Flooding is the most prevalent natural disaster globally. Increasing flood frequency affects developing nations as these countries lack strong forecasting systems. The most flood-prone urban regions are near the coast or riverbanks. Using The International Grand Global Ensemble (TIGGE) data, a coupled atmospheric-hydrologic ensemble flood forecasting model for the Sabarmati river was developed. Incorporating numerical weather prediction (NWP) information into flood forecasting systems can increase lead times from hours to days. When predicting the weather, we employed numerous NWP models from various prediction centers. European Center for Medium Range Weather Forecasts (ECMWF), United Kingdom Meteorological Office (UKMO) and National Centers for Environmental Prediction (NCEP) data with a 5-day advance time are coupled with the HEC-HMS model to provide ensemble stream flow predictions. The ensemble flood forecasting model uses the 2015 flood season as a test scenario. In this research, we discovered that TIGGE ensemble prediction data can be useful for prediction of stream flow and results showed effective flood forecasting for Sabarmati river. HEC-HMS, a semi-distributed hydrologic model, uses ECMWF, NCEP, and UKMO precipitation ensembles. ECMWF shows that 90% of the correlation with observed data and peak time and peak discharge is also match with the observed discharge with a peak on 29 July 2015 with 9,300 cumecs. Danger probability may be accurately predicted based on peak time and flood warning probability distributions.

  • Prediction of stream flow using ensemble precipitation for Sabarmati river basin.

  • Statistical Analysis of the ECMWF, UKMO and NCEP ensemble precipitation data for Sabarmati basin.

  • Development of the coupled Hydrological and Meteorological model for accurate flood prediction.

  • Statistical post-processing of the ensemble model and its verification for 5-day lead time.

Graphical Abstract

Graphical Abstract
TIGGE

THORPEX International Grand Global Ensemble

NWP

Numerical Weather Prediction

ECMWF

European Centre for Medium-Range Weather Forecasts

NCEP

National Centers for Environmental Prediction

UKMO

United Kingdom Meteorological Office

HEC-HMS

Hydrologic Engineering Center – Hydrologic Modeling System

ANN

Artificial Neural Network

EPS

Ensemble Prediction Systems

CWC

Central Water Commission

QPF

Quantitative Precipitation Forecast

DEM

Digital Elevation Model

LULC

Land Use Land Cover

HSG

Hydrological Soil Group

SCS-CN

Soil Conservation Service Curve Number

BMA

Bayesian Model Averaging

EMOS

Ensemble Model Output Statistics

PDF

Probability Density Function

NGR

Nonhomogeneous Gaussian Regression

cNLR

Censored-Non-homogeneous Logistic Regression

There have been a number of natural disasters that have taken place without warning throughout the last several decades. Many people agree that floods are unpredictable and have the ability to ruin both the lives of humans and animals, and property. It is very difficult to predict when and how often severe hydrometeorological events may cause flooding. Early warnings and flood measures to reduce human loss and property damage are based on accurate estimates of runoff volume and flood peaks. For sustainable water resource planning and management, the proper assessment of surface runoff in catchment areas requires an extensive understanding of the flood affecting factors. Understanding the hydrologic response of a region by simulating the rainfall and runoff is a well established method. The most typical use of rainfall–runoff models is to predict flood occurrences, measure water levels for different water conditions and forecast floods (Ahrens & Jaun 2007). Land use, slope, vegetation, and storm attributes such as length, volume and intensity of rainfall have a role in determining the quantity of surface runoff . Asia is the most flood-prone continent, accounting for over half of all flood-related deaths in the twentieth century (Bürger et al. 2009; Hapuarachchi et al. 2022). When it comes to dealing with an emergency caused by significant rains, decision-makers rely heavily on predictions. Precipitation is the most critical piece of information needed to predict floods. Flood forecasting is heavily influenced by two key factors: accuracy and lead time (Jha et al. 2018; Kumari et al. 2019). Forecasting floods using numerical weather prediction (NWP) precipitation products is one of the most effective techniques to increase the lead time of the forecast. The NWP enables the collection of valuable flood data and the dissemination of flood warnings ahead of time (Roulin & Vannitsem 2005). To get around the deterministic forecast, meteorologists and hydrologists are turning their attention to the inherent uncertainty in their respective systems. An ensemble forecast, rather than the usual single deterministic prediction, is increasingly taking its place (Roulin & Vannitsem 2005; Nair & Indu 2017). This is a shift from a deterministic forecast to an ensemble forecast. By taking into account the faulty boundary conditions and assimilation of data in the ensemble prediction, a deterministic forecast of atmospheric variables may be transformed into a fully probabilistic one. Precipitation and runoff forecasting have never been done this way before (Komma et al. 2007). An interactive grand global ensemble system was developed to account for the uncertainty of projections from several global models. As a part of a worldwide research effort, The International Grand Global Ensemble (TIGGE) collects and analyses prediction data from all of the world's main forecasting centers (Thielen et al. 2009). Multiple sources of uncertainty are combined into a probability distribution via TIGGE ensemble prediction.

When the ECMWF and the NCEP first developed ensemble predictions in 1992, they were frequently utilized in inflow forecasts, since they were based on a large number of different models. Flood forecasting, in particular, may benefit from the use of meteorological predictions. The ensemble predictions, which refer to numerous distinct forecasts created using various physical parameterizations or varied beginning circumstances, have made major progress in improving meteorological forecasts (Swinbank et al. 2016). (Saedi et al. 2020). Another use for the TIGGE is to create an early warning system based on operational medium-range ensemble predictions from the different numerical weather centers: the ECMWF, UKMO and NCEP. Each model's climatological probabilistic density function is used to determine the predicted likelihood of occurrence of severe meteorological events. Severe disasters like the 2010 Russian heatwave, the 2010 Pakistan floods, and 2012's Hurricane Sandy were all correctly predicted using this tool (Matsueda & Nakazawa 2015). According to Yang & Yang (2014), data-driven models, such as ANN and autoregressive models, are also employed for rainfall–runoff assessments, as well as predictions. A study by Cheng et al. (2005) found that the ANN model was capable of making accurate predictions about the long-term discharge of a reservoir. The quality and amount of the data, on the other hand, are critical to the success of these models (Wu et al. 2009). If data-driven models are utilized that do not have sufficient data, the prediction uncertainty will be greater. Data-driven models are not included in this research since it is difficult to get high-quality and large amounts of data. When it comes to predicting reservoir inflows, combining NWP with a hydrological model at the catchment size is a simple technique. However, a hydrometeorological prediction system comes with a lot of unknowns, such as boundary and beginning conditions and hydrological model parameters (Liu & Gupta 2007; Hostache et al. 2011; Zappa et al. 2011). The largest source of uncertainty in hydrometeorological predictions is rainfall projections (Rossa et al. 2011; Zappa et al. 2011). The NWP model generates varied rainfall estimates at the same place and time because of insufficient data, approximate forecast models owing to inevitable simplifications, random errors from early atmospheric conditions perturbing, and model parameterizations (Palmer 2001). Rather from being unexpected or devoid of information, differing rainfall estimates, according to Wilks (2006), are not perfectly predictable.

The Ensemble Prediction Systems have evolved over the previous decade and are now used to simulate the impact of observation uncertainty, poor boundary conditions, data assimilation, and other factors on weather forecasts. To anticipate the probability density function beyond the linear error increase in meteorological prediction, an EPS may be considered a system of finite deterministic integrations and regarded as the sole practical technique (Buizza 2008). EPS from each weather station can account for some of the NWP uncertainties that arise from beginning circumstances and stochastic physical processes (Roulin 2007). Grand ensemble (GE) or mixed multi-ensemble (ME) of EPSs from multiple meteorological centers may handle other issues in numerical implementation and data assimilation (Goswami et al. 2007). The ensemble predictions probabilistic character is better preserved when each model participating in the EPS at various weather centers is merged (He et al. 2009, 2010; Bao et al. 2011). As some of the uncertainties may be defined, ensemble weather prediction products can be utilized for hydrometeorological, hydrological (and geological disaster-related) weather forecast, and early flood warning (Bao & Zhao 2012).

When used to estimate streamflow, NWP models QPF are an important input to hydrological models (Coulibaly 2003; Cuo et al. 2011; Liu & Coulibaly 2011; Ahmed et al. 2014). Uncertainty stems from inaccuracies in the NWP model's beginning circumstances and in the atmospheric processes that are approximated, as well as in the NWP model's ability to predict the weather (Palmer et al. 2005). One estimate of streamflow with poor or high-quality precipitation forecasts would have an enormous influence on decision support, such as the management of water infrastructure, sending warnings of upcoming flood or drought, or scheduling reservoir operations. Many people are now interested in probabilistic forecasts that can be used to estimate the likelihood of any future weather event occurring, which will allow water management agencies and emergency services to prepare for the risks associated with low- or high-flow events several days or weeks in advance (Palmer 2002; Thirel et al. 2014; Tao et al. 2015). In order to provide accurate precipitation predictions, the NWP model must be perturbed and physically parameterized, both of which are technically demanding and computationally intensive processes. A post-processing step is required before QPFs (either ensemble or deterministic) provide valid estimates of any data (e.g., streamflow). Several post-processing techniques based on statistical models have been presented in the recent decade. Based on observations and NWP forecasts, a statistical model may be developed by exploiting the relationship between the two, estimating the model parameters using historical data, and reproducing post-processed ensemble forecasts of the future (Velázquez et al. 2010; Jinyin et al. 2016; Jha et al. 2018).

More than 5,500 major dams exist in India. For reservoirs to be effective in reducing flood damage, accurate inflow projections are essential. CWC gives inflow projections for over 150 places in India right now (Jain et al. 2022). An increase in this quantity is urgently required in order to provide projections for all big and minor dams, as well as key cities. It is necessary to employ a better flood forecasting model to give predictions at critical locations and sites, since we have a poorer flood forecasting system in India. According to Sudheer et al. (2019) and other researchers, accurate precipitation and inflow projections are critical to reservoir efficiency. Using ensemble predictions is critical, as Nanditha & Mishra (2021) explained in detail the present state of flood forecasting in India. Floods are becoming increasingly common as the frequency and severity of extreme precipitation events rises throughout most of India and in the world (Jain et al. 2022). The number of cloud-burst incidents is also increasing. Indian scientist lack the resources and expertise to accurately predict these catastrophes.

Using TIGGE data for early flood predictions and computer simulations of rainfall–runoff processes, this research intends to construct an atmospheric–hydrologic flood forecasting model for use in the future. ECMWF, UKMO, NCEP (ensemble) numerical models are used to assess the predictions of the TIGGE database over the Sabarmati basin. Deterministic, dichotomous, and probabilistic evaluation methodologies were used to evaluate the models’ abilities for the time period 2014–2020. The main novelties of the research are to predict stream flow using ensemble precipitation for Sabarmati river basin. This work focuses on statistical analysis of the ECMWF, UKMO and NCEP ensemble precipitation data for Sabarmati basin. The key feature of this research work is to develop the coupled Hydrological and Meteorological model for the accurate flood prediction with statistical post-processing of are ensemble model and its verification for 5-day lead time.

The region of study in this research is the Sabarmati basin of Gujarat, India. The Sabarmati basin is situated between 25°0′N, 71°37′E and 21°56′N, 73°40′E possessing a topographical region of 21,565 km2 which reaches out over conditions of Rajasthan 4,124 km2 (19%) and Gujarat 17,441 km2 (81%). Most of Sabarmati basin falls in Gujarat state comprised of managerial locales of Banaskantha, Sabarkantha, Mehsana, Gandhinagar, Ahmedabad and Kheda. The river begins in Aravalli slopes at an altitude of 762 m in Rajasthan in the Udaipur locale and falls into Arabian ocean at the Gulf of Cambay subsequent to draining 371 km. The mean longitudinal incline has been 2.05 m per km south-west way while the mean parallel width is around 300 m. The central tributaries of Sabarmati stream are Wakal, Sej, Harnav, Haathmati and Watrak. The basin is split into two sub-basins: the Upper and Lower Sabarmati sub-basins. They have also been divided into 51 watersheds, each representing a separate tributary system. The Sabarmati river and its tributaries are an interstate river that runs across Rajasthan and Gujarat. The upper Sabarmati basin is taken as the study of the research as it draining the water to the Dharoi Dam which is the most important dam structure on the Sabarmati river as shown in Figure 1. Total drainage area up to the Dharoi Dam is 4,208 km2.
Figure 1

Study area map of the Sabarmati river basin with a digital elevation model (DEM) of Upper Sabarmati basin.

Figure 1

Study area map of the Sabarmati river basin with a digital elevation model (DEM) of Upper Sabarmati basin.

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In every research study, data collection is the most critical phase. Various information from government agencies and web portals were needed for this investigation. In Figure 2, the chart shows the necessary data for this investigation. The ArcGIS platform will be used to assemble the data, and the resulting map will be useful in flood forecasting model development. In the Sabarmati basin, the CWC operates the hydro-observation stations. Various climatic characteristics are also measured at several hydro-observation locations. Furthermore, several of these stations are actively involved in flood forecasting activities. In the Sabarmati basin, there are two CWC flood forecasting stations: Dharoi Dam and Subash Bridge, Ahmedabad. These stations are wirelessly capable of transmitting flood warning information quickly. For the study area there are in total six rain gauge station and four discharge and gauge measurement sites available as shown in Figure 3. The Sabarmati basin receives an average annual rainfall of 750.0 mm.
Figure 2

Date collection for the ensemble forecasting model development.

Figure 2

Date collection for the ensemble forecasting model development.

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Figure 3

Rain gauge station and precipitation grid point in the upper Sabarmati basin.

Figure 3

Rain gauge station and precipitation grid point in the upper Sabarmati basin.

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By the middle of June, the southwest monsoon has arrived and will go by the first week of October. The southwest monsoon has a major impact on rainfall. The majority of the basin receives rainfall ranging from 600 to 800 mm. In the basin, a good network of hydrological and meteorological stations has been established. Wireless stations have been set up at different sites to transmit information on rainfall and discharge to a central control center, where it is utilized to make regulatory choices.

According to this research, the datasets that were utilized included observed daily precipitation and ensemble projections of daily rainfall. The Central Water Commission, Gandhinagar and the Gujarat State Water Statistics Center, Gandhinagar provided daily precipitation and inflow data for the last 30 years. As part of this study's ensemble precipitation prediction (Table 1), we used data from the ECMWF, NCEP, and UKMO, under TIGGE. The perturbed predictions are formed by altered beginning circumstances in the CF, which is built by a data-assimilation process (Ye et al. 2014). The forecasting lead period for all of these predictions is 1–15 days. It is possible to obtain these data for free at http://apps.ecmwf.int. In order to establish an inflow prediction, the research uses ensemble precipitation forecasts with a lead period of 1–5 days for the years 2014–2010. After interpolating prediction data to six rain gauges, the Thiessen polygon technique was used to calculate area precipitation.

The Indian Space Research Organization's Cartosat-1 Digital Elevation Model (CartoDEM) is a national DEM (ISRO). It is based on the Cartosat-1 stereo payload, which was launched in May 2005. The DEM used for this research is purchased from NRSC, Hyderabad for the finest resolution of 2.5 m × 2.5 m.

There are in total 10 tiles of CartoDEM which covered the whole study area. These DEM tiles were used in the development of the hydrological model as well as other maps, i.e., Slope map, Drainage map, etc. A Land Use Landcover map was prepared using the Supervised method in ArcGIS based on the Landsat 8 datasets downloaded from the USGS Earth Explorer. The Sabarmati river and its tributaries contributed 4.19 percent to the land cover class water bodies. The built-up land (which includes both urban and rural areas) accounts for 1.95 percent of the total land area, or 423.14 square kilometers. The basin's forest cover is 2,595.69 square kilometers, or 11.98 percent of its total area. The basin's wasteland accounts for 7.15 percent of the total surface, covering 1,549.13 square kilometers. Figure 4 shows the thematic map such as the LULC map and HSG (Hydrological soil group) map used for the hydrological modelling.
Figure 4

Landsat 8 image, LULC map and Hydrological Soil Group map for Sabarmati upper basin.

Figure 4

Landsat 8 image, LULC map and Hydrological Soil Group map for Sabarmati upper basin.

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To develop the ensemble flood forecasting model, we adopted the methodology shown in the flowchart in Figure 5. This section also discusses the testing and verification procedures used to assess the ensemble predictions performance. The approach for evaluating ensemble performance included retrieving several perturbed member predictions from various TIGGE data centers. Data from the TIGGE, which are ECMWF, NCEP and UKMO numerical weather forecasts and semidistributed hydrological model, are coupled, which are then reviewed and post-processed. Forecasting average inflow for the following forecast period is done using a multiple linear regression model that takes into account the previous period's precipitation, average inflow, and three TIGGE's three center forecasts for the next period's precipitation. To make better judgments based on the forecast information provided by the rainfall–runoff models and the TIGGE ensemble precipitation prediction data, which provides additional information for making decisions (Medina et al. 2019). For reservoir operations, using ensemble predictions may be problematic because of the wide range in information that is available, particularly during flood seasons.
Figure 5

Flowchart of the ensemble model developed for the Sabarmati river basin.

Figure 5

Flowchart of the ensemble model developed for the Sabarmati river basin.

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Rainfall–runoff model

The Hydrologic Engineering Center of the US Army Corps of Engineers (USACE) created the well known hydrologic modelling program HEC-HMS (HEC). Runoff volume, baseflow, and channel flow are all included in this model, which seeks to replicate the precipitation runoff processes that occur in watershed systems. It is not included in this study the vertical flow of water inside the soil layer. HEC-HMS has been used in several research studies to estimate rainfall–runoff at watershed size. It is acceptable for this investigation since the movement of soil during typhoons is believed to be minor. HEC-HMS has a wide variety of modules for each component. Precipitation surplus is defined as the remaining depth after the loss has been taken into account. Cumulative losses were calculated using the soil conservation service curve number (SCS-CN) loss technique (Yang & Yang 2014). The following equation is used to estimate surplus precipitation as a function of cumulative precipitation, soil cover, land use, and prior moisture:
A watershed's capacity to extract and hold storm precipitation is measured by its potential maximum retention (S), which is the sum of Pe and P. The SI unit is used to calculate the maximum retention S:
There are many variables that may be used to estimate the SCS-CN, which can be determined by land use, soil type and prior watershed moisture. Permeable soils with high infiltration rates have CN values between 100 (for water bodies) and 30 (for permeable soils with low values). Calibration and validation procedures were used to improve CN's initial value, depending on the soil type and land use of the catchment area. HEC-HMS uses an empirical model (the unit hydrograph) to convert rainfall excess (Pe) into surface runoff (kinematic wave). SCS unit hydrograph (SCS-UH) was used to estimate direct runoff in the research.

Ensemble prediction model

Ensemble precipitation

Three weather centers, namely the ECMWF, UKMO and NCEP were used to compile the ensemble precipitation forecasts (Pf). A ‘central’ unperturbed analysis is provided by each of the three chosen centers, along with a number of projections with concerned beginning circumstances. Equal weights were given to each forecaster. Buizza (2008)'s observation said that a forecasting system's ability to provide consistent predictions on successive days is a desired quality. Using the threat scores (TS) technique, the three weather centers and their GE were evaluated in this article. Total TS ranged from zero (no skill) to one (perfect). A boxplot graph shown in Figure 6 shows the raw ensemble data collected from the TIGGE centers. This shows the data had too much variation which required post-processing of the raw ensemble data before use in the rainfall–runoff model for flood prediction for any river basin.
Figure 6

Boxplot for the ensemble precipitation for 2015 flood event for 81 members.

Figure 6

Boxplot for the ensemble precipitation for 2015 flood event for 81 members.

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Post-processing of the Ensemble model

Forecasting scenarios (also known as ensemble members) based on beginning circumstances and physical parameterizations that have been significantly altered in the NWP system are used to create probabilistic predictions. Unfortunately, such ensemble predictions are unable to reflect the whole forecasting uncertainty since it is impossible to precisely and consistently represent all sources of error (Buizza 2018). As a result, ensemble projections tend to be skewed and too optimistic (Wilks 2018). In order to calibrate ensemble predictions, statistical post-processing might be performed. For risk assessment and decision making in business, agriculture, and finance, reliable weather predictions are essential. A good example of this is flood forecasting, which relies on accurate precipitation predictions to determine future streamflow (e.g. Aminyavari & Saghafian 2019). To eliminate systematic mistakes in future forecasts, statistical post-processing looks for structure in previous forecast–observation combinations. For example, Wilks (2018) lists a selection of post-processing ensemble prediction algorithms that have been developed in the recent several years.

Bayesian Model Averaging (BMA) and Ensemble Model Output Statistics (EMOS) are the two basic parametric techniques listed by Raftery et al. (2005) for the class of parametric methods (Gneiting et al. 2005). In the BMA technique, the single ensemble member predictions are weighted averaged to provide a predictive probability density function (PDF). These methods have found several uses, such as in Sloughter et al. (2007) and Schmeits & Kok's (2010) investigations on ensemble precipitation post-processing. The EMOS technique uses a parametric distribution whose parameters are dependent on the ensemble prediction to generate a predictive PDF. The Nonhomogeneous Gaussian Regression (NGR) technique is a popular EMOS model (Gneiting et al. 2005). As opposed to a homogeneous regression model, an inhomogeneous method expresses the predictive distribution's variance as a function of the ensemble's variance. Many studies such as Baran et al. (2013) and Hemri et al. (2014) have used the NGR model, which is based on the assumption of a Gaussian predictive distribution, to make postprocess precipitation projections. It is common to use EMOS with a left-censoring of the prediction distribution at zero for precipitation since it is a non-negative variable. Over the last several years, new methods for post-processing at hitherto undetected locations have emerged. A local model's post-processing parameters are geostatistically interpolated before being used in the interpolation approach. It is via the use of Geostatistical Model Averaging that Kleiber et al. (2011) first introduced geostatistical interpolation as part of a BMA post-processing framework. Precipitation predictions may now be predicted using the same methods used for normally distributed precipitation forecasts by Kleiber et al. (2011) and Pappenberger et al. (2008).

Censored logistic regression

It was found that cNLR was the most promising strategy when comparing EMOS models and BMA to the dataset in the research (Friedli et al. 2021). Over the course of the dataset, cross-validation was used to evaluate the performance of the models. One month at a time, the training dataset is reduced to 30 months and the model is trained using the remaining data. Predictive performance is then evaluated by comparing the observations from the models trained on the remaining months to those from the months that were left out. Two versions of the fundamental models are put to the test: as a result of using all stations’ data to build a global version of the model, the model may be applied to all locations at once. To implement the local version, each station's history data must be used to build a model for that station. The extra material contains further information about the cNLR model's various techniques and the results of a comparison of those approaches. It is a distributional regression model for the cNLR technique. If the ensemble prediction is correct, we suppose that the observed precipitation quantity (Y) carries a probability distribution with its moments influenced by this. The amount of precipitation is a non-negative number that may take any real value (if it rains) or the value zero (if it does not rain). These characteristics may be explained by using a zero-censored distribution model. If Y is a latent random variable and it meets the following criteria, then we may assume it exists:

Error estimation

A more natural definition of an average error, the mean absolute error (MAE), was proposed by Willmott & Matsuura (2005) as a replacement for the root mean square error (RMSE). In a collection of predictions, the MAE calculates the average error size without taking the direction of the mistakes into account. It assesses the consistency of a measurement. The safety and efficiency of a reservoir are closely related to the amount of water entering the reservoir. Thus, it is used as a performance indicator. It is easy to see how the gap between observed and predicted inflow is a good indicator of the overall performance. The MAE has the following definition, ranging from 0 to infinity:
where Oi is the observed inflow (m3/s); Ii is the predicted inflow (m3/s); i is time (hour); T is the entire evaluation time period (hour). The closer an MAE is to zero, the more accurate is the value.
An accurate assessment of the system's overall functioning requires an understanding of both the maximum and average input rates. The following is the definition of the percentage error (PE):
where Simulated and Observed = the simulated and observed peak inflow or cumulative inflow (m3/s).
The model predicts that precipitation has a direct correlation to the accuracy of that prediction. Therefore, the TIGGE precipitation ensemble prediction must be evaluated first. According to observations, the multi-model precipitation ensemble is based on ECMWF predictions, NCEP forecasts, and UKMO forecasts. To assess the accuracy of TIGGE's precipitation forecasts, three major rain events from 2015, 2017, and 2019 were chosen. The precipitation prediction from the ECMWF, NCEP, and UKMO ensemble forecasts, as well as the verification against observations, are shown in the Figure 7.
Figure 7

Scatter Plot, Spread skill plot and Histogram for the ensemble data set.

Figure 7

Scatter Plot, Spread skill plot and Histogram for the ensemble data set.

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Ensemble prediction of discharge

It is first necessary to calibrate and evaluate each model's inflow forecasts using datasets. ECMWF's 1–5 day ensemble predictions from 2007 to 2012 are then included into the operational model to give ensemble inflow forecasts. HEC-HMS models were used to simulate Dharoi reservoir's inflows during calibration and verification periods. The panels indicated that simulated inflows compared to observed inflows. With NSEs of 0.92 and 0.89 for the whole series, the combined rainfall–runoff model performs well in the calibration and verification phases. In this case, we can see that the combined model may provide strong results and be put to good use throughout the prediction period:

Forecast verification

The suggested approach's robustness, reliability, and efficacy are evaluated using deterministic and probabilistic verification measures. Accordingly, the produced ensembles are evaluated using deterministic measure and probabilistic measures. Normalized measurements are used to compare data in a straightforward manner. During both calibration and verification, the created ensembles are evaluated to ensure adequate evaluation of the findings (Khajehei & Moradkhani 2017).

Deterministic measures

Deterministic techniques are used to examine the variance in the mean ensemble precipitation prediction. In addition, a deterministic framework would be useful for studying the link between the observation and the raw prediction.

Absolute Percent bias measures the ensemble mean's divergence from the observation. Absolute percent bias should be set to zero at all times (Gupta et al. 1999; Moriasi et al. 2007):

Probabilistic measures

Deterministic measurements may be skewed by too or underly confident projections, hence probabilistic methods must be used to analyze the resulting forecast. Ensemble forecast reliability may be evaluated using probabilistic methods (DeChant & Moradkhani 2014, 2015). The Continuous Ranked Probability Skill Score (CRPSS) is used to evaluate the forecasting capacity of the created ensembles. Brier Score has been extended to include all conceivable thresholds using this normalized form of Continuous Ranked Probability Score (CRPS) (Hersbach 2000).

Continuous ranked probability score

To calculate CRPS, the squared distance between predicted and observed cumulative distribution functions is integrated (Hersbach 2000), and the following formula is used:

CDF (cumulative distribution function), Ftf(x) is the predicted probability CDF for the tth forecast scenario, Ft0(x) is the observed probability CDF, and T is the number of forecasts. The lower the CRPS number, the better, because CRPS tends to rise when prediction bias increases (whether in a positive or negative way). Mean absolute error is substituted for the CRPS in deterministic forecasts because it is the limiting value of the spread of CRPS when the prediction spread approaches zero. Percentage of daily observations is used to show the relative CRPS. Errors are normalized using relative CRPS, making it possible to compare results across catchments.

An ensemble precipitation's systematic bias may be assessed using the correlation coefficient (CC), RMSE, and relative bias (BIAS). The CC measures the degree of linear correlation between satellite-based precipitation data and gauge measurements.

Table 1

List of the meteorological forecast centers used in the study

Sr. no.Country/regionMeteorological centerCenter abbreviationEnsemble member
UK ECMWF European Center for Medium-Range Weather Forecast 50 + 1 
USA NCEP National Centers for Environmental Prediction 14 + 1 
Europe UKMO United Kingdom Meteorological Office 11 + 1 
Sr. no.Country/regionMeteorological centerCenter abbreviationEnsemble member
UK ECMWF European Center for Medium-Range Weather Forecast 50 + 1 
USA NCEP National Centers for Environmental Prediction 14 + 1 
Europe UKMO United Kingdom Meteorological Office 11 + 1 

There are a number of metrics used to evaluate the performance of an individual, such as the probability of detection (POD), false alarm ratio (FAR), miss rate (MISS), and critical success index (CSI). Table 2 shows the most often used contingency table (CSI).

Table 2

Contingency table for Hit and Miss alarm

Observed rain detected (Yes)Observed no rain (No)
Ensemble rain (Yes) Hit (H) False (F) 
Ensemble no rain (No) Miss (M) Null event 
Observed rain detected (Yes)Observed no rain (No)
Ensemble rain (Yes) Hit (H) False (F) 
Ensemble no rain (No) Miss (M) Null event 
Table 3

Ensemble model verification measures and their formula

Sr. no.Verification measuresFormulaPerfect/No skill
Root Mean Square Error  0/ 
Relative Root Mean Square Error  0/ 
Probability of Detection (Hit rate)  1/0 
False Alarm Ratio  0/1 
Frequency Bias  1/ 
Brier Score  0/1 
Brier Skill Score  1/ < =0 
Critical Index Ratio   
Sr. no.Verification measuresFormulaPerfect/No skill
Root Mean Square Error  0/ 
Relative Root Mean Square Error  0/ 
Probability of Detection (Hit rate)  1/0 
False Alarm Ratio  0/1 
Frequency Bias  1/ 
Brier Score  0/1 
Brier Skill Score  1/ < =0 
Critical Index Ratio   

Note: There are N forecast–observation samples, with F denoting the number of forecast–observation pairs, O denoting the observation matching to the prediction, PF denoting probability of precipitation, and PO denoting the probability of occurrence of observation. Like and signify the forecast average and observation average, BSref is normally the Brier Score of the reference probability prediction, typically the likelihood of event occurrence from climate data. H, M, F and T are generated from contingency table (Table 3).

Figure 7 shows the various plot for the ensemble data. Scatter plot shown in the figure represent the ensemble and observed data variation, While the spread skill plot shown in the figure shows the absolute error in the raw ensemble data. Rank histogram shows the frequency of the precipitation for the particular data sets.

Distinguishing between resolution and reliability and uncertainty provides BS when the BS is separated down into its component of reliability, uncertainty, and resolution. If you see a score close to 1, it is an indication of a bad prediction. Ranking Probability Score is an extension of BS that may be used in multiple-event scenarios, taking into account the prediction and observation probabilities together. It is possible to have an RPS of 0 or 1, with a perfect RPS of 0. Figure 8 shows the box plot of the Brier Score which represent the censored logistic regression (nCLR) and BMA method having the good Brier Score which is close to 0 compare to the other methods. So based on the Brier Score we can conclude that cNLR and BMA is the best method compare to the other four methods for the post-processing of the ensemble precipitation.
Figure 8

Brier Score and RPS plot for the various methods for ensemble data.

Figure 8

Brier Score and RPS plot for the various methods for ensemble data.

Close modal

In the context of discrete event forecasting, the relative operating characteristics (ROC) assess the accuracy of the prediction based on a threshold. The ROC curve assesses the quality of a choice based on a prediction probability for a probability forecast. It shows the trade-off between the POD and the probability of false detection (POFD). Higher POD values and lower POFD values correlate to improved results. The Area under the ROC curve reflects the performance forecasting ability, with more Area Under the Curve (AUC) indicating greater skill.

As shown in the Figure 9, the AUC which shows the majority of the methods, gives good results. If the value of the AUC curve is 0.5 the diagonal line, then cNLR, BMA and logreg methods shows the 0.5 AUC. While the other methods show the lower or higher AUC compared to these three methods. So, at the end of the verification of ensemble post-processing, nCLR and BMA are the two best methods that will be useful for the post-processing of the ensemble precipitation data. This method can be useful for stream flow prediction using the appropriate rainfall–runoff model.
Figure 9

AUC curve for the various methods of ensemble forecasting.

Figure 9

AUC curve for the various methods of ensemble forecasting.

Close modal
These three ensemble predictions are clearly seen in Figure 10. Precipitation forecasts by NCEP were much lower than observed maximums. There is a considerable mismatch in the timing of heavy rainfall projected by the UKMO ensemble outputs compared to observations. Ensemble members also have a wider range of predictions than in previous ensemble forecasts.
Figure 10

Ensemble rainfall plot of ECMW, UKMO, NCEP for the 2015 flood event.

Figure 10

Ensemble rainfall plot of ECMW, UKMO, NCEP for the 2015 flood event.

Close modal
The graph shown above in Figure 11 depicts the anticipated river flows during the 2015 flood event based on three different precipitation ensemble projections. All three ensemble predictions are able to accurately estimate the peak discharge and the time of occurrence. However, the size of the predicted discharges is rife with huge inaccuracies. The discharges predicted by UKMO were plainly considerably higher, while the discharges predicted by NCEP were significantly lower. In comparison to observed discharges, only ECMWF anticipated discharges are close to the actual values. When it comes to the other three occurrences, ECMWF's discharge predictions are consistently the best. Because the runoff generation strategy is better for humid areas, the simulation results are not excellent for situations like the one in 2015 (e.g., a drought). Disparities between the three ensembles in terms of anticipated discharges and the time of occurrence are enormous.
Figure 11

Ensemble discharge plot of ECMW, UKMO, NCEP for the 2015 flood event.

Figure 11

Ensemble discharge plot of ECMW, UKMO, NCEP for the 2015 flood event.

Close modal
The HEC-HMS model may, however, be driven by all 81 ensemble members, resulting in superensemble projections (see Figure 12). In addition to the range and probability distribution of discharges, superensemble predictions may include the superensemble mean of all 81 members. As seen in the Figure 12, discharges from three different climate models are presented together for a 1–5 day lead time. There is no doubt that the predicted peak discharges and the time of occurrence are in close agreement with observations. However, the anticipated magnitudes of peak discharges are quite variable. The ECMWF is shown to have the closest magnitude to the 2015 event, which is likely to be because it has the most ensemble members (50). The grand ensemble shows very good results compared to all three other centers. Ensemble mean discharges for the NCEP and UKMO are both below average owing to the less quantity of precipitation projected for each model. For NCEP and UKMO the amount of discharge can be accurately predicted, but there are considerable prediction errors owing to less or more precipitation than is expected for the other two systems. Figure 12 shows that 1-day and 2-day lead time ensemble discharges give an accurate performance as it is closely matched with the observed discharge. While the 3-day, 4-day and 5-day lead time ensemble discharges show the high error in the prediction of the peak discharge, the reason behind this error is that precipitation and initial conditions are not well predicted. Future research should focus on how to calibrate ensemble precipitation predictions from various forecast centers and how to assign different weights for different ensemble systems in order to increase peak discharge accuracy. The obtained results were compared with other researchers' results carried out for Sabarmati river basin and show the close correlation with the predicted results for the discharge and peak time. Verma (2022) carried out rainfall–runoff modelling using the ANN technique for the Sabarmati river basin that showed the good correlation of 0.82 for the Kheroj station. Another research study carried out by Patel (2020) for the Sabarmati river basin using hydrodynamic model a case study showed a good correlation with the Kheroj station's observed and predicted results.
Figure 12

Ensemble discharge for a 1 to 5 day lead time plot of ECMW, UKMO, NCEP for the for 2015 flood event.

Figure 12

Ensemble discharge for a 1 to 5 day lead time plot of ECMW, UKMO, NCEP for the for 2015 flood event.

Close modal
By drawing the exceedance diagram shown in Figure 13 of the ensemble predictions, one may analyze the accuracy of the ensemble forecasts. Excessive forecasts are seen in the exceeding diagram. In the rows and columns, the predictions are organized into a matrix known as a persistence diagram, and the lead times between each forecast are shown as well.
Figure 13

The warning table with exceedance plot for the flood event 2015.

Figure 13

The warning table with exceedance plot for the flood event 2015.

Close modal

This is referred to as a Hit if the observed occurrence is accurately predicted (H). A False Alarm (F) occurs when a simulation indicates the occurrence of an event that has not been observed, while Miss (M) marks an event that was observed but not predicted in simulation, and No Alarm implies an event that was neither forecast nor occurred in real time. Figure 13 shows that the models shows the good accuracy for the peak flood time which is 29 July 2015. Models shows 80–90% predicted data using the ensemble prediction technique having a close relationship with the observed datasets.

An atmospheric–hydrologic flood forecast model powered by TIGGE ensemble predictions in upper Sabarmati watershed during 2015 flood event is put up to examine possible advantages of utilizing the TIGGE database in flood forecasting. In order to predict the rainfall–runoff process, the semidistributed HEC-HMS model is used. The findings show that the HEC-HMS model is capable of simulating and predicting floods in the Sabarmati watershed with high accuracy and precision. The TIGGE archive dataset is a potential technique for delivering a pretty accurate warning 5 days in advance with similar discharge projections. Longer forecast lead time may help to increase the predictability, which is good for flood mitigation and preparation.

Multi-model forecasting techniques need to be developed. The usage of many EPS inputs should be done cautiously since each has a separate error structure and cannot be readily mixed. The GE's performance may be improved by assigning various weight coefficients to distinct weather predictions. The semidistributed hydrologic model HEC-HMS in conjunction with the TIGGE ensemble precipitation data is used in this study for flood forecasting. HEC-HMS is driven by TIGGE data from ECMWF, NCEP, and UKMO ensemble prediction products to create flood forecasts for the Sabarmati river watershed. Coupled model simulations reveal that the discharge during the occurrences may be accurately predicted by this semidistributed model. There are some gaps that exist amongst the model predicted results, which makes it difficult to accurately estimate when and where a peak discharge will occur. The amount of precipitation is a crucial factor in flood predictions. Although precipitation directly affects flood prediction precision, input data uncertainty into hydrological models have a significant effect as well. It is possible to improve hydrological forecasts by using ensemble precipitation prediction to generate more quantitative data. The study utilizes the 2015 floods in Sabarmati basin in North Gujarat, India, as an example and evaluates the influence on flood prediction results using the HEC-HMS model forecast and its ensemble forecast results as precipitation in the forecast period. When the precipitation decreases, the future precipitation has less influence on the flood prediction outcome. It is possible to improve the input information for a hydrological forecast by using the precipitation ensemble prediction in conjunction with a definite forecast. To improve forecasting accuracy, it is now able to accurately predict the shape and time of the flood peak. Many hydrologists and meteorologists have highlighted that anticipated precipitation has a significant influence on flood forecasts, and contemporary weather forecasting technology gives solid scientific support for predicting the precipitation in the forecast period.

The authors are thankful to the Civil Engineering Department, Sardar Vallabhbhai National Institute of Technology, Surat for providing an opportunity to do research work. The authors are also thankful to CWC, Gandhinagar and State Water Data center, Gandhinagar for their valuable support in data provision as well as guidance in this project. We would also like to expand our deepest gratitude to all those who have directly and indirectly funneled us in this research work. The authors are thankful to the Civil Engineering Department, Institute of Technology, Nirma University for sponsoring the funded research project with the sum of Rs. 1 lakh for conducting the research.

All relevant data are available from an online repository or repositories. Available from: https://drive.google.com/drive/folders/1k1YATti2aEHPiCKANQFb8fQIHH7YlUuw.

The authors declare that, they have conflict of interest with Nirma University, Institute of Technology, Ahmedabad for providing research funding with the sum of Rs. 1 Lakh to carry out this research work.

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