India's diverse geography presents significant flood risks, analyzed in this study using geographic information systems and multi-criteria decision analysis. This comprehensive flood risk assessment considers seven parameters: mean annual precipitation, elevation, slope, drainage density (DD), land use and land cover, proximity to roads, and distance to rivers. The findings indicate that flood vulnerability is primarily influenced by rainfall, elevation, and slope, with DD, land use, and proximity to roads and rivers also playing crucial roles. Experts weighed these factors to create a thorough flood risk map using the normalized rank index and normalized weight index, categorizing areas into five risk levels: very high, high, moderate, low, and very low. The study reveals that 3.40% of the area is at very high risk, 32.65% at high risk, 39.72% at moderate risk, 20.97% at low risk, and 3.25% at very low risk. These results highlight how human and natural factors interact to influence flood risk, with vulnerable areas characterized by low elevations, steep slopes, high drainage densities, and proximity to rivers or roads. The findings provide valuable insights for policymakers, scientists, and local authorities to develop strategies to mitigate flood losses across India's varied landscapes.

  • Integration of geographic information systems and multi-criteria decision analysis helps in comprehensive flood risk mapping.

  • A comprehensive analysis of multi-factor influences on flood risk is presented.

  • High-risk zones are identified with practical implications.

  • A significant contribution is made towards flood risk management in monsoon-influenced regions.

Flood risk assessment is a critical aspect of catastrophe management and resilience that usually involves several spatial and analytic techniques. Being a big, diverse country, India has suffered terrible floods before (Dhiman et al. 2019; Kedam et al. 2024). Climate change, rapid urbanization, land-use planning deficiency, and other factors exacerbate these natural disasters (Zhao et al. 2024). Together these factors amount to flood hazard assessment and mitigation (Aerts et al. 2018). The use of the geographic information system (GIS) and multi-criteria decision analysis (MCDA) technologies helps provide comprehensive data on flooding risks and can serve as a solid base for detailed flood risk maps throughout the world (Elkhrachy et al. 2023; Wei et al. 2023). Flooding in India comes with a wide scale of effects including a great number of casualties, damage to crucial services, and disturbance of livelihoods and communities (Mukherjee et al. 2023). Integration of GIS and MCDA, however critical, should be recognized considering the catastrophic effects of such disasters (Solanki et al. 2024). An all-embracing strategy involving these components would enable decision makers to identify vulnerability points and prepare mitigation strategies early to reduce risk exposure and consequently make India more resistant to such flood disasters (Afsari et al. 2022; Kumar 2024).

Many of these studies point to evidence that GIS, remote sensing, and other methodical tools are essential in identifying flood risk and vulnerability. According to Radwan et al. (2019), GIS and remote sensing techniques (RST) are instrumental in dry land risk assessment. Therefore, this proves why digital elevation models (DEMs), soil maps, and historical rainfall data should be utilized in various Regional Development Plans (RDPs). The findings indicate that RST and GIS will be effective tools in reducing flood risk as well as minimizing runoff and rainwater harvesting. Using GIS remotely sensed data, Saha & Agrawal 2020 have worked towards pre-flood assessment for the detection of prior floods and land use and land cover (LULC) classification analysis. Ghosh & Kar (2018) studied the flood risk in the lowest Gangetic basin, and particularly the Malda division of West Bengal. Compound hazard and vulnerability indices were used in conjunction with the analytical hierarchy process (AHP) to obtain a flooding risk map. In addition, the study shows that flood vulnerability is greatest in the north and west component of the district. Using the MCDA and AHP, Gupta & Dixit (2022) examine the flood risks in flood-prone areas of Assam, India. This includes several types of factors, namely, land use, meteorology, geology, and topography. The analysis of the results illustrates that the majority of the regions experience moderate to very high flood risk levels.

Tomar et al. (2021) propose a holistic system involving remote sensing, GIS, and field survey techniques for identifying flood-prone urban districts. This paper presents an innovative approach to the problem of an inefficient urban drainage system in the Yamuna River National Capital Territory of Delhi, India. This provides guidance for preparedness in anticipation of future flooding incidents and improves the understanding of what gives rise to more than the usual incidences of flooding. Matheswaran et al. (2019) extend their methods in determining flood risk in the South Asian region through clustering algorithms and multi-temporal remote sensing data for identifying flood centres or hot spots. This research also identifies potential pilot zones for flood index insurance products. However, a recent study by Ha et al. (2023) can provide insight into the analysis of flood risk in the Quang Binh province of Vietnam using the integrated machine learning (ML)-AHP framework. However, AHP plays a role in incorporating vulnerability factors, while ML models are used to make the flood hazard map. An outcome is a detailed flood risk map pinpointing variation zones. Hagos et al. (2022) focus on the Teji watershed, a rain-fed area that is prone to flooding. The research looks at data from soil, slope, elevation, drainage density (DD), and land use to estimate the flood risk. Such results feed into early warning mechanisms and flood prediction with respect to highly endangered and catastrophic zones for riverine floods.

Skakun et al. (2014) describe a novel approach to mapping flooding risks and hazards using time-series satellite images. This is an effective way of assessing flood risks when there are many uncertainties coupled with data deficiency. The above research demonstrates its use in Namibia's Katima Mulilo region. The study of Ahmed et al. (2022), conversely, presents a multi-criteria approach to mapping flood risk that considers mitigating capacities. As such, the research presents a holistic analysis of flood risk that incorporates several elements, such as hazards, susceptibilities, and mitigations. It seems that mitigation measures can be incorporated into flood risk management. Vojinovic et al. (2016) outlined a comprehensive methodology of flood risk assessment considering both quantitative and subjective factors. In other words, this method could also be used together with the conventional hazard assessment indicators as well as the community perception of risk. Baky et al. (2020) propose a different approach that encompasses the use of flood hazard and vulnerability index for flood risk assessment. Accordingly, the issue of risks implies paying attention to risk and its susceptibility in the assessment process. This also emphasizes the need for the use of GIS remote sensing as well as many other analytical tools in flood risk assessment.

India is a vast country that encompasses different ecologies ranging from sub-Himalayas to coastal lands, making flood management very challenging (Roy et al. 2021). Thus, monsoon, cyclone, and river morphology generate unique flood risk maps consisting of different areas across the whole territory. Therefore, the use of sophisticated geospatial technologies such as GIS with MCDA's ability to process decisions becomes crucial in understanding and handling the multiple causes leading to flood risks in this big country (Levy et al. 2007). This study thoroughly examines how integrating GIS and MCDA can be applied in flood hazard mapping and evaluation in India. Data collection is the first step in the process and involves gathering a variety of data. Soil types, land-use classification, topographical characteristics, rainfall patterns, river-flow data, and a myriad of meteorological and hydrology indicators are included in the list. For a good foundation towards flood hazard assessment, such a large amount of data is important. The next step in GIS is integrating various datasets into one coherent structure of information at one geographical point. With GIS technology spatial layers that contain data about elevation models, hydrologic features, land use, and other important data become possible (Zhou et al. 2023). They form an essential basis for subsequent study. Hazard modelling in GIS involves the use of mathematical algorithms that are employed in determining possible flood occurrences. These models comprise some parameters that assist in determining locations expected to be hit by floods such as rainfall intensity, geography, and river flows. This leads to the creation of a flood risk map indicating the susceptible spots. Vulnerability assessment represents the subsequent important step, and through MCDA analyses the susceptibility of different elements is exposed. This also includes infrastructure, ecosystems, and natural cultures besides humans. Susceptibility can also be with respect to population density, building materials, and proximity to essential facilities (Karymbalis et al. 2021; Yin et al. 2023).

In this process, each of the criteria in MCDA is assigned a score according to its importance. For instance, while reviewing the vulnerability of a location, population density could be weighed higher than transport infrastructure. The objective of developing a comprehensive vulnerability map is to show the specific areas and resources at risk of flooding. The basic element in this technique is overlay analysis that combines the GIS with MCDA to add the hazard-vulnerability layers (Nyimbili et al. 2018; Chen 2022). Through this procedure, hazardous areas together with vulnerable areas are grouped to form risky zones. In these locations, flood is expected to hit with the most intensity. These efforts build up to a risk assessment that determines total flood risk in different areas by integrating findings from hazard and vulnerability studies. This is risk assessment, upon which making informed decisions and prioritizing approaches for risk management can rely. The results produce the flood hazard mapping, which shows different levels of flood risk in the study area. These maps are essential for planning land use, emergency responses, and disaster preparation. This general approach has quite an impact. Using GIS and MCDA to determine high-risk zones helps prioritize adaptation versus mitigation for improving resilience to recurrent flood events in India. Additionally, sharing the flooding risk map is key to increasing public awareness and promoting community preparedness. Providing actionable information helps mitigate catastrophes and creates a sense of collective responsibility in tackling communal challenges.

Objectives of the study

The objectives of this study are to locate areas vulnerable to floods across India, estimate flooding threats, evaluate the susceptibility of communities and facilities to destruction by water, and rank precautions worth undertaking against flood risks. Supporting sustainable development, raising awareness, and developing the capacity to mitigate risks are the demonstrations of the applications of the GIS–MCDA approach. These objectives hope to increase India's disaster preparedness and resilience and thereby lessen the effects of flooding on people and property.

India is truly a special place that is blessed with different kinds of topographies such as rivers, mountains, valleys, plateaus, seas, deserts, and plains. India is situated towards the northern part of the Equator. It has an outstanding coastline that stretches for 7,517 km with a coastal perimeter of 5,423 km along the Peninsular Indian region and 2,094 km across the Andaman, Nicobar, and Lakshadweep Island chain. India is ranked the 7th largest nation in the world and has an area of 3,287,263 km2. In turn, this varied landscape spreads out into different areas, namely, plains, highlands, the southern peninsula, and deserts. The Himalayan Mountains embrace the northern part of India. India is made up of four huge regions, each exhibiting distinct natural features. The eastern and central part of the country, known as the Indo-Gangetic plain, dominates with its products and nutrients. Southwards, India is characterized by the prominent coastal ranges of the Western Ghats and the Eastern Ghats, each making a strong topographical statement. Also, the Aravalli and Vindhyachal Mountain Ranges make this combination of India's striking geographical features even more fascinating.

India is bordered by countries such as Afghanistan, Pakistan, Nepal, Bhutan, China, Myanmar, and Bangladesh. The international borders help enhance India's cultural and physical diversities, which makes for a distinct national image. However, amidst this scenic tapestry, India faces a significant challenge: flooding. Approximately 12.5% of the country's land is prone to flooding, making it the second most flood-affected nation globally, after Bangladesh. The flood season spans about four months, from June to the end of September, contributing nearly three-quarters of India's annual rainfall. Floods affect approximately 40 million hectares annually, with damages impacting over 3.6 million hectares of cultivated land on average.

India's topography ranges from the Himalayan Mountain range in the north to coastal plains in the south, with plateaus, deserts, and river valleys in between. Each of these regions has unique characteristics that influence climate, agriculture, population distribution, and development. India experiences a wide range of climatic conditions, from tropical in the south to temperate and alpine in the north. This variability affects agriculture, water resources, and habitation patterns. Human development indicators such as literacy, income, health, and infrastructure vary widely across states and even within states. Urban areas typically have higher development indices compared to rural areas.

In northern and northeastern India lie the Brahmaputra, Ganga, and Meghna River basins, which are among the areas most prone to floods. One major cause of floods includes excess rain that exceeds the capacity of rivers to receive downstream flow. However, the effect of poor drainage characteristics, excessive irrigation, rising water table caused by canal seepage, erosion, silt deposition in riverbeds, alteration in river courses, and barring of the flow of a river intensify this problem. Over time as the population grows and as more cities are developed, adding on to the existing ones, they occupy the floodplains making the situation worse with each passing day. Second, because of uneven rain distribution, floods that may appear as normal can become intense and occur even in places that do not usually face this kind of disaster. This leads to flooding being the most common natural hazard in India that manifests itself in several guises such as overflowing of riversides or waterlogging due to insufficient sewerage systems as well as the process of the eroded watershed and changed courses of rivers. Therefore, it is necessary to comprehend the intricate links between geographical issues and climatic variables that continue to pose serious challenges in Indian flood assessments and mapping for effective preparation against these disasters. Figure 1 shows the geographic location map of the study area.
Figure 1

Geographic location map of the study area.

Figure 1

Geographic location map of the study area.

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Flood susceptibility parameter

This section outlines the parameters used for flood susceptibility analysis: elevation, slope, drainage density, distance to roads, distance to rivers, rainfall, and land use/land cover. Each parameter is crucial in determining flood risk:

  • (a) Elevation: Lower elevations are more flood prone.

  • (b) Slope: Flat areas retain water longer, increasing flood risk.

  • (c) Drainage Density (DD): Higher DD leads to more surface runoff and greater flood risk.

  • (d) Distance to Roads: Roads can block water flow, heightening nearby flood risks.

  • (e) Distance to Rivers: Areas closer to rivers are more vulnerable to flooding.

  • (f) Rainfall: Higher rainfall contributes to increased runoff and flooding.

  • (g) Land Use/Land Cover (LULC): Impervious urban surfaces amplify runoff, while vegetation reduces it.

The following list provides data sources and methods used to quantify these parameters for GIS-based flood risk mapping.

The integration of GIS with MCDA represents a valuable approach for mapping flood risk and hazard zones within river basins. This strategy is very useful for designing flood control plans in remote communities and estimating the risk of populations living in these locations. The major goal of this research is to assess the spatial extent of flood danger zones in India and to identify communities at high risk during flood occurrences. For example, the MCDA approach is applied to define flood-prone areas, while the GIS overlay studies identify the settlements susceptible to flooding. The methodology considers seven essential spatial parameters: distance from rivers, proximity to the roads, LULC, slope, elevation, DD, and annual average rainfall. These findings identify such risky locations prone to flood hazards, providing significant data for policymaking, scientific research, and local administration to act in time and reduce overall losses.

The most important part of this research work was making the zonation map based upon several significant factors. Satellite imagery formed the primary data source. However, some supplementary data came from different maps issued by various government offices and departments. The data were subjected to extensive pre-processing before analysis. Later, these pre-prepared data layers were carefully included in a geo-database with respect to the GCS_WGS_1983 reference system. LULC maps were key data elements that were meticulously extracted from high-quality satellite images. The National Aeronautics and Space Administration (NASA) Shuttle Radar Topography Mission (SRTM) image provided a precise contour map marked out every 20 m for producing DEMs and slope maps. The rainfall distribution map for the specific region is based on Indian Meteorological Department data and this process is called inverse distance weighted interpolation.

The assessment of each element by the degree of importance towards flood generation was carried out with the aid of these maps at hand. The ones that had higher implications on flooding received higher ratings. These data layers were incorporated with the help of the weighted overlay analysis method in GIS. However, this resulted in the full-fledged development of a result map that depicts all the complicated links between the factors that trigger flood risk. Figure 2 shows the framework of the methodology. An important challenge in multi-criteria evaluation relates to the aggregation of information from multiple dimensions into a single assessment index. For this project, a set of base maps and images were developed for enhancing data assimilation, processing, and GIS activities. There was a lot of preliminary preparation involved in this analysis. This included data collection, extraction, transformation, geo-referencing, reclassification, and resampling. The field surveys and literature studies identified some contributing factors to floods, which included slope, elevation, DD, proximity to rivers and roads, average rainfall, and land usage considerations in flood hazard assessments.
Figure 2

Methodology flowchart.

Figure 2

Methodology flowchart.

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Weighted sum method

The weighted sum method is a mathematical methodology that is utilized in a variety of domains, including statistics, finance, decision analysis, and optimization (Bhosekar & Ierapetritou 2018; Yadav et al. 2018). Calculating a weighted average or sum of a group of variables entails multiplying each value by a given weight. The weights are assigned to the values to represent their respective relevance in the overall computation. This strategy is especially beneficial when dealing with various criteria or data points with varying degrees of relevance. The formula for computing the weighted sum is written as follows:
(1)
where ‘Weighted Sum’ is the computation's result, while ‘’ denote the assigned weights for the diverse values and ‘’ are the weighted values. This involves the multiplication of each value with its corresponding weight and their summation to determine the weighted total.

The selection of flood susceptibility parameters in this study is grounded in a comprehensive analysis of factors that significantly influence flood risk, supported by empirical evidence, literature reviews, and expert consultations. Topographical features such as elevation and slope are critical as they determine water flow and accumulation, with low-lying and flat areas being more prone to prolonged inundation. Climate factors, particularly average annual rainfall, are primary drivers of flooding, influencing the volume of surface runoff. Soil characteristics, represented by DD, help in understanding how quickly water is transported away from an area, impacting flood susceptibility. LULC data are essential to assess the influence of different land covers on water absorption and runoff, where urban areas typically exhibit higher runoff due to impervious surfaces. Additionally, infrastructure and socioeconomic factors, such as proximity to roads and rivers, are crucial as they can obstruct natural water flow, increase runoff, and indicate areas more susceptible to flooding due to river overflows. These parameters were integrated using GIS and MCDA to ensure a holistic and accurate flood susceptibility assessment, encompassing physical, climatic, and anthropogenic factors that contribute to flood risk.

Average annual rainfall

The average yearly rainfall for a certain region from 2018 to 2022 is shown on the graph in Figure 3. Rainfall in this area ranges from 225.47 to 3,187.6 mm/year, with the northwestern to the northeastern regions receiving most of the precipitation. Notably, the likelihood of flooding rises with rainfall. Figure 3 divides the average annual rainfall in the research region into five categories: very low (225.45–701.74), low (701.75–1,073.5 mm), medium (1,073.6–1,480 mm), high (1,480.1–2,107.3 mm), and very high (2,107.4–3,187.6 mm). But it is crucial to take this region's geography into account. It is distinguished by its height and steep hills. The middle and downstream regions feature very level topography, fairly moderate slopes, and insufficient drainage systems, despite somewhat heavier rainfall upstream. As such, these geomorphic features partially overwhelm the effect of rainfall on flood dangers.
Figure 3

Average annual rainfall (2018–2022).

Figure 3

Average annual rainfall (2018–2022).

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Figure 4(a)–4(e) depicts the annual rainfall for the years 2018–2022, respectively. The total quantity of rain that falls in an area over the course of a year is referred to as annual rainfall. It is computed by summing all the observed rainfall in that area. As shown in the figure, we analysed the yearly rainfall in the study area for the previous five years (2018–2022). It shows that the northeastern and southwestern parts of the study area received a lot of rain, while the upper northwest section of the study area received relatively little.
Figures 4

(a)–(e) The annual rainfall for the years 2018–2022.

Figures 4

(a)–(e) The annual rainfall for the years 2018–2022.

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Elevation

Elevation plays a pivotal role in influencing flood hazards within a specific watershed. Typically, lower-lying regions are susceptible to flooding during events of lower magnitude. In the study area, the elevation spans from a maximum of 8,685 m above mean sea level to a minimum of −46 m, as shown in Figure 5. The average elevation across the study area stands at 1,676.98 m. Interestingly, the category with the highest elevation is linked to a very low flood threat, while the group with the lowest elevation is related to a very high flood hazard.
Figure 5

Elevation map of the study area.

Figure 5

Elevation map of the study area.

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Slope

In a given region, the length and steepness of the topography have a considerable impact on flood inundation. While areas with steep and high slopes effectively direct floodwaters downstream, areas with relatively flat and moderate slopes typically endure extended periods of flooding. The Peninsular Plateau is geographically distinct from the plains of the Ganga and the Indus due to the presence of a range of mountains and hills, with elevations ranging from 460 to 1,220 m. Notable among these are the Aravalli, Vindhya, Satpura, Maikala, and Ajanta Ranges. On one side, the Peninsula is bordered by the Eastern Ghats, with an average elevation of about 610 m, and on the other side by the Western Ghats, generally ranging from 915 to 1,220 m and rising in some areas to over 2,440 m. A narrow coastal strip lies between the Western Ghats and the Arabian Sea, while a broader coastal region is found between the Eastern Ghats and the Bay of Bengal. The slope across India varies from 1.503 to 90°. A slope map of the study basin is shown in Figure 6, which divides it into five groups based on slope height: very low (1.503–53.21°) to very high (88.62–90°). The basin's northeastern region is particularly prone to floods because of its relatively flat slope, whereas the centre and northwest regions of the basin are mostly characterized by greater slopes. The northwest portion of the watershed is probably less likely to experience flooding episodes due to this change in slope.
Figure 6

Slope map of the study area.

Figure 6

Slope map of the study area.

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Drainage density

India's diverse drainage systems exhibit distinct flow patterns, primarily following the northeast to southwest slope of the region. Approximately 77% of these rivers drain into the Bay of Bengal, while the remaining 23% discharge into the Arabian Sea. In terms of their origin, nature, and characteristics, the drainage systems of India can be categorized into two main types: the Himalayan drainage and the Peninsular drainage. The density of drainage networks in a region serves as an important indicator of surface runoff and the potential for flooding. Higher drainage densities are associated with elevated surface runoff rates, thereby increasing the susceptibility to flooding. Five density categories – very high, high, medium, low, and very low – are shown on the DD map of the study area in Figure 7. A higher risk of flooding is indicated by areas with extremely high drainage densities, which are commonly found in metropolitan areas, beside major roadways, and in agricultural areas. The very high DD class ranges from 6.593–8.24 km/km2; the other classes are high (4.945–6.592 km/km2), moderate (3.297–4.944 km/km2), low (1.649–3.296 km/km2), and very low (0–1.648 km/km2) DD classes. Consequently, a higher DD corresponds to a greater flood hazard rating. To extract drainage networks from DEMs with a 20-m resolution, an algorithm was developed and implemented in a GIS environment. The line density analysis was used to calculate the DD area based on stream polyline features. Here it is 12.4972. The formula for calculating DD is expressed as follows:
(2)
where represents the total length of drainage in km, A is the total area of the study site in km2, and n represents the number of drainage networks within the watershed.
Figure 7

DD map of the study area.

Figure 7

DD map of the study area.

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Land use

The LULC composition of an area plays a crucial role in determining its vulnerability to flooding. Roads and residential areas are examples of impermeable surfaces that increase stormwater runoff. Bare lands are prone to soil erosion and result in high downstream runoff within the watershed. Conversely, areas with dense vegetation have a lower risk of flooding since vegetation promotes soil infiltration and reduces runoff generation. Data sourced from the Environmental System Research Institute reveal that the case study area encompasses various LULC types, including dense vegetation, cropland, bare land, built-up areas, and water bodies. Among these, cropland covers the largest portion, spanning 162,539,291 h, followed by vegetation at 7,916,282 h. About 10,860,343 h, or more, are covered by water in the case study region. These LULC types are categorized into several classes as seen in the land-use map of the study's area, as shown in Figure 8.
Figure 8

LULC map of the study area.

Figure 8

LULC map of the study area.

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Distances from roads

Roads represent a significant human-made factor contributing to flood hazards. In the study area, a road map has been created, delineating metalled roads, unmetalled roads, and tracks (footpaths). The primary purpose of this map is to identify potential obstructions resulting from road construction that can impede the natural flow of floodwaters. Roads, railways, bridges, and other infrastructure within a watershed can restrict the passage of flood discharges. Areas occupied by roads and structures have limited capacity to retain rainfall and snowmelt. The construction of roads and buildings often entails the removal of vegetation, soil, and natural depressions from the land surface. A map showing the research area's distances from roadways, which range from 0 to 7.577 units, is shown in Figure 9. To assess this distance, a classification into five classes has been applied: very low, low, moderate, high, and very high. The class with a range of 6.063–7.577 has been assigned the highest weight of 5, while the class with a range of 0–1.515 bears the lowest weight of 1. This categorization aids in determining the possible influence of roads on local flood threats.
Figure 9

Distance from roads map.

Figure 9

Distance from roads map.

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Distances from rivers

The proximity to a river serves as a crucial indicator of flood hazard, as regions situated near rivers are more susceptible to frequent flooding compared to those located further away from riverbanks. Areas near rivers are categorized as having a very high flood hazard, while areas at varying distances from rivers are considered to have a low flood hazard. Figure 10 shows a map with distances from rivers in the study area ranging from 0 to 8.13 units. These distances are classified into five classes, namely, very low, low, moderate, high, and very high. The class with a range of 6.51–8.13 has been assigned the highest weight of 5, while the class with a range of 0–1.63 bears the lowest weight of 1. This classification system aids in assessing flood hazards based on the proximity of the area to rivers.
Figure 10

Distance from rivers map.

Figure 10

Distance from rivers map.

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Ranking of area for flood risk mapping

For the analysis, ranking and weights were assigned to all the seven criteria used during flood risk vulnerability mapping in this study. The geospatial environment had been defined risks ranked 1–5, which served as the standard in classifying each criterion. After ranking all layers, the total weight of 100 that is spread proportionately across the seven parameters is then employed for vulnerability assessment based on priority. Subsequently, the normalized weight index (NWI) values were calculated using the raster tool. The NWI was determined by dividing the total weight by each individual criterion's weight. The integration of the normalized rank index and the NWI was performed using a weighted sum overlay analysis within the spatial analysis. Based on their relative impact on flood risk, which is ascertained using a combination of expert opinion, empirical data analysis, and statistical methods, parameters in the flood susceptibility evaluation are given weights. Empirical data analysis looks at past flood data to find trends and connections between different variables and the frequency of floods.

Table 1 presents the breakdown of the criteria used in a flood risk vulnerability assessment, each accompanied by its assigned weight and the corresponding NWI value. These values are crucial for understanding the relative importance of each criterion in assessing flood vulnerability in the study area. ‘Rainfall’ is the most influential factor, carrying a 25% weight and an NWI value of 0.25, signifying its substantial impact on flood vulnerability. ‘Distance to River’ is also significant with a 20% weight and an NWI value of 0.20, indicating its importance in flood risk assessment. ‘Drainage Density’ and ‘Elevation’ are both vital, each with a 15% weight and an NWI value of 0.15, showing their substantial influence on vulnerability. ‘Land Use/Land Cover’ and ‘Slope’ are moderately important, each with a 10% weight and an NWI value of 0.10. ‘Distance to Road’ is the least influential criterion with a 5% weight and an NWI value of 0.05.

Table 1

The weight and the corresponding NWI value

Sr. No.CriteriaWeight (%)NWI
LULC 10 0.10 
DD 15 0.15 
Distance to road 0.05 
Distance to river 20 0.20 
Slope 10 0.10 
Rainfall 25 0.25 
Elevation 15 0.15 
Sr. No.CriteriaWeight (%)NWI
LULC 10 0.10 
DD 15 0.15 
Distance to road 0.05 
Distance to river 20 0.20 
Slope 10 0.10 
Rainfall 25 0.25 
Elevation 15 0.15 

The flood risk maps for the study area are shown in Figure 11, where the risk of flooding is divided into five different categories, from very low to very high. The breakdown of these risk levels indicates that 3.40% of the area is classified as very high risk, 32.65% as high risk, 39.72% as moderate risk, 20.97% as low risk, and 3.25% as very low risk. The high and very high flood risk zones exhibit similar characteristics, including low slopes and elevations, high DD, proximity to roads and rivers, and moderately elevated average annual rainfall. The two main land-use forms that define these places are bare land and urban built-up. An in-depth analysis of the flood risk map highlights how the combination of urban development, high DD, and low topographical relief escalates the susceptibility to flooding in these regions. To generate these flood risk maps, the initial data underwent value assignments based on the factors specified in the accompanying table. The flood risk analysis was derived from this weighted assessment. The Risk Rank for flood susceptibility was assigned as follows: 5 for very high flood susceptibility, 4 for high flood susceptibility, 3 for moderate flood susceptibility, 2 for low flood susceptibility, and 1 for very low flood susceptibility, which is presented in Table 2. This ranking method provides an essential tool for efficient catastrophe planning and preparation by categorizing places according to their susceptibility to floods.
Table 2

The flood susceptibility risk ranking

Flood hazard classRisk rankArea (km2)Area (%)
Very high 1.35 3.40 
High 12.933 32.65 
Moderate 15.732 39.72 
Low 8.307 20.97 
Very low 1.287 3.25 
Total  39.609 100 
Flood hazard classRisk rankArea (km2)Area (%)
Very high 1.35 3.40 
High 12.933 32.65 
Moderate 15.732 39.72 
Low 8.307 20.97 
Very low 1.287 3.25 
Total  39.609 100 
Figure 11

Flood risk map of study area.

Figure 11

Flood risk map of study area.

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Table 3 presents an extensive analysis of the several elements that affect the study area's vulnerability to flooding. Each component is classified into distinct groups and given a corresponding Risk Rank. These variables include important components that are crucial in identifying an area's susceptibility to floods. There are many ranges for the attribute ‘Elevation’ ranging from very low to very high. It is notable that most of the region (58.21%) is made up of places with ‘Very Low’ elevation. Because low-lying locations are usually more vulnerable to flooding during flood occurrences, elevation is an important consideration when determining flood risk. The terrain's ‘Slope’ is then considered, with different slope angles ranging from very low to very high. Steep slopes often lead to rapid runoff, which can exacerbate flood risk. ‘Average Annual Rainfall’ is another key factor, partitioned into categories from very low to very high. Moderate rainfall areas are predominant at 41.47%, making them a focal point in the assessment. Rainfall patterns have a substantial influence on flooding, with intense rainfall events increasing the risk.

Table 3

Comprehensive breakdown of various factors influencing flood susceptibility

FactorClassFlood susceptibilityRisk RankArea
(km2)Percent (%)
Elevation (m) −46–501.8 Very low 35,892.29 58.21 
501.9–1,597 Low 10,828.38 17.56 
1,598–3,378 Moderate 3,473.172 5.63 
3,379–4,782 High 7,495.713 12.15 
4,783–8,685 Very high 11,458.39 18.58 
Slope (degree) 1.503°–53.21° Very low 0.36 0.017 
53.22°–77.51° Low 2.601 0.125 
77.52°–85.83° Moderate 22.473 1.084 
85.84°–88.61° High 165.213 7.97 
88.62°–90° Very high 1,881.045 90.79 
Average annual rainfall (mm) 225.47–701.74 Very low 5.463 13.57 
701.75–1,073.5 Low 10.638 26.44 
1,073.6–1,480 Moderate 16.686 41.47 
1,480.1–2,107.3 High 6.237 15.49 
2,107.4–3,187.6 Very high 1.206 2.99 
DD (km/km20.1666–69.701 Very low 23.58 11.28 
69.702–139.23 Low 70.218 33.62 
139.24–208.77 Moderate 72.315 34.61 
208.78–278.3 High 31.257 14.96 
278.31–347.84 Very high 11.538 5.52 
LULC Vegetation Very low 28,367.69 25.76 
Cropland Low 46,090.19 41.85 
Built-up land Moderate 24,120.32 21.90 
Bare land High 2,415.519 2.19 
Water body Very high 9,122.148 8.28 
Distance from Roads (m) 0–0.701 Very low 10.917 1.93% 
0.701–2.042 Low 36.63 6.46 
2.042–3.476 Moderate 79.605 14.04 
3.476–5.000 High 103.581 18.27 
5.000–7.775 Very high 336.267 59.30 
Distance from rivers (m) 0–0.712 Very low 11.736 2.06 
0.712–2.043 Low 41.508 7.28 
2.043–3.436 Moderate 85.842 15.08 
3.436–4.954 High 104.598 18.38 
4.954–7.895 Very high 325.53 57.20 
FactorClassFlood susceptibilityRisk RankArea
(km2)Percent (%)
Elevation (m) −46–501.8 Very low 35,892.29 58.21 
501.9–1,597 Low 10,828.38 17.56 
1,598–3,378 Moderate 3,473.172 5.63 
3,379–4,782 High 7,495.713 12.15 
4,783–8,685 Very high 11,458.39 18.58 
Slope (degree) 1.503°–53.21° Very low 0.36 0.017 
53.22°–77.51° Low 2.601 0.125 
77.52°–85.83° Moderate 22.473 1.084 
85.84°–88.61° High 165.213 7.97 
88.62°–90° Very high 1,881.045 90.79 
Average annual rainfall (mm) 225.47–701.74 Very low 5.463 13.57 
701.75–1,073.5 Low 10.638 26.44 
1,073.6–1,480 Moderate 16.686 41.47 
1,480.1–2,107.3 High 6.237 15.49 
2,107.4–3,187.6 Very high 1.206 2.99 
DD (km/km20.1666–69.701 Very low 23.58 11.28 
69.702–139.23 Low 70.218 33.62 
139.24–208.77 Moderate 72.315 34.61 
208.78–278.3 High 31.257 14.96 
278.31–347.84 Very high 11.538 5.52 
LULC Vegetation Very low 28,367.69 25.76 
Cropland Low 46,090.19 41.85 
Built-up land Moderate 24,120.32 21.90 
Bare land High 2,415.519 2.19 
Water body Very high 9,122.148 8.28 
Distance from Roads (m) 0–0.701 Very low 10.917 1.93% 
0.701–2.042 Low 36.63 6.46 
2.042–3.476 Moderate 79.605 14.04 
3.476–5.000 High 103.581 18.27 
5.000–7.775 Very high 336.267 59.30 
Distance from rivers (m) 0–0.712 Very low 11.736 2.06 
0.712–2.043 Low 41.508 7.28 
2.043–3.436 Moderate 85.842 15.08 
3.436–4.954 High 104.598 18.38 
4.954–7.895 Very high 325.53 57.20 

‘Drainage Density’ categorizes the density of watercourses, ranging from very low to very high. ‘Moderate’ DD zones are widespread, covering 34.61% of the area. DD influences how efficiently water can flow away from an area during heavy rainfall or floods. In terms of ‘LULC’ the study area comprises various risk levels from very low to very high. ‘Cropland’ dominates at 41.85%, reflecting the substantial role of land use in flood risk assessment. The ‘Distance from Roads’ is classified from very low to very high. Significantly, ‘Very Low’ distances make up 1.93%, being the most frequent class. Conversely, river proximity is an element of importance in flood hazard study as flows and the capacity of streams for drainage influence the risk. Ultimately, approximately 2.06% of the study area corresponds to ‘Very Low’ distances. Flood vulnerability analysis takes into consideration several things, one of them being proximity to rivers that are likely to overflow. The categorized Risk Ranks and thus this way of classifying gives a good basis for knowing where to look first when assessing flood risks as well as informational support for the development and organization of disaster mitigation policies and programmes in the study area.

Limitations of the study

The study provides a comprehensive flood risk assessment using GIS and MCDA, but several limitations must be acknowledged. First, the model applies a uniform weightage to various flood risk factors across the entire country. Given India's vast and diverse landscape, this approach may not fully capture the spatiotemporal variations inherent in different regions. Factors such as topography, climate, and human development vary significantly across India, and a single model might oversimplify these complexities. Additionally, the accuracy of flood risk maps heavily depends on the quality and resolution of the data used. In some regions, data may be outdated, incomplete, or of lower resolution, potentially impacting the reliability of the model's outputs. High-resolution data specific to smaller regions are necessary for more precise assessments. The model does not fully account for temporal variations, such as seasonal changes, annual climate variability, and long-term climate change impacts. Flood risk is dynamic and can fluctuate over time, necessitating models that can integrate temporal data for more accurate predictions. Moreover, socioeconomic factors, such as infrastructure quality, population density, and preparedness levels, are complex and region-specific. The model's approach to these factors may be overly simplistic, not fully capturing the nuanced impacts of human development and socioeconomic conditions on flood risk. Validation of the model against real-time flood events and historical data is ongoing, requiring continuous calibration and refinement to ensure accuracy and reliability across diverse regions of India. The initial results need to be corroborated with more localized studies and expert feedback. Lastly, the model's scalability and adaptability to different regions within India are limited in its current form. Regional studies and sub-models tailored to specific areas are necessary to enhance their relevance and accuracy. Adapting the model to local contexts will require significant effort and collaboration with regional stakeholders and experts.

Future scope

Future research directions will focus on enhancing the flood vulnerability assessment framework by integrating additional critical factors and methodologies. Factors such as soil type, deforestation rates, and infrastructure density, which significantly influence flood susceptibility, will be prioritized for inclusion. Incorporating these variables will provide a more comprehensive understanding of flood risk dynamics and improve the accuracy of our assessments. Moreover, there will be a concerted effort to analyse historical flood events to identify areas with recurrent vulnerabilities and patterns. This historical perspective will guide the refinement of our models and the development of proactive flood risk management strategies. Advanced GIS techniques and high-resolution remote sensing data will be leveraged to enhance spatial resolution and accuracy, enabling better capture of local-scale variations. Engagement with local communities and close collaboration with stakeholders, including government agencies and Non-Governmental Organizations (NGOs) will be crucial. Their insights and local knowledge will inform data collection efforts and ensure the relevance and applicability of our flood risk assessments. Furthermore, integrating climate change scenarios into our assessments will enable us to anticipate future flood risks and support adaptation strategies. Validation exercises against observed flood events and comparisons with existing flood risk assessments will be undertaken to ensure the reliability and effectiveness of our methodology. This validation process will drive ongoing refinement and improvement of our models. Ultimately, the aim is to provide decision support tools and actionable insights to policymakers and planners, facilitating informed decisions on flood mitigation, emergency response planning, and resilient infrastructure development.

Comprehensive analysis of the flood risk assessment in India has shown complex interrelationships among meteorological, geographic, and human factors contributing towards this existing problem of floods. Using GIS and MCDA, the research has been successful in offering significant knowledge on the intricate aspects of flood risk in India. Research reveals that there are several triggers of flood hazard in India and the three main ones include slope, elevation, and average yearly rainfall. Monsoons are characterized by large amounts of rainfall that come along annually in India, which makes it vulnerable to flooding. Other factors such as lower altitude and flat slopes can also increase the risk of floods to an area. Moreover, DD, LULC, and proximity to roads and rivers complicate this intricate topography of flood hazard. Each criterion was assigned a weight, according to its importance in relation to the others, thus constructing the flood risk map. The maps show different levels of flood risks that range from very low level to the highest level all over India. 3.40% of the area has been determined to be at a very high risk, while 32.65% comprises high-risk areas, 39.72% moderate risk, and 20.97% low-risk areas.

The participants have consented to the submission of the paper to the journal.

Y.P.S. conceptualized the process, and developed the methodology, rendered support in technical investigation and data collection, validated and visualized the work, wrote the original draft and reviewed the article; V.K. and D.K.T conceptualized the process, developed the methodology, visualized and supervised the study, reviewed the article; K.V.S., A.P., and D.J.M. rendered support in data collection, reviewed the article; A.P. and D.J.M. wrote the reviewed and edited the article. All authors read and approved the final version of the paper.

The authors declare that no funds, grants, or other support were received during the preparation of this paper.

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

The authors declare there is no conflict.

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