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− | <span title="the amount of a pollutant from both point and nonpoint sources that a waterbody can receive and still meet water quality standards"> [https://stormwater.pca.state.mn.us/index.php?title=Total_Maximum_Daily_Loads_(TMDLs) '''Total Maximum Daily Load''']</span> (TMDL) <span title="the portion of a receiving water's assimilative capacity that is allocated to one of its existing or future point sources of pollution"> '''Wasteload Allocations'''</span> (WLAs) approved by the U.S. Environmental Protection Agency (EPA) prior to the | + | |
+ | <span title="the amount of a pollutant from both point and nonpoint sources that a waterbody can receive and still meet water quality standards"> [https://stormwater.pca.state.mn.us/index.php?title=Total_Maximum_Daily_Loads_(TMDLs) '''Total Maximum Daily Load''']</span> (TMDL) <span title="the portion of a receiving water's assimilative capacity that is allocated to one of its existing or future point sources of pollution"> '''Wasteload Allocations'''</span> (WLAs) approved by the U.S. Environmental Protection Agency (EPA) prior to the November 16, 2020 issuance date of the <span title="A municipal separate storm sewer system (MS4) is a means of transportation, individually or in a system, (e.g. roads with drainage systems, municipal streets, catch basins, curbs, gutters, ditches, man-made channels, storm drains, etc.) that are: owned or operated by a public entity (e.g. cities, townships, counties, military bases, hospitals, prison complexes, highway departments, universities, etc.) with jurisdiction over disposal of sewage, industrial wastes, stormwater, or other wastes. This includes special districts under State law (sewer, flood control, or drainage districts, etc.), an authorized Indian tribal organization, or a designated and approved management agency under section 208 of the Clean Water Act; designed or used for collecting or transporting stormwater; not a combined sewer; and not part of a publicly owned treatment works."> [https://www.pca.state.mn.us/water/2020-ms4-general-permit '''MS4'''</span> (Municipal Separate Storm Sewer System) General Permit (permit)] must be addressed by permittees in their Stormwater Pollution Prevention Program (SWPPP) Document, which includes the [https://stormwater.pca.state.mn.us/index.php?title=2020_MS4_General_Permit_TMDL_Application TMDL Application Form]. The [https://www.epa.gov/laws-regulations/summary-clean-water-act Clean Water Act] requires the Minnesota Pollution Control Agency (MPCA) to include, in all <span title="The National Pollutant Discharge Elimination System (NPDES) addresses water pollution by regulating point sources that discharge pollutants to Waters of the United States (WOTUS)"> '''National Pollutant Discharge Elimination System'''</span> (NPDES) permits, discharge requirements that are consistent with requirements established in TMDLs. The permit requires applicants to submit information at the time of application on applicable WLAs and document how they will make progress on performance-based WLAs ([https://stormwater.pca.state.mn.us/index.php?title=Bacteria_in_stormwater bacteria], chloride, temperature), demonstrate they are currently meeting their numerical WLAs (oxygen demand, nitrate, [https://stormwater.pca.state.mn.us/index.php?title=Phosphorus total phosphorus] or [https://stormwater.pca.state.mn.us/index.php?title=Total_Suspended_Solids_(TSS)_in_stormwater total suspended solids]), or develop a compliance schedule for those numerical WLAs that are not being met. | ||
==Understanding Wasteload Allocations== | ==Understanding Wasteload Allocations== | ||
− | Wasteload allocations are allowable loads from regulated or future regulated sources in TMDLs. They are expressed as a load (i.e. pounds per day, kilograms per year, etc.) in TMDLs. They may also be expressed as a percent reduction in pollutant loading from existing conditions. The MPCA’s Stormwater Program believes the percent reduction, when provided in the TMDL report, is a useful expression of the information for implementation and planning because it provides an estimate on the magnitude of pollutant loading reduction needed for regulated entities to meet their assigned WLA(s) from the baseline year. | + | Wasteload allocations are allowable loads from regulated or future regulated sources in TMDLs. They are expressed as a load (i.e. pounds per day, kilograms per year, etc.) in TMDLs. They may also be expressed as a percent reduction in pollutant loading from existing conditions. The MPCA’s Stormwater Program believes the percent reduction, when provided in the TMDL report, is a useful expression of the information for implementation and planning because it provides an estimate on the magnitude of pollutant loading reduction needed for regulated entities to meet their assigned WLA(s) from the <span title="the year from which stormwater practices can be credited toward meeting a total maximum daily load (TMDL) wasteload allocation (WLA)"> '''[https://stormwater.pca.state.mn.us/index.php?title=Baseline_year baseline year]'''</span>. |
− | WLAs for MS4 sources are either individual or categorical. Individual WLAs provide a single load for each Permittee, whereas categorical WLAs group multiple Permittees into one load that collectively must be achieved by all contributing sources. Regardless of the type of WLA, the information required to be submitted at the time of application is the same. | + | WLAs for MS4 sources are either individual or [https://stormwater.pca.state.mn.us/index.php?title=Guidance_for_categorical_TMDLs categorical]. Individual WLAs provide a single load for each Permittee, whereas categorical WLAs group multiple Permittees into one load that collectively must be achieved by all contributing sources. Regardless of the type of WLA, the information required to be submitted at the time of application is the same. |
It is important to note watershed boundaries define TMDL study areas, while MS4 permits apply to a political boundary or jurisdiction. Further, WLAs apply only to the area that drains to the receiving water defined in the TMDL report. Therefore, it is possible that only a portion of a regulated entity’s area will be within the TMDL study area. Credit for pollutant removal from <span title="one of many different structural or non–structural methods used to treat runoff"> '''best management practices'''</span> (BMPs) can only be applied to the treatment applied to stormwater runoff generated within the TMDL study area for a particular WLA; however, BMPs often treat water generated both inside and outside the study area. | It is important to note watershed boundaries define TMDL study areas, while MS4 permits apply to a political boundary or jurisdiction. Further, WLAs apply only to the area that drains to the receiving water defined in the TMDL report. Therefore, it is possible that only a portion of a regulated entity’s area will be within the TMDL study area. Credit for pollutant removal from <span title="one of many different structural or non–structural methods used to treat runoff"> '''best management practices'''</span> (BMPs) can only be applied to the treatment applied to stormwater runoff generated within the TMDL study area for a particular WLA; however, BMPs often treat water generated both inside and outside the study area. | ||
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# in an EPA-approved TMDL, | # in an EPA-approved TMDL, | ||
# requiring more than a zero percent reduction, and | # requiring more than a zero percent reduction, and | ||
− | # for a waterbody that is listed as impaired on the Minnesota's 303(d) Impaired Waters List. | + | # for a waterbody that is listed as <span title="Impaired waters are bodies of water that exceed the limits of one or more parameters for surface water quality"> [https://stormwater.pca.state.mn.us/index.php?title=Special_Waters_and_Impaired_Waters '''impaired''']</span> on the Minnesota's 303(d) Impaired Waters List. |
− | The permit conditions apply only to those TMDLs approved prior to the | + | The permit conditions apply only to those TMDLs approved prior to the November 16, 2020 issuance date of the General Permit and are the only WLAs that must be addressed in the SWPPP Document. MPCA created the '''[https://www.pca.state.mn.us/sites/default/files/wq-strm4-93b.xlsx 2020 Municipal stormwater permit TMDL WLAs list]''' which is a spreadsheet that contains WLA information for all TMDLs approved prior to the effective date of the General Permit. Each line on the spreadsheet represents a different WLA. This spreadsheet also has a tab which lists the TMDL project webpage for each WLA. The information found on the TMDL project webpages and linked reports can provide helpful information to MS4s. |
− | In addition to the 2020 Municipal stormwater permit TMDL WLAs list, the MPCA created custom TMDL Application forms for each permittee, which need to be completed in order to comply with MS4 general permit. | + | In addition to the 2020 Municipal stormwater permit TMDL WLAs list, the MPCA created custom TMDL Application forms for each permittee, which need to be completed in order to comply with MS4 general permit. The link to the [[2020 MS4 General Permit TMDL Application]] forms is found here. Guidance for completing the forms is located [https://stormwater.pca.state.mn.us/index.php?title=Guidance_for_completing_the_MS4_Permit_TMDL_Application_Form here]. |
==Stormwater Pollution Prevention Program (SWPPP) development== | ==Stormwater Pollution Prevention Program (SWPPP) development== | ||
− | For each applicable WLA where a reduction in pollutant loading is required for bacteria, | + | Public entities that own or operate an MS4 are required to develop and implement a stormwater pollution prevention program (SWPPP) to reduce the discharge of pollutants from their storm sewer system, to the maximum extent practicable. The regulated entity must also identify best management practices (BMPs) they will implement to reduce pollution from reaching impaired waters covered by a total maximum daily load (TMDL) study. The following has been updated to reflect the TMDL related SWPPP requirements for the 2020 permit. |
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+ | '''Bacteria''': For each applicable WLA where a reduction in pollutant loading is required for bacteria, | ||
*the permittee must maintain a written or mapped inventory of potential source areas for bacteria, | *the permittee must maintain a written or mapped inventory of potential source areas for bacteria, | ||
*maintain a written plan to prioritize reduction activities that address the inventoried sources and areas, and | *maintain a written plan to prioritize reduction activities that address the inventoried sources and areas, and | ||
*identify who is responsible for implementing those items. | *identify who is responsible for implementing those items. | ||
− | The MPCA and partners have [https://stormwater.pca.state.mn.us/index.php?title=Checklist_for_bacteria_source_inventory developed a form] that can be used to fulfill this requirement. Permittees are not required to use it, but they must have a method to inventory and prioritize reduction activities. | + | The MPCA and partners have [https://stormwater.pca.state.mn.us/index.php?title=Checklist_for_bacteria_source_inventory developed a form] that can be used to fulfill this requirement. Permittees are not required to use it, but they must have a method to inventory and prioritize reduction activities. Guidance for meeting bacteria requirements [https://stormwater.pca.state.mn.us/index.php?title=Guidance_for_meeting_bacteria_TMDL_MS4_permit_requirements is located here]. |
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+ | '''Chloride''': If the permittee has an applicable waste load allocation (WLA) where a reduction in pollutant loading is required for chloride, | ||
+ | *they must document the amount of deicer applied each winter maintenance season to all permittee owned/operated surfaces, and | ||
+ | *conduct an assessment of the permittee's winter maintenance operations to reduce the amount of deicing salt applied to permittee owned/operated surfaces and determine current and future opportunities to improve BMPs. | ||
+ | The permittee may use the Agency's [https://smartsaltingtool.com/ Smart Salting Assessment Tool] or other available resources and methods to complete this assessment. The permittee must document the assessment. Guidance for meeting chloride requirements [https://stormwater.pca.state.mn.us/index.php?title=Guidance_for_meeting_chloride_TMDL_MS4_permit_requirements is located here]. | ||
− | If the permittee has an applicable waste load allocation (WLA) where a reduction in pollutant loading is required for temperature | + | '''Temperature''': If the permittee has an applicable waste load allocation (WLA) where a reduction in pollutant loading is required for temperature, |
− | * | + | *they must maintain a written plan that identifies specific activities that will be implemented to reduce thermal loading during the permit term; and |
− | * | + | *identify who will be responsible for implementing those activities. |
+ | Guidance for meeting temperature requirements [https://stormwater.pca.state.mn.us/index.php?title=Guidance_for_meeting_temperature_TMDL_MS4_permit_requirements is located here]. | ||
− | + | '''Oxygen demand, nitrate, TSS, TP''': If the applicant is claiming to meet an applicable WLA where a reduction in pollutant loading is required for [https://stormwater.pca.state.mn.us/index.php?title=Guidance_for_meeting_dissolved_oxygen_or_oxygen_demand_TMDL_MS4_permit_requirements oxygen demand], nitrate, TSS, or TP, the applicant must provide documentation to demonstrate the applicable WLA is being met. At a minimum, the applicant must provide the following information: | |
− | If the applicant is claiming to meet an applicable WLA where a reduction in pollutant loading is required for oxygen demand, nitrate, TSS, or TP, the applicant must provide documentation to demonstrate the applicable WLA is being met. At a minimum, the applicant must provide the following information: | ||
*a list of all structural stormwater BMPs implemented to achieve the applicable WLA, including the BMP type (e.g., constructed basin, infiltrator, filter, swale or strip, etc.), location in geographic coordinates, owner, and year implemented; and | *a list of all structural stormwater BMPs implemented to achieve the applicable WLA, including the BMP type (e.g., constructed basin, infiltrator, filter, swale or strip, etc.), location in geographic coordinates, owner, and year implemented; and | ||
*documentation using an Agency-approved method, which demonstrates the estimated reductions of oxygen demand (or its surrogate pollutants), nitrate, TSS, or TP from BMPs meet the MS4 WLA reductions included in the TMDL report, if that information is available (e.g., percent reduction or pounds reduced); or | *documentation using an Agency-approved method, which demonstrates the estimated reductions of oxygen demand (or its surrogate pollutants), nitrate, TSS, or TP from BMPs meet the MS4 WLA reductions included in the TMDL report, if that information is available (e.g., percent reduction or pounds reduced); or | ||
*documentation using an Agency-approved method, which demonstrates the applicant's existing load meets the WLA. | *documentation using an Agency-approved method, which demonstrates the applicant's existing load meets the WLA. | ||
− | This requirement is met by completing the TMDL application form. | + | This requirement is met by completing the TMDL application form. Guidance for completing the TMDL application form is [https://stormwater.pca.state.mn.us/index.php?title=Guidance_for_completing_the_MS4_Permit_TMDL_Application_Form here]. |
==Compliance schedules== | ==Compliance schedules== | ||
− | For each applicable WLA not met for oxygen demand, nitrate, total suspended solids (TSS), and total phosphorus (TP), at the time of application, a compliance schedule is required. Compliance schedules can be developed to include multiple WLAs and shall include | + | For each applicable WLA not met for oxygen demand, nitrate, [https://stormwater.pca.state.mn.us/index.php?title=Total_Suspended_Solids_(TSS)_in_stormwater total suspended solids] (TSS), and [https://stormwater.pca.state.mn.us/index.php?title=Phosphorus total phosphorus] (TP), at the time of application, a compliance schedule is required. Compliance schedules can be developed to include multiple WLAs and shall include |
− | *proposed BMPs or progress toward implementation of BMPs to be achieved during the permit term | + | *proposed BMPs or progress toward implementation of BMPs to be achieved during the permit term, |
− | *the year each BMP is expected to be implemented | + | *the year each BMP is expected to be implemented, |
− | *a target year the applicable WLA(s) will be achieved | + | *a target year the applicable WLA(s) will be achieved, and |
*if the applicant has an applicable WLA for TSS or TP, a cumulative estimate of TSS and TP load reductions (in pounds) to be achieved during the permit term and the Agency-approved method used to determine the estimate. | *if the applicant has an applicable WLA for TSS or TP, a cumulative estimate of TSS and TP load reductions (in pounds) to be achieved during the permit term and the Agency-approved method used to determine the estimate. | ||
This requirement is met by completing the TMDL application form. | This requirement is met by completing the TMDL application form. | ||
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*If a categorical WLA is expressed as a percent reduction, the reduction applies equally to all areas and MS4s included in the WLA. | *If a categorical WLA is expressed as a percent reduction, the reduction applies equally to all areas and MS4s included in the WLA. | ||
*If a categorical WLA is not expressed in terms of a percent reduction, the Permittee may determine their portion of the load based on their MS4’s land area in the TMDL study area. For example, if an MS4 constitutes 25 percent of the land area in a TMDL study area, the Permittee may be responsible for 25 percent of the categorical WLA. NOTE: Although it is not necessary for the applicant to identify an individual numeric load from a categorical WLA, it may be useful to consider during implementation planning and BMP selection. | *If a categorical WLA is not expressed in terms of a percent reduction, the Permittee may determine their portion of the load based on their MS4’s land area in the TMDL study area. For example, if an MS4 constitutes 25 percent of the land area in a TMDL study area, the Permittee may be responsible for 25 percent of the categorical WLA. NOTE: Although it is not necessary for the applicant to identify an individual numeric load from a categorical WLA, it may be useful to consider during implementation planning and BMP selection. | ||
− | *Are there opportunities to incorporate pollution prevention practices? | + | *Are there opportunities to incorporate [https://stormwater.pca.state.mn.us/index.php?title=Pollution_prevention pollution prevention practices]? |
*Are there upcoming projects planned and what pollutant reduction will these projects achieve? | *Are there upcoming projects planned and what pollutant reduction will these projects achieve? | ||
− | *Are there existing practices, both structural and non-structural, that may be modified or adapted to recognize additional pollutant removal? | + | *Are there existing practices, both [https://stormwater.pca.state.mn.us/index.php?title=Structural_stormwater_Best_Management_Practices structural] and [https://stormwater.pca.state.mn.us/index.php?title=Non-structural_stormwater_Best_Management_Practices non-structural], that may be modified or adapted to recognize additional pollutant removal? |
*Are there policy or ordinance updates that may provide a mechanism for the Permittee to require pollutant reductions from others (e. g. volume control ordinance)? | *Are there policy or ordinance updates that may provide a mechanism for the Permittee to require pollutant reductions from others (e. g. volume control ordinance)? | ||
*Are there opportunities to partner with other entities to achieve pollutant reductions to address WLAs? | *Are there opportunities to partner with other entities to achieve pollutant reductions to address WLAs? | ||
The applicant will include BMPs they plan to implement over the five-year permit term in the Compliance Schedule section of the TMDL Application form associated with the SWPPP Document. BMPs are often applicable to multiple WLAs and can reduce the contribution of multiple pollutants. For example, volume control practices are likely applicable to both nutrient and sediment WLAs. MPCA recommends selecting BMPs that address multiple WLAs when possible. | The applicant will include BMPs they plan to implement over the five-year permit term in the Compliance Schedule section of the TMDL Application form associated with the SWPPP Document. BMPs are often applicable to multiple WLAs and can reduce the contribution of multiple pollutants. For example, volume control practices are likely applicable to both nutrient and sediment WLAs. MPCA recommends selecting BMPs that address multiple WLAs when possible. | ||
− | It should be noted target dates that extend beyond the five-year permit term are expected for WLAs requiring a significant reduction in pollutant loading from an MS4. | + | It should be noted target dates that extend beyond the five-year permit term are expected for WLAs requiring a significant reduction in pollutant loading from an MS4. |
==Meeting Wasteload Allocations== | ==Meeting Wasteload Allocations== | ||
For permittees with best management practices in place, they may be meeting their applicable WLAs. This can be demonstrated through modeling exercises. Refer to [https://stormwater.pca.state.mn.us/index.php?title=Overview_of_models_used_to_meet_MS4_TMDL_permit_requirements Overview of models used to meet MS4 TMDL permit requirements] for more information. | For permittees with best management practices in place, they may be meeting their applicable WLAs. This can be demonstrated through modeling exercises. Refer to [https://stormwater.pca.state.mn.us/index.php?title=Overview_of_models_used_to_meet_MS4_TMDL_permit_requirements Overview of models used to meet MS4 TMDL permit requirements] for more information. | ||
+ | ==TMDL Annual Reporting Requirements for the 2020 permit== | ||
+ | Please see [[Guidance for completing the TMDL reporting form]]. | ||
− | + | [[Category:Level 3 - Regulatory/Municipal (MS4)/TMDLs]] | |
− |
Total Maximum Daily Load (TMDL) Wasteload Allocations (WLAs) approved by the U.S. Environmental Protection Agency (EPA) prior to the November 16, 2020 issuance date of the MS4 (Municipal Separate Storm Sewer System) General Permit (permit) must be addressed by permittees in their Stormwater Pollution Prevention Program (SWPPP) Document, which includes the TMDL Application Form. The Clean Water Act requires the Minnesota Pollution Control Agency (MPCA) to include, in all National Pollutant Discharge Elimination System (NPDES) permits, discharge requirements that are consistent with requirements established in TMDLs. The permit requires applicants to submit information at the time of application on applicable WLAs and document how they will make progress on performance-based WLAs (bacteria, chloride, temperature), demonstrate they are currently meeting their numerical WLAs (oxygen demand, nitrate, total phosphorus or total suspended solids), or develop a compliance schedule for those numerical WLAs that are not being met.
Wasteload allocations are allowable loads from regulated or future regulated sources in TMDLs. They are expressed as a load (i.e. pounds per day, kilograms per year, etc.) in TMDLs. They may also be expressed as a percent reduction in pollutant loading from existing conditions. The MPCA’s Stormwater Program believes the percent reduction, when provided in the TMDL report, is a useful expression of the information for implementation and planning because it provides an estimate on the magnitude of pollutant loading reduction needed for regulated entities to meet their assigned WLA(s) from the baseline year.
WLAs for MS4 sources are either individual or categorical. Individual WLAs provide a single load for each Permittee, whereas categorical WLAs group multiple Permittees into one load that collectively must be achieved by all contributing sources. Regardless of the type of WLA, the information required to be submitted at the time of application is the same.
It is important to note watershed boundaries define TMDL study areas, while MS4 permits apply to a political boundary or jurisdiction. Further, WLAs apply only to the area that drains to the receiving water defined in the TMDL report. Therefore, it is possible that only a portion of a regulated entity’s area will be within the TMDL study area. Credit for pollutant removal from best management practices (BMPs) can only be applied to the treatment applied to stormwater runoff generated within the TMDL study area for a particular WLA; however, BMPs often treat water generated both inside and outside the study area.
A single TMDL project may contain multiple wasteload allocations for a single MS4. This can occur in the following situations:
The term “applicable WLA” is used in the MS4 General Permit and is considered to be any wasteload allocation assigned to a regulated MS4 that is
The permit conditions apply only to those TMDLs approved prior to the November 16, 2020 issuance date of the General Permit and are the only WLAs that must be addressed in the SWPPP Document. MPCA created the 2020 Municipal stormwater permit TMDL WLAs list which is a spreadsheet that contains WLA information for all TMDLs approved prior to the effective date of the General Permit. Each line on the spreadsheet represents a different WLA. This spreadsheet also has a tab which lists the TMDL project webpage for each WLA. The information found on the TMDL project webpages and linked reports can provide helpful information to MS4s.
In addition to the 2020 Municipal stormwater permit TMDL WLAs list, the MPCA created custom TMDL Application forms for each permittee, which need to be completed in order to comply with MS4 general permit. The link to the 2020 MS4 General Permit TMDL Application forms is found here. Guidance for completing the forms is located here.
Public entities that own or operate an MS4 are required to develop and implement a stormwater pollution prevention program (SWPPP) to reduce the discharge of pollutants from their storm sewer system, to the maximum extent practicable. The regulated entity must also identify best management practices (BMPs) they will implement to reduce pollution from reaching impaired waters covered by a total maximum daily load (TMDL) study. The following has been updated to reflect the TMDL related SWPPP requirements for the 2020 permit.
Bacteria: For each applicable WLA where a reduction in pollutant loading is required for bacteria,
The MPCA and partners have developed a form that can be used to fulfill this requirement. Permittees are not required to use it, but they must have a method to inventory and prioritize reduction activities. Guidance for meeting bacteria requirements is located here.
Chloride: If the permittee has an applicable waste load allocation (WLA) where a reduction in pollutant loading is required for chloride,
The permittee may use the Agency's Smart Salting Assessment Tool or other available resources and methods to complete this assessment. The permittee must document the assessment. Guidance for meeting chloride requirements is located here.
Temperature: If the permittee has an applicable waste load allocation (WLA) where a reduction in pollutant loading is required for temperature,
Guidance for meeting temperature requirements is located here.
Oxygen demand, nitrate, TSS, TP: If the applicant is claiming to meet an applicable WLA where a reduction in pollutant loading is required for oxygen demand, nitrate, TSS, or TP, the applicant must provide documentation to demonstrate the applicable WLA is being met. At a minimum, the applicant must provide the following information:
This requirement is met by completing the TMDL application form. Guidance for completing the TMDL application form is here.
For each applicable WLA not met for oxygen demand, nitrate, total suspended solids (TSS), and total phosphorus (TP), at the time of application, a compliance schedule is required. Compliance schedules can be developed to include multiple WLAs and shall include
This requirement is met by completing the TMDL application form.
The compliance schedule must demonstrate that progress toward reducing pollutant loads will be achieved within the permit cycle. Per federal rule, dates and reporting on implementation of the interim milestones must be at least annual.
Reductions in pollutant loading are achieved by implementing Best Management Practices (BMPs). When selecting BMPs to include in a compliance schedule, the applicant should consider the following:
The applicant will include BMPs they plan to implement over the five-year permit term in the Compliance Schedule section of the TMDL Application form associated with the SWPPP Document. BMPs are often applicable to multiple WLAs and can reduce the contribution of multiple pollutants. For example, volume control practices are likely applicable to both nutrient and sediment WLAs. MPCA recommends selecting BMPs that address multiple WLAs when possible.
It should be noted target dates that extend beyond the five-year permit term are expected for WLAs requiring a significant reduction in pollutant loading from an MS4.
For permittees with best management practices in place, they may be meeting their applicable WLAs. This can be demonstrated through modeling exercises. Refer to Overview of models used to meet MS4 TMDL permit requirements for more information.
Please see Guidance for completing the TMDL reporting form.
This page was last edited on 5 January 2023, at 17:56.