Difference between revisions of "Dry ponds: TTT"

From LID SWM Planning and Design Guide
Jump to navigation Jump to search
 
(21 intermediate revisions by 2 users not shown)
Line 1: Line 1:
{{Clickable button|[[File:TTT.png|400 px|link=http://www.sustainabletechnologies.ca/wp/low-impact-development-treatment-train-tool/]]}}
+
[[File:Storage TTT.png|300px|thumb|[[Dry ponds]] are found in storage element in the LID TTT]]
[[File:Storage TTT.png|thumb|[[Dry ponds]] are found in storage element in the LID TTT.]]  
+
[[File:Pond curves.png|300px|thumb|The largest area is at the top, level 0 m; each subsequent lower depth has a smaller area]]  
  
Dry ponds are a storage element in the Treatment Train Tool.
+
The Low Impact Development Treatment Train Tool can analyze annual and event-based runoff volumes and pollutant load removal for dry ponds.
 +
 
 +
{{Clickable button|[[File:TTT.png|350 px|link=https://sustainabletechnologies.ca/lid-ttt/]]}}
 +
 
{|class="wikitable"
 
{|class="wikitable"
|+A [[rainwater harvesting]] cistern as a storage element (key parameters)
+
|+A [[Dry ponds|dry pond]] as a storage element (key parameters) in the Treatment Train Tool.
 +
|-
 +
!colspan = "2"|Stage Storage
 +
|-
 +
|Name||Important to have a unique name, to connect it with the catchment area
 +
|-
 +
|Storage type||Dry detention ponds
 
|-
 
|-
!colspan = "2" style="background: darkcyan; color: white; align = center"|Stage Storage
+
|Bottom elevation (m)||This is important to correspond with other components, <br>e.g. when the overflow is coupled to another BMP within a treatment train
 
|-
 
|-
|Name||Important to have a unique name, to associate with the subcatchment (harvesting area)
+
|Maximum depth (m)||
 
|-
 
|-
|Storage type||No removal
+
|Lined/unlined||Unlined (ideally)
 
|-
 
|-
|Bottom elevation (m)||This will be 0 for installations at ground level, but will often be underground. This is of greater importance when the overflow is coupled to another component within a treatment train
+
|Underlying soil||Choose from five; sandy soils drain more quickly.
 +
|-
 +
|Evaporation factor||?
 
|-
 
|-
|Maximum depth (m)||Height of the RWH cistern
+
|Suction head (mm)||?
 
|-
 
|-
|Lined/unlined||Lined
+
|Saturated conductivity (mm/hr)||?
 
|-
 
|-
|Evaporation factor||0
+
|Initial soil moisture deficit (fraction)||?
 
|-
 
|-
!colspan = "2" style="background: darkcyan; color: white; align = center"|Curves
+
!colspan = "2" align = center"|Curves
 
|-
 
|-
|colspan = 2|The Curves table is designed to accommodate ponds of roughly conical dimensions. Rainwater cistern are usually cuboid or cylindrical in shape, so that the area (m<sup>2</sup>) will remain the same throughout the depth. The top and bottom dimensions can be placed within the first two rows of the table.  
+
|colspan = 2|The Curves table is designed to accommodate the side slopes. The top line begins at 0 m, with subsequent depths in the following lines.  
 
|}
 
|}

Latest revision as of 16:06, 22 August 2025

Dry ponds are found in storage element in the LID TTT
The largest area is at the top, level 0 m; each subsequent lower depth has a smaller area

The Low Impact Development Treatment Train Tool can analyze annual and event-based runoff volumes and pollutant load removal for dry ponds.

TTT.png

A dry pond as a storage element (key parameters) in the Treatment Train Tool.
Stage Storage
Name Important to have a unique name, to connect it with the catchment area
Storage type Dry detention ponds
Bottom elevation (m) This is important to correspond with other components,
e.g. when the overflow is coupled to another BMP within a treatment train
Maximum depth (m)
Lined/unlined Unlined (ideally)
Underlying soil Choose from five; sandy soils drain more quickly.
Evaporation factor ?
Suction head (mm) ?
Saturated conductivity (mm/hr) ?
Initial soil moisture deficit (fraction) ?
Curves
The Curves table is designed to accommodate the side slopes. The top line begins at 0 m, with subsequent depths in the following lines.