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[[File:Cover Photo.PNG|thumb|750px|Inspection & Maintenance Guidance of vegetated stormwater best management practices that temporarily store rainwater and snowmelt from roofs, pavement, parking lots, etc. in depressed planting beds, concrete planters or swales. [[Acknowledgements|TRCA, 2016]]<ref> TRCA. 2016. Fact Sheet - Inspection and Maintenance of Stormwater Best Management Practices: Bioretention. https://sustainabletechnologies.ca/app/uploads/2018/02/Bioretention-and-Dry-Swales-Fact-Sheet.pdf</ref>]]
[[File:Cover Photo.PNG|thumb|750px|link=https://sustainabletechnologies.ca/app/uploads/2018/02/Bioretention-and-Dry-Swales-Fact-Sheet.pdf|Inspection & Maintenance Guidance of vegetated stormwater best management practices that temporarily store rainwater and snowmelt from roofs, pavement, parking lots, etc. in depressed planting beds, concrete planters or swales (TRCA, 2016)<ref> TRCA. 2016. Fact Sheet - Inspection and Maintenance of Stormwater Best Management Practices: Bioretention. https://sustainabletechnologies.ca/app/uploads/2018/02/Bioretention-and-Dry-Swales-Fact-Sheet.pdf</ref>]]


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==Overview==
==Overview==
[[Bioretention]] treats stormwater by slowing it down, filtering it through soil and plant roots, soaking it into the ground and evaporating it back to the atmosphere. Runoff water is delivered to the practice through [[inlet]]s such as [[curb cuts]], [[Curb cuts: Gallery|spillways]] or other concrete structures, sheet flow from pavement edges, or [[pipes]] connected to [[Pretreatment|catchbasins]] or [[Downspout disconnection|roof downspouts]]. The planting bed and side slopes are typically covered with a mixture of [[plants]], [[mulch]] and [[stone]]. Water in excess of its storage capacity overflows to another BMP or the municipal storm sewer. Filtered water is either infiltrated into the underlying soil to replenish groundwater, or collected by a [[Underdrain|sub-drain]] (i.e., underground perforated pipe) and discharged to the storm sewer system or another BMP. Depending on the permeability of the underlying soil or other constraints, it may be designed with no sub-drain for [[Bioretention: Full infiltration|full infiltration]], with a sub-drain for [[Bioretention: Partial infiltration|partial infiltration]], or with an impermeable liner and sub-drain for a [[Stormwater Tree Trenches|no infiltration practice]]. The sub-drain pipe may feature a flow restrictor (e.g., orifice cap or valve) for gradually releasing detained water and optimizing the amount drained by infiltration. Key components of bioretention practices for inspection and maintenance described further below.
[[Bioretention]] treats stormwater by slowing it down, filtering it through soil and plant roots, soaking it into the ground and evaporating it back to the atmosphere. Runoff water is delivered to the practice through [[inlet]]s such as [[curb cuts]], [[Curb cuts: Gallery|spillways]] or other concrete structures, sheet flow from pavement edges, or [[pipes]] connected to [[Pretreatment|catchbasins]] or [[Downspout disconnection|roof downspouts]]. The planting bed and side slopes are typically covered with a mixture of [[plants]], [[mulch]] and [[stone]]. Water in excess of its storage capacity overflows to another BMP or the municipal storm sewer. Filtered water is either infiltrated into the underlying soil to replenish groundwater, or collected by a [[Underdrain|sub-drain]] (i.e., underground perforated pipe) and discharged to the storm sewer system or another BMP. Depending on the permeability of the underlying soil or other constraints, it may be designed with no sub-drain for [[Bioretention: Full infiltration|full infiltration]], with a sub-drain for [[Bioretention: Partial infiltration|partial infiltration]], or with an impermeable liner and sub-drain for a [[Stormwater planters|no infiltration practice]]. The sub-drain pipe may feature a flow restrictor (e.g., orifice cap or valve) for gradually releasing detained water and optimizing the amount drained by infiltration. Key components of bioretention practices for inspection and maintenance described further below. <br>
</br>
 
{{textbox|Key components of [[bioretention]]/[[bioswales]] to pay close attention to are the:
*[[Inlets]]
*[[Filter media|Filter bed surface]]
*[[Overflow|Overflow outlets]]}}
Trash, debris and sediment builds up at these locations and can prevent water from flowing into or out of the practice.


==Associated Practices==
==Associated Practices==
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*'''[[Stormwater planters|Biofilter]]''': Bioretention cell or swale with an impermeable liner or containment structure and sub-drain.
*'''[[Stormwater planters|Biofilter]]''': Bioretention cell or swale with an impermeable liner or containment structure and sub-drain.
*'''[[Bioswale]] / [[Dry swale]] or [[Bioswale|Bioretention swale]]''': A gently sloping, linear oriented bioretention practice designed to be capable of conveying water across an elevation gradient. Also known as a bioswale or dry swale.
*'''[[Bioswale]] / [[Dry swale]] or [[Bioswale|Bioretention swale]]''': A gently sloping, linear oriented bioretention practice designed to be capable of conveying water across an elevation gradient. Also known as a bioswale or dry swale.
*'''[[Stormwater Tree Trenches]]''': Linear tree planting structures that feature supported impermeable or permeable pavements that promote healthy tree growth while also helping to manage runoff. Consist of subsurface trenches filled with modular structures and growing medium, or structurally engineered soil medium, supporting the overlying sidewalk.


==Inspection and Testing Framework==
==Inspection and Testing Framework==


{| class="wikitable" style="width: 1000px;"
[[File:Visual indicator bioretention.PNG|thumb|300px|Example of a visual indicator to be used when assessing the condition of a given LID feature. Here we see excessive sediment accumulation at the [[inlet]]/[[curb cut]] of a bioretention cell. Source: (TRCA, 2016).<ref>STEP. 2016. Low Impact Development Stormwater Management Practice Inspection and Maintenance Guide. https://sustainabletechnologies.ca/app/uploads/2016/08/LID-IM-Guide-2016-1.pdf</ref>.]]
|+'''Inspection and Testing Framework - Bioretention/Swales'''
{| class="wikitable" style="width: 900px;"
|+'''Visual Indicators Framework - Bioretention/Swales'''
|-
|-
!<br>'''Component'''
!<br>'''Component'''
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!<br>'''Verification Inspection'''
!<br>'''Verification Inspection'''
|-
|-
|rowspan="23"|'''Visual Indicators'''
|rowspan="2"|'''[[Bioretention: Sizing|Contributing Drainage Area]]'''
|-
|-
|CDA condition  
|CDA condition  
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|x
|x
|x
|x
|-
|rowspan="5"|'''[[Inlets|Inlet]]'''
|-
|-
|Inlet/Flow Spreader Structural Integrity
|Inlet/Flow Spreader Structural Integrity
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|x
|x
|
|
|-
|rowspan="4"|'''Perimeter'''
|-
|-
|BMP dimensions
|BMP dimensions
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|
|
|x
|x
|-
|rowspan="9"|'''[[Bioretention: Filter media|Filter Bed]]'''
|-
|-
|Standing water  
|Standing water  
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|x
|x
|x
|x
|-
|rowspan="4"|'''[[Vegetation|Planting Area]]'''
|-
|-
|Vegetation cover
|Vegetation cover
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|x
|x
|
|
|-
|rowspan="4"|'''[[Overflow|Outlet]]'''
|-
|-
|Monitoring well condition
|Monitoring well condition
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|x
|x
|x
|x
|-
|}<br>
</br>
[[File:Soil testing indicators.PNG|thumb|300px|The image above shows a manual soil corer, a split soil core sampler kit which preserves the soil sample for further testing (i.e., bulk density) and acrylic core sample tubes. All examples of tools to be use for soil characterization testing. Source: (TRCA, 2016).<ref>STEP. 2016. Low Impact Development Stormwater Management Practice Inspection and Maintenance Guide. https://sustainabletechnologies.ca/app/uploads/2016/08/LID-IM-Guide-2016-1.pdf</ref>.]]
{| class="wikitable" style="width: 900px;"
|+'''Testing Indicators Framework - Bioretention/Swales'''
|-
!<br>'''Component'''
!<br>'''Indicators'''
!<br>'''Construction Inspection'''
!<br>'''Assumption Inspection'''
!<br>'''Routine Operation Inspection'''
!<br>'''Verification Inspection'''
|-
|-
|rowspan="6"|'''Testing Indicators'''
|rowspan="6"|'''Testing Indicators'''
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==Construction Inspection Tasks==
==Construction Inspection Tasks==
[[File:LID-IM small.jpg|thumb|400px|Performance Inspection of a Rain garden. [https://sustainabletechnologies.ca/home/urban-runoff-green-infrastructure/low-impact-development/low-impact-development-stormwater-practice-inspection-and-maintenance-guide/ Photo source: TRCA].<ref>TRCA. 2019. Low Impact Development Stormwater Inspection and Maintenance Guide. https://sustainabletechnologies.ca/home/urban-runoff-green-infrastructure/low-impact-development/low-impact-development-stormwater-practice-inspection-and-maintenance-guide/</ref>]]
Construction inspections take place during several points in the construction sequence, specific to the type of LID BMP, but at a minimum should be done '''weekly''' and include the following:
Construction inspections take place during several points in the construction sequence, specific to the type of LID BMP, but at a minimum should be done '''weekly''' and include the following:
# During site preparation, prior to BMP excavation and grading to ensure the CDA is stabilized or that adequate ESCs or flow diversion devices are in place and confirm that construction materials meet design specifications
# During site preparation, prior to BMP excavation and grading to ensure the CDA is stabilized or that adequate ESCs or flow diversion devices are in place and confirm that construction materials meet design specifications
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# Prior to hand-off points in the construction sequence when the contractor responsible for the work changes (i.e., hand-offs between the storm sewer servicing, paving, building and landscaping contractors)
# Prior to hand-off points in the construction sequence when the contractor responsible for the work changes (i.e., hand-offs between the storm sewer servicing, paving, building and landscaping contractors)
# After every large storm event (e.g., 15 mm rainfall depth or greater) to ensure [https://sustainabletechnologies.ca/app/uploads/2020/01/ESC-Guide-for-Urban-Construction_FINAL.pdf Erosion Sediment Controls (ESCs)] and pretreatment or flow diversion devices are functioning and adequately maintained. View the table below, which describes critical points during the construction sequence when inspections should be performed prior to proceeding further. You can also download and print the table [https://wikidev.sustainabletechnologies.ca/images/7/7f/Construction_Inspection.pdf '''here''']<br>
# After every large storm event (e.g., 15 mm rainfall depth or greater) to ensure [https://sustainabletechnologies.ca/app/uploads/2020/01/ESC-Guide-for-Urban-Construction_FINAL.pdf Erosion Sediment Controls (ESCs)] and pretreatment or flow diversion devices are functioning and adequately maintained. View the table below, which describes critical points during the construction sequence when inspections should be performed prior to proceeding further. You can also download and print the table [https://wikidev.sustainabletechnologies.ca/images/7/7f/Construction_Inspection.pdf '''here''']<br>
</br>
[[File:LID-IM small.jpg|thumb|500px|Performance Inspection of a Rain garden. [https://sustainabletechnologies.ca/home/urban-runoff-green-infrastructure/low-impact-development/low-impact-development-stormwater-practice-inspection-and-maintenance-guide/ Photo source: TRCA].<ref>TRCA. 2019. Low Impact Development Stormwater Inspection and Maintenance Guide. https://sustainabletechnologies.ca/home/urban-runoff-green-infrastructure/low-impact-development/low-impact-development-stormwater-practice-inspection-and-maintenance-guide/</ref>]]
{| class="wikitable" style="width: 1000px;"
{| class="wikitable" style="width: 1000px;"
|+'''Bioretention/Swales: Construction Inspections'''<br>
|+'''Bioretention/Swales: Construction Inspections'''
</br>
|-
|-
!<br>'''Construction Sequence Step & Timing'''
!<br>'''Construction Sequence Step & Timing'''
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Table below describes routine maintenance tasks for [[bioretention]] practices, organized by BMP component, along with recommended minimum frequencies. It also suggests higher frequencies for certain tasks that may be warranted for BMPs located in highly visible locations or those receiving flow from high traffic areas (vehicle or pedestrian). Tasks involving removal of trash, debris and sediment and weeding/trimming of [[vegetation]] for BMPs in such contexts may need to be done more frequently (i.e., higher standards may be warranted).
Table below describes routine maintenance tasks for [[bioretention]] practices, organized by BMP component, along with recommended minimum frequencies. It also suggests higher frequencies for certain tasks that may be warranted for BMPs located in highly visible locations or those receiving flow from high traffic areas (vehicle or pedestrian). Tasks involving removal of trash, debris and sediment and weeding/trimming of [[vegetation]] for BMPs in such contexts may need to be done more frequently (i.e., higher standards may be warranted).


Individuals conducting [[vegetation]] maintenance and in particular, weeding (i.e., removal of undesirable vegetation), should be familiar with the species of [[Plants lista|plants]] specified in the planting plan and experienced in plant identification and methods of removing/controlling noxious weeds. Key resources on these topics are provided below at the links provided:
Individuals conducting [[vegetation]] maintenance and in particular, weeding (i.e., removal of undesirable vegetation), should be familiar with the species of [[Plant lists|plants]] specified in the planting plan and experienced in plant identification and methods of removing/controlling noxious weeds. Key resources on these topics are provided below at the links provided:
*[http://www.weedinfo.ca/en/ Agriculture and Agri-food Canada’s Weed Info database]
*[http://www.weedinfo.ca/en/ Agriculture and Agri-food Canada’s Weed Info database]
*[http://www.omafra.gov.on.ca/english/crops/facts/ontweeds/weedgal.htm Ontario Ministry of Agriculture, Food and Rural Affairs’ Ontario Weed Gallery]
*[http://www.omafra.gov.on.ca/english/crops/facts/ontweeds/weedgal.htm Ontario Ministry of Agriculture, Food and Rural Affairs’ Ontario Weed Gallery]
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*[http://www.agrifs.ir/sites/default/files/Weeds%20of%20North%20America%20%7BRichard%20Dickinson%7D%20%5B9780226076447%5D%20%282014%29_2.pdf Weeds of North America (book), 2014, by Richard Dickinson and France Royer, University of Chicago Press, 656 pgs.]
*[http://www.agrifs.ir/sites/default/files/Weeds%20of%20North%20America%20%7BRichard%20Dickinson%7D%20%5B9780226076447%5D%20%282014%29_2.pdf Weeds of North America (book), 2014, by Richard Dickinson and France Royer, University of Chicago Press, 656 pgs.]


{|class="wikitable" style="width: 1000px;"
{|class="wikitable" style="width: 1280px"
|+'''Bioretention/Swales: Key Components, Descriptions and Routine I&M Requriements'''
|+'''Bioretention/Swales: Key Components, Descriptions and Routine I&M Requirements'''
|-
|-
!Component
!style="width: 500px"|Comnponent
!Description
!style="width: 1500px"|Description  
!Inspection & Maintenance Tasks
!style="width: 1500px"|Inspection & Maintenance Tasks
!style="width: 500px"|<span style="color:green">('''Pass''')</span> Photo Example
!style="width: 550px"|<span style="color:red">('''Fail''')</span> Photo Example
|-
|-
|'''[[Bioretention: Sizing|Contributing Drainage Area (CDA)]]'''
|'''[[Bioretention: Sizing|Contributing Drainage Area (CDA)]]'''
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*Remove trash, debris and sediment from pavements (biannually to quarterly) and eavestroughs (annually);
*Remove trash, debris and sediment from pavements (biannually to quarterly) and eavestroughs (annually);
*Replant or seed bare soil areas as needed.
*Replant or seed bare soil areas as needed.
|[[File:Pass.PNG|300px|thumb|center|CDA has not changed in size or land cover. Sediment, trash or debris is not accumulating and point sources of contaminants are not visible.]]
|[[File:Fail bio.PNG|280px|thumb|center|Size of the CDA has changed from design assumptions. A point source for contaminants is visible (i.e. lack of sediment controls on adjacent construction site). (Photo Source: North Carolina Cooperative Extension)]]
|-
|-
|'''[[Pretreatment]]'''
|'''[[Pretreatment]]'''
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*Remove trash, debris and sediment annually to biannually or when the device sump is half full;
*Remove trash, debris and sediment annually to biannually or when the device sump is half full;
*Measure sediment depth or volume during each cleaning, or annually to estimate accumulation rate and optimize frequency of maintenance
*Measure sediment depth or volume during each cleaning, or annually to estimate accumulation rate and optimize frequency of maintenance
|[[File:Pretreatment pass bio.PNG|310px|thumb|center|[[Forebay]] is free of sediment, trash and debris and recently maintained. The large stones in the feature are used to slow down and spread out inflowing water into the feature and they remain well arranged and in place.]]
|[[File:Pretreatment fail bio.PNG|290px|thumb|center|An erosion gully occurring where bare soil is starting to become visible on the [[Vegetated filter strips|grass filter strip]] pretreatment feature at the inlet, thus indicating it is not effectively slowing and spreading out the inflow of stormwater to the BMP.]]
|-
|-
|'''[[Inlets]]'''
|'''[[Inlets]]'''
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*Measure sediment depth or volume during each cleaning or annually to estimate accumulation rate and optimize frequency of maintenance;
*Measure sediment depth or volume during each cleaning or annually to estimate accumulation rate and optimize frequency of maintenance;
*Remove woody [[vegetation]] from filter bed at [[inlets]] annually.
*Remove woody [[vegetation]] from filter bed at [[inlets]] annually.
|[[File:Inlets bio pass.PNG|285px|thumb|center|There is no evidence of damage or displacement of the inlet structure that would prevent runoff from freely entering the BMP.]]
|[[File:Inlets bio fail.PNG|300px|thumb|center|Accumulated sediment and vegetation is preventing stormwater from entering the BMP. Sediment on the pavement surface in front of the inlet indicates ponding is also occurring]]
|-
|-
|'''Perimeter'''
|'''Perimeter'''
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*Confirm the surface ponding footprint area dimensions are within ±10% of the design and that maximum surface ponding depth meets design specifications;
*Confirm the surface ponding footprint area dimensions are within ±10% of the design and that maximum surface ponding depth meets design specifications;
*Check for side slope erosion or damage that compromises water storage capacity
*Check for side slope erosion or damage that compromises water storage capacity
|[[File:Perimeter bio pass.PNG|305px|thumb|center|The footprint area of the bioretention cell does not significantly deviate from the final design and should not negatively affect its stormwater management treatment performance.]]
|[[File:Perimeter bio fail.PNG|300px|thumb|center|The footprint area of the BMP is significantly smaller than what was specified in the final design of this example and differ greater than the recommended SWM criteria requirements (>10%).]]
|-
|-
|'''[[Bioretention: Construction checklist|Filter Bed]]'''
|'''[[Bioretention: Construction checklist|Filter Bed]]'''
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*Repair sunken areas when ≥ 10 cm deep and barren/eroded areas when ≥ 30 cm long;
*Repair sunken areas when ≥ 10 cm deep and barren/eroded areas when ≥ 30 cm long;
*Remove sediment when > 5 cm deep or time to drain water ponded on the surface exceeds 48 hours.
*Remove sediment when > 5 cm deep or time to drain water ponded on the surface exceeds 48 hours.
|[[File:Filter bed bio pass.PNG|295px|thumb|center|There are no erosion gullies or bare soil areas on the filter bed surface and mulch cover remains in place.]]
|[[File:Filter bed bio fail.PNG|300px|thumb|center|Erosion gullies and bare soil areas are present on the filter bed surface, indicating that concentrated flow occurs regularly into the BMP feature. (Photo Source: CVC).]]
|-
|-
|'''[[Vegetation]]'''
|'''[[Vegetation]]'''
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*Replace dead plantings annually to achieve 80% cover by the third growing season;
*Replace dead plantings annually to achieve 80% cover by the third growing season;
*Do not apply chemical fertilizers.  
*Do not apply chemical fertilizers.  
|[[File:Vegetation bio pass.PNG|315px|thumb|center|The planted portion of the bioretention cell is completely covered with dense, attractive vegetation which helps to maintain its stormwater treatment function and aesthetic value.]]
|[[File:Vegetation bio fail .PNG|290px|thumb|center|A larger portion of the bioretention cell has no vegetation cover which reduces its aesthetic value and could be negatively affecting its stormwater treatment function. Much less than 80% of the planting area is covered by living vegetation requiring immediate maintenance and reseeding.]]
|-
|-
|'''[[Overflow|Overflow Outlet]]'''
|'''[[Overflow|Overflow Outlet]]'''
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*Keep free of obstructions;
*Keep free of obstructions;
*Remove trash, debris and sediment biannually to quarterly.
*Remove trash, debris and sediment biannually to quarterly.
|[[File:Overflow bio pass.PNG|320px|thumb|center|The overflow outlet is free of damage and obstruction and functions as originally designed.]]
|[[File:Overflow bio fail.PNG|280px|thumb|center|The overflow outlet is partially obstructed with trash and debris which reduces its capacity to safely convey excess water from the BMP, likely due to excess ponding thus obstructing outflow and impairing overall drainage function of the BMP.]]
|-
|-
|'''[[Underdrain|Sub-drain]]'''
|'''[[Underdrain|Sub-drain]]'''
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*Keep pipe and flow restrictor free of obstructions by flushing annually;
*Keep pipe and flow restrictor free of obstructions by flushing annually;
*Inspect flow restrictor frequently (e.g., biannually to quarterly).
*Inspect flow restrictor frequently (e.g., biannually to quarterly).
|[[File:Underdrain bio pass.PNG|310px|thumb|center|The perforated sub-drain pipe is not obstructed by sediment, debris or roots and shows no signs of damage.]]
|[[File:Underdrain bio fail.PNG|300px|thumb|center|Roots have penetrated the underdrain/sub-drain pipe and are substantially reducing its conveyance capacity. Structural damage, sediment/debris clogs or vegetation roots are visible and are reducing the conveyance capacity of the pipe by one third (33%) or more. (Photo Source: Pipelining Denver)]]
|-
|-
|'''[[Monitoring well]]'''
|'''[[Monitoring well]]'''
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|
|
*[[Wells|Standpipes]] should be securely capped on both ends and remain undamaged.
*[[Wells|Standpipes]] should be securely capped on both ends and remain undamaged.
|[[File:MonitoringWell bio pass.PNG|340px|thumb|center|The well is undamaged and accessible and the cap is in place and secured to prevent unauthorized access.]]
|[[File:MonitoringWell bio fail.PNG|300px|thumb|center|The well standpipe has been damaged by snow plowing, which impairs its use for monitoring and is a safety hazard. With the cap unable to be secured unauthorized access can also occur.]]
|}
|}


==How to Preserve Basic BMP Function==
==Tips to Preserve Basic BMP Function==
*Maintain grading of the filter bed (or [[Vegetated filter strips|grass filter strip]] if present) at [[curb cut]] [[inlets]] so at least 5 cm of the back of the curb is visible through regular sediment removal and regrading.
*Maintain grading of the filter bed (or [[Vegetated filter strips|grass filter strip]] if present) at [[curb cut]] [[inlets]] so at least 5 cm of the back of the curb is visible through regular sediment removal and regrading.
*To avoid over-compaction of the [[Bioretention: Filter media|filter media soil]], any maintenance tasks involving vehicle or foot traffic on the filter bed should not be performed during wet weather.
*To avoid over-compaction of the [[Bioretention: Filter media|filter media soil]], any maintenance tasks involving vehicle or foot traffic on the filter bed should not be performed during wet weather.
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==Rehabilitation & Repair==
==Rehabilitation & Repair==


'''Appendix C - Bad Examples'''
Table below provides guidance on rehabilitation and repair work specific to bioretention and dry swales organized according to BMP component.  
Table below provides guidance on rehabilitation and repair work specific to bioretention and dry swales organized according to BMP component.  
[[File:Sediment removal.PNG|thumb|500px|Technician conducting sediment removal to ensure infiltration rates for the practice are able to maintain > 25 mm/h. [https://sustainabletechnologies.ca/app/uploads/2018/02/Bioretention-and-Dry-Swales-Fact-Sheet.pdf Photo Source: TRCA, 2018]<ref>TRCA. 2018. Inspection and Maintenance of Stormwater Best Management Practices - Bioretention. Fact Sheet. https://sustainabletechnologies.ca/app/uploads/2018/02/Bioretention-and-Dry-Swales-Fact-Sheet.pdf</ref>]]


{|{| class="wikitable" style="width: 1000px;"
{|{| class="wikitable" style="width: 1000px;"
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*Schedule hydro-vac truck or drain-snaking service to clear the obstruction.
*Schedule hydro-vac truck or drain-snaking service to clear the obstruction.
|}
|}
[[File:Sediment removal.PNG|500px]]
<br>
Technician conducting sediment removal to ensure infiltration rates for the<br>
practice are able to maintain > 25 mm/h. [https://sustainabletechnologies.ca/app/uploads/2018/02/Bioretention-and-Dry-Swales-Fact-Sheet.pdf Photo Source: TRCA, 2018]<ref>TRCA. 2018. Inspection and Maintenance of Stormwater Best Management Practices - Bioretention. Fact Sheet. https://sustainabletechnologies.ca/app/uploads/2018/02/Bioretention-and-Dry-Swales-Fact-Sheet.pdf</ref>


==Inspection Time Commitments and Costs==
==Inspection Time Commitments and Costs==
Estimates are based on a typical partial infiltration bioretention design (i.e., includes a sub-drain); estimates for other designs (i.e., full infiltration and no-infiltration) can be found in the [https://sustainabletechnologies.ca/app/uploads/2016/08/LID-IM-Guide-7.1-Bioretention-and-Dry-Swales.pdf Low Impact Development (LID) Stormwater Management Practice Inspection and Maintenance Guide]
Estimates are based on a typical partial infiltration bioretention design (i.e., includes a sub-drain); estimates for other designs (i.e., full infiltration and no-infiltration) can be found in the [https://sustainabletechnologies.ca/app/uploads/2016/08/LID-IM-Guide-7.1-Bioretention-and-Dry-Swales.pdf Low Impact Development (LID) Stormwater Management Practice Inspection and Maintenance Guide]<br>
</br>


[[File:Time commit cost.PNG|thumb|left|450px|General time commitments and costs for inspection of bioretention and dry swale features with partial infiltration (in 2016 $ figures).<ref>TRCA. 2018. Inspection and Maintenance of Stormwater Best Management Practices. Bioretention - Fact Sheet. https://sustainabletechnologies.ca/app/uploads/2018/02/Bioretention-and-Dry-Swales-Fact-Sheet.pdf</ref>]]
[[File:Time commit cost.PNG|thumb|left|400px|General time commitments and costs for inspection of bioretention and dry swale features with partial infiltration (in 2016 $ figures).<ref>TRCA. 2018. Inspection and Maintenance of Stormwater Best Management Practices. Bioretention - Fact Sheet. https://sustainabletechnologies.ca/app/uploads/2018/02/Bioretention-and-Dry-Swales-Fact-Sheet.pdf</ref>]]


[[File:Cost per maintenance task.PNG|thumb|450px|Per-task cost estimates for maintenance and rehabilitation of a partial infiltration bioretention feature (in 2016 $ figures).<ref>TRCA. 2018. Inspection and Maintenance of Stormwater Best Management Practices. Bioretention - Fact Sheet. https://sustainabletechnologies.ca/app/uploads/2018/02/Bioretention-and-Dry-Swales-Fact-Sheet.pdf</ref>]]
[[File:Cost per maintenance task.PNG|thumb|400px|Per-task cost estimates for maintenance and rehabilitation of a partial infiltration bioretention feature (in 2016 $ figures).<ref>TRCA. 2018. Inspection and Maintenance of Stormwater Best Management Practices. Bioretention - Fact Sheet. https://sustainabletechnologies.ca/app/uploads/2018/02/Bioretention-and-Dry-Swales-Fact-Sheet.pdf</ref>]]


[[File:Life cycle costs.PNG|thumb|center|450px|Construction and life cycle cost estimates for bioretention and dry swale features with partial infiltration (in 2016 $ figures).<ref>TRCA. 2018. Inspection and Maintenance of Stormwater Best Management Practices. Bioretention - Fact Sheet. https://sustainabletechnologies.ca/app/uploads/2018/02/Bioretention-and-Dry-Swales-Fact-Sheet.pdf</ref>]]<br>
[[File:Life cycle costs.PNG|thumb|center|400px|Construction and life cycle cost estimates for bioretention and dry swale features with partial infiltration (in 2016 $ figures).<ref>TRCA. 2018. Inspection and Maintenance of Stormwater Best Management Practices. Bioretention - Fact Sheet. https://sustainabletechnologies.ca/app/uploads/2018/02/Bioretention-and-Dry-Swales-Fact-Sheet.pdf</ref>]]<br>
</br>
</br>


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The 8 page document prompts users to fill out details previously mentioned above on this page in other sections about various zones associated with [[Bioretention]] and [[Dry swale]] features (i.e. inlets, perimeter of the feature, filter bed, outlets, etc.) and describe why each area is a pass or fail, and if remediate action is required and under what timeframe it would be completed by. Furthermore, the forms prompt the reviewer to determine what type of  inspection is being conducted for the feature in question: Construction (C), Routine Operation (RO), Maintenance Verification (MV), or Performance Verification (PV). <br>
The 8 page document prompts users to fill out details previously mentioned above on this page in other sections about various zones associated with [[Bioretention]] and [[Dry swale]] features (i.e. inlets, perimeter of the feature, filter bed, outlets, etc.) and describe why each area is a pass or fail, and if remediate action is required and under what timeframe it would be completed by. Furthermore, the forms prompt the reviewer to determine what type of  inspection is being conducted for the feature in question: Construction (C), Routine Operation (RO), Maintenance Verification (MV), or Performance Verification (PV). <br>
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[[File:Continuous monitoring.PNG|thumb|500px|Staff conducting monitoring of bioretention's water level with the use of a [[Digital technologies|continuous water level data logger]] located in the feature's[[Wells|monitoring well]]. [https://sustainabletechnologies.ca/app/uploads/2018/02/Bioretention-and-Dry-Swales-Fact-Sheet.pdf Photo Source: TRCA, 2018]<ref>TRCA. 2018. Inspection and Maintenance of Stormwater Best Management Practices - Bioretention. Fact Sheet. https://sustainabletechnologies.ca/app/uploads/2018/02/Bioretention-and-Dry-Swales-Fact-Sheet.pdf</ref>]]
 
[[File:Continuous monitoring.PNG|thumb|300px|Staff conducting monitoring of bioretention's water level with the use of a [[Digital technologies|continuous water level data logger]] located in the feature's[[Wells|monitoring well]]. [https://sustainabletechnologies.ca/app/uploads/2018/02/Bioretention-and-Dry-Swales-Fact-Sheet.pdf Photo Source: TRCA, 2018]<ref>TRCA. 2018. Inspection and Maintenance of Stormwater Best Management Practices - Bioretention. Fact Sheet. https://sustainabletechnologies.ca/app/uploads/2018/02/Bioretention-and-Dry-Swales-Fact-Sheet.pdf</ref>]]


<pdf width="900" height="800">File:Bio Swale Inspection Sheet.pdf</pdf>
<pdf width="900" height="800">File:Bio Swale Inspection Sheet.pdf</pdf>


==References==
==References==

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