In a stepped spillway, the spillway face is provided with a series of steps from near the crest to the toe. This type of spillway is attractive for water resource management because it dissipates energy that is within the flow. When energy is dissipated by the steps, it reduces the energy reduction that otherwise must occur at the toe of the spillway. In the present study, nine physical stepped spillway models with slopes of 15, 25, 45° and with a number of steps varying from 5 to 50 have been constructed. The crest of the spillways have standard Ogee profiles and a constant slope extends from the crest to the spillway toe. Two different-sized flumes were used in the experiments (25 and 50 cm wide). Several physical models have been constructed in order to measure the energy dissipation. The purpose of this research is to investigate energy dissipation rate in spillways with different slopes. It was found that the two most important dimensionless factors influencing energy dissipation are the Froude number and q2/(gHdam3). The spillway slope and step number have less impact on the rate of energy dissipation. However, for a constant discharge over a stepped spillway, increasing spillway slope, and increasing the number of steps will increase the energy dissipation. Using multiple regressions, some useful relations for determination energy dissipating are obtained.

  • Energy dissipation rate is investigated in stepped spillways with different slopes.

  • It was found that the two most important dimensionless factors influencing energy dissipation are the Froude number and q2/(gHdam3).

  • The spillway slope and step number have less impact on the rate of energy dissipation.

  • Increasing spillway slope and increasing the number of steps will increase the energy dissipation.

Hdam

Spillway height (m);

g

Acceleration due to gravity (m/s2);

ΔH

Difference between specific energy upstream and downstream of chute (m);

y1

Downstream flow depth: i.e. d=qw/Vmax (m);

N

Number of steps on the chute (dimensionless);

y2

Depth of water after hydraulic jump or conjugate depth (m);

q

Discharge per unit width of chute (m2/s);

h/l

Stepped spillway slope (dimensionless);

h

Height of step (m);

l

Length of step (m);

H1

Specific energy at downstream of spillway (m);

Ht

Total specific energy at upstream of spillway (m);

Re

Reynolds number (dimensionless);

Fn

Froude number (dimensionless);

ρ

Water density (kg/m3);

μ

Water dynamic viscosity (N.s/m2);

yc

Critical depth:

Stepped spillways have been used since ancient times, about 3500 years ago. However, some relevant hydraulic aspects of these spillways remain unknown (Chanson 1994a). In recent decades, new dam construction technologies such as the use of roller-compacted concrete (RCC) has increased the development and attention to this type of spillway. Research shows that the amount of energy dissipated in stepped spillways exceeds that of smooth spillways (without steps) with the same dimensions. Significant energy loss allows a reduction of the depth of the cut, the length, and the height of the downstream stilling basin. Consequently, cost savings can be achieved with thoughtful construction.

Most researchers have pointed to two different types of flow regimes called nappe and skimming flow regimes. The first type occurs at low discharge and with high steps. The second type occurs in spillways with high discharge and low step heights (Horner 1971; Chanson 1994b; Salmasi et al. 2021). The transition flow regime is intermediate between nappe and skimming flow regimes and is not very important in terms of design. Oscillating flow over a stepped chute is a characteristic in transition flows (Nouri et al. 2020; Salmasi et al. 2020). In Figure 1, sketches of the three flow regimes are provided.

Figure 1

Schematic representations of the three flow regimes (Salmasi & Özger 2014).

Figure 1

Schematic representations of the three flow regimes (Salmasi & Özger 2014).

Close modal
Horner (1971) and Sorensen (1985) were probably the first researchers to classify flow over stepped spillways into nappe and skimming flow regimes. Based on experiments performed on stepped spillways, the conversion of a nappe flow to a skimming flow occurs at approximately 0.8yc/h (Chanson 1994b) where yc is the critical depth on the spillway (representative of discharge) and h is the vertical height of the step. Chanson (1994c) showed that in addition to the dimensionless parameter yc/h, the spillway slope is also effective in converting a nappe flow to a skimming flow. The results of that study showed that with a skimming flow regime, the discharge must be higher than a critical characteristic value [(yc)onset]. This characteristic onset of skimming flow regime was presented as follows (Chanson 1994c):
(1)

In Equation (1) l is the horizontal length of the step. Many researchers, including Peyras et al. (1992), Chamani & Rajaratnam (1999), and Matos & Quintela (1994), have argued that energy dissipation in the nappe flow regime is greater than in the skimming flow regime. However, according to Chanson (1994b), in long stepped spillways with established flow, the flow energy loss with the skimming flow exceeds that of nappe flow. In response, Matos & Quintela (1994) identified the error caused by air etrainment in the spillway and its effects on measuring flow depth. Consequently, they considered the Chanson (1994a, 1994b)'s conclusions to be questionable. Matos & Quintela (1994) did not consider the use of the aerated water depth downstrem of a spillway to calculate energy loss to be correct; they found that because of the use of aerated water depth instead of pure water depth, the amount of flow energy dissipation was overestimated. Determining the amount of energy loss by indirect methods using the conjugate depth of the hydraulic jump by Tazzi (1992) and Pegram et al. (1999) has also been reported.

Pegram et al. (1999) carried out experiments on stepped and smooth spillways with a slope of 59° and a height of 30 m (model scale was 1:10) and with step heights of 0.25, 0.5, 1.5 and 2 m. Experiments have shown that the energy dissipation contradicts the theoretical estimate of Rajaratnam (1990), who reported this rate to be 89%. The results also showed that the energy dissipation does not depend on the height of the steps. This result is true for the establishment or non-establishment of flow conditions.

Rice & Kadavy (1996) built a model of the stepped spillway of Salado Creek Dam in Texas. The height of the model was 85.35 cm, its slope was 21.8°, and the number of steps was 27. To compare the model, a smooth spillway (without steps) with the same height was made. The slope of the stepped spillway was much smoother than that of Christodoulou (1993) with a slope of 55°.

According to Rice & Kadavy (1996), energy loss should be greater for steep slopes compared to gentle slopes. The results of experiments showed that the energy dissipation in their experiments and results from Christodoulou (1993) show a very good agreement.

Chamani & Rajaratnam (1999) carried out experiments on a stepped spillway with a slope of 59° and with step heights of 125, 62.5 and 31.25 mm and another slope of 51° with step heights of 125 and 31.25 mm. By measuring the concentration of air bubbles entering the flow and its effect on increasing the depth of the flow, they calculated the depth of pure water/clean water (without air) and the pure water depth was used to determine the relative energy loss. The experimental results showed that the relative energy loss in the skimming flow regime varies between 48 and 63%.

Felder & Chanson (2011) performed experiments on a physical model of a stepped spillway with a height of 1 m and a slope of 26.6°. Five different cases were considered for the step heights and the residual energy downstream of the spillways were measured. Although the results showed that the number of steps did not have much effect on the residual downstream energy, a spillway with 10 steps of 10 cm height had less residual energy and thus more energy dissipation. For the five cases, the Darcy-Wiesbach roughness coefficient (f) varied from 0.12 to 0.37, which was consistent with the previous work of Felder & Chanson (2009) in which f varied from 0.1 to 0.35. Shoja et al. (2011) used genetic algorithms to determine the optimal dimensions of the Sarough Dam spillway located in West Azerbaijan province, Iran. The optimization process showed that the stepped spillway led to increased energy dissipation compared to a smooth spillway. This in turn led to the elimination or reduction of stilling basin dimensions downstream of the spillway. For fixed slopes, increasing the discharge reduces the relative energy dissipation, increasing the optimal height of the steps. By analyzing the data obtained from a large number of experiments, Salmasi (2009) showed that energy loss in stepped spillways is affected by the number of steps and for a fixed number of steps, a maximum energy loss can be achieved. Of course, this maximum energy dissipation varies from one spillway to another and depends on the slope of the spillway, the design discharge, and the height of the spillways. Salmasi (2009) also mentioned the new step-by-step design method for stepped spillways.

Due to the increasing importance of stepped spillways, many research studies have been carried out to identify factors that affect energy dissipation. These studies have mainly utilized scaled laboratory tests with physical models (e.g. Pegram et al. 1999; Roushangar et al. 2017). In addition, a few studies have relied upon numerical simulation (e.g. Eghbalzadeh & Javan 2012; Salmasi & Samadi 2018). Salmasi & Abraham (2021) used genetic algorithms for optimizing stepped spillways to maximize energy dissipation. In that study a stepped spillway with optimal dimensions was proposed as a replacement of the smooth spillway of Sarogh Dam located in West Azerbaijan province, Iran.

In the watershed management plan in Kohkiluyeh city, Iran, a number of mortar stone structures with an annual storage capacity of more than 2 million cubic meters will be implemented to strengthen groundwater aquifers. Figure 2 shows a stepped chute constructed in Kohkiluyeh city.

Figure 2

A stepped chute constructed in Kohkiluyeh city, Iran.

Figure 2

A stepped chute constructed in Kohkiluyeh city, Iran.

Close modal

Another example of the construction of a stepped spillway is seen in the earthen dam of Tang Khon river in Bushehr province, Dashtestan city in Iran. This earthen dam has a design flow of 109 m3/s, equivalent to a return period of 100 years, a reservoir volume of 350 million m3, a crest width of 5.5 m, and a crest length of 132 m. Figure 3 shows a panoramic image of the stepped spillway with a width of 19.3 m constructed in this dam.

Figure 3

Tang Khon earthen dam in Bushehr province, Iran and its stepped spillway.

Figure 3

Tang Khon earthen dam in Bushehr province, Iran and its stepped spillway.

Close modal

Moradabad earthen dam was built in 2009 in Firoozabad city, Iran. Figure 4 shows a stone stepped chute constructed with cement mortar. The length of the stepped spillway of this dam is 419 m, its width is 5 m, and its height is 14 m from the riverbed.

Figure 4

A stepped chute from Moradabad earthen dam in Firoozabad city, Iran.

Figure 4

A stepped chute from Moradabad earthen dam in Firoozabad city, Iran.

Close modal

In the present study, nine physical stepped spillway models with slopes of 15, 25 and 45° and with a number of steps varying from 5 to 50 have been constructed. The crest of the spillways have standard Ogee profiles and a constant slope extends from the crest to the spillway toe. Two different-sized flumes were used in the experiments (25 and 50 cm wide). Several physical models have been constructed in order to measure the energy dissipation. The purpose of this study is to investigate energy dissipation rate in spillways with different slopes.

This study was carried out in the laboratory of the Water Engineering Department, Faculty of Agriculture, University of Tabriz, Iran. Nine physical models of stepped spillways with slopes of 45, 25 and 15° and with a number of steps of 5, 10 and 15 were constructed and tested. Two flumes were used for these testing, a flume 50 cm in width and length of 10 m and the other flume with 25 cm width and 12 m length. The spillways with large scales had a slope of 45° and were 50 cm wide and 100 cm high. The spillways with small scales had slopes of 25 and 15° including 25 cm wide and 32 cm high. Table 1 lists some of the specifications of the physical models of the constructed spillways.

Table 1

General specifications of the physical model of stepped spillways

Flume width (cm)Number of experimentsNumber of stepsSpillway height (cm)Spillway slope (degrees)
50 93 5, 10, 15, 20, 35 and 50 100 45 
25 22 5, 10 and 15 32 25 
25 45 5, 10 and 15 32 15 
Flume width (cm)Number of experimentsNumber of stepsSpillway height (cm)Spillway slope (degrees)
50 93 5, 10, 15, 20, 35 and 50 100 45 
25 22 5, 10 and 15 32 25 
25 45 5, 10 and 15 32 15 

Figure 5 shows the longitudinal cross section of the flume with a width of 50 cm and a stepped spillway.

Figure 5

Longitudinal section of the flume, stepped spillway and flow control system in the flume (dimensions are shown in Table 1).

Figure 5

Longitudinal section of the flume, stepped spillway and flow control system in the flume (dimensions are shown in Table 1).

Close modal

The water flow enters the flums through a tank with a fixed height of 4.5 m by the control valve and is transferred downstream after passing over the spillway crest. To control the downstream water and the location of hydraulic jump, a vertical sliding gate was used at the end of the flume. The vertical sliding gate was adjusted in a manner to create a free hydraulic jump downstream of the stopped spillway. In this way both of the y1 and y2 depths (conjugate depths) were measured for the energy dissipation calculation (Equation (5)). The end gate is adjusted to cause a hydraulic jump. Then the conjugate depth (y2) was measured by point gauge. Then y1 is calculated using the hydraulic jump relation. Measurement of the conjugate depth (y2) has the benefit that the air bubbles are lower at y2 than in the y1 section. Clear water depth measurements (without air bubbles), will be more accurate (Khatibi et al. 2014).

Water depths upstream and downstream of the hydraulic jump was measured by a calibrated point gage with an accuracy of 0.1 mm at three points across the width of the flume. Discharge was measured by a 53° triangular weir. Although volumetric measurement of discharge is the most accurate method, several research studies show that triangular weirs provide reasonable accuracy for discharge easements. For example, readers are directed to the studies of Matos & Quintela (1994), Felder & Chonson (2011) and Salmasi & Abraham (2022).

In the water depth section before the hydraulic jump, air was input into the flow (especially at high discharge) and therefore in this section, the two-phase flow (water and air mixture) was measured by a point gauge. Measurement of the water depth after hydraulic jump was performed in a place where small air bubbles were observed in the water flow. Figures 6 and 7 show flow over the physical model of the stepped spillway prepared in this study.

Figure 6

Flow over stepped spillway (downstream view).

Figure 6

Flow over stepped spillway (downstream view).

Close modal
Figure 7

Close-up of flow over stepped spillway (side view), turbulent and energy dissipation at the toe of the spillway (Salmasi & Samadi 2018).

Figure 7

Close-up of flow over stepped spillway (side view), turbulent and energy dissipation at the toe of the spillway (Salmasi & Samadi 2018).

Close modal
In these experiments, depths before and after hydraulic jump were measured. However, to calculate the relative energy loss, the conjugate depth of the hydraulic jump was used due to the presence of fewer air bubbles in this section compared to the section upstream of the hydraulic jump (Salmasi 2003). The amount of energy upstream of the spillway crest, Ht, was calculated as follows:
(2)
In Equation (2), Hdam is equal to the height of the spillway. Its average value is 1 m for a spillway with a width of 50 cm. Conversely. The value of Hdam is 32 cm for a spillway with a width of 25 cm. Also, yc indicates the critical depth on the spillway. It is obtained from the relation yc = (q2/g)1/3, where q is the discharge per unit width of the spillway (m3/s/m) and g is the acceleration of the Earth's gravity equal to 9.81 m/s2. To calculate the energy downstream of the spillway and before the hydraulic jump, conjugate depths of the hydraulic jump were used as follows (Pegram et al. 1999):
(3)
(4)
In Equations (3) and (4), y1 and y2 are the measured depths before and after the hydraulic jump, respectively. It should also be noted that y1 and y2 represent the depths of the ‘water-air mixture/white water’ and the ‘water/clear water’, respectively. The relative energy loss is found from Equation (5):
(5)

In Equation (5), the H1 is the energy downstream of the spillway and before the hydraulic jump (Equation (3)), and the Ht is the total energy upstream of the spillway (Equation (2)), and the rest of the parameters have already been defined.

Dimensional analysis

The purpose of a dimensional analysis method is to find a relationship between effective physical parameters in a natural phenomenon. The obtained relationship among variables with dimensional analysis is usually simpler and can be transfered among unit systems (SI and atc).

Important and effective parameters of the flow through stepped spillways are grouped as follows:

  • Properties related to fluid including: liquid density (ρ), dynamic viscosity (μ), and gravity acceleration (g)

  • Flow-related characteristics including: flow depth (y) and flow velocity (V)

  • Geometric characteristics of the spillway, including: number of steps (N), height of the steps (h), horizontal length of the steps (l) and total height of spillway (Hdam).

The functional relationship can be summarized in Equation (6):
(6)
To convert Equation (6) to a dimensionless fomat, three iterative variables are selected: y, V and ρ. The three variables together include the dimensions M, L, T. Dimensional parameters are defined as follows:
The fourth dimensionless factor is related to the Reynolds number (Re), which is avoided due to the turbulence of the flow over stepped spillway and the creation of a large Reynolds number, and eventually Equation (6) will change to Equation (7):
(7)

The results are presented in four sections:

  1. Relative energy dissipation

  2. The effect of slope on energy dissipation

  3. Comparing the relative energy dissipation of this study with previously published results

  4. Statistical analysis of multivariate linear and nonlinear models for stepped spillways with different slopes of 45, 25 and 15°.

Relative energy dissipation

Figure 8 shows the results of relative energy dissipation in stepped spillways including 5–50 steps with a slope of 45°. The horizontal and vertical axes are both dimensionless. It should be noted that for the sake of brevity, other shapes for slopes of 25 and 15° are not provided in this section.

Figure 8

Relative energy dissipation in stepped spillways of 5–50 steps with a slope of 45°.

Figure 8

Relative energy dissipation in stepped spillways of 5–50 steps with a slope of 45°.

Close modal

According to Figure 8, it can be seen that the relative energy dissipation decreases with increasing dimensionless ratio yc/h. In other words, with increasing discharge, the effect of step roughness on energy dissipation decreases. Conversely, with increasing number of steps (and a reduction in the height of steps), the effect of steps on flow resistance decreases and therefore energy dissipation decreases.

Figure 9 presents another way to visualize the results, but with a change in the dimensionless factor on the horizontal axis. The interesting result is that by normalizing the dimensionless factor on the horizontal axis in yc/(hN), one line can be fitted for all test points so that a more compact equation can be obtained.

Figure 9

Relative energy dissipation in 5–50 step (normalized) stepped spillways with a 45° slope.

Figure 9

Relative energy dissipation in 5–50 step (normalized) stepped spillways with a 45° slope.

Close modal

The effect of slope on energy dissipation

In Figure 10, the effect of a 45° slope (maximum slope) on energy dissipation is compared to 25 and 15° slopes. The effect of the steep slope is probably related to the turbulence, the higher flow velocity, and the incomplete or complete effect of the hydraulic jump on each step (in the case of nappe flow regime). Experimental data show that there is no significant difference in relative energy dissipation between the 25 and 15° slope cases. However, the 25° slope is slightly larger than the 15° slope case. This is probably due to the short height of the spillway. As mentioned before, the spillway models with slopes of 25 and 15° had a height of 32 cm, and therefore the difference in the length of the sloping face on which the steps are located was also small. It seems that the effect of slope on taller spillways (such as the model with a height of 100 cm) will be more apparent. Further experimentation is needed to investigate this issue.

Figure 10

Effect of slope on relative energy dissipation in a 15-step stepped spillway.

Figure 10

Effect of slope on relative energy dissipation in a 15-step stepped spillway.

Close modal

Figure 11 shows the effect of slope on relative energy dissipation in a 15-step stepped spillway. Figure 5 uses the dimensionless factor yc/h and shows that the test points are closer to each other on three slopes and the slope effect has somehow appeared at the height of the steps. Figure 11 is a a normalization of Figure 10.

Figure 11

Effect of slope on relative energy dissipation in a 15-step stepped spillway (normalized).

Figure 11

Effect of slope on relative energy dissipation in a 15-step stepped spillway (normalized).

Close modal

Comparisons of the present results with prior publications

In Figure 12, the results of relative energy dissipation with a 45° slope from this study are compared with results of prior studies. Because the experiments of others have been performed on different slopes, we have tried to make comparisons for the most similar slopes.

Figure 12

Comparison between relative energy consumption with other researchers.

Figure 12

Comparison between relative energy consumption with other researchers.

Close modal

The selected slopes are between 40 and 51°, which are categorized as steep slopes. According to Figure 12, the changes in relative energy dissipation are similar amongst the different datasets. Another result is that increasing the slope increases energy dissipation due to the increase in the amount of exchange movement between the rotational flow under each step and the main flow. This exchange of motion between two currents at different velocities is also expressed by Felder & Chanson (2011).

In Figure 13, the results of this study are compared with the Felder & Chanson (2011) experiments. The dimensionless factor H1/yc was used on the vertical axis (a comparison was not possible in Figure 12), where H1 is obtained from Equation (3). Based on Figure 13, H1/yc varies on average from 2.5 to 4.5 and also decreases with increasing discharge. Another point is that the results of this study show excellent agreement with the results of Felder & Chanson (2011).

Figure 13

Comparison of energy in downstream of stepped spillway in present study with Felder & Chanson (2011) results.

Figure 13

Comparison of energy in downstream of stepped spillway in present study with Felder & Chanson (2011) results.

Close modal

Statistical analysis

Statistical analysis of multivariate linear models for slopes of 45, 25, and 15° will now be presented. All of the information was obtained from the experiments (test spillways in the flume with a widths of 25 and 50 cm), for slopes of 45, 25 and 15° and are provided. The degree and number of different steps ranging from 5 to 50 will be used in multivariate regression equations. Equation (7) obtained from dimensional analysis is considered. Regression equations were obtained by SPSS software. The results of the equations using a single dependent variable are presented in Table 2.

Table 2

Correlation between dependent variable with one independent dimensionless variable

EquationRegression equationR2
 0.898 
 0.477 
10  0.106 
11  0.052 
12  0.086 
EquationRegression equationR2
 0.898 
 0.477 
10  0.106 
11  0.052 
12  0.086 

According to Table 2, it can be seen that the largest regression coefficient is related to the presence of dimensionless parameters q2/(gHdam3). Figure 14 shows this relationship.

Figure 14

The best relationship between relative energy dissipation vs. q2/(gHdam3).

Figure 14

The best relationship between relative energy dissipation vs. q2/(gHdam3).

Close modal

For brevity, not all of the different regression combinations between other dimensionless parameters are shown; only selected equations are presented in Table 3.

Table 3

Selected equations of different combination between dimensionless parameters for stepped spillways with a slope of 45, 25 and 15°

EquationRegression equationR2
13  0.928 
14  0.865 
15  0.903 
16  0.845 
EquationRegression equationR2
13  0.928 
14  0.865 
15  0.903 
16  0.845 

According to Table 3, the correlation between relative energy dissipation and the Froude number (Fr) and q2/(gHdam3) is very high and the determination coefficient (R2) is 903 (Equation (15)).

Figure 15 shows the scatter plot for observed and predicted relative energy dissipation using regession relation (Equation (15)). For improved accuracy, the first equation in Table 3 in which the R2 is equal to 0.928 can be used. It can be seen that by increasing the slope of the spillway or the number of steps, the energy dissipation will also increase. Future work should be performed to investigate the suitableness of using a spillway with 1 m height.

Figure 15

Comparison between experimental data and the proposed relationship (Equation (15)) for estimating relative energy dissipation.

Figure 15

Comparison between experimental data and the proposed relationship (Equation (15)) for estimating relative energy dissipation.

Close modal

Nine physical models of stepped spillways with slopes of 45, 25, and 15° and with the number of steps ranging from 5 to 50 have been constructed and tested. The height of the models was 32 and 100 cm. The energy difference between upstream and downstream of the spillways was measured and then the relative energy dissipation was calculated. Air entrainment inflates the water flow over stepped spillways; the bulking of water due to high air entrainment forces designers to use a greater height for sidewalls in stepped spillways and for the downstream stilling basins.

The results showed that slope alone is not an effective factor for energy dissipation and should be used in combination with other factors. With increasing slope and spillway height, relative energy dissipation increases. It is suggested that the model of stepped spillways with a height of more than 1 m be made and the effect of slope be examined again to verify the robustness of the conclusions.

The most important factors are the Froude number and the dimensionless term q2/(gHdam3). Also, multivariate regression analysis providing relationships between the independent and dependent dimensionless variables was performed and useful relationships were provided to calculate energy dissipation. In engineering applications, for convenience, a smaller number of parameters can be used to calculate energy dissipation (although with acceptable accuracy). The following relationship is recommended for this purpose:

This research did not receive any specific grant from funding agencies in the public, commercial, or not-for-profit sectors. This paper is the outcome of a research project supported by the University of Tabriz research affairs office.

This article does not contain any studies with human participants or animals performed by any of the authors.

The authors declare that they have no conflict of interest.

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

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