Difference between revisions of "Rainwater harvesting: Sizing and modeling"

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[[File:Cistern Size.png|thumb|550px|Schematic diagram of the inputs and outputs to a rainwater harvesting cistern]]
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[[File:Cistern Size.png|thumb|Schematic diagram of the inputs and outputs to a rainwater harvesting cistern]]
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===Simple===
 
===Simple===
<blockquote>
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The following approximations 
*Five percent of the average annual yield can be estimated:
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Five percent of the average annual yield can be estimated:
*<strong>Y<sub>0.05</sub>= A × C<sub>vol, A</sub> × R<sub>a</sub> × e × 0.05</strong>
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<math>Y_{0.05} = A_{c} \times C_{vol,A}\times R_{a} \times e \times 0.05</math>
*Y<sub>0.05</sub> = Five percent of the average annual yield (L)
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{{plainlist|Where:
*A = The catchment area (m<sup>2</sup>)
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*''Y<sub>0.05</sub>'' is five percent of the average annual yield (L)
*C<sub>vol, A</sub> = The annual runoff coefficient for the catchment
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*''A<sub>c</sub>'' is the catchment area (m<sup>2</sup>)
*R<sub>a</sub> = The average annual rainfall depth (mm)
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*''C<sub>vol, A</sub>'' is the annual runoff coefficient for the catchment
*e = The efficiency of the pre-storage filter</blockquote>
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*''R<sub>a</sub>'' is the average annual rainfall depth (mm)
 +
*''e'' is the efficiency of the pre-storage filter}}
 +
*Filter efficiency (''e'') can be reasonably estimated as 0.9 pending manufacturer’s information.<br>
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*In a study of three sites in Ontario, STEP found the annual ''C<sub>vol, A</sub>'' of the rooftops to be around 0.8 [http://www.sustainabletechnologies.ca/wp/home/urban-runoff-green-infrastructure/low-impact-development/rainwater-harvesting/performance-evaluation-of-rainwater-harvesting-systems-toronto-ontario/]. This figure includes losses to evaporation, snow being blown off the roof, and a number of overflow events.
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----
 +
Five percent of the average annual demand can be estimated:
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<math>D_{0.05} = P_{d} \times n\times 18.25</math>
 +
{{plainlist|Where:
 +
*''D<sub>0.05</sub>'' is five percent of the average annual demand (L)
 +
*''P<sub>d</sub>'' is the daily demand per person (L)
 +
*''n'' is the number of occupants}}
 +
----
 +
Then the following calculations are based upon two criteria:
 +
# A design rainfall depth is to be captured entirely by the RWH system.
 +
# The average annual demand (''D'') is greater than the average annual yield (''Y'') from the catchment.
 +
When \(Y_{0.05}/D_{0.05}<0.33\), the storage volume required can be estimated:
 +
<math>V_{S} = A_{c} \times C_{vol,E}\times R_{d} \times e</math>
 +
{{plainlist|Where:
 +
*''V<sub>S</sub>'' is the volume of storage required (L)
 +
*''A<sub>c</sub>'' is the catchment area (m<sup>2</sup>)
 +
*''C<sub>vol,E</sub>'' is the design storm runoff coefficient for the catchment
 +
*''R<sub>d</sub>'' is the design storm rainfall depth (mm), and
 +
*''e'' is the efficiency of the pre-storage filter.}}
  
Filter efficiency (e) can be reasonably estimated as 0.9 pending manufacturer’s information.
+
*Careful catchment selection means that the runoff coefficient, for an individual rainstorm event (''C<sub>vol, E</sub>'') should be 0.9 or greater.
In a study of three sites in Ontario, STEP found the annual C<sub>vol, A</sub> of the rooftops to be around 0.8 [http://www.sustainabletechnologies.ca/wp/home/urban-runoff-green-infrastructure/low-impact-development/rainwater-harvesting/performance-evaluation-of-rainwater-harvesting-systems-toronto-ontario/]. This figure includes losses to evaporation, snow being blown off the roof, and number of overflow events.
+
----       
<blockquote>Five percent of the average annual demand (D<sub>0.05</sub>) can be estimated:
+
Finally, when \(0.33<Y_{0.05}/D_{0.05}<0.7\), the total storage required can be estimated by adding ''Y<sub>0.05</sub>'':
<br><strong>D<sub>0.05</sub> =  P<sub>d</sub> × n × 18.25</strong>
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<math>TotalStorage = V_{S} + Y_{0.05}</math>
<br>D<sub>0.05</sub> = Five percent of the average annual demand (L)
 
<br>P<sub>d</sub> = The daily demand per person (L)
 
<br>n = The number of occupants </blockquote>
 
Then the following calculations are based upon two criteria:
 
#A design rainfall depth is to be captured entirely by the RWH system.
 
#The average annual demand (D) is greater than the average annual yield (Y) from the catchment.
 
When Y<sub>0.05</sub>/ D<sub>0.05</sub> < 0.33, the storage volume required can be estimated:
 
<br><strong>V<sub>S</sub> = A × C<sub>vol</sub> × R<sub>d</sub> × e</strong>
 
<br>V<sub>S</sub> = Storage volume required (L)
 
<br>A = The catchment area (m<sup>2</sup>)
 
<br>C<sub>vol, E</sub> = The design storm runoff coefficient for the catchment
 
<br>R<sub>d</sub> = The design storm rainfall depth (mm), and
 
<br>e = The efficiency of the pre-storage filter.
 
/*Good catchment selection means that the runoff coefficient, for a rainstorm event (C<sub>vol, E</sub>) should be 0.9 or greater.
 
       
 
When 0.33 < Y<sub>0.05</sub>/ D<sub>0.05</sub>< 0.7, the total storage required can be estimated by adding Y<sub>0.05</sub>:
 
<br>
 
<strong>Total storage = V<sub>S</sub> + Y<sub>0.05</sub></strong>
 
 
----
 
----
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==STEP Rainwater Harvesting Tool==
 +
[[File:RWH_tank_capacity_table.jpg|thumb|500 px|Quick reference table generated using STEP RWH tool, (data for the City of Toronto (median annual rainfall 678 mm). Optimal cistern size is that providing at least a 2.5% improvement in water savings following an increase of 1,000 Litres in storage capacity.]]
 +
The Sustainable Technologies Evaluation Program have produced a rainwater harvesting design and costing tool specific to Ontario. The tool is in a simple to use Excel format and is free to download.<br>
 +
{{clickable button|[[File:Connect the Drops.PNG|200 px|link=http://www.sustainabletechnologies.ca/wp/home/urban-runoff-green-infrastructure/low-impact-development/rainwater-harvesting/rainwater-harvesting-design-and-costing-tool/]]}}
  
===STEP Rainwater Harvesting Tool===
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==STEP Treatment Train Tool==
[[File:RWH_tank_capacity_table.jpg|thumb|Quick reference table generated using STEP RWH tool, (data for the City of Toronto (median annual rainfall 678 mm). Optimal cistern size is that providing at least a 2.5% improvement in water savings following an increase of 1,000 Litres in storage capacity.]]
+
{{Clickable button|[[File:TTT.png|300 px|link=http://www.sustainabletechnologies.ca/wp/low-impact-development-treatment-train-tool/]]}}<br>
The Sustainable Technologies Evaluation Program have produced a rainwater harvesting design and costing tool specific to Ontario. The tool is in a simple to use Excel format and is free to download.
+
'''[[Rainwater harvesting: TTT]]'''
<strong>[http://www.sustainabletechnologies.ca/wp/home/urban-runoff-green-infrastructure/low-impact-development/rainwater-harvesting/rainwater-harvesting-design-and-costing-tool/| Rainwater Harvesting Tool]</strong>
 
----
 
  
===STEP Treatment Train Tool===
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==Cistern dimensions==
Once the size of cistern has been determined, it can easily be modeled in many open source and proprietary applications. For planning purposes, a RWH system could be integrated into a site plan using STEP's Treatment Train Tool.
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[[File:Cistern dimensions.jpg|thumb|The blue area indicates the only usable volume in this rainwater harvesting cistern, the depth between the pump inlet and the overflow.]]
In a typical configuration:
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The connections into and out of a rainwater cistern can have a dramatic effect on the actual usable volume. The only usable water within the cistern is that above the height of the pump intake, and below the invert of the overflow outlet. This dimension can easily become constrained where the outlet must lie beneath the frost line and where a high powered pump is required to elevate the water many storeys.
*The catchment (roof) would be 100% impervious
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* The depth of storage between the elevation of the inlet and overflow is unusable space, so the overflow should be located towards the top of the cistern.
*The rainwater harvesting system would be a 'Storage' Element with the following properties:
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* The depth of storage beneath the pump inlet is unusable, but may also be a useful zone for sediment to settle. A custom or cast-in-place vault could minimise this unused volume by tapering towards the the base.
**Storage type = No removal
 
**Lined
 
**Underlying soil = <em>doesn't matter, can ignore</em>
 
**Evaporation factor = 0
 
**Suction head (mm) = 0
 
**Saturated conductivity (mm/hr) = 0
 
**Initial soil moisture deficit (fraction) = 0
 
*The dimensions of the rainwater cistern can be placed into the fields:
 
#Bottom elevation (m)
 
#Maximum depth (m)
 
#Initial water depth (m)
 
#The Curves table is designed to accommodate ponds of roughly conical dimensions. A rainwater cistern is usually cuboid or cylindrical in shape, so that the area (m<sup>2</sup>) will remain the same throughout the depth.  
 
<strong>[http://www.sustainabletechnologies.ca/wp/low-impact-development-treatment-train-tool/|The Treatment Train Tool]</strong>
 
----
 
 
[[category:modeling]]
 
[[category:modeling]]

Latest revision as of 12:16, 26 October 2023

Schematic diagram of the inputs and outputs to a rainwater harvesting cistern

Simple[edit]

The following approximations Five percent of the average annual yield can be estimated:

Where:

  • Y0.05 is five percent of the average annual yield (L)
  • Ac is the catchment area (m2)
  • Cvol, A is the annual runoff coefficient for the catchment
  • Ra is the average annual rainfall depth (mm)
  • e is the efficiency of the pre-storage filter
  • Filter efficiency (e) can be reasonably estimated as 0.9 pending manufacturer’s information.
  • In a study of three sites in Ontario, STEP found the annual Cvol, A of the rooftops to be around 0.8 [1]. This figure includes losses to evaporation, snow being blown off the roof, and a number of overflow events.

Five percent of the average annual demand can be estimated:

Where:

  • D0.05 is five percent of the average annual demand (L)
  • Pd is the daily demand per person (L)
  • n is the number of occupants

Then the following calculations are based upon two criteria:

  1. A design rainfall depth is to be captured entirely by the RWH system.
  2. The average annual demand (D) is greater than the average annual yield (Y) from the catchment.

When \(Y_{0.05}/D_{0.05}<0.33\), the storage volume required can be estimated:

Where:

  • VS is the volume of storage required (L)
  • Ac is the catchment area (m2)
  • Cvol,E is the design storm runoff coefficient for the catchment
  • Rd is the design storm rainfall depth (mm), and
  • e is the efficiency of the pre-storage filter.
  • Careful catchment selection means that the runoff coefficient, for an individual rainstorm event (Cvol, E) should be 0.9 or greater.

Finally, when \(0.33<Y_{0.05}/D_{0.05}<0.7\), the total storage required can be estimated by adding Y0.05:


STEP Rainwater Harvesting Tool[edit]

Quick reference table generated using STEP RWH tool, (data for the City of Toronto (median annual rainfall 678 mm). Optimal cistern size is that providing at least a 2.5% improvement in water savings following an increase of 1,000 Litres in storage capacity.

The Sustainable Technologies Evaluation Program have produced a rainwater harvesting design and costing tool specific to Ontario. The tool is in a simple to use Excel format and is free to download.
Connect the Drops.PNG

STEP Treatment Train Tool[edit]

TTT.png
Rainwater harvesting: TTT

Cistern dimensions[edit]

The blue area indicates the only usable volume in this rainwater harvesting cistern, the depth between the pump inlet and the overflow.

The connections into and out of a rainwater cistern can have a dramatic effect on the actual usable volume. The only usable water within the cistern is that above the height of the pump intake, and below the invert of the overflow outlet. This dimension can easily become constrained where the outlet must lie beneath the frost line and where a high powered pump is required to elevate the water many storeys.

  • The depth of storage between the elevation of the inlet and overflow is unusable space, so the overflow should be located towards the top of the cistern.
  • The depth of storage beneath the pump inlet is unusable, but may also be a useful zone for sediment to settle. A custom or cast-in-place vault could minimise this unused volume by tapering towards the the base.