BMPs for stormwater infiltration
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BMPs for stormwater infiltration

Best Management Practices that infiltrate stormwater runoff into underlying soil include, but are not limited, to

infiltration basins,
infiltration trenches,
underground infiltration,
bioinfiltration,
permeable pavements, and
tree trenches and tree boxes.

These are discussed briefly below.

Infiltration basin

Photo of an infiltration basin. Source: Clark County, Washington, with permission.

Applications and treatment capabilities for infiltration basins
Applications		Treatment capabilities^{3, 4, 5}
Residential	Yes	TSS	High⁶
Commercial	Yes	TN	Medium/high
Ultra-urban	Limited¹	TP	Medium/high
Industrial	Yes²	Chloride	Low
Highway/road	Limited	Metals	High
Recreational	Yes	Oils and grease	High
		Pathogens	High
¹ Due to a size restriction; ² Unless the infiltration practice is located in an industrial area with exposed significant materials or from vehicle fueling and maintenance areas. Infiltration BMPs are PROHIBITED in these areas; ³Underground infiltration systems may have different (likely lower) pollutant removal capabilities than what is provided in this table. These systems may have a wider application range. ⁴ This is only for the portion of flow that enters the infiltration basin; by-passed runoff does not receive treatment; ⁵ Low = < 30%; Medium = 30-65%; High = 65 -100%); ⁶ Assumes adequate pre-treatment Sources: Schueler, 1987, 1992; USEPA 1993a, 1993b; Maniquiz et al., 2010; NPRPD, 2007; California Stormwater Manual, 2009; Pennsylvania Stormwater Manual, 2006

An infiltration basin is a natural or constructed impoundment that captures, temporarily stores, and infiltrates a design volume of water. For more information, see the following pages in this Manual.

Infiltration trench

Photo of a Infiltration trench in Lino Lakes

Applications and treatment capabilities for infiltration trenches
Applications		Treatment capabilities^{3, 4}
Residential	Yes	TSS⁵	High⁵
Commercial	Yes	TN	Medium/high
Ultra-urban	Limited¹	TP	Medium/high
Industrial	Yes²	Chloride	Low
Highway/road	Yes	Metals	High
Recreational	Yes	Oils and grease	High
		Pathogens	High
¹ Due to a size restriction; ² Unless the infiltration practice is located in an industrial area with exposed significant materials or from vehicle fuelling and maintenance areas. Infiltration BMPs are PROHIBITED in these areas; ³ This is only for the portion of flow that enters the infiltration basin; by-passed runoff does not receive treatment; ⁴ Low = < 30%; Medium = 30-65%; High = 65 -100%); ⁵ Assumes adequate pre-treatment Sources: Schueler, 1987, 1992; USEPA 1993a, 1993b; Maniquiz et al., 2010; NPRPD, 2007; California Stormwater Manual, 2009; Pennsylvania Stormwater Manual, 2006

An infiltration trench is a shallow excavated trench that is backfilled with a coarse stone aggregate. This design allows for the temporary storage of runoff in the void space of the material in addition to the storage above the aggregate within the trench. For more information, see the following pages in this Manual.

Bioinfiltration basin

Bioinfiltration basin (Source: CDM Smith)

Applications and treatment capabilities for bioinfiltration basins
Applications		Treatment capabilities^{2, 3}
Residential	Yes	TSS	High⁴
Commercial	Yes	TN	Low/Medium⁵
Ultra-urban	Limited⁷	TP	Medium/high⁶
Industrial	Yes¹	Chloride	Low
Highway/road	Yes	Metals	High
Recreational	Yes	Oils and grease	High
		Pathogens	High
¹ Unless the infiltration practice is located in an industrial area with exposed significant materials or from vehicle fuelling and maintenance areas. Infiltration BMPs are PROHIBITED in these areas; ² This is only for the portion of flow that enters the infiltration basin; by-passed runoff does not receive treatment; ³ Low = < 30%; Medium = 30-65%; High = 65 -100%); ⁴ Assumes adequate pre-treatment; ⁵ This assumes no underdrain; ⁶ Certain soil mixes can leach P; ⁷ Due to a size restriction Sources: EPA Factsheet, 1999; Davis et al., 2001, 2003, 2006; Hsieh and Davis, 2005; Hong et al., 2006; Hunt et al., 2006; NPRPD, 2007; Li and Davis, 2009; Diblasi et al., 2009; Passeport et al., 2009; Brown et at., 2011a, b; Komlos et al., 2012; Denich et al., 2013; Li and Davis, 2013; California Stormwater BMP

Bioinfiltration basins, often called rain gardens, use soil (typically engineered media or mixed soil) and native vegetation to capture runoff and remove pollutants. Both the media and underlying soil typically have high infiltration rates that allow captured water to infiltrate within a required drawdown time, usually 48 hours. For more information, see the following pages in this Manual.

Permeable pavement

Permeable pavement (Source: CDM Smith)

Applications and treatment capabilities for permeable pavement
Applications		Treatment capabilities^{2, 3}
Residential	Yes	TSS	High⁴
Commercial	Yes	TN	Medium/High
Ultra-urban	Yes	Nitrate	Low/Medium
Industrial	Yes¹	TP	Medium/High
Retrofit	Yes	Chloride	Low
Highway/road	Yes	Metals	High
Recreational	Yes	Oils and grease	High
		Pathogens	⁵
¹ Unless the infiltration practice is located in an industrial area with exposed significant materials or from vehicle fuelling and maintenance areas. Infiltration BMPs are PROHIBITED in these areas; ² This is only for the portion of flow that enters the infiltration basin; by-passed runoff does not receive treatment; ³ Low = < 30%; Medium = 30-65%; High = 65 -100%); ⁴ Assumes adequate pre-treatment; ⁵ Insufficient information Source: Schueler, 1987; Pratt et al, 1999; Adams, 2003; Brattebo and Booth, 2003; Adams, 2003; Bean et al, 2007; SEMCOG, 2008; International Stormwater Database, 2012

Permeable pavements allow stormwater runoff to pass through surface voids into an underlying stone reservoir/ subbase for temporary storage and/or infiltration. They are suitable for driveways, trails, parking lots, and roadways with lighter traffic. For more information, see the following pages in this Manual.

Tree box/Tree trench

Tree box (Source: CDM Smith)

Applications and treatment capabilities for tree box/tree trench
Applications		Treatment capabilities^{2, 3}
Residential	Yes	TSS	High⁴
Commercial	Yes	TN	Low/Medium
Ultra-urban	Yes	TP	Medium/High⁵
Industrial	Yes¹	Chloride	Low
Highway/road	No	Metals	High
Recreational	Yes	Oils and grease	High
		Pathogens	High
¹ Unless the infiltration practice is located in an industrial area with exposed significant materials or from vehicle fuelling and maintenance areas. Infiltration BMPs are PROHIBITED in these areas; ² This is only for the portion of flow that enters the infiltration basin; by-passed runoff does not receive treatment; ³ Low = < 30%; Medium = 30-65%; High = 65 -100%); ⁴ Assumes adequate pre-treatment; ⁵ Certain soil mixes can leach P. Source: see [1]

Tree trenches and tree boxes (collectively called tree BMPs), consist of trees planted within underground storage reservoirs designed to retain a volume of runoff for the purpose of uptake by trees. They are a variant of bioretention BMPs. For more information, see the following pages in this Manual.

Trees - general

Tree boxes/tree trenches

Underground infiltration and dry wells

Underground infiltration systems and dry wells have been installed below parking lots and other impervious surfaces on sites where insufficient space exists for a surface infiltration system. They are designed to temporarily store stormwater runoff before slowly infiltrating the water into the subsurface (Connecticut, 2004). There is limited information on the effectiveness of these systems in removing pollutants. Limited data suggests they may be less effective at removing mobile pollutants than surface-based infiltration systems.

One concern is that underground infiltration may meet the U.S. Environmental Protection Agency (EPA) definition of a Class V injection well. Class V injection wells are defined as any bored, drilled, or driven shaft, or any dug hole that is deeper than its widest surface dimension. Class V injection wells can also be an improved sinkhole, or a subsurface fluid distribution system (from U.S. EPA, June 2003). The U.S. EPA administers Class V injection well permits in Minnesota. Minimum requirements for installing, permitting, and operating a Class V well is defined by the USEPA.

A second concern pertains to the overall pollutant removal effectiveness of those underground infiltration systems that do not meet the definition of a Class V injection well. The document released by the Transport Research Synthesis titled “Issues of Concern Related to Underground Infiltration Systems for Stormwater Management and Treatment” provides a good overview of the concerns related to underground infiltration systems (MNDOT, 2009). Issues identified in this report include:

There is potential that an underground infiltration system meets the criteria of a Class V injection well.
There is insufficient knowledge of the fate of pollutants in the subgrade below the buried infiltration systems.
Roadways and parking lots with high volumes of traffic have higher concentrations of certain pollutants, including heavy metals and PAHs.
Underground systems do not allow for the pollutant removal that is accomplished through biological activity and vegetation uptake.
The minimum separation requirement of 3 feet between the bottom of the infiltration system and the seasonally high groundwater elevation may be insufficient for adequate pollutant removal. Additional study is recommended.
Maintenance of underground systems is critical for effective pollutant removal. However, access for maintenance is challenging. There are concerns that the difficult access is preventing owners from properly maintaining these systems.

This Manual currently does not provide guidance for design, construction, maintenance, and assessment of underground infiltration systems.

Enhanced turf

Infiltration can be enhanced on soils that have been improved or amended. This manual contains limited information on enhanced turf and does not provide guidance for design, construction, maintenance, and assessment of enhanced turf. Information on use of compost in soil and credits associated with improved turf can be found on the Turf page. A discussion of alleviating compaction from construction activities can be found here.

Warning: Enhanced turf cannot be used to meet requirements of the Construction Stormwater General permit because infiltrated water does not represent an instantaneous volume.

Unit processes for different infiltration BMPs

The following table provides a summary of unit processes for the different infiltration BMPs.

Unit processes of stormwater treatment techniques (Adapted from WEF, 2008)
Link to this table

Control	Infiltration basin	Infiltration trench	Bioinfiltration	Permeable pavement	Tree box/tree trench	Enhanced turf
Peak flow attenuation	X	X	X	X
Runoff volume reduction	X	X	X	X	X
Infiltration	X	X	X	X	X	X
Dispersion
Evapotranspiration			X		X
Runoff collection and usage			X¹	X¹
Sedimentation	X	X	X
Flotation	X		X
Laminar separation
Swirl concentration
Sorption	X	X	X	X
Precipitation	X	X	X	X
Coagulation	X	X	X	X
Filtration			X
Plant metabolism			X		X	X
Nitrification/denitrification	X	X	X
Organic compound degradation	X	X	X	X
Pathogen die off	X	X		X
Temperature reduction	X	X	X	X
Disinfection	X	X	X	X

¹ If underdrain is present

Related pages

BMPs for stormwater infiltration Revision as of 21:12, 22 September 2015 by Mtrojan (talk | contribs)(diff) ← Older revision | Latest revision (diff) | Newer revision → (diff) BMPs for stormwater infiltration

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