Difference between revisions of "Inspection and Maintenance: Green Roofs"

From LID SWM Planning and Design Guide
Jump to navigation Jump to search
Line 239: Line 239:
|
|
*Check for damage or vegetation;
*Check for damage or vegetation;
*Remove any vegetation or natural debris
*Remove any vegetation or natural debris annually to biannually.
annually to biannually.
|[[File:CDA Pass p.p.JPG|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:CDA Pass p.p.JPG|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:CDA Fail p.p.JPG|280px|thumb|center|Size of the CDA has changed from design assumptions (i.e. large asphalt area drains to a small portion of the permeable pavement). Evidence of surface ponding is visible.]]  
|[[File:CDA Fail p.p.JPG|280px|thumb|center|Size of the CDA has changed from design assumptions (i.e. large asphalt area drains to a small portion of the permeable pavement). Evidence of surface ponding is visible.]]  
|-
|-
|'''[[Inspection and Maintenance:Growing medium/filter bed|Growing medium/filter bed]]'''
|'''[[Green roof media|Growing medium/filter bed]]'''
|
|
Devices or features that retain trash, debris and sediment; help to extend the [[Cost analysis resources|operating life cycle]]; examples are eavestrough screens, [[Pretreatment|catch basin]] inserts and sumps, [[oil and grit separators]], [[inlets|geotextile-lined inlets]], [[Gravel diaphragms|gravel trenches]], [[Vegetated filter strips|grass filter strips]] and [[forebays]].
Flat or gently sloping area covered by growing medium and a mixture of plants. Growing medium varies according to the green roof system or product but is generally designed to be porous and lightweight with adequate fertility and moisture retention to support plant growth while maintaining drainage of excess water within a few hours after a storm or snowmelt event. May be covered by matting/other erosion control product to prevent rain/wind scour while plantings are becoming established.
|
|
*Remove trash, debris and sediment annually to biannually or when the device sump is half full;
*Check for standing water, animal burrows or damage from foot traffic, rain or wind scour;
*Measure sediment depth or volume during each cleaning, or annually to estimate accumulation rate and optimize frequency of maintenance.
*Replace erosion/scour protection where missing or uplifted;
*Remove trash and natural debris annually to biannually.
|[[File:Pretreat Pass p.p.JPG|280px|thumb|center|Although permeable pavers are generally considered [[pretreatment]] for other BMPs in a [[Low impact development treatment train tool|treatment train]] system, using eavestrough screens can act as pretreatment as they don't add to sediment build up and accumulation on the paver surface. (Photo Source: Guertin, 2010)<ref>Guertin, M. 2010. Simple Screen Gutter Guards Better Than Pro-Installed Systems (and way cheaper). Fine Homebuilding - The Daily Fix. Accessed July 17 2022. https://www.finehomebuilding.com/2010/08/17/simple-screen-gutter-guards-better-than-pro-installed-systems-and-way-cheaper</ref>]]  
|[[File:Pretreat Pass p.p.JPG|280px|thumb|center|Although permeable pavers are generally considered [[pretreatment]] for other BMPs in a [[Low impact development treatment train tool|treatment train]] system, using eavestrough screens can act as pretreatment as they don't add to sediment build up and accumulation on the paver surface. (Photo Source: Guertin, 2010)<ref>Guertin, M. 2010. Simple Screen Gutter Guards Better Than Pro-Installed Systems (and way cheaper). Fine Homebuilding - The Daily Fix. Accessed July 17 2022. https://www.finehomebuilding.com/2010/08/17/simple-screen-gutter-guards-better-than-pro-installed-systems-and-way-cheaper</ref>]]  
|[[File:Pretreat Fail p.p.JPG|300px|thumb|center|Build up of leads, sediment and leaf detritus in an eavestrough downspout disconnection leading to a permeable pavement surface. If not cleaned regularly this can lead to clogged pores between the pavers reducing the infiltration rate where the downspout deposits water onto the feature. (Photo Source: My Gutter Pro, 2021)<ref>My Gutter Pro. 2021. Clogged Downspout : Causes and Solutions. 10 April 2021. Accessed July 19 2022. https://mygutterpro.com/downspout-clog/</ref>]]  
|[[File:Pretreat Fail p.p.JPG|300px|thumb|center|Build up of leads, sediment and leaf detritus in an eavestrough downspout disconnection leading to a permeable pavement surface. If not cleaned regularly this can lead to clogged pores between the pavers reducing the infiltration rate where the downspout deposits water onto the feature. (Photo Source: My Gutter Pro, 2021)<ref>My Gutter Pro. 2021. Clogged Downspout : Causes and Solutions. 10 April 2021. Accessed July 19 2022. https://mygutterpro.com/downspout-clog/</ref>]]  
|-
|'''[[Inlets]]'''
|
Structures that deliver water to the BMP (e.g., impermeable pavement edges, [[pipes]] from roof downspouts or catchbasins).
|
*Keep free of obstructions;
*Remove trash, debris and sediment biannually to quarterly;
*Make note of sediment depth or volume during each cleaning or annually to estimate accumulation rate and optimize frequency of maintenance
|[[File:Inlet Pass p.p.JPG|285px|thumb|center|Impermeable pavement edges along the edge of the pervious concrete and impermeable asphalt graded so excess sheet flow is infiltrated down through the pores of the infiltration BMP. (Photo Source: Fairfax County, 2014)<ref>Fairfax County. 2014. Protecting our Environment, one Stormwater Practice at a Time - Permeable Pavements. April 2014. Accessed: July 20 2022. https://www.fairfaxcounty.gov/publicworks/sites/publicworks/files/assets/documents/pdf/factsheets/permeable-pavement.pdf</ref>]]
|[[File:Curb inlet grade.jpg|300px|thumb|center|Accumulated sediment, poor grading and vegetation is preventing stormwater from entering the [[swale]]. Sediment on the curb cut surface behind of the inlet indicates ponding is also occurring and is depositing water towards the permeable paver surface.]]
|-
|'''[[Permeable pavements: Specifications|Pavement Surface]]'''
|
The surface of the pavement, including pavers/pavement, joints and edge restraints (e.g., curbs, edging); should not allow water to pond on the surface so any observation or evidence of surface ponding (e.g., sediment caking on the pavement) indicates a drainage problem.
|
*Check for sediment, surface ponding, deformation, sink holes, damage and loss of joint fill;
*Remove trash regularly (biannually-quarterly);
*Grid systems with soil and grass fill are maintained like lawns;
*Sweep and vacuum interlocking and rigid pavements regularly (annually-biannually) with regenerative air/pure vacuum sweeper;
*Plow snow as needed and spread deicers sparingly during winter;
*Repair ruts or local sinking of 15 mm or greater over a 3 metre length, adjacent pavers or cracks in pervious concrete or porous asphalt are vertically offset by 5 mm or greater and paver joint fill is missing or below 15 mm from the paver surface.
|[[File:Pavesurface Pass p.p.JPG|350px|thumb|center|No damage, displacement or sinking of the permeable surface is visible and there are no weeds growing between paver joints.]]
|[[File:Pavesurface Fail p.p.JPG|280px|thumb|center|The pavement surface has sunk in local areas, creating a trip hazard and the potential for further damage from snow plowing and parked vehicles nearby.]]
|-
|-
|'''[[Vegetation]]'''
|'''[[Vegetation]]'''
|
|
Applies to grid paver systems only; a mixture of deep rooting perennial grasses or low growing ground covers, tolerant to both wet and dry conditions and salt (if receiving impermeable pavement runoff); roots uptake water and return it to the atmosphere, provide habitat for soil organisms that break down pollutants trapped in the soil and help maintain soil structure and permeability.
[[Green roofs: Planting|Plants]] should be tolerant of the harsh conditions prevalent on rooftops. Use of a wide variety of plants may improve resilience but complicates maintenance and may require staff or contractors trained in horticulture
|
|
*Grid systems with soil and grass fill are maintained like lawns;
*Maintenance is similar to a conventional [[perennials|perennial]] planting bed;
*In the first 2 months water frequently (biweekly in the absence or rain) and as needed (e.g., bimonthly) over the remainder of the first growing season;
*Water bi-weekly in the absence of rain during first two months and as needed for the remainder of the first [[Climate Trends in Ontario|growing season]];
*Remove weeds and undesirable plants biannually to quarterly;
*Remove undesirable [[vegetation]] biannually to quarterly;
*Replace/reseed dead plantings annually to achieve 80% cover by the third growing season;
*Prune [[shrubs]] and [[trees]] annually, and replace dead [[plants]] to maintain a minimum of 80% cover by the third growing season.   
*Do not apply chemical fertilizers.   
|[[File:Veg Pass p.p.JPG|315px|thumb|center|The vegetation cover on the permeable pavement is turf grass as specified in the final design and contains very few weeds. (Photo source: WEF).]]  
|[[File:Veg Pass p.p.JPG|315px|thumb|center|The vegetation cover on the permeable pavement is turf grass as specified in the final design and contains very few weeds. (Photo source: WEF).]]  
|[[File:Veg Fail p.p.JPG|290px|thumb|center|The turf grass cover on the permeable walkway is not thriving in some areas and needs cutting in others. It is also impairing the aesthetic value of the BMP.]]  
|[[File:Veg Fail p.p.JPG|290px|thumb|center|The turf grass cover on the permeable walkway is not thriving in some areas and needs cutting in others. It is also impairing the aesthetic value of the BMP.]]  
Line 290: Line 266:
|'''[[Overflow|Overflow Outlet]]'''
|'''[[Overflow|Overflow Outlet]]'''
|
|
Structures (e.g., catchbasin, curb-cut, [[swale]]) that convey flow that exceeds the storage capacity of the BMP to another drainage system (e.g., municipal storm sewer or other BMP).  
Flows exceeding the storage capacity of the BMP are conveyed to an adjacent drainage system via an [[overflow|overflow outlet structure]] and the roof drainage system.
|
|
*Keep free of obstructions;
*Remove trash, natural debris and clippings biannually to quarterly;
*Remove trash, debris and sediment biannually to quarterly.
*Flush with hose or pressure washer annually to biannually
|[[File:Overflow Pass p.p.JPG|320px|thumb|center|The overflow outlet is free of damage and obstruction and functions as designed to safely convey excess water from the BMP.]]  
|[[File:Overflow Pass p.p.JPG|320px|thumb|center|The overflow outlet is free of damage and obstruction and functions as designed to safely convey excess water from the BMP.]]  
|[[File:Overflow Fail p.p.JPG|280px|thumb|center|The overflow outlet is obstructed with sediment which impairs its function to convey excess water from the BMP.]]  
|[[File:Overflow Fail p.p.JPG|280px|thumb|center|The overflow outlet is obstructed with sediment which impairs its function to convey excess water from the BMP.]]  
|-
|-
|'''[[Underdrain|Sub-drain]]'''
|'''[[Green roofs#Irrigation|Irrigation System]]'''
|
|
Optional component; [[Pipes|perforated pipe(s)]] surrounded by [[gravel]] and may be wrapped in [[Geotextile|geotextile filter fabric]]; installed in the base or sub-base gravel layer to collect and convey treated water to an adjacent drainage system or other BMP; may also include a flow restrictor.
Most green roofs will require watering over their operating life cycle, especially during the first 2 months. Systems can range from simple hose bibs, garden hoses and sprinklers to intelligent automated systems that schedule watering based on weather forecasts and cistern water levels.  
|
|
*Keep pipe and flow restrictor free of obstructions by flushing annually;
*In the spring, reconnect all parts to the water supply, flush lines to clear out any debris or sediment and test to confirm that the system is undamaged and functioning well;
*Inspect flow restrictor regularly (e.g., biannually to quarterly).
*In the late fall/early winter, disconnect the system from the water supply, connect it to an air compressor and blow air through it to remove water and ensure the lines and parts are dry, shut off water supply to the roof, and drain all hose bibs;
*Remove any debris/sediment accumulated on filters biannually.
|[[File:Underdrain Pass p.p.JPG|310px|thumb|center|The solid section of the sub-drain pipe is not obstructed by sediment, debris or roots and shows no signs of damage.]]  
|[[File:Underdrain Pass p.p.JPG|310px|thumb|center|The solid section of the sub-drain pipe is not obstructed by sediment, debris or roots and shows no signs of damage.]]  
|[[File:Underdrain Fail p.p.JPG|300px|thumb|center|A section of the sub-drain pipe has been crushed which substantially reduces its conveyance capacity]]  
|[[File:Underdrain Fail p.p.JPG|300px|thumb|center|A section of the sub-drain pipe has been crushed which substantially reduces its conveyance capacity]]  
|-
|-
|'''[[Monitoring well]]'''
|'''[[Green roofs#Design|Protective layers]]'''
|
|
[[Wells|Perforated standpipe]] that extends from the bottom of the excavation to just below the pavement surface and contains perforations or slots to allow [[Digital technologies|measurement of subsurface water level]]; used to track drainage performance over the operating life cycle of the BMP.
May be one or two layers; designed to protect the roof deck from water damage, including a waterproofing membrane, a root barrier that protects the water-proofing membrane from root penetration and degradation by microbial activity.
|
|
*[[Wells|Standpipes]] should be securely capped on both ends and protected from damage by vehicular traffic by a casing.
*Repair isolated leaks in the water-proofing membrane through deconstruction of a small portion of the green roof, patching with new material, and reconstruction.
|[[File:Monitor Pass p.p.JPG|340px|thumb|center|The well is undamaged and accessible and the cap is in place and secured to prevent unauthorized access]]  
|[[File:Monitor Pass p.p.JPG|340px|thumb|center|The well is undamaged and accessible and the cap is in place and secured to prevent unauthorized access]]  
|[[File:Monitor Fail p.p.JPG|300px|thumb|center|The well cap is missing and the casing is clogged by sediment, preventing access for monitoring and allowing sediment to flow into the sub-drain system.]]  
|[[File:Monitor Fail p.p.JPG|300px|thumb|center|The well cap is missing and the casing is clogged by sediment, preventing access for monitoring and allowing sediment to flow into the sub-drain system.]]  
|-
|'''[[Flow through riser|Control Structure]]'''
|
Manhole or catchbasin to which the subdrain outlets that provides access to the [[underdrain]] and flow restrictor. Inspect for accessibility, damage and sediment.
|
*Remove trash, debris and sediment regularly (biannually/quarterly)..
|[[File:Control Struct Pass p.p.JPG|340px|thumb|center|TThere is some sediment accumulated in the manhole but it is not impairing the flow of stormwater into or out of the BMP. (Photo source: SWC Canada)]]
|[[File:Control Struct Fail p.p.JPG|300px|thumb|center|The manhole sump is full of sediment and debris and it is beginning to impair flow of stormwater into a perforated pipe of the exfiltration storm sewer system.]]
|}
|}

Revision as of 19:02, 8 August 2022

Inspection & Maintenance Guidance of Green roofs best management practices. These specialized roofs are specially engineered and designed to support the growth of vegetation while protecting the structural integrity of the roof, aiding in helping to cool the building and effectively infiltrate, absorb and retain precipitation (TRCA, 2018).[1]

Overview[edit]

Green roofs are engineered rooftop design features that allow the growth of vegetation on rooftops and have numerous benefits. These LID BMPs can also be referred to as vegetated roofs, rooftop gardens or eco-roofs. A green roof acts like a lawn, meadow or garden by intercepting and absorbing a portion of the rainwater or snowmelt that falls on it. The typical layers of a green roof (in ascending order from the roof surface) include a water-proofing membrane, drainage layer, lightweight growing media layer and the vegetation. Excess water that is not absorbed by the growing media or vegetation is collected by the underlying drainage layer, directed to outlet structures and conveyed via the roof drainage system to another BMP or the municipal storm sewer system. A portion of the water absorbed by green roofs is returned to the atmosphere by evaporation and transpiration by plants. Green roofs are typically designed to retain precipitation from small to medium-sized (e.g., 5 to 25 mm rainfall depth) storm events. Overflow outlets are necessary to safely convey flows from major storm events.

Generalized cross-section view of a green roof showing key components and common layers that make up this LID BMP (TRCA, 2018)[1]

Some of the benefits of green roofs include:

  • The ability to reduce the quantity of pollutants and runoff being discharged to municipal storm sewers and receiving waters (i.e., rivers, lakes and wetlands);
  • Growing media and plants retain pollutants deposited from the atmosphere and reduce metals and other pollutants from conventional roof materials transported by runoff;
  • Improve the energy efficiency of the building due to their insulating properties;
  • Reduce the urban heat island effect;
  • Can provide food and shelter for pollinators;
  • Can provide aesthetic value as attractive landscaped features.


Key components of Underground Infiltration Systems to pay close attention to are the:

Associated Practices[edit]

  • Intensive green roofs contain greater than 15 cm depth of growing media, can be planted with deeply rooted plants (e.g., shrubs and trees) and can be designed to handle pedestrian traffic.
  • Extensive green roofs consist of a thinner growing media layer (15 cm depth or less) and are typically planted with.
  • Blue roofs are systems that temporarily capture rainwater using the roof as storage and allow it to evaporate and/or to be used for non-potable requirements (i.e. irrigation, toilet flushing, truck washing) and ultimately offset potable water demands.

Inspection and Testing Framework[edit]

Maintneance of the Green roofs filter bed and vegetation composition/condition being performed by staff (TRCA, 2018).[1]
Visual Indicators Framework - Green Roofs

Component

Indicators

Construction Inspection

Assumption Inspection

Routine Operation Inspection

Verification Inspection
Perimeter
BMP dimensions x x x
Growing medium/filter bed
Green roof structural integrity x x x
Standing water x x x
Filter bed erosion x x
Vegetation
Vegetation cover x x x x
Vegetation condition x x
Vegetation composition x x x
Overflow outlets
Overflow outlet obstruction x x x x



Testing Indicators Framework - Green Roofs

Component

Indicators

Construction Inspection

Assumption Inspection

Routine Operation Inspection

Verification Inspection
Testing Indicators
Soil characterization testing x x (x)
Green roof irrigation system testing x x x
Green roof leak detection testing x x
Note: (x) denotes indicators to be used for Performance Verification inspections only (i.e., not for Maintenance Verification inspections)

Construction Inspection Tasks[edit]

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:

  1. During site preparation, prior to BMP installation to ensure the roof structure is ready for green roof construction work and confirm that BMP layout area matches approved design drawings and that construction materials meet design specifications
  2. After installation of leak detection system (if applicable) to ensure it was done properly
  3. At installation of water-proofing membrane, prior to installation of root barrier, drainage layer and overflow outlets to ensure it was done properly and to confirm that slopes are acceptable
  4. After installation of root barrier, drainage layer (including filter fabric/layer) and overflow outlets, prior to installation of growing medium and plants to ensure it was done properly and confirm that depth and slopes are acceptable
  5. After installation of growing medium layer and plants to ensure it was done properly and to confirm depth, slopes and elevations at overflow outlets are acceptable; After installation of irrigation system to confirm system is functioning
  6. Prior to hand-off points in the construction sequence when the contractor responsible for the work changes (i.e., hand-offs between the building and green roof installation contractors)
  7. After every large storm event (e.g., 15 mm rainfall depth or greater) to ensure roof drainage or flow diversion devices are functioning and adequately maintained. You can also download and print the table here


A technician using a non-invasive locate method to determine the source of a leak in a Green roof membrane (Construction Canada, 2012.)[2]


An example of a conceptual planting design for a green roof project in Mill Valley, California (O’Connell Landscape, 2010).[3]
Green Roofs: Construction Inspections

Construction Sequence Step & Timing

Inspection Item

Observations*
Site Preparation - During site preparation, prior to BMP installation Ensure the roof structure is ready for green roof construction work
BMP layout area and dimensions match approved design drawings
CDA is stabilized or runoff is diverted around BMP layout area
Construction materials have been confirmed to meet design specifications
Leak detection System - After installation of leak detection system (if applicable), prior to installation of water-proofing membrane Quality control check leak detection system installation
Water Proofing Membrane – After installation of waterproofing membrane, prior to installation of root barrier, drainage layer and overflow outlets Quality control check membrane installation
Confirm that slopes conform with approved design drawings
Root barrier / Drainage layer and Overflow outlets – After installation of root barrier, drainage layer (including filter fabric) and overflow outlets, prior to installation of growing medium layer and plants Quality control check root barrier and drainage layer installations
Installation of drainage layer (e.g., depth and slope) is acceptable
Installations of overflow outlets (e.g., elevation and slope) are acceptable
Filter bed – After installation of filter bed (growing medium layer and plants) Quality control check installation of any structural components of growing medium layer (if applicable)
Installation of growing medium (e.g., depth, elevations at overflow outlets) is acceptable
Growing medium is free of ruts, local depressions
Planting material meets approved planting plan specifications (plant types and quantities)
Quality control check installation of erosion matting/protection (if applicable)
Irrigation System - After installation of irrigation system Confirm installation is acceptable and system is functioning (through testing)

Routine Maintenance - Key Components and I&M Tasks[edit]

Regular inspections (twice annually, at a minimum) done as part of routine maintenance tasks over the operating phase of the BMP life cycle to determine if maintenance task frequencies are adequate and determine when rehabilitation or further investigations into BMP function are warranted.

The table below describes routine maintenance tasks for green roofs, 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 or high pedestrian traffic locations or intensive green roofs featuring shrubs, trees and a wider variety of vegetation types. Tasks involving removal of trash, debris and weeding/trimming or replacement of dead plants may need to be done more frequently in such contexts. For further guidance on maintenance of vegetation cover on green roofs, refer to ASTM D2400/E2400M-06 Standard Guide for Selection, Installation and Maintenance of Plants for Green Roof Systems (ASTM International, 2015)[4]

Individuals conducting vegetation maintenance and in particular, weeding (i.e., removal of undesirable vegetation), should be familiar with the species of 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:

Green Roofs: Key Components, Descriptions and Routine I&M Requirements
Comnponent Description Inspection & Maintenance Tasks (Pass) Photo Example (Fail) Photo Example
Perimeter

Separates the green roof from the roof edges and other structures; kept clear of vegetation and natural debris as a fire prevention measure. Parapets or other wind break structures may also be present around the perimeter to help prevent wind scour of growing media.

  • Check for damage or vegetation;
  • Remove any vegetation or natural debris annually to biannually.
CDA has not changed in size or land cover. Sediment, trash or debris is not accumulating and point sources of contaminants are not visible.
Size of the CDA has changed from design assumptions (i.e. large asphalt area drains to a small portion of the permeable pavement). Evidence of surface ponding is visible.
Growing medium/filter bed

Flat or gently sloping area covered by growing medium and a mixture of plants. Growing medium varies according to the green roof system or product but is generally designed to be porous and lightweight with adequate fertility and moisture retention to support plant growth while maintaining drainage of excess water within a few hours after a storm or snowmelt event. May be covered by matting/other erosion control product to prevent rain/wind scour while plantings are becoming established.

  • Check for standing water, animal burrows or damage from foot traffic, rain or wind scour;
  • Replace erosion/scour protection where missing or uplifted;
  • Remove trash and natural debris annually to biannually.
Although permeable pavers are generally considered pretreatment for other BMPs in a treatment train system, using eavestrough screens can act as pretreatment as they don't add to sediment build up and accumulation on the paver surface. (Photo Source: Guertin, 2010)[5]
Build up of leads, sediment and leaf detritus in an eavestrough downspout disconnection leading to a permeable pavement surface. If not cleaned regularly this can lead to clogged pores between the pavers reducing the infiltration rate where the downspout deposits water onto the feature. (Photo Source: My Gutter Pro, 2021)[6]
Vegetation

Plants should be tolerant of the harsh conditions prevalent on rooftops. Use of a wide variety of plants may improve resilience but complicates maintenance and may require staff or contractors trained in horticulture

  • Maintenance is similar to a conventional perennial planting bed;
  • Water bi-weekly in the absence of rain during first two months and as needed for the remainder of the first growing season;
  • Remove undesirable vegetation biannually to quarterly;
  • Prune shrubs and trees annually, and replace dead plants to maintain a minimum of 80% cover by the third growing season.
The vegetation cover on the permeable pavement is turf grass as specified in the final design and contains very few weeds. (Photo source: WEF).
The turf grass cover on the permeable walkway is not thriving in some areas and needs cutting in others. It is also impairing the aesthetic value of the BMP.
Overflow Outlet

Flows exceeding the storage capacity of the BMP are conveyed to an adjacent drainage system via an overflow outlet structure and the roof drainage system.

  • Remove trash, natural debris and clippings biannually to quarterly;
  • Flush with hose or pressure washer annually to biannually
The overflow outlet is free of damage and obstruction and functions as designed to safely convey excess water from the BMP.
The overflow outlet is obstructed with sediment which impairs its function to convey excess water from the BMP.
Irrigation System

Most green roofs will require watering over their operating life cycle, especially during the first 2 months. Systems can range from simple hose bibs, garden hoses and sprinklers to intelligent automated systems that schedule watering based on weather forecasts and cistern water levels.

  • In the spring, reconnect all parts to the water supply, flush lines to clear out any debris or sediment and test to confirm that the system is undamaged and functioning well;
  • In the late fall/early winter, disconnect the system from the water supply, connect it to an air compressor and blow air through it to remove water and ensure the lines and parts are dry, shut off water supply to the roof, and drain all hose bibs;
  • Remove any debris/sediment accumulated on filters biannually.
The solid section of the sub-drain pipe is not obstructed by sediment, debris or roots and shows no signs of damage.
A section of the sub-drain pipe has been crushed which substantially reduces its conveyance capacity
Protective layers

May be one or two layers; designed to protect the roof deck from water damage, including a waterproofing membrane, a root barrier that protects the water-proofing membrane from root penetration and degradation by microbial activity.

  • Repair isolated leaks in the water-proofing membrane through deconstruction of a small portion of the green roof, patching with new material, and reconstruction.
The well is undamaged and accessible and the cap is in place and secured to prevent unauthorized access
The well cap is missing and the casing is clogged by sediment, preventing access for monitoring and allowing sediment to flow into the sub-drain system.
  1. 1.0 1.1 1.2 TRCA. 2018. Fact Sheet - Inspection and Maintenance of Stormwater Best Management Practices: Green Roofs. https://sustainabletechnologies.ca/app/uploads/2018/02/Green-Roofs-Fact-Sheet.pdf
  2. Construction Canada. 2012. Waterproofing considerations for green roofs. Photo source: Detec Systems. 1 March 2012. Accessed August 8 2022. https://www.constructioncanada.net/waterproofing-considerations-for-green-roofs/2/
  3. O’Connell Landscape. 2010. FROM THE DRAWING BOARD: MILL VALLEY & CORTE MADERA PLANTINGS. Authored 13 January 2010. Accessed 08 August 2022. https://oclandscape.com/ocblog/from-the-drawing-board-mill-valley-corte-madera-plantings/
  4. ASTM International. 2015. Standard Guide for Selection, Installation, and Maintenance of Plants for Green Roof Systems. Designation: E 2400 – 06. http://hydro.engr.scu.edu/files/green_roof/ASTM_E2400-06.pdf
  5. Guertin, M. 2010. Simple Screen Gutter Guards Better Than Pro-Installed Systems (and way cheaper). Fine Homebuilding - The Daily Fix. Accessed July 17 2022. https://www.finehomebuilding.com/2010/08/17/simple-screen-gutter-guards-better-than-pro-installed-systems-and-way-cheaper
  6. My Gutter Pro. 2021. Clogged Downspout : Causes and Solutions. 10 April 2021. Accessed July 19 2022. https://mygutterpro.com/downspout-clog/