|
Table 1. Average water quality
data at individual sampling sites and for all sampling sites during
the winter and summer, Clearwater Lake, 1997.
| Site
| Sample
Period
During
1977
| Number
of
Samples
| Sample Depth
m
| Depth of Column Sampled
m
| Secchi Disk
Depth
m
| Turbidity
NTU
| pH
pH units
| Total
Kjeldahl Nitrogen
mg/L
| Ammonia- Ammonium Nitrogen
mg/L
| Un-ionized Ammonia Nitrogen
mg/L
| Nitrate-Nitrite Nitrogen
mg/L
| Total Phosphorus
mg/L
| Dissolved
Phosphorus
mg/L
| Chlorophyll
a
g/L
|
| WQ1201
| February
| 2
| 0.55
| | | 0.55
| 8.36
| 0.36
| 0.032
| 0.0007
| <0.01
| 0.015
| 0.012
| |
| WQ1201
| July to September
| 4
| | 2.81
| 2.5
| 2.90
| 8.52
| 0.25
| <0.020
| | <0.01
| 0.013
| 0.006
| 2.5
|
| WQ1208
| February
| 3
| 2.03
| | | 0.97
| 8.35
| 0.46
| <0.027
| <0.0006
| <0.01
| 0.017
| 0.011
| |
| WQ1208
| July to September
| 4
| | 13.5
| 6.75
| 0.91
| 8.51
| 0.25
| <0.020
| | <0.01
| 0.010
| 0.005
| <1.0
|
| WQ1209
| February
| 3
| 2.03
| | | 0.60
| 8.39
| 0.30
| <0.020
| <0.0005
| <0.01
| 0.017
| 0.014
| |
| WQ1214
| July to September
| 4
| | 14.25
| 7.13
| 0.98
| 8.51
| 0.33
| <0.023
| | <0.01
| 0.008
| 0.007
| <1.0
|
| WQ1224
| July to September
| 4
| | 11.25
| 6.5
| 1.05
| 8.53
| 0.25
| <0.020
| | <0.01
| 0.011
| 0.005
| <1.3
|
| All Sites
| February
| 8
| 1.66
| | | 0.73
| 8.37
| 0.38
| <0.026
| <0.0006
| <0.01
| 0.017
| 0.012
| 1.4
|
| All Sites
| July to September
| 16
| | 10.45
| 5.72
| 1.46
| 8.52
| 0.27
| <0.021
| | <0.01
| 0.010
| 0.005
| |
| All Sites
| February to September
| 24
| 1.66a
| 10.45b
| 5.72b
| 1.21
| 8.47
| 0.30
| <0.022
| <0.0006a
| <0.01
| 0.012
| 0.008
| 1.4b
|
| All Sites Minus WQ1201
| February to September
| 18
| 2.03a
| 13.0b
| 6.79b
| 0.91
| 8.47
| 0.31
| <0.022
| <0.0006a
| <0.01
| 0.012
| 0.008
| 1.1b
|
a = Available for 8 February samples
only.
b = Available for 16 July to September
samples only.
Table 2. Annual averages, Clearwater
Lake water quality from 1943 to 1997.
| Year
| Sample
Period
| Number
of
Samples
| Secchi Disk
Depth
m
| Turbidity
NTU
| pH
pH units
| Total
Kjeldahl Nitrogen
mg/L
| Ammonia- Ammonium Nitrogen
mg/L
| Un-ionized Ammonia Nitrogen
mg/L
| Nitrate-Nitrite Nitrogen
mg/L
| Total Phosphorus
mg/L
| Dissolved
Phosphorus
mg/L
| Chlorophyll
a
g/L
|
| 1943a
| July
| 2
| 9.75
| | 7.20
| | | |
| | | |
| 1961
| November
| 1
| | 2
| 8.18
| | | |
| | | |
| 1962
| January to October
| 9-10
| | 5.0
| 8.18
| | | |
| | | |
| 1970a
| July
| 4-24
| 5.36
| | 8.40
| | | |
| | | |
| 1974
| June to August
| 5-11
| | 0.5
| 8.40
| | | | 0.060
| <0.018d
| | |
| 1988b
| February to October
| 4
| | 0.65
| 8.14
| 0.71
| | | <0.150
| <0.014
| | |
| 1989c
| June
| 3-50
| | 0.22
| 8.45
| <0.22
| 0.009
| 0.0005c
| <0.018
| 0.011
| | |
| 1996a
| August
| | | 0.91
| 8.62
| <0.26
| 0.016
| 0.0022
| <0.028
| 0.033
| 0.027
| |
| 1997a
| February to September
| | 5.72e
| 1.21e
| 8.47
| <0.22
| <0.022
| <0.006
| <0.010
| 0.012
| 0.008
| <1.4
|
a = Includes samples collected between
surface and bottom.
b = Excludes a sample from April
27,1988 in which run-off is suspected.
c = Fifty samples for all perameters
except for calculated un-ionized ammonia for only three samples
for three sites where temperature was measured.
d = Total phosphorous calculated
from total phosphate.
e = Secchi Disk and Turbidity include
Site WQ1201 where the total depth is at or near Secchi disk depth.
If this data is excluded average Secchi disk depth would be 6.79
m and average turbidity would be 0.98 NTU.
Appendix 1: Water quality data,
Clearwater Lake, 1997.
| Site
| Sample
Date
| Sample Depth
m
| Depth of Column Sampled
m
| Secchi
Disk
Depth
m
| Turbidity
NTU
| pH
pH units
| Total
Kjeldahl Nitrogen
mg/L
| Ammonia- Ammonium Nitrogen
mg/L
| Un-ionized Ammonia Nitrogen
mg/L
| Nitrogen
Nitrate-Nitrite
mg/L
| Total Phosphorus
mg/L
| Dissolved
Phosphorus
mg/L
| Chlorophyll
a
g/L
|
| WQ1201
| 23-Feb-97
| 0.1
| | | 0.76
| 8.37
| 0.38
| 0.032
| 0.0007
| 0.01
| 0.017
| 0.013
| |
| WQ1201
| 23-Feb-97
| 1
| | | 0.33
| 8.35
| 0.34
| 0.032
| 0.0007
| < 0.01
| 0.013
| 0.011
| |
| WQ1201
| 07-Jul-97
| | 3
| 3
| 2.0
| 8.46
| 0.20
| < 0.02
| | < 0.01
| 0.016
| 0.002
| < 1
|
| WQ1201
| 05-Aug-97
| | 3
| 3
| 2.1
| 8.62
| 0.20
| < 0.02
| | < 0.01
| 0.017
| 0.016
| < 1
|
| WQ1201
| 17-Aug-97
| | 3.75
| 2
| 3.1
| 8.52
| 0.40
| < 0.02
| | < 0.01
| 0.013
| 0.003
| 6
|
| WQ1201
| 04-Sep-97
| | 1.5
| 2
| 4.4
| 8.5
| 0.20
| < 0.02
| | < 0.01
| 0.007
| 0.002
| 1
|
| WQ1208
| 23-Feb-97
| 0.1
| | | 1.1
| 8.37
| 0.51
| 0.022
| 0.0005
| 0.01
| 0.019
| 0.010
| |
| WQ1208
| 23-Feb-97
| 1
| | | 1.0
| 8.39
| 0.32
| < 0.02
| <0.0005
| < 0.01
| 0.017
| 0.015
| |
| WQ1208
| 23-Feb-97
| 5
| | | 0.81
| 8.31
| 0.55
| 0.038
| 0.0008
| < 0.01
| 0.017
| 0.010
| |
| WQ1208
| 07-Jul-97
| | 16
| 8
| 0.51
| 8.44
| 0.20
| < 0.02
| | < 0.01
| 0.011
| 0.002
| < 1
|
| WQ1208
| 05-Aug-97
| | 17
| 8.5
| 1.0
| 8.56
| < 0.2
| < 0.02
| | < 0.01
| 0.012
| 0.004
| < 1
|
| WQ1208
| 17-Aug-97
| | 11
| 5.5
| 1.2
| 8.54
| 0.40
| < 0.02
| | < 0.01
| 0.012
| 0.011
| 1
|
| WQ1208
| 04-Sep-97
| | 10
| 5
| 0.9
| 8.5
| 0.20
| < 0.02
| | < 0.01
| 0.005
| 0.002
| 1
|
| WQ1209
| 23-Feb-97
| 0.1
| | | 1.1
| 8.39
| 0.39
| < 0.02
| <0.0005
| 0.01
| 0.021
| 0.018
| |
| WQ1209
| 23-Feb-97
| 1
| | | 0.23
| 8.39
| 0.24
| < 0.02
| <0.0005
| < 0.01
| 0.015
| 0.010
| |
| WQ1209
| 23-Feb-97
| 5
| | | 0.48
| 8.38
| 0.27
| < 0.02
| <0.0005
| < 0.01
| 0.014
| 0.014
| |
| WQ1214
| 07-Jul-97
| | 16
| 8
| 0.53
| 8.45
| < 0.2
| < 0.02
| | < 0.01
| 0.003
| 0.002
| < 1
|
| WQ1214
| 05-Aug-97
| | 19
| 9.5
| 0.7
| 8.56
| < 0.2
| 0.03
| | < 0.01
| 0.013
| 0.012
| < 1
|
| WQ1214
| 17-Aug-97
| | 12
| 6
| 1.5
| 8.55
| 0.6
| < 0.02
| | < 0.01
| 0.011
| 0.011
| 1
|
| WQ1214
| 04-Sep-97
| | 10
| 5
| 1.2
| 8.51
| 0.3
| < 0.02
| | < 0.01
| 0.004
| 0.002
| 1
|
| WQ1224
| 07-Jul-97
| | 15
| 8
| 1.4
| 8.46
| < 0.2
| < 0.02
| | < 0.01
| 0.012
| 0.001
| < 1
|
| WQ1224
| 05-Aug-97
| | 10
| 8
| 0.6
| 8.62
| 0.20
| 0.02
| | < 0.01
| 0.013
| 0.013
| < 1
|
| WQ1224
| 17-Aug-97
| | 10
| 5
| 0.8
| 8.51
| 0.40
| < 0.02
| | < 0.01
| 0.013
| 0.002
| 2
|
| WQ1224
| 04-Sep-97
| | 10
| 5
| 1.4
| 8.51
| 0.20
| < 0.02
| | 0.01
| 0.004
| 0.002
| < 1
|
|