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. 2016 Oct 28;11(10):e0165513. doi: 10.1371/journal.pone.0165513

Table 1. The ecological summary statistics of the nine Cobb Seamount communities identified by the present study.

Frequency of occurrence Importance ranking
Community 1 2 3 4 5 6 7 8 1 2 3 4 5 6 7 8 9
n 11 52 120 68 81 82 301 427 489 11 52 120 68 81 82 301 427 489
Ochrophyta                                    
  Desmarestia viridis 46 0 0 0 0 0 0 0 0 7 35 37 37 35 43      
Rhodophyta                                    
  Corallinales spp. 100 100 24 0 9 0 0 0 0 12 2 45 5 8 7      
Porifera                                    
  cf Acarnus erithacus 55 8 0 0 0 0 0 0 0 8 16 26 23 21 29      
  Auletta sp. 0 0 3 2 1 0 0 0 0 40 30 25 44 45 37      
  Demospongiae sp. 0 37 1 2 0 0 0 0 0 32 5 22 22 15 23      
  Farrea occa 0 0 0 0 0 0 0 7 1             16 11 16
  Halichondria panacea 9 58 23 4 1 0 0 0 0 38 6 17 10 6 11      
  Rossellidae spp. 0 0 0 0 0 0 3 19 3             13 4 11
Cnidaria                                    
  Actiniaria sp. 0 0 0 0 0 0 35 0 0             2 6 6
  Anthoptilum spp. 0 0 0 0 0 0 1 3 15             10 18 7
  Bathypathes sp. 0   0 0 0 0 12 2 41             12 3 2
  Corynactis californica 91 0 0 0 0 0 0 0 0 1 25 27 24 22 30      
  Desmophyllum dianthus 0 2 31 6 9 0 0 2 0 22 19 6 19 39 12 26 24 22
  Gersemia sp. 0 0 0 0 0 0 0 3 0             20 15 17
  Halipteris willemoesi 0 0 0 12 0 15 0 0 0 33 22 18 9 16 10 0 0 0
  Heteropolypus ritteri 0 0 0 0 0 0 5 7 27             7 12 5
  cf Hormathiidae sp. 0 0 0 0 0 0 0 4 0             21 13 15
  Isididae spp. 0 0 0 0 0 0 1 34 9             5 2 12
  Lillipathes cf lillei 0 0 0 0 0 0 2 6 38             4 5 1
  Pennatulacea sp. 0 0 0 0 0 0 4 3 1             23 33 23
  Primnoidae spp. 0 0 0 0 0 0 0 25 1             6 1 8
  Stichopathes sp. 0 0 0 0 0 0 1 7 3             15 17 28
  Stomphia didemon 0 39 0 0 0 0 0 0 0 34 4 19 17 17 25      
  Stylaster spp. 0 14 98 13 93 1 0 4 0 13 7 1 3 1 3 24 14 14
  Swiftia simplex 0 0 0 0 0 0 0 4 1             17 19 27
Annelida                                    
  Paradexiospira sp. 9 0 32 12 1 1 0 0 0 43 14 4 43 10 17      
  Phyllochaetopterus prolifica 55 0 0 0 0 0 0 0 0 6 34 34 35 32 41      
  Protula pacifica 9 52 54 18 3 0 0 0 0 20 9 3 20 3 5      
  Spiochaetopterus costarum 9 12 3 54 1 50 0 0 0 27 20 8 2 4 4      
Arthropoda                                    
  Chionocetes tanneri 0 0 0 0 0 0 18 3 13             9 10 26
  Chirostylidae sp. 0 0 0 0 0 0 8 40 46             3 25 10
  Chorilia longipes 28 4 1 0 1 0 0 1 1 11 24 40 30 44 34 29 34 29
  Lithodes cousei 0 0 0 0 0 0 1 2 1             34 31 32
  Pargurus kennerlyi 0 19 22 32 77 72 0 0 0 15 12 9 18 2 6      
Mollusca                                    
  Calliostoma spp. 18 0 0 0 0 0 0 0 0 2 26 28 36 23 31      
  Crassadoma gigantean 55 0 0 0 0 0 0 0 0 4 32 32 33 30 39      
  Fusitriton oregonensis 0 8 12 3 5 0 0 0 0 30 38 14 32 43 21      
  Leptochiton rugatus 55 0 0 0 0 0 0 0 0 5 33 33 34 31 40      
  Tritoniidae spp. 0 0 0 0 0 0 0 1 1             27 29 31
Brachiopoda                                    
  Laqueus californianus 0 35 33 91 14 26 0 0 0 16 42 39 1 5 24      
Bryozoa                                    
  cf Reginella hippocrepis 27 6 0 0 0 0 0 0 0 10 15 35 36 33 42      
Echinodermata                                    
  Ampheraster sp. 0 0 0 0 0 0 3 1 2             30 28 35
  Apostichopus leukothele 0 14 23 12 9 1 0 0 0 21 44 10 42 34 15      
  Asteronyx loveni 0 0 0 6 0 45 0 0 0 26 17 11 29 9 2      
  Brisingidae sp. 0 0 0 0 0 0 0 0 8             14 21 9
  Ceramaster patagon 0 0 4 2 0 0 0 0 0 41 31 16 45 29 38      
  Florometra serratissima 27 64 0 2 1 1 1 4 0 17 1 12 13 13 19 28 20 18
  Henricia sanguine 0 6 6 2 1 0 0 0 0 37 23 24 39 37 27      
  Hippasteria phrygiana 0 0 0 2 0 0 1 2 0 45 41 41 14 42 45 33 26 19
  Mesocentrotus franciscanus 64 0 0 0 0 0 0 0 0 3 28 31 31 27 35      
  Ophiopholis bakeri a 0 10 37 0 0 0 0 0 0 23 39 2 7 7 13      
  Ophiura sarsii 0 0 2 2 21 94 0 0 0 18 11 7 6 40 1      
  Pannychia cf moseleyi 0 0 0 0 0 0 33 50 43             11 23 34
  Pseudarchaster sp. 0 0 0 0 0 0 1 6 0             19 8 13
  Psolus squamatus 0 0 0 0 0 0 4 3 27             8 7 4
  Pteraster sp. 0 0 0 0 0 0 0 1 1             31 32 33
  Rathbunaster californicus 0 2 8 2 1 7 0 2 0 35 229 823 227 120 36 25 22 21
  Stronglocentrotus pallidus 0 0 6 0 1 0 0 0 0 39 27 13 28 41 33      
  Thrissacanth sp. 0 0 0 0 0 0 0 3 0             22 16 20
Chordata                                    
  Antimora microlpis 0 0 0 0 0 0 0 1 0             35 30 30
  Ascidiacea sp. 1 (cream) 27 10 30 0 4 0 0 0 0 19 40 5 8 14 14      
  Ascidiacea sp. 2 (white) 18 8 3 0 1 0 0 0 0 14 18 42 21 38 28      
  cf Coryphaenoides acrolepis 0 0 0 0 0 0 7 4 3             18 35 24
  Cottidae sp. 0 12 8 3 6 26 0 0 0 24 43 38 15 25 9      
  Embassichthys bathybius 0 0 0 0 0 0 1 2 0             32 27 25
  Sebastes aleutianusb 0 2 3 15 1 0 0 0 0 36 37 43 4 26 26      
  Sebastes alutus 0 0 3 2 0 0 0 0 0 42 36 21 41 36 44      
  Sebastes emphaeus 0 27 14 15 1 0 0 0 0 25 10 30 25 11 16      
  Sebastes helvomaculatus 18 39 26 18 28 0 0 0 0 44 13 36 38 19 8      
  Sebastes rosaceus 36 2 2 2 0 0 0 0 0 9 45 44 40 24 32      
  Sebastes variegatus 0 0 10 12 3 0 0 0 0 31 21 20 11 28 22      
  Sebastes wilsoni 0 50 4 2 0 0 0 0 0 28 3 29 16 12 18      
  Sebastes zacentrus 0 23 13 0 3 0 0 0 0 29 8 15 12 18 20      
  Sebatolobus alascanus 0 0 0 0 0 0 85 19 7             1 9 3

For each community, the frequency of occurrence of benthic megafauna was calculated as the percentage of images in which the taxon was present (0% = absent, 100% = always present). The rank order of taxa importance for a community was assigned by the cluster analyses (1 = most important, no ranking = not included in the clustering process). The clustering of communities 1 to 6 and 7 to 9 considered 45 and 35 taxa respectively (which are therefore the lowest possible ranking values for those communities).

a O. bakeri was sparsely observed and inconsistently resolvable in AUV images but was observed in easily dense, resolvable patches in the ROV images. O. bakeri was therefore included in the ROV dataset but excluded from the AUV dataset.

b S. aleutianus and S. melanostictus are indistinguishable from images and these two species are recorded as one taxon.