Average Mantel correlation values comparing T-RFLP community composition and possible controlling factors within each stand, followed by number of stands with significant positive Mantel values. n = 3 stands per ecosystem, and n = 7–30 leaves per stand.
. | . | April . | . | . | August . | . |
---|---|---|---|---|---|---|
Ecosystem . | Prox. . | Leaf type . | Depth . | Prox. . | Leaf type . | Depth . |
BOWO | 0.22 (3) | 0.02 (1) | 0.04 (1) | 0.08 (1) | 0.06 (2) | −0.08 (0) |
SMBW | −0.04 (0) | 0.18 (3) | 0.1 (1) | 0.06 (1) | 0.26 (3) | 0.02 (0) |
SMRO | 0.08 (1) | 0.09 (1) | 0.05 (0) | 0.18 (2) | 0.13 (1) | 0.23 (2) |
. | . | April . | . | . | August . | . |
---|---|---|---|---|---|---|
Ecosystem . | Prox. . | Leaf type . | Depth . | Prox. . | Leaf type . | Depth . |
BOWO | 0.22 (3) | 0.02 (1) | 0.04 (1) | 0.08 (1) | 0.06 (2) | −0.08 (0) |
SMBW | −0.04 (0) | 0.18 (3) | 0.1 (1) | 0.06 (1) | 0.26 (3) | 0.02 (0) |
SMRO | 0.08 (1) | 0.09 (1) | 0.05 (0) | 0.18 (2) | 0.13 (1) | 0.23 (2) |
Average Mantel correlation values comparing T-RFLP community composition and possible controlling factors within each stand, followed by number of stands with significant positive Mantel values. n = 3 stands per ecosystem, and n = 7–30 leaves per stand.
. | . | April . | . | . | August . | . |
---|---|---|---|---|---|---|
Ecosystem . | Prox. . | Leaf type . | Depth . | Prox. . | Leaf type . | Depth . |
BOWO | 0.22 (3) | 0.02 (1) | 0.04 (1) | 0.08 (1) | 0.06 (2) | −0.08 (0) |
SMBW | −0.04 (0) | 0.18 (3) | 0.1 (1) | 0.06 (1) | 0.26 (3) | 0.02 (0) |
SMRO | 0.08 (1) | 0.09 (1) | 0.05 (0) | 0.18 (2) | 0.13 (1) | 0.23 (2) |
. | . | April . | . | . | August . | . |
---|---|---|---|---|---|---|
Ecosystem . | Prox. . | Leaf type . | Depth . | Prox. . | Leaf type . | Depth . |
BOWO | 0.22 (3) | 0.02 (1) | 0.04 (1) | 0.08 (1) | 0.06 (2) | −0.08 (0) |
SMBW | −0.04 (0) | 0.18 (3) | 0.1 (1) | 0.06 (1) | 0.26 (3) | 0.02 (0) |
SMRO | 0.08 (1) | 0.09 (1) | 0.05 (0) | 0.18 (2) | 0.13 (1) | 0.23 (2) |
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