Amphipoda

Rousou, Maria, Plaiti, Wanda, Lowry, Jim, Charalambous, Stephanos & Chintiroglou, Chariton Charles, 2020, Amphipoda species (Suborders: Amphilochidea and Senticaudata) from Vasiliko Bay, Cyprus: New records, information on their biogeography and an annotated checklist from the coasts of Cyprus, Zootaxa 4896 (3), pp. 373-408 : 375-378

publication ID

https://doi.org/ 10.11646/zootaxa.4896.3.3

publication LSID

lsid:zoobank.org:pub:EE3E9D88-F406-475A-A9BC-6DD6C24AC79F

DOI

https://doi.org/10.5281/zenodo.4389345

persistent identifier

https://treatment.plazi.org/id/5C3887CE-FFD2-BB43-2FA5-2B290C7AFAE3

treatment provided by

Plazi

scientific name

Amphipoda
status

 

Amphipoda View in CoL abundances and diversity

A total of 45,721 fauna individuals were counted (42 stations, 3 replicas, 126 samples), of which 2,122 individuals were amphipods ( Amphilochidea and Senticaudata ) (4.64 % of total macrofauna abundance). The Amphipoda were classified into 25 families and 52 species. The family Aoridae presented the highest densities (851 individuals), contributing to 42 % of overall amphipod abundance and in conjunction with four other families ( Aoridae , Oedicerotidae , Ampeliscidae , Dexaminidae and Phoxocephalidae ) counting to 77 % of overall amphipod abundance ( Fig. 2 View FIGURE 2 ). The family Ischyroceridae was present with six species, followed by Aoridae and Oedicerotidae with five species ( Fig. 3 View FIGURE 3 ).

A total of 24 species is reported for the first time in Cyprus, increasing the number of Amphipoda from 117 to 141 species. Two species were found to be constant in Vasiliko Bay ( M. periergos , Perioculodes longimanus ), seven species were common ( Ampelisca brevicornis , Ampelisca typica , Apherusa chiereghinii , Dexamine spinosa , Harpinia crenulata , Leptocheirus pectinatus , Leucothoe incisa ) and 43 species considered as rare. The species M. periergos that was described for the first time from the same stations in Vasiliko Bay ( Myers et al. 2018) presented the highest densities (676 individuals, ~32 %), followed by the species P. longimanus (311 individuals, ~14.6 %).

The highest amphipod abundances (per 0.1 m 2) were recorded in station 17 (located near dense P. oceanica meadows), station14 (deepest limit of P. oceanica meadow, near a fish farm), stations 2 and 5 (near a fish farm) and station 37 (Vasiliko port entrance) ( Fig. 4 View FIGURE 4 ). The high abundance values can be attributed to the dense populations formed by the M. periergos (15–42 individuals / 0.1 m 2).

The number of amphipod species per station ranged between 1 and 15, while no amphipods were recorded at station 42. The Species Richness index presented similar trends to the abundance distribution with the higher values being recorded in stations 2, 5, 14, 17, as well as in stations 9 and 30 ( Fig. 5 View FIGURE 5 ). Low numbers of species were observed near ports and at stations 6 and 8 located west of the Cape Dolos. With regard to the Shannon-Wiener index, the highest diversity indices were recorded in the deepest sampling stations, far away from P. oceanica meadows (stations 18, 30, 31, 36, 41) as well as in stations 9 and 14 ( Fig. 6 View FIGURE 6 ).

Spearman correlation coefficient indicated that the Shannon-Wiener index was positively correlated with depth (0.33, p<0.05) ( Table 2). A negative correlation with depth was observed for species Bathyporeia guilliamsoniana and A. brevicornis (p<0.01) and a positive for the species Leucothoe lilljeborgi , Jassa ocia , Lysianassina longicornis , Ampithoe ramondi, D. Spinosa (p<0.05), Eriopisa elongata , Harpinia crenulata , Pereionotus testudo and Westwoodilla rectirostris (p<0.01) ( Table 2).

The species Pontocrates sp., Aora spinicornis , P. longimanus (p<0.05), B. guilliamsoniana , A. brevicornis and Guernea (Guernea) coalita (p<0.01) were negatively correlated with organic matter while the species Dexamine spiniventris , Peltocoxa gibbosa , W. rectirostris , (p<0.05), H. crenulata and L. longicornis (p<0.01) presented a positive correlation ( Table 2).

Information on the distribution and ecology of the amphipod species recorded in Vasiliko Bay, is provided below.

GBIF Dataset (for parent article) Darwin Core Archive (for parent article) View in SIBiLS Plain XML RDF