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Volume 2-05, Chapter 3 - City of Wichita

Volume 2-05, Chapter 3 - City of Wichita

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Section 3.4.1 - Conventional Dry Detention Pond<br />

required to avoid creation <strong>of</strong> upland surface depressions that may retain run<strong>of</strong>f. The<br />

bottom area <strong>of</strong> storage facilities should be graded toward the outlet to prevent standing<br />

water conditions. A low flow or pilot channel across the facility bottom from the inlet to the<br />

outlet (<strong>of</strong>ten constructed with riprap or a concrete flume) is recommended to convey low<br />

flows and prevent standing water conditions.<br />

• To the extent practicable, the long axis <strong>of</strong> ponds should be oriented east-west to minimize<br />

wind wave bank erosion.<br />

• The local jurisdiction may require that the facility be placed in a reserve and/or<br />

establishment <strong>of</strong> a drainage easement the facility, which is accessible from a public road<br />

or other accessible easement. When required, the drainage easement should be at least<br />

20 feet wide, provide a minimum traversable width <strong>of</strong> 15 feet, have a maximum slope <strong>of</strong> no<br />

more than 10%, and be appropriately stabilized to withstand maintenance equipment and<br />

vehicles.<br />

Inlet and Outlet Structures<br />

• The discharge from inflow channels or pipes is to be stabilized with flared riprap aprons, or<br />

the equivalent. A sediment forebay or equivalent upstream pretreatment sized to 0.1 acreinch<br />

per impervious acre <strong>of</strong> contributing drainage should be provided for in-line dry<br />

detention basins that are located downstream <strong>of</strong> <strong>of</strong>f-line water quality treatment controls.<br />

• For a dry detention basin, the principal spillway or outlet structure (usually a concrete riser<br />

with orifices and an outlet pipe, or just an outlet pipe) is sized for its flood control functions<br />

(based on hydrologic routing calculations). Small outlet openings that will be subject to<br />

clogging or are difficult to maintain are not acceptable. Trash racks, hoods, or other<br />

protection against debris blockage <strong>of</strong> principal spillway outlets are required. See Section<br />

3.2.1 and <strong>Chapter</strong> 5.<br />

• See <strong>Chapter</strong> 4 and <strong>Chapter</strong> 5 for more information on the design <strong>of</strong> outlet works.<br />

• Seepage control or anti-seep collars should be provided for all outlet pipes through earth<br />

dams.<br />

• Riprap, plunge pools or pads, or other energy dissipators are to be placed at the end <strong>of</strong><br />

the pond outlet pipe to prevent scouring and erosion. If the basin discharges to a channel<br />

with dry weather flow, care should be taken to minimize tree clearing along the<br />

downstream channel, and to reestablish a vegetated riparian zone in the shortest possible<br />

distance.<br />

• A concrete emergency spillway is to be included in the stormwater pond design to safely<br />

pass the 100-year, 24-hour rainfall flood event. The spillway prevents pond water levels<br />

from overtopping the embankment. When applicable, the emergency spillway must be<br />

designed to State <strong>of</strong> Kansas requirements for dam safety and must be located so that<br />

downstream structures will not be impacted by spillway discharges.<br />

• A minimum <strong>of</strong> 1 foot <strong>of</strong> freeboard must be provided, measured from the top <strong>of</strong> the water<br />

surface elevation for the 100-year flood, to the lowest point <strong>of</strong> the dam embankment not<br />

counting the emergency spillway. The 100-year flood elevation for emergency spillway<br />

<strong>Volume</strong> 2, Technical Guidance Page 3 - 183

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