The effects of kinetic sorting on sediment mobility on steep slopes
ABSTRACT
In poorly mobile static armour, sorting is usually considered the result of hiding/exposure effects. We called this effect ‘static sorting’ in opposition to very efficient grain-to-grain mechanisms produced by a mobile mixture, called ‘kinetic sorting’. We hypothesized that kinetic sorting can be an important contributor to the morphodynamics of mountain streams and attempted to demonstrate this with new flume experiments.
Two long runs were produced with natural poorly sorted sediments, and with transport stages of the coarse fraction (defined by the ratio between the shear stress and the critical shear stress for transport), smaller and higher than 1, respectively. Both runs produced an efficient transfer downstream of the injected material, but with a major difference: the first run (no kinetic sorting) produced permanent armour figuring clusters, akin to what has already been observed in similar experiments; the second run (with kinetic sorting) also produced bed armouring, but this armour was periodically totally destroyed, leading to substantial bed erosion.
This phenomenon was explained by kinetic sorting, the effects of which are to produce an efficient downward migration of fine materials and bed surface armouring. The consequence is that fine materials are hidden to the flow during aggradation, allowing the slope to attain values much steeper than would have been expected at equilibrium for the mixture. However, whereas the surface armouring tends to stabilize the bed, construction of a layer of fine sediments at the subsurface also contributes to making it very unstable. These two contradictory effects explain the complex bed behaviours and the existence of very large bedload and slope fluctuations. Copyright © 2014 John Wiley & Sons, Ltd.
Introduction
In mountain streams, bed stability is controlled by the mobility of large stones present at the bed surface (Church and Zimmerman, 2007; Chartrand et al., 2011). Several studies have attempted to determine the conditions pertaining to this mobility: the threshold transport conditions were shown to vary with slope as a consequence of changing hydraulics (Mueller et al., 2005; Lamb et al., 2008; Recking, 2009; Ferguson, 2012; Bunte et al., 2013); the role of large floods and later bed recovery was investigated (Gintz et al., 1996; Lenzi, 2001; Lenzi et al., 2004; Turowski et al., 2009; Turowski et al., 2011); and the effects of the sediment supply condition were demonstrated (Gilbert, 1914; Curran and Wilcock, 2005b; Recking, 2012; Recking et al., 2012; Waters and Curran, 2012). However, more than in all other streams, grain sorting is evident in mountain streams; it is even prominent considering that in such streams longitudinal sorting essentially occurs at the form scale. This is well illustrated with step-pools, where clusters of coarse sediments in the steps alternate with zones of fine deposition in pools. Vertical sorting produces stratification, with fine sediments being embedded below a coarse surface (Pitlick et al., 2008). However, grain sorting observed on the bed at rest is usually considered to result from transport (i.e. selective transport by the flow), rather than being a real contributor to transport (i.e. a factor controlling grain mobility). Its direct contribution is often reduced to the concept of hiding/exposure, where the mobility of fine grains is reduced by the proximity of large grains, whereas the mobility of large grains is enhanced by their greater exposure to the flow (Einstein and Chien, 1953; Egiazaroff, 1965; Parker and Klingeman, 1982). We hypothesize here that this global concept (usually sufficient to explain the dynamics of sediment mixtures on slopes milder than approximately 1%) is not sufficient to explain the dynamics of mountain streams where the grain size distribution can be very large: static sorting of fine materials in immobile clean large grains coexists with kinetic sieving, i.e. a grain-to-grain mechanism by which finer particles percolate very efficiently downward within a moving coarser bed (Frey and Church, 2009, 2011).
Most studies on size sorting have investigated the infiltration of fine particles in a coarser immobile bed (Beschta and Jackson, 1979; Frostick et al., 1984; Lisle, 1989; Wooster et al., 2008). Motivations have included salmonid spawning substrate conditions, stratigraphical interpretation, placer mineral concentration and consequences of dam removal, forest fires and more generally land use change. In the idealized case of uniform spheres, the spontaneous infiltration of smaller spheres under the sole effect of gravity is a simple problem. It occurs when the size ratio of the larger to the smaller sphere is greater than about 6.5 (Troadec and Dodds, 1993). In the case of poorly sorted and variably shaped natural material, the problem is much more complicated (Luchnikov et al., 1999). For example, Gibson et al. (2009) studied the vertical distribution of the fine interstitial deposits with depth distinguishing between unimpeded static percolation and bridging where fine materials form a thin layer within a few large grain diameters below the surface.
From this point onwards, we will use the term ‘static sorting’ in lieu of spontaneous percolation or infiltration. When coarser particles are moving, transient void openings permit downward percolation of smaller particles, including those only slightly finer than moving coarser grains, a phenomenon variously called kinetic (Middleton, 1970), kinematic or dynamic, or random fluctuating sieving. We will herein call this phenomenon ‘kinetic sorting’.
Kinetic sorting can easily be observed in a simple experiment, without water: consider a coarse mixture deposited in a box; deposition of finer grains over this static coarse layer will have only limited movement downward by infiltration; but as soon as the box is vibrated, even very slightly, fine grains rapidly disappear from the surface as a consequence of the coarse grain displacement (Figure 1). This phenomenon has been poorly studied in relation to river morphodynamics, although it has been described qualitatively (Einstein, 1968; Parker and Klingeman, 1982). Kinetic sorting has been studied more in the powder and grain community and more oriented towards industrial applications. It has been studied experimentally and theoretically with dry granular material in inclined chute flows (Savage and Lun, 1988; Bridgwater, 1994). Most studies have considered a low size ratio, rarely above 5, where small particles invariably percolated downward. For higher ratios, coarser particles can be found at intermediate levels evolving continuously from the surface to deeper levels (Thomas, 2000). This more complex behaviour may be due to the relative importance of both kinetic sorting and static sorting experimentally. In a study of bedload at the grain scale, Hergault et al. (2010) studied kinetic sorting. A very small amount of smaller beads were introduced into a bedload flow initially only composed of larger moving beads. The result was a quasi-continuous layer of small particles located below the moving larger beads and above the quasi-immobile larger beads.

In mountain streams, the watershed supplies the channel with a mixture of very coarse sediments in addition to fine sand and gravels, and since in such streams flows usually transport the largest elements at near threshold conditions (Church and Zimmerman, 2007), kinetic sorting may be significant. This has been shown in a previous flume experiment (Recking, 2006; Recking et al., 2009), comprising 20 runs performed just above the threshold conditions with different sediment mixtures and with the slope considered within the range 1–9%. A very efficient vertical sorting process was evidenced by bed sampling, revealing the kinetic sorting phenomenon when the flow conditions were such that 1 < τ*/τc* < 2 (where τ* = RS/(1.65D) is the Shields number calculated for the diameter D, R is the flow hydraulic radius, S is the slope and τc* is the critical Shields stress for threshold motion of diameter D). It was also shown that this sorting process was responsible for a periodical bed behaviour, alternating between armouring and erosion, with peak solid discharges associated with bedload sheet migration. However, these experiments were all conducted above the threshold condition for the mobility of the coarser material (i.e. potentially producing kinetic sorting), and it was not possible to isolate the role of kinetic sorting by comparison with a reference experiment without kinetic sorting.
This has motivated this work, and we present the results of two long-duration runs (called Run 1 and Run 2) carried out near the threshold conditions, over ~100 h each and on a 12% slope, with the same graded sediment mixture matching natural grain size distributions. Both runs are characterized by a transport stage τ84*/τc84* ~ 1 (with τ* computed for diameter D84), but kinetic sorting was assumed to be negligible in Run 1 with τ84*/τc84* taken just below 1, and to exist in Run 2 with τ84*/τc84* taken just above 1. Both runs produced an efficient transfer downstream of the injected material, but with a major difference: the first run (no kinetic sorting) produced permanent armour figuring clusters, similar to what has already been observed in similar experiments; the second run (with kinetic sorting) also produced bed armouring, but this armour was periodically totally destroyed, leading to considerable bed erosion. The first part of the paper recalls the experimental set-up, the second part describes the experimental observations, the third part presents the measurement analysis, and finally implications for mountain stream morphodynamics are discussed.
Matherials and Methods
Experimental arrangement
The experimental setup consisted of a 6-m-long, 0.1-m-wide tilting flume. We chose to use a narrow flume in order to prevent the formation of bedforms (lateral bars) and we did not add lateral wall roughness in order to allow efficient lateral observations of how the bed evolved. Because of the large width-to-depth ratios used (W/d > 5), no side wall effects were expected for the hydraulics (Song et al., 1995). In addition, another 50 h of experiments (not shown here) have confirmed that all observations presented in this paper are reproduced similarly when the same sediment mixture and flow conditions are used with rough walls (obtained by gluing sediments on the glass walls, as shown in a video available as Supplementary Material to this paper).
The flow rate at the flume inlet was controlled by a constant head reservoir and measured using an electromagnetic flow-meter. The choice of a feed instead of a recirculating experiment is important (Parker and Wilcock, 1993). A recirculating experiment is more likely to represent the long-term evolution of an infinite channel in interaction with the transported sediment. Given that the objective of the present work was to study the effects of grain sorting, it was essential to maintain a constant grain size distribution at the flume entrance, and therefore a feed experiment was used. This choice is also consistent with mountain streams, especially in the upstream parts of the catchment where sediments are fed directly by hill slope processes. The sediment feeding device was composed of a feeding tank and a conveyor belt whose velocity was controlled during all the experiments with a special tachometer device (see Recking et al. 2009 for a more detailed description). The sediment mixture used for the experiments was obtained by mixing several nearly uniform mixtures whose median size was 1.0 mm, 2.1 mm, 4.9 mm, 9.0 mm, 12.5 mm and 18.7 mm; the final grain size distribution (noted hereafter GSD) respected a similitude with natural material (as described in Recking, 2013a) and was characterized by D16 = 1.8 mm, D30 = 2.1 mm, D50 = 3.2 mm, D84 = 9.0 mm and Dm = 6.0 mm (arithmetic mean diameter). The largest grains of the grain size distribution (corresponding to the 9.0 mm, 12.5 mm and 18.7 mm mixtures) were painted with three different colours in order to facilitate the experimental observations. To measure local and mean bed slope (difference between the bed height at the flume entrance and the bed height outlet divided by the total bed length), we used seven staff gauges placed along the flume side (with the same procedure as described in Recking et al., 2009).
The outlet bedload transport was sampled with a bucket every 5 min (the sample was dried and weighed) and also measured with a light table and a customized video system (Frey et al., 2003): at the outlet of the flume, the mixture of sand, gravel and water was forced to flow on a tilted transparent ramp placed above an illuminated waterproof box. A video camera was placed above the plate and operated in back-lighted mode. Software with specific libraries was developed to grab and save series of several images, which were processed with a segmentation algorithm (WIMA software, Ducottet, 1994) for computing the transport rate (see Frey et al., 2003 for greater detail).
To determine the surface GSD, digital images were collected (every 3 h) from approximately 1.5 m above the bed. The camera was attached to a mechanical arm moving along the channel and two kinds of shots were taken. A first shot captured about 10 cm × 1 m of the bed and was used to have a qualitative estimate of the bed armouring. A second shot captured about 10 × 15 cm of the bed and was used to compute the local bed surface grain size distribution, with a Wolman count procedure (Wolman, 1954); 100 stones were counted for each sample using a digital regular step grid. The run had to be stopped before each GSD measurement, and no impact of these stops could be detected when analysing the slope and bedload signals. In fact, when the flow was stopped, the sediments ceased to move within a few seconds, i.e. within a timeframe much smaller than the timeframe which characteristically controls the bed morphodynamics.
Experimental conditions



Run 1 (Static sorting) | Run 2 (Kinetic sorting) | |
---|---|---|
Q (L/s) | 0.3 | 0.55 |
Qs (g/s) | 6 | 60 |
U (m/s) | 0.28 | 0.33 |
d (cm) | 1.1 | 1.7 |
d/D84 | 1.2 | 1.9 |
![]() |
0.072 | 0.098 |
![]() |
0.084 | 0.084 |
![]() |
< 1 (0.86) | >1 (1.18) |
Duration (h) | 110 | 92 |

The strength of this equation stems from its having been obtained by another independent study using a different method. Whereas Equation 4 was obtained by investigating the effect of bedload transport on flow resistance (Recking, 2006, 2008). Shvidchenko et al. (2001) obtained the same equation (coefficient, 0.11–0.2, varying with grain diameter, and exponent, 0.278) using their own flume measurements.
The computed values are presented in Table 1 and indicate that discharges of Q = 0.3 L/s and 0.55 L/s produce transport stages of τ84*/τc84* = 0.86 and 1.18, respectively. These values are of course dependent on the equations used for their computation; this is why the theoretical approach was complemented with additional tests (by running water over a bed composed of 9 mm of uniform material), which confirmed no sediment movement for Q = 0.3 L/s and material entrainment for 0.55 L/s.
A bedload equation proposed in Recking et al. (2008b) was also used (with the mean diameter of the sediment mixture) to estimate the associated solid discharge for a 12% slope. The values obtained for Q = 0.3 L/s and 0.55 L/s were 8 g/s and 62 g/s, respectively. Each run was started with these computed values. Since we wanted self-made beds, the runs were started with slopes milder than the 12% theoretical equilibrium slope. For instance, Run 1 was started with a 9% slope and it required 200 h for the bed to reach equilibrium (when the mean bed slope stabilized and the average outlet solid discharge equalled the input value). Finally, the conditions were adjusted by trial and error and for each discharge Q = 0.3 L/s and 0.55 L/s, the solid discharge was 6 g/s and 60 g/s, respectively, for a mean bed slope of 12.2%. The total durations for Run 1 and Run 2 (started once the bed was considered at equilibrium) were 110 h and 92 h, respectively.
It is worth noting an important characteristic of these experiments, that is, for a given run, the flow and solid discharge were maintained constant at the inlet during the entire run. This implies that patterns and associated fluctuations observed in the flume are directly linked to the process of transport, and not to variations in the inlet values. This was a necessary condition with regard to the objectives of this study, which was to identify the effects of kinetic sorting on bedload transport and associated bed morphology.
Observations
Large fluctuations of the slope and bedload transport
A dynamic equilibrium was attained for Run 1 and Run 2, with a constant mean bed slope and outlet solid discharge, but with fluctuations measured around these mean values (the bed never stabilized). The main differences observed between Run 1 and Run 2 concern the amplitude of these fluctuations, occurring at different time and space scales (Figure 2). The slope fluctuations were larger in Run 2, where on five occasions (noted E1 to E5, separated by a time step of approximately 15 h), the slope attained a peak at the final stage of a long aggradation process, followed by sharp and rapid bed erosion. On the other hand, bedload fluctuations (with reference to the inlet bedload transport value) were larger in Run 1. Considering the mean input bedload values Qs-mean (6 g/s and 60 g/s for Run 1 and Run 2, respectively), the instantaneous bedload Qs measured at the flume outlet produced Qs/Qs-mean ratios as high as 10 for Run 1, whereas these ratios were smaller than 3 for Run 2.

Bed armouring in Run 1 and Run 2
Despite similar bed surface armouring could be measured in both runs, as shown by the pictures and the grain size distributions in Figure 3, the bed dynamic was very different. In Run 1 the armour was generalized to the entire channel surface and persistent throughout the experiment (except very short erosions occurring at the flume entrance as discussed later), whereas in Run 2 it usually developed over short distances, was very unstable and periodically destroyed, leading to local erosion. Only in a few circumstances, corresponding to the final stage of a long aggradation process preceding peaks E1 to E5, did the bed armour develop over the entire channel bed in Run 2. This bed state was always associated with reduced sediment mobility and minimum bedload transport.

A second difference between Run 1 and Run 2 is that in Run 1 the bed developed transverse clusters, forming step-like structures (but no clear step–pool sequences were observed), whereas in Run 2 the coarse sediments interacted in a more random pattern. Despite its permanent armour and transvers clusters, Run 1 produced an efficient transfer downstream of the injected sediment (no bed aggradation or erosion over the long term); this was possible by cluster destabilization and progressive migration, from place to place, of the largest elements, as was already described for step pool destruction (Rosport and Dittrich, 1995; Church and Zimmerman, 2007; Curran, 2007, 2012)
Vertical sorting in Run 2
In addition to bed surface armouring, very efficient vertical sorting was observed in Run 2. This could be observed visually through the transparent wall, but also by sampling the bed. The bed subsurface was sampled after manually removing the coarse surface over one grain diameter. Figure 4 presents two bed pictures of Run 2, taken at the same location with and without the bed surface, and the associated grain size distributions. It appears visually that the subsurface is composed essentially of fine sediments, which was confirmed by sieving. The thickness of the subsurface layer varied between one and several time the sand diameter in Run 2, whereas it was quasi-inexistent in Run 1.

Bedload sheet production in Run 1 and Run 2
In both runs, the bed armour was periodically destroyed, giving place to local erosion and downstream propagation of sediments, taking the form of bedload sheets (Iseya and Ikeda, 1987; Recking et al., 2009). These successive bed armouring and erosion episodes were responsible for high (with regards to the experiment duration and its critical time scales) frequency fluctuations of the upstream slope, with periods of about 15 min and 1 h for Run 1 and Run 2, respectively.
One important result is that bedload sheets were observed only where the coarse material was mobile (i.e. when kinetic sorting was possible): in Run 1 (with τ84*/τc84* <1) they were limited to the upstream part of the channel only (over a distance of approximately 0.5 m), close to the feeding device, where the coarse grains were mobile because of kinetic energy associated with the injection; in Run 2 (with τ84*/τc84* >1) bedload sheets were observed in all parts of the channel.
This capacity to produce bedload sheets has strongly impacted the dynamics of bedload transport measured at the flume outlet. In Run 2, bedload fluctuations were strongly controlled by bedload sheets, as shown in a video available as supplementary material to this paper. This was not the case for Run 1 where bedload sheets produced in the flume upstream part rapidly disappeared when interacting downstream with the bed armour, and almost never attained the flume outlet. Actually, in Run 1, bedload fluctuations were more the consequence of streamwise sorting, with increased mobility of sediments every time a cluster was destabilized immediately upstream of the outlet section.
Substantial bed erosion in Run 2
On five occasions, Run 2 developed complete bed surface armouring as the final stage of a long aggradation process (peaks E1 to E5 in Figure 2). This bed armour was systematically destroyed, replaced by considerable bed erosion affecting the entire flume length. Erosion events always started in the form of a bedload sheet at the upstream end of the flume (described above), before propagating downstream. The process of armour destruction was very similar to what has been described in other reports (Iseya and Ikeda, 1987; Kuhnle and Southard, 1988; Recking et al., 2009): by reducing bed roughness, fine materials transported in bedload sheets increase the transport efficiency of coarse material, which contributes to destabilizing the nearby local armour by impacting the gravel at rest, and the armour is destroyed from place to place in the downstream direction. This phenomenon is illustrated by a video provided as supplementary material to this paper (armour destruction in a bimodal material corresponding to Run 1 and Figure 5 in Recking et al., 2009). After each large erosion event, the resulting bed surface was composed essentially of fine sediments; but this bed state was always ephemeral, replaced by new clusters and bed armouring (new aggradation). Substantial bed erosion is shown in Figure 5, featuring the three associated bed states (from left to right): complete armour, transitional bed (armour destruction propagating from upstream to downstream) and finally, eroded bed. The slope change resulting from such erosion was always very high (3% in Figure 5). The associated GSDs are shown in Figure 6 and vary a great deal around the mean GSD (input mixture).


Analysis
Slope fluctuations
The amplitude of slope fluctuations is larger in Run 2 (between 11.3 and 14.5%) than in Run 1 (between 11.8 and 12.8%): this was an unexpected result, in contradiction with Recking et al. (2009), who observed a reduced amplitude of slope fluctuations with increasing flow conditions. However, in the experiments of Recking et al. (2009) the flow conditions were such that kinetic sorting was always possible, as in Run 2. The absence of kinetic sorting in Run 1 explains permanent armour, with no large bed erosion events, and small bed slope fluctuations limited successive local bed erosion at the flume upstream end only.
The slope signals measured for Run 1 and Run 2 also differ in shape. Both signals comprise a high frequency associated with bedload sheet production at the flume upstream end, but in Run 2 these high frequencies are superposed on low frequencies, absent in Run 1. The low frequencies of Run 2 in Figure 2 actually correspond to rapid episodes of slope increase and decrease (peaks). We identified five of these peaks in Figure 2, noted E1 to E5. Figure 7 plots the frequency distributions for the mean bed slope S and each local slope S12 (upstream) to S7v (downstream) for Run 2. Whereas the local slopes could vary between 8% and 17%, the resulting mean bed slope is constrained between 11 and 15%. This result is possible only if there is no correlation between the local slopes, which was confirmed by a correlation matrix showing a maximum correlation coefficient of 0.3 between two subsequent sections of the channel, and a decreasing coefficient when the distance between the two sections was increased. However, this absence of correlation was not true during the peaks preceding the large bed erosion events (peaks E1 to E5, Figure 2): each of them coincided with simultaneous maximum local slopes (between 13 and 17%), as indicated in Table 2.

Erosion | Time (h) | S12 | S23 | S34 | S45 | S56 | S67 | S7-v | S |
---|---|---|---|---|---|---|---|---|---|
E1 | 30.9 | 0.13 | 0.14 | 0.14 | 0.13 | 0.13 | 0.15 | 0.15 | 0.14 |
E2 | 45.1 | 0.19 | 0.15 | 0.15 | 0.15 | 0.15 | 0.15 | 0.14 | 0.15 |
E3 | 62.1 | 0.14 | 0.16 | 0.14 | 0.16 | 0.14 | 0.13 | 0.14 | 0.14 |
E4 | 77.4 | 0.14 | 0.14 | 0.14 | 0.17 | 0.15 | 0.14 | 0.13 | 0.15 |
E5 | 84.4 | 0.17 | 0.14 | 0.14 | 0.16 | 0.14 | 0.14 | 0.15 | 0.15 |
We used wavelet analyses to confirm these observations since they have recently been shown in several studies to be powerful tools to analyse bedload transport measurement time series (Singh et al., 2011; Singh et al., 2012). The advantage compared with the classic Fourier transform is that it has an easy space/time interpretation, showing where and at which time scale/frequency the energy of the signal is concentrated. We used the classical discrete decomposition using the Daubechies (1992) wavelet family. Three vanishing moments were chosen, since they led to optimal significant decomposition level numbers with regard to the run lengths, namely seven and eight decomposition levels for Runs 1 and 2, respectively. These levels correspond to the temporal scales over which the temporal signal is analysed, so that the magnitude of the signal as a function of these scales is simply the discrete wavelet spectrum returned by the transformation (Figure 8, top). The fraction of variance at each time scale has also been used as an average of the wavelet spectrum similar to the Fourier spectrum, so as to highlight the predominant time scales in each of the two runs (Figure 8, bottom).

Figure 8 presents the results for the mean bed slope analyses. In the bottom subplots, the x-axes represent time and the y-axes the percentage of variance at each time scale considered (the residual variance, i.e. the part of the signal not taken into account by decomposition, is 5 and 14% for Run 1 and Run 2, respectively, which is very small and, hence, considered satisfactory). Figure 8 (bottom) indicates that the maximum energy corresponds to the medium frequencies for Run 1 and Run 2, but that Run 2 is clearly characterized by more energy in the low frequencies (time scales ~2–5 h), which corresponds to the large bed erosion events in Run 2. The peak events in Run 2 can be traced back on the wavelet spectrum (Figure 8, top). Where a Fourier transform would have indicated the existence of low frequencies, the wavelet analysis shows that the peaks not only correspond to the low frequencies, but they also correspond to a concomitance of maximum energy in several levels of the decomposition. This is consistent with the concomitance of maximum slopes attained in each part of the flume before erosion, as described above.
Figure 9 presents the wavelet decomposition for the upstream and the downstream part of the flume. It shows that the low frequencies are more pronounced for the local downstream slope, implying that the complex slope fluctuation would reflect the behaviour of the different parts of the canal eroding and aggrading at different rates.

We conclude from the above results that high rates of bedload sheet production in the flume upstream part impose its high frequencies on the slope signal; these bedload sheets progressively feed the downstream part of the flume, which aggrades slowly, imposing its low frequencies on the slope signal. In the long term, substantial erosion occurs when aggradation is complete for the entire bed (simultaneous maximum local slopes for each part of the flume).
Bedload fluctuations
Figure 10 plots the fractional transport measured at the flume outlet for Run 1 and Run 2. For the sake of clarity, the signal was reduced to 4 h and to two sediment classes considering diameters above and below 3 mm (D50), and different scales were used for the y-axes (but same time scale on the x-axes).

Figure 10 shows that in Run 1, bedload fluctuations took the form of individual peaks, with a short time duration not exceeding a few minutes. Each peak corresponded to individual cluster destruction immediately upstream of the outlet section, and no clear correlation can be seen with the slope. In Run 2, transport events were longer than in Run 1 (up to 0.5 h) and are typical of what has already been described for bedload sheets (Kuhnle and Southard, 1988): (1) bedload transport correlates well with slope fluctuation (it drops to almost zero each time the bed aggrades and is maximum during slope decrease), and (2) coarse gravel (D > 3 mm) usually peaks shortly before the smaller materials (D < 3 mm) at the beginning of each pulse, which is consistent with a gravel peak controlled by impact effects at the leading edge of the migrating bedload sheets. These peaks correspond to the passage of bedload sheets described above and are shown in the videos provided as Supplementary Material.
Wavelet decomposition (shown in Figure 11 for Run 2) indicates similar results for both Run 1 and Run 2: high frequencies (almost no information in levels higher than 4) and an exponential shape of the variance ratios as a function of the time scale. Actually, the output solid discharge in Run 1 was controlled essentially by step–pool destruction occurring at the downstream end of the flume, and producing a quasi-binary response of the transport signal (zero or peak transport). This explanation also holds for Run 2, where no correlation could be observed between the transport intensity and amplitude of the slope fluctuation: transport rate in Run 2 alternates between near zero and a maximum value (associated with transport in bedload sheets as shown in Figure 10 and in the videos provided as Supplementary Material). The wavelet analysis also showed a negative correlation between the output solid discharge and the mean bed slope. In other words, an eroding bed was associated with a peak solid discharge and inversely, an aggrading bed was associated with a low solid discharge, which seems intuitive.

Discussion
Comparison with other observations made on steep slopes
The results presented above should be placed within the general context of research dealing with steep slope flume experiments. The Run 1 experiment is close to many other step–pool experiments (Rosport and Dittrich, 1995; Church and Zimmerman, 2007; Curran, 2007, 2012), showing poor mobility of coarse sediments (τ*/τc* < 1). On the other hand, Run 2 was characterized by constant sediment feeding, a natural mixture comprising a high percentage of sand (nearly 30%), a transport stage in the range 1 < τ*/τc* < 2 and a long duration (92 h): it corresponds to an experimental condition that has rarely (if at all) been considered (except in Recking et al., 2009, but with a strictly bimodal mixture).
Many steep slope experiments were conducted with a high shear stress ratio τ*/τc* > 2 (Smart and Jaeggi, 1983; Rickenmann, 1991; Recking et al., 2008a). It was shown that such flow conditions produce near equal mobility of the transported material and are associated with no bedload or slope fluctuations (Recking et al., 2009). On the other hand, step–pool flume experiments, all conducted on steep slopes with poorly sorted materials, did not report such large fluctuations, with superposed periods and bedload sheet production (Grant and Mizumura, 1992; Curran and Wilcock, 2005a; Comiti et al., 2009; Zimmermann, 2009). This can be explained by many factors including insufficient duration (most experiments published in the literature lasted less than 10 h), absence of constant sediment feeding and coarsening of the sediment mixture (the proportion of sand of our mixture was 30%). Only the experiments from Suzuki et al. (1998) and Ikeda and Iseya (1988), conducted on steep slopes with a large grain size distribution, produced high levels of bed erosion similar to that described here; however these experiments were too short (a few hours) to measure the complex fluctuation pattern described in Run 2.
Many reports have been published during the last two decades concerning the hydraulics, transported sediment and morphodynamics of step–pool streams (exhaustive reviews were reported by Chin and Wohl, 2005; Church and Zimmerman, 2007; Comiti and Mao, 2012). Because of the difficulty of measuring exceptional flow events capable of moving large boulders composing the steps, most of these studies have investigated the dynamics associated with relatively low flow conditions (τ*/τc* < < 1 for boulders); also considering the short time scale for field observation, the phenomenon described here could not be observed in these studies.
Mechanisms responsible for fluctuations
Some studies have proposed a statistical description of bedload fluctuations at the grain scale (Ancey et al., 2006; Ancey et al., 2008; Heyman et al., 2013), but none of the experiments conducted with nearly uniform material (Smart and Jaeggi, 1983; Rickenmann, 1991; Recking et al., 2008a) has described the large bedload and slope fluctuations we are considering here, whatever the Shields stress τ*/τc* ratio used. This was an argument put forward by Recking et al. (2009) for concluding that these fluctuations are the consequence of grain sorting only. Given the imposed flow conditions (fixed inlet discharge) and kinetic sorting, how can we explain the existence of quasi-periodical and finite amplitude fluctuations?
Local bed shear stress controls sediment mobility. Unfortunately, it was not possible to measure precisely the bed shear stress or the hydraulics in these steep slope experiments with small relative depth. In addition, even though the runs were performed with a constant discharge, the slope, grain size distribution and bedload transport always changed with time. As a consequence, the fractional transport could not be matched appropriately to the bed shear stress. However, shear stress alone does not explain the fluctuations observed because whatever the bed state and slope, stopping the sediment feeding always produced a rapid selective transport of fine material, as well as coarsening and stabilization of the bed surface. Only the association with sediment forcing leads to large fluctuations.

This function supports the existence of periodical slope and bedload fluctuations, as the efficiency term e (which depends on the GSD of the bed surface and of the transported sediments) changes throughout the experiment under the effect of grain sorting. The value of e is maximum in bedload sheets, where the transport of coarse material is very efficient. Actually, higher mobility of coarse gravels when transported within a mixture was demonstrated nearly a century ago by Gilbert (1914). Other later studies also demonstrated that injection of fine sediments can increase gravel transport efficiency for a given flow condition (Raudkivi and Ettema, 1982; Ferguson et al., 1989; Wilcock et al., 2001; Curran and Wilcock, 2005b) or destabilize a previously armoured and immobile bed (Jackson and Beschta, 1984; Cui et al., 2003; Venditti et al., 2010).
On the basis of Equation 5, Recking et al. (2009) proposed a general scenario for mechanisms leading to fluctuations: during aggradation, kinetic sorting produces an efficient downward migration of fine materials and bed surface armouring. For the given feeding rates, the low transport efficiency leads the slope to aggrade with respect to Equation 5. Inevitably, because aggradation cannot be infinite, it stops when a critical (maximum) slope is attained (or, considering the constant flow, when the flow power is strong enough for transporting the injected sediments). Then the injected fine material is no longer embedded (kinetic sorting stops) and is entirely transported once the armour interstices are filled. Reducing the bed roughness increases the transport efficiency of coarse material, and the slope erodes for this new efficiency following Equation 5. In this process, displacement of coarse material also contributes to destabilizing the nearby local armour by impacting the gravel at rest (Iseya and Ikeda, 1987; Kuhnle and Southard, 1988). This phenomenon is reproduced from place to place in the downstream direction, as long as the local slope is higher than required for the given transport rate efficiency. After erosion, the bed surface is composed of fine sediments essentially, but the reduced flow competence associated with the reduced slope rapidly leads to reduced mobility of coarse gravel (which usually is captured in small sediment waves), and the formation of new clusters, which progressively evolve into a new bed armour. From this point, the low transport rate efficiency leads to new bed aggradation, following Equation 5. As a consequence, for a given sediment mixture, the constancy of the eS product (Equation 5) maintains the slope fluctuations between two limiting values.
The above conceptual model explains local bed aggradation and erosion, as well as bedload sheets production. Extending it to the entire flume length explains the multi-scale bed erosions and associated superposed periods of the slope signal (Recking, 2013b).
Consequences for field applications
The authors acknowledge that what has been presented here was produced in a flume, and that more work is needed to confirm these results, especially in the field where the time scales necessary for observing similar processes would be much longer. However, more and more people live in mountain areas, and because catastrophic events due to mountain streams are generated not only by water discharge, but also by the transported solids, we believe that it is important not to neglect some of the aspects developed here.
The first consequence of these experiments is that evaluation of the degree of bed surface armouring may not be sufficient to predict the bed stability of mountain streams. Indeed, both Run 1 and Run 2 produced armoured beds; both runs provided efficient transfer downstream of the injected material, but over the long term only Run 1 had a permanent armour, whereas Run 2 (allowing kinetic sorting) produced substantial erosion.
The second consequence of these experiments is that a catastrophic flood event may not be necessary to produce significant bed erosion: such erosion was obtained in Run 2 with a constant flow and τ84*/τc84* ~ 1. Large events are known to control the morphology of mountain streams by destroying chain forces and allowing the availability for transport of finer sediments stored in the bed. These events able to move boulders are rare, with return periods estimated to be ~20–50 years (Whittaker and Jaeggi, 1982; Grant et al., 1990; Chin, 1998; Lenzi, 2001; Turowski et al., 2009; Molnar et al., 2010; Recking et al., 2012). Between two large events, the bed stores materials coming from the watershed. The experiments reported herein suggest that the channel will behave differently depending on whether the hydrological regime permits flows such that on average τ84*/τc84* < 1 or τ84*/τc84* > 1. If τ84*/τc84* < 1 the bed will store material until the next large event occurs. If τ84*/τc84* > 1, the bed will aggrade (with a velocity depending on the rate of the sediment supply) and substantial erosion can occur in response to internal bed stability criteria, even for low to moderate flow events.
A third consequence of these experiments is that for a given slope, sediment mixture and flow condition, a large set of bedload transport rates can exist. When fine sediments are mobilized in the bedload layer, they smooth the bed and enhance the transportation of coarse sediments. These effects were observed in channels connected to active hillslope processes (Recking, 2012; Recking et al., 2012) or when fine sediments stored in the bed are released in the recovery period following a large flow event (Gintz et al., 1996; Lenzi, 2001; Lenzi et al., 2004; Turowski et al., 2009). Here we demonstrated that because fine sediments cannot be stored indefinitely in the bed by kinetic sorting, they can also periodically participate in transport and produce peak bedload transport.
Conclusion
Grain sorting is a complex component of bedload transport, especially in steep mountain streams. We tried to demonstrate that, in addition to the classical concept of hiding/exposure effects, a very efficient grain-to-grain interaction in the moving layer co-exists, called kinetic sorting. We therefore conducted two lengthy flume experiments, with the same sediment mixture, but with two flow conditions characterized on average by τ84*/τc84* < 1 (Run 1, without kinetic sorting) and τ84*/τc84* > 1 (Run 2, with kinetic sorting).
Conducted under constant supply conditions, the experiments showed large fluctuations for slope and bedload transport. Both experiments were able to produce an armoured bed, but each time kinetic sorting was possible (at the flume entrance because of the kinetic energy associated with sediment injection in Run 1, and in all parts of the flume for Run 2), the armour was systematically and periodically destroyed, leading to peaks of solid discharge. This was explained because kinetic sorting produces a bed stratification during the aggrading phase of a bed construction and stops when a maximum slope is attained for the given flow. Thus, fine sediments are transported, and, by smoothing the bed, they increase the transport efficiency of the coarse sediments. This phenomenon, which finally leads to bed armour destruction, is reproduced from place to place in the downstream direction, as long as the local slope is higher than a critical value (which will depend on the grain size distribution and the flow for a given experiment).
From a practical point of view, this means that an armoured bed does not guarantee the stability of a mountainous channel, and that exceptional flow events may not be necessary to produce very large bed erosion. The ability of the stream to produce kinetic sorting should also be considered in risk mitigation strategies.
Acknowledgements
This research was supported by Irstea, the ANR GESTRANS project (ANR-09-RISK-004/GESTRANS), the French ‘Institut National des Sciences de l'Univers’ programme EC2CO-BIOHEFECT, and the EU Interreg projects Sedalp and Risba. The author would also like to thank three anonymous reviewers who greatly contributed to this paper by providing helpful reviews of an earlier version of this manuscript.