Research Article | | Peer-Reviewed

Flashflood Hazard Assessment in Yewa South Lga

Received: 1 February 2025     Accepted: 18 February 2025     Published: 7 March 2025
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Abstract

In the bid to accomplish the Sustainable Development Goals, several attempts have been made in Yewa South LGA to accomplish environmental sustainability (SDG7) and reduce the adverse effects of climate change (SDG13). The area has witnessed recurrent flash floods with deleterious effect to lives and properties due to anthropogenic factors coupled with incessant torrential rainfall events which are the major drivers of flood vulnerability in the area. Previous studies have adopted the use of GIS, Remote sensing or an integration both techniques with associated challenges. This study adopts the use of Hydrologic Engineering Centre’s Hydrologic Modelling System with Geographic Information Systems (HEC-GeoHMS) to evaluate the relationship between rainfalls, terrain characteristics, run off and stream flow as an alternative flood mitigation scheme. The catchment area was divided into forty-five sub basins over a 10m DEM, the run off hydrographs simulated and the hydrological characteristics modelled by using rainfall data between 1st June, 2022 – 31st May, 2023 as well as discharge data from Ogun-Osun River basin Development Authority (O-ORBDA). the model parameters were optimized for calibration and the calibrated model was thereafter validated using three statistical evaluation criteria which showed that there is a good simulation between the observed and estimated values (Rep = -2.24%, REv = 6.67%, NSE = 95.03%, and R2 = 0.83). Further analysis of the results showed that the flash flood is induced mainly by hydrologic characteristics of the area. This work therefore proposes to mitigate flood in Yewa South Local Government Area of Ogun State by modelling how excess water runs on the terrain thereby creating flash floods. The model will serve as an input for putting mitigation measures in place to arrest flash floods.

Published in Journal of Civil, Construction and Environmental Engineering (Volume 10, Issue 2)
DOI 10.11648/j.jccee.20251002.11
Page(s) 49-59
Creative Commons

This is an Open Access article, distributed under the terms of the Creative Commons Attribution 4.0 International License (http://creativecommons.org/licenses/by/4.0/), which permits unrestricted use, distribution and reproduction in any medium or format, provided the original work is properly cited.

Copyright

Copyright © The Author(s), 2025. Published by Science Publishing Group

Keywords

HEC-GeoHMS, Flashflood, Hazard, Mitigation, Hydrographs

1. Introduction
The growing population of Yewa and the increasing infrastructural development coupled with the incessant torrential rainfall events have increased the vulnerability of more lives and properties to flood disasters. Floods are caused by interaction of rainfall and the characteristics of the catchments.
How a catchment responds to rainfall under different physical characteristics such as soil properties, land use land cover, ground topography etc. , the aftermaths of which is a necessity to properly estimate the quantity of rainfall runoff generated in a watershed. The study of the responses of the catchments to the rainfall, the amount of the rainfall and movement of underground water, are fundamentals to predict the hazards of pollution, flood and mitigation measures to protect these resources.
Floods according to Sherif et al., are the aggregations of hydrological, geomorphological, and meteorological conditions This have become an annual event in Yewa, occurring in the form of river flood, flash floods and urban flood. Flash floods are built up by specified geographical and physical factors that are mandatory for mitigation scheme. The mitigation schemes are based on various earth sciences which includes hydrology, geomorphology and meteorology . Flash floods are special type of natural disasters that develops rapidly within a short duration. It is one of the most widespread environmental hazards in the world . In the recent times, the flood events have greeted many states and cities.
Yewa communities like most communities in Nigeria have experienced severe flooding incidents . It is on this premise that environmental activists some time ago called on the Federal Government to urgently declare a state of emergency on the environment to address issues relating to climate change as it spiraled into diseases and deaths thus, degrading the environment. This awareness is tagged world environment day and marked on every June 5 of the year.
Many researches have been conducted on flood risk assessment from diverse perspectives. The success of their outcome has been a function of the availability of qualitative data used, objectives of the flood risk assessment study and the expected results. The World Health Organization and the United Nations have both begun to emphasize that flash flood risk is becoming a growing concern in low-to-middle-income nations .
Olayinka & Irivbogbe applied the use of Remote Sensing, HEC-HMS, HEC-RAS and GIS to model and map flood in the adjoining areas of Lagos Island and part of Eti-Osa Local Government Areas of Lagos State . Flood hazard map and 3D views of the flood model results were prepared and buildings that are prone to risk were assessed.
Adewara & Olapeju integrated Rainfall, Soil, Land Use Land Cover (LULC), Digital Elevation Model (DEM), Normalized Difference Vegetative Index (NDVI), Topographic wetness Index (TWI) and Drainage Density to identify areas liable to flooding in Kogi State using ArcGIS and Spatial Multi-Criteria Decision Analysis (SMCDA) . Weighted overlay was performed to produce Hazard map of the state reclassification of the data. Results showed that the study area is characterized by low NDVI, low elevation and high rainfall waters, thus rendering the area highly vulnerable to flood.
In another development, Hassan et al., examined how urbanization, land use, and drainage infrastructure changes over the years contributes to flood risks and posited that improved drainage infrastructure is a necessary component to future resilience .
Very few researches have attempted to study flash flooding in Yewa South LGA of Ogun State, all of which have not studied it from environmental engineering perspective. Very few have studied it from hydraulic and hydrologic points of view, which is the bases for this present effort. Hydrological modelling has shifted from generating stream flow hydrographs into estimating distributed surface and subsurface flows. This paradigm shift necessitates a holistic description of the basin topography and the distributed properties of the hydrological processes acting on it . This present study integrates varieties of hydrologic flood data into Hydrologic computer program such as HEC-HMS and ArcGIS and statistically evaluating the outcomes which is a shortfall perceived in previous studies.
2. Materials and Method
2.1. The Study Area
The average coverage area of Ilaro is 622.226 km2. The main river traversing the study area is the Yewa river, travelling 25.748km long southwards from the Ogun river, cutting across major towns like Idogo, Ebute Erimi, Alapa, Ojete, Ibiwo, Ojumo, Oke-Odan among others. Approximately, about 40% of the towns in the LGA lie on flood plains. The river empties its content into the Atlantic Ocean through the Badagry waters. The river is mostly used for agricultural supports. The climate of Yewa is classified as Tropical wet and dry climate with temperatures between 88-99 degrees Celsius. Precipitation is highest in September and October with an average of 80mm according to Ogun Osun River Basin Development (O-ORBD). Predominantly, Yewa south is a relatively flat terrain, a factor which is attributable to its flood characteristics as indicated in Figure 1.
Figure 1. Elevation, Land Use Land Cover, Drainage Network and Slope maps of the study area.
2.2. Sources of Data
Several factors which demands research in details lead to the formation of flash floods: hydrometeorological, lithological and geomorphological, and anthropogenic factors . Anthropogenic factors are not the main causes of flash flood but they reinforce flash flood-producing forces. Lithological and geomorphological factors are precipitation, time of flow concentration, basin area etc while hydrometeorological factors are elevation within the basin, basin slope, land use land cover, rainfall, discharge flow data etc as shown in Figure 1 and Table 1.
Table 1. Data used for the study.

SN

Data

Purpose

Source

1

10m DEM

Data support for Hydrologic computations & modelling

NASA (https://urs.earthdata.nasa.gov/oauth/authorize?response_type= code&client_id=OLpAZlE4HqIOMr0TYqg7UQ&redirect_uri=https%3A%2F%2Fd53njncz5taqi.cloudfront.net%2Furs_callback&state=https%3A%2F%2Fsearch.earthdata.nasa.gov%2Fdownloads%2F5915390643%3Fee%3Dprod)

2

LULC

To estimate manning’s value at each river cross section

Sentinel-2 10m Land Use/Land Cover Time series Downloader (https://www.arcgis.com/apps/instant/media/index.html?appid=fc92d38533d440078f17678ebc20e8e2)

3

Drainage Network details

Hydrographic data

Office of Surveyor General of the Federation (OSGOF)

5

Discharge, flow

Hydrologic modelling

Ogun-Oshun River Basin Development Authority, O-ORBDA

Abeokuta, Ogun State, Nigeria

7

Monthly rainfall data

Hydrologic modelling

Ogun-Oshun River Basin Development Authority, O-ORBDA

Abeokuta, Ogun State, Nigeria

8

Soil

Run off Curve Number determination

Harmonized World Soil Database

Source: Authors compilation
2.3. HMS Data Input
Hydrometeorological, lithological and geomorphological, and anthropogenic parameters serve as inputs to HMS. They are assigned using the sub-basin parameters option in HEC-HMS. SCS for Loss Method was selected to get excess rainfall from total rainfall and the SCS unit hydrograph for Transform Method was chosen to convert excess rainfall to direct runoff. The loss models in HEC-HMS normally calculate the runoff volume by computing the volume of water that is intercepted, infiltrated, stored, evaporated, or transpired and subtracting it from the precipitation. In this study, the Soil Conservation Service Curve Number loss method was selected to estimate direct runoff from a specific or design rainfall as also adopted in .
3. Results
The ability of the simulated data to adequately match observed data is a function of acceptability of the result outcomes. Rainfall events were classed into 6 events as seen in table 2 below. Four rainfall events were selected for calibration while two rainfall events were selected for validation.
Table 2. Rainfall events selected for Calibration & Validation.

Events

Start date

Start time

End date

End time

Selection

Event 1

Jun 10th 2022

0:00

Jul 24th 2022

0:00

Calibration

Event 2

Aug 25th 2022

0:00

Aug 31st 2022

0:00

Calibration

Event 3

Sept 4th 2022

0:00

Sept 11th 2022

0:00

Calibration

Event 4

Oct 9th 2022

0:00

Oct 14th 2022

0:00

Calibration

Event 5

Jan 24th 2023

0:00

Jan 31st 2023

0:00

Validation

Event 6

Apr 4th 2023

0:00

May 19th 2023

0:00

Validation

3.1. Catchment Delineation
HEC-HMS was used to hydrologically discretize the region into sub-catchments for homogenous analysis of land-use, soil type, etc. in order to address the spatial distribution of catchment features.
Figure 2. Hydrologically Connected Sub-Basin.
Table 3. Loss parameters.

CN

Ɩ (Km)

Basin slope

Area (sqkm)

S = (1000/CN)-10

Y (%)

Tc

Lag (min)

Innitial Abstraction =0.2S

Subbasin-1

62

6.55294

0.01209

13.70213

6.129032

1.209

90.62141

3262.371

1.225806

Subbasin-10

62

5.24796

0.00404

3.758467

6.129032

0.404

131.2492

4724.972

1.225806

Subbasin-11

62

3.82998

0.00711

7.073021

6.129032

0.711

76.89842

2768.343

1.225806

Subbasin-12

62

6.14985

0.00264

15.15225

6.129032

0.264

184.3252

6635.706

1.225806

Subbasin-13

60

6.57634

0.00353

8.404761

6.666667

0.353

176.9694

6370.9

1.333333

Subbasin-14

62

7.68589

0.008

8.819081

6.129032

0.8

126.5626

4556.253

1.225806

Subbasin-15

62

6.05414

0.00351

3.610496

6.129032

0.351

157.8641

5683.108

1.225806

Subbasin-16

22

6.23839

0.00676

8.227196

35.45455

0.676

365.1611

13145.8

7.090909

Subbasin-18

81

4.09055

0.00916

4.468729

2.345679

0.916

42.05234

1513.884

0.469136

Subbasin-19

81

6.2618

0.00496

8.404761

2.345679

0.496

80.33987

2892.235

0.469136

Subbasin-2

81

6.16714

0.00685

13.82051

2.345679

0.685

67.53585

2431.29

0.469136

Subbasin-20

22

6.16102

0.01098

9.144617

35.45455

1.098

283.6748

10212.29

7.090909

Subbasin-21

21

5.86482

0.00767

12.72552

37.61905

0.767

339.7354

12230.47

7.52381

Subbasin-22

81

5.02807

0.01153

9.914067

2.345679

1.153

44.20984

1591.554

0.469136

Subbasin-23

21

4.51198

0.007

5.238179

37.61905

0.7

288.3231

10379.63

7.52381

Subbasin-25

81

10.14216

0.00883

14.20523

2.345679

0.883

88.5598

3188.153

0.469136

Subbasin-26

81

8.01266

0.00384

17.19425

2.345679

0.384

111.2163

4003.786

0.469136

Subbasin-27

21

5.2001

0.00528

10.44676

37.61905

0.528

371.9008

13388.43

7.52381

Subbasin-28

22

14.96004

0.00546

26.07252

35.45455

0.546

817.9931

29447.75

7.090909

Subbasin-29

81

4.20355

0.00762

7.635311

2.345679

0.762

47.12247

1696.409

0.469136

Subbasin-30

21

2.88634

0.0071

3.462525

37.61905

0.71

200.2551

7209.182

7.52381

Subbasin-31

62

3.61009

0.00743

5.504527

6.129032

0.743

71.74886

2582.959

1.225806

Subbasin-32

62

3.82998

0.00367

6.362759

6.129032

0.367

107.0334

3853.201

1.225806

Subbasin-33

22

5.3365

0.0101

6.895456

35.45455

1.01

263.66

9491.761

7.090909

Subbasin-34

62

3.12963

0.00572

4.735077

6.129032

0.572

72.9443

2625.995

1.225806

Subbasin-35

62

3.82386

0.01079

3.166583

6.129032

1.079

62.34274

2244.339

1.225806

Subbasin-36

81

3.36681

0.0067

3.314554

2.345679

0.67

42.07751

1514.791

0.469136

Subbasin-37

21

3.30777

0.00677

3.551308

37.61905

0.677

228.7013

8233.246

7.52381

Subbasin-4

81

4.33995

0.01123

7.191398

2.345679

1.123

39.82085

1433.55

0.469136

Subbasin-40

81

5.55639

0.007

7.132209

2.345679

0.7

61.46073

2212.586

0.469136

Subbasin-42

81

4.5181

0.00958

5.859658

2.345679

0.958

44.52403

1602.865

0.469136

Subbasin-43

22

7.56783

0.00695

11.71932

35.45455

0.695

420.3243

15131.67

7.090909

Subbasin-45

81

5.61542

0.00768

6.451542

2.345679

0.768

59.17493

2130.298

0.469136

Subbasin-49

81

7.69811

0.01034

14.82671

2.345679

1.034

65.63865

2362.991

0.469136

Subbasin-5

62

7.06291

0.00363

12.34079

6.129032

0.363

175.6017

6321.66

1.225806

Subbasin-50

61

4.74916

0.00674

8.108819

6.393443

0.674

96.23428

3464.434

1.278689

Subbasin-54

81

4.31655

0.01141

5.59331

2.345679

1.141

39.335

1416.06

0.469136

Subbasin-57

62

5.68668

0.00652

5.682092

6.129032

0.652

110.1687

3966.073

1.225806

Subbasin-6

21

3.30777

0.00889

3.018611

37.61905

0.889

199.5777

7184.798

7.52381

Subbasin-64

62

9.69121

0.00658

12.25201

6.129032

0.658

167.9904

6047.654

1.225806

Subbasin-69

81

5.52687

0.00469

5.238179

2.345679

0.469

74.76693

2691.61

0.469136

Subbasin-7

22

4.66061

0.00516

4.40954

35.45455

0.516

331.0009

11916.03

7.090909

Subbasin-71

62

4.85604

0.00452

4.113598

6.129032

0.452

116.6142

4198.113

1.225806

Subbasin-8

81

4.37558

0.0069

6.777079

2.345679

0.69

51.1348

1840.853

0.469136

Subbasin-9

61

8.78932

0.00867

16.27683

6.393443

0.867

138.842

4998.313

1.278689

Source: Authors results
3.2. Model Calibration
The model was calibrated and result of calibration is shown in figures 2 & 3. The Nash–Sutcliffe Efficiency (NSE) in equation 4 was used to test calibrated model to confirm that the hydrograph of observed values matches with the simulated values .
Table 4. Observed and simulated values before and after optimization.

Events

Observed

Peak Discharge (m3/s)

Total Volume (mm)

Simulated

Simulated

Bopt

Aopt

REp

Observed

Bopt

Aopt

REv

NSE

Event 1

18.37

31.8

19.6

-0.067

315.83

362.83

337.02

-0.067

0.958

0.741

Event 2

114.68

345.2

122.7

-0.070

156.13

142.01

166.3

-0.065

0.968

0.940

Event 3

230.21

205.8

248.6

-0.080

150.85

142.31

176.43

-0.170

0.829

0.623

Event 4

18.70

211.9

17.2

0.080

332.64

253.31

355.12

-0.068

0.965

0.709

Mean

95.49

198.68

102.03

0.03

226.188

218.02

243.034

0.079

0.940

0.800

Bopt = Before optimization, Aopt=After optimization, Rep = Relative Error of Peak Discharge, REv = Relative Error of Total volumes
Figure 3. Model Simulation before Calibration (Authors results).
NSE=1-t=1TQ0t-Qmt2t=1TQ0t-Q0-2(1)
Where;
Qo = mean of observed discharges (m3/s), and
Qm = modeled discharge (m3/s), and
Qot = observed discharge (m3/s) at time t.
According to Nash–Sutcliffe, model efficiency ranges from infinity to 1.
E = 1 implies that there is a perfect match between modeled discharge and the observed data.
E = 0 implies that that the predictions of model are as accurate as the mean of the observed data, E < 0 implies that the observed mean is a better predictor than the model.
Figure 4. Model Simulation after Calibration (Authors results).
3.3. Model Validation
The calibrated model result was further subjected to validation where two extreme events, events 5 and 6 shown in Table 4 within the 12 months rainfall data that are different from the four extreme rainfall events were used for the model validation.
Table 5. Observed and simulated values before and after optimization.

Events

Observed

Peak Discharge (m3/s)

Total Volume (mm)

Simulated

Simulated

Bopt

Aopt

REp

Observed

Bopt

Aopt

REv

NSE

Event 5

166.92

227.2

157.1

0.060

175.49

189.93

180.3

-0.027

0.983

0.987

Event 6

71.05

49.2

75.1

-0.060

144.79

178.08

145.45

-0.005

0.999

0.999

Mean

118.98

138.2

116.1

0.001

160.14

184.001

162.88

-0.016

0.992

0.993

Bopt= Before optimization, Aopt=After optimization, REp= Relative Error of Peak Discharge, REv = Relative Error of Total volumes
Three statistical evaluation criteria were used in this study and they showed that there is a good simulation between the observed and estimated values (REp= 0.001%, REv = -0.016%, NSE=0.992%, and R2= 0.993).
Table 6. Sub Basin Characteristics.

Hydrologic Elements

Area_sqkm

Peak Discharge (m3/s)

Loss Volume (mm)

Excess Volume (mm)

Direct Runoff Volume (mm)

Town

Subbasin-4, 18 & 22

21.57419379

4.5

144.96

585.52

585.38

Ilobi/Erinja

Subbasin-2, 12 & 36

32.2873051

3.9

192.64

537.74

531.71

Igbobe

Subbasin-1, 6, 16, 20, 28, 33 & 50

75.16934461

3.1

1170.93

533.29

486.30

Ilaro

Subbasin-26, 32 & 71

27.6706052

3

240.32

490.06

485.56

Idogo/Ipaja

Subbasin-29 42

13.49496895

2.7

96.64

390.38

390.23

Okuta

Subbasin-19 & 25

22.60999184

3.3

96.64

390.38

389.05

Erimi-Oguntade

Subbasin-8, 27 & 34

21.95891878

2.1

341.06

389.32

380.44

Ajelete

Subbasin-31 & 57

11.186619

1.2

192

294.92

293.27

Erimi-Ebute

Subbasin-5, 30, 37, 43

31.07394167

1.2

683.8

290.04

267.68

Owode

Subbasin-23 & 45

11.68972091

1.2

245.06

241.86

235.92

Ajilete

Subbasin-54

5.5933095

1.2

48.32

195.24

195.13

Oju-Ota

Subbasin-40

7.132209469

1.1

48.32

195.14

194.99

Iwoye

Subbasin-49

14.82670931

2.4

48.32

195.24

194.93

Alagbe

Subbasin-69

5.238178738

0.8

48.32

195.14

194.76

Araromi

Subbasin-14 & 21

21.54459956

1

292.74

194.18

184.57

Oke-Odan

Subbasin-35

3.166582627

0.4

96

147.46

147.32

Oke-Erinja

Subbasin-11

7.073021008

0.9

96

147.46

147.09

Ipake

Subbasin-10

3.75846723

0.3

96

147.46

145.1

Irogun-Akere

Subbasin-15

3.61049608

0.3

96

147.46

143.53

Ayekoshe

Subbasin-64

12.25201129

0.9

96

147.46

142.86

Ipaja

Subbasin-9

16.27682659

1.3

98.49

144.97

142.22

Elemuren

Subbasin-13

8.404761366

0.6

100

142.48

137.34

Kakanfo

Subbasin-7

4.409540294

0.1

194.32

49.14

41.6

Iweke

Source: Authors results
Table 7. Flash Flood Susceptibility Threshold.

Class

Susceptibility Threshold

500-600

Extremely High

400-500

Very High

300-400

High

200-300

Medium

100-200

Low

0-100

Very low

Source: Authors analysis
4. Discussion
The catchment was subdivided into 45 sub basins as shown in Figure 4 which were categorized into different CN based on the LULC as seen in Table 5. The LULC in Figure 1 showed that the area is dominated by crops, herbaceous grasslands, herbaceous wetlands, and Built-up areas (High/Low intensity Residential), which significantly contribute to the economic importance of the area.
4.1. Calibration and Validation
An NSE of 0.94 was obtained, thus indicating that the model and its parameters are very reliable since this value fall within NSE efficiency range from infinity to 1 according to Nash–Sutcliffe.
The model results with respect to observed data, NSE and Coefficient of determination (R2) shows the peak discharge and its relative errors as well as the total volume and its relative errors) in Table 3.
The simulated results of the peak discharge, total volume and their relative errors with respect to the observed data as well as the NSE and Coefficient of determination (R2) were validated using events 5 and 6 (Table 4 & Figure 3), implying that there is close semblance between the simulated and observed values (Table 4) for all the events. The average relative percentage error between observed and simulated peak flow values is -0.001% while average relative percentage error between observed and simulated total volume is -0.016%. A Coefficient of determination (R2 = 0.992) was obtained, showing that there is also a close agreement between the observed and simulated peak flow values. Using the NSE evaluation criteria, a better NSE value of 99.2% was obtained between the observed and simulated values.
These findings conform with the results of , and also gives acceptability to the overall model performance. A comparison of the model result with historical flood events data from O-ORBDA was performed which showed that the area is susceptible to flood at varying degrees, thus trusting the validity of the model, hence, a good reflection of ground reality as observed in .
4.2. Elevations
The slope of the catchment is divided into five classes, viz. very flat (0– 0.188 degrees), Gentle (0.188–0.421 degrees), Moderately gentle (0.421– 0.635), Gentle steep (0.635–0.895 degrees) and Steep (0.895 - 1.654 degrees), as shown in Figure 1. The maximum precipitation in the study area is usually from July to October, leading to increased devastating floods at these period. While 75% of flash floods occur in August, September and October (According to authors’ analysis).
The most destructive type of floods are flash floods in smaller basin areas. The smaller a basin the faster is the flood wave that is formed. For instance, the time it takes water to travel in Sub-basin 1 (13.7km2) is 3,262 minutes while the lag time in a smaller basin (sub-basin 35) with 3.166km2 area is 2,244 minutes as seen in Tables 5 and 6.
4.3. Sub Basin Areas and Runoffs
Data analysis demonstrated that the flash floods in Ilaro, Owode, Oke-Odan, Ajelete, Igbobe, Idogo, Olute, Akere, are more extreme having sub-basin coverage between 3.0km2 and 5.0km2 with corresponding lag times between 2,691 minutes and 7,185 minutes respectively as indicated in Table 5 & Table 6.
Based on the run off volumes in Table 6, the study area has been classified into six (6) flash flood susceptibility thresholds (Table 3): Extremely high (Ilobi/Erinja and Igbobe), Very high (Ilaro and Idogo/Ipaja), High (Okuta, Erimi-Oguntade and Ajelete), Medium (Erimi-Ebute, Owode and Ajilete), Low (Oju-Ota, Iwoye, Alagbe, Araromi, Oke-Odan, Oke-Erinja, Ipake, Irogun –Akere, Ayekoshe,, Ipaja,, Elemuren and Kakanfo) and Very low (Iweke) respectively.
5. Conclusion
The small nature of spatial and temporal scale of flash flood events makes its study to be complicated. Its main factors being hydrological and meteorological, lythological and geomorphological, as well as anthropogenic.
Beyond the conventional flood depth and hazard maps preparations, other flood triggering characteristics can be generated by integration of GIS, HEC-HMS numerical modelling approach and statistical analysis of the output hydrological characteristics.
Water levels from the drainage networks have dropped between 2020 and 2022 in Yewa. However, the duration of flooding continues to increase.
6. Recommendations
As historical records showed that the periods of floods keep increasing, there is high probability that these tendencies, according to climate change scenarios will persist in the future. To keep abreast of this tendency requires stepping up the existing methods of approaches to addressing flood issues by embracing the adopted method in this study. Successful flow rate data simulation of Yewa South LGA through rainfall-runoff modelling using HEC-HMS can be used for further hydrological analysis. To adopt this method in other areas, this present study envisaged establishment of gauging stations in catchment areas in Nigeria to have a more refined data since the quality of data output is a function of the input data.
Acknowledgments
The authors acknowledge the Ogun-Osun River Basin Development Authority (O-ORBDA), for providing the flow and Rainfall data; National Aeronautics and Space Administration (NASA), for making Elevation Data available for use. We appreciate the Sentinel-2 Land use Land cover data from the European Space Agency as well as the Drainage Network details from the Office of Surveyor General of the Federation (OSGOF). We also would like to thank the Hydrologic Engineering Centre and Environmental System Research Institute (ESRI) for enabling us to use their HEC-HMS and ArcGIS computer programs.
Abbreviations

O-ORBDA

Ogun-Osun River Basin Development Authority

NASA

National Aeronautics and Space Administration

OSGOF

Office of Surveyor General of the Federation

LULC

Land use Land Cover

DEM

Digital Elevation Model

HEC-HMS

Hydrological Engineering Center Hydrological Modelling Systems

HEC-RAS

Hydrological Engineering Center River Analysis Systems

HEC-GeoHMS

Hydrological Engineering Center Geospatial Hydrological Modelling Systems

ESRI

Environmental System Research Institute

GIS

Geographical Information Systems

CN

Curve Number

SCS

Soil Conservation Service

NDVI

Normalized Difference Vegetative Index

TWI

Topographic Wetness Index

SMCDA

Spatial Multi-Criteria Decision Analysis

SDG

Sustainable Development Goal

Declarations
Ethical Approval
The research is in conformity with the ethical soundness of project execution.
Consent to Participate
Authors declare that there is agreement among the research teams to be participative in the project.
Consent to Publish
Express permission is hereby given to Journal of Environmental Modelling and Software by all authors to publish the manuscript.
Author Contributions
Adebayo Adedokun: Conceptualization, Data curation, Formal analysis, Methodology, Writing original draft, Supervision
Monsur Adewara: Conceptualization, Data curation, Formal analysis, Methodology, Writing original draft, Investigation, Model calibration & validation, Writing review and editing
Oluwayemisi Adaradohun: Data curation, Writing review and editing, Investigation
Funding
This research is supported by the Tertiary Education Trust Fund (TetFund).
Conflicts of Interest
The authors declare no conflicts of interest.
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    Adedokun, A., Adewara, M., Adaradohun, O. (2025). Flashflood Hazard Assessment in Yewa South Lga. Journal of Civil, Construction and Environmental Engineering, 10(2), 49-59. https://doi.org/10.11648/j.jccee.20251002.11

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    Adedokun, A.; Adewara, M.; Adaradohun, O. Flashflood Hazard Assessment in Yewa South Lga. J. Civ. Constr. Environ. Eng. 2025, 10(2), 49-59. doi: 10.11648/j.jccee.20251002.11

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    AMA Style

    Adedokun A, Adewara M, Adaradohun O. Flashflood Hazard Assessment in Yewa South Lga. J Civ Constr Environ Eng. 2025;10(2):49-59. doi: 10.11648/j.jccee.20251002.11

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  • @article{10.11648/j.jccee.20251002.11,
      author = {Adebayo Adedokun and Monsur Adewara and Oluwayemisi Adaradohun},
      title = {Flashflood Hazard Assessment in Yewa South Lga
    },
      journal = {Journal of Civil, Construction and Environmental Engineering},
      volume = {10},
      number = {2},
      pages = {49-59},
      doi = {10.11648/j.jccee.20251002.11},
      url = {https://doi.org/10.11648/j.jccee.20251002.11},
      eprint = {https://article.sciencepublishinggroup.com/pdf/10.11648.j.jccee.20251002.11},
      abstract = {In the bid to accomplish the Sustainable Development Goals, several attempts have been made in Yewa South LGA to accomplish environmental sustainability (SDG7) and reduce the adverse effects of climate change (SDG13). The area has witnessed recurrent flash floods with deleterious effect to lives and properties due to anthropogenic factors coupled with incessant torrential rainfall events which are the major drivers of flood vulnerability in the area. Previous studies have adopted the use of GIS, Remote sensing or an integration both techniques with associated challenges. This study adopts the use of Hydrologic Engineering Centre’s Hydrologic Modelling System with Geographic Information Systems (HEC-GeoHMS) to evaluate the relationship between rainfalls, terrain characteristics, run off and stream flow as an alternative flood mitigation scheme. The catchment area was divided into forty-five sub basins over a 10m DEM, the run off hydrographs simulated and the hydrological characteristics modelled by using rainfall data between 1st June, 2022 – 31st May, 2023 as well as discharge data from Ogun-Osun River basin Development Authority (O-ORBDA). the model parameters were optimized for calibration and the calibrated model was thereafter validated using three statistical evaluation criteria which showed that there is a good simulation between the observed and estimated values (Rep = -2.24%, REv = 6.67%, NSE = 95.03%, and R2 = 0.83). Further analysis of the results showed that the flash flood is induced mainly by hydrologic characteristics of the area. This work therefore proposes to mitigate flood in Yewa South Local Government Area of Ogun State by modelling how excess water runs on the terrain thereby creating flash floods. The model will serve as an input for putting mitigation measures in place to arrest flash floods.
    },
     year = {2025}
    }
    

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  • TY  - JOUR
    T1  - Flashflood Hazard Assessment in Yewa South Lga
    
    AU  - Adebayo Adedokun
    AU  - Monsur Adewara
    AU  - Oluwayemisi Adaradohun
    Y1  - 2025/03/07
    PY  - 2025
    N1  - https://doi.org/10.11648/j.jccee.20251002.11
    DO  - 10.11648/j.jccee.20251002.11
    T2  - Journal of Civil, Construction and Environmental Engineering
    JF  - Journal of Civil, Construction and Environmental Engineering
    JO  - Journal of Civil, Construction and Environmental Engineering
    SP  - 49
    EP  - 59
    PB  - Science Publishing Group
    SN  - 2637-3890
    UR  - https://doi.org/10.11648/j.jccee.20251002.11
    AB  - In the bid to accomplish the Sustainable Development Goals, several attempts have been made in Yewa South LGA to accomplish environmental sustainability (SDG7) and reduce the adverse effects of climate change (SDG13). The area has witnessed recurrent flash floods with deleterious effect to lives and properties due to anthropogenic factors coupled with incessant torrential rainfall events which are the major drivers of flood vulnerability in the area. Previous studies have adopted the use of GIS, Remote sensing or an integration both techniques with associated challenges. This study adopts the use of Hydrologic Engineering Centre’s Hydrologic Modelling System with Geographic Information Systems (HEC-GeoHMS) to evaluate the relationship between rainfalls, terrain characteristics, run off and stream flow as an alternative flood mitigation scheme. The catchment area was divided into forty-five sub basins over a 10m DEM, the run off hydrographs simulated and the hydrological characteristics modelled by using rainfall data between 1st June, 2022 – 31st May, 2023 as well as discharge data from Ogun-Osun River basin Development Authority (O-ORBDA). the model parameters were optimized for calibration and the calibrated model was thereafter validated using three statistical evaluation criteria which showed that there is a good simulation between the observed and estimated values (Rep = -2.24%, REv = 6.67%, NSE = 95.03%, and R2 = 0.83). Further analysis of the results showed that the flash flood is induced mainly by hydrologic characteristics of the area. This work therefore proposes to mitigate flood in Yewa South Local Government Area of Ogun State by modelling how excess water runs on the terrain thereby creating flash floods. The model will serve as an input for putting mitigation measures in place to arrest flash floods.
    
    VL  - 10
    IS  - 2
    ER  - 

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  • Abstract
  • Keywords
  • Document Sections

    1. 1. Introduction
    2. 2. Materials and Method
    3. 3. Results
    4. 4. Discussion
    5. 5. Conclusion
    6. 6. Recommendations
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  • Acknowledgments
  • Abbreviations
  • Declarations
  • Author Contributions
  • Funding
  • Conflicts of Interest
  • References
  • Cite This Article
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