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 | 9 | 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.