Environment Publications 1998
 |
| Appendix 1. Water quality, Boggy Creek and Whitemud River, summers of 1996 and 1997.
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| Site
| Site
| Date
| Field
| pH
| Conductivity
| Solids
| Solids
| Turbidity
| Secchi
| Fecal
| Ammonia &
| Ammonia
| Un-ionized
| Nitrate-
| Total
| Total
| Dissolved
| Dissolved
| Oxygen
| Chlorophyll
|
| Description
| Number
| | Temperature
| | | Total
| Total
| | Disc
| Coliform MF
| Ammonium
| Total
| Ammonia
| Nitrite
| Kjeldahl
| Phosphorus
| Phosphorus
| Oxygen
| Saturation
| a
|
| | |
| | | Dissolved
| Suspended
| | | Organisms
| as N
| as NH3
| | Nitrogen
| Nitrogen
| | | |
| |
| | | Deg. C
| pH units
| uS/cm
| mg/L
| mg/L
| NTU
| m
| /100mL
| mg/L
| mg/L
| mg/L
| mg/L
| mg/L
| mg/L
| mg/L
| mg/L
| %
| ug/L
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| Boggy Cr. |
WQ0201
| 1-Apr-96
| 0.0
| 7.79
| 716
| 420
| < 5
| 3.4
| | < 10
| 0.762
| 0.927
| 0.0047
| 0.18
| 1.57
| 0.067
| 0.026
| 8.7
| 59%
| |
| PTH 16 |
WQ0201
| 13-May-96
| 4.0
| 8.29
| 498
| 350
| 6
| 0.80
| 0.5
| 60
| 0.040
| 0.049
| 0.0011
| 0.29
| 1.23
| 0.112
| 0.065
| 11.9
| 91%
| 12.0
|
| at Neepawa |
WQ0201
| 10-Jun-96
| 22.0
| 8.26
| 558
| 370
| < 5
| 1.9
| 0.7
| 10
| 0.026
| 0.032
| 0.0024
| 0.06
| 0.98
| 0.113
| 0.052
| 7.4
| 85%
| 5.5
|
| WQ0201
| 8-Jul-96
| 17.0
| 8.08
| 533
| 390
| 9
| 8.6
| | 850
| 0.104
| 0.127
| 0.0046
| 0.10
| 1.04
| 0.172
| 0.159
| 7.8
| 81%
| |
| WQ0201
| 15-Jul-96
| | 8.29
| 503
| 350
| 44
| 21.0
| | 130
| 0.056
| 0.068
| | 0.11
| 1.38
| 0.199
| 0.085
| 5.8
| | 17.0
|
| WQ0201
| 12-Aug-96
| 20.0
| 8.12
| 438
| 300
| 25
| 13.0
| 0.5
| 60
| 0.117
| 0.142
| 0.0071
| 0.17
| 1.56
| 0.204
| 0.103
| 3.1
| 34%
| 3.5
|
| WQ0201
| 29-Sep-96
| 10.0
| 8.44
| 439
| 300
| < 5
| 4.7
| | 220
| 0.055
| 0.067
| 0.0033
| 0.14
| 1.29
| 0.143
| 0.107
| 8.2
| 73%
| |
| WQ0201
| 9-Apr-97
| 0.0
| 7.72
| 692
| 450
| 9
| 5.6
| | 10
| 0.766
| 0.932
| 0.0040
| 0.12
| 1.42
| 0.069
| 0.036
| 10.0
| 68%
| |
| WQ0201
| 13-May-97
| 11.0
| 8.11
| 488
| 350
| 17
| 5.9
| 0.5
| 10
| < 0.02
| < 0.024
| < 0.0006
| < 0.01
| 0.99
| 0.077
| 0.032
| 8.6
| 78%
| 8.5
|
| WQ0201
| 10-Jun-97
| 22.0
| 8.12
| 560
| 400
| 7
| 3.9
| 0.4
| 80
| 0.030
| 0.036
| 0.0021
| 0.02
| 1.00
| 0.063
| 0.033
| 6.0
| 69%
| 6.0
|
| WQ0201
| 7-Jul-97
| 17.0
| 8.28
| 497
| 350
| 10
| 7.7
| | 100
| 0.040
| 0.049
| 0.0028
| 0.02
| 0.80
| 0.113
| 0.068
| 6.6
| 69%
| |
| WQ0201
| 15-Jul-97
| 23.0
| 7.94
| 502
| 310
| 10
| 6.8
| 0.7
| 30
| 0.060
| 0.073
| 0.0030
| 0.01
| 0.90
| 0.166
| 0.121
| 3.6
| 42%
| 6.0
|
| WQ0201
| 19-Aug-97
| 19.0
| 8.18
| 399
| 260
| 10
| 7.0
| 0.7
| 20
| 0.020
| 0.024
| 0.0013
| 0.03
| 1.70
| 0.174
| 0.102
| 4.4
| 48%
| 31.0
|
| WQ0201
| 6-Oct-97
| 11.0
| 7.96
| 464
| 420
| 19
| 15.0
| | 70
| 0.030
| 0.036
| 0.0007
| < 0.01
| 1.10
| 0.115
| 0.030
| 6.5
| 59%
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| Whitemud R.
| WQ1717
| 13-May-97
| 12.0
| 8.18
| 623
| 420
| 7
| 7.6
| 0.8
| < 10
| < 0.02
| < 0.024
| < 0.0008
| 0.01
| 0.89
| 0.098
| 0.069
| 7.2
| 67%
| 5.0
|
| downstream
| WQ1717
| 10-Jun-97
| 24.0
| 8.10
| 737
| 480
| 27
| 18.0
| 0.3
| 20
| 1.220
| 1.484
| 0.0926
| 0.37
| 2.90
| 0.520
| 0.300
| 5.9
| 71%
| 6.0
|
| of Spring Cr.
| WQ1717
| 15-Jul-97
| 24.0
| 7.84
| 540
| 490
| 20
| 19.0
| 0.5
| 40
| 0.110
| 0.134
| 0.0047
| 0.11
| 1.20
| 0.490
| 0.400
| 3.8
| 46%
| 7.0
|
| at Arden |
WQ1717
| 19-Aug-97
| 19.0
| 7.89
| 448
| 300
| 26
| 19.0
| 0.4
| 45
| 0.060
| 0.073
| 0.0020
| 0.13
| 1.00
| 0.290
| 0.210
| 4.8
| 52%
| 8.0
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| Whitemud R.
| WQ0200
| 13-May-96
| 5.0
| 8.33
| 625
| 440
| 6
| 3.5
| 0.75
| < 10
| 0.020
| 0.024
| 0.0006
| 0.01
| 1.12
| 0.127
| 0.078
| 11.3
| 88%
| 19.0
|
| PTH 16 |
WQ0200
| 10-Jun-96
| 23.0
| 8.42
| 820
| 570
| 7
| 9.7
| 0.7
| 60
| 0.021
| 0.026
| 0.0029
| 0.20
| 1.70
| 0.286
| 0.210
| 7.5
| 88%
| 38.0
|
| Arden Ridge
| WQ0200
| 15-Jul-96
| | 8.35
| 659
| 460
| 69
| 60.0
| | 50
| 0.020
| 0.024
| | 0.06
| 1.30
| 0.459
| 0.300
| 7.1
| | 34.0
|
| WQ0200
| 12-Aug-96
| 20.5
| 8.42
| 549
| 360
| 44
| 24.0
| 0.4
| 70
| 0.056
| 0.068
| 0.0066
| 0.01
| 1.81
| 0.363
| 0.123
| 6.6
| 74%
| 10.0
|
| WQ0200
| 13-May-97
| 11.0
| 8.22
| 622
| 410
| 9
| 7.5
| 0.7
| 50
| < 0.02
| < 0.024
| < 0.0008
| 0.02
| 0.88
| 0.097
| 0.070
| 6.0
| 55%
| 4.5
|
| WQ0200
| 10-Jun-97
| 24.0
| 8.32
| 702
| 490
| 28
| 21.0
| 0.4
| 20
| 0.020
| 0.024
| 0.0024
| < 0.01
| 1.10
| 0.208
| 0.118
| 6.3
| 76%
| 4.0
|
| WQ0200
| 15-Jul-97
| 25.0
| 8.17
| 553
| 520
| 38
| 26.0
| 0.4
| 50
| 0.040
| 0.049
| 0.0038
| 0.08
| 1.30
| 0.480
| 0.320
| 5.3
| 65%
| 18.0
|
| WQ0200
| 19-Aug-97
| 19.0
| 8.13
| 476
| 310
| 19
| 21.0
| 0.4
| 140
| 0.050
| 0.061
| 0.0029
| 0.17
| 1.00
| 0.320
| 0.250
| 7.0
| 76%
| 10.0
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| Whitemud R.
| WQ0199
| 13-May-96
| 7.0
| 8.28
| 646
| 420
| 5
| 2.3
| 0.5
| 30
| < 0.02
| < 0.024
| < 0.0007
| 0.21
| 1.20
| 0.111
| 0.053
| 10.5
| 86%
| 18.0
|
| PTH 16 |
WQ0199
| 10-Jun-96
| 23.0
| 8.37
| 794
| 550
| 14
| 14.0
| 0.5
| 30
| 0.021
| 0.026
| 0.0026
| 0.07
| 1.44
| 0.222
| 0.250
| 5.0
| 59%
| 28.0
|
| Gadstone |
WQ0199
| 15-Jul-96
| | 8.35
| 797
| 580
| 17
| 17.0
| | 20
| < 0.02
| < 0.024
| | 0.01
| 1.22
| 0.172
| 0.108
| 6.5
| | 15.0
|
| WQ0199
| 12-Aug-96
| 20.0
| 8.13
| 627
| 410
| 17
| 0.7
| 0.75
| 20
| 0.129
| 0.157
| 0.0080
| 0.02
| 1.34
| 0.240
| 0.104
| 3.6
| 40%
| 24.0
|
| WQ0199
| 13-May-97
| 11.0
| 8.28
| 635
| 420
| 27
| 20.0
| 0.5
| 10
| < 0.02
| < 0.024
| < 0.0009
| < 0.01
| 0.94
| 0.107
| 0.050
| 8.3
| 75%
| 4.5
|
| WQ0199
| 10-Jun-97
| 24.0
| 8.24
| 765
| 540
| 28
| 24.0
| 0.4
| 20
| 0.030
| 0.036
| 0.0031
| 0.01
| 1.00
| 0.124
| 0.063
| 5.6
| 67%
| 2.0
|
| WQ0199
| 15-Jul-97
| 25.0
| 8.30
| 617
| 370
| 16
| 10.0
| 0.6
| 50
| < 0.02
| < 0.024
| < 0.0025
| < 0.01
| 0.90
| 0.180
| 0.099
| 5.2
| 64%
| 12.0
|
| WQ0199
| 19-Aug-97
| 18.0
| 8.32
| 598
| 380
| 13
| 11.0
| 0.5
| 60
| < 0.02
| < 0.024
| < 0.0016
| < 0.01
| 1.20
| 0.179
| 0.117
| 6.6
| 70%
| 17.0
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| Whitemud R.
| WQ0197
| 1-Apr-96
| 0.0
| 7.59
| 774
| 480
| < 5
| 4.4
| | < 10
| 0.104
| 0.127
| 0.0004
| 0.77
| 0.91
| 0.067
| 0.055
| 6.4
| 44%
| |
| PTH 16 |
WQ0197
| 13-May-96
| 7.5
| 8.14
| 462
| 300
| 10
| 6.4
| 0.45
| 10
| 0.045
| 0.055
| 0.0011
| 0.02
| 1.13
| 0.096
| 0.059
| 9.5
| 79%
| 7.5
|
| Westbourne |
WQ0197
| 10-Jun-96
| 23.0
| 8.13
| 636
| 420
| 24
| 18.0
| 0.5
| < 10
| 0.036
| 0.044
| 0.0027
| 0.11
| 1.42
| 0.224
| 0.106
| 4.5
| 53%
| 11.0
|
| WQ0197
| 8-Jul-96
| 20.0
| 8.12
| 639
| 440
| 17
| 16.0
| | 20
| 0.036
| 0.044
| 0.0022
| 0.09
| 1.39
| 0.121
| 0.104
| 5.8
| 64%
| |
| WQ0197
| 15-Jul-96
| | 8.28
| 626
| 440
| 12
| 11.0
| | < 10
| 0.020
| < 0.024
| | 0.07
| 1.17
| 0.065
| 0.050
| 6.7
| | 1.0
|
| WQ0197
| 12-Aug-96
| 21.5
| 8.12
| 583
| 400
| < 5
| 5.5
| 0.75
| 40
| < 0.02
| < 0.024
| < 0.0013
| 0.08
| 1.19
| 0.076
| 0.060
| 5.4
| 62%
| 1.5
|
| WQ0197
| 29-Sep-96
| 9.0
| 8.40
| 669
| 420
| < 5
| 3.8
| | < 10
| 0.022
| 0.027
| 0.0011
| 0.02
| 0.86
| 0.070
| 0.058
| 9.6
| 83%
| |
| WQ0197
| 9-Apr-97
| 0.0
| 7.77
| 525
| 340
| 7
| 11.0
| | < 10
| 0.181
| 0.220
| 0.0011
| 0.90
| 1.06
| 0.191
| 0.045
| 4.5
| 31%
| |
| WQ0197
| 13-May-97
| 12.0
| 8.23
| 585
| 370
| 15
| 15.0
| 0.6
| 30
| 0.032
| 0.039
| 0.0014
| 0.04
| 0.98
| 0.066
| 0.030
| 8.6
| 80%
| 6.5
|
| WQ0197
| 10-Jun-97
| 24.0
| 8.25
| 720
| 500
| 18
| 15.0
| 0.4
| | < 0.02
| < 0.024
| < 0.0021
| 0.01
| 1.00
| 0.067
| 0.037
| 5.0
| 60%
| < 1.0
|
| WQ0197
| 7-Jul-97
| 18.0
| 8.37
| 571
| 370
| 12
| 10.0
| | 40
| < 0.02
| < 0.024
| < 0.0018
| 0.01
| 0.90
| 0.082
| 0.049
| 6.8
| 72%
| |
| WQ0197
| 15-Jul-97
| 26.0
| 8.26
| 601
| 500
| 23
| 16.0
| 0.4
| < 10
| < 0.02
| < 0.024
| <0.0024
| < 0.01
| 0.80
| 0.082
| 0.057
| 4.4
| 55%
| 4.0
|
| WQ0197
| 19-Aug-97
| 18.0
| 8.22
| 733
| 470
| 11
| 11.0
| 0.9
| 70
| < 0.02
| < 0.024
| < 0.0013
| 0.01
| 0.80
| 0.067
| 0.043
| 6.6
| 70%
| 1.0
|
| WQ0197
| 6-Oct-97
| 12.0
| 8.24
| 701
| 540
| 12
| 8.7
| | 10
| 0.050
| 0.061
| 0.0022
| < 0.01
| 0.70
| 0.460
| 0.300
| 8.7
| 81%
| |
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| Appendix 2. Water quality, Whitemud River tributaries, summers of 1996 and 1997.
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| |
| Site
| Site
| Date
| Field
| pH
| Conductivity
| Solids
| Solids
| Turbidity
| Secchi
| Fecal
| Ammonia &
| Ammonia
| Un-ionized
| Nitrate-
| Total
| Total
| Dissolved
| Dissolved
| Oxygen
| Chlorophyll
|
| Description
| Number
| | Temperature
| | | Total
| Total
| | Disc
| Coliform MF
| Ammonium
| Total
| Ammonia
| Nitrite
| Kjeldahl
| Phosphorus
| Phosphorus
| Oxygen
| Saturation
| a
|
| | |
| | | Dissolved
| Suspended
| | | Organisms
| as N
| as NH3
| | Nitrogen
| Nitrogen
| | | |
| |
| | | Deg. C
| pH units
| uS/cm
| mg/L
| mg/L
| NTU
| m
| /100mL
| mg/L
| mg/L
| mg/L
| mg/L
| mg/L
| mg/L
| mg/L
| mg/L
| %
| ug/L
|
| | |
| | | |
| | | |
| | | |
| | | |
| |
| Brookdale |
WQ1600
| 13-May-96
| 5.0
| 8.23
| 820
| 580
| 6
| 3.2
| 1.1
| 60
| < 0.02
| < 0.024
| < 0.0005
| < 0.01
| 1.02
| 0.116
| 0.070
| 9.7
| 76%
| 4.0
|
| Drain | WQ1600
| 10-Jun-96
| 24.0
| 8.32
| 998
| 730
| < 5
| 2.8
| 0.7
| 80
| < 0.02
| < 0.024
| < 0.0024
| 0.02
| 1.53
| 0.239
| 0.187
| 6.0
| 72%
| 4.0
|
| PTH 5 | WQ1600
| 15-Jul-96
| | 8.03
| 800
| 560
| 8
| 4.6
| | < 10
| < 0.02
| < 0.024
| | 0.03
| 1.14
| 0.244
| 0.158
| 5.8
| | 7.5
|
| WQ1600
| 12-Aug-96
| 18.5
| 8.10
| 1030
| 820
| < 5
| 3.6
| 1.1
| 40
| 0.061
| 0.074
| 0.0032
| 0.01
| 1.68
| 0.333
| 0.260
| 4.3
| 46%
| 1.7
|
| WQ1600
| 13-May-97
| 11.0
| 8.09
| 919
| 650
| 6
| 5.3
| 1.0
| 20
| 0.027
| 0.033
| 0.0008
| < 0.01
| 1.23
| 0.128
| 0.094
| 7.0
| 64%
| 2.0
|
| WQ1600
| 10-Jun-97
| 22.0
| 8.06
| 888
| 660
| 6
| 4.4
| 0.5
| 140
| 0.020
| 0.024
| 0.0012
| < 0.01
| 1.50
| 0.159
| 0.117
| 5.3
| 61%
| < 1.0
|
| WQ1600
| 15-Jul-97
| 24.0
| 7.90
| 832
| 680
| 8
| 2.6
| 0.6
| 20
| 0.040
| 0.049
| 0.0020
| < 0.01
| 1.40
| 0.320
| 0.250
| 3.7
| 44%
| 16.0
|
| WQ1600
| 19-Aug-97
| 17.0
| 7.69
| 738
| 480
| 6
| 4.0
| 0.4
| 70
| 0.020
| 0.024
| 0.0004
| < 0.01
| 1.20
| 0.180
| 0.111
| 4.2
| 44%
| 20.0
|
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| |
| Stony Creek
| WQ0635
| 13-May-97
| 12.0
| 8.30
| 773
| 520
| 6
| 3.2
| 0.3
| 210
| 0.032
| 0.039
| 0.0016
| 0.01
| 0.87
| 0.073
| 0.060
| 8.1
| 75%
| 2.5
|
| (Neepawa Cr.)
| WQ0635
| 10-Jun-97
| 20.0
| 8.08
| 771
| 560
| 9
| 5.3
| 0.3
| 930
| 0.060
| 0.073
| 0.0033
| 0.03
| 0.90
| 0.104
| 0.069
| 5.1
| 57%
| 1.0
|
| PTH 16 |
WQ0635
| 15-Jul-97
| 23.0
| 9.05
| 468
| 400
| 25
| 12.0
| 0.4
| 1040
| 0.080
| 0.097
| 0.0346
| 0.04
| 0.90
| 0.119
| 0.082
| 5.0
| 59%
| 2.0
|
| at Neepewa |
WQ0635
| 19-Aug-97
| 17.0
| 7.64
| 645
| 430
| 33
| 16.0
| 0.3
| > 2000
| 0.050
| 0.061
| 0.0008
| 0.01
| 1.10
| 0.135
| 0.058
| 3.0
| 31%
| 22.0
|
| | |
| | | |
| | | |
| | | |
| | | |
| |
| Spring Cr. |
WQ1716
| 13-May-97
| 11.0
| 8.03
| 852
| 580
| < 5
| 0.7
| 0.7
| 10
| < 0.02
| < 0.024
| < 0.0005
| < 0.01
| 0.81
| 0.105
| 0.105
| 6.2
| 56%
| < 1.0
|
| at Arden |
WQ1716
| 10-Jun-97
| 24.0
| 8.02
| 1000
| 710
| 12
| 8.1
| 0.5
| 40
| 0.020
| 0.024
| 0.0013
| < 0.01
| 1.60
| 0.490
| 0.400
| 4.8
| 58%
| < 1.0
|
| WQ1716
| 15-Jul-97
| 24.0
| 8.28
| 796
| 640
| 53
| 6.7
| 0.3
| 10
| 0.040
| 0.049
| 0.0045
| < 0.01
| 1.30
| 0.380
| 0.335
| 5.6
| 67%
| 3.0
|
| WQ1716
| 19-Aug-97
| 19.0
| 8.80
| 697
| 480
| 30
| 16.0
| 0.5
| 60
| 0.030
| 0.036
| 0.0069
| < 0.01
| 1.30
| 0.188
| 0.170
| 5.7
| 62%
| 1.0
|
| | |
| | | |
| | | |
| | | |
| | | |
| |
| Big Grass |
WQ1601
| 10-Jun-96
| 24.0
| 7.88
| 569
| 380
| 7
| 3.1
| 1.1
| < 10
| 0.041
| 0.050
| 0.0019
| 0.28
| 1.53
| 0.158
| 0.065
| 3.6
| 43%
| 2.0
|
| Drain, NE of
| WQ1601
| 15-Jul-96
| | 7.76
| 588
| 420
| 10
| 6.3
| | 40
| 0.031
| 0.038
| | 0.01
| 1.30
| 0.040
| 0.028
| 2.8
| | 1.5
|
| Gladstone |
WQ1601
| 12-Aug-96
| 21.8
| 7.68
| 552
| 380
| < 5
| 0.9
| 1.7
| 180
| < 0.02
| < 0.024
| < 0.0005
| 0.05
| 1.24
| 0.037
| 0.026
| 3.4
| 39%
| 1.5
|
| WQ1601
| 13-May-97
| 10.0
| 7.96
| 544
| 350
| 51
| 16.0
| 0.7
| < 10
| 0.021
| 0.026
| 0.0004
| 0.02
| 1.26
| 0.051
| 0.019
| 6.8
| 60%
| 4.5
|
| WQ1601
| 10-Jun-97
| 25.0
| 8.29
| 643
| 440
| 9
| 6.5
| 0.9
| 10
| 0.020
| 0.024
| 0.0024
| < 0.01
| 1.30
| 0.034
| 0.019
| 6.8
| 83%
| < 1.0
|
| WQ1601
| 15-Jul-97
| 26.0
| 8.41
| 703
| 640
| 22
| 7.6
| 0.9
| 510
| 0.020
| 0.024
| 0.0033
| < 0.01
| 1.40
| 0.074
| 0.030
| 4.5
| 56%
| 3.0
|
| WQ1601
| 19-Aug-97
| 20.0
| 8.35
| 659
| 450
| 8
| 7.0
| 0.5
| 40
| 0.030
| 0.036
| 0.0030
| < 0.01
| 1.60
| 0.053
| 0.028
| 5.6
| 62%
| < 1.0
|
| | |
| | | |
| | | |
| | | |
| | | |
| |
| Pine Cr. |
WQ1690
| 17-Jul-96
| 24.0
| 8.25
| 559
| 350
| 29
| 22.0
| 0.3
| 20
| 0.063
| 0.077
| 0.0066
| 0.02
| 0.80
| 0.121
| 0.050
| 6.6
| 79%
| 1.0
|
| at PR 350 |
WQ1690
| 12-Aug-96
| 21.0
| 8.41
| 568
| 380
| < 5
| 13.0
| 0.75
| 220
| 0.045
| 0.055
| 0.0054
| 0.02
| 0.72
| 0.069
| 0.049
| 8.3
| 94%
| 1.0
|
| WQ1690
| 13-May-97
| 12.0
| 8.36
| 552
| 350
| 8
| 7.6
| 0.5
| 10
| < 0.02
| < 0.024
| < 0.0012
| < 0.01
| 0.60
| 0.055
| 0.034
| 8.7
| 81%
| 2.5
|
| WQ1690
| 10-Jun-97
| 26.0
| 8.47
| 573
| 400
| 9
| 8.9
| 0.4
| 20
| < 0.02
| < 0.024
| < 0.0037
| < 0.01
| 0.50
| 0.059
| 0.034
| 10.0
| 125%
| < 1.0
|
| WQ1690
| 15-Jul-97
| 26.0
| 8.47
| 522
| 490
| 11
| 6.6
| 0.7
| 40
| < 0.02
| < 0.024
| < 0.0037
| 0.01
| 0.70
| 0.081
| 0.064
| 8.6
| 107%
| 2.0
|
| WQ1690
| 19-Aug-97
| 18.0
| 8.27
| 493
| 300
| 29
| 23.0
| 0.4
| 120
| 0.030
| 0.036
| 0.0022
| 0.10
| 0.60
| 0.118
| 0.072
| 7.6
| 81%
| 1.0
|
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