ADBNet

Assessment Comments

Assessment is based on: (1) results of the statewide survey of Iowa lakes conducted from 2009-2012 by Iowa State University (ISU), (2) results of the statewide ambient lake monitoring program conducted in 2008 by University Hygienic Laboratory (UHL), and (3) information from the IDNR Fisheries Bureau.

Basis for Assessment

SUMMARY: The Class A1 (primary contact recreation) uses are assessed (monitored) as “fully supported.”  The Class B(LW) (aquatic life) uses are assessed (monitored) as “fully supported.”  Fish consumption uses are “not assessed” due to a lack of information to base an assessment on.   Sources of data for this assessment include (1) results of the statewide survey of Iowa lakes conducted from 2009-2012 by Iowa State University (ISU), (2) results of the statewide ambient lake monitoring program conducted in 2008 by University Hygienic Laboratory (UHL), and (3) information from the IDNR Fisheries Bureau.

EXPLANATION: Results from the ISU and UHL lake surveys also suggest that the Class A1 uses at Nelson Lake are “fully supported.”  Using the median values from these surveys from 2008-2012 (approximately 14 samples), Carlson’s (1977) trophic state indices for Secchi depth, chlorophyll a, and total phosphorus were 45, 47, and 56 respectively for Nelson Lake.   According to Carlson (1977) the Secchi depth and  chlorophyll a values place Nelson Lake in the mesotrophic category, while the total phosphorus values place Nelson Park Lake in the eutrophic category.   These values suggest extremely low levels of chlorophyll a and suspended algae in the water, exceptional water transparency, and relatively low levels of phosphorus in the water column.  

The level of inorganic suspended solids is relatively low at this lake and does not suggest impairment due to high non-algal turbidity.   The median inorganic suspended solids concentration at Nelson Lake was 2.5 mg/L, and ranked 39th of the 134 monitored lakes.

Data from the 2008-2012 ISU and UHL surveys suggest a small population of cyanobacteria exists at Nelson Lake, which does not suggest impairment at this lake.   These data show that cyanobacteria comprised only 19% of the phytoplankton wet mass at this lake.   The median cyanobacteria wet mass (1.4 mg/L) and ranked 2nd of the 134 lakes sampled.  

The Class B(LW) (aquatic life) uses are assessed as “fully supported” based on information from the IDNR Fisheries Bureau and results from the ISU and UHL lake surveys.   The ISU and UHL lake surveys show that during 2008-2012 there were no violations of the Class B(LW) criterion for ammonia in 14 samples.   There was one violation of the Class B(LW) criterion for dissolved oxygen in 14 samples (7%).   This violation is not significantly greater than 10% of the samples and therefore based on IDNR's assessment methodology does not suggest impairment of the Class B(LW) uses.   There were no violations of the Class A1,B(LW) criterion for pH in 14 samples.   These results suggest "full support" of the Class B(LW) uses at Nelson Park Lake.

Fish consumption uses remain "not assessed" due to the lack of fish contaminant monitoring in this lake.