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Since the stormwater program advocates an accounting process for achieving the WLA, with a percent reduction in loading being the target, it is important to define the baseline condition from which calculations will be made. The baseline must include a year but may include additional information, such as a summary of BMPs considered in deriving the WLA. Baseline year is the year from which stormwater practices can be credited toward meeting a <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 allocation'''</span> (WLA). That is, any <span title="one of many different structural or non–structural methods used to treat runoff"> '''best management practice'''</span> (BMPs) or activity implemented during or after the baseline year that results in a reduction in pollutant loads from a municipal separate storm sewer system (MS4) to the impaired waterbody can be considered as progress towards meeting the MS4 wasteload allocation (WLA). | Since the stormwater program advocates an accounting process for achieving the WLA, with a percent reduction in loading being the target, it is important to define the baseline condition from which calculations will be made. The baseline must include a year but may include additional information, such as a summary of BMPs considered in deriving the WLA. Baseline year is the year from which stormwater practices can be credited toward meeting a <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 allocation'''</span> (WLA). That is, any <span title="one of many different structural or non–structural methods used to treat runoff"> '''best management practice'''</span> (BMPs) or activity implemented during or after the baseline year that results in a reduction in pollutant loads from a municipal separate storm sewer system (MS4) to the impaired waterbody can be considered as progress towards meeting the MS4 wasteload allocation (WLA). | ||
− | Most TMDL reports, TMDL Implementation Plans, or Watershed Restoration and Protection Strategy (WRAPs) reports now provide a baseline year. Many earlier TMDL reports did not provide this information. For TMDLs developed with short-term monitoring data, such as two or three years, the baseline year will be one of those years. When long-term monitoring data is used it is difficult to determine the appropriate baseline year. TMDL authors, TMDL project managers, Stormwater Program staff, and stakeholders | + | Most TMDL reports, TMDL Implementation Plans, or Watershed Restoration and Protection Strategy (WRAPs) reports now provide a baseline year. Many earlier TMDL reports did not provide this information. For TMDLs developed with short-term monitoring data, such as two or three years, the baseline year will be one of those years. When long-term monitoring data is used it is difficult to determine the appropriate baseline year. TMDL authors, TMDL project managers, Stormwater Program staff, and stakeholders work together to determine an appropriate baseline year. |
Examples of baselines from TMDLs developed in Minnesota are provided below. In general, more recently-approved TMDLs provide clearer target loads and baselines. | Examples of baselines from TMDLs developed in Minnesota are provided below. In general, more recently-approved TMDLs provide clearer target loads and baselines. |
Since the stormwater program advocates an accounting process for achieving the WLA, with a percent reduction in loading being the target, it is important to define the baseline condition from which calculations will be made. The baseline must include a year but may include additional information, such as a summary of BMPs considered in deriving the WLA. Baseline year is the year from which stormwater practices can be credited toward meeting a total maximum daily load (TMDL) wasteload allocation (WLA). That is, any best management practice (BMPs) or activity implemented during or after the baseline year that results in a reduction in pollutant loads from a municipal separate storm sewer system (MS4) to the impaired waterbody can be considered as progress towards meeting the MS4 wasteload allocation (WLA).
Most TMDL reports, TMDL Implementation Plans, or Watershed Restoration and Protection Strategy (WRAPs) reports now provide a baseline year. Many earlier TMDL reports did not provide this information. For TMDLs developed with short-term monitoring data, such as two or three years, the baseline year will be one of those years. When long-term monitoring data is used it is difficult to determine the appropriate baseline year. TMDL authors, TMDL project managers, Stormwater Program staff, and stakeholders work together to determine an appropriate baseline year.
Examples of baselines from TMDLs developed in Minnesota are provided below. In general, more recently-approved TMDLs provide clearer target loads and baselines.
The List of Approved TMDLs with MS4 WLAs (updated November 2019) includes the baseline year identified in the TMDL, or the MPCA recommended baseline year. Please click here to download the baseline year guidance document: File:TMDLbaselinesMS4.xlsx