采用地聚合物对黄土进行固化,通过三轴试验研究了硫酸盐侵蚀作用下固化黄土抗剪强度的劣化规律,结合电镜扫描分析了固化土的劣化机理。结果表明:掺入地聚合物可有效提升固化黄土的抗盐蚀性能,掺量越大,抗侵蚀性能提高越显著;随盐蚀时间增加,地聚合物固化黄土抗剪强度呈线性劣化趋势;盐蚀60 d后15%、20%固化土仍具有未扰动试样峰值偏应力的70%、77%,表现出良好的抗盐蚀性,但10%固化土劣化程度较高,其只具有未扰动试样峰值偏应力的45.4%,峰值偏应力下降明显,固化结构已有部分丧失;随盐蚀时间增加,60 d时15%和20%地聚合物固化土黏聚力仍保有初始值的70%以上,但10%地聚合物固化土劣化显著,降幅约为50%;盐蚀作用对内摩擦角的影响相对较小,盐蚀60 d后10%、15%和20%地聚合物固化土内摩擦角分别降低了22.7%、13.3%和8.6%;电镜扫描发现硫酸盐溶液对地聚合物固化黄土的结构劣化表现为:短期内孔隙水侵蚀作用较为显著,长期浸泡过程中硫酸根离子会与地聚合物反应,导致水化产物分解,故宏观强度下降。
Geopolymer was employed to stabilize loess, and the degradation behavior of its shear strength under sulfate erosion was investigated through triaxial tests, and scanning electron microscopy analysis was conducted to further understand the degradation mechanism of the stabilized loess. The results show that: The incorporation of geopolymer can effectively improve the salt erosion resistance of cured loess, and the higher the incorporation rate, the more significant the improvement of erosion resistance. With the increase of salt erosion time, the shear strength of geopolymer-stabilized loess shows a linear deterioration trend. After 60 days of salt corrosion, 15% and 20% stabilized soil still possess 70% and 77% of the peak partial stress of undisturbed specimens, showing good salt corrosion resistance. However, the degradation degree of 10% solidified soil is relatively high, with only 45.4% of the peak deviatoric stress of undisturbed samples. The peak deviatoric stress decreases significantly, and the solidified structure has been partially lost. At 60 days, the cohesion of 15% and 20% solidified soil can still retain more than 70% of their original values, but the 10% geopolymer solidified soil deteriorates significantly, with a decrease of about 50%. The effect of salt erosion on the internal friction angle is relatively small, which decreases by 22.7%, 13.3% and 8.6% respectively for 10%, 15% and 20% geopolymer stabilized loess. The scanning electron microscopy analysis shows that the structural deterioration of geopolymer solidified loess caused by sulfate solution is manifested in two aspects: In the short term, the pore water erosion is more significant;In the long-term immersion process, sulfate ion reacts with GP, resulting in the decomposition of hydration products, therefore the macro strength decreases.
[1] 陈正汉,郭楠.非饱和土与特殊土力学及工程应用研究的新进展[J].岩土力学,2019,40(1):1-54.
[2] 郭连星.碱激发地聚物固化盐渍土冻融干湿循环耐久性研究[D].兰州:兰州大学,2022.
[3] Abbas R,Khereby M A,Ghorab H Y,et al.Preparation of geopolymer concrete using Egyptian kaolin clay and the study of its environmental effects and economic cost[J].Clean Technologies and Environmental Policy,2020,22(3):669-87.
[4] Scrivener K L,Kirkpatrick R J.Innovation in Use and Research on Cementitious Material[J].Cement and Concrete Research,2007,38(2):128-136.
[5] 孙兆云,韦金城,王林,等.烧结法赤泥-沥青粉固化剂稳定粉土的路用性能研究[J].工程科学与技术,2021,53(4):101-109.
[6] 张书政,龚克成.地聚合物[J].材料科学与工程学报,2003,21(3):430-436.
[7] 林天干,何华,许东风,等.地聚合物加固软土力学性能及微观试验研究[J].长江科学院院报,2018,35(10):108-112.
[8] 陈柯宇,吴大志,胡俊涛,等.废弃玻璃替代河砂对地聚合物砂浆性能的影响[J].建筑材料学报,2022,25(6):577-584.
[9] 俞家人,陈永辉,陈庚,等.地聚物固化软黏土的力学特征及机理分析[J].建筑材料学报,2020,23(2):364-371.
[10] 王超杰,李逢源,郭成超,等.高聚物固化粉土的力学特性与固结机理[J].建筑材料学报,2022,25(6):598-606.
[11] 乔子秦.工业废渣复合固化黄土的强度特性及影响因素研究[D].兰州:兰州大学,2018.
[12] 张豫川,乔子秦,高飞,等.工业废渣复合固化黄土强度特性及影响因素研究[J].长江科学院院报,2019,36(3):103-109.
[13] 赵彦旭,向俊燃,吕擎峰,等.碱激发剂对地聚物固化黄土工程特性的影响[J].北京工业大学学报,2021,47(6):636-643.
[14] 向俊燃.水玻璃对碱激发地聚物固化黄土工程特性影响研究[D].兰州:兰州大学,2020.
[15] 杨世玉,赵人达,靳贺松,等.粉煤灰地聚物砂浆早期强度的影响参数研究[J].工程科学与技术,2020,52(6):162-169.
[16] Noushini A,Castel A,Aldred J,et al.Chloride diffusion resistance and chloride binding capacity of fly ash-based geopolymer concrete[J].Cement and Concrete Composites,2020,105:103290.
[17] 吴燕开,史可健,胡晓士,等.海水侵蚀下钢渣粉+水泥固化土强度劣化试验研究[J].岩土工程学报,2019,41(6):1014-1022.
[18] Zheng S N,Qi L,He R,et al.Erosion damage and expansion evolution of interfacial transition zone in concrete under dry-wet cycles and sulfate erosion[J].Construction and Building Materials,2021,307:124954.
[19] Pasupathy K,Singh C D,Sanjayan J.Durability performance of fly ash-based geopolymer concrete buried in saline environment for 10 years[J].Construction and Building Materials,2021,281:122596.
[20] 孙爽.季冻区玄武岩纤维水泥粉砂土力学性能及损伤特征研究[D].长春:吉林大学,2022.
[21] Chen R,Zhu Y,Lai H P,et al.Stabilization of soft soil using low-carbon alkali-activated binder[J].Environmental Earth Sciences,2020,79(22):1-13.
[22] 郑旭.碳化固化土的耐久性能试验研究[D].南京:东南大学,2015.
[23] 吴刚.工程材料的扰动状态本构模型(Ⅰ)——扰动状态概念及其理论基础[J].岩石力学与工程学报2002(6):759-765.
[24] 宁宝宽,陈四利,郑楠.硫酸盐对水泥土的侵蚀作用研究[A]//第九届全国岩石力学与工程学术大会论文集[C].沈阳:科学出版社,2006:726-730.
[25] 傅小茜,冯俊德,谢友均.硫酸盐侵蚀环境下水泥土的力学行为研究[J].岩土力学,2008,29(增1):659-662.
[26] Bortnovsky O,Sobalik Z,Tvaruzkova Z,et al.Structure and stability of geopolymers synthesized from kaolinitic and shale clay residues[A]//Geopolymer Institute.Proceedings of the Geopolymer 2005 World Congress[C].Melbourne:Geopolymer Institute,2005:81-84.
[27] 黄伟,汪时机,程明书,等.水泥改性膨胀土在侵蚀环境下的干湿循环效应研究[J].硅酸盐通报,2018,37(2):649-659.
[28] 孔希红.玻璃纤维水泥土强度及抗硫酸盐侵蚀性能试验研究[J].新型建筑材料,2020,47(4):57-59,64.