1,069 research outputs found
Uranium in the eastern margin of western Siberian plate, or how to overcome crisis of uranium
Теоретические построения [5], свидетельствующие о катагенно-осадочном, эксфильтрационном происхождении железных руд Западно-Сибирского бассейна являются дополнительным фактором принципиальной возможности глубинного происхождения не только радиоактивных металлов, но и ванадия, марганца, благородных металлов и железа. Theoretical constructions [5], which provide evidence of catagenic-aqueous, exfiltration origin of ores of Western Siberian basin, are an additional attribute of principal opportunity for deep seated origin of not only radioactive metals, but also of vanadium, manganese, noble metals and ferrum
ICAM-1-expressing neutrophils exhibit enhanced effector functions in murine models of endotoxemia
This work was supported by funds from the Wellcome Trust (098291/Z/12/Z and 101604/Z/13/Z) (S.N.) and the British Heart Foundation (FS/11/19/28761) (A.W.)
Shifts in targeting of class switch recombination sites in mice that lack μ switch region tandem repeats or Msh2
The mechanisms that target class switch recombination (CSR) to antibody gene switch (S) regions are unknown. Analyses of switch site locations in wild-type mice and in mice that lack the Sμ tandem repeats show shifts indicating that a 4–5-kb DNA domain (bounded upstream by the Iμ promoter) is accessible for switching independent of Sμ sequences. This CSR-accessible domain is reminiscent of the promoter-defined domains that target somatic hypermutation. Within the 4–5-kb CSR domain, the targeting of S site locations also depends on the Msh2 mismatch repair protein because Msh2-deficient mice show an increased focus of sites to the Sμ tandem repeat region. We propose that Msh2 affects S site location because sequences with few activation-induced cytidine deaminase targets generate mostly switch DNA cleavages that require Msh2-directed processing to allow CSR joining
The requirement for lymphocyte function-associated antigen 1 in homotypic leukocyte adhesion stimulated by phorbol ester.
Variation in Organophosphate Pesticide Metabolites in Urine of Children Living in Agricultural Communities
Children of migrant farmworkers are at increased risk of exposure to organophosphate pesticides because of “carry-home” transport processes and residential location. Although this at-risk status is generally recognized, few available reports describe the extent of this exposure among agricultural communities. We quantified dialkyl phosphate (DAP) levels in serial samples of urine from 176 children, 2–6 years of age, in three Oregon communities hosting differing agricultural industries: pears, cherries, and fruit berries. Up to three spot samples of urine were collected from children at the beginning, mid-point, and end of their parents’ work seasons. The median levels of dimethylthiophosphate (DMTP), the most commonly detected metabolite, was significantly higher in urine samples from children in each of the three agricultural communities (17.5, 19.0, and 41.0 ng/mL) relative to a reference group of children who lived in an urban community and whose parents did not work in agriculture (6.5 ng/mL; Kruskal-Wallis, p < 0.001). After controlling for age, sex, and weight, the median level of DMTP in children in the pear community was 1.92 times higher than the level in children of the berry community [95% confidence interval (CI), 1.14–3.23] and 1.75 times higher than the level in children of the cherry community (95% CI, 0.95–3.23). We observed increasing levels of DMTP across the work season only within the berry community. Levels decreased in the cherry community and remained constant in the pear community. Substantial temporal variation within the children followed demonstrates the need for multiple urine samples to most accurately characterize longer term and/or cumulative exposure. The observed variability in urinary DAP levels, between communities and over time, could be attributed to the types and amounts of organophosphate pesticides used, the timing of applications and degradation of residues in the environment, work operations and hygiene practices, the proximity of housing to orchards and fields, or the movement of these working families. Additional studies of variation in pesticide exposure across agricultural regions are needed
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