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首页> 外文期刊>Journal of Nuclear Materials: Materials Aspects of Fission and Fusion >Glass-bonded iodosodalite waste form for immobilization of I-129
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Glass-bonded iodosodalite waste form for immobilization of I-129

机译:用于固定I-129的玻璃键合的碘癸酸盐废物形式

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Immobilization of radioiodine is an important requirement for current and future nuclear fuel cycles. Iodosodalite [Na-8(AlSiO4)(6)I-2] was synthesized hydrothermally from metakaolin, NaI, and NaOH. Dried unwashed sodalite powders were used to synthesize glass-bonded iodosodalite waste forms (glass composite materials) by heating pressed pellets at 650, 750, or 850 degrees C with two types of sodium borosilicate glass binders. These heat-treated specimens were characterized with X-ray diffraction, Fourier-transform infrared spectroscopy, scanning electron microscopy, energy dispersive spectroscopy, thermal analysis, porosity and density measurements, neutron activation analysis, and inductively-coupled plasma mass spectrometry. For the best waste form produced (pellets mixed with 10 mass% of glass binder and heat-treated at 750 degrees C), the maximum possible elemental iodine loading was 19.8 mass%, but only similar to 8-9 mass% waste loading of iodine was retained in the waste form after thermal processing. Other pellets with higher iodine retention either contained higher porosity or were incompletely sintered. ASTM C1308 and C1285 (product consistency test, PCT) experiments were performed to understand chemical durability under diffusive and static conditions. The C1308 test resulted in significantly higher normalized loss compared to the C1285 test, most likely because of the strong effect of neutral pH solution renewal and prevention of ion saturation in solution. Both experiments indicated that release rates of Na and Si were higher than for Al and I, probably due to a poorly durable Na-Si-O phase from the glass bonding matrix or from initial sodalite synthesis; however the C1308 test result indicated that congruent dissolution of iodosodalite occurred. The average release rates of iodine obtained from C1308 were 0.17 and 1.29 gm(-2) d(-1) for 80 or 8 m(-1), respectively, and the C1285 analysis gave a value of 2 x 10(-5) g m(-2) d(-1), which is comparable to
机译:放射性碘的固定化是当前和未来的核燃料循环的一个重要要求。 Iodosodalite的[Na-8(AlSiO4)(6)I-2〕是由偏高岭土,碘化钠,和NaOH水热合成。未洗涤的干燥粉末方钠石通过在650,750,或850度下加热压片用两种类型的硼硅酸钠玻璃的粘合剂用于合成玻璃粘合iodosodalite废物体(玻璃复合材料)。这些热处理后的试样利用X射线衍射,傅里叶变换红外光谱法,扫描电子显微镜,能量色散光谱学,热分析,孔隙度和密度测量,中子活化分析,和电感耦合等离子体质谱法。为产生最佳废物形式(与玻璃粘合剂和热处理,在750℃下的10质量%的混合粒料),最大可能元素碘负载量为19.8质量%,但只类似于碘的8-9质量%废料加载被保留在热处理后的废物体。具有较高碘保留其它粒料或者含有较高的孔隙率或不完全进行烧结。 ASTM C1308和C1285(产品一致性试验,PCT)进行实验以了解漫射和在静态条件下的化学稳定性。该C1308测试结果为显著较高的标准化的损失相比,C1285测试,最有可能的,因为中性pH溶液重建和预防工作的解决方案离子饱和的强烈影响。这两个实验表示Na和Si的释放速率比为Al和余高,可能是由于从玻璃粘合基质或从初始方钠石的合成耐用很差的Na-Si-O的相;但是C1308试验结果表明全等溶解iodosodalite发生。从C1308得到碘的平均释放速率为0.17和1.29克(-2)d(-1),80或8米(-1),分别与C1285分析得到的2×10的值(-5)克(-2)d(-1),这与

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