaCl molecular emissions were 0.38 mg/L and 1.03 mg/L, respectively. In addition, Br and I amounts were studied by molecular emission [66].

Classification by Molecular Emission

There are many research studies on classification analysis based on molecular emission. We summarized the research studies on the energetic materials, plastics, and biomedical samples.

4.1.4 Energetic Sample Classification

The direct chemical detection of energetic materials and explosives in real time is a particularly challenging problem. LIBS is a suitable technology to detect energetic materials. The first research study on explosives was reported by the U.S. Army Research Laboratory. De Lucia et al. [67] observed that the laser-produced plasma did not initiate any of the energetic materials and could be used to identify explosives. The C2 molecular emission and the H, O, and N emission intensity ratios were the necessary parameters to identify the explosive [68]. In addition, the relationship between the various kinds of explosives and plasma emission could be established by the ratio of the atomic/molecular emission intensities and the CN and C2 molecular emission decay rates with time [39]. Furthermore, the double pulse could improve the discrimination of explosives by decreasing the contributions of atmospheric N2 and O2 to the LIBS signal in the remote and on-line ways [69]. Partial least square discriminant analysis (PLS-DA) was used for distinguishing explosives at 50 m. The results showed that the correct classification rate was 80%, and the false positive rate remained at 7.8% [70].

For other research studies, Moros et al. [71] imported the original intensities of the most relevant emission signals (C:CN:C2:H:N:O) to different machine learning classifiers. False positive and false negative rates better than 5% were achieved. Yang et al. [72] captured three commonly used explosives (RDX, HMX, and PETN) molecular emissions in the long-wave infrared region (LWIR; range from 5.6 to 10 μm). The results showed that molecular emission signatures in the LWIR region could rapidly identify the different explosives.

Other energetic materials, such as solid propellants and petroleum, can also be studied by molecular emission. Solid propellants chemical aging is one of the most important problems for assessing the shelf-life of chemical propellants. Farhadian et al. [73] investigated and compared the CN and AlO molecular emissions of different kinds of solid propellants. The intensity ratios of the molecular emissions (CN, C2, and AlO) were also considered [74]. El-Hussein et al. [75] studied the different grades of petroleum crude oil by C2 and CN molecular emission. The results showed that the C2 and CN molecular emissions were related to the American Petroleum Institute (API) gravity values of the various oil samples with the possibility of identifying the API gravity values of unknown oil samples.

4.1.5 Plastic Sample Classification

LIBS technology is not affected by the plastic shape and surface contaminants and can be used in online, rapid detection in industrial applications. The intensity ratio of molecular emission can be used to complete the identification of different types of plastics without an algorithm model. Anzano et al. [76] studied four kinds of plastic samples. The ratios of C2/C could be used to classify those plastic samples. Barbier et al. [46] investigated plastic samples in the He atmosphere. The results showed that the plot of C2/He against CN/He was sufficient to identify the four groups of plastics employed in this study.

Researchers combine emission intensity ratios with statistical and stoichiometric methods to plastic samples. Banaee et al. [77] studied six plastic samples by ratios of the emission lines and molecular bands were analyzed by k-nearest neighbors (KNN) and soft independent modeling of class analogy (SIMCA). The results showed the average classification accuracies of 98% for KNN and 92% for SIMCA. Further, Banaee et al. [78] input the ratios of the CN and C2 molecular emissions, and the atomic emissions of C, N, Cl, O, and H were discriminated by discriminant function analysis (DFA) with the accuracy of 99%. Junjuri et al. [37] used an fs laser to enhance the effect of distinguishing the plastics by the principal component analysis (PCA) and artificial neural network (ANN), and the discriminant accuracy was 100%.

4.1.6 Biomedical Samples Classification

The development of reliable sensors to detect biological residuals is important for security terrorist activity and is a high priority for the military and homeland security. Gottfried et al. [79] collected the molecular emission of CN, C2, and CaOH from bacterial residues in the aluminum substrate, and the intensity and ratio of the emission were each input into the PLS-DA model. The results showed that the intensity/ratio models were able to correctly identify more types of residues in the presence of interferents. Baudelet et al. [80, 81] collected the CN molecular emission from the native CN band in Escherichia coli by the fs laser, and the emissions could be used to identify the bacterium [81]. In a low- pressure CO2 atmosphere, Delgado et al. [45] analyzed adenine, glycine, pyrene, and urea mixed with carbons. The results indicated LIBS with a potential for exploring life in the space environment. Yang et al. [82] detected the solid pharmaceutical tablet of Tylenol and buffering in the ultraviolet/ visible/ NIR (UVN) range (200–1,100 nm) and LWIR (Longwave infrared) range (5.6–10 μm), respectively. The molecular emissions were highly specific and could distinguish between tablets.

Process Monitoring

Molecular emission can identify intermediate chemical species among the combustion and explosive explosions in situ, which is helpful to understand the process. In this section, we summarized molecular emission research in combustion and explosion.

Molecular emissions of combustion intermediates can indicate the flame’s structure and burning quality. Ghezelbash et al. [25] investigated the CH, CH*, C2, and CO molecular emissions in different areas in the laminar diffusion of methanol, ethanol, and n-propanol alcohol flames. The strong molecular emissions of CH and CH* were from the blue zones (with low combustion quality). Kotzagianni et al. [83] demonstrated that the CN molecular emissions at 388.3 nm can be used to study the radial and axial variation within the flames. Li et al. [84] concluded that the femtosecond filament-induced spectrum contained rich information about the CN, CH, and C2 molecular emissions from the combustion intermediates of the butane flame.

The explosive ignited by the laser is similar to optical breakdown, and the molecular emissions that radiated from the process can be used to study it. Rao et al. [33] induced seven explosive molecules utilizing fs and ns lasers in the air and argon atmosphere. They observed the intensity ratio of CN/C2 emission increase with an increasing percentage of O atoms, indicating the oxygen balance of explosive molecules. They further concluded that the ratio of atomization/fragmentation could indicate the explosive properties. A similar research by Kalam et al. [85] found the ratios of (CN + C2)/(C + H + N + O) correlated well with the detonation parameters, namely, oxygen balance, velocity of detonation, detonation pressure, and chemical energy. It supported the understanding and improvement of the discrimination procedures for such hazardous materials. In addition, aluminum powder was added to molecular explosives to study its chemistry at high temperatures. Gottfried et al. [86] ablated cyclotrimethylenetrinitramine (RDX) mixed with aluminum power at (0:1, 1:1, 2:1, and 4:1). The results showed that Al could combine with O to generate AlO molecular emission, which reduced the oxidation reaction of the explosive and reduced the adequacy of the reaction.

5 Conclusion and Prospects

In this review, we overviewed experiment parameters and the application of molecular emissions. The results showed molecular emission is emitted from a time of low electron temperature and density in the plasma. The intensity is strong when the laser energy is close to the ablation threshold and UV laser wavelength (266 nm) in the ns laser system. In the counterparts, the fs laser can produce more abundant molecular emissions owing to less heating effect. The UV laser is economic and maintainable compared with the fs laser. We consider the UV laser maybe a better choice for molecular emission analysis. In addition, the ambient atmosphere should be considered in molecular emissions, such as N and O species in air surroundings. For the quantitative study, molecular emissions, including isotopic and halogen molecules, can detect a wider range of matter content. For the classification study, molecular emission can distinguish matters with similar elements, such as energetic materials, plastics, and biomedical samples. Furthermore, researchers studied the combustion process and characteristics of explosives and the degrees of explosion in situ and in real time.

Molecular emission is a kind of useful spectral line in LIBS; the study can further focus on detection of halogens, isotopes, and organic samples in the field. However, the complex radiation process confined the application LIBS. To apply laser-induced molecular emission in the field, it is necessary to study the molecular formation mechanism and optimize the parameters of the experimental system, reducing the disturbance of the ambient.

Author Contributions

FX helped with the writing and editing of the original draft. FX and SM helped organize the draft. CZ carried out the investigation. DD contributed to investigation, methodology, and conceptualization.

Funding

This research was financially supported by the Distinguished Young Scientists Program of Beijing Natural Science Foundation (JQ19023) and the Distinguished Scientist Development Program of the Beijing Academy of Agriculture and Forestry Sciences (JKZX201904). This review also funded by National & Local Joint Engineering Laboratory For Agricultural Internet of Things (PT2021-06).

Conflict of Interest

The authors declare that the research was conducted in the absence of any commercial or financial relationships that could be construed as a potential conflict of interest.

Publisher’s Note

All claims expressed in this article are solely those of the authors and do not necessarily represent those of their affiliated organizations, or those of the publisher, the editors, and the reviewers. Any product that may be evaluated in this article, or claim that may be made by its manufacturer, is not guaranteed or endorsed by the publisher.

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Keywords: laser-induced breakdown spectroscopy, molecular emissions, isotope, halogen, energetic samples, plastic samples, biomedical samples, process monitoring

Citation: Xu F, Ma S, Zhao C and Dong D (2022) Application of Molecular Emissions in Laser-Induced Breakdown Spectroscopy: A Review. Front. Phys. 10:821528. doi: 10.3389/fphy.2022.821528

Received: 24 November 2021; Accepted: 04 January 2022;
Published: 27 January 2022.

Edited by:

Yufei Ma, Harbin Institute of Technology, China

Reviewed by:

Minchao Cui, Northwestern Polytechnical University, China
Anmin Chen, Jilin University, China

Copyright © 2022 Xu, Ma, Zhao and Dong. This is an open-access article distributed under the terms of the Creative Commons Attribution License (CC BY). The use, distribution or reproduction in other forums is permitted, provided the original author(s) and the copyright owner(s) are credited and that the original publication in this journal is cited, in accordance with accepted academic practice. No use, distribution or reproduction is permitted which does not comply with these terms.

*Correspondence: Daming Dong, damingdong@hotmail.com

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