Difference between revisions of "Bioretention: TTT"
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− | {|class=" | + | {{Clickable button|[[File:TTT.png|350 px|link=http://www.sustainabletechnologies.ca/wp/low-impact-development-treatment-train-tool/]]}} |
+ | [[File:LID TTT.png|thumb|[[Bioretention cells]] are found within the LID toolbox]] | ||
+ | {|class="wikitable" | ||
|- | |- | ||
− | + | !colspan = "2" align = center"|Surface | |
|- | |- | ||
− | |Berm height (mm) | + | |width = 210px|Berm height (mm) |
− | | | + | |Ponding depth, maximum (e.g. 300 mm), sometimes referred to as 'bowl depth' |
|- | |- | ||
|Surface roughness (Manning’s n) | |Surface roughness (Manning’s n) | ||
|Lower numbers indicate less surface obstruction and result in faster flow | |Lower numbers indicate less surface obstruction and result in faster flow | ||
Suggested ranges: | Suggested ranges: | ||
− | * Mown grass (dependent on density) 0.03 – 0.06<ref name = SWMM> Oregon State Univ., Corvallis. Dept. of Civil, Construction and Environmental Engineering.; Environmental Protection Agency, Cincinnati ONRMRL. Storm Water Management Model Reference Manual Volume I Hydrology (Revised). 2016:233. https://nepis.epa.gov/Exe/ZyPURL.cgi?Dockey=P100NYRA.txt Accessed August 23, 2017.</ref> | + | * [[Turf|Mown grass]] (dependent on density) 0.03 – 0.06<ref name = SWMM> Oregon State Univ., Corvallis. Dept. of Civil, Construction and Environmental Engineering.; Environmental Protection Agency, Cincinnati ONRMRL. Storm Water Management Model Reference Manual Volume I Hydrology (Revised). 2016:233. https://nepis.epa.gov/Exe/ZyPURL.cgi?Dockey=P100NYRA.txt Accessed August 23, 2017.</ref> |
− | * | + | * [[Stone]] 0.03 – 0.05 |
* Planted (highly dependent on density) 0.05 – 0.15 | * Planted (highly dependent on density) 0.05 – 0.15 | ||
|- | |- | ||
|Surface slope (%) | |Surface slope (%) | ||
− | |If the slope > 3% a series of [[ | + | |If the slope > 3% a series of [[Check dams]] or weirs should be included in the design. |
|- | |- | ||
− | + | !colspan = "2" align = center"|'''Soil (bioretention filter media)''' | |
|- | |- | ||
|Thickness (mm) | |Thickness (mm) | ||
|Depth of filter media | |Depth of filter media | ||
|- | |- | ||
− | |Porosity | + | |Porosity of filter media |
− | |Suggest | + | |Suggest [[Bioretention media storage|0.35]] unless otherwise tested |
|- | |- | ||
|Field capacity (fraction) | |Field capacity (fraction) | ||
Line 30: | Line 32: | ||
|Suggested value 0.03 <ref name = SWMM/> | |Suggested value 0.03 <ref name = SWMM/> | ||
|- | |- | ||
− | | | + | |Hydraulic conductivity (mm/hr) |
|Suggested range 25 – 250 mm/hr | |Suggested range 25 – 250 mm/hr | ||
|- | |- | ||
Line 39: | Line 41: | ||
|Suggested range 50 - 60 <ref name = SWMM/> | |Suggested range 50 - 60 <ref name = SWMM/> | ||
|- | |- | ||
− | + | !colspan = "2" align = center"|'''Storage''' | |
|- | |- | ||
|Thickness (mm) | |Thickness (mm) | ||
|Depth of storage aggregates layer | |Depth of storage aggregates layer | ||
|- | |- | ||
− | | | + | |Porosity of storage reservoir aggregate |
− | |Suggest | + | |Suggest value 0.4 unless otherwise tested |
|- | |- | ||
|Seepage rate (mm/hr) | |Seepage rate (mm/hr) | ||
Line 51: | Line 53: | ||
|- | |- | ||
|Clogging factor | |Clogging factor | ||
− | | | + | |Maybe up to 0.5 to account for some anticipated maturation. |
|- | |- | ||
− | |Design | + | |Design [[drainage time]] (hrs) |
− | | | + | |Maximum permissible time to fully drain the storage reservoir. |
|- | |- | ||
− | + | !colspan = "2" align = center"|'''Drain (underdrain)''' | |
|- | |- | ||
|Flow coefficient | |Flow coefficient | ||
Line 65: | Line 67: | ||
|- | |- | ||
|Offset height | |Offset height | ||
− | |This is the height from the base of the cell to the height at which the drain discharges. In some designs this may be the height of the perforated pipe within the storage layer | + | |This is the height from the base of the cell to the height at which the drain discharges. In some designs this may be the height of the perforated pipe within the storage layer; in others this height is adjusted by creating an upturn in the discharge pipe.[[Bioretention: Partial infiltration]] |
|} | |} | ||
− | + | ||
+ | [[category: modeling]] |
Latest revision as of 16:31, 22 April 2020
Surface | |
---|---|
Berm height (mm) | Ponding depth, maximum (e.g. 300 mm), sometimes referred to as 'bowl depth' |
Surface roughness (Manning’s n) | Lower numbers indicate less surface obstruction and result in faster flow
Suggested ranges:
|
Surface slope (%) | If the slope > 3% a series of Check dams or weirs should be included in the design. |
Soil (bioretention filter media) | |
Thickness (mm) | Depth of filter media |
Porosity of filter media | Suggest 0.35 unless otherwise tested |
Field capacity (fraction) | Suggested range 0.10 - 0.12 [1] |
Wilting point (fraction) | Suggested value 0.03 [1] |
Hydraulic conductivity (mm/hr) | Suggested range 25 – 250 mm/hr |
Conductivity slope | Suggested value 45 [1] |
Suction head (mm) | Suggested range 50 - 60 [1] |
Storage | |
Thickness (mm) | Depth of storage aggregates layer |
Porosity of storage reservoir aggregate | Suggest value 0.4 unless otherwise tested |
Seepage rate (mm/hr) | Infiltration rate of native soil |
Clogging factor | Maybe up to 0.5 to account for some anticipated maturation. |
Design drainage time (hrs) | Maximum permissible time to fully drain the storage reservoir. |
Drain (underdrain) | |
Flow coefficient | Suggested value 1 |
Flow exponent | Suggested value 1 |
Offset height | This is the height from the base of the cell to the height at which the drain discharges. In some designs this may be the height of the perforated pipe within the storage layer; in others this height is adjusted by creating an upturn in the discharge pipe.Bioretention: Partial infiltration |
- ↑ 1.0 1.1 1.2 1.3 1.4 Oregon State Univ., Corvallis. Dept. of Civil, Construction and Environmental Engineering.; Environmental Protection Agency, Cincinnati ONRMRL. Storm Water Management Model Reference Manual Volume I Hydrology (Revised). 2016:233. https://nepis.epa.gov/Exe/ZyPURL.cgi?Dockey=P100NYRA.txt Accessed August 23, 2017.