8 research outputs found

    Determination of the elemental distribution of human joint bones by SR micro-XRF

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    In humans the toxic trace element lead (Pb) mainly accumulates in the skeletal tissue where it resides for a long period. Although Pb is known to play a role in bone and cartilage diseases, the distribution of Pb in these tissues is mostly unknown. Therefore synchrotron-radiation-induced micro x-ray fluorescence analysis (SR m-XRF) in various geometries was used to determine the distributions of Pb, Ca, Zn and Sr at the cartilage-bone interface in human femoral heads and patellae. SR m-XRF results were matched with backscattered electron (BE) images providing information on structural features of the tissue. Conventional SR m-XRF at HASYLAB beamline L showed that Pb mostly accumulates in a zone of some micrometers around the transition between non-calcified and calcified cartilage. However, the relatively large sample thickness did not allowmore precise conclusions. Exploiting the 3D capabilities of confocal SR m-XRF and SR microfluorescence tomography at ANKA Fluo-Topo beamline and HASYLAB beamline L, the spatial resolution could be improved and a highly specific accumulation of Pb at the tidemark, the calcification front between non-calcified and calcified cartilage,was detected. Itwas found that Pb and Zn accumulation coincide at the tidemark. Since the tidemark plays an important role in osteoarthritis, the results may strengthen other authors’ conclusions that Pb is associated with this joint disease. Although offering less spatial resolution when compared tomicro-tomography, confocal SR m-XRF is best suited for such studies. It facilitates the comparison of element maps with other imaging techniques like BE imaging

    Improved micro x-ray fluorescence spectrometer for light element analysis

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    (or μg/cm²) were obtained by measuring various thin metal foils under different conditions

    Assessment of chemical species of lead accumulated in tidemarks of human articular cartilage by X-ray absorption near-edge structure analysis

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    A highly specific accumulation of the toxic element lead was recently measured in the transition zone between non-calcified and calcified normal human articular cartilage. This transition zone, the so-called ‘tidemark’, is considered to be an active calcification front of great clinical importance. However, little is known about the mechanisms of accumulation and the chemical form of Pb in calcified cartilage and bone. Using spatially resolved X-ray absorption near-edge structure analysis (m-XANES) at the Pb L3-edge, the chemical state of Pb in the osteochondral region was investigated. The feasibility of the m-XANES set-up at the SUL-X beamline (ANKA synchrotron light source) was tested and confirmed by comparing XANES spectra of bulk Pb-reference compounds recorded at both the XAS and the SUL-X beamline at ANKA. The m-XANES set-up was then used to investigate the tidemark region of human bone (two patella samples and one femoral head sample). The spectra recorded at the tidemark and at the trabecular bone were found to be highly correlated with the spectra of synthetic Pb-doped carbonated hydroxyapatite, suggesting that in both of these very different tissues Pb is incorporated into the hydroxyapatite structure

    Test-retest reliability of pulmonary oxygen uptake and muscle deoxygenation during moderate- and heavy-intensity cycling in youth elite-cyclists

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    This is the author accepted manuscript. The final version is available from Taylor & Francis via the DOI in this recordTo establish the test-retest reliability of pulmonary oxygen uptake ( O2), muscle deoxygenation (deoxy[heme]) and tissue oxygen saturation (StO2) kinetics in youth elitecyclists. From baseline pedaling, 15 youth cyclists completed 6-min step transitions to a moderate- and heavy-intensity work rate separated by 8 min of baseline cycling. The protocol was repeated after 1 h of passive rest. O2 was measured breath-by-breath alongside deoxy[heme] and StO2 of the vastus lateralis by near-infrared spectroscopy. Reliability was assessed using 95% limits of agreement (LoA), the typical error (TE) and the intraclass correlation coefficient (ICC). During moderate- and heavy-intensity step cycling, TEs for the amplitude, time delay and time constant ranged between 3.5-21.9% and 3.9-12.1% for O2 and between 6.6-13.7% and 3.5-10.4% for deoxy[heme], respectively. The 95% confidence interval for estimating the kinetic parameters significantly improved for ensemble-averaged transitions of O2 (p<0.01) but not for deoxy[heme]. For StO2, the TEs for the baseline, end-exercise and the rate of deoxygenation were 1.0-42.5% and 1.1-5.5% during moderate- and heavy-intensity exercise, respectively. The ICC ranged from 0.81-0.99 for all measures. Test-retest reliability data provides limits within which changes in O2, deoxy[heme] and StO2 kinetics may be interpreted with confidence in youth athletes

    Effects of EMFs from Undersea Power Cables on Elasmobranchs and Other Marine Species.

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    Anthropogenic electromagnetic fields (EMFs) have been introduced into the marine environmentaround the world and from a wide variety of sources for well over a century. Despite this, littleis known about potential ecological impacts from EMFs. For decades, power transmissioncables have been installed across bays and river mouths, and connecting near-shore islands to themainland, with little consideration of possible effects to marine species from EMFs. At a time ofgreater environmental awareness, the US now faces the possibility of a new source of EMFs overa much greater extent of the seabed from offshore renewable energy facilities in coastal waters.This literature review synthesizes information on the types of power cables and models theexpected EMFs from representative cables. Available information on electro- and magnetosensitivityof marine organisms, including elasmobranchs (sharks and rays) and other fishspecies, marine mammals, sea turtles, and invertebrates is summarized and used in conjunctionwith the power cable modeling results to evaluate the level of confidence the existing state ofknowledge provides for impact assessment. Gaps in our knowledge of power cablecharacteristics and the biology needed to understand and predict impacts are summarized andform the basis of recommendations for future research priorities. Potential mitigationopportunities are described with a discussion of their potential secondary impacts as well assuggested methods for monitoring mitigation effectiveness. Finally, because interest in offshorerenewable energy has increased throughout US coastal waters, there is a concern that organismscould be exposed to multiple seabed power cables. Cumulative effects of this exposure are discussed
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