Table 6. Datasets showing laboratory sample results and summary statistics for scenarios used for calibration and validation of regression models with continuous monitors at Fanno Creek, Durham, Oregon.
[Discharge, turbidity, and specific conductance data were from records at stream gages and continuous monitors. Occasional Clean Water Services samples were collected at higher discharges than shown here, but continuous monitors were not deployed at the time so samples could not be used for this study. Note that USGS uses suspended sediment concentration (SSC) rather than total suspended solids (TSS). SSC and TSS data were combined without adjustment for Scenario 2 and Scenario 3. Abbreviations: FNU, Formazin Nephelometric Unit; n, number of samples (numbers for individual models may vary where missing values or outliers were removed); NWIS, National Water Information System water quality database; USGS, U.S. Geological Survey; ft3/s, cubic foot per second; µS/ cm, microsiemens per centimeter; mg/L, milligram per liter; No./100 mL, colony count per 100 milliliters]
Scenario and summary statistic |
Calibration |
Validation |
Discharge (ft3/s) |
Turbidity (FNU) |
Specific conductance (µS/cm) |
Total suspended solids (mg/L) |
Total phosphorus (mg/L) |
E. coli (No. /100 mL) |
Total suspended solids (mg/L) |
Total phosphorus (mg/L) |
E. coli (No. /100 mL) |
Scenario 1 |
Autosampler (2002–03), n = 54 |
Clean Water Services ambient monitoring (2001–04), n = 98 |
Minimum |
7.1 |
5.7 |
110.0 |
4.0 |
0.08 |
180 |
2.0 |
0.08 |
56 |
Maximum |
134.4 |
131 |
245.0 |
196.0 |
0.47 |
10,000 |
260.0 |
0.60 |
12,000 |
Mean |
65.7 |
47 |
159.5 |
51.0 |
0.19 |
2,829 |
16.9 |
0.15 |
763 |
Median |
63.9 |
38 |
146.0 |
37.1 |
0.15 |
1,300 |
7.2 |
0.14 |
325 |
Standard deviation |
31.0 |
30 |
34.7 |
45.6 |
0.10 |
3,174 |
34.8 |
0.08 |
2,020 |
Scenario 2 |
Autosampler (2002–03) + USGS NWIS (2001–07), n = 131 |
Clean Water Services ambient monitoring (2001–04), n = 98 |
Minimum |
1.12 |
1.4 |
63.8 |
0.5 |
0.08 |
180 |
2.0 |
0.08 |
56 |
Maximum |
505.0 |
131 |
394.0 |
242.0 |
0.47 |
10,000 |
260.0 |
0.60 |
12,000 |
Mean |
49.1 |
28 |
187.2 |
29.9 |
0.15 |
2,829 |
16.9 |
0.15 |
763 |
Median |
33.2 |
17 |
182.2 |
12.5 |
0.14 |
1,300 |
7.2 |
0.14 |
325 |
Standard deviation |
65.0 |
29 |
52.7 |
40.9 |
0.07 |
3,174 |
34.8 |
0.08 |
2,020 |
Scenario 3 |
Autosampler peak discharge samples, USGS NWIS high flow 2001–07, Clean Water Services first monthly + high flow, n = 96 |
Autosampler non-peak discharge samples, USGS non-high flow, Clean Water Services remaining monthly and non-high flow, n = 80 |
Minimum |
1.1 |
3.9 |
63.8 |
2.0 |
0.08 |
67 |
0.5 |
0.08 |
56 |
Maximum |
505.0 |
131 |
281.0 |
242.0 |
0.47 |
6,300 |
260.0 |
0.60 |
10,000 |
Mean |
57.9 |
25 |
177.5 |
26.3 |
0.14 |
824 |
29.6 |
0.17 |
1,565 |
Median |
35.4 |
17 |
168.0 |
13.5 |
0.13 |
345 |
10.0 |
0.14 |
520 |
Standard deviation |
80.7 |
26 |
48.8 |
39.4 |
0.05 |
1,428 |
40.7 |
0.09 |
2,546 |
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First posted June 18, 2010
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