Illinois Urban Manual
PRACTICE STANDARD
INLET PROTECTION - STRAW BALE BARRIER
(no.) CODE 863
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(Source: Lake County Soil and Water Conservation District - Illinois)
DEFINITION
A temporary sediment control barrier formed around a storm drain drop inlet
consisting of a row of entrenched and anchored straw bales.
PURPOSE
The purpose of this practice is to help prevent sediment from entering storm
drains until the contributing watershed is stabilized.
CONDITIONS WHERE PRACTICE APPLIES
A straw bale barrier type of inlet protection applies where new or existing
storm sewers receive sediment-laden runoff. This method is applicable for drop
inlets only.
This method is applicable where the inlet drains a small, nearly level area
with slopes generally less than 5% and shallow sheet flows not exceeding 0.5 cfs
are expected.
The immediate land area around the inlet should be relatively flat (less than
1% slope) and located so that accumulated sediment can be easily removed.
This method does not apply to inlets receiving concentrated flows, such as in
street or highway medians.
This method applies where effectiveness is required for 3 months or less.
This practice can be used in combination with other temporary inlet
protection devices such as practice standards
INLET PROTECTION – BLOCK
& GRAVEL 850, INLET
PROTECTION – EXCAVATED DRAIN 855,
INLET PROTECTION –
FABRIC DROP 860 or
INLET PROTECTION – GRAVEL & WIRE MESH 861.
CRITERIA
The drainage area to each straw bale barrier inlet protection shall be one
acre or less.
The inside edge of the bales shall be a maximum of 2 feet from the edge of
the inlet.
Straw bale barrier inlet protection shall be installed prior to the storm
sewer system becoming functional.
Filter fabric may be added to the upstream side of the straw bales to enhance
sediment removal. The fabric shall meet the requirements as shown in material
specification 592 GEOTEXTILE,
Table 1 or 2, Class 1 with an AOS of at least 30 for non-woven and 50 for woven.
The choice to use filter fabric must also consider the larger ponding area that
will result.
CONSIDERATIONS
In developing areas, installation of streets and storm sewer networks usually
occur before the construction of homes, businesses or other developments. During
this, and subsequent phases of construction, unprotected soil is susceptible to
erosion. Storm sewers that are operational before their drainage areas are
stabilized often carry large amounts of sediment to lakes, detention ponds,
streams, or other natural or constructed drainageways. As a result, the water
quality of the receiving body of water is detrimentally affected. In cases of
extreme sediment loading, the storm sewer may clog completely or lose a major
portion of its capacity. To avoid these problems, it is necessary to prevent
sediment from entering the system at the inlets.
Storm drain inlet protection consists of several types of inlet filters and
traps. Each type differs in application dependant upon site conditions and type
of inlet. Not all designs are appropriate in all cases. The user must carefully
select a design suitable for the needs and site conditions.
Straw bale inlet protection should be considered for trapping sediment where
sheet and rill erosion is occurring in small, relatively flat drainage areas.
Straw bale inlet protection should not be used in areas of concentrated flow.
At the time storm sewer inlet and associated appurtenances become
operational, areas adjacent to the structures are most likely at final grade or
will not be altered for extended periods. This is the time when practice
standard TEMPORARY SEEDING 965 and other appropriate
controls should be implemented to reduce soil erosion.
Based on field observations in Illinois and other states, straw barriers have
not been as effective as a sediment control measure as they could be. There are
four major reasons for this. First, improper use of straw bales has been a major
problem. Straw bale barriers have been used in drainageways where high water
velocities and/or volumes have destroyed them or significantly impaired their
effectiveness. Second, improper placement and installation of the barriers, such
as staking the bales directly to the ground with no soil seal or entrenchment,
has allowed undercutting and flow around the ends. This has resulted in
additions of, rather than removal of, sediment from runoff waters. Third,
inadequate inspection and maintenance lowers the effectiveness of these
barriers. Fourth, because straw bales decompose in the presence of moisture,
they have a very limited life span.
Runoff from areas larger than one acre should be routed through a properly
designed practice such as
IMPOUNDMENT
STRUCTURE-ROUTED 842, or
TEMPORARY SEDIMENT TRAP 960.
PLANS AND SPECIFICATIONS
Plans and specifications for installing straw bale barrier inlet protection
shall be in keeping with this standard and shall describe the requirements for
applying the practice to achieve its intended purpose. At a minimum include the
following items:
- Inlet location.
- The depth of trench required to bed the bales
- The method(s) required to anchor the bales.
- Filter fabric specifications if used.
All plans shall include the installation, inspection and maintenance
schedules with the responsible party clearly identified.
Standard drawing INLET
PROTECTION - STRAW BALE BARRIER PLAN IL-563 may be used as the plan sheet.
OPERATION AND MAINTENANCE
Straw bale barrier inlet protection shall be inspected after every runoff
producing rain and repairs made as needed.
Close attention shall be paid to the repair of damaged bales, end runs and
undercutting beneath bales.
Necessary repairs to the barrier or replacement of bales shall be
accomplished promptly.
Sediment shall be removed and the barrier restored to its original dimensions
when the sediment has accumulated to one-half the barrier height. Removed
sediment shall be deposited in a suitable area in such a manner that it will not
erode.
When the contributing drainage area has been adequately stabilized, remove
all materials and any unstable soil, and either salvage or dispose of it
properly Bring the disturbed area to proper grade, then smooth and compact it.
Appropriately stabilize all bare areas around the inlet.
REFERENCES
North Carolina Sedimentation Control Commission, 1988. Erosion and Sediment
Control Planning and Design Manual. NC
Virginia Department of Conservation and Recreation, Division of Soil and
Water Conservation, 1992. Virginia Erosion and Sediment Control Handbook, 3rd
ed., VA
NRCS IL
November 1999
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