EROSION AND SEDIMENTATION
The purpose of this section is to provide guidance in the design of effective management of
erosion and sedimentation and to protect water quality and the general health, safety and welfare
of the residents
of the City of Chickasha.
Development activity shall not be conducted unless appropriate erosion and
sedimentation facilities are designed, installed and maintained throughout the life of
All erosion and
sediment control methods shall be indicated on the final construction
and/or building permit plans.
All earth slopes and earth areas, new or existing, subject to erosion, such as, adjacent
to trickle channels, inlet structures, and outlet structures,
within any area designated
for detention or drainage; shall be slab sodded with Bermuda sod or have permanent
established growth of vegetation. All vegetation areas shall be fertilized, watered, and
in an established growing condition prior to completion
or acceptance of any storm
water drainage facility, and/or development.
General Design Principals. Practical combinations of the following principles shall be
utilized, as a minimum, in planning measures to be installed for any
The land disturbing activity shall conform to existing topography and soil type
so as to create the lowest practicable erosion potential.
The disturbed area and the duration of exposure of bare earth to erosive
shall be kept to a practicable minimum through construction
scheduling and management.
Cut and fill operations should be kept to a minimum.
Disturbed soil shall be stabilized as quickly as practicable.
Natural vegetation shall be retained,
protected, and supplemented whenever
Temporary vegetation or mulching shall be employed to protect exposed critical
areas during development.
Permanent vegetation and structural erosion control measures shall be installed
prior to final
acceptance of developments, or as soon as seasonal planting
General Practice: Soil and water conservation measures include but are not
necessarily restricted to vegetation, sediment basins, dikes, grade stabilization
sediment traps, land grading, diversions, waterways or outlets, and rip
Vegetative practices shall be applied to control erosion. The practice can be either
temporary and/or permanent depending on the site specific needs.
EROSION AND SEDIMENT CONTR
Long term permanent seeding, sprigging, or planting which produces vegetative cover
including Bermuda grass, Kentucky 31 Tall Fescue and Weeping Love grass shall be
used to control erosion on a permanent basis.
Short term seeding, p
roducing temporary vegetative cover such as small grains like
oats, rye and wheat, and sudans and sorghums shall be used to control immediate
erosion. This practice effective for areas where soil is left exposed for a period of 6 to
12 months shall not be
deemed permanent erosion control.
Straw Bale Dike may be utilized where no other practice is feasible, a temporary
barrier with a life expectancy of three months or less can be installed across or at the
toe of a slope for the contributing drainage areas,
in accordance with the adopted
Hay and sod mulching, as a temporary measure, may be used for embankment
stabilization in areas where surface runoff is to be directed down a slope.
Erosion matting shall be used for channel embankment and slope
a permanent erosion control cover has not been established prior to use. The specified
material shall be installed as recommended by the manufacturer of the proposed
A stabilized construction entrance shall be built in
accordance with the adopted
standards to reduce or eliminate the tracking or flowing of sediment onto public right
A concrete or stone outlet structure shall be constructed in areas where the entire
drainage area to the structure is not stabi
lized or where there is a need to dispose
runoff at a protected outlet or where concentrated flow for the duration of the period
of construction needs to be diffused.
A grade stabilization structure in the form of a paved chute or flume shall be
tructed to prevent erosion, were concentrated flow of surface runoff is to be
conveyed down a slope of 3% or greater.
Storm water detention facilities may be used temporarily as sediment basins. A
temporary outlet structure for the storm water detent
ion facility to work as a sediment
pond shall be constructed. At the end of the construction activity, the developer shall
remove all collected sediment from the detention facility and outlet structure and
return the facility to a previous condition and/or
to the approved cross