209 research outputs found

    Polar Bear and Mammoth on the Pribilof Islands

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    Museum specimens of polar bear from the Pribilof Islands include the skull of an individual shot on St. Paul, and fragmentary remains of uncertain geologic age from a lava cave in Bogoslof Hill, St. Paul, once thought to represent a distinct species. Mammoth remains have been discovered from time to time beginning in 1836, and are here regarded as in part valid evidence that the mammoth actually lived in the area. The literature pertaining to these species on the Pribilof Islands is reviewed.L’ours polaire et le mammoth dans les Pribilof.  (Au musée Smithsonian) Les spécimens d’ours polaire des îles de Pribilof comprenent le crâne d’un individu abattu sur l’île Saint-Paul, et des restes fragmentaires, d’âge géologique incertain, provenant d’une caverne dans les laves du mont Bogoslof, sur Saint-Paul, et qu’on a déjà cru représenter une espèce distincte.  On a découvert de temps à autre, depuis 1836, des restes de mammouth, et l’auteur les considère comme une preuve partielle valide que le mammouth a vraiment vécu dans la région.  On passe en revue les références pertinentes à ces deux espèces pour les Pribilof

    200-BP-1 Prototype Hanford Barrier - 15 Years of Performance Monitoring

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    Engineered surface barriers are recognized as a remedial alternative to the removal, treatment and disposal of near-surface contaminants at a variety of waste sites within the DOE complex. One issue impacting their acceptance by stakeholders the use of limited data to predict long-term performance. In 1994, a 2-ha multi-component barrier was constructed over an existing waste disposal site at Hanford using natural materials. Monitoring has been almost continuous for the last 15 yrs and has focused on barrier stability, vegetative cover, plant and animal intrusion, and the components of the water balance, including precipitation, runoff, storage, drainage, and percolation. The total precipitation received from October 1994 through August 2008 was 3311 mm on the northern half (formerly irrigated), and 2638 mm on the southern, non-irrigated half. Water storage in the fine-soil layer shows a cyclic pattern, increasing in the winter and decreasing in the spring and summer to a lower limit of around 100 mm, regardless of precipitation, in response to evapotranspiration. Topographic surveys show the barrier and side slopes to be stable and the pea-gravel admix has proven effective in minimizing erosion through the creation of a desert pavement during deflationary periods. Three runoff events have been observed but the 600-mm design storage capacity has never been exceeded. Total percolation ranged from near zero amounts under the soil-covered plots to over 600 mm under the side slopes. The asphaltic concrete prevented any of this water from reaching the buried waste thereby eliminating the driving force for the contaminant remobilization. Plant surveys show a relatively high coverage of native plants still persists after the initial revegetation although the number of species decreased from 35 in 1994 to 10 in 2009. Ample evidence of insect and small mammal use suggests that the barrier is behaving like a recovering ecosystem. In September 2008, the north half of the barrier was burned to remove vegetation and study the effects of fire on barrier performance. The most immediate effects has been on water storage patterns with the bare surface showing a slower accumulation of water, a smaller peak storage and a delayed release relative to the unburned side due to evaporation . Nonetheless the residual storage at the end of the year was similar for the burned and unburned sides

    Numerical Modeling of 90Sr and 137Cs Transport from a Spill in the B-Cell of the 324 Building, Hanford Site 300 Area

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    To characterize the extent of contamination under the 324 Building, a pit was excavated on the north side of the building in 2010 by Washington Closure Hanford LLC (WCH). Horizontal closed-end steel access pipes were installed under the foundation of the building from this pit and were used for measuring temperatures and exposure rates under the B-Cell. The deployed sensors measured elevated temperatures of up to 61 C (142 F) and exposure rates of up to 8,900 R/hr. WCH suspended deactivation of the facility because it recognized that building safety systems and additional characterization data might be needed for remediation of the contaminated material. The characterization work included additional field sampling, laboratory measurements, and numerical flow and transport modeling. Laboratory measurements of sediment physical, hydraulic, and geochemical properties were performed by Pacific Northwest National Laboratory (PNNL) and others. Geochemical modeling and subsurface flow and transport modeling also were performed by PNNL to evaluate the possible extent of contamination in the unsaturated sand and gravel sediments underlying the building. Historical records suggest that the concentrated 137Cs- and 90Sr-bearing liquid wastes that were spilled in B-Cell were likely from a glass-waste repository testing program associated with the Federal Republic of Germany (FRG). Incomplete estimates of the aqueous chemical composition (no anion data provided) of the FRG waste solutions were entered into a geochemical speciation model and were charge balanced with nitrate to estimate waste composition. Additional geochemical modeling was performed to evaluate reactions of the waste stream with the concrete foundation of the building prior to the stream entering the subsurface

    Differentiating Anti-Lamina Lucida and Anti-Sublamina Densa Anti-BMZ Antibodies by Indirect Immunofluorescence on 1.0 M Sodium Chloride-Separated Skin

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    L'immunofluorescence indirecte sur la peau séparée est une méthode fiable pour différencier les anticorps contre la lame transparente et les anticorps contre la sous-lame dense des maladies bulleuses et la différenciation entre les anticorps est essentielle pour un diagnostic exact chez certains malades. Les anticorps contre la lame transparente dans la pemphigoïde bulleuse peuvent présenter plusieurs spécificités
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