TABLE 4.
Pearson Correlation of Hydrologic Metrics With Measures of Urbanization, Non-Urban Forest Cover, and Benthic Index of Biological Integrity Scores in 16 Stream Basins.
| arcsin sqrt (%Total Impervious Area) |
arcsin sqrt (%Urban) |
arcsin sqrt (%Forest) |
Benthic Index of Biological Integrity |
|||||
|---|---|---|---|---|---|---|---|---|
| r | p | r | p | r | p | r | p | |
| Benthic Index of Biological Integrity | −0.733 | 0.001 | −0.748 | 0.001 | 0.731 | 0.001 | ||
| log (Low Pulse Count) | 0.530 | 0.035 | 0.443 | 0.086 | −0.450 | 0.080 | −0.664 | 0.005 |
| log (Low Pulse Duration) | −0.587 | 0.017 | −0.589 | 0.016 | 0.559 | 0.025 | 0.766 | 0.001 |
| Low Pulse Range | 0.087 | 0.750 | −0.085 | 0.754 | 0.009 | 0.973 | −0.036 | 0.896 |
| log (High Pulse Count) | 0.700 | 0.003 | 0.757 | 0.001 | −0.716 | 0.002 | −0.844 | <0.0001 |
| log (High Pulse Duration) | −0.638 | 0.008 | −0.638 | 0.008 | 0.634 | 0.008 | 0.801 | 0.0002 |
| High Pulse Range | 0.772 | <0.001 | 0.807 | <0.001 | −0.759 | 0.001 | −0.854 | <0.0001 |
| log (Fall Rate) | 0.023 | 0.932 | 0.048 | 0.859 | −0.003 | 0.990 | −0.317 | 0.231 |
| log (Rise Rate) | 0.001 | 0.997 | 0.020 | 0.941 | 0.024 | 0.931 | −0.265 | 0.321 |
| Fall Count | 0.426 | 0.100 | 0.372 | 0.156 | −0.402 | 0.123 | −0.420 | 0.106 |
| Rise Count | 0.543 | 0.030 | 0.506 | 0.046 | −0.530 | 0.035 | −0.529 | 0.035 |
| Flow Reversals | 0.688 | 0.003 | 0.681 | 0.004 | −0.696 | 0.003 | −0.652 | 0.006 |
| TQmean | −0.527 | 0.036 | −0.455 | 0.077 | 0.491 | 0.053 | 0.685 | 0.003 |
| R-B Index | 0.736 | 0.001 | 0.645 | 0.007 | −0.683 | 0.004 | −0.703 | 0.002 |
| Seven-day minimum flow | −0.266 | 0.319 | −0.188 | 0.485 | 0.245 | 0.360 | 0.057 | 0.835 |
| Date of annual daily minimum | −0.364 | 0.165 | −0.296 | 0.266 | 0.381 | 0.145 | 0.475 | 0.063 |
Note: Values given in boldface indicate significance based on Benjamini and Hochberg False Discovery Rate control (p=0.05; k=15) (Verhoeven et al., 2005).