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 3.2.2 - Extended Dry Detention Pond<br />
• Design may be subject to the requirements <strong>of</strong> the Kansas dam safety program based on<br />
the volume, dam height, and level <strong>of</strong> hazard.<br />
• Earthen embankments shall have side slopes no steeper than 3:1 (horizontal to vertical).<br />
• Vegetated slopes shall be less than 20 feet in height and shall have side slopes no<br />
steeper than 4:1 (horizontal to vertical). Riprap-protected slopes shall be no steeper than<br />
3:1. Geotechnical slope stability analysis is recommended for slopes greater than 10 feet<br />
in height.<br />
• Areas above the normal high water elevations <strong>of</strong> the detention facility should be sloped<br />
toward the basin to allow drainage and to prevent standing water. Careful grading is<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 />
• Ponds cannot be located within a stream or any other navigable waters <strong>of</strong> the U.S.,<br />
including wetlands, without obtaining applicable local, Kansas and federal permits.<br />
• Dry extended detention ponds located in floodplains or backwater areas must perform as<br />
specified for peak flow control for any tailwater condition, up to the Base Flood Elevation<br />
(BFE). The potential for back flow into the pond must be addressed with flap gates or by<br />
providing sufficient volume to receive backflow up to the BFE, and still provide peak flow<br />
control surcharge volume in the pond (above the BFE).<br />
Inlet and Outlet Structures<br />
• Discharge into the pond from inflow channels or pipes are to be stabilized with flared<br />
riprap aprons, or the equivalent. A sediment forebay or equivalent upstream pretreatment<br />
with a volume <strong>of</strong> 0.1 inches per impervious acre <strong>of</strong> contributing drainage shall be provided<br />
upstream <strong>of</strong> the pond. The pre-treatment storage volume is part <strong>of</strong> the total WQ v required.<br />
• An orifice capable <strong>of</strong> detaining the WQ v for 24 hours must be provided. The orifice shall be<br />
adequately protected from clogging using designs found in chapter 5.<br />
• Likewise, the outlet structure must have an orifice capable <strong>of</strong> detaining the CP v for 24<br />
hours. Orifice protection requirements are the same as for the WQ v .<br />
• For peak flow control, discharge is controlled by a principal spillway, typically consisting <strong>of</strong><br />
a riser and outlet pipe. The WQ v and CP v orifices are usually incorporated into the riser.<br />
Additional orifices and weirs are incorporated into the riser to control the 2 through 100-<br />
year design storms.<br />
• Small outlets that will be subject to clogging or are difficult to maintain are not acceptable.<br />
• See <strong>Volume</strong> 2, <strong>Chapter</strong>s 4 and 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.<br />
<strong>Volume</strong> 2, Technical Guidance Page 3 - 49