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[[File:Pdf image.png|100px|thumb|alt=pdf image|<font size=3>[https://stormwater.pca.state.mn.us/index.php?title=File:Operation_and_maintenance_(O%26M)_of_filter_strips_-_Minnesota_Stormwater_Manual.pdf Download pdf]</font size>]]
 
[[File:Filter strip before rain garden 1.jpg|300px|thumb|alt=Image of a vegetated filter strip|<font size=3>Image of a vegetated filter strip</font size>]]
 
[[File:Filter strip before rain garden 1.jpg|300px|thumb|alt=Image of a vegetated filter strip|<font size=3>Image of a vegetated filter strip</font size>]]
{{alert|This page provides information on a green stormwater infrastructure topic|alert-success}}
 
  
[https://stormwater.pca.state.mn.us/index.php?title=Erosion_protection_and_sediment_monitoring,_removal,_and_disposal_%E2%80%93_protecting_your_investment Erosion protection]</span><br>
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{{alert|Filter strips, when vegetated, provide water quality benefits, may provide some stormwater volume reduction, and may provide typical benefits of vegetation, such as habitat, depending on the vegetation type.|alert-success}}
[https://stormwater.pca.state.mn.us/index.php?title=Sustainable_Service_Life Sustainable service life]</span><br>
 
[[Operation and maintenance (O&M) of filter strips]]<br>
 
[https://stormwater.pca.state.mn.us/index.php?title=Vegetated_filter_strip_detailed_maintenance_activity_description Vegetated filter strips]</span>
 
  
==Overview of typical O&M issues==
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This page provides guidance for operation and maintenance (O&M) of filter strips. <span title="an area of permanent vegetation or other material used to reduce sediment, organics, nutrients, pesticides, and other contaminants from runoff and to maintain or improve water quality.> '''[https://stormwater.pca.state.mn.us/index.php?title=Overview_for_pretreatment_vegetated_filter_strips Filter strips]'''</span> are designed to filter <span title="Small solid particles which remain in suspension in water as a colloid or due to the motion of the water, suspended solids can be removed by the sedimentation because of their comparatively large size."> '''[https://stormwater.pca.state.mn.us/index.php?title=Total_Suspended_Solids_(TSS)_in_stormwater suspended solids]'''</span> from runoff as water passes over the filter strip. Most filter strips are vegetated, with grass and <span title="A perennial plant or simply perennial is a plant that lives more than two years"> '''perennial'''</span> <span title="A species that has been observed in the form of a naturally occurring and self-sustaining population in historical times. Non-natives do not meet this definition."> '''native vegetation'''</span> most widely used.
  
<span title="Pretreatment vegetated filter strips are designed to provide sedimentation and screening (by vegetation) to treat stormwater runoff prior to entering a structural stormwater BMP. Pretreatment vegetated filter strips are especially effective at capturing excess sediment in stormwater runoff by settling solids. Pretreatment vegetated filter strips provide limited (due to size) volume reduction, peak flow reduction, infiltration, and biological treatment. Stormwater management processes not provided in pretreatment vegetated filter strips include filtration and sorption."> [https://stormwater.pca.state.mn.us/index.php?title=Overview_for_pretreatment_vegetated_filter_strips '''Vegetated filter strip''']</span>, also known as buffer strips or buffers, are vegetated land areas between a pollutant source and a surface water body. They can be stand-alone practices or used as a pre-treatment practice to other practices like bioretention or ponds. They reduce the flow velocity of water and filter and infiltrate pollutants such as sediment from stormwater.  Vegetated filter strips may be subject to high public visibility, trash loads, sedimentation, pedestrian traffic, and even vehicular traffic or loads. <br><br>
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Supplemental information can be found on the page called [[Operation and maintenance of filter strips - supplemental information]]. Supplemental information includes the following.
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*Removing sediment and debris buildup
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*Preventing or minimizing <span title"the removal or erosion of material captured by a stormwater device, typically a result of subsequent high flow volumes or rates or inadequate maintenance of the device"> '''washout'''</span> and erosion of the <span title="Pretreatment reduces maintenance and prolongs the lifespan of structural stormwater BMPs by removing trash, debris, organic materials, coarse sediments, and associated pollutants prior to entering structural stormwater BMPs. Implementing pretreatment devices also improves aesthetics by capturing debris in focused or hidden areas. Pretreatment practices include settling devices, screens, and pretreatment vegetated filter strips."> [https://stormwater.pca.state.mn.us/index.php?title=Pretreatment '''pretreatment''']</span> vegetated filter strip
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*Vegetation establishment
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*Maintaining vegetation
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*Snow storage
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*Maintenance agreements
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*Additional references
  
Vegetated filter strips require dedicated and regular maintenance to ensure proper and long-lasting operation, and in most cases a vegetated filter strip should be designed to be effective for at least 10 years (NRCS, 2010). The most frequently cited O&M concerns for vegetated filter strips include:
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==Overview of typical O&M issues==
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<span title="Pretreatment vegetated filter strips are designed to provide sedimentation and screening (by vegetation) to treat stormwater runoff prior to entering a structural stormwater BMP. Pretreatment vegetated filter strips are especially effective at capturing excess sediment in stormwater runoff by settling solids. Pretreatment vegetated filter strips provide limited (due to size) volume reduction, peak flow reduction, infiltration, and biological treatment. Stormwater management processes not provided in pretreatment vegetated filter strips include filtration and sorption."> [https://stormwater.pca.state.mn.us/index.php?title=Overview_for_pretreatment_vegetated_filter_strips '''Vegetated filter strip''']</span>, also known as buffer strips or buffers, are vegetated land areas between a pollutant source and a surface water body (also called a <span title="A stream, river, lake, ocean, or other surface or groundwaters into which treated or untreated wastewater is discharged"> '''receiving water'''</span>). They can be stand-alone practices or used as <span title="Pretreatment reduces maintenance and prolongs the lifespan of structural stormwater BMPs by removing trash, debris, organic materials, coarse sediments, and associated pollutants prior to entering structural stormwater BMPs. Implementing pretreatment devices also improves aesthetics by capturing debris in focused or hidden areas. Pretreatment practices include settling devices, screens, and pretreatment vegetated filter strips."> [https://stormwater.pca.state.mn.us/index.php?title=Pretreatment '''pretreatment''']</span> to other practices like <span title="Bioretention is a terrestrial-based (up-land as opposed to wetland) water quality and water quantity control process. Bioretention employs a simplistic, site-integrated design that provides opportunity for runoff infiltration, filtration, storage, and water uptake by vegetation. Bioretention areas are suitable stormwater treatment practices for all land uses, as long as the contributing drainage area is appropriate for the size of the facility. Common bioretention opportunities include landscaping islands, cul-de-sacs, parking lot margins, commercial setbacks, open space, rooftop drainage and street-scapes (i.e., between the curb and sidewalk). Bioretention, when designed with an underdrain and liner, is also a good design option for treating Potential stormwater hotspots. Bioretention is extremely versatile because of its ability to be incorporated into landscaped areas. The versatility of the practice also allows for bioretention areas to be frequently employed as stormwater retrofits."> '''bioretention practices'''</span> or <span title="A stormwater retention basin that includes a combination of permanent pool storage and extended detention storage above the permanent pool to provide additional water quality or rate control"> [https://stormwater.pca.state.mn.us/index.php?title=Stormwater_ponds '''wet ponds''']</span>. They reduce the flow velocity of water and filter and <span title="Infiltration Best Management Practices (BMPs) treat urban stormwater runoff as it flows through a filtering medium and into underlying soil, where it may eventually percolate into groundwater. The filtering media is typically coarse-textured and may contain organic material, as in the case of bioinfiltration BMPs."> [https://stormwater.pca.state.mn.us/index.php?title=Stormwater_infiltration_Best_Management_Practices '''infiltrate''']</span> pollutants such as sediment from stormwater.  Vegetated filter strips may be subject to high public visibility, trash loads, <span title="Sedimentation is the process by which solids are removed from the water column by settling. Sedimentation practices include dry ponds, wet ponds, wet vaults, and other devices."> [https://stormwater.pca.state.mn.us/index.php?title=Stormwater_sedimentation_Best_Management_Practices '''sedimentation''']</span>, pedestrian traffic, and even vehicular traffic or loads. Vegetated filter strips can provide <span title="Benefits derived from ecosystems and ecosystem functions. Examples of benefits include clean water, nutrient cycling, pollination, and detoxification of wastes."> '''ecosystem services'''</span> such as <span title="The movement and exchange of organic and inorganic matter back into the production of matter. Examples include the nutrient, phosphorus, and carbon cycles."> '''nutrient cycling'''</span> and storage, carbon <span title="to remove or withdraw"> '''sequestration'''</span>, <span title="Adjustments in ecological, social, or economic systems in response to actual or expected climatic stimuli and their effects or impacts."> '''climate adaptation'''</span>, and habitat for bees, butterflies, and other insects and small animals that pollinate.
  
*Flow channelization and erosion.
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Vegetated filter strips require dedicated and regular maintenance to ensure proper and long-lasting operation, and in most cases a vegetated filter strip should be designed to be effective for at least 10 years
*Insufficient/inadequate vegetative cover.
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([https://bwsr.state.mn.us/common-alternative-practice-2-nrcs-filter-strip-standard-mn-393391-practice-standards-public-waters NRCS], 2010). The most frequently cited O&M concerns for vegetated filter strips include
*Sediment and debris accumulation leading to practice clogging.
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*flow channelization and erosion,
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*insufficient/inadequate vegetative cover, and
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*sediment and debris accumulation leading to practice clogging.
  
 
The sections below describe best practices to prevent or minimize these common problems.
 
The sections below describe best practices to prevent or minimize these common problems.
  
 
==Design phase O&M considerations==
 
==Design phase O&M considerations==
Designers should design these practices in ways that prevent or minimize O&M issues. Examples include:
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[[file:Filter strip design schematic 1.png|500px|thumb|alt=filter strip schematic|<font size=3>Schematic illustrating design features for a pretreatment vegetated filter strip.</font size>]]
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Designers should design these practices in ways that prevent or minimize O&M issues. Examples include the following.
  
*Using a maximum drainage area to filter strip area ratio of 6:1
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*Using a maximum <span title="The total drainage area, including pervious and impervious surfaces, contributing to a BMP"> '''[https://stormwater.pca.state.mn.us/index.php?title=Contributing_drainage_area_to_stormwater_BMPs contributing drainage area]'''</span> to filter strip area ratio of 6:1
*Limiting the lateral slope to less than or equal to 1%
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*Limiting the lateral slope from contributing impervious surfaces to less than or equal to 1%
 
*Checking that the maximum groundwater level is 2 to 4 ft below the filter strip
 
*Checking that the maximum groundwater level is 2 to 4 ft below the filter strip
*Providing a vegetation design plan, emphasizing erosion resistant and native plantings (see [http://www.pca.state.mn.us/publications/manuals/stormwaterplants.html Plants for Stormwater Design]</span>) to enhance pollinator and wildlife habitat, improve <span title="Infiltration Best Management Practices (BMPs) treat urban stormwater runoff as it flows through a filtering medium and into underlying soil, where it may eventually percolate into groundwater. The filtering media is typically coarse-textured and may contain organic material, as in the case of bioinfiltration BMPs."> [https://stormwater.pca.state.mn.us/index.php?title=Stormwater_infiltration_Best_Management_Practices '''infiltration''']</span> and <span title="Loss of water to the atmosphere as a result of the joint processes of evaporation and transpiration through vegetation"> '''evapotranspiration'''</span>, reduce urban <span title="an urban area having higher average temperature than its rural surroundings owing to the greater absorption, retention, and generation of heat by its buildings, pavements, and human activities."> '''heat island'''</span> effect, provide optimized carbon sequestration, and provide climate adaptation. Site-specific plant selections should take into account sun exposure, shade, proximity to traffic corners (visibility issues), interior vs exterior plantings, salt-tolerant plants, etc. The selection of plantings suitable to their immediate surroundings will minimize long-term care and replacement frequency.  
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*Providing a vegetation design plan, emphasizing erosion resistant and native plantings (see [https://www.pca.state.mn.us/water/plants-stormwater-design Plants for Stormwater Design]) to enhance pollinator and wildlife habitat, improve <span title="Infiltration Best Management Practices (BMPs) treat urban stormwater runoff as it flows through a filtering medium and into underlying soil, where it may eventually percolate into groundwater. The filtering media is typically coarse-textured and may contain organic material, as in the case of bioinfiltration BMPs."> [https://stormwater.pca.state.mn.us/index.php?title=Stormwater_infiltration_Best_Management_Practices '''infiltration''']</span> and <span title="Loss of water to the atmosphere as a result of the joint processes of evaporation and transpiration through vegetation"> '''evapotranspiration'''</span>, reduce urban <span title="an urban area having higher average temperature than its rural surroundings owing to the greater absorption, retention, and generation of heat by its buildings, pavements, and human activities."> '''heat island'''</span> effect, provide optimized <span title="The process of capturing and storing atmospheric carbon dioxide.> '''carbon sequestration'''</span>, and provide <span title="Adjustments in ecological, social, or economic systems in response to actual or expected climatic stimuli and their effects or impacts."> '''climate adaptation'''</span>. Site-specific plant selections should take into account sun exposure, shade, proximity to traffic corners (visibility issues), interior vs exterior plantings, salt-tolerant plants, etc. The selection of plantings suitable to their immediate surroundings will minimize long-term care and replacement frequency.  
*Designing the filter strip length based on the <span title="A soil classification system (Natural Resource Conservation System) based on runoff potential. Groups include A soils (coarse textured with very low runoff potential), B soils (medium coarse textured with low runoff potential), C soils (fine to moderate textured with moderate runoff potential), and D soils (fine textured with high runoff potential)."> '''[https://stormwater.pca.state.mn.us/index.php?title=Design_infiltration_rates hydrologic soil group]'''</span>, slope, and vegetation (PADEP 2006).
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*Designing the filter strip length based on the <span title="A soil classification system (Natural Resource Conservation System) based on runoff potential. Groups include A soils (coarse textured with very low runoff potential), B soils (medium coarse textured with low runoff potential), C soils (fine to moderate textured with moderate runoff potential), and D soils (fine textured with high runoff potential)."> '''[https://stormwater.pca.state.mn.us/index.php?title=Design_infiltration_rates hydrologic soil group]'''</span>, slope, and vegetation ([http://www.depgreenport.state.pa.us/elibrary/GetFolder?FolderID=4673 PADEP], 2006).
 
*Providing [https://stormwater.pca.state.mn.us/index.php?title=Pretreatment pretreatment]</span> (e.g. gravel trench spreader) if necessary. Pretreatment can be used to dampen the effects of high or rapid inflow, dissipate energy, provide additional storage, and prevent the BMP from becoming overloaded by sediment. Pretreatment is a required part of infiltration and filtration practices covered under the Minnesota Construction Stormwater General Permit. Vegetated filter strips are often used as a [https://stormwater.pca.state.mn.us/index.php/Overview_for_pretreatment_vegetated_filter_strips pretreatment practice]</span> to meet the intent of the stormwater permit, as identified in [https://stormwater.pca.state.mn.us/index.php?title=2018_Minnesota_Construction_Stormwater_Permit sections 16 and 17]</span>, but are designed with a different set of standards when they are a standalone structural practice.  
 
*Providing [https://stormwater.pca.state.mn.us/index.php?title=Pretreatment pretreatment]</span> (e.g. gravel trench spreader) if necessary. Pretreatment can be used to dampen the effects of high or rapid inflow, dissipate energy, provide additional storage, and prevent the BMP from becoming overloaded by sediment. Pretreatment is a required part of infiltration and filtration practices covered under the Minnesota Construction Stormwater General Permit. Vegetated filter strips are often used as a [https://stormwater.pca.state.mn.us/index.php/Overview_for_pretreatment_vegetated_filter_strips pretreatment practice]</span> to meet the intent of the stormwater permit, as identified in [https://stormwater.pca.state.mn.us/index.php?title=2018_Minnesota_Construction_Stormwater_Permit sections 16 and 17]</span>, but are designed with a different set of standards when they are a standalone structural practice.  
*Installing berms where necessary to direct the flow and prevent bypassing.
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*Installing <span title="a level space, shelf, or raised barrier (usually made of compacted soil) separating two areas"> '''berms'''</span> where necessary to direct the flow and prevent <span title="Stormwater runoff in excess of the design flow, which is diverted around a stormwater structure"> '''bypassing'''</span>.
 
*Prohibiting any kind of traffic through the installation of a visible barrier or signage.
 
*Prohibiting any kind of traffic through the installation of a visible barrier or signage.
 
*Providing educational signage to increase public awareness.
 
*Providing educational signage to increase public awareness.
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Designers should consult and include any local requirements regarding <span title="Green stormwater infrastructure is designed to mimic nature and capture rainwater where it falls. Green infrastructure reduces and treats stormwater at its source while while also providing multiple community benefits such as improvements in water quality, reduced flooding, habitat, carbon capture, etc."> '''green infrastructure'''</span>. O&M considerations often depend on whether the practice is located on public land, private land, or in the public right of way. For example, plantings in the public right of way that conflict with any traffic safety considerations could require increased O&M, such as pruning or complete removal.
 
Designers should consult and include any local requirements regarding <span title="Green stormwater infrastructure is designed to mimic nature and capture rainwater where it falls. Green infrastructure reduces and treats stormwater at its source while while also providing multiple community benefits such as improvements in water quality, reduced flooding, habitat, carbon capture, etc."> '''green infrastructure'''</span>. O&M considerations often depend on whether the practice is located on public land, private land, or in the public right of way. For example, plantings in the public right of way that conflict with any traffic safety considerations could require increased O&M, such as pruning or complete removal.
  
Designers should also recognize the need to perform frequent maintenance to remove trash or excess sediment, check for clogging, and if necessary perform practice cleaning. Designers can incorporate design solutions to facilitate maintenance activities. Examples include:
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Designers should also recognize the need to perform frequent maintenance to remove trash or excess sediment, check for clogging, and if necessary perform practice cleaning. Designers can incorporate design solutions to facilitate maintenance activities. Examples include
*Incorporating multiple and easy site access points
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*incorporating multiple and easy site access points, and
*Providing recommendations of vegetation appropriate to the location
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*providing recommendations of vegetation appropriate to the location.
  
The designer should also provide a site-specific O&M plan that includes the following:
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The designer should also provide a site-specific O&M plan that includes the following.
 
*Construction inspection schedule and checklists
 
*Construction inspection schedule and checklists
 
*Post-construction routine maintenance schedule and checklists
 
*Post-construction routine maintenance schedule and checklists
 
*Operating instructions for the practice (if applicable)
 
*Operating instructions for the practice (if applicable)
  
For more design information on [https://stormwater.pca.state.mn.us/index.php?title=Design,_construction,_operation_and_maintenance_specifications_for_pretreatment_vegetated_filter_strips vegetated filter strips]</span>.
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For more design information on [https://stormwater.pca.state.mn.us/index.php?title=Design,_construction,_operation_and_maintenance_specifications_for_pretreatment_vegetated_filter_strips vegetated filter strips, link here]</span>.
  
 
==Construction phase O&M considerations==
 
==Construction phase O&M considerations==
Proper construction methods and sequencing play a significant role in reducing O&M problems. Some key items during the construction phase include:
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Proper construction methods and sequencing play a significant role in reducing O&M problems. Some key items during the construction phase include the following.
*Before construction begins:
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*'''Before construction begins'''
**Check the grading where the practice will be placed to enable sheet flow from the level spreader and throughout the filter strip. Grading must be uniformly perpendicular to the direction of flow to prevent channelized runoff.  
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**Check the grading where the practice will be placed to enable <span title="Water, usually storm runoff, flowing in a thin layer over the ground surface. A synonym is overland flow."> '''sheet flow'''</span> from the <span title="Level Spreaders are measures that reduce the erosive energy of concentrated flows by distributing runoff as sheet flow to stabilized vegetative surfaces."> '''level spreader'''</span> and throughout the filter strip. Grading must be uniformly perpendicular to the direction of flow to prevent <span title="Water flow focused into individual straight pathways rather than across a broad area (sheet flow)"> '''channelized flow'''</span>.  
**Protect the proposed filter strip from the surrounding area by using upstream sediment traps or barriers and diversions to direct stormwater flows from the contributing drainage area away from the practice.
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**Protect the proposed filter strip from the surrounding area by using upstream <span title="Sediment traps and basins are settling ponds formed by excavation and/or an embankment"> [https://stormwater.pca.state.mn.us/index.php?title=Sediment_control_practices_-_Sediment_traps_and_basins '''sediment traps''']</span> or barriers and diversions to direct stormwater flows from the contributing drainage area away from the practice.
 
**Install any needed <span title="Practices designed to prevent or minimize erosion> [https://stormwater.pca.state.mn.us/index.php?title=Erosion_prevention_practices '''erosion''']</span> and <span title="practices designed to prevent or minimize loss of eroded soil at a site"> [https://stormwater.pca.state.mn.us/index.php?title=Sediment_control_practices '''sediment controls''']</span> in your construction site and prepare a [https://stormwater.pca.state.mn.us/index.php?title=SWPPP_Template_for_Small_Construction_Sites storm water pollution prevention plan (SWPPP)]</span>.  
 
**Install any needed <span title="Practices designed to prevent or minimize erosion> [https://stormwater.pca.state.mn.us/index.php?title=Erosion_prevention_practices '''erosion''']</span> and <span title="practices designed to prevent or minimize loss of eroded soil at a site"> [https://stormwater.pca.state.mn.us/index.php?title=Sediment_control_practices '''sediment controls''']</span> in your construction site and prepare a [https://stormwater.pca.state.mn.us/index.php?title=SWPPP_Template_for_Small_Construction_Sites storm water pollution prevention plan (SWPPP)]</span>.  
 
**Designate a stormwater supervisor to make sure someone is responsible for erosion and sediment control.
 
**Designate a stormwater supervisor to make sure someone is responsible for erosion and sediment control.
 
**Hold a pre-construction meeting with the designer and the installer to review the construction plans and the sequencing of construction.
 
**Hold a pre-construction meeting with the designer and the installer to review the construction plans and the sequencing of construction.
*During construction:
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*'''During construction'''
 
**Construct any pretreatment devices first.  
 
**Construct any pretreatment devices first.  
 
**Implement soil stabilization measures until permanent vegetation is established.
 
**Implement soil stabilization measures until permanent vegetation is established.
 
**Use as much of the existing topsoil on the site as possible to enhance plant growth.
 
**Use as much of the existing topsoil on the site as possible to enhance plant growth.
**Prevent soil compaction by marking boundaries of the practice to ensure no construction traffic occurs on the practice. Foot traffic should be minimized if possible.  
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**Prevent <span title="The compression of soil particles into a smaller volume, which reduces the size of pore space available for air and water."> '''soil compaction'''</span> by marking boundaries of the practice to ensure no construction traffic occurs on the practice. Foot traffic should be minimized if possible.  
 
**Ensure that the plant and vegetation mix conforms to the vegetation design plan.
 
**Ensure that the plant and vegetation mix conforms to the vegetation design plan.
 
**Inspect the practice during construction to ensure that the vegetated filter strip practice is built in accordance with the approved design and standards and specifications.  
 
**Inspect the practice during construction to ensure that the vegetated filter strip practice is built in accordance with the approved design and standards and specifications.  
*After construction:
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*'''After construction'''
 
**Verify that the vegetated filter strip practice was built in accordance with the approved design and standards and specifications.  
 
**Verify that the vegetated filter strip practice was built in accordance with the approved design and standards and specifications.  
 
**Verify that the filter strip area is fully stabilized with vegetation prior to removing any barriers, diversions, or erosion and sediment control measures.
 
**Verify that the filter strip area is fully stabilized with vegetation prior to removing any barriers, diversions, or erosion and sediment control measures.
 
**Verify that the practice directs flow as intended over the entirety of the practice. This serves as a verification that the practice is functional at the time of construction.   
 
**Verify that the practice directs flow as intended over the entirety of the practice. This serves as a verification that the practice is functional at the time of construction.   
**Use a detailed inspection checklists that include sign-offs by qualified individuals at the completion of construction, to ensure that the contractor’s interpretation of the plan is acceptable to the professional designer. An example construction phase inspection checklist is provided further down below.
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**Use a detailed inspection checklists that include sign-offs by qualified individuals at the completion of construction, to ensure that the contractor’s interpretation of the plan is acceptable to the professional designer. An example construction phase inspection checklist is provided [https://stormwater.pca.state.mn.us/index.php?title=Operation_and_maintenance_(O%26M)_of_filter_strips#Useful_resources below].
 
**Review and discuss the plant warranty/establishment period with the plant provider to understand the conditions under which failing plants will be replaced.  
 
**Review and discuss the plant warranty/establishment period with the plant provider to understand the conditions under which failing plants will be replaced.  
**Determine if stormwater should be kept offline from the practice until the seedlings are established.
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**Determine if stormwater should be kept <span title="A stormwater system in which part or all of the stormwater runoff is diverted from the primary treatment practice. Partial diversion is employed for bypass runoff, which is runoff in excess of the designed treatment volume of the practice. Full offline diversion is employed as a temporary means to divert all runoff from a stormwater practice, typically to avoid erosion of exposed soil or establishment of vegetation."> '''offline'''</span> from the practice until the seedlings are established.
**The design/construction team should provide the O&M team with the following information to be included in the O&M plan:
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**The design/construction team should provide the O&M team with the following information to be included in the O&M plan.
 
***The plant warranty.  
 
***The plant warranty.  
***The “as-built” plans of the practice
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***The <span title="As-built refers to a drawing that shows the existing dimensions and conditions of a stormwater structure or device."> '''as-built'''</span> plans of the practice
 
***A list of conditions that might cause failure of the practice if not properly maintained.
 
***A list of conditions that might cause failure of the practice if not properly maintained.
  
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Some important post-construction considerations are provided below along with recommended maintenance standards.  
 
Some important post-construction considerations are provided below along with recommended maintenance standards.  
*A site-specific '''Operations and Maintenance Plan''' should be prepared by the designer prior to putting the practice into operation. This plan should provide any operating procedures related to the practices. The plan should also provide clear maintenance expectations, activities, and schedules. Include photos if possible. Be clear about who is responsible for the maintenance and the type of expertise that will be needed for distinct O&M activities. The O&M plan should include an anticipated budget for O&M activities. The O&M plan should also include an example O&M inspection checklist and an example maintenance report. Example O&M plans and checklists are provided in the “Useful Resources” section.  
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*A site-specific '''Operations and Maintenance Plan''' should be prepared by the designer prior to putting the practice into operation. This plan should provide any operating procedures related to the practices. The plan should also provide clear maintenance expectations, activities, and schedules. Include photos if possible. Be clear about who is responsible for the maintenance and the type of expertise that will be needed for distinct O&M activities. The O&M plan should include an anticipated budget for O&M activities. The O&M plan should also include an example O&M inspection checklist and an example maintenance report. Example O&M plans and checklists are provided in the [https://stormwater.pca.state.mn.us/index.php?title=Operation_and_maintenance_(O%26M)_of_filter_strips#Useful_resources Useful Resources section].  
*A legally binding and enforceable maintenance agreement should be executed between the practice owner and the local review authority that provides adequate access for the inspection, maintenance, and necessary equipment. Example maintenance agreements are provided in the “Useful Resources” section.
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*A legally binding and enforceable maintenance agreement should be executed between the practice owner and the local review authority that provides adequate access for the inspection, maintenance, and necessary equipment. Example maintenance agreements are provided in the [https://stormwater.pca.state.mn.us/index.php?title=Operation_and_maintenance_(O%26M)_of_filter_strips#Useful_resources Useful Resources section].
 
*Inspection and maintenance activities are distinct and can be done as separate activities or together. Inspection will typically assess the practice for any O&M issues, whereas maintenance will address the O&M issues identified by the inspection. A dedicated inspection effort on a large number of BMPs can help prioritize maintenance activities.  
 
*Inspection and maintenance activities are distinct and can be done as separate activities or together. Inspection will typically assess the practice for any O&M issues, whereas maintenance will address the O&M issues identified by the inspection. A dedicated inspection effort on a large number of BMPs can help prioritize maintenance activities.  
 
*While maintenance is being conducted, ensure that no heavy vehicle traffic occurs on the vegetated filter strip and foot traffic is limited to avoid compaction.
 
*While maintenance is being conducted, ensure that no heavy vehicle traffic occurs on the vegetated filter strip and foot traffic is limited to avoid compaction.
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==Maintenance costs==
 
==Maintenance costs==
Maintenance costs will vary on a number of factors, including but not limited to:
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Maintenance costs will vary on a number of factors, including but not limited to the following.
*Size of the practice and its contributing drainage area
+
*Size of the practice and its <span title="The total drainage area, including pervious and impervious surfaces, contributing to a BMP"> '''[https://stormwater.pca.state.mn.us/index.php?title=Contributing_drainage_area_to_stormwater_BMPs contributing drainage area]'''</span>
 
*Type of plantings used
 
*Type of plantings used
 
*Site visit frequency
 
*Site visit frequency
Line 101: Line 110:
 
*Equipment needed
 
*Equipment needed
  
Preventative maintenance is key to minimizing major costs associated with repairs. The annual cost of maintaining filter strips (mowing, weeding, inspection, litter removal, etc.) is generally between $100 and $1,400 per acre (based on 2006 cost estimate, PADEP 2006). Maintenance may be higher the first few years, while plants are being established.
+
Preventative maintenance is key to minimizing major costs associated with repairs. The annual cost of maintaining filter strips (mowing, weeding, inspection, litter removal, etc.) is generally between $100 and $1,400 per acre (based on 2006 cost estimate, [http://www.depgreenport.state.pa.us/elibrary/GetFolder?FolderID=4673 PADEP 2006]). Maintenance may be higher the first few years, while plants are being established.
  
 
==Useful resources==
 
==Useful resources==
  
 
===Additional detailed O&M information===
 
===Additional detailed O&M information===
More detailed information regarding specific maintenance activities are provided in the [[Vegetated filter strip detailed maintenance activity description]] page<br><br>
+
Supplemental information can be found on the page called [[Operation and maintenance of filter strips - supplemental information]]. Supplemental information includes the following.
Topics discussed include:
+
*Removing sediment and debris buildup
*Removing sediment debris build up
+
*Preventing or minimizing <span title"the removal or erosion of material captured by a stormwater device, typically a result of subsequent high flow volumes or rates or inadequate maintenance of the device"> '''washout'''</span> and erosion of the <span title="Pretreatment reduces maintenance and prolongs the lifespan of structural stormwater BMPs by removing trash, debris, organic materials, coarse sediments, and associated pollutants prior to entering structural stormwater BMPs. Implementing pretreatment devices also improves aesthetics by capturing debris in focused or hidden areas. Pretreatment practices include settling devices, screens, and pretreatment vegetated filter strips."> [https://stormwater.pca.state.mn.us/index.php?title=Pretreatment '''pretreatment''']</span> vegetated filter strip
*Preventing or minimizing washouts and erosion of the pretreatment vegetated filter strip
 
 
*Vegetation establishment
 
*Vegetation establishment
 
*Maintaining vegetation
 
*Maintaining vegetation
*Snow Storage
+
*Snow storage
 
*Maintenance agreements
 
*Maintenance agreements
*Additional References
+
*Additional references
  
 
===Case studies===
 
===Case studies===
Line 120: Line 128:
  
 
===Maintenance training documents and videos===
 
===Maintenance training documents and videos===
*Chesapeake Stormwater Network: Filter Strips and Grass Channels Webcast Slides
+
*[https://chesapeakestormwater.net/tag/filter-strip/ Chesapeake Stormwater Network: Filter Strips and Grass Channels Webcast Slides]
*UMass Amherst: Vegetative Filter Strips May Deter Pesticide Runoff
+
*[https://www.youtube.com/watch?v=Sw-Aj7ADfWw UMass Amherst: Vegetative Filter Strips May Deter Pesticide Runoff] - YouTube video
  
 
===O&M resource catalog===
 
===O&M resource catalog===
MPCA has compiled publicly available O&M resources related to green infrastructure. This non-exhaustive catalog is intended as a resource to practitioners.  
+
MPCA has compiled [https://stormwater.pca.state.mn.us/index.php?title=Green_infrastructure_operation_and_maintenance_catalog_wiki_table publicly available O&M resources] ([https://stormwater.pca.state.mn.us/index.php?title=File:Green_Infrastructure_Operation_and_Maintenance_Resource_Catalogue.xlsx Excel format]) related to green infrastructure. This non-exhaustive catalog is intended as a resource to practitioners.
https://docs.google.com/spreadsheets/d/1TNGVghLhudcWPgXKLbLAu2cUWv6O3ZeS7-FIuLSGIPM/edit#gid=0
 
  
 
{{:Example O&M plans, checklists, reports, and maintenance agreements for vegetated filter strips}}
 
{{:Example O&M plans, checklists, reports, and maintenance agreements for vegetated filter strips}}
 +
 +
==References==
 +
*PADEP. 2006. [http://www.depgreenport.state.pa.us/elibrary/GetFolder?FolderID=4673 Pennsylvania Stormwater Best Management Practices Manual]. Volume 34.
 +
*NRCS, 2010. [https://bwsr.state.mn.us/common-alternative-practice-2-nrcs-filter-strip-standard-mn-393391-practice-standards-public-waters Conservation Practice Standard].
 +
 +
<noinclude>
 +
 +
==Related pages==
 +
*[[Overview for pretreatment vegetated filter strips]]
 +
*[[Design, construction, operation and maintenance specifications for pretreatment vegetated filter strips]]
 +
===Green infrastructure O&M===
 +
*[[Green Stormwater Infrastructure (GSI) and sustainable stormwater management]]
 +
*Operation and maintenance of green infrastructure practices
 +
**[[Operation and maintenance of bioretention and other stormwater infiltration practices]]
 +
**[[Operation and maintenance of bioretention and other stormwater infiltration practices - supplemental information]]
 +
**[[Operation and maintenance (O&M) of tree trenches and tree boxes]]
 +
**[[Operation and maintenance of tree trenches and tree boxes - supplemental information]]
 +
**[[Operation and maintenance (O&M) of green roofs]]
 +
**[[Operation and maintenance of green roofs - supplemental information]]
 +
**[[Operation and maintenance (O&M) of swales]]
 +
**[[Operation and maintenance of swales - supplemental information]]
 +
**[[Operation and maintenance (O&M) of filter strips]]
 +
**[[Operation and maintenance of filter strips - supplemental information]]
 +
**[[Operation and maintenance (O&M) of stormwater and rainwater harvest and use/reuse practices]]
 +
**[[Operation and maintenance (O&M) of stormwater and rainwater harvest and use/reuse practices - supplemental information]]
 +
**[[Operation and maintenance (O&M) of stormwater treatment wetland practices]]
 +
**[[Operation and maintenance (O&M) of permeable pavement]]
 +
**[[Operation and maintenance (O&M) of permeable pavement - supplemental information]]
 +
 +
[[Category:Level 3 - Best management practices/Specifications and details/Operation and maintenance]]
 +
</noinclude>

Latest revision as of 13:37, 30 December 2022

image
Image of a vegetated filter strip
Image of a vegetated filter strip
Green Infrastructure: Filter strips, when vegetated, provide water quality benefits, may provide some stormwater volume reduction, and may provide typical benefits of vegetation, such as habitat, depending on the vegetation type.

This page provides guidance for operation and maintenance (O&M) of filter strips. Filter strips are designed to filter suspended solids from runoff as water passes over the filter strip. Most filter strips are vegetated, with grass and perennial native vegetation most widely used.

Supplemental information can be found on the page called Operation and maintenance of filter strips - supplemental information. Supplemental information includes the following.

  • Removing sediment and debris buildup
  • Preventing or minimizing washout and erosion of the pretreatment vegetated filter strip
  • Vegetation establishment
  • Maintaining vegetation
  • Snow storage
  • Maintenance agreements
  • Additional references

Overview of typical O&M issues

Vegetated filter strip, also known as buffer strips or buffers, are vegetated land areas between a pollutant source and a surface water body (also called a receiving water). They can be stand-alone practices or used as pretreatment to other practices like bioretention practices or wet ponds. They reduce the flow velocity of water and filter and infiltrate pollutants such as sediment from stormwater. Vegetated filter strips may be subject to high public visibility, trash loads, sedimentation, pedestrian traffic, and even vehicular traffic or loads. Vegetated filter strips can provide ecosystem services such as nutrient cycling and storage, carbon sequestration, climate adaptation, and habitat for bees, butterflies, and other insects and small animals that pollinate.

Vegetated filter strips require dedicated and regular maintenance to ensure proper and long-lasting operation, and in most cases a vegetated filter strip should be designed to be effective for at least 10 years (NRCS, 2010). The most frequently cited O&M concerns for vegetated filter strips include

  • flow channelization and erosion,
  • insufficient/inadequate vegetative cover, and
  • sediment and debris accumulation leading to practice clogging.

The sections below describe best practices to prevent or minimize these common problems.

Design phase O&M considerations

filter strip schematic
Schematic illustrating design features for a pretreatment vegetated filter strip.

Designers should design these practices in ways that prevent or minimize O&M issues. Examples include the following.

  • Using a maximum contributing drainage area to filter strip area ratio of 6:1
  • Limiting the lateral slope from contributing impervious surfaces to less than or equal to 1%
  • Checking that the maximum groundwater level is 2 to 4 ft below the filter strip
  • Providing a vegetation design plan, emphasizing erosion resistant and native plantings (see Plants for Stormwater Design) to enhance pollinator and wildlife habitat, improve infiltration and evapotranspiration, reduce urban heat island effect, provide optimized carbon sequestration, and provide climate adaptation. Site-specific plant selections should take into account sun exposure, shade, proximity to traffic corners (visibility issues), interior vs exterior plantings, salt-tolerant plants, etc. The selection of plantings suitable to their immediate surroundings will minimize long-term care and replacement frequency.
  • Designing the filter strip length based on the hydrologic soil group, slope, and vegetation (PADEP, 2006).
  • Providing pretreatment (e.g. gravel trench spreader) if necessary. Pretreatment can be used to dampen the effects of high or rapid inflow, dissipate energy, provide additional storage, and prevent the BMP from becoming overloaded by sediment. Pretreatment is a required part of infiltration and filtration practices covered under the Minnesota Construction Stormwater General Permit. Vegetated filter strips are often used as a pretreatment practice to meet the intent of the stormwater permit, as identified in sections 16 and 17, but are designed with a different set of standards when they are a standalone structural practice.
  • Installing berms where necessary to direct the flow and prevent bypassing.
  • Prohibiting any kind of traffic through the installation of a visible barrier or signage.
  • Providing educational signage to increase public awareness.

Designers should consult and include any local requirements regarding green infrastructure. O&M considerations often depend on whether the practice is located on public land, private land, or in the public right of way. For example, plantings in the public right of way that conflict with any traffic safety considerations could require increased O&M, such as pruning or complete removal.

Designers should also recognize the need to perform frequent maintenance to remove trash or excess sediment, check for clogging, and if necessary perform practice cleaning. Designers can incorporate design solutions to facilitate maintenance activities. Examples include

  • incorporating multiple and easy site access points, and
  • providing recommendations of vegetation appropriate to the location.

The designer should also provide a site-specific O&M plan that includes the following.

  • Construction inspection schedule and checklists
  • Post-construction routine maintenance schedule and checklists
  • Operating instructions for the practice (if applicable)

For more design information on vegetated filter strips, link here.

Construction phase O&M considerations

Proper construction methods and sequencing play a significant role in reducing O&M problems. Some key items during the construction phase include the following.

  • Before construction begins
    • Check the grading where the practice will be placed to enable sheet flow from the level spreader and throughout the filter strip. Grading must be uniformly perpendicular to the direction of flow to prevent channelized flow.
    • Protect the proposed filter strip from the surrounding area by using upstream sediment traps or barriers and diversions to direct stormwater flows from the contributing drainage area away from the practice.
    • Install any needed erosion and sediment controls in your construction site and prepare a storm water pollution prevention plan (SWPPP).
    • Designate a stormwater supervisor to make sure someone is responsible for erosion and sediment control.
    • Hold a pre-construction meeting with the designer and the installer to review the construction plans and the sequencing of construction.
  • During construction
    • Construct any pretreatment devices first.
    • Implement soil stabilization measures until permanent vegetation is established.
    • Use as much of the existing topsoil on the site as possible to enhance plant growth.
    • Prevent soil compaction by marking boundaries of the practice to ensure no construction traffic occurs on the practice. Foot traffic should be minimized if possible.
    • Ensure that the plant and vegetation mix conforms to the vegetation design plan.
    • Inspect the practice during construction to ensure that the vegetated filter strip practice is built in accordance with the approved design and standards and specifications.
  • After construction
    • Verify that the vegetated filter strip practice was built in accordance with the approved design and standards and specifications.
    • Verify that the filter strip area is fully stabilized with vegetation prior to removing any barriers, diversions, or erosion and sediment control measures.
    • Verify that the practice directs flow as intended over the entirety of the practice. This serves as a verification that the practice is functional at the time of construction.
    • Use a detailed inspection checklists that include sign-offs by qualified individuals at the completion of construction, to ensure that the contractor’s interpretation of the plan is acceptable to the professional designer. An example construction phase inspection checklist is provided below.
    • Review and discuss the plant warranty/establishment period with the plant provider to understand the conditions under which failing plants will be replaced.
    • Determine if stormwater should be kept offline from the practice until the seedlings are established.
    • The design/construction team should provide the O&M team with the following information to be included in the O&M plan.
      • The plant warranty.
      • The as-built plans of the practice
      • A list of conditions that might cause failure of the practice if not properly maintained.

Post-construction phase O&M

Effective short and long-term operation of vegetated filter strips requires a dedicated and routine maintenance plan with clear guidelines, expectations, and schedules. Proper maintenance will not only increase the expected lifespan of the facility but will improve aesthetics and property value. A maintenance plan clarifying maintenance responsibilities should be required for all practices.

Some important post-construction considerations are provided below along with recommended maintenance standards.

  • A site-specific Operations and Maintenance Plan should be prepared by the designer prior to putting the practice into operation. This plan should provide any operating procedures related to the practices. The plan should also provide clear maintenance expectations, activities, and schedules. Include photos if possible. Be clear about who is responsible for the maintenance and the type of expertise that will be needed for distinct O&M activities. The O&M plan should include an anticipated budget for O&M activities. The O&M plan should also include an example O&M inspection checklist and an example maintenance report. Example O&M plans and checklists are provided in the Useful Resources section.
  • A legally binding and enforceable maintenance agreement should be executed between the practice owner and the local review authority that provides adequate access for the inspection, maintenance, and necessary equipment. Example maintenance agreements are provided in the Useful Resources section.
  • Inspection and maintenance activities are distinct and can be done as separate activities or together. Inspection will typically assess the practice for any O&M issues, whereas maintenance will address the O&M issues identified by the inspection. A dedicated inspection effort on a large number of BMPs can help prioritize maintenance activities.
  • While maintenance is being conducted, ensure that no heavy vehicle traffic occurs on the vegetated filter strip and foot traffic is limited to avoid compaction.
  • Minimize use of any fertilizer.
  • Avoid mowing when the ground is wet. Doing so can create rutting from the wheels.
  • Vegetated filter strips should not be used for permanent snow storage because this will extend the duration of ineffective treatment caused by increased snowpack. Other snow and salting considerations can be found on the Vegetated filter strip detailed maintenance activity description page.

Overview and schedule of general maintenance activities for vegetated filter strips
Link to this table

First Year of Operation
Activity Frequency Time period Level of effort O&M benefita
Inspect the level spreader for sediment buildup and the vegetation for signs of erosion, bare spots, and overall health. At least twice after storm events 0.5 inches Within the first 6 months 1-2 hours 1,5
Check for evidence of clogging or failing of the inlet, outlet, and bypass pipes. At least twice after storm events 0.5 inches Within the first 6 months <1 hour 1
Remove any stormwater diversion or barriers once seedlings are established. Once When plants are sufficiently established 1-2 hours 1,2,3,4,5
Supplemental watering during drier periods, particularly if keeping stormwater offline until plant seedlings are established. 1/week initially During first 2 months 1-2 hours 2,3,4,5,6
As needed First growing season 1-2 hours 2,3,4,5,6
Mow grass in surrounding area to 3-4 inches As needed During growing season 1 hour 1,2,3,4,5,6
Removal of sediment and debris from the toe of slope or level spreader. Biannually In spring and fall 1-2 hours 1,5
Reseed bare spots as needed. As needed First growing season 2-4 hours 1,2,3,4,5,6
After First Year of Operation
Activity Frequency Time Period Level of Effort per Visit O&M Benefita
Inspect the level spreader for sediment buildup and the vegetation for signs of erosion, bare spots, and overall health. Annually and after storm events larger than the 10-year return period After winter and after storm events larger than the 10-year return period 1-2 hours 1,5
Mow the grass or vegetation only if needed. Avoid mowing when the ground is wet. As needed During growing season 1-2 hours 1,2,3,4,5,6
Inspect for and remove excess sediment in the pre-treatment device and/or in the main treatment area. Monthly All year long 4 hours if removal is needed 1
Remove sediment and debris from the toe of slope or level spreader. Biannually In spring and fall 1-2 hours 1,5
Remove trash and debris from the pre-treatment device and/or in the main treatment area. Monthly during rainy season All year long. Cleaning may need to be done more frequently during the summer storm season and less during the drier winter season 1-2 hours 1,5
Mow grass in surrounding area to 3-4 inches As needed During growing season 1 hour 1,2,3,4,5,6
Weed and remove invasive plants Twice during growing season During growing season 1-2 hours 2,3,4,5
Inspect plant composition and health and replace as needed Annually In fall or spring 4 hours if plant replacement is needed 2,3,4,5,6
Reseed bare spots as needed. Biannually In spring and fall 1-2 hours 1,2,3,4,5,6
Supplemental watering during drier periods, particularly if keeping stormwater offline until plant seedlings are established. As needed during extended dry periods Dry periods 1-2 hours 2,3,4,5,6
Spring cleanup (cut back and remove last year’s material) Annually In spring 2-4 hours 2,3,4,5
Fall cleanup (removed excessive leaf litter, particularly in areas with lots of trees) Annually In fall 2-4 hours 2,3,4,5
After 5+ Years of Operation (non-routine maintenance)
Activity Frequency Time Period Level of Effort per Visit O&M Benefita
After long term operation of the practice, some occasional and infrequent maintenance activities might be required, such as bigger repairs, soil regeneration, regrading, or redesign of key elements of the practice. As needed As needed Could be significant depending on the activity 1,2,3,4,5,6

Key to Maintenance Benefits:

  1. Proper stormwater flow and infiltration
  2. Creation and maintenance of wildlife habitat
  3. Creation and maintenance of pollinator habitat
  4. Nutrient cycling and storage
  5. Aesthetics and public enjoyment
  6. Carbon sequestration


Common problems and how to troubleshoot them for vegetated filter strips
Link to this table



Consult with a landscaper or horticulturist. Check that plants are suited to the local conditions. Replace soils and plants
Symptom Possible Causes Solution
Channelization of flow Improper grading Install infiltration trench or level gravel spreader trench upstream of practice
Erosion Improper (too steep) grading and/or plant loss Correct for drainage and flow path issues to make sure flows are evenly distributed. Make sure the flow paths are unobstructed
Vegetation is not able to establish Plant selection is inappropriate for the site Consult with a landscaper or horticulturist. Check that plants are suited to the local conditions. Make sure BMP is protected from snow storage or salt application.


Maintenance costs

Maintenance costs will vary on a number of factors, including but not limited to the following.

  • Size of the practice and its contributing drainage area
  • Type of plantings used
  • Site visit frequency
  • Level of maintenance needed
  • Local weather conditions
  • Staffing needs (number of staff, external vs. internal staff, etc)
  • Travel time between sites
  • Efficiencies of scale (single GI vs. a cluster of GI)
  • Equipment needed

Preventative maintenance is key to minimizing major costs associated with repairs. The annual cost of maintaining filter strips (mowing, weeding, inspection, litter removal, etc.) is generally between $100 and $1,400 per acre (based on 2006 cost estimate, PADEP 2006). Maintenance may be higher the first few years, while plants are being established.

Useful resources

Additional detailed O&M information

Supplemental information can be found on the page called Operation and maintenance of filter strips - supplemental information. Supplemental information includes the following.

  • Removing sediment and debris buildup
  • Preventing or minimizing washout and erosion of the pretreatment vegetated filter strip
  • Vegetation establishment
  • Maintaining vegetation
  • Snow storage
  • Maintenance agreements
  • Additional references

Case studies

Maintenance training documents and videos

O&M resource catalog

MPCA has compiled publicly available O&M resources (Excel format) related to green infrastructure. This non-exhaustive catalog is intended as a resource to practitioners.

Example O&M plans, checklists, reports, and maintenance agreements for vegetated filter strips
Link to this table

Document Link
Operation and maintenance plan O&M Plan for commercial building in Fairhaven, MA
Construction phase inspection checklist Fairfax County, VA
Virginia DEQ BMP Clearinghouse
O&M inspection checklist MPCA Checklist
University of Kentucky
City of Roseville, CA
City of Durham, NC
O&M example report Milwaukee Metropolitan Sewerage District (MMSD)
Metropolitan St. Louis Sewer District (MSD)
Maintenance Agreements Example Maintenance Agreement 1
Example Maintenance Agreement 2
Example Maintenance Agreement 3


References


Related pages

Green infrastructure O&M

This page was last edited on 30 December 2022, at 13:37.