1. 6.3 Sediment management options
Phil Lawrence

2. Summary sediment management strategy
Limit the diversion of coarser sediments
Transport fine sediments through canals to the fields
Make provision for the inevitable rise in command levels

3. Limiting the diversion of coarser sediments: four options
Locate intakes at outside of bends
Sediment excluding intakes
Limit diversion when wadi flows high –throttling structures or close gates
Secondary sediment control

4. (1) Location of intakes at bends
The low flow channel carrying flood recession flows forms at the outside of a wadi bend. (Traditional intakes are placed at the outside of wadi bends for this reason.)
In floods bed load sweep will move the largest sediments towards the inside of a bend and away from an intake.

5. Bed load sweep at a channel bend

6. Traditional intake showing location at the outside of a wadi bend

7. Limiting the diversion of coarser sediments
Locate intakes at outside of bends
(2) Sediment excluding intakes
Limit diversion when wadi flows high –throttling structures or close gates
Secondary sediment control

8. Example of a spate sediment excluding intake

9. Features of the “spate” intake
No divide wall, flows can approach from any direction including parallel to the weir
Intake aligned to minimise the diversion angle
Curved channel with floor set lower than the intake gate sill encourages coarser sediments to move through the sluiceway
In this case a fuse plug was used

10. Limitations of sediment excluding intakes in spate schemes
Spate intakes divert all the wadi flows except for the short periods, sometimes only minutes, during flood peaks when wadi flows exceed the intake capacity. Sediment exclusion only effective during these periods.
Sluice gates have to be operated in response to rapidly varying spate flows – mechanised gates desirable but not often affordable.
It is not unusual for farmers to block the sluice gate as they do not want to loose water – in some systems however the downstream farmers take their water from the sluice gate and this makes the sluice gate operated

11. Downstream area irrigated from scour sluice

12. Limiting the diversion of coarser sediments
Locate intakes at outside of bends
Sediment excluding intakes
(3) Limit diversion when wadi flows high –throttling structures or close gates
Secondary sediment control

13. Basic intake

14. Limit diversion from flood peaks
For simple un-gated intakes use flow throttling structures with a rejection spillway to limit the flows entering a canal.
For gated intakes consider closing canal gates during short periods of high flow. (There are problems of responding to rapidly varying flows, and farmers reluctance to “waste” water) Flow throttling structures with a rejection spillway are also used with gated intakes to ensure that canals are not damaged by excessive flows if the gates are left open during very large floods .

15. Limitation to throttling structures
May not be like by farmers – too much of the flow is lost
May attract trash and become clogged

16. Limiting the diversion of coarser sediments
Locate intakes at outside of bends
Sediment excluding intakes
Limit diversion when wadi flows high –throttling structures or close gates
(4) Secondary sediment control

17. Secondary sediment control
Settling basins
Canal sediment extractors

18. Wadi Mawr settling basins

19. Models are used design settling basins/gravel traps
Model predictions include:
Variation in sediment concentrations and grain sizes passing through a basin it fills with sediment.
Estimates of the frequency of sediment sluicing or de-silting operations.
The time period required to flush the basin and the volume of water needed for flushing.
The dimensions of an escape channel to convey sediment flushed from a basin to the river or disposal point.

20. Minimising trapping fine sediments
A disadvantage of settling basins in spate schemes is their high trap efficiency for fine sediments at low flows or when basins are empty.
To minimise the trap efficiency for fine sediments:
Basins should be relatively narrow, with sediment storage obtained by increasing the length, rather than the width or depth of the basin.
If it is considered necessary substantial reductions in the trap efficiency for fine sediments can be made if the tail water level in the basin is lowered for very low basin discharges. One possibility is to provide a notched weir at the basin exit, so that tail water levels are substantially lowered when the basin discharge is very low.

21. Secondary sediment control for spate schemes
Settling basins – Mechanically excavated or flushed basins can provide high sediment trap efficiencies with a low, or in the case of mechanically excavated basin, zero, “wastage” of water for sediment flushing. But sediment trap efficiency varies as a basin fills, and also with the basin discharge which varies from zero to full supply discharge in spate schemes.
Canal sediment extractors – Trap coarse sediment with a relatively constant trap efficiency but require continuous flushing flows of between 10% and 15 % of the canal discharge. Conventional extractors not suitable for use in spate schemes.

22. Limitations to secondary sedimentation control
Not easy to get it right – i.e. catching the coarse and not the fine sediment
Requires space, esp. if sediment loads are high – this space may not be there
Cleaning requires adequate organization
In case of flushing systems, farmers may object on water being used for this

23. Desilting a small basin

24. Based on work of
Philip Lawrence