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Megaloblastic anemia, associated with surgically produced gastrointestinal abnormalities.

Two of the mechanisms for vitamin B(12) deficiency, leading to megaloblastic anemia, are the result of surgically produced abnormalities of the gastrointestinal tract. The basic mechanism is different for each lesion. Total gastrectomy results in complete lack of intrinsic factor which is necessary for vitamin B(12) absorption. It is believed that if patients survive long enough and are not given prophylactic vitamin B(12) therapy, all would develop megaloblastic anemia. Intestinal anastomosis leading to stasis of intestinal contents, with overgrowth of bacteria may cause vitamin B(12) deficiency through bacterial interference with the utilization of vitamin B(12). Use of radioactive vitamin B(12) (cobalt(60)-labeled B(12)) has led to a better understanding of the pathogenesis of both types of megaloblastic anemia. The radioactive vitamin provides a useful tool for study of its absorption from the gastrointestinal tract.

Anastomosis, Surgical↗

Chromium-cage complex as contrast agent in MR imaging--biodistribution studies of the [57Co]cobalt analogue.

The synthesis and T1 and T2 relaxivities of the Cr(III)-(NH2)-Sar-cage complex is reported. An outer-sphere relaxation mechanism is postulated for the relaxivity of the complex. Tissue distribution studies in mice using a [57Co]cobalt analogue as a radioactive tracer showed that the complex is excreted rapidly in the urine. Some renal uptake of the complex is seen. Appreciable uptake of labelled cage complex was observed in 3-methylcholanthrene induced murine rhabdomyosarcoma.

Animals↗

Effect of pH, ionic strength and fulvic acid on the sorption and desorption of cobalt to bentonite.

Humic substances and bentonite have attracted great interest in radioactive waste management. Here the sorption of cobalt on bentonite in the presence and absence of fulvic acid (FA) under ambient conditions was studied. The effects of pH, ionic strength, FA and solution concentrations on cobalt sorption to bentonite were also investigated using batch techniques. The results indicate that the sorption of cobalt is strongly dependent on pH and is independent of ionic strength under our experimental conditions. Surface complexation is considered the main mechanism of cobalt sorption to bentonite. In the presence of FA, little effect of FA on cobalt sorption was found at pH<6; a positive effect of FA on cobalt sorption was found for pH 6-8; and a negative effect of FA on cobalt sorption was found at pH>8. The addition sequences of FA/Co(2+) to the bentonite suspension on the sorption of cobalt to FA-coated bentonite were also studied. The results indicated that the sorption is not influenced by the addition sequences. Some possible mechanisms are discussed.

Journal Article↗

Fate of heavy metals and radioactive metals in gasification of sewage sludge.

The fates of radioactive cadmium, strontium, cesium, cobalt, arsenic, mercury, zinc, and copper spiked into sewage sludge were determined when the sludge was gasified by a process that maximizes production of char from the sludge (ChemChar process). For the most part the metals were retained in the char product in the gasifier. Small, but measurable quantities of arsenic were mobilized by gasification and slightly more than 1% of the arsenic was detected in the effluent gas. Mercury was largely mobilized from the solids in the gasifier, but most of the mercury was retained in a filter composed of char prepared from the sludge. The small amounts of mercury leaving the gasification system were found to be associated with an aerosol product generated during gasification. The metals retained in the char product of gasification were only partially leachable with 50% concentrated nitric acid.

Environmental Monitoring↗

Acid leaching studies of neutron-irradiated chyrsotile asbestos.

Samples of chrysotile from Quebec (UICC B and Jeffrey 4T-30) and from the Coalinga region of California (Calidria RG-144) were irradiated with thermal neutrons in a reactor. The main activation products induced were 46Sc, 51Cr, 59Fe and 60Co. Accurately weighed samples of the irradiated materials were dispersed in N HCl by hand shaking for 10 s. After leaching for predetermined periods at 25 degrees C, the samples were filtered and the concentrations of Mg determined in the filtrates by inductively-coupled plasma atomic emission spectrometry (IPC-AES) and the activities of the four radionuclides by high resolution gamma-ray spectrometry. Similar measurements were made on solutions obtained by refluxing samples of irradiated chrysotile with 2N HCl for 2 h. The specific activities of each of the four activation products were calculated in arbitrary units and, as the concentrations of Sc, Cr, Fe and Co in the UICC B sample had already been determined, it was possible to estimate the concentrations of these elements in the other two samples. Similarities in the leaching patterns of magnesium and of the activation products showed that with all samples, high proportions of the parent trace elements were present in the form of isomorphous substitutes for magnesium in structural brucite. Agreement was closest with the Calidria chrysotile in which all the radionuclides had a similar pattern. With the Jeffrey and UICC B samples, the presence of a high proportion of the iron as relatively insoluble magnetite accounted for the observed discrepancy in behaviour between 59Fe and Mg. More detailed calculation of leaching rates over specific time intervals showed that, initially, 51Cr and 60Co dissolved more rapidly than Mg but that this was followed by a period in which the opposite was the case. It was concluded that the Calidria RG-144 sample is an ideal candidate for studies of magnesium dissolution in vivo.

Asbestos, Amphibole↗

Cobalt-60 bombs.

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Bombs↗

Migration of radionuclides controlled by several different migration mechanisms through a sandy soil layer.

Column experiments have been carried out on the migration of 60Co and 137Cs through a sandy soil layer in order to examine the migration of radionuclides controlled by several different migration mechanisms. Radionuclide concentration distribution between the effluent and the sandy soil layer was measured after 10 L of the solution containing the radionuclides were introduced into the column from the top of the layer at a constant flow rate. Most of the 60Co and 137Cs remained attached to the layer, and a small amount of each radionuclide; at concentrations of 0.3 and 0.1%, respectively; flowed out from the soil layer. The migration of the mobile fraction of these radionuclides is different from that expected of an ideal cation. These results suggest that the mobile fraction of these radionuclides migrates as non-cationic forms which are not adsorbed into the soil matrix by equilibrium ion exchange.

Cesium Radioisotopes↗