Water diversion projects in high-latitude areas often reduce the risk of ice jams in winter by reducing the water transfer flow, which might cause the waste of water transfer benefits. This paper establishes a real-time prediction system of water temperature in winter, which can predict the change in water temperature by inputting the air temperature forecast data and the current hydraulic data. Taking the middle route of the south-to-north water diversion project as the background, the model parameters calibration and system application testing at different time periods are carried out. The results show that the prediction errors of water temperature for the 1 and 7 days are relatively small, and the prediction errors of water temperature at four observation stations can be controlled within ±0.3 and ±0.6 °C, with the root mean square error (RMSE) ranging from 0.07 to 0.25 and 0.12 to 0.36, respectively. The 15-day water temperature prediction results are greatly affected by air temperature input conditions. The prediction errors for the first 7 days are relatively small, ranging from −0.59 to 0.36 °C, and the errors for the last 8 days increase as the accuracy of the air temperature forecast decreases, ranging from −2.42 to 0.22 °C.

  • Establish a water temperature prediction model based on the characteristics of the water diversion projects.

  • The accuracy of water temperature predictions for different time periods is tested in practical applications.

  • Water temperature prediction and project scheduling are effectively combined.

The construction of water diversion projects is an effective way to promote the redistribution of regional water resources and alleviate the water shortage problems in industry, agriculture, and daily life caused by continuous population growth (Langford et al. 2015; Shandany et al. 2018; Long et al. 2020). However, the winter operation and management of water diversion projects located in high-latitude areas still face the threat of ice jams and ice dams. The middle route of the south-to-north water diversion project (MRSNWDP) in China, with a total length of 1,432 km, is a typical water transfer canal system. Due to the large span of the project from south to north latitudes, the water flows from low latitudes to high latitudes, causing significant heat loss along the way. In addition, the air temperature in the canal system north of the Yellow River during winter is low, which makes it easy to produce ice damage problems (Wen et al. 2015). The water flows by gravity, and the main canal has no other online storage reservoirs and limited storage capacity. Also, it adopts the operation mode of the constant water level before the gate. Consequently, it is difficult to dispatch water in winter (Duan et al. 2016). Ice jam is a phenomenon in which a large number of frazil slush accumulates under the ice cover, quickly blocking part of the flow cross-section and causing the upstream water level to rise, mainly occurring in the freeze-up period (Barrette & Lindenschmidt 2023). After the canal system freezes, large-flow water transfer conditions will accelerate the flow velocity of drift ice, forming accumulations at the narrow channels and around hydraulic structures, increasing the risk of ice jam occurrence (Ettema et al. 2009). Water diversion projects often reduce the water flow to suppress the ice jam risk. However, premature and large-scale use of small-flow water transfer methods may cause temporal and spatial losses of water transfer benefits, aggravating the water shortage dilemma in winter. Taking the Beijumahe Controlled Gate at the end of the project as an example, the design flow through the gate is 50 m3/s, while the actual flows in the four winters of 2011–2015 were 11–17 m3/s, accounting for only about 30% of the design flow (Duan et al. 2016). Therefore, it is necessary to finely adjust the time and range of adopting small-flow water transfer based on the water temperature prediction results of the project in winter to improve its safety and efficiency.

At present, the study of water transfer in winter mainly involves ice monitoring, ice prediction modeling methods, and promoting the development of water diversion project information technology. Effective ice monitoring can provide key information for the winter operation of artificial water infrastructure in cold regions (Norvanchig & Randhir 2021; Zhang et al. 2021). Hydrological gauges and pressure recorders are used to monitor the evolution of long-term flow conditions, and empirical models were established to predict ice based on changes in water levels and flows (Beltaos & Burrell 2010; Beltaos et al. 2011). Another research direction is the development of satellite image icing monitoring methods. Liu et al. (2009) reported on the application of high spatiotemporal resolution satellite data in ice observation. Unterschultz et al. (2009) demonstrated the potential of using synthetic aperture radar (SAR) satellite images to identify ice jams during breakup, intact ice, and open water bodies. Chaouch et al. (2014) proposed a method that can distinguish between ice covers and flowing water from remote sensing photography. Both ground sensors and satellite photography have problems with high maintenance costs or insufficient accuracy. Since drones entered the commercial market a few years ago, their prices have become cheaper and have been used in ice monitoring in river and water diversion projects to compensate for these shortcomings (Liu et al. 2019; Chen & Liu 2023).

The hydrological conditions in cold regions, especially in the middle and high latitudes, are sensitive to climate change (Hu et al. 2017). The seasonal accumulation of glaciers and snow become important sources of river flow after they melt (Barnett et al. 2005; Mohammadi et al. 2023). In addition, due to the recent sustained emissions of greenhouse gases, rising air temperatures and changes in precipitation will greatly affect the hydrological conditions in cold regions in the future (Minville et al. 2008; Adam et al. 2009; Huziy et al. 2013; Rasouli et al. 2015). Therefore, hydrological modeling in cold regions has become a research focus for scholars (Cooper et al. 2011; Brown et al. 2014; Gao et al. 2018; Burger et al. 2019; Mohammadi et al. 2023). On the one hand, scholars attempted to reveal the impact of climate change on hydrological conditions and established ice jam occurrence prediction models by collecting hydro-climatic data (Massie et al. 2002; Chen & Ji 2005; Wang et al. 2012; Guo et al. 2018). On the other hand, there are also many studies on the ice jam formation mechanism, numerical simulation, and predicting the probability of ice jam formation. Combined with the prototype observation data of the winter ice regime in the MRSNWDP in the past 5 years, Duan et al. (2016) analyzed the characteristics of the temporal and spatial distribution of the ice conditions. Sui et al. (2002) studied the relationship between water level, ice jam thickness, and ice flow and revealed the empirical relationship between ice thickness and the Froude number. Xu et al. (2010) studied several ice mechanics problems in the water transfer of the MRSNWDP during the ice period, which provided a reference for water transfer scheduling. Guo et al. (2011) conducted a numerical simulation of the whole water transfer process during the ice period in typical years and gave suggestions for safe water transfer scheduling of the MRSNWDP in winter. Shen et al. (1995) proposed a fine river ice model, suitable for river networks, and established a two-dimensional dynamic transport theory, which has been continuously improved to form the DynRICE model, and then validated the model using historical measured data.

The rapid development and widespread application of information technology have provided new management tools for the construction and operation of water diversion projects. The application of new technologies such as GIS (Geographic Information System), BIM (Building Information Modeling), the Internet of Things, digital twin, and big data is conducive to improving the real-time scheduling capability of the project and realizing efficient water transfer, safe water transfer, and intelligent water transfer. BIM + GIS technology has been applied in the operation and management of the Jiaodong Water Diversion Project in Shandong Province and the Dianchi Lake Water Replenishment Project in Yunnan Province, China (Dai et al. 2018; Han et al. 2022). Liu et al. (2021) proposed an integrated visualization framework based on BIM, which integrates data collection, data analysis, early warning release, and emergency response, improving the automation level and emergency management efficiency of water diversion project operation. Meanwhile, the digital twin technology is also an effective tool to ensure the safety and efficiency of water transfer. Liu et al. (2023) proposed a digital twin framework including a real-time self-correcting model that can provide timely fault detection for the daily scheduling of water diversion projects. Ye et al. (2023) proposed a data-driven and physics-based coupled real-time model predictive control (MPC) method for real-time regulation of hydropower plant operation, which has a higher accuracy, faster decision-making efficiency, and real-time feedback correction mechanism compared to traditional models.

In summary, some progress has been made in ice monitoring, ice prediction, and promoting the development of project informatization in water diversion projects. However, a complete and real-time ice prediction method has not yet been formed, and ice prediction and project scheduling have not been effectively combined. Moreover, scholars often establish statistical or intelligent algorithmic models to predict water temperature or the probability of ice jam formation by inputting information such as air temperature and precipitation. Water temperature measurement is an important part of on-site observation and significantly impacts the analysis of the ice evolution in the project (Cook et al. 2006; Turcotte et al. 2012, 2014; Maheu et al. 2016). Researchers use many high-precision temperature sensors to collect water temperature data to study the water temperature change process and then analyze its influencing factors, which are the basis for analyzing ice evolution. This study establishes a water temperature prediction model for long-distance water diversion projects in winter based on the heat exchange principle and river ice hydraulics theory and tests the model's effects on short-term and medium- to long-term water temperature prediction by actual cases. Compared with other studies, the model proposed in this paper is more suitable for water diversion projects, and its accuracy is tested in practical applications (Shen et al. 1993, 1995).

Real-time water temperature prediction system in winter

A real-time water temperature prediction system for long-distance water diversion projects in winter is established, as shown in Figure 1. This system represents an integrated platform that predicts future water temperature changes by inputting air temperature forecast data, water temperature, water level, and flow of the project. These are then reported to the project management department, providing a reference for water transfer scheduling in winter. The system consists of three parts, including input data, water temperature prediction model, and output results:
  • (1)

    Input data: The input data include two parts: air temperature data and hydraulic data. Future weather forecasts, hourly air temperature changes, and current water temperature, water level, and flow data for the whole project are obtained through docking with the China Meteorological Data Network and the project management department. The project monitoring department reads the hydraulic information of the canal pools in real-time through sensors, and the accuracy of the input data is improved by manual field testing at some nodes. Moreover, the obtained data are entered into the database to do the rationality analysis, realize the data organization and correction, and then be transmitted to the model.

  • (2)

    Water temperature prediction model: The model predicts water temperature for three scenarios, including open canal, drift ice, and freeze-up. The input parameters to the model include the project generalization, the project operating plans, the total simulation time, and the heat exchange coefficients. The project operation plans include the adjustment of the water level before the gate, the flow through the gate, and the diversion flow at the water outlet. The heat exchange coefficients include the water surface heat exchange coefficient and the ice surface heat exchange coefficient. These parameters need to be adjusted according to the actual situations. Finally, the predictive values of the pool water temperature are compared and analyzed with the measured values, and the model is continuously corrected and optimized to improve its accuracy.

  • (3)

    Output results: The output results are the predictive values of the future water temperature, which are stored in the database. Water temperature is the basis for analyzing the ice evolution, and when the predictive water temperature is below 0 °C, there is a risk of freeze-up in the canal system. In this case, further predicting the range and time of icing in the canal system is necessary. Then, an ice prediction report is prepared and submitted it to the project dispatching department. Finally, the project dispatching department controls the gate openings to adjust the water transfer flow based on this report.

Figure 1

Real-time water temperature prediction system for long-distance water diversion projects in winter.

Figure 1

Real-time water temperature prediction system for long-distance water diversion projects in winter.

Close modal

Water temperature prediction model for canal systems

The water diversion project can be generalized into a series canal system, as shown in Figure 2. Multiple controlled gates divide the canal pools to form a series canal system, and a pool consists of two gates, including upstream and downstream gates. Qu and Qd are the flows through the upstream and downstream gates of a pool, respectively, m3/s; G(i) is the opening of the gate, m; i is the serial number of the gates and pools; Qout is the flow transferred from the main canal to the submain canal through the outlet, and Qdown is the water demand of downstream users, m3/s. The flow relationship of the steady flow state is shown in the following equations (Liu et al. 2015; Xu et al. 2023):
(1)
(2)
Figure 2

Schematic diagram of canal system generalization.

Figure 2

Schematic diagram of canal system generalization.

Close modal

Unsteady flow simulation module

In the model, the unsteady flow equations of an open canal are used to simulate the hydraulic response characteristics of the canal system under the conditions of floating ice cover formation and open canal flow. The governing equations are as follows (Yao et al. 2009; Liu et al. 2011):

Continuity equation:
(3)
Momentum equation:
(4)
where Z is the water level, m; h is the water depth, m; Q is flow, m3/s; B is the width of the water surface, m; A is the cross-sectional area of the water flow, m2; C is Chezy coefficient; t is the time variable, s; x is the spatial variable, m; qx is the interval inflow, m3/s; vqs is the average velocity of lateral inflow in the flow direction, m/s; u is the velocity of water flow along the axis direction, m/s; s is the canal bottom slope gradient; R is the hydraulic radius, m; g is the acceleration of gravity, m/s2. For prismatic canals, there is a relationship, as shown in the following equation:
(5)

When a floating ice cover is formed in the canal, the wetted perimeter and roughness coefficient of the canal are both affected by the ice cover (Wei & Huang 2002; Yang 2018).

Water temperature simulation module

This model ignores the influences of the canal bottom on the water temperature and uses the convection equation to describe the water temperature change process, as shown in the following equation (Lal & Shen 1991; Liu 2019):
(6)
where Cp is the specific heat capacity of water, J/(kg · °C); Tw is the cross-sectional average water temperature, °C; φ is the heat released by the water body per unit time, W/m2; ρ is the water density, kg/m³; D is the cross-sectional average water depth, m.
  • (1)
    When the canal is an open one, water heat exchange exists between the water surface and the atmosphere:
    (7)
    where φwa is the heat exchange quantity between the water surface and the atmosphere, W/m2; hw is the heat exchange coefficient between the water surface and the atmosphere, W/(m2 · °C); Ta is the air temperature, °C.
  • (2)
    When the water surface is completely frozen, the heat released by the water body is completely converted into the thickness variation of the ice cover. It is assumed that the heat exchange only exists between the lower surface of the ice body and the water body:
    (8)
    (9)
    where φwi is the heat exchange quantity between water and the lower surface of the ice cover, W/m2; hwiw is the heat exchange coefficient between water and the lower surface of the ice cover, W/(m2·°C); κ is the empirical coefficient.
  • (3)
    When the water surface is in a state of drift ice or partially frozen, two forms of heat exchange between the water surface and the ice surface are considered:
    (10)
    (11)
    (12)
    where Ca is the proportion of ice covering the water surface, %; φia is the heat exchange quantity between the ice surface and the atmosphere, W/m2; Tis is the upper surface temperature of the ice cover, °C; hi is the ice cover thickness, m; Δh1 is the virtual ice cover thickness, m; hwai is the heat exchange coefficient between the ice surface and the atmosphere, W/(m2·°C).

Drift ice simulation module

When the water body is supercooled, frazil slush will be produced. The ice concentration in the water body is expressed as (Lal & Shen 1991):
(13)
where Ci is the proportion of ice in the water body, %; ρi is the ice density, kg/m3; Li is the ice latent heat, J/kg.
The ice concentration convection equation is used to represent the movement of drift ice with water flow, as shown in the following equation (Liu 2019):
(14)

Freezing simulation module

The model is set as follows:

  • (1)

    An initial ice cover will be formed in the canal cross-section when the proportion of ice covering the water surface exceeds 80% (Ca ≥ 80%) (Liu 2019).

  • (2)

    If the Froude number is less than 0.06 and the flow velocity is less than 0.5 m/s, ice floes will form a smooth cover of a single layer of ice floes through juxtaposition. The modeling of the freezing process is described in the literature (Liu et al. 2013).

  • (3)

    If the Froude number is greater than 0.06 or the flow velocity is greater than 0.5 m/s, surface ice elements can under turn or submerge at the leading edge to form a thicker ice cover (Ma et al. 2009).

  • (4)

    Ice formed in a pool cannot flow through the downstream gate to the downstream pool.

After complete freeze-up (Ca = 100%), mainly the ice cover thickness changes are simulated. Considering the influences of air temperature and water temperature on the ice cover thickness, the changes in ice cover thickness in a period of time are as follows:
(15)
where Δhi is the variation of ice thickness during the Δt time period, m.
If the upper surface of the ice cover is covered with snow, it is assumed that the heat exchange between the upper surface of the snow and the atmosphere only causes changes in snow thickness, and the changes in ice cover thickness are only affected by water temperature:
(16)
where Δhsnow is the variation of snow thickness during the Δt time period, m; φas is the heat exchange quantity between the upper surface of the snow and the atmosphere, W/m2; hsnow is the snow thickness, m; ρsnow is the snow density, kg/m³; α is the constant coefficient; Tss is the upper surface temperature of the snow, °C.
When the heat absorbed by the ice cover is greater than the heat required for melting, the excess heat will increase the water temperature in the pool, as shown in the following equation:
(17)
where ΔTw is the increase in water temperature during the Δt time period, °C.

Study area

As shown in Figure 3, this paper takes the canal section from the Anyanghe Controlled Gate to the Beijuma Controlled Gate of the MRSNWDP as the study area, and the names and locations of the gates it passes through are shown in Table 1. The project runs in a south–north direction with a large latitude span, and the average air temperature gradually decreases from south to north as the latitude increases. Therefore, there is a phenomenon of gradual freezing from the Beijumahe Controlled Gate at the downstream end to the upstream of the canal section, and the water temperature at the Beijumahe Controlled Gate becomes a key observation point for ice conditions. Since the entire project was opened to water in 2014, the water flow in the canal north of Anyang has been affected by the cold temperatures in winter, resulting in different degrees of ice damage problems and a decrease in water transfer capacity. In the winter of 2015–2016, affected by rare cold waves, ice jams occurred in many places of the canal section from the Puyanghe Controlled Gate to the Beijumahe Controlled Gate (Duan et al. 2016). The total length of ice jams was about 26.5 km, and the length of the ice jams in a single pool was 3.2–7.1 km. Ice jams encroached on the canal cross-section, raising the upstream water levels in the pools, which might threaten the dam's safety and interrupt the water supply (Huang et al. 2019).
Table 1

Summary of the gates along the route

Serial numberControlled gate nameLocation
Anyanghe Controlled Gate Anyang City, Henan Province 
Zhanghe Controlled Gate Handan City, Hebei Province 
Mangniuhe Controlled Gate Handan City, Hebei Province 
Qinhe Controlled Gate Handan City, Hebei Province 
Minghe Controlled Gate Handan City, Hebei Province 
Nanshahe Controlled Gate Xingtai City, Hebei Province 
Qilihe Controlled Gate Xingtai City, Hebei Province 
Baimahe Controlled Gate Xingtai City, Hebei Province 
Liyanghe Controlled Gate Xingtai City, Hebei Province 
10 Wuhe Controlled Gate Xingtai City, Hebei Province 
11 Huaihe Controlled Gate Shijiazhuang City, Hebei Province 
12 Jiaohe Controlled Gate Shijiazhuang City, Hebei Province 
13 Guyunhe Controlled Gate Shijiazhuang City, Hebei Province 
14 Hutuohe Controlled Gate Shijiazhuang City, Hebei Province 
15 Cihe Controlled Gate Shijiazhuang City, Hebei Province 
16 Shahebei Controlled Gate Shijiazhuang City, Hebei Province 
17 Modaogou Controlled Gate Baoding City, Hebei Province 
18 Tanghe Controlled Gate Baoding City, Hebei Province 
19 Fangshuihe Controlled Gate Baoding City, Hebei Province 
20 Puyanghe Controlled Gate Baoding City, Hebei Province 
21 Gangtou Controlled Gate Baoding City, Hebei Province 
22 Xiheishan Controlled Gate Baoding City, Hebei Province 
23 Puhe Controlled Gate Baoding City, Hebei Province 
24 Beiyishui Controlled Gate Baoding City, Hebei Province 
25 Fenzhuanghe Controlled Gate Baoding City, Hebei Province 
26 Beijumahe Controlled Gate The border between Hebei Province and Beijing City 
Serial numberControlled gate nameLocation
Anyanghe Controlled Gate Anyang City, Henan Province 
Zhanghe Controlled Gate Handan City, Hebei Province 
Mangniuhe Controlled Gate Handan City, Hebei Province 
Qinhe Controlled Gate Handan City, Hebei Province 
Minghe Controlled Gate Handan City, Hebei Province 
Nanshahe Controlled Gate Xingtai City, Hebei Province 
Qilihe Controlled Gate Xingtai City, Hebei Province 
Baimahe Controlled Gate Xingtai City, Hebei Province 
Liyanghe Controlled Gate Xingtai City, Hebei Province 
10 Wuhe Controlled Gate Xingtai City, Hebei Province 
11 Huaihe Controlled Gate Shijiazhuang City, Hebei Province 
12 Jiaohe Controlled Gate Shijiazhuang City, Hebei Province 
13 Guyunhe Controlled Gate Shijiazhuang City, Hebei Province 
14 Hutuohe Controlled Gate Shijiazhuang City, Hebei Province 
15 Cihe Controlled Gate Shijiazhuang City, Hebei Province 
16 Shahebei Controlled Gate Shijiazhuang City, Hebei Province 
17 Modaogou Controlled Gate Baoding City, Hebei Province 
18 Tanghe Controlled Gate Baoding City, Hebei Province 
19 Fangshuihe Controlled Gate Baoding City, Hebei Province 
20 Puyanghe Controlled Gate Baoding City, Hebei Province 
21 Gangtou Controlled Gate Baoding City, Hebei Province 
22 Xiheishan Controlled Gate Baoding City, Hebei Province 
23 Puhe Controlled Gate Baoding City, Hebei Province 
24 Beiyishui Controlled Gate Baoding City, Hebei Province 
25 Fenzhuanghe Controlled Gate Baoding City, Hebei Province 
26 Beijumahe Controlled Gate The border between Hebei Province and Beijing City 
Figure 3

Study area.

Model parameters calibration

According to the parameter calibration of the water surface heat exchange coefficient and ice surface heat exchange coefficient for ice conditions in the winter of 2016–2017, it is determined that the heat exchange coefficient under open canal conditions is about 13 W/(m2·°C), and the heat exchange coefficient under ice cover conditions is about 26 W/(m2·°C). The simulation process of pool water temperature is shown in Figure 4. It can be seen that the water temperature change trend of the simulation results is consistent with the measured values. The closer the verified pool is to the downstream, the greater the water temperature prediction errors, but the errors are less than 0.5 °C.
Figure 4

Water temperature simulation at some gates in the winter of 2016–2017.

Figure 4

Water temperature simulation at some gates in the winter of 2016–2017.

Close modal

Work program

The air temperature and hydraulic data used in this paper are provided by the project management department of the MRSNWDP. The measured water temperature data are provided by the automated water temperature monitoring system along the project. In addition, the Changjiang River Scientific Research Institute is responsible for on-site monitoring to improve the accuracy of the input data through manual field testing and review at some nodes, including Gate 14 (Hutuohe Controlled Gate), Gate 21 (Gangtou Controlled Gate), Gate 24 (Beiyishui Controlled Gate), and Gate 26 (Beijumahe Controlled Gate). This study focuses on numerical simulation and modeling to compare the predictive and measured values of water temperature to test and optimize the model's accuracy. To test the water temperature prediction effects of the model, the water temperature of the canal system was predicted for three periods: 1-day, short-term, and medium- to long-term, and the simulation time is from 1 January to 24 February 2022.

1-day water temperature prediction effect

Starting from 31 December 2021, the water temperature of the canal system will be predicted daily based on the measured water temperature at 8:00 a.m. on that day and future air temperature forecast data, and the water temperature predictive results of the next day at 8:00 a.m. will be provided to the project management and ice monitoring departments before 12:00 noon. Figure 5 shows the fitting process between the predictive and actual values of water temperature on the first day, 1 January 2022. The water temperature prediction error refers to the difference between the predictive and measured water temperature values. As can be seen from the figure, the measured water temperature values on 31 December and 1 January at 8:00 a.m. are similar. The overall trend of the predictive and measured water temperatures on 1 January is consistent, except for the prediction errors of the two gates, Gate 9 (Liyanghe Controlled Gate) and Gate 11 (Huaihe Controlled Gate), which are −1.15 and 1.04 °C, respectively, and the errors of other gates are within ±1 °C. Due to abnormal values in the input water temperature data, the amplitude of the water temperature wave propagated downstream, causing an increase in error downstream.
Figure 5

Comparison of water temperature prediction results on 1 January 2022.

Figure 5

Comparison of water temperature prediction results on 1 January 2022.

Close modal
During the water temperature prediction process from 1 January to 5 January, it was found that the measured water temperature values provided by the automated water temperature monitoring system were not suitable for use in this study due to the obvious fluctuations in spatial distribution, which may be influenced by the measuring instruments such as water temperature sensors, despite the tendency to gradually decrease from upstream to downstream (Yin 2023). If the accuracy of the measured water temperature provided by the water temperature monitoring system is not high, it will directly affect the model's prediction accuracy and the subsequent error analysis, hindering the optimization of the model parameters. Therefore, starting from 6 January, this study adopted the manually measured data from the Changjiang River Scientific Research Institute at the four observation stations to replace the automated water temperature monitoring data and used the proximity interpolation method to process the abrupt values of the input water temperature data. The comparison process between the predictive and measured water temperature values is shown in Figure 6. The water temperature prediction errors at four observation stations are within −0.2 to 0.1 °C, with an error interval length of 0.3 °C. The error at the Beijumahe Controlled Gate is only 0.02 °C, which is 93.5% less than the error on January 1.
Figure 6

Comparison of water temperature prediction results on 6 January 2022.

Figure 6

Comparison of water temperature prediction results on 6 January 2022.

Close modal
Ten consecutive 1-day water temperature predictions were conducted from 6 to 15 January, and the prediction errors are shown in Figure 7. It can be seen that the prediction errors of water temperature at the four stations can basically be controlled within ±0.3 °C, and the trends of the error changes are the same. Due to the comprehensive influence of the model generalization method, input data of air temperature and water temperature, errors at individual gates, such as the Hutuohe Controlled Gate, reached 0.42 °C on 12 January, which is acceptable.
Figure 7

Comparison of ten consecutive 1-day water temperature prediction errors.

Figure 7

Comparison of ten consecutive 1-day water temperature prediction errors.

Close modal

We calculate the root mean squared error (RMSE) of water temperature at four observation stations from 6 to 15 January, as shown in Table 2. Spatially, the RMSE of water temperature at the four observation stations from 6 to 15 January is relatively small, at no more than 0.2. Temporally, except for the RMSE of the water temperature at the four stations on 12 January reaching 0.25, the RMSE at other times does not exceed 0.2. The errors at the Beijumahe Controlled Gate are smaller, which are within the range of ±0.22 °C, and the RMSE is about 0.11.

Table 2

RMSE of water temperature predictions at four observation stations from 6 to 15 Jan

DateWater temperature prediction errors at four observation stations (°C)
RMSE of water temperature predictions for this day at four stations
Hutuohe Controlled GateGangtou Controlled GateBeiyishui Controlled GateBeijumahe Controlled Gate
6 Jan 0.10 −0.19 0.03 0.02 0.11 
7 Jan 0.15 −0.02 0.06 0.17 0.12 
8 Jan 0.06 −0.23 −0.16 −0.06 0.15 
9 Jan 0.12 −0.05 0.01 0.02 0.07 
10 Jan 0.15 −0.14 −0.19 −0.04 0.14 
11 Jan 0.20 −0.21 −0.09 0.22 0.19 
12 Jan 0.42 0.21 0.04 0.18 0.25 
13 Jan 0.03 −0.27 −0.29 0.00 0.20 
14 Jan 0.11 −0.21 −0.06 0.02 0.12 
15 Jan 0.11 0.02 0.13 −0.02 0.09 
RMSE from 6 to 15 Jan 0.18 0.18 0.13 0.11 
DateWater temperature prediction errors at four observation stations (°C)
RMSE of water temperature predictions for this day at four stations
Hutuohe Controlled GateGangtou Controlled GateBeiyishui Controlled GateBeijumahe Controlled Gate
6 Jan 0.10 −0.19 0.03 0.02 0.11 
7 Jan 0.15 −0.02 0.06 0.17 0.12 
8 Jan 0.06 −0.23 −0.16 −0.06 0.15 
9 Jan 0.12 −0.05 0.01 0.02 0.07 
10 Jan 0.15 −0.14 −0.19 −0.04 0.14 
11 Jan 0.20 −0.21 −0.09 0.22 0.19 
12 Jan 0.42 0.21 0.04 0.18 0.25 
13 Jan 0.03 −0.27 −0.29 0.00 0.20 
14 Jan 0.11 −0.21 −0.06 0.02 0.12 
15 Jan 0.11 0.02 0.13 −0.02 0.09 
RMSE from 6 to 15 Jan 0.18 0.18 0.13 0.11 

7-day water temperature prediction effect

Considering the higher accuracy of the air temperature forecast for the coming week, the 7-day water temperature was used to represent the short-term water temperature prediction to provide a reference for the project water transfer. The model was used to predict the water temperature changes along the project from 6 to 16 January for five consecutive 7-day periods, including from 6 to 12 January, from 7 to 13 January, from 8 to 14 January, from 9 to 15 January, from 10 to 16 January. Then, the prediction errors and RMSE of water temperature at four observation stations were calculated, as shown in Figure 8 and Table 3. Figure 8 shows that five consecutive 7-day water temperature prediction errors are controlled within ±0.6 °C, with the RMSE ranging from 0.12 to 0.36, at four stations. The error range and RMSE at the Hutuohe Controlled Gate are the largest from 6 to 12 January, which are from −0.55 to 0.57 °C and 0.36, respectively. The error range at the Beijumahe Controlled Gate is from −0.5 to 0.3 °C, with an average value of the RMSE of 0.19, which is smaller than those at the other three stations. This is because, in the parameter calibration process, more emphasis was placed on fitting the predictive and measured water temperatures at the Beijumahe Controlled Gate compared to the other stations. It is recommended to implement segmented prediction and fine processing to improve the accuracy of water temperature prediction for the entire canal system.
Table 3

RMSE of five consecutive 7-day water temperature predictions from 6 to 16 January

Hutuohe Controlled GateGangtou Controlled GateBeiyishui Controlled GateBeijumahe Controlled GateAverage value
From 6 to 12 Jan 0.36 0.21 0.19 0.13 0.22 
From 7 to 13 Jan 0.27 0.16 0.18 0.14 0.19 
From 8 to 14 Jan 0.27 0.21 0.20 0.13 0.20 
From 9 to 15 Jan 0.12 0.25 0.23 0.35 0.24 
From 10 to 16 Jan 0.21 0.19 0.28 0.21 0.22 
Average value 0.25 0.20 0.22 0.19 
Hutuohe Controlled GateGangtou Controlled GateBeiyishui Controlled GateBeijumahe Controlled GateAverage value
From 6 to 12 Jan 0.36 0.21 0.19 0.13 0.22 
From 7 to 13 Jan 0.27 0.16 0.18 0.14 0.19 
From 8 to 14 Jan 0.27 0.21 0.20 0.13 0.20 
From 9 to 15 Jan 0.12 0.25 0.23 0.35 0.24 
From 10 to 16 Jan 0.21 0.19 0.28 0.21 0.22 
Average value 0.25 0.20 0.22 0.19 
Figure 8

Comparison of five consecutive 7-day water temperature prediction errors.

Figure 8

Comparison of five consecutive 7-day water temperature prediction errors.

Close modal

15- and 21-day water temperature prediction effect

The 15- and 21-day water temperatures were used to represent the medium- to long-term water temperature prediction, and the model was used for three 15-day water temperature predictions and one 21-day water temperature prediction from 11 January to 24 February, as shown in Figure 9. Then, the error range and RMSE of water temperature predictions were calculated, as shown in Table 4. In this 21-day water temperature prediction from 11 to 31 January, water temperature prediction errors at the four stations range from −0.35 to 0.67 °C, and the RMSE range from 0.20 to 0.38, with an average value of 0.32. In the three 15-day water temperature predictions from 25 January to 9 February, from 30 January to 13 February, and from 10 February to 24 February, the range of water temperature prediction errors is from −0.59 to 0.36 °C in the first 7 days, and the range is larger in the later 8 days, ranging from −2.42 to 0.22 °C, which is even larger than the range of 21-day water temperature prediction errors. Moreover, Figure 9 shows that after February 15, the predictive water temperatures are gradually lower than the measured water temperatures, and the errors are increasing, error at the Gangtou Controlled Gate on 23 February reaching −1.95 °C, error at the Beiyishui Controlled Gate on 24 February reaching −2.18 °C, and error at the Beijumahe Controlled Gate on 23 February reaching −2.42 °C. As can be seen in Table 4, the RMSE of the last two 15-day water temperature predictions is significantly larger than the first and even larger than the 21-day water temperature prediction. The above phenomenon is caused by the fact that the water temperature prediction accuracy of this model is strongly influenced by the input air temperature forecast data. The project runs along the mountains from south to north, with complex air temperature changes along the way, and the accuracy of long-term air temperature forecast is poor, leading to larger water temperature prediction errors in the later stage. We compare these four air temperature forecasts with the measured air temperature on the day, as shown in Figure 10, and calculate the error range and RMSE of the four air temperature forecasts at the four stations, as shown in Table 5. The error range of the air temperature forecast at the four stations in the 15-day water temperature prediction from 10 to 24 February is from −6.5 to 7 °C, with an average RMSE of 3.68, which is higher than the previous three air temperature forecasts. In addition, the air temperature forecast values are lower than the actual air temperature values after 17 February, resulting in the water temperature predictive values being lower than the measured values in the later stage of this prediction.
Table 4

RMSE of 15- and 21-day water temperature predictions at four observation stations

RMSE of water temperature predictions
Average valueRange of prediction errors (°C)
Hutuohe Controlled GateGangtou Controlled GateBeiyishui Controlled GateBeijumahe Controlled Gate
From 11 to 31 Jan (21-day) 0.37 0.20 0.38 0.31 0.32 −0.35 to 0.67 
From 25 Jan to 8 Feb (15-day) 0.33 0.41 0.27 0.28 0.32 −0.68 to 0.23 
From 30 Jan to 13 Feb (15-day) 0.86 0.90 0.76 0.81 0.83 −1.92 to 0.36 
From 10 to 24 Feb (15-day) 0.30 0.94 0.99 1.20 0.86 −2.42 to 0.33 
RMSE of water temperature predictions
Average valueRange of prediction errors (°C)
Hutuohe Controlled GateGangtou Controlled GateBeiyishui Controlled GateBeijumahe Controlled Gate
From 11 to 31 Jan (21-day) 0.37 0.20 0.38 0.31 0.32 −0.35 to 0.67 
From 25 Jan to 8 Feb (15-day) 0.33 0.41 0.27 0.28 0.32 −0.68 to 0.23 
From 30 Jan to 13 Feb (15-day) 0.86 0.90 0.76 0.81 0.83 −1.92 to 0.36 
From 10 to 24 Feb (15-day) 0.30 0.94 0.99 1.20 0.86 −2.42 to 0.33 
Table 5

RMSE of 15- and 21-day air temperature forecasts at four observation stations

RMSE of air temperature forecasts
Average valueRange of forecast errors (°C)
Hutuohe Controlled GateGangtou Controlled GateBeiyishui Controlled GateBeijumahe Controlled Gate
From 11 to 31 Jan (21-day) 2.70 3.30 2.05 2.61 2.67 −3 to 6 
From 25 Jan to 8 Feb (15-day) 1.93 2.59 0.91 1.79 1.81 −4 to 6 
From 30 Jan to 13 Feb (15-day) 2.09 1.94 2.37 2.22 2.16 −6.5 to 3.5 
From 10 to 24 Feb (15-day) 3.32 4.20 3.92 3.29 3.68 −6.5 to 7 
RMSE of air temperature forecasts
Average valueRange of forecast errors (°C)
Hutuohe Controlled GateGangtou Controlled GateBeiyishui Controlled GateBeijumahe Controlled Gate
From 11 to 31 Jan (21-day) 2.70 3.30 2.05 2.61 2.67 −3 to 6 
From 25 Jan to 8 Feb (15-day) 1.93 2.59 0.91 1.79 1.81 −4 to 6 
From 30 Jan to 13 Feb (15-day) 2.09 1.94 2.37 2.22 2.16 −6.5 to 3.5 
From 10 to 24 Feb (15-day) 3.32 4.20 3.92 3.29 3.68 −6.5 to 7 
Figure 9

Comparison of 15- and 21-day water temperature predictions.

Figure 9

Comparison of 15- and 21-day water temperature predictions.

Close modal
Figure 10

Comparison of 14- and 21-day air temperature forecasts.

Figure 10

Comparison of 14- and 21-day air temperature forecasts.

Close modal

From the prediction results, the overall water temperature of the canal system in the winter of 2021–2022 is higher than 0 °C, and no icing occurred, which is consistent with the actual situation. Compared with models that use intelligent algorithms, such as adaptive fuzzy inference systems and BP neural networks, this model has physical mechanisms (Wang et al. 2012; Song et al. 2020; Chaplot 2021). However, the numerical solution of the model has accumulated errors in long-distance and long-time simulations. Moreover, the input meteorological conditions are the daily average air temperature data of meteorological stations in prefecture-level cities, and the scarcity of stations leads to poor data representation, affecting the model prediction accuracy. Therefore, the accuracy of the model can be improved by optimizing the model parameters, improving the temperature representativeness of the meteorological stations along the project, shortening the simulation time and range, and improving the monitoring quality of measured data.

This study uses the numerical simulation method to establish a water temperature prediction model, which can predict the future water temperature results by inputting air temperature data and hydraulic data of the project. Then, the icing conditions in the project for a certain period of time in the future can be further predicted. The main conclusions are as follows:

  • (1)

    The model predicts the long-distance water temperature for 1 and 7 days with small errors. When the prediction period is the 1-day, the prediction errors of 10 consecutive water temperature predictions from 6 to 15 January at four observation stations can be controlled at ±0.3 °C, with the RMSE ranging from 0.07 to 0.25. When the prediction period is the 7-day, the prediction errors of five consecutive water temperature predictions from 6 to 16 January at four stations can be controlled at ±0.6 °C, with the RMSE ranging from 0.12 to 0.36. For the Beijumahe Controlled Gate at the end of the project, the error ranges are from −0.22 to 0.22 °C and from −0.5 to 0.3 °C, with the RMSE of 0.11 and 0.19, respectively.

  • (2)

    The accuracy of 15-day water temperature prediction is greatly affected by the accuracy of the air temperature forecast, and the range of prediction errors is from −2.42 to 0.36 °C. The range of prediction errors for the first 7 days is from −0.59 to 0.36 °C, and the range for the last 8 days is from −2.42 to 0.22 °C. This is because a decrease in the accuracy of air temperature forecasts can lead to a decrease in the accuracy of water temperature predictions. The 21-day water temperature prediction was conducted only once, with the range of prediction errors from −0.35 to 0.67 °C and the range of RMSE from 0.20 to 0.38. It is necessary to organize more water temperature predictions for similar periods in the subsequent studies to test the model's medium- and long-term water temperature prediction accuracy.

  • (3)

    This study establishes a real-time water temperature prediction system for water diversion projects, which can use the water temperature prediction model to predict future water temperature changes and then predict the freezing range and freezing time of the project so as to dynamically adjust the water flow by time and space and reduce the waste of water transfer benefits caused by the use of a small flow in the whole project at a fixed time, realizing safe water transfer, efficient water transfer, and intelligent water transfer. However, there is no actual freeze-up that occurred in the verification years, so it is not possible to conduct actual tests on prediction effects of the water temperature under drift ice and freezing conditions, freezing time, and freezing range, and the model parameters also need to be continuously optimized in later applications.

This work was supported by the National Key Research & Development Plan of China (No. 2022YFC3202500), the Open Research Fund of Key Laboratory of River Basin Digital Twinning of Ministry of Water Resources (No. Z0202042022), the National Science Foundation of China (No. 51779196), and the Graduate Innovation and Entrepreneurship Foundation of Wuhan University of Science and Technology (No. JCX2022023).

All relevant data are included in the paper or its Supplementary Information.

The authors declare there is no conflict.

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