Difference between revisions of "Filtration"

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Filtration is the process by which stormwater runoff is conveyed through a filter medium to remove solid particles and associated pollutants.  Several stormwater practices use filtration through sand or gravel media as the primary mechanism for treatment of urban runoff.   
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[[File:Filtration.png|500px|right|frame|Media based systems are depth filters that capture particles both on the surface and within the media matrixMembrane filters are surface filters that remove all particles greater than a specified size at the surface of the filter.  Membranes are typically much thinner than shown in the diagram above. Both filtration systems can be oriented vertically or horizontally (Green Synergy Engineering, 2024).<ref>Green Synergy Engineering. 2024. Depth vs Membrane Filter. https://www.greensynergy.my/post/depth-vs-membrane-filter</ref>]]
Stormwater passes through a filter based on the pressure difference on either side of the filter.  In most stormwater treatment applications, the pressure difference is created by gravity (or hydraulic head). As the filter becomes [[clogging|clogged]], higher pressure is needed to drive stormwater through the filter, until a point is reached at which flow through the treatment system must be redirected to another flow path (usually a [[overflow|bypass]] within or upstream of the system).
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==Overview==
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As stormwater flows over impervious surfaces such as pavement and rooftops, it collects sediment and other pollutants before entering nearby waterways. Stormwater filtration is a key element of urban runoff management, helping to improve [[Water quality|water quality]] by removing suspended solids and associated pollutants. Filtration can help achieve total suspended solids (TSS) removal targets and contributes to overall watershed health (Purvis et al., 2018).<ref>Purvis, R. A., Winston, R. J., Hunt, W. F., Lipscomb, B., Narayanaswamy, K., McDaniel, A., Lauffer, M. S., & Libes, S. (2018). Evaluating the Water Quality Benefits of a Bioswale in Brunswick County, North Carolina (NC), USA. Water, 10(2), 134. https://doi.org/10.3390/w10020134</ref> Filtration works by conveying stormwater through a [[Bioretention: Filter media|filter medium]] that captures solid particles. In most stormwater treatment systems, water is driven through the filter by a pressure difference created by gravity or hydraulic head.
  
==Types of filtration==
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==Applications==
Two common types of filter media used in stormwater treatment are granular media, such as sand, and membranes: 
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Stormwater practices that use filtration as a mechanism for treatment of runoff include:
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*[[Bioretention]] technologies have been shown to effectively filter sediment from parking lot, road and residential runoff (STEP, 2019).<ref>Sustainable Technologies Evaluation Program. 2019. Comparative Performance Assessment of Bioretention in Ontario. https://sustainabletechnologies.ca/app/uploads/2019/10/STEP_Bioretention-Synthesis_Tech-Brief-New-Template-2019-Oct-10.-2019.pdf</ref>
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*[[Permeable pavements]] can filter runoff through the surface pores or media between pavers, as well as through the bedding and base layers. Most of the [[sediment]] directed onto the pavements is trapped near the surface where it can be more easily accessed for cleaning.
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*[[Filtration Manufactured Treatment Devices]] such as [https://sustainabletechnologies.ca/app/uploads/2020/06/High-rate-treatment-bioretention-filter-tech-brief.pdf the Filterra® high flow curb inlet filtration MTD] have achieved 80% TSS removal during runoff events.
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*[[Stormwater planters]] filter runoff through a planting bed of filter media and can be installed in tight urban spaces
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*[[Pretreatment]] options, such as [[Vegetated filter strips|vegetated filter strips]] and catch basin inserts
  
'''Granular media''' is a multilayer lattice or matrix that traps solids as water flows through the tortuous channels in the media.  Clogging may occur when solid particles form a film or cake on top of the filter or accumulate within the media channels to the point where the channels become occluded. 
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{{:Filtration: Gallery}}
  
'''Membranes''' have very thin separation lattices with openings or pores that remove all particles larger than the nominal pore size of the filter at the surface, thereby acting much like a sieve.   Membranes are often pleated to increase the surface area, allowing for more particles to be trapped prior to clogging.
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==Key system design parameters==
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===Types of filter media===
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Careful consideration should be given to the type of filter media used in an LID system. Two common types of [[Media filters|filter media]] used in stormwater treatment are granular media and membranes: 
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*'''Granular media''' is a multilayer lattice or matrix that traps solids as water flows through the tortuous channels in the media. Examples of granular media include [[sand]] and [[Aggregates|gravel]].
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*'''[[Geotextiles|Membranes]]''' have very thin separation lattices with openings or pores that remove all particles larger than the nominal pore size of the filter at the surface, thereby acting much like a sieve. Membranes are often pleated to increase the surface area, allowing for more particles to be trapped prior to clogging.
  
 
Some filters include [[additives]] such as zeolite or iron to enhance the contaminant removal process for target water quality variables by increasing chemical adsorption and/or precipitation.
 
Some filters include [[additives]] such as zeolite or iron to enhance the contaminant removal process for target water quality variables by increasing chemical adsorption and/or precipitation.
  
==Key system design parameters==
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===Sizing===
When sizing filtration systems for specific sites using local historical rainfall records, several key system design parameters need to be considered.  These are defined in the sizing section of the Filtration MTD page.  
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When sizing filtration systems for specific sites using local historical [[Understanding rainfall statistics|rainfall]] records, several key system design parameters need to be considered.  These are defined in the sizing section of the [[Filtration MTD]] page.  
Non-proprietary bioretention systems are sized as filters much more conservatively based on design storms, surface ponding depth and minimum media infiltration rates.  The ratio of drainage area imperviousness to the surface area of bioretention facilities (referred to as the impervious-to-pervious ratio) is often many times lower than that for filtration MTDs.  This ensures longer intervals for sediment maintenance and significant reductions in stormwater volumes through infiltration. See here for more information on sizing.  
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Non-proprietary [[bioretention]] systems are sized as filters much more conservatively based on design storms, surface ponding depth and [[Flow through media|minimum media infiltration rate]].  The ratio of drainage area imperviousness to the surface area of bioretention facilities (referred to as the impervious-to-pervious ratio) is often many times lower than that for filtration MTDs.  This ensures longer intervals for sediment maintenance and significant reductions in stormwater volumes through infiltration.
Permeable pavements can also be considered to be a type of filter. In this case, runoff and rainwater is filtered through the surface pores or granular media between the pavers, as well as through the bedding and base layers. Most of the sediment directed onto the pavements is trapped near the surface where it can be more easily accessed for cleaning.  Since permeable pavements need to maintain a high rate of infiltration to avoid ponding, the area of impervious surface draining on to them should be no larger than the area of the permeable pavement itself. See here for more information on permeable pavement sizing.
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[[File:Screenshot 2025-07-14 135310.png|300px|thumb|right|Filter media replacement in bioretention system (Filterra®)<ref>Contech Engineered Solutions. 2024. Filterra Vault Owner’s Manual. https://www.conteches.com/media/wlrdhu4w/filterra-vault-om.pdf</ref>]]
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==Maintenance considerations==
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[[File:MaintenancePICP.png|thumb|300px|Vehicle used for vacuum maintenance of permeable pavements. ]]
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[[Inspections and maintenance#Practice-specific Inspection and Maintenance|Practice-specific maintenance guides]] are available for each LID BMP. General maintenance considerations for filter-based LIDs include:
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*'''[[Inspections and maintenance|Inspection and maintenance frequency]]''': Routine inspections and maintenance are needed to assess and resolve issues, such as [[Sedimentation|sediment]] buildup. [[Maintenance, Rehabilitation and Repair|Frequency of visits]] depends on a variety of factors. LID BMP designs should include safe access for maintenance and inspection crews and confined space entry procedures should be considered for subsurface systems. [[Monitoring]] should also be undertaken to assess function.
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*'''Sediment removal''': Filters can become [[clogging|clogged]] with sediment, organic material, and trash, reducing flow capacity and treatment performance. When solid particles form a film on the filter's surface or accumulate within the media channels, higher pressure is needed to drive stormwater through the filter. Eventually, a point is reached at which flow through the treatment system must be redirected to another flow path (usually a bypass within or upstream of the system). Regular vacuuming or manual removal of accumulated materials is commonly required.
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*'''[[Sorbtive media|Media]] replacement''': Filter bed media can lose effectiveness over time due to clogging, chemical saturation, erosion, animal burrows, and compaction. Media may need to be replaced, regraded, or core aerated.
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*'''[[overflow|Overflow bypass functionality]]''': Ensure bypass structures are functioning to prevent flooding or erosion when filters are clogged or overwhelmed by large runoff events.
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==References==

Latest revision as of 18:02, 18 July 2025

Media based systems are depth filters that capture particles both on the surface and within the media matrix. Membrane filters are surface filters that remove all particles greater than a specified size at the surface of the filter. Membranes are typically much thinner than shown in the diagram above. Both filtration systems can be oriented vertically or horizontally (Green Synergy Engineering, 2024).[1]

Overview[edit]

As stormwater flows over impervious surfaces such as pavement and rooftops, it collects sediment and other pollutants before entering nearby waterways. Stormwater filtration is a key element of urban runoff management, helping to improve water quality by removing suspended solids and associated pollutants. Filtration can help achieve total suspended solids (TSS) removal targets and contributes to overall watershed health (Purvis et al., 2018).[2] Filtration works by conveying stormwater through a filter medium that captures solid particles. In most stormwater treatment systems, water is driven through the filter by a pressure difference created by gravity or hydraulic head.

Applications[edit]

Stormwater practices that use filtration as a mechanism for treatment of runoff include:

Key system design parameters[edit]

Types of filter media[edit]

Careful consideration should be given to the type of filter media used in an LID system. Two common types of filter media used in stormwater treatment are granular media and membranes:

  • Granular media is a multilayer lattice or matrix that traps solids as water flows through the tortuous channels in the media. Examples of granular media include sand and gravel.
  • Membranes have very thin separation lattices with openings or pores that remove all particles larger than the nominal pore size of the filter at the surface, thereby acting much like a sieve. Membranes are often pleated to increase the surface area, allowing for more particles to be trapped prior to clogging.

Some filters include additives such as zeolite or iron to enhance the contaminant removal process for target water quality variables by increasing chemical adsorption and/or precipitation.

Sizing[edit]

When sizing filtration systems for specific sites using local historical rainfall records, several key system design parameters need to be considered. These are defined in the sizing section of the Filtration MTD page. Non-proprietary bioretention systems are sized as filters much more conservatively based on design storms, surface ponding depth and minimum media infiltration rate. The ratio of drainage area imperviousness to the surface area of bioretention facilities (referred to as the impervious-to-pervious ratio) is often many times lower than that for filtration MTDs. This ensures longer intervals for sediment maintenance and significant reductions in stormwater volumes through infiltration.

Filter media replacement in bioretention system (Filterra®)[6]

Maintenance considerations[edit]

Vehicle used for vacuum maintenance of permeable pavements.

Practice-specific maintenance guides are available for each LID BMP. General maintenance considerations for filter-based LIDs include:

  • Inspection and maintenance frequency: Routine inspections and maintenance are needed to assess and resolve issues, such as sediment buildup. Frequency of visits depends on a variety of factors. LID BMP designs should include safe access for maintenance and inspection crews and confined space entry procedures should be considered for subsurface systems. Monitoring should also be undertaken to assess function.
  • Sediment removal: Filters can become clogged with sediment, organic material, and trash, reducing flow capacity and treatment performance. When solid particles form a film on the filter's surface or accumulate within the media channels, higher pressure is needed to drive stormwater through the filter. Eventually, a point is reached at which flow through the treatment system must be redirected to another flow path (usually a bypass within or upstream of the system). Regular vacuuming or manual removal of accumulated materials is commonly required.
  • Media replacement: Filter bed media can lose effectiveness over time due to clogging, chemical saturation, erosion, animal burrows, and compaction. Media may need to be replaced, regraded, or core aerated.
  • Overflow bypass functionality: Ensure bypass structures are functioning to prevent flooding or erosion when filters are clogged or overwhelmed by large runoff events.

References[edit]

  1. Green Synergy Engineering. 2024. Depth vs Membrane Filter. https://www.greensynergy.my/post/depth-vs-membrane-filter
  2. Purvis, R. A., Winston, R. J., Hunt, W. F., Lipscomb, B., Narayanaswamy, K., McDaniel, A., Lauffer, M. S., & Libes, S. (2018). Evaluating the Water Quality Benefits of a Bioswale in Brunswick County, North Carolina (NC), USA. Water, 10(2), 134. https://doi.org/10.3390/w10020134
  3. Sustainable Technologies Evaluation Program. 2019. Comparative Performance Assessment of Bioretention in Ontario. https://sustainabletechnologies.ca/app/uploads/2019/10/STEP_Bioretention-Synthesis_Tech-Brief-New-Template-2019-Oct-10.-2019.pdf
  4. Enviropod. 2022. https://www.enviropod.com/en-ca/products/littatrap
  5. Philadelphia Water Department. 2025. Stormwater Planters. https://water.phila.gov/gsi/tools/stormwater-planter/
  6. Contech Engineered Solutions. 2024. Filterra Vault Owner’s Manual. https://www.conteches.com/media/wlrdhu4w/filterra-vault-om.pdf