No significant differences
were found in the numbers of non-indigenous taxa between these habitats (P > 0.05); neither were there any significant differences in the abundance of macrofauna, both native and alien, between the various habitat types ( Figure 6b). The median abundance of native species for the whole study area was 11 553 indiv. m− 2, whereas that for alien species was 178 indiv. m− 2. The species occurring most commonly on the bottom of Puck Bay was G. tigrinus (frequency = 44%); the frequencies of two other non-indigenous taxa – Marenzelleria spp. and M. arenaria – were very MK-2206 similar (37 and 36% respectively). The frequency of P. antipodarum in the study area was 19%, but that of A. improvisus was only 7%. The amphipod G. tigrinus was present on the sandy unvegetated bottom (frequency of occurrence = 36%) but was far more common on sea beds overgrown with plants (> 50%) ( Figure 7). Its abundance on a sea bed covered with vascular plants or Chara spp. was also greater and differed significantly from that on a soft unvegetated sea bed (P < 0.05) ( Figure 8a). The median abundance on a sea bed covered with
vascular plants or Chara spp. was 44 indiv. m− 2, and the greatest abundance on such a vegetated sea bed was 6399 indiv. m− 2. In contrast, the polychaete Marenzelleria spp. displayed a clear preference for an unvegetated sandy bottom (frequency of occurrence = 51%). On a sea bed covered with algal mats the frequency of this species was 42%, but in localities covered by both PARP activation vascular plants and Chara spp. it did not exceed 25% ( Figure 7). The abundance of Marenzelleria spp. on a soft bottom was significantly greater than on bottoms with vascular plants or Chara spp. (P < 0.01). The median abundance in the first of these
habitat types was 44 indiv. m− 2. The respective maximum abundances on bottoms covered with algal mats, a soft sea bed, on a bottom covered with vascular plants and on one covered with Chara spp. were 2444 indiv. m− 2, Edoxaban 1866 indiv. m− 2, 578 indiv. m− 2 and 222 indiv. m− 2 ( Figure 8b). The frequency of occurrence of M. arenaria ranged from 31% on a soft unvegetated bottom to 41% on a vegetated one ( Figure 7). No significant differences were found between the abundances of this mollusc in the habitats investigated (P > 0.05) ( Figure 8c). The frequency of the mud snail P. antipodarum on a soft unvegetated bottom and on one covered with algal mats was 25%, whereas on a vegetated one it was no greater than 16% ( Figure 7). The difference in the abundances of P. antipodarum was greater and statistically significant (P < 0.05) only between a bottom without plant cover and one overgrown with Chara spp. ( Figure 8d). The barnacle A. improvisus was present in all the habitat types examined except on bottoms covered with algal mats.