Review of Research on Prediction Models for Residual Life of Concrete Structures
Abstract
:1. Introduction
2. Aging and Failure Mechanisms of Concrete Structures
2.1. Rebar Corrosion and the Decline of Concrete’s Mechanical Properties
2.2. Crack Propagation and Structural Damage
2.3. Chloride Ion Penetration and Concrete Corrosion
3. Classification of Lifespan Prediction Models
3.1. Physical Lifespan Prediction Models
3.1.1. Carbonation Depth Model
3.1.2. Chloride Ion Penetration Model
- represents the chloride ion concentration at time t and depth ,
- is the initial concentration, typically the chloride ion concentration in the concrete,
- is the surface concentration, corresponding to the concentration at the concrete surface exposed to water or air,
- is the chloride diffusion coefficient,
- erf denotes the error function.
- represents the initial chloride ion diffusion coefficient,
- is the reference time,
- is the coefficient for time-dependent decay.
3.2. Empirical Models
3.2.1. Empirical Formulas
3.2.2. Applicability and Limitations of Empirical Models
3.2.3. Integrating Empirical Models with Real-Time Data
3.3. Statistical Lifespan Prediction Models
3.3.1. Regression Analysis Models
3.3.2. Bayesian Networks for Lifespan Prediction
3.4. Machine Learning-Based Lifespan Prediction Models
3.4.1. Artificial Neural Networks (ANNs)
3.4.2. Support Vector Machines (SVMs)
3.4.3. Random Forests and Decision Trees
4. Model Validation and Prediction
4.1. Validation Methods
4.2. Expansion and Application of Evaluation Metrics
4.3. Sensitivity Analysis and Uncertainty Analysis
5. Application Cases of Models
6. Analysis of Advantages and Disadvantages of Existing Models
7. Research Progress and Development Trends
8. Conclusions
- Combining real-time monitoring data with advanced machine learning algorithms to improve prediction accuracy and robustness;
- Exploring hybrid models that integrate the strengths of both physical and data-driven models to enhance adaptability in complex environments;
- Developing more precise nonlinear and multiscale modeling techniques to accommodate environmental and material variations;
- Optimizing model validation and evaluation methods to improve their reliability and applicability in practical engineering projects;
- By combining experimental data with field monitoring data, future research should continue to explore how to effectively integrate these two sources in order to further optimize the predictive capability of models and improve the accuracy of concrete structure durability assessments.
Funding
Conflicts of Interest
References
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Corrosion Product | Conditions for Corrosion Occurrence | Effect on Concrete Cover | Effect on Corrosion Process | Relative Effect During Continuous Corrosion Process |
---|---|---|---|---|
Carbonate Products [20] | Reaction of carbon dioxide with calcium hydroxide, forming calcium carbonate | Reduces the alkalinity of the concrete, compromising the concrete cover of the reinforcement | Lowers the pH of concrete; the steel protection layer gradually fails, promoting steel corrosion | Moderate |
Chloride Products [21] | Chloride ions penetrate, particularly in marine or high-salinity environments | Increases the permeability of concrete, diminishing its protective capacity | Directly breaks down the steel passivation layer, initiates corrosion, causes pitting (localized corrosion) | High |
Sulfate Products [22] | Sulfates react with cement hydration products to form expansive compounds | Causes expansion and cracking, damaging the concrete structure | Expanding reactions create cracks, increasing permeability and accelerating corrosion | Low |
Corrosion rate at 40 mm cover (µA/cm2) | |||
Cement Type | Crack width | Percentage change | |
0.2 mm | 0.7 mm | ||
Ordinary Portland Cement | 1.20 | 1.48 | 23% |
7% Silica Fume Blended Cement | 0.59 | 1.03 | 75% |
30% Fly Ash Blended Cement | 0.39 | 0.50 | 28% |
50% Ground Granulated Blast Furnace Slag Blended Cement | 0.35 | 0.53 | 51% |
Corrosion rate at 20 mm cover (µA/cm2) | |||
Cement Type | Crack width | Percentage change | |
0.2 mm | 0.7 mm | ||
Ordinary Portland Cement | 2.65 | 3.23 | 22% |
7% Silica Fume Blended Cement | 0.67 | 1.12 | 67% |
30% Fly Ash Blended Cement | 0.64 | 0.71 | 11% |
50% Ground Granulated Blast Furnace Slag Blended Cement | 0.39 | 0. 51 | 31% |
Carbonation Conditions | Statistical Indicators | Fick Model | New Model |
---|---|---|---|
20 °C Carbonation | Mean error value (%) | 1.80% | 0.78% |
Standard deviation σ (%) | 1.91% | 0.35% | |
30 °C Carbonation | Mean error value (%) | 6.67% | 2.67% |
Standard deviation σ (%) | 7.70% | 3.39% |
Model | Disadvantages | Advantages |
---|---|---|
The model in reference [45]: : chloride concentration in the pore fluid at depth from the concrete surface after time of exposure to a chloride environment; : free chloride concentration at the concrete surface; erf: error function; : the coefficient of Cl− diffusion. | 1. Assumes chloride diffusion is uniform, ignoring the pores and cracks in concrete, which affects accuracy. 2. Assumes the diffusion coefficient remains constant, whereas it actually changes with time and environmental conditions. 3. In extreme environments such as high or low temperatures, the model’s applicability and accuracy decrease. | 1. The formula is based on Fick’s second law, with a simple structure that is easy to apply. 2. It is consistent with experimental data for short-term and medium-term exposures (90 to 520 days). 3. Suitable for different types of concrete and exposure environments. |
The model in reference [46]: : chloride concentration at distance x and time ; : chloride concentration at the concrete surface; erf: error function; : the initial chloride diffusion coefficient; m: the empirical coefficient that represents the time-dependent variation of the diffusion coefficient. | 1. The m coefficient depends on the mix ratio and environment, requiring calibration. 2. Extensive experimental data are needed for validation and adjustment. 3. Long-term predictions (e.g., decades) face uncertainties regarding diffusion coefficient behavior. | 1. Incorporating time-dependent diffusion coefficients enhances long-term chloride concentration predictions. 2. Predictions align well with actual data, especially in marine environments. 3. Suitable for various concrete mixes and environmental conditions. |
The model in reference [47]: : chloride concentration inside the concrete; : chloride concentration at the surface of the concrete; : depth of chloride penetration; : exposure time; : initial chloride diffusion coefficient; : age factor representing how diffusion changes with concrete age; : initial exposure time (when the concrete starts being exposed); : reference time for the initial measurements. | 1. Assumes chloride binding is time-independent and linear, which may not reflect actual behavior. 2. When the age factor is high, it may underestimate chloride penetration depth, leading to overly conservative predictions. 3. For short-term exposure, the model may overestimate the diffusion coefficient, leading to inaccurate predictions. | 1. Introduces a time-dependent diffusion coefficient, more accurately reflecting the change in chloride diffusion over time. 2. Provides a more accurate prediction of chloride penetration, especially under long-term exposure conditions like marine environments. 3. Aligns better with measured chloride penetration profiles in real-world applications. |
The model in reference [48]: : the chloride ion concentration at position and time ; : the stabilized surface chloride ion concentration; : the coefficient representing the influence of water–cement ratio on the stabilized surface chloride ion concentration; : the impact of sulfate ions on the chloride ion concentration on the concrete surface; erf: error function; : the chloride diffusion coefficient of the concrete measured at the hydration age. | 1. The model features complex mathematical expressions, requires large computational resources, and is highly sensitive to input parameters, requiring precise measurements. 2. In real marine environments, the diffusion coefficient undergoes dynamic changes due to the inhomogeneity and variability of the medium, and the boundary conditions are uncertain, which adds challenges to its field application. | 1. The model is particularly suitable for describing diffusion processes involving dynamic changes in both time and space variables. 2. It can be applied to diffusion processes under complex boundary conditions, taking into account the changes in substances over time. |
Reference | Type | Advantages | Disadvantages | Applicable Conditions |
---|---|---|---|---|
Reference [70] | Neural Networks | Strong adaptability, no gradient information required, optimization potential | Sensitive to network architecture, difficult to optimize, risk of overfitting | Complex and nonlinear problems with large datasets |
Reference [65] | SVMs | High prediction accuracy, adaptable to complex problems, strong optimization capability | Requires many parameters, computationally complex | Small high-dimensional datasets |
Reference [71] | Random Forests | Handles high-dimensional data, easy to apply | Lack of interpretability, long computation time | Exploratory analysis when relationships are unclear |
Reference [72] | Decision Trees | Can handle multiple data types, requires little data preprocessing | Instability, prone to bias | Data need clear classification, applicable to structured data |
Context | Model Prediction Accuracy | Importance of Field Data | |
---|---|---|---|
Reference [78] | Field validation of chloride ion diffusion in UK harbors | At 1.17 and 6.17 years, model predictions closely matched the monitoring data. At year 18, the model slightly underestimated chloride ion diffusion at deeper layers, with about 10% error. | Highlights the role of field data in validating the model’s performance over time, showing discrepancies at deeper layers at later years. |
Reference [79] | Study of chloride ion diffusion coefficients in aging structures along the South China Sea | For the HPW6 structure, the measured chloride ion surface concentration was 1.78%, while the model predicted 4.13%. | Demonstrates how field data from actual aging structures provides critical validation for model predictions, emphasizing real-world applications. |
Reference [80] | Geothermal power plant concrete exposed to chloride- and sulfate-rich geothermal water | Field data show that, after 18 years, chloride ions had penetrated into deeper layers in normal concrete and began corroding the reinforcement; ultra-high-durability concrete performed better at the same time, although the diffusion occurred slightly earlier, but the overall trend was consistent with the model. | Field data confirmed that the actual chloride diffusion rate was faster than predicted in normal concrete, validating the importance of monitoring for accurate durability modeling. |
Reference [81] | Lifecycle modeling of concrete cracking and reinforcement corrosion in Changfeng Creek Bridge, China | The study predicts, through lifecycle modeling, that reducing the maintenance cycle (e.g., shortening it from 12 years to 4 years) can significantly extend the service life of the bridge. Field data from regular monitoring revealed an extension of approximately 15 years. | This case highlights the importance of field monitoring in ensuring the long-term durability of infrastructure and optimizing models. |
Model Type | Advantages | Disadvantages | Applicable Scenarios |
---|---|---|---|
Physical Models | Strong theoretical foundation, capable of simulating long-term degradation processes, incorporates environmental factors | Computationally complex, requires accurate data, limited applicability | Suitable for simpler controlled environments, such as laboratory settings or less complex engineering projects |
Empirical Models | Simple, fast, cost-effective, highly adaptable | Limited precision, reliant on past data, not applicable to all situations | Ideal for scenarios with available data, especially for quick preliminary assessments |
Statistical Models | Based on data-driven predictions, adaptable to complex environments, capable of handling uncertainty | Requires high-quality data, difficult to interpret | Best for data-rich complex environments with numerous variables and uncertainties |
Machine Learning Models | High accuracy, capable of handling complex data and problems, real-time prediction updates | Requires large amounts of data and computational resources, difficult to interpret model mechanisms | Best suited for environments that require high-precision predictions, real-time monitoring, and substantial data support |
Hybrid Models | Strong theoretical foundation, capable of simulating long-term degradation processes, incorporates environmental factors | Complex models that require multidisciplinary knowledge for integration | Ideal for engineering projects that need to consider multiple factors, complex structures, or dynamic environments |
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Qi, L.; Peng, X.; Yang, Q.; Xia, K.; Xu, B. Review of Research on Prediction Models for Residual Life of Concrete Structures. Coatings 2025, 15, 693. https://doi.org/10.3390/coatings15060693
Qi L, Peng X, Yang Q, Xia K, Xu B. Review of Research on Prediction Models for Residual Life of Concrete Structures. Coatings. 2025; 15(6):693. https://doi.org/10.3390/coatings15060693
Chicago/Turabian StyleQi, Linyuan, Xi Peng, Qiuwei Yang, Kangshuo Xia, and Bin Xu. 2025. "Review of Research on Prediction Models for Residual Life of Concrete Structures" Coatings 15, no. 6: 693. https://doi.org/10.3390/coatings15060693
APA StyleQi, L., Peng, X., Yang, Q., Xia, K., & Xu, B. (2025). Review of Research on Prediction Models for Residual Life of Concrete Structures. Coatings, 15(6), 693. https://doi.org/10.3390/coatings15060693