Laser-Induced Breakdown Spectroscopy for the Discrimination of Explosives Based on the ReliefF Algorithm and Support Vector Machines

Abstract

Real-time explosive detectors must be developed to facilitate the rapid implementation of appropriate protective measures against terrorism. We report a simple yet efficient methodology to classify three explosives and three non-explosives by using laser-induced breakdown spectroscopy. However, the similarity existing among the spectral emissions collected from the explosives resulted in the difficulty of separating samples. We calculated the weights of lines by using the ReliefF algorithm and then selected six line regions that could be identified from the arrangement of weights to calculate the area of each line region. A multivariate statistical method involving support vector machines was followed for the construction of the classification model. Several models were constructed using full spectra, 13 lines, and 100 lines selected by the arrangement of weights and areas of the selected line regions. The highest correct classification rate of the model reached 100% by using the six line regions.

Introduction

In recent years, explosions from terrorist attacks have spread across the globe. The advanced detection of explosives has attracted the interest of scientists in communities. Many techniques for explosive detection are well established and include Gas chromatography-Mass spectrometry [1]; Terahertz spectroscopy [2]; Raman spectroscopy [3–5]; photo-fragmentation, followed by laser-induced fluorescence [6]; and photoacoustic spectroscopy [7]. Although explosives can be detected by these advanced spectral methods, they require sample pretreatment and long detection time. A fast, in-situ method should be developed to identify hidden explosives in transit areas characterized by a high flux of people and goods. Hidden explosives can be recognized through the detection of their trace vapors or dispersed particles. The capabilities of laser-induced breakdown spectroscopy (LIBS) make it an attractive technique for the ultra-rapid, in situ identification of explosives [7, 8]. Given the atomic spectroscopy technique of LIBS, molecularly specific chemical identification is complicated by the similar stoichiometry of threats. Spectrochemical information obtained from a surface interrogated by LIBS provides the elemental composition of a potential surface contaminant and the surface through ablation. From an analytical point of view, explosives with different molecular structures and substantially constituent elements can be identified by atom emission [9–11].

LIBS is a rapid detection method with high efficiency and accuracy. In LIBS, a tightly focused laser pulse (usually a nanosecond laser) is used to create a micro plasma (10,000–20,000 K) on the surface of a sample. During cooling, the hot plasma emits light radiation at characteristic wavelengths; the radiation provides information on the identity of the elemental and molecular species present in the sample. LIBS has been prolifically evaluated for the detection/identification of explosive residues [12–26], chemical and biological materials [27–29], landmines [30], geological materials [28], and plastic [31]; for food authentication [32]; and other applications [33]. As an emerging analytical tool, LIBS has numerous advantages, including in situ application, ability to detect multiple elements and trace materials, and rapid microanalysis; it also does not require a separate sample preparation process [34].

Among the multivariate techniques demonstrated to be viable to classify an unknown sample as an explosive or a harmless product, the most widely used is elemental peaks ratios [35], principal component analysis (PCA) [36–41]. Several other chemometric methods, including soft independent modeling of class analogy [42], partial least squares Discriminant Analysis (PLS-DA) [43, 44], support vector machines (SVMs) [45], and artificial neural network, have been applied to LIBS spectra for classification and identification [46]. For example, Gottfried et al. applied PCA and PLS-DA on the LIBS spectra of carbonate, fluorite, silicate, and soil and reported a correct classification rate (CCR) of >95%. Femtosecond laser is also used to investigate spectral signatures of molecular and atomic species in air and argon atmospheres to correlate the spectral emission with the chemical structure for energetic materials, the correlation studies are expected to support the understanding and improve the discrimination procedures for hazardous materials [47, 48].

In the current paper, we present the results of our initial classification studies for three common explosives, namely, RDX, HMX, CL-20, and three interferences, namely, flour, talcum powder, and polytetrafluoroethylene (PTFE). The principal component that contains most of the variance information of the PCA algorithm is often used for data processing. However, the useful information that classifies different samples is not necessarily projected on the components with large variance. Selecting the principal component by using differences in contribution degrees will lead to serious information loss and classification deterioration. From the perspective of classification, the ReliefF algorithm selects the components with high weight and good effect as principal components to avoid the loss of important information in PCA algorithm. Therefore, we used a chemometric SVM method for the classification of the six test samples. We divided the spectral data of the tested samples into training and test sets. We calculated the weight of the lines of the training set by using the ReliefF algorithm and then selected element lines that could be identified from the National Institute of Standards and Technology database on the basis of the arrangement of weight to construct an SVM model for the classification of the samples. The data size and calculation time were decreased by using the element lines instead of complete spectra as input variables for the SVM model. Although our proposed methodology has only been applied to six samples, it could be generalized and possibly used to classify other explosives.

Materials and Methods

Experimental Setup

A schematic of the LIBS set-up used in this work is shown in Figure 1. Plasma was generated using an actively Q-switched Nd:YAG nanosecond laser. Typical lasers were used for the LIBS experiments. The lasers produced 10 ns and 80 mJ pulses at 1,064 nm with a maximum repetition rate of 10 Hz. Laser beam transmission was adjusted using three reflective mirrors and focused by a 100 mm convex lens onto the sample surface. The sample was mounted on an X-Y-Z translation stage with a resolution of 0.1 mm. We ensured that each laser pulse interacts with the fresh area of the sample. Emission from a plasma spark was collected by a two-fiber optic bundle that was 600 μm in diameter. A lens with a 30 mm focal length and 25 mm diameter was placed in front of the fiber bundle to sufficiently focus the plasma spark, thus allowing each fiber to collect the same emission. Each fiber output was sent to a two-channel-gated charge-coupled device (CCD) spectrometer developed by AVANTES B.V. Spectral information from each CCD was stitched together to yield LIBS spectra with a full spectral coverage of 190–1,100 nm and resolution of 0.3 nm. The operation of the spectrometer was controlled using customized electronics, including a high-speed photodetector and a digital delay/pulse generator (DG535). DG535 was connected to a photodetector, which produced a delay signal upon detecting a plasma spark to control spectral collection by the spectrometer. All LIBS spectra were collected with a 1.28 μs delay to eliminate plasma continuum effects and a 2 ms integration time synchronized with the shooting of the laser pulse.

FIGURE 1

Sample Preparation

Explosive samples of research-grade RDX (C₃H₆N₆O₆), HMX (C₄H₈N₈O₈), and CL-20 (C₆H₆N₁₂O₁₂) were provided by our School of Materials Science and Engineering at the Beijing Institute of Technology. The three possible interferent samples flour, talcum powder, and PTFE were also used for the study. All of the samples were in powder form. A piece of double-sided adhesive tape was secured on a glass slide, and the sample powder (approximately 1 g or less) was then crushed and spread with a Teflon block on top of the tape. Excess sample was shaken off, leaving a uniform thin layer of powder on the tape. We used the ultrasonic thickness gauge DR85 to measure the thickness of the powder layer which the total amount of sample with a thickness of 20 μm on 20 × 40 mm²-thin films upon the tape was approximately 20–30 mg.

Data Acquisition and Analysis

Although a double-sided adhesive tape is composed of organic compounds containing C, H, N, O, and other elements, we ignored the interference of the tape to the test the samples because of its weak spectral intensity. Multiple LIBS spectra were collected for each thin film. Each LIBS spectrum was collected from a single laser pulse and on a fresh shot. A total of 100 individual spectra from each sample of thin film were acquired. The spectra of each sample were randomly divided into two parts: training set and test set. For each sample, 70 spectra were used as the training set to build the classification model, and the 30 remaining spectra of each sample served as the test set to assess the discrimination ability of the model. Data analysis was performed without applying any spectral subtraction to the datasets.

For our LIBS experimental platform, we used SVM Toolbox program in Matlab version 2016a (MathWorks, Natick, United States) running Win7 on an Intel Core i7-4790K CPU with a 3.6 GHz processor and 8 GB of RAM. The LIBS spectrum collection software was provided by AVANTES B.V.

Results

Figure 2 shows the LIBS spectra of the six samples on a slide collected from a single pulse in ambient air. The features of interest were the atomic emission peaks labeled in the spectra. All of the samples, except for talcum powder, exhibited similar LIBS spectral characteristics in the 230–1,000 nm region. Each spectrum of the samples consisted of numerous strong emission lines contributed by Ca, Na, Mg, K, Fe, O, H, and N, whereas that of the explosives exhibited few strong emission lines. In the spectra of the explosives, O and N emission lines could be attributed to ambient air, whereas Ca, Na, K, Fe, and Mg emission lines were likely from common contaminants. In flour, the intensity of K lines was stronger than that of the five other samples because of nutritional requirements. CN lines, the characteristic emission feature of the spectra of explosives, were absent from the spectra of the talcum powder. Regardless of ablation mechanisms and dissociation pathways followed by any organic compound, all of the spectra of the explosives showed sequences of the violet system attributed to the CN fragment, which is generated mainly through the recombination of C with atmospheric N in the plume. C2 lines, another characteristic emission feature of organic compound, were present in the PTFE, which were mostly attributed to C=C fragments. Table 1 shows the major spectral lines of the six samples.

FIGURE 2

Discussion

SVM Model Using Full Spectra

To classify the six samples, we used SVM multivariate analysis to construct a classification model. SVM is a very common classifier. It has been popular for more than 10 years, and its classification ability is stronger than that of neural networks. The discrimination model was built on the basis of three one-versus-one SVM classifiers. SVM classifiers distinguish two classes of data by finding the best hyperplane that separates the data points of one class from those of the other class. In cases when binary classification problems do not have a simple hyperplane as a useful separating criterion, nonlinear transformation with kernel functions can be used [49].

A total of 420 full spectra of the six samples in the training set were used to construct the SVM model. The model built by using the min–max normalization preprocessing of full spectral data was called SVM1. The time needed by our computer to calculate the two models was 35 s. After modeling, we used the test set to assess the discrimination ability of the model. The test set was also constructed using min–max normalization preprocessing with the same parameters used in the model construction preprocessing. Table 2 shows the CCR of the SVM model. The average CCR result of the models reached 93.34%.

Lines Selected Based on Intensities

To construct a model with few input variables for classification, we studied the distribution of the intensities of different lines. Figure 3 shows the intensities of different lines and their standard deviation. Different samples had different intensities for the same line. For the lines of CN 386.16 nm and Ca 393.366 nm and the Potassium line of K 766.49 nm, PTFE, talcum powder, and flour had the strongest intensity, respectively. The lines of H, O, and N had different intensities in the six samples, which may be beneficial to the classification. A 3D plot of the intensity of Na 588.89 nm versus that of H 656.28 nm and K 766.49 nm, which had high weight values, is shown in Figure 4. The data separated into three distinct clusters. The first cluster comprised flour, which evidently separated from the other samples. The second cluster comprised HMX and talcum powder, which slightly overlapped. The third cluster comprised CL-20, RDX, and PTFE, which seriously overlapped. A 3D plot of the intensity of H 656.28 nm versus that of O 777.417 nm and N 742.24 nm is shown in Figure 5. The data of the six samples separated into six distinct clusters, indicating that three lines would be beneficial for classification. Because the spectral line of C 247 nm was not obvious and the carbon element had a strong peak in the CN band, two characteristic spectral lines CN 386.16 nm and CN 387.14 nm were selected to represent the carbon element. According to the composition of the elements, Ca 393.36 nm, Ca 396.84 nm, Na 588.89 nm, Na 589.59 nm, H_α 656.28 nm, N 742.24 nm, N 744.18 nm, N 746.86 nm, K 766.49 nm, K 769.89 nm, O 777.42 nm were very easy to identify as a single characteristic spectral line with high intensity. A total thirteen lines were selected to construct the SVM models. Table 3 lists the selected lines to construct the model. An SVM model called SVM2 was constructed using the 13 lines and test set to assess the discrimination ability of the model. Table 4 shows the CCR of the model. The CCR of the model was up to 99.44%.

FIGURE 3

FIGURE 4

FIGURE 5

Feature Selection Based on the relieff Algorithm

The Relief algorithm was first proposed by Kira [50] and initially limited to classify two types of data. The algorithm is a feature weighting algorithm that assigns different weights on the basis of the correlation of each feature and category. The weights of features that are less than a certain threshold will be removed. The correlation of features and categories in the algorithm is based on the ability of features to distinguish neighboring samples. It is widely used because of its relative simplicity, high operation efficiency, and satisfactory results; however, its limitation is that it can only process two types of data. Therefore, Kononenko [51] proposed ReliefF to extend the Relief algorithm in 1994. ReliefF algorithms can manage multiple categories of problems. They randomly take a sample R from the training sample set, find the k neighbor samples (near hits) from the same class of R and k neighbor samples (near misses) from the different classes of each R in the sample set, and then update the weight of each feature. The weight of each feature can be represented by Eq. (1).

In Eq. (1), represents the difference between samples R1 and R2 on feature A. represents the jth nearest neighbor sample in class C, and represents the k nearest neighbors from the same class of R. represents the proportion of class C, and represents the proportion of class randomly selected in the samples. can be represented by Eq. (2).

To reduce the calculation time of the model, we used the ReliefF algorithm to calculate the weight of each line of the full spectra (k = 10) and then selected the first 100 lines that involved high weights (weight threshold >0.05). The intensities of 100 lines were selected to construct the SVM models. Similarly, an SVM model called SVM3 was constructed with data preprocessing. The calculation time of the model was 9.2 s in our computer. After modeling, we used the test set to assess the discrimination ability of the model. Table 5 shows the CCR of the model. The CCR result of model reached 98.33%.

Areas of Line Regions Selected From the Weight Calculated by the relieff Algorithm

The value of k, which indicates the number of nearest neighbors in a sample, is crucial because different values of k affect the weight of each line in the ReliefF algorithm. Figure 6 shows the calculated weights of the top 100 lines with different values of k. Several line regions, such as CN bands, Na, Hα, K, and Fe, were easily identified. Na and K contributed higher weights than the non-metallic elements C, N, O, and H, which showed very weak weights, except for Hα. Each line region showed great similarity with different k values. Figure 7 shows the differences of intensity between different line regions. For the CN band region, the difference of six samples was not obvious, except for talcum powder. For talcum powder the lines of Mg 382.97 nm and Mg 383.57 nm contributed most of intensity in CN band region, the main component of which is magnesium silicate (Mg₃ [Si₄O₁₀](OH)₂). For the Potassium line of K 766.49 nm, flour had the strongest intensity, which may be attributed to nutritional needs. In addition, the K line region was composed of two major lines, including K 766.69 nm and K 769.89 nm. Given the low resolution of our spectrometer and Stark broadening, the high weight of lines calculated using ReliefF consisted of center and nearby lines. Therefore, most of the spectral lines with high weight values were composed of the central lines of Na, K, and H and their nearby lines. We selected six line regions that could be easily identified from the top 100 weights and calculated the areas under the line regions. Figure 8 shows the area calculation of CN band region based on the weight threshold (>0.05). We selected the boundary of each line region on the basis of the feature line of elements and calculated the area of region subtracted by the base line. Table 6 shows the selected line regions and their boundaries. All six areas used min–max normalization to construct the SVM model to classify the six samples. Similarly, a model called SVM4 was constructed, and the test set was used to assess the discrimination ability of the model. Table 7 shows the CCR of the model constructed using areas of selected line regions. The CCR of the model reached 100%.

FIGURE 6

FIGURE 7

FIGURE 8

In summary, an unsatisfactory result was obtained using the full spectra to classify the six samples. Although we further reduced the number of selected lines to construct the model, the CCR of the model reached 99.44% but was no longer raised. Excellent classification results could be obtained using the ReliefF algorithm to calculate the areas of six line regions instead of the full spectra of a model. In order to construct a classification model with the fewest input variables, we selected six line regions that could be easily identified from the top 100 arranged weights of lines by using the ReliefF algorithm. The boundary of each line region was determined on the basis of the top 100 arranged weights to calculate the area for constructing the classification model. The CCR of the model reached 100%. Most importantly, the line regions selected used to construct a classification model were easy to detect and identify. The few spectral lines selected to construct the model reduced the calculation time and increased the classification efficiency. These advantages promote the potential of the proposed LIBS–SVM model for the accurate and rapid classification of explosives.

Conclusion

Three explosives and three possible interferents were discriminated using the ReliefF algorithm and SVM under laboratory conditions. First, we constructed an SVM model by using the full spectra of the six samples. The CCR of the model reached 93.34%. Second, to construct a model with few input variables for the best classification, we selected 13 lines on the basis of the elemental composition of the organic compounds and the ease of identification to construct the SVM models. The CCR of the models reached 99.44%. Third, we used the ReliefF algorithm to calculate the weight values of each line and then selected 100 lines from the arranged weight values to construct the SVM models. The CCR of the model reached 98.34%. Finally, six line regions selected by using the ReliefF algorithm to construct the SVM classification model. The CCR of the model reached 100%.

This study was performed under atmospheric conditions. O, H, N, and C in the atmosphere could influence the LIBS spectrum of samples. In this study, we acquired the LIBS spectra of pure, not mixed, explosives. Thus, the LIBS spectra of the mixed explosives on the organic substrates were expected to be more complex than those of pure explosives on simple substrates. Further studies on the effects of external factors on the performance of SVM are currently underway.

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