m |
m |
||
Line 89: | Line 89: | ||
<tr> | <tr> | ||
<td>Institutional</td> | <td>Institutional</td> | ||
− | <td></td> | + | <td>17-140</td> |
− | <td></td> | + | <td>80</td> |
<td></td> | <td></td> | ||
</tr> | </tr> |
Event mean concentrations for total suspended solids.
Link to this table
Land cover/land use | Range (mg/L) | Recommended value (mg/L) | Notes |
---|---|---|---|
Commercial | 42-164 | 75 | If applicable to models being used, adjust curve numbers/runoff coefficients when calculating loads |
Industrial | 70-170 | 93 |
|
Residential | 42-101 | 73 | |
High-density/Multi-family residential | Calculate |
|
|
Medium density residential | Calculate |
|
|
Low density residential | Calculate |
|
|
Freeways/transportation | 50-90 | 87 | |
Mixed | 47-188 | 76 or calculate |
|
Parks and recreation | Use value for open space or calculate |
|
|
Open space | 11-70 | 21 | |
Conventional roof | <10 | ||
Institutional | 17-140 | 80 | |
Forest/shrub/grassland | 26-140 | 72 | Sediment concentrations from forested areas vary widely with factors such as slope and forest condition. Concentrations may be very high, but the annual volume of runoff is typically much less than non-forested areas. |
Open water and wetlands | see Notes (next column) |
|
|
Cropland (row crops) | 50-160 | Literature review was not adequate to recommend an emc | |
Pasture | 75-150 | 84 | Concentrations are a function of intensity of use. |