TRENCH FILL REVETMENT
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1. CATEGORY

1.0 – River Training

2. DESIGN STATUS

Level II

3. ALSO KNOWN AS

Buried windrow revetment, riprap fill-trench, setback revetment.

4. DESCRIPTION

Trench fill revetments are constructed by excavating a trench along the top of the bank and placing stone riprap in the trench. As the bank erodes, the stone is undercut and "launches" down the bank line, resulting in a more gradual, protected slope. Earth removed for excavation of the trench may be used to cover the riprap, thus completely concealing it until it is launched (USACE, 1981).

5. PURPOSE

Trench fill revetments are installed to provide lateral stability to a channel by allowing natural erosive processes to form a gentle slope on the streambanks in reaches where some soil loss can be tolerated. The self launching stone provides a less intrusive technique for stabilization when compared to riprap installations on the entire bank, and eliminates the need for smoothing or flattening the slope.

6. PLANNING

Useful for Erosion Processes:
Toe erosion with upper bank failure
Scour of middle and upper banks by currents
Local scour
  Erosion of local lenses or layers of noncohesive sediment
  Erosion by overbank runoff
  General bed degradation
  Headcutting
  Piping
  Erosion by navigation waves
  Erosion by wind waves
  Erosion by ice and debris gouging
  General bank instability or susceptibility to mass slope failure

Spatial Application:
Instream
Toe
Midbank
Top of Bank

Hydrologic / Geomorphic Setting
Resistive
  Redirective
Continuous
  Discontinuous
Outer Bend
  Inner Bend
  Incision
Lateral Migration
  Aggradation

Conditions Where Practice Applies:

Trench fill revetments are placed along banks that are actively eroding, but where some additional bank loss can be tolerated. HEC-23 states that riprap fill-trench is effective in controlling lateral stream instability, but generally unsuitable for addressing local scour, contraction scour, or vertical stream instability. Controlling local scour at bridge abutments is listed as a possible secondary use. HEC-23 indicates that riprap fill trench is suitable for all types of river environments, and requires a moderate investment of resources for maintenance.

Trench Fill Revetments are often used where a smoothly aligned and stabilized channel is required, often for navigational purposes (Biedenharn, et. al., 1997). This is a good technique to use when construction within the stream channel is very difficult due to rapid erosion, high velocities, or other factors (Biedenharn, et. al., 1997).

Complexity:

Low.

Design Guidelines / Typical Drawings:

Trench-Fill Revetments should be constructed with well-graded, self-launching stone (USACE, 1981). Larger stone sizes will require thicker applications than smaller stones, to produce a revetment of the same relative thickness.

Shape of the stone toe is not critical. For trench-fill revetments, the height of the stone section is generally one-half to one times the length (Biedenharn, et. al., 1997).

Trench-Fill Revetment Typical Drawing

7. ENVIRONMENTAL CONSIDERATIONS / BENEFITS

Excavation of the trench requires disturbance of a corridor along the top bank, and therefore this measure is not recommended for sites where the top bank supports valuable riparian vegetation. Terrestrial habitat values of steep eroding banks where trench fill revetments are normally placed are usually improved, especially if the revetment formed by the launched stone and the top bank area disturbed by excavation is allowed to revegetate. Benthic aquatic habitat at the bank toe may be improved by the addition of stable substrate (Shields et al., 1995).

8. HYDRAULIC LOADING

Permissible shear and velocity for trench fill revetments is related to the size of rock used in construction. Other factors, such as the angularity of the stone, the thickness of the layers of stone, and the angle at which the faces of the stone structure are constructed also come into play. Detailed guidance for sizing stone for bed and bank stabilization structures is beyond the scope of this guideline, and many approaches are available (See Special Topic: Designing Stone Structures). However, the Maynord (1995) equation gives a D50 stone size for an angular stone riprap revetment of 0.875 m (2.9 ft) if the near-bank vertically-averaged velocity is 3.5 m/s (11.5 ft/s), and flow depth = 1 m (3.3 ft), and stone is placed on a bank slope of 1V:1.5H. Use of riprap larger than this is unusual.

9. COMBINATION OPPORTUNITIES

Stone is sometimes piled along the top bank in a linear ridge called a windrow revetment, instead of burying it in a trench.

10. ADVANTAGES

11. LIMITATIONS

12. MATERIALS AND EQUIPMENT

Stone size and application rates for demonstration sites along the Missouri River constructed in the late 1970s ranged from 10.4 to 17.9 t/m (3.5 to 6.0 T/ft) of bank protected. Stone sizes used for windrow revetments along larger rivers have included 90 and 180 kg (200-lb and 400-lb) maximum size gradations (Henderson and Shields, 1984).

13. CONSTRUCTION / INSTALLATION

Construction is usually conducted from the top of bank, and care should be exercised in operating heavy equipment at the top of steep banks (Keown, 1983). In addition, geotechnical analyses are recommended to examine the impact on bank slope stability of adding weight in the form of riprap fill. After erosion undermines the trench and stone begins to launch, stone may be added on an “as-needed” basis until the bank stabilizes. Alternatively, if the bank reaches a stable configuration without launching some of the stone, it may be excavated for use elsewhere. Site-specific conditions determine the amount of stone required to reach equilibrium.

14. COST

Construction costs for windrow revetment placed along the Missouri River ranged from $190 to $590 /m ($58 to $180/ft) of bank protected (1984 dollars) (Henderson and Shields, 1984). Costs per unit bank length of protected bank were slightly lower than those for other types of stone structures, such as reinforced revetment, composite revetment, hard points (short spurs), earth core dikes, and refusals (USACE, 1981).

15. MAINTENANCE / MONITORING

Trench fill revetments should be monitored following each significant storm event through the first season and then on an annual basis to determine whether the system is functioning properly. Rock may be added as needed once undermining has occurred.

16. COMMON REASONS / CIRCUMSTANCES FOR FAILURE

17. CASE STUDIES AND EXAMPLES

Red River, Louisiana. Almost the entire foreshore has eroded and the river is ready to undercut some of the stone.  Note the triangular section of stone at the toe. This is the amount of stone (plus a factor of safety) available to launch into the scour hole when the river undercuts some of this stone.

(from Workshop Notes, David Derrick, USACE)

Red River, Louisiana. Trench-Fill Revetment following construction. The river will erode the foreshore and then move against the trench fill and will undermine and launch some of the toe stone.

(from Workshop Notes, David Derrick, USACE)

18. RESEARCH OPPORTUNITIES

None Identified

19. REFERENCES

Biedenharn, D. S., Elliott, C. M., & Watson, C. C.  (1997).  The WES Stream Investigation and Streambank Stabilization Handbook.  US Army Engineer Waterways Experiment Station, Vicksburg, Mississippi. (pdf)

Henderson, J. E. and Shields, F. D., Jr. 1984. Environmental features for bank protection projects. Technical Report E-84-11, U. S. Army Engineer Waterways Experiment Station, Vicksburg, MS, 150 pp.

Keown, M. P. 1983. Streambank protection guidelines for landowners and local governments. U. S. Army Engineer Waterways Experiment Station, Vicksburg, Miss., 60 pp.

Lagasse, P. F., Byars, M. S., Zevenbergen, L. W. and Clopper, P. E. 1997. Bridge scour and stream instability countermeasures: Experience, selection and design guidance. Hydraulic Engineering Circular No. 23, FHWA HI 97-030, Washington, D. C., pp. 1.3-1.11. (pdf)

Shields, F. D., Jr., Cooper, C. M., and Testa, S. 1995. Towards greener riprap: environmental considerations from micro- to macroscale. In C. R. Thorne, S. R. Abt, F. B. J. Barends, S. T. Maynord, and K W. Pilarczyk. (eds.). River, coastal and shoreline protection: erosion control using riprap and armourstone. John Wiley & Sons, Ltd., Chichester, U. K., 557-574.

U. S. Army Corps of Engineers (USACE). 1981. Final Report to Congress, The Streambank Erosion Control Evaluation and Demonstration Act of 1974, Section 32, Public Law 93-251. Main Report. Washington, D. C.