The overall Time  × Treatment Protein Tyrosine Kinase inhibitor interaction was not significant (P = 0.06, Table 1). However, OC sites and MPA sites were similar to each other ‘Before’ towed demersal fishing was excluded and were significantly different to each other ‘After’ (P = 0.002, Table 1). Four of the six indicator sessile RAS (Ross coral P. fascialis, sea squirt P. mammillata,

Dead man’s fingers A. digitatum and branching sponges) significantly increased in Abundance from the ‘Before’ MPA to the ‘After’ MPA relative to Open Controls (P < 0.05; Fig. 6, Table 2). While pink sea fans (E. verrucosa) and hydroids showed an increasing trend over time, there was no significant Time  × Treatment interaction ( Fig. 5, Table 2). If protected from towed demersal fishing activity, sedimentary habitats between rocky reefs contribute to the reef ecosystem by supporting diverse epibenthic Assemblages. While some of the species observed here were characteristic of sediment habitats (mobile: sole Solea solea, common starfish Asterias rubens, common hermit crab P. bernhardus; sessile: parchment Worm, Chaetopterus variopedatus), some mobile or sessile species

observed on the pebbly sand are typically found on hard substratum (Reef Associated Species). Mobile RAS included brown crab (Cancer pagurus), that lives in rocky crevices, ballan wrasse (L. bergylta), cuckoo wrasse (L. mixtus) and goldsinny wrasse (Ctenolabrus rupestris) that are territorial around rocky habitats. Of particular relevance for this study, however, were the 24 observed sessile Selleckchem APO866 RAS, such as ross coral (P. fascialis), sea squirt (P. mammillata) and dead man’s fingers (A. digitatum). These ecosystem engineers give structural complexity to the sea bed, providing habitats that act as nurseries, protection from predation and safe settlement opportunities for larvae ( Bradshaw et al., 2003, Eggleston et al., 1990, Lima and Dill, 1990, Mittelbach, 1984 and Pirtle et al., 2012). P. fascialis, which plays a key role in the formation of biogenic reef nursery areas ( Cocito and Ferdeghini, C-X-C chemokine receptor type 7 (CXCR-7) 2001 and McKinney and Jackson, 1989), increased

by an average of 385% in the MPA over the three years following protection from towed demersal fishing. Branching sponges, which provide structural complexity for larval settlement and shelter from predators ( Auster, 1998, Auster et al., 1997, Auster et al., 1996 and Bradshaw et al., 2003), increased in Abundance by an average of 414% in the MPA. Hydroids also provide structure for larval settlement ( Bradshaw et al., 2001), and had a mean increase of 229% inside the MPA over time, though this was not statistically different to the controls due to high variability. Phallusia mammillata and A. digitatum, which also add structural complexity to benthic habitats, both significantly increased in Abundance over three years in the MPA (467% and 2541% respectively). Similarly, E.