1,957
Views
9
CrossRef citations to date
0
Altmetric
ORIGINAL ARTICLES

Red sea urchins (Echinus esculentus) and water flow influence epiphytic macroalgae density

, , , &
Pages 375-384 | Accepted 10 Jun 2014, Published online: 03 Nov 2014

Figures & data

Figure 1. Map showing the 636 stations with kelp (Laminaria hyperborea) recorded in northern Norway (Nordland County), from Salten in the south (southernmost station at 66.8°N) to the Lofoten area in the north (northernmost station at 68.6°N).
Figure 1. Map showing the 636 stations with kelp (Laminaria hyperborea) recorded in northern Norway (Nordland County), from Salten in the south (southernmost station at 66.8°N) to the Lofoten area in the north (northernmost station at 68.6°N).

Table I. Mean, standard deviation (SD), minimum and maximum values for the environmental variables used as predictors in the analyses.

Table II. Correlation matrix (Pearson's R) for the environmental variables.

Table III. Overview of the best models explaining the density of the epiphytic macroalgae on kelp (Laminaria hyperborea) stipes and the density of red sea urchins (Echinus esculentus). We present the models with ΔAICc < 4, i.e. the models receiving equally good support from the data (according to Burnham et al. Citation2011).

Figure 2. Partial response curves (with 95% confidence interval) showing the density of epiphytic macroalgae on kelp (Laminaria hyperborea) stipes against wave exposure at low, moderate and high maximum current speed levels (upper panel) and against maximum current speed at low, moderate and high wave exposure index levels (lower panel). Predictor variables were transformed to zero skewness at a 0–1 scale in order to achieve normally distributed residuals.
Figure 2. Partial response curves (with 95% confidence interval) showing the density of epiphytic macroalgae on kelp (Laminaria hyperborea) stipes against wave exposure at low, moderate and high maximum current speed levels (upper panel) and against maximum current speed at low, moderate and high wave exposure index levels (lower panel). Predictor variables were transformed to zero skewness at a 0–1 scale in order to achieve normally distributed residuals.
Figure 3. Partial response curves (with 95% confidence interval) showing the density of epiphytic macroalgae on kelp (Laminaria hyperborea) stipes (upper panel) and the density of red sea urchins (Echinus esculentus, lower panel), both plotted against depth in the southern, mid and northern regions of the study area. Predictor variables were transformed to zero skewness at a 0–1 scale in order to achieve normally distributed residuals.
Figure 3. Partial response curves (with 95% confidence interval) showing the density of epiphytic macroalgae on kelp (Laminaria hyperborea) stipes (upper panel) and the density of red sea urchins (Echinus esculentus, lower panel), both plotted against depth in the southern, mid and northern regions of the study area. Predictor variables were transformed to zero skewness at a 0–1 scale in order to achieve normally distributed residuals.
Figure 4. Partial response curves (with 95% confidence interval) showing the density of epiphytic macroalgae on kelp (Laminaria hyperborea) stipes against the density of red sea urchins (Echinus esculentus). Density classes are 0: absent, 1: single individuals, 2: scarce (∼2–3 ind.) and 3: common/moderately dense (∼4–6 ind.).
Figure 4. Partial response curves (with 95% confidence interval) showing the density of epiphytic macroalgae on kelp (Laminaria hyperborea) stipes against the density of red sea urchins (Echinus esculentus). Density classes are 0: absent, 1: single individuals, 2: scarce (∼2–3 ind.) and 3: common/moderately dense (∼4–6 ind.).