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 ARS  Vol.9 No.4 , December 2020
Exploitation of Satellite Data for the Mapping of Areas at Risk of Flooding in Grand-Bassam (Côte d’Ivoire)
Abstract: In order to better identify spatially the areas at risk of flooding for the riparian populations of Grand-Bassam during strong floods, a study aimed at developing hazard and vulnerability maps from RADAR Sentinel-1 and optical images Sentinel-2 has been put in place. The flood hazard study highlighted the flooded areas in Grand-Bassam. These areas represent 747.7 ha, or 1.02% of the total surface. The vulnerability map produced using the maximum likelihood method identified eight (8) land use classes. These are the classes Water, Dense forest, Secondary forest, Swamp forest, Industrial crops, Food crops, Habitats and bare soils. It made it possible to highlight the socio-economic interests of Grand-Bassam. The flood risk map developed from the intersection of the themes of the vulnerability map and that of the hazard has enabled the recognition of risk areas which are located near the source of the risk (Comoé River) and at low altitudes. These are Moossou, Petit Paris, Quartier Phare and Quartier France.

1. Introduction

Floods caused by floods are a common and recurring phenomenon in the history of mankind. Nevertheless, in recent years, these phenomena seem to be occurring at an accelerated rate and are becoming more devastating. Precise knowledge of these random phenomena is necessary for risk prevention [1]. In order to provide precise answers to the understanding of flooding problems, several studies have already been carried out around the world [2] [3] [4].

In Côte d'Ivoire, given the recurrence of these events, understanding and forecasting floods is an interesting means of flood risk prevention. However, flood forecasting through geographic information systems is currently very poorly developed, which leads to a lack of control over these phenomena in both urban and rural areas.

The coast of Côte d’Ivoire has many socio-economic interests. However, the recent floods observed undermine these interests. In fact, each year these floods cause considerable damage, namely the destruction of bridges, roads, habitats, plantations, etc.

Grand-Bassam, for its part, is faced with the phenomena of floods and floods linked to the repeated closure of the mouth of the Comoé River. These phenomena cause disasters and cause significant human and material damage. The example of the events of October 2019 is striking. Since Monday, October 14, the torrential rains which fell on the District of Abidjan and its suburbs caused flooding in several districts of Grand-Bassam including Azuretti, district France, Petit Paris, district Phare, Moossou and Ebrah, causing more than 5000 victims.

Geospatial technologies have their place in this management. Indeed, remote sensing provides many advantages. The acquisition of radar data is independent of weather conditions. These data have a greater ability to penetrate the natural environment. Several authors including [5] [6] use these data for flood mapping, respectively in the Moselle department (France) and in the San-Pédro region (Côte d’Ivoire).

Knowledge of hazards and flood risks is a fundamental prerequisite for their prevention. Hence the need for this study entitled: “Exploitation of satellite data for the mapping of areas at risk of flooding in Grand-Bassam (Côte d’Ivoire)”.

2. Materials and Methods

2.1. Study Area

Grand-Bassam is located in the South East of the Ivory Coast bordering the Atlantic Ocean (Figure 1). It is located 36.2 km from Abidjan and its geographical coordinates are 05˚14' North latitude and 03˚45' West longitude. The locality of Grand-Bassam is the capital of the department of Grand-Bassam in the administrative region of southern Comoé. It includes three sub-prefectures which are Grand-Bassam, Bonoua and Bongo.

The Grand-Bassam area is drained by three rivers which are: the Comoé river and the Ebrié and Ouladine lagoons. These waters have crept into all the depressions, thus creating multiple arms. These rivers meet to form the largest estuary on the Ivorian coast at Grand-Bassam [7]. From a climatic point of view, the wetland is subject to an equatorial climate of transition with four alternating rainy and dry seasons. The great rainy season from April to June is interrupted by a short dry season from July to September. The long dry season lasts from December to March and is preceded by the short rainy season which lasts from

Figure 1. Geographical location of Grand-Bassam.

October to November. The coastal facies is very humid with an average annual rainfall exceeding 1500 mm. The annual average temperature is 26.2˚C. Grand- Bassam is characterized by a plain whose altitudes rarely exceed 50 m. The relief is made up of flat and sandy soil, more or less marshy lowlands with the presence in places of forest islands [6].

2.2. Available Data

To carry out this work, the data used mainly consists of remote sensing data. These are three Sentinel-1 RADAR images and one Sentinel-2 optical image. Regarding the Sentinel-1 RADAR data, we have, one (1) excluding floods and two (2) during the flood period. The characteristics of these images are presented in Table 1 and Table 2.

Sentinel-1 and Sentinel-2 data was provided by the Copernicus program's Sentinel data distribution platform with a policy of free and open data access to everyone with a guarantee of long-term continuity (https://scihub.copernicus.eu/dhus/#/home).

2.3. Methodology

2.3.1. Pre-Processing of “RADAR Data”

· Calibration

Multilooking made it possible to have square pixels on the ground and to

Table 1. Sentinel-1 RADAR data characteristics.

Table 2. Sentinel-2 optical data characteristics.

reduce flickering. To carry out the multilookage, it is necessary to find the average pixel size along the Prange radar sight and to project it on the ground using the angle of incidence at the center of the scene θC according to Equation (1):

P range sol = P range sin ( θ C ) (1)

where, P range sol the size of the pixel on the ground.

We then calculate the following ratio in order to know the number of lines to be averaged:

R = P range sol P a z (2)

where: Paz: pixel size in azimuth. The number of views has been set to 5 views.

· Terrain correction

The use of SAR radar images in conjunction with other sources of information (optical images, GPS) requires that they be properly georeferenced. Georeferencing is an operation which consists in projecting images in the plane to make them conform to a projection system. Thus, all the images used were georeferenced in the WGS 84 geodetic system and in the UTM projection in zone 30 North.

· Filtering

RADAR images are subject to the effects of speckle, which makes them difficult to use without prior processing. The filter used for the removal of speckles is that proposed by [5]. The advantage of this filter lies in its ability to effectively reduce speckles in homogeneous and heterogeneous areas and to conserve both the spatial resolution and the reflectivity levels of targets or isolated heterogeneous structures [8]. This filter is one of the filters best suited to processing multipolarized SAR images [6] [9] [10].

2.3.2. Flood Hazard Mapping

It was possible to isolate the flood zones by simply thresholding the numerical values of the radar backscatter coefficient. Indeed, the thresholding of an image makes it possible in particular to identify and isolate certain values which identify objects which have the same spectral characteristics.

Pixels in flood zones have values less than −15 dB. All the pixels whose numerical value is lower than the threshold value of −15 dB have to be assigned to the class “flood zones”. This is also the case with [6], who used it to discriminate against flooded areas in the San-Pédro region (Côte d’Ivoire).

2.3.3. Vulnerability Study

The aim here is to highlight the threatened socio-economic issues. To do this, an image of Sentinel 2 is used to make the land use map. The coupling of the land use map with the field campaigns is carried out in order to map the threatened socio-economic issues, to quantify them and to highlight the sensitivity of the environment to the risk of flooding. Information on land use is obtained from classifications supervised by the maximum likelihood method [7]. Photo- interpretation of composite images from optical data, combined with aerial photographs and calculated indices, identified land cover classes. For a good appreciation of the landscape units, three classifications were made from the three colored compositions (true colors, infrared and atmospheric penetration).

2.3.4. Estimate of the Flood Risk

The flood risk takes into account the flood hazard and the vulnerability to flooding. The method used to obtain the risk is the direct application of its mathematical definition which results in the following formula [11]:

R = A * V (3)

with: A: Alea; R: Risk; V: Vulnerability.

3. Results

3.1. Mapping of Flooded Areas

The histogram thresholding applied to the various Sentinel-1 RADAR images made it possible to highlight the flooded surfaces. Figure 2 illustrates the flood conditions of Grand-Bassam. The flooded areas represent 747.7 ha, or 1.02% of the total area for the 17th, and 101.8 ha, or 0.14% of the total area for the 29th.

We note that these flood hazard zones occur mainly near the Comoé River (Figure 2).

The superposition of the flooded areas on the relief map provides information on the areas favorable to flooding. Note that the flooded areas are located at the lowest altitudes; between 0 and 8.2 m altitude.

Figure 2. Maps of flooded areas obtained from RADAR Sentinel-1 satellite images.

3.2. Vulnerability to Flooding

Information on land use was obtained from classifications supervised by the maximum likelihood method. This method, carried out on the basis of photo-interpretation of satellite images coupled with field investigations, made it possible to produce the land use map essential for a good analysis of vulnerability to flooding (Figure 3). The land use map made it possible to highlight the socio-economic interests of Grand-Bassam.

From these results to determine land use, we determined eight classes. Floods affect populations and areas with socio-economic interests. This is highlighted through the flood risk map (Figure 4).

4. Discussion

The characterization of the flood hazard, carried out using the thresholding histogram method, made it possible to discriminate the flooded areas in Grand-Bassam. The results show that 747.7 ha of land were flooded on October 17, 2019 and 101.8 ha on October 29, 2019. This corresponds respectively to 1.02% and 0.14% of the studied area. These observed values, considered to be considerable, are the product of the abundant rains that fell during the month of

Figure 3. Land use in the study area.

Figure 4. Map of areas at risk of flooding.

October 2020 in the locality of Grand-Bassam. Similar studies carried out by [6] in San-Pédro also showed heavy flooded areas. This region, characterized by abundant rains reaching 2000 mm per year, was the subject of a catastrophic event in July 2017. This study showed that 6007 ha of land had been inundated on June 16, 2017. In addition, the superposition of the flooded surfaces on the relief map showed that the floods occur in areas of low altitudes (0 - 8.2) m. Indeed, the flat or slightly undulating relief of Grand-Bassam is not very conducive to good drainage of rainwater. It promotes diffuse runoff in these areas, which leads to rapid soil saturation. We are therefore witnessing flooding by runoff of accumulated rainwater. Moreover, according to [12], relief is an essential factor conditioning the flow of water on the ground surface. Low slope areas are in places submersible during the wettest months (June to September) of the rainy season in Man region.

In terms of vulnerability to flooding, the land use map produced using the maximum likelihood method identified eight (8) classes in the following proportions: Water 24%, Dense forest 8%, Secondary forest 16%, Swamp forest 2%, Industrial crops 34%, Food crops 1%; Habitats 10%, Bare soils 5%. Its analysis made it possible to recognize the issues on the ground vulnerable to flooding. These are areas of economic and social interest marked by the presence of habitats and industrial and food crops. These results are in the same field as those of [10], with differences in size linked to the different areas studied. In addition, the analysis of the land use reveals that the way of occupying the space accentuates the vulnerability to floods. Thus, the innumerable more or less regular real estate transactions create ecological conditions where rainwater can no longer penetrate into the ground. They therefore flow towards the lowest point, the mouth of the Comoé River. And, with the mouth closed, the water finds its place where it can, makes its bed as it wants. This is in agreement with the study carried out by [13] in Agboville which states that the way of occupying the land is an essential factor conditioning the submersion process. The people of Agboville prefer to occupy the lowlands which they consider favorable for petty trade and rice cultivation. However, by settling on these sites, they regularly obstruct the drainage paths of runoff water and therefore expose themselves to flooding. Regarding the spatialization of risk, the crossing between the vulnerability and hazard maps reveals that floods affect both areas of economic interest and populations. Thus, 560 ha of industrial crops and 80 ha of food crops are flooded on October 17, 2019; and, regarding habitats, 19 ha were flooded. The economic issues that have suffered considerable impacts are industrial crops representing 2.23% of the flooded area. As for Habitats, the results obtained are significant (0.26% of the flooded area) insofar as these floods cause environmental degradation, material damage and social disturbances. This is corroborated by the work of [6] in the city of San-Pédro; these indicate that many socio-economic interests namely: port, industrial, residential, agricultural areas are damaged by the floods in this city.

5. Conclusions

In conclusion, this study, based on the RADAR and optical image processing phase, allowed a spatial characterization of the flood risk linked to the flood of October 14, 2019 in Grand-Bassam. The spatial characteristics obtained are the estimate of the extension of the water according to the relevance of the RADAR information and the classification of the types of land use in the flooded plain.

The spatialization of the water carried out by histogram thresholding applied to the Sentinel-1 RADAR images made it possible to discriminate the flooded areas. They are estimated at 747.7 ha, or 1.02% of the total area. The maximum likelihood method allowed us to know the distribution of land use and to assess the flooded areas. A total of eight (8) land use classes have been identified. These are the classes Water 24%, Dense forest 8%, Secondary forest 16%, Swamp forest 2%, Industrial crops 34%, Food crops 1%; Habitats 10%, Bare soils 5%.

The coupling of maps relating to the themes of hazard and vulnerability made it possible to identify areas at risk of flooding in Grand-Bassam. These areas are located at low altitudes and near the Comoé River. These areas are represented by Moossou, Petit Paris, Quartier Phare and Quartier France. A total of three (3) interest classes are exposed to the risk of flooding. These are the Habitats, Industrial crops and Food crops classes.

The results obtained show that the contribution of RADAR Sentinel-1 and Sentinel-2 optical data for flood mapping is significant.

However, a 2D numerical modeling would be interesting in non-permanent flow in order to predict the areas likely to be flooded and the maximum height of the water level in the event of overflow of the bed of the Sassandra river at San-Pédro.

Cite this paper: Kouassi, K. , Kouadio, Z. , Konan-Waidhet, A. , Affessi, A. and Kouassi, K. (2020) Exploitation of Satellite Data for the Mapping of Areas at Risk of Flooding in Grand-Bassam (Côte d’Ivoire). Advances in Remote Sensing, 9, 117-126. doi: 10.4236/ars.2020.94007.
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