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Low Impact Development Manual for Michigan - OSEH - University ...

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Hydrology<br />

Additional design considerations <strong>for</strong> wet ponds<br />

• Wet ponds must be able to receive and retain<br />

enough flow from rain, runoff, and groundwater<br />

to ensure long-term viability. A permanent water<br />

surface in the deeper areas of the wet pond should<br />

be maintained during all but the driest periods. A<br />

relatively stable permanent water surface elevation<br />

will reduce the stress on vegetation in an area<br />

adjacent to the pond. A wet pond should have a<br />

drainage area of at least 10 acres (five acres <strong>for</strong><br />

pocket wet ponds) or some means of sustaining<br />

constant inflow. Even with a large drainage area,<br />

a constant source of inflow can improve the<br />

biological health and effectiveness of a wet pond<br />

while discouraging mosquito growth.<br />

Additional considerations <strong>for</strong> constructed wetlands<br />

• Constructed wetlands must be able to receive<br />

and retain enough flow from rain, runoff, and<br />

groundwater to ensure long-term viability.<br />

Hydrologic calculations (e.g., a water balance)<br />

should be per<strong>for</strong>med to verify this. Shallow<br />

marsh areas can become dry at the surface but<br />

not <strong>for</strong> greater than one month, even in the most<br />

severe drought. A permanent water surface in the<br />

deeper areas of the constructed wetland should be<br />

maintained during all but the driest periods. The<br />

average target pool depth to maintain emergent<br />

wetland vegetation is six to 12 inches. Maximum<br />

water depths of three to four feet should not be<br />

exceeded <strong>for</strong> more than 12 hours at a time, <strong>for</strong><br />

more than a few days out of the year. The deeper<br />

the water and the longer it sits the greater the<br />

chances that a wetland vegetation monoculture,<br />

such as cattails, will develop. A relatively stable<br />

normal water surface elevation reduces the stress<br />

Table 7.9<br />

Definitions of Wetland Vegetation Zones<br />

Vegetation Zone Description<br />

Open Water Areas between 18-inches and 6-feet deep<br />

Emergent Areas up to 18-inches deep<br />

<strong>Low</strong> Marsh Portion of the emergent zone between 6- and 18-inches deep<br />

High Marsh Portion of the emergent zone up to 6-inches deep<br />

Ephemeral Storage Areas periodically inundated during runoff events<br />

Buffer Area outside of maximum water surface elevation<br />

on wetland vegetation. A constructed wetland must<br />

have a drainage area of at least 10 acres (five acres<br />

<strong>for</strong> “pocket” wetlands) or some means of sustaining<br />

constant inflow. Even with a large drainage area,<br />

a constant source of inflow can improve the<br />

biological health and effectiveness of a constructed<br />

wetland. <strong>Michigan</strong>’s precipitation is generally well<br />

distributed throughout the year and is there<strong>for</strong>e<br />

suited <strong>for</strong> constructed wetlands.<br />

Stormwater Functions and<br />

Calculations<br />

Volume reduction<br />

Dry ponds and underground detention systems do not<br />

provide an appreciable amount of volume reduction.<br />

Although not typically considered a volume-reducing<br />

BMP, wet ponds and constructed wetlands can achieve<br />

some volume reduction through infiltration and evapotranspiration,<br />

especially during small storms and high<br />

temperature periods.<br />

According to the International Stormwater BMP<br />

Database, wet ponds have an average annual volume<br />

reduction of seven percent (Strecker et al., 2004).<br />

Hydrologic calculations should be per<strong>for</strong>med to verify<br />

that the wet pond or constructed wetland will have<br />

a viable amount of inflow can also predict the water<br />

surface elevation under varying conditions. The volume<br />

stored between the predicted water level and the lowest<br />

outlet elevation will be removed from the storm that<br />

occurs under those conditions.<br />

Peak rate mitigation<br />

Inflow and discharge hydrographs must be calculated<br />

<strong>for</strong> each design storm. Hydrographs should be based<br />

on a 24-hour rainfall event. The Natural Resources<br />

Conservation Service’s (NRCS) 24-hour Type II rainfall<br />

distribution should be used.<br />

LID <strong>Manual</strong> <strong>for</strong> <strong>Michigan</strong> – Chapter 7 Page 181

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