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| ==Design Assumptions== | | ==Design Assumptions== |
| Bioretention is an ideal technology for fitting functional vegetation into urban landscapes and treating runoff collected from nearby impervious surfaces.
| | Infiltration trenches are an ideal technology for installing below any type of landscape with requirements to infiltrate excess stormwater whilst conveying excess. Components include: layers of coarse [[aggregate]] (to bed the pipe, store and redistribute water), [[underdrain|perforated pipe or udnerdrains]] and [[geotextile]]. <br> |
| Components include: a 'filter bed' with [[filter media]], storage layer of [[reservoir aggregate]], [[planting]] and a finishing surface layer of [[mulch]] and/or [[stone]]. | |
| Additional components include an [[underdrain]] to remove excess water and soil additives to enhance [[Nutrients|pollutant removal]]. <br>
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| Design and operation and maintenance program assumptions used to generate cost estimates are based on tool default values and the following STEP recommendations: | | Design and operation and maintenance program assumptions used to generate cost estimates are based on tool default values and the following STEP recommendations: |
| * Native soil infiltration rates for Full, Partial and No Infiltration Design scenarios were assumed to be 20 mm/h, 10 mm/h and 2 mm/h, respectively, and a safety factor of 2.5 was applied to calculate the design infiltration rate. | | * Native soil infiltration rates for Full, Partial and No Infiltration Design scenarios were assumed to be 20 mm/h, 10 mm/h and 2 mm/h, respectively, and a safety factor of 2.5 was applied to calculate the design infiltration rate. |
| * Operation and maintenance (O&M) cost estimates assume annual inspections, removal of trash and debris twice a year, removal of sediment from pretreatment structures annually, and removal of weeds twice a year (where applicable). Verification inspections are included every 5 years to confirm adequate maintenance, and every 15 years to confirm adequate drainage performance through in-situ surface infiltration rate testing (where applicable) | | * Operation and maintenance (O&M) cost estimates assume annual inspections, removal of trash and debris twice a year, removal of sediment from pretreatment structures annually, and removal of weeds twice a year (where applicable). Verification inspections are included every 5 years to confirm adequate maintenance, and every 15 years to confirm adequate drainage performance through in-situ surface infiltration rate testing (where applicable) |
| *Maximum impervious drainage area to permeable surface area (I:P area) ratio of 20:1. | | * Designed with an impervious drainage area to treatment facility area ratio of between 5:1 and a maximum of 20:1. |
| * Length to width ratio of bioretention area is 10:1. | | * Length to width ratio of infiltration trench area recommended from facilities receiving road or parking lot runoff is 10:1. |
| * Default filter media depth of 1.0 metres to accommodate trees in planting plan. | | * Should be set back at least four (4) metres from building foundations. |
| * Default mulch depth of 75 millimetres. | | * Overflow pipes should discharge to pervious areas located at least 2m from building foundations and slope away from building or to a storm sewer. |
| * An underdrain (200 mm diameter perforated pipe) is included in Partial Infiltration and No Infiltration design configurations only. | | * Default filter media depth of 1.0 metres to accommodate trees in planting plan. |
| | * Trench bottom width is generally between 0.60 and 2.4 metres. |
| | * Default maximum depth of 3 - 4 metres, as there are cost implications with using trench boxes to retain the side walls. |
| | * An underdrain (300 mm diameter perforated pipe) is included in Partial Infiltration & Full Infiltration design configurations. |
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| ===Notes=== | | ===Notes=== |
| * Designs include [[pretreatment]] through stone diaphragms at [[Curb cuts|curb inlets]] and two inlet structure sumps (Rain Guardian bunkers). | | * Designs include [[pretreatment]] through hydrodynamic separator ([[Oil and Grit Separator]]). |
| * Operation and maintenance cost estimates assume rehabilitation of the filter media bed surface is required after 25 years of operation. | | * Operation and maintenance cost estimates assume rehabilitation of the filter media bed surface is required after 25 years of operation. |
| * The tool calculates costs for new (greenfield) development contexts and includes costs for contractor overhead and profit, material, delivery, labour, equipment (rental, operating and operator costs), hauling and disposal. | | * The tool calculates costs for new (greenfield) development contexts and includes costs for contractor overhead and profit, material, delivery, labour, equipment (rental, operating and operator costs), hauling and disposal. |