• 文献检索
  • 文档翻译
  • 深度研究
  • 学术资讯
  • Suppr Zotero 插件Zotero 插件
  • 邀请有礼
  • 套餐&价格
  • 历史记录
应用&插件
Suppr Zotero 插件Zotero 插件浏览器插件Mac 客户端Windows 客户端微信小程序
定价
高级版会员购买积分包购买API积分包
服务
文献检索文档翻译深度研究API 文档MCP 服务
关于我们
关于 Suppr公司介绍联系我们用户协议隐私条款
关注我们

Suppr 超能文献

核心技术专利:CN118964589B侵权必究
粤ICP备2023148730 号-1Suppr @ 2026

文献检索

告别复杂PubMed语法,用中文像聊天一样搜索,搜遍4000万医学文献。AI智能推荐,让科研检索更轻松。

立即免费搜索

文件翻译

保留排版,准确专业,支持PDF/Word/PPT等文件格式,支持 12+语言互译。

免费翻译文档

深度研究

AI帮你快速写综述,25分钟生成高质量综述,智能提取关键信息,辅助科研写作。

立即免费体验

地下工程中水泥基材料碳化的试验研究

Experimental Study on Carbonation of Cement-Based Materials in Underground Engineering.

作者信息

Zheng Jun, Zeng Gang, Zhou Hui, Cai Guanghua

机构信息

China Railway 11th Bureau Group Co., Ltd., Wuhan 430061, China.

State Key Laboratory of Geomechanics and Geotechnical Engineering, Institute of Rock and Soil Mechanics, Chinese Academy of Sciences, Wuhan 430071, China.

出版信息

Materials (Basel). 2022 Jul 29;15(15):5238. doi: 10.3390/ma15155238.

DOI:10.3390/ma15155238
PMID:35955173
原文链接:https://pmc.ncbi.nlm.nih.gov/articles/PMC9369855/
Abstract

The corrosive water environment has a decisive influence on the durability of a diversion tunnel lining. In this paper, the effects of carbonation on cement-based materials in water-immersion and saturated-humidity environments were studied by increasing the CO concentration. The results show that under conditions of water-immersion and saturated humidity, the color of the non-carbonation region is dark, while the carbonation region is gray, and the color boundary is obvious. However, in an atmospheric environment, there is no zone with a dark color and the color boundary is not obvious. In a saturated-humidity environment, the carbonation depth increases over time and changes greatly, and its value is about 16.71 mm at 200 days. While in a water-immersion environment, the carbonation depth varies little with time and the value is only 2.31 mm. The carbonation depths of cement mortar samples in different environments generally follow a linear relationship with the square root of time. The carbonation coefficient in a saturated-humidity environment is more than nine times that in the water-immersion environment. In a water-immersion environment, the carbonation causes a large loss of calcium in cement-based materials, and their Ca/Si ratio obviously decreases. The calcium silicon ratio (Ca/Si) of cement-based materials in a water-immersion environment is 0.11, which is much less than 1.51 in a water-saturated environment and 1.49 in an atmospheric environment. In a saturated-humidity environment, the carbonation only reduces the pH of the pore solution in the carbonation region, and the structural stability of cement-based materials is not degraded. The number of pores of all radii after carbonation in a water-immersion environment exceeds that in a saturated-humidity environment, and the total pore volume and average pore radius in a water-immersion environment are also larger than in a saturated-humidity environment, so the water-immersion environment accelerates the development and expansion of pores. The research results can provide some theoretical and technical support for the design, construction, and safe operation of diversion tunnel linings.

摘要

腐蚀性水环境对引水隧洞衬砌的耐久性具有决定性影响。本文通过提高CO浓度,研究了碳化在水浸和饱和湿度环境下对水泥基材料的影响。结果表明,在水浸和饱和湿度条件下,未碳化区域颜色较深,而碳化区域为灰色,颜色边界明显。然而,在大气环境中,不存在深色区域,颜色边界不明显。在饱和湿度环境中,碳化深度随时间增加且变化较大,200天时其值约为16.71mm。而在水浸环境中,碳化深度随时间变化较小,值仅为2.31mm。不同环境下水泥砂浆样品的碳化深度一般与时间的平方根呈线性关系。饱和湿度环境下的碳化系数是水浸环境下的九倍多。在水浸环境中,碳化导致水泥基材料中钙大量流失,其Ca/Si比明显降低。水浸环境中水泥基材料的钙硅比(Ca/Si)为0.11,远低于水饱和环境中的1.51和大气环境中的1.49。在饱和湿度环境中,碳化仅降低了碳化区域孔隙溶液的pH值,水泥基材料的结构稳定性未退化。水浸环境中碳化后所有半径的孔隙数量均超过饱和湿度环境,水浸环境中的总孔隙体积和平均孔隙半径也大于饱和湿度环境,因此水浸环境加速了孔隙的发展和扩张。研究结果可为引水隧洞衬砌的设计、施工及安全运行提供一定的理论和技术支持。

https://cdn.ncbi.nlm.nih.gov/pmc/blobs/0096/9369855/3956f1b77a20/materials-15-05238-g015.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/0096/9369855/c0d7227e5061/materials-15-05238-g001.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/0096/9369855/728cce7da620/materials-15-05238-g002.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/0096/9369855/ebbcbcd55e34/materials-15-05238-g003.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/0096/9369855/08504355e41e/materials-15-05238-g004.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/0096/9369855/e4c655f654f0/materials-15-05238-g005.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/0096/9369855/ffc9f4feb99c/materials-15-05238-g006.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/0096/9369855/fe1aec39ea86/materials-15-05238-g007.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/0096/9369855/4636efcad577/materials-15-05238-g008.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/0096/9369855/645901812166/materials-15-05238-g009.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/0096/9369855/b6af8fa9f45b/materials-15-05238-g010.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/0096/9369855/50a4c341256e/materials-15-05238-g011.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/0096/9369855/c721ea8a5f05/materials-15-05238-g012.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/0096/9369855/c1214035cbfc/materials-15-05238-g013.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/0096/9369855/63d58fbac8b7/materials-15-05238-g014a.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/0096/9369855/3956f1b77a20/materials-15-05238-g015.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/0096/9369855/c0d7227e5061/materials-15-05238-g001.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/0096/9369855/728cce7da620/materials-15-05238-g002.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/0096/9369855/ebbcbcd55e34/materials-15-05238-g003.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/0096/9369855/08504355e41e/materials-15-05238-g004.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/0096/9369855/e4c655f654f0/materials-15-05238-g005.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/0096/9369855/ffc9f4feb99c/materials-15-05238-g006.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/0096/9369855/fe1aec39ea86/materials-15-05238-g007.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/0096/9369855/4636efcad577/materials-15-05238-g008.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/0096/9369855/645901812166/materials-15-05238-g009.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/0096/9369855/b6af8fa9f45b/materials-15-05238-g010.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/0096/9369855/50a4c341256e/materials-15-05238-g011.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/0096/9369855/c721ea8a5f05/materials-15-05238-g012.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/0096/9369855/c1214035cbfc/materials-15-05238-g013.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/0096/9369855/63d58fbac8b7/materials-15-05238-g014a.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/0096/9369855/3956f1b77a20/materials-15-05238-g015.jpg

相似文献

1
Experimental Study on Carbonation of Cement-Based Materials in Underground Engineering.地下工程中水泥基材料碳化的试验研究
Materials (Basel). 2022 Jul 29;15(15):5238. doi: 10.3390/ma15155238.
2
Radon exhalation from cement-based materials under accelerated carbonation.水泥基材料在加速碳化条件下的氡析出。
Environ Sci Pollut Res Int. 2023 Apr;30(17):50610-50619. doi: 10.1007/s11356-023-25831-x. Epub 2023 Feb 17.
3
Effects of CO Concentration and the Uptake on Carbonation of Cement-Based Materials.一氧化碳浓度及吸收对水泥基材料碳化的影响。
Materials (Basel). 2022 Sep 16;15(18):6445. doi: 10.3390/ma15186445.
4
Effect of water-to-cement ratio induced hydration on the accelerated carbonation of cement pastes.水胶比诱导的水化对水泥砂浆加速碳化的影响。
Environ Pollut. 2021 Jul 1;280:116914. doi: 10.1016/j.envpol.2021.116914. Epub 2021 Mar 17.
5
Investigation on the Carbonation Behavior of Alkali-Activated Pastes Served under Windy Environments.有风环境下碱激发浆体碳化行为的研究。
Materials (Basel). 2023 Jan 14;16(2):825. doi: 10.3390/ma16020825.
6
Pore Filling Effect of Forced Carbonation Reactions Using Carbon Dioxide Nanobubbles.使用二氧化碳纳米气泡的强制碳酸化反应的孔隙填充效应
Materials (Basel). 2020 Sep 29;13(19):4343. doi: 10.3390/ma13194343.
7
The effect of storage in an inert atmosphere on the release of inorganic constituents during intermittent wetting of a cement-based material.在惰性气氛中储存对水泥基材料间歇湿润过程中无机成分释放的影响。
J Hazard Mater. 2002 Apr 26;91(1-3):159-85. doi: 10.1016/s0304-3894(01)00383-1.
8
Effects of carbonation and leaching on porosity in cement-bound waste.碳酸化和浸出对水泥固化废弃物孔隙率的影响。
Waste Manag. 2007;27(7):977-85. doi: 10.1016/j.wasman.2006.05.008. Epub 2006 Jul 14.
9
Synergistic Effects of Environmental Relative Humidity and Initial Water Content of Recycled Concrete Aggregate on the Improvement in Properties via Carbonation Reactions.环境相对湿度与再生混凝土骨料初始含水量对碳化反应改善性能的协同效应
Materials (Basel). 2023 Jul 26;16(15):5251. doi: 10.3390/ma16155251.
10
Experimental Study on Carbonation Durability of Kaolin Strengthened with Slag Portland Cement.矿渣硅酸盐水泥增强高岭土碳化耐久性的试验研究
Materials (Basel). 2022 Feb 7;15(3):1240. doi: 10.3390/ma15031240.

引用本文的文献

1
Sustainable Recycling Techniques of Pavement Materials.路面材料的可持续回收技术
Materials (Basel). 2022 Dec 7;15(24):8710. doi: 10.3390/ma15248710.

本文引用的文献

1
Tropical extreme droughts drive long-term increase in atmospheric CO growth rate variability.热带极端干旱导致大气 CO 增长率变异性长期增加。
Nat Commun. 2022 Mar 7;13(1):1193. doi: 10.1038/s41467-022-28824-5.
2
The Performance Evaluation of Asphalt Mortar and Asphalt Mixture Containing Municipal Solid Waste Incineration Fly Ash.含城市固体废弃物焚烧飞灰的沥青胶浆和沥青混合料性能评价
Materials (Basel). 2022 Feb 14;15(4):1387. doi: 10.3390/ma15041387.
3
Effects of Sulfate during CO2 Attack on Portland Cement and Their Impacts on Mechanical Properties under Geologic CO2 Sequestration Conditions.
在地质封存 CO2 条件下 CO2 侵蚀过程中硫酸盐的作用及其对力学性能的影响。
Environ Sci Technol. 2015 Jun 2;49(11):7032-41. doi: 10.1021/es506349u. Epub 2015 May 21.
4
Degradation of well cement by CO2 under geologic sequestration conditions.地质封存条件下二氧化碳对油井水泥的降解作用。
Environ Sci Technol. 2007 Jul 1;41(13):4787-92. doi: 10.1021/es062828c.