Pickerel Lake IA 04-RAC-1180

Data Sources:

Class A1 - Indicator Bacteria: No Data

Class A1 - pH

Class A1 - Lake TSI's

• 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 A1 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 A1 and Class BLW uses are impaired in these shallow systems.
• DNR's assessment methodology indicates that at least two assessment/listing cycles with a TSI value less than or equal to 63 are necessary to suggest de-listing of an impairment. The chlorophyll a TSI value for the 2010 assessment listing cycle was 78, which based on DNR's assessment/listing methodology indicated an impairment based on the narrative criteria protecting against aesthetically objectionable conditions. Because the TSI value for the 2020 assessment/listing cycle was less than the trigger of 65 (2020 listing for chlorophyll a was 57), and because the TSI value for the current listing cycle is also 58, based on DNR's methodology, these values suggest "full support" of the Class A1 and Class BLW uses protecting against aesthetically objectionable conditions and the impairment (5a) for chlorophyll a is suggested for delisting for the 2022 assessment/listing cycle.

Class BLW - Conventional Parameters:

According to DNR's methodology, a river must meet water quality standards for two consecutive cycles to suggest de-listing.Therefore, Pickerel Lake will remain listed for the 2022 cycle as "not supported" its Class BLW uses due to dissolved oxygen.

Class BLW - Protection of Submerged Aquatic Vegetation:

• 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.
• DNR's assessment methodology indicates that at least two assessment/listing cycles with a median growing season total suspended solids concentration of 30 mg/L to suggest de-listing of the SAV impairment. The total suspended solids concentration for the 2010 assessment listing cycle was 45, which based on DNR's assessment/listing methodology indicated an impairment. Because the total suspended solids concentration for the 2020 assessment/listing cycle was less than the trigger of 30 (2020 listing for SAV was 12), and because the total suspended solids concentration for the current listing cycle is also 12, based on DNR's methodology, these values suggest "full support" of the Class A1 and Class BLW uses protecting against aesthetically objectionable conditions and the impairment (5a) for SAV is suggested for delisting for the 2022 assessment/listing cycle.

Class HH: No Data