Rain gardens are shallow depressions in the landscape that typically
include plants and a mulch layer or ground cover. In addition to providing
increased groundwater recharge, they are expected to provide pollutant
treatment. Pollutant treatment in rain gardens has been attributed to
adsorption, decomposition, ion exchange, and volatilization (Prince
George's County Bioretention Manual, 2002). Rain gardens can be used
in residential settings to accept runoff from a roof or other impervious
surface. In a commercial setting, bioretention areas are similar to rain
gardens, but are often larger, and have an engineered design.
Rain garden at Tolland Agricultural Center (courtesy of Vivan Felten, NRCS). For detailed about this project from the CT LID database, click here.
Design considerations during review
One important note: rain gardens are not water gardens! The gardens
are typically designed to infiltrate water very quickly: around 4-6 hours. This
rapid infiltration will eliminate the chances of creating mosquito habitat.
If an improperly installed rain garden is holding water for excessive periods
of time after a storm, the installer should repair the problem. Compaction of
the rain garden material and/or premature clogging through siltation of the infiltration surface
will lead to excessive ponding.
Residential rain gardens are often sized to hold one inch of runoff in above-ground
storage from the contributing impervious surface. This sizing method has two
benefits: first, the garden will capture the dirtiest portion of the runoff,
or the "first flush". Second, in many parts of the country, the majority
(around 90%) of storms are one inch or less in size. What this means is that
sizing the garden to contain this volume of water will give the most benefit,
without oversizing it to try to contain larger, more infrequent events that
are a much smaller portion of the total yearly runoff volume.
Bioretention areas at larger commercial sites should be designed by an engineer.
The Bioretention Manual referenced above contains guidance on this. Although
bioretention areas at larger commercial sites should have engineered design,
you can easily design and create a rain garden for your own home! A guide for residential rain gardens in Connecticut is available
through the University of Connecticut extension.A manual from
the Wisconsin DNR also provides thorough
guidance.
Click on image above to view larger image (pdf).
For more information, visit the following sections of the CT Stormwater Quality Manual:
Chapter 4, Section 4.4.2
Chapter 11, Filtering Practices, P-4
Rain gardens in residential areas may be part of an overall LID approach to
a site. There are several things to look for on such a plan:
Look for the rain garden to be placed so that it will accept runoff from an
impervious area such as a roof, driveway, or patio. How will the water enter
the garden? Will it be diverted from a gutter and flow over grass, or will there
be a pipe from the gutter downspout to the garden? A rain garden with a direct
pipe will need to have stone or some other durable material where the pipe enters
the garden to slow the water down and reduce erosion. A garden that accepts
flow from a grassed area needs to have a broad entrance point for the water
so that the flow does not become concentrated and cause erosion. These types
of items should be shown on the plan detail.
The garden should not be placed closer than 10 feet to a house that has a foundation
with below-grade space, to avoid water problems in the basement. The garden
also should not be placed closer than about 10 feet to a well, or near a septic
system.
A rain garden should not be in or very close to wetland soils. If the garden
is proposed to be placed near wetland delineation lines, odds are the soils
won't have a sufficient infiltration rate, and ponding may occur for long periods
of time. This will create a nuisance condition, and will increase the likelihood
of mosquito production.
A rain garden should not be placed in an area that has a shallow depth to bedrock, or less than 2 feet from the bottom of the garden.
Check the proposed plant list, and make sure that wetland plants are not proposed.
A rain garden is not designed to have wetland plants. Plants listed in Appendix
A of the CT Stormwater
Quality manual that are in "Zone 4 Riparian Fringe" are most appropriate
for rain gardens. Another list of suggested
rain garden plants for Connecticut has been compiled by John Alexopoulos
in the Plant Science department at the University of Connecticut.
A special soil mix may be recommended, or native soils may be used if the infiltration
rate is sufficient. If a special mix is not recommended, look for some justification
as to why the native soils are sufficient.
An underdrain may be installed beneath the soil layer, to prevent excessive
ponding. This drain may be connected to the stormwater system, but if it is
possible, it is better to let it run out onto a lawn or wooded area, as a foundation
drain does. This will minimize the amount of water that enters the stormwater
system, and help to preserve the predevelopment hydrology of the site.
Bioretention areas may be part of an LID approach for a commercial site. There
are several things to look for on such a plan:
Look at the plan for the site and find out how stormwater is entering the
bioretention area. This may be accomplished through the use of curb cuts (see
photo), or by a larger area utilizing sheet flow off a paved surface. Either
way, the entrance point into the garden should be stabilized with stone or another
durable material to reduce erosion.
The profile detail of the bioretention area should show the ponding area depth,
which is typically 6 inches. This can be greater to increase storage, but aesthetics
and safety issues need to be considered also.
The detail should also show the specifications for the media. Typically, a
mix should have a high sand content (at least 50%) to encourage rapid infiltration.
The remainder of the mix is typically composed of some sort of compost or peat
(20-30%), and topsoil (20-30%) with low clay content.
Older designs called for geotextile fabric to be placed beneath the soil media,
to protect the gravel around an underdrain. However, the 2002
Bioretention Manual recommends a pea gravel blanket in place of the geotextile.
The fabrics have been found to clog over time, and have led to decreased infiltration
rates.
An underdrain is typical on commercial bioretention, and is likely tied in
to the stormwater system. The drainpipe may also drain to grade if slope permits. These components should be shown in the detail on the plan.
A structured overflow is also typical of commercial bioretention. This may
be accomplished by a raised structure in the garden itself, or a bypass to a
catch basin outside of the facility when the maximum ponding depth is reached.
Although either design is sufficient, the use of both is redundant and adds
unnecessary cost.
Bioretention at Staples in Branford. For detailed about this project from the CT LID database, click here.
Bioretention at Evergreen Walk mall in South Windsor. For detailed about this project from the CT LID database, click here.
Are you looking for more local examples of bioretention? Visit CT NEMO's LID database for Connecticut. This site contains searchable database for LID practices, engineering firms familiar with LID, and construction companies who have installed LID practices.
Video of rain garden at Middlesex Extension Center in winter.
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