Difference between revisions of "Infiltration Trench: Life Cycle Costs"

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==Overview==
 
==Overview==
[[Infiltration trenches]] (also referred to as ‘infiltration galleries’) are design variations that consist of linear, rectangular or trapezoidal shape, with a bottom generally between 0.6 and 2.4 m wide. Linear trench geometries will drain faster than round or square shapes due to their larger perimeters. These geotextile-lined excavation facilities should have a nearly level or gently sloping bottom grade to spread flow evenly. Similar to soakaways, they are also filled with [[stone]] or other void-forming structures. They are well suited to sites where available space for infiltration is limited to strips of land between buildings or properties, or along road right-of-ways.  
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[[Infiltration trenches]] typically consist of linear-oriented, rectangular- or trapezoidal-shaped trench excavations between 0.6 and 2.4 m wide that are lined with geotextile, backfilled with clear stone aggregate and located underground. They are well suited to sites where available space for infiltration is limited to strips of land between buildings or properties, or along road right-of-ways. Trench depth is determined by the infiltration rate of the underlying native soil and maximum acceptable time to fully drain the facility (i.e., drainage time). STEP has prepared life cycle costs estimates for infiltration trenches located on highly permeable native soil (Full Infiltration design), and moderately permeable native soil (Partial Infiltration design) scenarios for comparison.  Cost estimates for both design scenarios are based on a 2,000 m<sup>2</sup> asphalt drainage area, runoff control target of 25 mm depth and 72 hour drainage period, which can be viewed below. To generate your own life cycle cost estimates customized to the development context, design criteria, and constraints applicable to your site, access the updated [https://sustainabletechnologies.ca/lid-lcct/ LID Life Cycle Costing Tool (LCCT) here].
STEP has prepared life cycle costs estimates for each design configuration, based on a 2,000 m<sup>2</sup> road drainage area, runoff control target of 25 mm depth and 72 hour drainage period, for comparison which can be viewed below. To generate your own life cycle cost estimates customized to the development context, design criteria, and constraints applicable to your site, access the updated [https://sustainabletechnologies.ca/lid-lcct/ LID Life Cycle Costing Tool (LCCT) here].
 
  
 
==Design Assumptions==
 
==Design Assumptions==
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 [[aggregates]] (to bed the pipe, store and redistribute water), [[underdrain|perforated pipe or underdrains]] and [[geotextile]]. <br>
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Infiltration trenches are an ideal technology for installing below any type of landscape with requirements to infiltrate excess stormwater while safely conveying excess flows during major storm events. Components include: reservoir [[aggregates| aggregate]] to store runoff water, perforated pipe to deliver and distribute flow to the trench, [[geotextile]], [[Inlets|inlet structures]], [[Pretreatment| pretreatment devices or features]] and [[Wells| monitoring wells]] to track drainage performance of the facility over its operating lifespan. Optional components include a flow restrictor to control the release rate of the facility, and surface drains to safely convey flows in excess of the storage capacity of the design.<br>
  
 
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.  
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* Native soil infiltration rates for Full, and Partial Infiltration Design scenarios were assumed to be 20 mm/h and 10 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. Verification inspections are included every 5 years to confirm adequate maintenance, and every 15 years to confirm adequate drainage performance through in-situ trench water level monitoring during natural storm events.
* Designed with an impervious drainage area to treatment facility area ratio of between 5:1 and a maximum of 20:1.
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* Trench width of 2.0 metres.
* Length to width ratio of infiltration trench area recommended from facilities receiving road or parking lot runoff is 10:1.
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* Maximum impervious drainage area to permeable surface area (I:P area) ratio of 20:1.
* Should be set back at least four (4) metres from building foundations.
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* Trench depth of 580 mm and surface area of 198.73 m<sup>2</sup> (I:P area ratio of 10:1) on 20 mm/h native soil (Full Infiltration Design)
* Overflow pipes should discharge to pervious areas located at least 2m from building foundations and slope away from building or to a storm sewer.
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* Trench depth of 290 mm and surface area of 366.58 m<sup>2</sup> (I:P area ratio of 5.5:1) on 10 mm/h native soil (Partial Infiltration Design)
* 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.
 
  
 
===Notes===
 
===Notes===
* Designs include [[pretreatment]] through hydrodynamic separator ([[Oil and Grit Separator]]).
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* Designs include [[pretreatment]] through two (2) hydrodynamic separators (i.e., [[Oil and Grit Separator| oil and grit separators]]) located upstream of trench inlets, and two (2) 150 mm diameter monitoring wells per trench.
 
* 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.  
 
** Land value and equipment mobilization and demobilization costs are not included, assuming BMP construction is part of overall development site construction.
 
** Land value and equipment mobilization and demobilization costs are not included, assuming BMP construction is part of overall development site construction.
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==Construction Costs==
 
==Construction Costs==
  
[[File:ConstructionTable InfilTrench Full Infil.PNG|thumb|left|615px|'''Construction Costs Per Unit Drainage Area (CAD$/m<sup>2</sup>) - Full Infiltration Design, 25 mm Treatment''']]
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[[File:ConstructionTable InfilTrench Full Infil 2023.PNG|thumb|left|615px|'''Construction Costs Per Unit Drainage Area (CAD$/m<sup>2</sup>) - Full Infiltration Design, 25 mm Retention''']]
  
 
[[File:ConstructionTable InfilTrench Partial Infil.PNG|thumb|center|615px|'''Construction Costs Per Unit Drainage Area (CAD$/m<sup>2</sup>) - Partial Infiltration Design, 25 mm Retention''']]
 
[[File:ConstructionTable InfilTrench Partial Infil.PNG|thumb|center|615px|'''Construction Costs Per Unit Drainage Area (CAD$/m<sup>2</sup>) - Partial Infiltration Design, 25 mm Retention''']]
  
  
<small>'''Note:''' Please click on each image to enlarge to view associated construction cost estimates.</small><br>
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<small>'''Note:''' Click on each image to enlarge to view associated construction cost estimates.</small><br>
  
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Above you can find breakdowns of construction costs by expense type for each infiltration trench design scenario:<br>
  
Above you can find a cost breakdown of a 1000m<sup>2</sup> in two different configurations:<br>
 
 
#[[Infiltration trenches|Infiltration Trench: Full Infiltration]]  
 
#[[Infiltration trenches|Infiltration Trench: Full Infiltration]]  
 
#[[Infiltration trenches|Infiltration Trench: Partial Infiltration]]
 
#[[Infiltration trenches|Infiltration Trench: Partial Infiltration]]
  
As can be seen, regardless of design configuration, Material & Installation expenses represent the largest portion of total construction costs (75 to 76%).
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As can be seen, regardless of design configuration, Material & Installation expenses represent the largest portion of total construction costs (76%).
  
 
==Life Cycle Costs==
 
==Life Cycle Costs==
Below are capital and life cycle cost estimates for the two [[Infiltration trenches|infiltration trench]] configurations over 25- and 50-year time periods. The estimates of maintenance and rehabilitation (life cycle) costs represent net present values. Operation and maintenance costs are predicted to represent 38% of total life cycle costs over the 25-year evaluation period, and increase to 51% of total life cycle costs over the 50-year period, due to increased levels of litter removal, replacement of filter cloth and disposal of collected sediment (every 4 - 8 years), cleaning out the catchbasin and the [[Oil and Grit Separator|Oil and Grit Separator/Hydrodynamic Separator]] annually, as well as flushing the internal pipes every 10 years.  
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Below are capital and life cycle cost estimates for the two [[Infiltration trenches|infiltration trench]] configurations over 25- and 50-year time periods. The estimates of maintenance and rehabilitation (life cycle) costs represent net present values. Operation and maintenance costs are predicted to represent 39% of total life cycle costs over the 25-year evaluation period, and increase to 52% of total life cycle costs over the 50-year period, due flushing of inlet, distribution and outlet pipes every 10 years.  
  
  
 
===25-Year life cycle cost break down===
 
===25-Year life cycle cost break down===
  
[[File:25yr LCCT InfilTrench Full Infil.PNG|thumb|left|615px|'''Infiltration Trench: Full Infiltration''']]
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[[File:25yr LCCT InfilTrench Full Infil 2023.PNG|thumb|left|615px|'''Infiltration Trench: Full Infiltration''']]
  
[[File:25yr LCCT InfilTrench Partial Infil.PNG|thumb|center|615px|'''Infiltration Trench: Partial Infiltration''']]
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[[File:25yr LCCT InfilTrench Partial Infil 2023.PNG|thumb|center|615px|'''Infiltration Trench: Partial Infiltration''']]
  
  
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===50-Year life cycle cost break down===
 
===50-Year life cycle cost break down===
  
[[File:50yr LCCT InfilTrench Full Infil.PNG|thumb|left|615px|'''Infiltration Trench: Full Infiltration''']]
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[[File:50yr LCCT InfilTrench Full Infil 2023.PNG|thumb|left|615px|'''Infiltration Trench: Full Infiltration''']]
  
[[File:50yr LCCT InfilTrench Partial Infil.PNG|thumb|center|615px|'''Infiltration Trench: Partial Infiltration''']]
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[[File:50yr LCCT InfilTrench Partial Infil 2023.PNG|thumb|center|615px|'''Infiltration Trench: Partial Infiltration''']]
  
  
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==Cost Summary Tables==
 
==Cost Summary Tables==
Total life cycle cost estimates for the two [[Infiltration trenches|infiltration trench]] configurations vary substantially with the [[Infiltration trenches|Infiltration Trench: Partial Infiltration]] design being highest ($85,288.88), followed closely by the [[Infiltration trenches|Infiltration Trench: Full Infiltration]] design being ($69,805.90).<br>
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Total life cycle cost estimates over the 50 year evaluation period for the two [[Infiltration trenches|infiltration trench]] design configurations vary substantially with the [[Infiltration trenches|Infiltration Trench: Partial Infiltration]] design being highest ($183.197.71), followed closely by the [[Infiltration trenches|Infiltration Trench: Full Infiltration]] design being ($150,128.87).<br>
  
 
It is notable that a sensitivity analysis was conducted in 2019 to compare construction cost estimates generated by the tool to actual costs of implemented projects. '''The analysis found that tool estimates were typically within ±14% of actual construction costs'''<ref>Credit Vally Conservation (CVC). 2019. Life-cycle costing tool 2019 update: sensitivity analysis. Credit Valley Conservation, Mississauga, Ontario. https://sustainabletechnologies.ca/app/uploads/2020/04/LCCT-Sensitivity-Analysis_March2020.pdf</ref>
 
It is notable that a sensitivity analysis was conducted in 2019 to compare construction cost estimates generated by the tool to actual costs of implemented projects. '''The analysis found that tool estimates were typically within ±14% of actual construction costs'''<ref>Credit Vally Conservation (CVC). 2019. Life-cycle costing tool 2019 update: sensitivity analysis. Credit Valley Conservation, Mississauga, Ontario. https://sustainabletechnologies.ca/app/uploads/2020/04/LCCT-Sensitivity-Analysis_March2020.pdf</ref>
  
 
===Full Infiltration===
 
===Full Infiltration===
[[File:North Dakota State U infiltration trench.jpg|800px|thumb|Good use of geotextile, being limited to preventing fines from entering the trench from above. Read more about the performance of this feature in comparison to [[bioretention]]] BMPs in Vaughan, ON. (Source: STEP, 2016<ref>Performance Comparison of Surface and Underground Stormwater Infiltration Practices - TECHNICAL BRIEF. Low Impact Development Series. https://sustainabletechnologies.ca/app/uploads/2016/08/BioVSTrench_TechBrief__July2015.pdf</ref>)]]
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[[File:North Dakota State U infiltration trench.jpg|thumb|1000px|Good use of geotextile, being limited to preventing fines from entering the trench from above. Read about the performance of infiltration trenches in comparison to [[bioretention]]. (Source: STEP, 2016<ref>Performance Comparison of Surface and Underground Stormwater Infiltration Practices - TECHNICAL BRIEF. Low Impact Development Series. https://sustainabletechnologies.ca/app/uploads/2016/08/BioVSTrench_TechBrief__July2015.pdf</ref>)]]
  
[[File:Design Table InfilTrench Full Infil.PNG|700px]]<br>
+
[[File:Design Table InfilTrench Full Infil 2023.PNG|700px]]<br>
 
</br>
 
</br>
 +
 
===Partial Infiltration===
 
===Partial Infiltration===
[[File:Design Table InfilTrench Partial Infil.PNG|700px]]<br>
+
[[File:Design Table InfilTrench Partial Infil 2023.PNG|700px]]<br>
 
</br>
 
</br>
  
 
==References==
 
==References==

Latest revision as of 20:50, 17 January 2023

Infiltration trench located at the Honda Campus, Markham, ON. Read about the performance of this practice in the technical brief (Source: STEP, 2015)[1].


Overview[edit]

Infiltration trenches typically consist of linear-oriented, rectangular- or trapezoidal-shaped trench excavations between 0.6 and 2.4 m wide that are lined with geotextile, backfilled with clear stone aggregate and located underground. They are well suited to sites where available space for infiltration is limited to strips of land between buildings or properties, or along road right-of-ways. Trench depth is determined by the infiltration rate of the underlying native soil and maximum acceptable time to fully drain the facility (i.e., drainage time). STEP has prepared life cycle costs estimates for infiltration trenches located on highly permeable native soil (Full Infiltration design), and moderately permeable native soil (Partial Infiltration design) scenarios for comparison. Cost estimates for both design scenarios are based on a 2,000 m2 asphalt drainage area, runoff control target of 25 mm depth and 72 hour drainage period, which can be viewed below. To generate your own life cycle cost estimates customized to the development context, design criteria, and constraints applicable to your site, access the updated LID Life Cycle Costing Tool (LCCT) here.

Design Assumptions[edit]

Infiltration trenches are an ideal technology for installing below any type of landscape with requirements to infiltrate excess stormwater while safely conveying excess flows during major storm events. Components include: reservoir aggregate to store runoff water, perforated pipe to deliver and distribute flow to the trench, geotextile, inlet structures, pretreatment devices or features and monitoring wells to track drainage performance of the facility over its operating lifespan. Optional components include a flow restrictor to control the release rate of the facility, and surface drains to safely convey flows in excess of the storage capacity of the design.

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, and Partial Infiltration Design scenarios were assumed to be 20 mm/h and 10 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. Verification inspections are included every 5 years to confirm adequate maintenance, and every 15 years to confirm adequate drainage performance through in-situ trench water level monitoring during natural storm events.
  • Trench width of 2.0 metres.
  • Maximum impervious drainage area to permeable surface area (I:P area) ratio of 20:1.
  • Trench depth of 580 mm and surface area of 198.73 m2 (I:P area ratio of 10:1) on 20 mm/h native soil (Full Infiltration Design)
  • Trench depth of 290 mm and surface area of 366.58 m2 (I:P area ratio of 5.5:1) on 10 mm/h native soil (Partial Infiltration Design)

Notes[edit]

  • Designs include pretreatment through two (2) hydrodynamic separators (i.e., oil and grit separators) located upstream of trench inlets, and two (2) 150 mm diameter monitoring wells per trench.
  • 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.
    • Land value and equipment mobilization and demobilization costs are not included, assuming BMP construction is part of overall development site construction.
    • Design and Engineering cost estimates are not calculated by the tool and must be supplied by the user.
    • The tool adds 10% contingency and additional overhead as default.
  • All cost estimates are in Canadian dollars and represent the net present value (NPV) as the tool takes into account average annual interest and discount rates over the 25 and 50 year operating life cycle periods.
  • Unit costs are based on 2018 RSMeans standard union pricing.
  • Additional costs associated with retrofit or redevelopment contexts is assumed to be 16% of the cost estimate for new (greenfield) construction contexts.
    • Retrofit construction cost estimates are included in the 'Costs Summary' section for comparison.

Construction Costs[edit]

Construction Costs Per Unit Drainage Area (CAD$/m2) - Full Infiltration Design, 25 mm Retention
Construction Costs Per Unit Drainage Area (CAD$/m2) - Partial Infiltration Design, 25 mm Retention


Note: Click on each image to enlarge to view associated construction cost estimates.

Above you can find breakdowns of construction costs by expense type for each infiltration trench design scenario:

  1. Infiltration Trench: Full Infiltration
  2. Infiltration Trench: Partial Infiltration

As can be seen, regardless of design configuration, Material & Installation expenses represent the largest portion of total construction costs (76%).

Life Cycle Costs[edit]

Below are capital and life cycle cost estimates for the two infiltration trench configurations over 25- and 50-year time periods. The estimates of maintenance and rehabilitation (life cycle) costs represent net present values. Operation and maintenance costs are predicted to represent 39% of total life cycle costs over the 25-year evaluation period, and increase to 52% of total life cycle costs over the 50-year period, due flushing of inlet, distribution and outlet pipes every 10 years.


25-Year life cycle cost break down[edit]

Infiltration Trench: Full Infiltration
Infiltration Trench: Partial Infiltration


Note: Click on each image to enlarge to view associated life cycle cost estimate.

50-Year life cycle cost break down[edit]

Infiltration Trench: Full Infiltration
Infiltration Trench: Partial Infiltration


Note: Click on each image to enlarge to view associated life cycle cost estimate.

Cost Summary Tables[edit]

Total life cycle cost estimates over the 50 year evaluation period for the two infiltration trench design configurations vary substantially with the Infiltration Trench: Partial Infiltration design being highest ($183.197.71), followed closely by the Infiltration Trench: Full Infiltration design being ($150,128.87).

It is notable that a sensitivity analysis was conducted in 2019 to compare construction cost estimates generated by the tool to actual costs of implemented projects. The analysis found that tool estimates were typically within ±14% of actual construction costs[2]

Full Infiltration[edit]

Good use of geotextile, being limited to preventing fines from entering the trench from above. Read about the performance of infiltration trenches in comparison to bioretention. (Source: STEP, 2016[3])

Design Table InfilTrench Full Infil 2023.PNG

Partial Infiltration[edit]

Design Table InfilTrench Partial Infil 2023.PNG

References[edit]

  1. Hydrologic Assessment of LID Honda Campus, Markham, ON - TECHNICAL BRIEF. Accessed Dec 19 2022. https://sustainabletechnologies.ca/app/uploads/2015/07/Honda_TechBrief_July2015.pdf
  2. Credit Vally Conservation (CVC). 2019. Life-cycle costing tool 2019 update: sensitivity analysis. Credit Valley Conservation, Mississauga, Ontario. https://sustainabletechnologies.ca/app/uploads/2020/04/LCCT-Sensitivity-Analysis_March2020.pdf
  3. Performance Comparison of Surface and Underground Stormwater Infiltration Practices - TECHNICAL BRIEF. Low Impact Development Series. https://sustainabletechnologies.ca/app/uploads/2016/08/BioVSTrench_TechBrief__July2015.pdf