Tidal Zonation of Periwinkles
How does the abundance of marine molluscs vary across tidal zones?
Hypothesis
Null: There will be no significant difference in mollusc abundance across the 3 tidal zones. Alternative: Mollusc abundance in the high intertidal zone will be significantly higher than in the low intertidal zone, reflected by significant correlations with abiotic variables.
Results
Discussion
The alternative hypothesis was not supported by our model, as there was no significant zonation of mollusc abundance [Table 2]. This is likely due to landscape heterogeneity [Fig. 1]. However, H-sites were environmentally distinct from L-sites; the former significantly colder, deeper, and lower in altitude than the latter [Fig. 2, Table 2.]. GLMs found a significant negative correlation between mollusc abundance and temperature [Table 3.] and regression analysis revealed a significant negative correlation between abundance and elevation, indicating H-sites were preferential [Fig. 3]. Although species were not identified, the vast majority were periwinkles (Littorinidae) which are found to dominate high intertidal zones (Wickramasinghe et al., 2021). However, research finds they are absent in subtidal beds where submersion is permanent (Saier, 2000), and actively select the mid-intertidal (Apolinario et al., 1999), contradicting our findings. This suggests a bell curve gradient should be found; quadratic regression may have been more appropriate than linear models in this case. Periwinkle abundance was measured by shell count, but this does not indicate organism presence. Future experiments should check for a foot to confirm presence. Moreover, existing literature suggests rock characteristics affect periwinkle density, which was not integrated in our models. Rugosity and % bare rock were positively correlated with abundance (Carlson et al., 2006), indicating preferences for rough surfaces onto which they can firmly latch, withstanding waves in the middle-low intertidal zones. Our experiment highlights how mollusc zonation is impacted by landscape heterogeneity during low tide, where intertidal zones are exposed to abiotic changes (e.g. temperature, salinity, water depth). Further research should assess marine molluscs’ microhabitat preferences to comprehensively predict how population densities may shift under the growing threat of climate change, so preemptive decisions can be made regarding their conservation (eg. artificial rock introduction to increase pooled habitat availability in the mid intertidal zone).
References
Apolinario, M., Coutinho, R. and Baeta-Neves, M.H. (1999). Periwinkle (Gastropoda: Littorinidae) habitat selection and its impact upon microalgal populations. Revista Brasileira de Biologia, 59(2), pp.211–218. doi:https://doi.org/10.1590/s0034-71081999000200005.
Carlson, R.L., Shulman, M.J. and Ellis, J.C. (2006). Factors Contributing to Spatial Heterogeneity in the Abundance of the Common Periwinkle Littorina Littorea (.L). Journal of Molluscan Studies, 72(2), pp.149–156. doi:https://doi.org/10.1093/mollus/eyi059.
Saier, B. (2000). Age-dependent zonation of the periwinkle Littorina littorea (L.) in the Wadden Sea. Helgoland Marine Research, 54(4), pp.224–229. doi:https://doi.org/10.1007/s101520000054.
Wickramasinghe, M.P., Sudarshani, K.A.M. and Wegiriya, H.C.E. (2021). The diversity of marine invertebrate macrofauna in selected rocky intertidal zones of Matara, Sri Lanka. Asian Journal of Conservation Biology, 10(1), pp.15–21. doi:https://doi.org/10.53562/ajcb.ozdk5526.