Assessment Comments
Assessment is based on results of water quality, aquatic vegetation, and fish monitoring conducted by the IDNR shallow lakes and wetlands monitoring program from 2008 through 2010 and information from the IDNR Wildlife Bureau.
Basis for Assessment
SUMMARY: The Class B(LW) aquatic life uses are assessed (monitored) 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 at this wetland also suggest impairment due to aesthetically objectionable conditions. The fish consumption uses remain "not assessed" due to the lack of water quality information upon which to base an assessment. Sources of data for this assessment include results of water quality, aquatic vegetation, and fish monitoring conducted by the IDNR shallow lakes and wetlands monitoring program from 2008 through 2010 and information from the IDNR Wildlife Bureau. This is the same assessment as 2012 assessment/listing cycle as no new data were collected between 2010 and 2012.
EXPLANATION: Results of water quality monitoring conducted at South Twin Lake indicate that the aquatic life uses should be assessed (monitored) as "not supported" due to high levels of total suspended solids and algae at this lake. 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.
Using the overall median values from the IDNR shallow lakes and wetlands monitoring program from 2008 through 2010 (approximately 17 samples), the median growing season total suspended solids concentration was 40 mg/L; this median value exceeds the UMRCC guideline. Thus, based on (1) suppression of SAV growth, (2) the resultant production of undesirable aquatic life, and (3) IDNR’s assessment and listing methodology, the aquatic life uses at South Twin Lake are assessed as “not supported” due to high levels of total suspended solids.
In addition, the level of algae also suggests impairment of the aquatic life uses at South Twin Lake. The Carlson’s (1977) trophic state index value for chlorophyll a was 71. According to Carlson (1977), the index value for chlorophyll a places South Twin Lake in the hypereutrophic category and suggests extremely high levels of chlorophyll a and suspended algae in the water.
NOTE: The TSI value for Secchi depth is not used to evaluate the attainment of aquatic life goals 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 instance, 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.
Additional monitoring of fish and aquatic vegetation populations at South Twin Lake by IDNR staff also suggests that the high levels of total suspended solids and algae have adverse effects on fish populations and limit the production of rooted aquatic vegetation in this wetland. These results further indicate that the aquatic life uses of this wetland should be assessed as "not supported."
According to the local DNR Wildlife Biologist (Mahn), siltation at South Twin Lake is a problem but probably not a serious one because (1) the wetland has a rather small watershed and (2) most of the contributing watershed comes from the outlet of North Twin Lake and contains relatively little silt. The majority of the land immediately surrounding South Twin Lake, however, is intensively farmed and thus contributes to a siltation problem. Some progress has been made on the north side of the lake on private property with the establishment of grass that reduces silt. DNR has purchased a small tract on the southwest side of the lake that includes a small wetland and some adjacent uplands which have been seeded to native grasses. The primary water quality problems at South Twin Lake are increased turbidity, reduced light penetration, suppressed aquatic vegetation, and an accelerated eutrophication of this wetland. A large populations of common carp population exists in the wetland and no doubt plays a significant role in the turbidity problem and the suppression of rooted aquatic vegetation.
Fish consumption uses remain "not assessed." In general, Iowa wetlands are not managed for recreational fisheries; thus, fish contaminant monitoring is not typically conducted at these waterbodies.
