In the present study, an optimal rain gauge network has been derived for predicting runoff in the Middle Tapi Basin, India. This study employs a statistical approach by Hall and the recently developed BHARAT (Best Holistic Adaptable Ranking of Attributes Technique) method. BHARAT, primarily designed for industrial applications, has been adapted to address the hydrological challenge of selecting key rain gauges. The lumped conceptual NAM rainfall–runoff model has been developed for the evaluation of rain gauges ranked by each approach. The reliability of Hall's network is affirmed through its commendable performance in statistical assessments of simulated runoff. However, the outcome difference between BHARAT and Hall's method is not pronounced. It is worth noting that Hall's method places primary emphasis on rain gauge stations based solely on measured rainfall, overlooking other hydrological parameters in the selection process. In contrast, BHARAT offers flexibility by considering all relevant attributes to identify optimal alternatives. Both Hall's method and BHARAT exhibit dependable applicability for hydrological applications, with each method presenting unique strengths in the design of rain gauge networks. The observations highlight that the newly developed BHARAT technique, characterized by its simplicity and user-friendly interface, exhibits robust applicability for hydrological applications comparable to Hall's method.

  • The optimal rain gauge network has been designed for reliable hydrologic applications.

  • BHARAT, a recently innovated technique for industrial problem-solving and decision-making, is utilized to select key rain gauges and the results of designed rain gauges have been compared with that of the traditional Hall's approach.

  • The effectiveness of the networks designed by each approach is evaluated using a hydrologic model.

An accurate runoff prediction is the most important aspect of water resources management under an extremely changing climate. Data availability and reliable meteorological conditions are important aspects for accurate runoff prediction. The primary requirement for runoff prediction is precipitation (Mehta et al. 2023b). Due to unforeseen reasons, it may not always be possible to get the measured rainfall data from all the rain gauges installed in the basin (Lohani et al. 2014). Reliable rainfall data are important for various applications such as water budget studies, flood prediction and control, reservoir operation and water resources management (Obled et al. 1994; Ajami et al. (2008); Shaghaghian & Abedini 2013; Sit et al. 2020). Thus, an optimal rain gauge network that efficiently helps to predict the runoff is necessary. In the Middle Tapi Basin (MTB) of India, the rain gauges are installed haphazardly and no spatial distribution has been observed. Due to this, the areas represented by rain gauges to be considered for hydrological applications overlap while other parts of basins are found to be ungauged. In these circumstances, an efficient rain gauge network is required. Thus, in the present study, the optimal rain gauge network for the MTB has been designed for reliable application of the measured rainfall for hydrological applications. Various techniques have been used for the rain gauge network design globally based on the catchment characteristics and recommendations by the standard codes or methods Basalirwa et al. (1993); Moore et al. 2000; Tsintikidis et al. 2002; Adhikary et al. 2015). The traditional statistical approach developed by Hall (1972) has been utilized for a selection of key rain gauges based on ranking. Kar et al. (2015) have applied Hall's approach to selecting key rain gauges for the lower Mahanadi Basin, India. Hall's method considers the rainfall measured by each rain gauge to rank the key rain gauges accordingly. Mehta et al. (2023a) used hierarchical clustering and the Thiessen polygons for designing the rain gauge network for the Narmada River Basin and suggested that the Thiessen polygon-based method is proven to be effective for reliable runoff prediction. Other multi-criteria decision-making (MCDM) techniques such as the analytical hierarchy process (AHP) and TOPSIS can also be used for the selection of key rain gauges considering the factors affecting the selection of the rain gauges. Within the literature, numerous multiple attribute decision-making (MADM) methods have gained significant attention for the selection or ranking of attributes (Tella & Balogun 2020; Shadmehri Toosi et al. (2020); Chowdhury et al. (2021); Ouali et al. (2022); Lyu & Yin (2023); Mehri et al. 2024). Shaikh et al. (2024) linked AHP and fuzzy logic for flood hazard mapping in urban areas. Fuzzy logic has been incorporated for various applications such as rainfall–runoff modelling, runoff prediction, flood frequency analysis, groundwater modelling etc (Chau et al. 2005; Jothiprakash & Magar 2009; Kar et al. (2012); Kisi et al. (2013); Kumar et al. (2015); Hussain et al. (2019); Ramkar & Yadav (2021); Asaad et al. (2022)). However, each approach carries its own set of strengths and weaknesses (Rao & Lakshmi 2021). For instance, the TOPSIS method demands extensive computations, becoming more complex as the number of alternatives and attributes increases. The ranking of alternatives in TOPSIS can differ based on the normalization technique employed for the data. Razavi Toosi & Samani (2014) proposed an integrated method consisting of MADM with ANP (analytical network process), fuzzy TOPSIS along fuzzy max–min set techniques for the evaluation of water transfer projects. In the case of the VIKOR method, greater computational complexity exists (Opricovic & Tzeng 2007). Furthermore, varying ranking lists might yield different outcomes even with the same attribute weights, and the ‘majority of attributes’ technique might hold weights ranging from 0 to 1 Rao (2024a). An innovative approach named BHARAT has been explored in the present study which was recently developed by Rao (2024b) and has been designed to solve industrial problems. The novelty of the present work lies in the exploration of the BHARAT algorithm for the hydrologic problem of selection of key rain gauges of the MTB for reliable runoff prediction. The designed rain gauge network has been evaluated based on the runoff response at the outlet, for which the lumped conceptual hydrologic model has been developed. Yadav & Yadav (2024) utilized the BHARAT MADM technique to rank the best available EPS (ensemble prediction system) and showed that BHARAT can be effectively used for decision-making. Various hydrological models are used worldwide for developing the rainfall–runoff relation globally. The open-source hydrological models using HEC-HMS can be an effective model for developing the relation between rainfall and runoff (Bhattacharya et al. 2019; Thameemul Hajaj et al. 2019; Hussain et al. 2021; Patel & Yadav 2022). Kantharia et al. (2024) have used a neuro-fuzzy model for rainfall-runoff simulation and focused on the consideration of soil moisture. Panchal & Yadav (2023b) utilized artificial neural network and multiple linear regression methods for runoff prediction, but these methods utilize longer periods of data length. The lumped conceptual hydrologic model using the MIKE 11 NAM model has been used successfully around the globe (Singh et al. (2014); Loliyana & Patel (2015); Kumar et al. 2020; Mohite et al. 2020; Sneha et al. 2020; Teshome et al. (2020); Parvaze et al. 2021; Panchal & Yadav 2023a). The present study pursues two primary objectives: the development of a rain gauge network and an assessment of the applicability of the MADM technique. BHARAT, a recently innovated technique for industrial problem-solving and decision-making, is utilized to select key rain gauges, ensuring reliability in hydrologic applications. In this investigation, the MADM technique BHARAT and the statistical approach of Hall's method have been employed to optimize the design of a rain gauge network tailored for the MTB. The effectiveness of the networks generated by each approach is evaluated using a hydrologic model, and the resulting runoff is compared against observed data.

For the current study, the MTB was selected due to the presence of the major reservoir Ukai, which is prone to flooding-conditions in downstream areas, particularly Surat City. Surat is not only a prominent textile hub in India but also ranks among the country's top smart cities. The Ukai dam, situated across the Tapi River, is the second-largest reservoir in Gujarat after the Sardar Sarovar dam. It serves purposes such as irrigation, flood control, and power generation. It is located 94 km away from Surat within the Tapi basin. The present study focuses on the MTB, spanning from the Hathnur dam to Ukai dam, covering an area of 32,829 km2. The Tapi River, stretching 297 km, flows through the Khandesh Region of Maharashtra in the MTB and contributes to the Ukai reservoir. The Tapi basin receives rainfall from June to September and has faced major floods during the years 1998, 2006, 2013, and 2019. The MTB has been selected for this study due to its history of severe flooding, exacerbated by extreme rainfall over short durations. This situation necessitates rapid decision-making for the operation of the Ukai reservoir. Sudden releases from the reservoir often lead to flooding in downstream areas, including Surat City. Additionally, the basin has an uneven and random distribution of rain gauge stations, which can result in inaccurate runoff estimates. Therefore, developing reliable runoff predictions using the key rain gauge network in the MTB would be invaluable for stakeholders and dam operators. However, the methodology framework developed in this study is applicable to any basin worldwide. Figure 1 displays the map of the study area. To acquire the necessary data, the Shuttle Radar Topography Mission (SRTM) Digital Elevation Model (DEM) of the study area was downloaded from Earth Explorer. Hydro-meteorological data on a daily scale, including daily rainfall, inflows, and evaporation data, were collected for the present analysis. The sources of data collected for the present study are shown in the flow chart of the methodology in Figure 3.
Figure 1

(a) Map of the study area and (b) line diagram of the Tapi River and its major tributaries.

Figure 1

(a) Map of the study area and (b) line diagram of the Tapi River and its major tributaries.

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The purpose of this study is twofold: firstly, to identify and select key rain gauge stations that exhibit overlapping areas, and secondly, to ensure that these selected stations adequately represent a substantial portion of the ungauged basin. The critical selection of these rain gauge stations with overlapping areas is paramount, as it plays a pivotal role in facilitating accurate hydrological modelling within the study area. The rain gauge stations located in the MTB are shown in Table 1. Among all the stations, the stations named Nandurbar and Visarwadi do not have continuous measured rainfall data and the station named Visarwadi was discontinued after the year 1982. Thus, 26 rain gauge stations have been considered for the present study. In line with the IS 4987-1968 guidelines, which recommend one rain gauge station per 520 km2 in flat regions, Figure 2 illustrates the coverage area of each rain gauge station, utilizing ARC GIS 10.3 for analysis. It has been observed that 14 rain gauge stations possess overlapping coverage, while significant sections of the basin remain ungauged. Therefore, careful selection and consideration aim to contribute to more efficient hydrological modelling processes in the basin. Thus, in the present study Hall's approach and applicability of the newly developed MADM technique, BHARAT, is used to design an efficient rain gauge network.
Table 1

List of rain gauge stations in the MTB with their locations

Sr. no.StationsLat.Long.
Akkalkuwa 21.550 74.014 
Amalner 21.050 75.067 
Bhadgaon 20.667 75.233 
Bhusawal 21.044 75.780 
Chalisgaon 20.450 75.017 
Chopda 21.250 75.300 
Dharangaon 21.000 75.000 
Dhule 20.900 74.783 
Erandol 20.933 75.333 
10 Gidhade 21.283 74.800 
11 Jalgaon 21.050 75.560 
12 Jamner 20.817 75.783 
13 Kalvan 20.500 74.033 
14 Malegaon 20.550 74.533 
15 Nandgaon 20.317 74.667 
16 Nandurbar 21.333 74.250 
17 Pachora 20.667 75.367 
18 Pansemal 21.667 74.700 
19 Parola 20.883 75.117 
20 Sagbara 21.550 73.800 
21 Sakri 21.000 74.300 
22 Satna 20.600 74.200 
23 Shahada 21.550 74.467 
24 Shirpur 21.350 74.833 
25 Taloda 21.567 74.217 
26 Uchchhal 21.167 73.750 
27 Visarwadi 21.167 73.967 
28 Yaval 21.167 75.700 
Sr. no.StationsLat.Long.
Akkalkuwa 21.550 74.014 
Amalner 21.050 75.067 
Bhadgaon 20.667 75.233 
Bhusawal 21.044 75.780 
Chalisgaon 20.450 75.017 
Chopda 21.250 75.300 
Dharangaon 21.000 75.000 
Dhule 20.900 74.783 
Erandol 20.933 75.333 
10 Gidhade 21.283 74.800 
11 Jalgaon 21.050 75.560 
12 Jamner 20.817 75.783 
13 Kalvan 20.500 74.033 
14 Malegaon 20.550 74.533 
15 Nandgaon 20.317 74.667 
16 Nandurbar 21.333 74.250 
17 Pachora 20.667 75.367 
18 Pansemal 21.667 74.700 
19 Parola 20.883 75.117 
20 Sagbara 21.550 73.800 
21 Sakri 21.000 74.300 
22 Satna 20.600 74.200 
23 Shahada 21.550 74.467 
24 Shirpur 21.350 74.833 
25 Taloda 21.567 74.217 
26 Uchchhal 21.167 73.750 
27 Visarwadi 21.167 73.967 
28 Yaval 21.167 75.700 
Figure 2

Overlapping rainfall measurement areas by randomly installed rain gauges in the MTB.

Figure 2

Overlapping rainfall measurement areas by randomly installed rain gauges in the MTB.

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Figure 3

Flowchart of the methodology.

Figure 3

Flowchart of the methodology.

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In the present study, rain gauges installed in the MTB have been ranked based on their attributes such as measured rainfall, the elevation of the rain gauge station, the correlation between observed rainfall with areal average storm rainfall and the distance of the rain gauge station from the catchment outlet. The recently innovated MADM technique named BHARAT by Rao (2024b) has been explored to rank the rain gauge stations that can be used effectively for runoff prediction. Another statistical approach by Hall (1972) has been used for the ranking and selection of key rain gauges. The rain gauge network designed by each approach has been evaluated based on the runoff response using the MIKE NAM conceptual model. The study utilizes ten years of continuous daily data on rainfall, discharge, and evaporation to design the rain gauge network. The lumped conceptual hydrologic model has been simulated for a period of seven years (year 2007–2013) and validated for three years (years 2014–2016). The detailed methodology flowchart is shown in Figure 3.

BHARAT

In multi-attribute decision-making methods, each decision table comprises alternatives, attributes, performance measures for each alternative, and the corresponding weights of attributes. Using the information within the decision table and employing the chosen decision-making technique, the decision-maker is tasked with evaluating each alternative to determine the optimal choice. Figure 4 provides the steps involved in the suggested decision-making methodology in the present study. A detailed explanation of the steps can be found in Rao (2024b).
  • Step 1: Define the alternative and the attributes. In the present study, the rain gauges have been considered as the alternatives as the aim of the study is to select the key rain gauge. The measured rainfall, Thiessen areas, correlation between individual measured rainfall and areal average storm rainfall, distance from the outlet and the elevation of the rain gauge stations are considered as the attributes. The attributes' data are shown in Table 2 with the best values of attributes in bold font.

  • Step 2: The attributes need to be weighted as per the rank given by the decision-maker. The weights can be assigned by the ranking given to each attribute by a single decision-maker or a group of decision-makers. In the present study, ranks have been assigned conceptually by a single decision-maker based on the hydrological importance of each attribute as shown in Table 3. Rainfall is the most important attribute to generate the runoff, and thus it has been ranked as 1. The second rank has been given to the Thiessen areas as they have an important effect on the runoff generated at each sub-basin and at the catchment outlet. The correlation between individual measured rainfall and the areal storm rainfall is an important factor at third rank as per its importance in selecting the key rain gauge. The shorter distance to the outlet will lead the runoff to reach the catchment outlet faster. Thus, it has been given a rank of 4 and the elevation of the rain gauge stations has been ranked at 5.

Figure 4

Steps followed for the BHARAT MADM approach.

Figure 4

Steps followed for the BHARAT MADM approach.

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Table 2

Attribute data and the ‘best’ value

AttributesAvg. storm areal rainfallElevation (m)Distance from the outlet (m)Area of Thiessens (km2)Correlation between rainfall measured and avg. areal storm rainfall
 Akkalkuwa 120.23 124 60,307 985.42 0.7395 
 Amalner 54.81 185 207,060 634.77 0.918 
 Bhadgaon 59.57 260 337,553 768.28 0.78 
 Bhusawal 59.55 204 278,731 859.83 0.9 
 Chalisgaon 55.70 340 363,448 1403.90 0.758 
 Chopda 76.75 194 228,167 2045.36 0.888 
 Dharangaon 67.21 226 213,720 471.07 0.902 
Alternatives Dhule 44.63 259 226,600 1,667.19 0.847 
Erandol 68.15 210 260,420 794.19 0.805 
Gidhade 54.54 140 159,081 1,115.13 0.749 
Jalgaon 59.74 198 275,480 798.32 0.282 
Jamner 55.09 253 322,257 2,037.39 0.937 
Kalvan 61.42 597 493,753 1,379.96 0.758 
Malegaon 47.46 431 438,035 1,650.10 0.665 
Nandgaon 46.53 471 439,851 1,500.51 0.482 
Pachora 59.23 260 325,776 1,190.37 0.754 
Pansemal (Toppa) 74.16 241 141,929 1,085.33 0.901 
 Parola 65.63 255 229,607 683.84 0.912 
 Sagbara 118.07 191 44,843 661.12 0.811 
 Sakri 48.79 431 276,165 2,751.13 0.659 
 Satna 53.59 562 477,921 1,493.76 0.772 
 Shahada 64.59 125 112,560 1,462.95 0.891 
 Shirpur 73.91 150 158,885 1,228.20 0.874 
 Taloda 93.13 122 82,503 1,081.77 0.856 
 Uchchhal 91.89 116 16,515 1,570.16 0.597 
 Yaval 72.16 215 273,118 1,515.63 0.844 
AttributesAvg. storm areal rainfallElevation (m)Distance from the outlet (m)Area of Thiessens (km2)Correlation between rainfall measured and avg. areal storm rainfall
 Akkalkuwa 120.23 124 60,307 985.42 0.7395 
 Amalner 54.81 185 207,060 634.77 0.918 
 Bhadgaon 59.57 260 337,553 768.28 0.78 
 Bhusawal 59.55 204 278,731 859.83 0.9 
 Chalisgaon 55.70 340 363,448 1403.90 0.758 
 Chopda 76.75 194 228,167 2045.36 0.888 
 Dharangaon 67.21 226 213,720 471.07 0.902 
Alternatives Dhule 44.63 259 226,600 1,667.19 0.847 
Erandol 68.15 210 260,420 794.19 0.805 
Gidhade 54.54 140 159,081 1,115.13 0.749 
Jalgaon 59.74 198 275,480 798.32 0.282 
Jamner 55.09 253 322,257 2,037.39 0.937 
Kalvan 61.42 597 493,753 1,379.96 0.758 
Malegaon 47.46 431 438,035 1,650.10 0.665 
Nandgaon 46.53 471 439,851 1,500.51 0.482 
Pachora 59.23 260 325,776 1,190.37 0.754 
Pansemal (Toppa) 74.16 241 141,929 1,085.33 0.901 
 Parola 65.63 255 229,607 683.84 0.912 
 Sagbara 118.07 191 44,843 661.12 0.811 
 Sakri 48.79 431 276,165 2,751.13 0.659 
 Satna 53.59 562 477,921 1,493.76 0.772 
 Shahada 64.59 125 112,560 1,462.95 0.891 
 Shirpur 73.91 150 158,885 1,228.20 0.874 
 Taloda 93.13 122 82,503 1,081.77 0.856 
 Uchchhal 91.89 116 16,515 1,570.16 0.597 
 Yaval 72.16 215 273,118 1,515.63 0.844 

Note: the best values of attributes are indicated in bold.

Table 3

Ranks given to the attributes and computed weights

AttributesRanksWeights
Avg. storm areal rainfall 0.31948 
Area of Thiessens (km20.21298 
Correlation between rainfall measured and average storm rainfall 0.17426 
Distance from the outlet (m) 0.15335 
Elevation 0.13991 
AttributesRanksWeights
Avg. storm areal rainfall 0.31948 
Area of Thiessens (km20.21298 
Correlation between rainfall measured and average storm rainfall 0.17426 
Distance from the outlet (m) 0.15335 
Elevation 0.13991 
The weights have been computed by the reciprocal of the reciprocal of ranks assigned divided by the total sum of the weights for each rank. The weights of attributes based on the given rank can be computed by Equation (1):
(1)
  • Step 3: The data of the attributes needs to be normalized in the next step. Standardize the data of each attribute relative to the ‘optimal’ value associated with the attribute for various alternatives. Iterate through this normalization process for all attributes to obtain the standardized data. The term ‘best’ denotes the maximum value for a beneficial attribute and the minimum value for a non-beneficial attribute. In the present work, the attributes rainfall, correlation and elevation are higher as beneficial attributes, as the higher value should be responsible for higher runoff at the outlet. The attribute of the Thiessen area has been considered minimum as the best attribute, as the IS 4987:1994 recommends installing one rain gauge per 520 km2. The shorter distance would lead the runoff to reach the outlet with a shorter lead time. Thus, the distance has been considered minimum as the ‘best’ attribute to rank the key rain gauge. Normalize the performance measures of alternatives xji (for j = 1, 2, …, n; i = 1, 2, …, m). The normalized value (xji) normalized for an alternative link to a beneficial attribute is xji/xi·best, and for a non-beneficial attribute, it is xi·best/xji. Here, xi·best represents the optimal value of the ith attribute. This method of normalizing the data based on the ‘best’ values effectively reveals the relative positions of the alternatives concerning the ‘best’ attribute values. The normalized values of attributes are shown in Table 4.

  • Step 4: Compute the BHARAT score by multiplying the normalized values of the attribute by the weights assigned to each attribute. Compute the total score of alternatives by summing the individual scores of the attributes. Table 5 shows the computed BHARAT score for each alternative. Arrange the scores in descending order. The first 15 ranked rain gauges as shown in Table 6 have been selected in the rain gauge network according to their BHARAT scores.

Table 4

Normalized BHARAT attributes

AttributesAvg. storm areal rainfall (mm)Elevation (m)Distance from the outlet (m)Area of Thiessens (km2)Correlation between rainfall measured and avg. areal storm rainfall
Akkalkuwa 1.000 0.208 0.274 0.478 0.789 
Amalner 0.456 0.310 0.080 0.742 0.980 
Bhadgaon 0.495 0.436 0.049 0.613 0.832 
Bhusawal 0.495 0.342 0.059 0.548 0.961 
Chalisgaon 0.463 0.570 0.045 0.336 0.809 
Chopda 0.638 0.325 0.072 0.230 0.948 
Dharangaon 0.559 0.379 0.077 1.000 0.963 
Dhule 0.371 0.434 0.073 0.283 0.904 
Erandol 0.567 0.352 0.063 0.593 0.859 
Gidhade 0.454 0.235 0.104 0.422 0.799 
Jalgaon 0.497 0.332 0.060 0.590 0.301 
Jamner 0.458 0.424 0.051 0.231 1.000 
Kalvan 0.511 1.000 0.033 0.341 0.809 
Malegaon 0.395 0.722 0.038 0.285 0.710 
Nandgaon 0.387 0.789 0.038 0.314 0.514 
Pachora 0.493 0.436 0.051 0.396 0.805 
Pansemal (Toppa) 0.617 0.404 0.116 0.434 0.962 
Parola 0.546 0.427 0.072 0.689 0.973 
Sagbara 0.982 0.320 0.368 0.713 0.866 
Sakri 0.406 0.722 0.060 0.171 0.703 
Satna 0.446 0.941 0.035 0.315 0.824 
Shahada 0.537 0.209 0.147 0.322 0.951 
Shirpur 0.615 0.251 0.104 0.384 0.933 
Taloda 0.775 0.204 0.200 0.435 0.914 
Uchchhal 0.764 0.194 1.000 0.300 0.637 
Yaval 0.600 0.360 0.060 0.311 0.901 
AttributesAvg. storm areal rainfall (mm)Elevation (m)Distance from the outlet (m)Area of Thiessens (km2)Correlation between rainfall measured and avg. areal storm rainfall
Akkalkuwa 1.000 0.208 0.274 0.478 0.789 
Amalner 0.456 0.310 0.080 0.742 0.980 
Bhadgaon 0.495 0.436 0.049 0.613 0.832 
Bhusawal 0.495 0.342 0.059 0.548 0.961 
Chalisgaon 0.463 0.570 0.045 0.336 0.809 
Chopda 0.638 0.325 0.072 0.230 0.948 
Dharangaon 0.559 0.379 0.077 1.000 0.963 
Dhule 0.371 0.434 0.073 0.283 0.904 
Erandol 0.567 0.352 0.063 0.593 0.859 
Gidhade 0.454 0.235 0.104 0.422 0.799 
Jalgaon 0.497 0.332 0.060 0.590 0.301 
Jamner 0.458 0.424 0.051 0.231 1.000 
Kalvan 0.511 1.000 0.033 0.341 0.809 
Malegaon 0.395 0.722 0.038 0.285 0.710 
Nandgaon 0.387 0.789 0.038 0.314 0.514 
Pachora 0.493 0.436 0.051 0.396 0.805 
Pansemal (Toppa) 0.617 0.404 0.116 0.434 0.962 
Parola 0.546 0.427 0.072 0.689 0.973 
Sagbara 0.982 0.320 0.368 0.713 0.866 
Sakri 0.406 0.722 0.060 0.171 0.703 
Satna 0.446 0.941 0.035 0.315 0.824 
Shahada 0.537 0.209 0.147 0.322 0.951 
Shirpur 0.615 0.251 0.104 0.384 0.933 
Taloda 0.775 0.204 0.200 0.435 0.914 
Uchchhal 0.764 0.194 1.000 0.300 0.637 
Yaval 0.600 0.360 0.060 0.311 0.901 

Note: the best values of attributes are indicated in bold.

Table 5

Computation of BHARAT scores for alternatives

AttributesAvg. storm areal rainfall (mm)Elevation (m)Distance from the outlet (m)Area of Thiessens (km2)Correlation between rainfall measured and avg. areal storm rainfallTotal BHARAT score
Akkalkuwa 0.319 0.029 0.042 0.102 0.138 0.630 
Amalner 0.146 0.043 0.012 0.158 0.171 0.530 
Bhadgaon 0.158 0.061 0.008 0.131 0.145 0.502 
Bhusawal 0.158 0.048 0.009 0.117 0.167 0.499 
Chalisgaon 0.148 0.080 0.007 0.071 0.141 0.447 
Chopda 0.204 0.045 0.011 0.049 0.165 0.475 
Dharangaon 0.179 0.053 0.012 0.213 0.168 0.624 
Dhule 0.119 0.061 0.011 0.060 0.158 0.408 
Erandol 0.181 0.049 0.010 0.126 0.150 0.516 
Gidhade 0.145 0.033 0.016 0.090 0.139 0.423 
Jalgaon 0.159 0.046 0.009 0.126 0.052 0.392 
Jamner 0.146 0.059 0.008 0.049 0.174 0.437 
Kalvan 0.163 0.140 0.005 0.073 0.141 0.522 
Malegaon 0.126 0.101 0.006 0.061 0.124 0.417 
Nandgaon 0.124 0.110 0.006 0.067 0.090 0.396 
Pachora 0.157 0.061 0.008 0.084 0.140 0.451 
Pansemal (Toppa) 0.197 0.056 0.018 0.092 0.168 0.531 
Parola 0.174 0.060 0.011 0.147 0.170 0.561 
Sagbara 0.314 0.045 0.056 0.152 0.151 0.718 
Sakri 0.130 0.101 0.009 0.036 0.123 0.399 
Satna 0.142 0.132 0.005 0.067 0.144 0.490 
Shahada 0.172 0.029 0.023 0.069 0.166 0.458 
Shirpur 0.196 0.035 0.016 0.082 0.163 0.492 
Taloda 0.247 0.029 0.031 0.093 0.159 0.559 
Uchchhal 0.244 0.027 0.153 0.064 0.111 0.600 
Yaval 0.192 0.050 0.009 0.066 0.157 0.475 
AttributesAvg. storm areal rainfall (mm)Elevation (m)Distance from the outlet (m)Area of Thiessens (km2)Correlation between rainfall measured and avg. areal storm rainfallTotal BHARAT score
Akkalkuwa 0.319 0.029 0.042 0.102 0.138 0.630 
Amalner 0.146 0.043 0.012 0.158 0.171 0.530 
Bhadgaon 0.158 0.061 0.008 0.131 0.145 0.502 
Bhusawal 0.158 0.048 0.009 0.117 0.167 0.499 
Chalisgaon 0.148 0.080 0.007 0.071 0.141 0.447 
Chopda 0.204 0.045 0.011 0.049 0.165 0.475 
Dharangaon 0.179 0.053 0.012 0.213 0.168 0.624 
Dhule 0.119 0.061 0.011 0.060 0.158 0.408 
Erandol 0.181 0.049 0.010 0.126 0.150 0.516 
Gidhade 0.145 0.033 0.016 0.090 0.139 0.423 
Jalgaon 0.159 0.046 0.009 0.126 0.052 0.392 
Jamner 0.146 0.059 0.008 0.049 0.174 0.437 
Kalvan 0.163 0.140 0.005 0.073 0.141 0.522 
Malegaon 0.126 0.101 0.006 0.061 0.124 0.417 
Nandgaon 0.124 0.110 0.006 0.067 0.090 0.396 
Pachora 0.157 0.061 0.008 0.084 0.140 0.451 
Pansemal (Toppa) 0.197 0.056 0.018 0.092 0.168 0.531 
Parola 0.174 0.060 0.011 0.147 0.170 0.561 
Sagbara 0.314 0.045 0.056 0.152 0.151 0.718 
Sakri 0.130 0.101 0.009 0.036 0.123 0.399 
Satna 0.142 0.132 0.005 0.067 0.144 0.490 
Shahada 0.172 0.029 0.023 0.069 0.166 0.458 
Shirpur 0.196 0.035 0.016 0.082 0.163 0.492 
Taloda 0.247 0.029 0.031 0.093 0.159 0.559 
Uchchhal 0.244 0.027 0.153 0.064 0.111 0.600 
Yaval 0.192 0.050 0.009 0.066 0.157 0.475 
Table 6

Rain gauges selected by BHARAT

AttributesBHARAT scoreRank
Sagbara 0.71756 
Akkalkuwa 0.62987 
Dharangaon 0.62413 
Uchchhal 0.59962 
Parola 0.56149 
Taloda 0.55869 
Pansemal (Toppa) 0.53137 
Amalner 0.53000 
Kalvan 0.52192 
Erandol 0.51607 10 
Bhadgaon 0.50237 11 
Bhusawal 0.49918 12 
Shirpur 0.49173 13 
Satna 0.49015 14 
Chopda 0.47471 15 
AttributesBHARAT scoreRank
Sagbara 0.71756 
Akkalkuwa 0.62987 
Dharangaon 0.62413 
Uchchhal 0.59962 
Parola 0.56149 
Taloda 0.55869 
Pansemal (Toppa) 0.53137 
Amalner 0.53000 
Kalvan 0.52192 
Erandol 0.51607 10 
Bhadgaon 0.50237 11 
Bhusawal 0.49918 12 
Shirpur 0.49173 13 
Satna 0.49015 14 
Chopda 0.47471 15 
The basin consists of 26 rain gauges amongst which 15 rain gauges have been selected which have been ranked higher by BHARAT. The optimum number of rain gauges recommended by IS 4987:1994 is nine for the MTB. For comparison of the performance of the rain gauges to that of those selected by Hall's approach, 15 rain gauges have been selected. The rain gauges selected using BHARAT have been placed on the map and based on the location of the rain gauge stations, the Thiessens have been generated and are shown in Figure 5. The weighted rainfall time-series with the Thiessen weights has been used as an input to the MIKE NAM conceptual model. The runoff has been predicted at catchment outlet Ukai. The runoff generated by the Bharat network has been compared with the observed runoff and is shown in the hydrographs in Figure 8 and the scatter plot in Figure 9.
Figure 5

Thiessens generated for the rain gauge network designed by BHARAT.

Figure 5

Thiessens generated for the rain gauge network designed by BHARAT.

Close modal

Hall's method

In 1972, Hall introduced an effective method to identify the key station network, a vital step in establishing the best rain gauge network. The process involves computing correlation coefficients between average storm rainfall and individual station recordings. These coefficients are then ranked in descending order, with the station showing the highest correlation becoming the first key station. After excluding this station's data, the process repeats to find the second key station, using the next set of correlation coefficients. This iterative method gradually expands the key station network. At each stage, the overall variance is analyzed to assess the network's performance. Incorporating more rain gauges increases the multiple correlation coefficient while decreasing the sum of squared deviations. Eventually, a saturation point is reached where further improvements in either coefficient or deviation sum become negligible. In this study, the number of rain gauges in the representative network is considered optimal for estimating areal rainfall, following Hall's approach (Kar et al. 2015).

After scrutinizing a decade's worth of daily rainfall data for the monsoon period from July to August of 26 rain gauge stations, significant rain gauges have been pinpointed. The correlation coefficient between the average storm rainfall and the rainfall recorded at each station has been calculated and ranked in descending order. The station exhibiting the highest correlation coefficient is identified as the primary key station, and its data are excluded from the dataset. This process is reiterated to ascertain subsequent key rain gauge stations, with each cycle selecting the station showing the highest correlation coefficient, as depicted in Table 7. Notably, Jamner station displayed the highest correlation, while Satna exhibited the lowest. To assess the key station network, the root mean square error (RMSE) was calculated between each station and the average storm rainfall of the group. The RMSE values were analyzed as additional stations were incorporated into the key station network. Figure 6 illustrates the relationship between the number of stations and their corresponding RMSE values. This represents how the RMSE is decreased by adding the selected key rain gauges into the rain gauge network. The rain gauge station is removed from the network if it increases the RMSE. Thus, from the rain gauge network of 26 rain gauges, 15 key rain gauges have been selected by Hall's approach.
Table 7

Prioritized sequence of rain gauges by Hall's method

Sr.no.Stations at the prioritized sequenceCorrelations for prioritized sequence
Jamner 0.878 
Amalner 0.846 
Parola 0.828 
Pansemal 0.818 
Dharangaon 0.810 
Shahada 0.805 
Bhusawal 0.786 
Shirpur 0.769 
Taloda 0.748 
10 Dhule 0.743 
11 Chopda 0.738 
12 Sagbara 0.693 
13 Bhadgaon 0.673 
14 Kalvan 0.655 
15 Yaval 0.673 
16 Akkalkuwa 0.648 
17 Sakri 0.629 
18 Chalisgaon 0.635 
19 Malegaon 0.620 
20 Pachora 0.592 
21 Erandol 0.497 
22 Uchchhal 0.696 
23 Gidhade 0.552 
24 Nandgaon 0.595 
25 Jalgaon 0.534 
26 Satna 0.432 
Sr.no.Stations at the prioritized sequenceCorrelations for prioritized sequence
Jamner 0.878 
Amalner 0.846 
Parola 0.828 
Pansemal 0.818 
Dharangaon 0.810 
Shahada 0.805 
Bhusawal 0.786 
Shirpur 0.769 
Taloda 0.748 
10 Dhule 0.743 
11 Chopda 0.738 
12 Sagbara 0.693 
13 Bhadgaon 0.673 
14 Kalvan 0.655 
15 Yaval 0.673 
16 Akkalkuwa 0.648 
17 Sakri 0.629 
18 Chalisgaon 0.635 
19 Malegaon 0.620 
20 Pachora 0.592 
21 Erandol 0.497 
22 Uchchhal 0.696 
23 Gidhade 0.552 
24 Nandgaon 0.595 
25 Jalgaon 0.534 
26 Satna 0.432 
Figure 6

Plot of RMSE with number of rain gauges.

Figure 6

Plot of RMSE with number of rain gauges.

Close modal
The key rain gauges selected by Hall's method are listed in Table 8 and have been considered as the Hall's rain gauge network and the Thiessens have been generated based on the location of the key rain gauges. The Thiessen polygons for Hall's network are shown in Figure 7 and the weighted time-series of rainfall according to the Thiessen weights have been computed to use as input to the hydrologic model.
Table 8

Rain gauges selected by Hall's method

Sr. no.Station name
Jamner 
Amalner 
Parola 
Pansemal 
Dharangaon 
Shahada 
Taloda 
Dhule 
Kalvan 
10 Malegaon 
11 Pachora 
12 Erandol 
13 Gidhade 
14 Nandgaon 
15 Jalgaon 
Sr. no.Station name
Jamner 
Amalner 
Parola 
Pansemal 
Dharangaon 
Shahada 
Taloda 
Dhule 
Kalvan 
10 Malegaon 
11 Pachora 
12 Erandol 
13 Gidhade 
14 Nandgaon 
15 Jalgaon 
Figure 7

Thiessens generated for rain gauge network designed by Hall's method.

Figure 7

Thiessens generated for rain gauge network designed by Hall's method.

Close modal
Figure 8

Hydrographs of observed vs simulated discharge by BHARAT's and Hall's rain gauge networks.

Figure 8

Hydrographs of observed vs simulated discharge by BHARAT's and Hall's rain gauge networks.

Close modal
Figure 9

Scatter plot of observed vs simulated discharge for BHARAT's and Hall's rain gauge networks.

Figure 9

Scatter plot of observed vs simulated discharge for BHARAT's and Hall's rain gauge networks.

Close modal

The lumped conceptual rainfall–runoff model

A fully lumped model simplifies the representation of a catchment by using a single, spatially averaged value for each input variable and model parameter across the entire area. However, there are a few limitations of the lumped model. While inputs like precipitation may naturally vary across the catchment, the lumped model assumes a uniform value – such as an areal average – at each time-step. Likewise, despite the catchment having varied land-cover types (such as forests, croplands, and urban areas) with distinct hydrological properties like infiltration and runoff, the model consolidates these differences into one average value for each property. In the present study, the hydrologic model has been employed exclusively to validate the designed rain gauge network. In this study, it is used specifically to assess the effectiveness of the designed network. For more accurate and appropriate results, especially given the basin's characteristics, key rain gauges could be modelled using a semi-distributed or distributed hydrologic model. However, the focus is on recommending rain gauge network optimization techniques, and to evaluate the rain gauge network, the use of the lumped conceptual model is deemed appropriate. The MIKE 11-NAM rainfall–runoff model has gained significant usage across various Asian countries due to its advantages, such as low data-requirements, satisfactory performance, and a straightforward structure. Nevertheless, the process of calibrating the model parameters for this hydrological model can prove to be time-consuming and challenging when employing manual calibration methods. The MIKE 11-NAM model operates through a lumped conceptual approach, treating each sub-catchment area as a uniform unit. These elements represent average values for the entire sub-catchment and encompass water storage in four interconnected forms: snow, overland flow, interflow, and baseflow. The model utilizes a linear reservoir framework to depict these storage forms. In evaluating the rain gauge network's efficacy as designed by each method, the MIKE NAM conceptual model has been developed. This model leverages time-series data of rainfall, evaporation, and observed discharge to gauge the rain gauge network's performance. The hydrologic model has been developed for the period from 1 January 2007 to 31 December 2013 having daily rainfall, in which flood was observed on 23 September 2013 at Ukai. Utilizing data from the results of BHARAT and Hall's method, Thiessens have been created, and weighted factors have been derived. These weighted factors have been employed to generate the weighted time-series of rainfall, subsequently used as input for the MIKE NAM model. The calibrated model parameters of MIKE NAM are shown in Table 9. The developed hydrologic model is helpful in evaluating the performance of both the rain gauge networks.

Table 9

Calibrated parameter values of the NAM model

Sr. no.Model parameterCalibrated value
Maximum water content in surface storage (Umax14.7 
Maximum water content in root zone storage (Lmax161 
Overland flow runoff coefficient (CQOF) 0.721 
The time constant for routing interflow (CKIF) 223.9 
Time constant for routing overflow flow (CK1,2) 35.3 
Root zone threshold value for overland flow (TOF) 0.08 
Root zone threshold value for interflow (TIF) 0.121 
Root zone threshold value for GW recharge (TG) 0.536 
Time constant for routing baseflow (CKBF) 2,957 
Sr. no.Model parameterCalibrated value
Maximum water content in surface storage (Umax14.7 
Maximum water content in root zone storage (Lmax161 
Overland flow runoff coefficient (CQOF) 0.721 
The time constant for routing interflow (CKIF) 223.9 
Time constant for routing overflow flow (CK1,2) 35.3 
Root zone threshold value for overland flow (TOF) 0.08 
Root zone threshold value for interflow (TIF) 0.121 
Root zone threshold value for GW recharge (TG) 0.536 
Time constant for routing baseflow (CKBF) 2,957 

Comparison of the rain gauge network designed by BHARAT and Hall's method

The rainfall measured by the rain gauge stations selected by BHARAT and Hall's method, as listed in Table 6 and Table 8, have been modelled in the MIKE NAM for seven years of continuous daily data from 2007 to 2013. Here, two independent hydrologic models are simulated using rainfall data from rain gauges selected using BHARAT (Table 6) and Hall's approach (Table 8). The developed hydrologic model has been validated for the data for three years, from 2014 to 2016. The runoff generated by the designed rain gauge networks has been compared with the observed runoff data to evaluate the model performance. Figure 8 shows the observed and simulated runoff for BHARAT's and Hall's network. The scatter plot as shown in Figure 9 has been generated to check the correlation between the observed and simulated discharge for the calibration period. The statistical performance measures have been computed to check the accuracy of both the rain gauge networks. It is observed that the models simulated for Hall's network as well as BHARAT's network have performed fairly well and can be said to be reliable.

The model has been validated for three years from year 2014 to year 2016 and the scatter plot and hydrograph between observed and simulated runoff for the validation period are shown in Figure 10. The results show good agreement between observed and simulated runoff for BHARAT's rain gauge network as compared with Hall's network.
Figure 10

Scatter plot and hydrographs for observed and simulated runoff by Hall's network and BHARAT's network.

Figure 10

Scatter plot and hydrographs for observed and simulated runoff by Hall's network and BHARAT's network.

Close modal

Table 10 presents the computed performance measures, with comparisons revealing that BHARAT's network outperforms Hall's. Correlation coefficients, Nash–Sutcliffe efficiency (NSE), and index of agreement (d) show higher values for BHARAT's network. BHARAT's method demonstrates reasonably good results for the hydrologic model, validating its efficiency in evaluating the rain gauge network. The validation period's outcomes also demonstrate strong performance, showing good alignment between observed and simulated runoff for both rain gauge networks designed by BHARAT and Hall's method.

Table 10

Statistical performance measures

Calibration (2007–2013)
Validation (2014–2016)
Statistical parametersBHARATHallBHARATHall
Correlation coefficient  0.890 0.732 0.873 0.788 
Pearson's correlation coefficient 0.943 0.856 0.934 0.888 
NRMSE  1.397 1.979 1.402 1.858 
NSE  0.886 0.732 0.870 0.772 
d  0.968 0.915 0.966 0.940 
Calibration (2007–2013)
Validation (2014–2016)
Statistical parametersBHARATHallBHARATHall
Correlation coefficient  0.890 0.732 0.873 0.788 
Pearson's correlation coefficient 0.943 0.856 0.934 0.888 
NRMSE  1.397 1.979 1.402 1.858 
NSE  0.886 0.732 0.870 0.772 
d  0.968 0.915 0.966 0.940 

Efficient rain gauge network design is the most important aspect for river basins which have randomly installed rain gauges in the basin or when basins are ungauged or partially gauged. Tekleyohannes et al. (2021) have used MCDA (multi-criteria decision analysis) combined with kriging and entropy for designing an optimized rain gauge network for the Tekeze River of Ethiopia and revealed that leveraging a combination of MCDA, kriging, and entropy methods proves beneficial in optimizing both the spatial distribution and the appropriate count of rain gauge stations within a given basin. Kar et al. (2015) utilized the HC clustering method to identify crucial rain gauge stations, forming two clusters, each with seven rain gauges. Notably, the unequal distribution of rain gauges within clusters underscores the flexibility of this approach, acknowledging the influence of basin characteristics and rainfall patterns. It is crucial to recognize that the applicability of clustering methods may not be universal across basins due to inherent variations. The AHP was used for designing the optimal rain gauge network by Kar et al. (2015). However, AHP demands extensive surveys and expert opinions, making it time-consuming. Traditional methods like Hall's approach rank rain gauges based solely on measured rainfall, overlooking other factors that can influence the importance of different gauges. Our proposed MADM approach, named BHARAT, addresses these limitations by considering multiple attributes in the ranking process. However, it is crucial to apply domain knowledge and expertise when selecting and weighing these attributes and alternatives in the BHARAT method. The ranking of attributes should be informed by the expertise of the subject matter to ensure accurate and relevant results. The resulting runoff from BHARAT demonstrates a commendable correlation with observed runoff, showcasing its reliability. The innovative application of BHARAT in this study not only addresses the limitations of traditional methods but also offers a more efficient and adaptable solution for rain gauge network optimization. This advancement is of global significance for hydrologists and researchers, providing a robust methodology that minimizes the drawbacks of traditional approaches. The proposed framework recommends designing a key rain gauge network for the basin to streamline runoff and flood prediction during emergencies. This approach is particularly useful when it is not feasible to collect data from all installed rain gauges, or when time constraints make it impractical to use data from every station. By focusing on these strategically selected key rain gauges, the framework allows for reliable runoff estimates without taking excessive time for modelling that involves all available rain gauge data. This framework will help timely forecasting of floods which eventually help local authorities to take mitigation measures. The study's findings contribute to the global hydrological community by presenting a novel framework that can be tailored to diverse basin characteristics, enhancing the precision of runoff predictions and advancing the field of hydrological modelling on a broader scale.

In the MTB, India, the existing network of 26 rain gauges is distributed randomly, which often leads to overlapping measurements and inefficiencies in streamflow forecasting. Identifying key rain gauges is critical to optimize this network, improve data utility and enhance runoff predictions. The present study applies Hall's method and the BHARAT MADM technique to address this challenge. Hall's method focused solely on rainfall data, identifying key gauges based on statistical importance. However, it lacked the flexibility to consider other hydrological factors influencing runoff, limiting its applicability in comprehensive flood forecasting scenarios. In contrast, the BHARAT MADM technique, originally developed for industrial applications, was applied as a novel approach to hydrological problem-solving. By incorporating multiple parameters such as upstream runoff, rainfall variability, and spatial distribution, BHARAT enabled a more informed selection of rain gauges. Optimization using BHARAT resulted in a streamlined rain gauge network that significantly enhanced the accuracy of hydrologic models. Performance evaluation showed a 29.4% reduction in NRMSE during calibration and a 24.5% reduction during validation, demonstrating the superiority of the BHARAT-based network over Hall's method. These results emphasize BHARAT's ability to provide a more comprehensive framework for rain gauge selection, contributing to more efficient and reliable flood forecasting. The applicability of the BHARAT MADM approach is an important and valuable tool for decision-makers and hydrologists. Prioritizing strategically selected rain gauges avoids overloading hydrologic models with redundant data while maintaining accuracy.

Future work may focus on the real-time operational flood forecasting system with the integration of the BHARAT MADM technique. This can be tested for other hydrologic basins having varying climatic conditions, LULC patterns and changing rainfall patterns to validate the broader applicability of both approaches. The incorporation of real-time remote-sensing and satellite data sets could further enhance the reliability and precision of the designed rain gauge network and hydrologic model. This could ensure that the flood control and streamflow forecasting strategies remain robust and reliable.

This research did not receive any specific grant from funding agencies in the public, commercial, or not-for-profit sectors.

A.P. contributed to data curation, writing – original draft preparation, software, validation, editing. S.M.Y. contributed to visualization, conceptualization, supervision, and review.

Data cannot be made publicly available; readers should contact the corresponding author for details.

The authors declare there is no conflict.

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