GSECARS X-ray Microprobe for Earth and Environmental Science Matthew Newville, Peter Eng, Steve Sutton, Mark Rivers Consortium for Advanced Radiation Sources.

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GSECARS X-ray Microprobe for Earth and Environmental Science Matthew Newville, Peter Eng, Steve Sutton, Mark Rivers Consortium for Advanced Radiation Sources (CARS) University of Chicago, Chicago, IL X-ray Absorption (XANES / EXAFS) Objective for Earth and Environmental Sciences: X-ray Microprobe techniques: oxidation state of selected element near-neighbor distances and coordination numbers abundance and spatial correlations of heavy elements X-ray Fluorescence (XRF), Fluorescence Mapping Determine chemical associations, speciation, and structure of heavy elements on heterogeneous samples: soils, sediments, aggregates, plant material, isolated inclusions, or contaminants.

Focusing: Kirkpatrick-Baez mirrors: Rh-coated Si, typically using 3x3  m spot sizes, at 50mm from end of mirrors. Incident Beam: LN 2 cooled Si (111) Sample Stage: x-y-z stage, 1  m resolution Samples in air or He, typically Fluorescence detector: 16-element Ge detector / DXP electronics, Lytle Detector, or Wavelength Dispersive Spectrometer Data Collection: custom software for XRF, mapping and XAFS, based on EPICS. Optical Microscope: 5x to 50x objective to external video system. GSECARS XRF/XAFS Microprobe Station Slits: typically 200 to 300  m, accepting ~20% of undulator beam at 50m from source.

The table-top Kirkpatrick-Baez mirrors use four-point benders and flat, trapezoidal mirrors to dynamically form an ellipsis. They can focus a 300x300  m beam to 1x1  m. With a typical working distance of 100mm, and a focal distance and spot-size independent of energy, they are ideal for micro-XRF and micro-EXAFS. We use Rh-coated silicon for horizontal and vertical mirrors to routinely produce 2x3  m beams for XRF, XANES, and EXAFS. Kirkpatrick-Baez Focusing Mirrors

Multi-Element Ge Detector: energy resolution ~250 eV, which separates most fluorescence lines, and allow a full XRF spectrum (or the windowed signal from several lines) to be collected in a second. This is limited in total count rate (to ~250KHz), so multiple elements (10 to 30) are used in parallel. Detection limits are at the ppm level for XRF. XANES and EXAFS can be measured on dilute species (~10ppm) in heterogeneous environments. X-ray Fluorescence Detectors Wavelength Dispersive Spectrometer: has higher resolution (~20eV), and smaller solid angle. This can be used for XAS, and is able to separate fluorescence lines that cannot be resolved with a Ge detector.

John Mavrogenes, Andrew Berry (Australian National University), GSECARS Hydrothermal ore deposits are important sources of Cu, Au, Ag, Pb, Zn, and U. Metal complexes in high-temperature, high- pressure solutions are transported until cooling, decompression, or chemical reaction cause precipitation and concentration in deposits. To further understand the formation of these deposits, the nature of the starting metal complexes need to be determined. XRF and  XAFS are important spectroscopic tools for studying the chemical speciation and form of these metal complexes in solution. This is challenging to do at and above the critical point of water (22MPa, 375 o C). Fluid inclusions from hydrothermal deposits can be re-heated and used as sample cells for high temperature spectroscopies. Natural Cu and Fe-rich brine / fluid inclusions in quartz from Cu ore deposits from New South Wales, Australia were examined at room temperature and elevated temperatures by XRF mapping and XAFS. Metal Speciation in Hydrothermal Fluid Inclusions 100  m

Understanding the metal complexes trapped in hydrothermal solutions in minerals is key to understanding the formation of ore deposits. Cu 25 o C Cu 495 o C Fe 25 o C Fe 495 o C 65  m Natural Cu and Fe-rich brine and vapor- phase fluid inclusions in quartz from Cu ore deposits were examined at room temperature and elevated temperatures by XRF mapping and EXAFS. Initial Expectation: chalcopyrite (CuFeS 2 ) would be precipitated out of solution at low temperature, and would dissolve into solution at high temperature. We would study the dissolved solution at temperature. Cu speciation in Hydrothermal Fluid Inclusions Result: XRF mapping (2  m pixel size) showed that for large vapor-phase inclusions, a uniform distribution of Cu in solution at room temperature was becoming less uniform at temperature. This was reversible, and seen for multiple inclusions. XRF Mapping

These results are consistent with Fulton et al [Chem Phys Lett. 330, p300 (2000)] study of Cu solutions near critical conditions: Cu 2+ solution at low temperature, and Cu 1+ associated with Cl at high temperatures. Cu XANES: Speciation in Fluid Inclusions XANES measurements at low and high temperatures for the vapor-phase inclusions show dramatic differences: Low temp: Cu 2+, aqueous solution High temp: Cu 1+, Cl or S ligand.

Cu XAFS in Fluid Inclusions Cu 2+ O O 2.35Å 1.96Å Cl 2.09Å Cu 1+ Low temp High temp EXAFS from the high temperature phase: Fit (red) to 450C Cu solution XAFS in vapor- phase fluid inclusion (blue). Good fits can be obtained with 1 Cl at ~2.09Å and 1 O at ~2.00Å, or 2 Cl at ~2.08Å. These findings are consistent with the model of for aqueous Cu 1+ of Fulton et al. J. A. Mavrogenes, A. J. Berry, M. Newville, S. R. Sutton, Am. Mineralogist 87, p1360 (2002)

X-ray computed microtomography (CMT) gives 3D images of the x-ray absorption coefficient. An absorption image is collected as the angle  is rotated through 180 o, and the 3D image is reconstructed in software. In some cases, element-specific images can be made by tuning the x-ray energy above and below an absorption edge. Fluorescence x-ray tomography use a focused beam, scanned across the sample. The sample is rotated around  and translated in x. Fluorescence x-rays are collected as for XRF maps. Transmission x-rays are measured as well to give an overall density tomograph. data collection is relatively slow – one slice can be made at a time. can be complicated by self-absorption. can collect multiple fluorescence lines. X-ray Fluorescence Tomography: Overview broad x-ray beam rotation stage Sample Phosphor CCD camera  fluorescence detector Transmission detector x visible light focused x-ray beam Sample  rotation and translation stages fluoresced x-rays

Fluorescence detector: multi-element Ge detector Sample stage: x-y-z-  Sample, mounted on silica fiber, or in ‘shrink-wrap’ tube, on a goniometer head KB mirrors, with Pb tape shield Fluorescence Tomography: Experimental Setup Optical microscope

x  The raw fluorescence tomography data consists of elemental fluorescence (uncorrected for self-absorption) as a function of position and angle: a sinogram. This data is reconstructed as a virtual slice through the sample by a coordinate transformation of (x,  )  (x, y). The process can be repeated at different z positions to give three-dimensional information. Fluorescence sinograms collected simultaneously for Zn, Fe, and As for a cross-section of As-contaminated cattail root (photo, right): x: 1100  m in 10  m steps  : 180  in 3  steps Fluorescence Tomography: Sinograms Zn FeAs

Nicole Keon, Daniel Brabander, Harold Hemond (MIT), GSECARS Studying a Superfund site (Wells G+H wetland, which gained notoriety in A Civil Action), a reservoir with ~10 tons of arsenic within the upper 50cm of the sediment. Most of the arsenic is sequestered in the wetland peat sediments with relatively As concentration in the groundwater. In contrast, riverbed sediments in the wetland have higher concentrations of aqueous arsenic, despite lower solid phase concentrations. Can the metabolic activity of wetland plants, such as Typha latifolia (cattail) explain the sequestration of arsenic in the wetland? Where is As in the wetland plants? What elements are associated with As? What is the As oxidation state? Wells G&H Typha latifolia root: reconstructed slices from fluorescence  - tomography, showing As concentrated on the root exterior, associated with Fe and Zn. Arsenic Distribution in Cattail Roots AsFe ZnCu Slicing the root would cause enough damage that 2D elemental maps would be compromised. Tomography can be used to make a virtual slice of the root.

As XANES XANES measurements on the Typha latifolia cattail roots show mixed As oxidation state – roughly equal portions As 3+ and As 5+. The As 3+ fraction did vary between different root samples, and even along a single root. Is there a spatial dependence to the As oxidation state?

As XANES, Oxidation State Tomograms Fluorescence tomograms made at 2 different energies: E As total As concentration E As 3+ As 3+ concentration would show spatial dependence of the As oxidation state. XANES measurements on the Typha latifolia cattail roots show mixed As oxidation state – roughly equal portions As 3+ and As 5+. The As 3+ fraction did vary between different root samples, and even along a single root. Is there a spatial dependence to the As oxidation state?

The As 3+ / As ratio is heterogeneous (boxed areas). As 5+ appears correlated with metals (Fe, Cu, Zn). As oxidation tomograms for Cattail Roots As 3+ As total As 3+ total As 5+ appears at location with high Cu and Zn. As 5+ appears at location with high Fe. More detailed spatial and oxidation state information would need faster data collection rates.

Future Directions and Microprobe Improvements The GSECARS microprobe station is running well and productively, combining  XRF, mapping, XANES, and EXAFS for a wide range of problems in geological, soil, and environmental sciences. Areas for Improvement: Data collection speed / efficiency Even using DXP electronics for the multi-element detector, the detector is the rate limiting step for maps and XAFS. Being able to read out the detector faster will help speed up mapping and XAFS collection. Using new x-ray beam position monitor with fast feedback, our 1-m long beamline KB mirrors can be used to stabilize the beam position at the ~200  m slit in front of the small KB mirrors. Beam positional stability, especially during XAFS scans Ease of focus to below 2  m