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As
siting or expanding landfills becomes increasingly difficult,
you might consider the use of mechanically stabilized
earth walls for adding airspace.
By
Thomas M. Yanoschak
Mechanically
stabilized earth (MSE) walls offer engineers the ability
to construct near-vertical earthen walls, reducing the
amount of land required for embankment construction.
Whereas a typical unreinforced soil might be able to
achieve maximum stable slopes of between 3:1 (H:V) and
2:1, or 18.4° through 26.6°, the use of soil
reinforcement allows construction of slopes of 1:3 (71.6°)
and even 1:6 (80.5°). The allowable slope of a
reinforced embankment is determined by the quantity
and placement of reinforcing elements and also the type
of facing selected for the wall.
Example:
Solid Waste Application
| Figure
1. Plan View and Cross-Section of a Hypothetical
Landfill at Capacity |
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| Figure
2. Possible MSE Wall Configuration |
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| Figure
3. Alternate MSE Wall Design |
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Figures 1
through 3 illustrate how incorporation of an MSE wall
can increase the waste-disposal capacity of an existing
landfill without significantly increasing its footprint.
Figure 1
shows a plan view and a cross-section of a hypothetical
landfill that has reached capacity. The sideslopes of
the 1,000- x 1,000-ft. landfill are 3:1 (18.4°)
with a height of 143 ft. The fill is bordered by a 55-ft.-wide
perimeter berm (crest width of 25 ft., sideslope width
of 30 ft.). The gross volume of the landfill is approximately
2.4 million yd.3
Figure 2
shows a possible MSE wall configuration in which the
outer toe of the perimeter berm is kept constant but
soil reinforcement is used to increase the outer slope
of the perimeter berm from 3:1 (18.4°) to 1:3 (71.6°).
An MSE wall with a height of approximately 18 ft. will
maintain the crest width of the perimeter berm at 25
ft. but allow a continuation of the interior sideslope
of the berm that would be lined to provide an additional
17 ft. of disposal depth throughout the landfill. In
this example, approximately 700,000 yd.3
(29%) of additional volume is gained.
Figure 3
is an alternate MSE wall design in which the edge of
the waste is kept constant in order to meet minimum
buffer requirements for the landfill or to avoid regulatory
requirements for a lateral expansion. The MSE wall with
a 1:3 (71.6°) outer slope and extending 30 ft.
above the existing perimeter berm maintains the 25-ft.
crest width and the current limit of waste. Although
this design requires a wedge of structural fill within
the limits of waste, it allows an additional 30 ft.
of disposal depth, resulting in approximately 1,070,000
yd.3 (45%) of added volume after subtraction
of the structural wedge volume.
MSE Wall
Design
While metal
strips and high-strength polyester geotextiles have
been used in MSE soil reinforcement, by far geogridsa
geosynthetic material consisting of connected parallel
sets of tensile ribs with apertures of sufficient size
to allow strike-through of surrounding soil, stone,
or other geotechnical materialare in common use
today. Geogrids can be uniaxial or biaxial, depending
on the orientation of the load-carrying ribs, and either
flexible or rigid, depending on the method of manufacture.
Uniaxial geogrids are designed to carry tensile loads
along one principal direction, while biaxial geogrids
are designed to carry tensile loads in two principal
directions located 90° apart.
Biaxial geogrids
are used for wrapping the face of the MSE wall and as
secondary reinforcement near the face since they are
more capable of resisting shallow, multidirectional-type
failures that might occur near the face. Biaxial geogrids
are also used in soft-soil conditions where additional
bearing capacity is desired, such as beneath structures
or roadways located over soft soils.
Rigid geogrids
are manufactured from sheet plastic, usually high-density
polyethylene for uniaxial geogrids and polypropylene
for biaxial geogrids. The geogrid is formed by punching
holes in the sheet and cold-stretching (post-tensioning)
the sheet in the direction of strength. Uniaxial geogrids
are therefore stretched in one direction, while biaxial
geogrids are stretched in two.
Flexible
geogrids are made of high-tenacity polyester yarns sprayed
with a protective coating, such as latex or polyethylene,
to facilitate handling and to avoid ultraviolet and
chemical degradation of the polyester yarns.
Probably
the most important design property of a geogrid, and
possibly the most confusing, is its strength. Strength
values are often given in the machine direction
and crossmachine direction and usually
represent minimum average roll values. The machine
direction of the geogrid typically exhibits the greater
strength.
Geogrid product
literature often lists the wide-width strip tensile
strength of the product as determined by ASTM D4595
(ASTM, 1994), also known as the ultimate tensile strength
(Tult). This value, however, should never
be used directly in the design of long-lasting structures,
such as MSE walls forming a perimeter berm around a
landfill, that will have to remain in place for many
years. The wide-width value should be reduced by factors
that account for creep deformation, installation damage,
and chemical/biological degradation. This reduced-strength
value is termed the long-term design strength (LTDS)
and can typically equal half of the wide-width strength.
The Geosynthetic
Research Institute (GRI) has developed a methodology
for determining LTDS for geogrids. This methodology,
known as GRI-GG4, has been adapted for rigid geogrids
(GRI-GG4a) (GRI, 1993a) and flexible geogrids (GRI-GG4b)
(GRI, 1993b). The LTDS for flexible geogrids is calculated
as follows:
LTDS = Tult
[1/FSID x FSCR x FSCD
x FSBD x FSJNT]
where
FSID = partial factor of safety for installation
damage,
FSCR
= partial factor of safety for creep deformation,
FSCD
= partial factor of safety for chemical degradation,
FSBD
= partial factor of safety for biological degradation,
and
FSJNT
= partial factor of safety for joints (seams and connections).
FSID
accounts for damage that can occur to the geogrid
during transportation, installation, equipment traffic,
fill placement, and fill compaction. Values can be obtained
by comparing the before- and after-installation tensile
strengths of exhumed samples. Values, however, are dependent
on backfill type and installation conditions.
FSCR
is determined from a standardized tension creep test
and is a measure of the highest load the geogrid can
sustain without exceeding 10% strain over 100 years.
FSCD
accounts for degradation of the geogrid due to chemical
exposure, ultraviolet exposure, and hydrolysis effects
on polyester.
FSBD
is a means by which the effects of bacterial and fungal
resistance can be taken into account. This value is
usually 1.0 for most geogrids, indicating no reduction
in strength, due to the inherent resistance of the geogrid
materials or coatings to biological activity.
FSJNT
allows reductions in strength due to the seaming or
joining of geogrid layers to be accounted for in the
LTDS calculation. Most MSE wall designs require that
a primary reinforcement layer of geogrid be installed
perpendicular to the wall from a single roll without
joints or seams. In this case, FSJNT would
be 1.0.
The methodology
for calculating the LTDS for rigid geogrids is similar
to that used for flexible geogrids, except for the addition
of a partial factor of safety for junction strength
of the geogrid, FSJNT, in the denominator
of the equation.
Most geogrid
manufacturers have performed testing on their products
to determine suitable values for the above reduction
factors. Manufacturers recommendations for these
values should be used in the design, provided that the
MSE wall will not experience any unusually harsh conditions
during installation or the life of the wall. Harsh conditions
might warrant project-specific testing.
The tensile
modulus of a geogrid is also an important strength property
in design of MSE walls. High-tensile moduli are desirable
since they allow development of high-tensile strengths
at low deformations. The design strength of geogrids
should be adjusted to ensure that deformations produced
at the anticipated stresses do not lead to excessive
deformation that could jeopardize the stability of the
wall or affect aesthetics. Design based on the LTDS
typically yields acceptable deformations, although this
should be checked on a case-by-case basis.
The tensile
forces developed within an MSE wall are transferred
from the soil to the geogrid by the frictional resistance
and bearing stresses developed between the geogrid and
the soil. The amount of stress transferred to the geogrid
is dependent on the geogrids geometric structure
and the surrounding soil properties. The amount of embedment
length of the geogrid beyond the potential failure surface
is affected by the ability of the geogrid to interlock
with the surrounding soil.
Stress transfer
between geogrids and backfill soils can be evaluated
in the laboratory using pullout tests. Generally, granular
backfill soils exhibit greater stress transfer and therefore
are preferred for MSE wall construction. The cohesive
component of shear stress, such as in clayey soils,
is often ignored in MSE wall design in order to include
an additional factor of safety in the calculations.
Many other
properties are reported by geogrid manufacturers in
their product specifications. Although these properties
are important to ensure product conformance with specified
values, they are generally not used directly in wall
design, unlike the strength and geogrid-soil interaction
properties previously described. These properties may
include rib/strand count, aperture size, open area,
thickness, weight, carbon black content, flexural rigidity,
junction strength, and junction efficiency.
MSE Wall
Stability
Whether a
geogrid is uniaxial, biaxial, rigid, or flexible, it
develops tensile stresses within the MSE wall in essentially
the same manner. A pullout force is exerted on the geogrid
as a result of the steepened face of the MSE wall that
would otherwise fail if the geogrid were not present.
This pullout force is transferred to the geogrid by
means of the frictional resistance between the geogrid
and the soil on both the upper and lower surfaces of
the longitudinal and transverse ribs and by means of
bearing resistance against the front surface of the
transverse ribs. To counteract the pullout force, resisting
forces are developed within the geogrid in the same
manner as the pullout forces, except that they act in
the opposite direction. For a stable condition to exist,
resisting forces must exceed pullout forces.
The wedge
of soil that would otherwise move outward is held in
place by the geogrid. The length of geogrid located
between the face of the wall and the failure plane,
designated as pullout length, is where the pullout
tensile stress (TP) is developed within the geogrid.
To keep the unstable wedge of soil from moving outward,
an equal or greater resisting tensile stress (TR) must
be developed within the stable soil mass within the
resisting length of the geogrid. If TR<TP, then
the geogrid embedded in the stable soil will pull out
and the wall will fail.
Another important
concept is that the pullout and resisting stresses developed
within the geogrid must not exceed the tensile strength
of the geogrid. If this were to occur, the geogrid would
either excessively deform or break and the wall would
fail.
Actual MSE
wall designs will often have several geogrid layers
of varying length, tensile strength, and vertical spacing.
This complexity in design is necessary to account for
many different types of failure planes that can develop
behind the wall. A geogrid designed to resist failure
along a particular failure plane might not be adequate
to resist failure along a different, but equally probable,
failure plane. To ensure that all potential failure
planes are addressed, designers use iterative slope-stability
programs, such as STABGR (Duncan and Wong, 1984), that
can evaluate numerous failure planes quickly. Some geogrid
manufacturers also produce proprietary software for
MSE wall analysis, such as StrataWall by Strata Systems
Inc. The designer adjusts the geogrid strength, spacing,
and length until an acceptable minimum factor of safety
against failure is achieved, typically 1.5 for static
conditions and 1.0 for dynamic and seismic conditions.
Failures
can be classified as either internal or external, depending
on whether or not the failure extends through the reinforced
soil mass. The wall designer, often the geogrid manufacturer,
is responsible for ensuring internal stability, while
the landfill design engineer is responsible for ensuring
external stability. Table 1 lists several factors that
affect the internal and external stability of MSE walls.
| Table
1. Factors Affecting MSE Wall Stability |
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Internal
Stability
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Length
and spacing of geogrid
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Adjust
as necessary
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Strength
of geogrid
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Adjust
as necessary
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Frictional
resistance between soil and geogrid
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High
values lead to more efficient designs
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Soil
type
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Granular,
free-draining soil is best
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Dynamic,
seismic, and surcharge loads
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Design
accordingly
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Wall
facing type
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Ensure
appropriate for slope and climate
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Wall
maintenance
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Remove
large, deep-rooted vegetation; maintain small,
shallow-rooted vegetation; monitor for proper
drainage
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External
Stability
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Drainage
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Install
free-draining soil or perforated drainage pipes
behind wall
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Width
of MSE wall
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Increase
width if global stability is a problem
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Soil
and waste type behind wall
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Ensure
accurate properties are used in stability analyses
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Dynamic,
seismic, and surcharge loads
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Design
accordingly
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Foundation
soils
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Undercut
unsuitable soils
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Slopes
behind walls
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Steeper
slopes generally require more reinforcement
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Setback
of slopes behind walls
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Smaller
setbacks generally require more reinforcement
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Water
table
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High
water tables reduce external stability
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Facing
Options
By far, the
MSE wall-facing option used most often in solid waste
applications involves extending the biaxial geogrid
layers beyond the edge of the wall and wrapping them
over the layer of soil that is placed over the geogrid.
Welded wire forms are used to ensure that the layer
is constructed at the proper setback from the previous
layer and to aid in the placement of geosynthetics.
Secondary biaxial geogrid is then rolled out parallel
to the wall face, such that a portion of the geogrid
overhangs the welded wire forms. Erosion control matting
is placed over the biaxial geogrid for soil retention.
The next lift of soil is placed and compacted over the
biaxial geogrid and erosion control matting to the top
of the welded wire forms, and the free end of the geogrid
is wrapped over the top of the soil lift. The facing
materials are structurally tied into the wall by the
primary uniaxial geogrid layers that are extended to
the wall face. The process is repeated for each subsequent
lift of soil.
The advantages
of the facing option include its low cost when compared
with the precast concrete panel and decorative block
options and its ability to be hydroseeded to support
vegetative growth. Another advantage of this design
is its ability to absorb the wall movements previously
described without noticeable cracking. The primary disadvantage
is the need for periodic maintenance to remove large,
deep-rooted vegetation that could distort or damage
the facing components and primary geogrids.
Economic
Analysis
Table 2 lists
some of the factors that must be evaluated when determining
the economic feasibility of an MSE wall.
The cost
of MSE walls increases exponentially with height because
of increased geogrid lengths, decreasing spacings at
the base of the wall, and increased fill volumes. Accurate
cost estimating requires input from consultants, geogrid
manufacturers, and contractors who are experienced in
MSE wall applications. Construction costs should include
land, material, installation, contractor markup, and
bonding costs, as well as a contingency. The cost of
making modifications to the existing landfill components
should also be evaluated. In situations where additional
waste will be placed over a previously placed final
cover, the cost of removing the final cover should be
accounted for.
Construction
quality-assurance requirements for MSE wall construction
typically include observations and testing for proper
excavation to suitable soils, proper placement of backfill
to prevent damage to geogrids, adequate compaction of
backfill, soil properties, strength of geogrids, placement
of geogrids, and facing installation.
Operational
factors that should be included in an MSE cost analysis
include additional maintenance requirements, such as
the periodic removal of unsuitable vegetation from the
face, periodic inspections for wall integrity, and additional
leachate pumping costs. The MSE wall will also limit
access to the landfill. Traffic will most likely be
required to enter and exit the landfill from one or
more permanent ramps built into the design or from locations
where the MSE wall does not exist. Operational difficulties
resulting from narrow working faces and the necessity
for long and frequently changing haul roads should be
evaluated.
A potential
disadvantage is that once an MSE wall is in place, future
lateral expansions become impractical. Retrofitting
a wall to provide gravity drainage and lining the steep
outer slopes of the wall present serious obstacles.
Closure and postclosure costs that should be evaluated
include final-cover construction costs and maintenance
costs. Placing only 20 or 30 ft. of waste over a slope
that has already received final cover might not be cost-effective.
| Table
2. Factors Affecting MSE Wall Costs |
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Preconstruction
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Conceptual
design
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Cost
estimating
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Permitting
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Construction
drawings and bid documents
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Bidding
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Construction
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Geogrid
type and placement
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Structural
fill type and availability
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Facing
option
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Additional
liner requirements
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Additional
land purchase
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Loss
of existing final cover
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Sump
modifications
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Gas
system modifications
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Stormwater
system modifications
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Construction
quality assurance
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Operational
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Additional
maintenance requirements
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Constraints
on accessibility
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Lost
expansion opportunity
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Closure/Postclosure
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Additional
final-cover requirements
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Additional
postclosure maintenance
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Evaluation
of Alternatives
Cost comparisons
should be made once several landfill expansion options
have been identified and thorough cost estimates have
been prepared. At this stage it is helpful to present
the cost information in the following format:
UnitCost
= TC / NetCY
where
UnitCost
= unit cost per cubic yard of developed airspace ($/yd.3),
TC = total
cost of developing landfill expansion ($), and
NetCY = net
solid waste disposal capacity of landfill expansion
(yd.3).
Once this
calculation is made, the various expansion options can
be ranked according to UnitCost to determine the most
cost-efficient alternatives. At this point, the landfill
owner or operator should be able to determine whether
the cost of developing the additional airspace can be
absorbed by the current market conditions. Future market
conditions should also be estimated for the period of
time when the expansion will come on-line. Factors such
as waste-volume increases/decreases and the opening
or closure of competing landfills or transfer stations
should be evaluated.
The lowest
UnitCost, however, should not necessarily determine
which expansion option to choose. The net airspace gained
by an option should be considered. The owner or operator
might be able to accept a lower profit margin if it
will result in a substantial increase in airspace, therefore
delaying the need for future expansions or development
of a new landfill.
MSE walls
provide the landfill owner or operator with an option
for potentially expanding a landfill when the traditional
lateral or vertical expansion is either not feasible
or not cost-effective. Successful incorporation of an
MSE wall in a landfill design, however, requires careful
evaluation of the many design variables. A thorough
and accurate cost analysis should be performed during
the conceptual design phase to ensure that an MSE wall
will be cost-effective.
References
ASTM.
"Test Method D4595-86 (1994) Standard Test Method
for Tensile Properties of Geotextiles by the Wide Width
Strip Method." American Society for Testing and
Materials, West Conshohocken, PA. 1994.
Berg,
R.R., V.E. Chouery-Curtis., and C.H. Watson. "Critical
Failure Planes in Analysis of Reinforced Slopes."
Proceedings of Geosynthetics 89 Conference.
San Diego, CA. 1989.
Christopher,
B.R. "FHWA Guideline for Reinforced Soil Design,
Theory and Practice." Federal Highway Administration,
Washington, DC.
Duncan,
J.M. and K.S. Wong. "STABGM A Computer Program
for Slope Stability Analysis with Circular Slip Surfaces
and Geogrid Reinforcement: Users Manual." Virginia
Polytechnic Institute and State University, Blacksburg,
VA. 1984.
GRI.
"GG4a: Determination of Long-Term Design Strength
of Stiff Geogrids." Geosynthetic Research Institute,
Drexel University, Philadelphia, PA. 1993a.
GRI.
"GG4b: Determination of Long-Term Design Strength
of Flexible Geogrids." Geosynthetic Research Institute,
Drexel University, Philadelphia, PA. 1993b.
Koerner,
R.M. Designing With Geosynthetics, Fourth Edition.
Prentice Hall, Upper Saddle River, NJ. 1997a.
Tensar
Corporation. "Guidelines for the Design of Tensar
Geogrid Reinforced Soil Retaining Walls." Tensar
Technical Note TTN:RW 1. 1988.
Guest
author Thomas M. Yanoschak, P.E., is project manager
with Camp Dresser & McKee in Raleigh, NC.
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