Assessment Summary
The Class BLW use remains 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 shallow lake also suggested impairment due to aesthetically objectionable conditions. All other designated uses remain “not assessed.”
Assessment Explanation
Data Sources:
|
Data Source
|
Data Source ID
|
Data Type
|
Data Age
|
Site ID
|
Site
Name
|
Site
Description
|
|
Iowa DNR
|
6
|
WQ
|
CY 2018-2021
|
22130004
|
South
Twin Lake
|
|
Class BLW – Shallow Lake TSI:
|
Site ID
|
Data Source ID
|
Parameter Name
|
# Samples / # Years
|
Minimum Value
|
Maximum Value
|
Median Value
|
Median TSI Violation?
|
Assessment Type
|
Support Level
|
|
22130004
|
6
|
Chlorophyll a TSI
|
35 / 4
|
42
|
90
|
70
|
YES
|
MONITORED
|
NOT
|
The TSI value for Secchi depth is not used to evaluate the
attainment of the 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 BLW use, but the index value is limited by the
depth of the lake. Thus, the combination of total suspended solids and
chlorophyll a was used to determine whether or not the Class BLW use was
impaired in these shallow systems.
Class BLW - Binomial 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
|
|
22130004
|
6
|
Dissolved Oxygen
|
16 / 4
|
7.5
|
15.5
|
10.1
|
0
|
NA / NA
|
4
|
NO
|
MONITORED
|
FULL
|
|
22130004
|
6
|
pH
|
11 / 3
|
8.18
|
8.98
|
8.68
|
0
|
NA / NA
|
3
|
NO
|
MONITORED
|
FULL
|
|
22130004
|
6
|
Temperature
|
16 / 4
|
14.6
|
28.8
|
22.8
|
0
|
NA / NA
|
4
|
NO
|
MONITORED
|
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
|
|
22130004
|
6
|
Total suspended solids
|
33 / 4
|
23
|
470
|
66
|
YES
|
MONITORED
|
NOT
|
Guidelines for wetland assessment from the Upper Mississippi
River Conservation Committee’s Water Quality Technical Section (2003) state
that a median 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 (SAV) in wetlands and shallow lakes.
High levels of total suspended solids impede the growth of SAV. SAV 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 BLW - Toxic Parameters:
|
Site ID
|
Data Source ID
|
Parameter Name
|
# Samples / # Years
|
Maximum Value
|
Mean Value
|
Median Value
|
# Acute / Chronic Violations
|
>1 Acute / Chronic Violation
|
Assessment Type
|
Support Level
|
|
22130004
|
6
|
Ammonia
|
5 / 1
|
0.025
|
0.02
|
0.02
|
0 / 0
|
NO
|
EVALUATED
|
FULL
|
Class HH - No Data
Additional Notes:
Additional monitoring of fish and aquatic vegetation
populations at South Twin Lake by DNR 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.