Assessment Summary
The Class A1 use was assessed as “not supported” due to levels of indicator bacteria that exceeded Iowa’s water quality standard and due to poor water transparency caused by algae blooms. The Class BLW use was assessed (evaluated) as “WINOFI” due to a fish kill. The Class HH (fish consumption) use was assessed as "fully supported" based on fish tissue sampling data.
Note: A TMDL for nutrients and siltation at Lake MacBride was prepared by DNR and approved by EPA in 2005. Because however, the Section 303(d) impairment due to indicator bacteria and DO violations at this lake were not addressed in the TMDL, this lake was placed in IR Category 5a (impaired; TMDL required).
Assessment Explanation
Data Sources:
|
Data Source
|
Data Source ID
|
Data Type
|
Data Age
|
Site ID
|
Site Name
|
Site Description
|
|
Iowa DNR
|
6
|
WQ
|
CY 2018-2018
|
14000212
|
McBride bac 1
|
|
|
Iowa DNR
|
6
|
WQ
|
CY 2018-2018
|
21520001
|
Lake Macbride Beach
(Lake Macbride State Park)
|
|
|
Iowa DNR
|
6
|
WQ
|
CY 2016-2020
|
22520001
|
Lake Macbride
(maximum water depth)
|
|
|
Iowa DNR
|
6
|
WQ
|
CY 2018-2018
|
22520006
|
Lake Macbride near
Cottage Grove
|
|
|
Iowa DNR
|
6
|
WQ
|
CY 2018-2018
|
22520007
|
Lake Macbride near
campground
|
|
|
Iowa DNR
|
6
|
WQ
|
CY 2018-2019
|
14000237
|
McBride N Arm
|
|
|
Iowa DNR
|
6
|
WQ
|
CY 2018-2019
|
14000238
|
McBride S Arm
|
|
|
Iowa DNR
|
6
|
FT
|
See Below
|
81
|
Lake Macbride
|
WSW of Solon
|
Class A1 - Indicator Bacteria:
|
Site ID
|
Data Source ID
|
# Samples per Year (2018/ 2019/2020)
|
2018 Geometric Mean
|
2019 Geometric Mean
|
2020 Geometric Mean
|
Violates Annual Geometric Mean?
|
# 2018 SSM violations / SSM Violations needed for impairment
|
# 2019 SSM violations / SSM Violations needed for impairment
|
# 2020 SSM violations / SSM Violations needed for impairment
|
Violates Annual SSM Significantly >10% Rule?
|
Assessment Type
|
Support Level
|
|
14000212
|
6
|
6/0/0
|
10
|
NA
|
NA
|
NO
|
0 / NA
|
NA
|
NA
|
NO
|
Evaluated
|
Full
|
|
21520001
|
6
|
15/15/13
|
263
|
20
|
35
|
YES
|
9 / 4
|
2 / 4
|
3 / 4
|
YES
|
Monitored
|
Not
|
|
22520001
|
6
|
9/3/3
|
3
|
5
|
5
|
NO
|
0 / 3
|
0 / NA
|
0 / NA
|
NO
|
Monitored
|
Full
|
|
22520006
|
6
|
6/0/0
|
7
|
NA
|
NA
|
NO
|
0 / NA
|
NA
|
NA
|
NO
|
Evaluated
|
Full
|
|
22520007
|
6
|
5/0/0
|
8
|
NA
|
NA
|
NO
|
0 / NA
|
NA
|
NA
|
NO
|
Evaluated
|
Full
|
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
|
|
14000237
|
6
|
26 / 2
|
7.7
|
9.2
|
8.7
|
4
|
6
|
NO
|
Monitored
|
Full
|
|
14000238
|
6
|
27 / 2
|
7.5
|
9.3
|
8.7
|
2
|
6
|
NO
|
Monitored
|
Full
|
|
22520001
|
6
|
47 / 5
|
7.3
|
9.2
|
8.5
|
3
|
8
|
NO
|
Monitored
|
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
|
|
22520001
|
6
|
Chlorophyll a TSI
|
45 / 5
|
24
|
80
|
62
|
NO
|
Monitored
|
Full
|
|
22520001
|
6
|
Secchi TSI
|
16 / 5
|
47
|
70
|
63
|
NO
|
Monitored
|
Full
|
|
22520001
|
6
|
Total Phosphorus TSI
|
45 / 5
|
49
|
88
|
63
|
NA
|
NA
|
NA
|
|
22520001
|
6
|
Fixed suspended solids
|
16 / 5
|
0.4
|
5
|
1
|
NA
|
NA
|
NA
|
Although the index value for Chlorophyll a is below the
impairment trigger of 65 for this assessment cycle, the Class A1 use of Lake Macbride was listed as "not supported"due to aesthetically objectionable
conditions. Based on DNR's methodology, the median TSI value for Chlorophyll a
must be 63 or less for two consecutive assessment/listing cycles before a lake can be removed from the state's Section 303(d) list (IR Category 5). Therefore,
Lake Macbride will remain listed as "not supported" for the 2022
assessment/listing cycle.
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
|
|
14000237
|
6
|
Ammonia
|
25 / 2
|
0.025
|
0.3
|
0.1
|
NA
|
0 / 0
|
5
|
NO
|
Monitored
|
Full
|
|
14000238
|
6
|
Ammonia
|
26 / 2
|
0.02
|
0.44
|
0.08
|
NA
|
0 / 0
|
6
|
NO
|
Monitored
|
Full
|
|
22520001
|
6
|
Ammonia
|
44 / 5
|
0.0003
|
0.85
|
0.08
|
NA
|
0 / 0
|
8
|
NO
|
Monitored
|
Full
|
|
14000237
|
6
|
Dissolved Oxygen
|
26 / 2
|
4.1
|
15.9
|
9.9
|
1
|
NA / NA
|
6
|
NO
|
Monitored
|
Full
|
|
14000238
|
6
|
Dissolved Oxygen
|
27 / 2
|
5.6
|
16.2
|
10.3
|
0
|
NA / NA
|
6
|
NO
|
Monitored
|
Full
|
|
22520001
|
6
|
Dissolved Oxygen
|
47 / 5
|
1.3
|
17.9
|
9.3
|
1
|
NA / NA
|
8
|
NO
|
Monitored
|
Full
|
|
14000237
|
6
|
pH
|
26 / 2
|
7.7
|
9.2
|
8.7
|
4
|
NA / NA
|
6
|
NO
|
Monitored
|
Full
|
|
14000238
|
6
|
pH
|
27 / 2
|
7.5
|
9.3
|
8.7
|
2
|
NA / NA
|
6
|
NO
|
Monitored
|
Full
|
|
22520001
|
6
|
pH
|
47 / 5
|
7.3
|
9.2
|
8.5
|
3
|
NA / NA
|
8
|
NO
|
Monitored
|
Full
|
|
14000237
|
6
|
Temperature
|
26 / 2
|
9.3
|
29.1
|
21.6
|
0
|
NA / NA
|
6
|
NO
|
Monitored
|
Full
|
|
14000238
|
6
|
Temperature
|
27 / 2
|
9.9
|
28.9
|
21.5
|
0
|
NA / NA
|
6
|
NO
|
Monitored
|
Full
|
|
22520001
|
6
|
Temperature
|
47 / 5
|
9.7
|
28.7
|
22.5
|
0
|
NA / NA
|
8
|
NO
|
Monitored
|
Full
|
Class BLW - Lake Planktonic Cyanobacteria:
|
Site ID
|
Data Source ID
|
# Samples
|
Maximum Cyanobacteria Wet Mass
|
Maximum Cyanobacteria % Composition
|
Median Cyanobacteria Wet Mass
|
Median Cyanobacteria % Composition
|
Median Cyanobacteria Concentration = 75th Percentile
|
Assessment Type
|
Support Level
|
|
22520001
|
6
|
6
|
707.76
|
93.1%
|
8.53
|
78.3%
|
NO
|
Evaluated
|
NA
|
Class BLW - Fish Kill:
The Class BLW uses are assessed (evaluated) as “WINOFI” due to a fish kill that on June 7, 2011. According to DNR's
assessment methodology, the occurrence of a single pollutant-caused fish kill,
or a fish kill of unknown origin, on a waterbody or waterbody reach during the most
recent assessment period indicates a severe stress to the aquatic community and
suggests that the aquatic life uses should be assessed as “impaired.” If a
cause of the kill was not identified during the DNR investigation, or if the
kill was attributed to non-pollutant causes (e.g., winterkill), the assessment
type will be considered “evaluated” and will be placed in IR subcategory 3b
and will be added to the state list of waters in need of further investigation
Class HH - Fish
Tissue Sampling:
|
Site ID
|
Biopart
|
Year
|
Species
|
# in sample / # of samples
|
Avg Length (cm)
|
(Avg) Hg (ppm)
|
Chlordane (ppm)
|
Sum PCBs (ppm)
|
|
81
|
tissue plug
|
2020
|
channel catfish
|
4
|
55.7
|
0.084
|
|
|
|
Support Level
|
Full
|
|
|
|
|
|
|
|