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#Discharges associated with industrial activity except for construction activity. Discharges associated with industrial activity may need to obtain coverage under a separate NPDES/SDS permit once day‐to‐day operational activities commence even if construction is ongoing. | #Discharges associated with industrial activity except for construction activity. Discharges associated with industrial activity may need to obtain coverage under a separate NPDES/SDS permit once day‐to‐day operational activities commence even if construction is ongoing. | ||
#Discharges from non‐point source agricultural and silvicultural activities excluded from NPDES permit requirements under [https://www.gpo.gov/fdsys/pkg/CFR-2015-title40-vol22/pdf/CFR-2015-title40-vol22-sec122-3.pdf 40 CFR pt. 122.3(e)]. | #Discharges from non‐point source agricultural and silvicultural activities excluded from NPDES permit requirements under [https://www.gpo.gov/fdsys/pkg/CFR-2015-title40-vol22/pdf/CFR-2015-title40-vol22-sec122-3.pdf 40 CFR pt. 122.3(e)]. | ||
− | #Discharges to the waters identified below unless the requirements of Appendix A are complied with: | + | #Discharges to the waters identified below unless the requirements of [[https://stormwater.pca.state.mn.us/index.php?title=2013_Construction_stormwater_permit#APPENDIX_A Appendix A] Appendix A] are complied with: |
::<p>a. Discharges into outstanding resource value waters as listed in [https://www.revisor.mn.gov/rules/?id=7050.0180 Minn. R. 7050.0180, subp. 3, 4, 5, 6, 6a and 6b].</p> | ::<p>a. Discharges into outstanding resource value waters as listed in [https://www.revisor.mn.gov/rules/?id=7050.0180 Minn. R. 7050.0180, subp. 3, 4, 5, 6, 6a and 6b].</p> | ||
::<p>b. Discharges into trout waters as listed in [https://www.revisor.mn.gov/rules/?id=6264.0050 Minn. R. 6264.0050, subp. 2 and 4].</p> | ::<p>b. Discharges into trout waters as listed in [https://www.revisor.mn.gov/rules/?id=6264.0050 Minn. R. 6264.0050, subp. 2 and 4].</p> | ||
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===II.B. APPLICATION AND DURATION OF COVERAGE=== | ===II.B. APPLICATION AND DURATION OF COVERAGE=== | ||
#Application Required.<p>a. The owner and operator shall submit a complete and accurate on‐line application form with the appropriate fee to the MPCA for each project that disturbs one (1) or more acres of land or for a common plan of development or sale that will ultimately disturb one (1) or more acres. If the applicant is not able to apply on‐line, contact the MPCA for technical assistance or a waiver.</p> | #Application Required.<p>a. The owner and operator shall submit a complete and accurate on‐line application form with the appropriate fee to the MPCA for each project that disturbs one (1) or more acres of land or for a common plan of development or sale that will ultimately disturb one (1) or more acres. If the applicant is not able to apply on‐line, contact the MPCA for technical assistance or a waiver.</p> | ||
− | <p>b. For certain projects or common plans of development or sale disturbing 50 acres or more, the application must be submitted at least 30 days before the start of construction activity. This requirement pertains to projects that have a discharge point on the project that is within one mile (aerial radius measurement) of, and flows to, a special water listed in [ | + | <p>b. For certain projects or common plans of development or sale disturbing 50 acres or more, the application must be submitted at least 30 days before the start of construction activity. This requirement pertains to projects that have a discharge point on the project that is within one mile (aerial radius measurement) of, and flows to, a special water listed in [https://stormwater.pca.state.mn.us/index.php?title=2013_Construction_stormwater_permit#APPENDIX_A Appendix A, Part B]. or waters listed as impaired under section 303(d) of the federal Clean Water Act ([http://www.pca.state.mn.us/index.php/water/water-types-and-programs/minnesotas-impaired-waters-and-tmdls/minnesotas-impaired-waters-and-total-maximum-daily-loads-tmdls.html see the MPCA’s website]) where the identified pollutant(s) or stressor(s) are phosphorus (nutrient eutrophication biological indicators), turbidity, dissolved oxygen, or biotic impairment (fish bioassessment, aquatic plant bioassessment and aquatic macroinvertebrate bioassessment). Applicants of projects listed in this part must submit a complete and accurate application form and SWPPP including all calculations for the Permanent Stormwater Management System (see [[III. STORMWATER DISCHARGE DESIGN REQUIREMENTS|Parts III.A.‐D]].).</p> |
− | #All persons meeting the definition of owner and operator are Permittees and must be listed on the application. The owner is responsible for compliance with all terms and conditions of this permit. The operator is responsible for compliance with Parts II.B, II.C, [[III. STORMWATER DISCHARGE DESIGN REQUIREMENTS#III.B. SWPPP AMENDMENTS|III.B‐F]], [[IV. CONSTRUCTION ACTIVITY REQUIREMENTS|IV]], [[V. GENERAL PROVISIONS|V]], and applicable construction activity requirements found in [ | + | #All persons meeting the definition of owner and operator are Permittees and must be listed on the application. The owner is responsible for compliance with all terms and conditions of this permit. The operator is responsible for compliance with Parts II.B, II.C, [[III. STORMWATER DISCHARGE DESIGN REQUIREMENTS#III.B. SWPPP AMENDMENTS|III.B‐F]], [[IV. CONSTRUCTION ACTIVITY REQUIREMENTS|IV]], [[V. GENERAL PROVISIONS|V]], and applicable construction activity requirements found in [https://stormwater.pca.state.mn.us/index.php?title=2013_Construction_stormwater_permit#APPENDIX_A Appendix A, Part C]. of this permit and is jointly responsible with the owner for compliance with those portions of the permit. |
#Permit Coverage Effective Date: The commencement of any construction activity (e.g., land disturbing activities) covered under [[I. PERMIT COVERAGE AND LIMITATIONS #I.A. PERMIT COVERAGE|Part I.A]]. of this permit is prohibited until permit coverage under this permit is effective.<p>a. For projects listed in Part II.B.1.a. permit coverage will become effective seven (7) calendar days after the electronic submittal date or the postmarked date of a complete application form.</p><p>b. For projects listed in Part II.B.1.b. permit coverage will become effective 30 calendar days after the electronic submittal date, the postmarked date or MPCA date stamp (whichever is first) of the complete application. For incomplete applications (e.g., lack of fees or signature) or incomplete SWPPPs (e.g., missing calculations, Best Management Practice (BMP) specifications, estimated quantities of the BMPs, or timing of BMP installation narrative), the permit becomes effective 30 calendar days after all required information is submitted.</p> | #Permit Coverage Effective Date: The commencement of any construction activity (e.g., land disturbing activities) covered under [[I. PERMIT COVERAGE AND LIMITATIONS #I.A. PERMIT COVERAGE|Part I.A]]. of this permit is prohibited until permit coverage under this permit is effective.<p>a. For projects listed in Part II.B.1.a. permit coverage will become effective seven (7) calendar days after the electronic submittal date or the postmarked date of a complete application form.</p><p>b. For projects listed in Part II.B.1.b. permit coverage will become effective 30 calendar days after the electronic submittal date, the postmarked date or MPCA date stamp (whichever is first) of the complete application. For incomplete applications (e.g., lack of fees or signature) or incomplete SWPPPs (e.g., missing calculations, Best Management Practice (BMP) specifications, estimated quantities of the BMPs, or timing of BMP installation narrative), the permit becomes effective 30 calendar days after all required information is submitted.</p> | ||
#Coverage Notification: Permittee(s) will be notified of coverage in a manner as determined by the Commissioner (e.g., e‐mail, online notification or letter). | #Coverage Notification: Permittee(s) will be notified of coverage in a manner as determined by the Commissioner (e.g., e‐mail, online notification or letter). | ||
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#Knowledgeable person/chain of responsibility: As part of the SWPPP, the owner must identify a person knowledgeable and experienced in the application of erosion prevention and sediment control BMPs who will oversee the implementation of the SWPPP, and the installation, inspection and maintenance of the erosion prevention and sediment control BMPs (see [[III. STORMWATER DISCHARGE DESIGN REQUIREMENTS#III.F. TRAINING REQUIREMENTS|Part III.F.1]].) before and during construction. The owner must identify in the SWPPP who will have the responsibility for long‐term operation and maintenance of the Permanent Stormwater Management System (see [[III. STORMWATER DISCHARGE DESIGN REQUIREMENTS#III.D. PERMANENT STORMWATER MANAGEMENT SYSTEM|Part III.D]].). The owner shall include in the SWPPP a chain of responsibility with all operators on the site, or if not known, the title or position of the responsible party, to ensure that the SWPPP will be implemented and stay in effect until the construction project is complete, the entire site has undergone Final Stabilization, and an NOT has been submitted to the MPCA. Once the identity of the responsible party is known, the SWPPP must be amended to inc lude this information. | #Knowledgeable person/chain of responsibility: As part of the SWPPP, the owner must identify a person knowledgeable and experienced in the application of erosion prevention and sediment control BMPs who will oversee the implementation of the SWPPP, and the installation, inspection and maintenance of the erosion prevention and sediment control BMPs (see [[III. STORMWATER DISCHARGE DESIGN REQUIREMENTS#III.F. TRAINING REQUIREMENTS|Part III.F.1]].) before and during construction. The owner must identify in the SWPPP who will have the responsibility for long‐term operation and maintenance of the Permanent Stormwater Management System (see [[III. STORMWATER DISCHARGE DESIGN REQUIREMENTS#III.D. PERMANENT STORMWATER MANAGEMENT SYSTEM|Part III.D]].). The owner shall include in the SWPPP a chain of responsibility with all operators on the site, or if not known, the title or position of the responsible party, to ensure that the SWPPP will be implemented and stay in effect until the construction project is complete, the entire site has undergone Final Stabilization, and an NOT has been submitted to the MPCA. Once the identity of the responsible party is known, the SWPPP must be amended to inc lude this information. | ||
#Training documentation: The Permittee(s) shall ensure the individuals identified in [[III. STORMWATER DISCHARGE DESIGN REQUIREMENTS#III.F. TRAINING REQUIREMENTS|Part III.F]]. have been trained in accordance with this Permit’s training requirements. The Permittee(s) shall ensure the training is recorded in or with the SWPPP before the start of construction or as soon as the personnel for the project have been determined. Documentation shall include:<p>a. Names of the personnel associated with this project that are required to be trained per [[III. STORMWATER DISCHARGE DESIGN REQUIREMENTS#III.F. TRAINING REQUIREMENTS|Part III.F.1]]. of this permit.</p><p>b. Dates of training and name of instructor(s) and entity providing training.</p><p>c. Content of training course or workshop including the number of hours of training.</p> | #Training documentation: The Permittee(s) shall ensure the individuals identified in [[III. STORMWATER DISCHARGE DESIGN REQUIREMENTS#III.F. TRAINING REQUIREMENTS|Part III.F]]. have been trained in accordance with this Permit’s training requirements. The Permittee(s) shall ensure the training is recorded in or with the SWPPP before the start of construction or as soon as the personnel for the project have been determined. Documentation shall include:<p>a. Names of the personnel associated with this project that are required to be trained per [[III. STORMWATER DISCHARGE DESIGN REQUIREMENTS#III.F. TRAINING REQUIREMENTS|Part III.F.1]]. of this permit.</p><p>b. Dates of training and name of instructor(s) and entity providing training.</p><p>c. Content of training course or workshop including the number of hours of training.</p> | ||
− | #Designs, calculations, and narrative: The SWPPP must incorporate the requirements of Part III (Stormwater Discharge Design Requirements) including calculations, Part IV (Construction Activity Requirements) and [ | + | #Designs, calculations, and narrative: The SWPPP must incorporate the requirements of Part III (Stormwater Discharge Design Requirements) including calculations, Part IV (Construction Activity Requirements) and [https://stormwater.pca.state.mn.us/index.php?title=2013_Construction_stormwater_permit#APPENDIX_A Appendix A] for the project. A narrative describing the timing for installation of all erosion prevention and sediment control BMPs and permanent stormwater management systems required in Part III, [https://stormwater.pca.state.mn.us/index.php?title=2013_Construction_stormwater_permit#APPENDIX_A Appendix A] must also be included in the SWPPP. |
− | #SWPPP components: The SWPPP requirements must be incorporated into the project's final plans and specifications and/or project documentation, as appropriate, and must include:<p>a. Location and type of all temporary and permanent erosion prevention and sediment control BMPs along with procedures to be used to establish additional temporary BMPs as necessary for the site conditions during construction. Standard details and/or specifications for the BMPs used on the project must be included in the final plans and specifications for the project.</p><p>b. Quantities: Estimated preliminary quantities tabulation anticipated at the start of the project for the life of the project must be included for all erosion prevention and sediment control BMPs in the SWPPP (e.g., linear feet of silt fence or ft<sup>2</sup> of erosion control blanket).</p><p>c. Impervious surface: The number of acres of impervious surface for both pre‐ and postconstruction must be specified.</p><p>d. Site map: A site map with existing and final grades, including dividing lines and direction of flow for all pre‐and post‐construction stormwater runoff drainage areas located within the project limits must be included. The site map must indicate the areas of steep slopes. The site map must also include impervious surfaces, soil types and locations of potential pollutant-generating activities as identified in [[III. STORMWATER DISCHARGE DESIGN REQUIREMENTS#III.F. TRAINING REQUIREMENTS|Part IV.F]].</p><p>e. Locations of areas not to be disturbed: Buffer zones, as required for temporary BMPs during construction in [[IV. CONSTRUCTION ACTIVITY REQUIREMENTS#IV.C. SEDIMENT CONTROL PRACTICES|Part IV.C.9]]., or if required as permanent BMPs in [ | + | #SWPPP components: The SWPPP requirements must be incorporated into the project's final plans and specifications and/or project documentation, as appropriate, and must include:<p>a. Location and type of all temporary and permanent erosion prevention and sediment control BMPs along with procedures to be used to establish additional temporary BMPs as necessary for the site conditions during construction. Standard details and/or specifications for the BMPs used on the project must be included in the final plans and specifications for the project.</p><p>b. Quantities: Estimated preliminary quantities tabulation anticipated at the start of the project for the life of the project must be included for all erosion prevention and sediment control BMPs in the SWPPP (e.g., linear feet of silt fence or ft<sup>2</sup> of erosion control blanket).</p><p>c. Impervious surface: The number of acres of impervious surface for both pre‐ and postconstruction must be specified.</p><p>d. Site map: A site map with existing and final grades, including dividing lines and direction of flow for all pre‐and post‐construction stormwater runoff drainage areas located within the project limits must be included. The site map must indicate the areas of steep slopes. The site map must also include impervious surfaces, soil types and locations of potential pollutant-generating activities as identified in [[III. STORMWATER DISCHARGE DESIGN REQUIREMENTS#III.F. TRAINING REQUIREMENTS|Part IV.F]].</p><p>e. Locations of areas not to be disturbed: Buffer zones, as required for temporary BMPs during construction in [[IV. CONSTRUCTION ACTIVITY REQUIREMENTS#IV.C. SEDIMENT CONTROL PRACTICES|Part IV.C.9]]., or if required as permanent BMPs in [https://stormwater.pca.state.mn.us/index.php?title=2013_Construction_stormwater_permit#APPENDIX_A Appendix A, Part C.3]., must be described and identified on plan sheets or project maps in the SWPPP.</p><p>f. Construction phasing: Location of areas where construction will be phased to minimize duration of exposed soil areas must be described.</p><p>g. Maps of surface waters and wetlands: The SWPPP must include a map of all surface waters, existing wetlands, and stormwater ponds or basins which can be identified on maps such as United States Geological Survey 7.5 minute quadrangle maps, the National Wetland Inventory map or equivalent maps within one mile (aerial radius measurement) from the project boundaries that will receive stormwater from the construction site, during or after construction. Where surface waters receiving stormwater associated with construction activity will not fit on the plan sheet, they must be identified with an arrow, indicating both direction and distance to the surface water. The SWPPP must identify if the surface water is a special or impaired water. The site map must also show construction activity areas that are adjacent to and drain to Public Waters for which the Department of Natural Resources has promulgated “work in water restrictions” during specified fish spawning time frames.</p><p>h. Final stabilization: Methods to be used for Final Stabilization of all exposed soil areas must be described.</p><p>i. BMP design factors: The SWPPP must account for the following factors in designing the temporary erosion prevention and sediment control BMPs:</p><p>i. The expected amount, frequency, intensity, and duration of precipitation.</p><p>ii. The nature of stormwater runoff and run‐on at the site, including factors such as expected flow from impervious surfaces, slopes, and site drainage features.</p><p>iii. If any stormwater flow will be channelized at the site, the Permitte(s) must design BMPs to control both peak flowrates and total stormwater volume to minimize erosion at outlets and to minimize downstream channel and streambank erosion.</p><p>iv. The range of soil particle sizes expected to be present on the site.</p><p>j. Soil Management: Methods used to minimize soil compaction and preserve topsoil must be described. Minimizing soil compaction is not required where the function of a specific area of the site dictates that it be compacted.</p><p>k. Maintenance plan: For projects that include permanent stormwater treatment systems, the SWPPP must include a maintenance plan identifying who will be performing future maintenance of the system.</p><p>l. Chemical treatments: Any specific chemicals and the chemical treatment systems that may be used for enhancing the sedimentation process on the site, and how compliance will be achieved with the requirements in [[III. STORMWATER DISCHARGE DESIGN REQUIREMENTS#III.C. TEMPORARY SEDIMENT BASINS|Part IV.C.10]]., must be described.</p><p>m. Documentation of infeasibility: If the Permittee(s) determine(s) that compliance with the requirement for temporary sediment basins ([[III. STORMWATER DISCHARGE DESIGN REQUIREMENTS#III.C. TEMPORARY SEDIMENT BASINS|Part III.C]].) is infeasible on the project site; the Permittee(s) must document that determination and the substitute BMPs in the SWPPP. If Permittee(s) cannot obtain right‐of‐way for the permanent stormwater management system; the Permittee(s) must document the infeasibility of obtaining right‐of‐way ([[III. STORMWATER DISCHARGE DESIGN REQUIREMENTS#III.D. PERMANENT STORMWATER MANAGEMENT SYSTEM|Part III.D]].)</p> |
#Stormwater pollution mitigation measures identified in environmental review or other required review: The SWPPP must include any stormwater mitigation measures approved as part of a final environmental review document, endangered species review, archeological or other required local, state or federal review conducted for the project. For the purposes of this permit provision, mitigation measures means actions necessary to avoid, minimize, or rectify (e.g., repairing, rehabilitating, restoring), reducing, eliminating or compensating for impacts related to: (1) stormwater discharges associated with the project’s construction activity; and (2) erosion prevention, sediment control and the Permanent Stormwater Management System for the project. | #Stormwater pollution mitigation measures identified in environmental review or other required review: The SWPPP must include any stormwater mitigation measures approved as part of a final environmental review document, endangered species review, archeological or other required local, state or federal review conducted for the project. For the purposes of this permit provision, mitigation measures means actions necessary to avoid, minimize, or rectify (e.g., repairing, rehabilitating, restoring), reducing, eliminating or compensating for impacts related to: (1) stormwater discharges associated with the project’s construction activity; and (2) erosion prevention, sediment control and the Permanent Stormwater Management System for the project. | ||
#Karst areas: The SWPPP must identify additional or different measures necessary (e.g. impervious liner in pond bottom) to assure compliance with surface and groundwater standards in Minn. R. chs. [https://www.revisor.mn.gov/rules/?id=7050 7050] and [https://www.revisor.mn.gov/rules/?id=7060 7060] in karst areas and to ensure protection of drinking water supply management areas (see [https://www.revisor.mn.gov/rules/?id=4720.5100 Minn. R. 4720.5100], subp. 13). | #Karst areas: The SWPPP must identify additional or different measures necessary (e.g. impervious liner in pond bottom) to assure compliance with surface and groundwater standards in Minn. R. chs. [https://www.revisor.mn.gov/rules/?id=7050 7050] and [https://www.revisor.mn.gov/rules/?id=7060 7060] in karst areas and to ensure protection of drinking water supply management areas (see [https://www.revisor.mn.gov/rules/?id=4720.5100 Minn. R. 4720.5100], subp. 13). | ||
− | #Impaired Waters and Total Maximum Daily Loads (TMDLs): The SWPPP must address the following:<p>a. For projects that have a discharge point on the project that is within one mile (aerial radius measurement) of and which flows to an impaired water, the Permittee(s) must identify the impaired water(s) in the SWPPP, and whether or not there is a USEPA‐approved TMDL for the pollutant(s) or stressor(s) identified in [ | + | #Impaired Waters and Total Maximum Daily Loads (TMDLs): The SWPPP must address the following:<p>a. For projects that have a discharge point on the project that is within one mile (aerial radius measurement) of and which flows to an impaired water, the Permittee(s) must identify the impaired water(s) in the SWPPP, and whether or not there is a USEPA‐approved TMDL for the pollutant(s) or stressor(s) identified in [https://stormwater.pca.state.mn.us/index.php?title=2013_Construction_stormwater_permit#APPENDIX_A Appendix A, Part B.10]. Unless otherwise notified by the MPCA in writing, the Permittee(s)’ identification of impaired waters must be based on the most recent USEPA approved section 303(d) Clean Water Act list of impaired waters and USEPA approved TMDLs at the time a complete permit application is submitted. The Permittee(s)’ identification must include those TMDLs, applicable to the project’s stormwater discharge, that were approved at any time prior to permit application submittal and are still in effect.</p><p>b. If the TMDL identifies specific implementation activities regarding construction stormwater that would apply to the site discharges, the Permittee(s) must include the BMPs identified in the TMDL and any other specific construction stormwater related implementation activities identified in the TMDL.</p> |
===III.B. SWPPP AMENDMENTS=== | ===III.B. SWPPP AMENDMENTS=== | ||
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#Where the calculation in Part III.C.1. has not been performed, a temporary sediment basin providing 3,600 cubic feet of live storage per acre drained to the basin shall be provided for the entire drainage area of the temporary basin. | #Where the calculation in Part III.C.1. has not been performed, a temporary sediment basin providing 3,600 cubic feet of live storage per acre drained to the basin shall be provided for the entire drainage area of the temporary basin. | ||
#Temporary basin outlets must be designed to prevent short‐circuiting and the discharge of floating debris. The basin must be designed with the ability to allow complete basin drawdown for maintenance activities, and must include a stabilized emergency overflow to prevent failure of pond integrity. The outlet structure must be designed to withdraw water from the surface in order to minimize the discharge of pollutants, except that the use of a surface withdrawal mechanism for discharge of the basin may be temporarily suspended during frozen conditions. Energy dissipation must be provided for the basin outlet (see [[IV. CONSTRUCTION ACTIVITY REQUIREMENTS#V.B. EROSION PREVENTION PRACTICES|Part IV.B.5]].). | #Temporary basin outlets must be designed to prevent short‐circuiting and the discharge of floating debris. The basin must be designed with the ability to allow complete basin drawdown for maintenance activities, and must include a stabilized emergency overflow to prevent failure of pond integrity. The outlet structure must be designed to withdraw water from the surface in order to minimize the discharge of pollutants, except that the use of a surface withdrawal mechanism for discharge of the basin may be temporarily suspended during frozen conditions. Energy dissipation must be provided for the basin outlet (see [[IV. CONSTRUCTION ACTIVITY REQUIREMENTS#V.B. EROSION PREVENTION PRACTICES|Part IV.B.5]].). | ||
− | #Sediment Basins must be situated outside of surface waters and any buffer zone required under Appendix A.C.3, and must be designed to avoid draining water from wetlands unless the impact to the wetland is in compliance with the requirements of [ | + | #Sediment Basins must be situated outside of surface waters and any buffer zone required under [https://stormwater.pca.state.mn.us/index.php?title=2013_Construction_stormwater_permit#APPENDIX_A Appendix A.C.3], and must be designed to avoid draining water from wetlands unless the impact to the wetland is in compliance with the requirements of [https://stormwater.pca.state.mn.us/index.php?title=2013_Construction_stormwater_permit#APPENDIX_A Appendix A, Part D]. |
#The temporary basins must be constructed and made operational prior to 10 or more acres of disturbed soil draining to a common location. | #The temporary basins must be constructed and made operational prior to 10 or more acres of disturbed soil draining to a common location. | ||
#Where a temporary sediment basin meeting the requirements of this part is infeasible, equivalent sediment controls such as smaller sediment basins, and/or sediment traps, silt fences, vegetative buffer strips, or any appropriate combination of measures are required for all down‐slope boundaries of the construction area and for side‐slope boundaries as dictated by individual site conditions. In determining whether installing a sediment basin is infeasible, the Permittee(s) must consider public safety and may consider factors such as site soils, slope, and available area on site. This determination of infeasibility must be documented in the SWPPP per [https://stormwater.pca.state.mn.us/index.php?title=2013_Construction_stormwater_permit#III.A._STORMWATER_POLLUTION_PREVENTION_PLAN_CONTENT Part III.A.5.m]. | #Where a temporary sediment basin meeting the requirements of this part is infeasible, equivalent sediment controls such as smaller sediment basins, and/or sediment traps, silt fences, vegetative buffer strips, or any appropriate combination of measures are required for all down‐slope boundaries of the construction area and for side‐slope boundaries as dictated by individual site conditions. In determining whether installing a sediment basin is infeasible, the Permittee(s) must consider public safety and may consider factors such as site soils, slope, and available area on site. This determination of infeasibility must be documented in the SWPPP per [https://stormwater.pca.state.mn.us/index.php?title=2013_Construction_stormwater_permit#III.A._STORMWATER_POLLUTION_PREVENTION_PLAN_CONTENT Part III.A.5.m]. | ||
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<p>When constructing any of the permanent stormwater management systems in this part, the Permittee(s) must incorporate the following design parameters:</p> | <p>When constructing any of the permanent stormwater management systems in this part, the Permittee(s) must incorporate the following design parameters:</p> | ||
#Infiltration/Filtration<p>a. Infiltration/Filtration options include but are not limited to: infiltration basins, infiltration trenches, rainwater gardens, sand filters, organic filters, bioretention areas, natural or enhanced swales, dry storage ponds with underdrain discharge, off‐line retention areas, and natural depressions. Infiltration must be used only as appropriate to the site and land uses. The method selected by the Permittee(s) must remove settleable solids, floating materials, and oils and grease from the runoff to the maximum extent practicable before runoff enters the infiltration/filtration system. Filtration systems must be designed to remove at least 80 percent of total suspended solids. When designing the system the Permittee(s) must evaluate the impact of constructing an infiltration practice on existing hydrologic features (e.g., existing wetlands) and the system must be designed to maintain pre‐existing conditions (e.g., do not breach a perched water table that is supporting a wetland). For a discussion of potential stormwater hotspots, groundwater warnings, design measures, maintenance considerations or other retention, detention, and treatment devices, see the Minnesota Stormwater Manual found on the MPCA’s website.</p><p>b. Infiltration systems must not be excavated to final grade until the contributing drainage area has been constructed and fully stabilized unless rigorous erosion prevention and sediment controls are provided (Part III.D.1.c.).</p><p>c. When an infiltration system is excavated to final grade (or within three (3) feet of final grade), the Permittee(s) must employ rigorous erosion prevention and sediment controls (e.g., diversion berms) to keep sediment and runoff completely away from the infiltration area. The area must be staked off and marked so that heavy construction vehicles or equipment will not compact the soil in the proposed infiltration area.</p><p>d. To prevent clogging of the infiltration or filtration system, the Permittee(s) must use a pretreatment device such as a vegetated filter strip, small sedimentation basin, or water quality inlet (e.g., grit chamber) to settle particulates before the stormwater discharges into the infiltration or filtration system.</p><p>e. The Permittee(s) must design infiltration or filtration systems that provide a water quality volume (calculated as an instantaneous volume) of one (1) inch of runoff (or one (1) inch minus the volume of stormwater treated by another system on the site) from the new impervious surfaces created by the project.</p><p>f. The Permittee(s) must design the infiltration/filtration system to discharge the water quality volume routed to the system through the soil surface or filter media within 48 hours or less. dditional flows that cannot be infiltrated or filtered within 48 hours must be routed to bypass the system through a stabilized discharge point. The Permittee(s) must design the infiltration system to provide a means to visually verify that the system is discharging through the soil surface or filter media within 48 hours or less.</p><p>g. The Permittee(s) shall employ appropriate on‐site testing consistent with the recommendations found in the Minnesota Stormwater Manual to verify soil type and to ensure a minimum of three (3) feet of separation from the seasonally saturated soils (or from bedrock) and the bottom of the proposed infiltration/filtration system.</p><p>h. The Permittee(s) must ensure filtration systems with less than three (3) feet of separation from seasonally saturated soils or from bedrock are constructed with an impermeable liner.</p><p>i. The Permittee(s) must design adequate maintenance access (typically eight (8) feet wide).</p><p>j. Infiltration is prohibited when the infiltration system will be constructed in:</p><p>i. Areas that receive discharges from vehicle fueling and maintenance.</p><p>ii. Areas with less than three (3) feet of separation distance from the bottom of the infiltration system to the elevation of the seasonally saturated soils or the top of bedrock.</p><p>iii. Areas that receive discharges from industrial facilities which are not authorized to infiltrate industrial stormwater under an NPDES/SDS Industrial Stormwater Permit issued by the MPCA.</p><p>iv. Areas where high levels of contaminants in soil or groundwater will be mobilized by the infiltrating stormwater.</p><p>v. Areas of predominately Hydrologic Soil Group D (clay) soils unless allowed by a local unit of government with a current MS4 permit.</p><p>vi. Areas within 1,000 feet up‐gradient, or 100 feet down‐gradient of active karst features unless allowed by a local unit of government with a current MS4 permit.</p><p>vii. Areas within a Drinking Water Supply Management Area (DWSMA) as defined in [https://www.revisor.mn.gov/rules/?id=4720.5100 Minn. R. 4720.5100], subp. 13., unless allowed by a local unit of government with a current MS4 permit.</p><p>viii. Areas where soil infiltration rates are more than 8.3 inches per hour unless soils are amended to slow the infiltration rate below 8.3 inches per hour or as allowed by a local unit of government with a current MS4 permit.</p> | #Infiltration/Filtration<p>a. Infiltration/Filtration options include but are not limited to: infiltration basins, infiltration trenches, rainwater gardens, sand filters, organic filters, bioretention areas, natural or enhanced swales, dry storage ponds with underdrain discharge, off‐line retention areas, and natural depressions. Infiltration must be used only as appropriate to the site and land uses. The method selected by the Permittee(s) must remove settleable solids, floating materials, and oils and grease from the runoff to the maximum extent practicable before runoff enters the infiltration/filtration system. Filtration systems must be designed to remove at least 80 percent of total suspended solids. When designing the system the Permittee(s) must evaluate the impact of constructing an infiltration practice on existing hydrologic features (e.g., existing wetlands) and the system must be designed to maintain pre‐existing conditions (e.g., do not breach a perched water table that is supporting a wetland). For a discussion of potential stormwater hotspots, groundwater warnings, design measures, maintenance considerations or other retention, detention, and treatment devices, see the Minnesota Stormwater Manual found on the MPCA’s website.</p><p>b. Infiltration systems must not be excavated to final grade until the contributing drainage area has been constructed and fully stabilized unless rigorous erosion prevention and sediment controls are provided (Part III.D.1.c.).</p><p>c. When an infiltration system is excavated to final grade (or within three (3) feet of final grade), the Permittee(s) must employ rigorous erosion prevention and sediment controls (e.g., diversion berms) to keep sediment and runoff completely away from the infiltration area. The area must be staked off and marked so that heavy construction vehicles or equipment will not compact the soil in the proposed infiltration area.</p><p>d. To prevent clogging of the infiltration or filtration system, the Permittee(s) must use a pretreatment device such as a vegetated filter strip, small sedimentation basin, or water quality inlet (e.g., grit chamber) to settle particulates before the stormwater discharges into the infiltration or filtration system.</p><p>e. The Permittee(s) must design infiltration or filtration systems that provide a water quality volume (calculated as an instantaneous volume) of one (1) inch of runoff (or one (1) inch minus the volume of stormwater treated by another system on the site) from the new impervious surfaces created by the project.</p><p>f. The Permittee(s) must design the infiltration/filtration system to discharge the water quality volume routed to the system through the soil surface or filter media within 48 hours or less. dditional flows that cannot be infiltrated or filtered within 48 hours must be routed to bypass the system through a stabilized discharge point. The Permittee(s) must design the infiltration system to provide a means to visually verify that the system is discharging through the soil surface or filter media within 48 hours or less.</p><p>g. The Permittee(s) shall employ appropriate on‐site testing consistent with the recommendations found in the Minnesota Stormwater Manual to verify soil type and to ensure a minimum of three (3) feet of separation from the seasonally saturated soils (or from bedrock) and the bottom of the proposed infiltration/filtration system.</p><p>h. The Permittee(s) must ensure filtration systems with less than three (3) feet of separation from seasonally saturated soils or from bedrock are constructed with an impermeable liner.</p><p>i. The Permittee(s) must design adequate maintenance access (typically eight (8) feet wide).</p><p>j. Infiltration is prohibited when the infiltration system will be constructed in:</p><p>i. Areas that receive discharges from vehicle fueling and maintenance.</p><p>ii. Areas with less than three (3) feet of separation distance from the bottom of the infiltration system to the elevation of the seasonally saturated soils or the top of bedrock.</p><p>iii. Areas that receive discharges from industrial facilities which are not authorized to infiltrate industrial stormwater under an NPDES/SDS Industrial Stormwater Permit issued by the MPCA.</p><p>iv. Areas where high levels of contaminants in soil or groundwater will be mobilized by the infiltrating stormwater.</p><p>v. Areas of predominately Hydrologic Soil Group D (clay) soils unless allowed by a local unit of government with a current MS4 permit.</p><p>vi. Areas within 1,000 feet up‐gradient, or 100 feet down‐gradient of active karst features unless allowed by a local unit of government with a current MS4 permit.</p><p>vii. Areas within a Drinking Water Supply Management Area (DWSMA) as defined in [https://www.revisor.mn.gov/rules/?id=4720.5100 Minn. R. 4720.5100], subp. 13., unless allowed by a local unit of government with a current MS4 permit.</p><p>viii. Areas where soil infiltration rates are more than 8.3 inches per hour unless soils are amended to slow the infiltration rate below 8.3 inches per hour or as allowed by a local unit of government with a current MS4 permit.</p> | ||
− | #Wet Sedimentation Basin<p>a. The Permitte(s) must design the basin to have a permanent volume of 1,800 cubic feet of storage below the outlet pipe for each acre that drains to the basin. The basin’s permanent volume must reach a minimum depth of at least three (3) feet and must have no depth greater than 10 feet. The basin must be configured such that scour or resuspension of solids is minimized.</p><p>b. The Permittee(s) must design basins to provide live storage for a water quality volume (calculated as an instantaneous volume) of one (1) inch of runoff (or one (1) inch minus the volume of stormwater treated by another system on the site) from the new impervious surfaces created by the project.</p><p>c. The Permittee(s) must design basin outlets such that the water quality volume is discharged at no more than 5.66 cubic feet per second (cfs) per acre of surface area of the pond.</p><p>d. The Permittee(s) must design basin outlets to prevent short‐circuiting and the discharge of floating debris. Basin outlets must have energy dissipation.</p><p>e. The Permittee(s) must design the basin to include a stabilized emergency overflow to accommodate storm events in excess of the basin’s hydraulic design.</p><p>f. The Permittee(s) must design adequate maintenance access (typically eight (8) feet wide).</p><p>g. The Permittee(s) must design sediment Basins to be situated outside of surface waters and any buffer zone required under [ | + | #Wet Sedimentation Basin<p>a. The Permitte(s) must design the basin to have a permanent volume of 1,800 cubic feet of storage below the outlet pipe for each acre that drains to the basin. The basin’s permanent volume must reach a minimum depth of at least three (3) feet and must have no depth greater than 10 feet. The basin must be configured such that scour or resuspension of solids is minimized.</p><p>b. The Permittee(s) must design basins to provide live storage for a water quality volume (calculated as an instantaneous volume) of one (1) inch of runoff (or one (1) inch minus the volume of stormwater treated by another system on the site) from the new impervious surfaces created by the project.</p><p>c. The Permittee(s) must design basin outlets such that the water quality volume is discharged at no more than 5.66 cubic feet per second (cfs) per acre of surface area of the pond.</p><p>d. The Permittee(s) must design basin outlets to prevent short‐circuiting and the discharge of floating debris. Basin outlets must have energy dissipation.</p><p>e. The Permittee(s) must design the basin to include a stabilized emergency overflow to accommodate storm events in excess of the basin’s hydraulic design.</p><p>f. The Permittee(s) must design adequate maintenance access (typically eight (8) feet wide).</p><p>g. The Permittee(s) must design sediment Basins to be situated outside of surface waters and any buffer zone required under [https://stormwater.pca.state.mn.us/index.php?title=2013_Construction_stormwater_permit#APPENDIX_A Appendix A, Part C.3]. and they must be designed to avoid draining water from wetlands unless the impact to the wetland is in compliance with the requirements of [https://stormwater.pca.state.mn.us/index.php?title=2013_Construction_stormwater_permit#APPENDIX_A Appendix A, Part D].</p> |
− | #Regional Ponds<p>When the entire water quality volume cannot be retained onsite, the Permittee(s) can use or create regional ponds provided that they are constructed ponds, not a natural wetland or water body, (wetlands used as regional ponds must be mitigated for, see [ | + | #Regional Ponds<p>When the entire water quality volume cannot be retained onsite, the Permittee(s) can use or create regional ponds provided that they are constructed ponds, not a natural wetland or water body, (wetlands used as regional ponds must be mitigated for, see [https://stormwater.pca.state.mn.us/index.php?title=2013_Construction_stormwater_permit#APPENDIX_A Appendix A, Part D]) and designed in accordance with this permit’s design requirements (Part III.D.2.) for all water from impervious surfaces that reach the pond. Permittee(s) shall not construct regional ponds in wetlands, regardless of their condition, quality or designation by local plans, unless the mitigative sequence in [https://stormwater.pca.state.mn.us/index.php?title=2013_Construction_stormwater_permit#APPENDIX_A Appendix A, Part D]. of this permit has been completed. There must be no significant degradation of the waterways between the project and the regional pond. The owner must obtain written authorization from the applicable local governmental unit (LGU) or private entity that owns and maintains the regional pond. The LGU’s or private entity’s written authorization must identify that the regional pond will discharge the water q uality volume (one (1) inch of runoff from the impervious watershed area) at no more than 5.66 cfs per acre of surface area of the pond. The owner must include the LGU’s or private entities’ written authorization in the SWPPP. The LGU’s or private entity’s written authorization must be obtained before the owner finalizes the SWPPP and before any application for this permit is made to the MPCA.</p> |
===III.E RECORD RETENTION=== | ===III.E RECORD RETENTION=== |
GENERAL PERMIT AUTHORIZATION TO DISCHARGE STORMWATER ASSOCIATED WITH CONSTRUCTION ACTIVITY UNDER THE NATIONAL POLLUTANT DISCHARGE ELIMINATION SYSTEM/STATE DISPOSAL SYSTEM PROGRAM
Link to the 2013 Construction Strormwater Permit - pdf version File:Wq-strm2-68a.pdf
Construction activity does not include a disturbance to the land of less than five (5) acres for the purpose of routine maintenance that is performed to maintain the original line and grade, hydraulic capacity, or original purpose of the facility. Pavement rehabilitation that does not disturb the underlying soils (e.g., mill and overlay projects) is not considered construction activity.
a. The Permittee(s) of those ongoing projects shall amend the SWPPP for the project to meet the requirements of this reissued permit no later than 18 months after the issuance date of this reissued permit if the termination‐of‐coverage requirements in Part II.C. will not be met within 18 months of the issuance date of this reissued permit and shall thereafter comply with this permit. However, additional permanent treatment required in this reissued permit is not required for previously permitted projects.
b. If the previously permitted ongoing project will meet the termination‐of‐coverage requirements in Part II.C. within 18 months of the issuance date of this reissued permit, the Permittee(s) shall comply with the 2008 construction general permit until the project is complete and a Notice of Termination (NOT) consistent with Part II.C. of this reissued permit is submitted.
c. If a previously permitted ongoing project will not be able to meet the terms and conditions of this reissued permit (other than the additional permanent treatment requirement) and will continue longer than 18 months after the issuance date of this permit, the Permittee(s) shall apply for an individual permit in accordance with Minn. R. ch. 7001.
This permit does not authorize discharges related to the following activities:
a. Discharges into outstanding resource value waters as listed in Minn. R. 7050.0180, subp. 3, 4, 5, 6, 6a and 6b.
b. Discharges into trout waters as listed in Minn. R. 6264.0050, subp. 2 and 4.
c. Discharges into wetlands as defined in Minn. R. 7050.0186 subd.1a.B.
d. Discharges from projects that have not completed applicable Environmental Review requirements under state or federal laws.
e. Discharges that adversely impact or contribute to adverse impacts on a state or federally listed endangered or threatened species or adversely modify a designated critical habitat.
f. Discharges that adversely affect properties listed or eligible for listing in the National Register of Historic Places or affecting known or discovered archeological sites.
The owner must develop an accurate and complete SWPPP in accordance with Part III. (Stormwater Discharge Design Requirements) of this permit prior to submitting the application for coverage. The SWPPP is not required to be submitted to the MPCA (unless the project size is 50 acres or more and will discharge to certain waters as described in Part II.B.1.b.) but is to be retained by the owner in accordance with Part III.E. (Record Retention). The owner’s failure to prepare an accurate and complete SWPPP prior to submitting the application is grounds for MPCA to revoke the permit.
a. The owner and operator shall submit a complete and accurate on‐line application form with the appropriate fee to the MPCA for each project that disturbs one (1) or more acres of land or for a common plan of development or sale that will ultimately disturb one (1) or more acres. If the applicant is not able to apply on‐line, contact the MPCA for technical assistance or a waiver.
b. For certain projects or common plans of development or sale disturbing 50 acres or more, the application must be submitted at least 30 days before the start of construction activity. This requirement pertains to projects that have a discharge point on the project that is within one mile (aerial radius measurement) of, and flows to, a special water listed in Appendix A, Part B. or waters listed as impaired under section 303(d) of the federal Clean Water Act (see the MPCA’s website) where the identified pollutant(s) or stressor(s) are phosphorus (nutrient eutrophication biological indicators), turbidity, dissolved oxygen, or biotic impairment (fish bioassessment, aquatic plant bioassessment and aquatic macroinvertebrate bioassessment). Applicants of projects listed in this part must submit a complete and accurate application form and SWPPP including all calculations for the Permanent Stormwater Management System (see Parts III.A.‐D.).
a. For projects listed in Part II.B.1.a. permit coverage will become effective seven (7) calendar days after the electronic submittal date or the postmarked date of a complete application form.
b. For projects listed in Part II.B.1.b. permit coverage will become effective 30 calendar days after the electronic submittal date, the postmarked date or MPCA date stamp (whichever is first) of the complete application. For incomplete applications (e.g., lack of fees or signature) or incomplete SWPPPs (e.g., missing calculations, Best Management Practice (BMP) specifications, estimated quantities of the BMPs, or timing of BMP installation narrative), the permit becomes effective 30 calendar days after all required information is submitted.
a. Construction activity has ceased for at least 90 days.
b. At least 90 percent (by area) of all originally proposed construction activity has been completed and permanent cover established on those areas.
c. On areas where construction activity is not complete, permanent cover has been established.
d. The site is in compliance with Part IV.G.2. and Part IV.G.3. and where applicable, Part IV.G.4. or Part IV.G.5.
The owner must develop a Stormwater Pollution Prevention Plan (SWPPP). The SWPPP shall be completed prior to submitting any permit application and prior to conducting any construction activity by any required Permittee(s). For stormwater discharges from construction activity where the owner or operator changes, the new owner or operator can implement the original SWPPP created for the project, modify the original SWPPP, or develop and implement their own SWPPP. Permittee(s) shall ensure either directly or through coordination with other Permittee(s) that their SWPPP meets all terms and conditions of this permit and that their activities do not render another party’s erosion prevention and sediment control BMPs ineffective. The SWPPP must include the following:
a. Names of the personnel associated with this project that are required to be trained per Part III.F.1. of this permit.
b. Dates of training and name of instructor(s) and entity providing training.
c. Content of training course or workshop including the number of hours of training.
a. Location and type of all temporary and permanent erosion prevention and sediment control BMPs along with procedures to be used to establish additional temporary BMPs as necessary for the site conditions during construction. Standard details and/or specifications for the BMPs used on the project must be included in the final plans and specifications for the project.
b. Quantities: Estimated preliminary quantities tabulation anticipated at the start of the project for the life of the project must be included for all erosion prevention and sediment control BMPs in the SWPPP (e.g., linear feet of silt fence or ft2 of erosion control blanket).
c. Impervious surface: The number of acres of impervious surface for both pre‐ and postconstruction must be specified.
d. Site map: A site map with existing and final grades, including dividing lines and direction of flow for all pre‐and post‐construction stormwater runoff drainage areas located within the project limits must be included. The site map must indicate the areas of steep slopes. The site map must also include impervious surfaces, soil types and locations of potential pollutant-generating activities as identified in Part IV.F.
e. Locations of areas not to be disturbed: Buffer zones, as required for temporary BMPs during construction in Part IV.C.9., or if required as permanent BMPs in Appendix A, Part C.3., must be described and identified on plan sheets or project maps in the SWPPP.
f. Construction phasing: Location of areas where construction will be phased to minimize duration of exposed soil areas must be described.
g. Maps of surface waters and wetlands: The SWPPP must include a map of all surface waters, existing wetlands, and stormwater ponds or basins which can be identified on maps such as United States Geological Survey 7.5 minute quadrangle maps, the National Wetland Inventory map or equivalent maps within one mile (aerial radius measurement) from the project boundaries that will receive stormwater from the construction site, during or after construction. Where surface waters receiving stormwater associated with construction activity will not fit on the plan sheet, they must be identified with an arrow, indicating both direction and distance to the surface water. The SWPPP must identify if the surface water is a special or impaired water. The site map must also show construction activity areas that are adjacent to and drain to Public Waters for which the Department of Natural Resources has promulgated “work in water restrictions” during specified fish spawning time frames.
h. Final stabilization: Methods to be used for Final Stabilization of all exposed soil areas must be described.
i. BMP design factors: The SWPPP must account for the following factors in designing the temporary erosion prevention and sediment control BMPs:
i. The expected amount, frequency, intensity, and duration of precipitation.
ii. The nature of stormwater runoff and run‐on at the site, including factors such as expected flow from impervious surfaces, slopes, and site drainage features.
iii. If any stormwater flow will be channelized at the site, the Permitte(s) must design BMPs to control both peak flowrates and total stormwater volume to minimize erosion at outlets and to minimize downstream channel and streambank erosion.
iv. The range of soil particle sizes expected to be present on the site.
j. Soil Management: Methods used to minimize soil compaction and preserve topsoil must be described. Minimizing soil compaction is not required where the function of a specific area of the site dictates that it be compacted.
k. Maintenance plan: For projects that include permanent stormwater treatment systems, the SWPPP must include a maintenance plan identifying who will be performing future maintenance of the system.
l. Chemical treatments: Any specific chemicals and the chemical treatment systems that may be used for enhancing the sedimentation process on the site, and how compliance will be achieved with the requirements in Part IV.C.10., must be described.
m. Documentation of infeasibility: If the Permittee(s) determine(s) that compliance with the requirement for temporary sediment basins (Part III.C.) is infeasible on the project site; the Permittee(s) must document that determination and the substitute BMPs in the SWPPP. If Permittee(s) cannot obtain right‐of‐way for the permanent stormwater management system; the Permittee(s) must document the infeasibility of obtaining right‐of‐way (Part III.D.)
a. For projects that have a discharge point on the project that is within one mile (aerial radius measurement) of and which flows to an impaired water, the Permittee(s) must identify the impaired water(s) in the SWPPP, and whether or not there is a USEPA‐approved TMDL for the pollutant(s) or stressor(s) identified in Appendix A, Part B.10. Unless otherwise notified by the MPCA in writing, the Permittee(s)’ identification of impaired waters must be based on the most recent USEPA approved section 303(d) Clean Water Act list of impaired waters and USEPA approved TMDLs at the time a complete permit application is submitted. The Permittee(s)’ identification must include those TMDLs, applicable to the project’s stormwater discharge, that were approved at any time prior to permit application submittal and are still in effect.
b. If the TMDL identifies specific implementation activities regarding construction stormwater that would apply to the site discharges, the Permittee(s) must include the BMPs identified in the TMDL and any other specific construction stormwater related implementation activities identified in the TMDL.
The Permittee(s) must amend the SWPPP as necessary to include additional requirements, such as additional or modified BMPs that are designed to correct problems identified or address situations whenever:
Where ten (10) or more acres of disturbed soil drain to a common location, the Permittee(s) must provide a temporary sediment basin to provide treatment to the runoff before it leaves the construction site or enters surface waters. A temporary sediment basin may be converted to a permanent basin after construction is complete. The temporary basin is no longer required when permanent cover has reduced the acreage of disturbed soil to less than ten (10) acres draining to a common location. The Permittee(s) is/are encouraged, but not required, to install temporary sediment basins where appropriate in areas with steep slopes or highly erodible soils even if less than ten (10) acres drains to one area. The basins must be designed and constructed according to the following requirements:
The Permittee(s) shall design the project so that all stormwater discharged from the project during and after construction activities does not cause a violation of state water quality standards, including nuisance conditions, erosion in receiving channels or on downslope properties, or a significant adverse impact to wetlands caused by inundation or decrease of flow.
The Permittee(s) shall construct a permanent stormwater management system meeting the requirements of this Part, or if the project is located in a jurisdiction subject to a NPDES/SDS Municipal Separate Storm Sewer System (MS4) permit and that permit has established permanent treatment requirements that include volume reduction, the Permittee(s) can comply with the permanent treatment requirements established under the MS4 permit in lieu of the permanent treatment requirements of this permit.
Where a project’s ultimate development replaces vegetation and/or other pervious surfaces with one (1) or more acres of cumulative impervious surface, the Permittee(s) must design the project so that the water quality volume of one (1) inch of runoff from the new impervious surfaces created by the project is retained on site (i.e. infiltration or other volume reduction practices) and not discharged to a surface water. For purposes of this part, surface waters does not include man‐made drainage systems that convey stormwater to a compliant permanent stormwater management system.
For those projects where infiltration is prohibited (see Part III.D.1.j.), the Permittee(s) shall consider other methods of volume reduction and the water quality volume (or remainder of the water quality volume if some volume reduction is achieved) must be treated by a wet sedimentation basin, filtration system, regional ponding or equivalent methods prior to the discharge of stormwater to surface waters.
Where the proximity to bedrock precludes the installation of any of the permanent stormwater management practices outlined in Part III.D., other treatment, such as grassed swales, filtration systems, smaller ponds, or grit chambers, is required prior to the discharge of stormwater to surface waters.
For work on linear projects with lack of right‐of‐way where the Permittee(s) cannot obtain an easement or other permission for property needed to install treatment systems capable of treating the entire water quality volume on site, the Permittee(s) must maximize the water quality volume that can be treated prior to discharge to surface waters. Treatment can be provided through other methods or combination of methods such as grassed swales, filtration systems, smaller ponds, or grit chambers, prior to discharge to surface waters. A reasonable attempt must be made to obtain right‐of‐way during the project planning process. Documentation of these attempts must be in the SWPPP per Part III.A.5.m. in the section addressing infeasibility.
When constructing any of the permanent stormwater management systems in this part, the Permittee(s) must incorporate the following design parameters:
a. Infiltration/Filtration options include but are not limited to: infiltration basins, infiltration trenches, rainwater gardens, sand filters, organic filters, bioretention areas, natural or enhanced swales, dry storage ponds with underdrain discharge, off‐line retention areas, and natural depressions. Infiltration must be used only as appropriate to the site and land uses. The method selected by the Permittee(s) must remove settleable solids, floating materials, and oils and grease from the runoff to the maximum extent practicable before runoff enters the infiltration/filtration system. Filtration systems must be designed to remove at least 80 percent of total suspended solids. When designing the system the Permittee(s) must evaluate the impact of constructing an infiltration practice on existing hydrologic features (e.g., existing wetlands) and the system must be designed to maintain pre‐existing conditions (e.g., do not breach a perched water table that is supporting a wetland). For a discussion of potential stormwater hotspots, groundwater warnings, design measures, maintenance considerations or other retention, detention, and treatment devices, see the Minnesota Stormwater Manual found on the MPCA’s website.
b. Infiltration systems must not be excavated to final grade until the contributing drainage area has been constructed and fully stabilized unless rigorous erosion prevention and sediment controls are provided (Part III.D.1.c.).
c. When an infiltration system is excavated to final grade (or within three (3) feet of final grade), the Permittee(s) must employ rigorous erosion prevention and sediment controls (e.g., diversion berms) to keep sediment and runoff completely away from the infiltration area. The area must be staked off and marked so that heavy construction vehicles or equipment will not compact the soil in the proposed infiltration area.
d. To prevent clogging of the infiltration or filtration system, the Permittee(s) must use a pretreatment device such as a vegetated filter strip, small sedimentation basin, or water quality inlet (e.g., grit chamber) to settle particulates before the stormwater discharges into the infiltration or filtration system.
e. The Permittee(s) must design infiltration or filtration systems that provide a water quality volume (calculated as an instantaneous volume) of one (1) inch of runoff (or one (1) inch minus the volume of stormwater treated by another system on the site) from the new impervious surfaces created by the project.
f. The Permittee(s) must design the infiltration/filtration system to discharge the water quality volume routed to the system through the soil surface or filter media within 48 hours or less. dditional flows that cannot be infiltrated or filtered within 48 hours must be routed to bypass the system through a stabilized discharge point. The Permittee(s) must design the infiltration system to provide a means to visually verify that the system is discharging through the soil surface or filter media within 48 hours or less.
g. The Permittee(s) shall employ appropriate on‐site testing consistent with the recommendations found in the Minnesota Stormwater Manual to verify soil type and to ensure a minimum of three (3) feet of separation from the seasonally saturated soils (or from bedrock) and the bottom of the proposed infiltration/filtration system.
h. The Permittee(s) must ensure filtration systems with less than three (3) feet of separation from seasonally saturated soils or from bedrock are constructed with an impermeable liner.
i. The Permittee(s) must design adequate maintenance access (typically eight (8) feet wide).
j. Infiltration is prohibited when the infiltration system will be constructed in:
i. Areas that receive discharges from vehicle fueling and maintenance.
ii. Areas with less than three (3) feet of separation distance from the bottom of the infiltration system to the elevation of the seasonally saturated soils or the top of bedrock.
iii. Areas that receive discharges from industrial facilities which are not authorized to infiltrate industrial stormwater under an NPDES/SDS Industrial Stormwater Permit issued by the MPCA.
iv. Areas where high levels of contaminants in soil or groundwater will be mobilized by the infiltrating stormwater.
v. Areas of predominately Hydrologic Soil Group D (clay) soils unless allowed by a local unit of government with a current MS4 permit.
vi. Areas within 1,000 feet up‐gradient, or 100 feet down‐gradient of active karst features unless allowed by a local unit of government with a current MS4 permit.
vii. Areas within a Drinking Water Supply Management Area (DWSMA) as defined in Minn. R. 4720.5100, subp. 13., unless allowed by a local unit of government with a current MS4 permit.
viii. Areas where soil infiltration rates are more than 8.3 inches per hour unless soils are amended to slow the infiltration rate below 8.3 inches per hour or as allowed by a local unit of government with a current MS4 permit.
a. The Permitte(s) must design the basin to have a permanent volume of 1,800 cubic feet of storage below the outlet pipe for each acre that drains to the basin. The basin’s permanent volume must reach a minimum depth of at least three (3) feet and must have no depth greater than 10 feet. The basin must be configured such that scour or resuspension of solids is minimized.
b. The Permittee(s) must design basins to provide live storage for a water quality volume (calculated as an instantaneous volume) of one (1) inch of runoff (or one (1) inch minus the volume of stormwater treated by another system on the site) from the new impervious surfaces created by the project.
c. The Permittee(s) must design basin outlets such that the water quality volume is discharged at no more than 5.66 cubic feet per second (cfs) per acre of surface area of the pond.
d. The Permittee(s) must design basin outlets to prevent short‐circuiting and the discharge of floating debris. Basin outlets must have energy dissipation.
e. The Permittee(s) must design the basin to include a stabilized emergency overflow to accommodate storm events in excess of the basin’s hydraulic design.
f. The Permittee(s) must design adequate maintenance access (typically eight (8) feet wide).
g. The Permittee(s) must design sediment Basins to be situated outside of surface waters and any buffer zone required under Appendix A, Part C.3. and they must be designed to avoid draining water from wetlands unless the impact to the wetland is in compliance with the requirements of Appendix A, Part D.
When the entire water quality volume cannot be retained onsite, the Permittee(s) can use or create regional ponds provided that they are constructed ponds, not a natural wetland or water body, (wetlands used as regional ponds must be mitigated for, see Appendix A, Part D) and designed in accordance with this permit’s design requirements (Part III.D.2.) for all water from impervious surfaces that reach the pond. Permittee(s) shall not construct regional ponds in wetlands, regardless of their condition, quality or designation by local plans, unless the mitigative sequence in Appendix A, Part D. of this permit has been completed. There must be no significant degradation of the waterways between the project and the regional pond. The owner must obtain written authorization from the applicable local governmental unit (LGU) or private entity that owns and maintains the regional pond. The LGU’s or private entity’s written authorization must identify that the regional pond will discharge the water q uality volume (one (1) inch of runoff from the impervious watershed area) at no more than 5.66 cfs per acre of surface area of the pond. The owner must include the LGU’s or private entities’ written authorization in the SWPPP. The LGU’s or private entity’s written authorization must be obtained before the owner finalizes the SWPPP and before any application for this permit is made to the MPCA.
The SWPPP (original or copies) including, all changes to it, and inspections and maintenance records must be kept at the site during construction by the Permittee(s) who has/have operational control of that portion of the site. The SWPPP can be kept in either the field office or in an on‐site vehicle during normal working hours.
All owner(s) must keep the following records on file for three (3) years after submittal of the NOT as outlined in Part II.C. This does not include any records after submittal of the NOT.
The Permittee(s) shall ensure the following individuals identified in this part have been trained in accordance with this Permit’s training requirements.
a. Individual(s) preparing the SWPPP for the project
b. Individual(s) overseeing implementation of, revising, and amending the SWPPP and individual(s) performing inspections as required in Part IV.E. One of these individual(s) must be available for an onsite inspection within 72 hours upon request by the MPCA.
c. Individual(s) performing or supervising the installation, maintenance and repair of BMPs. At least one individual on a project must be trained in these job duties.
The Permittee(s) must implement the SWPPP and the requirements of this part. The BMPs identified in the SWPPP and in this permit must be selected, installed, and maintained in an appropriate and functional manner that is in accordance with relevant manufacturer specifications and accepted engineering practices.
The Permittee(s) shall complete stabilization of the remaining portions of any temporary or permanent ditches or swales within 14 calendar days after connecting to a surface water or property edge and construction in that portion of the ditch has temporarily or permanently ceased.
Temporary or permanent ditches or swales that are being used as a sediment containment system during construction (with properly designed rock‐ditch checks, bio rolls, silt dikes, etc.) do not need to be stabilized during the temporary period of its use as a sediment containment system. These areas must be stabilized within 24 hours after no longer being used as a sediment containment system.
Applying mulch, hydromulch, tackifier, polyacrylamide or similar erosion prevention practices is not acceptable stabilization in any part of a temporary or permanent drainage ditch or swale.
a. Temporary or permanent drainage ditches and sediment basins that are designed as part of a sediment containment system (e.g., ditches with rock‐check dams) require sediment control practices only as appropriate for site conditions.
b. If the down gradient sediment controls are overloaded (based on frequent failure or excessive maintenance requirement), the Permittee(s) must install additional upgradient sediment control practices or redundant BMPs to eliminate the overloading, and the SWPPP must be amended to identify these additional practices as required in Part III.B 1.‐3.
a. The Permittee(s) must install a vehicle tracking BMP to minimize the track out of sediment from the construction site. Examples of vehicle tracking BMPs include (but are not limited to) rock pads, mud mats, slash mulch, concrete or steel wash racks, or equivalent systems.
b. The Permittee(s) must use street sweeping if such vehicle tracking BMPs are not adequate to prevent sediment from being tracked onto the street (see Part IV.E.5.d.).
a. The Permittee(s) must use conventional erosion and sediment controls prior to chemical addition to ensure effective treatment. Chemicals may only be applied where treated stormwater is directed to a sediment control system which allows for filtration or settlement of the floc prior to discharge.
b. Chemicals must be selected that are appropriately suited to the types of soils likely to be exposed during construction, and to the expected turbidity, pH, and flow rate of stormwater flowing into the chemical treatment system or area.
c. Chemicals must be used in accordance with accepted engineering practices, and with dosing specifications and sediment removal design specifications provided by the manufacturer or provider/supplier of the applicable chemicals.
a. Date and time of inspections
b. Name of person(s) conducting inspections
c. Findings of inspections, including the specific location where corrective actions are needed
d. Corrective actions taken (including dates, times, and party completing maintenance activities)
e. Date and amount of all rainfall events greater than 1/2 inch (0.5 inches) in 24 hours. Rainfall amounts must be obtained by a properly maintained rain gauge installed onsite, a weather station that is within 1 mile of your location or a weather reporting system that provides site specific rainfall data from radar summaries.
f. If any discharge is observed to be occurring during the inspection, a record of all points of the property from which there is a discha rge must be made, and the discharge should be described (i.e., color, odor, floating, settled, or suspended solids, foam, oil sheen, and other obvious indicators of pollutants) and photographed.
g. Any amendments to the SWPPP proposed as a result of the inspection must be documented as required in Part III.B. within seven (7) calendar days.
a. Where parts of the project site have permanent cover, but work remains on other parts of the site, the Permittee(s) may reduce inspections of the areas with permanent cover to once per month.
b. Where construction sites have permanent cover on all exposed soil areas and no construction activity is occurring anywhere on the site, the site must be inspected during non‐frozen ground conditions at least once per month for a period of twelve (12) months. Following the twelfth month of permanent cover and no construction activity, inspections may be terminated until construction activity is once again initiated unless the Permittee(s) is/are notified in writing by the MPCA that erosion issues have been detected at the site and inspections need to resume.
c. Where work has been suspended due to frozen ground conditions, the inspections may be suspended. The required inspections and maintenance schedule must begin within 24 hours after runoff occurs at the site or 24 hours prior to resuming construction, whichever comes first.
a. All perimeter control devices must be repaired, replaced, or supplemented when they become nonfunctional or the sediment reaches one‐half (1/2) of the height of the device. These repairs must be made by the end of the next business day after discovery, or thereafter as soon as field conditions allow access.
b. Temporary and permanent sedimentation basins must be drained and the sediment removed when the depth of sediment collected in the basin reaches one‐half (1/2) the storage volume. Drainage and removal must be completed within 72 hours of discovery, or as soon as field conditions allow access (see Part IV.D.).
c. Surface waters, including drainage ditches and conveyance systems, must be inspected for evidence of erosion and sediment deposition during each inspection. The Permittee(s) must remove all deltas and sediment deposited in surface waters, including drainage ways, catch basins, and other drainage systems, and restabilize the areas where sediment removal results in exposed soil. The removal and stabilization must take place within seven (7) days of discovery unless precluded by legal, regulatory, or physical access constraints. The Permittee(s) shall use all reasonable efforts to obtain access. If precluded, removal and stabilization must take place within seven (7) calendar days of obtaining access. The Permittee(s) is/are responsible for contacting all local, regional, state and federal authorities and receiving any applicable permits, prior to conducting any work in surface waters.
d. Construction site vehicle exit locations must be inspected for evidence of off‐site sediment tracking onto paved surfaces. Tracked sediment must be removed from all paved surfaces both on and off site within 24 hours of discovery, or if applicable, within a shorter time to comply with Part IV.C.6.
e. Streets and other areas adjacent to the project must be inspected for evidence of off‐site accumulations of sediment. If sediment is present, it must be removed in a manner and at a frequency sufficient to minimize off‐site impacts (e.g., fugitive sediment in streets could be washed into storm sewers by the next rain and/or pose a safety hazard to users of public streets).
The Permittee(s) shall implement the following pollution prevention management measures on the site:
a. Building products that have the potential to leach pollutants must be under cover (e.g., plastic sheeting or temporary roofs) to prevent the discharge of pollutants or protected by a similarly effective means designed to minimize contact with stormwater.
b. Pesticides, herbicides, insecticides, fertilizers, treatment chemicals, and landscape materials must be under cover (e.g., plastic sheeting or temporary roofs) to prevent the discharge of pollutants or protected by similarly effective means designed to minimize contact with stormwater.
c. Hazardous materials, toxic waste, (including oil, diesel fuel, gasoline, hydraulic fluids, paint solvents, petroleum‐based products, wood preservatives, additives, curing compounds, and acids) must be properly stored in sealed containers to prevent spills, leaks or other discharge. Restricted access storage areas must be provided to prevent vandalism. Storage and disposal of hazardous waste or hazardous materials must be in compliance with Minn. R. ch. 7045 including secondary containment as applicable.
d. Solid waste must be stored, collected and disposed of properly in compliance with Minn. R. ch. 7035.
e. Portable toilets must be positioned so that they are secure and will not be tipped or knocked over. Sanitary waste must be disposed of properly in accordance with Minn. R. ch. 7041.
The Permittee(s) must ensure Final Stabilization of the site. Final Stabilization is not complete until all requirements of Parts IV.G.1‐5. are complete:
This permit prohibits discharges of any material other than stormwater treated in compliance with this permit and discharges from dewatering or basin draining activities in accordance with Part IV.D.1.‐2. Prohibited discharges include (but are not limited to) wastewater from washout of concrete, stucco, paint, form release oils, curing compounds and other construction materials, fuels, oils, or other pollutants used in vehicle and equipment operation and maintenance, soaps or solvents used in vehicle and equipment washing and maintenance, and other hazardous substances or wastes.
This permit may not be assigned or transferred by the Permittee(s) except when transfer occurs in accordance with the applicable requirements of Part II.B.5.
Nothing in this permit must be construed to relieve the Permittee(s) from civil or criminal penalties for noncompliance with the terms and conditions provided herein. Nothing in this permit must be construed to preclude the initiation of any legal action or relieve the Permittee(s) from any responsibilities, liabilities, or penalties to which the Permittee(s) is/are or may be subject to under Section 311 of the Clean Water Act and Minn. Stat. § 115 and 116, as amended. The Permittee(s) is/are not liable for permit requirements for activities occurring on those portions of a site where the permit has been transferred to another party as required in Part II.B.5. or the Permittee(s) has/have submitted the NOT as required in Part II.C.
The provisions of this permit are severable. If any provision of this permit, or the application of any provision of this permit to any circumstances, is held invalid, the application of such provision to other circumstances, and the remainder of this permit must not be affected thereby.
The Permittee(s) must comply with the provisions of Minn. R. 7001.0150, subp. 3 and Minn. R. 7001.1090, subp. 1(A), 1(B), 1(C), 1(H), 1(I), 1(J), 1(K), and 1(L).
The Permittee(s) must allow access as provided in 40 CFR 122.41(i) and Minn. Stat. § 115.04. The Permittee(s) shall allow representatives of the MPCA or any member, employee or agent thereof, when authorized by it, upon presentation of credentials, to enter upon any property, public or private, for the purpose of obtaining information or examination of records or conducting surveys or investigations.
All requirements in this Appendix are in addition to BMPs already specified in the permit. Where provisions of Appendix A, conflict with requirements elsewhere in the permit, the provisions in Appendix A take precedence. All BMPs used to comply with this Appendix must be documented in the SWPPP for the project. If the terms and conditions of this Appendix cannot be met, an individual permit will be required in accordance with Minn. R. ch. 7001.
Additional BMPs and enhanced runoff controls identified in this Part are required for discharges to the following special waters (Part B.1 through B.9 of Appendix A) and impaired waters (Part B.10 of Appendix A). The BMPs identified for each special or impaired water are required for those areas of the project draining to a discharge point on the project that is within one mile (aerial radius measurement) of a special or impaired water and flows to that special or impaired water.
a. Impaired Water Without an Approved TMDL or With an Approved TMDL and No Waste Load Allocation:
If runoff from the site discharges to an impaired water, and a TMDL has not been approved by USEPA or there is a USEPA approved TMDL that does not establish a Waste Load Allocation (WLA) for construction stormwater, discharges to these waters must incorporate the BMPs outlined in C.1 and C.2 of this Appendix.
b. Impaired Water With an Approved TMDL and WLA:
If runoff from the site discharges to an impaired water for which there is a USEPA approved TMDL that establishes a WLA for construction stormwater, and the TMDL does not identify any specific implementation activities that would apply to the site discharges, discharges to these waters must incorporate the BMPs outlined in C.1 and C.2 of this Appendix.
If the TMDL identifies specific implementation activities regarding construction stormwater that would apply to the site discharges, the Permittee(s) must include the following in the SWPPP:
i. Identify the receiving water, the areas of the site discharging to it, and the pollutant(s) identified in the TMDL and
ii. BMPs identified in the TMDL and any other specific construction stormwater related implementation activities identified in the TMDL.
Note on impaired waters listing terminology: The terms in parenthesis in Appendix A Part B.10 above are the most current terminology used to list waters as impaired at the time of permit issuance. These terms are subject to change. For example, at one time waters were listed as impaired for phosphorus and now those same waters are listed as impaired for nutrient eutrophication biological indicators. If the terminology changes for one of the pollutant(s) or stressor(s) identified in the permit, the MPCA will keep a list of the new terms on its construction stormwater website.
If the project has any discharges with the potential for significant adverse impacts to a wetland, (e.g., conversion of a natural wetland to a stormwater pond) the Permittee(s) must demonstrate that the wetland mitigative sequence has been followed in accordance with D.1 or D.2 of this Appendix.
a. Avoid all significant adverse impacts to wetlands from the project and post-project discharge.
b. Minimize any unavoidable impacts from the project and post-project discharge.
c. Provide compensatory mitigation when the Permittee determines that there is no reasonable and practicable alternative to having a significant adverse impact on a wetland. For compensatory mitigation, wetland restoration or creation shall be of the same type, size and whenever reasonable and practicable in the same watershed as the impacted wetland.
This permit does not replace or satisfy any environmental review requirements, including those under the Minnesota Environmental Policy Act or the National Environmental Policy Act. The owner must verify that any environmental review required by law, including any required Environmental Assessment Work sheets or Environmental Impact Statements, Federal environmental review, or other required review is complete before making application for coverage under this permit, and the owner must incorporate any stormwater mitigation measures required as the result of any environmental review into the SWPPP for the project. If any part of your common plan of development or sale requires environmental review, coverage under this permit cannot be obtained until such environmental review is complete.
This permit does not replace or satisfy any review requirements for endangered or threatened species, from new or expanded discharges that adversely impact or contribute to adverse impacts on a listed endangered or threatened species, or adversely modify a designated critical habitat. The owner must conduct any required review and coordinate with appropriate agencies for any project with the potential of affecting threatened or endangered species, or their critical habitat.
This permit does not replace or satisfy any review requirements for historic places or archeological sites, from new or expanded discharges that adversely affect properties listed or eligible for listing in the National Register of Historic Places or affecting known or discovered archeological sites. The owner must be in compliance with National Historic Preservation Act and conduct all required review and coordination related to historic preservation, including significant anthropological sites and any burial sites, with the Minnesota Historic Preservation Officer.
a. A predominance of hydric soils
b. Inundated or saturated by surface water or groundwater at a frequency and duration sufficient to support a prevalence of hydrophytic vegetation typically adapted for life in a saturated soil condition and
c. Under normal circumstances support a prevalence of such vegetation.