{"title":"Carbonation Effect on the Chloride Profile","authors":"C. Andrade","doi":"10.23967/dbmc.2020.232","DOIUrl":null,"url":null,"abstract":". In natural marine exposures, the chloride profile may have a maximum in the concrete surface (surface concentration) or this maximum may appear some mm or even centimeters, in depth. This fact has been attributed to a) a “washing effect” due the continuous action of the sea water, b) the wet and dry “convection” induced by the action of the sea water waves c) the leaching of the hydroxide ions or d) the carbonation of the external layer of concrete. In a test in the laboratory, the profile resulting in a diffusion chloride test in most of the cases presents the maximum in the surface of the specimen but seldom has this maximum beyond the surface. This behaviour in natural and in laboratory conditions, although noticed, has not been satisfactorily explained. The author has addressed the problem in a previous communication. In present one shows evidences on the role of the carbonates/bicarbonates in the water of the testing solution. It can be deduced from the analysis of the profiles obtained with de-carbonated solutions that the carbonates/bicarbonates ions compete with the chlorides in the binding with the hydrated cement phases, which results in a modification of the chloride profile and a different diffusion coefficient. The maximum seems to be produced by the higher mobility of the chloride with respect to the carbonate/bicarbonate. The bound chlorides are displaced by the carbonation and the free chlorides move inside forward. In the external parts less total chlorides are noticed because the free chlorides are function of the bound chlorides.","PeriodicalId":409611,"journal":{"name":"XV International Conference on Durability of Building Materials and Components. eBook of Proceedings","volume":"55 1","pages":"0"},"PeriodicalIF":0.0000,"publicationDate":"2020-09-25","publicationTypes":"Journal Article","fieldsOfStudy":null,"isOpenAccess":false,"openAccessPdf":"","citationCount":"0","resultStr":null,"platform":"Semanticscholar","paperid":null,"PeriodicalName":"XV International Conference on Durability of Building Materials and Components. eBook of Proceedings","FirstCategoryId":"1085","ListUrlMain":"https://doi.org/10.23967/dbmc.2020.232","RegionNum":0,"RegionCategory":null,"ArticlePicture":[],"TitleCN":null,"AbstractTextCN":null,"PMCID":null,"EPubDate":"","PubModel":"","JCR":"","JCRName":"","Score":null,"Total":0}
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Abstract

. In natural marine exposures, the chloride profile may have a maximum in the concrete surface (surface concentration) or this maximum may appear some mm or even centimeters, in depth. This fact has been attributed to a) a “washing effect” due the continuous action of the sea water, b) the wet and dry “convection” induced by the action of the sea water waves c) the leaching of the hydroxide ions or d) the carbonation of the external layer of concrete. In a test in the laboratory, the profile resulting in a diffusion chloride test in most of the cases presents the maximum in the surface of the specimen but seldom has this maximum beyond the surface. This behaviour in natural and in laboratory conditions, although noticed, has not been satisfactorily explained. The author has addressed the problem in a previous communication. In present one shows evidences on the role of the carbonates/bicarbonates in the water of the testing solution. It can be deduced from the analysis of the profiles obtained with de-carbonated solutions that the carbonates/bicarbonates ions compete with the chlorides in the binding with the hydrated cement phases, which results in a modification of the chloride profile and a different diffusion coefficient. The maximum seems to be produced by the higher mobility of the chloride with respect to the carbonate/bicarbonate. The bound chlorides are displaced by the carbonation and the free chlorides move inside forward. In the external parts less total chlorides are noticed because the free chlorides are function of the bound chlorides.
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碳酸化对氯化物剖面的影响
。在自然海洋暴露中,氯化物剖面可能在混凝土表面有一个最大值(表面浓度),或者这个最大值可能出现在几毫米甚至几厘米的深度。这一事实归因于a)海水持续作用的“冲刷效应”,b)海水波浪作用引起的干湿“对流”,c)氢氧化物离子的浸出,d)混凝土外层的碳化作用。在实验室的试验中,在大多数情况下,导致扩散氯化物试验的剖面在试样表面出现最大值,但很少在表面以外出现最大值。这种行为在自然和实验室条件下,虽然注意到,但没有令人满意的解释。作者在之前的通信中已经解决了这个问题。目前有证据表明碳酸盐/重碳酸盐在测试溶液中的作用。通过对脱碳化溶液剖面的分析,可以推断出碳酸盐/碳酸氢盐离子在与水化水泥相结合时与氯化物竞争,从而导致氯化物剖面的改变和扩散系数的不同。最大值似乎是由氯化物相对于碳酸盐/碳酸氢盐的高迁移率产生的。结合的氯化物在碳化作用下移位,自由的氯化物向内移动。由于游离氯化物是结合氯化物的函数,所以在外部部分总氯化物较少。
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