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Canadian Centre canadien Light de rayonnement Source synchrotron

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  • Canadian Centre canadien Light de rayonnement Source synchrotron

  • The Canadian Light Source: A New Tool for Mining and Environmental Headaches

    J.N. Cutler Canadian Light Source Inc.

  • 3

    Light lets you see!

    Interaction of light with matter is very simple, that’s why scientists use it.

    The energy of light determines what it lets you “see”

    Visible light let you see “large” things X-rays let you see “through” things

  • 4

    The Construction Site

  • 5

    ESRF Animation

  • 6

    1. E-gun 2. Transfer Line & Booster ring

    3. Storage ring 4. Beamline &

    end station

    Synchrotron Facility Components

  • 8

    Booster Ring First injection in June > 10 mA ramped to 2.9

    GeV and extracted. Commissioning

    complete

    1x2mm

  • Synchrotron Hall, Main Floor

  • 10

    Electromagnetic Spectrum angstrom micron millimetre

  • 11

    Sample Microprobe Beamline Layout

    ASI

  • 12

    Canadian Light Source Inc. Vision

    To advance Canadian scientific and industrial capabilities by operating the Canadian Light Source facility as the national synchrotron research and development centre of excellence.

  • 13

    Multi-disciplinary Opportunities Advanced materials – hybrid materials, stress, transistors, foams

    Metals/ceramics, coatings, fibers, polymers, pulp/paper, welding Information technologies (IT), storage, semi-conductors, sensors MEMS (micro-electrical-mechanical systems); Nano-technologies

    Health & Life Sciences – biotech (human, animal, plant) Designer pharmaceuticals, medical imaging (cell chemistry) Genome & proteomics (protein functionality) Viruses; treatment therapies; diagnostics; implantable devices

    Earth Sciences – geology, mining, industrial processing Environmental geo-chemistry, bio-active stability analysis Oil tribology, fingerprinting, soils in situ, corrosion Remediation assessments, waste management

  • 14

    IR Microscopy of a fluid inclusion

    Bantignies et. al. , SR News 11,31-37, 1998

  • 15

    Infrared Study of Organic Material on Marine Sediment

    Bare silica, low PAH Clay, OM, high PAH

    20 microns SEM image of a silica particle. (Right) IR image of organic material on the silica particles. Red and yellow areas indicate high PAH concentration.

    • PAHs present on silica particles were found associated with organic carbon locations. These organic matter regions containing PAHs are colonized by bacteria during biodegradation studies.

    Upal et al., Environ. Sci. Technol., 2000, 34, 1729.

    PresenterPresentation NotesThis is analysis of PAH uptake in a sediment/marine environment: This silica particle has clay attached, and trying to locate the PAH distribution on it was the project, finding that the Bacteria were also localised there was important to know. Microscale Location, Characterization, and Association of Polycyclic Aromatic Hydrocarbons on Harbor Sediment Particles UPAL GHOSH, J . SEBGILLETTE, RICHARD G . LUTHY ,RICHARD N . ZAREEnviron. Sci. Technol. 2000, 34, 1729-1736

  • 16

    17.65 8.83 5.90 4.43 3.55 2.97 2.56d-Scale(A)

    x10^3

    10

    20

    30

    40

    50

    60

    Inte

    nsity

    (Cou

    nts)

    CuKa (0.01 deg/step), 50kV 200mA

    Synchrotron x-ray (0.01 deg/step), 0.7 A

    Comparing synchrotron & lab results

    17.65 8.83 5.90 4.43 3.55 2.97 2.56d-Scale(A)

    x10^3

    10

    20

    30

    40

    50

    60

    Inte

    nsity

    (Cou

    nts)

    CuKa (0.01 deg/step), 50kV 200mA

    Synchrotron x-ray (0.01 deg/step), 0.7 A

    CANMET/Devon

  • 17

    hν Atom1 Atom2

    E0 e

    X-ray Absorption Spectroscopy (XAS) using Synchrotron Light

    )()()()(

    0

    0

    EEEE

    µµµχ −≡

  • 18

    Soil Chemistry

    2465 2470 2475 2480 2485 2490 2495

    AMAB014

    Photon Energy (eV)

    Sulphide

    Sulphonic acid

    S K-edge

    Sulphate

    Sulphoxide

  • 19

    Determination of Sulphur in Soil

    2465 2470 2475 2480 2485 2490 2495

    0.0

    0.5

    1.0

    1.5

    2.0

    2.5

    3.0 ASD10908 LFH Sulphide (40%) Sulphoixde (6%) Sulphonic Acid (40%) Sulphate (14%) Fit

    µx (a

    rb. u

    nits

    )

    Photon Energy (eV)

    • quantification of sulphur in soil

  • 20

    XPS of S 2p of FeS2 c

    SR at 206 eV

    Schaufuss, Nesbitt , Bancroft, et al. , J.Elect. Spect. . 1998 Nesbitt et al . Amer. Min, 2000, 2001

  • 21

    Synchrotron Experimental Set-up

    A

    A

    A

    I0

    I

    I

    SR ring

    Au mesh

    Sample

    Total Electron Yield (top 50 Å)

    Fluorescence Yield (top 500 Å)

    µx=log (I0/I)

    hν’

  • 22

    Environmental; Mine Tailings

    Rj Neighbour in jth shell

    Photoelectron wave

    Scattered e wave

    Nature & bio-availability of heavy metals in mine waste

    Examine diffusion of materials into surrounding eco-system

  • 23

    11.8 12.0 12.2 12.4 12.6 12.8 13.0 13.2

    12.4 12.8 13.2

    Photon Energy (keV)

    • Element specific

    • Sensitive to local structure

    • Non-invasive

    • Applicable to all sample physical states

    • In Situ

    Characteristic X-ray Absorption Spectra from Raffinate, Leach Residue and Tailings

    As K

    Se K

    Pb LIII

    Tailing Sample Gypsum dissolution

    Leach Residue

    Raffinate Fe/As 3.5

  • 24

    Determination of Chemical States Using Arsenic X-ray Absorption Spectroscopy

    • Position of maximum absorption is related to oxidation state of arsenic

    • Tailing samples show a broadening due to a mixture of oxidation states

    11.86 11.87 11.88 11.89

    As K FeAsS As2O3 FeAsO4 Tailing

    As+5As+3As-1

    Photon Energy (keV)

  • 25

    Characterization of Chemical States within Leach Residue

    • XANES spectroscopy can be used to determine oxidation states within a sample

    • Leach residue is a mixture of at least 3 different oxidation states

    11.86 11.87 11.88 11.890.0

    0.5

    1.0

    1.5

    2.0 As-1 31%

    As3+ 19%As5+ 50%

    Photon Energy (keV)

    Leach Residue FeAsS As2O3 "Amorphous" FeAsO4 Sum

  • 26

    2 3 4 5 6 7 8 9 10

    -0.2

    -0.1

    0.0

    0.1

    0.2

    0.3 "Amorphous" FeAsO4 Raffinate Tailing

    k[Å-1]

    XAFS Comparison of Reference Compound to Raffinate and Tailing Samples

    χ(k)

    • Raffinate and tailings are different than “amorphous” FeAsO4

  • 27

    XAFS Comparison of Reference Compounds to Raffinate and Tailings

    Crystalline FeAsO4

    Arsenate adsorbed on FeOOH

    FeAsO4

    Raffinate

    Tailing

    2 4 6 8 10 12k[Å-1]

    k3χ(

    k)

  • 28

    Structural Environment around Arsenic within a Raffinate & Tailing Sample

    • Tailings & raffinate are different

    • Raffinate appears to contain some “amorphous” FeAsO4

    2.0 2.2 2.4 2.6 2.8 3.0 3.2 3.40.00

    0.02

    0.04

    0.06

    0.08

    0 1 2 3 4 5 6 7 80.00

    0.02

    0.04

    0.06

    0.08

    0.10

    0.12

    0.14

    0.16

    0.18

    0.20

    0.22

    Mag

    nitu

    de o

    f Fou

    rier T

    rans

    form

    of k

    3 χ(k

    )

    Crystalline FeAsO4 "Amorphous" FeAsO4 Arsenate adsorbed on FeOOH Neutralized raffinate Tailing

    R (Å)

    As-Fe

    As-O

  • 29

    11.86 11.88 11.90

    11.88

    Microprobe Study of Mine Tailings

    11.86 11.90

    Energy (keV)

    As(0) + As(III) As(V)

    Nickel Map Arsenic Map

    Iron Map Calcium Map

    500 µm

    500 µ

    m

    Energy (keV)

    As(0) + As(III)

    As(V)

    Photon Energy: 12 keV Spot size: 5µm

  • 30

    Selenium in the Environment

    12645 12650 12655 12660 12665 12670 12675 1268012650 12660 12670 12680

    CRC 292800-4200 ppb Se

    Se(+VI)Se(+IV)

    Se(0)Se(-II)

    CRC 30800-1300 ppb Se

    CRC 341600-1700 ppb Se

    Photon Energy (eV)

    http://www.uky.edu/%7Ersilver/CommunityService/coal.jpg

  • 31

    Effects of Earthworms on Soil Manganese Picture of the studied worm burrow.

    Mn K-edge micro-XANES spectra.

    • Earthworms move materials through soils

    • Fecal matter often contains higher levels of metals than surrounding soil

    • Not only do worms move material but they change the speciation of the metals

  • 32

    Toxic Metal Attenuation by Root-borne Carbonate Nodules

    •Zn and Mn correlate with nodules •Fe and Pb are fairly uniformly distributed •As is heterogenous and poorly correlated with epidermis

    S. Fendorf, C. Hansel, GeoCARS APS

  • 33

    Cadmium-Challenged Corn Roots

    Distance (microns, Arb. zero)

    1750 1800 1850 1900 1950 2000 2050 2100 2150 2200

    Nor

    mal

    ized

    Cou

    nts

    Distance (microns, Arb. zero)

    50 100 150 200 250 300 350

    Nor

    mal

    ized

    Cou

    nts

    Control Cadmium-Challenged

    Ca maps

    Cu map Naftel et al.

  • 34

    Micro-Imaging and Tomography Uranium fuel particle from Chernobyl B. Salbu, K.

    Janssens, T. Krekling, A. Simionovici, M. Drakopoulos, C. Raven, I. Snigireva, A. Snigirev, O. C. Lind, D. H. Oughton, F. Adams, V.a. Kashparov

    ESRF

    Chernobyl West

    Chernobyl North

  • 35

    glucose

    cellulose

    Using SR to see the wood from the trees

    • measurement of microfibril angle within wood

  • 36

    Opportunities • Characterization (oxidation states and mineralogy) of

    metals in solids – tailings – sludges from water treatment plants – sediments from limnocorrals – wetland uptake

    • sulphur associated with ARD • biochemistry of SRBs and

    bioreactors

  • 37

    Conclusion

    The uses of synchrotron light are as limitless as your

    imagination is!

  • www.cls.usask.ca

    www.lightsource.ca

    Slide Number 1The Canadian Light Source: A New Tool for Mining and Environmental HeadachesLight lets you see!The Construction SiteESRF AnimationSynchrotron Facility ComponentsBooster RingSynchrotron Hall, Main FloorElectromagnetic SpectrumSample Microprobe Beamline LayoutCanadian Light Source Inc. VisionMulti-disciplinary OpportunitiesIR Microscopy of a fluid inclusionInfrared Study of Organic Material on Marine SedimentComparing synchrotron & lab resultsX-ray Absorption Spectroscopy (XAS) using Synchrotron LightSoil ChemistryDetermination of Sulphur in SoilXPS of S 2p of FeS2Synchrotron Experimental Set-upEnvironmental; Mine TailingsCharacteristic X-ray Absorption Spectra from Raffinate, Leach Residue and TailingsDetermination of Chemical States Using Arsenic X-ray Absorption SpectroscopyCharacterization of Chemical States within Leach ResidueXAFS Comparison of Reference Compound to Raffinate and Tailing SamplesXAFS Comparison of Reference Compounds to Raffinate and TailingsStructural Environment around Arsenic within a Raffinate & Tailing SampleMicroprobe Study of Mine TailingsSelenium in the EnvironmentEffects of Earthworms on Soil ManganeseToxic Metal Attenuation by Root-borne Carbonate NodulesCadmium-Challenged Corn RootsMicro-Imaging and TomographySlide Number 35OpportunitiesConclusionwww.cls.usask.ca