Volume 2-05, Chapter 3 - City of Wichita
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