Almost every year, Vietnam suffers floods resulting in the loss of many lives and considerable costs for damaged and lost properties. This study proposes a forecasting system that couples the dynamical downscaling technique with hydrologic models to forecast real-time flood events with a lead time ranging from one to three days. This approach is demonstrated by applying a regional numerical weather prediction and physically based hydrologic model to the Thanh My and Nong Son watersheds. System inputs are provided by two global NWPs, the global forecasting system (GFS) and the global spectral model (GSM). A WEHY-WRF was selected as the hydrologic-atmospheric component for the proposed system. WEHY-WRF was successfully implemented and validated before testing the real-time forecasting system over the Nong Son-Thanh My watersheds. Overall, the comparison between the model simulations and corresponding observations shows the rainfall and flood forecast by WEHY-WRF-GFS match quite well with observation data and perform better than WEHY-WRF-GSM. However, all forecasting results are generally encouraging considering the correlation coefficients for most events are acceptable. The forecast methodology has demonstrated it as a comprehensive reliable technology that may be universally applied for flood prediction through the coupling of dynamical downscaling technique and hydrologic models.

  • This study proposes a forecasting system that couples the dynamical downscaling technique with hydrologic models to forecast real-time flood events with a lead time ranging from one to three days.

  • The forecast methodology has demonstrated it is a comprehensive reliable technology that may be universally applied for flood prediction through the coupling of dynamical downscaling technique and hydrologic models.

Floods are among the most frequent hydro-meteorological hazards, particularly in Vietnam which is affected by monsoon and tropical climate regimes. Almost every year people in Vietnam suffer floods; many lives were lost each time, and the costs for the damaged and lost properties were considerable (Tran et al. 2009; Navrud et al. 2012; Chau et al. 2015; Chinh et al. 2016; Vu & Ranzi 2017). Hillslope flows initiated by severe precipitation events caused recent floods in Vietnam (Ngo et al. 2020; Satofuka 2020; Trinh et al. 2020). The precipitation preceding such disasters can lead to flood only a few hours following rainfall observation by satellites, radars, or ground stations. This is especially true in regions with steep mountainous terrain that typically have hydropower plants and dams (Soula et al. 1998; Fenn et al. 2005; Schad et al. 2012). Fenn et al. (2005) found evidence of a flood event rising to a peak in 1.5 h, with out-of-bank flows lasting around 5 h in Boscastle in the UK. According to Soula et al. (1998), floods can reach maximum activity in only 3.5 h following the first observation of rain cells by a ground station and S-Band radar. In Vietnam, Schad et al. (2012) reported that the water level of the Chieng Khoi reservoir rose at the rapid rate of 2.5 cm h−1 and exceeded the critical level of 11.9 m, initiating overflow of the spillover after several hours.

Traditional flood detection and forecasting are commonly based on the information of rainfall and other variables (e.g. river discharges, water levels, flood stages) either measured at certain locations of the watershed and river reaches or simulated by hydrological-hydraulic models (e.g. de Roo et al. 2003; Thielen et al. 2009). These methods provide forecast lead times that vary according to the size of the basin and are relatively short for such small, steep catchments because the lead times are basically determined based on the lag time between rainfall and runoff concentration (Werner et al. 2005). They allow a short period of time for people in downstream areas to take precautionary actions and for local decision-makers to prepare for potential evacuation or other measures. In light of these observations, flood forecasting and early warning systems are needed to provide information on the starting time, duration, and magnitude of possible floods with longer lead time in the future.

An accurate and reliable forecast and warning system could enhance and improve the effectiveness of emergency responses (Nam et al. 2014; Chen et al. 2015; Hussain et al. 2021). Nevertheless, the rapid response of flood following the observation of rainfall limits the amount of lead time available for the implementation of emergency management measures such as the evacuation of potential flooding areas. The improvement in lead time for the runoff-river level forecasts is dependent on the ability to gain information ahead of the runoff event's occurrence, which in turn, can improve the amount of lead time that is available for emergency management measures. The knowledge of future rainfall and other climatic conditions at different lead times, ranging from the next few hours to the coming 2–3 days, is fundamental to providing the necessary lead times for flood forecasting. Appropriate lead times cannot be covered by observations of rainfall only after it has fallen to the ground. When very short forecast horizons on the order of 3 h or less are beneficial, extrapolative, and trend-based meteorological techniques are used. The use of such techniques is known as ‘nowcasting’, resulting in short-range quantitative precipitation forecasting (Barr et al. 2020; Shehu & Haberlandt 2021). Beyond this 3-h horizon, numerical weather prediction (NWP) models have to be used for quantitative precipitation forecasting. Currently, atmospheric models can provide forecast results with a lead time of more than 10 days. Despite this, a 1–3-day forecast is recommended due to the larger uncertainty associated with longer lead time forecasting (Adamowski 2008). NWP models are widely researched and developed in many places including the United States, Japan, and Europe. Along with the rapid development of science and technology in recent years, especially in the field of information technology and computer science, the level of detail and the creation of global NWP models has been increasing. Among the many available models, the GFS (global forecasting system) of America and the GSM (global spectral model) of Japan stand out. GFS is the global spectrum model of the US National Centers for Environmental Predictions (NCEP). GFS began its operational use at the National Meteorological Center, the predecessor of NCEP until 1988. The model is regularly improved and upgraded. To date, the model has had two configurations including one with a horizontal resolution of 35 km and 64 vertical layers (for forecasts of 7.5 days ∼180 h), and one with a horizontal resolution of 70 km and 64 vertical layers for forecasts of about 16 days ∼ 360 h (Han et al. 2017). The GSM, developed by the Japan Meteorological Agency (JMA), employs primitive equations to express the resolvable motions and states of the atmosphere. The model originally had a horizontal resolution of T63 and 16 vertical layers up to 10 hPa with a sigma-coordinate (Mizuta et al. 2006; Yamaguchi et al. 2012). Multiple upgrades and developments have led to improvements such as a spectral resolution of TL959, a highest altitude of 0.01 hPa, and assimilated 4D-Var with 100 vertical layers together with common and vertical initialization processes. Currently, GSM provides 84-h forecasting time for operations at 00, 06, 12, and 18. GSM is currently one of the highest-resolution global models (about 20 km). However, free versions are only available at ∼ 60 km resolution, which is equivalent to the resolution of GFS (JMA 2013). These two NWP datasets can be downloaded directly from their associated organizations.

In this study, the dynamical downscaling technique is coupled with a hydrologic model for the detection and forecast of real-time flood events with a lead time ranging from 1 to 3 days. The objectives of this study are: (1) proposing a new approach to forecast real-time flood events and longer lead time; (2) testing the flood forecasting system over Thanh My and Nong Son watersheds in central Vietnam. This approach is demonstrated by applying regional NWP and physically based hydrologic models to the Thanh My and Nong Son watersheds in central Vietnam with system inputs provided from different global NWPs (GFS and GSM). The present study seeks to overcome the research challenge of flood detection and forecasting and help improve the flood warning and forecasting practices in Vietnam.

River tributaries in central Vietnam originate from elevated mountain ranges, lying along the border between Vietnam and Laos. They flow through narrow floodplains and finally empty into the East Sea of Vietnam. These rivers are very short in length and have tributaries with steep bed slopes. Rapid changes in land use for agricultural expansion and economic development have enhanced the acceleration of catchment responses. About 72% of the study region is mountainous or hilly and mainly covered by forested areas (Chau et al. 2015). The region has often experienced large rainfall and flooding during the wet seasons, from September to December, accounting for 85% of the average annual water availability. The dry season, from January to August, accounts for 15% of average annual water availability. River flows measured in floodplains in the region show that six out of the seven major floods in the last 50 years occurred in the period from 1995 to 2010 (Nam et al. 2015). Proposing appropriate technologies for flood prediction with greater forecast horizons is indeed essential to reduce the pressure on the existing flood defense system and assist in better preparation for flood damage reductions.

The selected central Vietnam study watersheds, Thanh My and Nong Son, belong to the Vu Gia and Thu Bon Rivers respectively (as seen in Figure 1). These two watersheds cover a drainage area of 5,220 km2, with Thanh My accounting for 2,020 km2 and Nong Son accounting for 3,200 km2.
Figure 1

Plan view of the Thanh My and Nong Son watersheds in Vietnam.

Figure 1

Plan view of the Thanh My and Nong Son watersheds in Vietnam.

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This study aims to develop a flood forecast system by coupling physically based atmospheric and hydrologic models. The required atmospheric data used to set up the initial and boundary conditions in mesoscale simulations over Thanh My and Nong Son watersheds are taken from the two global NWP datasets, the GFS and GSM. A schematic of the proposed flood forecast system is illustrated in Figure 2.
Figure 2

Schematic of the flood forecast system.

Figure 2

Schematic of the flood forecast system.

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There are four main components forming the flood forecast system. The first component is retrieving and decoding data from global NWPs; the second is the dynamical downscaling of global NWPs outputs by means of a regional-scale model; the third is merging the atmospheric output into the hydrological model; the fourth is the implementation of the hydrological forecast models; and the last is flood warning platform that continuously provides information of atmospheric and flood conditions with a lead time of 1–3 days for selected locations. It is noted that this system automatically updates forecasting every 12 h based on retrieval of GFS and GSM atmospheric data.

WRF model setup

Due to its successful application in Vietnam, the Weather Research and Forecasting (WRF) model is recommended for application in this study despite the availability of similar mesoscale NWP models (Raghavan et al. 2012; Ho et al. 2019; Trinh et al. 2020, 2021). Since its first release in 2000, the WRF model has performed a wide range of meteorological applications across scales from tens of meters to thousands of kilometers (Skamarock et al. 2005). With respect to real-time operational weather forecasting, the WRF model offers a flexible and computationally efficient platform, while offering advances in physics, numerical methods, and data assimilation, as contributed by many research community developers. As a result, the WRF model is currently in operational use at NCEP and other meteorological modeling centers around the world.

The mesoscale WRF model setup for Thanh My and Nong Son watersheds employed the outputs from the GFS and GSM models. These outputs were used as the initial and boundary conditions of the WRF model. In this study, the WRF model was configured with three nested domains, as shown in Figure 1. The outer domain (D1) covers the whole of Vietnam, Cambodia, Laos, Thailand and parts of China, and the Philippines, having a spatial resolution of 54 km (39 × 49 horizontal grid points), similar to the spatial resolution of the boundary datasets. The domain (D2) in between the outer and inner domains covers central Vietnam with a resolution of 18 km (45 × 60 horizontal grid points). The innermost and smallest domain (D3) covers the study area with a spatial resolution of 6 km (60 × 51 horizontal grid points).

A key step in setting up the mesoscale WRF model was the selection of parameterization schemes in the model configuration. An optimal physical parameterization scheme is crucial for extreme rainfall prediction. There are available parameterization schemes which have been implemented for various weather patterns in Vietnam (Raghavan et al. 2012; Minh et al. 2018; Ho et al. 2019; Trinh et al. 2021). In this study, the model configuration was examined with 17 parameterization schemes as suggested in the literature involving nine different microphysics schemes, six cumulus parameterizations, five planetary boundary layers schemes, and four radiation physics parameterizations, as presented in Table 1. In addition, the WRF model provides forecast atmospheric data hourly with 18 meteorological levels.

Table 1

Seventeen combinations of physics parameterizations for mesoscale WRF model configuration

Parameterization schemesMicrophysicsCumulus parameterizationPlanetary boundary layerRadiation physics
WSM3 Grell-3 BouLac New Goddard 
WSM3 New SAS BouLac New Goddard 
WSM3 Tiedtke BouLac New Goddard 
WSM3 Betts–Miller–Janjic BouLac New Goddard 
WSM3 Grell–Freitas BouLac New Goddard 
WSM3 Old Simplied ArakawaSchuber BouLac New Goddard 
Eta (Ferrier) Tiedtke BouLac New Goddard 
SBU-YLin Tiedtke BouLac New Goddard 
WSM3 Tiedtke BouLac New Goddard 
10 WSM6 Tiedtke MYNN2 New Goddard 
11 Goddard Tiedtke YSU New Goddard 
12 Thompson Tiedtke UW New Goddard 
13 Milbrandt 2-mom Tiedtke YSU New Goddard 
14 Morrison 2-mom Tiedtke BouLac Goddard 
15 CAM 5.1 Tiedtke BouLac Dudhia 
16 CAM 5.1 Tiedtke BouLac New Goddard 
17 Goddard Tiedtke BouLac Dudhia 
Parameterization schemesMicrophysicsCumulus parameterizationPlanetary boundary layerRadiation physics
WSM3 Grell-3 BouLac New Goddard 
WSM3 New SAS BouLac New Goddard 
WSM3 Tiedtke BouLac New Goddard 
WSM3 Betts–Miller–Janjic BouLac New Goddard 
WSM3 Grell–Freitas BouLac New Goddard 
WSM3 Old Simplied ArakawaSchuber BouLac New Goddard 
Eta (Ferrier) Tiedtke BouLac New Goddard 
SBU-YLin Tiedtke BouLac New Goddard 
WSM3 Tiedtke BouLac New Goddard 
10 WSM6 Tiedtke MYNN2 New Goddard 
11 Goddard Tiedtke YSU New Goddard 
12 Thompson Tiedtke UW New Goddard 
13 Milbrandt 2-mom Tiedtke YSU New Goddard 
14 Morrison 2-mom Tiedtke BouLac Goddard 
15 CAM 5.1 Tiedtke BouLac Dudhia 
16 CAM 5.1 Tiedtke BouLac New Goddard 
17 Goddard Tiedtke BouLac Dudhia 

Calibration and validation of WRF model

Dynamical downscaling is applied to generate a high-resolution quantitative rainfall forecast over the targeted watersheds. Thus, the mesoscale WRF model calibration and validation were performed against observed rainfall data. The observation data were derived from two different sources, the Vietnam Gridded Precipitation (VnGP) and observations from five rain gauges. VnGP was developed based on daily rainfall observation across Vietnam from 1980 to 2010 with a resolution of 0.1° (Nguyen-Xuan et al. 2016). Rain gauge observations in the area have been available since 1979. In the present study, WRF-simulated daily basin average precipitation was compared to observation data.

Model calibration was initiated through the selection of an optimal parameterization scheme from the 17 considered. Model performance was assessed and evaluated for the downscaled variables of the D3 domain using the Nash–Sutcliffe efficiency (NSE). Two extreme events were selected for model calibration and validation. Calibration was performed with an event from 1 October to 31 October 2008. An event from 24 October to 10 November 2009 was employed for model validation. These two events were selected due to their impacts to the study region as mentioned in Nam et al. (2011, 2014). Table 2 shows model performance statistics for the downscaled rainfall at domain D3 from two global datasets examined with 17 parameterization schemes and 1-, 2-, and 3-day forecast lead times. The overall score exhibits that GSM-based downscaling results outperform those of the GFS is global forecasting system (GFS), especially the forecasts with 1-day lead time. The statistics also indicate that using the same parameterization scheme results in significant variance for the selected global NWP datasets. It is found that the optimal parameterization scheme for the GFS dataset consists of WSM3 (Hong et al. 2004) as the microphysics processes, Grell–Freitas (Fowler et al. 2016) as cumulus parameterization, BouLac (Bougeault & Lacarrere 1989) as the planetary boundary layer, and New Goddard (Chou & Suarez 1999) as the radiation physics. Meanwhile, the parameterization scheme selected for the GSM dataset consists of Goddard (Tao & Simpson 1993) as the microphysics processes, Tiedtke (Tiedtke 1989) as the cumulus parameterization, BouLac (Bougeault & Lacarrere 1989) as the planetary boundary layer, and Dudhia (Dudhia 1989) as the radiation physics. These model configurations are summarized in Table 3.

Table 2

NSE for area-averaged daily precipitation between WRF simulations for domain D3 and ground observations using two global NWP datasets during 1 Oct 2008 to 30 Nov 2008

Parameterization schemesDownscaling from GFS
Downscaling from GSM
Forecast lead timeForecast lead time
 1-day 2-day 3-day 1-day 2-day 3-day 
0.44 0.10 0.21 0.36 0.39 0.41 
0.05 0.35 −0.09 0.25 −0.10 0.07 
0.47 0.42 0.20 0.66 0.27 0.15 
−0.03 0.06 −0.07 0.49 0.01 −0.05 
0.62 0.41 0.40 0.39 0.12 0.04 
0.41 0.24 0.23 0.42 0.05 0.07 
0.19 0.25 0.27 0.63 0.21 0.13 
0.24 0.12 0.15 0.69 0.27 0.14 
0.49 0.06 0.06 0.63 0.21 0.13 
10 −0.08 −0.52 −0.95 0.66 0.25 0.15 
11 0.31 0.20 0.01 0.71 0.29 0.10 
12 0.01 0.14 0.13 0.62 0.21 0.12 
13 0.15 0.21 0.09 0.66 0.27 0.14 
14 0.03 0.04 0.11 0.67 0.27 0.16 
15 0.31 0.14 0.21 0.67 0.35 0.28 
16 0.40 0.21 0.20 0.66 0.38 0.29 
17 0.42 0.12 0.13 0.74 0.48 0.40 
Mean 0.26 0.15 0.08 0.58 0.23 0.16 
Parameterization schemesDownscaling from GFS
Downscaling from GSM
Forecast lead timeForecast lead time
 1-day 2-day 3-day 1-day 2-day 3-day 
0.44 0.10 0.21 0.36 0.39 0.41 
0.05 0.35 −0.09 0.25 −0.10 0.07 
0.47 0.42 0.20 0.66 0.27 0.15 
−0.03 0.06 −0.07 0.49 0.01 −0.05 
0.62 0.41 0.40 0.39 0.12 0.04 
0.41 0.24 0.23 0.42 0.05 0.07 
0.19 0.25 0.27 0.63 0.21 0.13 
0.24 0.12 0.15 0.69 0.27 0.14 
0.49 0.06 0.06 0.63 0.21 0.13 
10 −0.08 −0.52 −0.95 0.66 0.25 0.15 
11 0.31 0.20 0.01 0.71 0.29 0.10 
12 0.01 0.14 0.13 0.62 0.21 0.12 
13 0.15 0.21 0.09 0.66 0.27 0.14 
14 0.03 0.04 0.11 0.67 0.27 0.16 
15 0.31 0.14 0.21 0.67 0.35 0.28 
16 0.40 0.21 0.20 0.66 0.38 0.29 
17 0.42 0.12 0.13 0.74 0.48 0.40 
Mean 0.26 0.15 0.08 0.58 0.23 0.16 
Table 3

Selected mesoscale WRF model configurations for different global NWP datasets

Parameterization schemeGFS datasetGSM dataset
Microphysics processes WSM3 Goddard (Tao & Simpson 1993
Cumulus parameterization Grell-Freitas (Fowler et al. 2016Tiedtke (Dudhia 1989; Tiedtke 1989
Planetary boundary layer BouLac (Bougeault & Lacarrere 1989BouLac (Bougeault & Lacarrere 1989
Radiation physics New Goddard (Chou & Suarez 1999Dudhia (Dudhia 1989
Parameterization schemeGFS datasetGSM dataset
Microphysics processes WSM3 Goddard (Tao & Simpson 1993
Cumulus parameterization Grell-Freitas (Fowler et al. 2016Tiedtke (Dudhia 1989; Tiedtke 1989
Planetary boundary layer BouLac (Bougeault & Lacarrere 1989BouLac (Bougeault & Lacarrere 1989
Radiation physics New Goddard (Chou & Suarez 1999Dudhia (Dudhia 1989

Visual comparison between the downscaled rainfall and corresponding observations shows good agreement for the 1-day lead time forecast and reasonable agreement for forecasts in the range of 2–3 days lead time. Basin-averaged comparisons for the two datasets are presented in Figure 3.
Figure 3

Time series of basin average daily observed (Obs) and downscaled rainfall at domain D3 with 1-, 2-, and 3-day lead time during 1–31 October 2008, downscaling from GSM dataset (left) and GFS dataset (right) over Thanh My and Nong Son watersheds.

Figure 3

Time series of basin average daily observed (Obs) and downscaled rainfall at domain D3 with 1-, 2-, and 3-day lead time during 1–31 October 2008, downscaling from GSM dataset (left) and GFS dataset (right) over Thanh My and Nong Son watersheds.

Close modal
As a result, the selected configurations for GFS and GSM were tested using validation data. Figure 4 shows the timeseries comparisons of ground observations and the downscaled basin average rainfall with 1-, 2-, and 3-day lead time derived from the two different global NWP models over the Thanh My and Nong Son watersheds during the event from 24 October to 10 November 2009. Generally, the validation showed good agreement between the simulation results and observations. Statistical criteria supporting the agreement of the simulation results to observation data are shown in Table 4a and 4b. Statistical criteria, such as the correlation coefficient and NSE, show that the simulation performance for the daily precipitation is in the ‘satisfactory’ range (0.86 ≤ R ≤ 0.98 and 0.67 ≤ NSE ≤ 0.88).
Table 4a

Statistical test values of WRF-simulated results based on GFS and VnGP for basin average precipitation 1-, 2-, 3-day lead time from 24 Oct to 10 Nov 2009 over Thanh My and Nong Son watersheds

Event from 24 Oct to 10 Nov 2009-GFSObs1-day2-day3-day
Mean (mm) 13.95 19.23 19.88 18.36 
Standard deviation (mm) 24.16 30.30 29.25 24.66 
Correlation coefficient  0.98 0.94 0.86 
Nash–Sutcliffe efficiency  0.83 0.74 0.67 
Event from 24 Oct to 10 Nov 2009-GFSObs1-day2-day3-day
Mean (mm) 13.95 19.23 19.88 18.36 
Standard deviation (mm) 24.16 30.30 29.25 24.66 
Correlation coefficient  0.98 0.94 0.86 
Nash–Sutcliffe efficiency  0.83 0.74 0.67 
Figure 4

Mesoscale WRF model validation for Thanh My and Nong Son watersheds for the event during 24 October to 10 November 2009, downscaling from GSM dataset (left) and GFS dataset (right) with forecast with a lead time of 1- to 3-day.

Figure 4

Mesoscale WRF model validation for Thanh My and Nong Son watersheds for the event during 24 October to 10 November 2009, downscaling from GSM dataset (left) and GFS dataset (right) with forecast with a lead time of 1- to 3-day.

Close modal

It is noted that this result is a real-time precipitation forecast with a 1- to 3-day lead time, and the precipitation forecast updated the initial and boundary conditions every 12 h. The boundary condition was continuously updated using retrieved GFS and GSM forecast data, while the initial condition was updated by the previous time step result. Therefore, the calibration and validation are encouraging and the selected configurations are reliable for further forecast applications including atmospheric and flood forecasts.

Physically based hydrological models

Watershed environmental hydrology model

The watershed environmental hydrology (WEHY) model was developed at the Hydrologic Research Laboratory, UC Davis in the early 2000s. WEHY is a physically based model formulated using conservation of mass, momentum, and/or energy equations of water flow in various flow domains (Chen et al. 2004a; Kavvas et al. 2004, 2006, 2013). WEHY can simulate runoff generation through five computational components including, unsaturated flow, subsurface storm flow, overland flow, groundwater flow, and channel flow components, which are computed in parallel. These computations yield the flow discharge to the stream network and the underlying unconfined groundwater aquifer of the target watersheds, which are in dynamic interaction with both the surface and subsurface hillslope processes. The WEHY hydrologic module can be used either for event-based runoff prediction or for long-term continuous-time runoff simulation. Thus, the WEHY model shows good performance over different regions including California, Thailand, Turkey, Malaysia, and Vietnam (Kure et al. 2013; Wuthiwongyothin et al. 2015; Trinh et al. 2016, 2022a; Amin et al. 2017; Gorguner et al. 2019; Ho et al. 2019). Application of the WEHY model to a watershed includes four major steps: (1) delineation of the river network and model computational units (MCUs); (2) preprocessing of atmospheric data as input for the model; (3) estimation of geomorphology and land surface parameters for the delineated watershed; and (4) model calibration and validation using independent datasets (simulation versus observation data). The first step in the model configuration is the delineation of the stream network as shown in Figure 5. There are 42 MCUs and 21 reaches for the Thanh My catchment and 66 MCUs and 33 stream reaches for the Nong Son catchment based on the ASTER Global Digital Elevation Model (DEM) with a spatial resolution of 30 m (Tachikawa et al. 2011). The second data processing step involves merging the atmospheric output into the hydrological model. The mesoscale WRF model's eight different output variables (precipitation, air temperature, wind speed, shortwave radiation, long-wave radiation, pressure, mixing ratio, and geopotential height) were converted into a standard format for WEHY's applications. The eight different variables were calculated for each delineated MCU for the Thanh My and Nong Son catchments. This step is an automatic process due to the coupling between the regional climate model and WEHY. For a further review of this step, see Chen et al. (2004a, 2004b) and Trinh et al. (2020).
Figure 5

Delineated MCUs map and stream network at Thanh My and Nong Son watersheds.

Figure 5

Delineated MCUs map and stream network at Thanh My and Nong Son watersheds.

Close modal
Third, the estimation of geomorphology and land surface parameters involves the processing of land cover, soil, and elevation data. Soil parameters are significant components of the WEHY model. These data were obtained from global SoilGrids data (1 km) from the International Soil Reference and Information Centre (Hengl et al. 2014; Trinh et al. 2018). Land cover parameters are also important for the hydrologic model implementation and were collected from the global land cover characterization dataset (Loveland et al. 2000). Leaf area index (LAI) parameters are collected from satellite images under Modis (https://modis.gsfc.nasa.gov/data/dataprod/mod15.php). Both soil and land parameters were estimated for the MCUs (Kavvas et al. 2013) as shown in Figures 6 and 7.
Figure 6

Month averages of LAI data over Thanh My and Nong Son watersheds.

Figure 6

Month averages of LAI data over Thanh My and Nong Son watersheds.

Close modal
Figure 7

Computed soil hydraulic parameter maps for Thanh My and Nong Son watersheds.

Figure 7

Computed soil hydraulic parameter maps for Thanh My and Nong Son watersheds.

Close modal

Calibration for WEHY model based on forecasted rainfall data

Simulated WEHY flow data were compared with corresponding observations for calibration and validation. After the hydrologic model was validated for both Nong Son and Thanh My, the hydrologic data were reconstructed from 1950 through 2010 and were then evaluated by time series analysis as can be seen in Figures 8 and 9 as well as in Table 4c and 4d. Visual comparison between the model simulations and corresponding observations at Nong Son and Thanh My gauging stations (Figures 8 and 9) shows good agreement. The rising and receding segments of the simulated hydrographs, as well as the timing and magnitude of the simulated peak discharges, are very similar to the corresponding observations. Statistical criteria, such as the Nash–Sutcliffe efficiency coefficients, show that the simulation performance for the simulated flow is in the ‘satisfactory’ range (0.51 ≤ NSE ≤ 0.86) for the 1-day forecast at Nong Son station and for the 1-day forecast at Thanh My station (0.58 ≤ NSE ≤ 0.82) under both GSM and GFS data based on the daily flow comparisons. In general, the model-simulated flow matches the corresponding observed data well for the 1- and 2- day forecasts, Although not for the 3-day forecast at Thanh My station. Note that these calibration and validation results use forecasted precipitation data, thus the exhibited results are acceptable with correlation coefficients that range from 0.52 to 0.95. After the successful implementation and validation of the atmospheric-hydrologic component, reservoir operation rules are applied for Thanh My and Nong Son watersheds.
Figure 8

Calibration of WEHY simulations using forecast atmospheric data from WRF-GSM, WRF-GFS, and observation for forecast with a lead time of 1- to 3-day basin average precipitation during 1 October to 31 October 2008 at Nong Son and Thanh My gauging stations.

Figure 8

Calibration of WEHY simulations using forecast atmospheric data from WRF-GSM, WRF-GFS, and observation for forecast with a lead time of 1- to 3-day basin average precipitation during 1 October to 31 October 2008 at Nong Son and Thanh My gauging stations.

Close modal
Figure 9

Calibration of WEHY simulations using forecast atmospheric data from WRF-GSM, WRF-GFS, and observation with a lead time of 1- to 3-day during 31 October to 10 November 2009 at Nong Son and Thanh My gauging stations.

Figure 9

Calibration of WEHY simulations using forecast atmospheric data from WRF-GSM, WRF-GFS, and observation with a lead time of 1- to 3-day during 31 October to 10 November 2009 at Nong Son and Thanh My gauging stations.

Close modal
Application of reservoir operation rule for Thanh My and Nong Son watersheds
There are two main dams over Thanh My and Nong Son watersheds including Song Tranh 2 and Dak Mi 4 (Figure 10).
Figure 10

Locations of Dak Mi 4 dam, Dak Mi 4 hydropower plant, and Song Tranh 2 dam at NS-TM watersheds.

Figure 10

Locations of Dak Mi 4 dam, Dak Mi 4 hydropower plant, and Song Tranh 2 dam at NS-TM watersheds.

Close modal

The Song Tranh 2 and Dak Mi 4 dams were constructed in 2006 and 2007 and started operation in 2010 and 2012, respectively. Song Tranh 2's dam and power plant are located in the main stream of the Nong Son watershed, while Dak Mi 4's main dam is in the Thanh My watershed and its power plant is located in the Nong Son watershed. Dak Mi 4's dam is roughly 3 km from its power plant. Summary information about the two dams is provided in Table 5.

Table 4b

Statistical test values of WRF-simulated results based on GSM and VnGP for basin average precipitation 1-, 2-, and 3-day lead time from 24 Oct to 10 Nov 2009 over Thanh My and Nong Son

Event from 24 Oct to 10 Nov 2009-GSMObs1-day2-day3-day
Mean (mm) 13.95 15.77 14.14 14.67 
Standard deviation (mm) 24.16 29.14 21.68 19.56 
Correlation coefficient  0.97 0.935 0.88 
Nash–Sutcliffe efficiency  0.88 0.87 0.77 
Event from 24 Oct to 10 Nov 2009-GSMObs1-day2-day3-day
Mean (mm) 13.95 15.77 14.14 14.67 
Standard deviation (mm) 24.16 29.14 21.68 19.56 
Correlation coefficient  0.97 0.935 0.88 
Nash–Sutcliffe efficiency  0.88 0.87 0.77 

In this study, existing operating rules for the Song Tranh 2 and Dak Mi 4 reservoirs are applied. The dam operation subprogram requires customization for each of the main reservoirs in the selected watersheds (Song Tranh 2, and Dak Mi 4 Reservoirs). The operation rules were initially implemented following available documentation but had to be further refined by model simulations. Representation of the operation rules for these dams is crucial to accurately simulate flow conditions using the WEHY model.

The operation rules from 2011 to 2019 for the Song Tranh 2, and Dak Mi 4 reservoirs were obtained from the Vietnam Electricity Company. These operation rules were incorporated into the WEHY model in the dam operation subprogram. WEHY's dam operation subprogram is based on relationship functions among surface area (F), water elevation (Z), and storage (W) as shown in Figure 11, and the current operation rule, as shown in Figure 12. It is noted that the total outflow is the summation of power plant and spillway outflows. The dam operation within WEHY simulated the outflow based on the historical reservoirs water levels. In the following section, the forecasted flow data produced after applying the reservoir operation rules for Nong Son and Thanh My will be reported.
Figure 11

Relationship among surface area, water elevation, and storage at Dak Mi 4 and Song Tranh 2 reservoirs.

Figure 11

Relationship among surface area, water elevation, and storage at Dak Mi 4 and Song Tranh 2 reservoirs.

Close modal
Figure 12

The current reservoir operation including reservoir water level, outflow from power plant, from spillway, total outflow, and inflow for (a) Song Tranh 2; (b) Dak Mi 4 reservoirs.

Figure 12

The current reservoir operation including reservoir water level, outflow from power plant, from spillway, total outflow, and inflow for (a) Song Tranh 2; (b) Dak Mi 4 reservoirs.

Close modal

Following the successful implementation and validation of the atmospheric and hydrologic components of the proposed system, the real-time forecasting system is tested using several extreme events that were reported in Loi et al. (2019) and Nguyen et al. (2021). The selected area covers complex topography, climate, and land use activities. It is subject to heavy rainfall and frequent flooding, with an average of three to five flood events per year. Flood events often occur consecutively in a short time. The rise and fall of floods are quick in the upper and middle areas but slow in the downstream areas. According to Luu & von Meding (2018), historic floods recorded during the 19 years from 1997 to 2015 left 726 dead and resulted in economic damage of 614.6 million USD in the downstream areas. Four main flood events, occurring between 2012 and 2015, were selected to test the real-time forecasting system. They were selected based on the availability of historical flood records and atmospheric data, and the timing of the construction of the two main dams.

Precipitation forecast

Forecasts of rainfall data for events in 2012, 2013, 2014, and 2015 are produced using the atmospheric component of the model with input provided from both global forecast data GSM and GFS. The lead time for these events ranged from 1 to 96 h. The rainfall events in 2012, 2013, 2014, and 2015 started at 7 am on 5 October, 7 am on 14 October 14, 7 am on 14 November, and 7 am on 1 November, respectively. Figure 13 presents forecast and observation rainfall data with the line representing observation data, the bar charts are the forecast rainfall data based on GFS and GSM. The visual comparison reveals good agreement between the WRF-GFS model simulations and corresponding observations. The timing and magnitude of the simulated peak are close to those of historical rainfall events in 2012, 2013, and 2015. The rainfall forecast results based on WRF-GSM showed underestimation in the 2012, 2013, and 2015 events, but the timing of the simulated peak is well represented. Statistical analysis (NSE and R) is displayed in Table 6. The best result was obtained from WRF-GFS in the 2012 event which had an NSE of 0.52. Overall, the results of WRF-GFS are satisfactory as correlation coefficients are larger than 0.5. The rainfall forecast results based on WRF-GSM did not match as well with the historical record; however, these results are quite encouraging considering their acceptable correlation coefficients. These results could be improved by applying assimilation and bias correction methods.
Table 4c

Statistical test values of WEHY-simulated results based on WRF-GSM and WRF-GFS for 1-, 2-, and 3-day outlet flow from 1 Oct to 31 Oct 2008 at Nong Son and Thanh My watersheds

Event from 1 Oct to 31 Oct 2008-GSMNong Son
Thanh My
Obs1-day2-day3-dayObs1-day2-day3-day
Mean (m3/s) 1,193 1,250 1,121 1,015 368 371 322 249 
Standard deviation (m3/s) 1,287 1,215 978 802 330 414 325 183 
Correlation coefficient  0.91 0.88 0.75  0.82 0.65 0.53 
Nash–Sutcliffe efficiency  0.816 0.762 0.533  0.79 0.50 0.31 
Nong Son
Thanh My
Event from 1 Oct to 31 Oct 2008-GFSObs1-dayObs1-dayObs1-dayObs1-day
Mean (m3/s) 1,193 1,399 1,378 1,130 368 295 247 185 
Standard deviation (m3/s) 1,287 1,144 1,005 715 330 348 273 169 
Correlation coefficient  0.91 0.83 0.81  0.84 0.75 0.52 
Nash–Sutcliffe efficiency  0.86 0.72 0.65  0.82 0.58 0.2 
Event from 1 Oct to 31 Oct 2008-GSMNong Son
Thanh My
Obs1-day2-day3-dayObs1-day2-day3-day
Mean (m3/s) 1,193 1,250 1,121 1,015 368 371 322 249 
Standard deviation (m3/s) 1,287 1,215 978 802 330 414 325 183 
Correlation coefficient  0.91 0.88 0.75  0.82 0.65 0.53 
Nash–Sutcliffe efficiency  0.816 0.762 0.533  0.79 0.50 0.31 
Nong Son
Thanh My
Event from 1 Oct to 31 Oct 2008-GFSObs1-dayObs1-dayObs1-dayObs1-day
Mean (m3/s) 1,193 1,399 1,378 1,130 368 295 247 185 
Standard deviation (m3/s) 1,287 1,144 1,005 715 330 348 273 169 
Correlation coefficient  0.91 0.83 0.81  0.84 0.75 0.52 
Nash–Sutcliffe efficiency  0.86 0.72 0.65  0.82 0.58 0.2 
Figure 13

Time series of observed and forecasted hydrographs for the testing rainfall event in 2012 (a), 2013 (b), 2014 (c), and 2015 (d).

Figure 13

Time series of observed and forecasted hydrographs for the testing rainfall event in 2012 (a), 2013 (b), 2014 (c), and 2015 (d).

Close modal

Flood forecast

The forecasted atmospheric data from both models including WRF-GFS and WRF-GSM provided input for the hydrologic component to forecast flood over the NS-TM basin. In Figure 14, a visual comparison between the model simulations and corresponding observations show good agreement between the flow forecast based on WEHY-GFS and the observation data. Flow forecast results based on WRF-GSM did not match as well with historical records as the WRF-GFS; however, these results are quite encouraging based on their acceptable correlation coefficients. The correlation coefficient (R) and NSE values tabulated in Table 7 allow for the evaluation of the model's performance under various stations and datasets. Among the different forecast results, the best was obtained for WEHY-GFS in the 2012 event, which had an NSE value of 0.9. These statistical comparisons substantiate the impression given by the visual inspection of flow results.
Table 4d

Statistical test values of WEHY-simulated results based on WRF-GSM and WRF-GFS for 1-, 2-, and 3-day outlet flow from 31 Oct to 10 Nov 2009 at Thanh My and Nong Son watersheds

Event from 31 Oct to 10 Nov 2009-GSMNong Son
Thanh My
Obs1-day2-day3-dayObs1-day2-day3-day
Mean (m3/s) 1,608 1,208 1,152 1,188 709 535 572 622 
Standard deviation (m3/s) 1,090 1,144 1,221 1,138 505 553 603 638 
Correlation coefficient  0.89 0.89 0.93  0.89 0.97 0.95 
Nash–Sutcliffe efficiency  0.64 0.62 0.75  0.62 0.81 0.78 
Nong Son
Thanh My
Event from 31 Oct to 10 Nov 2009-GFSObs1-dayObs1-dayObs1-dayObs1-day
Mean (m3/s) 1,608 1,702 1,634 1,264 709 573 600 660 
Standard deviation (m3/s) 1,090 1,303 1,217 947 505 713 648 563 
Correlation coefficient  0.81 0.86 0.78  0.94 0.86 0.72 
Nash–Sutcliffe efficiency  0.51 0.67 0.52  0.58 0.52 0.35 
Event from 31 Oct to 10 Nov 2009-GSMNong Son
Thanh My
Obs1-day2-day3-dayObs1-day2-day3-day
Mean (m3/s) 1,608 1,208 1,152 1,188 709 535 572 622 
Standard deviation (m3/s) 1,090 1,144 1,221 1,138 505 553 603 638 
Correlation coefficient  0.89 0.89 0.93  0.89 0.97 0.95 
Nash–Sutcliffe efficiency  0.64 0.62 0.75  0.62 0.81 0.78 
Nong Son
Thanh My
Event from 31 Oct to 10 Nov 2009-GFSObs1-dayObs1-dayObs1-dayObs1-day
Mean (m3/s) 1,608 1,702 1,634 1,264 709 573 600 660 
Standard deviation (m3/s) 1,090 1,303 1,217 947 505 713 648 563 
Correlation coefficient  0.81 0.86 0.78  0.94 0.86 0.72 
Nash–Sutcliffe efficiency  0.51 0.67 0.52  0.58 0.52 0.35 
Table 5

Information on Song Tranh 2 and Dak Mi 4 dams

ReservoirWatershedConstruction beganOpening dateHeightCapacity (106 m3)
Song Tranh 2 Nong Son 2006 2010 180m 730 
Dak Mi 4 Thanh My 2007 2012 262.0 312.38 
ReservoirWatershedConstruction beganOpening dateHeightCapacity (106 m3)
Song Tranh 2 Nong Son 2006 2010 180m 730 
Dak Mi 4 Thanh My 2007 2012 262.0 312.38 
Table 6

Statistical test values of precipitation results based on WRF-GSM and WRF-GFS for the selected watershed

EventCoefficientGFSGSM
From 5 to 8 Oct 2012 NSE 0.52 0.35 
R 0.85 0.93 
From 14 to 17 Oct 2013 NSE 0.85 0.23 
R 0.998 0.89 
From 14 to 17 Nov 2014 NSE 0.29 −0.01 
R 0.65 0.79 
From 1 to 4 Nov 2015 NSE −0.22 −0.84 
R −0.14 −0.18 
EventCoefficientGFSGSM
From 5 to 8 Oct 2012 NSE 0.52 0.35 
R 0.85 0.93 
From 14 to 17 Oct 2013 NSE 0.85 0.23 
R 0.998 0.89 
From 14 to 17 Nov 2014 NSE 0.29 −0.01 
R 0.65 0.79 
From 1 to 4 Nov 2015 NSE −0.22 −0.84 
R −0.14 −0.18 
Table 7

Statistical test values of flow results based on WEHY-WRF-GSM and WEHY-WRF-GFS for the selected watershed

StationEventModelNSERΔW (%)Δpeak (%)
Thanh My 2012 GFS 0.83 0.96 9.24 −10.41 
GSM 0.25 0.95 42.15 28.62 
2013 GFS 0.50 0.80 13.13 2.25 
GSM 0.54 0.98 36.35 38.93 
2014 GFS 0.19 0.91 40.75 24.48 
GSM 0.35 0.65 6.46 −7.41 
2015 GFS 0.29 0.96 35.26 43.09 
GSM 0.63 095 25.31 29.14 
Nong Son 2012 GFS 0.90 0.95 4.73 11.01 
GSM 0.68 0.86 7.14 27.42 
2013 GFS 0.77 0.96 17.73 −7.17 
GSM 0.38 0.86 22.72 47.39 
2014 GFS 0.67 0.91 4.45 19.34 
GSM 0.39 0.98 −38.15 −8.32 
2015 GFS 0.48 0.74 7.86 12.18 
GSM 0.35 0.71 −3.11 22.82 
StationEventModelNSERΔW (%)Δpeak (%)
Thanh My 2012 GFS 0.83 0.96 9.24 −10.41 
GSM 0.25 0.95 42.15 28.62 
2013 GFS 0.50 0.80 13.13 2.25 
GSM 0.54 0.98 36.35 38.93 
2014 GFS 0.19 0.91 40.75 24.48 
GSM 0.35 0.65 6.46 −7.41 
2015 GFS 0.29 0.96 35.26 43.09 
GSM 0.63 095 25.31 29.14 
Nong Son 2012 GFS 0.90 0.95 4.73 11.01 
GSM 0.68 0.86 7.14 27.42 
2013 GFS 0.77 0.96 17.73 −7.17 
GSM 0.38 0.86 22.72 47.39 
2014 GFS 0.67 0.91 4.45 19.34 
GSM 0.39 0.98 −38.15 −8.32 
2015 GFS 0.48 0.74 7.86 12.18 
GSM 0.35 0.71 −3.11 22.82 
Figure 14

Statistical test values of WEHY-simulated results based on WRF-GSM and WRF-GFS at Nong Son and Thanh My watersheds.

Figure 14

Statistical test values of WEHY-simulated results based on WRF-GSM and WRF-GFS at Nong Son and Thanh My watersheds.

Close modal

It is noted that ΔW% and Δpeak% are volume and peak error, calculated as a percentage as given by the following equations.

(1)
(2)
where is the volume of the forecasted flood with a lead time of 72 h, is the volume of observation data, is the peak of the forecasted flood with a lead time of 72 h, and is the peak of observation data.
Figure 15 shows the volume and peak errors between WEHY-GSM and WEHY-GFS over Nong Son and Thanh My stations during the selected flood events in 2012, 2103, 2014, and 2015. As shown by the errors plotted in Figure 15, the errors of volume and peak of the WEHY-GSM were higher than those of the WEHY-GFS in some years and the opposite in other years. This comparison illustrates that both the GFS and GSM forecast information have uncertainty in their simulation. Note also that the calculated R and NSE values display contrasting results, as they represent different evaluations of the fitness of a model. R demonstrates the strength of a linear relationship between two variables, while the NSE is a normalized statistic that determines the relative magnitude of the residual variance (‘noise’) compared to the measured data variance (‘information’) (Nash & Sutcliffe 1970). As such, good values of R (if the linear relationship between two variables is high) and low values of NSE (if the relative magnitude between two variables is high) can coexist for the same dataset.
Figure 15

Volume and peak error between WEHY-GSM and WEHY-GFS over NS and TM stations during the selected flood events in 2012, 2103, 2014, and 2015.

Figure 15

Volume and peak error between WEHY-GSM and WEHY-GFS over NS and TM stations during the selected flood events in 2012, 2103, 2014, and 2015.

Close modal

WEHY-WRF-GSM showed higher volume and peak errors, particularly in the 2012 and 2013 events. Despite these errors, the forecasting results are encouraging due to their acceptable correlation coefficients for most of the events. The reliability and accuracy of these forecasting results can be improved by applying assimilation and bias correction methods, particularly in the selected locations (Trinh et al. 2022b). For the reliability of the 2–3 days precipitation and flood forecasts, it is necessary to update these forecasts by upper air sounding observations, ground weather observations, remote-sensed observations (radar or satellite), and real-time ground precipitation and flow gauge observations.

This study proposed a forecasting system that coupled a dynamical downscaling technique and hydrologic models to forecast real-time flood events with a lead time ranging from 1 to 3 days. The WEHY-WRF models were selected as the hydrologic-atmospheric components for the proposed system. The WEHY-WRF models were successfully implemented and validated before testing a real-time forecasting system over the Nong Son-Thanh My watershed. There are four significant historical flood records selected for evaluation of the real-time rainfall-flood testing system. Overall, the comparison between the model simulations and corresponding observations show the rainfall and flood of the WEHY-WRF-GFS forecast match quite well with observation data. The rainfall and flood forecast results based on WEHY-WRF-GSM did not match as well with the historical record as the WEHY-WRF-GFS results; however, these results are quite encouraging based on their acceptable correlation coefficients and encouraging NSE. Some limitations remain in the proposed approach, including missing bias correction and data assimilation. In the future, improvements can be made through data assimilation of rainfall and flood forecast, which will merge the WEHY-WRF prediction outputs with the observed hydrometric, automatic hydro-meteorological data, and real-time quantitative radar data. In addition, future work includes developing an automatically updating forecast every 6 h and continuously providing information on atmospheric, and flood with a lead time of 2–3 days (depending on requirements as well as forecasting objectives) for selected locations. The flood forecast also can be coupled with the hydraulic-sedimentation models to estimate flood inundation and sediment transport during real-time extreme flood events (Tu et al. 2020). The flood forecasting and warning system could no doubt assist management authorities during flooding events. An accurate and reliable forecast could enhance and improve the effectiveness of emergency responses. In addition, reliable forecast data will assist with decision-making focused on reducing the effects of flood risks on society in an economically and environmentally sustainable manner.

This research was funded by the Vietnam National Foundation for Science and Technology Development (NAFOSTED), Ministry of Science and Technology, under grant number 105.06-2019.326.

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

The authors declare there is no conflict.

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