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Authors:
Tim Lancaster, North American
Green, Inc., Don Lutyens, American Excelsior Company, and Deron
Austin, Synthetic Industries
 
In the last several years many areas
of the U.S. have been drastically affected by torrential rainfalls
and flooding. Although most of
these "natural" disasters are indeed caused by nature,
mans impact on the environment and land use has magnified
the destructive forces and the resulting damages. A major contributor
to the flooding problems, which seem to occur all too often, is
the "hardening" of our natural landscapes. The replacement
of forests and fields with impervious sidewalks, streets, parking
lots and roofs has resulted in increased run-off volumes which
exceed the capacity of our existing drainage systems.
Ironically, even mans own attempts to manage storm water
and control erosion have added to the problem. The use of "hard
armor" materials such as rock riprap, concrete and asphalt
to line and stabilize drainage channels inhibits water infiltration,
reduces filtration of sediment and other potential pollutants,
and increases run-off volumes. The result - more polluted water
feeding into our over-burdened streams and reservoirs at a faster
pace. In addition to adverse environmental effects, hard armor
erosion control materials pose other concerns, prompting todays
engineers and designers to employ more natural, vegetative solutions.
To extend the erosion resistance capabilities of vegetative "soft
armor" channel linings, modern geosynthetic turf reinforcement
mattings (TRMs) are widely used for immediate erosion protection
and long-term vegetative reinforcement. This article will explore
the use of geosynthetically reinforced vegetation for permanent
channel stabilization and its many benefits over one of the most
commonly used types of "hard armor" protection, rock
riprap.
Engineering Performance
"Hard armor" materials such as rock riprap were once thought to be the only suitable
lining systems for channels exposed to high water flows. Vegetative channel linings
were simply out of the question where expected flow velocities exceeded 8 feet
per second (ft/s) (Chow, 1959) or shear stresses topped the 3.7 pounds per square
foot (lbs/sf) mark (Chen and Cotton, 1988). Since their first use in 1979, TRMs
have proven their ability to substantially increase the erosion resistance of
natural vegetation. Two independent channel lining studies performed by CIRIA
(Hewlett, etal, 1987) and the Texas Department of Transportation (Northcutt,
1997), suggest that some types of TRMs can more than double the erosion resistance
of vegetation, enabling its use in channels where velocities exceed 15 ft/s and
when shear stresses reach 8 lbs/sf. Compared to the Federal Highway Administrations
recommendations for rock riprap, this level of protection is equivalent to that
of 24 inch (d50) stone (Chen and Cotton, 1988). This revelation is to the delight
of many designers who appreciate the lower cost, lower maintenance, safety and
environmental benefits of "soft armor" vegetative linings.
Aesthetics
In the past, aesthetics
was not considered by engineers an important factor in erosion
control materials selection. Today, as the urban sprawl lays a
maze of paved roads, sidewalks and parking lots, "greenways" have become
scarce. This loss of green space, in conjunction with heightened public environmental
awareness and the ever increasing demands of owners, has engineers re-thinking
the aesthetic aspects of materials used to stabilize drainage channels. On
urban projects, these areas may offer the only opportunity to provide a natural
setting within an otherwise grey, manmade landscape. Though rock is a completely
natural material, its associated with and causes the same "hardening" effect
as manmade pavements such as concrete or asphalt. Hence, the use of vegetation
to soften and naturalize the appearance of drainage channels is becoming
the preferred method.
Wildlife Habitat
Vegetation
not only improves aesthetics, vegetative channel linings function
as living components in the surrounding ecosystem.
Grasses and flowers can
provide food and habitat to draw and support preferred wildlife species.
Though rock riprap may provide improved fish habitat when used in perennial
streambeds, when used in intermittent drainage channels, it often harbors
undesirable species such as mosquitoes, snakes and rodents.
Clean Water
Vegetative channel
linings are also efficient at trapping and filtering sediment and
pollutants in storm water. In recent research conducted
on three different
types of vegetation with varying densities and heights, in-stream vegetative
stands increased sedimentation from 200 to 700 % versus unvegetated stream
beds, with up to 81 % retention of the trapped sediments following clean
water flush events (Abt et.al., 1995). Plants, along with microorganisms
within the soil, can metabolize and convert many pollutants often carried
by sediments into non-harmful compounds. Though rock riprap linings will
also capture some sediment, rock has no way of "neutralizing" these pollutants.
The sediment and its attached pollutants trapped during one storm event will
often be washed out of the rocks and carried downstream during the next.
Noise Abatement
Furthermore,
vegetation offers an absorptive buffer for noise. This can be
quite beneficial in channels along highways through
heavily populated areas
where noise pollution is a problem. Rock linings have little capacity
for sound absorption.
Maintenance
At first thought,
one might expect riprap to require less maintenance than vegetation.
Just after it's installed, rock has a nice,
neat appearance.
But what happens a year or two down the road? Water- or wind-carried
seeds (often from weeds) deposit in the void spaces between rocks,
resulting
in an unattractive combination of rocks and weeds. Since
rock cannot be safely
mowed over with riding equipment, maintenance must be performed with
weed-eaters or pesticide sprayers to eliminate weed growth. Furthermore,
the voids
in a rock lining not only harbor weeds, they also collect
debris and litter.
Pulling litter out of rock linings can be a very laborious and even dangerous
task for maintenance crews. Other potential costs and/or hazards associated
rock riprap linings, include: increased maintenance time due to
use of extreme care when mowing around the rock; excessive
wear and tear on machinery from accidentally hitting rocks with
mower blades; lost work days from employees due to injury from
flying debris; damage to personal property from flying rocks and
debris; and possible law suits from injury and vehicle damage.
On the other hand, vegetative
channel linings can typically be maintained simply by mowing to
the preferred height
using conventional riding equipment. In a well manicured setting,
this may require frequent mowings and occasional fertilizer applications.
However, in many situations where native grasses or low maintenance
species are used, mowing and fertilization may only be necessary
once a year. In regards to litter removal, hand collection can
be done safely, and the use of a power rake where litter is heavy
can simplify the task.
Safety
The potential hazards
of rock riprap go beyond those associated with maintenance activities.
If the channel is in a residential
or public area, riprap poses
a risk for children and pedestrians who may trip and fall when playing
on or walking across the jagged surface. Along roadsides,
riprap linings are
an obstacle to vehicles that stray from the pavement, causing reduced
control of the vehicle and possibly more severe damage to the car
and its passengers. Vandalism
When
riprap is installed, the only thing holding it in place is the
weight of the rock itself. Though its weight may be sufficient
to resist movement
under high velocity water flow, it can be helpless against the most damaging
force known to man - the little boy next door. A report from the field tells
the story. The use of detention basins around subdivisions is a typical approach
to water and sediment management. In one state, the most commonly used lining
for the out-fall channels from the basins is rock riprap. Inspections in
the spring by Department of Natural Resources officials after installation
of many of these channels the previous autumn revealed a puzzling loss of
rock from the channel surfaces. Knowing that the rock didn't wash away, state
inspectors conducted an investigation. What they found out was, the rocks "walked" away
over winter, carried by neighborhood children up to the detention basin and
thrown onto the frozen surface of the detention basin to try to break the
ice.
Materials Installation
The benefits of vegetative
linings are realized even before they are in place. Installation
of rock riprap typically requires excavation of a bed at least
twice as deep as the mean diameter stone, lining the bed with a geotextile,
and placement of two or more layers of stone in the bed. This entire process,
aside from geotextile installation, requires heavy equipment. From dump trucks
hauling loads of rock to the site to backhoes excavating the beds and placing
the rock, each step is a time consuming, expensive task. [With just a
little more effort it takes to hand place the geotextile under riprap, a
TRM can be installed.] (note: use this statement also in a box)
No excavation, heavy equipment, or skilled equipment operators are required.
The area is simply raked to form a seedbed and treated with seed and any
necessary soil amendments. The TRMs are rolled out over the treated area
and secured in place with relatively small trenches, stakes and/or staples,
and in some cases top-dressed with a fine layer of soil and more seed. Fig.
1) Proper installation of rock riprap requires an expensive, time-consuming
three step process with heavy equipment. Installation becomes more
labor intensive and potentially hazardous when gabion baskets,
installed by hand, must be used to encapsulate the rock.
Cost Effectiveness
Putting all other benefits
aside, the first consideration in erosion control materials selection
must be cost-effectiveness. For channel lining applications,
many engineers have adopted the design procedures presented by the
Federal Highway Administration (FHWA) in the most recent HEC
#15 manual (Chen and
Cotton, 1988). This design methodology utilizes maximum shear stress
calculations in determining the suitability of various lining
materials. However, at the
time the HEC #15 was developed, little was known about the vegetative
reinforcement properties of geosynthetic mattings. Furthermore,
this design methodology
lacks the cost information needed to determine the most cost-effective
lining. Fig.
2) Both 12 inch riprap (foreground) and
a turf reinforcement matting (downstream section) were installed
in this channel in September.
Following heavy winter rains, the rock portion shows signs of erosion.
In comparison, the TRM downstream has worked with early vegetation
growth to prevent scouring of the channel surface.
The following Tables 1. and 2. present up-to-date permissible
shear stresses for one type of TRM and hard armor material, along
with approximate installed costs for the Indianapolis, Indiana
area (Lancaster and Spangler, 1996).
Table 1. Comparison of Performance Limits and Unit Cost
Material Type |
Permissible Shear Stress (lbs/sf) |
Installed Cost($/sy)* |
8" Riprap |
2.671 |
25.00
|
TRM (unvegetated) |
3.202 |
7.00 |
18" Riprap |
6.001 |
35.00 |
TRM (partially vegetated) |
6.003 |
7.00 |
24" Riprap |
8.001 |
45.00 |
TRM (vegetated) |
8.004 |
7.00 |
* Costs may vary considerably for different regions and types
of TRMs
1 Based on FHWA HEC #15 Recommendations for double layered rock
lining (size = d50)
2 Based on laboratory flume testing with a commercial TRM on bare
soil (failure @ .5 inches soil loss)
3 Extrapolated from laboratory flume testing
4 Based on laboratory flume testing and outdoor channel testing
at the Texas Transportation Institute (failure @ .3 inches soil
loss)
This information can be used in general
to complement HEC #15 design procedures. These figures suggest
that certain turf reinforcement
mattings can provide similar protection, even before vegetation
growth, as 8 inch rock riprap, at less than 1/3 the cost. Once
vegetation begins to establish through the matting, the degree
of protection increases to that of 18 inch rock, at 1/5 of the
cost. Once vegetation becomes fully established, it has similar
erosion resistance as 24 inch riprap, at 1/6 the cost!
To see how this affects overall project costs, let's consider
linings for two small channels where calculated shear stresses
exceed the limits of unreinforced vegetation.
Table 2. Comparison of Installed Costs (12 ft x 750 ft channels
(1,000 sys))
| Calculated Shear Stress
(lbs/sf) |
|
Total Installed Cost |
| |
2 yr storm |
100 yr storm |
Lining Option |
(U.S. Dollars)
|
| Channel "A" |
2.5 |
6.0 |
TRM |
$ 7,000 |
| |
|
|
18 inch riprap |
$ 35,000 |
| Channel "B" |
3.0 |
8.0 |
TRM |
$ 7,000 |
| |
|
|
24 inch riprap |
$ 45,000 |
Based on these
applications, using a TRM to control erosion and reinforce vegetation
in place of rock would
save $ 28,000 - $ 38,000. This money could be put into the owner's
pocket, or used by the engineer to address other areas which may
have been disregarded due to a limited budget.
Fig
3) Like electricity, water follows the path of least resistance.
The roughness of rock can create problems for improperly placed
linings. Here, water has eroded around a rock-lined chute. Weed
growth in the rock poses further headaches for highway maintenance
crews.
Conclusions
Geosynthetically reinforced vegetation
can provide a lower cost, lower maintenance, less hazardous and
more aesthetically and
environmentally pleasing alternative
to riprap in areas requiring high performance erosion protection (see Table
3.). However, the vegetation and its stand characteristics, along with the
erodibility of the soil, will significantly affect the erosion resistance
of this type of system. Further analysis through the United States Department
of Agriculture design procedures for "Grass-Lined Open Channels" (Ag Handbook
#667) (Temple, etal, 1987) can assist in evaluating different vegetative
stands and soil types. Areas where vegetation is difficult to establish and
maintain as a dense, healthy stand may necessitate hard armor protection.
Table 3. Summary of Lining System Features
|
Feature |
TRM Reinforced Vegetation |
Rock Riprap |
|
Permissible Shear Stress |
8.00 lbs/sf (fully vegetated) |
8.00 lbs/sf (24 in rock) |
|
Aesthetics (color) |
Natural Green |
Grey |
|
Wildlife Attraction |
Desirable Species |
Pests |
|
Water Filtration/Treatment |
Excellent |
Poor |
|
Noise Abatement |
Yes |
No |
|
Maintenance |
Low - Medium |
Low - High |
|
Hazard Risk |
None |
Low - High |
|
Risk of Vandalism |
None - Low |
Low - High |
|
Installation Labor Requirements |
Unskilled |
Skilled |
|
Installation Equipment |
Hand tools |
Dump truck / backhoe |
|
Installation Time |
Fast (50 - 100 sys/man/hr) |
Slow (< 50 sys/hr) |
|
Material Delivery |
Lightweight Rolls |
Heavy truckloads |
|
Installed Cost |
$ 5.00 - $ 13.00 / sy |
$ 20.00 - $ 45.00 / sy |
References
Abt, S.R., Clary, W.P., Thornton,
C.I., 1995. "Sediment
Entrapment Potential of Submerged Stream Channel Vegetation",
Proceedings of the International Erosion Control Associations
26th Annual Conference, Feb. 28th March
3rd, Atlanta, GA, pp. 409 420.
Chen, Y.H, and G.K. Cotton. 1988. Design of Roadside Channels
with Flexible Linings. Federal Highway Administration,
HEC #15. National Technical Information Service, Springfield,
VA. 124 pgs.
Chow, V.T. 1959. Open Channel Hydraulics. McGraw-Hill
Book Company, New York, New York. p. 185.
Hewlett, H.W.M., etal. 1987. Design of Reinforced Grass Waterways.
Construction Industry Research and Information Association (CIRIA)
Report 116. Ciria, 6 Storey's Gate, London, England. 116 pgs.
Lancaster, T., and E. Spangler. 1996. "Soft Armor vs. Hard Armor
Channel Linings: A Cost Effective Analysis". Erosion Discussion
Newsletter, North American Green, Inc.
Northcutt, P. 1997. TXDOT/TTI Hydraulics
and Erosion Control Laboratory Field Performance Testing
of Selected Erosion Control
Products, Final Performance Analysis - 1995-96 Evaluation Cycle,
Class 1 - "Slope Protection", Class 2 - "Flexible Channel Liners".
Texas Department of Transportation Construction & Maintenance
Division. 177 pgs.
Temple, D.M., etal. 1987. Stability Design of Grass-Lined
Open Channels. U.S. Department of Agriculture, Agricultural
Handbook 667. 175 pgs.
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