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. 2018 Aug 30;48(6):539–551. doi: 10.1007/s13280-018-1088-x

Table 1.

Abiotic variables of the examined marinas and control areas. See Appendix S1 for method description

Variables Category Pairs t/F-valuesa p values
1 2 3 4 5 6 7
x¯ ± SE x¯ ± SE x¯ ± SE x¯ ± SE x¯ ± SE x¯ ± SE x¯ ± SE
Berths (no.) Marina 13 26 391 160 39 45 25
Control 1 1 9 3 2 0 0
Jetties (no.) Marina 6 6 11 13 7 6 4
Control 1 0 3 1 1 0 0
Water surface area (ha) Marina 4.38 5.66 8.52 9.74 2.07 3.40 3.02 0.47 0.655
Control 8.15 1.24 5.57 10.2 3.38 1.75 3.13
Water retention time (days) Marina 8.0 1.4 0.08 0.06 15.7 1.5 1.8 − 1.30 0.240
Control 15.1 0.4 0.02 0.11 25.6 1.6 1.0
Wave exposure (Log10 m2 s−1) Marina 3.1 3.4 3.3 3.4 3.2 4.6 3.2 − 1.41 0.209
Control 3.6 3.5 3.9 3.6 2.9 4.7 3.0
Maximum depth (m) Marina 3 6 20 6 3 3 3 1.00 0.356
Control 3 6 15 6 3 3 3
Sampling depth (m) Marina 1.5 ± 0.2 1.9 ± 0.2 1.5 ± 0.3 1.8 ± 0.1 1.3 ± 0.2 1.4 ± 0.2 1.2 ± 0.2 6.09 0.016
Control 1.7 ± 0.1 2.6 ± 0.2 1.7 ± 0.3 1.8 ± 0.2 2.2 ± 0.3 1.4 ± 0.2 1.5 ± 0.1
Salinity (PSU) Marina 6.6 ± < 0.1 4.8 ± < 0.1 4.8 ± < 0.1 5.4 ± < 0.1 5.2 ± < 0.1 6.1 ± < 0.1 5.5 ± < 0.1 1.68 0.242
Control 6.6 ± < 0.1 5.2 ± < 0.1 6.4 ± < 0.1 5.7 ± < 0.1 5.0 ± < 0.1 6.4 ± < 0.1 5.3 ± < 0.1
Total nitrogen conc. (µmol L−1) Marina 23.3 ± 0.9 20.7 ± 1.6 20.5 ± 1.0 19.9 ± 0.4 63.5 ± 1.8 21.3 ± 1.3 32.2 ± 2.1 1.14 0.326
Control 21.8 ± 0.8 20.5 ± 0.5 23.6 ± 0.4 19.1 ± 0.7 33.2 ± 0.8 22.7 ± 1.9 27.7 ± 0.9
Total phosphorous conc. (µmol L−1) Marina 0.90 ± 0.11 0.51 ± 0.05 0.59 ± 0.06 0.42 ± 0.02 3.48 ± 0.07 1.04 ± 0.09 1.73 ± 0.14 1.03b 0.350
Control 0.90 ± 0.05 0.49 ± 0.01 0.98 ± 0.01 0.54 ± 0.02 1.07 ± 0.02 0.80 ± 0.06 0.57 ± 0.02
Turbidity (NTU) Marina 2.7 ± 0.3 6.5 ± 0.1 4.9 ± 0.1 7.7 ± 0.1 5.3 ± 0.1 2.0 ± 0.1 2.8 ± 0.3 0.61b 0.464
Control 3.4 ± 0.2 2.6 ± 0.3 1.8 ± 0.1 1.7 ± 0.1 2.6 ± 0.6 2.5 ± 0.5 6.5 ± 0.1
Dominant substrate (> 90%) Marina M, ST, B, BR M, G M, SA M, SA M M, SA, G M 0.25 0.784
Control M M, G M, SA, ST M, SA, G, ST M, BR M, SA, ST M

M mud, SA sand, G gravel, ST stones, B boulders, BR bedrock

aDifferences between marina and control sites in area, retention time, wave exposure and maximum depth were tested with paired t-tests (inlets as replicates), while differences in sampling depth, salinity, nutrient concentrations and turbidity were tested with mixed effects models (stations as replicates), where the random factor inlet was nested within marina–control pairs. Differences in substrate composition were tested with a PERMANOVA with marina–control pairs as random strata

bTests were performed on log10-transformed values