Swan Lake IA 04-UDM-1232
Dickinson County S23T100NR35W 2 mi. N of Superior.
- Cycle
- 2022
- Release Status
- Final
- Overall IR
- 5 - Water is impaired or threatened and a TMDL is needed.
- Trend
- Stable
- Created
- 12/30/2021 9:00:13 AM
- Updated
- 2/17/2022 2:48:31 PM
The Class BLW use was assessed as "not supported" due to high levels of total suspended solids that leads to an impairment of the narrative criteria protecting against undesirable or nuisance aquatic life, high levels of algae that lead to impairment due to aesthetically objectionable conditions, and violations of the class BLW criteria for pH. All other designated uses were “not assessed.”
Data Sources: Data Source Data Source ID Data Type Data Age Site ID Site
Name Site
Description Iowa DNR 6 WQ CY 2016-2016 22300019 Little
Swan Lake
Iowa DNR 6 WQ CY 2019-2020 22300022 Swan
Lake Lake
Deep Point Class A1 - Indicator Bacteria: No Data Class A1 - pH Site ID Data Source ID # Samples / # Years Minimum Value Maximum Value Mean Value # Violations Violations needed for impairment Violates Significantly >10% Rule? Assessment Type Support Level 22300019 6 5 / 1 8.9 11.4 10 4 2 YES Evaluated Not 22300022 6 5 / 2 8.03 9.37 8.52 1 2 NO Evaluated Full Class A1 - Lake TSI's Site ID Data Source ID Parameter Name # Samples / # Years Minimum Value Maximum Value Median Value Median TSI Violation? Assessment Type Support Level 22300019 6 Chlorophyll a TSI 5 / 1 65 81 78 YES Evaluated Not 22300022 6 Chlorophyll a TSI 5 / 2 70 82 73 YES Evaluated Not 22300019 6 Total Phosphorus TSI 5 / 1 69 95 90 NA NA NA 22300022 6 Total Phosphorus TSI 5 / 2 63 95 84 NA NA NA 22300019 6 Inorganic suspended solids 5 / 1 13.8 49.5 31.6 NA NA NA The TSI value for Secchi depth is not used to evaluate the
attainment of aquatic life use in shallow lakes. Due to the depth of these
shallow lakes, TSI values for Secchi depth can be misleading. In some
instances, the Secchi disk remains visible at the bottom of the lake and the
depth of the lake is recorded as the Secchi depth. In these instances, water
clarity may be sufficient to support the Class B(LW) uses, but the index value
is limited by the depth of the lake. Thus the combination of total suspended
solids and chlorophyll a will be used to determine whether or not the Class
B(LW) uses are impaired in these shallow systems. Class BLW - Conventional Parameters: Site ID Data Source ID Parameter Name # Samples / # Years Minimum Value Maximum Value Mean Value # Violations # Acute / Chronic Violations Violations needed for impairment Violates Significantly >10% Rule? Assessment Type Support Level 22300019 6 Ammonia 5 / 1 0.025 0.242 0.09 NA 0 / 2 2 NO Evaluated Full 22300022 6 Ammonia 5 / 2 0.05 0.22 0.13 NA 0 / 0 2 NO Evaluated Full 22300019 6 Dissolved Oxygen 5 / 1 7.64 9.12 8.29 0 NA / NA 2 NO Evaluated Full 22300022 6 Dissolved Oxygen 5 / 2 9.68 16.21 12.04 0 NA / NA 2 NO Evaluated Full 22300019 6 pH 5 / 1 8.9 11.4 10 4 NA / NA 2 YES Evaluated Not 22300022 6 pH 5 / 2 8.03 9.37 8.52 1 NA / NA 2 NO Evaluated Full 22300019 6 Temperature 5 / 1 16.5 25.4 22.3 0 NA / NA 2 NO Evaluated Full 22300022 6 Temperature 5 / 2 12.5 32.4 21.2 1 NA / NA 2 NO Evaluated Full Class BLW - Protection of Submerged Aquatic Vegetation: Site ID Data Source ID Parameter Name # Samples / # Years Minimum Value Maximum Value Median Value Median Value = SAV Assessment Type Support Level 22300019 6 Total suspended solids 5 / 1 21.2 78.5 54 Yes Evaluated Not 22300022 6 Total suspended solids 5 / 2 26 290 51 Yes Evaluated Not Guidelines
for wetland assessment from the Upper Mississippi River Conservation
Committee’s Water Quality Technical Section (2003) state that an average total
suspended solids concentration during the growing season of less than 30 mg/L
is necessary to provide sufficient water clarity to support the growth of
submersed aquatic vegetation in wetlands and shallow lakes. High levels of
total suspended solids impede the growth of submersed aquatic vegetation (SAV).
Submersed aquatic vegetation is critical to the health of wetland and shallow
lake ecosystems. The elimination of SAV can degrade habitat quality such that
undesirable aquatic species such as cyanobacteria, common carp and fathead
minnows dominate. As such, the suppression of SAV constitutes a violation of
Iowa’s narrative water quality criteria protecting against undesirable or
nuisance aquatic life.
Class HH - No Data