September-October 2000

Interview: Streambank Solutions

Edward Perry, Ph.D., speaks on hard-armoring techniques and bioengineering.

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By Janice Kaspersen

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EC: Realistically speaking, what are your options under extreme conditions when maximum performance is required?

Perry: Plain grass and reinforced grass (grass within geogrid or concrete block) have been used for erosion control ditches and waterways, and limiting velocity versus flow-duration information is available. Grass is not recommended for use if the flow duration is longer than about two days. While the maximum sustainable design velocity for more conventional hard materials, such as rock revetment, concrete bulkheads, and gabions, is generally known from hydraulic model studies, failure thresholds and performance behavior for bioengineering materials, such as woody species, has only recently been addressed. Maximum flow velocities should not exceed 3 fps for herbaceous plantings, 3-5 fps for woody and herbaceous mixed plantings, and 5-8 fps for woody plantings alone. Maximum flows above 8 fps require a more substantial bioengineering treatment such as coir fiber or geotextile roll, brush mattress, and wattling. The larger the stream or the stronger the flow, the more probable that hard materials will be incorporated into the bioengineering design. This is also true when an expensive or critical facility is being threatened. The "hard material" may be a log crib or a structure incorporating rock.

EC: How effectively can techniques be combined?

Perry: Combining hard and soft armoring is the key to their success. This is particularly useful in the toe and splash zones of the streambank. Hard structures are used to protect the toe of the streambank and the upstream and downstream ends of the armoring to prevent flanking. Toe protection can also be achieved by deflector dikes (hard points, groins, bendway weirs, and stream barbs) that protrude into the water, deflect the current away from the eroded bank, and induce sedimentation. These dikes may be composed of rock, vegetation, or a combination of both.

Some special consideration is necessary during the design phase of a project combining hard and soft armoring. Some lead time is required because plants for bioengineering are acquired by purchasing, collecting from the wild, or propagating and growing. Timing of planting is critical for bioengineering. Planting during hot summer months should be avoided. Planting during the dormant season prior to flood events to permit establishment of roots, especially for herbaceous plants, is preferred.

Monitoring and aftercare of a bioengineering treatment up to and after the first one or two flood events is essential. Following repair of weak spots, the bioengineering treatment will gain strength with time as the vegetation becomes established.

EC: How do the costs of hard-armor solutions compare to those of "softer" solutions in terms of planning, materials, and labor?

Perry: Bioengineering has a steeper learning curve than conventional hard-armor methods because it has recently come to the forefront as the method of choice and there are a limited number of people trained in the discipline. The success of bioengineering in streambank protection in the US is due in a large part to pioneering efforts of Robbin Sotir (www.sotir.com). Given the design guidance now available, the planning costs of bioengineering and conventional hard armor should be about the same.

Material and labor costs for bioengineering and conventional hard armoring vary tremendously depending on availability of materials, hauling distances, labor rates for the geographic area, and other factors. A common denominator for arriving at costs is labor in terms of person hours required to install the particular treatment. Then material costs, equipment rental, and so on are added onto this. In general, since bioengineering streambank protection is labor-intensive, the cost advantage will be greatest in regions where labor is inexpensive, skilled in agriculture, and conscientious.

EC: Describe a specific streambank stabilization project. What options were considered, and how did they compare?

Perry: This project is discussed in Allen and Leech's Bioengineering for Streambank Erosion Control. It compares the actual costs of bioengineering treatments with the estimated costs of traditional erosion control - in this case, riprap revetment - under similar conditions in the same areas. The table shows comparisons for two cases, Court Creek in Illinois and the Upper Truckee River in California.

Location and ConditionsTypes of TreatmentCosts , $/lin. ft.
Court Creek, IL
10-ft. bank height
3-fps local velocity
1V:1H graded sideslope
Dormant post and rock toe $15 (actual)

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10-ft. bank height
1V:2H sideslope
1.5-ft. rock thickness
0.5-ft. bedding material
$40/ton delivered and placed

Riprap revetment$60 (est.)
Upper Truckee River, CA
6-ft. bank height
4-fps local velocity
Vegetative geogrid $104 (actual)
8-ft. bank height
1V:2H sideslope
$20/ton delivered and placed
Riprap revetment $27 (est.)

What is not shown in the Upper Truckee River example is that the site is next to a golf course and the sponsor is trying to provide shaded riverine aquatic (SRA) habitat for native brown trout. The vegetative geogrid will provide SRA by providing willows that overhang the bank. The riprap revetment requires a flatter slope and uses more valuable golf course land. Thus, the project objectives and potential benefits and impacts must be considered when comparing various streambank-protection options. And this doesn't even take into consideration the damage Tiger Woods could do to his Titleist Titanium 975 driver in the unlikely event that his golf ball ever landed in the riprap revetment!

Author's Bio: Janice Kaspersen is the editor of Erosion Control magazine.

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