research papers
Robust framework and software implementation for fast speciation mapping
aUniversité Paris-Saclay, CNRS, Ministère de la Culture, UVSQ, IPANEMA, F-91192 Saint-Aubin, France, bStanford Radiation Lightsource (SSRL), SLAC National Accelerator Laboratory, Menlo Park, CA, USA, cSynchrotron SOLEIL, F-91192 Gif-sur-Yvette, France, dLaboratoire de Biomathématiques, EA 7537 – BioSTM, Faculté de Pharmacie de Paris – Université Paris Descartes, 4 Avenue de l'Observatoire, F-75006 Paris, France, eService de Biostatistique et d'Informatique Médicale, Hôpital Saint-Louis, Assistance Publique Hôpitaux de Paris, 1 Avenue Claude-Vellefaux, F-75010 Paris, France, and fUniversité Paris-Saclay, F-91190 Saint-Aubin, France
*Correspondence e-mail: serge.cohen@synchrotron-soleil.fr, loic.bertrand@universite-paris-saclay.fr
One of the greatest benefits of synchrotron radiation is the ability to perform chemical MicroAnalysis Toolkit software, and a dedicated script developed under the R environment. The procedure is exemplified through the study of a of a typical fossil specimen. The algorithm provides accurate speciation and concentration mapping while decreasing the data collection time by typically two or three orders of magnitude compared with the collection of whole spectra at each pixel. Whereas acquisition of spectral datacubes on large areas leads to very high irradiation times and doses, which can considerably lengthen experiments and generate significant alteration of radiation-sensitive materials, this sparse procedure brings the total irradiation dose greatly below radiation damage thresholds identified in previous studies. This approach is particularly adapted to the chemical study of heterogeneous radiation-sensitive samples encountered in environmental, material, and life sciences.
through X-ray absorption spectroscopies (XAS). imaging of large sample areas can be performed with either full-field or raster-scanning modalities. A common practice to reduce acquisition time while decreasing dose and/or increasing spatial resolution is to compare images collected at a few diagnostic energies. Several authors have used different multivariate data processing strategies to establish speciation maps. In this manuscript, the theoretical aspects and assumptions that are often made in the analysis of these datasets are focused on. A robust framework is developed to perform speciation mapping in large bulk samples at high spatial resolution by comparison with known references. Two fully operational software implementations are provided: a user-friendly implementation within theKeywords: synchrotron imaging; software; chemical speciation; X-ray absorption spectroscopy; heterogeneous materials.
1. Introduction
Microscale chemical speciation is essential to describe a material's local composition, structure and properties in heterogeneous samples. Synchrotron-based X-ray absorption near-edge spectroscopy (XANES) is one of the main analytical methods used for this purpose, and it has been applied in a variety of scientific fields such as environmental sciences, heritage sciences, Earth and meteorite geology, and plant sciences (Gardea-Torresdey et al., 2005; Linge, 2008; Cotte et al., 2010; Bertrand et al., 2012; Etschmann et al., 2014; Henderson et al., 2014; Gueriau et al., 2016). This excitation spectroscopy probes the energy levels of unoccupied electronic states from core levels upon X-ray Of particular interest for the characterization of heterogeneous materials is the use of focusing optics to acquire XANES in a spatially resolved manner. As X-ray optics have continued to improve in terms of reducing the size of focused beams, and synchrotron X-ray sources have become brighter, the ability to collect high-resolution X-ray images has become more and more routine. Two different experimental methodologies have been used to collect speciation images in transmission.
The first strategy uses a large beam and a spatially resolved detector to collect `instantaneous' images of the transmitted et al. was one of the first studying chemical contrast in imaging using transmitted radiographs above and below the of interest to create the chemical contrast (Kinney et al., 1986). These concepts have further been developed with full-field XANES, where the thin section of a sample is positioned in front of an extended X-ray beam; radiographs are collected at successive points on an area detector positioned downstream (Ade et al., 1992; De Andrade et al., 2011; Fayard et al., 2013). This approach can be used without additional X-ray optics to collect high-resolution (typically micrometres) images using a luminescent screen and a visible microscope (Fayard et al., 2013; Tack et al., 2014; Rau et al., 2002; Sciau & Wang, 2019), or make use of X-ray condensing optics to illuminate the sample, followed by an X-ray imaging optical element, such as a Fresnel zone plate, to image the transmission onto an area detector as in transmission X-ray microscopy (TXM) with resolutions in the tens of nanometres (Holt et al., 2013; Liu et al., 2012a; Nelson et al., 2011; Meirer et al., 2011; Li et al., 2015).
through the sample at successive given excitation energies – effectively taking a of the sample at each The work of KinneyA second strategy uses an X-ray focused microbeam to scan across a sample surface. In scanning transmission X-ray microscopy (STXM), the intensity of a transmitted beam is collected while varying the energy of the incoming beam and raster-scanning the sample with a fixed microscopic or nanoscopic X-ray beam (Zhang et al., 1994; Flynn et al., 1999; Jacobsen et al., 2000).
Both strategies allow for the position-sensitive detection of transmitted intensities in the presence of and without the sample. The resulting maps allow reconstruction of a XANES spectrum at each pixel. Both are performed by measuring the transmitted X-ray intensities, which requires that samples are thinned down to allow for typically 10–20% of incident photons to cross the sample. Obviously, since the
is imposed by the of the element whose speciation is being studied, it cannot be increased to improve transmission as in hard X-ray radiography or tomography. At low X-ray energies of a few keV or below, this imposes stringent constraints on sample thickness, equivalent to those requested in At greater energies of 8–22 keV, samples must still be thinned from a few dozen to a few hundred micrometres, which can be very constraining for samples. The transmission method is further constrained by the concentration of the element to be measured, as it needs to show strong enough absorption contrast across the energies to be measured.When it is not possible or desirable to prepare thin sections, fluorescence detection of XANES signals from the surface of a thick sample is an option. This typically involves scanning the sample as in the second strategy above by detecting the fluorescent signal with an energy-dispersive K-shell XRF yield for 3d transition metals of the fourth period (Sc–Zn) ranges from 16% to 46%. While XRF emission is isotropic, the solid angles of most fluorescence detectors are limited, and only a small fraction of the total fluorescence signal can be measured. In addition, matrix effects (reabsorption of fluoresced photons) can significantly impact the collected signal. XRF detection is usually strongly count-rate limited, further decreasing yields of detection and signal-to-noise ratios. This methodology has been applied to a wide host of samples, including geological systems to examine transition metal speciation (Sutton et al., 1995, 2002) and more dilute biological systems (Pushie et al., 2014; Pickering et al., 2000; Oram et al., 2011).
(XRF) detector generally placed at 90° with respect to the incident X-ray beam. In this geometry, a higher must reach the sample in order to obtain a signal-to-noise ratio identical to that of a transmission geometry. For example, theWhile the collection of transmission and fluorescence images as a function of incident X-ray energy is a relatively common technique in the literature (Kaulich et al., 2011; Lombi et al., 2011; Wang et al., 2013; Collins & Ade, 2012; Liu et al., 2012b; Pickering et al., 2000), the treatment and analysis of the datasets is not always straightforward. Several hundred images at different energies are often collected in full-field imaging, aiming to reconstruct a `complete' XANES spectrum in each pixel. However, in dilute fluorescence experiments where raster-scan XRF imaging must be performed, a full complement of energies may take a prohibitive amount of experimental time. A selection of a limited number of energies must therefore be made using the chemical knowledge of the system, in order to contrast different chemical species in the specimen. Several review articles have pioneered the idea of mapping the chemical nature of the sample by collecting XRF data at several varied excitation energies (Bertsch & Hunter, 2001; Marcus, 2010). This can be done by exploiting the contrast between different species at, for example different resonances in the S K-edge spectra for organic and inorganic forms in fossilized leaf materials (Edwards et al., 2014). Lerotic et al. (2004) used for the analysis of multiple energy datasets. Other authors have proposed statistical treatments like principal component analysis (PCA) while the data collection is on-going to help identify regions of interest in the sample in both transition metal systems (Mayhew et al., 2011; Etschmann et al., 2014) and complex sulfur speciation systems (Farfan et al., 2018).
In this manuscript, we focus on the theoretical aspects and assumptions that are often made in the analysis of these datasets. A robust framework is developed to perform speciation mapping in large thick samples at high spatial resolution by comparison with known references. We show that, with the proper experimental setup and the measurement of images over a selected number of energy points, the linear decomposition of the XANES signal yields the relative concentration of individual chemical species and the total concentration of the element. While using a linear decomposition, this method takes advantage of the increased number of effective data measurements at each pixel in the image, which results in improved overall counting statistics. The method minimizes beam exposure to the sample, which is particularly important in the case of samples that may be sensitive to radiation damage, such as the real paleontological sample on which the effectiveness of this approach is tested.
The low computational cost of the involved multivariate algorithm combined with the usefulness of the produced results make the proposed method suitable to inline use while collecting X-ray data and furthermore provides useful hints to the experimental design. To facilitate this aspect, the proposed approach has been integrated and deployed into a freely available software package, the MicroAnalysis Toolkit (Webb, 2011), and a dedicated package developed under the R environment. This approach is of interest for the study of a wide range of materials containing different chemical forms of an element, as frequently encountered in many fields of materials science.
2. Methods – sparse XAS
The following approximations have been made considering that the
signal is detected in fluorescence, on a thick sample (an infinitely thin sample would give similar approximations), regarding a target element diluted in a matrix presenting a significant regularity.2.1. Notations
Let I0 be the incident beam intensity, and θ and ϕ the angles between the sample surface and the incident and detected beam, respectively (Fig. 1). For the purpose of clarity, Table 1 presents a list of notations used in the manuscript. The experimental frame is set such that the incident beam propagates along the axis, the axis is vertical pointing upward and is such that forms a direct orthonormal frame. The fluorescence is measured at a right angle from the incident beam such that = . We consider that the measured fluoresced signal propagates along . Note that, although these constraints correspond to usual geometries and simplify the remaining computation, they have no direct consequence on the overall result.
|
We assume that we collect the experimental fluoresced intensity If Exp from a rectangular parallelepiped of thickness d. The thickness in the beam direction is then e = . We attach to the sample a frame with the axis orthogonal to the entry face and pointing inward the sample, the unitary vertical vector pointing upward and parallel to the entry face such that forms a direct orthonormal basis. Both orthonormal frames have their origin on the sample surface such that voxels on the surface are characterized by x = y = 0 or u = 0 according to the set of coordinates used. We will also use to point to the position of a voxel irrespective of the coordinate system used. The pixel coordinates on the sample surface are noted (v,z) with implied u = 0. The incident and fluoresced energies are denoted E and Ef, respectively. We included a possible indirect dependency of I0 in (E,v,z) as fluctuations of I0 occur in the scanning timescale which we express as I0[t(E,v,z)].
2.2. Algorithmic development
2.2.1. XRF from an elementary volume: general case
The
for the voxel at is noted , and can be decomposed aswhere is the matrix E and is the of species k around the `target' elemental edge considered – the linear combination standing if the atom probed exists as K distinct chemical forms. In the energy range which is usually considered for studies, photo-absorption is by far the main photon–matter interaction mechanism leading to fluorescence. Hence we will consider all along our computation that global absorption, be it by the matrix or the target element, is photo-absorption related. Furthermore, since the incident energy E is close to the of the target element, it is unlikely that the fluoresced signal produces any secondary sources of fluorescence from this element and hence we consider only primary fluorescence signal.
that varies slowly with energyLet us first consider the general case by computing the contribution of a given voxel = (x0, y0, z0),
Line (1) of this equation corresponds to factors independent of (x0,y0,z0): the incident beam I0[t(E,v,z)], and the detector characteristics, that accounts for its () and the solid angle it covers (Ω). Note that considering that Ω is constant for all values of x in the sample assumes that the detector is sufficiently far away from the voxel of interest to consider the incoming fluorescent beam as a parallel beam coming from the infinite.
Line (2) corresponds to the decrease of the incident
due to absorption while the incident beam penetrates in the direction to the voxel of interest.Line (3) accounts for the quantity of fluorescence emitted by the elementary volume irradiated by the incident microbeam. It takes into account the K species of the target element whose edges are probed and their amount in the given voxel. The latter will be called the fluorescence source term.
of theFinally, Line (4) of this equation considers that the fluorescence emission at Ef is attenuated due to reabsorption in the sample on the outgoing path expressed in its integral form arising from the Beer–Lambert law. Finally, we have the error term that we will omit from now on to simplify notations.
2.2.2. Target element diluted within the matrix
Assuming that the K species of the target element are very diluted in the matrix, the , is largely dominated by its matrix-related contribution
Under this hypothesis, the amplitude of the attenuation, both on the incident and fluoresced beam, is made independent of the concentration of the species of the target element. In this approximation, the absorption of the target element affects only the fluorescence source term.
2.2.3. Matrix and target element of homogeneous composition at the scale of the probed volume
We consider that both the composition of the matrix and the concentrations of the target element in its various species, , vary sufficiently slowly so that they can be considered as constant on the neighbourhood corresponding to the measure in each value of (v, z). More precisely, if we consider the = (x0 = 0, y0, z0) = (u0 = 0, v0, z0) voxel, we assume that there is a homogeneity radius, noted l, greater than the radius of the volume probed by the beam when the sample is fixed and such that
Combining these hypotheses with the one developed in the previous paragraph we obtain an analytical expression of the measured fluorescence originating from a voxel centred on , showing a simple dependency on the concentrations ,
2.2.4. Characteristic matrix absorption and thickness of the sample
In the previous equation, terms in the exponential can be grouped and the -x0 term can be factorized and we can define = + , such that the expression of the contribution of a voxel becomes
lc(Ef,v,z) = can be interpreted as the characteristic attenuation length of the experimental setup, and we need to have to satisfy the hypothesis of a homogeneous matrix and target element species composition. Furthermore, if d, the thickness of sample, satisfies we can treat the sample as infinitely thick. This condition, together with the hypothesis expressed in the previous section, basically states that the matrix has a homogeneity radius which is both greater than the beam radius and the of the incident beam interaction.
2.2.5. Summation along the incident beam
Equation (8) is implicitly an infinitesimal form, corresponding to
This can now be summed over the path of the incident beam (in x0), considering a semi-infinite sample, leading to the intensity of the fluorescence signal measured when the pixel (v, z) is illuminated by the probe,
which is a linear equation from the viewpoint of . We can then estimate the coefficients of these linear equations by measuring K spectra of references that are linearly independent. The simplest way would be to measure K spectra such that the a priori known concentrations are = ; in other words, K reference spectra corresponding to a single species in a unique matrix.
2.2.6. Reference and normalized spectra
In the general case corresponding to the approximations (10) the reference spectra allowing estimation of the parameters [] through the knowledge of must be measured under the same conditions, the same matrix, and the same experimental setup as the measurements made during the sparse experiment. This is in the best cases unpractical and in most cases unfeasible.
However, the X-ray absorption spectra on an energy domain allowing to probe an electron edge bear specificity that will allow us to relax these constraints.
2.2.7. Approximate affine behaviour of the matrix
First, considering the matrix alone in the typical energy domain probed during an
experiment, we approximate the using a first-order Taylor expansion leading to an affine function. This holds as long as no constituent of the matrix has a fluorescence edge in the domain,In this setting we can approximate the value of ,
basically stating that has very small variation when E varies within a small energy domain.
2.2.8. Linear composition of near-edge absorption spectra
The contribution of the different electronic levels of an atom to the absorption signals that correspond to different absorption edges is composed by simple addition of the effects at each of the edges taken individually. Thus the approximation described above is valid and usable for the contribution of the absorption of unprobed edges, and the K species probed can be written as the sum of an affine contribution and a contribution representing the very edge probed for each species, measured through fluorescence signal, ,
of thewith
In equation (15), the term corresponds to the out-of-edge change in slope, i.e. the slope correction applicable to equation (14) for the part of the spectrum collected at . If , one can, on a small domain that does not extend too much after the edge energy E edge, neglect aedge and therefore write
with
Equation (16) defines , the normalized spectra of the K reference species at the probed edge, which under the current approximations are unaffected by the matrix used to measure the reference spectra, as long they are measured in fluorescence mode at energy Ef. Indeed, under the current approximations the dependence of the measurement to the matrix is encoded within and which in turn are not affected by the species of the probed element, whilst bedge depends only on the edge probed. In other words, equation (16) allows us to model the reference spectra using species-independent terms (parameters: , ), a matrix-independent term {}, and a term independent of both (). In this context, can be obtained by measuring the reference species in any matrix and at any concentration provided that the approximation of the diluted sample holds, as usually done.
Note finally that the affine absorption behaviour of the matrix, characterized in equation (11) by Am and Bm, is accounted for with the parameters and .
2.2.9. Linear combination of reference spectra
We may now rewrite equation (10) using the approximation from equation (13) for and equation (16) for ,
which states that for a given (v,z) position the measured signal, If Expf(E,v,z)/I0[t(E,v,z)] is an affine function of and with coefficients:
C0(v,z) = for the intercept;
= for the coefficient of ;
Ck(v, z) = for the coefficient of each of ;
where Dm(Ef,v,z) = is independent of the incident energy E.
For any given coordinate set (v, z) on the sample, one can estimate the above expressed coefficient, , by performing a linear least-squares fitting of measurements corresponding to energies such that the vector and are linearly independent. The estimated coefficients correspond indeed to the relative concentration of each of the K species that could be present in the samples at coordinates (v,z) hence providing a relative estimation of .
2.2.10. Further notational simplification
Since the absolute scale of equation (17) cannot be easily computed from information one usually has a priori on the system, there is no incentive to keep the full notations. We can simplify the notation by integrating the scaling factors within the parameters without altering the relative values of Ck(v, z) taken from different pixels. For pixel (v, z) the scale is directly integrated in Ck(v, z), while the slope and intersect of the affine baseline will be noted as A(v, z) and B(v, z) which leads to equation (20) in the main text.
2.2.11. Validation of the model and estimation of the relative accuracy
Under the model developed above, as long as the matrix of the sample is homogeneous, the estimated coefficients C0(v, z) and should be strictly correlated, within measurement noise error, as they both should be correlated to the estimated sum of relative concentrations, C sum(v, z) = . Indeed, such correlations are very unlikely to be present by chance and the quality of the correlations can be used as a marker of the validity of the proposed model. Furthermore, as the proposed method is used to perform speciation imaging, hence collecting data on a large set of (v, z) coordinates, these correlations can be verified on the basis of a significant number of data points.
Note, however, that if the hypothesis of the C0(v, z) and estimation are affected since only and depend on the matrix. In these circumstances and become functions of the probed coordinates, (v, z), and the correlations that are described above no longer stand. Then C sum(v, z) is the only available estimate of the relative concentration of the probed element at the different measured coordinates.
of the matrix is no longer met, only theFinally, within the framework of linear least squares, one can compute the condition number, κ, of the design matrix as soon as and are known, and before performing any measure on the actual sample. With κ known it is easy to obtain an upper bound on relative errors in relative concentrations, , given a level of relative errors, also termed signal-to-noise ratio, in fluorescence signal measurements,
Through this simple inequality, which can be computed very early in the experiment design, one can set the appropriate exposure time to reach the fluorescence signal-to-noise ratio, , so as to reach a predefined requirement in terms of accuracy of the relative species concentrations.
Under such conditions, the experimental (v, z) results from a linear combination of the K reference spectra and of an affine baseline,
spectrum at any given pixel of coordinateswhere If Exp(E, v, z) is the fluorescence signal measured when illuminating pixel (v, z) at an E, and I0[t(E,v,z)] is the incident beam intensity at the moment t(E, v, z), when If Exp(E, v, z) is measured. models the summed up slow varying background from spectra of the sample and of the references, and is the quantity of the species k in the elementary volume dV probed. Γ is a proportionality constant depending on the XRF yield of the probed element and on the geometry of the setup (solid angle of the detector, etc.), is the apparent of the matrix, accounting for both incident beam and fluoresced signal attenuation, at pixel (v, z), and is a zero mean stochastic error term which is independent from one measurement to the next.
The parameters , and can be estimated using the linear least-squares fit of the equation system to the measurements. With the previous assumption of a zero-mean , these estimates are unbiased; with the additional assumption of independence, constant variance, and Gaussian (normal) distribution, they correspond to E can be accounted for in the affine baseline [equation (13)], thus we can simplify our equation to
estimation. From now, we will simplify the notations by keeping the error term out of all expressions. Note that by normalizing the reference spectra, , we bring on an arbitrary unit and as such there is not much interest in obtaining rather than . Finally the very limited dependence that has in terms ofFor a given (v, z) pixel position and using N probing energies , equation (20) produces a linear system of N equations and K+2 unknowns [Ck(v, z), A(v, z) and B(v, z)].
The linear least-squares solution requires that the number of equations is at least equal to the number of unknowns, .
Interestingly, when all needed references are identified, = C sum(v, z) is proportional to the absorbing element concentration. This provides an elemental relative concentration map as a side result of the full procedure.
3. Open source software implementation
The MicroAnalysis Toolkit package (Webb, 2011) under the `XANES Fitting' analysis option. The latter package utilizes a combination of self-written routines in Python (VanRossum & Drake, 2010) with the SciPy (Jones et al., 2001) package used for minimization. Compiled versions and source code for the software updated with these routines is made available as of version 1.5 under an open source licence in parallel to this publication (Webb, 2010). File formats from many synchrotron sources worldwide are able to load, and the list of compatible data formats is expanding upon request. The program is freely available and can be run on multiple operating system platforms.
procedure described here has been integrated into the most recent versions of theIn addition, a specific script was developed under the R statistical environment (R Development Core Team, 2011) and is made freely available with this publication. The script is annotated so as to provide a step-by-step description of the data processing, in such a way that it is easy for a user to adapt it to its own data. The script starts from raw XRF data and covers all steps up to decomposition and statistical analysis. In particular, several diagnosis steps are present in this script, as a contribution to data validation, while not all described in this manuscript.
The script and all datasets needed to reproduce the presented results can be found at https://doi.org/10.5281/zenodo.3748752.
4. Application to a fossil sample
The proposed procedure was tested in a study of the distribution of the oxidation states of cerium in a paleontological sample at micrometric scales, as a typical heterogeneous sample containing an element with two distinct valencies.
An exception among rare-earth elements, the element cerium exists in both the +III and +IV oxidation states. The resulting sensitivity to redox conditions makes the ). Synchrotron mapping allows studying directly the speciation of cerium within ancient samples (such as sediment or bone; Gueriau et al., 2015). Yet, a significant difficulty is that a high radiation dose can result in the photo-oxidation of Ce(III) to Ce(IV) during collection of entire XANES spectra, thereby biasing the measured data (Gueriau et al., 2015).
of cerium a frequently used proxy of the chemistry of past environments (German & Elderfield, 1990We studied a loose fragment (not a cross section) of well preserved soft tissues (mineralized muscles) around a bone of a yet undescribed ?gonorynchiform fish (where `?' indicates that the supposed identification has not yet been corroborated by a complete anatomical description) coming from the Late Cretaceous levels of the Djebel Oum Tkout locality in Morocco [ca. 95 million years old, Figs. 2(a) and 2(b)]. We produced rapid maps of cerium speciation of the sample at the Lucia beamline of the SOLEIL synchrotron source (Vantelon et al., 2016) over a 6466 pixel area (120 µm × 210 µm with a scan step of 2 µm × 2 µm; beam size 3.0 µm × 2.5 µm (H × V); 2.8 ×1010 photons s−1 in the focused spot) using the sparse procedure presented above. Spectra of cerium III and IV reference compounds were collected using the procedure given by Gueriau et al. (2015).
Gueriau et al. (2015) studied a series of cross sections from well preserved fossil teleost fishes and crustaceans from the same locality [see Fig. 4 of Gueriau et al. (2015)] using a limited number of points to limit photo-oxidation changes they observed within a few tens seconds during acquisition. They selected six excitation energies: below the L3 of cerium (5680 eV), in the post-edge region (5765 and 5900 eV) and at energies corresponding to three main spectral features that allow distinguishing Ce(III) from Ce(IV) in cerium-containing compounds — a white line at 5726 eV resulting from the electron transition and two peaks that partly overlap with the former attributed to the and the transitions, where L denotes a hole in ligand orbitals (at 5733 and 5736 eV, respectively) (Takahashi et al., 2000).
In the loose soft tissue fragment of the ?gonorynchiform fish, the procedure developed here (using the same excitation energies) reveals the presence of a fraction of cerium in the redox +IV state {[Ce(IV)]/[Ce(tot)] = 25.6 ± 8.3%} over the whole mapped area, suggesting slightly oxidative local conditions of burial [Figs. 2(c)–2(f)]. This value agrees well with the indirect data obtained from micro- and macroscale elemental concentration profiles measured at the site (so-called `REE patterns'), which also display a slight negative cerium anomaly attributed to oxidative burial conditions (Gueriau et al., 2015). The total cerium concentration, [Ce(tot)], was mapped in the sample using two different approaches. The cerium distribution shown in Fig. 2(d) is the result of the usual processing of an XRF dataset collected after the cerium edge (5900 eV), while Fig. 2(e) shows the [Ce(tot)] map derived from the proposed procedure. Since the latter takes advantage of the total collection time of the several XRF maps at different energies, it led to a far higher signal-to-noise ratio than the single-energy XRF map, without the need to switch to an additional incident energy significantly above the associated with the element. While the total concentration of cerium differs significantly between bone and surrounding mineralized muscles, the distribution of the Ce(IV) fraction relative to total cerium appears very stable and homogeneous between bone (27.2 ± 2.9%) and the surrounding mineralized muscles [27.7 ± 5.2%, Fig. 2(g)], which corroborates the validity of the redox proxy at different length scales in the presence of varying cerium ion concentrations.
A dwell time of 1 s per pixel was used. The dead-times associated with the movements of the scanning motors led to a total collection time of about 165 min per i.e. about 16.5 h for the full dataset (collection at six excitation energies). The typical acquisition time for a single full spectrum was 243 s, dead-times included: the collection of the same dataset with a complete spectrum per pixel would therefore have taken 436 h, i.e. about 26 times longer. While the collection of a full spectrum under these conditions would have resulted in a surface irradiation dose (Howells et al., 2009; Bertrand et al., 2015) of 5.3 GGy, this value was reduced by a similar factor of 26 to about 200 MGy per pixel, with a counting time of 9.2 s per pixel, significantly less than the dose leading to a change in speciation, as shown by the photo-oxidation kinetics of cerium in comparable specimens (Gueriau et al., 2015, Fig. 3C).
The sparse
approach produced maps of cerium speciation and total concentration allowing comparison of different physiological zones and showing homogeneous speciation, even if the concentration of the varies considerably on the map.5. Conclusion
X-ray absorption imaging can be used to establish chemical speciation at sub-micrometric to centimetric spatial scales over large sample areas. However, as observed in many samples, including the example discussed here of cerium speciation in fossil paleontological materials, the traditional way of collecting
spectra, which requires the accumulation of data for sometimes several minutes per point, can create changes in the redox state of the sample at the points of analysis. With the increased of synchrotron X-ray sources, this approach leads to the deposition of large radiation doses in small sample volumes. Such alterations can occur in many samples and present a significant risk to the quality of the measurement. The procedure presented here with the implementation of the provided software allows to produce speciation and total elemental composition maps by collecting several individual XRF maps across the of the element of interest at relatively low total irradiation doses. Although similar procedures have been reported many times in the past, we show with a rigorous framework that the determination of proportions of individual species can be solved accurately, in particular by making explicit the typical assumptions and conditions used when collecting XRF data on thick samples. A particular advantage of this low-dose imaging approach, that we propose to denominate as see-XAS (sparse XAS), is that not only can speciation of the sample be obtained at thousands or millions of micro-scale locations to reconstruct high-resolution images of the speciation but also that the actual dose in a given pixel is much lower (up to several orders of magnitude) owing to the selective nature of the number of energies collected. This constitutes a true risk mitigation procedure that can be invaluable for radiation-sensitive samples in the fields of cultural heritage, environment, life and materials science.Footnotes
‡Current affiliation: Institute of Earth Sciences, University of Lausanne, CH-1015 Lausanne, Switzerland.
Acknowledgements
PG thanks D. B. Dutheil, S. Charbonnier, G. Clément, N.-E. Jalil, H. Bourget, B. Khalloufi (MNHN), A. Tourani, F. Khaldoune (Cadi Ayyad University, Marrakesh) and P. M. Brito (Rio de Janeiro State University) for collecting the fossils. E. Janots (Université Grenoble Alpes, Grenoble) is warmly acknowledged for providing us Ce(III) and Ce(IV) standard XANES data. We thank D. Vantelon and N. Trcera (SOLEIL) for their support at the Lucia beamline.
Funding information
SW acknowledges support from the Jean d'Alembert fellowship program at Université Paris-Saclay. Study of heritage materials at IPANEMA and the SOLEIL synchrotron was supported by the Research Infrastructures activity IPERION CH of the Horizon2020 program of the European Commission (Grant Agreement No. 654028). Beam time was funded by the SOLEIL synchrotron under project no. 20141143. Stanford Synchrotron Radiation Lightsource, SLAC National Accelerator Laboratory, is supported by the US Department of Energy, Office of Science, Office of Basic Energy Sciences under contract no. DE-AC02-76SF00515.
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