铝合金与 mkpc 和波特兰水泥在金属-基体界面上的相互作用

IF 3.1 3区 地球科学 Q1 GEOCHEMISTRY & GEOPHYSICS
C. Fernández-García , P. Padilla-Encinas , R. Fernández , M.C. Alonso
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引用次数: 0

摘要

研究考虑了固定放射性铝的水泥基质。这两种材料之间的界面过程关系到储存库的长期稳定性。本研究比较了 CEM I 型普通硅酸盐水泥(OPC)和替代硅酸盐混合水泥(CEM IV 和 CEM I + 50% 硅灰)以及磷酸镁钾水泥(MKPC)。镁含量为 3.5% 的 Al A1050 和 Al AA5754 被用作活性金属合金。采用了两种暴露条件:(1) 水浸;(2) 密封塑料薄膜隔离。对长期腐蚀监测(Ecorr、icorr 和 Vcorr)进行了评估,以了解基体中铝反应性的影响。对相关的 H2 释放进行了量化,以了解金属/基质界面的变化。此外,还对孔隙离子浓度和孔隙微观结构进行了评估。试验结束后,对金属/基质界面的变化进行了分析。研究表明,经过 300 天的水浸泡后,CEM I + 50% 硅灰基质将孔隙溶液 pH 值降至 10.5,而 CEM I 仍为高碱性(pH 值为 12.9),CEM IV 则没有明显降低(pH 值为 12.3)。相比之下,MKPC 的 pH 值最低(7-9.8)。MKPC 的铝腐蚀率较低,其次是 CEM I + 50% SF,因为它们的 pH 值较低。在铝/CEM I 基质界面上观察到厚度为 90-50 μm 的腐蚀产物层,由铝和氧构成。此外,在基体(约 1 毫米深)中检测到铝的富集,从而形成了埃特林岩结核。在与释放的大量 H2 有关的界面处检测到了空隙。MKPC 基体由于反应活性较低,释放的 H2 较少,因此在金属/基体界面处没有发生任何变化。在金属表面附近观察到一个均匀致密的区域(30 μm),富含磷、钾和镁。
本文章由计算机程序翻译,如有差异,请以英文原文为准。

Interaction of aluminum alloys with MKPC and Portland-based cements on the metal-matrix interface

Interaction of aluminum alloys with MKPC and Portland-based cements on the metal-matrix interface

Cementitious matrices are considered for the immobilisation of radioactive aluminium. The processes occurring at the interface between both materials are relevant for the long-term stability of the repository. The present study compares Ordinary Portland cement (OPC), CEM I-type, with alternative Portland blended cement (CEM IV and CEM I + 50% silica fume) and magnesium potassium phosphate cement (MKPC). Al A1050 and Al AA5754, with 3.5% Mg, have been used as reactive metal alloys. Two exposure conditions were employed: (1) water immersion and (2) isolated in sealed plastic films. Long-term corrosion monitoring (Ecorr, icorr and Vcorr) was evaluated to understand the effect of Al reactivity in the matrix. The associated H2 release was quantified to understand the changes at the metal/matrix interface. Furthermore, pore ion concentrations and the pore microstructure were evaluated. The metal/matrix interface alterations were analysed at the end of the tests. The study revealed that after 300 days of water immersion, the CEM I + 50% of silica fume matrix had reduced the pore solution pH down to 10.5 compared to CEM I, which remained high alkaline (pH 12.9), and CEM IV with no significant decreases (pH 12.3). In contrast, MKPC showed the lowest pH (7–9.8). Low Al corrosion rates were found with MKPC, followed by CEM I + 50% SF according to their lower pH. A corrosion product layer of 90-50 μm thickness was observed at the Al/CEM I matrix interface constituted of aluminium and oxygen. Furthermore, enrichment in Al was detected in the matrix (around 1 mm depth), causing the formation of ettringite nodules. Voids were detected at the interface level associated with the high volume of H2 released. The MKPC matrix showed no alteration at the metal/matrix interface due to the lower reactivity of the matrix and lower H2 release. A homogeneous and dense region (30 μm) rich in phosphorous, potassium and magnesium was observed near the metal surface.

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来源期刊
Applied Geochemistry
Applied Geochemistry 地学-地球化学与地球物理
CiteScore
6.10
自引率
8.80%
发文量
272
审稿时长
65 days
期刊介绍: Applied Geochemistry is an international journal devoted to publication of original research papers, rapid research communications and selected review papers in geochemistry and urban geochemistry which have some practical application to an aspect of human endeavour, such as the preservation of the environment, health, waste disposal and the search for resources. Papers on applications of inorganic, organic and isotope geochemistry and geochemical processes are therefore welcome provided they meet the main criterion. Spatial and temporal monitoring case studies are only of interest to our international readership if they present new ideas of broad application. Topics covered include: (1) Environmental geochemistry (including natural and anthropogenic aspects, and protection and remediation strategies); (2) Hydrogeochemistry (surface and groundwater); (3) Medical (urban) geochemistry; (4) The search for energy resources (in particular unconventional oil and gas or emerging metal resources); (5) Energy exploitation (in particular geothermal energy and CCS); (6) Upgrading of energy and mineral resources where there is a direct geochemical application; and (7) Waste disposal, including nuclear waste disposal.
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