m |
m |
||
Line 82: | Line 82: | ||
</tr> | </tr> | ||
</table> | </table> | ||
− | <font size=2><sup>a</sup> Removal rates show in table are a composite of five sources: [(http://www.bmpdatabase.org ASCE/EPA International Database]; [http://yosemite.epa.gov/r10/water.nsf/95537302e2c56cea8825688200708c9a/159859e0c556f1c988256b7f007525b9/$FILE/Evaluating%20the%20Impact%20of%20Watershed%20Treatment.pdf Caraco] (Center for Watershed protection, 2001)]; [http://www.mde.state.md.us/programs/Water/StormwaterManagementProgram/MarylandStormwaterDesignManual/Pages/programs/waterprograms/sedimentandstormwater/stormwater_design/index.aspx Maryland Department of the Environment](2000); [http://www.stormwaterok.net/CWP%20Documents/CWP-07%20Natl%20Pollutant%20Removal%20Perform%20Database.pdf Winer] (Center for Watershed Protection, 2000); [http://wwwalker.net/p8/) P8] modeling (William Walker)<br> | + | <font size=2><sup>a</sup> Removal rates show in table are a composite of five sources: [(http://www.bmpdatabase.org ASCE/EPA International Database]; [http://yosemite.epa.gov/r10/water.nsf/95537302e2c56cea8825688200708c9a/159859e0c556f1c988256b7f007525b9/$FILE/Evaluating%20the%20Impact%20of%20Watershed%20Treatment.pdf Caraco] (Center for Watershed protection, 2001)]; |
+ | |||
+ | [http://www.mde.state.md.us/programs/Water/StormwaterManagementProgram/MarylandStormwaterDesignManual/Pages/programs/waterprograms/sedimentandstormwater/stormwater_design/index.aspx Maryland Department of the Environment](2000)]; | ||
+ | |||
+ | [http://www.stormwaterok.net/CWP%20Documents/CWP-07%20Natl%20Pollutant%20Removal%20Perform%20Database.pdf Winer] (Center for Watershed Protection, 2000); [http://wwwalker.net/p8/) P8] modeling (William Walker)<br> | ||
<sup>b</sup> Average removal efficiency expected under MPCA Sizing Rules 1 and 3<br> | <sup>b</sup> Average removal efficiency expected under MPCA Sizing Rules 1 and 3<br> | ||
<sup>c</sup> Upper limit on phosphorus removal with increased sizing and design features, based on national review<br> | <sup>c</sup> Upper limit on phosphorus removal with increased sizing and design features, based on national review<br> |
BMP group | BMP design variation | Average TP removal rateb | Maximum TP removal ratec | Average soluble P removal rated,g |
---|---|---|---|---|
Bioretention | Underdrain | 65 | 75 | 60 |
Infiltration | 100 | 100 | 100 | |
Filtration | Sand filter | 50 | 55 | 0 |
Dry swale | 0 | 55 | 0 | |
Wet swale | 65 | 75 | 70 | |
Infiltrationf | Infiltration trench | 100 | 100 | 100 |
Infiltration basin | 100 | 100 | 100 | |
Stormwater ponds | Wet pond | 50 | 65 | 70 |
Multiple pond | 60 | 75 | 75 | |
Stormwater wetlands | Shallow wetland | 40 | 55 | 50 |
Pond/wetland | 55 | 75 | 65 |
a Removal rates show in table are a composite of five sources: [(http://www.bmpdatabase.org ASCE/EPA International Database]; Caraco (Center for Watershed protection, 2001)];
Maryland Department of the Environment(2000)];
Winer (Center for Watershed Protection, 2000); P8 modeling (William Walker)
b Average removal efficiency expected under MPCA Sizing Rules 1 and 3
c Upper limit on phosphorus removal with increased sizing and design features, based on national review
d Average rate of soluble phosphorus removal in the literature
e See section on calculating credits for each BMP in this Manual.
f Note that the performance numbers apply only to that portion of total flow actually being treated; it does not include any runoff that bypasses the BMP
gNote that soluble P can transfer from surface water to groundwater, but this column refers only to surface water
hNote that 100% is assumed for all infiltration, but only for that portion of the flow fully treated in the infiltration facility; by-passed runoff or runoff diverted via underdrain does not receive this level of treatment.