Table 2 Pearson correlation coefficients among the water chemistry parameters, habitat parameters and land uses at the sampling stations in the Qing River basin.
From: Estimating the nutrient thresholds of a typical tributary in the Liao River basin, Northeast China
Parameter | TP | TN | NH4+-N | CODCr | BOD5 | DO | pH | EC | NO3−N | Chloride | Sulfate | FCC | TBC |
---|---|---|---|---|---|---|---|---|---|---|---|---|---|
Physical-Chemical Parameter | |||||||||||||
TP | 1 | ||||||||||||
TN | 0.226 | 1 | |||||||||||
NH4+-N | 0.295 | −0.077 | 1 | ||||||||||
CODCr | 0.711** | 0.409* | 0.474** | 1 | |||||||||
BOD5 | 0.707** | 0.151 | 0.187 | 0.680** | 1 | ||||||||
DO | 0.164 | −0.433* | 0.198 | 0.228 | 0.355* | 1 | |||||||
pH | 0.027 | −0.5 | 0.306 | 0.006 | −0.014 | 0.711** | 1 | ||||||
EC | 0.420* | 0.190 | 0.785** | 0.558** | 0.377** | 0.080 | −0.008 | 1 | |||||
NO3−N | −0.312 | 0.646** | 0.433 | 0.404 | 0.068 | −0.055 | −0.146 | −0.561* | 1 | ||||
Chloride | 0.250 | 0.461* | 0.908** | 0.562* | −0.101 | −0.575** | −0.323 | 0.894** | 0.544* | 1 | |||
Sulfate | 0.221 | 0.690** | 0.755** | 0.708** | −0.128 | −0.534* | −0.682** | 0.829** | 0.447 | 0.736** | 1 | ||
FCC | 0.212 | 0.047 | 0.183 | 0.149 | 0.332 | −0.343 | −0.367 | 0.396 | 0.375 | 0.393 | 0.305 | 1 | |
TBC | −0.027 | 0.608** | 0.377 | 0.137 | −0.063 | −0.231 | −0.202 | 0.406 | 0.314 | 0.256 | 0.449 | −0.004 | 1 |
Habitat Descriptors | |||||||||||||
Epifaunal Substrate⁄Available Cover | −0.35* | −0.226 | −0.313 | −0.539** | −0.302 | −0.105 | −0.029 | −0.293 | −0.257 | −0.659** | −0.711** | −0.100 | −0.463* |
Embeddedness | −0.378* | −0.372* | −0.377* | −0.574** | −0.326 | −0.093 | −0.024 | −0.372* | −0.253 | −0.659** | −0.697** | −0.060 | −0.493* |
Velocity/Depth Regime | −0.354* | −0.329 | −0.266 | −0.507** | −0.332 | −0.106 | −0.020 | −0.267 | −0.235 | −0.609** | −0.673** | −0.088 | −0.382 |
Sediment Deposition | −0.374* | −0.376* | −0.341* | −0.571** | −0.356* | −0.117 | −0.035 | −0.318 | −0.258 | −0.645** | −0.669** | −0.116 | −0.508* |
Channel Flow Status | −0.354* | −0.366* | −0.304 | −0.537** | −0.338* | −0.092 | −0.006 | −0.317 | −0.245 | −0.578** | −0.683** | −0.106 | −0.431 |
Channel Alteration | −0.416* | −0.381* | −0.275 | −0.517** | −0.362* | −0.048 | 0.016 | −0.303 | −0.225 | −0.573* | −0.676** | −0.045 | −0.392 |
Frequency of Riffles | −0.352* | −0.345* | −0.252 | −0.518** | −0.338* | −0.111 | −0.010 | −0.259 | −0.263 | −0.595** | −0.708** | −0.086 | −0.443 |
Bank Stability | −0.346* | −0.343* | −0.216 | −0.482** | −0.309 | −0.092 | −0.014 | −0.227 | −0.196 | −0.511* | −0.674** | −0.076 | −0.369 |
Vegetative Protection | −0.366* | −0.354* | −0.293 | −0.533** | −0.333 | −0.128 | −0.053 | −0.293 | −0.229 | −0.602** | −0.690** | −0.066 | −0.417 |
Riparian Vegetative Zone Width | −0.354* | −0.369* | −0.293 | −0.519** | −0.311 | −0.102 | −0.033 | −0.295 | −0.187 | −0.573* | −0.686** | −0.033 | −0.448 |
Land Use | |||||||||||||
Cropland | 0.497** | 0.650** | 0.374* | 0.664** | 0.435** | −0.080 | −0.196 | 0.524** | 0.308 | 0.717** | 0.698** | 0.088 | 0.632* |
Urban Land | 0.779** | 0.105 | 0.527** | 0.738** | 0.751** | 0.368* | 0.121 | 0.623** | 0.322 | 0.820** | 0.356 | 0.313 | 0.234 |
Forest Land | −0.549** | −0.615** | −0.408* | −0.698** | −0.484** | 0.038 | 0.169 | −0.56** | −0.312 | −0.738** | −0.693** | −0.100 | −0.623** |
Population | 0.813** | 0.074 | 0.520** | 0.788** | 0.832** | 0.388* | 0.153 | 0.571** | 0.118 | 0.536* | 0.166 | 0.309 | 0.099 |