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. 1998 Dec 8;95(25):14843–14847. doi: 10.1073/pnas.95.25.14843

Table 1.

Mean diversity for forested and agricultural streams in the Little Tennessee and French Broad Rivers

Diversity indices Forest (L. Tennessee) Forest (Fr. Broad) Agriculture (L. Tennessee) Agriculture (Fr. Broad) Land use
River basin
F P F P
Invertebrates
 Taxonomic richness 59.3  ±  3.6 59.7  ±  7.9 48.7  ±  3.6 39.0  ±  5.4 8.25 ∗∗ 0.73 n.s.
 Margalef’s index 7.9  ±  0.4 8.1  ±  0.9 6.2  ±  0.4 5.2  ±  0.6 12.86 ∗∗ 0.46 n.s.
 EPT 40.5  ±  3.4 45.2  ±  6.7 32.0  ±  3.4 25.0  ±  4.4 9.34 ∗∗ 0.06 n.s.
 NCBI 2.7  ±  0.1 2.5  ±  0.1 3.3  ±  0.2 3.4  ±  0.2 28.14 ∗∗ 0.02 n.s.
 Invertebrate  density 1858  ±  496 1441  ±  211 2635  ±  758 3015  ±  1958 1.17 n.s. 0.01 n.s.
Fishes
 Species richness 14.5  ±  3.3 11.7  ±  1.7 23.2  ±  1.2 16.8  ±  2.3 9.22 ∗∗ 4.56
 Margalef’s index 4.4  ±  0.9 3.7  ±  0.5 6.7  ±  0.4 4.7  ±  0.6 6.33 4.04 n.s.
 Fish abundance 1096  ±  256 757  ±  149 2212  ±  354 1772  ±  377 12.76 ∗∗ 1.70 n.s.
Fish + invertebrate
 Species richness 73.8  ±  4.3 71.3  ±  7.2 71.8  ±  3.3 56.2  ±  7.2 2.21 n.s. 2.48 n.s.

Mean diversities are given ±SE (n = 6). Results of two-way ANOVA are shown, with Tukey’s test for land use (all forest vs. agriculture combined) and river basin (all Little Tennessee vs. French Broad) treatments. (∗, P < 0.05; ∗∗, P < 0.01; n.s., not significant; NCBI, North Carolina Biotic Index.)