Atomic spectrometry update: review of advances in the analysis of metals, chemicals and materials

Simon Carter a, Robert Clough b, Andy Fisher *b, Bridget Gibson c, Ben Russell d and Julia Waack c
aHull Research and Technology Centre, BP, Saltend, East Yorkshire, UK
bSchool of Geography, Earth and Environmental Sciences, University of Plymouth, Drake Circus, Plymouth PL4 8AA, UK. E-mail: afisher@plymouth.ac.uk
cIntertek Sunbury Technology Centre, Shears Way, Sunbury, Middlesex, UK
dNational Physical Laboratory, Nuclear Metrology Group, Teddington, Middlesex, UK

Received 1st October 2019 , Accepted 1st October 2019

First published on 23rd October 2019


Abstract

There has been a large increase in the number of papers published that are relevant to this review over this review period. The growth in popularity of LIBS is rapid, with applications being published for most sample types. This is undoubtedly because of its capability to analyse in situ on a production line (hence saving time and money) and its minimally destructive nature meaning that both forensic and cultural heritage samples may be analysed. It also has a standoff analysis capability meaning that hazardous materials, e.g. explosives or nuclear materials, may be analysed from a safe distance. The use of mathematical algorithms in conjunction with LIBS to enable improved accuracy has proved a popular area of research. This is especially true for ferrous and non-ferrous samples. Similarly, chemometric techniques have been used with LIBS to aid in the sorting of polymers and other materials. An increase in the number of papers in the subject area of alternative fuels was noted. This was at the expense of papers describing methods for the analysis of crude oils. For nanomaterials, previous years have seen a huge number of single particle and field flow fractionation characterisations. Although several such papers are still being published, the focus seems to be switching to applications of the nanoparticles and the mechanistic aspects of how they retain or bind with other analytes. This is the latest review covering the topic of advances in the analysis of metals, chemicals and materials. It follows on from last year’s review1–6 and is part of the Atomic Spectrometry Updates series.


1 Metals

The largest single topic researched in the area of the atomic spectrometric analysis of metals in this review period has been that of laser induced breakdown spectrometry (LIBS). This is especially true for the ferrous metals where LIBS can be used at the production line, providing real-time analysis and hence cutting costs.

There have been three review papers that have discussed the application of LIBS. One by Fu et al.7 discussed, with 168 references, the accuracy improvement that has happened to calibration free LİBS in recent years (mainly since 2010). Calibration-free LIBS was first proposed in 1999, but its use has been limited because it does not provide the same accuracy as other LIBS techniques or of more traditional methods of analysis. The review discussed methods for the accurate measurement of spectral intensity, the spatial and temporal window of local thermal equilibrium and the accurate calculation of temperature and the electron number density. Also discussed was the use of standard samples in combination with the calibration free LIBS algorithm. The authors acknowledge that this loses some of the advantages, i.e. it is no longer truly calibration-free, but since it is a new direction of research, it was included. The review’s final section offered conclusions and their perspectives for future research. A review by Noll et al.8 was entitled ‘LIBS analyses for industrial applications – an overview of developments from 2014 to 2018’. It contained 39 references and focused on the combined use of in-line measured three-dimensional geometry information and LİBS for high speed sorting tasks, e.g. of refractories. Also included were identification of steel blooms in a rolling mill and the recovery of valuable materials from the end of life electronic goods. The authors emphasised that LİBS instrumentation can be used in exceptionally harsh environments with measuring distances often between a few cm and a few metres from the sample. In general, the closer to the material the smaller the spectrometer need be. A discussion of the commercial hand-held spectrometers, several of which have been produced recently, was also presented. The third review was of a more general type and covered LIBS mapping in the biomedical, geological and industrial flields.9 This review presented (with 151 references) descriptions of the recent instrumental configurations, data processing methodologies and applications relating to LIBS-based imaging. The instrumental configurations discussed including the scanning configuration, the focusing systems, laser properties and spectral detection tools.

1.1 Ferrous metals

In addition to the review by Noll, discussed previously, numerous applications of LIBS have also been reported. A large number of these have used a chemometric tool to aid in regression or to aid classification of steel type. The first topic to be discussed in detail will be those papers that have described the chemometric tools used to aid regression. Kim et al.10 developed a LIBS device and tested it for the determination of alloying elements, e.g. Cr, Mn, Ni and Ti in low-alloy steel samples. The low spectral resolution of the spectrometer (0.9 nm) ensured that it was impossible to resolve these elements spectrally from other species. Partial least squares regression (PLSR) was therefore employed to extract the unresolved spectral features enabling calibration and quantification. This still proved to be very difficult for the congested part of the spectrum in which the Cr and Ti were being measured. It was, therefore, decided to use the first derivatives of the LIBS spectra. This enhanced the performance of the spectrometer further. Singh and Sarkar11 also used PLSR and compared its performance in terms of accuracy and precision with Principal Component Regression (PCR). Identical LIBS spectra from stainless steel samples were used for the comparison. A detailed study was undertaken of the role of the two algorithms so that an understanding of how they form the regression could be obtained. It was concluded that there were situations where both algorithms are equally appropriate and other situations where the use of one would be more suitable than the other. These situations were identified and some guidelines for other users presented.

Many papers have used machine learning or similar algorithms to “train” models to aid analysis. They usually use a series of samples to train a model and then test the model on ‘unknown’ samples. Analysis at elevated temperature is regarded as being less accurate than when undertaken at room temperature. Yang et al.12 attempted to overcome this problem to reduce costs and enhance the potential of on-line analysis. They collected LIBS data at room temperature and then applied ‘transfer learning’ to the spectra obtained at higher temperature. Fifteen standard samples were used to train the model at room temperature and four at elevated temperature. A further three “test” samples were then analysed at elevated temperature. The model was tested for determining Cr in certified alloy steel samples. The proposed method reduced the average absolute and relative errors by 1.8% and 20.6%, respectively. Mei et al.13 attempted to overcome the self-absorbance interferences and matrix effects that can be so prevalent in LIBS analyses. A multivariate calibration approach called genetic algorithm-kernel extreme learning machine (GA-KELM) was used to enable the quantification of Cr, Cu, Mn, Mo, Ni, Si, Ti and V in 47 certified steel and iron samples. A full description of the complex process was given. The performance of the model in terms of R-squared factor and root mean square errors of calibration were favourable compared with those obtained using traditional partial least squares. The conclusion was that the method could reduce matrix and self-absorption effects during LIBS analyses. Li et al.14 also attempted to overcome interference effects during LIBS analyses. They developed a semi-supervised quantitative analysis procedure that was based on a co-training regression model using a selection of effective unlabelled samples. Again, a large number of samples of known composition were used to train the model (11 CRMs) and five samples were used as labelled concentrations. The model was tested on seven other CRM samples for the determination of Cr in high alloy steel samples. A full description of the construction of the model was given. Results were impressive, with the root mean square error decreasing from 1.80% to 0.84% and the relative prediction error decreasing from 9.15% to 4.04%. The other paper of this type that deserves mention was presented by Guo et al.15 This paper also reported improved accuracy of LIBS analyses, this time using a hybrid sparse partial least squares and a least squares support vector machine model. The models were used to determine total Fe and the oxides Al2O3 CaO, MgO and SiO2 in iron ore samples. Again, 24 samples were used to train the model and only 12 used for prediction. The two models were used for different things: the sparse partial least squares was used to select variables and establish the multi-linear regression model between spectral data and concentrations and the least squares – support vector machine was used to compensate for non-linear effects. The hybrid model out-performed either of the two individual models with root mean square error of prediction values of 0.0456, 0.0962, 0.642, 0.2157 and 0.359, for total, Al2O3, CaO Fe, and MgO, SiO2 respectively.

Many of the mathematical models used for aiding regression have also been used for classification processes. A paper by Guo et al.16 compared the use of partial least squares – discriminant analysis with a support vector machine approach to classify different steel types. Forty steels with similar composition were analysed using LIBS. The spectra were then treated using the two algorithms with the partial least squares providing discrimination between 96.25% of the samples and the support vector machine 95%. The paper then described how a hybrid of the two algorithms was made, called least squares support vector machine, which yielded 100% discrimination efficiency. Shin et al.17 used LIBS followed by PCA to distinguish between different stainless steels, cast steels, aluminium alloys and copper alloys. A PCA of the full LIBS spectra provided good discrimination power but at the expense of computing time. This is a potential problem when used for sorting in the scrap metal industry as many hundreds of samples per day may require analysis. Consequently, the authors decreased the number of variables input to the PCA model. This was achieved by first obtaining full LIBS spectra and then using PCA to identify the input variables of greater significance for each element to be determined. The PCA was then repeated only on these more significant variables for future analyses. Although discrimination was marginally less good than PCA on the full spectra, the computational time required was decreased by a factor of at least 20. Xie et al.18 developed a novel method to achieve precise compositional prediction of steel samples based on wavelet packet transform and relevance vector machine (a machine learning technique that uses Bayesian inferences to obtain solutions for regression and probabilistic classification) analysis of LIBS data. The authors discussed the algorithms and how the spectral features extracted using the wavelet packet transform differed from those extracted using the traditional method. Using the absolute error of prediction and the mean relative error as measurement criteria, the wavelet packet transform out-performed the traditional method for extracting relevant spectral features to be introduced to the relevance vector machine. A better performance of the relevance vector machine was achieved through a modified Laplacian kernel function. The mean values of the root mean square error prediction of the modified relevance vector machine, the calibration curve, the unmodified relevance vector machine and the support vector machine were 0.159, 0.210, 0.303 and 0.179, respectively. It was concluded that the use of the wavelet packet transform of LIBS data followed by the modified relevance vector machine possessed superior efficiency generalisation ability and robustness for accurate and reliable compositional prediction.

Three papers discussed the analysis of steels used in the nuclear industry. In one paper, a LIBS spectrometer was developed that utilised a fibre-optic to deliver the laser energy.19 The spectrometer design was presented and the authors optimised the distance between the end of the fibre-optic and the sample. A clear optimum, based on the maximal spectral intensity and minimal spectral fluctuations, was observed. When the distance was too short, self-absorption was observed and too long a distance led to plasma density and temperature dissipating after as little as 1 μs. The spectrometer developed was then used under optimal conditions to determine Co, Cr, Cu, Fe, Mn, Mo, Nb, Ni and Si in Z3CN20-09 steel samples, which are normally used for structural materials in the pipelines of nuclear power plants. The same research group also used this instrument for the analysis of both Z3CN20-09 and 16MND5 steels, the second of which is used for the nuclear reactor pressure vessels.20 Under the same incidence laser power, the plasma from the Z3CN20-09 produced significantly lower emission intensity compared with the 16MNDS steel. This was attributed to it containing Cr at much higher concentration. This led to problems for calibration between different sample types. The authors reported the use of internal standardisation, support vector machine and random forest regression calibrations being established. Under optimal conditions, the Cr present at a concentration of 19.3% in the Z3CN20-09 was determined with a relative error of 3.5%, whereas when it was present at trace amounts (e.g. 0.11% in the 16MND5) the best root mean square error of prediction was 0.032% by weight. The Mn content which was present at between 1.19 and 1.51% by weight in both steels, was determined with a relative error of approximately 10%. The third paper used LIBS to analyse type 316 stainless steel weld parts that had been corroded by exposure to liquid lithium for 30 days at 450 °C.21 Repeated analysis of the same spot enabled depth-profile analysis with sub-micron depth resolution to be obtained. The extent of penetration of Li in the steel matrix was a measure of the level of corrosion.

The measurement of the corrosion of steels is another topic of interest. As well as the paper by Ke et al. above,21 several others have been published during this review period. Many of these have come from one group who also specialised in using LIBS.22–24 In the first, they used LIBS to obtain temporally and spatially resolved analysis of T91 steel which is used extensively for building industrial pressure-bearing heat exchange surfaces. The surfaces of several samples of the steel that had been aged to different extents were analysed and atom to ion line ratios and matrix element to alloying element ratios measured. The spectrometer and analytical procedure were described in full. For lesser aged steel, the maximum line intensity was located at greater height above the sample at a delay time of between 300 and 700 ns. Conversely, the steels aged to a greater extent gave maximum intensity just above their surface for the same time delay range. The line intensity ratios were dependent on the delay time and on the age of the steel. In addition, it was also noted that the depth and volume of the craters left from the LIBS analysis depended on sample age, with older samples providing deeper craters with greater volume. The second and third of the papers23,24 both used chemometric packages to assist in the estimation of the steel aging process. Lu et al.23 analysed eight T91 and seven 12CrMoV steels and then used ANOVA and logistic regression filter to reduce the number of LIBS variables into a smaller, more manageable number for introduction to the classification models logistic regression and support vector machine. Three different feature selection methods were tested and their effects on the models discussed. The performance of the models could be improved to some degree by implementation of all of the feature selection methods. However, one called layered interval wrapper performed the best. For T91 steel the prediction accuracy improved to 0.92 for logistic regression and 0.94 for the support vector machine when the layered interval wrapper was used to streamline the data. Without its use, prediction was less impressive (0.76 and 0.81). Results were less impressive for the 12MoCrV steels, but prediction accuracy still improved from 0.69 for both models to 0.87 for logistic regression and 0.90 for support vector machine. Unsurprisingly, it was concluded that the layered interval wrapper is a very effective feature selection method. The final paper by this research group24 also analysed T91 steels with different degrees of micro-structure ageing and then used a range of multivariate analysis methods to correlate the surface hardness (measured using emission line intensity) with age. These methods included PCA, canonical correlation analysis (both used to identify the important variables from the entire spectrum), and then two regression algorithms to form calibrations using the selected variables: partial least squares regression and support vector regression. Results demonstrated that coupling canonical correlation analysis with support vector regression enabled a hardness estimation to be made from spectral line intensity. Maximum values for mean relative error, RSD and root mean square error of prediction were 2.47%, 2.94% and 6.14, respectively. The other papers in this research area used methods other than LIBS. Barlow et al.25 used X-ray absorption near edge spectroscopy (XANES) as well as XRF to characterise erosion at a buried polymer–steel interface. The samples were exposed to high pH potash brine to induce corrosion. The XRF was used to determine Cl, Fe, K and Mn and then construct maps so that areas of anodic pits could be identified. The XANES was used to determine the phase of the Fe corrosion products present. The second paper26 was very similar. The XRF maps were produced using an excitation energy just above the metallic Fe K-edge threshold. The maps produce a sharp contrast between areas with and without corrosion. The μ-XANES was again used for confirmation.

Calibration free LIBS is a technique that is rapid, low-cost and is highly adaptable. However, it suffers badly from problems associated with self-absorption from major elements, it has few usable spectral lines from trace elements and requires correction of the relative efficiency of the experimental system. This means that accuracy and long term stability of calibration free LIBS can be compromised very easily. Several papers have described methodologies to overcome these deficiencies. As discussed previously, a recent development has been to combine calibration-free LIBS algorithms with standards. Although some advantages are lost, the overall effect is an improvement in accuracy. Hao et al.27 used an instrument made in-house and a two point standardisation method to measure the trace elements Al, Cr, Cu, Mn, Mo, Ni, Si, Ti and V in low alloy steel samples. The method was described in detail in the paper and was used prior to quantitative analysis of real samples. Six test samples were analysed every 24 hours for three days. Instrumental drift was effectively overcome using the two point calibration method. In addition, the average relative errors of repeated measurements decreased by 11, 3, 15, 45, 54, 16, 32, 91 and 11% for Al, Cr, Cu, Mn, Mo, Ni, Si, Ti and V, respectively when compared with data obtained without the standardisation. A method using a standard reference line combined with one point calibration was described by Fu et al.28 who determined six analytes in three stainless steels and five heat-resistant steels. The Stark broadening and Saha–Boltzmann plot for Fe was used to calculate the electron number density and plasma temperature, respectively. The standard reference line method alone was compared with the standard reference line method combined with one point calibration in an attempt to overcome the aforementioned problems with calibration-free LIBS. The combined use of the two methods improved the accuracy of the quantitative analysis. In addition, careful examination of the intercept along with the one-point calibration also improved the LOD. One point calibration was also employed by Hao et al.29 who also used multi-line calibration to determine Cr, Mn, Ni and Ti in low alloy steel samples. A combination of the methods led to improvements in the average relative errors by 22, 9, 21 and 36% for Cr, Mn, Ni and Ti, respectively. The advantages of the system are that it does not require a large number of standard samples, has no complicated calculations and it provides a flexible, low cost quantitative LIBS analysis method.

As described previously, there is huge potential for LIBS to be employed at the production line of steel plants. This saves time, money and modifications to formulations can be made rapidly. Two papers have discussed such an application. Zeng et al.30 combined a near IR instrument with a LIBS system to measure the temperature and the composition of molten carbon steel simultaneously. This was because the combined system utilised the same optical system and the same light collection fibre optic. The full schematic of the system was presented in the paper. Method validation for the thermometry was achieved by comparison with data from a commercial pyrometer. The relative root mean square error between the two was only 0.95%. The relative standard errors of Cr and Mn detection were lower than 10%. The other paper, by Cabalin et al.,31 described the installation and use of a stand-off, on-line LIBS system at a steel production plant in Bilbao. The LIBS system had been reported in a previous publication. The present paper discussed its installation 3.6 m from the hot billet in the continuous casting line and then its optimisation. Its positioning just before the oxy-cutting unit was ideal because it is at this point that billets of different steels need to be identified. Minor constituents such as Pb (from 0 to 0.17%) or V (0 to 0.1%) were useful in aiding discrimination between different steel types. The results from the system were compared with those obtained using an off-line LIBS system in a laboratory and with those from optical emission spectrometry. The results from all three were in good agreement. They were also in agreement with a mathematical model designed to predict the temporal evolution of the elemental content in the intermix region.

There is a large number of more simple applications of the analysis of iron and steels. One of the more novel of these was reported by Hegetschweiler et al.32 who described the use of single particle ICP-MS for the determination of titanium and niobium carbonitride precipitates in acid digests of micro-alloyed steels. The composition and particle size distribution of these particles are of importance for the mechanical properties of the steel. The single particle ICP-MS methodology is normally used for the analysis of nanoparticles, so this was a real application useful to industry. The results obtained from the ICP-MS were compared with those from electron microscopy. The single particle ICP-MS analysed over 2000 particles in one minute whereas the electron microscopy method could analyse far fewer. Both techniques identified two distinct particle populations: smaller particles contained only Nb and larger particles that contained both Nb and Ti. Electron microscopy also yielded information on the morphology of the particles. The larger ones were complex and ‘overgrown’ structures. The combination of the two techniques enabled a better understanding of the precipitation process that forms the particles during steel production at different stages of the thermo-mechanical – rolling process. This, in turn, would help improve the rolling process and help production.

Two applications have used ICP-MS to determine analytes in ferrous materials. In one by Steenstra33 laser ablation-ICP-MS (LA-ICP-MS) was used to determine analytes in iron-rich alloys. The premise of the work was to assess the matrix effects that occur when calibration is against glass standards rather than matrix matched standards. This was achieved using a 193 nm excimer laser system operating at ns firing times to ablate the materials and then compare the data obtained with those from electron probe microanalysis (EPMA). Measurements from LA-ICP-MS consistently overestimated the concentration of volatile elements and under-estimated the concentrations of non-volatile elements compared with EPMA data. An attempt to quantify the matrix interferences was made resulting in the fractionation index being presented. This index was independent of the concentration and on the type of iron-rich alloy under analysis. Values for the fractionation index ranged from 0.14 for the most volatile analyte to 1.8 for the most refractory element. The authors then used their findings to interrogate previously published data and to calculate metal-silicate partition coefficients. Comparison was made between corrected and uncorrected LA-ICP-MS data, where the corrected data were obtained by multiplying the uncorrected data by the appropriate fractionation index. Results demonstrated that erroneous data would be used if correction were not undertaken. The conclusion was that such a correction should be made for all samples of this type when analysed using LA-ICP-MS with this type of laser. A study by Wada et al.34 determined ultra-trace S in high purity metals including zinc and iron using isotope dilution-sector field-ICP-MS (ID-SF-ICP-MS). After dissolution of the metal, a chromatographic separation of the S from the metal matrix was undertaken using an alumina column. This served two functions: to prevent polyatomic interferences arising from the metal matrix and to prevent signal suppression arising from space-charge effects. The sector field instrument used was also capable of removing polyatomic interferences through use of medium resolution mode. Operating parameters such as detector dead time (that affects precision) and the washout conditions (to remove the possibility of memory effects) were optimised. The method was validated through analysis of the iron CRM JSS-001-4. The result obtained (1.86 ± 0.12 mg kg−1) was in good agreement with the certified value (1.90 ± 0.40 mg kg−1).

Three papers also reported applications for steel analysis using LIBS. Amongst this number is one by Zeng et al.35 who described the use of a portable fibre-optic LIBS system for the determination of the minor elements Cr, Mn, Ti and V in steel and pig iron. The R2 values for the calibration curves for the four analytes were all better than 0.99 and their root mean square errors of cross-validation were 0.0501, 0.0054, 0.0205 and 0.0245 weight percent for Mn, Ti, V and Cr, respectively. Six test samples were used with average relative errors being 5.6, 2.5, 11.7 and 13.0% for Cr, Mn, Ti and V, respectively. The data were comparable to those obtained using a normal LIBS setup. A paper by Cui et al.36 described the use of a collinear long-short double pulse LIBS system for the determination of Mn in steel washer samples. The long pulse (60 μs) was generated using a Nd:YAG laser operated in free running mode. The performance of the long-short double pulse LIBS was compared with that of the single pulse version. When operated under the same conditions, the double pulse LIBS had far superior linearity of calibration (R2 of 0.988) compared with the single pulse LIBS (R2 = 0.810) and had greater sensitivity. The second of these was attributed to the pre-irradiation effect. In addition, precision was also improved (10.5% RSD compared with 29.3% for single pulse LIBS). The biggest effect of the double pulse LIBS was on the average relative error of prediction which was 4.9% compared with the huge value of 94.9% obtained using only single pulse. The last paper of interest in this section was presented by Li et al.37 who used μ-LIBS assisted by laser induced fluorescence (LIF) to determine Si in low alloy steels. The presence of Si in steels has an important role in hardness and strength improvement. Unfortunately, it also leads to increased problems with corrosion and is harmful to ductility and therefore its concentration requires monitoring. The paper described the analytical setup and the mechanism by which the LIF assists the μ-LIBS. A comparison of analytical figures of merit for both the μ-LIBS-LIF and for μ-LIBS alone under their individual optimal working conditions indicated that the combination was far superior. The μ-LİBS-LIF yielded a calibration with R2 of 0.9998, a LOD of 2.8 mg kg−1 and a root mean square error of cross validation (RMSECV) of 63 mg kg−1. To the authors’ knowledge, this was the first time a LOD of less than 10 mg kg−1 had been reported using LIBS.

1.2 Non-ferrous metals

The readers’ attention should be drawn to the review papers discussed in Section 1, since these are equally applicable to the analysis of non-ferrous materials. As with the ferrous metals, LIBS continues to increase in popularity. In common with the applications for ferrous metals, one of the most popular areas of study has been the use of algorithms to improve the accuracy of measurement, to overcome interferences or to improve the long term stability. An example was presented by Pan et al.38 who described an efficient procedure for the construction and selection of calibration models for LIBS analysis. The procedure included the data pre-processing, construction of the calibration model and then the calculation of analyte concentrations in the samples. All of these steps could be pre-programmed with no further manual intervention. Using the developed procedure, the concentrations of 10 analytes were determined in nickel-based alloys. Most analytes had an average relative standard error of less than 10%. Zhan et al.39 used the machine learning algorithm called random forest for pattern recognition of LIBS spectra to aid in the classification of different aluminium alloys. As with the majority of such papers, a training set of samples is required for the model to function correctly. Once trained, the model can be used for test or unknown samples. The best classification accuracy obtained was 98.59%. The accuracy was dependent on the number of trees in the random forest and on the size of the training set of samples. It was concluded that LIBS with random forest provides a rapid, accurate and precise way of classifying aluminium alloys. Owolabi and Gondal40 also used algorithms to improve the performance of LIBS. They used a hybridisation of Extreme Learning Machine (ELM – a non-linear method that can approximate any non-linear relation) and Support Vector Regression (SVR – a non-linear tool based on learning theory). The former can, on occasion, suffer from over-fitting which can effect its accuracy. The SVR overcomes the problem of over-fitting if its parameters are properly optimised. The hybrid algorithm was used with LIBS analysis of seven standards bronze samples. A comparison of ELM-SVR, SVR-ELM, SVR and ELM was made, with best data in terms of root mean square error, being obtained for ELM-SVR. Each of the models had their hyper-parameters optimised using a gravitational search algorithm prior to the comparison. Three different normalisation techniques were compared by Sattar et al.41 for the minimisation of matrix effects during the LIBS analysis of silver–zinc binary compounds. These methods were: normalisation with background, internal normalisation and three point smoothing. The LIBS spectra of five composites were determined using various laser irradiances, with calibration for the Ag being at 338.28 nm and the Zn at 481.053 nm. The slopes of the calibration graphs provided an evaluation of the matrix effects. After optimising the parameter settings, the best analytical results were obtained using the three point smoothing normalisation method which yielded calibration curves with R2 values of between 0.995 and 0.998. Two papers were published by the same research group who explored ways of improving accuracy for different LIBS systems.42,43 In one,43 Fe, Mg and Zn were determined in aluminium alloys using fibre optic-LIBS. Use of spatially resolved fibre optic-LIBS enabled the workers to collect spectra at different positions along a direction parallel to the surface of the sample rather than from the centre of the plasma. By selecting different acquisition positions along the X-axis, it was possible to overcome problems associated with self-absorption. Root mean square errors of cross validation were improved from 0.388 to 0.172, 0.348 to 0.224 and from 0.097 to 0.024 weight% for Fe, Mg and Zn, respectively. In the other application42 a method of calibration entitled ‘Single Sample Calibration’ was developed and tested for the determination of several major elements (Cr, Cu, Fe, Mo, Nb, Ni and Zn) in three sets of matrix matched certified samples. A full description of the method was given. Compared with multi-point calibration, the results were much improved. Using Cu as an example, the R2 value, the root mean square error of cross validation and the average relative error improved from 0.40 to 0.97, 3.55 to 0.76 weight% and from 5.19 to 1.05%, respectively. The average RSD also decreased from 16.22 to 1.15%. The average relative error was dependent on the concentration range of the analyte, but was less than 5% for all ranges except 0–10 weight%, where it was 5.16%. For much higher concentration ranges, e.g. 90–100% the average relative error was 0.44%. Another paper to discuss the use of a chemometrics package in conjunction with LIBS was by Shin et al.17 This paper was discussed in detail in Section 1.1.

Partial least squares regression was used by Takahashi et al.44 for the underwater LIBS analysis of brass samples. The concentrations of Cu and Zn were determined using several different signal processing steps. These included normalisation, smoothing and background subtraction. Eleven certified brass samples were analysed to ascertain accuracy. Of the processing steps used, the normalisation provided the best results because it reduced the effects of both peak and background fluctuations. Database segmentation by excitation temperature further improved the partial least squares calculations. The method was applicable to real-time analysis and could potentially be used for fast, accurate and automated analysis at oceanic pressure.

One paper described the use of LIBS in situ to provide multi-elemental analysis and detect failures in an additive manufacturing process.45 A compact LIBS instrument was designed and installed on an industrial robot for real time analysis of the formation of a highly resistant coating of nickel alloy reinforced with tungsten carbide particles. The positioning of the probe within the production line had to be chosen carefully because of the inhomogeneity of the tungsten carbide particles in the upper surface layer. Scanning electron microscopy was used to check that the LIBS sampling had no deleterious effect on the cladding process. The LIBS analysis of the main elements (Ni and W) yielded data in good agreement with those obtained using offline XRF measurements. The conclusion was that LIBS was a very good prospect for the on-line measurement of the cladding process. A similar paper was also presented by Lednev et al.46 who used LIBS to quantify loose metal powders by first attaching them to double-sided tape. The technique reportedly worked even for materials of very different particle density, e.g. tungsten carbide and nickel alloy powder. Again, the methodology was validated by offline XRF analysis. A third similar paper by the same group was also reported.47

Two papers discussed calibration free LIBS analysis of non-ferrous samples. In one by Mal et al.48 a thorough explanation of what is required for calibration-free LIBS, and why, was given. Accuracy is known to depend enormously on obtaining optically thin conditions (since self-absorption occurs at optically thick conditions) and local thermal equilibrium. Evaluation of the temporal evolution of the plasma enabled the authors to identify the optimal temporal window where both of these fundamental criteria were met. This was achieved by studying the plasma temperature through the emissions of atomic Cu via a Boltzmann plot and estimating electron number density through the Stark broadening of the profile of the Cu ion wavelength at 510.5 nm. These estimates were then inserted to a one-line calibration-free LIBS algorithm to determine the percentage composition of three copper alloys. Results were in good agreement with those obtained using EDX. The other paper, by Li et al.49 corrected for self-absorption effects during calibration-free-LIBS using a new method which they entitled ‘black body radiation referenced self-absorption correction’. An algorithm was devised that calculated plasma temperatures and collection efficiency of the optical collection setup by comparing the measured spectrum with the corresponding theoretical black body radiation for self-absorption correction. The proposed method had several advantages over existing methods including simpler programming, higher computational efficiency and independence from line-broadening coefficients that, even if available, may not be very accurate. Titanium alloy samples were used as the testing materials. Correction of self-absorption effects was demonstrated by improved linearity of the Boltzmann plots and accuracy of the analysis was also improved when compared with data obtained when the algorithm was not used.

Three papers have discussed the use of laser ablation-spark induced breakdown spectroscopy (LA-SIBS) for the analysis of copper alloys,50 aluminium alloys51 and both brass and aluminium alloys.52 This technique uses a spark to re-excite a plasma produced by a laser ablation unit and then the light emitted is characterised and quantified. A Nd:YAG laser operating at 1064 nm and at a repetition rate of 1 kHz was used to ablate the samples in the first instance and then the spark was used to prolong the plasma and promote the breakdown of the ablated sample further. In one example,51 the detection limits for Cr, Cu, Mg and Mn were 9, 7.8, 11.1 and 20.1 mg kg−1 which represented improvements of 4–10 fold compared with ordinary LIBS. Precision was excellent, with RSD values of 3–4% being obtained. Another of the papers50 described the compact multi-channel fibre-based spectrometer used. Detection limits for Al and Pb using the system in a non-gated operation mode were 1.9 and 15.5 mg kg−1; again representing an improvement of between 6 and 11 fold compared with those obtained using LIBS alone under the same laser-ablation conditions. The third of the papers52 used a gated pulsed high voltage power supply as power source for the spark discharge and then studied the delay between the high voltage pulse and the laser pulse. The orientation of the electrodes was also studied. By changing electrode orientation and by increasing the time delay, it was possible to change the discharge from a V-shape to a parallel arrangement. Both configurations had advantages. The V-shaped discharge could ablate more sample and increase the diameters and depths of the craters, whereas the parallel arrangement was more discrete in that it did not ablate new sample area other than that already ablated by the laser. In the parallel configuration, emission intensity decreased with increasing time delay but increased with discharge voltage. Under optimal conditions, improvements in sensitivity were again reportedly 4–10 fold better than standard LIBS.

Two papers have reported the analysis of solder. In one by Huang et al.53 a forensic analysis of lead-tin solders was undertaken using ICP-MS. The authors pointed out that lead-tin solder is an integral part of many improvised explosive devices and therefore a forensic analysis of them could help in evidence gathering. Samples of solder (approx. 10 mg) were acid digested using 2 mL of nitric and 0.5 mL of hydrochloric acids and then heating to 150 °C. After further addition of nitric (8 mL) and hydrochloric (2 mL) acids, the digest was diluted to 50 mL. Samples were then diluted a further 100-fold prior to analysis. The analytes Bi, Cu, Ni and Sb as well as Pb and Sn were then determined. External calibration was achieved through acid digestion and appropriate dilution of the standard solder sample NIST SRM 1131. Eight different solder samples were analysed and distinguishable differences between the analytes were observed enabling a discrimination to be made. The authors then extended the study to see the effects of a heating gun on two different solder types. An increase in Cu concentration was observed for the sample with a rosin core. This contamination could, according to the authors, be used to provide information on the type of soldering gun used if the solder used contained a rosin core. The other paper described the use of LA-ICP-MS to analyse lead-free solder chips.54 The analytes Ag, Cu, Pb and Sn were determined. Calibration was achieved using a standard solution matrix matched to the Sn content of the sample. This solution had to be prepared in nitric acid to prevent precipitation of Ag. This helped maintain linearity of the Ag calibration curve. Analysis of NMIJ CRM 8203-a provided data in good agreement with certified values as long as the fluence of the LA system was maintained at over 12 J cm−2. At fluences below that, elemental fractionation occurred. It was noticeable that uncertainty values were very high. This was attributed to potential inhomogeneity of the sample at the micro-scale.

A host of other disparate applications have been published. These included a room temperature chelate vapour generation prior to atomic fluorescence detection for Ni determination in a variety of samples including aluminium alloy.55 The alloy (0.1 g) was dissolved in 30 mL of 6 M HCl. The presence of methanol or ethanol at a concentration of 2% v/v enhanced vapour generation by a factor of 2.6. Under optimal conditions, a vapour formation efficiency of 50% was achieved. The LOD was 1.12 ng mL−1 and precision at 40 ng mL−1 (n = 10) was 2.9%. The mechanism of formation of the Ni-diethyldithiocarbamate chelate vapour was not fully understood and will be examined in future work. Alkali and alkaline earth elements caused no interference, but transition elements, e.g. Fe, Mn and Zn did – even at quite low concentration. These interfering ions had to be removed using a solvent-impregnated resin with a tertiary amine extractant prior to the vapour generation step. The method was validated through the analysis of a certified water sample (GSB07-3186-2014) and digests of a certified aluminium alloy (LD2). Results were in good agreement with certified values.

The analysis of high purity metals has been the subject of three papers. One by Medvedev et al.56 described the analysis of high purity cadmium. The solid sample was weighed into an electrothermal vaporisation (ETV) device prior to detection using ICP-OES. The temperature program of the ETV device was optimised and an ash/char temperature of 900 °C was sufficiently high to remove the cadmium matrix. The analytes (Al, Au, Be, Bi, Co, Cr, Fe, Ga, In, Mn, Ni, Re, Sn and V) were then vaporised at 2400 °C and transferred to the ICP-OES instrument for detection. Detection limits were improved by a factor of between 3 and 670 when compared with ICP-OES using a 2% cadmium solution and conventional nebulisation. No suitable CRM was available and so method validation was through an independent technique (ICP-MS) and through spike/recovery experiments. It is noticeable that Cu, Pb and Zn are not among the analytes. This is presumably because they will also be at least partially lost at a char temperature of 900 °C. A paper by Fu et al.57 described the analysis of high purity (5 N, i.e. better than 99.999% pure) cobalt powder using a triple quadrupole ICP-MS instrument. The sample was first dissolved using a mixture of nitric and hydrochloric acids with microwave assistance. The dissolved samples then underwent analysis using the instrument with a range of reaction gases being tested to overcome interferences. Addition of oxygen enabled the analytes As, P, S, Se and V to be determined at their respective oxide mass, e.g. AsO+ at m/z 91, etc. Addition of hydrogen to the reaction cell helped shift interferences on Ca and Si enabling the two analytes to be determined at their own isotopic mass. A mixture of ammonia and helium introduced to the cell helped form cluster ions and enabled interference-free determination of Cr, Cu, Fe, Mn, Ni, Ti and Zn. The same reaction gas mixture also enabled Al, Mg and Na to be determined because polyatomic interferences on these analyte isotopes formed cluster ions and were, hence, shifted away from the measurement regions. In all cases, matrix effects were overcome by the on-line addition of internal standard elements. Detection limits were in the range 0.02–97.5 ng L−1 and calibration curves demonstrated good linearity. Analyte spikes gave recoveries in the range 91.6–109%, which was deemed acceptable. The third paper58 determined S in copper metal and copper alloys using isotope dilution (ID)-LA-ICP-MS. The aim of the study was to combine the benefits of ID and LA-ICP-MS to avoid the time-consuming and laborious sample preparation procedures (matrix separation) that are usually required for conventional ID-MS for the determination of S. The samples were spiked with the isotopically enriched solution, dissolved and then the resulting digests absorbed onto polyethylene frits. The frits were then analysed using LA-ICP-MS. The advantages of the method included the very low S signal in the blank samples and that spiking with known amounts of S showed that the frits absorbed more than 99.5% of the S. Calibration curves demonstrated good linearity up to 40 μg of S. The methodology was validated through the use of the reference materials BAM-376a, BAM-228 and BAM-227 which delivered 2, 5 and 11 μg of S to the frits, respectively. Pre-analysis of the samples using external calibration LA-ICP-MS had indicated values of 0.9, 5.1 and 8.5 μg g of S (measured at m/z 32). Results for the ID-LA-ICP-MS were compared with those using conventional ID-ICP-MS with Pearson’s coefficient correlating the two sets of data giving a value of 0.999. The relative expanded measurement uncertainty of the ID-LA-ICP-MS data ranged between 10 and 26%. The procedure was, according to the authors, traceable metrologically to the SI because of an unbroken chain of comparisons, each with their own uncertainty budget. The overall methodology was deemed to be reliable and acceptable.

The determination of Hg during the analysis of dental amalgams using LIBS was described by Castellon et al.59 Several samples with matrices composed of differing proportions of silver, copper and tin were analysed. Delay times between the laser pulse and the measurement of the spectra were tested over the range 1 to 5 μs. Calibration curves were prepared and steps were taken to compensate for the matrix effects and changes in electron number density and plasma temperature that arise from them. The paper discussed this in detail as well as the effect of the delay time on the accuracy of analysis.

Two papers were presented that discussed the analysis of parts of nuclear reactors. A paper by Galmed et al.60 discussed the measurement of surface hardness of titanium samples that had been bombarded by carbon ions. The titanium samples comprise the inner reactor walls of a nuclear plant and their exposure to energetic ions is known to change their physical properties. The authors used LİBS for the analysis. The surface hardness was assessed by measuring variation in the plasma excitation temperature. The results were in good agreement with those obtained using conventional means. A similarly nuclear themed application was presented by Warchilova et al.61 These authors described the use of LA-ICP-MS for monitoring the corrosion of nickel-based samples used as structural materials for nuclear reactors that had been exposed to molten fluoride salts.

1.3 Cultural heritage: metals

With cultural heritage samples, it is usual to try and inflict as little damage as possible. This is true whether they be metal objects, ceramics, glasses or any other material. The premise, of course, is that there is little point in analysing priceless materials if they are to be destroyed or disfigured during the analysis. The use of analytical techniques that are either non-destructive (e.g. XRF) or minimally destructive (e.g. LA-ICP-MS/OES, LIBS) are therefore more common than other techniques. A review of LIBS analyses in cultural heritage samples was presented (with 212 references) by Botto et al.62 The review covered several material types including pottery, metals, pigments, glass etc. It also covered the use of different types of LIBS analysis and LIBS used in conjunction with other techniques, including Raman, XRF and MS. Specific applications, e.g. those analyses made under water and those used in support of restoration were also discussed. New trends for LIBS in the area were also discussed. These include μ-LIBS, 3D elemental imaging and nanoparticle enhanced LIBS.

A paper by Lazic et al.63compared the techniques of LIBS, XRF and PIXE for the analysis of egg tempera pigments on gypsum, oil paints on gypsum, glazed ceramics and Roman coins. The LIBS analyses were undertaken for all sample types, an XRF instrument was used for the coins and a portable XRF instrument used for the pigments and ceramics and the PIXE was used to analyse pigments and ceramics. Both major and minor analytes were determined. The results were compared as were the possibilities for lateral and depth-resolved data. The PIXE was capable of best lateral resolution (1 μm) compared with the LIBS (10–50 μm) and the μ-XRF (50–100 μm). In all cases, the sensitivity decreased with the spot size. For depth resolution, the LIBS had by far the best resolution (1 μm compared with tens of μm for the other techniques).

The reliability of the data produced using a portable XRF instrument when analysing corroded copper-tin alloys was discussed in a paper by Robotti et al.64 Samples of copper–tin alloy (88[thin space (1/6-em)]:[thin space (1/6-em)]12), similar in composition to ancient Egyptian alloys, were corroded in three different solutions containing aggressive anions. Solution 1 was ammonium chloride and ammonium carbonate, solution 2 was potassium chloride, copper sulfate pentahydrate and sodium sulfate decahydrate adjusted to pH 3 using sulfuric acid and solution 3 was copper nitrate and sodium chloride. After the corrosion period of up to three months, the samples were removed, and analysed using portable XRF. Cross-sections of the samples were also analysed using SEM-EDS. A chloride-based solution led to a de-cuprification and made the XRF data less accurate. This was attributed to a build up of tin compounds. Another problem was the onset of bronze disease, i.e. the formation of atacamite and paratacamite. Using the “patina” and “metals” algorithms of the instrumental software enabled accurate information to be obtained from samples immersed in solutions 1 and 3. However, without their use, it was impossible to obtain accurate data.

Many of the applications for cultural heritage samples give good detail of the archaeology aspect, but are often somewhat light on analytical detail. Those that give no detail will therefore not be discussed further. Those that give an indication of method validation/quality control or those that use the data in a novel fashion, e.g. elucidating trade routes, provenance studies etc. are shown in Table 1.

Table 1 Cultural heritage applications of metals
Analyte Matrix Technique Comments Ref.
Ag and Cu A tetradrachm from the period of the emperor Claudius XPS, TOF-SIMS, SEM-EDX Surface analysis techniques as well as some depth profiling using TOF-SIMS used to identify composition and distribution of analytes. Minimal damage caused 65
Ag, Au, Cu Necklace of Carambolo hoard μ-XRF Portable μ-XRF instrument developed that had a spot beam with radius of a few μm. The technical details of the instrument were given. Ternary diagrams plotted to distinguish between two different alloys used to manufacture some of the pins of the necklace 66
Cu, Pb, Sn Soldering found on handle attachments of Roman situlae μ-EDXRF, SEM-EDS, optical microscopy μ-EDXRF instrument used that had a spot size of approximately 70 μm in diameter. Quantitative analysis using fundamental parameters method. Two reference materials used: phosphor bronze 551 and leaded bronze C 50.01. Solders contained 30–60% Sn 67
Organic coatings Ancient silver artefacts XRF Thickness of protective organic coatings on silver artefacts determined. Three mylar sheets with certified thicknesses were placed on a silver substrate and measured for validation. Three different quantification protocols tested: empirical and theoretical calibrations and a fundamental parameters approach. Data compared with the eddy current technique. The empirical approach provided the most accurate data 68
Various (16) Ancient gold products from the Black Sea region LA-ICP-MS Micro-geochemical features of micro-inclusions in the artefacts examined using LA-ICP-MS. Platinum group elements and other metals determined. Ternary plots of Ir, Os and Ru used to distinguish samples from different sites. Two sources of gold identified and cupellation suggested as being the most common method of refinement 69
Various (18 + REE) Slag materials from early iron production in Croatia XRF, ICP-MS, ICP-OES, SEM-EDS Microwave assisted digestion employed for ICP-OES and MS detection. Pellets prepared for XRF analysis. Two CRM used for validation: NIST 1155 a steel and TRM-2 rare earth ore. Analytical data underwent auto-scaling and logarithmic transformation prior to being input to hierarchical cluster analysis and PCA. Three types of slag identified: iron rich tap slag, bloom slag and ceramic-rich slag 70
Various (16) Prehistoric bronze artefacts from Naples and Salerno in Italy μ-XRF, ICP-MS, X-ray powder diffraction, SEM-EDS Provenance study of artefacts made using Pb isotope ratios. Samples (5 mg) were dissolved in HNO3, passed through a column of Sr-Spec resin and the matrix components washed off using 1 mL of 1 M HNO3. Lead eluted with 3 mL of 0.01 M HNO3 and isotope ratios determined on a multicollector ICP-MS instrument. Mass bias was corrected for using Tl and NIST 981 was used for monitoring external reproducibility 71
Various (Ag, As, Bi, Cu, Ni, Sb and Sn) + Pb isotopes Late Roman Republican lead artefacts from Portugal ICP-MS Twenty two samples acid digested and analysed using quadrupole ICP-MS. NIST 981 common Pb isotope standard and BCR 288 used for quality control purposes. Factor analysis and cluster analysis using Ward’s method used for data analysis. Binary plots used for Pb isotope ratios. Galena was the most probable Pb source although some samples with high Cu may have been produced from litharge. Lead isotope ratios indicate a probable Iberian provenance 72


2 Organic chemicals and materials

2.1 Organic chemicals

Overcoming matrix effects remains a challenge within the analytical community; especially in secondary ion mass spectrometry (SIMS). This can impact the results. In order to establish the extent of matrix effects three binary organic mixtures were sputtered with argon and analysed utilising 25 keV Bi3+ and depth profiles obtained using SIMS.73 It was observed that matrix effects approximately scale with mass to charge ratios as smaller effects were noted for low mass ions. In addition, the presence of hydrogen was crucial as the likelihood of charge transfer decreases after a loss of H+ and therefore becomes less favourable. The authors discussed the theory of the observed phenomenon in great detail and could conclude that ion velocity, fragment chemistry and the point of secondary ion point of origin are all contributing factors to the observed matrix effects.

Routine determination of Br has been a challenge in AAS because of its resonance line lying in the UV region at 148.86 nm. Turhan et al.74 therefore developed a method to determine Br via the molecular absorption of BaBr (520.819 nm). Following method optimisation, pyrolysis and volatilisation temperatures were set at 700 and 2200 °C, respectively. Neither Pd modifier nor a Zr coating was utilised in the developed method. The formation of molecular BaBr was achieved by using 10 μL of 25 mg L−1 Ba. Spike recovery studies on commercial drug samples showed no significant non-spectral interferences. The characteristic mass was 4.0 ng with a method LOD of 1.7 ng. However, it was noticed that spike studies were only performed for two of the four drug samples present. It would have further supported the accuracy of the developed method had all four samples been investigated for their spike recovery. In addition, excellent linearity of R2 = 0.999 was reported. However, this had only been investigated for a range of up to 1 μg Br, which seems rather narrow. Nonetheless, it was a promising approach to enable Br detection using AAS.

2.2 Fuels and lubricants

This year the numbers of papers in this section has increased, particularly in the fields of crude oils and alternative fuels. There seems to have been a shift from conventional oil and crude oil analysis to more environmentally friendly alternatives, some somewhat unconventional such as Amazonian Sailfin Catfish. There also seems to be interest in using fly ash and other by-products as possible feed stocks for other industries such as REE extraction, possibly reflecting the global demand for these elements in the modern world and the subsequent increase in their price.

The analysis of coal has seen a decrease in papers this year, including in the number using LIBS. However, ETV seems to have had a renaissance as it is perceived to be more environmentally friendly than conventional sample dissolutions with solvents and acids. The technique of ETV was used by several authors as a sample introduction step linked to other instrumentation.

2.2.1 Petroleum products – gasoline, diesel, gasohol and exhaust particulates. Three papers were of interest in this section, the first by Souza et al.75 investigated the use of GF AAS for the determination of volatile and non-volatile Ni and V in gasohol after extraction by emulsion breaking. The determination by difference of the total, non-volatile and volatile fractions containing Ni and V was carried out by assessing the differences in the thermal behaviour of the species during the pyrolysis step. The detection limits for Ni were 3.5 μg L−1 for total content and 1.7 μg L−1 for the non-volatile fraction and for V 1.1 μg L−1 for total content and 0.42 μg L−1 for the non-volatile fraction. This is an interesting approach and yields more information on the forms of the Ni and V present and their possible origin than the total Ni and V concentrations alone.

The next paper of interest, by Wu et al.,76 described a method for the determination of As, Cd, Hg, Pb and S in fuels using ETV-ICP-MS. The aim of this method was to simplify sample preparation from acid digestion or ashing to a simple emulsion step and to minimise interferences. The sample was introduced in the form of an emulsion and Pd used as a modifier. Oxygen was used in the dynamic reaction cell of the instrument and As was measured as AsO at m/z 91 and S as SO at m/z 48. The detection limits estimated from standard addition curves were 0.07, 0.1, 0.07, 0.07 and 39 ng g−1 for As, Cd, Hg, Pb and S, respectively. A number of samples were analysed and good correlation between the ETV-ICP-MS method and conventional sample digestion was obtained.

Lu et al.77 described a method for the determination of S in petroleum fuels using sector field ICP-MS. Legislation by the EU requires that gasoline and diesel contain less than 10 μg g−1 of S and they are looking to lower this limit. Therefore, more sensitive methods for this analysis are currently required. For this method the samples were diluted 1000 fold with IPA or an IPA-toluene mix and Co added as an internal standard. The dilution factor could be decreased if lower detection limits were needed. The isotopes 32S and 34S were used for the analysis with the resolution of the sector field ICP-MS instrument adjusted to 4000 to resolve the polyatomic interferences. Detection limits for this method were between 0.09 and 0.17 ng g−1.

2.2.2 Coal, peat and other solid fuels. The first contribution in this section is from Henn et al.78 who assessed the feasibility of As, Sb, Se and Te determination in coal using ETV-ICP-MS. In order to overcome the limitations of sample preparation methods, ETV was proposed for the introduction of solid coal samples to the ICP-MS instrument. A permanent modifier was made on the graphite platform by adding a solution of 1000 mg L−1 Ir to it and then drying using an IR lamp. Samples were weighed on to the graphite platform, which was then inserted into the furnace connected to the ICP-MS instrument. The analysis was acquired in peak hopping mode and the peak area integrated. The Ar dimer signal was monitored to compensate for plasma oscillations during the vaporisation step. Samples and the CRMs NIST1632b, NIST1632c and NIST1635 were also digested using a conventional method to compare with the new ETV method. Results from both methods showed good agreement with the certified values. The LOQs from the ETV method were 0.03 μg g−1 for As, 0.01 μg g−1 for Sb, 0.03 μg g−1 for Se and 0.006 μg g−1 for Te. These compared favourably with the LOQs obtained using the digestion method which were 0.02 μg g−1 for As, 0.04 μg g−1 for Sb, 0.07 μg g−1 for Se and 0.007 μg g−1 for Te.

A paper by Iqbal et al.79 was the first of two LIBS papers and investigated the compositional analysis of Coal using calibration-free LIBS. A high-power Q-switched Nd:YAG Laser, (532 nm, 5 ns pulse width and 10 Hz repetition rate) was used and the optical emission spectra were obtained using a HR 4000 spectrometer covering the wavelength region from 200 nm to 1100 nm. The emission spectrum contained the lines for Ca, Si, Fe, Ti, Mg, Na, K, Li, Al and C along with traces of Ba, Sr and Mn. The intensities of the observed spectral lines were corrected for self-absorption using the internal reference line. The excitation temperature was calculated using the Boltzmann plot method and the Stark broadened H-alpha line profile was used to determine the electron number density. A calibration-free technique with a fixed slope was used for the quantification of C and other elements and a laser-ablation time of flight LA-TOF-MS instrument was used to obtain mass spectra of the same samples. All the elements identified in the optical emission spectrum were also observed in the LA-TOF-MS mass spectrum. A CRM coal sample SARM 20 and a sample of the Pakistani Thar Coal were analysed. The values obtained for the CRM were in good agreement with the certified values. The second paper in this section to use LIBS was submitted by Yao et al.80 who investigated the LIBS spectral properties of coal with different volatile contents. Five coal samples with different amounts of volatile components were analysed and were compared with the same coal samples after heating at 900 °C for 7 minutes to produce char samples. The intensities of nearly all the emission lines were lower for the raw samples than those of the char samples. This indicated that a large amount of energy from the laser pulse is used in the pyrolysis process causing variation in the elemental results. This was improved by using the char samples which showed less variation.

Zhu et al.81 described an interesting new instrument for laser ablation single particle aerosol mass spectrometry for the direct analysis of raw coal samples. Particles were ablated from the surface of the solid material and these particles then entered the single particle aerosol mass spectrometry instrument for on-line simultaneous size and chemical composition analysis. The results were then processed by software to characterise the coal sample. The main components observed in the mass spectra of the samples included metallic and non-metallic elements, elemental carbon, organic carbon, and other compounds. The particles ablated from the five coal samples were divided into nine classes according to their primary chemical composition and were used as particle markers to characterise the coal samples. This approach avoided time-consuming chemical digestion procedures usually used for coal characterisation. Although the method has merit, further work on optimisation of the data analysis methodology is required to achieve the levels of accuracy required for its routine use.

Another interesting paper, by Husakova et al.82 described the determination of 11 elements in fly ash by orthogonal acceleration ICP-TOF-MS. This analysis is commonplace on conventional ICP-MS instruments, however the orthogonal acceleration ICP-TOF-MS instrument has some advantages over conventional quadrupole instruments. This includes its higher resolution which can be an advantage for resolving interferences observed in conventional ICP-MS instruments. The CRMs CTA-FFA-1 and NIST 1633b were used for validation of the method and were prepared using microwave extraction with NH4F. Eleven elements were determined: As, Be, Cs, Li, Ni, Rb, Sb, Se, Tl, U and W. All recoveries were within ± 10% of the certified values. The LOD values obtained were 150, 98, 2.1, 37, 314, 209, 31, 476, 1.6, 0.09 and 17 μg kg−1, respectively.

The final paper in this section is by Souza et al.83 who investigated petroleum coke sample preparation strategies for Ce and La determination using ICP-OES employing a desolvating nebuliser. Various digestion strategies were tested, however microwave induced combustion using 400 mg of coke, an oxygen pressure of 20 bar and the addition of 50 μL of 6 mol L−1 NH4NO3 with the final solution containing 2.5 mol L−1 HNO3 gave the best recoveries. The concentrations of Ce and La obtained in the final solutions were 0.65 ± 0.07 and 3.32 ± 0.08 μg g−1, respectively. These compared well with data obtained using NAA with agreement between the two being greater than 94%.

2.2.3 Oils – crude oil and lubricants. One review article containing 73 references from Sama et al.84 was of note in this section. It covered recent trends in elemental speciation of crude oils and heavy petroleum fractions. This article covers most techniques including GC-ICP-MS- and OES, LC-ICP-MS- and OES, TLC ICP-MS and GPC-ICP-MS and gives a reasonable overview of the current state of play of these techniques with regard to crude oils and their fractions. Another paper in this section was by Sanchez et al.85 who looked at the analysis of crude oil and heavy fractions using a high temperature torch integrated sample introduction system. The elemental analysis of heavy cuts is problematic because of their high viscosity and because they require large dilution factors to avoid nebuliser blocking and matrix effects that are commonly seen with conventional solvent dilution work. The authors described a method using a low inner volume spray chamber with a wall temperature set at 400 °C. This increased the analyte transport efficiency to virtually 100% regardless of sample matrix allowing universal calibration for all matrix types. The resulting sensitivity was an order of magnitude higher than that seen using a conventional spray chamber and quantitation limits were reduced by a factor of between 2 and 20 depending on the sample and element considered. The high transport efficiency, lower sample dilution and narrower peaks also allowed increases in sample throughput by a factor of 2.

A contribution by Vieira et al.86 described a method for the determination of Ca, Mg, Na and Sr using a nano-emulsion and ICP-OES analysis. The emulsion was prepared from 0.2 g of crude oil, 1.0 mL of HNO3, 0.6 mL of o-xylene and 0.80 g of Triton X-100 made up to 20 mL. This emulsion proved to be stable for 8 days. The accuracy of the procedure was evaluated through the analysis of standard reference materials NIST 1085b and NIST 1634c and by addition/recovery tests. The values obtained with this procedure were in accordance with the certified values for Ca, Mg and Na for both standard reference materials. Spike recoveries in crude oil were between 92.8 ± 3.8 and 102 ± 7.2% for all elements.

A novel paper by Ruhland et al.87 investigated the analysis of metal containing nanoparticles in gas condensates using asymmetric field flow fractionation coupled with ICP-MS/MS. Fractograms obtained indicated the presence of nanoparticles containing a number of elements including Al, As, Co, Fe, Hg, Mn, P, S, Ti and Zn. This work is very much in the development stage and identified the need for new field flow fractionation membranes that are more suitable for organic matrices. This is however a promising field for future work.

A paper by Fetter et al.88 described a sample preparation protocol for the accurate determination of radiogenic Pb and stable Zn isotopic compositions of crude oil. This protocol which can be used on sample sizes as low as 5 mL used liquid–liquid extraction into an aqueous phase followed by standard anion-exchange column chromatography to separate the elements of interest. The sample was split into two aliquots with 95% being used for multicollector-ICP-MS isotopic determinations while the other 5% was used for conventional ICP-MS quantitative measurements. Reproducibility was on a par with routine state-of-the-art Pb and Zn isotopic measurements for other types of geological materials and procedural blanks were negligible relative to the amounts of Pb and Zn typically separated from the crude oils.

Silva et al.89 undertook a study to show the feasibility of REE determinations in crude oils using ETV-ICP-MS. A citric acid modifier was used to produce calibrations using aqueous solutions and pyrolysis and vaporisation temperatures were 700 and 2200 °C, respectively. Since the REE have the affinity to form refractory compounds inside the electrothermal vaporiser, the use of a modifier gas (Freon R-12) at a flow of 3.0 mL min−1 was necessary for this analysis. The influence of sample quantity was evaluated, and accurate results were obtained even using a relatively high mass of crude oil (up to 18 mg). Accuracy was evaluated by comparison of these results with those obtained using ICP-MS with an ultrasonic nebulizer after a high pressure microwave assisted wet digestion and a microwave induced combustion procedure. No statistical difference was observed between the results. The limits of quantification for REE by ETV-ICP-MS were 0.02–0.8 ng g−1, which were lower than those obtained using the ultrasonic nebulizer ICP-MS technique (0.6–5.1 ng g−1). Negligible blank values and precision of better than 12% RSD show the feasibility of the proposed ETV-ICP-MS method for routine determination of REE in crude oils.

An interesting paper from Michel et al.90 described a portable XRF technique for the rapid identification of Deepwater Horizon oil residues. Oil residues are found on Gulf of Mexico beaches because of the Deepwater Horizon incident alongside oil residues from natural seepage and other anthropogenic sources. To identify the origin of oil residues found on the beaches it is critical to have techniques that can be used in the field and can provide rapid identification. In this technique no extraction steps were performed on the samples prior to analysis. A total of 595 sub-samples from 119 unique samples were used to train interpretable machine learning models to infer the presence or absence of Deepwater Horizon oil from the XRF data. Twenty five elements were used for the model which was able to determine with 95% accuracy if the sample was of Deepwater Horizon origin. This approach could be widely applied to different oil spills worldwide to aid oil spill identification.

2.2.4 Alternative fuels. The first contribution in this section is from Lourenco et al.91 who described a method based on reverse-phase dispersive liquid–liquid micro-extraction for the extraction and preconcentration of Ca K, Mg and Na in biodiesel samples. Flame spectrometry was used for analysis in the emission mode for K and Na and in absorption mode for Ca and Mg. The extraction/preconcentration step of the analysis was performed using a mixture of isopropanol and HNO3. The aqueous phase containing the analytes was separated by centrifugation. Parameters such as sample mass, volume of dispersant and extractant solutions, use of ultrasound, centrifugation time and temperature were evaluated. Analysis was performed using external calibration with aqueous reference solutions. The LOQ for Ca, K, Mg and Na was 0.05, 0.02, 0.08 and 0.04 μg kg−1, respectively. The accuracy was evaluated by recovery tests, which ranged from 93.9 to 108.1%, with a precision of better than 3% RSD for all analytes. The proposed method was then applied to five biodiesel samples produced from different raw materials. Compared with conventional sample preparation techniques this method was simple, low cost with low reagent consumption and provides LOQ values significantly below the limits required for these elements in biodiesel. A similar extraction method was proposed by da Silva et al.92 This method was developed for the determination of Ca, K, Mg and Na in biodiesel using AAS and was based on the extraction of the analytes into a ‘micro drop’ of an acid/alcohol extraction solution at the bottom of a conical tube. The best results were obtained with a sample mass of 3.0 g and 780 μL of 5.0% (v/v) HNO3/isopropyl alcohol at a ratio of 3[thin space (1/6-em)]:[thin space (1/6-em)]1. The efficiency of the sample preparation procedure was evaluated using a recovery test, with recoveries within 90.2–94.7% for all elements being obtained at a precision of better than 2%. The LOD were 32.3, 5.8, 4.3 and 3.0 μg kg−1 for Ca, K, Mg and Na, respectively.

A similar approach was also used by Vinhal et al.93 for the GFAAS determination of Cu, Ni, Pb and V in gasolines containing ethanol. This was an emulsion-breaking extraction method, again using HNO3 and a short chain alcohol. After breaking the bottom phase containing water, the dispersing agent and ethanol were analysed using GFAAS. Recovery tests were performed and produced analyte recoveries of between 87 and 116%. The LODs for this method were 0.7, 0.1, 0.8 and 1.6 μg L−1 for Cu, Ni, Pb and V, respectively.

An interesting method was proposed by Meira et al.94 who described the determination of Cd, Cr, Cu, Mn, Pb and V in ethanol fuels using XRF after magnetic solid phase extraction using CoFe2O4nanoparticles impregnated with 1-(2-pyridylazo)-naphthol. The extraction and preconcentration step was followed by direct determination of the analytes in the solid phase using EDXRF. The proposed method produced detection limits of: 0.013, 0.012, 0.012, 0.011, 0.016 and 0.009 mg L−1 for Cd, Cr, Cu, Mn, Pb and V, respectively. This method was then successfully applied to the extraction and determination of these analytes in ethanol fuel samples.

Barela et al.95 developed a method for microwave assisted ultraviolet light digestion of biodiesel and subsequent analysis by sector field ICP-MS. In this method a microwave with high pressure quartz vessels was used with ultraviolet radiation generated by a cadmium electrodeless discharge lamp working at 288 nm inside each quartz vessel. For the digestions, a sample size of 950 mg with 10 mL of 7 mol L−1 HNO3 was optimum resulting in 4740 mg L−1 of C in the final solutions. The reduction of the C content in the solutions to below 5000 mg L−1 was important to reduce possible polyatomic interferences. This method was suitable for the simultaneous determination of Ca, Co, Cr, Cu, Mn, Ni, Pb, Sr and V. Low resolution was used for all elements except Cr which required medium resolution to resolve the ArC interference seen at m/z 52. Detection limits for this method were below 1 ng g−1 for all elements except Cu, Mn and Ni which were 6.9, 4.8 and 2.8 ng g−1, respectively. This is an interesting method but somewhat expensive and time-consuming for commercial routine industrial analysis where simpler, quicker methods are available for these elements at these detection limits.

A paper utilizing sector field multi-collector ICP-MS was presented by Barela et al.95 This described a method for the direct lead isotopic analysis of bioethanol using multi-collector ICP-MS with a total consumption sample introduction system. In biodiesel samples, the determination of the total content of Pb is the normal analytical measurement made. However, isotopic analysis can give information on geographical provenance and type of raw material used for production. In this study isotopic reference materials for Pb (NIST SRM 981) and, to correct for mass bias, Tl (NIST SRM 997) were used. A high temperature torch integrated sample introduction system was also used, operating at 125 °C to minimise mass bias. The results showed a lighter Pb isotopic composition for the bioethanol samples than the NIST Pb standard but they are similar to those reported for wine and other alcoholic beverages coming from fermentation and distillation processes.

Two papers describing methods for the analysis of biomass were of note. The first, by Liu et al.,96 described combining polarizing filtered planar laser induced fluorescence with simultaneous laser absorption, quantitative LIBS and two colour pyrometry to analyse a burning biomass pellet. The K release during the combustion of biomass fuel pellets was investigated. The temporal release profiles of volatile atomic K and its compounds from a corn straw pellet showed a single peak, whereas woody biomass pellets produced a dual-maxima distribution. For both biomass types the highest concentrations of K occurred in the devolatilisation stage. The mass ratios between volatile atomic K and its compounds in corn straw and poplar were 0.77% and 0.79%, respectively. These values agree well with chemical equilibrium predictions that 0.68% of total K will be in atomic form. A two-step kinetic model of K release was developed which gave better predictions during the devolatilisation stage than the existing single-step model. Finally, a map of K transformation processes during combustion was developed.

The second biomass paper by Viljanen et al.97 described the real time release of Ca, K and Na during thermal conversion of biomass using quantitative microwave assisted LIBS. A new burner which allowed linear calibration of LIBS measurement for release studies during thermal conversion was developed. Many of these fuels contain high concentrations of alkali metals and chlorine which are harmful for boiler structures and may cause operational problems. Therefore, detailed quantitative information on release behaviour is required. The analytical performance of conventional LIBS measurement was significantly improved by introducing microwave radiation to the laser-induced plasma. An enhancement of linearity and a 60-fold improvement of LOD were observed with microwave-assisted LIBS compared with conventional LIBS. The LOD of Ca, K and Na were 16 ppb, 19 ppb and 10 ppb, respectively. In-flame microwave radiation-LIBS measurement was then applied to record time-traces of K, Na and Ca during thermal conversion of a poplar pellet.

2.3 Pharmaceuticals and personal care products

Spectrochemical elemental analysis has become a requirement for pharmaceuticals and the raw materials used for their production. This is to comply with regulations issued by the International Council for Harmonization of Technical Requirements for Registration of Pharmaceuticals for Human Use (ICH Q3D). There is a requirement to determine impurities to ever lower levels. A review containing 54 references of the research and development articles and scientific papers published since 2000 (ref. 98) focused on ICP-OES and ICP-MS analysis of pharmaceutical products. The review included aspects of sample preparation, potential interferences, different calibration approaches as well as their analytical performance and validation parameters. The coupled technique of LC-ICP-MS has become an extremely useful tool for elemental speciation. A review focusing on the analytical performance in organic matrices and the effect interfaces have on factors such as efficiency, resolution, sensitivity and extra-column solute dispersion was published recently.99 For this purpose, 55 published studies were evaluated. Interfaces in the form of the sample introduction systems (nebuliser and spray chamber) and a flow-splitter to reduce the organic solvent load are most common. However, their effect on peak broadening during the initial separation has often not been addressed. An excellent graphical representation was given, highlighting that extra-column variance introduced by the interface can significantly affect the separation by reducing the available number of plates and therefore the method’s performance in terms of resolution and sensitivity. A second review highlighted that ICP-MS has become a valuable detection method when coupled to separation techniques such as (U) HPLC.100 Coupling methods and quantifying approaches for the detection of, for example, Br, Cl, I, P, S and Se in non-metal drugs were reviewed (149 references). In addition, the authors stressed the need for derivatisation when an ICP-MS detectable hetero-element is missing. This can be achieved by derivatising –OH, –COOH, –SH or –NH2 functional groups.

Sample preparation remains a vital aspect of any analytical approach and recent publications have focused on its optimisation. An ultrasonic assisted micro-extraction of Cd and Pb in lipsticks and eye shadow utilising deep eutectic solvent was developed.101 This approach is more favourable compared with the use of other ionic liquid solvents as they are biodegradable, biocompatible as well as non-toxic. An extensive multivariate approach (Plackett–Burman design) enabled the authors to show that the main factors affecting the extraction were time, volume of deep eutectic solvent and pH. Both Cd and Pb were complexed with ammonium pyrrolidine dithiocarbamate. Compared with other studies, the designed approach performed well, but LODs were amongst the higher ones reported. Results of multi-level spike studies further demonstrated excellent performance of this method with reported recoveries of 96.6–98.4% for Cd and 97.0–98.7% for Pb. Similarly, Koosha et al.102 developed a Cd extraction and preconcentration procedure following an extensive multivariate approach. Factors such as pH, concentration of complexing agent, volume of solvent, number of injections and time were assessed using a Plackett–Burman design. The optimisation of these factors was achieved following a Box–Behnken design and resulted in the following optimal parameters: complexing agent was 0.00155 mol L−1 1-nitroso-2-naphthol, extraction solvent was 130 μL of octanol, an ionic strength of 2 mol L−1 NaCl and a pH of 6.5. A linear range of 2.5–650 μg L−1 (R2 0.997) was achieved as well as a limit of detection of 0.68 μg L−1. Excellent intra-day and inter-day precision of <2% were demonstrated. Applying the developed procedure to water, pharmaceutical materials and a certified reference sample showed spike (n = 3) recoveries of 96.8–102.7%, highlighting the excellent accuracy and precision of the extraction. In addition, it was a highly specific approach as no interferences were observed for the 18 ions investigated.

Generally, sample preparation for traditional ICP-OES approaches is very labour intensive and can involve the use of strong acids such as HF, which is a serious safety concern and is often avoided by laboratories completely. Speranca et al.103 reported a method of sample preparation that involved using polyvinyl alcohol to convert sunscreen sample into a solid. The obtained thin sample disc was analysed using LIBS to determine the Ti concentration. The LIBS spectra obtained were normalised and standardised utilising instrumental software. Results obtained using a digestion followed by ICP-OES detection were in agreement with LIBS results when applying a multi linear regression multivariate calibration. However, no actual spike studies were performed. This would be beneficial in future studies to assess the method’s accuracy. Currently, a labour-intensive and time-consuming ICP-OES preparation is used as a reference method. However, the recovery of the digestion has not been investigated and is likely to be affected by the multistep process. This work reported a promising alternative with simplified sample preparation helping to avoid the use of strong acids.

A different sample preparation approach utilised a sequential co-precipitation scheme. This was based on Mg(OH)2 and CaF2 precipitation for detection of Cd in multivitamin/mineral supplements utilising an isotope dilution (ID) – ICP-MS method.104 The authors aimed to remove matrix interference (Mo and spiked Sn) from the supplements. Best results were achieved following a three-step co-precipitation approach. Interfering Ca was first precipitated in the form of CaF2 after the addition of hydrofluoric acid, which also resulted in significant Mo and Sn co-precipitating. Addition of triethylamine to the supernatant further reduced Mo and Sn levels. After further addition of triethylamine 99.7% of Mo and 96.5% of Sn were successfully removed from the sample solution. In addition, this approach also removed salts (Ca, Cu, Fe, K, Mg, Mn, P and Zn) commonly found in the supplement matrix. This is beneficial as it helps to avoid matrix suppression effects as well as preventing salt build up in the ICP-MS components. Applying the developed procedure to CRMs showed excellent recoveries (ranging from 95.6 to 98.5%) for all three Cd isotopes assessed. In addition, it was demonstrated that 99.6 and 97.7% of Mo and Sn, respectively were removed from the supplement CRM. One drawback of this method is the safety concern arising from the use of HF. However, for experienced, well trained analysts this should not present any difficulties.

Ansar et al.105 developed a capillary electrophoresis (CE)-ICP-MS/MS method for the detection of S (external and intra-liposomal) in doxorubicin HCL liposomal formulations, which are used in the treatment of leukaemia and various cancers. These liposomes encapsulate doxorubicin and promote targeted drug delivery as well as reducing negative side effects. The CE was utilised to separate external and intra-liposomal S which was achieved within 8 min. Traditional detection methods, such as UV/vis spectrometry and conductivity measurements rely on the disintegration of the liposomes in order to measure intracellular S. This step becomes obsolete with the developed ICP method as the plasma itself disintegrates the liposomes. Utilising a triple quadrupole ICP-MS instrument, the interfering oxygen dimer at m/z 32 can be avoided as the mass transition of 32S+ to 32S16O+ was achieved utilising O2 as the reaction gas. Other figures of merit include a calibration range of 3–600 μg mL−1, spike recovery of 95–102%, a LOD of 0.8 μg mL−1, LOQ of 2.6 μg mL−1 and inter- and intra-day precision at 3.2–4.4% and 1.9–5.8%, respectively.

Mercury remains an important contaminant monitored within pharmaceutical formulations. The determination of thimerosal and inorganic Hg in vaccines utilising Fe3+-induced degradation with cold vapour atomic fluorescence spectrometry (CV-AFS) detection was reported by Xu et al.106 Ferric iron has an induction effect on the vaporisation of organic Hg and was introduced into both sample and carrier stream. Inorganic Hg was determined in the presence of potassium borohydride and the concentration of thimerosal was calculated by subtraction of inorganic Hg concentration from the total detected amount of Hg. The presence of Fe3+ increased the fluorescence signal of thimerosal at concentrations of up to 10 mg L−1, while not affecting the fluorescence signal of inorganic Hg. The developed method was applied to the analysis of rabies and hepatitis-B vaccines that had been spiked (n = 3) with total Hg and thimerosal at three different levels, each. Excellent spike recoveries of 96.0–103% and 97.5–103% were obtained for inorganic Hg and thimerosal, respectively.

In recent years, the use of e-cigarettes has increased considerably. Hence, there is a need to ensure they are safe to use and meet regulatory requirements. Utilising gallium as an internal standard, Kamilari et al.107 analysed e-cigarette liquids and their individual components for the presence of heavy metals (As, Cd, Cr, Cu, Ni and Pb). In contrast to a more traditional ICP based approach, the authors utilised total reflection XRF for the analysis. Results showed some individual components exceeding the regulatory limits for Cd and Cr. However, considering the dilution of these within the final product, the levels were judged to be acceptable. It was noted that no method validation data were available, which would be beneficial to illustrate the analytical performance of this method. In addition, it would have supported the method’s performance claims to compare results with those obtained using other analytical methods.

In common with last year’s review, the manipulation and processing of large amounts of data has been the focus of a number of studies. Some spectroscopy techniques, e.g. LIBS, are favourable because of their quasi-non-destructive nature and the speed of analysis. However, due to the large amount of data created, the interpretation requires time and expertise. A curve fitting regression model used in combination with WDXRF was utilised for the detection of Cd, Ni and Pb in seven pharmaceutical powders.108 The authors compared this methodology with results obtained by applying ordinary least squares regression and partial least square approaches. Performance in terms of correlation (R2) and root mean square error (RMSE), which represents the average distribution scatter, was assessed. In 86% of data sets, curve fitting regression produced statistically smaller RMSE compared with the other two methodologies when calculated on a validation data set. The overall absolute error achieved was 3–5 ppm, which does not meet the needs of pharmaceutical applications. Nonetheless, it is a promising WDXRF quantification method for less demanding applications. In addition, it could further enhance the performance of more efficient XRF systems such as total reflection XRF. It has been shown that analytical performance could be enhanced when using a multiple spectral line correction approach for the determination of Bi in different medicines utilising microwave induced plasma optical emission spectrometry (MIP-OES).109 By summing the intensities of multiple Bi lines (223.061 and 306.772 nm) for both calibration standards and samples, it was possible to improve the analytical performance. The LODs reported were ∼10 times lower compared with a more traditional direct analysis approach. In addition, the results were compared with a hydride generation method as well as a standard addition approach. Performance was comparable to that of hydride generation, without the need for time-consuming sample preparation. This is a promising technique for faster analysis with enhanced performance. However, it needs to be assessed for specific cases if lower specificity can be accepted for faster and more cost-effective analysis.

The suitability of Machine learning has been evaluated in analytical chemistry. In an effort to decrease sample preparation time, Parhizakar et al.110 assessed the suitability of attenuated total reflectance infrared (ATR-IR) spectroscopy in combination with partial least square – least square support vector machine modelling for the determination of Fe in ferrous syrups and drops. The spectra were baseline corrected (standard normal variate method). For this purpose, 158 samples were used to calibrate the model to then allow the analysis of 40 test specimens. In addition, Fe concentrations were obtained utilising AAS. This resulted in a multivariate model of spectral data obtained with both methods, allowing the prediction of Fe content utilising the developed model. The authors addressed the potential of over-training, which can be an issue for machine learning methods. Excellent correlation was observed for both calibration and cross-validation samples with R2 values of 0.99 and 0.98, respectively. Since pharmaceutical preparations need to abide by strict regulations, it remains questionable if machine learning methods can fulfil the required precision and accuracy of more traditional methods. Nevertheless, it could prove to be useful, for example, to identify potential counterfeit preparations.

This approach to counterfeit identification has been investigated, for example, utilising EDXRF in combination with principal component analysis (PCA) and Soft Independent Modelling of Class Analogies (SIMCA).111 The XRF spectra (scanning Na to U) were obtained for Plavix tablets, an anti-platelet medication. Reference samples were available from registered manufacturers or purchased in pharmacies. In order to account for normal variation two of the reference samples were generic samples containing the same active ingredient, but a different salt. Utilising the data obtained using EDXRF scans, PCA was able to visualise the similarities and differences between these reference samples and 10 suspected counterfeit samples. Both PCA on its own and when utilised with SIMCA enabled the authors to distinguish counterfeit samples from authentic samples allowing for fast screening of suspect samples. In addition, other analytical methods (HPLC) were applied to confirm the authenticity of one of the suspect samples. However, it was noted that the validated SIMCA model was no more capable of distinguishing samples than the simpler PCA. In fact, PCA was able to show clearer discrimination between the counterfeit samples compared with SIMCA.

2.4 Organic materials: cultural heritage applications

A recent review assessing the work published over 20 years and citing 125 references, focused on the use of portable and laboratory-based instruments for the analysis of mediaeval wall paintings.112 The authors pointed out that the work published in more recent years has focused on identifying degradation processes in an effort to aid preservation and restoration. Multi-technique approaches have been proven to yield the most information. Techniques that have been utilised were, for example, XRF, UV/vis, FT-IR and Raman spectroscopy as well as SEM-EDS, MS and GC-MS. When sample preservation was not crucial, LIBS has proven useful for elemental characterisation. It should be noted though that the damage inflicted using LIBS can be minimal. A second review (84 references)113 highlighted the increasing use of synchrotron X-ray nano-probes in cultural heritage studies. Utilising nano-X-ray fluorescence, nano-X-ray diffraction and nano-X-ray absorption spectroscopy, it is possible to obtain insights into elemental composition, crystalline structure and speciation, respectively. The challenges that remain are the focusing of the beam, the sample preparation as well as data acquisition, analysis and interpretation.

The potential of X-ray luminescence for cultural heritage applications has been investigated by analysing samples of various shapes and dimension.114 Initial tests with laboratory-based equipment showed results comparable to those obtained utilising cathodoluminescence and ion-beam-induced luminescence. This justified further optimisation with the aim of establishing a portable set up. For this purpose, a lead collimator, which narrows the X-rays from a tungsten anode to a spot, was utilised. The generated light was passed through a collecting lens and further transported to the spectrometer (250–630 nm) via an optical fibre. To avoid scatter X-rays, lead shielding was employed. In addition, a camera was utilised to evaluate the area under study. The collection lens was vital to obtain maximised signal and enable luminescence signals for a portable device which was based on a typical XRF set up. The developed device recorded luminescence spectra with an integration time of three minutes. This allowed the discrimination of lapis lazuli samples and aided provenance studies.

A hybrid system was developed for the analysis of heritage stones and model wall paintings that utilised pulsed laser excitation Raman, laser-induced fluorescence (LIF) and laser-induced breakdown spectroscopy signals.115 For this purpose a nanosecond Q-switched Nd:YAG laser and a spectrograph were utilised. The spectrograph was coupled with a time-gated intensified charge coupled device which enabled detection with temporal resolution. Raman and LIF spectra were obtained simultaneously, whereas after a changeover of approximately 2 minutes LIBS could be used. It took about 10 minutes to change to different excitation wavelength utilised in this work (532, 355, and 266 nm). The Raman results enabled the differentiation of sulfate-based stones from those made of carbonate, whereas LIF provided information with regards to the nature of the organic residues. Moreover, the time-resolved LIF signals provided information of fluorescence origin, which can help to identify organic and inorganic emitters in both matrices studied. The combined results obtained for the model wall painting analysed by the hybrid system allowed identification of the pigment as red vermillion (HgS).

In common with other fields, data manipulation and interpretation remains a most vital step in the analysis of cultural heritage samples. Cheung116 reported a three-step pre-processing scheme for plume laser induced fluorescence, a minimally destructive multi-element analysis technique the data from which may be used for chemometric sorting. It was possible to reduce the single-shot uncertainty from 54% down to only 6.5% by rejecting dim featureless parts of the spectra as outliers (dimmest 5–10% of captured spectra), as well as subtracting the baseline. Finally, taking advantage of the linearity of fluorescence, the spectral areas were normalised. The developed scheme was applied to pre-process red seal inks and Chinese black inks which were consequently sorted using PCA. Applying this methodology, clean sorting was achieved even when using single-shot spectra.

The development of a reliable and fast classification of LIBS spectra based on various computational intelligence models was reported.117 The aim was to simplify the current labour-intense process of LIBS data interpretation. Fifty ink samples were applied to 50 paper samples. Then LIBS spectra (185–904 nm) were collected utilising a Q-switched Quantel Ultra Nd:YAG laser working at a wavelength of 1064 nm and a 6 channel spectrometer equipped with a charge coupled device detector. Initial visual inspections after PCA allowed differentiation of the various papers used. However, the identification of inks proved to be more challenging. Hence, seven different computational intelligence algorithms, as well as pre-processing of the obtained spectra, were assessed for their ability to separate paper-ink samples. Best results were achieved utilising the random forest method achieving an accuracy, sensitivity, and specificity of 99.1, 86.3 and 99.5%, respectively. The methodology could provide useful information for both cultural heritage and forensic applications from an identification point of view (Table 2).

Table 2 Applications of atomic spectroscopy of organic materials
Analyte Matrix Technique Comments Ref.
As, Ba, Cd, Cr, Pb Commercial fertilisers MIP-OES Microwave assisted digestion of samples. “Multi-energy calibration” used for elemental determination. Digested sample split in two. One aliquot mixed 1[thin space (1/6-em)]:[thin space (1/6-em)]1 with a standard and the other mixed 1[thin space (1/6-em)]:[thin space (1/6-em)]1 with a blank. Multiple wavelengths used for determination. Full description was given. Agreement with certified values for the CRM NIST 695 was between 96 and 101%. Spikes yielded recoveries of 92–105%. Comparison with external calibration and standard additions made, with developed method being far superior for some elements 118
Dinitrotoluene (DNT) isomers Condensed phase LIMS followed by LIBS Direct analysis of ground and pelletised powder samples of three DNT isomers. Samples were irradiated at 266 nm and the optical emission (300–900 nm) passed to a CCD containing spectrograph via optical fibre. Initial laser shot (energy below ablation threshold) allowed collection of mass spectra. Second laser shot of higher energy at the same location enabled associated LIBS spectra. Combined approach allowed differentiation of three DNT isomers following processing by discriminant function analysis 119
Various (12) Drugs HR-CS AAS Time and wavelength-resolved screening test following acid digestion enabled pass/fail approach for elements detected at levels above LOD. The LODs reported were lower than permitted concentration as per guideline for elemental impurities in drugs. If any of the elements were detected they could be quantified separately. Method validation was performed. In drugs analysed Cr, Cu and Ni resulted in fails. However, once quantified levels were below permitted concentration 120
Various Painting Exit from the Theatre Synchrotron macro XRF High energy synchrotron scans were performed at 12.9 keV and 38.5 keV. This enabled visualisation of new As, Cd, Cu, Sb, and Sb details in an underlying landscape 121
Various Wall paintings External reflection FTIR, sequentially shifted Raman spectroscopy and XRF Analysis performed directly on wall paintings; multi-analytical non-invasive approach allowing both mineralogical and chemical analysis of pigments. Main pigments identified were calcite, cinnabar, red and yellow ochre, green earths, Egyptian blue and carbon black 122
Al, Ba, Ca, Co, Cu, Cr, Fe, K, P, Rb, S, Si, Sr, Ti, Zn Painting model samples LIBS, XRF Depth resolved analysis of created model paintings. Unusual for cultural heritage field to use LIBS because of its partially destructive nature. However, LIBS (Nd:YAG laser 266 nm) used to distinguish layers of different composition and to estimate their thickness as well as chemical composition. Results obtained by XRF analysis were comparable to those obtained utilising LIBS 123
Multiple (scan 350–850 nm) Paper Laser-induced fluorescence spectroscopy Direct analysis of paper samples which enabled determination of the paper’s age based on changes of the first derivative of the spectral peak at 443 nm (exponential curve R2 = 0.99). Classification of paper samples was achieved through principal component analysis and k-means clustering algorithm 124
Multiple Pigments on gypsum ground, glazed ceramic, Roman coin LIBS, XRF and PIXE Comparative analysis of different matrices to establish best suited technique. Once difference in sample area and thickness was taken into account results obtained for various techniques agreed well. LIBS showed superior sensitivity, but its destructive nature needs to be considered 63
Relative intensity Al/O Aluminised 2,4,6-trinitrotoluene LIBS (in air and argon atmosphere) For the LIBS analysis a Nd:YAG laser at 1064 nm and with a 7 ns pulse duration was employed. Plasma emissions were recorded and principal component analysis was applied to differentiate samples. A calibration curve utilising relative intensities of Al/O enabled determination of detonation velocity and pressure as well as Al content in aluminised TNT 125


2.5 Polymers and composites

There is no doubt that the most extensively researched analytical topic for polymers is LIBS classification. As well as numerous applications, a review article by Liu et al.126 has also been presented. The review, containing 82 references, covered the instruments that have been used for plastic analysis, methods of discrimination between different plastic types, the qualitative and quantitative analysis of plastics and other applications. Also discussed were the calibration protocols used (including calibration-free LIBS) and the chemometric algorithms used to help classification of different plastic types. The last section discussed the use of LIBS for the analysis of plastic toys, food containers and e-waste. The authors finished off by proposing potential future applications and areas of research.

In addition to the review discussed above, numerous applications of the LIBS analysis of plastics for sorting or classification purposes have also been described. Many of them have the same format, i.e. the LIBS spectra of assorted plastics are used to train an algorithm and then the algorithm is used to identify the plastic type of ‘unknown’ samples. Included in this type of paper is one by Liu et al.127 that described differentiation between 11 plastic types. There were 20 samples of each plastic type and each sample was analysed at 10 different places to minimise any effects of laser pulse energy on the spectra produced. The spectra produced were interrogated using several algorithms including random forest, random forest with Variable Importance, Partial Least Squares Discrimination Analysis (PLSDA) and Partial Least Squares Discrimination Analysis with Variable Importance (PLSDAVI). A brief description of each was given to aid a new worker in the field. This included a helpful schematic diagram for the PLSDAVI. Of the 2200 spectra collected (11 × 20 × 10), 1980 were used for training the models and 220 were treated as unknowns. All of the algorithms had a high success rate of correct classification, with the variable importance versions being even more successful than those not using it. The most successful algorithm was VI followed by PLSDA which had a success rate of 99.55%. An added bonus was that it also had the shortest classification time (0.096 ms). Other good examples of this type of paper are two by the same research group.128,129 These papers used the C–N line at 388.3 nm and the atom lines of C (247.86 nm), H (656.3 nm) and O (777.3 nm) and the unsupervised learning algorithm k-means and cluster analysis to differentiate 20 industrial polymers. In the paper by Tang et al.,129 self-organising maps (a type of artificial neural network) was also used. When self-organising maps alone was used, only 18 of the 20 plastics could be differentiated; with polycarbonate and polystyrene being problematic. When k-means was used as well, the success rate was 99.2%. It was also in excess of 99% in the paper by Guo et al.128 Jull et al.130 used LIBS followed by k-nearest neighbour and Soft Independent Modelling by Class Analogy (SIMCA) to analyse several types of recyclable materials. These included brown, green and clear glass, aluminium, tin and the polymers polyethylene terephthalate (PET), high density polyethylene and the bioplastics Novatein and polylactic acid. Although the glass types could not be distinguished, the biopolymers could easily be separated from the other polymers. The k-nearest neighbour algorithm provided better classification than SIMCA. Similar results were obtained when the range of the LIBS spectra was decreased from 182.26–908.07 nm to 313.20–495.12 nm. Another example was by Roh et al.131 who used LIBS along with PCA and Independent Component Analysis, Fuzzy C-means, Fuzzy C-means clustering algorithm and Radial Basis Function Neural Networks Classifier to classify black plastics. Black plastics can be extra-problematic to classify because the usual technique of IR cannot be used. Again, a brief description was given of how each of the algorithms works. The black plastics polypropylene, polystyrene and acrylonitrile butadiene styrene were classified according to their resin type with a maximum success rate of 95.83%. A further paper, by Kim and Choi132 used the C/H line intensity ratio, the presence of the C–C delocalised bonds, and any signal from a heteroatom to distinguish between the black plastics polypropylene, acrylonitrile butadiene styrene, PET and polystyrene. The PET was easily identifiable because of the strong O peak at 777.2 nm, but the other plastics could also be identified through the other measurands. The final paper in this sub-section was presented by Dastjerdi et al.133 who used LIBS combined with the Support Vector Machine model to separate polyvinyl chloride (PVC) from other polymers. Again, the basic principles of the algorithm were given along with schematic diagrams of the LIBS setup and the automated sorting system. Although not infallible, the method did manage a successful differentiation 90.5% of the time. The authors concluded that the combination of LIBS and Support Vector Machine had great potential for such a differentiation.

Techniques other than LIBS have also been used to distinguish between different polymer types. Two papers by Madiona et al. used TOF-SIMS followed by multivariate analysis techniques to distinguish between similar polyamide materials134 and between PET, PTFE polymethyl methacrylate and low density polyethylene.135 In recent years TOF-SIMS has advanced significantly with the most recent instruments having far greater capability and resolution compared with previous versions. The higher resolution leads to a larger dataset and therefore algorithms have been used to reduce these to a more manageable level. In the first example,134 self-organising maps and PCA were used to differentiate between seven polyamide samples (types of nylon). The PCA separated a few sample types, but failed to differentiate between all of them. However, following ‘up-binning’ (where more data is inserted through higher spectral resolution) both supervised and unsupervised training of the self-organising maps led to successful differentiation (98% and 99%, respectively). The successful differentiation was true for both positive and negative ion modes during the TOF-SIMS analysis when spectra covering the mass range 1–500 m/z. The other application135 was very similar, but with data within the spectral range 1–300 m/z used at an interval of 0.01 m/z, i.e. 30[thin space (1/6-em)]000 equal segments. This ‘up-binning’ enabled decreased user intervention, removal of bias and provided a larger dataset so that all features within a mass range can be taken into account. The authors concluded that their approach held a great deal of potential in the field of materials and biomaterials analysis.

Several other applications of the analysis of polymers have been produced during this review period. This has included a LA-ICP-MS and LA-ICP-OES method utilising a novel calibration approach.136 The paper, by Villasenor et al., reported the determination of Al, As, Ca, Cr, Hg, Mg, Si, Ti and Zn in the polymers polyethylene and polypropylene. The calibration method was entitled ‘dried droplet calibration approach’ and involved a small volume (at the μL range) of an aqueous standard being placed on the polymer surface and then dried prior to LA sample introduction. The concentrations of the analytes in the samples were obtained by extrapolation of the calibration curves. The method reportedly overcame matrix effects that are a known problem for LA sample introduction because the sample and the added standard were ablated simultaneously and hence the generated aerosols reached the plasma at the same time. Accuracy of the method was demonstrated through the analysis of three CRMs. In general, good agreement between experimental results and the certified values was obtained. The exceptions were for elements that are very volatile, e.g. As and Hg or those that are present at very low concentration, e.g. Ti. These analytes showed significant deviation from the certified values.

Three papers have described the determination of silicone materials.137–139 In the first example, Vogel et al. coupled size exclusion chromatography (SEC) with ICP-OES to obtain speciation information of polydimethylsiloxanes in volatile and non-volatile solvents. The SEC enabled separation of silicones over the mass range 311–186[thin space (1/6-em)]000 Da and the ICP-OES gave good sensitivity detection with LOD being below mg L−1. The average precision was 5.5% RSD. The second paper was presented by Ledesma et al.138 who reported the determination of silicone material contaminants on epoxy composites. The surface analysis techniques of XPS and LIBS were used with data from the two being compared with respect to their reliability. The advantages of LIBS over XPS in terms of speed, lack of necessity for sample preparation, real-time results and ease of use were all highlighted. The Si concentrations determined showed an excellent correlation between the two techniques. The paper by Chen et al.139 used LIBS to evaluate the tracking and erosion test performance of materials. The normal test, termed the inclined plane is very time-consuming and the LİBS test was significantly faster. Twenty seven materials were tested with either the aluminium hydroxide or the silica in the fillers being the target analytes. Thermogravimetry was also undertaken on the materials. Full experimental details of all three tests were given including a schematic diagram of the LIBS system. The LIBS spectra were complex and, although some Al lines, e.g. 308.2 nm, could clearly be identified, further assistance was required to obtain more information. The authors therefore used PCA and a neural network algorithm. The PCA could distinguish between several of the sample types but not all. The neural Networks algorithm used after the PCA enabled distinction between the rest.

Laser ablation along with other techniques has been used for polymer analysis. Bezemer et al.140 used LA-ICP-MS, XRF and IRMS to obtain analytical data from the plastic caps of flash bangers and then used PCA on the data to classify them. A total of 202 samples were tested by LA-ICP-MS and 53 elements screened for. For blue caps, only 13 analytes were present in all samples and a further 26 analytes were present in at least one sample. The white caps had fewer elements and those that were present were at lower concentration. Only 89 samples were analysed using XRF. Since it has far lower sensitivity, it was less useful. However, it did analyse the whole of the cap rather than a small spot and therefore did not suffer potential inhomogeneity problems experienced by LA-ICP-MS. For those analytes that could be detected using both techniques (Ca, Cr, Cu, Mg, S and Si) correlation between the two was very good. The XRF analysis of post-explosion caps was not straightforward because the samples were no longer flat and were also contaminated by residues of the explosive powder. The PCA analysis of the LA-ICP-MS data identified seven classes of blue cap and three classes of white cap. Isotope ratio measurements of C and H gave further discrimination. It was concluded that the protocol could easily be applied to forensic samples. Another example of LA-ICP-MS this time in tandem with LİBS was presented by Bonta and Limbeck.141 Under normal circumstances, both techniques suffer matrix effects and often require matrix matched standards for calibration. The techniques used in tandem, i.e. data obtained using both instruments from one laser shot, actually overcomes these problems. A full description of the system was supplied including the sample preparation procedure which involved the samples being spin coated as a layer on a high purity silicon wafer. The LIBS was capable of determining alkali and alkaline earth elements and LA-ICP-MS was used to determine other elements at the μg g−1 range. Analytical data from the combined techniques were input to PCA. The protocol was applied to three plastic types (polymethyl methacrylate, polyimide and polyvinylpyrrolidine) totalling 23 samples. The PCA could easily differentiate between the three polymer types. Future work would involve the analysis of more polymer types and to investigate the possibility of depth-profile measurements.

Two papers have claimed novel instrumentation for the analysis of polymers.142,143 The paper by Pardede et al.143 utilised a novel double pulse LİBS system to determine Cl, F and H in PTFE and PVC. Normally, halogens show very poor sensitivity during LİBS analysis. However, using two lasers firing at an aluminium target in a helium atmosphere produced a helium plasma that was capable of exciting the analytes in the samples. One of the lasers was a nanosecond Nd:YAG operating at 54 mJ and the other a picosecond Nd:YAG laser operating at 2 mJ. Both lasers operated at their fundamental wavelength. Full details of the setup were provided. The system was also applied to the determination of H and D in a zircaloy sample. The authors proposed a mechanism by which the excitation occurred. The other proof of principle paper142 described the use of a compact near edge X-ray fine structure (NEXAFS) microscope to form an elemental map on a 30 × 30 μm2 piece of PET. The paper described in detail the source, the system, the spectral measurements and the results, with a useful schematic diagram of the instrument also being provided. Briefly, in the proposed system spatially localised spectra are taken using a broad band soft X-ray source and the overall image is obtained by rastor scanning. Using conventional synchrotron sources, the image is obtained from a series of full field images taken at different energies.

Several more straightforward applications have been published. This includes one by Devouge-Boyer et al.144 who described the determination of Cu, K and I in polyamide samples. The analysis is necessary because excess I can lead to corrosion of the electronic components in the automotive industry. Sample (0.200 g) was cut into small pieces and placed in a microwave bomb. Nitric acid (5 mL) was added and the bomb heated using microwave irradiation to 150 °C and maintained at that temperature for 30 min. After cooling, the digests were transferred to polypropylene flasks and diluted to 50 mL using ultrapure water. The acid digest could then be analysed using ICP-OES for the Cu and K content. The I was determined using ICP-MS following dilution of 1 mL of the acid digest with 24 mL of 0.5% ammonia solution (to decrease memory effects). Unfortunately, no CRM was used to validate the method. However, a spike of 50 mg kg−1 I yielded a recovery of 100 ± 0.8%. The LOD was calculated to be 150 ng L−1 for ICP-MS correlating to 0.9 mg kg−1 in the solid material. A microwave assisted alkaline extraction using ammonia or TMAH yielded results approximately 10% lower than the acid extraction. Analysis of the plastics yielded I concentrations from below LOD to 1000 mg kg−1 with a precision of between 2.2 and 4.5% RSD. A total of 18 analytes were determined in high purity polyimide materials using either ICP-OES or ICP-MS detection.145 Santos et al. used a microwave induced combustion on a sample size of 600 mg to bring the analytes into a more readily analysed form. A range of absorbing solutions was tested with a mixture of 4 mol L−1 HCl and 3 mol L−1 nitric acid providing full recovery for all analytes except Cr, whereas water yielded no better than 65% recovery and nitric acid improving recovery of only some of the analytes. The sample powder had to be mixed with ammonium chloride volatilisation aid for complete recovery of Cr. Method validation was achieved through the analysis of the CRM EC 680K – low density polyethylene. Analytical data obtained were in good agreement with certified values (better than 94% and with a t-test indicating that there was no significant difference). Detection limits were at the ng g−1 range. A paper by Lazic et al. described the LIBS and portable XRF determination of Sb in some widely used plastic objects.146 The portable XRF instrument operating in the low-density plastics mode was used to give reference Sb values for the LIBS determinations and to provide an indication of the concentrations of some other, potentially interfering elements. Initially, the LIBS was tested on high purity antimony in order to identify the most prominent wavelengths. Unfortunately, the most prominent lines occurred in the UV region and were interfered with by Fe, Si and Ti. Weaker ionic lines occurred in the visible region. Despite there being a weak Fe interference, the Sb wavelength at 276.99 nm was used for all measurements. The authors provided details of how the Fe signal was subtracted from the total signal yielding a reliable Sb measurement. Samples including luggage tags, light bulb fittings, Christmas decorations and numerous others were analysed giving Sb concentrations between the LOD (approximately 1400 mg kg−1) up to over 65[thin space (1/6-em)]000 mg kg−1. A full experimental description was provided along with schematic diagrams of the LIBS setup.

3 Inorganic chemicals and materials

In a continuation of the previous year’s review, papers detailing the development, or interesting application, of atomic spectrometry have been grouped into the following topic areas; inorganic chemicals, building materials, catalysts and forensic analysis. A lack of papers covering the analysis of fertilizers sees this topic removed from this year’s review.

3.1 Inorganic chemicals

This review period has seen an eclectic assortment of matrix types from aluminium smelt cells to inorganic supplements, examples of which are included in Table 3. Dos Santos et al.147 reported the use of ICP-OES for the determination of phosphine gas released from aluminium phosphide fumigants. The proposed procedure comprised the passing of moist air over the sample and collecting the released gas in a bubbler containing acidified potassium permanganate to convert phosphine to soluble phosphate. The resulting solutions were diluted and the P determined using ICP-OES at the P 213.618 nm analytical line. Ten commercial samples of fumigants were analysed with good agreement with the more laborious molybdenum complexation spectrophotometry method.
Table 3 Applications of atomic spectrometry to the analysis of inorganic materials
Analytes Matrix Technique Comments Ref.
Al, Ca, F, Mg, Na Aluminium smelt cells WD XRF A high accuracy XRF method as an alternative to XRD for calculation of cryolite ratio in smelt bath samples. Samples were ground and pressed to pellets with cellulose prior to analysis 150
As, Cd Multi-vitamin/mineral supplements ICP-MS A three step sequential coprecipitation of As and Cd using TEA and HF–NH4OH for the removal of high salt interferences such as Ca, K, Mg, Na together with other interferences from Mo, Mn and Sn 151
F, K, O, P F doped potassium titanyl phosphate crystals GD-TOF-MS Combined instrumental and mathematical corrections for the interferences of 38Ar2+ and 1H316O+ on 19F+ 152
K Biochar fertilizer LIBS Addition of Li2CO3 to increase the electron density of the plasma and increase the emission intensity of analyte 153


Confirmation of the quality of high purity solvents is critical for both analytical and industrial applications such as semiconductor production. To that end, an electrolyte cathode discharge atomic emission spectrometry method was reported for the direct determination of metallic impurities in high purity NH4OH, H2O2 and H2SO4.148 The system consisted of a tungsten anode wire, glass capillary tube for flowing the cathode solution and an atomic emission spectrometer with a Czerny–Turner Grating monochromator. The optimised operating parameters included a 2 mm inter-electrode gap with a 770 V, 56 mA discharge. The system was capable of determining Ag, Ca, Cd, Cu, Fe, Mg, Mn, Pb and Zn with detection limits ranging between 2 and 52 ng mL−1. Results for all materials were comparable to those obtained using GFAAS and ICP-MS methods. A detailed description of the optimisation of ICP-MS/MS for the determination of non-metallic impurities in ultrapure TMAH was produced by Fu et al.149 The report details the selection, advantages and optimisation of mass shift reaction with O2 and H2 for interference removal on each analyte, As, B, Cl, P, S, Se and Si. The use of MS/MS significantly reduced the detection limits for each analyte when compared with standard He collision mode ICP-MS. For example, the LOD for Cl reduced from 41.8 μg L−1 to 3.1 μg L−1 when employing a hydrogen mass shift and setting Q1 = 35/Q2 = 37. Accuracy was examined using spike/recovery experiments and comparing with results obtained using SF-ICP-MS.

3.2 Building materials

The determination of Cl is still one of the main tasks for the evaluation of reinforced concrete structures as chloride penetration to the rebar is the dominant damage process affecting structural lifetime. The analytical technique of LIBS can be a fast and reliable method to quantify Cl in cement-bound materials and its use has been reviewed and validated by Millar et al.154 The group described the production of a series of reference materials of varying Cl salts and additives and their use for calibration. A calibration model with a precision of s(x0) = 0.023 wt% was obtained and mean error of the validation test set was 0.595 ± 0.063 wt%, which was comparable to standardised methods such as potentiometric titration or photometry. A second paper by the same group discussed a similar application of the determination of total Cl content in cement pastes.155 The use of Cl molecular lines as a means of avoiding purged spectrometers for Cl determination was reported.156 Calcium monochloride radicals, formed in the plasma, have observable band emissions at 593.4 nm and 621.2 nm. Determining Cl using these molecules avoids any purge requirements. Furthermore, the shot-to-shot reproducibility was increased by calculation of the intensity ratio of Cl related and unrelated molecular bands e.g. CaCl[thin space (1/6-em)]:[thin space (1/6-em)]CaOH ratios. The LOD was 0.075 wt% Cl related to the cement mass. This is below the critical threshold of 0.2 wt% of chlorides related to the cement in reinforced concrete. Micro-XRF was used by Bran-Anleu et al.157 for mapping Cl in hardened cement. The paper discussed, in detail, the preparation of relevant standards and appropriate sample preparation. The method LOQ was 0.011 wt%, but more importantly, it offered accurate spatially resolved analysis with minimal sample destruction.

ElFaham et al.158 showed a linear relationship between the compressive strength of concrete and the ratio of calcium atomic and ionic emission line intensities observed using LIBS. The report highlighted the importance of correction for self-absorbance of the calcium lines, doing so by comparison of electron densities with those computed from the hydrogen Hα-line at 656.27 nm which was in the same spectra under the same state. The technique was considered a useful semi-non-destructive concrete strength test. A second paper by ElFaham, discussed the use of online LIBS for the fast processing of cement waste material for prospective co-processing.159 However, LIBS alone was not sufficient as it could not identify low level of hazardous heavy metals, therefore a combined approach with ICP-OES was necessary. Guo et al.160 demonstrated that LIBS was successful for the on-line component analysis of powder cement. Calibration models based on PLS and support vector regression (SVR) methods were used to quantify Al, Ca, Fe, Mg and Si in cement with comparable accuracy to the specimens analysed off line as pressed powders.

The development of portable devices is helping researchers to resolve problems in the field in a fast and easy way. The use of handheld EDXRF instruments to aid the understanding of degradation processes that take place in bricks exposed to marine environments was discussed by Morillas et al.161 The team performed the bulk of the analysis in situ, choosing to verify select results in the laboratory. Handheld XRF was also use by Ramacciotti et al.162 for the analysis of archaeological mortar specimens located in Sagunto, Spain. Again, the team chose to verify samples in the laboratory highlighting that whilst portable instruments are useful, laboratory analysis is still required for ultimate confidence in the trueness of results.

Garcia-Florentino et al.163 demonstrated the usefulness of a combined macro- and micro EDXRF instrument for the analysis of historical mortars. The report highlighted the importance of sample homogeneity at the chosen resolution for true quantification, as well as the necessity of suitably matrix-matched reference standards. With the exception of the lightest elements (Na and Mg) there was good agreement with result obtained using WDXRF methods employing pressed pellet and fused bead preparations, as well ICP-MS analysis following an alkaline fusion preparation. A TXRF-based quantitative methodology for the determination of Ca, Fe, K, Mn, Pb, Rb, Sn, Sr and Ti in water and acid extracts of mortars from culturally important buildings was reported.164 Samples were prepared by mixing a 1 mL portion of sample with 50 μL of 100 mg L−1 Rh solution. A 10 μL aliquot was then transferred to a reflector disk, prepared with silicon, and dried under an IR lamp. Calibration was based on fundamental parameters with internal standardisation using the known Rh concentration. The LODs ranged from 0.01–12 mg L−1, depending on the analyte. The method proved to be a quick and simple alternative to the more classic quantitative techniques such as ICP-MS. Acid leaching of concrete and the determination of the acid soluble elements by ICP-MS was shown to be a useful tool to establish common origin of fragments for forensic investigations.165 As only part of the sample was dissolved during leaching, the concentration ratios of nine elements: Ba, Ce, Cu, Nd, Pb, Rb, Sr, Zn and Zr, normalised to the concentration of La were used as a means of determining whether two specimens were of the same material. This approach negated the need to calculate moisture content and the extracted weight of the sample to be determined.

Yakubenko et al.166 provided a detailed description of the optimisation of a microwave digestion methodology prior to ICP-OES analysis. The optimised method allowed for complete digestion of 0.1 g of sample with 11 mL of a mixture of HF, HCl, HNO3 and H3PO4 acids (6[thin space (1/6-em)]:[thin space (1/6-em)]3[thin space (1/6-em)]:[thin space (1/6-em)]1[thin space (1/6-em)]:[thin space (1/6-em)]1) following a five-step heating profile and a mid-run addition of 2 g of H3BO3. Whilst the method proved to be accurate by recovery of reference values of a standard sample, it is the writer’s opinion that a simpler, and potentially safer, approach would be to use XRF following fused bead preparations.

3.3 Catalysts

A review of the current state and problems of analytical control of spent automobile catalysts was produced by Alekseeva et al. (65 references)167. The review focuses on the chemical preparation of samples using autoclave and microwave procedures, assay procedures and spectroscopic developments. Kim et al.168 discussed the increased ICP-OES matrix complexity from interfering elements present when determining PGMs obtained from low-grade ores and recycled automotive catalytic converters. Low-grade grade ores are often rich in other metals such as Al, Ca, Cu, Cr, Fe, Mg, Mn, Pb and Si, all of which were found to cause either spectral, ionisation or chemical interferences with the common PGM analytical lines. The team used statistical analysis of the measured interferences to determine a set of guidelines for selecting the appropriate analytical lines depending on the matrix complexity. A rapid LIBS method as an alternative to chemical digestion followed by ICP-OES procedures for the determination of PGMs in supported catalysts was reported by Jaine and Mucalo.169 A series of bespoke reference materials was produced by evaporation of known volumes of liquid stock solutions in a Pyrex beaker, followed by reconstitution in neat ethanol containing 50 mg of poly(vinyl pyrrolidone) and 2.97 g of silica or alumina support material. The solutions were evaporated again to produce supported metal nanoparticles. The production was confirmed using TEM. Reference concentrations were determined using NAA and they were then used to produce a PLS model for calibration of the LIBS system following pelletisation of the powered materials. The entire work flow for sample analysis required less than 10 min and concentrations were predicted with as little as 0.1 wt% error. A LIBS system with a motorised XYZ sample stage was used for mapping the diffusion of Ni and V containing asphaltenes into mesoporous alumina supports.170 The benefits of such a system include having good sensitivity and spacial resolution without the need to subject materials to vacuum as with SEM.

Electrochemical flow cells coupled with ICP-MS continue to be used for the determination of anodic and cathodic dissolution of fuel cells. The configuration enables potential- and time resolved dissolution monitoring of individual metal counterparts with extremely high sensitivity and has been effectively employed to monitor electrochemical dissolution of Pt–SnO2/C electrocatalysts in ethanol cells,171 Pt/C electrocatalysts172 and commercial PtCo alloys under cyclic potentials.173

The ability to study the behaviour of catalysts under operational conditions is important when trying to understand activation and deactivation mechanisms. It was therefore no surprise that multiple example of operando and in situ characterisation featured during the review period. In situ XAS with millisecond time resolution was utilised by Gonzalez-Flores et al. to understand the synergistic effects of Ni–Fe water oxygen evolution reaction catalysts under cyclic potentials.174 Analysis was performed at the beamline KMC-3 (bending magnet) of the Berlin synchrotron radiation source (BESSY). All X-ray absorption signals were collected in fluorescence mode, with detection at right angle to the exciting X-ray beam. K-edge absorption spectra of the sample were recorded immediately before and after each time-resolved experiment, to normalize the time-resolved data and to assess film dissolution. The team discovered that the Fe sites do not undergo a distinctive redox transition but are enslaved by the oxidation state changes of the Ni ions. Another sub-second time resolved XAS application was reported by a team at the Diamond Light Source, UK.175 Although not capable of electrochemical cycling experiments, the setup is capable of reproducible cycling between different states triggered by gas atmosphere, light, temperature, etc. and opens up new perspectives for mechanistic studies on materials such as automotive catalysts, selective oxidation catalysts and photocatalysts.

In situ XAS was utilised to follow the formation of precursor-dependant supported Pd nanoparticles during calcination.176 Gamma-Al2O3 and activated carbon supports were loaded with various metal precursors, e.g. Pd(NO3)2, PdCl2 and Pd(OAc)2. The results indicated that the thermal stability of the metal precursor plays an important role in the size and speciation of the formed Pd nanoparticles after the activation process. Beale et al. investigated the effect of oxidation state and geometry of Fe species present on prepared Fe-containing zeolites on the selective reduction of NO with NH3 using high energy resolution fluorescence detected X-ray absorption near-edge spectroscopy (HERFD-XANES) and Kβ XES at the I2O beamline at Diamond Light Source, UK.177 Samples were measured under flowing gas using a borosilicate capillary tube heated to 300 °C. The study revealed that highest activity was achieved when octahedral Fe3+ species were formed when preparing the catalyst. The technique was also used for the characterisation of Cu species on Cu–CHA zeolites used for the same reaction.178 Chemometric methods were employed to pinpoint the composition impact on the material reducibility and highlight Cu-speciation-productivity relationships. Operando HERFD-XANES and XES was also used by Zhou et al.179 to gain mechanistic insight into the photothermal catalytic oxidation of CO over Pt/TiO2. The technique was sensitive enough to uncover changes in electronic structure of the Pt sites under light illumination that led to increased oxidation. This resulted in a 20-fold rate increase in CO oxidation at 45 °C compared with non-illuminated material.

Methods of surface specific analysis of catalytic materials unsurprisingly continues to be a growing area of research. Mino et al.180 provided a comparative review of the key X-ray micro- and nanoprobes available for space-resolved characterisation of solid materials. The paper, containing 660 references, covers the general concepts, characterisation strategies and recent significant applications, whilst highlighting their views on possible future development areas.

Physico-chemical insights into the surface structure of alumina- and silica-supported catalytically active iron oxide nanostructures were obtained using TOF-SIMS with a Bi3+ primary ion source.181 Powdered samples were pelletised and attached to a Si wafer for analysis using a 30 keV primary ion acceleration voltage with an analysis area of 500 μm × 500 μm. Interrogation of the spectra revealed secondary cluster ions Fe–O–Al showing a strong chemical interaction between the catalytic species and support. However, this was less pronounced for the respective Si species on the silica supported catalyst which was also found to have lower catalytic performance.

Müller et al.182 reported the application of extreme ultraviolet LA-TOF-MS for the nanoscale depth profiling of CoNCN-coated electrodes. The self-developed laser, operating at 46.9 nm, represents a factor of 4 reduction in wavelength with respect to the previously reported state-of-the-art 193 nm excimer laser. A reduction of the wavelength was used as an alternative to a shorter pulse duration in order to enhance the ablation characteristics and obtain smaller quasi-non-destructive ablation pits. The reported instrumental setup provided lateral resolution of 80 nm, depth resolution of 20 nm and a detection limit of approximately 50 ppm depending on the analyte of interest.

3.4 Forensics applications

As found in previous review periods, the analysis of gunshot residues (GSR) dominates the forensic application of atomic spectrometry techniques. Dona-Fernandez et al.183 evaluated the performance of a portable LIBS system for the optimisation of GSR evidence collection. The portable instrument was able to determine the characteristic GSR elements Ba, Pb and Sb at the crime scene, allowing target collection of evidence for verification by the established SEM methods. A laboratory-based 2D scanning LIBS system was used to produce elemental maps of GSR around bullet holes.184 Forty-five pieces of fabric were shot at known distances to create training set for PCA and a further 28 materials were analysed as test specimens. The LIBS analysis resulted in 100% correct identification of the shooting distance compared with a 78.6% correct classification using the conventional chemical colour test. Furthermore, the LIBS analysis produced a permanent digital image that could be further interrogated if required. A comparison of different swabs for the sampling of GSR from gunshot wounds prior to analysis using ICP-MS was reported.185 Four different swab types: tapes in graphite, Leukosilk (R) white tape, 3 M (R) transparent tape and a cotton swab wet with 10% HNO3 were compared for their ability to collect the highest amounts of GSR from skin samples with the lowest contribution to the blank. The cotton swab with nitric acid was the best performer. McKenzie-Coe et al. described the detection of discharge residue from skin swabs using TIMS-MS.186 The method was based on the simultaneous extraction of inorganic and organic species using 15-crown-5 ether. The analytical performance was illustrated as a proof of concept for the case of the simultaneous detection of Ba2+, Cu+, K+, NO3, Pb2+, diphenylamine, ethyl centralite and 2,4 dinitrotoluene in positive and negative MS modes.

A single particle ICP-MS technique was investigated as a screening technique for GSR nanoparticles recovered from a shooter’s hand.187 Unlike many single particle ICP-MS applications where a single mass is monitored, the authors reported the monitoring of analyte pairs by ‘hopping’ between the two masses. The paper described the optimised quadrupole and detector parameters to ensure high ion velocity and minimum quadrupole settling and detector deadtime. This allowed single events to be detected for each element. Material was washed from the shooters hand with ultrapure water and analysed without further treatment allowing simple sample collection and rapid analysis. Comanescu et al.188 utilised the low detection limits achievable using GFAAS to study the background levels of Ba, Pb and Sb on vehicle surfaces. Samples were collected on wet cotton swabs, which were then extracted with nitric acid for analysis. Instrumental limits of detection were 0.052, 0.06 and 0.013 μg per swab for Ba, Pb and Sb, respectively. Transfer of the GSR was dependent on both the shooting conditions and the exposure time. Multiple random vehicle swabs and the low detection limits allowed very low cut-off lower limits, below which it is impossible to determine whether a sample is GSR positive or not. The values obtained were 0.04 μg for Sb, and values of at least 0.10 μg of Ba and Pb. These were a significant improvement when compared with 0.3–0.5 μg achieved using NAA.

3.5 Ceramics and refractories

3.5.1 Industrial ceramics. Ceramics are, by nature, difficult to dissolve and are very resistant to heat. Their analysis can therefore be problematic. Most methods therefore rely on the direct analysis of the solid materials. Consequently, analytical techniques such as LA-ICP-MS, LIBS, XRF or glow discharge methods are commonly reported.

The LIBS analysis of aluminium oxide powder materials has been reported in two papers. A paper by Myhre et al.189 deliberately mixed alumina powder with metal oxide powders of Eu or Sm and then pressed them at 15 tons into pellets with dimensions of 1 cm diameter and 2 mm thickness. Two approaches to building a univariate simple linear regression curve were taken. One correlated the known concentration of an analyte in a standard to the normalised value of an integrated emission line to give a response signal. The integrated area of a nearby background region was used to normalise the data. The second approach used the intensity at one of two Al wavelengths to normalise the data. Both methods were described in the paper. Linearity extended from 0.086 to 12.4 weight%. The LOD for the analytes depended on which wavelengths were used, but ranged from 0.001 to 0.108% for Eu and from 0.001 to 0.183% for Sm, respectively. The second paper, by Pandey et al.,190 described the determination of Ni impurities in alumina powders of different particle size. Three materials were used for the analysis, the first had a particle size of 190 ± 64 nm, the second of 500 ± 160 nm, but was prone to agglomeration forming particles with an average hydrodynamic size of 1.7 μm (although this varied between tens of nm to hundreds of μm). The third material had an average particle size of 35 ± 13 μm. Samples were doped with a Ni solution to varying concentrations, dried and then pressed into pellets of known density. Sensitivity of the LIBS analyses increased as the grain size increased for a given density. It was concluded that both the particle size and the density of the pellet should be specified when preparing calibration curves.

A study undertaken by Takahara et al.191 developed a method for ceramic powder analysis that minimised both matrix effects and position effects of spin coated samples. Different certified silicon nitride powders (10 mg) were suspended in a solution of polymethyl methacrylate (0.1% in 990 μL of toluene and 10 μL of 100 mg L−1 Ga added as an internal standard). The materials were then spin coated on quartz disks and the samples analysed for Cr, Fe and Mn using TXRF. A poor correlation was observed between fluorescence intensity and standard concentration which was not improved through the use of an internal standard. This was attributed to the internal standard being in a different part of the spin coating rather than in the ceramic powder. It therefore did not correct for matrix effects. However, the background intensity ratio did improve the correlation coefficient of the empirical calibrations, effectively overcoming grain size, position differences, sample particle shape irregularities and matrix effects.

The technique of LA-ICP-MS was reported for the determination of Pb isotope ratios in lead-glazed ceramics192 and for the examination of the mass transfer of additive elements in barium titanate ceramics during the sintering process.193 The first example used a multi-collector instrument to collect the isotope ratios and used Tl to correct for mass bias effects. The ratios of 206Pb[thin space (1/6-em)]:[thin space (1/6-em)]204Pb, 207Pb[thin space (1/6-em)]:[thin space (1/6-em)]204Pb, 208Pb[thin space (1/6-em)]:[thin space (1/6-em)]204Pb, 207Pb[thin space (1/6-em)]:[thin space (1/6-em)]206Pb and 208Pb[thin space (1/6-em)]:[thin space (1/6-em)]206Pb obtained using LA-ICP-MS were within 0.027% of those obtained using conventional nebulisation. The proposed method provided accurate and precise lead isotopic compositions using non-matrix-matched standards for calibration, was minimally damaging to the sample, could obtain data within 10 minutes per sample and was highly spatially resolved. The paper by Sakate et al.193 analysed multi-layered ceramic capacitors. Two barium titanate pellets containing different concentrations of Ho and Mn with the sintering agent Si were prepared and then sintered. Once prepared, the samples were analysed in a helium atmosphere which was then ad-mixed with argon before entry to the plasma. The operating parameters and method were discussed in the paper. The mass transfer of Mn was significantly higher than that of Ho during the sintering process. It was concluded that LA-ICP-MS could be used to improve the manufacture of the ceramic capacitors.

Tang et al.194determined K in ceramic raw materials using LIBS. The LIBS setup and operating parameters were described at length in the paper. Materials were pressed into pellets at a pressure of 20 MPa to increase the density prior to analysis. Initially, self-absorption effects were severe, limiting the accuracy obtained. A method of profile fitting using a Lorentz function was developed to overcome these problems. The rationale behind the selection of the analysis wavelengths and the theory of the Lorenz function were given in the paper. The methodology was validated through the use of seven certified materials with a K2O content ranging from 0.049–8.6%. These materials were also ceramic raw materials and included feldspar, clay and kaolin. When using the Lorentz function, the regression improved from 0.993 to 0.998, the root mean square error of cross validation improved from 0.458 to 0.145 and the average relative error decreased from 13.7% to 5.1%.

Gold-coated ceramics were analysed using glow discharge (GD)-TOF-MS by Bouza et al.195 Insulating samples are not easy to analyse using GD because the voltage drop across the sample leads to low power deposition and non-efficient sputtering. The ceramic samples were 6 mm thick and were coated with gold with a thickness determined to be in the range 20–120 nm. The operating conditions were carefully optimised to obtain good sputtering. The optimal conditions were: 30 W of RF power, 95 Pa pressure in the discharge chamber, and a pulse width of 500 ms with a period of 1.49 ms. In addition to analysing the ceramics, it was also possible to analyse the gold coating. This was found to contain impurities of Bi, Ir, Pd, Pt and Rh.

3.5.2 Cultural heritage: ceramics. As usual, this has been a very popular area of research with non- or minimally damaging analysis techniques being the most common. Reviews or overviews are often the most useful articles for workers new to an area and this year has provided an example for cultural heritage ceramics. A critical review, by Botto et al.,62 discussed the applications of LIBS to archaeology and cultural heritage. Sample types included metalliferous samples, glass, pigments, bones and teeth and pottery. The review, containing 212 references, was conveniently split into the relevant sections and included the more recent research topics of nanoparticle enhanced and underwater LIBS. Also included were micro-LIBS and 3D elemental imaging. Another overview, by Nord and Billstrom196 containing 148 references, discussed the use of isotopes in cultural heritage. As well as the well-known isotopes of Pb and Sr that are used for provenance elucidation, a series of other analytes were also discussed. The review was split into numerous sections that discussed methods of analysis, the different isotopes determined and what the isotopic information could be used for. Included among the isotopes were 14C, tritium, 36Cl, 230Th, 232Th and 210Pb for dating purposes, and a host of less common stable isotopes for provenance studies. Analytical techniques discussed, albeit briefly, included isotope ratio mass spectrometry, SIMS, TIMS, MC-ICP-MS and fission track methods. The authors also provided insights into potential future applications. A final review, by Panchuk et al.,197 was a tutorial on the application of chemometric methods to XRF data. The review, containing 146 references, discussed the different subject areas, e.g. forensic, cultural heritage, agriculture, etc. and gave a useful pie diagram clearly demonstrating that the most common methods used are PCA, hierarchical cluster analysis and partial least squares. Numerous other chemometric methods including artificial neural networks, linear discriminant analysis, soft independent modelling of class analogy, etc., were also discussed. A description of how many of the methods work was given, with the main three given in detail.

A paper by Lazic et al.63compared the techniques of LIBS, XRF and PIXE for the analysis of egg tempera pigments on gypsum, oil paints on gypsum, glazed ceramics and Roman coins. This paper was discussed in more detail in Section 1.3 and will therefore not be discussed further here.

Other papers in this research area have been summarised in tabular form (Table 4). The papers summarised have some novelty, either in term of the analysis itself or in the chemometric analysis of the analytical data. Numerous other papers do exist, but from an atomic spectrometric perspective, they offer little in terms of novelty.

Table 4 Applications of atomic spectrometry to the analysis of cultural heritage ceramics
Analytes Matrix Technique Comments Ref.
Al, Ca, Fe, Mg and Si Archaeological ceramics from China LIBS Data from the LIBS analysis of 35 ceramics from different Chinese dynasties were treated using five different pre-processing techniques. These were: normalised by maximum integrated intensity, by extremum integrated intensity, mean centering, first order derivatives and second order derivatives. The data were then treated using variable importance threshold values. The treated data were then interrogated using the random forest chemometrics technique. Under optimal conditions, the sensitivity, specificity and accuracy were described as being 0.8528, 0.9710 and 0.9433, respectively. The procedure was sufficiently efficient to distinguish samples from different dynasties 198
Al, Fe, K, Mg, Si and Ti Archaeological pottery from India LIBS Analysis of pot sherds using LIBS and SEM-EDS with results from the two being in good agreement. The LIBS analysis required no sample preparation, was quick and could be used in situ. The types of clay used were identified and the firing temperature was determined to be less than 800 °C 199
Nd and Sr Raw materials, ceramic replicas and ancient pottery TIMS The samples were acid digested and the analytes separated from the matrix by ion exchange techniques. The 87Sr[thin space (1/6-em)]:[thin space (1/6-em)]86Sr and 143Nd[thin space (1/6-em)]:[thin space (1/6-em)]144Nd ratios were obtained using TIMS were used as a tool for provenance determination. The method was validated using NIST SRM 987 for Sr and the La Jolla Nd reference standard. The isotopic characterisation was an effective fingerprint for pottery 200
Various (16) Pre-colonial pottery from Brazil EDXRF, PIXE A total of 63 fragments of pottery from three sites analysed using computed radiography (for internal structure), EDXRF and PIXE. Analytical data were analysed using multivariate statistics such as hierarchical cluster analysis and PCA to separate and correlate the samples. Samples were split into two clusters: one from two of the sites and the other from the third. This indicated that samples from two of the sites were made from the same clay 201
Various (>20) Late bronze age Cypriot ceramics WDXRF, ICP-MS For XRF analysis, potsherd were ground to a powder and fused to form a glass. Powders were acid digested prior to ICP-MS analysis. It is unusual for a cultural heritage paper to destroy/significantly damage the sample nowadays. Binary plots of the data enabled a trading system to be elucidated 202
Various (16) Late Byzantine period pottery from Serbia WDXRF, ICP-OES, FTIR, μ-Raman, XRD Pottery samples (63) from different periods covering 13th–15th century from the same monastery were analysed using multiple techniques. Microwave assisted acid digestion was undertaken prior to ICP analysis. Multivariate statistics (PCA) performed on FTIR and powder XRD data. Combining the data from all the techniques demonstrated that there was no significant difference between any of the samples mineralogical or chemical composition, indicating continuous pottery preparation. Firing temperatures were also estimated 203
Various (22) Prehistoric pottery from Japan XRF Pottery sherds from a Japanese island from two time periods analysed using XRF. Samples mixed 1[thin space (1/6-em)]:[thin space (1/6-em)]10 with flux and fused into a glass bead. Calibration was against synthetic standards. Analytical data input to PCA cluster analysis and scatter diagrams. Results from the three classification techniques were in good agreement, with five provenance groupings identified. Most had been imported from Honshu 204
Various (20) Late antique pottery from the Balearic Islands XRF, XRD, optical microscopy Sherds from 78 ceramics were pulverised into a powder, mixed 1[thin space (1/6-em)]:[thin space (1/6-em)]20 with a flux and fused into a glass bead prior to XRF analysis. Dendrograms and PCA used on analytical data to garner provenance information. Results indicated that the area was participating in trade with other regions 205
Various Chinese blue and white Kraak porcelain from Ming dynasty μ-XRF, XANES Two different groups of samples were analysed using XRF with a fundamental parameters standard-free quantification method. Main body, two glaze layers and pigment were all analysed. Data were input to PCA. Results demonstrated that the two groups of samples came from the same source. The XANES was used to analyse the cobalt pigment 206
Various (46) Ceramics from France LA-ICP-MS Inclusions in the pottery were analysed using LA-ICP-MS. Four standard reference materials analysed to monitor accuracy. Data input to PCA, hierarchical cluster analysis and ternary diagrams. Methodology enabled discrimination between imported and local pottery and also managed to link the pottery with the source rock 207
Various (13) Qingbai porcelains from a Java sea shipwreck Portable XRF The provenance of porcelains found in a shipwreck dating from 12th–13th century was undertaken. Portable XRF used to determine analytes. Data input to hierarchical cluster analysis, binary plots and PCA. Glazes and pastes both analysed. Different manufacturing sites clearly identified 208
Various (17) Potsherds from the Yaeyama Islands, Japan XRF microscopy Two analysis methods used: elemental mapping and multi-point spectral measurement, enabling an elemental distribution on the surface as well as a detailed multi-point elemental composition to be obtained. The data were introduced to PCA and non-metric multi-dimensional scaling analysis 209


3.6 Glasses

3.6.1 Industrial glasses. One of the more common themes of analysis in this review period has been the elucidation of corrosion mechanisms. Two papers by Rodrigues et al. discussed the use of SIMS210 and TOF-SIMS211 to examine surface alteration of glasses under museum-like environments. Other techniques, e.g. μ-Raman and FTIR were also used in both studies. In the first paper,210 the effect of room temperature and relative humidity on degradation of replicas of three soda-rich glass types were studied. The thickness of the altered layer was proportional to the exposure time and to the relative humidity of the atmosphere. Data indicated that Na was leached from lower level in the glass leading to deficient areas whereas the surface became enriched. In the second paper, the secondary ions determined included Al, As, Ca, Fe, H, K, Mg, Mn, Na, Pb, Si and some molecular species. Results demonstrated that Ca and Pb played dominant roles in the hydration and hydrolysis of the glass surfaces. Again, different conditions likely to be found in a museum environment were tested. A third paper to discuss corrosion of glass was presented by Zhang et al.212 These authors used TOF-SIMS to monitor the H/Na interface on a corroded International Simple Glass. The H/Na interface could be imaged directly using positive ion imaging without any auxiliary sputtering beam under high vacuum (2 × 10−8 mbar). The H background was approximately 5% in the pristine glass, rising to 15% in the alteration layer.

The forensic analysis of glass has also been a topic of interest. In common with the analysis of other forensic sample types, minimally destructive analytical approaches are adopted. Seyfang et al.213 discussed the TOF-SIMS, sensitive high resolution ion microprobe (SHRIMP) and SEM-EDS analysis of glass frictionators in 0.22 calibre rimfire ammunition. Such materials have replaced the antimony sulfide frictionator in a lot of ammunition. The composition of the glass particles does not change after use. In this study, 37 samples from 25 different manufacturers in 11 countries were analysed along with five standard reference glasses. For the TOF-SIMS analysis, the signals from 52 analyte ions were ratioed against the 28Si+ signal and the resulting data input to PCA. The SHRIMP analysis determined 6Li+, 7Li+, 204Pb+, 206Pb+, 207Pb+, 208Pb+, 232Th+ and 238U+. The major isotopes of Be, Li, Mg, O and Si were also detected. Using TOF-SIMS data alone, 94.1% of the sample brands could be discriminated using a pairwise comparison. The SEM-EDS was capable of discriminating only 79.4% of the samples. When SHRIMP analysis was combined with the other techniques, successful discrimination was achieved for 95.6% of brands.

Several other applications of the analysis of glass were presented. Two of them discussed the use of LIBS. Skruibis et al.214 used multiple pulses from a femtosecond Yb:potassium gadolinium tungstate laser (Yb:KGW) to improve the analytical performance of LIBS. The laser operated at an average power of 5 W and at 60 kHz, producing a wavelength of 1030 nm and a pulse width of 280 fs. The effect of a water film of thickness 0.8 mm on the LIBS analysis of glass was determined. The single pulse LIBS signal diminished significantly in the presence of water. This was attributed to quenching. The signal from multiple pulse LIBS was less affected, being both stronger and having longer duration. It has recently been found that the presence of nanoparticles enhances the LIBS sensitivity. Sanchez-Ake et al.215 used gold nanoparticles deposited on the sample and produced from a gold thin film coated on the sample to enhance the sensitivity of the LIBS analysis of glass. The thickness of the film, the laser fluence and the number of laser pulses were all studied. The nanoparticles produced from the thin film gave a lower signal to noise ratio than the pre-formed nanoparticles. The mechanism of enhanced sensitivity was hypothesised as being improved heat transfer from the particles to the glass surface. This enabled lower laser fluence to be used.

The final paper of interest to industrial glass analysts was presented by Zhang et al.216 who devised a solution-based calibration method for LA-ICP-MS analysis. The system employed a desolvating nebuliser system that was connected to the instrument via a Y piece between the LA cell and the spectrometer. The desolvating nebuliser system employed a semi-permeable membrane drier tube with a counter flow of argon to sweep the moisture away. Internal standards corrected for the differences in aerosol transport efficiencies between the nebuliser and the LA system. The method was validated through the analysis of several glass CRMs (NIST 610 – NIST 616) and Acrylonitrile Butadiene Styrene reference materials (GBW 08407 – 08411). Results were in good agreement with certified values. Detection limits for REE and other elements such as Cd, Co, Cr, Mn, Ni, Pb and Zn were at the ng g−1 range. The results obtained from the analysis of biological materials were compared with those obtained using solution-based nebulisation and were also in good agreement.

3.6.2 Cultural heritage: glasses. In accordance with other cultural heritage sample types, non- or minimally destructive methods of analysis, e.g. LA, LIBS, varying forms of XRF etc. are used extensively for glass samples. The large majority of papers describing the analysis of cultural heritage glasses are summarised in Table 5 because although interesting they are often not a significant advance in atomic spectroscopy. Instead, the ones discussed in the table describe a sample introduction system or chemometric analysis of the data to try to elucidate provenance, trade routes, etc.
Table 5 Applications of the analysis of cultural heritage glasses
Analytes Matrix Technique Comments Ref.
Various (20) Antique glass from Cyprus LA-ICP-MS Rare earth elements and others determined and data analysed using PCA to elucidate extent of re-cycling. Once elements common in re-cycling (Co, Cu, Pb, Sb and Zn) had been removed from data sets, provenance could be elucidated. Analytical accuracy verified using NIST 612 217
Various (>40) Late antique Apulian glass samples LA-ICP-MS, EPMA, SEM-EDS Trace elemental data and isotope ratios of 87Sr/86Sr and 143Nd/144Nd determined. Analytical data investigated using ternary diagrams enabling provenance determination. Analytical validation was achieved using USGS BCR-2, with accuracy being within 20% for analytes at the sub ppm level. Re-cycling of glass also studied. Different parts of one glass sample were identified as coming from different batches 218
Various (∼30) Late antique and early Christian glasses from Bulgaria ETV-ICP-OES Finely ground glass (0.2–1 mg) analysed directly using CF4 as an evaporation aid. Calibration achieved using dried aqueous standards or with certified materials (coal BCR-038, stream sediment GBW 07312 and soda lime glass BAM-S005. The content of some major and minor elements used to determine the type of glass and potential origin 219
Various (55) Archaeological glasses from Prague castle LA-ICP-MS, EPMA Major, minor and trace analytes determined with analytical accuracy validated using NIST 612. Analytical data interrogated using binary and ternary diagrams as well as PCA. Three sets of glass identified: wood ash glass, potash glass and potassium crystal-clear glass. Some glasses found in Lisbon found to have the same chemical signature, indicating a possible trade 220
Various (>40) Bronze age glass beads from Poland LA-ICP-MS NIST 610 and glasses from the Corning glass museum were used for method validation with the latter comparing results with literature values. Two groups were distinguished depending on the MgO to K2O ratio. High Mg glasses were thought to originate in Mesopotamia whereas high K glasses came from Italy 221
Various Mycenaean glass from Greece XRF, SEM-EDS, PGAA Ternary diagrams and PCA used to distinguish between samples manufactured in Greece and those imported from Egypt. NIST 620 and NIST 621 used for method validation. Data obtained from the different techniques were compared and were, in general, in good agreement 222
Various Early Islamic glass from Egypt LA-ICP-MS Method validation using NIST 610, NIST 612 and Corning glasses B, C and D. Analytical data from Al, Ca, Mg, Na, Ti and Zr were analysed using PCA which identified four main composition types. Other analytes associated with colouring or opacification, e.g. Cu, Pb, Sb, Sn and Zn were also determined 223
Various (>50) Glass beads from early medieval Illyricum LA-ICP-MS An ArF laser operating at 193 nm was used for ablation of the samples (48 glass beads and four vessel fragments). Method validated using NIST 610 and 612 and Corning B, C and D. Chronological and geographic differences of some beads could be distinguished through the source of the Co colorant. Other analytes also used to elucidate trade and re-cycling 224
Various (20) Plant ash glass from United Arab Emirates LA-ICP-MS, XRF, ICP-OES Nd isotope information obtained using pneumatic nebulisation – multi-collector ICP-MS following acid digestion of the sample and successive ion exchange analyte isolation procedures. The LA-ICP-MS employed a ns ArF excimer laser to determine Sr isotope ratios. Other analytes determined using ICP-OES following a fusion sample preparation procedure or μ-XRF for volatile analytes such as S. The elemental composition indicated a unique source 225
Various (>30) 9th–15th century glasses from South East Asia LA-ICP-MS Single point analysis of glass samples. Method validation using NIST 610 and 612 as well as Corning glasses B and D. Analytical data analysed using PCA. Three compositional groups were identified. One of middle eastern origin, another from Southeast Asia and the third from China. The extent of regional exchange/trade was elucidated 226
Various (19) Early Byzantine glass in Serbia PIGE, PIXE Rapid, non-destructive analysis of glass. NIST 620 and 621 glasses used for method validation. Power transformation performed on analytical data prior to insertion into PCA. Hierarchical cluster analysis did not make clear distinction between types of glass, but PCA identified three distinct groups of windowpane glass 227


A review of LIBS for cultural heritage and archaeological samples was presented by Botto et al.62 The review, containing 212 references, had sections for the analysis of metals, pigments, pottery and ceramic objects, bones, teeth and other organic materials and glasses. Other sections concentrated on the combination of LIBS with other techniques, e.g. Raman, XRF and MS. A further section discussed underwater applications of LIBS. The final sections concentrated on the most recent applications, e.g. those that use nanoparticles to enhance the LIBS signal and those that perform 3D mapping.

3.7 Nuclear materials

Accurate measurement of isotopic ratios in materials for nuclear safeguards and forensics is a popular subject area, most commonly through the measurement of actinide elements using ICP-MS or TIMS. The absence of reference materials or limited application of those reference materials that are available is also mentioned or addressed in several studies. The measurement of nuclear materials to improve understanding of fallout from the Fukushima Nuclear Power Plant accident is addressed in several studies. Similarly, the monitoring of material properties in operating reactors to minimise the risk of accidents occurring also features in numerous studies. As the sensitivity and interference removal capability of multiple techniques continue to improve, decommissioning radionuclides that are more challenging to measure (such as 93Zr and 129I) are now considered to be routinely measurable, with ICP-MS and accelerator mass spectrometry (AMS) commonly used, as well as TIMS, SIMS, XRF and LIBS. For the testing of material properties for nuclear fusion, LIBS remains the dominant measurement technique. Across all nuclear material applications, a common theme is minimising the procedural time, either through direct, non-destructive analysis, or rapid online radiochemical separation prior to measurement.
3.7.1 Nuclear forensics. Accurate measurement of isotopic ratios in nuclear materials is a key area for identifying the source of contamination following a radiological incident and for locating the source of illegally acquired nuclear material. The capabilities developed can also be applied to numerous other fields including geological dating and historical climate change studies. The measurement of actinide isotope ratios is the most common, in particular U and Pu using ICP-MS or TIMS.

Quemet et al. compared two approaches for minor U isotope ratio measurements using TIMS, which was conducted within a framework developed by the International Atomic Energy Agency for nuclear material round robin exercises.228 The total evaporation method was compared with the classical method with multi-dynamic sequences with respect to accuracy, analysable quantity, analysis time and versatility. Applying a mathematical correction of the abundance sensitivity and the detector calibration reduced the uncertainty and bias of the classical method compared with the total evaporation method. The same author used the total evaporation TIMS method for measurement of Am isotopic ratios as part of a round-robin exercise organised by the Analytical Methods Committee of the French Atomic Energy Commission.229 For the 241Am[thin space (1/6-em)]:[thin space (1/6-em)]243Am isotopic ratio and Am concentration, biases below 0.0001% and 0.02%, and estimated expanded uncertainties of 0.1% and 0.8% were calculated, respectively.

Improving the sample loading procedure for TIMS was the focus of some studies. Baruzzini et al. used Pt and Re porous ion emitter sources to investigate isotopic fractionation in U and Pu reference standards.230 A comparison of the correction of fractionation using the linear, the Power and the Russell’s laws was a further focus of the study. The porous ion emitter sources were successful, with Pu and U isotopic ratio values agreeing with those on the certificate. For both elements, the Power law was the most suitable for the experimental setup used, although all laws produced results that were statistically identical to the certificates. In a separate study, Mannion et al.231 used a polymer thin film for ultra-trace measurements of Pu. The aim was to simplify the single filament sample preparation method and to eliminate sample losses associated with the resin bead loading method whilst maintaining sensitivity and accuracy. Rhenium filaments were coated with a toroidal, hydrophilic anion-exchange polymer spot surrounded by a hydrophobic base polymer, which were loaded with 10 pg of New Brunswick Laboratory Certified Reference Material.128 The use of dimpled filaments improved sample loading of drop deposits, and the polymer coating improved the shelf-life of the filaments, enabling bulk production. The 239Pu:242Pu values measured were in good agreement with the certified values and no sample losses were recorded over 65 analyses.

Actinide isotope ratio detection using MC-ICP-MS remains a popular topic. Ronzani et al. measured multiple U isotopes in various particles using MC-ICP-MS coupled with laser ablation.232 The laser aerosol and water vapour were simultaneously injected using a desolvating nebuliser and mass bias, gain factors, polyatomic and tailing interferences were all corrected. Particles of a few hundred nm were successfully measured, with detection limits in the attogram range achievable. The relative standard uncertainties ranged from 3.3% to 32.8% for 234U:238U, and from 0.4% to 4.0% for 235U:238U. Krachler et al. also employed LA-ICP-MS for U-bearing materials, focusing on evaluation of homogeneity using line-scan analysis.233 The procedure was validated using two low-enriched CRMs (∼1 wt% and ∼4 wt% 235U), with the experimental values agreeing well with the certified value. Following this, two UO2 pellets prepared from identical source materials were measured, with the 235U isotopic abundance ranging from 0.75–1.6% in the first sample and 0.45–3.0% in the second sample. This unexpected variation provided information not previously known on the production process of the materials, and showed the technique developed would be valuable for forensic investigation of unknown nuclear material. Varga et al. used LA-MC-ICP-MS for measurement of U isotope ratios in six CRMs.234 The powdered materials were pressed into pellets prior to analysis, with good agreement between experimental and certified values being obtained. Subsequent SEM measurement of ablated material revealed that only 5 ng of material was used per measurement. Therefore, LA-ICP-MS can be considered a quasi-non-destructive technique, and the material can be further analysed by other techniques. In a separate study, Wang et al. dissolved U particles prior to MC-ICP-MS measurement of isotopic ratios.235 The relative expanded uncertainty in the reference materials measured ranged from 3.5% (k = 2) for 234U:235U to 15% for 230Th:234U.

Several other analytical techniques were also applied to measurement of actinide isotope ratios for forensic applications. Chamizo et al. demonstrated the capabilities of AMS upgraded with He stripping for U transmission and assessment of background sources that affect 236U:238U measurement.236 Scattered 238U3+ molecular fragments were detected that were not identified previously using Ar gas, with a maximum U3+ stripping efficiency of ∼50% when operating at an energy of 650 keV. However, the overall background using He (0.8–1.3 × 10−10) was at least a factor of three higher compared with Ar gas. A study by Hotchkis et al. also tested He gas stripping, with an efficiency of >40% for +3 charge states at an energy of 1 MeV.237 In the case of Pu, sub-attogram detection limits were achieved for several isotopes, with an ionisation efficiency and overall detection efficiency of 3% and >1%, respectively. Song et al. used LIBS to analyse U isotopes in a series of fused glassy disks.238 The 235U content ranged from natural abundance to ∼94 atom%, and the LIBS spectra were analysed using a database of 12 U-lines in the region of 423.3–424.5 nm. Multi-pair spectral fitting produced an analytical bias of ±1% for absolute ratios (235U[thin space (1/6-em)]:[thin space (1/6-em)](235U + 238U)), compared with ±4% for single–line pair fitting (424.412 nm for 235U and 424.437 nm for 238U). The inclusion of hyperfine structure and Stark broadening into the algorithm as fitting parameters was investigated, but was found to cause overfitting, negatively impacting the analytical accuracies. Wang et al. employed laser ionisation mass spectrometry (LIMS) in combination with SEM for rapid determination of U isotope ratios in bulk samples and single particles of ∼50 μm diameter.239 The deviation from certified values was <1%, with a measurement uncertainty of <5%.

Whilst studies using TIMS and LA-ICP-MS highlighted the benefits of direct measurement of solid samples, others focused on reducing the procedural time for destructive analysis techniques using online chemical separation prior to detection. Studies by Fenske et al. and Roach et al. described the development of rapid analysis of post-irradiation debris (RAPID).240,241 This is an automated online separation and direct analysis method for measurement of >40 elements at pg levels. The study focused on measurement of highly enriched U and measurement of anthropogenic isotopes in a bulk uranium matrix. The isotopic ratios measured were within 1–2% of the expected values based on results from isotopic depletion and decay modelling software. Martelat et al. coupled capillary electrophoresis with MC-ICP-MS for online isotope ratio measurements.242 A method using acetic acid as the electrolyte and complexing agent was applied to the separation of U, Pu and the minor actinides Am and Cm. Reproducibility of several parts per thousand for U and Pu isotope ratios was obtained, which was considered comparable to TIMS. Compared with ion exchange separation, the analysis time was shorter and the analyte mass and liquid waste were reduced to ng and μL levels, respectively. A description of the interface between the CE and ICP-MS instruments was also presented.

The ICP-MS instruments equipped with a reaction cell have been proven to offer online interference separation for multiple radionuclides, including actinide elements. Childs et al. used CO2 reaction gas for separation of U and Pu isotopes based on the differential formation of single and doubly charged oxide reaction cell products.243 Uranium was determined as UO2+, with isotope ratios measured within 12% of expected values for several reference materials in nitric acid and digested cellulose filter paper solutions. The stability of the Pu signal at higher CO2 flow rates and 238U tailing and 238UH interference removal needed to be improved further before the same samples could be measured for Pu isotopic composition. A study by Xing et al. achieved U/Pu separation using NH3 as a reaction gas, with U forming UNH and UNH2, whilst Pu did not react.244 Limits of detection of 0.55 fg mL−1 and 0.09 fg mL−1 were achieved for 239Pu and 240Pu, respectively, and the method was successfully applied to measurement of 239Pu:240Pu in sediment reference materials.

The ongoing need for suitable reference materials to validate mass spectrometric procedures for isotopic ratio measurements was identified and addressed in several studies. Penkin et al. measured the isotopic composition of ten U chemicals and standards from various suppliers using TIMS.245 In most cases, materials were depleted in 234U and 235U and enriched in 236U compared with what was expected in natural U. This is significant in the case of materials that are measured by end-users expecting natural uranium composition. The technique of TIMS was also applied to the certification of the isotopic composition of the IRMM 2019–2029 series of uranium nitrate solutions.246 Uranium hexafluoride materials were converted into uranyl nitrate solutions, with the 235U[thin space (1/6-em)]:[thin space (1/6-em)]238U ratio measured using a 233U:236U double spike for materials with low 236U abundance. Dittmann et al. used AMS to characterise a new mixed Pu standard (239Pu, 240Pu, 242Pu, 244Pu) for isotopic ratio measurements.247 The standard was prepared by gravimetric mixing of single isotope standards from the Institute of Reference Materials and Measurements and measured by five AMS instruments and one MC-ICP-MS in an inter-comparison exercise. Mathew et al. undertook an evaluation of 240Pu:239Pu values in a CRM that was produced, characterised and certified between 1966 and 1971.248 The motivations were improved isotope ratio measurement capability since 1971 (specifically TIMS in this study), and the systematic bias previously measured in multiple U isotopes in several standards. In CRM138, a 240Pu:239Pu bias of 0.07–0.08% was measured, which was higher than any bias reported for any U CRM from the same series of standards. A study by Parsons-Davis et al. also focused on the lack of up-to-date measurements, focusing on the nuclear decay data for 238U by measuring the decay constant using isotope dilution mass spectrometry, based on the ingrowth of 234Th in high purity 238U solutions.249 The current decay constant is based on a single value from 1971, and the preliminary result calculated was in good agreement with that determined by alpha counting within the elevated uncertainty (0.462% (k = 2)).

3.7.2 Nuclear decommissioning and waste monitoring. Nuclear decommissioning requires measurement of a range of sample matrices containing various radionuclides and activity levels. As measurement techniques have improved, the number of radionuclides measurable has increased, contributing to the global need for safe and cost-effective decommissioning. A number of papers have demonstrated the high throughput and increased number of radionuclides measurable using mass spectrometric techniques, often combined with rapid online sample preparation techniques. Other studies have recognised that, equally important to accurate waste characterisation, is the long-term monitoring of radionuclides in waste storage and disposal facilities and the environment surrounding them.

Accelerator mass spectrometry was successfully used for measuring multiple radionuclides. Enachescu et al. used AMS for measurement of 14C in a facility that could handle activities that could not be tolerated in laboratories dedicated to 14C dating.250 The bulk and depth profile concentrations of 14C were measured in thermal column disks of a decommissioned reactor, with activities of 75 kBq g−1 close to the reactor core, compared with 0.7 Bq g−1 close to the end of the column, which is significant for waste categorisation. The presence of 14C in irradiated steel was assessed using compound specific radiocarbon analysis (CSRA) AMS by Cvetkovic et al.251 to better understand the release of 14C during anoxic steel corrosion in the cementitious near field of a low/intermediate level repository. Carbon-14 bearing formate, acetate and lactate were the main corrosion products identified, but further work was required on the source of stable C and temporal evolution of the species detected. The same authors combined ion chromatography with AMS for measurement of 14C in the femtomolar to picomolar range in a leaching solution from neutron-activated steel.252 Hosoya et al. demonstrated improvements in 36Cl measurement by AMS by reducing the isobaric interference from 36S.253 Sample preparation using AgBr under acidic conditions was combined with detection of 36Cl at a charge state of +8 to optimise 36S interference removal. A 36Cl:Cl background of 3 × 10−15 was achieved. A further radionuclide relevant to decommissioning is 41Ca, which can be measured using AMS, provided isobaric 41K can be removed. Fu et al. outlined the potential need for 41K interference correction using 39K at 41Ca[thin space (1/6-em)]:[thin space (1/6-em)]40Ca ratios of 10−11 to 10−12 in previous studies,254 before demonstrating that AMS is capable of 41Ca:40Ca background levels of close to 10−13 without interference correction. The method was tested on 41Ca tracer samples.

The technique of AMS was also applied to the assessment of migratory behaviour of radionuclides in decommissioning wastes and storage and disposal facilities. Quinto et al. applied AMS to low-level detection of 99Tc that may be present following nuclear energy production, and in groundwater after diffusion through bentonite which is used as a barrier in some storage facilities.255 A gas-filled analysing magnet in AMS was proven to effectively remove the isobaric 99Ru interference in samples including seawater, a peat bog lake and groundwater, with measurement at the fg g−1 level achieved. This would be applicable to routine environmental monitoring. Zhang et al. addressed the challenges of low-level 129I detection of airborne radioactivity using AMS.256 Samples were collected on a glass fibre filter, followed by pyrolysis and AgI–AgCl co-precipitation prior to measurement. A chemical yield of 81.5 ± 5.8% was achieved, with a detection limit of 1.3 × 104 atoms per m3. The method was used to analyse samples in an inland Chinese city, with iodine concentrations and 129I[thin space (1/6-em)]:[thin space (1/6-em)]127I ratios comparable to those collected in Japan before the Fukushima accident. The procedure developed can help to improve understanding of the transport and dispersion of radioactive iodine contamination away from nuclear sites, as well as for rapid measurement for emergency preparedness.

The measurement of the long-lived fission and activation product93Zr was the focus of several studies, given its contribution to the total nuclear waste inventory over long timescales. The most significant interference that must be removed is isobaric, monoisotopic 93Nb. Pavetich et al. investigated the properties of AMS for removal of 93Nb, including different molecular ion species and the 93Nb background in different sample holder materials.257 A 93Zr background of ∼10−12 was achieved, with a 93Nb suppression factor of 13[thin space (1/6-em)]000–90[thin space (1/6-em)]000 in the detector. The removal of isobaric 93Nb was investigated by Hain et al. using a passive absorber and a gas filled magnet in combination with a time-of-flight path to identify neighbouring 92Zr and 94Zr, and final measurement by AMS.258 A range of ion beam energies was investigated to determine the stopping powers of both 93Zr and 93Nb as a function of energy. The 93Zr detection limits using the passive absorber and gas-filled magnet were 1 × 10−10 and 5 × 10−11, respectively. Asai et al. measured 93Zr using ICP-MS following separation employing a microvolume (0.08 cm bed volume) anion exchange cartridge (TEDA).259 The separation was complete in just over one minute, with accurate detection of 93Zr and all stable Zr isotopes in a spent nuclear fuel pellet using isotope dilution mass spectrometry. The isotopic composition was consistent with the values predicted in a burnup calculation code (an algorithm that models the events during nuclear reactions).

Automated and rapid separation techniques were developed for multiple radionuclides for decommissioning and environmental monitoring applications. Goldstein et al. combined sequential chemical separation with multiple ion counting ICP-MS for detection of Am, Np and Pu in a single aliquot in environmental samples.260 The sequential chemical separations included co-precipitations and extractions using resins such as TEVA and 50wX8. Measurement of a single aliquot reduces the procedural time, and the method was validated using environmental reference materials, achieving good agreement with certified values on samples with >3 × 106 atoms 241Am. Kolacinska et al. compared different chromatographic methods for separation of 99Tc using a sequential injection analysis lab on valve system coupled with ICP-MS.261 Factors including sorption capacity and selectivity were assessed, with the extraction chromatography resin TEVA proving to be the optimal approach. A minimum detectable limit of 6 mBq L−1 was achieved in 50 minutes. The procedure was validated using reactor coolant and sewage, river water surrounding the reactor and an inter-laboratory exercise. Furukawa et al. focused on the sample introduction system of an ICP-MS instrument coupled with solid phase extraction to improve 90Sr sensitivity.262 Compared with using Ar gas alone, an Ar–N2 mixture introduced into the nebuliser improved the sensitivity by a factor of 3.7, removing the need for relatively time-consuming custom tuning of the instrument to improve sensitivity. A detection limit of 0.3 Bq L−1 was achieved within 30 minutes, and results for environmental water from the Fukushima Nuclear Power Plant agreed with values from radiometry.

3.7.3 Nuclear accident response. Although it has been eight years since the accident at the Fukushima Nuclear Power Plant, there are still multiple papers published on the subject, with a common area being long-term monitoring of the surrounding environment, and characterisation of materials at the site. The ability of different analytical techniques to be deployed in the immediate aftermath of a radiological incident also remains a popular area of research.

Radioactive caesium isotopes ( 135 Cs: 137 Cs) have been identified as a useful long-term tracer in the environment surrounding Fukushima. Bu et al. applied a two-stage chemical separation procedure to achieve separation factors of >100 from multiple interfering elements prior to TIMS measurement, including Rb that can act as an ionisation suppressor.263 The method achieved an isotope ratio precision that was generally better than 10% for samples containing as little as 10 fg 137Cs. The method was validated on contaminated marine sediment from the North Pacific. A separate study by Sakamoto et al. aimed to develop a technique that could achieve micro-imaging capability and selective elemental detection that would be applicable to fine particles in a mixture of other constituents.264 A TOF-SIMS instrument and wavelength tuneable Ti/sapphire lasers were developed for interference-free resonance ionisation of target elements. Using two lasers at different wavelengths for a two-step resonance ionisation of Cs led to the successful measurement of a contaminated radioactive particle with no interference from isobaric Ba isotopes. This represents a significant reduction in procedural time compared with offline chemical separation.

Mishra et al. measured total U by ICP-MS and 235U:238U using TIMS in Fukushima-contaminated soil and water samples to investigate the mobilisation of radionuclides in soil into aquatic systems.265 Soils were chemically characterised, and whilst there was no evidence of 235U enrichment from isotopic ratio measurements, the U distribution coefficients ranged from 30–36[thin space (1/6-em)]000 L kg−1. This shows the importance of soil characteristics on U mobility, in particular Fe, Mn and CaCO3 concentration, soil pH and organic content. In a separate study, Stan-Sion et al. set up a new AMS study for low-level measurement of 129I in North Pacific seawater in response to ongoing public concern following the accident.266 The 129I concentrations ranged from 0.9–1.6 × 108 atoms L−1, with concentrations up to 6.4 × 108 atoms L−1 in a river close to the damaged reactor. The authors concluded that Fukushima and its vicinities were an isolated area of contamination.

Total reflection XRF (TXRF) was also applied to analysis of materials and the environment affected by the Fukushima accident. Matsuyama et al. developed a method that could measure U in 15 minutes using TXRF at a minimum detectable activity below the effluent standard value in drainage water of 20 mBq cm−3,267 suggesting it could be deployed as a routine analytical technique. Solutions were prepared by mixing a multi-element standard with a liquid containing the components of demolition debris, with Gaussian fitting performed to overcome the Rb K-alpha peak overlapping with the U L-alpha and Th L-alpha peaks. The same technique was applied by Yoshii et al., with 10 μL of sample solutions dropped onto a quartz optical flat directory both with and without extraction chromatography separation.268 Following chemical separation, there was no overlap in the TXRF spectrum from the Rb K alpha peak, and the measurement time needed to reach the detection limit described was 5 minutes. This compared favourably to 15 minutes in unseparated samples.

As well as Fukushima, the release of radionuclides and materials in the immediate aftermath of a nuclear accident was also considered in some papers. Obada et al. used surface analysis techniques (XPS and TOF-SIMS), Raman spectroscopy and SEM to understand the behaviour of radioactive Cs and I released from degraded fuel and into the reactor coolant system following an accident in pressurised water reactors.269 Caesium-iodide aerosols were deposited on oxidised surfaces representative of a reactor coolant system following an accident, and the materials were analysed following reheating at up to 750 °C in air or steam. The composition of the carrier gas during reheating had a significant impact on Cs release. Song et al. used a range of techniques including ICP-AES, XRD, SEM and EPMA to investigate the potential chemical and physical properties of post-accident fuel debris.270 A series of melting and solidification experiments was performed with different U[thin space (1/6-em)]:[thin space (1/6-em)]Zr atom ratios and Zr oxidation indexes from 36–100%. The composition of particles was found to vary between different particles and within particles, highlighting the complexity of material produced following a nuclear accident, and the importance of complete characterisation.

3.7.4 Reactor materials. The long-term monitoring of materials used during reactor operation and reprocessing is key to ensuring safe and efficient operation, in particular the presence, behaviour and subsequent removal of impurities. Rapid and non-destructive techniques are frequently tested for routine analysis of reactor materials that reduced the time, handling, exposure and secondary waste associated with destructive analysis. A range of analytical techniques are used, in contrast to some other applications where one or two techniques are dominant.

Several studies investigated the applications of LIBS for reactor material components. Qiu et al. used fibre-optic LIBS instrument for multi-elemental analysis of a steel sample used for main pipelines in nuclear power plants (Z3 CN20-09 M).19 A key focus of the paper was the distance between the fibre output end face and the lens, which was studied using plasma diagnostic methods. Self-absorption was observed if the distance was shorter than optimal, and the plasma temperature and density became lower if the distance was longer than optimal. Fibre-optic LIBS was also used for measurement of steel by Wu et al., with the Cr content of the steel noted as having an impact on the emission intensity of the laser produced plasma from the steel.20 Fobar et al. used double pulse LIBS on a robotic system for remote detection of Cl contamination on a stainless-steel surface canister, overcoming the issue of having no direct line of site for the canister.271 The field deployable configuration is useful for harsh environments and constrained space, with detection of Cl concentrations down to 10 mg m−2. A hand-held LIBS instrument was evaluated by Manard et al. to determine rare earth elements in a uranium oxide matrix, as a rapid and on-site approach that reduces handling, transport and exposure to radioactive materials.272 Europium, Nd and Yb were spiked into a uranium oxide powder and measured with preliminary detection limits were of the order of hundreds of mg kg−1. The rare earth elements tested could be distinguished when tested on National Institute for Standards and Technology glass and uranium SRMs.

X-ray – based techniques were also recognised for impurity measurements. Sanyal et al. used TXRF to measure multiple elements at ng μg mL−1 levels in plutonium samples.273 A small volume (2 μL) of solution previously separated from the plutonium matrix was deposited on TXRF supports. The ng levels of Pu deposited meant that samples could be analysed without having to operate in a cumbersome glovebox, as well as limiting worker exposure and radioactive waste. The average relative standard deviation for spiked plutonium solutions was 4.5% (k = 1), increasing to 10.6% for two real plutonium samples with elemental concentrations of 0.2–61 μg mL−1. Measurement employing TXRF of 100–160 ng of Pu was reported by Dhara et al.,274 with 10% collodion solution in amyl acetate added to the deposited sample to fix Pu on the TXRF supports. An average precision of 3% (k = 1) was calculated, with a standard deviation of 6% from expected values based on a sample size of 100–160 ng of Pu. Pandey et al. used WDXRF to characterise mixed oxide nuclear fuels.275 With U content ranging from 2.9–4.2 weight%, the RSD for U and Th was 0.4% and 0.25%, respectively, with good agreement with results obtained following chemical analysis.

Trace and ultra-trace analysis of materials was carried out using destructive techniques, most commonly ICP-MS. Nagar et al. measured metallic impurities in U–Zr alloy fuel after solvent extraction to separate U and Zr matrix elements to <10 μg mL−1.276 Recoveries of 36 elements were determined using a standard addition method, with a relative standard deviation of <10% for more than 90% of elements tested, and detection limits of between 0.01 and 1.1 μg L−1. Reilly et al. also used ICP-MS to trace Ca, Mg and Th contaminants during the production of U metal produced using bomb reduction of suitable U precursors.277 Samples were first doped with Th from 0–1000 μg g−1, and then, following a digestion of the reduced metal, analysed. Results showed that Th fractionation was most significant at concentrations of <100 μg g−1, whilst a significant portion of U and Ca migrated into the digestion crucible walls.

The accurate assessment of graphite impurities is important given its role as a neutron moderator during reactor operation. Plukiene et al. measured samples from a RBMK-1500 reactor using a range of techniques (including neutron activation analysis, gamma activation analysis and ICP-MS).278 The aim was to obtain the missing information on impurity distributions in nuclear graphite constructions, and then compare the data with historical inter-comparison measurements. The results provided new limits of the maximum impurity concentrations that could be present. Wu et al. assessed the impact of molten fluoride salt (2LiF–BeF2 (FLiBe)) exposure on the ability of graphite (IG-110) to absorb tritium.279 After exposing the graphite to the molten salt for 12 hours at 700 °C, samples were measured using techniques including XPS, GDMS, XRD and Raman spectroscopy. Graphite fluorination and changes in microstructure were confirmed, with the possible introduction of new active sites that form once existing ones are consumed. This is potentially an advantage for chemisorption of tritium.

3.7.5 Fusion. The characterisation of materials designed for fusion reactors remains a popular topic, with a focus on material damage and retention of contaminants during operation. The dominant technique is still LIBS, although a range of other spectrometric and bespoke analytical techniques have also been applied.

Maddaluno et al. reported the retention and surface composition of deuterium (measured as a proxy for 3H) using LIBS in the Mo (titanium zirconium molybdenum) toroidal limiter tiles from the Frascati Tokamak Upgrade during short breaks in operation or during maintenance.280 A single pulse technique was used under high vacuum, nitrogen or argon atmosphere, with differences in detection ability and resolution of D-alpha and H-alpha recorded between the three. The aim was to perform extended LIBS analysis of retained deuterium using a robotic arm. Zhao et al. developed a remote in situ LIBS method for diagnosing the composition of plasma facing components, allowing measurement at a specific discharge operation or under specific plasma conditions.281 Depth and lateral resolutions of ∼100 nm and ∼3 mm were achieved, respectively, and elements and impurities including deuterium were successfully detected. The aim is to deploy the system in upcoming facilities such as ITER.

Paris et al. compared LIBS with two Nd/YAG lasers with 0.15 and 8 ns pulse durations for the quantitative assessment of fuel retention in first walls, with special focus on deuterium-doped W/Al coatings of ∼3 μm thickness.282 In the case of ps laser, deuterium was detected at considerably lower fluence values and with an acceptable degree of accuracy. Li et al. applied LIBS in combination with XRD and SEM/EDX for assessing Er2O3 as a coating to prevent liquid lithium corrosion in a tokamak device.283 The LIBS measured the depth distribution of Li and other elements in the corroded layer, with depth profiles obtained as a function of laser pulse number. The results were consistent with EDX line-scanning of the target specimen cross-section, indicating that the liquid Li penetration depth can implicate the corrosion resistance of the oxide layer.

The characteristics of LIBS in various pressure environments on the quantitative determination of Mo in the multi-component alloy first wall material in the Experimental Advanced Superconducting Tokamak (EAST) was the focus of a study by Liu et al.284 Normalisation methods and the partial least squares methods were combined, with different normalisation methods compared for their impact on spectral accuracy and uncertainty. Partial least square methods based on inter-element interference were better than the other methods for Mo elemental determination. A second study by the same author focused on the use of LIBS for diagnosing Li-wall conditioning and Li–H/deuterium co-deposition on the first wall of the EAST.285 The deuterium fuel and co-deposition of multiple impurities was observed, whilst the degree of re-deposition of Li coating on the first wall could be assessed. The conditioning technique applied reduced the H/H+ deuterium ratio due to strong Li adsorption, enhancing long-pulse H-mode plasma operation. The possibility of in situ measurement of deposition, co-deposition and dynamic retention on the EAST first wall using laser induced ablation spectroscopy (LIAS) was published by Hu et al.286 The study draws attention to the commissioning of a system with high temporal resolution during long pulse discharges.

A range of techniques other than LIBS were also applied to measurement of fusion-related materials. Laser induced ablation quadrupole mass spectrometry (LIA-QMS) of graphite limiter tiles for quantitative H determination was investigated by Oelmann et al. to improve understanding of plasma wall interactions and lifetime of plasma facing components.287 A series of locations were analysed, with H implantation observed in erosion zones, where a low fuel content is present due to the high temperature during plasma operation. Results compared favourably to thermal desorption spectrometry and simultaneously performed LIBS. Energy resolving mass spectrometry was used by Dinca et al. for investigating co-sputtering of W–Al materials in a dual-High Power Impulse Magnetron Sputtering discharge, operating with different Ar-deuterium gas mixtures.288 The sputtering gas composition had a significant impact on the total ion flux and composition, with a difference in deuterium abundance in single and dual- High Power Impulse Magnetron Sputtering operation. Multiple techniques including XRD and GD-OES were also used, with the results showing high deuterium retention (up to 21 atomic%) in the mixed W–Al layers that was more dependent on the W-in depth concentration than the Al.

Tungsten was the focus of two studies by Zhang et al. In the first, a newly developed space-resolved spectrometer at 30–520 angstrom was developed to measure a radial profile of W line emission in the EAST tokamak.289 Accurate profiles were achieved for impurities including Ar, Fe, O and W. The second study investigated W degradation in plasma-facing materials due to H permeation and trapping.290 Several techniques (ToF-SIMS, SIMS and focused ion beam combined with SEM and TEM) were used to characterise two polycrystalline W plates implanted with H. The results revealed detailed information on H behaviour, including the timescale of release at room temperature following ion implantation and blister formation of the as-implanted W that remained following thermal annealing.

Fazinic et al. identified the composition of metal dust in fusion reactors as a key topic with regards to safe operation, and focused on determining the composition of dust in the JET tokamak.291 Simultaneous Nuclear Reaction Analysis and Particle Induced X-ray Emission (PIXE) with a focused four MeV He-3 microbeam was used, focusing on Be-rich particles from the deposition zone of the inner divertor tile. The main components of the dust were[thin space (1/6-em)]:[thin space (1/6-em)]deuterium from the fuel, Be and W from the plasma-facing components and Cr and Ni from the antennae grills for auxiliary plasma heating. The analysis identified large Be-rich particles (>90 atom%), and small Al and or Si-rich particles containing other elements such as Fe, Cu or Ti.

3.8 Electronic materials

There have been three reviews published that are pertinent to thıs section. The first, by Noll et al.8 was an overview of LIBS for industrial applications which covered the developments from 2014 to 2018. This was reviewed in more detail in other sections, including Section 1, metals. It will not, therefore, be discussed further here. The other review, by Costa et al.,292 reviewed (with 84 references) the use of LIBS for the chemical analysis of waste electrical and electronic equipment (WEEE). The review was split into convenient sections starting with an introduction containing bar charts demonstrating the rapid increase in use of LIBS over the last 20 years. This was followed by sections on data handling, approaches for qualitative and quantitative analysis, the identification of polymers in WEEE and the analysis of printed circuit boards. It finished off with some potential areas of future research. Many of the applications discussed were also presented in easy to access tables. The third review was presented by Gamez and Finch293 who gave an overview of recent advances in surface elemental mapping using the glow discharge techniques GD-OES and GD-MS. The review, which contained 49 references, discussed instrumental advances, applications and 3D elemental surface mapping. The advantages of glow discharge, e.g. the speed at which it can map a surface compared with other techniques, were also discussed. Among the instrumental advances described are changes to the discharge chamber design so that larger samples can be analysed and the use of different spectrometers, e.g. monochromators, acousto-optic tunable filters and push-broom hyperspectral imagers.
3.8.1 Wafers, thin films and multi-layer samples. Measuring the thickness of thin films or layered samples is very important. However, results can be variable. A paper by Sakurai and Kurokawa294 reported the results of a round robin study for layer thickness determination using reference-free XRF. Two samples were obtained both containing layers of gold, nickel and copper. A total of 11 companies participated in the study producing 15 datasets. A variety of instrumentation (WDXRF and EDXRF) utilising assorted X-ray tubes (Ag, Mo, Pd, Rh and W) was used in the study and the participants were allowed to use whatever operating condition they wanted. Data were collected and a couple of outliers identified using Grubb’s test. A comparison of XRF data with those obtained using ICP-OES, ICP-MS or ID-ICP-MS following dissolution of the individual layers was made. Results were in good agreement. The overall precision of the XRF data were 4.3–6.6%.

A paper by van der Heide295 emphasised the critical need for SIMS depth-profiling during the fabrication of complementary metal oxide semiconductors (CMOS). The high sensitivity, low LOD and acceptably rapid throughput make it the technique of choice for this application. The paper has no research per se, but it provides a good overview of the capabilities of SIMS and discusses the future applications, e.g. analysis of three dimensional structures. Topics covered include the existing SIMS depth-profiling approaches for 2D and 3D structures, in-fabrication SIMS deployment, data analysis tools for the in-fabrication SIMS derived depth profiles that use pattern recognition and hybrid characterisation approaches. The authors suggested that a hybrid of XRD and SIMS could potentially be viable.

The need for reference materials is as relevant to these sample types as any other, but thus far, there is a distinct paucity. Honicke et al.296 have reported the development of thin layer reference materials that have a total mass deposition at the ng level for analytes such as Ca, Cu, Fe, La, Mo, Ni, Pb and Pd. Two samples were prepared by physical vapour deposition on silicon nitride membranes. One sample had 10-times lower deposition than the other. Other materials were prepared that had single element films and others were prepared on silicon wafers. Samples were characterised using a multitude of techniques including three different synchrotron radiation beamlines at the BESSY II electron storage ring employing a reference-free XRF approach. Homogeneity of the samples was tested at the PO4 beamline at DESY. Good precision was obtained during the measurements, indicating good precision during manufacture.

The analysis of wafers or silicon substrates has been the focus of several papers because contamination of the wafers can have a huge effect on the quality and quantity of the end product. Mejstrik et al.297 discussed the re-installation of a TXRF instrument for silicon wafer surface analysis. A thorough description of the spectrometer as well as the robotic wafer manipulator was given. The authors prepared and validated a reference wafer with a known concentration of Ni contaminant. This was to be analysed after a set amount of time or after a set number of measurements. The wafer was then used as a reference for the analysis of some certified wafers. However, agreement with certified values was poor. The authors then used NIST 1640 spiked on to blank wafers as a second external check. Results for the Ni as well as Co, Cr, K and Mn were in good agreement with certified values, although the Cu, Fe and Zn data were in less good agreement. The authors concluded that the original certified wafers must have been contaminated during storage. A comparison of data obtained using the techniques of TXRF, TOF-SIMS, Deep Level Transient Spectroscopy and techniques used for the measurement of carrier lifetime was presented by Polignano et al.298 Various experiments were undertaken aiming to mimic assorted processes, including wet processes, ion implantation, surface contamination etc. Correlation between TXRF and TOF-SIMS data was pretty good with the TOF-SIMS being better at determining the light elements than the TXRF. The relative advantages and disadvantages of each of the techniques were discussed. It was concluded that no one technique was capable of measuring the surface contaminants and the diffusivity. Two papers have discussed the determination of O in silicon. One reported the use of SIMS299 and the other the use of LIBS.300 In the paper by Jakiela,299 several modifications to the instrument were required. A very high primary flux of Cs+ (14.5 keV at an intensity of ∼300 nA) was used, the turbomolecular vacuum pump was replaced with an ion pump, a titanium sublimation pump was also used to improve vacuum further (to 2 × 10−10 Torr when the ion beam was on) and the cryo-shield surrounding the sample chamber was cooled using liquid nitrogen. Once everything had been optimised, the LOD for O was 1015 atoms cm−3. This was, according to the authors, at least 10 times lower than that reported in any other application. Further studies elucidated oxygen indiffusion and outdiffusion during annealing in Ar and in vacuum. It was noted that the results are qualitatively and quantitatively different for float zone silicon compared with Czochralski-grown silicon. The paper by Davari300 described the LIBS analysis and experimental setup in detail. Two LIBS protocols were compared. One simply used the intensity at the O wavelength at 777.19 nm. This, however, yielded both poor calibration (R2 = 0.44) and sensitivity. The other method used both the 777.12 nm O line and a Si line at 781 nm. This internal standardisation procedure improved linearity of calibration significantly (R2 = 0.95) and led to less error. By using the Si internal standardisation, fluctuations in plasma excitation temperatures could also be accounted for. Under optimal conditions, the LOD was 8 ppm O, which was lower than that obtainable using a Standard FTIR method.

Grazing incidence XRF (GIXRF) has been reported for the analysis of thin films by three groups of workers. In one, Maderitsch et al.301 used it to analyse organic light emitting diodes. Samples were prepared such that a buffer layer was deposited on a substrate and then a hole transport layer followed by a host layer were deposited on that. Samples were analysed using a combination of the two non-destructive techniques of GIXRF and X-ray reflectometry (XRR), with the diffraction instrument having an additional fluorescence detector added. An added advantage of the two techniques is that they require virtually no sample preparation. The angle curves produced from the two techniques were processed using the software package called JGIXA. The S distribution in the layers was dependent on the sample preparation method of the host layer. In addition to determining the distribution of S, the combined GIXRF/XRR approach provided information such as layer thickness as well as surface and interface roughness. A second paper to combine GIXRF and XRR analysis was presented by Pessoa et al.302 who used the techniques to analyse telluride-based films that are often used for data storage devices and photovoltaic cells. The performance of both lab-based and synchrotron-based instrumentation was assessed for the characterisation of ultra-thin (<10 nm) titanium-tellurium films that had been prepared by physical vapour deposition and then capped with a 5 nm Ta passivation layer. Both setups were sufficiently sensitive to provide accurate chemical depth profiles, with data compared with those obtained using TOF-SIMS, XPS and plasma profiling TOF-MS. Inter-diffusion between the tellurium and tantalum cap was observed by all techniques. The third paper was presented by Yamada et al.303 who studied the alloying of gold-copper layers using an assortment of techniques including GIXRF, XRR, XRD and conventional XRF. The GIXRF was undertaken using a benchtop total reflection WDXRF instrument. The samples were prepared and then some were heat treated at 300 °C for one hour. The angle-dependent GIXRF profiles were very different between heated and non-heated samples. Theoretical calculations indicated that alloying was occurring, even though the temperature was so low. The other non-destructive techniques confirmed the data found using GIXRF.

Hermann et al.304 used calibration-free LIBS to analyse nickel – chromium – molybdenum thin films with thickness of 150 nm that had been prepared using pulsed laser deposition. The experimental setup was described in detail and the operating conditions used assumed to produce a plasma in local thermal equilibrium. These conditions were an atmospheric pressure of argon with an ultraviolet laser pulse of ns duration. Optimisation of the delay time between laser pulse and the detector gate identified times of 1 or 2 μs to be optimal. The data produced by the system were input to a simple algorithm enabling concentrations to be calculated. The data obtained were supported by data obtained using Rutherford backscattering spectrometry and energy dispersive X-ray spectroscopy. The analytical performance of the LIBS technique was superior to either of the other techniques used.

Depth-profile analysis of chromium – nickel metal thin films with a sub-100 nm depth resolution was achieved using near UV fs-LA-ICP-TOF-MS by Kaser et al.305 The laser beam was guided through a homogenisation scheme which was based on aperture-assisted diffraction and re-assembly of the beam by an optical lens. The setup was described in full with a helpful schematic being provided. The setup produced craters that were cylindrical in shape. Fluences between 0.6 and 1 J cm−2 were applied resulting in an ablation rate of 27 nm per pulse. It was possible to depth-profile nine alternating layers of nickel and chromium each of which had a depth of approximately 60 nm.

3.8.2 Solar cell materials. The analysis of solar cells or the copper indium gallium selenide (CIGS) thin films in solar cells is still receiving attention from some researchers. Two papers have used LIBS for such an analysis.306,307 In the first example, Choi et al.306 determined the effects of varying the laser spot size between 35 and 150 μm on the LIBS data produced. If the spectral lines are chosen correctly, then the signal intensity ratio rather than intensity alone should be used because it is nearly independent of laser spot size. Using the concentration ratio method the CIGS layer composition could be determined accurately, differing only 5% from data obtained using ICP-OES. The other paper to use LIBS for CIGS analysis was presented by Xiu et al.307 who optimised the operating parameters of the LIBS analysis and then provided both qualitative and quantitative data rapidly.

A LA-ICP-MS method of analysing silicon solar cells for contaminants such as Ag, Cu and Ni arising from plated metal contacts was reported by Colwell et al.308 Once prepared, the cells were heat-treated to 200 °C for up to 1000 hours prior to the analysis. The surface contamination was removed through a wet etching process involving mixtures of nitric and hydrochloric/hydrofluoric acids before LA-ICP-MS identified the analytes that had penetrated the silicon wafer. No suitable silicon reference material was available, so NIST 614 glass was used as a non-matrix-matched standard for calibration. A study of the laser operating conditions was undertaken which demonstrated that high energy laser pulses doubled crater depth and led to a build up of re-solidified Si around the crater. This, in turn, decreased analysis speed and led to a decrease in transport efficiency to the plasma. Another problem observed was a very high uncertainty (∼50%). This was hypothesised to arise through non-uniformity in cell preparation as well as the line-scanning method used for LA-ICP-MS analysis.

Jang et al.309 reported the quantitative analysis and band gap determination of CIGS absorber layers using a variety of instrumental techniques (XRF, LA-ICP-MS and ICP-OES). The bulk composition of the samples was determined using XRF and, after an acid digestion, ICP-OES. A fundamental parameters calibration approach was used to obtain the concentration ratios for XRF. Data obtained using femtosecond LA-ICP-MS were compared with those obtained using XRF. Elemental depth profiles were also obtained using SIMS and XPS. The band gap energy was calculated using a simple ratio method, i.e. Ga/(In + Ga).

The setup, operation and application of a laser induced ablation quadrupole mass spectrometer for the depth resolved-analysis of thin film solar cells and of hydrogenated/deuterated thin films deposited on glass was reported by Oelmann et al.310 After the introduction the authors described the setup in detail, giving schematic diagrams of the instrument. The idea of the instrument is that a picosecond laser operating at 355 nm ablates the sample and then the volatile gaseous products are analysed using the mass spectrometer. As with most laser-based depth-profile analyses, the same spot has to be sampled on numerous occasions. The spot was examined using surface profilometry and a confocal microscope to gauge depth per laser shot. The linear relation between the signal and the gas pressure within the ablation chamber simplified its calibration and reduced the uncertainties compared with other techniques. Very high vacuum was required to obtain sensitivity below the percent level. However, no sample preparation was required and the method is flexible with respect to the ablation rate. The picosecond laser pulse ensures that the thermal penetration depth is similar to the ablation rate, enabling a depth resolution of approximately 100 nm to be achieved. Data were compared with those obtained using LIBS, with good agreement being achieved.

3.8.3 Electronic equipment and devices. Numerous papers have been published that describe the analysis of lithium ion batteries or their components. The large majority use atomic spectrometry only as a peripheral or supportive tool and therefore do not bring any novelty to the field of atomic spectrometry. These papers will therefore not be discussed in this review. Several papers have discussed the use of LIBS for 3D mapping of the electrodes within the batteries. These have included two papers by Imashuku et al. who analysed the anode311 and the cathode materials.312 Both papers monitored the Li signal at 610.4 nm under a reduced argon atmosphere of 1000 Pa. In the first example, the graphite anode of a battery was analysed until a depth of 150 μm had been reached, i.e. the LIBS laser sampled from the same spot effectively drilling through the sample. Areas of both homogeneous and inhomogeneous Li content were observed after the charge and discharge processes. The areas of inhomogeneous Li distribution after the charge process were attributed to a preferentially reacted area in the anode. The inhomogeneous areas found after the charge–discharge process were thought to be attributable to the low desolvation reaction rate of the Li ions at the solid electrolyte interphase. The inhomogeneous Li distributions were consistent with the charge–discharge curves and the Li ion transfer mechanism. The second paper studied the Li distribution in the LiCoO2 cathode material.312 A calibration curve was constructed comprising varying amounts of lithium carbonate in cobalt oxide (Co3O4) giving ratios of Li to Co of 0, 0.01, 0.1, 0.3, 0.51, 0.62, 0.80 and 0.99. The distribution of Li in the cycled material as determined using LIBS was in close agreement with the data obtained using XAS, but the precision was less good. The conclusion of both papers was that LIBS was capable of semi-quantitative determination of Li distribution in the electrodes, but was far simpler to apply than XAS. A third paper describing the analysis of electrodes using LIBS was presented by Smyrek et al.313 This paper was focused more on the manufacture of structured nickel manganese cobalt electrodes through embossing or laser structuring or the unstructured electrode. However, the LİBS analysis and the instrumentation were described in full. The fully quantitative LIBS data were used to study chemical degradation mechanisms and the impact of the electrode architecture on the Li distribution.

The elemental mapping of lithium ion battery components was described in two papers by the same research group. The first used LA-ICP-MS314 and the second TXRF.315 In the paper by Evertz et al.,315 post mortem analysis of the electrolytes within the cells was undertaken using a novel calibration strategy. A specialist device capable of dispensing nanoliter volumes was employed to inject small volumes of electrolyte or standard onto quartz glass prior to the analysis. Three configurations were prepared: alternating pattern (30 electrolyte droplets, 30 standard droplets), centered pattern (28 electrolyte droplets, 13 standard droplets) and octagonal (24 electrolyte droplets and nine Standard droplets). Validation was achieved through an acid digestion followed by ICP-OES analysis. Recovery rates for the TXRF analyses were between 98 and 105%, which compared favourably to the 85–90% achieved using a conventional application procedure. The centered pattern gave the best results in terms of recovery and precision. However, there were some problems noted with the technique. This included the Co being below the LOD and the Ni concentration detected being three times that of Mn – even though they were known to be in the electrolyte at the same concentration. The paper by Harte et al.314 described the optimisation of a LA-ICP-MS method in terms of speed and frequencies and determined the effect on the spatial resolution of the mapping experiments. Higher scan speeds led to a decrease of 60% in time and gas consumption.

Two papers have discussed the analysis of mobile phone components. A paper by Bookhagen et al.316 discussed how 34 mobile phones from different manufacturers were disassembled and then the components acid digested using a microwave digestion system. Analysis using ICP-OES and ICP-MS was then undertaken on the digests. Method validation was achieved through the analysis of the CRM ERM (R)–EZ505 electronic scrap. Results for the eight certified elements were in reasonable agreement with certified values (Be, Ni and Pd were 100 ± 1%, Au, Cu and In were 100 ± 11% and Pt was 100 ± 20%). The problematic analyte was Ag that had poor recovery and precision (75 ± 35%). This was attributed to the presence of hydrochloric acid in the digestion mixture. In addition to the eight certified elements, a further 49 were also determined. Analysis of the printed circuit boards demonstrated that the most abundant elements in decreasing order were Cu, Fe, Si, Ni, Sn, Zn, Ba, Al, Cr and Ti. These 10 analytes accounted for approximately 80% of the weight of the board. The other paper described the use of LIBS to determine In in liquid crystal displays of mobile phones.317 Two calibration strategies were compared: conventional univariate calibration and multi-energy calibration. After phone disassembly the indium tin oxide films were mixed with a resin and pressed into a pellet. For the multi-energy calibration model, two pellets were pressed. One with sample, a standard and cellulose binder and the other with sample plus a blank (silica). The full procedure and the strategy behind each calibration model was given in the text. Results were compared with the standard method of microwave assisted acid digestion (Method EPA 3052) followed by ICP-OES detection. All of the LIBS data showed greatest accuracy where the analyte signal was normalised against the signal at the C wavelength at 193.09 nm. This had to be performed before the data were input to either calibration model. The LOD and LOQ for the univariate calibration were 0.3 and 1 mg kg−1, respectively, compared with the multi-energy calibration values of 2.1 and 7 mg kg−1. The In content ranged from 35 to 47 mg kg−1. The conclusion was that both strategies could usefully be used for recycling and e-waste management.

The analysis of computer hard disk or Random Access Memory components has been reported by Castro and Pereira318 and by Nolot et al.319 In the first example, over 50 hard disks from assorted manufacturers were collected and then disassembled so that both of the magnets (actuator and spindle) were isolated. These were then heated to remove the magnetism and ground using a knife mill before being sieved. Several acid digestion approaches (microwave assisted and hot block) using different acid concentrations were compared. No suitable CRM was available and so spike/recovery tests were undertaken. Overall, the treatment providing best results was using 100 mg of sample and a hot block using 7 mol L−1 nitric acid. The elements present at highest concentration were Fe, Nd and Pr. The analytical data were input to PCA and Hyperspectral Image to help classify the disks. The paper by Nolot319 described the use of TOF-SIMS, GIXRF and XRR to investigate the influence of variations in the deposition process of tantalum oxide on the tantalum oxide/metal structure of tantalum-based random access memory devices. Titanium nitride and nickel were tested as the bottom electrode material since they are both candidates to replace noble materials. All three techniques demonstrated significant inter-mixing between the titanium nitride and tantalum in the tantalum oxide titanium nitride stacks, even when optimised tantalum oxide deposition conditions were used. However, TOF-SIMS also demonstrated that if a H* plasma step was used during the atomic layer deposition process of the tantalum oxide, the oxidation of the Ni and the inter-mixing of tantalum oxide and Ni were both minimised. The X-ray-based techniques also indicated the influence of the H* plasma on the nickel – based samples when used with the model-based multi-layer combined analysis. It was concluded that GIXRF and XRR may be used as non-destructive and sensitive depth-profiling techniques.

The final sub-section of this part of the review is a mixture of other sample types that do not fit into any of the other sub-sections easily. Some of these are precursor materials, e.g. tetraethyl orthosilicate, were analysed for impurities using SF-ICP-MS by Lu et al.320 It was pointed out that such materials have to be of very high purity and therefore the contaminant levels must be very low. However, once dilution of the material has occurred so that it could be introduced to the ICP-MS instrument the concentration of the potential contaminants are likely to be at the pg L−1 level, which is too low to be measured reliably. A simple liquid–liquid extraction using isopropanol and water was used to isolate the analytes of interest from the matrix and actually provide a preconcentration factor of approximately 19. Although some interfering species were also extracted, these could be overcome by use of an appropriate resolution factor on the SF-ICP-MS instrument. Spike – recovery tests yielded acceptable data (94–113%) and precision was better than 9.46%. An interesting application was reported by Wang et al.321 who used LIBS to analyse high voltage transmission line insulators. Under normal circumstances, these can only be analysed during a power cut, when samples are removed, taken back to a laboratory and tested for sugars, bird droppings and heavy metal particulates. The rapid LİBS test that may be undertaken in situ, with minimal sample damage is therefore a clear advance in methodology. The study optimised the LIBS conditions (laser energy, delay time, etc.) and then the analytical data produced were analysed using PCA, k-means and partial least squares regression. These multivariate techniques gave a significant improvement in trace metal contamination analysis compared with normal calibration. Another LİBS application was described by Wang et al.322 who used it to determine the halide concentrations in the quantum dots CsPb(X)3 where X can be Br or Cl. These are materials that can be used to prepare nanometer scale semiconductors. Again, LIBS operating conditions were optimised and several samples with different Br/Cl ratio were analysed. Calibration curves correlating weight to LIBS emission intensity were obtained using mixtures of CuBr2 and CaCl2. The LIBS method showed better sensitivity than electron dispersive spectroscopy without the need for sample preparation.

3.9 Nanostructures

Atomic spectrometry, through techniques such as XRD, XPS, XRF, single nanoparticle (sNP) ICP-MS and ICP-OES has a key role in the characterisation and detection of NPs with over 150 papers published in the period covered by this ASU. However, most of the articles only mention the technique(s) used without any further analytical detail and as such are not discussed here.

In any growing analytical field method validation protocols and metrology tend to develop at a slower rate than the methodologies used, although this should not be the case and a metrological approach should be the starting point for method development. It is timely then that the current status of NP detection, with a focus on analytical metrology, has been reviewed by Lopez-Sanz et al.323 The review (with 139 cited references) proposes some metrological definitions for NPs and covers the analytical methods used for both their characterisation and detection. The latter was split into two areas; methods in which NPs are used to extract and/or pre-concentrate other target analytes and methods where the NP is the analyte. After a brief section on microscopy-based techniques the main focus is on the use of separation by CE, FFF and LC coupled with a variety of detectors including dynamic light scattering (DLS), multiangle light scattering (MALS), ICP-MS and UV. The use of these techniques reported over the past five years was summarised in a table (60 references) with many also being discussed in the text. The authors pointed out that maintaining sample integrity during both analyte characterisation studies and detection methodologies is, as for any analysis, still the key to providing analytical validity. However, this can prove more challenging because of the tendency of NPs to aggregate and the wide range of complex matrices, e.g. from consumer products to biota, which may contain them. It was also pointed out that whilst NPs are available as standards, often containing a stabilising agent, with a given mass concentration, particle concentration, size or size distribution these parameters may change upon dilution (or other use) into a different matrix. A further problem highlighted is the lack of available CRMs for method validation and that, from a strict metrological point of view, recovery studies are only admissible when the other alternatives are not available. Bustos et al. at NIST reported on the validation of sNP ICP-MS for routine measurements of nanoparticle size and number size distribution.324 The validation comprised three stages: (i) calibration based on the certified particle size of NIST SRM 8013 (Au NPs); (ii) comparison with HR-SEM data as a reference method (which is traceable to the SI) and (iii) evaluation of the uncertainty associated with the measurement of the found mean particle size to enable comparison of the sNP ICP-MS and HR-SEM methods. After method optimisation the particle size results obtained for NIST SRMs 8012 and 8013 by sNP ICP-MS were 27.2 ± 0.1 and 54.1 ± 0.1 nm, respectively. These data were in good agreement with those obtained using HR-SEM of 27.0 ± 0.1 and 54.7 ± 0.4 nm, respectively and also with the certified values of 26.8 ± 0.1 and 54.7 ± 0.4 nm, respectively. The particle size distributions obtained by both methods for the two SRMs were also in good agreement with the sNP ICP-MS data showing a broader tail in both sides of the distribution than the HR-SEM data. Both analytical approaches were also used to characterise commercial AuNP suspensions of three different sizes (30, 60, and 100 nm). The measurements revealed the existence of two distinct sub-populations of particles in the number size distributions for four of the 60 nm commercial suspensions. The paper also gave a detailed account of the uncertainty estimations and concluded that additional work is still needed to establish the metrological traceability of sNP ICP-MS for NP size determination. This is because of the assumption that all particles are spherical and that the TEM data supplied by commercial producers of NPs may be inadequate.

In single NP (sNP) ICP-MS analysis it is usual, due to instrumental limitations on the need for rapid data collection and processing, for only one isotope to be monitored during an analytical run. Two research groups however have explored the acquisition of multiple isotope data using sNP ICP-MS. The first of these papers, by Naasz et al. explored the capabilities of two quadrupole ICP-MS and two TOF-ICP-MS instruments for determining the composition, size distribution, and concentration of BiVO4, (Bi0.5Na0.5)TiO3, steel (IRMM-383 CRM) and Au-core/Ag-shell NPs.325 Both instrument types used could estimate the size of Au-core/Ag-shell NPs with uncertainties ranging from 25 to 50% relative. Measurements by the two quadrupole ICP-MS instruments generally had the lower uncertainty estimate. For the other multi-element nanoparticles, the particle sizes found were not in agreement with those obtained from analysis using SEM. The data presented for the particle number concentration appears acceptable for the Au/Ag NPs but again differences were reported with the SEM data for the other types of NP analysed. The particle mass concentration presented again shows poor agreement with the expected values. These differences between the expected and found data were attributed to aggregation and/or agglomeration of the NPs in solution prior to analysis. Thus, these results emphasise the need for maintaining sample integrity prior to analysis as highlighted in the previous paragraph. With regard to identifying multi-element NPs, the TOF instruments could determine the four different elements in the steel NP ion cloud simultaneously without a reduction in sensitivity. This was not the case for the two quadrupole ICP-MS instruments. This is, in part, because of the much greater number of data points that can be acquired during a single particle event which were calculated to be up to 15 for TOF-ICP-MS and 1 to 2 for quadrupole ICP-MS. The paper by Hirata et al. (in Japanese) on multi-isotope sNP ICP-MS used a MC-ICP-MS instrument, equipped with a high-time resolution data integration system, to measure the elemental composition, the 195Pt[thin space (1/6-em)]:[thin space (1/6-em)]194Pt ratio and particle size distribution of Pt and Au/Pt NPs.326 Sample introduction was by the laser ablation in a liquid technique, the Pt signals were measured using Daly counters whilst the Au signal was monitored on the electron multiplier of the instrument. The results obtained showed that the repeatability of the isotope ratio measurements was mainly controlled by the counting statistics of the signal. This suggested that effective data acquisition could be achieved under transient signals produced from the NPs. Both the measured NP size and the Au[thin space (1/6-em)]:[thin space (1/6-em)]Pt ratio of the NPs varied significantly with changes in the laser ablation conditions and possible mechanisms for these observed variations were discussed in the paper.

With all analytical techniques there is a continual quest to improve the methodologies and NP analysis is no exception. The use of an online micro-droplet calibration approach, with the aim of achieving matrix independent nanoparticle sizing, was reported by Hendriks et al. this year.327 To achieve this, a micro-droplet generator, which included a desolvation device, was inserted between the spray chamber outlet and the torch of the ICP-TOF-MS instrument. A calibrated video camera was used to determine the size of the micro-droplets introduced. Thus, conventionally aspirated NPs and the calibrants in the micro-droplets were introduced simultaneously to the instrument. After optimisation, which included sampling depth, nebuliser gas flow, acid related matrix effects and accounting for space charge effects, the method was applied to the determination of Au NPs in phosphate buffered saline (PBS). The PBS attenuated the Au signal, with a decrease in attenuation observed with decreasing PBS concentration, such that the measured mean particle size decreased, and the size distribution broadened with increasing PBS concentration. The authors pointed out that ‘real’ samples could be diluted prior to analysis to reduce matrix effects but that this is not always possible if the number of NPs in the original sample is low. In addition, it was also noted that matrix matching of the calibrants and samples could also be undertaken. It would have been of great interest to see the latter approach undertaken here and the results obtained with the micro-droplet calibration approach compared with calibrants prepared in PBS. For sNP analysis it is necessary to know the sample transport efficiency of the analyte to the plasma and this is usually measured by either analysing a NP standard or gravimetrically. It can also be advantageous to have a high transport efficiency value if the sample size is limited or if it has low analyte concentrations. The transport efficiencies of three different sample transport systems were assessed by Lin et al.328 These were: a high-performance concentric nebulizer with a heated cyclonic spray chamber and a three-stage Peltier-cooled desolvation system (HPCN), a conventional sample introduction system and a total consumption system. In each case the sample flow rate was estimated gravimetrically and for the HPCN and total consumption systems the sample was introduced via a sample loop of 60 and 100 μL, (with flow rates of 10 and 100 μL min−1), respectively. Commercially available Pt nanoparticles with a size of 70 nm were diluted to a concentration range of 60 to 1.2 × 105 particles per mL for the study. The transport efficiencies of the conventional sample introduction system, the total consumption system, and the HPCN were 10.6, 99.4, and 103.6%, respectively with the lower value for conventional nebulisation attributed to the smaller Sauter mean diameter obtained from this device. The size detection limits obtained were 11.6, 11.6, and 7.2 nm for the conventional sample introduction system, total consumption system and HPCN-APEX, respectively whilst the particle number LOD values were 126, 154 and 14, respectively. Interestingly the sensitivity, on a signal intensity per Pt mass basis was similar for all three systems.

The linear dynamic range of sNP can be limited by momentary signal pulse pile-ups at the electron multiplier detector. These can be mitigated by signal broadening from the use of a collision gas in ICP-MS.329 In this study by Rush et al. the simultaneous secondary electron multiplier was operated in both dual (pulse counting switching to analog) and pulse counting only modes. With no collision gas and the electron multiplier in dual mode, the linear response for Au NPs was from 20 to 150 nm whilst with He as a collision gas the linear range extended to 250 nm. In pulse counting mode, both with and without the He collision gas, the linear response was reduced to 20 to 60 nm. This is presumably due to detector overload from the increased signal from particles larger than 60 nm in diameter. It is now possible to acquire sNP data with a dwell time as short as 10 μs. The effect of using the short dwell times of 10, 20, 50, and 100 μs was investigated by Kana et al.330 It was found that zero signal values occurred inside the transient signal corresponding to an individual NP with the probability of this increasing with decreasing dwell time and NP size. This leads to the false detection of a larger number of smaller peaks with a consequent effect on the calculated particle size distribution. Therefore, a new approach to identifying the ‘true’ particle signal was developed which consisted of searching for an uninterrupted zero signal point sequence with a total length of 50 μs or 100 μs. Only the 100 μs delay between adjacent peaks resulted in values of the number of detected peaks, the most frequent peak areas and the width of peak area distribution that were virtually independent of the dwell time. The same research group then applied the method to the detection of Ag NPs in water samples collected from river Vltava in the Czechia.331 The Ag NP content ranged from 0.1 to 3.2 ng mL−1 with a particle size range of 32 to 1114 nm and a number concentration range of 340 to 1670 particles mL−1 with uncertainties in the latter two values in the range of 40 and 15%, respectively.

A number of reports on the use of separation techniques coupled with ICP-MS for the detection of NPs have been published in the period covered by this review. Bouzas-Ramos et al. developed a procedure, based on the measurement of a metal[thin space (1/6-em)]:[thin space (1/6-em)]sulfur ratio, for an assessment of the bioconjugation between CdSe/ZnS quantum dots and a monoclonal antibody with a known amino acid sequence.332 The CdSe/ZnS QDs were conjugated to rat antibody (Ab) via the amine groups of the Ab and asymmetric flow field flow fractionation (AF4)-ICP-MS was used as the separation and detection system. Oxygen was used as a reaction gas for S and Se measurements, as 48S16O+ and 80Se16O+ respectively, whilst 106Cd was measured directly. As the Cd and S content of the quantum dots and the S content of the antibody was known the measured signal from the AF4 peaks in the fractogram could be used to calculate the quantum dot to Ab ratio, with full details of these calculations given in the paper. The authors concluded that the proposed approach is general and could be applied to any type of NP containing S in the core, shell or on surface attached ligands and conjugated to any S containing biomolecules. Iron-carbohydrate NPs are used to treat iron-deficiency anaemia but regulatory acceptance of generic forms of this drug is hampered by lack of a direct method to monitor the fate of Fe NPs in clinical samples. An HPLC-ICP-MS based method has thus been developed by Neu et al. to address this.333 The separation of the NPs from serum samples was undertaken using two SEC columns (3 μm, 300 Å, 4.6 mm × 300 mm and 3 μm, 300 Å, 4.6 mm × 50 mm) in series with a mobile phase of 10 mmol L−1 Tris (pH 7.4) flowing at 0.4 mL min−1 in 20 min. This allowed the separation of the Fe drug from other iron binding species, e.g. transferrin, albumin, ferritin and citrate. The ICP-MS was operated in collision cell mode with He as the collision gas with a solution of transferrin, introduced by a post-column switching valve used to monitor signal drift at the beginning and end of each HPLC separation. Peak identification of the compounds eluted was by fraction collection and either matrix-assisted laser desorption ionisation (MALDI)-MS or ES-MS. The HPLC-ICP-MS LOD value for the Fe drug was 0.3 mg L−1. The transformations of Au NPs in a cell culture medium, Dulbecco’s Modified Eagle Medium, which contained 10% fetal bovine serum and antibiotics, were studied by Lopez-Sanz et al. using AF4-ICP-MS with the AF4 carrier solution being 0.01% sodium dodecyl sulfate.334 The AF4-ICP-MS fractograms showed that the culture medium induced oxidation of the Au NPs to ionic Au which was subsequently conjugated with proteins or other matrix components. An increase in Au NP size was also observed which the authors suggested could be due to the formation of a protein corona or to an aggregation/agglomeration process. Most reports on NP detection cover aqueous environmental or biological samples but this year sees a report by Ruhland et al. of the FFFF-ICP-MS detection of natural NPs present in a gas condensate sample using tetrahydrofuran as the carrier liquid.87 The results obtained confirmed the presence of various NPs and colloids, some containing aromatic compounds as well as various metals, including Hg in the gas condensate. Offline sNP ICP-MS was used to confirm the presence of the Hg-containing NPs which were identified as HgS by STEM-EDX. Other particulate matter containing Al, As, Cd, Co, Cu, Fe, Mn, Pb, P, S, Se, Ti, V and Zn was also identified which could make the upstream use of the gas condensate problematic if, for example, catalysis is involved. Tan et al. coupled a differential mobility analyser with an ICP-MS instrument operated in sNP mode to determine the geometry of Au nanorods.335 The differential mobility analyser step size was 2 nm with a step dwell time of 31 s and samples were introduced via electrospray. Coupling of the differential mobility analyser to the ICP-MS instrument was via a gas exchange device, utilised to solve the incompatibility of air in the plasma, connected by conductive silicone tubing achieving a gas exchange efficiency of about 90%. Using this setup Au nanorods in the size range 12 × 50 (d × L) nm to 38 × 135 nm were successfully identified with each analysis taking 150 s. A full explanation of the theory and calculations required is given in the text.

Silver NPs are widely used due to their anti-microbial properties. A method was developed by Rujido-Santos et al., with an emphasis on sample integrity during Ag NP extraction, to quantify them in moisturising creams.336 The Ag NPs were separated from the samples using ultrasonic assisted extraction. One hundred mg of sample was suspended in 20 mL of methanol and the sample tube placed in an ice bath, the power level set to 60% (total power not given), and subjected to 15 × 59 s sonication cycles with a delay of 59 s between each cycle. For all but one sample sonication resulted in a clear extract while the remaining sample was centrifuged prior to analysis of the supernatant. Samples were diluted 40 fold in 1% v/v glycerol and further sonicated for 5 minutes before analysis using sNP ICP-MS. The RSD of the procedure (given by the analysis of 11 extracts from one sample) was 5%. The spike recovery for Ag NPs of 20, 40 and 60 nm ranged between 90 and 109%. The LOQ for the Ag NP concentration was 8.25 × 105 Ag NPs g−1 the size LOD in size was within the 5–13 nm range depending on the calculation method used. Finally, moisturising creams prescribed for atopic dermatitis and on general sale were analysed for total Ag and for Ag NPs. Each of the three creams analysed was found to contain NPs with mean sizes of 35, 52 and 91 nm and the Ag NP content was found to be between 0.2 and 1.1% of the total Ag content which ranged from 0.001 to 2.3 μg g−1.

Table 6 shows other applications of nanomaterial characterisation presented in the literature during the time period covered by this ASU.

Table 6 Applications of nanomaterial characterisation
Analyte Matrix Technique Comments Ref.
Ag+, Ag NPs Odour remover spray and anti-bacterial spray ICP-OES Analytes adsorbed onto a silica gel functionalised with 3-aminopropyltriethoxysilane. The Ag+ was eluted with thiourea whereas the Ag NPs were oxidised to Ag+ then eluted with thiourea 337
Ag Phosphate buffered saline leachates from silver NP coated alloys comprising titanium, aluminium and vanadium XRD, FT-IR, SEM, AFM, ICP-MS Dispersion of AgNPs on the surface of Ti6Al4V and Ti6Al4V modified with a titania nanotube layer using a chemical vapour deposition method employing {Ag5(O2CC2F5)(5)(H2O)(3)}. After 14 days of immersion of the nanocomposite material in a phosphate buffered saline the Ag content in the saline was 2.5 mg L−1 338
Ag+ and Ag NPs Cell culture medium, acetone, sodium chloride solutions and alcohol ICP-OES, XRD, TEM, UV/vis Synthesis of <10 nm Ø Ag NPs from AgNO3 by bioreduction with Chlamydomonas reinhardtii. The Ag NPs were stable over time in the cell culture media, acetone, NaCl (9 and 27 g L−1) and 70% reagent alcohol solutions for >300 days at 4 °C 339
Ag Catechin, catechin-borax or polycatechin NPs containing silver UV/vis, DLS, XRD, TEM, ICP-MS AgNPs synthesised from AgNO3 and catechin borax or polycatechin. The mean NP sizes were Polycatechin 8.5 nm, catechin-borax 18.4 nm and catechin 42.3 nm. Anti-microbial efficacy assessed against both Gram +ve and −ve bacteria, increased with decreasing NP size. A solution of 1.25 μg Ag mL−1 of polycat@AgNPs reduced biofilm viability and mass by 99.9% and 99.1%, respectively 340
Ag Silver nanoparticles LA-ICP-MS Japanese language paper. Size distribution determined using an ArF laser with nanosecond pulses. Results obtained compared favourably with solution nebulisation data for NP sizes ranging between 10 and 100 nm Ø. The developed LA-ICP-MS technique would be suitable for Ag NP mapping in tissue samples 341
Ag and Au Silver and gold NPs UV/vis, dynamic light scattering (DLS), FT-IR, XRD, TEM, EDX, ICP-MS Synthesis of colloidal AuNPs and bimetallic Ag/Au alloy nanoparticles using starch as a reducing and capping agent. Mean particle sizes of 28.5 and 9.7 nm for AuNPs and Ag/AuNPs, respectively. Dose-dependent anti-microbial action of NPs with antibiotic-resistant bacterial strains. NPs showed cytocompatibility towards human dermal fibroblast. Dose-dependent anti-cancer effect found for human melanoma cells 342
Au Certified gold nanoparticles sNP ICP-MS Chinese language paper. Discussion on the effects of dwell time and settling time on the analysis of nanoparticles using sNP ICP-MS. Au NPs from NIST and NCNST (30, 40 and 60 nm) analysed. Shorter dwell and settling times improved signal to noise ratio and “determination efficiency”. The optimal conditions were a dwell time of 0.05 ms and a settling time of 0. Experimentally found and certified sizes agreed. The LOD of size and number concentration of Au NPs were 8 nm and 1.1 × 105 particles L−1, respectively 343
Au Gold nanoparticles FFFF-ICP-MS Separation and detection of Au NPs with different coatings, tannic acid and citrate and stabilising agents (polyethylene glycol, polyvinylpyrrolidone and branched polyethylene imine 344
Co, Cu, Mg, Ni, Zn CuO NPs and CuO NPs doped with varying amount of Co, Mg, Ni and Zn ICP-OES, FT-IR, XRD, XPS, TEM, SEM, BET Doping of CuO NPs to modify magnetic properties. Characterisation using a range of techniques. Concentration and number of dopants shown to have a crucial role in structural, morphological and magnetic properties of CuO nanostructures 345
Fe Magnetic arginine-functionalised polypyrrole nanocomposite FTIR, XRD, EDX, TEM, BET, XPS and IC-ICP-MS Nanocomposite fabricated by in situ polymerisation of pyrrole monomer in the presence of arginine and Fe3O4 NPs for use as CrVI sorbent from mine leachates. Maximum absorption capacity of 320 mg g−1 was obtained at 25 °C and pH 2 346
Fe Fe NPs embedded in Citrus limetta peel ICP-MS, XRD, XPS, TEM NP size 4–70 nm. Used for reduction of CrVI to CrIII with Fe NPs oxidised to FeII and FeIII. One g of material reduced 33 mg of CrVI 347
Fe Iron NPs functionalised with 3-mercaptopropionic acid ICP-OES Fe3O4 NPs prepared from FeCl2, FeCl3 and NH4OH in solution deoxygenised with N2 gas and at 70 °C. Then functionalised with 3-mercaptopropionic acid in toluene. Adsorption of Ag+, Hg2+ and Pb2+ from aqueous solution at a pH > 4 348
Fe and Pt FePt nanocrystals XRD, Small Angle X-ray Scattering (SAXS), TEM, ICP-OES, ICP-MS Non-aqueous sol–gel synthesis of FePt nanoparticles in the absence of in situ stabilizers achieved by using PtII acetylacetonate, FeIII acetylacetonate, benzyl ether, benzylamine, hexamethylenediamine, 1,2-hexadecanediol, oleic acid, oleylamine and triethylene glycol 349
PEGylated I NPs Mouse serum HPLC-TQ-ICP-MS, DLS, Micro-CT NMR PEGylated I NPs synthesised from NaI, polyethylene glycol-b-polystyrene and polyvinyl phenol in dimethylsulfoxide. The NPs were spiked into mouse serum and then quantified using HPLC-ICP-MS. A polymeric RP column (150 × 0.3 mm ID, 8 μm), mobile phase of 10 mmol L−1 ammonium acetate[thin space (1/6-em)]:[thin space (1/6-em)]methanol (98[thin space (1/6-em)]:[thin space (1/6-em)]2) at 5 μL min−1 was employed for the separation. A LOD of 2 μg mL−1 was obtained with the high value attributed to endogenous I complexed with serum proteins 350
Se NPs Selenium nanoparticles in an organic preparation matrix MIP-OES Synthesis of Se NPs using SeIV and either glucose, ascorbic acid or yeast. Reactions monitored online using photochemical vapour generation with 15% acetic acid. A LOD of 0.52 mg L−1 was achieved although matrix effects from the reaction mixture were observed 351
Sn Tin on SiO2 NPs FFFF, ICP-MS Collected fractions from FFFF analysed for Sn content using ICP-MS. A 10 kDa polyethersulfone membrane with 0.25 mmol L−1 ammonium carbonate as carrier solution provided a good separation with minimal particle–membrane interaction. Tin adsorption onto silica NPs Increased with decreasing NP size, 98.5%, 44.9%, and 6.5% for 60 nm, 100 nm and 200 nm NPs, respectively, when 40 μL of SnCL2 (100 mg L−1) was added to 200 μL silica NPs (10 mg mL−1) 352
Zn ZnO nanorod and nanowire arrays GIXRD, SEM, EDX, ICP-OES Nanorods and nanowires synthesised using a two-step sol–gel/hydrothermal process from zinc acetate dihydrate and methanolic NaOH at 60 °C. Apoptotic assay of PC12 cells showed greater cell adhesion to nanowires than to nanorods 353
Various (7) CdSe/ZnS, InP/ZnS, and CuInS/ZnS quantum dots UV/vis, TEM, ICP-MS, zeta sizer and FTIR Organic-to-water phase transfer behaviour CdSe/ZnS, InP/ZnS, and CuInS/ZnS quantum dots, coated with three different ligands: oleic acid, oleylamine and octadecylamine were compared under different environmental conditions including humic acid content, pH and ionic strength. The transfer rate increased as pH lowered and in the presence humic acids 354


4 Conflicts of interest

There are no conflicts to declare.

5 Glossary of terms

2DTwo dimensional
3DThree dimensional
AASAtomic absorption spectrometry
AESAuger electron spectrometry
AFFFAsymmetric field flow fractionation
AF4Asymmetric flow-field flow fractionation
AFSAtomic fluorescence spectrometry
AFMAtomic force microscopy
AMSAccelerator mass spectrometry
ANOVAAnalysis of variants
APMAtom probe microscopy
APTAtom probe tomography
ASTMAmerican Society for Testing of Materials
ATRAttenuated total reflection
BCRCommunity bureau of reference
CCDCharge coupled device
CECapillary electrophoresis
CIGSCopper indium gallium selenide
CRMCertified reference material
CPFAASCollinear photofragmentation atomic absorption spectrometry
CSContinuum source
CTComputerised tomography
CVCold vapour
CXRFCoincidence X-ray fluorescence
DADiscriminant analysis
DLSDynamic light scattering
DLTVDiode laser thermal vaporisation
DRCDynamic reaction cell
DSCDifferential scanning calorimetry
EBSElastic back scattering spectroscopy
EDAXEnergy dispersive X-ray analysis
EDSEnergy dispersive spectrometry
EDTAEthylenediaminetetraacetic acid
EDXRDEnergy dispersive X-ray diffraction
EDXRFEnergy dispersive X-ray fluorescence
ELMExtreme learning machine
EPMAElectron probe microanalysis
ERDAElastic recoil detection analysis
ESI-MSElectrospray ionisation mass spectrometry
ETAASElectrothermal atomic absorption spectrometry
ETVElectrothermal vaporisation
EXAFSExtended X-ray absorption fine structure
FAASFlame atomic absorption spectrometry
FFFFFlow field flow fractionation
FIFlow injection
FI-CVGFlow injection chemical vapour generation
FTIRFourier transform infrared
FWHMFull width at half maximum
GA-KELMGenetic algorithm-kernel extreme learning machine
GCGas chromatography
GD-MSGlow discharge mass spectrometry
GD-OESGlow discharge optical emission spectrometry
GI-SAXSGrazing incidence small angle X-ray scattering
GIXRDGrazing incidence X-ray diffraction
GIXRFGrazing incidence X-ray fluorescence
HGHydride generation
HPLCHigh performance liquid chromatography
HR-CS-AASHigh resolution continuum source atomic absorption spectrometry
hTISISHeated torch integrated sample introduction system
IAEAInternational Atomic Energy Agency
IBAIon beam analysis
ICAIndependent component analysis
ICPInductively coupled plasma
ICP-MSInductively coupled plasma mass spectrometry
ICP-OESInductively coupled plasma optical emission spectrometry
ICP-QMSInductively coupled plasma quadrupole mass spectrometry
ICP-TOF-MSInductively coupled plasma time-of-flight mass spectrometry
IDIsotope dilution
IL-DLLMEIonic liquid-dispersive liquid–liquid microextraction
IPInstitute of petroleum
IRMSIsotope ration mass spectrometry
ISOInternational Organisation for Standardisation
LALaser ablation
LASILLaser ablation of sample in liquid
LCLiquid chromatography
LEISLow energy ion scattering
LIBSLaser induced breakdown spectrometry
LIFLaser induced fluorescence
LIPSLaser induced plasma spectroscopy
LODLimit of detection
LOQLimit of quantification
LTELocal thermal equilibrium
MALDI-TOFMatrix-assisted laser desorption ionisation time-of-flight
MALSMultiangle light scattering
MCMulticollector
MEISMedium energy light scattering
MHCDMicro hollow glow discharge
MIPMicrowave induced plasma
MIP-AESMicrowave plasma atomic emission spectrometry
MSMass spectrometry
MCR-ALSMulti curve resolution-alternating least squares
MWTNMicrowave thermal nebuliser
NAANeutron activation analysis
NAARNeutron activation autoradiography
Nd:YAGNeodymium doped-yttrium aluminium garnet
Nd:YLFNeodymium doped-yttrium lithium fluoride
NDNeutron diffraction
NEXAFSNear edge X-ray fine structure
NISTNational Institute of Standards and Technology
NMRNuclear magnetic resonance
NRANuclear reaction analysis
OESOptical emission spectrometry
PBSPhosphate buffered saline
PCAPrincipal component analysis
PCRPrincipal component regression
PDAPhase-doppler anemometry
PETPolyethylene terephthalate
PGAAPrompt gamma neutron activation analysis
PGMPlatinum group metals
PIGEParticle induced gamma ray emission
PIXEParticle-induced X-ray emission
PLSPartial least squares
PLSDAPartial least squares discriminant analysis
PLSDAVIPartial least squares discriminant analysis with variable importance
PLSRPartial least squares regression
ppbParts per billion
ppmParts per million
PSDAParticle size distribution analysis
PVGPhotochemical vapour generation
RBSRutherford backscattering spectrometry
RDARegularised discriminant analysis
REERare earth elements
rfRadiofrequency
RIMSResonance ionisation mass spectrometry
RMSECVRoot mean square error of cross validation
RSDRelative standard deviation
SECSize exclusion chromatography
SEMScanning electron microscopy
SEM-EDSScanning electron microscopy-energy dispersive spectrometry
SFSector field
SHRIMPSensitive high resolution ion microprobe
SIBSSpark induced breakdown spectrometry
SIFT-MSSelected ion flow tube mass spectrometry
SIMCASoft independent modelling of class analogy
SIMSSecondary ion mass spectrometry
SPSingle particle
SRSynchrotron radiation
SRMStandard reference material
SRSSynchrotron radiation source
SXRFSynchrotron X-ray fluorescence
SVRSupport vector regression
STXMScanning transmission X-ray microscopy
TETrace element
TEMTransmission electron microscopy
TGAThermogravimetric analysis
TIMSThermal ionisation mass spectrometry
TOFTime of flight
TLCThin layer chromatography
TPRTemperature programmed reduction
TXRFTotal reflection X-ray fluorescence
UOPUniversal oil products standards
USGSUnited States geological survey
UV/visUltraviolet-visible
VOCVolatile organic carbon
VUVVacuum ultraviolet
WC-AESTungsten coil atomic emission spectrometry
WDXRFWavelength dispersive X-ray fluorescence
WEEEWaste electrical and electronic equipment
XAFSX-ray absorption fine structure spectrometry
XANESX-ray absorption near-edge structure
XASX-ray absorption spectroscopy
XPSX-ray photoelectron spectroscopy
XRDX-ray diffraction
XRFX-ray fluorescence
XRPDX-ray powder diffraction
XRRX-ray reflectometry

6 References

  1. S. Carter, R. Clough, A. Fisher, B. Gibson, B. Russell and J. Waack, J. Anal. At. Spectrom., 2018, 33(11), 1802–1848 RSC.
  2. R. Clough, C. F. Harrington, S. J. Hill, Y. Madrid and J. F. Tyson, J. Anal. At. Spectrom., 2018, 33(7), 1103–1149 RSC.
  3. E. H. Evans, J. Pisonero, C. M. M. Smith and R. N. Taylor, J. Anal. At. Spectrom., 2018, 33(5), 684–705 RSC.
  4. J. R. Bacon, O. T. Butler, W. R. L. Cairns, J. M. Cook, R. Mertz-Kraus and J. F. Tyson, J. Anal. At. Spectrom., 2019, 34(1), 9–58 RSC.
  5. A. Taylor, N. Barlow, M. P. Day, S. Hill, N. Martin and M. Patriarca, J. Anal. At. Spectrom., 2019, 34(3), 426–459 RSC.
  6. C. Vanhoof, J. R. Bacon, A. T. Ellis, L. Vincze and P. Wobrauschek, J. Anal. At. Spectrom., 2018, 33(9), 1413–1431 RSC.
  7. H. B. Fu, Z. B. Ni, H. D. Wang, J. W. Jia and F. Z. Dong, Plasma Sci. Technol., 2019, 21(3), 034001 CrossRef CAS.
  8. R. Noll, C. Fricke-Begemann, S. Connemann, C. Meinhardt and V. Sturm, J. Anal. At. Spectrom., 2018, 33(6), 945–956 RSC.
  9. L. Jolivet, M. Leprince, S. Moncayo, L. Sorbier, C. P. Lienemann and V. Motto-Ros, Spectrochim. Acta, Part B, 2019, 151, 41–53 CrossRef CAS.
  10. H. Kim, S. H. Nam, S. H. Han, S. Jung and Y. Lee, Opt. Laser Technol., 2019, 112, 117–125 CrossRef CAS.
  11. M. Singh and A. Sarkar, J. Appl. Spectrosc., 2018, 85(5), 962–970 CrossRef CAS.
  12. J. H. Yang, X. M. Li, H. L. Lu, J. W. Xu and H. X. Li, J. Anal. At. Spectrom., 2018, 33(7), 1184–1195 RSC.
  13. Y. G. Mei, S. S. Cheng, Z. Q. Hao, L. B. Guo, X. Y. Li, X. Y. Zeng and J. L. Ge, Plasma Sci. Technol., 2019, 21(3), 034020 CrossRef CAS.
  14. X. M. Li, H. L. Lu, J. H. Yang and F. Chang, Plasma Sci. Technol., 2019, 21(3), 034015 CrossRef CAS.
  15. Y. M. Guo, L. B. Guo, Z. Q. Hao, Y. Tang, S. X. Ma, Q. D. Zeng, S. S. Tang, X. Y. Li, Y. F. Lu and X. Y. Zeng, J. Anal. At. Spectrom., 2018, 33(8), 1330–1335 RSC.
  16. J. J. Lin, X. M. Lin, L. B. Guo, Y. M. Guo, Y. Tang, Y. W. Chu, S. S. Tang and C. J. Che, J. Anal. At. Spectrom., 2018, 33(9), 1545–1551 RSC.
  17. S. Shin, Y. Moon, J. Lee, H. Jang, E. Hwang and S. Jeong, Plasma Sci. Technol., 2019, 21(3), 034011 CrossRef CAS.
  18. S. C. Xie, T. Xu, G. H. Niu, W. L. Liao, Q. Y. Lin and Y. X. Duan, J. Anal. At. Spectrom., 2018, 33(6), 975–985 RSC.
  19. Y. Qiu, J. Wu, X. W. Li, T. Liu, F. Xue, Z. F. Yang, Z. Zhang and H. Yu, Spectrochim. Acta, Part B, 2018, 149, 48–56 CrossRef CAS.
  20. J. Wu, H. Yu, Y. Qiu, Z. Zhang, T. Liu, F. Xue, W. W. Yu, X. W. Li and A. C. Qiu, J. Phys. D: Appl. Phys., 2019, 52(1), 014006 CrossRef.
  21. C. Ke, Y. Li, X. Liu, F. J. Gou, X. R. Duan and Y. Zhao, Fusion Eng. Des., 2018, 136, 1647–1652 CrossRef CAS.
  22. S. Z. Lu, M. R. Dong, Q. F. Chen, J. W. Huang, Y. S. Yu and J. D. Lu, Spectrochim. Acta, Part B, 2019, 151, 1–11 CrossRef CAS.
  23. S. Z. Lu, S. Shen, J. W. Huang, M. R. Dong, J. D. Lu and W. B. Li, Spectrochim. Acta, Part B, 2018, 150, 49–58 CrossRef CAS.
  24. J. W. Huang, M. R. Dong, S. Z. Lu, W. B. Li, J. D. Lu, C. Y. Liu and J. H. Yoo, J. Anal. At. Spectrom., 2018, 33(5), 720–729 RSC.
  25. B. C. Barlow, A. Situm, B. Guo, X. X. Guo, A. P. Grosvenor and I. J. Burgess, Corros. Sci., 2018, 144, 198–206 CrossRef CAS.
  26. A. Situm, X. X. Guo, B. C. Barlow, B. Guo, I. J. Burgess and A. P. Grosvenor, Corros. Sci., 2018, 145, 35–46 CrossRef CAS.
  27. Z. Q. Hao, L. Liu, M. Shen, R. Zhou, J. M. Li, L. B. Guo, X. Y. Li, Y. F. Lu and X. Y. Zeng, J. Anal. At. Spectrom., 2018, 33(9), 1564–1570 RSC.
  28. H. B. Fu, H. D. Wang, J. W. Jia, Z. B. Ni and F. Z. Dong, Appl. Spectrosc., 2018, 72(8), 1183–1188 CrossRef CAS PubMed.
  29. Z. Q. Hao, L. Liu, R. Zhou, Y. W. Ma, X. Y. Li, L. B. Guo, Y. F. Lu and X. Y. Zeng, Opt. Express, 2018, 26(18), 22926–22933 CrossRef CAS PubMed.
  30. Q. Zeng, C. Y. Pan, T. Fei, X. K. Ding, S. B. Wang and Q. P. Wang, J. Appl. Spectrosc., 2018, 85(5), 817–822 CrossRef.
  31. L. M. Cabalin, T. Delgado, J. Ruiz, D. Mier and J. J. Laserna, Spectrochim. Acta, Part B, 2018, 146, 93–100 CrossRef CAS.
  32. A. Hegetschweiler, O. Borovinskaya, T. Staudt and T. Kraus, Anal. Chem., 2019, 91(1), 943–950 CrossRef CAS PubMed.
  33. E. S. Steenstra, J. Berndt, S. Klemme and W. van Westrenen, J. Anal. At. Spectrom., 2019, 34(1), 222–231 RSC.
  34. A. Wada, N. Nonose, M. Ohata and T. Miura, Talanta, 2018, 189, 289–295 CrossRef CAS PubMed.
  35. Q. D. Zeng, F. Deng, Z. H. Zhu, Y. Tang, B. Y. Wang, Y. J. Xiao, L. B. Xiong, H. Q. Yu, L. B. Guo and X. Y. Li, Plasma Sci. Technol., 2019, 21(3), 034006 CrossRef CAS.
  36. M. C. Cui, Y. Deguchi, Z. Z. Wang, S. Tanaka, Y. Fujita and S. D. Zhao, Appl. Spectrosc., 2019, 73(2), 152–162 CrossRef CAS PubMed.
  37. J. M. Li, M. L. Xu, Q. X. Ma, N. Zhao, X. Y. Li, Q. M. Zhang, L. Guo and Y. F. Lu, Talanta, 2019, 194, 697–702 CrossRef CAS PubMed.
  38. C. Y. Pan, J. He, G. Q. Wang, X. W. Du, Y. B. Liu and Y. H. Su, Plasma Sci. Technol., 2019, 21(3), 034012 CrossRef CAS.
  39. L. Y. Zhan, X. H. Ma, W. Q. Fang, R. Wang, Z. S. Liu, Y. Song and H. F. Zhao, Plasma Sci. Technol., 2019, 21(3), 034018 CrossRef CAS.
  40. T. O. Owolabi and M. A. Gondal, J. Intell. Fuzzy Syst., 2018, 35(6), 6277–6286 Search PubMed.
  41. H. Sattar, L. Y. Sun, M. Imran, R. Hai, D. Wu and H. B. Ding, Plasma Sci. Technol., 2019, 21(3), 034019 CrossRef.
  42. R. Yuan, Y. Tang, Z. H. Zhu, Z. Q. Hao, J. M. Li, H. Y. Yu, Y. X. Yu, L. B. Guo, X. Y. Zeng and Y. F. Lu, Anal. Chim. Acta, 2019, 1064, 11–16 CrossRef CAS PubMed.
  43. W. J. Lu, Z. H. Zhu, Y. Tang, S. X. Ma, Y. W. Chu, Y. Y. Ma, Q. D. Zeng, L. B. Guo, Y. F. Lu and X. Y. Zeng, Opt. Express, 2018, 26(23), 30409–30419 CrossRef CAS PubMed.
  44. T. Takahashi, B. Thornton, T. Sato, T. Ohki, K. Ohki and T. Sakka, Appl. Opt., 2018, 57(20), 5872–5883 CrossRef CAS PubMed.
  45. V. N. Lednev, P. A. Sdvizhenskii, R. D. Asyutin, R. S. Tretyakov, M. Y. Grishin, A. Y. Stavertiy, A. N. Fedorov and S. M. Pershin, Opt. Express, 2019, 27(4), 4612–4628 CrossRef CAS PubMed.
  46. V. N. Lednev, P. A. Sdvizhenskii, M. Y. Grishin, M. A. Davidov, A. Y. Stavertiy, R. S. Tretyakov, M. V. Taksanc and S. M. Pershin, Spectrosc. Lett., 2018, 51(4), 184–190 CrossRef CAS.
  47. V. N. Lednev, P. A. Sdvizhenskii, R. D. Asyutin, R. S. Tretyakov, M. Y. Grishin, A. Y. Stavertiy and S. M. Pershin, Addit. Manuf., 2019, 25, 64–70 CrossRef CAS.
  48. E. Mal, R. Junjuri, M. K. Gundawar and A. Khare, J. Anal. At. Spectrom., 2019, 34(2), 319–330 RSC.
  49. T. Q. Li, Z. Y. Hou, Y. T. Fu, J. L. Yu, W. L. Gu and Z. Wang, Anal. Chim. Acta, 2019, 1058, 39–47 CrossRef CAS PubMed.
  50. X. Y. He, R. H. Li and F. J. Wang, Plasma Sci. Technol., 2019, 21(3), 034005 CrossRef CAS.
  51. X. Y. He, B. Q. Chen, Y. Q. Chen, R. H. Li and F. J. Wang, J. Anal. At. Spectrom., 2018, 33(12), 2203–2209 RSC.
  52. Y. R. Wang, Y. H. Jiang, X. Y. He, Y. Q. Chen and R. H. Li, Spectrochim. Acta, Part B, 2018, 150, 9–17 CrossRef CAS.
  53. L. Huang, D. Beauchemin and C. Dalpe, J. Anal. At. Spectrom., 2018, 33(10), 1784–1789 RSC.
  54. K. Ido, H. Obayashi, Y. B. Zhu, T. Hirata, A. Hokura, N. Nonose and K. Inagaki, Anal. Sci., 2018, 34(6), 693–699 CrossRef CAS PubMed.
  55. G. P. Ma, X. C. Duan and J. S. Sun, Spectrochim. Acta, Part B, 2018, 149, 57–61 CrossRef CAS.
  56. N. S. Medvedev, O. V. Lundovskaya and A. I. Saprykin, Microchem. J., 2019, 145, 751–755 CrossRef CAS.
  57. L. Fu, S. Y. Shi, X. Q. Chen and H. L. Xie, Microchem. J., 2018, 139, 236–241 CrossRef CAS.
  58. P. Phukphatthanachai, J. Vogl, H. Traub, N. Jakubowski and U. Panne, J. Anal. At. Spectrom., 2018, 33(9), 1506–1517 RSC.
  59. E. Castellon, P. P. Martinez, J. Alvarez, F. Bredice, F. Borges, M. V. Muniz, C. Sanchez-Ake, V. Palleschi and R. Sarmiento, Spectrochim. Acta, Part B, 2018, 149, 229–235 CrossRef CAS.
  60. A. H. Galmed, C. Steenkamp, I. Ahmed, A. du Plussis, H. von Bergmann, M. A. Harith and M. Maaza, Appl. Phys. B: Lasers Opt., 2018, 124(12), 225 CrossRef.
  61. T. Warchilova, V. Dillingerova, R. Skoda, T. Simo, O. Matal, T. Vaculovic and V. Kanicky, Spectrochim. Acta, Part B, 2018, 148, 113–117 CrossRef CAS.
  62. A. Botto, B. Campanella, S. Legnaioli, M. Lezzerini, G. Lorenzetti, S. Pagnotta, F. Poggialini and V. Palleschi, J. Anal. At. Spectrom., 2019, 34(1), 81–103 RSC.
  63. V. Lazic, M. Vadrucci, R. Fantoni, M. Chiari, A. Mazzinghi and A. Gorghinian, Spectrochim. Acta, Part B, 2018, 149, 1–14 CrossRef CAS.
  64. S. Robotti, P. Rizzi, C. Soffritti, G. L. Garagnani, C. Greco, F. Facchetti, M. Borla, L. Operti and A. Agostino, Spectrochim. Acta, Part B, 2018, 146, 41–49 CrossRef CAS.
  65. R. N. S. Sodhi, P. Brodersen, S. Boccia, A. Anastassiades and C. Zaccagnino, J. Vac. Sci. Technol., B: Nanotechnol. Microelectron.: Mater., Process., Meas., Phenom., 2018, 36(3), 03F104 Search PubMed.
  66. I. Ortega-Feliu, S. Scrivano, B. Gomez-Tubio, F. J. Ager, M. L. de la Bandera, M. A. Respaldiza, A. D. Navarro and C. San Martin, Microchem. J., 2018, 139, 401–409 CrossRef CAS.
  67. F. Lopes, R. J. C. Silva, M. F. Araujo, V. H. Correia, L. Dias and J. Mirao, Microchem. J., 2018, 138, 438–446 CrossRef CAS.
  68. S. Porcinai and M. Ferretti, Spectrochim. Acta, Part B, 2018, 149, 184–189 CrossRef CAS.
  69. V. V. Zaykov, I. Y. Melekestseva, E. V. Zaykova, D. Fellenger and D. Motz, Archaeometry, 2018, 60(6), 1290–1305 CrossRef CAS.
  70. I. Nemet, S. Roncevic, A. Bugar, T. Z. Ferri and L. Pitarevic, J. Anal. At. Spectrom., 2018, 33(12), 2053–2061 RSC.
  71. G. Balassone, M. Mercurio, C. Germinario, C. Grifa, I. M. Villa, G. Di Maio, S. Scala, R. de’ Gennaro, C. Petti, M. C. Del Re and A. Langella, Measurement, 2018, 128, 104–118 CrossRef.
  72. S. S. Gomes, M. F. Araujo, A. M. M. Soares, J. Pimenta and H. Mendes, Microchem. J., 2018, 141, 337–345 CrossRef CAS.
  73. M. P. Seah, R. Havelund, S. J. Spencer and I. S. Gilmore, J. Am. Soc. Mass Spectrom., 2019, 30(2), 309–320 CrossRef CAS PubMed.
  74. N. Turhan, N. Ozbek and S. Akman, J. Anal. At. Spectrom., 2019, 34(3), 577–582 RSC.
  75. V. S. Souza, L. S. G. Teixeira, M. G. A. Korn, U. Cerqueira and M. A. Bezerra, Fuel, 2019, 242, 479–486 CrossRef CAS.
  76. C. H. Wu, S. J. Jiang and A. C. Sahayam, Spectrochim. Acta, Part B, 2018, 147, 115–120 CrossRef CAS.
  77. C. W. Lu, H. Y. Hung, H. C. Sung, Y. S. Sheu, W. L. Lin and S. P. Wu, J. Anal. At. Spectrom., 2019, 34(3), 570–576 RSC.
  78. A. S. Henn, E. M. M. Flores, V. L. Dressler, M. F. Mesko, J. Feldmann and P. A. Mello, J. Anal. At. Spectrom., 2018, 33(8), 1384–1393 RSC.
  79. S. M. Z. Iqbal, Z. Uddin, N. Ahmed, Z. A. Umar and M. A. Baig, Laser Phys., 2019, 29(3), 036101 CrossRef CAS.
  80. S. C. Yao, J. B. Zhao, Z. Z. Wang, Y. Deguchi, Z. M. Lu and J. D. Lu, Spectrochim. Acta, Part B, 2018, 149, 249–255 CrossRef CAS.
  81. H. Zhu, M. Liu, T. Guo, L. Xu, J. G. Dong, J. L. Feng, P. Cheng and Z. Zhou, J. Anal. At. Spectrom., 2018, 33(7), 1158–1167 RSC.
  82. L. Husakova, I. Urbanova, T. Sidova and M. Safrankova, J. Anal. Chem., 2018, 73(7), 650–660 CrossRef CAS.
  83. J. P. Souza, K. Kellermann, M. S. Camargo, D. P. Moraes, D. Pozebon and J. S. F. Pereira, J. Anal. At. Spectrom., 2018, 33(8), 1284–1291 RSC.
  84. S. G. Sama, C. Barrere-Mangote, B. Bouyssiere, P. Giusti and R. Lobinski, TrAC, Trends Anal. Chem., 2018, 104, 69–76 CrossRef.
  85. R. Sanchez, J. Lefevre and J. L. Todoli, J. Anal. At. Spectrom., 2019, 34(4), 664–673 RSC.
  86. L. V. Vieira, T. T. B. Marchezi, E. V. R. de Castro, G. P. Brandao and M. Carneiro, Fuel, 2019, 244, 352–358 CrossRef CAS.
  87. D. Ruhland, K. Nwoko, M. Perez, J. Feldmann and E. M. Krupp, Anal. Chem., 2019, 91(1), 1164–1170 CrossRef CAS PubMed.
  88. N. Fetter, J. Blichert-Toft, P. Telouk and F. Albarede, Chem. Geol., 2019, 511, 112–122 CrossRef CAS.
  89. J. S. Silva, A. S. Henn, V. L. Dressler, P. A. Mello and E. M. M. Flores, Anal. Chem., 2018, 90(11), 7064–7071 CrossRef CAS PubMed.
  90. A. P. M. Michel, A. E. Morrison, C. T. Marx and H. K. White, Environ. Sci. Technol. Lett., 2019, 6(1), 34–37 CrossRef CAS.
  91. E. C. Lourenco, E. Eyng, P. R. S. Bittencourt, F. A. Duarte, R. S. Picoloto and E. L. M. Flores, Talanta, 2019, 199, 1–7 CrossRef CAS PubMed.
  92. K. R. N. da Silva, A. D. Greco, M. Z. Corazza and J. L. Raposo, Anal. Methods, 2018, 10(26), 3284–3291 RSC.
  93. J. O. Vinhal and R. J. Cassella, Spectrochim. Acta, Part B, 2019, 151, 33–40 CrossRef CAS.
  94. L. A. Meira, J. S. Almeida, F. D. Dias, P. P. Pedra, A. L. C. Pereira and L. S. G. Teixeira, Microchem. J., 2018, 142, 144–151 CrossRef CAS.
  95. P. S. Barela, J. P. Souza, J. S. F. Pereira, J. C. Marques, E. I. Muller and D. P. Moraes, J. Anal. At. Spectrom., 2018, 33(6), 1049–1056 RSC.
  96. Y. Z. Liu, Z. H. Wang, J. Xia, L. Vervisch, K. D. Wan, Y. He, R. Whiddon, H. Bahai and K. F. Cen, Proc. Combust. Inst., 2019, 37(3), 2681–2688 CrossRef CAS.
  97. J. Viljanen, H. Zhao, Z. Zhang, J. Toivonen and Z. T. Alwahabi, Spectrochim. Acta, Part B, 2018, 149, 76–83 CrossRef CAS.
  98. P. Pohl, A. Bielawska-Pohl, A. Dzimitrowicz, P. Jamroz and M. Welna, TrAC, Trends Anal. Chem., 2018, 101, 43–55 CrossRef CAS.
  99. M. Bernardin, F. Bessueille-Barbier, A. Le Masle, C. P. Lienemann and S. Heinisch, J. Chromatogr. A, 2018, 1565, 68–80 CrossRef CAS PubMed.
  100. B. Klencsar, S. W. Li, L. Balcaen and F. Vanhaecke, TrAC, Trends Anal. Chem., 2018, 104, 118–134 CrossRef CAS.
  101. T. G. Kazi, H. I. Afridi, M. Bhatti and A. Akhtar, Ultrason. Sonochem., 2019, 51, 40–48 CrossRef CAS PubMed.
  102. E. Koosha, M. Ramezani and A. Niazi, Int. J. Environ. Anal. Chem., 2018, 98(6), 506–519 CrossRef CAS.
  103. M. A. Speranca, D. F. Andrade, J. P. Castro and E. R. Pereira, Opt. Laser Technol., 2019, 109, 648–653 CrossRef CAS.
  104. J. White, A. Celik, R. Washington, V. Yilmaz, T. Mitchum and Z. Arslan, Microchem. J., 2018, 139, 242–249 CrossRef CAS PubMed.
  105. S. M. Ansar and T. Mudalige, Int. J. Pharm., 2019, 561, 283–288 CrossRef CAS PubMed.
  106. Q. Xu, Z. H. Wang, L. H. Jin, P. Liu, Y. Tian, S. X. Zhang and C. Q. Zhang, Anal. Methods, 2018, 10(18), 2144–2150 RSC.
  107. E. Kamilari, K. Farsalinos, K. Poulas, C. G. Kontoyannis and M. G. Orkoula, Food Chem. Toxicol., 2018, 116, 233–237 CrossRef CAS PubMed.
  108. P. Kikongi, C. Fauteux-Lefebvre, J. Salvas and R. Gosselin, Spectrochim. Acta, Part B, 2018, 147, 59–70 CrossRef CAS.
  109. A. F. Oliveira, M. H. Gonzalez and A. R. A. Nogueira, Microchem. J., 2018, 143, 326–330 CrossRef CAS.
  110. E. Parhizkar, H. Saeedzadeh, F. Alunadi, M. Ghazali and A. Sakhteman, Iran. J. Pharm. Res., 2019, 18(1), 72–79 CAS.
  111. H. Rebiere, A. Kermaidic, C. Ghyselinck and C. Brenier, Talanta, 2019, 195, 490–496 CrossRef CAS PubMed.
  112. I. Costantini, K. Castro and J. M. Madariaga, Anal. Methods, 2018, 10(40), 4854–4870 RSC.
  113. M. Cotte, A. Genty-Vincent, K. Janssens and J. Susini, C. R. Phys., 2018, 19(7), 575–588 CrossRef CAS.
  114. A. Re, M. Zangirolami, D. Angelici, A. Borghi, E. Costa, R. Giustetto, L. M. Gallo, L. Castelli, A. Mazzinghi, C. Ruberto, F. Taccetti and A. Lo Giudice, Eur. Phys. J. Plus, 2018, 133(9), 362 CrossRef.
  115. A. Martinez-Hernandez, M. Oujja, M. Sanz, E. Carrasco, V. Detalle and M. Castillejo, J. Cult. Herit., 2018, 32, 1–8 CrossRef.
  116. N. H. Cheung, J. Anal. At. Spectrom., 2019, 34(3), 616–622 RSC.
  117. K. Rzecki, T. Sosnicki, M. Baran, M. Niedzwiecki, M. Krol, T. Lojewski, U. R. Acharya, O. Yildirim and P. Plawiak, Sensors, 2018, 18(11), 3670 CrossRef PubMed.
  118. R. C. Machado, A. B. S. Silva, G. L. Donati and A. R. A. Nogueira, J. Anal. At. Spectrom., 2018, 33(7), 1168–1172 RSC.
  119. T. Delgado, J. M. Vadillo and J. J. Laserna, J. Anal. At. Spectrom., 2018, 33(9), 1469–1476 RSC.
  120. P. Mattiazzi, D. Bohrer, E. Becker, C. Viana, P. C. Nascimento and L. M. Carvalho, Talanta, 2019, 197, 20–27 CrossRef CAS PubMed.
  121. L. M. Smieska, J. Twilley, A. R. Woll, M. Schafer and A. M. DeGalan, Microchem. J., 2019, 146, 679–691 CrossRef CAS.
  122. C. Germinario, I. Francesco, M. Mercurio, A. Langella, D. Sali, I. Kakoulli, A. De Bonis and C. Grifa, Eur. Phys. J. Plus, 2018, 133(9), 359 CrossRef.
  123. E. Pospisilova, K. Novotny, P. Porizka, D. Hradil, J. Hradilova, J. Kaiser and V. Kanicky, Spectrochim. Acta, Part B, 2018, 147, 100–108 CrossRef CAS.
  124. H. Zhang, S. Wang, K. K. Chang, H. F. Sun, Q. Q. Guo, L. Z. Ma, Y. T. Yang, C. H. Zou, L. Wang and J. D. Hu, Appl. Spectrosc., 2018, 72(6), 913–920 CrossRef CAS PubMed.
  125. A. H. Rezaei, M. H. Keshavarz, M. K. Tehrani and M. R. Darbani, Cent. Eur. J. Energ. Mater., 2019, 16(1), 3–20 CrossRef.
  126. K. Liu, D. Tian, C. Li, Y. C. Li, G. Yang and Y. Ding, TrAC, Trends Anal. Chem., 2019, 110, 327–334 CrossRef CAS.
  127. K. Liu, D. Tian, H. X. Wang and G. Yang, Anal. Methods, 2019, 11(9), 1174–1179 RSC.
  128. Y. M. Guo, Y. Tang, Y. Du, S. S. Tang, L. B. Guo, X. Y. Li, Y. F. Lu and X. Y. Zeng, Plasma Sci. Technol., 2018, 20(6), 065505 CrossRef.
  129. Y. Tang, Y. M. Guo, Q. Q. Sun, S. S. Tang, J. M. Li, L. B. Guo and J. Duan, Optik, 2018, 165, 179–185 CrossRef CAS.
  130. H. Jull, J. Bier, R. Kunnemeyer and P. Schaare, Spectrosc. Lett., 2018, 51(6), 257–265 CrossRef CAS.
  131. S. B. Roh, S. B. Park, S. K. Oh, E. K. Park and W. Z. Choi, J. Mater. Cycles Waste Manage., 2018, 20(4), 1934–1949 CrossRef CAS.
  132. E. Kim and W. Z. Choi, J. Mater. Cycles Waste Manage., 2019, 21(1), 176–180 CrossRef.
  133. M. V. Dastjerdi, S. J. Mousavi, M. Soltanolkotabi and A. N. Zadeh, Iran. J. Sci. Technol., Trans. A: Sci., 2018, 42(2), 959–965 CrossRef.
  134. R. M. T. Madiona, S. E. Bamford, D. A. Winkler, B. W. Muir and P. J. Pigram, Anal. Chem., 2018, 90(21), 12475–12484 CrossRef CAS PubMed.
  135. R. M. T. Madiona, N. G. Welch, S. B. Russell, D. A. Winkler, J. A. Scoble, B. W. Muir and P. J. Pigram, Surf. Interface Anal., 2018, 50(7), 713–728 CrossRef CAS.
  136. A. Villasenor, M. Boccongelli and J. L. Todoli, J. Anal. At. Spectrom., 2018, 33(7), 1173–1183 RSC.
  137. K. Vogel, A. Wegener, M. Pursch, P. Luschas and M. Wiesmann, Spectroscopy, 2019, 34(1), 38–46 Search PubMed.
  138. R. Ledesma, F. Palmieri, B. Campbell, W. Yost, J. Fitz-Gerald, G. Dillingham and J. Connell, Appl. Spectrosc., 2019, 73(2), 229–235 CrossRef CAS PubMed.
  139. P. Chen, X. L. Wang, X. Li, Q. S. Lyu, N. X. Wang and Z. D. Jia, Sensors, 2019, 19(5), 1087 CrossRef CAS PubMed.
  140. K. Bezemer, R. Woortmeijer, M. Koeberg, W. Wiarda, P. Schoenmakers and A. van Asten, Forensic Sci. Int., 2018, 290, 336–348 CrossRef CAS PubMed.
  141. M. Bonta and A. Limbeck, J. Anal. At. Spectrom., 2018, 33(10), 1631–1637 RSC.
  142. P. Wachulak, M. Duda, A. Bartnik, A. Sarzynski, L. Wegrzynski and H. Fiedorowicz, Spectrochim. Acta, Part B, 2018, 145, 107–114 CrossRef CAS.
  143. M. Pardede, T. J. Lie, J. Iqbal, M. Bilal, R. Hedwig, M. Ramli, A. Khumaeni, W. S. Budi, N. Idris, S. N. Abdulmadjid, A. M. Marpaung, I. Karnadi, I. Tanra, Z. S. Lie, H. Suyanto, D. P. Kurniawan, K. H. Kurniawan, K. Kagawa and M. O. Tjia, Anal. Chem., 2019, 91(2), 1571–1577 CrossRef CAS PubMed.
  144. C. Devouge-Boyer, S. Mouda, O. Gueguen and S. Marcotte, Talanta, 2018, 189, 568–572 CrossRef CAS PubMed.
  145. R. F. Santos, S. M. Cruz, S. R. Krzyzaniak, F. A. Duarte, P. A. Mello and E. M. M. Flores, Microchem. J., 2019, 146, 492–497 CrossRef CAS.
  146. V. Lazic, M. Filella and A. Turner, J. Anal. At. Spectrom., 2018, 33(11), 1917–1924 RSC.
  147. E. J. Dos Santos, G. F. Zagonel, A. B. Herrmann, E. B. Fantin and R. E. Sturgeon, Anal. Methods, 2018, 10(41), 5047–5050 RSC.
  148. R. Manjusha, R. Shekhar and S. Jaikumar, Microchem. J., 2019, 145, 301–307 CrossRef CAS.
  149. L. Fu, H. L. Xie, S. Y. Shi and X. Q. Chen, Spectrochim. Acta, Part B, 2018, 144, 1–6 CrossRef CAS.
  150. O. E. Bezrukova, S. D. Kirik, S. G. Ruzhnikov, I. S. Yakimov and P. S. Dubinin, Spectrochim. Acta, Part B, 2019, 152, 52–58 CrossRef CAS.
  151. E. Begu, B. Snell and Z. Arslan, Microchem. J., 2019, 145, 412–418 CrossRef CAS PubMed.
  152. V. Bodnar, A. Ganeev, A. Gubal, N. Solovyev, O. Glumov, V. Yakobson and I. Murin, Spectrochim. Acta, Part B, 2018, 145, 20–28 CrossRef CAS.
  153. C. P. de Morais, A. I. Barros, M. A. Bechlin, T. V. Silva, D. Santos, G. S. Senesi, M. S. Crespi, C. A. Ribeiro, J. A. G. Neto and E. C. Ferreira, Talanta, 2018, 188, 199–202 CrossRef CAS PubMed.
  154. S. Millar, C. Gottlieb, T. Gunther, N. Sankat, G. Wilsch and S. Kruschwitz, Spectrochim. Acta, Part B, 2018, 147, 1–8 CrossRef CAS.
  155. S. Millar, S. Kruschwitz and G. Wilsch, Cem. Concr. Res., 2019, 117, 16–22 CrossRef CAS.
  156. T. Dietz, J. Klose, P. Kohns and G. Ankerhold, Spectrochim. Acta, Part B, 2019, 152, 59–67 CrossRef CAS.
  157. P. Bran-Anleu, F. Caruso, T. Wangler, E. Pomjakushina and R. J. Flatt, Microchem. J., 2018, 141, 382–387 CrossRef CAS.
  158. M. M. ElFaham, M. Okil and N. M. Nagy, Opt. Laser Technol., 2018, 106, 69–75 CrossRef CAS.
  159. M. M. Elfaham and U. Eldemerdash, Opt. Laser Technol., 2019, 111, 338–346 CrossRef CAS.
  160. Z. W. Guo, L. X. Sun, P. Zhang, L. F. Qi, H. B. Yu, P. Zeng, Z. H. Zhou, W. Wang and Y. Z. Shi, Spectrosc. Spectral Anal., 2019, 39(1), 278–285 CAS.
  161. H. Morillas, C. Garcia-Florentino, I. Marcaida, M. Maguregui, G. Arana, L. F. O. Silva and J. M. Madariaga, Spectrochim. Acta, Part B, 2018, 146, 28–35 CrossRef CAS.
  162. M. Ramacciotti, S. Rubio, G. Gallello, M. Lezzerini, S. Columbu, E. Hernandez, A. Morales-Rubio, A. Pastor and M. de la Guardia, J. Spectrosc., 2018, 9736547 Search PubMed.
  163. C. Garcia-Florentino, M. Maguregui, M. Romera-Fernandez, I. Queralt, E. Margui and J. M. Madariaga, Anal. Chem., 2018, 90(9), 5795–5802 CrossRef CAS PubMed.
  164. C. Garcia-Florentino, M. Maguregui, E. Margui, L. Torrent, I. Queralt and J. M. Madariaga, Spectrochim. Acta, Part B, 2018, 143, 18–25 CrossRef CAS.
  165. M. Kasamatsu, T. Igawa, S. Suzuki and Y. Suzuki, Anal. Sci., 2018, 34(6), 729–733 CrossRef CAS PubMed.
  166. E. V. Yakubenko, O. V. Tolmachyeva, I. I. Chernikova and T. N. Ermolaeva, Inorg. Mater., 2018, 54(14), 1392–1396 CrossRef CAS.
  167. T. Y. Alekseeva, Y. A. Karpov, O. A. Dal’nova, V. V. Es’kina, V. B. Baranovskaya and L. D. Gorbatova, Inorg. Mater., 2018, 54(14), 1421–1429 CrossRef CAS.
  168. J. Kim, J. Anawati and G. Azimi, J. Anal. At. Spectrom., 2018, 33(8), 1310–1321 RSC.
  169. J. E. Jaine and M. R. Mucalo, Spectrochim. Acta, Part B, 2018, 145, 58–63 CrossRef CAS.
  170. F. Trichard, F. Gaulier, J. Barbier, D. Espinat, B. Guichard, C. P. Lienemann, L. Sorbier, P. Levitz and V. Motto-Ros, J. Catal., 2018, 363, 183–190 CrossRef CAS.
  171. P. Jovanovic, F. Ruiz-Zepeda, M. Sala and N. Hodnik, J. Phys. Chem. C, 2018, 122(18), 10050–10058 CrossRef CAS.
  172. A. Pavlisic, P. Jovanovic, V. S. Selih, M. Sala, N. Hodnik and M. Gaberscek, J. Electrochem. Soc., 2018, 165(6), F3161–F3165 CrossRef CAS.
  173. R. K. Ahluwalia, D. D. Papadias, N. N. Kariuki, J. K. Peng, X. P. Wang, Y. F. Tsai, D. G. Graczyk and D. J. Myers, J. Electrochem. Soc., 2018, 165(6), F3024–F3035 CrossRef CAS.
  174. D. Gonzalez-Flores, K. Klingan, P. Chernev, S. Loos, M. R. Mohammadi, C. Pasquini, P. Kubella, I. Zaharieva, R. D. L. Smith and H. Dau, Sustainable Energy Fuels, 2018, 2(9), 1986–1994 RSC.
  175. A. A. Guda, A. L. Bugaev, R. Kopelent, L. Braglia, A. V. Soldatov, M. Nachtegaal, O. V. Safonova and G. Smolentsev, J. Synchrotron Radiat., 2018, 25, 989–997 CrossRef CAS PubMed.
  176. C. W. Lopes, J. L. Cerrillo, A. E. Palomares, F. Rey and G. Agostini, Phys. Chem. Chem. Phys., 2018, 20(18), 12700–12709 RSC.
  177. M. Agote-Aran, I. Lezcano-Gonzalez, A. G. Greenaway, S. Hayama, S. Diaz-Moreno, A. B. Kroner and A. M. Beale, Appl. Catal., A, 2019, 570, 283–291 CrossRef CAS.
  178. A. Martini, E. Alladio and E. Borfecchia, Top. Catal., 2018, 61(14), 1396–1407 CrossRef CAS.
  179. Y. Zhou, D. E. Doronkin, Z. Y. Zhao, P. N. Plessow, J. Jelic, B. Detlefs, T. Pruessmann, F. Studt and J. D. Grunwaldt, ACS Catal., 2018, 8(12), 11398–11406 CrossRef CAS.
  180. L. Mino, E. Borfecchia, J. Segura-Ruiz, C. Giannini, G. Martinez-Criado and C. Lamberti, Rev. Mod. Phys., 2018, 90(2), UNSP 025007 CrossRef.
  181. C. H. Park, I. H. Kim, C. M. Choi, J. S. Jin, M. C. Choi and Y. D. Kim, Int. J. Mass Spectrom., 2018, 433, 47–54 CrossRef CAS.
  182. R. Müller, I. Kuznetsov, Y. Arbelo, M. Trottmann, C. S. Menoni, J. J. Rocca, G. R. Patzke and D. Bleiner, Anal. Chem., 2018, 90(15), 9234–9240 CrossRef PubMed.
  183. A. Dona-Fernandez, I. de Andres-Gimeno, P. Santiago-Toribio, E. Valtuille-Fernandez, F. Aller-Sanchez and A. Heras-Gonzalez, Forensic Sci. Int., 2018, 292, 167–175 CrossRef CAS PubMed.
  184. C. Vander Pyl, O. Ovide, M. Ho, B. Yuksel and T. Trejos, Spectrochim. Acta, Part B, 2019, 152, 93–101 CrossRef CAS.
  185. D. Merli, A. Amadasi, D. Mazzarelli, A. Cappella, E. Castoldi, S. Ripa, L. Cucca, C. Cattaneo and A. Profumo, J. Forensic Sci., 2019, 64(2), 558–564 CrossRef CAS PubMed.
  186. A. McKenzie-Coe, S. Bell and F. Fernandez-Lima, Anal. Methods, 2018, 10(35) RSC.
  187. R. D. Heringer and J. F. Ranville, Forensic Sci. Int., 2018, 288, E20–E25 CrossRef CAS PubMed.
  188. M. A. Comanescu, T. J. Millett and T. A. Kubic, J. Forensic Sci., 2019, 64(2), 565–569 CrossRef CAS PubMed.
  189. K. G. Myhre, M. J. Mehta, M. Z. Martin and M. T. Du, Spectrochim. Acta, Part B, 2018, 149, 30–34 CrossRef CAS.
  190. S. J. Pandey, R. Locke, R. M. Gaume and M. Baudelet, Spectrochim. Acta, Part B, 2018, 148, 99–104 CrossRef CAS.
  191. H. Takahara, A. Ohbuchi and K. Murai, Spectrochim. Acta, Part B, 2018, 149, 276–280 CrossRef CAS.
  192. C. L. Zong, Z. A. Bao, W. L. Ran, X. Ling, L. Chen, K. Y. Chen and H. L. Yuan, Anal. Methods, 2018, 10(21), 2456–2463 RSC.
  193. D. Sakate, Y. Iwazaki, Y. Kon, T. Yokoyama and M. Ohata, Anal. Sci., 2018, 34(6), 739–742 CrossRef CAS PubMed.
  194. Y. Tang, L. B. Guo, S. S. Tang, Y. W. Chu, Q. D. Zeng, X. Y. Zeng, J. Duan and Y. F. Lu, Appl. Opt., 2018, 57(22), 6451–6455 CrossRef CAS PubMed.
  195. M. Bouza, L. Lobo, R. Muniz, R. Pereiro, J. Esparza and J. A. Garcia, J. Anal. At. Spectrom., 2018, 33(3), 502–507 RSC.
  196. A. G. Nord and K. Billstrom, Heritage Sci., 2018, 6, 25 CrossRef.
  197. V. Panchuk, I. Yaroshenko, A. Legin, V. Semenov and D. Kirsanov, Anal. Chim. Acta, 2018, 1040, 19–32 CrossRef CAS PubMed.
  198. J. Qi, T. L. Zhang, H. S. Tang and H. Li, Spectrochim. Acta, Part B, 2018, 149, 288–293 CrossRef CAS.
  199. P. Singh, E. Mal, A. Khare and S. Sharma, J. Cult. Herit., 2018, 33, 71–82 CrossRef.
  200. A. De Bonis, I. Arienzo, M. D’Antonio, L. Franciosi, C. Germinario, C. Grifa, V. Guarino, A. Langella and V. Morra, J. Archaeol. Sci., 2018, 94, 51–59 CrossRef CAS.
  201. R. A. Ikeoka, C. R. Appoloni, M. A. Rizzutto and A. M. Bandeira, Microchem. J., 2018, 138, 384–389 CrossRef CAS.
  202. S. Haciosmanoglu, M. Kibaroglu, G. Sunal, E. Kozal and P. Gutsuz, Archaeometry, 2018, 60(3), 471–488 CrossRef CAS.
  203. S. Stojanovic, V. Bikic, L. Milicic, I. R. Evans, N. V. Y. Scarlett, H. E. A. Brand and L. Damjanovic-Vasilic, Microchem. J., 2019, 146, 557–567 CrossRef CAS.
  204. S. Ichikawa, T. Matsumoto, T. Nakamura and T. Kurisaki, X-Ray Spectrom., 2019, 48(2), 110–128 CrossRef.
  205. M. A. C. Ontiveros, E. Tsantini, L. Fantuzzi and J. Ramon, Archaeological and Anthropological Sciences, 2019, 11(2), 627–649 CrossRef.
  206. E. De Pauw, P. Tack, E. Verhaeven, S. Bauters, L. Acke, B. Vekemans and L. Vincze, Spectrochim. Acta, Part B, 2018, 149, 190–196 CrossRef CAS.
  207. B. Gehres and G. Querre, Archaeometry, 2018, 60(4), 750–763 CrossRef CAS.
  208. W. P. Xu, L. C. Niziolek and G. M. Feinman, J. Archaeol. Sci., 2019, 103, 57–71 CrossRef CAS.
  209. H. Aoyama, K. Yamagiwa, S. Fujimoto, J. Izumi, R. Ishikawa, S. Kameshima and T. Arakaki, X-Ray Spectrom., 2018, 47(4), 265–272 CrossRef CAS.
  210. A. Rodrigues, S. Fearn, T. Palomar and M. Vilarigues, Corros. Sci., 2018, 143, 362–375 CrossRef CAS.
  211. A. Rodrigues, S. Fearn and M. Vilarigues, Corros. Sci., 2018, 145, 249–261 CrossRef CAS.
  212. J. D. Zhang, Y. Y. Zhang, M. Collin, S. Gin, J. J. Neeway, T. S. Wang and Z. H. Zhu, Surf. Interface Anal., 2019, 51(2), 219–225 CrossRef CAS.
  213. K. E. Seyfang, H. J. Kobus, R. S. Popelka-Filcoff, A. Plummer, C. W. Magee, K. E. Redman and K. P. Kirkbride, Forensic Sci. Int., 2018, 293, 47–62 CrossRef CAS PubMed.
  214. J. Skruibis, O. Balachninaite, S. Butkus, V. Vaicaitis and V. Sirutkaitis, Opt. Laser Technol., 2019, 111, 295–302 CrossRef CAS.
  215. C. Sanchez-Ake, T. Garcia-Fernandez, J. L. Benitez, M. B. de la Mora and M. Villagran-Muniz, Spectrochim. Acta, Part B, 2018, 146, 77–83 CrossRef CAS.
  216. G. X. Zhang, Q. Li, Y. Zhu and Z. Wang, Spectrochim. Acta, Part B, 2018, 145, 51–57 CrossRef CAS.
  217. A. Ceglia, P. Cosyns, N. Schibille and W. Meulebroeck, Archaeological and Anthropological Sciences, 2019, 11(1), 279–291 CrossRef.
  218. E. Gliozzo, E. Braschi, F. Giannetti, A. Langone and M. Turchiano, Archaeological and Anthropological Sciences, 2019, 11(1), 141–170 CrossRef.
  219. A. K. Detcheva and J. Hassler, C. R. Acad. Bulg. Sci., 2018, 71(4), 476–482 CAS.
  220. S. Krizova, G. Blazkova and R. Skala, Microchem. J., 2018, 142, 236–250 CrossRef CAS.
  221. T. Purowski, L. Kepa and B. Wagner, Archaeological and Anthropological Sciences, 2018, 10(6), 1283–1302 CrossRef.
  222. N. Zacharias, M. Kaparou, A. Oikonomou and Z. Kasztovszky, Microchem. J., 2018, 141, 404–417 CrossRef CAS.
  223. N. Schibille, B. Gratuze, E. Ollivier and E. Blondeau, J. Archaeol. Sci., 2019, 104, 10–18 CrossRef CAS.
  224. E. Neri, B. Gratuze and N. Schibille, Archaeological and Anthropological Sciences, 2019, 11(3), 1107–1122 CrossRef PubMed.
  225. A. Van Ham-Meert, P. Claeys, S. Jasim, B. Overlaet, E. Yousif and P. Degryse, Archaeological and Anthropological Sciences, 2019, 11(4), 1431–1441 CrossRef.
  226. A. Carter, L. Dussubieux, M. Polkinghorne and C. Pottier, Archaeological and Anthropological Sciences, 2019, 11(3), 1013–1027 CrossRef.
  227. R. Balvanovic, M. M. Stojanovic and Z. Smit, J. Radioanal. Nucl. Chem., 2018, 317(2), 1175–1189 CrossRef CAS.
  228. A. Quemet, A. Ruas, V. Dalier and C. Rivier, Int. J. Mass Spectrom., 2019, 438, 166–174 CrossRef CAS.
  229. A. Quemet, A. Ruas, V. Dalier and C. Rivier, Int. J. Mass Spectrom., 2018, 431, 8–14 CrossRef CAS.
  230. M. L. Baruzzini, H. L. Hall, K. J. Spencer and F. E. Stanley, Int. J. Mass Spectrom., 2018, 430, 57–62 CrossRef CAS.
  231. J. M. Mannion, C. R. Shick, G. A. Fugate, B. A. Powell and S. M. Husson, Talanta, 2018, 189, 502–508 CrossRef CAS PubMed.
  232. A. L. Ronzani, A. Hubert, F. Pointurier, O. Marie, N. Clavier, A. C. Humbert, J. Aupiais and N. Dacheux, Rapid Commun. Mass Spectrom., 2019, 33(5), 419–428 CrossRef CAS PubMed.
  233. M. Krachler, Z. Varga, A. Nicholl, M. Wallenius and K. Mayer, Microchem. J., 2018, 140, 24–30 CrossRef CAS.
  234. Z. Varga, M. Krachler, A. Nicholl, M. Ernstberger, T. Wiss, M. Wallenius and K. Mayer, J. Anal. At. Spectrom., 2018, 33(6), 1076–1080 RSC.
  235. W. Wang, S. Fang, J. Xu, Z. M. Li, X. L. Yuan and X. P. Shen, Chin. J. Anal. Chem., 2018, 46(8), 1245–1252 CAS.
  236. E. Chamizo and M. Lopez-Lora, Nucl. Instrum. Methods Phys. Res., Sect. B, 2019, 438, 198–206 CrossRef CAS.
  237. M. A. C. Hotchkis, D. P. Child, M. B. Froehlich, A. Wallner, K. Wilcken and M. Williams, Nucl. Instrum. Methods Phys. Res., Sect. B, 2019, 438, 70–76 CrossRef CAS.
  238. J. J. Song, G. C. Y. Chan, X. L. Mao, J. D. Woodward, R. W. Smithwick, T. G. Schaaff, A. C. Stowe, C. D. Harris, R. E. Zheng, V. Zorba and R. E. Russo, Spectrochim. Acta, Part B, 2018, 150, 67–76 CrossRef CAS.
  239. F. Wang, Y. Zhang, Y. G. Zhao, D. F. Guo, S. K. Xie, J. Tan, J. Y. Li and J. Lu, Meas. Sci. Technol., 2018, 29(9), 095903 CrossRef.
  240. E. K. Fenske, B. D. Roach, D. C. Glasgow, R. H. Ilgner and J. M. Giaquinto, J. Radioanal. Nucl. Chem., 2019, 320(1), 153–163 CrossRef CAS.
  241. B. D. Roach, E. K. Fenske, R. H. Ilgner, C. R. Hexel, T. J. Haverlock and J. M. Giaquinto, J. Chromatogr. A, 2019, 1587, 155–165 CrossRef CAS PubMed.
  242. B. Martelat, H. Isnard, L. Vio, E. Dupuis, T. Cornet, A. Nonell and F. Chartier, Anal. Chem., 2018, 90(14), 8622–8628 CrossRef CAS PubMed.
  243. D. A. Childs and J. G. Hill, J. Radioanal. Nucl. Chem., 2018, 318(1), 139–148 CrossRef CAS.
  244. S. Xing, W. C. Zhang, J. X. Qiao and X. L. Hou, Talanta, 2018, 187, 357–364 CrossRef CAS PubMed.
  245. M. Penkin, S. Boulyga, B. Dabbs, D. Fischer, M. Humphrey, A. Kochetkov, A. Koepf and M. Sturm, J. Radioanal. Nucl. Chem., 2018, 316(2), 791–798 CrossRef CAS.
  246. S. Richter, C. Venchiarutti, C. Hennessy, U. Jacobsson, R. Bujak, J. Truyens and Y. Aregbe, J. Radioanal. Nucl. Chem., 2018, 318(2), 1359–1368 CrossRef CAS.
  247. B. A. Dittmann, R. Buompane, E. Chamizo, M. Christl, A. Dewald, T. Dunai, C. Feuerstein, K. Fifield, M. Frohlich, S. Heinze, F. Marzaioli, C. Munker, A. Petraglia, C. Sirignano, E. Strub, H. A. Synal, F. Terrasi, S. Tims and A. Wallner, Nucl. Instrum. Methods Phys. Res., Sect. B, 2019, 438, 189–192 CrossRef CAS.
  248. K. J. Mathew, C. Ottenfeld, R. Keller and A. Slemmons, J. Radioanal. Nucl. Chem., 2018, 318(1), 395–400 CrossRef CAS.
  249. T. Parsons-Davis, J. Wimpenny, C. B. Keller, K. Thomas, K. M. Samperton, P. R. Renne, R. Mundil, K. Moody, K. Knight, M. J. Kristo and R. Williams, J. Radioanal. Nucl. Chem., 2018, 318(1), 711–721 CrossRef CAS.
  250. M. Enachescu and C. Stan-Sion, Radiocarbon, 2019, 61(2), 435–444 CrossRef CAS.
  251. B. Z. Cvetkovic, G. Salazar, D. Kunz, J. Tits, S. Szidat and E. Wieland, Radiocarbon, 2018, 60(6), 1711–1727 CrossRef CAS.
  252. B. Z. Cvetkovic, G. Salazar, D. Kunz, S. Szidat and E. Wieland, Analyst, 2018, 143(13), 3059–3067 RSC.
  253. S. Hosoya, K. Sasa, T. Takahashi, T. Matsunaka, M. Matsumura, H. T. Shen, Y. Ota, K. Takano, Y. Ochiai and K. Sueki, Nucl. Instrum. Methods Phys. Res., Sect. B, 2019, 438, 131–135 CrossRef CAS.
  254. Y. C. Fu, W. J. Zhou, P. Cheng and L. Y. Zhang, Nucl. Instrum. Methods Phys. Res., Sect. B, 2019, 438, 162–165 CrossRef CAS.
  255. F. Quinto, C. Busser, T. Faestermann, K. Hain, D. Koll, G. Korschinek, S. Kraft, P. Ludwig, M. Plaschke, T. Schafer and H. Geckeis, Anal. Chem., 2019, 91(7), 4585–4591 CrossRef CAS PubMed.
  256. L. Y. Zhang, X. L. Hou, Y. C. Fu, M. Fang and N. Chen, J. Anal. At. Spectrom., 2018, 33(10), 1729–1736 RSC.
  257. S. Pavetich, A. Carey, L. K. Fifield, M. B. Froehlich, S. Halfon, A. Kinast, M. Martschini, D. Nelson, M. Paul, A. Shor, J. H. Sterba, M. Tessler, S. G. Tims, L. Weissman and A. Wallner, Nucl. Instrum. Methods Phys. Res., Sect. B, 2019, 438, 77–83 CrossRef CAS.
  258. K. Hain, B. Deneva, T. Faestermann, L. Fimiani, J. M. Gomez-Guzman, D. Koll, G. Korschinek, P. Ludwig, V. Sergeyeva and N. Thiollay, Nucl. Instrum. Methods Phys. Res., Sect. B, 2018, 423, 42–48 CrossRef CAS.
  259. S. Asai, Y. Hanzawa, M. Konda, D. Suzuki, M. Magara, T. Kimura, R. Ishihara, K. Saito, S. Yamada and H. Hirota, Talanta, 2018, 185, 98–105 CrossRef CAS PubMed.
  260. S. J. Goldstein, K. A. Hinrichs, A. J. Nunn, D. W. Gurganus, R. S. Amato and W. J. Oldham, J. Radioanal. Nucl. Chem., 2018, 318(1), 695–701 CrossRef CAS.
  261. K. Kolacinska, Z. Samczynski, J. Dudek, A. Bojanowska-Czajka and M. Trojanowicz, Talanta, 2018, 184, 527–536 CrossRef CAS PubMed.
  262. M. Furukawa, M. Matsueda and Y. Takagai, Anal. Sci., 2018, 34(4), 471–476 CrossRef CAS PubMed.
  263. W. T. Bu, L. Tang, X. M. Liu, Z. T. Wang, M. Fukuda, J. Zheng, T. Aono, S. Hu and X. L. Wang, J. Anal. At. Spectrom., 2019, 34(2), 301–309 RSC.
  264. T. Sakamoto, M. Morita, K. Kanenari, H. Tomita, V. Sonnenschein, K. Saito, M. Ohashi, K. Kato, T. Iguon, T. Kawai, T. Okumura, Y. Satou and I. Wakaida, Anal. Sci., 2018, 34(11), 1265–1270 CrossRef CAS PubMed.
  265. S. Mishra, S. Kasar, A. Takamasa, N. Veerasamy and S. K. Sahoo, J. Environ. Radioact., 2019, 198, 36–42 CrossRef CAS PubMed.
  266. C. Stan-Sion, Nucl. Instrum. Methods Phys. Res., Sect. B, 2019, 438, 107–112 CrossRef CAS.
  267. T. Matsuyama, Y. Izumoto, K. Ishii, Y. Sakai and H. Yoshii, Spectrochim. Acta, Part B, 2018, 149, 35–41 CrossRef CAS.
  268. H. Yoshii, Y. Izumoto, T. Matsuyama, K. Ishii and Y. Sakai, Spectrochim. Acta, Part B, 2018, 148, 183–187 CrossRef CAS.
  269. D. Obada, A. S. Mamede, N. Nuns, A. C. Gregoire and L. Gasnot, Appl. Surf. Sci., 2018, 459, 23–31 CrossRef CAS.
  270. J. Song, B. Min, S. Hong, S. An and S. Hong, Prog. Nucl. Energy, 2018, 106, 345–356 CrossRef CAS.
  271. D. G. Fobar, X. Xiao, M. Burger, S. Le Berre, A. T. Motta and I. Jovanovic, Prog. Nucl. Energy, 2018, 109, 188–194 CrossRef CAS.
  272. B. T. Manard, E. M. Wylie and S. P. Willson, Appl. Spectrosc., 2018, 72(11), 1653–1660 CrossRef CAS PubMed.
  273. K. Sanyal, S. Dhara and N. L. Misra, Anal. Chem., 2018, 90(18), 11070–11077 CrossRef CAS PubMed.
  274. S. Dhara, K. Sanyal, S. Paul and N. L. Misra, J. Anal. At. Spectrom., 2019, 34(2), 366–374 RSC.
  275. A. Pandey, S. Dhara, F. A. Khan, A. Kelkar, P. Kumar, R. B. Bhatt and P. G. Behere, J. Radioanal. Nucl. Chem., 2019, 319(3), 775–781 CrossRef CAS.
  276. B. K. Nagar, M. K. Saxena and B. S. Tomar, At. Spectrosc., 2018, 39(5), 185–192 CAS.
  277. D. D. Reilly, M. T. Athon, J. E. Corbey, I. I. Leavy, K. M. McCoy and J. M. Schwantes, J. Nucl. Mater., 2018, 510, 156–162 CrossRef CAS.
  278. R. Plukiene, E. Lagzdina, L. Juodis, A. Plukis, A. Puzas, R. Gvozdaite, V. Remeikis, Z. Revay, J. Kucera, D. Ancius and D. Ridikas, Radiocarbon, 2018, 60(6), 1861–1870 CrossRef CAS.
  279. H. L. Wu, F. Carotti, R. Gakhar, N. Patel and R. O. Scarlat, J. Fluorine Chem., 2018, 211, 159–170 CrossRef CAS.
  280. G. Maddaluno, S. Almaviva, L. Caneve, F. Colao, V. Lazic, L. Laguardia, P. Gasior, M. Kubkowska and F. T. U. Team, Nuclear Materials and Energy, 2019, 18, 208–211 CrossRef.
  281. D. Y. Zhao, C. Li, Z. H. Hu, C. L. Feng, Q. M. Xiao, R. Hai, P. Liu, L. Y. Sun, D. Wu, C. L. Fu, J. M. Liu, N. Farid, F. Ding, G. N. Luo, L. Wang and H. B. Ding, Rev. Sci. Instrum., 2018, 89(7), 073501 CrossRef PubMed.
  282. P. Paris, J. Butikova, M. Laan, A. Hakola, I. Jogi, J. Likonen, E. Grigore and C. Ruset, Nuclear Materials and Energy, 2019, 18, 1–5 CrossRef.
  283. Y. Li, C. Ke, X. Liu, F. J. Gou, X. R. Duan and Y. Zhao, Fusion Eng. Des., 2018, 136, 1640–1646 CrossRef CAS.
  284. J. M. Liu, D. Wu, C. L. Fu, R. Hai, X. Yu, L. Y. Sun and H. B. Ding, Plasma Sci. Technol., 2019, 21(3), 034017 CrossRef CAS.
  285. P. Liu, D. Y. Zhao, L. Y. Sun, C. L. Fu, J. M. Liu, C. Li, R. Hai, C. F. Sang, Z. H. Hu, Z. Sun, J. S. Hu, L. Wang, J. L. Chen, Y. F. Liang, G. N. Luo, H. Ding and E. Team, Plasma Phys. Controlled Fusion, 2018, 60(8), 085019 CrossRef.
  286. Z. H. Hu, N. Gierse, C. Li, J. Oelmann, D. Y. Zhao, M. Tokar, X. Jiang, D. Nicolai, J. Wu, F. Ding, S. Brezinsek, H. B. Ding, G. N. Luo and C. Linsmeier, Fusion Eng. Des., 2018, 135, 95–101 CrossRef CAS.
  287. J. Oelmann, C. Li, S. Brezinsek, M. Rasinski, C. P. Dhard, R. Konig, V. Winters and C. Linsmeier, Nuclear Materials and Energy, 2019, 18, 153–158 CrossRef.
  288. P. Dinca, V. Tiron, I. L. Velicu, C. Porosnicu, B. Butoi, A. Velea, E. Grigore, C. Costin and C. P. Lungu, Surf. Coat. Technol., 2019, 363, 273–281 CrossRef CAS.
  289. L. Zhang, S. Morita, Z. W. Wu, Z. Xu, X. D. Yang, Y. X. Cheng, Q. Zang, H. Q. Liu, Y. Liu, H. M. Zhang, T. Ohishi, Y. J. Chen, L. Q. Xu, C. R. Wu, Y. M. Duan, W. Gao, J. Huang, X. Z. Gong and L. Q. Hu, Nucl. Instrum. Methods Phys. Res., Sect. A, 2019, 916, 169–178 CrossRef CAS.
  290. J. D. Zhang, W. L. Jiang, Z. H. Zhu, L. Shao, L. Price, J. T. Zhao and T. S. Wang, J. Nucl. Sci. Technol., 2018, 55(7), 703–708 CrossRef CAS.
  291. S. Fazinic, T. Tadic, M. Vuksic, M. Rubel, P. Petersson, E. Fortuna-Zalesna and A. Widdowson, Anal. Chem., 2018, 90(9), 5744–5752 CrossRef CAS PubMed.
  292. V. C. Costa, J. P. Castro, D. F. Andrade, D. V. Babos, J. A. Garcia, M. A. Speranca, T. A. Catelani and E. R. Pereira, TrAC, Trends Anal. Chem., 2018, 108, 65–73 CrossRef CAS.
  293. G. Gamez and K. Finch, Spectrochim. Acta, Part B, 2018, 148, 129–136 CrossRef CAS.
  294. K. Sakurai and A. Kurokawa, X-Ray Spectrom., 2019, 48(1), 3–7 CrossRef CAS.
  295. P. A. W. van der Heide, J. Vac. Sci. Technol., B: Nanotechnol. Microelectron.: Mater., Process., Meas., Phenom., 2018, 36(3), 03F105 Search PubMed.
  296. P. Honicke, M. Kramer, L. Luhl, K. Andrianov, B. Beckhoff, R. Dietsch, T. Holz, B. Kanngiesser, D. Weissbach and T. Wilhein, Spectrochim. Acta, Part B, 2018, 145, 36–42 CrossRef.
  297. A. Mejstrik, P. Kregsamer, M. Fugger and C. Streli, Spectrochim. Acta, Part B, 2018, 149, 163–166 CrossRef CAS.
  298. M. L. Polignano, G. Borionetti, A. Galbiati, S. Grasso, I. Mica and A. Nutsch, Spectrochim. Acta, Part B, 2018, 149, 313–321 CrossRef CAS.
  299. R. Jakiela, A. Barcz, J. Sarnecki and G. K. Celler, Surf. Interface Anal., 2018, 50(7), 729–733 CrossRef CAS.
  300. S. A. Davari, P. A. Taylor, R. W. Standley and D. Mukherjee, Talanta, 2019, 193, 192–198 CrossRef CAS PubMed.
  301. A. Maderitsch, D. Ingerle, T. Bretschneider, M. Rauwolf, C. Pflumm, H. Buchholz, H. Borchert, C. Streli and J. Parisi, Spectrochim. Acta, Part B, 2018, 148, 188–192 CrossRef CAS.
  302. W. Pessoa, A. Roule, E. Nolot, Y. Mazel, M. Bernard, M. C. Lepy, Y. Menesguen, A. Novikova, P. Gergaud, F. Brigidi and D. Eichert, Spectrochim. Acta, Part B, 2018, 149, 143–149 CrossRef CAS.
  303. T. Yamada, H. Takahara, A. Ohbuchi, W. Matsuda and Y. Shimizu, Spectrochim. Acta, Part B, 2018, 149, 256–260 CrossRef CAS.
  304. J. Hermann, E. Axente, F. Pelascini and V. Craciun, Anal. Chem., 2019, 91(3), 2544–2550 CrossRef CAS PubMed.
  305. D. Kaser, L. Hendriks, J. Koch and D. Gunther, Spectrochim. Acta, Part B, 2018, 149, 176–183 CrossRef CAS.
  306. J. H. Choi, H. J. Lee, S. H. Lee, J. H. In and S. Jeong, Thin Solid Films, 2018, 660, 314–319 CrossRef CAS.
  307. J. S. Xiu, S. M. Liu, S. G. Fu, T. Wang, M. X. Meng and Y. Y. Liu, Appl. Opt., 2019, 58(4), 1040–1047 CrossRef CAS PubMed.
  308. J. Colwell, P. Hsiao, W. Zhang, X. Wang, R. Akter and A. Lennon, J. Anal. At. Spectrom., 2018, 33(3), 422–430 RSC.
  309. Y. J. Jang, J. Lee, K. B. Lee, D. Kim and Y. Lee, J. Anal. Methods Chem., 2018, 6751964 Search PubMed.
  310. J. Oelmann, N. Gierse, C. Li, S. Brezinsek, M. Zlobinski, B. Turan, S. Haas and C. Linsmeier, Spectrochim. Acta, Part B, 2018, 144, 38–45 CrossRef CAS.
  311. S. Imashuku, H. Taguchi, S. Fujieda, S. Suzuki and K. Wagatsuma, Electrochim. Acta, 2019, 293, 78–83 CrossRef CAS.
  312. S. Imashuku, H. Taguchi, T. Kawamata, S. Fujieda, S. Kashiwakura, S. Suzuki and K. Wagatsuma, J. Power Sources, 2018, 399, 186–191 CrossRef CAS.
  313. P. Smyrek, T. Bergfeldt, H. J. Seifert and W. Pfleging, J. Mater. Chem. A, 2019, 7(10), 5656–5665 RSC.
  314. P. Harte, M. Evertz, T. Schwieters, M. Diehl, M. Winter and S. Nowak, Anal. Bioanal. Chem., 2019, 411(3), 581–589 CrossRef CAS PubMed.
  315. M. Evertz, T. N. Kroger, M. Winter and S. Nowak, Spectrochim. Acta, Part B, 2018, 149, 118–123 CrossRef CAS.
  316. B. Bookhagen, W. Obermaier, C. Opper, C. Koeberl, T. Hofmann, T. Prohaska and J. Irrgeher, Anal. Methods, 2018, 10(31), 3864–3871 RSC.
  317. D. F. Andrade, F. M. Fortunato and E. R. Pereira, Anal. Chim. Acta, 2019, 1061, 42–49 CrossRef CAS PubMed.
  318. J. P. Castro and E. R. Pereira, Talanta, 2018, 189, 205–210 CrossRef CAS PubMed.
  319. E. Nolot, B. Caby, R. Gassilloud, M. Veillerot and D. Eichert, Spectrochim. Acta, Part B, 2018, 149, 71–75 CrossRef CAS.
  320. C. W. Lu, H. Y. Hung, W. L. Lin and S. P. Wu, Spectrochim. Acta, Part B, 2018, 149, 243–248 CrossRef CAS.
  321. N. X. Wang, X. L. Wang, P. Chen, Z. D. Jia, L. M. Wang, R. H. Huang and Q. S. Lv, Sensors, 2018, 18(8), 2623 CrossRef PubMed.
  322. M. H. Wang, M. J. Zhao, S. Ye, M. Zhu, R. X. Yi, L. W. Liu and J. L. Qu, J. Anal. At. Spectrom., 2018, 33(5), 713–719 RSC.
  323. S. Lopez-Sanz, F. J. G. Bernardo, R. C. R. Martin-Doimeadios and A. Rios, Anal. Chim. Acta, 2019, 1059, 1–15 CrossRef CAS PubMed.
  324. A. R. M. Bustos, K. P. Purushotham, A. Possolo, N. Farkas, A. E. Vladar, K. E. Murphy and M. R. Winchester, Anal. Chem., 2018, 90(24), 14376–14386 CrossRef PubMed.
  325. S. Naasz, S. Weigel, O. Borovinskaya, A. Serva, C. Cascio, A. K. Undas, F. C. Simeone, H. J. P. Marvin and R. J. B. Peters, J. Anal. At. Spectrom., 2018, 33(5), 835–845 RSC.
  326. T. Hirata, S. Yamashita, T. Suzuki and M. Ishida, Bunseki Kagaku, 2019, 68(2), 81–88 CrossRef CAS.
  327. L. Hendriks, B. Ramkorun-Schmidt, A. Gundlach-Graham, J. Koch, R. N. Grass, N. Jakubowski and D. Gunther, J. Anal. At. Spectrom., 2019, 34(4), 716–728 RSC.
  328. F. H. Lin, S. Miyashita, K. Inagaki, Y. H. Liu and I. H. Hsu, J. Anal. At. Spectrom., 2019, 34(2), 401–406 RSC.
  329. L. A. Rush, M. C. Endres, M. Liezers, J. D. Ward, G. C. Eiden and A. M. Duffin, Talanta, 2018, 189, 268–273 CrossRef CAS PubMed.
  330. A. Kana, M. Loula, R. Koplik, M. Vosmanska and O. Mestek, Talanta, 2019, 197, 189–198 CrossRef CAS PubMed.
  331. M. Loula, A. Kana, R. Koplik, J. Hanus, M. Vosmanska and O. Mestek, Anal. Lett., 2019, 52(2), 288–307 CrossRef CAS.
  332. D. Bouzas-Ramos, J. I. Garcia-Alonso, J. M. Costa-Fernandez and J. R. Encinar, Anal. Chem., 2019, 91(5), 3567–3574 CrossRef CAS PubMed.
  333. H. M. Neu, S. A. Alexishin, J. E. P. Brandis, A. M. C. Williams, W. J. Li, D. J. Sun, N. Zheng, W. L. Jiang, A. Zimrin, J. C. Fink, J. E. Polli, M. A. Kane and S. L. J. Michel, Mol. Pharm., 2019, 16(3), 1272–1281 CrossRef CAS PubMed.
  334. S. Lopez-Sanz, N. R. Farinas, R. D. R. Martin-Doimeadios and A. Rios, Anal. Chim. Acta, 2019, 1053, 178–185 CrossRef CAS PubMed.
  335. J. J. Tan, Y. Yang, H. El Hadri, M. D. Li, V. A. Hackley and M. R. Zachariah, Analyst, 2019, 144(7), 2275–2283 RSC.
  336. I. Rujido-Santos, L. Naveiro-Seijo, P. Herbello-Hermelo, M. D. Barciela-Alonso, P. Bermejo-Barrera and A. Moreda-Pineiro, Talanta, 2019, 197, 530–538 CrossRef CAS PubMed.
  337. P. Anekthirakun and A. Imyim, Microchem. J., 2019, 145, 470–475 CrossRef CAS.
  338. A. Radtke, M. Grodzicka, M. Ehlert, T. M. Muziol, M. Szkodo, M. Bartmanski and P. Piszczek, Int. J. Mol. Sci., 2018, 19(12), 3962 CrossRef PubMed.
  339. A. Rahman, S. Kumar, A. Bafana, S. A. Dahoumane and C. Jeffryes, Molecules, 2019, 24(1), 98 CrossRef PubMed.
  340. S. Oliver, H. Wagh, Y. L. Liang, S. Yang and C. Boyer, J. Mater. Chem. B, 2018, 6(24), 4124–4138 RSC.
  341. S. Yamashita, T. Suzuki and T. Hirata, Bunseki Kagaku, 2019, 68(1), 1–7 CrossRef.
  342. D. Lomeli-Marroquin, D. M. Cruz, A. Nieto-Arguello, A. V. Crua, J. J. Chen, A. Torres-Castro, T. J. Webster and J. L. Cholula-Diaz, Int. J. Nanomed., 2019, 14, 2171–2189 CrossRef CAS PubMed.
  343. R. P. Luo, L. N. Zheng, L. Li, J. Wang, W. Y. Feng, X. H. Yu and M. Wang, Chin. J. Anal. Chem., 2018, 46(6), 925–930 CAS.
  344. R. Saenmuangchin and A. Siripinyanond, Anal. Bioanal. Chem., 2018, 410(26), 6845–6859 CrossRef CAS PubMed.
  345. N. Anjuthaprabha and R. Manimekalai, J. Coord. Chem., 2019, 72(1), 83–101 CrossRef CAS.
  346. M. Chigondo, H. K. Paumo, M. Bhaumik, K. Pillay and A. Maity, J. Mol. Liq., 2019, 275, 778–791 CrossRef CAS.
  347. U. Dalal and S. N. Reddy, Environ. Sci. Pollut. Res., 2019, 26(11), 10631–10640 CrossRef CAS PubMed.
  348. S. G. Lanas, M. Valiente, M. Tolazzi and A. Melchior, J. Therm. Anal. Calorim., 2019, 136(3), 1153–1162 CrossRef CAS.
  349. T. Preller, D. Menzel, S. Knickmeier, J. C. Porsiel, B. Temel and G. Garnweitner, Nanomaterials, 2018, 8(5), 297 CrossRef PubMed.
  350. C. Tang, A. W. York, J. L. Mikitsh, A. C. Wright, A. M. Chacko, D. R. Elias, Y. D. Xu, H. K. Lim and R. K. Prud’homme, Macromol. Chem. Phys., 2018, 219(11), 1700592 CrossRef.
  351. M. Bartosiak, J. Giersz and K. Jankowski, Microchem. J., 2019, 145, 1169–1175 CrossRef CAS.
  352. N. L. Zulfah and A. Siripinyanond, J. Anal. Sci. Technol., 2018, 9, UNSP 19 CrossRef.
  353. M. Ghaffari, F. Mortarzadeh and M. Safavi, Ceram. Int., 2019, 45(1), 1179–1188 CrossRef CAS.
  354. D. Marsan, H. Sengul and A. M. A. Ozdil, Environ. Sci.: Nano, 2019, 6(3), 879–891 RSC.

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