Durability Performance of Concrete with Fly Ash as Fine Aggregate Eroded by Chloride Salt

,e aim of this study is to investigate the durability of concrete with fly ash as a fine aggregate (CFA) in chloride salt environments. ,e natural diffusion method is used to analyze the concrete strength, chloride ion concentration, and diffusion coefficient after chloride salt erosion in a laboratory environment. In addition, scanning electron microscopy, X-ray diffraction, and Mercury intrusion porosimetry are performed to clarify the deterioration mechanism of concrete in chloride salt environments.,e results indicate that owing to the chloride ion binding effect, the concrete porosity decreases and the concrete strength increases after chloride salt immersion. ,e decreased porosity caused by delayed hydration is primarily due to Friedel’s salt and CaCO3 produced during chloride ion erosion. CFA has a lower chloride diffusion coefficient and lower chloride concentration compared with ordinary concrete at all depths. In general, CFA exhibits excellent resistance to chloride salt erosion.


Introduction
e significant accumulation of fly ash not only causes environmental issues, but also poses a threat to human health [1]. China is the top producer of fly ash worldwide [2]. e low fly ash use efficiency and significant emissions by China have significantly deteriorated the surrounding water quality and atmosphere. erefore, effective techniques should be developed to utilize fly ash in the construction field. In recent years, the research and application of fly ash in concrete technology have progressed considerably [3].
In chloride salt environments, steel corrosion is the primary factor that affects the durability of concrete structures. Chloride ions diffuse through concrete crack channels deep into the reinforcing steel surface, thereby damaging the passivation films on the surface [4][5][6]. When concrete structures are exposed to marine or deicing salt environments for long periods, chloride ions penetrate into the concrete, causing the reinforcement to corrode. is action decreases the effective bearing area of the reinforcing steel. Furthermore, the volume expansion caused by corrosion facilitates the cracking of the concrete protective layer, thereby ultimately reducing the bearing capacity and shortening the service life of the concrete structure [7].
Improving the pore structure and reducing the chloride penetration rate in concrete are effective measures to prolong the service life of reinforced concrete structures. Scholars have conducted extensive research regarding the application of fly ash concrete in chloride environments. It is concluded that fly ash can improve the internal porosity of concrete and increase its density. e partial replacement of cement with fly ash delays the depassivation of steel reinforcement, decelerates corrosion [8,9], and improves the performance of concrete against chloride salt erosion.
Free chloride ions in the concrete pore solution, which destroy the passive film of the reinforcing steel and result in steel corrosion, are detrimental to concrete, not the total amount of chloride ions [10]. C 3 A and C 4 AF in cement can chemically react with chloride ions to produce Friedel salts and calcium chloride oxide (Ca 3 Cl 2 O 2 ) [11], and the hydration product, calcium silicate hydrate (C-S-H) gel, generates an adsorption effect on chloride ions. is can effectively reduce the harmful chloride ions in concrete via a reaction with Friedel salts and Ca 3 Cl 2 O 2 [10]. e service life of reinforced concrete structures can be increased by 50%-200% owing to the chloride binding effect [12]. Glass et al. [13] discovered that the binding capacity of chloride ions increased with C 3 A content, even when different cement types were used. When the C 3 A content was increased from 2.43% to 14%, the chloride ion concentration threshold required for reinforcing steel corrosion increased by 2.85, which significantly delayed corrosion [14]. However, factors such as mineral admixtures, temperature, and chloride salt solution concentration can affect the chloride binding capacity of concrete [15]. Fly ash and other mineral admixtures are widely used in concrete applications. Studies [16][17][18] have shown that the partial replacement of cement with fly ash improves the chloride binding capacity. Cheewaket et al. [16] investigated the free and total chloride ion contents of concrete produced with fly ash at 0%-50% substitution rates using water-and acid-soluble methods; they discovered that by increasing the fly ash content, the chloride ion binding capacity increased, whereas the free chloride content decreased, thereby retarding the corrosion of reinforcing steel. e concrete mix proportion, material type, and other factors affect the formation of the internal microstructure of concrete during hardening; consequently, resistance to the chloride penetration of concrete is affected [19]. e microstructure of concrete must be examined to reveal the material properties including the permeability [20]. e resistance of concrete to chloride ion attack provides a visual response to changes in its internal microstructure. Changes in the microstructure directly affect the macroscopic mechanical properties and durability of concrete [21]. Fly ash considerably affects the composition and microstructure of concrete hydration products [22]. e volcanic ash reaction densifies the concrete matrix, and the ash reacts with calcium hydroxide during cement hydration to produce additional C-S-H and calcium aluminate hydrate (C-A-H), thereby reducing the concrete porosity and optimizing the internal microinterface. Consequently, a dense matrix is generated, and a high-strength material that resists chloride ion diffusion into the concrete interior is formed [23,24]. e time at which steel bar rusting is initiated and the rusting degree depend on the diffusion coefficient of chloride ions [25]. Researchers have applied Fick's second diffusion law to describe chloride ion diffusion in concrete [26]. e parameters of Fick's second diffusion law model provide a clear physical interpretation and can be used effectively to simulate existing test results [27]. Fly ash slightly affects the diffusion coefficient of chloride ions in early age concrete [28]. However, with extended exposure time, it significantly affects the diffusion coefficient of chloride ions. In later exposure stages, fly ash can significantly decrease the diffusion rate of chloride ions in concrete. Fly ash decreases the diffusion coefficient of chloride ions by 15%-50% [29,30], thereby extending the expected service life of concrete structures. An optimal limit exists when using fly ash as a partial replacement for cement [31,32]. When the replacement rate of fly ash exceeds the optimal value, the diffusion coefficient increases, which adversely affects the diffusion properties of anti-chlorine ions [33]. e relationship between the chloride diffusion coefficient and pore structure characteristics must be clarified to effectively reduce the chloride diffusion coefficient. Studies regarding the microstructure of fly ash concrete indicate that fly ash can refine the internal pore structure. When fly ash was used, the number of large pores decreased [21], the number of fine pores increased, and the total porosity and average pore size decreased significantly, thereby enhancing the resistance of concrete to chloride ion attack [22].
However, the positive effect of fly ash as a cement replacement material is limited. Seo et al. [34] recommend using fly ash as a partial replacement of fine aggregate (CFA), where some of the fly ash serves as a cementitious material with a volcanic ash effect, with the remainder having a microaggregate effect. CFA exhibits higher early age strength than fly ash concrete [35].
Most of the studies above pertain to the chloride ion binding and diffusion coefficients of fly ash concrete. Meanwhile, studies that investigate the performance of CFA in chloride salt environments are scarce. In this study, a laboratory natural diffusion method was adopted to investigate the durability of CFA in chloride salt environments. e chloride ion content at different depths was determined using chemical methods, and the chloride ion diffusion coefficient was determined based on Fick's second law of diffusion.
e deterioration mechanism of concrete in chloride salt environments was determined using microstructural analysis techniques (SEM, MIP, and XRD). e technique of using CFA to prevent chloride salt erosion was investigated from macroscopic and microscopic perspectives, thereby promoting the development of concrete materials for environmental protection and high performance.

Materials.
e binder was Grade P·O 42.5 ordinary Portland cement. e fine aggregate used for the tests was the middle sand of the second zone, which had a good assembly and distribution with an apparent density of 2600 kg/m 3 and a fineness modulus of 2.71. e coarse aggregate was a continuous collection of 5∼20 mm natural crushed stone with an apparent density of 2700 kg/m 3 , a crushing index of 10.2%, and a needle-like content of 9.7%. e fly ash was Grade III, and its chemical composition and physical properties are listed in Tables 1 and 2.

Experimental Design.
e design standard value of concrete strength was C45, and the water-cement ratio was 0.42 (OPC). For the same water-cement ratio, the same fly ash volume was used to replace the fine aggregates to form CFA. e replacement percentages of fly ash were 10%, 20%, 30%, and 40%, and the corresponding serial numbers were denoted as CFA-10, CFA-20, CFA-30, and CFA-40, respectively, as shown in Table 3. Equation (1) was used to calculate the unit consumption of fly ash in concrete.

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where ρ s and ρ FA are the densities of the fine aggregate and fly ash (kg/m 3 ), respectively, and m s and m FA are the unit consumption of the fine aggregate and fly ash (kg), respectively.

Concrete Specimen Preparation and Casting.
Based on the mix ratios, 100 mm × 100 mm × 100 mm cube specimens and 100 mm × 100 mm × 400 mm prismatic specimens were prepared. e cube specimens were used to determine the compressive strength of the CFA, whereas the prismatic specimens were used to determine the chloride ion content. After 24 h, the molds were removed and moved to a standard curing room for curing at 20 ± 2°C and relative humidity ≥95%. After curing for 28 days, the specimens were removed from the curing room. e top surface, bottom surface, and two small sides were sealed with epoxy resin to ensure onedimensional diffusion of chloride ions into the concrete. e specimens were immersed in NaCl solutions with mass concentrations of 0%, 1.5%, 3.5%, and 5% and subjected to compressive strength and chloride ion content tests after chloride salt immersion for 90 d.

Test Method.
After the concrete specimens were immersed in the corrosive solution and corroded for 90 days, they were removed from the solution. e compressive strengths of the cube specimens were then determined [36] ( Figure 1).
Samples were obtained from the two sides of the prismatic specimen using the drilling method (Figure 2(a)). A small drilling machine with a drill bit diameter of 8 mm was used for drilling. Powder samples were obtained layer by layer along the erosion surface every 1, 2, and 5 mm within depths of 10, 10-20, and 20-30 mm, respectively. e free chloride ion content (C f ) and total chloride ion content (C t ) in each sample were determined via chemical titration (Figure 2(b) and 2(c)) based on JTJ 270-98 [37].

Compressive Strength.
e compressive strength results of CFA after soaking in different salt solutions are presented in Figure 3(a). e growth rate of strength relative to immersion in water is shown in Figure 3 As the replacement rate of fly ash increased, the CFA strength increased gradually. Under 1.5% and 3.5% NaCl solution concentrations, the CFA-40 group exhibited the highest strength, i.e., 75.8 and 77.8 MPa, respectively. When immersed in the 5% NaCl solution concentration, the compressive strength of the CFA-30 group increased only slightly, i.e., reaching 80.9 MPa, compared with that of the CFA-40 group. In the typical fly ash concrete, the Ca(OH) 2 content in the hydration products decreases as the fly ash content increases and does not fully participate in the volcanic ash reaction. Moreover, a significant amount of unhydrated fly ash glass in the concrete is expelled during the convection of the internal and external media, thereby increasing the concrete porosity. For CFA, fly ash replaces the fine aggregates in OPC, and the cement quantity remains the same. Hence, the active ingredients in fly ash can fully react with the Ca(OH) 2 of cement hydration products, thereby inducing a zeolite reaction and generating a C-S-H gel that can fill the internal pores of the concrete. Furthermore, fly ash exhibits the characteristics of small particles and has a large specific surface area. Hence, it can fill the large pores between the cement and aggregate particles and exhibit an excellent microaggregate filling effect, thereby densifying the concrete. Figure 3(b) shows the growth rate of compressive strength. Longitudinally, as the salt concentration increased, the concrete strength increased to some extent. e growth rates of compressive strength in the 1.5%, 3.5%, and 5% salt solutions were approximately 5.5%, 8.8%, and 11.4%, respectively, which were within the 15% error range. e concrete in the chloride salt environment due to the chloride ion binding effect increased the concrete strength, although the increase was insignificant. In the short term, chloride salts can promote the development of concrete strength. e intrusion of chloride ions, which results in the corrosion of the reinforcement, is a more important subject.

Chloride Ion Concentration.
e chloride ions are divided into bound and free chloride ions. e latter play a decisive role in the corrosion process of steel reinforcement and are widely recognized as such.    NaCl-5% NaCl-0% NaCl-1.5% NaCl-3.5%

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In a laboratory environment, the natural diffusion method can be applied to investigate the diffusion behavior of chloride ions in concrete, and precisely reflect the combination and diffusion characteristics of concrete and chloride ions [38]. e distributions of the free chloride ion concentration of CFA containing different fly ash contents are shown in Figure 4. e concentration of free chloride ions at each depth in each concrete group increased gradually with the salt solution concentration. e chloride ion concentrations at different depths of the CFA with varying fly ash contents were lower than those of the control concrete. e penetration depth of the chloride ions increased gradually with the salt solution concentration, and a free chloride ion concentration of up to 0.02% (mass fraction) was adopted as an index to evaluate the penetration depth of CFA. e penetration depths of the OPC and CFA-40 concrete specimens in the 1.5% NaCl solution were 16 and 11 mm, respectively. When the salt solution concentration was increased to 5%, the corresponding penetration depths increased to 20 and 18 mm, respectively. is difference was caused by the increased salt solution concentration and increased gradient difference between the internal and external chloride ion concentrations, which induced the chloride ion diffusion effect. e distance at which chloride ions underwent directional migration increased at high chemical potential gradients. Figure 5 shows the trend of the total chloride ions at different salt solution concentrations. In the 5%, 3.5%, and 1.5% NaCl solution immersion environments, the free chloride ion concentrations at a 1 mm depth from the surface were 0.85%, 0.75%, and 0.55%, respectively, whereas the total chloride ion concentrations were 0.87%, 0.80%, and 0.61%, respectively. is behavior is attributed to the chloride ion binding properties. e trends for the total and free chloride ion contents in the three different salt solution concentrations were similar, and the variations in the free and total chloride ion concentrations with depth were exponential. e free and total chloride ion contents at different depths decreased gradually as the replacement rate of fly ash increased. e resistance of CFA to chloride ion penetration peaked at a fly ash content of 40%. First, the small size of the fly ash particles enhanced the compactness of the cementing materials, thereby improving the filling and impermeability of the concrete. Second, the volcanic ash effect of the fly ash reduced the less stable Ca(OH) 2 content, optimized the slurry structure, and improved the resistance of concrete to chloride ion attack [39]. e high Al 2 O 3 content of fly ash accelerated the generation of chloride ion-binding Friedel salts and increased the bound chloride ion content. erefore, it significantly improved the resistance of concrete to chloride salt attack.

Chloride Ion Binding Capacity.
e measured free and total chloride ion contents were used to calculate the binding capacity, R, of chloride ions to concrete. Nilsson et al. [40] defined the chloride binding capacity, R, as follows: where R is the chloride ion binding capacity, C b is the bound chloride ion content (%), and C f is the free chloride ion content (%). e R values of the chloride binding capacity for different fly ash replacement rates are shown in Figure 6. A weak correlation between chloride salt concentration and binding capacity was observed. e binding capacity values for OPC immersed in the 5%, 3.5%, and 1.5% salt solution concentrations were 0.101, 0.105, and 0.109, respectively; i.e., the values increased slightly as the salt solution concentration increased. e chloride ion binding capacity of CFA increased gradually with the fly ash content, and that of the CFA with 40% fly ash reached approximately 0.42. Studies [15,16] show that the chloride ion binding capacity of fly ash concrete ranges from 0.15 to 0.25, whereas that of CFA ranges from 0.15 to 0.42, which is significantly higher than that of fly ash concrete in the current study. e chloride binding capacity of concrete depends on physical adsorption and chemical bonding, in which chloride ions react with C 3 A to yield calcium chloroaluminate hydrate (C 3 A·CaCl 2 ·10H 2 O), known as Friedel's salt [41], which retards the rate of chloride ion penetration. e aluminium phase content of the raw material is vital to the binding of chloride ions; among the contents, C 3 A is positively correlated with the chloride ion binding ability. Moreover, C-S-H gels can absorb some chloride ions [42], and the secondary hydration reaction of fly ash produces additional C-S-H gels, which reduces the alkalinity of the internal pore solution of concrete, thereby increasing the physical adsorption capacity. Consequently, the binding property of CFA is more significant than that of fly ash concrete.

Chloride Ion Diffusion Coefficient.
e erosion patterns of CFA produced with different fly ash contents immersed in different salt solution concentrations were examined. e obtained results were as expected, and for the specimens soaked in the NaCl salt solutions, the variation in the chloride ions with depth obeyed Fick's second law of diffusion. Fick's second law of diffusion [43] can be expressed as follows: e boundary conditions for the chloride ion diffusion in concrete can be expressed as follows:

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Bringing the boundary conditions into (3), we can find the following: e inverse solution of the diffusion coefficient leads to the derivation of the formula for the chloride ion diffusion coefficient as follows: where C 0 is the initial chloride ion concentration in concrete (an initial concentration of 0.0001% was assumed), C s is the chloride ion concentration at the concrete surface (%), D is the chloride ion diffusion coefficient (m 2 ·s −1 ), x is the distance between the erosion interface and the concrete surface (mm), t is the duration of the chloride ion diffusion (s), and erf is the Gaussian error function. Figure 7 shows the fitted chloride ion diffusion coefficients. Highly concentrated salt solutions increase the possibility of chloride ion attack, and chloride ion diffusion increases accordingly as the salt solution concentration increases. e diffusion coefficients of chloride ions immersed in the 5% NaCl solution were generally higher than those in the 1.5% and 3.5% NaCl solutions. e diffusion coefficient of the OPC group in the 1.5% NaCl solution was 5 × 10 −12 m 2 ·s −1 , and that of the CFA-40 group was   6 Advances in Materials Science and Engineering 2.7 × 10 −12 m 2 ·s −1 , which is a reduction by 46% compared with the OPC group. When the salt solution concentration was 5%, the OPC group specimens indicated a diffusion coefficient of 9.4 × 10 −12 m 2 ·s −1 , whereas the CFA-40 group specimens indicated a diffusion coefficient of 3.9 × 10 −12 m 2 ·s −1 . Although all the diffusion coefficient values increased in the highly concentrated salt solutions, the increasing degree was different. Specifically, the diffusion coefficients for the OPC and CFA-40 groups increased by 88% and 43%, respectively. e CFA diffusion coefficient decreased gradually as the amount of blended fly ash increased. Compared with ordinary concrete, the chloride diffusion coefficients of the CFA-40 group specimens in the 1.5%, 3.5%, and 5% NaCl environments decreased by 58%, 46.1%, and 46%, respectively. is indicates that CFA with a 10%-40% replacement rate of fly ash is better than ordinary concrete in terms of resistance to chloride ion attack.

MIP.
Concrete is a nonhomogeneous material whose pore characteristics influence its permeability. e classical seepage theory suggests that the pore structure of a material determines its permeability properties. MIP is generally used for determining pore size distribution. is method is widely used to characterize the total porosity and pore size distribution of concrete. e influence of the pore size  Advances in Materials Science and Engineering distribution of CFA on the corrosion resistance to chloride ions was analyzed. In this study, the pore size of concrete is divided into four levels: < 20 nm (harmless pores), 20-50 nm (less harmful pores), 50-200 nm (harmful pores), and >200 nm (multi-harmful pores). Figure 8 shows the differential log-aperture relationship curve. Compared with the OPC group concrete, the pores of the CFA-40 group concrete were smaller, and the proportion of small pores was higher. e most probable pore size for the OPC group decreased from 35.423 to 32.414 nm, and that of the CFA-40 group decreased from 34.876 to 32.141 nm. After soaking in the 3.5% NaCl salt solution, the pore sizes were redistributed, and the pore structure was optimized. e proportions of different pore sizes were calculated based on the MIP data ( Figure 9). e percentages of <20 nm pores in the OPC and CFA-40 group specimens were 37.3% and 63.7% in clear water, respectively. e CFA specimens had lower porosity, more refined pore sizes, and higher density than the OPC concrete specimens; additionally, they exhibited a good pore structure.
After soaking in the 3.5% NaCl solution, the percentage of <20 nm pores in the OPC group specimens increased from 37.3% to 55.5%, and the percentage of 20-50 nm pores decreased from 43.9% to 34.9%. Correspondingly, the percentage of <20 nm pores in the CFA-40 group specimens decreased from 63.7% to 58.6%, but the percentage of 20-50 nm pores increased from 27.4% to 38.1% due to chloride binding properties. e <20 nm pores were filled gradually with more salt as the generated chemical products continued to increase and filled the pores; when the chemical binding products increased to a certain degree, the small pores ruptured. Consequently, the proportion of <20 nm pore size decreased after the immersion of CFA-40 in the 3.5% salt solution. Figure 10 shows the pore characterization parameters obtained during the MIP analysis. In clear water, the average pore diameter of the CFA-40 group specimens was 33.7% lower than that of the OPC group specimens, and the total pore area increased. is increase indicates that the volume of large pores in CFA decreased, whereas the number of small pores increased; additionally, the pore system compactness improved, and the pore structure was refined and optimized. e optimized pore structure strengthened the concrete and rendered the concrete structure more resistant to chloride ion penetration.
After soaking in clean water, the porosity of the CFA-40 group specimens decreased by 2.68% compared with that of the OPC group specimens. e reduced porosity of CFA was caused by the fly ash microaggregate filling effect as well as the volcanic ash effect, although the former was dominant. In contrast to water immersion [44], the decrease in porosity after immersion in a salt solution is primarily attributed to  Advances in Materials Science and Engineering Friedel's salts, CaCO3, and other substances produced during chloride ion erosion. Figure 11 shows the XRD patterns of the concrete specimens. e characteristic peaks of SiO 2 appeared in the diffraction spectra of each specimen, and the SiO 2 came from raw materials, such as the fly ash and coarse aggregate. Friedel's salt diffraction peak appeared near 11.2°in the concrete specimens after erosion by the NaCl salt solution; that is, Friedel's salt formed during the chemical reaction between the chloride ions and raw materials. e Friedel salt diffraction peak of the CFA containing 40% fly ash was more significant than that of the OPC group specimens. e AFt diffraction peak appeared near 9°, and the AFt peak of the concrete specimen in the clear water was more significant than that in the 3.5% NaCl salt solution. ere are different explanations for the weakening of the AFt peak. Zibara [45] suggested that in chloride salt solutions with high concentrations, AFt may be transformed to Friedel's salts, thus acting as a binding agent for chloride ions. Ekolu et al. [46] opine that AFt and AFm are destroyed to form Friedel's salts when the chloride ion concentration exceeds 0.5 mol/L (approximately 0.6 mol/L for a 3.5% NaCl solution by a mass fraction).

XRD.
Compared to the concrete specimens immersed in clear water, the Ca(OH) 2 diffraction peak significantly decreased and the CaCO 3 diffraction peak increased after 90 days of immersion in the NaCl solution.
e appearance of the Friedel salt diffraction peak was inevitably related to the strengths of the Ca(OH) 2 and CaCO 3 diffraction peaks. When the chloride ions penetrated the concrete, the following reaction occurred:   , and HO − in the AFm phase, thus generating Friedel's salts. When CO 3 2is replaced, it reacts to form CaCO 3 , which is insoluble in water. us, the CaCO 3 diffraction peaks in the XRD patterns were significantly enhanced. Figure 12 shows SEM images of the microscopic morphology of the concrete specimens. e hydration reaction of C 3 A with gypsum produced the AFt phase because the raw materials contained gypsum. e OPC and CFA-40 group specimens produced many needle-like prismatic AFt phase crystals after soaking in water (Figure 12(a) and 12(b)). e high-concentration salt solution disrupted the AFt phase and combined with Cl − to produce Friedel's salt hexagonal plates. Figures 12(c) and 12(d) show the microscopic morphology after immersion in the 3.5% NaCl salt solution. e AFt phase distribution of needle-like prismatic crystals was sparse, and the content was relatively small. Moreover, the formation of Friedel's salt was observed. CFA-40 group specimens had a spherical glass body of the unreacted fly ash with a layer of hydration products on the surface. Furthermore, the fly ash reduced the orientation of the concrete interface. Hence, the aggregate and paste formed a matrix, improving concrete impermeability.

Conclusions
In this study, the durability performance of CFA in a chloride salt environment was investigated. e following conclusions were obtained: (1) e strength of the concrete specimens increased after they were immersed in chloride salt, where a higher chloride salt concentration resulted in higher concrete strength. With the use of microscopic analysis, it was evident that in the clear water group, the CFA strength increase was primarily dominated by the fly ash microaggregate filling effect. After salt solution erosion, the CFA strength increase was primarily due to the chloride ion binding effect, which generated salts (primarily F salt), CaCO 3 , and other products inside the concrete. ese materials filled the internal pores of the concrete and decreased the porosity of the concrete specimens. (2) e chloride ion binding capacity correlated weakly with the chloride salt concentration but correlated strongly with the fly ash content. e chloride ion aggregation capacity improved gradually as the fly ash content increased. e binding capacity of CFA containing 40% fly ash was 0.42. is value is significantly higher than that of fly ash cement concrete owing to the higher aluminium phase in CFA, which provided the components required to bind the chloride ions. (3) e salt solution concentration affected the chloride ion concentration and diffusion coefficient at different depths of the concrete specimens. e higher the salt solution concentration, the greater the diffusion coefficient. e chloride ion diffusion coefficient and chloride ion concentration at different CFA depths were lower than those of the control concrete, and the resistance of CFA to chloride salt attack was significantly higher than that of the control concrete. (4) After CFA was immersed in the chloride salt solution, Friedel's salt was generated because of the binding effect of chloride ions. e distribution of needle-like prismatic AFt phase crystals inside the concrete was sparse, and the content was relatively low. is might be because the high-concentration salt solution dissolved the AFt phase to generate AFm, and the chloride ions replaced CO 3 2in the AFm phase. Hence, Friedel's salt was generated, which subsequently reacted with Ca+ to yield CaCO 3 (which is insoluble in water), thereby increasing the CaCO 3 content. (5) Concrete produced with fly ash fine aggregates exhibited low porosity and a good pore structure. Based on the test results, CFA exhibited high resistance to chloride ion attack.

Data Availability
e data used to support the findings of this study are available from the corresponding author upon request.

Conflicts of Interest
e authors declare that there are no conflicts of interest regarding the publication of this article.

Authors' Contributions
Dongsheng Zhang participated in conceptualization, methodology, formal analysis, data analysis, and resources; prepared the original draft; and revised and edited the paper. Qingyi Ai contributed to methodology, formal analysis, data analysis, and resources and prepared the original draft. Sen Li worked on investigation and visualization. Mingjie Mao helped with investigation, supervision, and project administration; prepared the original draft; and revised and edited the paper. Jiabin Li revised and edited the paper. All authors approved the final version of the paper.