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Dry ponds may include a deep pool in the sediment forebay to minimize scour and sediment resuspension, but the main basin does not retain a permanent pool of water. As a result, contaminants cannot settle between storm events, nor is there dilution of pollutants during storms. Consequently, while dry ponds are effective for [[Erosion|erosion]] and flood control, they may need to be paired with other LID features in a [[Treatment train|treatment train]] to improve water quality beyond the basic treatment level of 60% long-term TSS removal (MOE, 2003)<ref name="MOE"></ref>.
 
Dry ponds may include a deep pool in the sediment forebay to minimize scour and sediment resuspension, but the main basin does not retain a permanent pool of water. As a result, contaminants cannot settle between storm events, nor is there dilution of pollutants during storms. Consequently, while dry ponds are effective for [[Erosion|erosion]] and flood control, they may need to be paired with other LID features in a [[Treatment train|treatment train]] to improve water quality beyond the basic treatment level of 60% long-term TSS removal (MOE, 2003)<ref name="MOE"></ref>.
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To assess whether a SWMF needs sediment removal, three factors are required:
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*Current storage capacity (from sediment depth measurements or TSS load modelling).
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*Minimum efficiency allowed (5% reduction, per MOE 2003).
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*The facility’s efficiency–storage relationship, to compare storage loss with the 5% efficiency threshold.
      
==Modeling==
 
==Modeling==

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