Volume 1, Issue 2 pp. 221-239
RESEARCH ARTICLE
Open Access

Around seven decades river course shifting and bank erosion susceptibility of river Mujnai

Sudipa Sarkar

Sudipa Sarkar

Department of Geography, Sidho-Kanho-Birsha University, Purulia, India

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Biswajit Bera

Corresponding Author

Biswajit Bera

Department of Geography, Sidho-Kanho-Birsha University, Purulia, India

Correspondence Biswajit Bera, Department of Geography, Sidho-Kanho-Birsha University, Ranchi Rd, P.O. Purulia, Sainik School, Purulia 723104, India.

Email: [email protected]

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First published: 09 November 2022

Sudipa Sarkar and Biswajit Bera are contributed equally to this study.

Abstract

River bank erosion is a destructive fluvio-hydrological hazard particularly inhabited flood plain of the dynamic Himalayan foreland basin. Every year during monsoonal months, morphology of the landscape is continuously modifying through the dynamic river system. The principal objectives of this study are (i) to identify the river bank erosion susceptibility through BESI (River Bank Susceptibility Index) model which has been modified from Rosgen's (2001) Bank Erosion Hazard Index (BEHI) model and historical reconstruction (from 1955 to 2021) of the river course of Mujnai and (ii) to examine the principal factors of river bank erosion particularly for the river Mujnai within Himalayan Foreland Basin. Sedimentary bank facies analysis has also been done to ascertain the causes of river bank instability. Hence, rate of bank migration, changes of channel width, channel sinuosity index (SI), channel length, erosion and accretion of the river bank, and so forth have been measured through geospatial techniques. Result showed that the younger Quaternary sediments are prone to erosion and BESI result illustrated that around 28% areas are under high erosion zones like Deoagaon, Dhulagaon, Hedayet Nagar, and Dalimpur villages in Alipurduar district. Average maximum width of the channel was recorded in 1980 (147.92 m). Additionally, the lateral migration in case of left bank was around 141.08 m (in the 1980) and 192.62 m in right bank (in 1980) while the shifting rate was 14.10 m/y and 17.51 m/y respectively. Quaternary bank materials, bioturbation and indistinct laminations of river bank are principal regulating factors behind bank erosion in this area. Monsoonal high-velocity flow, bank full discharge and severe flood incidents accelerate the bank erosion vulnerability, particularly in this dynamic flood plain. Soft engineering techniques such as bioengineering, geo-textile fabric, tree, grass and brush revetment should be implemented at high bank erosion vulnerable sites of river Mujnai.

1 INTRODUCTION

River is a principal natural sculpturing element on earth surface (Leopold et al., 1964; Wohl, 2020). Various natural processes and its responses are accountable for river bank erosion, transportation and deposition (Charlton, 2007; Wohl, 2020) but sometimes human activities (Chamling et al., 2022; Gregory, 2006) (through land use and land cover modification) provoke the frequency and magnitude of riverbank erosion mostly at the alluvial floodplain region. Primarily river bank erosion is a combination of geomorphological and hydrological processes (Rosgen, 2001) whereas widespread detachment of non-cohesive materials within the bank occurs through hydraulic action at the stage of liquefaction (Bera et al., 2019; Dharamdial & Khanbilvardi, 1988; Fujita et al., 2000; Hooke, 1979). Basically, the rate of sediment yield and sediment connectivity to the channel with flood plain encourages the mechanism of river bank erosion (Fujita et al., 2000; Rosgen & Silvey, 1996). Processes of river bank erosion are generally regulated by different external and internal factors (Bera et al., 2019; Hughes, 2016) and repeated bank failure also assists channel planform adjustment and partial stability of river bank (Bera et al., 2019; Khan et al., 2022; Wellmeyer et al., 2005). Consequently, some physical factors like the presence of riparian vegetation (Hughes, 2016), plant roots penetration in depth of soil (Abernethy & Rutherfurd, 2000), compactness, lithology and structure of soil, channel width, channel depth, bank angle, climatic condition (rainfall pattern and intensity) (Wolman, 1959), hydraulic regime, and so forth and various anthropogenic factors like pattern of land use (Collins et al., 2001), drainage congestion due to construction of roads, railways across the rivers and stream bank protection have been identified as principal driving forces for riverbank erosion at different riparian environment on the earth surface (Rinaldi & Casagli, 1999). In recent years, the quality of alluvial floodplains is being deteriorated due to extensive agricultural practices and this process promotes a high rate of soil erosion. Channel bed siltation is being amplified because of surface runoff through landscape connectivity and dynamic channel bars accelerate channel avulsion through extensive bank failures (Bera et al., 2019; Ghosh & Bera, 2022). Excessive soil loss of river bank is harmful for the ecological function as well as the water quality of river (Han et al., 2020; Higgit, 1993).

In recent decades, a few developing countries have continuously been suffering due to severe river bank erosion (in different extents and magnitude) along with failing agricultural land within the river channel. The river bank failure is largely dominant in the humid tropical riparian environment (Collins et al., 2001; Terry et al., 2002). The high erosion rate of gully and ravines is leading to huge sediment yield and ultimately it delivers to rivers, particularly in tropical eastern and semi-arid Australia (Fanning, 1999; McCloskey et al., 2016; Olley & Wasson, 2003).

Furthermore, riparian barren or less vegetated bank side is also prone to huge bank failure (Simon & Collison, 2002). The lateral channel migration, nodal and regional channel avulsion, thalweg shifting, changes in river width and confluence dynamics are very common fluvio-hydrological characteristics in riparian flood plain environment (Bera et al., 2019; Ghosh et al., 2022a). Therefore, proper management of riparian tract can minimize the problem of soil erosion and excessive sediment supply to the rivers (Hughes, 2016). River bank erosion leads to lateral migration of channel and formation of meandering channel belt. Noncohesive stream bank material and climatic factors (mainly rainfall and temperature) influence the magnitude of bank failure (Wolman, 1959) while the concave bank is more prone to erosion. Sometimes, consequences of bank erosion accelerate the configuration of meandering loop and alter hydrological regime of the river channel (Bera et al., 2019; Hooke, 1979; Schumm, 1963).

Several scholars have extensively studied about the tropical rivers, especially on the nature, mechanism and consequences of river bank erosion using modern techniques (Bartley et al., 2008; Bera et al., 2019; Ghosh et al., 2022a). A study showed that the total sediment load had been increased (about 55%) due to river bank erosion in a British River (Walling & Collins, 2005). Many pioneering works about riverbank erosion were traced in the scientific inquiry of causes and rates of bank failure (Henshaw et al., 2013), the processes and drivers of riverbank erosion (Hooke, 1979) and the rate of accretion (Chu et al., 2006; De Jong et al., 1999; Mukherjee et al., 2017; Yao et al., 2011), way of migration through bank erosion (Lawler, 1993), impact of intensive rainfall and soil erosion (Ellison, 1945) and river bank susceptibility (Kimiaghalam et al., 2015). Scientific research carried out on diverse magnitude of bank erosion through the stratigraphic sedimentary bank facies and litho logs analysis (Bera et al., 2019).

With the advancement of science and technology, geospatial techniques have been successfully applied in various fields of space and earth science research (Chamling & Bera, 2020a; Sarkar et al., 2021). Waterbody delineation (Lu et al., 2011), river bank lines identification (Lahiri & Sinha, 2012; Sarma & Phukan, 2004), measurements of channel width, channel length, channel sinuosity ratio calculation (Gugliotta & Saito, 2019) and reconstruction of the historical flow path through satellite image analysis etc. can be executed by application of RS and GIS. Although, since the 1960s, many scientific studies conducted on channel morphology (Gordon & Meentemeyer, 2006; Zimmermann & Church, 2001), channel dynamics, erosion and accretion, fluvial restoration applying statistical and machine and deep learning models. Recent studies carried out on historical evolution and morphological transformation of old course of Brahmaputra–Meghna river using satellite imagery with remote sensing techniques (Rashid et al., 2021) and the estimation of suspended sediment concentration of the Lower Yangtze River (Wang & Lu, 2010) based on MODIS data.

River Mujnai is an important left-hand tributary of river Jaldhaka and in recent decades, the fertile floodplain is highly populated. Every year during monsoon, hectares of hectares agricultural land are being engulfed within the channel bed of river Mujnai. Few stretches of river Mujnai are very vulnerable and risk prone due to repeated bank failure incidents. There is no as such scientific study which has been conducted previously on susceptibility of bank erosion of river Mujnai. In this context, it is a big research gap that has been identified. Noncohesive bank materials, flood plain extensive agriculture and high sediment yield and formation of dynamic channel bars have been considered as probable hypotheses for the reason behind severe bank erosion in this study area. The significance of the study is to find out the magnitude of bank erosion susceptibility zones based on applied model. Local administrators can take appropriate mitigation measures from this research finding. The principal objectives of this research are (i) to identify the riverbank erosion potential zones with the help of Bank Erosion Susceptibility Index (BESI), and (ii) to examine the principal factors of riverbank erosion particularly for the river Mujnai within Himalayan Foreland Basin.

2 MATERIALS AND METHODS

2.1 Study site and its geomorphological setting

River Mujnai (62.45 km) is a tributary of river Jaldhaka which originates from Hantapara uplands (Southern part of Bhutan hill) near Madarihat in the district of Alipurduar (West Bengal) (Figure 1). It is flowing on the vast tract of Alipurduar and Coochbehar districts of West Bengal. The entire unit of Mujnai basin lies on Quaternary (Holocene) alluvial sedimentary foothill zone of Himalaya. This region of North Bengal is recognized as Dooars (Doors of Bhutan) (Rudra, 2018). When this sub-Himalayan river crosses the Himalayan Frontal Thrust (HFT); it debouches on the Terai piedmont zone. Sudden drop of channel gradient creates large-scale sediment accumulation on the channel bed and forms multiple types of dynamic channel bars (Ghosh & Bera, 2022). Rivers like Rehti, Titi, Pagli are being drained to the Mujnai in Alipurduar district of west Bengal. The average annual rainfall of the Alipurduar and Coochbehar district is 3160 mm and 3049 mm respectively (IMD). Foothill zone is also tectonically very active and dynamic (Ghosh & Bera, 2022).

Details are in the caption following the image
Location map of the study area.

This floodplain is characterized by more or less flat surface and it is dissected by numerous tributaries and distributaries while formation of spill channel is due to drainage congestion (Ghosh & Bera, 2022). This foothill zone makes interlacing drainage system and channel avulsion is occurred due to different fluvio-hydrological factors (Ghosh et al., 2022a). For the current research, the study reach has been divided into three segments (based on channel geometry and geomorphic uniformity) such as Segment–I, Segment–II, and Segment–III. Random sampling (N-26) techniques along both bank sides (Left and right) of river Mujnai have been chosen to improve the accuracy of the result. Most of the previous studies had been considered minimum 20 random samples to assess the river bank vulnerability study and sampling number depends on nature of the river bank and severity of bank erosion.

2.2 Design of new Bank Erosion Susceptibility Index (BESI) model

BESI is the modified form Bank Erosion Hazard Index (BEHI) method. The original BEHI method was propounded by Rosgen (2001). Rosgen's BEHI method is completely based on primary data. Rosgen (2001) considered five principal parameters to identify the stream bank vulnerability zones. These parameters are bank height/bank full height, root depth/bank height, root density, surface protection (including vegetation) and bank angle. Here, some modification should be required for the better performance of the model in addition with some important parameters (erosivity factors) which are responsible for river bank erosion. Similarly, modification is necessary to identify the river bank erosion potential hotspots with improvement of accuracy level of the bank erosion susceptibility model. Previously, we selected these above-mentioned sample sites and finally prepared a bank erosion vulnerability index map. But after monsoon, we visited these sites for practical verification and we got reverse results, that is, moderate bank erosion susceptibility sites were severely affected due to large-scale bank failure and somewhere high bank erosion susceptibility sites (according to Rosgen) were not affected or collapsed. We thoroughly investigated the reasons behind the inverse results and all sample sites have been thoroughly examined. After seasonal investigation, three important factors such as bank material or bank stratification, subsurface hydrological condition and riparian vegetation have been considered for BESI mapping. Here, bank material or bank stratification means composition of river bank. It is composed of sand, silt, clay, boulder, gravel, pebble and cobble, and so forth with various sedimentary structures (cross-bedding, trough and lamination). Sand-bearing bank layer is more prone to erosion compared with clay due to low cohesiveness or stickiness of sand whereas gravel, pebble and cobble have comparatively moderate to high resistant power. Subsurface hydrological condition is classified into five important groups such as dry, damp, wet, dripping and flowing. Dripping and flowing subsurface hydrological conditions accelerate bank erosion rate due to continuous infiltration and percolation processes through the porous medium. Riparian vegetation plays significant role to protect river bank erosion and failure. Deep-rooted trees and few grass species can tightly hold the bank materials. Hence, therefore, BEHI method has been slightly modified. Weightage value of different sub-categories (bank material, subsurface hydrological condition and riparian vegetation) has been properly assigned as per their relative significance. Finally, new map was prepared using Bank erosion Susceptibility Index (BESI) method and it shows high accuracy and precision level for spatiotemporal landuse planning.

In case of BESI method, authors have added three more important susceptibility factors such as bank material, subsurface hydrological condition and riparian vegetation for better performance of the model. Here, bank height (BH) is the vertical depth from top of the bank to the channel bed while the bank full height (BFH) is generally measured by visual estimation of inundation of the river bank during over bank flow or flood. Root depth (RD) means the length of plant roots into the soil while root density (RD₁) denotes the percentage of root in a given unit area of the bank surface. Similarly, surface protection (SP) signifies various natural (including natural vegetation) and anthropogenic impoundment on the bank whereas bank angle (BA) is the angle of inclination of bank with respect to surface. It is measured by Clinometer. Bank material (BM) is the composition of river bank (consolidated, semi-consolidated, non-cohesive materials and hard rock) which is shaped through the geological evolution over time. Sub-surface hydrological condition (SSHC) of river bank means the various hydrological characteristics like flowing, dripping, dry, damp and wet while riparian vegetation (RV) is the existing plants and grasses over the river or stream bank. The ratio of bank height and bank full height (BH/BFH) and ratio between root depth and bank height (RD/BH) have been considered for this new model like BESI. Data regarding river bank susceptibility were obtained through field observation and 26 random samples have been collected along the river from both sides uniformly (Supplementary File S1). Table 1 indicated the individual assigned BESI scores and total weightage value. The total susceptibility values have been categorized into six classes such as very low (8.0–15.20), low (16.0–31.12), moderate (32.0–47.20), high (48.0–63.20), very high (64.0–72.0), and extreme (73.0–80.0).

Table 1. Metrics of river bank susceptibility for BESI model (Modified after Rosgen, 2001)
BESI category Bank height/bankfull height RootDepth (% of BFH) Root Density/BH (%) Surface Protection (%) Bank Angle (degrees) Bank material Sub surface Hydrological condition Riparian vegetation type BESI Score
Very low 1.0–1.1 90–100 80–100 80–100 0–20 1.0–1.1 1.0–2.0 2.0–3.0 8.0–15.20
Index 1.0–1.9 1.0–1.9 1.0–1.9 1.0–1.9 1.0–1.9 1.0–1.9 1.0–1.9 1.0–1.9
Low 1.11–1.19 50–89 55–79 55–79 21–60 1.1–2.0 2.1–4.0 3.1–5.0
Index 2.0–3.9 2.0–3.9 2.0–3.9 2.0–3.9 2.0–3.9 2.1–3.9 2.0–3.9 2.0–3.9 16.0–31.12
Moderate 1.2–1.5 30–49 30–54 30–54 61–80 2.1–3.0 4.1–6.0 5.1–6.0
Index 4.0–5.9 4.0–5.9 4.0–5.9 4.0–5.9 4.0–5.9 4.0–5.9 4.0–5.9 4.0–5.9 32.0–47.20
High 1.6–2.0 15–29 15–29 15–29 81–90 3.1–5.9 6.1–7.0 6.1–7.0
Index 6.0–7.9 6.0–7.9 6.0–7.9 6.0–7.9 6.0–7.9 6.0–7.9 6.0–7.9 6.0–7.9 48.0–63.20
Very high 2.1–2.8 5–14 5–14 10–14 91–119 6.0–8.9 7.1–8.0 7.1–8.0
Index 8.0–9.0 8.0–9.0 8.0–9.0 8.0–9.0 8.0–9.0 8.0–9.0 8.0–9.0 8.0–9.0 64.0–72.0
Extreme >2.8 <5 <5 <10 >119 <10 <10 <10
Index 10 10 10 10 10 10 10 10 73.0–80.0
  • Abbreviations: BESI, Bank Erosion Susceptibility Index; BFH, bank full height; BH, bank height.

2.3 Sedimentary bank facies (SBF) analysis

River bank materials, their composition, sedimentological structures and fluvial hydraulics play significant role to erode river bank particularly noncohesive bank (Bera et al., 2019; Lawler et al., 1999). So, it can be studied for the susceptibility and magnitude of river bank erosion through spatiotemporal scale. Here, sedimentary bank facies study has been done in the post-monsoon (December) season of 2021. Three specific bank facies sites have been chosen due to presence of distinct layers sedimentary structures and Site–I is located at Jaldhaka–Mujnai confluence point of Mukuldanga (Coochbehar District). Site–II is located at Pashim Falakata (near Mujnai Railway Bridge) while Site–III is located at Harinathpur Village of Falakata on the left bank of the Mujnai river.

The bank facies study has been conducted in two phases (i) during field and (ii) post field. During the field phase, the facies trench (the prominent layers of lithological units and structures of both the river bank of Mujnai) was identified and measured systematically. Soil samples have also been collected from different prominent layers of bank facies sites to know about the nature of erodibility of the bank. Soil samples have been tested in the laboratory of National Bureau of Soil Science and Land use Planning (NBSSLUP). During post field phase, diagrams of litho facies or river bank facies (Composition, structure and bioturbation) have been prepared on LogPlot version 7.4 software platforms.

2.4 Temporal bank line extraction

In this present study, Topographical sheet of United States Army Map (1955) has been used. Here, firstly the map has been geo-referenced through geo-coding system and projected on GIS environment. MSS (1980), TM (1990), TM (2000), ETM+ (2010), and OLI (2021) multispectral satellite images have been used for delineation of different temporal bank lines of the river. Images have been collected from the USGS earth Explorer (https://earthexplorer.usgs.gov/) site. All the satellite data (Table 2) layers have been stacked and geo-rectified in the Erdas Imagine 2014 platform and projected to the UTM (Universal Tranverse Marcator) projection system on WGS-1984 datum using Arc GIS 10.3.1.

Table 2. Details of datasets (satellite Images) used for the study
Sl. No. Date of acquisition Satellite/Sensor Path/Row Spatial resolution (in m)
1. 03/04/1980 LANDSAT 1-5 MSS 148/42, 149/42 60
2. 06/05/1990 LANDSAT-4/5 TM 148/42, 149/42 30
3. 04/02/2000 LANDSAT-4/5 TM 148/42, 149/42 30
4. 07/03/2010 LANDSAT-7ETM+ 148/42, 149/42 30
5. 04/03/2021 LANDSAT 8OLI/TIRS 148/42, 149/42 30

2.4.1 NDWI and MNDWI

For the bank line extraction of river Mujnai, satellite images have been processed through different band combinations. Water line extraction has been done through spectral indices like Normalized Difference Water Index (NDWI) and Modified Normalized Difference Water Index (MNDWI) and the extracted raster data has been converted into vector data.

MNDWI formula was formerly propounded by Xu (2006). Later on, many researchers have worldwide applied and also slightly modified the formula for better result (Gazi et al., 2020; Jiang et al., 2014).

Basically, NDWI is a method to delineate the water body from the different bands of satellite imageries and it differentiates the land border from water bodies through the reflectance and absorption of spectral signatures. It is following as
urn:x-wiley:27504867:media:rvr219:rvr219-math-0001()
urn:x-wiley:27504867:media:rvr219:rvr219-math-0002()
where, ρ denotes the reflectance value from the band of Landsat images. However, in case of Landsat TM/ETM+ data, the band combination is Blue (Band-1), Green (Band-2), Red (Band-3) whereas NIR (near Infra Red) is Band-4.SWIR1 and SWIR 2 are bands 5 and 7, respectively.

2.5 Measurement of lateral migration of bank lines, width, channel length, and sinuosity index

Lateral migration or oscillation of river bank is a fluvio-hydrological process. Demarcation of bank lines, lateral migration of channel and changing channel pattern have been computed from different data (topographical maps and satellite images) applying geospatial techniques. Remote sensing and GIS techniques are very helpful for the study of fluvio-hydrological condition of river (Gogoi & Goswami, 2013; Thakur et al., 2011). The process of manual digitization has been performed on the GIS platform for all the consecutive years (Rhoads & Kenworthy, 1995). The entire studied stretch of river Mujnai has been divided into three segments (Figure 2) where 16 cross-sections (CS) have been drawn for the measurement of lateral shifting of bank line in different years. The technique of bank line extraction has been adopted from the given formula (Giardino & Lee, 2011).
urn:x-wiley:27504867:media:rvr219:rvr219-math-0003()
Where, Dm represents distance of channel migration in m and T1 and T2 denote the years of created polygon for river.
Details are in the caption following the image
Three segments of river Mujnai (Studied reach) (a) Segment–I, (b) Segment–II, and (c) Segment–III.

First, layers of multiple polygons of river Mujnai have been created to measure the channel width while polygons of changes of river width have been calculated distinctly for each cross-section of three segments through the measuring tool in Arc 10.3.1 GIS software.

Channel length and channel sinuosity refer the geometric attribute of a river. Channel length within its actual geometry has been measured through different datasets. Sinuosity index is the ratio between actual channel length and valley length of river and it was measured following Schumm's equation (Schumm, 1963).
urn:x-wiley:27504867:media:rvr219:rvr219-math-0004()

The lateral migration or movement of bank line of River Mujnai has been measured orthogonally with proper geometry. Quantification of bank line shifting has been assessed at 16 cross sections of three segments of river Mujnai. Total erosion and accretion areas have been calculated through geometry calculator in Arc GIS platform to comprehend the nature of erosion and accretion (Baki & Gan, 2012).

3 RESULT

3.1 Result of BESI model

26 sampling sites have been selected for the running of BESI model. Bank erosion potentiality zonation map at village level has been prepared (Figure 3) based on calculated BESI value of each site (Table 3). Total 17 villages of Alipuduar district have been assessed through the collected samples. The results denoted that out of total studied villages, 28.74% areas fall under the High, 25.55% areas come under Moderate and 22.90% and 8.03% come under very High and Extreme erosion prone zones as per BESI computation. Paschim Deogaoan, Uttar Deoagon, and Dalimpur villages are highly vulnerable to bank erosion. Falakata and Barodoba villages are comparatively less vulnerable rather Dhulagaon, Hedayetnagar and Purba Jhar Beltali falls under very high vulnerable zone.

Details are in the caption following the image
BESI zonation of Mujnai river bank.
Table 3. BESI calculation for each sampling location
Sampling sites RBH = BH/BFH BESI Score RD/BH BESI Score Root Density (RD₁) BESI Score Surface protection (SP) BESI Score Bank angle(BA) BESI Score Bank material (Type) BESI Score Sub surface hydrological condition(Type) BESI Score Riparian vegetation (Type) BESI Score Total BESI Score
1 1.00 1.45 65.00 2.95 80.00 1.00 55.00 2.95 20.00 1.45 1.00 1.32 2.00 2.95 2.00 1.00 15.07
2 1.25 2.95 43.00 4.40 50.00 4.00 58.00 2.10 35.00 2.95 6.0 6.95 2.0 2.95 4.0 4.95 31.25
3 1.15 2.95 12.00 8.50 78.00 2.95 83.00 1.45 23.00 2.95 18.0 10.00 12.0 10.00 9.0 8.50 47.30
4 1.10 1.90 75.00 2.20 80.00 1.45 55.00 2.95 80.00 5.90 3.00 5.90 4.00 3.90 3.10 2.00 26.20
5 1.19 3.90 90.00 1.00 55.00 2.00 55.00 2.95 20.00 1.45 1.00 1.32 2.00 2.95 2.00 1.00 16.57
6 1.35 4.95 50.00 2.00 50.00 4.00 58.00 2.10 35.00 2.95 6.0 6.95 2.0 2.95 4.0 4.95 30.85
7 1.10 1.90 55.00 2.10 82.00 1.01 55.00 2.95 20.00 1.45 1.00 1.32 2.00 2.95 2.00 1.00 14.68
8 1.11 2.00 78.00 2.20 77.00 3.90 55.00 2.95 80.00 5.90 3.00 5.90 4.00 3.90 3.10 2.00 28.75
9 1.65 6.01 79.00 3.90 79.00 3.90 32.00 4.95 45.00 2.95 5.0 4.95 6.0 6.95 2.00 2.95 36.56
10 1.40 4.95 67.00 2.95 70.00 2.95 73.00 2.95 46.00 2.95 5.0 4.95 6.0 6.95 6.0 6.95 35.60
11 1.18 2.95 70.00 2.95 65.00 2.95 86.00 1.45 17.00 1.45 9.0 8.50 5.0 4.95 6.00 6.95 32.15
12 1.30 4.95 20.00 6.95 25.00 6.95 90.00 1.45 27.00 2.95 9.0 8.50 2.0 2.95 1.00 4.95 39.65
13 1.40 4.95 18.00 6.95 23.00 6.95 62.00 2.95 26.00 2.95 10.0 10.00 5.00 4.95 8.00 8.50 48.20
14 1.90 7.00 10.00 8.50 35.00 4.50 10.00 8.00 85.00 6.10 8.50 8.70 9.00 10.00 7.20 8.00 60.80
15 1.10 4.95 80.00 1.45 54.00 4.95 18.00 6.90 41.00 2.95 18.0 10.00 12.0 10.00 5.0 6.95 48.15
16 1.12 2.95 35.00 4.95 52.00 4.95 15.00 8.50 95.00 8.50 7.0 6.95 6.0 6.95 9.0 10.00 53.75
17 1.33 4.95 30.00 4.95 40.00 4.95 26.00 6.95 90.00 6.95 3.0 2.95 6.0 6.95 4.0 4.95 43.60
18 2.50 8.60 20.00 6.78 5.00 10.00 30.00 4.00 92.00 8.20 3.20 6.00 6.30 6.00 6.10 6.00 55.58
19 1.00 1.45 12.00 8.50 80.00 1.45 91.00 1.45 15.00 1.45 4.0 4.95 6.0 6.95 12.0 10.00 36.20
20 2.80 9.00 14.00 8.60 15.00 8.50 14.00 9.00 38.00 6.00 6.0 8.00 2.0 8.00 8.0 8.50 65.60
21 2.90 10.00 11.00 9.00 28.00 8.90 10.00 8.50 95.00 8.70 5.0 9.20 5.0 10.00 3.0 9.20 73.50
22 2.50 8.50 5.00 10.00 14.00 9.00 54.00 8.50 80.00 8.50 9.0 10.00 9.0 10.00 3.0 10.00 74.50
23 2.10 8.50 15.00 6.95 7.00 8.00 25.00 6.95 85.00 6.95 9.00 10.00 8.0 8.50 9.00 10.00 65.85
24 2.50 8.50 80.00 1.45 35.00 4.95 51.00 4.95 55.00 3.90 14.0 10.00 6.0 6.95 8.00 9.00 49.70
25 1.17 2.95 10.00 8.50 50.00 4.95 13.00 10.00 100.00 8.50 2.0 2.95 3.0 2.95 2.0 2.95 43.75
26 1.30 4.95 20.00 6.95 25.00 6.95 90.00 1.45 27.00 2.95 9.0 8.50 2.0 2.95 1.00 4.95 39.65
  • Abbreviations: BESI, Bank Erosion Susceptibility Index; BFH, bank full height; BH, bank height; RD, root depth.

Out of 26 sample sites, three sites are located at Paschim and Uttar Deogaon on the right bank of river Mujnai. Here, bank height is more than 2.2 m and bank angle is very high (more than 80°) due to periodic toe erosion of the bank. Consequently, deep rooted grass, shrubs like vegetation and bank protection (like bamboo fence, wooden log. etc.) have been noticed at the Site no. 4, 5, and 6 (left bank). River bank materials are mainly dominated with wet sand and silt most of the sites of river Mujnai.

3.2 Analysis of sedimentary bank facies (SBF)

Spatial variability of the river bank erosion depends on geological setting of the study area. Mujnai river basin is the subbasin of river Jaldhaka. This Himalayan foreland basin is basically composed of Quaternary alluvium deposits and it is tectonically very active and fast changing landscape. When Himalayan Rivers cross the Himalayan Frontal Thrust (HFT), they debouch on the piedmont zone as well as quaternary alluvial flood plain. Different sized sediments with gravel, pebble and cobbles are being deposited on vast floodplain due to sudden drop of channel gradient. Altitude of this plain varies from 50 to 75 m. Here, the SBF site–1 (right bank of river Mujnai), the L1 (0.65 m) is dominated by sand and silt with presence of mica (muscovite) while sub-surface hydrological condition shows semi wet as well as damp (Figure 4a). Similarly, the second layer (L2–1.05 m) of this facies is dominated by clay and silt whereas this layer is very much compacted in nature and it is connected with flowing water. During bankfull discharge, the upper layer is very susceptible to erosion particularly during monsoonal months. The upper layer is partially bioturbated by micro soil animals. This animal activities help to erode particularly during flood.

Details are in the caption following the image
Sedimentary bank facies (a) Site–I (b) Site–II, and (c) Site–III.

Around 2.55 m height of left bank of river Mujnai (Site 2) has been exposed through continuous bank failure. It is situated near Paschim Falakata village of Alipurduar district. We have observed three distinct layers at the facies site (Figure 4b). Hence, the upper most layer (L1) is contained of sand and silt and it is indistinctly laminated. This layer is dominated by plant roots and grasses. This layer is (1.1 m) characterized with wet subsurface hydrological condition. Similarly, 0.45 m thick layer 2 (L2) is dominated by silt and clay whereas, the thin mud bands and signatures of oxidation have been found within this horizon and subsurface hydrology shows wet condition. Accordingly, the lower layer or L3 (1.0 m thickness) is also composed of semi consolidated sand and silt (more than 85%) and small proportion of clay (15%) (Table 4). Muscovite and biotite minerals have also found in the lower layer which is connected with post monsoonal water level of river. Erosion capacity of this layer is very high due to lack of compactness or semi-consolidated nature of these materials.

Table 4. Soil textural classification (according to USDA)
Layers Sand Silt Clay USDA soil type
Site–I Layer 1 (Sample 1) 82.50 15.00 2.50 Sand
Layer 2 (Sample 2) 16.75 49.00 34.25 Clay loam
Site–2 Layer 1 (Sample 1) 32.00 59.00 9.00 Silt loam
Layer 2 (Sample 2) 11.00 55.00 34.00 Loamy sand
Layer 3 (Sample 3) 61.00 25.00 14.00 Silt loam
Site–3 Layer 1 (Sample 1) 10.40 63.75 25.85 Loamy sand
Layer 2 (Sample 2) 85.40 10.60 4.00 Clay loam
Layer 3 (Sample 3) 5.25 72.45 22.30 Silt loam
Layer 4 (Sample 4) 80.00 12.00 8.00 Silty clay loam
Layer 5 (Sample 5) 21.00 42.00 37.00 Sandy loam

Five prominent horizons have been identified at SBF Site 3 (Figure 4c). Total height of the facies was approximately 2.14 m, where top layer or L1 (0.45 m) is basically composed of sand and silt along with sparse vegetation (Partheniam hysterophorous) and grasses. It is bioturbated along with development of minor cracks. Sub-surface hydrological imprint shows damp condition. Surface crown of cracks has also been developed far away from the bank. L2 (0.26 m) is characterized by dry laminated semi compacted sands. Similarly, L3 (0.23 m) is contained by silt and clay while this layer is also slightly oxidized and it is absolutely bioturbated with damp hydrological condition. L4 (0.16 m) is composed of loose sands which signify indistinct lamination along with dry and damp hydrological conditions. Consequently, the lowermost layer or L5 (1.04 m) is also contained by clay (37%) with silt (42%) and sand (21%) (Figure 5) which shows indistinct lamination. This layer is also characterized by wet hydrological condition due to directly connected with flowing water.

Details are in the caption following the image
Textural classification of soil collected from different layers of facies I, II and III.

3.3 Channel length and Sinuosity Index (SI)

Channel length of three segments of river Mujnai has been assessed through geospatial technique. The average length of Segment–I is 9.81 km whereas the total length of segment–II and III has been measured around 21.20 km and 13.79 km respectively. After 1990, the channel length of Segment–I (7.20 km) was decreased as a result the SI (1.15) of river channel Mujnai was also decreased. Similarly, after 2010, channel length of segment–II was 21.87 km and SI was 1.72, while Segment–II is being reduced its length after 2010 whereas, the SI was 2.00. It has shown in Table 5 that the channel sinuosity has been increased in 2021 in three segments of river Mujnai. The channel length and sinuosity was 9.71 km and 1.77 in Segment–I, whereas, 19.44 km was the channel length of Segment–II with SI of 2.14 while Segment–III has been measured its flowing path as 14.25 km with SI of 2.59. Channel length is directly proportional with SI.

Table 5. Various significant parameter of river channel
Attributes Year
1963 1980 1990 2000 2010 2021
Segment–I Actual length (km) 10.69 11.25 7.2 8.25 9.65 9.79
Straight length/axial length (km) 6.3 7.02 6.25 5.62 6.1 5.54
Stretch area (Sq. km) 1.1 1.79 1.01 0.9 1.3 1
Channel width(Avg in m) 72.63 132.58 85.58 75.82 75 74.09
Channel sinuosity 1.7 1.6 1.15 1.47 1.58 1.77
1963 1980 1990 2000 2010 2021
Segment–II Actual length (km) 22.3 19.58 21.87 22.25 21.78 19.44
Straight length/axial length (km) 12.3 11.2 12.69 10.36 12.32 9.07
Stretch area (Sq. km) 1.47 1.18 1.5 1.39 1.28 1.04
Channel width(Avg in m) 70.29 129.29 79.35 82.52 77.47 72.02
Channel sinuosity 1.81 1.75 1.72 2.15 1.77 2.14
1963 1980 1990 2000 2010 2021
Segment–III Actual length (km) 13.68 15.21 11.32 14.58 12.68 14.25
Straight length/axial length (km) 5.18 5.11 6.24 5.68 6.35 5.5
Stretch area (Sq. km) 1.4 2.25 1.01 1.18 1.3 1.35
Channel width(Avg in m) 86.16 133.14 78.79 78.2 73.5 75.74
Channel sinuosity 2.64 2.98 1.81 2.57 2 2.59

3.4 Changes of river width

Width of Mujnai River has been significantly changed over the study period. Over the 66 years (1955–2021) of time span, the average width of the channel was 90.06 m whereas the average width of Segment I, II and III was 90.74, 90.61, and 90.13 m, respectively. The maximum width (avg: 129.69 m) of Mujnai was measured in the year 1980. Figure 6 shows that the width of the river has been gradually decreased from the year 1980 to 1990 and further it was increased after 1990. After 2000, river Mujnai was flowing within the narrow channel path while further it has been increased in the year 2021(average width 92.99 m). In the year 1980, CS-4 section showed the maximum width which was 170.63 m (within Segment–I) whereas, in Segment–II, and III, maximum width showed across the section CS-6 and CS-13, respectively. Maximum width in Segment–I, II, and III was noticed across the section CS-4 (99.58 m), CS-11 (97.50 m), and CS-15 (110.30 m) in the year 1990. The maximum width was measured in the section CS-4 (103.72 m), CS-10 (110.63 m), and CS-12 (96.52 m) in the year 2000 in three segments (I, II, and III) of river Mujnai. Although in the year 2010, the average channel width of Mujnai (78.38 m) was decreased but the maximum width was noticed across the section CS-4 (107.26), CS-11 (104.61 m), and CS-15 (102.47 m) in Segment I, II, and III. However, in the recent year (2021), river Mujnai is flowing within comparatively wide channel path rather than previous decades. So, maximum channel width of three segments has been noticed across the sections CS-4 (107.26 m), CS-10 (113.20 m), and CS-15 (102.47 m) accordingly (Online Supporting Information File S2).

Details are in the caption following the image
Cross-section wise changes of channel width (1955–2021) (a) Segment–I (b) Segment–II, and (c) Segment–III.

3.5 Accretion - erosion dynamics and lateral migration of bank line

River Mujnai oscillates its flow path and shifted bank lines over the entire study period. Figure 7 showing cross section wise lateral movement of channel in three segments (I, II, & III). The maximum length of shifting (320.48 m in Segment–I) has been noticed in section CS-1(right bank) in between the years 1955 and 1980. Right and left bank of Mujnai were shifted across the section CS–3 during 1980 and 1990 while, in between 1990 and 2000, it has shown that maximum lateral movement across section CS–5 in left bank (239.43 m) and minimum movement (64.93 m) in the right bank (CS–2) were calculated. Highest average shifting rate (40.30 m/y) noticed during the period 1980 to 1990 in the left bank of river Mujnai (Segment–I). Accordingly, in between 2000 and 2010, the left and right bank were avulsed slightly and the average rate of channel movement was 3.90 m/y (left bank) and 6.94 m/y (right bank). Hence, in between the years 2010 and 2021, the channel shifted rapidly rather than previous year which was measured as 10.59 m/y for the left and 8.22 m/y for the right. However, in segment–II, both the right and left bank were migrated quickly (avg. migration rate was 14.30 m/y and 17.02 m/y) during the period 1955 to 1980. Figure 7 showed that during 1980–1990, the highest oscillation of right bank (746.49 m) and left bank (634.62) have been recorded across the section CS-11 while the maximum shifting of left and right bank (during 1990–2000) has been measured across the section CS-10. Consequently, the minimum rate of shifting (10.20 m) across section CS-11 in the left bank was noticed. Furthermore, in between 2000 and 2010, the left bank of the channel was migrated with the rate of 12.21 m/y but the right bank was moved comparatively slower rate (5.40 m/y). The bank line of river Mujnai was shifted speedily during the period of 2010–2021 whereas the average shifting rate of right and left bank was 2.27 m/y and 28.92 m/y, respectively (Online Supporting Information File S3).

Details are in the caption following the image
Bank line shifting of river Mujnai in different years, i.e., (a) 1963–1980 for stretch-I (b) 1980 to 1990 for stretch-I (c) 1990–2000 for stretch-I (d) 2000–2010 for stretch-I (e) 2010–2021 for stretch-I (f) 1963–1980 for stretch-II (g) 1980–1990 for stretch-II (h) 1990–2000 for stretch-II (i) 2000–2010 for stretch-II (j) 2010–2021 for stretch-II (k) 1963–1980 for stretch-III (l) 1980–1990 for stretch-III (m) 1990–2000 for stretch-III (n) 2000–2010 for stretch-III (o) 2010–2021 for stretch-III.

On the other hand, both the bank line gradually and concurrently shifted within the segment–I during the period 1955–1980. Thus, the significant shifting of right bank was noticed across section CS-13 (159.82 m) and the shifting distance of left bank was 146.37 m (CS-13). Similarly, the maximum rate of migration in the left bank (131.91 m/y) and right bank (117.45 m/y) has been measured in the segment–III during 1980–1990. Maximum shifting of left bank (39.20 m) and right bank (68.39 m) across section CS-12 has been recorded for the one decade (2000–2010) but section CS-13 showed the maximum left and right bank movement during 2010–2021. However, in this period, the rate of migration of left and right bank of segment–III was 41.13 m (Cs-12) and 47.89 m (Cs-13).

4 DISCUSSION

Bank erosion of river Mujnai is the key concern of the present study. However, both the primary (field data) and secondary (satellite imagery and topographical sheet) datasets have been used for the study and bank erosion status has been assessed through the geospatial and quantitative techniques. Significant higher flow velocity of channel influences the rate of channel avulsion (Moran et al., 2017) and toe erosion of concave bank (Yu et al., 2015). Whereas, the mechanism of widening and narrowing processes is related to composition of bank material and however, channel width is associated with these processes (Manners et al., 2014). Temporal variations of channel migration have been computed and it has shown the significant changes within the studied period.

A meandering channel Mujnai (average sinuosity ratio is 1.98) is located in the eastern part of Himalayan foreland basin. The result shows that around 50% area was moderate to high erosion prone where the bank height (BH) is relatively higher (mean height more than 1.5 m). Similarly, the high susceptible zones have high bank angle (BA) which influences the bank failure incident particularly in this study area. The riparian vegetation plays a vital role as natural surface protection element (Bera et al., 2019; Murgatroyd & Ternan, 1983) whereas the low susceptible areas show moderate to high riparian vegetation cover. High bank height with concave bank is always vulnerable to bank erosion or bank failure (Figure 8). There is no exception in this Quaternary alluvial flood plain of river Mujnai basin. Here, due to the formation of point bar at convex river bank side, the thalweg line has been shifted towards the concave bank side and the concave bank is being repeatedly eroded (Bera et al., 2019). The riparian area is mainly covered by different plants and grasses. Most of the cases, the varieties of agricultural crops and monsoonal paddy are being practiced on the entire flood plain and river bank due to fertile soils. Irrigation water infiltrates into the ground and this process helps to accelerate the soil erosion as well as river bank failure. The noncohesive riverbank materials play significant role for repeated bank failure at different pockets of river Mujnai (Figure 8). River bank erosion and failure is higher during monsoonal months due to high velocity flow and bank full discharge while post and pre monsoonal months also increase bank erosion vulnerability due to prolong dry spell. Post monsoon period also erodes riverbank at different sides of river Mujnai where sand layer (lower most layer) is attached with surface flow line. Toe erosion is so prominent near the sand layer as a result slumping and rotational fall are more common at higher bank height particularly in Deoagaon, Dhulagaon, Hedayet Nagar and Dalimpur villages. It has been observed that the cavitations and eddies are frequently formed at the concave river bank side due to sudden obstacles of flow and high velocity. These processes also assist the mechanism of bank erosion particularly on dynamic flood plain of river Mujnai basin. The surface and sub-surface hydrological conditions greatly influence the mechanism and high rate of bank erosion. Similarly, flowing and dripping conditions directly provoke the rate of river bank erosion particularly during monsoonal months (June–September) while dry, damp and wet sub-surface hydrological conditions also regulate moderate bank erosion rate during pre and post monsoonal periods predominantly in this flood plain (Bera et al., 2019; Ghosh & Bera, 2022; Ghosh et al., 2022b). First, we applied BEHI model and prepared final bank erosion vulnerability map. After repeated field verification, we got minor error in this final output. So we slightly modified this model considering three important bank erosion vulnerability factors like bank materials, subsurface hydrological conditions and riparian vegetation. Finally we designed new model (BESI) and identified more prominent bank erosion vulnerability zones. Therefore, if the BESI value is higher, the area is more potential for bank erosion. On the other hand, the hydro-geomorphological setting of the area indicates the nature of bank erosion. In this context, hydraulic interaction of upstream leads to changes (Newson & Large, 2006) in the downstream fluvio-hydrological regime of river Mujnai.

Details are in the caption following the image
(a) Repeated slumping occurs at left bank of river Mujnai at Paschim Falakata village due to erosion and accretion and thalweg point shifting towards the concave bank side. (b) Severe bank failure occurs at left banks side of river Mujnai at Paschim Falakata village due to unconsolidated bank materials during post monsoon season and middle sand layer is responsible for bank failure. River bank and flood accelerate the mechanism of this location. (c) Distinct horizons exposed at left bank side of river Mujnai during post monsoonal season at near Harinathpur village. Micro animal burrows along with indistinct laminations have been also exposed in the bank facies. (d) Steep, concave scarps also been developed due to repeated slumping and subsidence season at near Harinathpur village.

Sedimentary bank facies describes and denotes the river bank stratification as well as depositional history of fluvial aggradations (Bera et al., 2019; Miall, 1985). The entire study area is characterized by quaternary alluvium that represents the amalgamation of fine sand, silts and clay of fluvial deposits (Ghosh et al., 2022a; Singh & Awasthi, 2011). Three natural bank facies have been studied where two sites, the lower most layers are non-cohesive sand with indistinct laminations and rest site, the middle layer is sand with micro animal burrows. These studied bank facies sites are located at concave bank side where channel thalweg point is situated. Channel point bar is situated just at opposite site as a result river flow strikes directly at concave bank side and erosion takes place due to exposed non-cohesive sand layer through the multiple fluvio-hydrological processes such as hydraulic action, corrosion and cavitations. Flowing water enters into the sand layer along with animal burrows and at the point of liquefaction stage, flow with sediments start quickly. This Quaternary non-cohesive layer with flowing, dripping, wet and dry cycle of subsurface hydrological conditions extremely stimulate the bank erosion or bank failure rate as well as mechanism at different pockets of river bank Mujnai. Helical flow and development of eddies are responsible for toe erosion at vulnerable erosion sites. In this milieu, role of bank materials is also very much important for bank erosion (Bera et al., 2019). The modified BESI model also considered these significant factors.

Channel sinuosity strongly influences the sediment yield, delivery ratio, accumulation rate and channel gradient. When natural cut-offs occur on dynamic flood plain, the sinuous and meandering channel become straight channel. The planform configuration of channel is characterized with the channel sinuosity, channel length, channel width etc. The Bhutan–Bengal foothill produces million tones of sediments annually through unscientific dolomite mining and deforestation (Bera et al., 2021; Chamling & Bera, 2020a2020b; Saha et al., 2022). These sediments transfer to river Mujnai through multiple left and right hand tributaries. When sediments deposit on channel bed, the straight channel takes sinuous or meandering channel. These channel patterns broadly help bank erosion process as a result channel planform or nodal and local avulsion take place immediately on the dynamic Himalayan flood plain (Ghosh et al., 2022a2022b). A scientific study showed that there is direct positive correlation between the quaternary sediments and the higher incision of the channel (Timer, 2003). In this present research (66 years studied time period), the channel length of all the segments (after 1980 up to 2010) becomes shorter (due to formation of cutoffs) and furthermore (2021) it has been significantly increased. It is concluded that the river bank is more prone to erosion due to sinuous and meandering channel path. Here, abrupt changes of width in downstream have been amplified in between the years 1980 and 1990. The bank failure was mostly happened due to severe flood incidents.

Bank line migration and oscillation are the causes of lateral movement of river bank within the riparian floodplain. The channel of river Mujnai has been tried to adjust within the flow path through the fluvio-hydraulic processes over the time. The flood plain evolution and channel avulsion is largely controlled by neo-tectonic activities of Himalayas (Chakrabarti Goswami et al., 2013). The Foothill Rivers are very dynamic and they are always trying to adjust within their flow path on the younger sediments. Many researchers have studied on channel dynamics, channel avulsion, dynamic confluence shifting, tectonic activities, rainfall pattern and distribution, the quality of water (Sarkar et al., 2021), and so forth particularly on Himalayan foreland basin. Most of the studies identified the above mentioned factors which have been playing significant role in this tectonic belt of Himalayan foothill.

5 CONCLUSION

River bank erosion leads to sediment yield and this is the common phenomenon for the rivers of Himalayan foreland basin (Ghosh et al., 2022a). From around seven decades study (1955–2021), the planform of river Mujnai has been considerably modified through lateral movement, erosion-accretion dynamics and human intervention. The bank erosion of meandering course of river Mujnai has been assessed by Bank Erosion Susceptibility Index (BESI) which has been modified from Rosgen's (2001) BEHI model considering additional three important factors. The erosion vulnerability is higher (approximately 28% areas) in upper segment compared with lower and middle segments of the river channel due to Quaternary noncohesive bank materials with bioturbation and indistinct laminations. Monsoonal high velocity, bank full discharge and severe flood incidents are also accelerating the bank erosion vulnerability particularly in this flood plain (Ghosh and Bera, 2022). Maximum changes of channel width have been noticed during 1980 (avg: 129.69 m) to 1990 (avg: 90.30 m) at the three segments. The scatter riparian vegetation protected the bank as natural channel bank protection element but anthropogenic stress is being triggered the magnitude of bank erosion. In the recent years, high rate of bank erosion as well as channel avulsion is being frequently occurred at the downstream due to impact of channelization or river engineering (construction of bridge, culverts, embankment, revetment, etc.). This scientific study identified some bank erosion vulnerability hotspots and direct causative factors. The BESI model gives more rational and accurate results compared with BEHI model. So, modification is required for the better performance of the model and it helps to build new sustainable floodplain management strategies for the reduction of river bank erosion risk. To combat the massive bank erosion, some sustainable environmental measures can be implemented like zigzag bamboo piling works, rock-filled gabions, retaining wall, gravity walls, cantilever walls, sheet pilling walls, flow control structures, bioengineering, geo-textile fabric, and tree and brush revetment. More applied research or further study is highly needed to discover the exact amount of sediment yield within the basin, flood routing, basin connectivity and tectonic effects on the dynamic flood plain of river Mujnai basin. Govt. should provide more funds and data of river hydraulics for the benefits of the society as well as applied research and development. From this research gap, various new research wings will reopen for scholars and scientists.

ACKNOWLEDGMENT

We thank Geological Survey of India and the local people of North Bengal for providing the valuable information and laboratory assistance. There is no funding for this investigation.

    CONFLICTS OF INTEREST

    The authors declare no conflicts of interest.

    ETHICS STATEMENT

    None declared.

    DATA AVAILABILITY STATEMENT

    The analyzed data that support the findings of this study are available within the article and its supplementary information files.

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