![]() |
![]() |
![]() |
|
|||||||||
![]() |
![]() |
|
|
|
|
|||||||
![]() |
![]() |
![]() |
|
|||||||||
![]() |
|
|||||||||||
|
|
|
|
||||||||||
![]() |
![]() |
|
||||||||||
|
|
|
|
|
|||||||||
|
|
|
|
|
|||||||||
|
|
|
|
|
|
|
|
|
|
|
|
|
|
![]() |
![]() |
![]() |
![]() |
![]() |
![]() |
Soil Media Mix |
||
|
Selection of the appropriate fill soil media for a bioretention area is important to ensure adequate drainage, reduce pollutant loads, and support plant growth.
The following "recipe" for a bioretention soil media, or fill-soil mix, works best:
|
![]() |
Soil ChemistryTo support plant growth while removing phosphorus from runoff, the fill soil must have a P-index between 10 and 30. If the bioretention area is not designed to reduce phosphorus in runoff, a P-Index for the fill soil of 25 to 40 is recommended. For additional information on the soil P-index, visit About the P-Index / P-Index Conversion. In addition to having a low P-Index, it is best for fill media to have a relatively high cation exchange capacity (CEC). Higher CECs describe soils that have a greater ability to capture and retain phosphorus. While a minimum CEC has yet to be established, CECs exceeding 10 are expected to work relatively well at removing target pollutants in bioretention systems. |