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An undisturbed buffer zone of not less than 100 linear feet from a special water is required in the construction stormwater general permit. See [https://stormwater.pca.state.mn.us/index.php?title=MN_CSW_Permit_Section_23_Discharges_to_Special_(Prohibited,_Restricted,_Other)_and_Impaired_Waters Section 23] of the permit. Determining if your site is near special water can be quickly determined using the [https://pca-gis02.pca.state.mn.us/CSW/index.html online mapping tool]. Examples include the Mississippi River, Lake Superior, scenic or recreational river segments, wilderness areas, trout streams, and calcareous fens.
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=Temporary natural buffers for surface waters and permanent buffers for special waters=
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[[File:Riparian buffers.PNG|right|thumb|300 px|alt=This photo shows Riparian buffers|<font size=3>Riparian buffers</font size>]]
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The National Pollutant Discharge Elimination System (NPDES) Construction Stormwater Permit issued by the Minnesota Pollution Control Agency (MPCA) has two distinct buffer zone requirements, each with a different purpose. During construction, a temporary undisturbed buffer of not less than 50 feet from any “Surface Water” such as lakes, rivers, streams and wetlands is required as a sediment control Best Management Practice (BMP). For the purpose of the natural buffer requirement, surface water buffers are not required adjacent to road ditches, judicial ditches, county ditches, stormwater conveyance channels, storm drain inlets and sediment basins.
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A permanent undisturbed buffer of not less than 100 linear feet from a “Special Water” is required to provide protection from urban runoff and preserve scenic quality after construction is complete. Special Waters and Natural Buffers are defined in Section 23 and Section 25 of the permit, respectively. Determining if your site is near a Special Water can be quickly verified using the [https://pca-gis02.pca.state.mn.us/CSW/index.html online mapping tool.]
  
==Riparian buffers==
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==Function of buffers==
[[File:Riparian buffers.PNG|right|thumb|300 px|alt=This photo shows Riparian buffers|<font size=3>Riparian buffers</font size>]]
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A riparian buffer is a band of vegetation bordering a body of water. Riparian buffers improve water quality, wildlife and property value. Buffers provide a number of water quality safeguards including trapping and removal of sediment and other contaminants in stormwater as well as maintenance of fish and wildlife habitat. Scientific studies on buffer function demonstrate that to provide these safeguards effectively, buffers must be at least 50 feet wide. To be most effective, however, buffers should be coupled with on-site management of pollutants, including good stormwater management and erosion and sedimentation control.
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==Permit requirements for a temporary 50-foot natural buffer==
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When working near any surface water, the general permit requires that a temporary undisturbed natural buffer zone of 50 feet must be preserved during construction when surface water is located within 50 feet of the project’s earth disturbances and stormwater flows to the surface water. Natural buffer preservation is not required adjacent to road ditches, judicial ditches, county ditches, stormwater conveyance channels, storm drain inlets, and sediment basins. The 50-foot natural buffer is not intended to take the place of other required erosion and sediment control measures. Runoff and flow must be treated by perimeter control and other BMP’s prior to the stormwater being discharged into the existing natural vegetated buffer area. The permittee is not required to enhance the quality of the existing vegetation although enhancement of existing vegetation is allowed and encouraged. As an example, 50 feet of existing landscaping including bare ground would satisfy the natural buffer requirement. Delineating the buffer area in your Stormwater Pollution Prevention Plan (SWPPP) is highly recommended. The 50-foot buffer does not apply if there is no stormwater discharging to the surface water or all stormwater flows have been diverted.
  
Riparian buffers are vegetated zones adjacent to streams and wetlands that represent a best management practice (BMP) for controlling many pollutants found in typical stormwater runoff. Many studies have shown that by maintaining a buffer around surface waters pollutant impacts from sediment, phosphorus, nitrogen and thermal impacts can be greatly reduced. In addition to the benefits of buffers as a long term stormwater BMP, maintaining a buffer during construction reduces the risk of a sediment discharge when it rains.
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If the required buffer is infeasible, redundant sediment control BMPs are required. Redundant sediment controls must be placed at least 5 feet apart unless limited by lack of available space. This means the permittee will need to provide another level of protection in addition to the usual perimeter control BMP that is required in order to reasonably insure the same amount of pollutant removal that a natural vegetated buffer would provide. Sediment control BMPs include, but are not limited to, silt fence, bio rolls, earth dikes, drainage swales, rock logs and compost logs. Guidance for proper design and placement of these BMP’s can be found in the [http://stormwater.pca.state.mn.us/index.php/Main_Page Minnesota Stormwater Manual] or on EPA’s Construction Stormwater web page [https://www.epa.gov/npdes/stormwater-discharges-construction-activities Permit Requirements for a Permanent 100-ft Buffer Zone.]
  
==Permit requirements==
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When working near Special Waters, the general permit requires that a permanent undisturbed buffer zone of at least 100 feet be maintained at all times, both during construction and as a permanent feature post construction. The permit provides for exceptions to this requirement when a water crossing or other encroachment is necessary to complete the project. There may be other situations where construction within the buffer is unavoidable. Other examples may include work being done to restore the buffer or remove refuse from within the buffer zone. Existing impervious surfaces (structures or pavement, e.g.) can be replaced by new impervious surfaces of the same size or smaller. The new impervious surface may be located in a different area within the buffer but should not be moved closer to the water body.
When working near special waters, the general permit requires that an undisturbed buffer zone of at least 100 feet be maintained at all times. However the permit is clear regarding certain exceptions to this requirement such as water crossings or limited water access. There may be other situations where construction within the buffer is unavoidable. Some other examples include work being done to restore the buffer or remove refuse from within the buffer zone. Existing impervious surfaces (structures or pavement, e.g.) can be replaced by new impervious surfaces of the same size or smaller. The new impervious surface may be located in a different area within the buffer but should not be moved closer to the water body.
 
  
 
If the project involves the relocation of impervious surfaces, any environmental or scenic impacts over the existing conditions must be mitigated. If the impervious surface cannot be sited on a parcel without encroaching upon the buffer, the project may still be allowed coverage under this general permit if all water quality and scenic impacts are mitigated and documented in the SWPPP. An entire structure or a majority of a structure must not be located within the buffer zone unless it is a replacement. Scenic impacts must consider the aesthetic change caused by the project from all views from outside the project area.
 
If the project involves the relocation of impervious surfaces, any environmental or scenic impacts over the existing conditions must be mitigated. If the impervious surface cannot be sited on a parcel without encroaching upon the buffer, the project may still be allowed coverage under this general permit if all water quality and scenic impacts are mitigated and documented in the SWPPP. An entire structure or a majority of a structure must not be located within the buffer zone unless it is a replacement. Scenic impacts must consider the aesthetic change caused by the project from all views from outside the project area.
  
Contact the Minnesota Pollution Control Agency (MPCA) during the design phase of the project to determine what additional BMPs may be necessary. If, after discussing the proposed project with the MPCA, and a determination is made that the project will qualify for the listed exception, restoration of the buffer zone must blend into and match the adjacent landscape visually. BMPs must also be selected to blend into the surrounding area as much as possible. Restoration of the buffer must be with the same/similar vegetation that existed prior to disturbance or would exist in a natural condition if not previously altered by human activities.
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Contact the MPCA during the design phase of the project to determine what additional BMP’s may be necessary. If, after discussing the proposed project with the MPCA, and determination is made that the project will qualify for the listed exception, restoration of the buffer zone must blend into and match the adjacent landscape visually. BMPs must also be selected to blend into surrounding area as much as possible. Restoration of the buffer must be with the same/similar vegetation that existed prior to disturbance or that would exist in a natural condition if not previously altered by human activities.
  
 
==Trout streams==
 
==Trout streams==
Trout are a unique species of fish that rely on cold water habitats for survival. Exposure to sunlight can cause adverse warming of the water. The shade provided by trees is very important to minimizing thermal impacts to trout streams. The removal of woody vegetation and replacement with grassy vegetation is not allowed by this permit unless the reasons are absolutely necessary and completely documented in the SWPPP.
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Trout are a unique species of fish that rely on cold water habitats for survival. Exposure to sunlight can cause adverse warming of the water. The shade provided by trees is very important to minimizing thermal impacts to trout streams. The removal of woody vegetation and replacement with grassy vegetation is not allowed by this permit unless the reasons are absolutely necessary and completely documented on the SWPPP.
  
 
==Encroachment on the buffer zone==
 
==Encroachment on the buffer zone==
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==Best Management Practice selection==
 
==Best Management Practice selection==
The BMPs should be selected with the designation of the receiving water in mind.
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BMPs should be selected with the designation of the receiving water in mind.
 
 
For example, if the receiving water is designated as a trout stream, as much stormwater as possible should be infiltrated or other methods of minimizing stormwater temperature increases must be used. If the receiving water is designated as a Scenic or Recreational River Segment, the SWPPP should include methods of minimizing the aesthetic impacts from structures within the buffer such as screening with trees in addition to water quality BMPs. Consider another example: If portion of a structure must be located within the buffer zone, stormwater should be routed away from the special water whenever possible. If stormwater cannot be directed away, it should be routed using BMPs such as enhanced grass swale or flow over vegetated areas. For design information on enhanced swales, see the “Protecting Water Quality in Urban Areas” design manual, found on the [https://www.pca.state.mn.us/water/stormwater MPCA Stormwater website].
 
  
==Buffer zone design==
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For example, if the receiving water is designated as a trout stream, as much stormwater as possible should be infiltrated or other methods that will minimize stormwater temperature increases must be used. If the receiving water is designated as a Scenic or Recreational River Segment, the SWPPP should include methods of minimizing the aesthetic impacts from structures within the buffer such as screening with trees in additional to water quality BMPs.
The buffer zone area is designated as 100 feet, measured horizontally from the water’s ordinary high water (OHW) mark. The OHW for Lake Superior is the water line at an elevation of 601.5, as defined in the North Shore Management Plan. The Minnesota Department of Natural Resources has established the OHW for all other Special Waters. The elevations can be found on the MDNR’s website or by calling a local MDNR-area hydrologist.
 
  
==Buffer requirements for other surface waters==
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Consider another example: If a portion of a structure must be located within the buffer zone, stormwater should be routed away from the receiving water whenever possible. If stormwater cannot be directed away, it should be routed using BMPs such as enhanced grass swales or flow over vegetated areas. Other common erosion and sediment control measures that could be used include silt fence, diversion berms, sod strips, fiber rolls, straw bales, ditch checks and sediment ponds. A combination of erosion and sediment control BMPs may be used as well. Buffer zone BMPs must be maintained throughout the duration of all land disturbing activities and lagging of the buffer zone prior to any land disturbing activities is highly recommended.
When working near all other waters that are not defined as special, the permit requires that a 50 foot natural buffer is preserved, unless infeasible, between the land disturbing activity and the surface water. A natural buffer consists of any undisturbed cover that existed prior to the land-disturbing activity, including vegetation, barren ground or exposed rock. This requirement does not apply to construction sites that drain to a drainage ditch, judicial ditch, county ditch, conveyance channel, storm drains, or sediment basins. If construction cannot be restricted from the buffer, redundant sediment control BMPs are required.
 
  
 
==Local requirements==
 
==Local requirements==

Revision as of 21:26, 13 February 2019

Temporary natural buffers for surface waters and permanent buffers for special waters

This photo shows Riparian buffers
Riparian buffers

The National Pollutant Discharge Elimination System (NPDES) Construction Stormwater Permit issued by the Minnesota Pollution Control Agency (MPCA) has two distinct buffer zone requirements, each with a different purpose. During construction, a temporary undisturbed buffer of not less than 50 feet from any “Surface Water” such as lakes, rivers, streams and wetlands is required as a sediment control Best Management Practice (BMP). For the purpose of the natural buffer requirement, surface water buffers are not required adjacent to road ditches, judicial ditches, county ditches, stormwater conveyance channels, storm drain inlets and sediment basins.

A permanent undisturbed buffer of not less than 100 linear feet from a “Special Water” is required to provide protection from urban runoff and preserve scenic quality after construction is complete. Special Waters and Natural Buffers are defined in Section 23 and Section 25 of the permit, respectively. Determining if your site is near a Special Water can be quickly verified using the online mapping tool.

Function of buffers

A riparian buffer is a band of vegetation bordering a body of water. Riparian buffers improve water quality, wildlife and property value. Buffers provide a number of water quality safeguards including trapping and removal of sediment and other contaminants in stormwater as well as maintenance of fish and wildlife habitat. Scientific studies on buffer function demonstrate that to provide these safeguards effectively, buffers must be at least 50 feet wide. To be most effective, however, buffers should be coupled with on-site management of pollutants, including good stormwater management and erosion and sedimentation control.

Permit requirements for a temporary 50-foot natural buffer

When working near any surface water, the general permit requires that a temporary undisturbed natural buffer zone of 50 feet must be preserved during construction when surface water is located within 50 feet of the project’s earth disturbances and stormwater flows to the surface water. Natural buffer preservation is not required adjacent to road ditches, judicial ditches, county ditches, stormwater conveyance channels, storm drain inlets, and sediment basins. The 50-foot natural buffer is not intended to take the place of other required erosion and sediment control measures. Runoff and flow must be treated by perimeter control and other BMP’s prior to the stormwater being discharged into the existing natural vegetated buffer area. The permittee is not required to enhance the quality of the existing vegetation although enhancement of existing vegetation is allowed and encouraged. As an example, 50 feet of existing landscaping including bare ground would satisfy the natural buffer requirement. Delineating the buffer area in your Stormwater Pollution Prevention Plan (SWPPP) is highly recommended. The 50-foot buffer does not apply if there is no stormwater discharging to the surface water or all stormwater flows have been diverted.

If the required buffer is infeasible, redundant sediment control BMPs are required. Redundant sediment controls must be placed at least 5 feet apart unless limited by lack of available space. This means the permittee will need to provide another level of protection in addition to the usual perimeter control BMP that is required in order to reasonably insure the same amount of pollutant removal that a natural vegetated buffer would provide. Sediment control BMPs include, but are not limited to, silt fence, bio rolls, earth dikes, drainage swales, rock logs and compost logs. Guidance for proper design and placement of these BMP’s can be found in the Minnesota Stormwater Manual or on EPA’s Construction Stormwater web page Permit Requirements for a Permanent 100-ft Buffer Zone.

When working near Special Waters, the general permit requires that a permanent undisturbed buffer zone of at least 100 feet be maintained at all times, both during construction and as a permanent feature post construction. The permit provides for exceptions to this requirement when a water crossing or other encroachment is necessary to complete the project. There may be other situations where construction within the buffer is unavoidable. Other examples may include work being done to restore the buffer or remove refuse from within the buffer zone. Existing impervious surfaces (structures or pavement, e.g.) can be replaced by new impervious surfaces of the same size or smaller. The new impervious surface may be located in a different area within the buffer but should not be moved closer to the water body.

If the project involves the relocation of impervious surfaces, any environmental or scenic impacts over the existing conditions must be mitigated. If the impervious surface cannot be sited on a parcel without encroaching upon the buffer, the project may still be allowed coverage under this general permit if all water quality and scenic impacts are mitigated and documented in the SWPPP. An entire structure or a majority of a structure must not be located within the buffer zone unless it is a replacement. Scenic impacts must consider the aesthetic change caused by the project from all views from outside the project area.

Contact the MPCA during the design phase of the project to determine what additional BMP’s may be necessary. If, after discussing the proposed project with the MPCA, and determination is made that the project will qualify for the listed exception, restoration of the buffer zone must blend into and match the adjacent landscape visually. BMPs must also be selected to blend into surrounding area as much as possible. Restoration of the buffer must be with the same/similar vegetation that existed prior to disturbance or that would exist in a natural condition if not previously altered by human activities.

Trout streams

Trout are a unique species of fish that rely on cold water habitats for survival. Exposure to sunlight can cause adverse warming of the water. The shade provided by trees is very important to minimizing thermal impacts to trout streams. The removal of woody vegetation and replacement with grassy vegetation is not allowed by this permit unless the reasons are absolutely necessary and completely documented on the SWPPP.

Encroachment on the buffer zone

Construction activity under this general permit is not allowed when encroaching on the buffer zone if additional stormwater treatment BMPs are not possible. BMPs must address both erosion-prevention and sediment-control during construction and post-construction stormwater treatment if new impervious surfaces are being created. For example, in some areas it may not be possible to construct stormwater treatment systems such as an infiltration area because of the proximity to bedrock. In this situation, an enhanced swale or another practice may be used as an alternative.

If encroachment into the buffer zone is necessary, additional BMPs must be utilized to mitigate any water-quality or scenic impacts or to preserve the wilderness, scientific, recreational or other special characteristics that make the water an Outstanding Resource Value Water.

Best Management Practice selection

BMPs should be selected with the designation of the receiving water in mind.

For example, if the receiving water is designated as a trout stream, as much stormwater as possible should be infiltrated or other methods that will minimize stormwater temperature increases must be used. If the receiving water is designated as a Scenic or Recreational River Segment, the SWPPP should include methods of minimizing the aesthetic impacts from structures within the buffer such as screening with trees in additional to water quality BMPs.

Consider another example: If a portion of a structure must be located within the buffer zone, stormwater should be routed away from the receiving water whenever possible. If stormwater cannot be directed away, it should be routed using BMPs such as enhanced grass swales or flow over vegetated areas. Other common erosion and sediment control measures that could be used include silt fence, diversion berms, sod strips, fiber rolls, straw bales, ditch checks and sediment ponds. A combination of erosion and sediment control BMPs may be used as well. Buffer zone BMPs must be maintained throughout the duration of all land disturbing activities and lagging of the buffer zone prior to any land disturbing activities is highly recommended.

Local requirements

In addition to the requirements for buffer impacts set forth by the NPDES program. Permittees should to be aware of additional local requirements. Examples include Mississippi River Management Plan, North Shore Management Plan or any state or local shoreline ordinance.

More information

For more information, call the MPCA Stormwater Hotline at 651-757-2119 or 800-657-3804.