Experimental Investigation of MgAl-NO2 andMgAl-CO3 LDHs on Durability of Mortar and Concrete

Two kinds of layered double hydroxides (LDHs), MgAl-NO2 (N-LDH) and MgAl-CO3 (C-LDH), were incorporated to study the durability of mortar and concrete. *e LDH contents of mortar were 1%, 2%, and 4% by mass and the LDH contents of concrete were 0.5%, 1%, 2%, 4%, respectively.*e effect of LDHs on sulfate resistance of mortar was studied through dry-wetting cycle test, compressive strength test, and flexural strength test. In addition, the effects of LDHs on pore structure, chloride resistance, carbonation resistance, shrinkage, and creep of concrete were investigated by SEM, mercury injection test, XRD, chloride ion diffusion coefficient test, chloride salt corrosion depth test, carbonation depth test, shrinkage test, and creep test. *e results showed that LDHs can improve the ability of resisting ion corrosion, carbonization, shrinkage, and creep, reduce the pore content, and optimize the pore structure of mortar and concrete to some extent. Moreover, 4% LDHs had a better effect on improving the durability of mortar and concrete compared to 0.5%, 1%, and 2% LDHs, and the effect of C-LDH was better than N-LDH.


Introduction
Due to the long-term penetration and corrosion, cement in concrete in marine environment and saline soil area reacted with aluminum, sulfate, and calcium to form expansion stress, which caused volume expansion and reduced the mechanical properties and durability of the concrete [1][2][3][4][5][6][7]. erefore, reducing the penetration rate and concentration of corrosive salts in the concrete is conducive to improve the performance of concrete.
Hydrotalcite compounds are a kind of typical anion intercalation materials, also known as layered double hydroxides (LDHs), which have the characteristics of interlayer anion exchange, thermal stability, memory effect, acidity, and basicity [8,9] and have been widely applied in many fields, such as catalyst [10], adsorbent [11,12], drug storage and sustained-release agents [13][14][15], intercalated optical materials [16], and pollution treatment [17,18]. For example, in the aspect of concrete admixtures, the polycarboxylate group was inserted into the interlayer of LDHs to slowly release the effect of water reducing agent, which can extend the water reducing effect time and improve the slump operation time of concrete [19,20]. e interlayer anion exchange property of LDHs was the most important practical property, namely, different anions can enter the interlayer structure of LDHs through exchange behavior, causing the change of the charge density of the laminate and the electrostatic interaction between the laminate and the interlayer anions, and finally changing the interlayer spacing, resulting in a new intercalation structure of LDHs [8]. When the charge density and the diameter of the anion were higher and smaller, the anions were more likely to enter the interlayer. On the contrary, the anions were easier to be replaced. e exchange capacity of common anions in LDHs (equal to the stability of the new structure) was in the order of CO 3 2− > SO 4 2− > OH − > F − > Cl − > NO 3 − , that is, the former anions can be substituted with the latter anions [21]. Based on the principle that the stability of nitro LDHs was better than chlorine LDHs, a small amount of nitro LDHs (usually 1-5% of the mass of cementitious materials) was added into concrete to solidify chloride ions in concrete through ion exchange, the transmission rate of chloride ions in concrete was delayed, and the durability of concrete was improved [22][23][24][25][26][27]. e research by Qu et al. [28] showed that adding 1% Ca-Al-NO 3 LDHs into concrete can reduce the chloride ion content by 17%-53%. Chen [29] studied the removal mechanism of Ca-Al-NO 3 LDHs on chloride ion in hardened cement paste and found that LDHs can adsorb Cl − in cement through ion exchange, so as to reduce the concentration of Cl − in the paste, and the maximum binding amount of the chloride ion can reach 3.38 mg/g. In addition, the types of interlayer anions of LDHs had different inhibitory effects on chloride ion with the order from strong to weak being NO 2 -LDH >NO 3 -LDH >C 6 H 5 COO-LDH >CrO 4 -LDH [30]. Yang et al. [22,31,32] studied the corrosion resistance of p-aminobenzoate LDHs and nitro LDHs on steel bars, and the results showed that the former had higher binding capacity to chloride ions. e crystallinity of LDHs had a great influence on the early strength of cement slurry. When the crystallinity of LDHs was high, it promoted the hydration reaction of C 3 A in cement and inhibited the hydration reaction of C 3 S, resulting in relatively low early strength [33]. Guan and Zou [34,35] evaluated the influence of Li-Al LDHs on the early performance of sulphoaluminate cement clinker. e research results explained that LDHs can increase the early hydration rate of sulphoaluminate cement, increase the contents of early hydration products, and improve the compressive strength.
Compared with noncalcined LDHs, the adsorption of anions on calcined LDHs was significantly improved [36][37][38] because the layered structure of LDHs was destroyed. However, due to the structure memory effect of LDHs, the layered structure of LDHs was restored after encountering CO 3 2− , SO 4 2− , and Cl − . In this process, these ions can be adsorbed in the middle of the layered structure and then playing the role of solidifying the harmful ions [39,40]. When the calcination temperature of LDHs was higher than 252.8°C, then the structural changes occurred [38]. At present, the common calcination temperature is between 450°C and 650°C [38,41]. Yoon [42] researched the adsorption of chloride in concrete by Mg-Al LDHs (CLDH) calcined at 450°C. e results showed that the chloride ions were adsorbed in the process of structural reconstruction. e measured ion binding capacities of CLDH were 153 mg/ g, which were highly equivalent to the theoretical ion binding capacity of Friedel's salt (121 mg/g). Chen [43] investigated the feasibility of the application of CLDH in UHPC. e research results exhibited that the best dosage of CLDH in UHPC was 1%, and the porosity of concrete decreased and the strength increased. e removal efficiency of CLDH was better than that of fly ash and silica fume. In ordinary concrete, with the increase of CLDH content to 3%, the porosity of concrete displayed a downward trend, and the hydration of cement was promoted [44]. e research results of Duan [36] and Duan et al. [41] also showed that the calcined CLDH can refine the pore structure of concrete. e research results of Geng [45] revealed that the influence of reaction temperature on the chloride binding capacity of CLDH was 38°C > 50°C ≈ 20°C > 3°C. When the pH value was higher than 12.5, increasing the pH value would reduce the chloride binding capacity of CLDH.
At present, there is a lack of systematic research on the effect and mechanism of LDHs on the durability of mortar and concrete with different strength grades. Magnesium aluminum carbonate hydrotalcite (C-LDH) is the most common and widely used hydrotalcite in the market at present with relatively low price. Magnesium aluminum nitrate hydrotalcite (N-LDH) is not stable, and the interlayer nitrate ions are easily replaced by other ions, which is usually used as the precursor of ion exchange. erefore, this paper used two typical LDHs, N-LDH and C-LDH, to study the influence of sulfate attack resistance of mortar. Additionally, the influence of LDHs and their content on chloride ion permeability, carbonation, shrinkage, and creep on different strength grades of concrete (C30 and C50) were explored.

Raw Materials.
e main chemical components of Ordinary Portland Cement, fly ash, magnesium aluminum nitrate hydrotalcite (N-LDH), and magnesium aluminum carbonate hydrotalcite (C-LDH, without calcination) used in this study are shown in Table 1. e cement was the P.O 42.5 R cement produced by Hebei Yanxin Building Materials Co., Ltd. e physical properties are displayed in Table 2. e fly ash was level I coal ash from Shijingshan. e stones were 5∼25 mm continuous graded gravel with an apparent density of 2650 kg/m 3 , a crushing index of 12%, and a mud content of less than 0.3%. e sand was 0.5∼2.0 mm ISO standard sand with an apparent density of 2500 kg/m 3 , a fineness modulus of 2.3, SiO 2 content of greater than 96%, and a mud content of no more than 0.2%. e superplasticizer was naphthalene series superplasticizer (solid) with water reduction rate of 20%. e mixing water was tap water. e main technical indicators of LDHs are listed in Table 3.

Sample Preparation.
e sample of cement mortar test was prepared as follows. e mix ratio of mortar is shown in Table 4. e cement, standard sand, water, and LDHs were mixed evenly to make mortar by a mixer, then poured into a 40 mm × 40 mm × 160 mm rubber sand mold, and demolded after standing for 24 h. e samples were cured for 28 d under standard conditions (temperature 20 ± 2°C, relative humidity ≥ 95%) and then placed in an oven at 80°C for drying 48 h. Finally, the samples were located in a dry-wet circulation machine for the dry-wetting cycle test of sulfate. e samples of concrete test were prepared based upon the mix ratio shown in Table 5. Before the durability study, we studied the influence of N-LDH and C-LDH on the mechanical properties of concrete. e results showed that when the content of N-LDH and C-LDH in concrete was higher than 4%, the mechanical properties of concrete decreased greatly. erefore, the incorporation of both N-LDH and C-LDH adopts the external-adding method with the amount of 0.5%, 1%, 2%, and 4% of the mass of cement. e cementitious materials, sand, stone, water, and LDHs were mixed evenly in proportion and then poured into a 100 mm × 100 mm × 100 mm mold. After 24 h, the samples were demolded and then cured for 28 d in standard conditions (temperature 20 ± 2°C, relative humidity ≥ 95%). e concrete samples were prepared for chloride ion resistance test by selecting one surface of the cured concrete samples as the exposed surface with the other five surfaces sealed with epoxy resin. e sealed samples were immersed in a water tank containing 3.5% NaCl solution. e exposed surfaces were faced up and the distance to the liquid surface was 5 cm. To prevent water evaporation, the tank was sealed with a plastic sheet. e concrete samples were prepared for carbonization resistance test as follows. e cured samples were placed in a drying oven at 60°C for 48 h. One surface of the sample was used as the exposed surface, and the other surfaces were sealed with epoxy resin. e concrete samples were prepared for shrinkage test and creep test as follows. e cementitious materials, sand, stone, water, and LDHs were mixed based upon Table 5  e total chloride ion content of the samples was determined by CLU-V rapid chloride ion content tester. e instrument electrode was calibrated before the test, and then the chloride ion selective electrode and the saturated calomel electrode were inserted vertically into the solution for 2 min. e data were recorded after the equipment stabilized. e determination result was expressed as the percentage of chloride ion by the mass of the powder sample.   Advances in Materials Science and Engineering

Microscopic Morphology Analysis (SEM) of Concrete.
After the concrete samples were dried, the FEI Quanta200 scanning electron microscope (SEM) produced by FEI Company in the Netherlands was used to observe the microscopic morphology of the samples. e technical parameters of SEM were as follows: acceleration voltage, 200V∼30 kV; magnification, 25∼200000; resolution, 3.5 nm.

Chloride Corrosion Depth Test of Concrete.
Chlorine salt long-term immersion method was adopted to study the effect of LDHs on chloride ion penetration resistance of concrete. Four groups of concrete samples were utilized, five in each group. e sealed samples with the exposed surface facing up were immersed in a water tank containing 3.5% NaCl solution for 180 d. e test solution was changed every 15 d to remain the concentration. e test blocks soaked to the standard age were taken out and cleaned with deionized water and placed in a drying oven at 60°C for 48 h. e concrete powder was taken by layers, and the concrete powder sample was screened through a square hole of 0.08 mm and placed in a drying oven at 105°C for 24 h and then sealed for preservation. 2 g powder was placed in 150 mL deionized water and stirred with a glass rod. After the powder precipitated, the upper liquid was tested by the chloride ion content measuring instrument.

Chloride Ion Diffusion Coefficient of Concrete.
e rapid chloride ion diffusion coefficient method (RCM method) was used to study the chloride ion permeability resistance of concrete affected by LDHs, carried out in accordance with GB/T 50082-2009 (standard for test methods of long-term performance and durability of ordinary concrete). Four groups of the concrete, five samples in each group, were investigated. After the test was completed, the samples were cleaned and broken, and 0.1 mol/L AgNO 3 solution was sprayed on the broken surface. e depth of chloride ion corrosion was measured after 15 min.

Sulfate Dry-Wetting Cycle Test of Mortar.
e sulfate dry-wetting cycle test was used to evaluate the sulfate corrosion resistance of mortar within LDHs. Four groups of mortar samples were tested, four samples in each group. All the mortar samples were immersed in 5% Na 2 SO 4 solution for 15 h, air-dried for 1 h, temperature-dried for 6 h with 60°C, and cooled down for 2 h. Each dry-wetting cycle was lasting for 24 h. e test solution was changed every 15 d. e number of dry-wet cycles was set to 0, 20, 40, 60, 80, 100, and 120. e appearance change, mass change rate, compressive strength, and flexural strength were used as evaluation indexes of cement mortar sample under set cycle times.

Carbonation Resistance Test of Concrete.
According to the carbonation test in GB/T 50082-2009 (standard for test methods of long-term performance and durability of ordinary concrete), four groups of concrete samples, four samples in each group, were evaluated. e sealed test blocks Note. L-0 and H-0 are C30 and C50 concrete without LDHs, respectively. CL and NL are C30 concrete with C-LDH and N-LDH, respectively. CH and NH are C50 concrete with C-LDH and N-LDH, respectively. Note. MN and MC represent cement mortar mixed with N-LDH and C-LDH, respectively. e incorporation of both N-LDH and C-LDH adopts the external-adding method with the amount of 1%, 2%, and 4% of the mass of cement.
were placed in the carbonization box for 3 d, 7 d, 14 d, and 28 d. After taken out, the exposed surface of the test block was broken in the pressure testing machine and sprayed on with 1% phenolphthalein alcohol solution. en, the carbonization depth of concrete was measured after 30 s.
where ϕ t is the creep coefficient with loading time of t (d), ε t is the creep strain value with loading time of t (d), and ε 0 is the initial strain value with loading time of 0.

Chloride Ion Corrosion Resistance of Concrete
e chloride ion diffusion coefficient of concrete indicates the ability to resist the chloride ion permeability. When the chloride ion diffusion coefficient increased, the chloride ion diffused in concrete more easily, meaning the chloride ion permeability resistance of concrete decreased [46]. It can be seen from Figure 1 that for both C30 and C50 concrete, the chloride ion diffusion coefficient of concrete decreased gradually with the increase of LDH content, indicating that the chloride ion permeability resistance of concrete increased. As can be seen from Figure 1(a), for C30 concrete, when the dosages of the two LDHs were the same, the chloride ion diffusion coefficient of concrete mixed with C-LDH was slightly lower than that of concrete mixed with N-LDH, and the chloride ion diffusion coefficient of NL-4 and CL-4 decreased by 26.3% and 30.3%, respectively, compared with L-0, indicating that C-LDH was more effective in resisting the diffusion of chloride ions in concrete. Because the specific surface area of N-LDH was relatively small (<9 m 2 /g) [47] and the anion exchange capacity between layers was limited, the NO 3 − between layers was difficult to be completely replaced by Cl − . As a result, the resistance to chloride ion permeability of N-LDH was relatively weaker. As can be seen from Figure 1(b), the variation trend of C50 concrete with LDHs was basically the same as C30 concrete, and the chloride ion diffusion coefficient decreased with the increase of LDHs. When the content of LDHs was 4%, the chloride ion diffusion coefficient of C50 concrete decreased the most, and the chloride ion diffusion coefficient of NH-4 and CH-4 decreased by 30.2% and 31.5%, respectively, compared with H-0. e test results showed that the incorporation of LDHs can improve the chloride ion permeability resistance of concrete.

Long-Term Immersion
Method. RCM method cannot fully reflect the real diffusion process of chloride ions in concrete [48,49], and it was difficult to describe the solidification behavior of chloride ions in concrete with LDHs. In order to more truly reveal the influence of LDHs on the chloride ion permeability resistance of concrete, this paper used the chloride salt long-term immersion method to achieve this goal. Figure 2 shows the curves of chloride ion content variation (mass percentage of the powder) of all samples tested by chlorine salt long-term immersion method with corrosion depth. As can be seen from the figure, with the increase of chloride salt corrosion depth, the chloride ion content of all samples exhibited a trend of decline. Compared with the control group, the chloride ion concentration in the concrete samples with LDHs was smaller. For C30 concrete, when the dosages of LDHs were 4%, compared with L-0, the chloride ion concentration of NL-4 and CL-4 at 25 mm decreased by 20.6% and 39.1%, respectively. e variation trend of C50 concrete was basically the same as C30 concrete. Compared with H-0, the chloride ion concentration of NH-4 and CH-4 at 25 mm decreased by 36.8% and 55.4%, respectively. e experimental results displayed that the incorporation of LDHs can improve the resistance to chloride ion permeability of concrete and the degree of ion concentration reduction was higher in C50 concrete. Besides, the effect of C-LDH was better than N-LDH.
In order to display the chloride ion permeability depth of different samples more visually, the chloride ion content test results of each powder sample at a distance of 9∼11 mm from the exposed surface are depicted in Figure 3. For C30 concrete, with the increase of the content of LDHs, the content of chloride ion at 9∼11 mm of each sample generally showed a downward trend. Compared with L-0, the chloride ion concentration of NL-4 and CL-4 decreased the most, reaching up to 50.7% and 57.7%, respectively. For C50 concrete, the chloride ion concentration of NH-4 and CH-4 decreased by 53% and 58.7%, respectively. erefore, the incorporation of N-LDH and C-LDH reduced the chloride ion concentration in concrete and improved the chloride ion permeability resistance of concrete to a certain extent. Additionally, the chloride ion permeability resistance effect of C-LDH was better than that of N-LDH.

Hydration Products.
In order to explore whether the addition of LDHs reacted with chloride ions in concrete, the powders of L-0, NL-2, NL-4, CL-2, and CL-4 samples, which were 9∼11 mm away from the exposed surface, were Advances in Materials Science and Engineering analyzed by XRD, as shown in Figure 4. It was found that the main hydration products of each sample after being immersed in chloride solution for 180 d included calcium hydroxide, ettringite, Friedel's salt (Ca 4 Al 2 O6·10H 2 O), and LDHs. Hence, it was concluded that after intruding into concrete, the chloride ions reacted with cement clinker mineral tricalcium aluminate (C 3 A) to form Friedel's salt. Because the structure of Friedel's salt was also a lamellar, the main laminate was composed of calcium aluminum cationic hydroxide (Ca 2 Al(OH) 6 + ) and the interlayer anion was chloride ion. It was difficult to distinguish because the diffraction peak of Friedel's salt overlapped with the peak of LDHs [50,51]. In order to identify the diffraction peaks of Friedel's salt and LDHs, the XRD patterns of each sample were amplified near 2θ � 11.24°, 22.9°, and 60.5°, as shown in Figure 5.
It can be seen from Figure 5 that diffraction peaks of LDHs intercalated with chloride ion appeared in the vicinity of 2θ � 11.3°, 22.9°, and 60.5°, respectively, corresponding to e crystal plane diffraction peaks are clear and have no impurity peak, indicating that the material has a high crystallinity and a good layered structure. e Friedel's salt diffraction peaks of L-0 only appeared near 2θ � 11.3°and 22.75°. Figure 6 shows the XRD comparison of N-LDH and C-LDH before and after chloride ion adsorption. Table 6 shows the layer spacing of each LDH. As can be seen from Figure 6(a), layer spacing did not change much after C-LDH reaction, that is, the structure did not change much. In addition, due to the large specific surface area and strong adsorption of C-LDH, it can be concluded that chloride ions entered the structural layers through the adsorption of C-LDH. Compared with N-LDH, it can be seen from Figure 6(b) that the diffraction peaks corresponding to the (003) and (006) crystal faces of N-LDH after the reaction shifted to a large angle direction, and the lamellar spacing changed from 0.8848 nm before the reaction to 0.7791 nm after the reaction, and the lamellar spacing decreased somewhat. is is because the replacement ability of Cl − is better than that of NO 3− , and the effective radius of Cl − is smaller than that of NO 3− , so the lamellar spacing of N-LDH after the reaction was reduced, which indicated that Cl − entered the structural layers through the ion exchange of N-LDH. erefore, it was believed that N-LDH and C-LDH can absorb chloride ions in concrete environment through interlayer anion exchange and adsorption, respectively, generating magnesium aluminum hydrotalcite intercalated with chloride ion, thus reducing chloride ion concentration in the concrete.

Pore Structure of Concrete.
According to the pore size, the pore structure of concrete can be divided into the following categories: harmless pores (less than 20 nm), less harmful pores (20∼100 nm), harmful pores (100∼200 nm), and much harmful pores (more than 200 nm). e mercury injection test results of each sample are shown in Figure 7. After processing the data in the figure, the pore contents of different categories and the most available pore sizes distribution of each sample were obtained, as shown in Figure 8. Table 7 shows the values of pore content of each sample.
From Figures 7 and 8 and Table 7, it can be concluded that the total pore volume of L-0 and H-0 was 0.1162 mg/L and 0.0693 mg/L. Compared with L-0, the pore volume of H-0 reduced by 40.4%, indicating that reducing the watercement ratio can reduce the porosity of concrete. Compared with L-0, the total pore volume of NL-2, CL-2, NL-4, and CL-4 decreased by 3.9%, 8.4%, 10.9%, and 12.7%, respectively. Compared with H-0, the total pore volume of NH-2, CH-2, NH-4, and CH-4 decreased by 9.1%, 18.3%, 23.7%, and 28.4%, respectively. erefore, it was illustrated that the porosity of concrete decreased with the increase of LDH content in a certain range, and the effect of C-LDH was obviously better than N-LDH.

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Compared with L-0, the harmless pore content of NL-2, CL-2, NL-4, and CL-4 decreased by 1.2%, 2.0%, 5.6%, and 7.5%, respectively. e less harmful pore content decreased by 0.4%, 0.5%, 1.3%, and 1.4%, respectively. e harmful pore content decreased by 14.4%, 33.6%, 43.0%, and 47.9%, respectively, and the much harmful pore content decreased by 24%, 24.2%, 24.7%, and 28.7%, respectively. Compared with H-0, the harmless pore content of NH-2, CH-2, NH-4, and CH-4 decreased by 14.6%, 15.7%, 20.2%, and 22.5%, respectively. e less harmful pore content decreased by 1.1%, 1.8%, 2.6%, and 4.1%, respectively. e harmful pore content decreased by 21.6%, 36.3%, 62.7%, and 76.6%, respectively, and the much harmful pore content decreased by 25.7%, 32.5%, 36.5%, and 42.6%, respectively. e reason was the porosities of L-0 and H-0 which were relatively larger, so LDHs can fill the pores in the concrete to a certain extent and absorb a part of the water in the environment through the interlayer water storage and physical adsorption function. us, the water-cement ratio of concrete was reduced and the compactness of concrete increased so that the contents of harmless pore, less harmful pore, harmful pore, and much harmful pore reduced. For C30 concrete, the addition of LDHs made the most probable pore size of concrete shift to the direction of smaller pore size, which indicated that LDHs can optimize the pore structure of C30 concrete and increase the compactness of concrete. For C50 concrete, the effect of LDHs on the most available pore size was relatively small due to its high density.  Advances in Materials Science and Engineering rough the above experimental analysis, it can be revealed that the incorporation of LDHs in a certain range can reduce the content of harmless pores, less harmful pores, harmful pores, and much harmful pores of concrete and improve the pore structure of concrete, and the effect of C-LDH was better than that of N-LDH. erefore, it was deduced that LDHs can improve the compressive strength and flexural strength of concrete. It should be noted that the C-LDH used in this paper has not been calcined. Figure 9 describes the appearance changes of blank sample, MN-2, MN-4, MC-2, and MC-4 after 0, 40, 80, and 120 cycles of dry-wetting process. As can be seen from the figure, with the increase of the number of cycles, all the samples began to suffer from different degrees of damage. When the dry-wetting cycles were 40 times, the surface of the sample began to become rough and the bare aggregate appeared. When the number of cycles were 80, the surface of each sample began to crack and slightly expand. e edges and corners of the blank sample began to crack and peel off. When the number of cycles reached 120, the blank sample had been corroded very seriously. e surface was loose and some parts fell off. Besides, some white crystals appeared on the surface of the exposed material. For the samples mixed with LDHs, the corrosion phenomenon of MN-4 and MC-4 was relatively lighter, and the surface cracks were few. However, the surface cracks of MN-2 and MC-2 were wide, and the surface and edges of MN-2 peeled off. erefore, the corrosion of MN-2 and MC-  Figure 4: XRD pattern of concrete powder with LDHs at a distance of 9∼11 mm from the exposed surface of concrete. 8 Advances in Materials Science and Engineering 2 was more serious than that of MN-4 and MC-4. According to the change of appearance phenomenon, the sulfate corrosion resistance of the five types of the samples was in the order: MC-4 > MN-4 > MC-2 > MN-2 > blank sample. e mass changes rate of each sample is shown in Figure 10. Some findings were listed. First of all, with the increase of the number of dry-wet cycles, the mass of all samples showed a trend of first increase and then decrease.

Resistance to Sulfate Attack of Mortar.
e mass of blank sample reached the maximum value with the number of cycles of 80, and the mass of blank sample increased by 6.42%. At the 60 th , 80 th , and 100 th cycles, the masses of MN-1, MN-2, and MN-4 increased by 4.87%, 4.95%, and 3.8%; 5.4%, 5.47%, and 4.05%; and 7.11%, 7.15%, and 5.92%, respectively. At the 60 th , 80 th , and 100 th cycles, the masses of MC-1, MC-2, and MC-4 increased by 6.01%, 6.09%, and 4.24%; 6.61%, 6.64%, and 4.89%; and 6.88%, 7.04%, and 5.71%, respectively. It can be seen that the mass of each sample was relatively large when the number of cycles was 80. Secondly, after 120 cycles, the mass of blank sample decreased by 2.54% while the mass of MN-1, MN-2, and MN-4 increased by 0.5%, 1.37%, and 2.71%. In Figure 10(b), the variation pattern of sample mass was   , it reacted with hydration products to produce ettringite and gypsum in large quantities. As the volume of these products was about 2.5 times than that of the original hydration products, great internal expansion stress was generated in the material [52]. When the expansion stress exceeded the tensile and shear ultimate strengths of the material, the new cracks were produced, eventually resulting in the sample cracked and the quality declined. In the early stage of the test, N-LDH and C-LDH can prevent SO 4 2− intruding into the mortar through interlayer anion exchange and adsorption so that the mass change rate of the sample within LDHs in-  According to the strength test results, the compressive strength and flexural strength of mortar samples with the 1% and 2% contents of LDHs were lower than those with 4% content of LDHs after 120 dry-wetting cycles. With the increase of the dosage of LDHs, the porosity of the sample decreased and the pore structure was optimized. us, the Advances in Materials Science and Engineering strength increased to a certain extent, and the effect of C-LDH was better than that of N-LDH.

Carbonation Resistance of Concrete.
e relationship between concrete carbonation depth and age is shown in Figure 13. Firstly, for each sample, the carbonation depth of concrete increased with the increase of carbonation time. Secondly, at the early stage of carbonation, the carbonation depth of all samples decreased with the increase of the content of LDHs, indicating that the incorporation of LDHs can improve the carbonation resistance of concrete at the early stage. irdly, after 28 d of carbonation, the carbonation depth of concrete decreased with the increase of the content of LDHs. For C30 concrete, the carbonation depths of NL-4 and CL-4 were 10.33 mm and 9.62 mm after 28 d, which decreased by 20.1% and 25.6% compared with the blank sample, respectively. For C50 concrete, the carbonation depths of NH-4 and CH-4 were 5.08 mm and 4.73 mm after 28 d, which were 19.1% and 24.7% lower than the blank sample, respectively. erefore, the incorporation of LDHs reduced the carbonation depth of concrete, and the carbonation resistance of C-LDH was better than that of N-LDH. Figure 14 shows the carbonation depth values of L-0, CL-2, NL-2, H-0, CH-2, and NH-2 at the carbonation age of 28 d. It can be seen that the carbonation depths of NL-2 and CL-2 at 28 d decreased by 14.8% and 24.3%, respectively, compared with L-0. e carbonation depths of NH-2 and CH-2 at 28 d decreased by 16.1% and 21.7%, respectively, compared with H-0. erefore, the carbonization resistance of C-LDH was better than that of N-LDH. e reason was  that the specific surface area of C-LDH was larger than N-LDH [53] with a stronger interlayer water storage capacity. us, the water-cement ratio of concrete was reduced more obviously so that the pore structure was more compacted and the density was smaller. e carbonization regions of L-0, CL-2, and NL-2 and H-0, CH-2, and NH-2 were sampled for XRD analysis, as shown in Figure 15, after carbonization for 28 d, and Table 8 exhibits the mass fraction of each substance. It can be seen that the main products of each sample after carbonization were calcium carbonate, silica, and dolomite, and Ca(OH) 2 had almost been consumed. After adding LDHs into the concrete, the amount of CaCO 3 in the carbonization zone was reduced. For example, compared with L-0, the amount of CaCO 3 in carbonization zones of NL-2 and CL-2 was reduced by 31.3% and 50.4%, respectively. Compared with H-0, the amount of NH-2 and CH-2 was decreased by 9.9% and 15.3%, respectively.
In order to verify the test results of XRD, the carbonization region of NL-2 and CL-2 was sampled. e micromorphology of the samples was analyzed after drying, as shown in Figure 16. Under SEM, the LDHs were lamellar and attached to the surface of C-S-H gel. erefore, we can conclude that the concrete mixed with N-LDH and C-LDH absorbed CO 3 2− in the concrete environment and generated magnesium aluminum hydrotalcite structure with carbonate intercalation.
According to the conclusion of chloride ion absorption in Section 3.1.3, it can be seen that C-LDH has a strong adsorption effect and N-LDH has a strong ion exchange effect. Since both of them have a certain resistance to CO 2 , it can be concluded that N-LDH adsorbs CO 3 2through ion exchange, while C-LDH adsorbs CO 3 2− through adsorption.

Shrinkage Performance of Concrete.
e experimental results of the influence of the LDHs on the shrinkage performance of concrete are shown in Figure 17. It can be seen that the shrinkage of C30 and C50 concrete with N-LDH and C-LDH at different ages showed a downward trend. With the increase of the amount of LDHs, the shrinkage values of the concrete decreased. When the contents of N-LDH and C-LDH in the concrete were the same, the shrinkage of C50 concrete was lower than that of C30 concrete. In addition, the shrinkage of concrete with C-LDH decreased more, compared with the concrete with N-LDH.
In order to assess the variation of concrete shrinkage after adding N-LDH and C-LDH, the shrinkage test results of C30 and C50 concrete at the age of 28 d were studied, as shown in Figure 18. It was calculated that the shrinkage of NL-2, Cl-2, NL-4, and CL-4 decreased by 5.3%, 8.4%, 15.4%, and 16.3%, respectively, compared with L0. Compared with H0, the shrinkage of NH-2, CH-2, NH-4, and CH-4 decreased by 18.3%, 21.1%, 30.1%, and 33.3%, respectively. By analyzing the above results together with the experimental results in Section 3.2, it can be found that the decreasing trend of shrinkage was consistent with the decreasing trend of total porosity of concrete. erefore, we believed that the main reason for the decrease of shrinkage rate of concrete after adding N-LDH or C-LDH was that N-LDH or C-LDH absorbed part of the water in the environment through interlayer water storage and physical adsorption function, thus reducing the water-cement ratio of the concrete, increasing the compactness and improving the pore structure of concrete.

Creep Performance of Concrete.
e experimental results of the influence of LDHs on the creep performance of concrete are depicted in Figure 19. It can be seen that when N-LDH and C-LDH were added into C30 or C50, the creep coefficient of concrete displayed a downward trend. e creep coefficient decreased with the contents of N-LDH and C-LDH increased. Compared with N-LDH, the creep coefficient of the concrete with the same content of C-LDH decreased more. Hence, it was concluded that N-LDH and C-LDH both can reduce the creep coefficient of the concrete, and the effect of C-LDH was better than N-LDH. e creep coefficient test results of C30 and C50 concrete at the age of 28 days are marked in Figure 20. It can be seen that the creep coefficients of NL-2, CL-2, NL-4, and CL-4 decreased by 2.0%, 4.5%, 5.2%, and 7.1%, respectively, compared with L0. Compared with H0, the creep coefficients of NH-2, CH-2, NH-4, and CH-4 decreased by 9.8%, 11.1%, 12.4%, and 18.5%, respectively.

Conclusions
In this paper, two typical LDH materials, magnesium aluminum nitrate hydrotalcite (N-LDH) and magnesium aluminum carbonate hydrotalcite (C-LDH), were introduced into mortar and concrete to explore the influence on durability. e maximum content of N-LDH and C-LDH is 4%. It can be seen from this paper that with the gradual increase of N-LDH and C-LDH content, the durability indexes of the studied concrete are improved. erefore, we speculate that when the content of N-LDH and C-LDH is higher than 4%, the durability index will continue to improve. When the content of N-LDH and C-LDH is less than 4%, the following conclusions are drawn: (1) N-LDH and C-LDH can remove chloride ions in solution by anion exchange and adsorption, respectively. e diffusion coefficient of chloride ions in concrete decreased with the increase of the content of LDHs. Both N-LDH and C-LDH can react with chloride ions intruding into concrete and generate magnesium aluminum hydrotalcite intercalated with chloride ions, thus reducing the concentration of chloride ions inside the concrete. C-LDH was better than N-LDH in improving chloride ion permeability resistance of concrete. (2) e proper amount of LDHs can optimize the pore structure of concrete to a certain extent, and the addition of LDHs can reduce the content of harmless pores, less harmful pores, harmful pores, and much harmful pores of concrete. C-LDH was better than N-LDH in improving concrete pore structure. (3) e mass change rate, compressive strength, and flexural strength of mortar increased firstly and then decreased with the increase of dry-wetting cycles. N-LDH and C-LDH can adsorb SO 4 2− in the environment. With the increase of LDHs, the sulfate corrosion resistance of mortar was improved, and the sulfate corrosion resistance of C-LDH was better than that of N-LDH.
(4) N-LDH and C-LDH can remove CO 3 2− in the environment through the interlayer anion exchange and adsorption, respectively, and the adsorption capacity of C-LDH was better than that of N-LDH. At the early stage of carbonization, the carbonation resistance of concrete increased with the increase of LDHs. When the age was 28 d, the carbonation depth of concrete decreased with the increase of LDHs. Both N-LDH and C-LDH can adsorb CO 3 2− in concrete environment and produce lamellar magnesium aluminum carbonate hydrotalcite. C-LDH was better than N-LDH in improving the carbonization resistance of concrete. (5) e shrinkage and creep of concrete can be reduced by adding LDHs into concrete because of the optimization of pore structure, and the effect of C-LDH was better than that of N-LDH.

Data Availability
All the research data have been included in the manuscript and the figures.

Conflicts of Interest
e authors declare that the research was conducted in the absence of any commercial or financial relationships that could be construed as potential conflicts of interest.