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Fe(Ⅲ)-montmorillonite: Basic Properties And Diffusion Of Tracers Relevant To Alteration Of Bentonite In Deep Geological Disposal

机译:Fe(Ⅲ)-蒙脱土:深部地质处置中与膨润土蚀变有关的示踪剂的基本性质和扩散

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In the deep geological repository of high-level nuclear waste (HLW), the interaction of carbon steel (Fe) overpack container and the back-fill clay mineral, montmorillonite (mont), is an important issue to be clarified in view of the long-term performance of clay mineral as an engineered barrier. To arrive at some understanding of the altered clay at the Fe/clay interface, Fe(Ⅲ)-mont is used here for preliminary investigation to see if there is any considerable difference in the basic properties, mainly diffusion of tracers with respect to Na-mont, although Fe(Ⅲ)-mont is not a realistic analogue of altered clay in the reducing chemistry conditions anticipated in the subsurface of HLW, unlike Fe(Ⅱ)-mont which is difficult to prepare and handle in the ambient atmosphere due to its gradual oxidation. Fe(Ⅲ)-mont was prepared by the conventional cation exchange method with 0.4 M FeCl_3 solution. The total Fe(Ⅲ) ions adsorbed was about 1.42 meq/g, while the CEC of parent clay was 1.2 meq/g. Thus ~ 18% excess Fe (Ⅲ) ions were present presumably as iron oxy hydroxide, i.e., about 2 wt.% with respect to FeOOH or Fe(OH)_3 in the bulk sample. The sample was further characterized by X-ray diffraction (XRD), infrared (IR), thermogravimetry, magnetization, and the methylene blue (MB) adsorption. From these conventional techniques, the minor Fe-oxide phase associated with the Fe(Ⅲ)-mont could not be detected, although we cannot rule out its existence. The paramagnetic behavior of Fe(Ⅲ)-mont was evident from the Curie-Weiss plot (300 K down to 5 K). Some basic properties like osmotic swelling, diffusion of tracers and thermal stability are evaluated here. The osmotic swelling of Fe(Ⅲ)-mont was very low, ~ 5 ml/g, while that of Na-mont was >40 ml/g. Apparent diffusion coefficient (D_a) of tracers viz., ~(22)Na~+, HTO and ~(36)Cl~- was determined using compacted (dry density, ρ_d = 1.0,1.6 Mg m~(-3)), water-saturated Fe(Ⅲ)-mont. There was no considerable change in D_a of these tracers in Fe(Ⅲ)-mont when compared to that in Na-mont, in spite of higher pore water availability in Fe(Ⅲ )-mont due to reduced swelling. For instance at ρ_d = 1.6 and 25 ℃, D_a (×10~(-1)m~2/s) of ~(22)Na~+ (2.6) was same as that in Na-mont whereas D_a of HTO (11.4) and ~(36)Cl~- (1.0) have varied marginally. For comparison, the corresponding D_a (×10~(-11) m~2/s) values in Na-mont were 2.7,7.2 and 3.4, respectively. Also, at ρ_d = 1.6, the diffusion activation energy (E_A, kJ mol~(-1)) of HTO (17.5) in Fe (Ⅲ)-mont was comparable to that in free water, however, E_A of ~(36)Cl~- (13.1) was remarkably low, which may be ascribed to the so-called 'anion exclusion' effect. Furthermore, thermal stability of Fe(Ⅲ)-mont indicated the existence of interlayer Fe(Ⅲ) in the ionic state up to ~190 ℃, based on the XRD and MB adsorption test. On heating to >200 ℃, irreversible dehydration of interlayer cations occurred, and the chemisorption of NH_3 indicated two distinct acid sites at about 300 ℃ and 600 ℃.
机译:在高级别核废料(HLW)的深层地质处置库中,鉴于长期以来,需要澄清的一个重要问题是碳钢(Fe)外包装容器与回填粘土矿物蒙脱土(mont)的相互作用。粘土矿物作为工程屏障的长期性能。为了对Fe /粘土界面处的蚀变粘土有一些了解,此处使用Fe(Ⅲ)-mont进行初步研究,以查看基本特性是否存在相当大的差异,主要是示踪剂相对于Na-的扩散mont,尽管Fe(Ⅲ)-mont在HLW地下预期的还原化学条件下不是变质粘土的现实类似物,与Fe(Ⅱ)-mont不同,Fe(Ⅱ)-mont由于其高聚物难以在环境中制备和处理逐渐氧化。采用传统的阳离子交换法,用0.4 M FeCl_3溶液制备Fe(Ⅲ)-mont。吸附的Fe(Ⅲ)离子总量约为1.42meq / g,而母体粘土的CEC为1.2meq / g。因此,大概有18%的Fe(Ⅲ)离子以氢氧化铁的形式存在,即,相对于整体样品中的FeOOH或Fe(OH)_3约为2 wt。%。通过X射线衍射(XRD),红外(IR),热重分析,磁化和亚甲基蓝(MB)吸附进一步表征样品。从这些常规技术中,虽然我们不能排除它的存在,但无法检测到与Fe(Ⅲ)-mont有关的微量Fe-氧化物相。 Fe(Ⅲ)-mont的顺磁行为在居里-魏斯图(300 K到5 K)中很明显。这里评估了一些基本特性,例如渗透溶胀,示踪剂的扩散和热稳定性。 Fe(Ⅲ)-mont的渗透溶胀非常低,约为5 ml / g,而Na-mont的渗透溶胀> 40 ml / g。示踪剂的表观扩散系数(D_a),即〜(22)Na〜+,HTO和〜(36)Cl〜-使用压实法确定(干密度,ρ_d= 1.0,1.6 Mg m〜(-3)),水饱和Fe(Ⅲ)-mont。尽管在Fe(Ⅲ)-mont中,这些示踪剂的D_a与Na-mont中的D_a没有显着变化,尽管由于溶胀减少,在Fe(Ⅲ)-mont中的孔隙水利用率更高。例如在ρ_d= 1.6和25℃时,〜(22)Na〜+(2.6)的D_a(×10〜(-1)m〜2 / s)与Na-mont相同,而HTO的D_a(11.4 )和〜(36)Cl〜-(1.0)略有变化。为了比较,Na-mont中相应的D_a(×10〜(-11)m〜2 / s)值分别为2.7、7.2和3.4。同样,在ρ_d= 1.6时,HTO(17.5)在Fe(Ⅲ)-mont中的扩散活化能(E_A,kJ mol〜(-1))与自由水中的相当,但是,E_A为〜(36)。 Cl-(13.1)非常低,这可能归因于所谓的“阴离子排斥”效应。此外,根据XRD和MB吸附试验,Fe(Ⅲ)-mont的热稳定性表明离子态的中间层Fe(Ⅲ)的存在高达190℃。加热到> 200℃时,发生层间阳离子的不可逆脱水,NH_3的化学吸附表明在约300℃和600℃存在两个不同的酸位。

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