m |
|||
(3 intermediate revisions by the same user not shown) | |||
Line 40: | Line 40: | ||
*Providing a vegetation design plan, emphasizing the following considerations | *Providing a vegetation design plan, emphasizing the following considerations | ||
**Utilizing native plantings that enhance pollinator and wildlife habitat, improve infiltration and <span title="Practices designed to prevent or minimize erosion> [https://stormwater.pca.state.mn.us/index.php?title=Erosion_prevention_practices '''erosion protection''']</span> | **Utilizing native plantings that enhance pollinator and wildlife habitat, improve infiltration and <span title="Practices designed to prevent or minimize erosion> [https://stormwater.pca.state.mn.us/index.php?title=Erosion_prevention_practices '''erosion protection''']</span> | ||
− | *<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 climate adaptation. Native plantings typically require less maintenance and replacement than non-native plantings because they are adapted to the local climate ([https:// | + | *<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 climate adaptation. Native plantings typically require less maintenance and replacement than non-native plantings because they are adapted to the local climate ([https://stormwater.pca.state.mn.us/index.php?title=Minnesota_plant_lists see Plants for Stormwater Design]). |
**Site-specific plantings that 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. | **Site-specific plantings that 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. | ||
*Providing educational signage for swales in residential areas to increase public awareness | *Providing educational signage for swales in residential areas to increase public awareness | ||
Line 176: | Line 176: | ||
**[[Operation and maintenance (O&M) of permeable pavement - supplemental information]] | **[[Operation and maintenance (O&M) of permeable pavement - supplemental information]] | ||
− | [[Category: | + | [[Category:Level 3 - Best management practices/Structural practices/Wet swale]] |
+ | [[Category:Level 3 - Best management practices/Specifications and details/Operation and maintenance]] | ||
</noinclude> | </noinclude> |
This page provides guidance for operation and maintenance (O&M) of swales. This includes dry swales, wet swales, bioswales, and high gradient step pools.
Supplemental information can be found on the page called Operation and maintenance of swales - supplemental information. Supplemental information includes the following.
A grass or dry swale is a general term for filtration or infiltration conveyance practice, but there are a wide variety of designs depending on the site requirements. The key functions of swales are to convey water with reduced peak velocities and to perform water quality treatment with filtration and infiltration. Swales have the benefit of providing ecological function in areas dominated by development and impervious surface. These practices are ideal for urban settings, which creates an opportunity for humans to impact their function through vandalism, littering, and vehicular traffic.
These practices, like other green stormwater infrastructure, require regular maintenance to ensure proper and long-lasting ecosystem and stormwater function. If properly maintained, swales can operate effectively for 20-50 years, depending on the design type. Vegetated dry swales may perform properly for up to 50 years (Malvern Borough, 2013). The most frequently cited O&M concerns for swales include the following.
The sections below describe best practices to prevent or minimize these common problems.
Swales, like other infiltration practices in urban areas, may be subject to higher public visibility, greater trash loads, pedestrian traffic, vandalism, and vehicular loads. Designers should design these practices in ways that prevent or minimize O&M issues. Examples include the following.
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. Swales are particularly subject to traffic considerations and regulations, given their frequent placement in public right-of-way.
The designer should also provide a site-specific O&M plan that includes the following.
For more information on design criteria for dry swale (grass swales).
Proper construction methods and sequencing play a significant role in reducing O&M problems. Some key items during the construction phase include the following.
Effective short and long-term performance of grass swales requires a dedicated and routine maintenance plan with clear guidelines, expectations, and schedules. Proper maintenance will not only increase the effectiveness of the swale at treating stormwater runoff, but will create a viable green space supporting ecological function. 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.
Overview and schedule of general maintenance activities for swales
Link to this table
Activity | Frequency | Time Period | Level of Effort | O&M Benefit1 |
---|---|---|---|---|
Check that there is no ponding | 48 hours after event | All year long | 1 hour | 1 |
Inspect entire BMP after rainfall | After any event greater than 0.5” | All year long (or during area’s rain season) | 2-4 hours | 1 |
Correct earthwork if inlet scouring or unwanted flow paths develop | As needed | All year long | >4 hours | 1 |
Spot reseed bare patches and eroding areas | As needed | First growing season | 2-4 hours | 3,4,5 |
Supplemental watering during drier periods, particularly if keeping stormwater offline until plant seedlings are established. | As needed | Dry periods | 1-2 hours | 3,4,5 |
Remove any stormwater diversion or barriers once seedlings are established. | Once | When plants are sufficiently established | 1-2 hours | 1,2,3,4,5 |
Inspect and remove invasive plants and weeds during plant community establishment | Monthly | First growing season | 1-2 hours | 5,6 |
Mowing (dry swales) side slopes and/or grass filter strip to maintain 4-12” of height | Seasonally | As needed (do not interrupt any vegetative establishment) | 2-4 hours | 1 |
Activity | Frequency | Time Period | Level of Effort | O&M Benefit1 |
Check that there is no ponding | 48 hours after event | All year long | 1 hour | 1 |
Inspect inlet/outlet structures for structural damage and clogging. | Annually | All year long | 1-2 hours | 1 |
Correct earthwork if inlet scouring or unwanted flow paths develop | As needed | All year long | >4 hours | 1 |
Mowing (dry swales) side slopes and/or grass filter to maintain 4-12” of height | Seasonally | All year long | 2-4 hours | 1 |
Inspect for trash and debris | Seasonally | All year long | 2-4 hours | 1,5 |
Check for evidence of clogging in the pre-treatment device and/or in the main treatment area. | Biannually | In spring and fall | 1-2 hours | 1 |
Inspect and remove excess sediment in the pre-treatment device and/or in the main treatment area. | Annually | In spring (post- snowmelt) and fall | 4 hours if removal is needed | 1 |
Inspect plant composition and health and replace as needed (maintain >95% vegetative cover) | Biannually | In fall or spring | 4 hours if plant replacement is needed | 4,5 |
Prune and weed to maintain appearance and proper vegetative cover | As needed | Growing season | 1-2 hours | 4,5,6, |
Activity | Frequency | Time Period | Level of Effort per Visit | O&M Benefit1 |
After long term operation of the practice, some occasional and infrequent maintenance activities might be required, such as bigger repairs, soil regeneration, 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 |
1Key to Maintenance Benefits:
|
Common problems and how to troubleshoot them for swales
Link to this table
Symptom | Possible Causes | Solution |
---|---|---|
Standing water within the swale for more than 48 hours | Soil media may be clogged with accumulated sediment or the outlet structures may be clogged with trash or de |
|
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 will vary on a number of factors, including but not limited to the following.
Maintenance costs will vary depending on the size of the practice, its contributing drainage area, type of plantings, and whether it is part of a larger green infrastructure effort. Preventative maintenance is key to minimizing major costs associated with repairs. A general rule of thumb to estimate annual maintenance costs is 5%-7% of the installation costs for swales (CWP, 2017). In 2014 dollars, the annual cost of maintenance is approximately $0.06-$0.12 per square foot of practice, which adjusts to $0.07-$0.14 in 2021 dollars, as estimated in the National Stormwater Calculator (Clary, 2017). Maintenance may be higher the first few years, while plants are being established.
Maintenance costs should account for the number of hours of labor, the cost for different types of labor expertise required, and any equipment needed to successfully complete the maintenance activities.
More detailed information regarding specific maintenance activities are provided here. Topics discussed include
Example O&M plans, checklists, reports, and maintenance agreements for swales
Link to this table
Document | Link |
---|---|
Operation & Maintenance Plan | |
Construction phase inspection checklist |
|
O&M inspection checklist |
|
O&M example report | |
Maintenance Agreements |
This page was last edited on 28 January 2023, at 17:19.