INTERNATIONAL JOURNAL OF RESEARCH AND INNOVATION IN SOCIAL SCIENCE (IJRISS)  
ISSN No. 2454-6186 | DOI: 10.47772/IJRISS | Volume IX Issue XI November 2025  
Assessing the Socioeconomic Implications of Flood Risk in  
Ratnapura District, Sri Lanka  
Ashvin Wickramasooriya1 and Navoda Ranasinghe2  
1Department of Geography, University of Peradeniya, Peradeniya, Sri Lanka  
2Postgraduate Institute of Agriculture, University of Peradeniya, Peradeniya, Sri Lanka  
Received: 24 October 2025; Accepted: 31 October 2025; Published: 26 December 2025  
ABSTRACT  
The core objective of this research is to leverage geospatial technology for assessing flood risk in Sri Lanka's  
Ratnapura district while also examining the socioeconomic ramifications of flood occurrences in the area.  
Situated in Sri Lanka's central highlands, Ratnapura faces significant flood vulnerability, notably during the  
Southwest monsoon period spanning from May to September. Through a comprehensive consideration of  
influential factors in flood occurrences and the utilization of the Multi-Criteria Decision Analysis method, a  
flood risk map of the Ratnapura district has been constructed using ArcGIS 10.3 software. Analysis of the flood  
risk map indicates that 15.4% of the district is classified as having a very high flood risk, while roughly 31.5%  
is deemed to have low risk. Furthermore, overlaying thematic layers for road networks, buildings, land use, and  
settlements with the flood risk thematic layer reveals that approximately 4,000 human settlements, 1,200 main  
buildings, 35 schools, 100,000 acres of cultivated land, and 190 kilometres of major roads are situated in areas  
characterized by very high flood risk. Consequently, this scenario presents various socioeconomic challenges,  
including loss of life, damage to infrastructure, destruction of crops, and harm to livestock. Therefore, it is  
imperative to introduce effective flood mitigation measures, develop comprehensive flood management  
strategies, and promptly implement them. This proactive approach is crucial for minimizing the socioeconomic  
impact of future flood events in the region.  
Keywords: flood risk, multi criteria decision analysis method, GIS, consistency ratio  
INTRODUCTION  
In the 21st century, floods have emerged as one of the most devastating, frequent, and widespread catastrophic  
events worldwide (Bishaw, K. 2012) [2], (Emmanuel, U. et al, 2015) [5]. Floods give rise to a plethora of  
environmental and socio-economic consequences within affected regions. Notably, floods account for a  
significant 31% of economic losses resulting from natural disasters (Emmanuel, U. et al, 2015) [5], underscoring  
the importance of studying this phenomenon. Floods, characterized by the overflow of water inundating land,  
can lead to damage to agricultural lands, urban areas, and even the loss of human lives (Rahmati, O. et al, 2016)  
[10]. These deluges can be triggered by various meteorological and hydrological events, including intense  
precipitation during the rainy season, excessive surface runoff, and a sharp increase in river discharge.  
Anthropogenic factors, such as poor urban planning, inadequately designed drainage channels, improper  
agricultural practices, and land-use changes, are among the dominant factors contributing to flood occurrences.  
A natural hazard encompasses the likelihood of catastrophic events along with their key physical attributes  
(Mourato, S. et al, 2012) [8]. Vulnerability refers to the conditions shaped by physical, social, economic, and  
environmental factors or processes that heighten the susceptibility of individuals, communities, assets, or  
systems to the impacts of hazards (Palliyaguru, R. et al, 2014) [9].  
South Asia's geographical location renders it highly susceptible to natural disasters, making it one of the most  
flood-vulnerable regions globally. Moreover, countries in this region exhibit a high level of vulnerability due to  
a lack of resources, including adaptive and coping capacities (Rahmati, O. et al, 2016) [10]. In Sri Lanka, flood  
losses have significantly increased in recent decades, with major floods often associated with the two monsoon  
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seasons. During the Southwest monsoon season (May-September), the Western, Southern, and Sabaragamuwa  
provinces are prone to floods. In contrast, during the Northeast monsoon (December-February), the Eastern,  
Northern, and North-central provinces are susceptible to flooding, rivers along the western slopes of the hilly  
central areas cause floods in the lower flood plains of Kalu Ganga and Kelani Ganga, particularly during these  
periods. Notably, Sri Lanka has experienced severe floods in recent history, including in 2003, 2011, 2012, 2016,  
and 2017. The 2003 floods affected 23 districts, impacting 733,479 people and resulting in the loss of 151 lives.  
In late May 2017, floods affected 15 districts, causing the loss of 213 lives and the displacement of 79  
individuals. Additionally, these flood events incurred substantial property losses, estimated at around 70 billion  
rupees (Rahmati, O. et al, 2016)[10]. In Sri Lanka, the Ratnapura district has experienced the highest number of  
recorded flood events, followed by Kalutara, Galle, Kurunegala, and Ampara districts. Notably, flooding in  
Ratnapura and Kalutara is closely associated with the Kalu Ganga basin, which covers an area of 2,690 km2 and  
ranks as the second-largest river basin in Sri Lanka, featuring a river channel spanning approximately 100 km  
(De Silva, M.M.G.T., and Kawasaki, A., 2018) [3].  
According to the Department of Irrigation (2016), this basin receives an annual mean rainfall of 4,000mm, with  
a total annual water discharge of 7.3 billion cubic meters, most of which occurs during the southwest monsoon.  
While floods impact the area annually, some years witness critical floods, defined by the Irrigation Department  
as those exceeding 24.4 meters above sea level at the Ratnapura stream flow measuring gauge. Critical floods  
occurred in 1913, 1940, 1941, 1947, 2003, and 2017 (De Silva, M.M.G.T. and Kawasaki, A., 2018)[3]. While  
floods may be unavoidable and uncontrollable, addressing these issues through risk zone mapping and a  
comprehensive analysis of various criteria can enhance preparedness, prevention, and risk reduction efforts.  
Flood vulnerability mapping plays a pivotal role in establishing early warning systems and formulating strategies  
for future flood management (Rahmati, O. et al, 2016) [10]. Utilizing remote sensing and GIS techniques allows  
for a detailed examination of multiple criteria, facilitating a deeper understanding of the nature and behaviour of  
flood hazards, and the identification of vulnerable areas (Saeid, J. et al, 2021) [11]. One popular approach for  
assessing flood risk is the use of numerical models (Dutta, D., 2007) [4]. Several studies have employed GIS-  
based multi-criteria decision analysis (MCDA) to assess index-based flood hazards by examining the factors that  
influence floods (Kazakis, N., 2015) [6], (Wu, Y., et. al., 2015) [15]. The GIS-MCDA technique leverages GIS  
capabilities for processing geospatial data and the adaptability of MCDA to combine factual data such as rainfall,  
land use, soil type, slope, and drainage density with value-based data (Yahaya, S., et al, 2010) [16]. Despite  
various government initiatives to enhance disaster management in the Ratnapura area, it remains vulnerable,  
with numerous individuals enduring severe property damage and loss of life during major flood events. This  
paper's objective is to integrate GIS and multiple-criteria decision analysis (MCDA) techniques to develop a  
flood hazard map for the Ratnapura district in Sri Lanka. The study will also analyze flood risk in the area using  
the created flood hazard map.  
Study Area  
Ratnapura district is located within the upcountry-wet zone of Sri Lanka, an area characterized by an average  
annual rainfall of 3,000mm. This region faces heightened vulnerability to flash floods and riverine floods,  
primarily due to substantial rainfall in the upper watersheds and its positioning in the floodplains of the Kalu  
River. The Kalu River serves as the principal source responsible for flood occurrences in Ratnapura district  
(Amaraweera, P.H., et.al, 2018) [1]. Spanning an expansive area of about 2,803km2, the Kalu River basin  
witnesses an annual discharge of approximately 3 million cubic meters per square kilometer per year, marking  
it as the highest in the country (Wickramasooriya, A.K. and Walpita, L.S., 2021) [13]. Certain parts of the upper  
Kalu River basin experience even more substantial rainfall depths, exceeding 5,000mm, leading to a significant  
volume of discharge (Liyanarachchi, P. and Chandana, P.G., 2004) [7]. The vulnerability to flooding is  
particularly pronounced in this region, where nearly 90% of agricultural land, predominantly paddy fields, is  
situated along the tributaries in the floodplain. Additionally, both commercial and residential areas in Ratnapura  
town are densely built up and highly susceptible to flooding (Wickramagamage, P., 2011) [12].  
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Figure 1. Ratnapura district in Sri Lanka  
Road network of the study area  
Figure 2 illustrates the road network within the Ratnapura district. It's worth noting that several major roads link  
important commercial cities such as Colombo, Batticaloa, and Kandy, and these vital transportation arteries are  
situated near the Kalu River. This close proximity exposes them to the risk of being impacted by potential future  
flood events. Moreover, the figure emphasizes the existence of numerous main roads and minor roads near the  
Kalu River and its branches. These areas are especially prone to flooding, posing a significant risk of inundation  
to the road infrastructure during flood events.  
Figure 2. Road network in the Ratnapura district  
Settlements in the study area  
Settlements in the Ratnapura district correspond to the dispersion of the human population in the region. Figure  
3 illustrates the population density across divisional secretariats in the Ratnapura district.  
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ISSN No. 2454-6186 | DOI: 10.47772/IJRISS | Volume IX Issue XI November 2025  
Figure 3. Population density in the Ratnapura district  
Flood vulnerability in the study area  
The maps indicate settlements in Ratnapura district are vulnerable to floods near the Kalu River. Current  
inundation maps lack socioeconomic factors, potentially underestimating impacts on settlements and roads. This  
study aims to analyze future flood impacts comprehensively, addressing gaps in understanding socioeconomic  
implications. By considering both settlements and road networks, it seeks to improve disaster management  
strategies for Ratnapura district.  
MATERIALS AND METHODOLOGY  
Material  
Secondary digital data at a 1:50,000 scale was obtained from the Survey Department of Sri Lanka, as outlined  
in Table 1. This dataset served as a primary source of geographic information for the study  
Table 1. Data types and data sources  
Data Type  
Contour  
Scale  
1:50,000  
Source  
Survey Department of Sri Lanka  
Survey Department of Sri Lanka  
Survey Department of Sri Lanka  
Survey Department of Sri Lanka  
Land use  
Road  
1:50,000  
1:50,000  
1:50,000  
Settlements  
The study on Ratnapura incorporated various data sources. Apart from primary data, it utilized the Ratnapura  
development plan by the Urban Development Authority, Google images, Landsat images, population data from  
the Census and Statistical Department, settlement information from the Urban Development Authority of Sri  
Lanka, and past flood inundation maps from the Ministry of Defense. These diverse sources ensured accuracy  
and reliability in the study's outcomes.  
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Methodology  
The primary objective of this study is to identify the areas in the Ratnapura district with the highest and lowest  
flood risk. This goal is accomplished through a series of sequential steps, outlined in Figure 4.  
Figure 4. Summary of the research methodology  
The primary steps of the study can be summarized as follows:  
Preparation of Georeferenced Digital Maps: This step entails utilizing the collected digital maps to  
generate georeferenced maps and compiling a database containing digital thematic layers essential for  
flood hazard analysis.  
Weightage Calculation for Factors: Utilizing the Pairwise Comparison Method, specifically the  
Analytical Hierarchy Process (AHP), weightages are computed for the various factors influencing flood  
hazards in the area. These criteria are determined following the guidelines provided by the Disaster  
Management Centre.  
Rank Assignment for Factors:Different conditions within these factors are assigned ranks based on a scale  
introduced by Saaty, T. L. in 1988. This step is crucial for understanding the relative importance of each  
factor concerning flood hazards.  
Flood Hazard Map Preparation:Using the Multi-Criteria Decision Analysis Method and a weighted  
overlay analysis approach, a flood hazard map is prepared for the study area. This map integrates the  
factors, weightages, and rankings to identify and visualize areas with varying degrees of flood risk within  
the Ratnapura district.  
Preparation georeferenced thematic layers and database  
A meticulously constructed digital database has been assembled, comprising essential digital thematic layers  
necessary for analyzing flood risk within the area. These digital layers serve as crucial resources for conducting  
geographical information systems (GIS) applications and making informed decisions. Sourced from various  
institutions such as the Department of Survey and the Disaster Management Centre of Sri Lanka, the digital  
thematic layers have been standardized to a consistent scale of 1:50,000, georeferenced, and converted into raster  
format. This ensures compatibility with ArcGIS software for seamless analysis and utilization. Such meticulous  
preparation of the digital database lays the foundation for the comprehensive assessment of flood risk in the  
Ratnapura district.  
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Calculation of weightages for factors or parameters  
In the process of preparing the flood hazard map for the study area, the expertise of key departments, including  
the Department of Irrigation, Department of Meteorology, and Disaster Management Centre, was leveraged.  
These experts provided valuable insights into the main factors that influence the creation of floods and the  
relative importance of these factors in contributing to flood events. The primary factors considered in the analysis  
of flood hazard were:  
Topography and Elevation: Analyzing the terrain elevation and slope characteristics to identify low-lying  
areas prone to flooding and to understand the flow of water during flood events.  
Land Use and Land Cover: Examining the types of land use and land cover within the study area to  
understand how human activities impact flood vulnerability and to identify areas susceptible to urban  
flooding.  
Infrastructure and Drainage Systems: Assessing the effectiveness of existing infrastructure, including  
drainage networks and flood control measures, in mitigating flood risk and protecting communities.  
By incorporating insights from these key departments and considering these primary factors, the flood hazard  
map aims to provide a comprehensive understanding of flood risk within the Ratnapura district.  
To create a comprehensive flood hazard map, different weightages were calculated for each of these three factors.  
These weightages were determined based on their relative importance, utilizing the square pair-wise comparison  
method, as detailed in Table 2. This approach allowed for a more accurate assessment of flood risk within the  
study area, considering the varying influences of these key factors.  
Table 2. Square pairwise comparison matrix of analysing weightages  
Water buffer  
Land use  
Elevation  
Water buffer  
Land use  
Elevation  
Total  
1
4
2
0.25  
0.50  
1.75  
1
4
9
0.25  
1
3.25  
The preparation of the flood hazard map for the study area benefitted from the expertise of professionals in flood  
hazard, vulnerability, and risk analysis from key institutions, including the Department of Irrigation, Department  
of Meteorology, and the Disaster Management Centre. These experts played a pivotal role in identifying the  
primary factors that contribute to the occurrence of floods and assessing the relative importance of these factors  
in the context of flood creation. Their insights and expertise were invaluable in ensuring the accuracy and  
reliability of the flood hazard map, contributing to a comprehensive understanding of flood risk within the study  
area.  
This collective knowledge and expertise formed the foundation of the flood hazard map, ensuring a thorough  
and well-informed assessment of flood risk within the study area. The analysis of flood hazard in the study area  
focused on three primary factors: elevation, distance from the main river and its tributaries (water buffer), and  
land use types within the region. These factors were considered central to understanding and assessing flood risk  
within the area. To quantify the relative importance of these three factors, different weightages were calculated  
for each of them. This calculation was conducted using the square pair-wise comparison method, as indicated in  
Table 2. Assigning weightages to these factors is a fundamental step in comprehensively evaluating flood risk,  
as it provides a structured and data-driven approach to understanding the significance of each factor in  
contributing to the creation of floods in the study area.  
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Calculation of normalized weightage values  
The initial weightings for the three primary factors affecting flood hazard underwent additional processing to  
improve analysis accuracy. This processing included normalization, leading to the values outlined in Table 3.  
Normalization is a standard procedure in multi-criteria decision analysis (MCDA), ensuring all factors share a  
consistent scale for direct comparison, thereby refining analysis precision. These normalized values are crucial  
for a more precise and detailed evaluation of flood risk within the study area.  
Table 3. Normalized Matrix  
C1  
0.571428571  
0.142857143  
0.285714286  
1
C2  
0.44444  
0.11111  
0.44444  
1
C3  
0.615384615  
0.076923077  
0.307692308  
1
Weightage  
0.544  
C1  
C2  
0.110  
0.346  
1
C3  
Total  
The Analytical Hierarchy Process (AHP) was used to assign weights to factors affecting flood formation: river  
proximity (water buffer), elevation, and land use. Weights allotted were 0.544, 0.346, and 0.110, respectively.  
These weights are pivotal in gauging factors' importance in flood risk assessment. To validate reliability, a  
Consistency Ratio (CR) analysis was conducted. CR evaluates consistency in weight allocation, indicating  
deliberate judgment in pairwise comparisons. CR ≤ 0.1 is deemed acceptable, suggesting a consistent matrix;  
CR > 0.1 necessitates matrix revision due to potential inconsistency. This analysis ensures weight validity for  
subsequent flood risk assessments.  
Analysis of Consistency Ratio (CR)  
The accuracy of created weightages are anslysed using Consistency Ratio equation given in below.  
CR = CI / RI  
Where, CR is the Consistency Ratio and CI is the Consistency index  
CI = (λmax n) / (n 1)  
(1)  
(2)  
Where, λmax is the Principal Eigen Value, n is the Number of criteria and RI is the Random Consistency Index  
(RI) which can be obtained using the standard values given in the Table 4.  
Table 4. Random Indices for matrices of various sizes  
n
1
2
3
4
5
6
7
8
9
10  
11  
12  
13  
14  
15  
0.5 0.9 1.1 1.2 1.3 1.4 1.4 1.5 1.5 1.5 1.5 1.5 1.5  
RI  
0
0
8
2
4
2
1
5
1
2
4
6
8
9
Source: GIS-based Multi-Criteria Decision Analysis (Estoque, R, C, 2011). (n no of indices in the matrix)  
The analysis involves three indices (n = 3) in the matrix, and the Random Index (RI) for this case is determined  
to be 0.58. To calculate the Consistency Index (CI) for the analysis, the following steps are typically followed.  
However, the specific calculation is not provided in your message. The formula to calculate CI is as follows:  
CR = CI / RI = 0.05912032  
(3)  
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CI = (λmax n) / (n 1) = 0.0342898  
(4)  
With a Consistency Ratio (CR) of 0.05912, well below the 0.1 threshold, the weight calculation process  
demonstrates strong consistency. This assures the reliability of assigned weights for factors (distance from river,  
elevation, land use type) in flood hazard analysis. Such consistency fortifies the accuracy and validity of flood  
risk assessment, ensuring a sturdy analytical base.  
Assign ranks for different conditions within factors  
Recognizing the limitations of applying uniform weightage to factors in addressing their diverse conditions, the  
study has introduced tailored ranking systems for each condition's specific impact on flood formation. This  
customized approach is vital because varying conditions within a factor can exert differing degrees of influence  
on flood hazards. For instance, areas near rivers may face greater flood risks than those farther away. Thus, it's  
essential to assign varying weightage to significant conditions within each factor. To accomplish this, three  
ranking systems calibrated to address specific conditions within the factors have been developed. These systems  
follow Saaty's 9-point scale, where a rating of 9 indicates the highest influence on flood creation, and 1 suggests  
minimal impact. By incorporating these customized ranking systems delineated in Tables 5, Table 6, and Table  
7, a more nuanced and precise evaluation of flood hazard in the study area is facilitated. This approach  
acknowledges the diverse impacts of different conditions within the factors, thereby enhancing the accuracy of  
flood hazard assessment.  
Table 5. Distance from the drainage network (water buffer)  
Class  
Distance from the river  
(m)  
Rank  
1
2
3
4
5
<200  
9
8
6
2
1
200 - 500  
500 - 1000  
1000 - 1500  
>1500  
Table 6. Elevation  
Class  
Elevation (m)  
Rank  
1
2
3
4
<200  
9
5
4
2
201 - 500  
501 - 1000  
> 1000  
Table 7. Land use type  
Class  
1
Land use type  
Water  
Rank  
9
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2
3
4
5
Paddy  
Chena, Home Gardens and Other Croplands  
Rubber  
7
5
4
3
Coconut, Tea  
The absence of certain relative scales in the analysis indicates either the non-existence of specific conditions or  
their negligible impact on flood hazard analysis within the study area. Consequently, ranks such as 7, 5, 4, and  
3 for distance from the drainage network, ranks 8, 6, 2, and 1 for land use, and ranks 8, 6, 5, 3, and 1 for elevation  
were omitted from consideration.  
This exclusion likely stems from the understanding that these ranks either do not exist in the study area or have  
minimal influence on flood hazard analysis. It was decided to exclude them as the conditions they represent are  
believed to have effects similar to other conditions within their respective factors, rendering their individual  
consideration unnecessary for the analysis. As a result, the study chose to consolidate some relative ranks to  
streamline the assessment process.  
Preparation of flood hazard map  
The flood hazard map was crafted by integrating Geographical Information Systems (GIS) applications with the  
Multi-Criteria Decision Analysis (MCDA) system. MCDA, a widely adopted decision-making method, utilizes  
digital maps to bolster decision-making processes. It serves as a robust tool for analyzing spatial data and  
facilitating informed decisions.  
In this analysis, the weighted pixels of all three factors i.e. distance from the river, elevation, and land use were  
superimposed using ArcGIS software. This integration yielded a Flood Hazard Index (FHI) for all pixels on the  
map. The FHI values, expressed as percentiles, can be computed using the following equation:  
FHI = ∑ WiRj  
(3)  
(4)  
FHI = W1*Rj + W2*Rj + W3*Rj  
FHI - Flood Vulnerability Index, W - Weightage assigned for factor, R - Rank assigned for conditions within a  
factor (from 1 to 9), i - No of factors, j - Appropriate rank of the factor  
FHI = [(Elevation Weight × Elevation Rank) + (Distance from the River Weight × Distance from the  
River Rank) + (Land Use Weight × Land Use Rank)]  
(5)  
This formula amalgamates the weighted values of each factor with the corresponding ranks assigned to the  
conditions within those factors. The resultant Flood Hazard Index (FHI) values offer a numerical gauge of flood  
hazard, ranging from 1.00 to 9.00. This quantitative representation enables the assessment of flood risk levels  
across different areas of the study region.  
The creation of the flood hazard map for the study area entailed the utilization of both fuzzy overlay and weighted  
overlay methods. These techniques are frequently employed in geographic information systems (GIS) and spatial  
analysis to generate comprehensive thematic maps that offer insights into various aspects of the landscape.  
The procedure included the preparation of three distinct ranked thematic layers, each corresponding to one of  
the factors considered in the study:  
Ranked Distance to the River or Water Buffer Thematic Layer: This layer assesses the proximity of areas  
to the river or water buffer, considering the various conditions and their influences on flood hazard.  
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Ranked Elevation Thematic Layer: This layer focuses on the elevation of different areas within the study  
region and how it impacts flood hazard.  
Ranked Land Use Thematic Layer: This layer considers the types of land use in the area and their  
respective effects on flood hazard.  
The thematic layers were constructed according to the ranking systems devised for each factor, as detailed in the  
study. Alongside these thematic layers, the previously calculated weightages for each factor, as discussed earlier,  
were considered. These weightages serve a crucial role in determining the relative significance of each factor in  
the overall flood hazard assessment. By incorporating both the ranked thematic layers and the assigned  
weightages, the flood hazard map for the Ratnapura district was generated. The process of overlay analysis is  
illustrated in the Figure 5. This map provides a visual depiction of the diverse flood risk levels throughout the  
district, considering the impact of the selected factors and their respective conditions.  
Figure 5. Weighted Overlay analysis method  
RESULTS AND DISCUSSION  
Preparation of ranked water buffer thematic layer  
The weighted water buffer thematic layer for the Ratnapura district was developed based on the drainage  
network, as illustrated in Figure 1. This thematic layer evaluates flood hazard by considering the proximity to  
rivers and their tributaries. The water buffer zones were categorized into five classes, each representing varying  
distance ranges: less than 200m, between 200m - 500m, between 500m - 1000m, between 1000m - 1500m, and  
greater than 1500m. To assign ranks to these classes, a scale derived from Saaty's 9-point scale was employed.  
However, it's worth noting that not all ranks on the 9-point scale were utilized in the criteria. Ranks 7, 5, 4, and  
3 were omitted, attributed to the absence of conditions represented by these ranks in the study area or their  
combination due to similar behaviour concerning their impact on flood hazard. The incorporation of this water  
buffer thematic layer, alongside the assigned ranks, contributes to the assessment of flood hazard in the  
Ratnapura district. It provides detailed insights into how proximity to water bodies influences flood risk in  
different regions, as depicted in Figure 6.  
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Figure 6. Ranked water buffer map  
Preparation of the ranked elevation thematic layer  
In the study area, elevation was categorized based on criteria assessing its role in flood formation. Four elevation  
classes were established, with each class assigned a relative rank to signify its influence on flood hazard. The  
ranks assigned to different elevation classes, namely less than 200m, between 200m to 500m, between 500m to  
1000m, and greater than 1000m, are 9, 5, 4, and 2, respectively.  
Figure 7. Ranked elevation map  
These ranked elevation classes were used to create the ranked elevation thematic layer, as shown in Figure 7.  
This thematic layer provides valuable information for the flood hazard assessment, helping to understand how  
varying elevations in different areas of the study region influence flood risk.  
Preparation of ranked land use thematic layer  
The land use types in the Ratnapura district were classified into five classes based on criteria designed to analyze  
flood hazard. Ranks for these land use classes, reflecting their influence on flood hazard are Water - 9, Paddy  
Lands - 7, Chena, Home Gardens, and Other Cropland - 5, Rubber, Coconut, and Tea Lands - 4, and Other Land  
Uses 3. As illustrated in Figure 8, the distribution pattern of these land use types across the study area plays a  
significant role in flood hazard analysis. For instance, paddy lands, mainly situated in low-lying areas and near  
rivers and their tributaries, are correlated with elevated flood risk. Conversely, tea lands, positioned in higher  
elevated regions, are associated with reduced flood risk. This insight into land use types and their respective  
ranks enriches our understanding of how various land uses influence flood hazard in the Ratnapura district.  
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Figure 8. Ranked land use map  
Preparation of Flood Hazard Map  
In the methodology section, the detailed process of creating the flood hazard map for the Ratnapura district is  
outlined. The map was generated by incorporating the ranked thematic layers of water buffer, elevation, and land  
use. Furthermore, the digital georeferenced road network and settlement layers were employed to evaluate flood  
vulnerability in the Kalutara district.  
Weighted Overlay  
Figure 9. Preparation of Flood Hazard Map using weighted overly procedure  
The weightages allocated to the three factors i.e. water buffer, elevation, and land use were computed using the  
pairwise comparison method, resulting in the following values: 0.544 for water buffer, 0.346 for elevation, and  
0.110 for land use. These weightage values, along with the relative ranks assigned to different conditions within  
each factor, were taken into consideration during the application of the weighted overlay procedure, as illustrated  
in Figure 9.  
The weighted overlay analysis technique, available within the ArcGIS software, was utilized to generate the  
flood hazard map for the Ratnapura district, as depicted in Figure 10. This technique facilitates the integration  
of various factors, each assigned with its respective weightage and ranked conditions, to produce a  
comprehensive map representing flood hazard across the district. The flood hazard map categorizes flood-prone  
areas in the Ratnapura district into different risk levels, including very high risk, high risk, moderate risk, low  
risk, and very low risk. A summary of the findings based on the map is provided in Figure 11.  
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Figure 10. Flood Hazard Map of the Ratnapura District  
Figure 11. Flood hazard situation in the Ratnapura district  
Very High Flood Hazard Areas: These areas are primarily located along the sides of the main rivers and their  
tributaries, situated in the Southeast and Northwest regions of the district. They are at the highest risk of flooding.  
High Flood Hazard Areas: High-risk areas are characterized by paddy and rubber lands, which are relatively flat  
and situated at lower elevations near water bodies. These areas have a significant risk of flooding.  
Moderate Flood Hazard Areas: These areas are distributed in the district, with some variability in elevation and  
distance from water bodies.  
Low Flood Hazard Areas: Low-risk areas are found in the North-eastern and South-western elevated parts of the  
district, which are situated farther away from water bodies.  
Very Low Flood Hazard Areas: These areas are also located in the North-eastern and South-western elevated  
regions, and they are the least susceptible to flooding.  
Notably, the city of Ratnapura, the main urban centre in the district, falls within the high flood hazard zone.  
According to the flood hazard map, the distribution of these risk categories in the Ratnapura district is as follows:  
Very Low Hazardous  
Low Hazardous  
: 25.47%  
: 6.00%  
Moderate Hazardous  
High Hazardous  
: 20.92%  
: 32.22%  
: 15.39%  
Very High Hazardous  
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This information provides a clear understanding of the varying levels of flood risk across different parts of the  
Ratnapura district, which can be valuable for disaster preparedness and urban planning  
Analysis of socioeconomic impact due to flood risk in Ratnapura district  
This study had a primary focus on analyzing the social and economic impacts resulting from flood risk in the  
Ratnapura district. To carry out this analysis, three critical socioeconomic vulnerability indicators were taken  
into consideration. These indicators are:  
Road Network: The condition and resilience of the road network in the district, particularly in flood-  
prone areas, were evaluated to understand the impact of flooding on transportation infrastructure.  
Human Settlements: The vulnerability of human settlements to flood events was assessed, including  
factors like population density and proximity to flood-prone areas.  
Agricultural Production: The study examined the impact of flooding on agricultural activities,  
particularly focusing on the production of crops, which is a vital component of the local economy.  
By considering these three key socioeconomic vulnerability indicators, the study aimed to provide a  
comprehensive understanding of the social and economic consequences of flood risk in the Ratnapura district.  
This information is crucial for developing effective disaster management and mitigation strategies to reduce the  
impact of floods on the local community and economy.  
Flood impact associated with road network  
To assess the flood impact on the road network in the Ratnapura district, a detailed analysis was conducted to  
identify areas with high flood risk that intersect with major and minor roads. The flood hazard map provided  
insights into this analysis, and as a result, three distinct zones with very high to high impact areas were  
demarcated, as shown in Figure 12.  
These zones encompass sections of key roadways, including the Colombo Batticaloa main road (A4), Panadura  
Ratnapura (A8) main road, Galle-Deniyaya (A17) main road, Palmadulla Embilipitiya (A18) main road, and  
certain segments of class B major roads. Notably, the majority of the very high and high flood risk areas are  
closely situated near the tributaries of the Kalu River, as well as some tributaries of the Walawe River. The three  
high-hazard zones are predominantly situated in low-lying floodplains, significantly contributing to the very  
high flood risk and potential impact on the road network in these areas.  
This information is pivotal for disaster management and road infrastructure planning, as it identifies vulnerable  
areas where flood-related disruptions to transportation routes can be anticipated during flood events.  
Figure 12. Flood risk in road network in the Ratnapura district  
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Flood impact associated with human settlements  
The study identified three regions within the study area facing very high to high flood risk, encompassing  
Eheliyagoda, Kuruwita, Kiriella, Elapatha, and Palmadulla District Secretary divisions. These areas are  
particularly susceptible to flooding, emphasizing the necessity of implementing flood mitigation and  
preparedness measures. Furthermore, by overlaying settlement maps with the flood hazard map, the study  
pinpointed several settlements situated in high flood risk areas. Approximately 4000 human settlements, 1200  
main buildings, and 35 schools are located in these high-risk areas. This information underscores the potential  
impact on the local population, infrastructure, and educational facilities in the event of a flood (Figure 13).  
Figure 13. Flood risk in settlement densities in the Ratnapura district  
Understanding the vulnerability of these settlements is crucial for disaster management and preparedness,  
emphasizing the importance of implementing strategies to safeguard lives and property in high-risk areas within  
the Ratnapura district.  
Flood impact associated with cultivated lands  
To evaluate the flood impact on agricultural lands in the Ratnapura district, an overlay analysis was conducted  
to identify areas with high flood risk intersecting with agricultural zones. Insights from the flood hazard map  
guided this analysis, revealing two major zones with very high to high impact areas, as depicted in Figure 14.  
Figure 14. Flood risk in Paddy and Rubber lands in the Ratnapura district  
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These zones primarily comprise paddy and rubber lands, situated in relatively flat and low-elevated areas along  
the tributaries and floodplains of the Kalu and Walawe Rivers. These areas are concentrated in the North-western  
and South-eastern parts of the district. The primary factor contributing to the very high flood risk and potential  
impact on agriculture in these zones is their low elevation and proximity to water bodies. Consequently, these  
very high and high flood risk areas are highly vulnerable to flooding, posing significant socioeconomic  
challenges, particularly concerning the loss of crop production and livestock. Understanding the vulnerability of  
these agricultural lands is imperative for implementing strategies to mitigate the economic impact of floods on  
the local agricultural sector.  
Validation of the created flood model  
For model validation, we compared the generated flood hazard map with a range of secondary datasets. For that,  
historical flood inventory, inundation maps and water-level reports obtained from the Disaster Management  
Centre (Disaster Management Centre, n.d.) and satellite-derived inundation maps Using TerraSAR-X Satellite  
Data (IWMI and Disaster Management Centre Sri Lanka, 2017) were compared with the generated hazard map.  
Generated flood hazard maps were also cross-validated using findings from previous research on flood-  
inundation patterns within the Rathnapura Municipal Council, which provides evidence on recurrent flood-prone  
areas in the district (Jayaprakash, Jayathilake & Munasinghe, 2016).  
Figure 15. Mapping inundation extent for Kalu ganga basin in the Western province of Sri Lanka using  
TerraSAR-X Satellite data  
To strengthen the socioeconomic dimension of the analysis GN level census and administrative indicators  
obtained from the Department of Census and Statistics, including population counts, settlement distributions and  
major income sources (Department of Census and Statistics Sri Lanka, 2020). Data on road networks and land  
use were derived from the Disaster Management Centre, Sri Lanka (Disaster Management Centre, n.d.). It  
provide more comprehensive representation of both physical and socioeconomic vulnerability patterns across  
Ratnapura District.  
CONCLUSION  
The Ratnapura district, nestled in the central highlands of Sri Lanka, faces recurrent floods, particularly during  
the Southwest monsoonal period spanning from May to September. These inundations pose significant  
socioeconomic hurdles, especially in the low-lying floodplains adjacent to the Kalu River. This research  
endeavors to unravel the distinctive flood risk landscape in the Ratnapura district, focusing on pivotal flood-  
contributing factors: proximity to the drainage network, elevation, and prevailing land use patterns within the  
area. Employing the weighted overlay analysis method in ArcGIS 10.3 software, the study crafted a  
comprehensive flood risk map for the Ratnapura district.  
The resultant map delineated regions into five categories: very low hazardous, low hazardous, moderate  
hazardous, high hazardous, and very high hazardous, encompassing approximately 25.47%, 6.00%, 20.92%,  
32.22%, and 15.39% of the total district area, respectively. Yet, the study's ambit extended beyond mere  
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identification of flood-prone zones; it juxtaposed the flood hazard map with data on road networks, human  
settlements, and land use patterns within the study domain.  
This exhaustive analysis unveiled specific roads, such as segments of the Colombo Batticaloa main road (A4),  
Panadura Ratnapura (A8) main road, Galle-Deniyaya (A17) main road, and Palmadulla Embilipitiya (A18)  
main road, as being particularly vulnerable to flooding. Furthermore, densely inhabited District Secretary  
divisions, including Eheliyagoda, Kuruwita, Kiriella, Elapatha, Palmadulla, along with certain individual  
settlements, emerged as highly susceptible to flood hazards. Moreover, paddy fields and rubber plantations,  
situated in flat, low-lying areas along the tributaries and floodplains of the Kalu and Walawe Rivers, were  
identified as flood-prone territories. Inundations in these regions possess the potential to unleash diverse  
socioeconomic ramifications in the Ratnapura district, particularly concerning the road infrastructure, human  
habitation, and agricultural output.  
In light of the identified high and very high flood risk areas, the implementation of effective flood mitigation  
strategies becomes imperative to curtail the socioeconomic fallout in the Ratnapura district and bolster resilience  
against future flood events.  
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