Research Article
Biodiversity of Three Backwaters in the South West Coast of India
Table 7
Karl Pearson correlation showing the significance (5%) by relating the number of fishes and sediment parameters of Kadinamkulam backwater.
| Name of fish | Organic carbon | Total phosphorous | Total nitrogen | Copper | Lead | Manganese | Nickel | Zinc |
| Oreochromis mossambicus | 0.27 | 0.23 | 0.23 | −0.03 | −0.26 | −0.40 | 0.42 | 0.11 | Etroplus suratensis | −0.13 | −0.10 | −0.10 | −0.36 | −0.21 | −0.34 | 0.34 | 0.33 | Etroplus maculatus | −0.17 | −0.09 | −0.09 | 0.13 | −0.09 | −0.01 | −0.23 | −0.28 | Terapon jarbua | −0.56* | 0.24 | 0.24 | −0.26 | 0.01 | 0.01 | −0.02 | −0.10 | Caranx sehfsciatis | −0.69* | 0.00 | 0.00 | −0.13 | 0.01 | 0.09 | −0.30 | −0.21 | Caranx ignobilis | −0.83** | −0.18 | −0.18 | −0.37 | 0.11 | 0.06 | −0.14 | −0.38 | Chanda ranga | 0.15 | 0.21 | 0.21 | 0.50* | −0.78** | −0.79** | −0.42 | 0.52* | Chanda nama | 0.08 | 0.08 | 0.08 | 0.35 | −0.24 | −0.14 | −0.34 | −0.12 | Mugil cephalus | −0.05 | 0.34 | 0.34 | 0.20 | −0.64* | −0.72** | −0.12 | 0.53* | Channa marulius | −0.14 | −0.18 | −0.18 | −0.23 | 0.12 | 0.08 | 0.19 | −0.33 | Channa striatus | 0.17 | −0.36 | −0.36 | 0.15 | 0.11 | 0.17 | −0.23 | −0.23 | Megalops cyprinoides | −0.09 | 0.38 | 0.38 | 0.10 | −0.77** | −0.79** | 0.03 | 0.83** | Gerres filamentosus | 0.18 | 0.12 | 0.12 | 0.46 | −0.01 | 0.22 | −0.48 | −0.08 | Puntius filamentosus | 0.67* | 0.06 | 0.06 | 0.54* | −0.20 | −0.13 | −0.03 | 0.11 | Anabas testudineus | −0.37 | −0.03 | −0.03 | −0.25 | −0.30 | −0.46 | 0.16 | 0.06 | Mystus gulio | −0.17 | 0.13 | 0.13 | −0.35 | −0.51* | −0.68* | 0.46 | 0.68* | Arius arius | −0.30 | −0.33 | −0.33 | −0.56* | 0.47 | 0.40 | 0.34 | −0.44 | Tachysurus subrostratus | 0.30 | 0.38 | 0.38 | 0.52* | −0.11 | 0.03 | −0.19 | 0.07 | Valamugil cunnesius | 0.10 | 0.18 | 0.18 | 0.50* | −0.60* | −0.47 | −0.53* | 0.52* | Liza parsia | 0.27 | 0.12 | 0.12 | 0.63* | −0.21 | 0.04 | −0.64* | 0.13 | Elops machnata | 0.26 | −0.23 | −0.23 | 0.25 | 0.10 | 0.21 | −0.23 | −0.03 | Hyphorhampus improvis | 0.14 | −0.29 | −0.29 | 0.40 | −0.15 | 0.04 | −0.58* | 0.03 | Periophthalmus weberi | −0.39 | −0.06 | −0.06 | 0.22 | −0.12 | 0.02 | −0.54* | −0.24 | Glossogobius giuris | 0.23 | −0.17 | −0.17 | 0.52* | −0.15 | 0.07 | −0.58* | 0.12 | Anguilla bengalensis | 0.65* | 0.04 | 0.04 | 0.75** | −0.27 | −0.07 | −0.40 | 0.17 | Scylla serrata | −0.18 | 0.26 | 0.26 | 0.07 | −0.73** | −0.84** | −0.03 | 0.66* | Penaeus monodon | 0.10 | −0.44 | −0.44 | 0.35 | 0.02 | 0.19 | −0.41 | −0.03 | Penaeus indicus | 0.00 | −0.25 | −0.25 | −0.04 | 0.69* | 0.78** | −0.12 | −0.50* | Metapenaeus brevicornis | 0.10 | 0.24 | 0.24 | 0.52* | −0.18 | 0.05 | −0.61* | 0.12 | Metapenaeus dobsoni | 0.14 | −0.02 | −0.02 | 0.49 | −0.17 | 0.05 | −0.64* | 0.12 |
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Significant, **highly significant.
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