The objective of this study is to determine the optimum size of stone revetment for different water standing durations and critical drawdown rates for 80% height of flood. The model bank was constructed using soil sourced from the Parlalpur ferry ghat of the Ganga River in Kaliachak, West Bengal, with a field density of 1,500 kg/m3 achieved by maintaining a 10% moisture content (MC) in the model bank soil. The model riverbank was prepared considering Froude (F) similitude having a distorted depth scale of 1/20 and a linear scale of 1/200. In this study, effective stone sizes (D10) – 2.33, 3.22, 4.58, 6.31, and 8.84 mm – were used. These stone sizes were investigated in conjunction with three water standing durations: 15, 30, and 45 min. The bank slope was prepared at 1V:1.5H, and a drawdown ratio of 80% was maintained. The effectiveness of stone revetment size was analysed in terms of the percentage loss of stone revetment and the percentage loss of the model bank's cross-sectional area. The outcomes of this study indicate that the 6.31 mm stone size exhibits optimal performance.

  • Optimized stone size was determined.

  • This underscores the importance of careful stone selection, considering soil characteristics.

  • The findings of this study offer valuable insights into the temporal dynamics of bank stability under real-world hydrological conditions, which are beneficial for engineers.

  • The importance of synergetic impact of drawdown and velocity for designing the stone revetment for river bank protection.

The hazards of riverbank failure and land loss present a global concern. West Bengal witnesses significant distress among riverside residents annually, leading to substantial expenditures on protection efforts, amounting to hundreds of crores (Thakur et al. 2012; Mondal & Patel 2020). Unfortunately, many of these protective measures fail to endure beyond the subsequent monsoon seasons (Deng et al. 2022), because most of the protection has been done without a proper understanding of the causes of failure. Bank stability analysis is a complex problem in comparison with a normal slope stability problem (Khatun et al. 2019). Under submergence, a soil mass effective stress decreases, lowering its shear strength (Li & Aubertin 2010). As a result, the mechanical and physical characteristics of the soil vary as the water-level varies (Parker et al. 2008). The pace and direction of seepage flow are regulated by changes in the water level of a submerged riverbank (Okeke et al. 2020). When the external water-level changes without giving the water on the bank enough time to drain, it is known as a sudden or rapid drawdown (Berilgen 2007). It is widely acknowledged that seepage into the bank, as opposed to seepage in the opposite direction, increases the stability of the bank due to matric suction, and that seepage from the bank towards the river decreases the shear strength of the bank material (Semmad et al. 2022), thereby reducing its stability due to an increase in positive pore water pressure that also leads to bank failure (Dapporto et al. 2003; Rinaldi et al. 2004; Nardi et al. 2011).

For the protection of riverbanks, several methods and materials, such as vanes, bank pitching, spurs, groynes, guide vanes, jack-jetty systems, board fencing, tetrahedral frames, natural geotextiles such as jute geotextile (JGT), vetiver grass, soil nailing, grouting, geotextile, and geogrid, have been used in the field. Stone revetment is also one of the methods to protect the riverbank. The effect of turbulence intensity on riprap stability was studied experimentally by Amirshahi et al. (2022). The stable riprap size was increased by 2.5 times when turbulence was increased from 10% to 25%. Myagmar et al. (2023) did the cost–benefit analysis of bioengineering and mechanical methods for bank protection. Zhou et al. (2024) explored the field and conducted a numerical study on bank failure, considering the direct action of flow and the application of river stage change to bank revetment.

Depending on the nature of riverbank failure with respect to geotechnical properties and hydraulic loading, specific measures for protecting the banks have been made (Duong Thi & Do Minh 2019). Stone revetment is one of the popular methods among others to protect against the failure of the riverbank (Craig & Zale 2001; Schmetterling et al. 2001; Reid & Church 2015). Depending on the construction method adopted, ripraps can be classified as either dumped or placed (Ravindra et al. 2020). Dumped riprap comprises stones that are haphazardly deposited, whereas placed riprap involves arranging stones in an interlocking pattern (Hiller et al. 2018). Stone revetment offers flexible protection with self-healing capacity, low construction costs, long-lasting performance, and easy repair (Jafarnejad et al. 2017; Jafarnejad et al. 2019).

For designing riprap (stone revetment), several methods and codes are available such as IRC:89-1997 (1997), IS:14262 (1995), Hydraulic Engineering Circular No. 11 (Brown & Clyde 1989), Escarameia & May (1992), Pilarczyk (1990), Maynord et al. (1989), Maynord (1992), and Isbash (1935). All these methods considered mean flow velocity as the most important factor in determining the rock size for the protection of riverbanks. Water-level depletion, also called sudden drawdown, is also one of the causes of the failure of the riverbank (Kim et al. 2023; Zhou et al. 2023). Jamal et al. (2024) showed the importance of the drawdown and time on bank failure. Despite these valuable observations, a notable research gap remains. Specifically, there is a need to investigate the optimal size of stone revetment, the impact of drawdown, improvements in the vertical settlement of protected bank, the potential for shifts in failure locations, and the duration of protected bank exposure against the water level.

An attempt has been made to find out the optimal effective size of stone for different water exposure times and sudden drawdown. A total of 45 design experiments have been performed in the fabricated model. The percentage loss of the cross-sectional area of the most damaged section of the model bank and the percentage loss of stone revetment for different sizes and different periods were considered in this study.

Physical model tests of a riverbank were conducted in this study to examine the impact of the time and size of stone for effective protection under drawdown. The model bank was prepared with soil collected from Parlalpur ferry ghat on the river Ganga, Kaliachak, Malda district, West Bengal State, India. Gravity is a dominating factor in the modelling of riverbanks. Froude (F) similitude is suitable for the physical modelling of the riverbank. In their experimental study on the stability of riverbanks, Khatun et al. (2019) took a scale of 1:25. Jafarnejad et al. (2019) and Aziz & Islam (2023) took a scale range of 1:20 to 1:30, respectively. Considering these studies, a distorted scale of (linear) Lr = 1/200 and a (depth) of Hr = 1/20 were taken for the preparation of the bank model. The height of the bank at the selected site was 3.2 m. A bank height of 16 cm was kept in the model to simulate the 3.2 m height in the field. Other parameters of the model and prototype are mentioned in Table 1.

Table 1

Dimensions of flume

ParametersValue (flume)Riverbank (model)Riverbank (prototype)
Length 90 cm 90 cm 180 m 
Width 40 cm 24 cm – 
Depth 25.5 cm 16 cm 3.2 m 
Standing time 15, 30, and 45 min  11.15, 22.3, and 33.45 h 
ParametersValue (flume)Riverbank (model)Riverbank (prototype)
Length 90 cm 90 cm 180 m 
Width 40 cm 24 cm – 
Depth 25.5 cm 16 cm 3.2 m 
Standing time 15, 30, and 45 min  11.15, 22.3, and 33.45 h 

The moisture content (MC) of the bank soil was kept at 10% to achieve the field density of 1,500 kg/m3. The whole setup for the model tests was constructed in the laboratory at Aliah University, Kolkata, India. A series of experiments was conducted to assess the effectiveness of various stone sizes (D10) in protecting the model riverbank. Five different stone sizes – 2.33, 3.22, 4.58, 6.31, and 8.84 mm – were chosen. Each stone size was evaluated under three different water standing times: 15, 30, and 45 min. The slope of the bank was kept at 1V:1.5H and the drawdown ratio was 80%. The effective size of the stone was determined in terms of the percentage loss of stone revetment and the percentage loss of the cross-sectional area of the model bank. A total of 45 design experiments were performed to find the effectiveness of stone size. The profile of the maximum damage area was taken to represent the failure plane of the model riverbank. Simultaneously, the loss of stone revetment under different durations was also taken for effectiveness of the protected bank. The model setup was erected in a laboratory of 90 cm long, 40 cm wide, and 25.5 cm deep for the model bank preparation. The inlet and outlet capacity of the model was 250 and 68 ml/s, respectively (Figure 1).
Figure 1

Laboratory model.

Figure 1

Laboratory model.

Close modal

Material

Soil properties

The soil was collected from the Parlalpur ferry ghat of river Ganga, Kaliachak, Malda district, West Bengal, India, for the preparation of the model bank. The soil collected from the riverbank site was air-dried and pulverized. The collected soil sample was characterized for index and engineering properties according to the procedure mentioned in different Indian Standards. All tests were conducted in the Geotechnical Engineering Laboratory of Aliah University, Kolkata, India.

Soil investigation reveals that the soil was silty clay. The index and engineering properties of the soil are tabulated (Table 2) (IS:2720-Part-1, 2, 3, 4, 5, 12, 17).

Table 2

Physical properties of the soil

PropertiesValues
Specific gravity 2.61 
Grain size distribution Sand – 8.36%, silt – 60.67%, 
clay – 30.88% 
Silt factor 0.229 
Co-efficient of uniformity (Cu) 3.72 
Co-efficient of curvature (Cc) 0.38 
Permeability (cm/s) 2.8 × 10−7 
Shear strength parameters C – 0.6 kN/m2 
Ø – 15.20° 
Liquid limit 40.2 
Plastic limit 19.2 
Plasticity index 18.36 
PropertiesValues
Specific gravity 2.61 
Grain size distribution Sand – 8.36%, silt – 60.67%, 
clay – 30.88% 
Silt factor 0.229 
Co-efficient of uniformity (Cu) 3.72 
Co-efficient of curvature (Cc) 0.38 
Permeability (cm/s) 2.8 × 10−7 
Shear strength parameters C – 0.6 kN/m2 
Ø – 15.20° 
Liquid limit 40.2 
Plastic limit 19.2 
Plasticity index 18.36 

Stone revetment properties

The aggregate was collected from the quarry. The detailed properties of the aggregate are tabulated in Table 3 (ASTM 1993, 2007; IS:2386 (1963)).

Table 3

Properties of aggregate

PropertiesTesting specificationValues
The specific gravity of CA ASTM C127  2.62 
The specific gravity of FA ASTM C128  2.65 
Water absorption of CA (%) ASTM C127  0.62 
Water absorption of FA (%) ASTM C128  0.62 
Impact value (%) IS:2386 (Part IV) 22.2 
Loss angles abrasion value (%) IS:2386 (Part IV) 20.5 
Shape test value (%) IS:2386 (Part I) 21.3 
PropertiesTesting specificationValues
The specific gravity of CA ASTM C127  2.62 
The specific gravity of FA ASTM C128  2.65 
Water absorption of CA (%) ASTM C127  0.62 
Water absorption of FA (%) ASTM C128  0.62 
Impact value (%) IS:2386 (Part IV) 22.2 
Loss angles abrasion value (%) IS:2386 (Part IV) 20.5 
Shape test value (%) IS:2386 (Part I) 21.3 

Note: CA, coarse aggregate; FA, fine aggregate.

Preparation of the model riverbank

For model riverbank preparation, the soil sample was collected from the Parlalpur at a depth of 1.2 m of the river Ganga, Kaliachak, Malda district, West Bengal. After being air-dried and pulverized, the sample was sieved through a 4.75 mm sieve. To obtain the necessary bulk density for a 10% MC, the model riverbank of a slope of 1V:1.5H was prepared in three layers using a compaction energy of 20.49 kJ/m3. The top surface of the model bank was protected with the varying stone sizes (D10) of 2.33, 3.22, 4.58, 6.31, and 8.84 mm. The water level was maintained at 80% height of the bank and the duration of exposure to water was 15, 30, and 45 min. The drawdown rate was maintained at 4.5 mm/s while adjusting the outlet valve and the pump. Vertical settlement, along the slope for different points, was measured using the profile gauge to find the profile of the bank after the drawdown. The failure profile of the bank was used to calculate the percentage loss of the area of the model bank. The weight of the remaining stone on the bank was taken after the test. This observation was used to analyse the percentage loss of stone revetment after drawdown for different durations and the different sizes of stone (Table 4). A schematic diagram of the model bank protected with stone revetment is shown in Figure 2.
Table 4

Summary of the experimental programme

Aggregate size (D10) (mm)Drawdown rate (mm/s)Original C/S area of bank (cm2)Weight of aggregate (g)No. of trial experimentsAverage weight after the test (g)Water standing time (min)% Loss of aggregateAverage area changing (cm2)% Loss of area
2.33 4.5 mm/s 192 2,413 1,481.58 15 38.6 145.73 24.10 
2,413 1,322.32 30 45.2 127.20 33.75 
2,413 1,298.19 45 46.2 123.61 35.62 
3.22 3,256 2,399.67 15 26.3 168.00 12.5 
3,256 2,324.78 30 28.6 162.62 15.3 
3,256 2,272.69 45 30.2 160.51 16.4 
4.58 3,924 3,088.19 15 21.3 170.50 11.2 
3,924 2,958.70 30 24.6 165.50 13.8 
3,924 2,939.08 45 25.1 164.93 14.1 
6.31 4,543 3,988.75 15 12.2 178.18 7.2 
4,543 3,893.35 30 14.3 176.83 7.9 
4,543 3,875.18 45 14.7 176.06 8.3 
8.84 6,023 4,932.84 15 18.1 172.42 10.2 
6,023 4,770.22 30 20.8 164.16 14.5 
6,023 4,752.15 45 21.1 163.01 15.1 
Aggregate size (D10) (mm)Drawdown rate (mm/s)Original C/S area of bank (cm2)Weight of aggregate (g)No. of trial experimentsAverage weight after the test (g)Water standing time (min)% Loss of aggregateAverage area changing (cm2)% Loss of area
2.33 4.5 mm/s 192 2,413 1,481.58 15 38.6 145.73 24.10 
2,413 1,322.32 30 45.2 127.20 33.75 
2,413 1,298.19 45 46.2 123.61 35.62 
3.22 3,256 2,399.67 15 26.3 168.00 12.5 
3,256 2,324.78 30 28.6 162.62 15.3 
3,256 2,272.69 45 30.2 160.51 16.4 
4.58 3,924 3,088.19 15 21.3 170.50 11.2 
3,924 2,958.70 30 24.6 165.50 13.8 
3,924 2,939.08 45 25.1 164.93 14.1 
6.31 4,543 3,988.75 15 12.2 178.18 7.2 
4,543 3,893.35 30 14.3 176.83 7.9 
4,543 3,875.18 45 14.7 176.06 8.3 
8.84 6,023 4,932.84 15 18.1 172.42 10.2 
6,023 4,770.22 30 20.8 164.16 14.5 
6,023 4,752.15 45 21.1 163.01 15.1 

Note: C/S, cross-sectional.

Figure 2

(a) Schematic diagram, (b) model bank, (c) during the water test and (d) after the test.

Figure 2

(a) Schematic diagram, (b) model bank, (c) during the water test and (d) after the test.

Close modal

The data obtained by the series of experiments have been examined to find the influence of the size of the stone, drawdown, and water standing time on the model bank.

Impact of the time and size of stone on the maximum vertical settlement of the bank

Figure 3 presents the maximum vertical settlement observed in the model riverbank for varying water standing durations. The study revealed distinct fluctuations in the vertical settlement of the bank based on different effective stone revetment protection sizes. The experimental findings indicate that during the initial standing time, the model bank experienced a maximum vertical settlement of 32.2 mm. As the water standing duration increased from 15 to 30 and 45 min, the vertical settlement exhibited an escalation of 25.69% and 31.88%, respectively. This phenomenon can be attributed to the saturation of the model bank. The increase in water standing duration led to reduced shear strength within the bank, allowing for higher settlement. During the drawdown, the dissipation of pore water pressure from the bank caused the failure of the model bank. Furthermore, the results demonstrate that between the 30- and 45-minute water standing durations, the settlement increased by only 4.9%. This finding suggests that beyond a certain point of water standing time, the vertical settlement tends to stabilize and remain relatively constant (Jamal et al. 2024). This stabilization can be attributed to the soil reaching a state of saturation and limiting further failure or settlement.
Figure 3

Effect of water-level observation time on vertical settlements and the size of stone.

Figure 3

Effect of water-level observation time on vertical settlements and the size of stone.

Close modal

The study results provide valuable insights into the influence of stone size on the vertical settlement of the model riverbank. Notably, there is a clear relationship between stone size and the extent of vertical settlement, as shown in Figure 3. As the stone size increases, the vertical settlement of the bank decreases significantly, with settlements ranging from 32.3 mm for smaller stone sizes to 15.3 mm for larger stone sizes. This decrease represents a substantial reduction in vertical settlement, amounting to a 52.6% decrease. Additionally, an interesting pattern emerges in the data. There exists an optimal stone size of around 6.33 mm, at which the vertical settlement is minimized. Beyond this optimal size, further increases in stone size increase settlement. This pattern underscores the notion that simply using larger stone sizes does not guarantee optimal protection for the model bank. These findings highlight the importance of tailoring the choice of stone size to the specific characteristics of the soil and the intended purpose of the bank protection. It is not a one-size-fits-all solution, and an optimum stone size should be determined based on factors such as the type of soil and the environmental conditions. This insight is invaluable for engineering and design considerations in riverbank protection as it emphasizes the need for a customized approach in selecting the most effective stone revetment size to ensure the stability and protection of riverbanks.

Analysis of the vertical erosion rate in relation to time and stone size

In this study, the drawdown rate was considered as 4.5 mm/s (Khatun et al. 2019). Considering this drawdown rate, maximum vertical erosion rates were analysed for different time durations and the different sizes of stone (Figure 4). The results show that the erosion rate did not follow the same rate as the drawdown rate. It indicates that the failure of the bank takes some time after the drawdown to achieve the maximum vertical erosion. The model bank shows a slow sliding of the bank due to slow releasing of pore water pressure from the bank, which will cause outward forces from the back of the bank, resulting in the failure of the bank. The results show that for the 2.33 mm size of stone and 15-min observation time, the erosion rate was 2.15 mm/min. As the size of the stone increased, the rate of vertical erosion decreased from 2.15 to 1.37, 1.04, 0.6, and 1.02 mm/min for the stone revetment sizes of 3.22, 4.58, 6.31, and 8.84 mm, respectively. It can be observed from Figure 4 that the vertical erosion gains its optimum value for the revetment size of 6.31 mm. With further increase in the size to 8.84 mm, the vertical erosion rate again increases. The results show the same pattern for other cases of observation times. Considering all observation times for different riprap sizes, it was concluded that the 6.31 mm size of stone revetment was the optimum size for arresting the model bank failure.
Figure 4

Effect of time and stone size on the erosion rate.

Figure 4

Effect of time and stone size on the erosion rate.

Close modal

Shifting of maximum settlement location along the model riverbank

Figure 5 offers valuable insights into the displacement of the maximum vertical settlement location along the model river bank (Aziz & Islam 2023). These observations were derived from physically identifying the point of maximum vertical settlement and then measuring the corresponding distance. The initial observation, conducted at 15 min with a 2.33 mm stone size, revealed that the maximum vertical settlement was located at 168.2 mm from the bank's toe, accounting for 41.67% of the total bank length.
Figure 5

Effect of size and observation time on shifting of the maximum vertical location from the toe.

Figure 5

Effect of size and observation time on shifting of the maximum vertical location from the toe.

Close modal
Figure 6

Effect of size and time on the reduction of cross-sectional area and riprap of the model bank.

Figure 6

Effect of size and time on the reduction of cross-sectional area and riprap of the model bank.

Close modal
Figure 7

Profile of the model bank protected with (a) D10 = 2.33 mm stone revetment, (b) D10 = 3.22 mm stone revetment, (c) D10 = 4.58 mm stone revetment, (d) D10 = 6.31 mm stone revetment, and (e) D10 = 8.84 mm stone revetment.

Figure 7

Profile of the model bank protected with (a) D10 = 2.33 mm stone revetment, (b) D10 = 3.22 mm stone revetment, (c) D10 = 4.58 mm stone revetment, (d) D10 = 6.31 mm stone revetment, and (e) D10 = 8.84 mm stone revetment.

Close modal

With extended observation times of 30 and 45 min, the location of maximum vertical settlement shifted further from the toe, reaching 192.3 and 193.8 mm, respectively. These distances represented 33.3% and 32.8% of the total bank length. These results suggest that as water standing time increases, the point of maximum vertical settlement tends to move away from the bank's toe, with a relatively stable pattern emerging after the 30-min mark. Furthermore, the size of the stone influenced the shifting of the maximum settlement location from the bank's toe. As the stone size increased from 2.33 to 3.22, 4.58, 6.31, and 8.84 mm, the shifting of the failure location was observed at 120.1, 48, 72.1, and 96.1 mm, respectively. These findings highlight that a stone size of 4.58 mm appeared to be most effective in preventing the shifting of the failure location along the bank. In summary, Figure 5 illustrates how the maximum vertical settlement location changes relative to time and stone size. The results emphasize the influence of these factors on the stability and protection of the riverbank, with important implications for the design of revetment and strategies to prevent the shifting of failure locations.

Impact of the time and size of stone on the model bank area

Figure 6 illustrates the variation in the model bank's area loss across different water standing durations and stone sizes. The analysis reveals that employing solely large stone sizes does not effectively mitigate the model bank's failure. Therefore, determining the effective size and weight per unit area of the deployed stone is crucial before implementing bank protection measures. The graphical representation demonstrates a trend wherein increasing effective stone sizes corresponds to improved bank protection. Specifically, a 6.31 mm stone size consistently exhibits optimal performance across all standing times. Beyond this size, a decrease in effectiveness is observed, resulting in greater area loss for the bank and stone revetment. Initially, the bank possessed a cross-sectional area of 192 cm2 and a surface area of 2,595.6 cm2.

Using 2.33 mm stone initially resulted in a required weight of 2,413 g. Subsequent observations at 15-, 30-, and 45-min standing times revealed declining cross-sectional areas of 145.73, 127.20, and 123.61 cm2, indicating area losses of 24.1%, 33.75%, and 35.62%, respectively. Correspondingly, stone losses were noted at 38.6%, 45.2%, and 46.2% for the 2.33 mm size and 15-, 30-, and 45-min durations. However, employing a 6.31 mm stone revetment demonstrated area losses of 7.2%, 7.9%, and 8.3%, with revetment losses of 12.2%, 14.3%, and 14.7% for the same time intervals. This optimal size notably safeguarded the bank area by 91%–93%, with minimal impact from varying water standing durations. Overall, the data underscore the significance of the 6.31 mm stone size, emphasizing its efficacy in protecting bank areas while exhibiting lower susceptibility to the effects of differing water standing durations.

Model bank profile study for different conditions

The different profiles of the model bank before and after the experiment are shown in Figure 7. The bank profile of the model bank was measured with the help of a measuring gauge. Initially, the vertical rod of the measuring gauge was lowered down to determine the initial model bank profile. After the drawdown, the most damaged section of the model bank was located, and the measuring rod was lowered down to measure the deformation. The difference between the initial reading of the rod and the reading after the test gave the profile of the bank. It has been observed that the effective size (D10) of 2.33 mm shows failure from the crest of the model bank for time durations of 15, 30, and 45 min. The percentage area loss of the bank for a particular location was 24.10%, 33.75%, and 35.62%, respectively. The difference in area loss between 30 and 45 min of water exposure is not significant. The same pattern is observed for other sizes of the stone. As the size increases, the location of failure also shows a significant improvement in shifting towards the toe of the model bank (Jafarnejad et al. 2017, 2019). The effective size of 6.33 mm shows the maximum protection of the model bank in terms of area loss and stone revetment loss. The area and revetment losses for the size of 6.33 mm were less than 10% and 15%, respectively. Losses increase above the 6.33 mm size of stone in area and riprap.

In the present study, the stability of a stone revetment-protected model bank and the response against the different temporal variations were analysed. The outcome of this study may be recommended in field applications for the stable revetment for silt-dominated clay riverbanks or small pond banks. The principal findings are outlined below:

  • (1)

    The study identifies 6.31 mm as the optimal stone revetment size for model bank protection in a laboratory-developed boundary condition. This size shows the minimum loss of revetment (12.2%–14.7%) and cross-sectional area loss (7.2%–8.3%). This finding indicates the critical role of precise stone-sizing in optimizing riverbank protection.

  • (2)

    The study challenges the common fact that larger stones give good protection. Stones with an 8.84 mm diameter, compared with the optimal 6.31 mm size, exhibited reduced benefits, increased area losses, and more revetment dislodgment. This underscores the importance of careful stone selection, considering soil characteristics.

  • (3)

    The maximum vertical bank settlement during various water exposure times reveals that after achieving full saturation, the substantial settlement variations cease. These findings offer valuable insights into the temporal dynamics of bank stability under real-world hydrological conditions, benefitting engineers.

  • (4)

    During the drawdown, the dissipation of pore water pressure emerged as a key mechanism leading to bank failure. So, for designing any protection work, the synergetic impact of drawdown and velocity has to be considered.

All authors have read, understood, and have complied as applicable with the statement on ‘Ethical responsibilities of Authors’, as found in the Instructions for Authors.

This research received no external funding.

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

The authors declare there is no conflict.

Amirshahi
S. M.
,
Zarrati
A. R.
,
Tabarestani
M. K.
&
Tabesh
M.
2022
Effect of turbulence intensity on riprap stability over streambeds
.
Journal of Hydraulic Engineering
148
(
10
),
06022013
.
ASTM
1993
Standard Method of Test for Specific Gravity and Absorption of Coarse Aggregate
.
ASTM C127-88, ASTM International, West Conshohocken, PA, USA
.
ASTM
2007
Standard Test Method for Relative Density (Specific Gravity) and Absorption of Fine Aggregate
.
ASTM C128-22, ASTM International, West Conshohocken, PA, USA
.
Aziz, S. & Islam, M. S. 2023 Erosion and runoff reduction potential of vetiver grass for hill slopes: a physical model study. International Journal of Sediment Research 38 (1), 49–65.
Berilgen
M. M.
2007
Investigation of stability of slopes under drawdown conditions
.
Computers and Geotechnics
34
(
2
),
81
91
.
Brown
S. A.
&
Clyde
E. S.
1989
Design of Riprap Revetment. Hydraulic Engineering Circular 11
,
Federal Highway Administration
,
McLean, VA, USA
.
Craig
A. J.
&
Zale
A. V.
2001
Effects of Bank Stabilization Structures on Fish and Their Habitat: A Literature Review
.
Montana Cooperative Fishery Research Unit, US Army Corps of Engineers and Governor's Upper Yellowstone River Task Force
,
MT, USA
.
Dapporto
S.
,
Rinaldi
M.
,
Casagli
N.
&
Vannocci
P.
2003
Mechanisms of riverbank failure along the Arno River, Central Italy
.
Earth Surface Processes and Landforms
28
,
1303
1323
.
Deng
S.
,
Xia
J.
,
Zhou
M.
,
Zhou
Y.
,
Liu
X.
&
Li
Z.
2022
Riparian groundwater level variation and its impacts on bank erosion in the Middle Yangtze River
.
Water Resources Research
58
(
7
),
e2022WR032354
.
Escarameia
M.
&
May
R. W. P.
1992
Channel Protection: Turbulence Downstream of Structures
.
Rep. No. SR313
,
Hydraulics Research Ltd, Wallingford
,
UK
.
Hiller
P. H.
,
Aberle
J.
&
Lia
L.
2018
Displacements as failure origin of placed riprap on steep slopes
.
Journal of Hydraulic Research
56
(
2
),
141
155
.
IRC:89-1997
1997
Guidelines for Design and Construction of River Training and Control Works for Road Bridges
.
Indian Roads Congress
,
New Delhi, India
.
IS 14262
1995
Planning and Design of Revetment – Guidelines
.
Bureau of Indian Standards
,
New Delhi, India
.
IS:2386 (Part I through IV)
1963
Methods of Test for Aggregates for Concrete
.
Bureau of Indian Standards Publications, New Delhi, India
.
IS:2720-Part 1
1983
Methods of Test for Soils. Preparation of Dry Soil Samples for Tests
.
Bureau of Indian Standards Publications
,
New Delhi, India
.
IS:2720-Part 2
1973
Methods of Test for Soils. Determination of Water Content
.
Bureau of Indian Standards Publications
,
New Delhi, India
.
IS:2720-Part 3-Sec-2
1980
Methods of Test for Soils. Determination of Specific Gravity
.
Bureau of Indian Standards Publications
,
New Delhi, India
.
IS:2720-Part 4
1985
Methods of Test for Soils. Grain Size Analysis
.
Bureau of Indian Standards Publications
,
New Delhi, India
.
IS:2720-Part 5
1985
Methods of Test for Soils. Determination of Liquid and Plastic Limit
.
Bureau of Indian Standards Publications
,
New Delhi, India
.
IS:2720-Part 12
1981
Methods of Test for Soils. Determination of Shear Strength Parameters of Soil
.
Bureau of Indian Standards Publications
,
New Delhi, India
.
IS:2720-Part 17
1986
Methods of Test for Soils. Laboratory Determination of Permeability
.
Bureau of Indian Standards Publications
,
New Delhi, India
.
Isbash
S. V.
1935
Construction of Dams by Dumping Stones in Flowing Water
(Dorijikov, A., trans.)
.
War Dept, US Engineer Office, Engineering Division
,
Eastport, ME, USA
.
Jafarnejad
M.
,
Franca
M. J.
,
Pfister
M.
&
Schleiss
A. J.
2017
Time-based failure analysis of compressed riverbank riprap
.
Journal of Hydraulic Research
55
(
2
),
224
235
.
Jafarnejad
M.
,
Franca
M. J.
,
Pfister
M.
&
Schleiss
A. J.
2019
Design of riverbank riprap using large, individually placed blocks
.
Journal of Hydraulic Engineering
145
(
2
),
04019042
.
https://doi.org/10.1061/(asce)hy.1943-7900.0001641
.
Jamal
M.
,
Mondal
A.
,
Adil
M. R.
,
Khatun
S.
&
Tandel
Y.
2024
The intermediate river bank protection technique in critical geo-fluvial conditions using jute rope grid
.
Indian Geotechnical Journal
.
doi:10.1007/s40098-023-00851-z
.
Maynord
S. T.
1992
Riprap Stability: Studies in Near-Prototype Size Laboratory Channel
.
Technical Rep. No. HL-92-5
,
US Army Engineer Waterways Experiment Station
,
Vicksburg, MS, USA
.
Maynord
S. T.
,
Ruff
J. F.
&
Abt
S. R.
1989
Riprap design
.
Journal of Hydraulic Engineering
115
(
7
),
937
949
.
https://doi.org/10.1061/(ASCE)0733-9429(1989)115:7(937)
.
Mondal
S.
&
Patel
P. P.
2020
Implementing vetiver grass-based riverbank protection programmes in rural West Bengal, India
.
Natural Hazards
103
,
1051
1076
.
https://doi.org/10.1007/s11069-020-04025-5
.
Myagmar
K.
,
Darkhijav
B.
,
Renchin
T.
&
Chultem
D.
2023
Cost–benefit analysis for riverbank erosion control approaches in the steppe area
.
Environment, Development and Sustainability
25
(
9
),
9251
9266
.
Nardi
L.
,
Rinaldi
M.
&
Solari
L.
2011
An experimental investigation on mass failures occurring in a river bank composed of sandy gravel
.
Geomorphology
163–164
,
56
69
.
Okeke
C. A. U.
,
Azuh
D.
,
Ogbuagu
F. U.
&
Kogure
T.
2020
Assessment of land use impact and seepage erosion contributions to seasonal variations in riverbank stability: the Iju River, SW Nigeria
.
Groundwater for Sustainable Development
11
,
100448
.
Pilarczyk
K. W.
1990
Coastal Protection
A.A. Balkema
,
Rotterdam, The Netherlands
.
Ravindra
G. H. R.
,
Gronz
O.
,
Dost
J. B.
&
Sigtryggsdóttir
F. G.
2020
Description of failure mechanism in placed riprap on steep slope with unsupported toe using smartstone probes
.
Engineering Structures
221,
111038
.
Reid
D.
&
Church
M.
2015
Geomorphic and ecological consequences of riprap placement in river systems
.
JAWRA – Journal of the American Water Resources Association
51
(
4
),
1043
1059
.
Rinaldi
M.
,
Casagli
N.
,
Dapporto
S.
&
Gargini
A.
2004
Monitoring and modelling of pore water pressure changes and riverbank stability during flow events
.
Earth Surface Processes and Landforms
29
,
237
254
.
Schmetterling
D. A.
,
Clancy
C. G.
&
Brandt
T. M.
2001
Effects of riprap bank reinforcement on stream salmonids in the western United States
.
Fisheries Habitat
26
(
7
),
6
13
.
Semmad
S.
,
Jotisankasa
A.
,
Mahannopkul
K.
&
Inazumi
S.
2022
A coupled simulation of lateral erosion, unsaturated seepage and bank instability due to prolonged high flow
.
Geomechanics for Energy and the Environment
32
,
100301
.
Zhou
Y.
,
Qi
S. C.
,
Wang
L.
,
Chen
M. L.
,
Xie
C.
&
Zhou
J. W.
2023
Instability analysis of a quaternary deposition slope after two sudden events of river water fluctuations
.
European Journal of Environmental and Civil Engineering
27
(
7
),
2488
2506
.
This is an Open Access article distributed under the terms of the Creative Commons Attribution Licence (CC BY 4.0), which permits copying, adaptation and redistribution, provided the original work is properly cited (http://creativecommons.org/licenses/by/4.0/).