The ecology of deep and shallow coral reefs : results of a workshop on coral reef ecology held by the American Society of Zoologists, Philadelphia, Pennsylvania, December 1983 ecologyofdeepsha00work Year: 1983 (29) Reef Flot Reef Slope! I -IOm) Reef Slope (30-40m) (39) (30) CARRIE BOW BELIZE LIGHTHOUSE BELIZE BECERRO HONDURAS ® CARRIE BOW, BELIZE (24h) i pjpiNa sanctae-cbuos 2 ACANTHOPHOBA SPEClFERA 3 LAURENCIA INTRICATA 4 HALIMEDA TUNA 5 LIAGORA Sp. 6 SABGASSUM POLfCEBATIUM 7 5TYP0P0DIUM ZONALE 8 CRYPTONEMIA CBENULATA 9 HALIMEDA OISCOIDEA 10 HALIMEDA GOBEAUII 11 BHIPOCEPHALUS PHOENIX 12 L0
The ecology of deep and shallow coral reefs : results of a workshop on coral reef ecology held by the American Society of Zoologists, Philadelphia, Pennsylvania, December 1983 ecologyofdeepsha00work Year: 1983 (29) Reef Flot Reef Slope! I -IOm) Reef Slope (30-40m) (39) (30) CARRIE BOW BELIZE LIGHTHOUSE BELIZE BECERRO HONDURAS ® CARRIE BOW, BELIZE (24h) i pjpiNa sanctae-cbuos 2 ACANTHOPHOBA SPEClFERA 3 LAURENCIA INTRICATA 4 HALIMEDA TUNA 5 LIAGORA Sp. 6 SABGASSUM POLfCEBATIUM 7 5TYP0P0DIUM ZONALE 8 CRYPTONEMIA CBENULATA 9 HALIMEDA OISCOIDEA 10 HALIMEDA GOBEAUII 11 BHIPOCEPHALUS PHOENIX 12 L080PH0BA VABIEGATA D LIGHTHOUSE, BELIZE (I9h) 1 LAUBENCIA PAPILLOSA 2 PADINA SANCTAE-CBUCIS 3 SABGASSUM POLrCEBATIUM 4 DIGENIA SIMPLEX 5 TUBBINABIA TBICOSTATA 6 L080PH0BA VABIEGATA 7 HALIMEDA COPIOSA 8 GELIDIELLA ACEBOSA 9 HALIMEDA TUNA 10 HALIMEDA GOBEAUII 11 HALIMEDA OPUNTIA 12 BHIPOCEPHALUS PHOENIX INDIVIDUALS EATEN () ) 20 40 60 80 100 SIGNIFICANTLY DIFFERENT FROM 1125) (191 1(10) ^2(ii) E3(iO) B3(37) 8(20) BliOl 0i2O) 3(20) H(i5) 3(19) 20 40 60 80 100 © BECERRO, HONDURAS () 0 20 40 60 BO I ACANTHOPHOBA SPICIFEBA 100 LAUBENCIA PAPILLOSA TUBBINABIA TRICOSTATA HALIMEOA OISCOIDEA HALIMEDA TUNA PADINA Sp BHIPOCEPHALUS OBLONGUS STTPOPODIUM 20NALE 4-12 4-12 4-12 -3 -3 -3 -3 -3 -3 -3 -3 -3 6- 6 6 8 8 1-3 1-3 1-5 1-5 I 12 12 12 12 12 11,12 11,12 11,12 12 5 8 â 9 REEF FLAT REEF SLOPE (I-IOm) , 2 . 2 - 3 - 3 -3 1REEF SLOPE (30-40m) Fig. 1. The mean of Thalassia eaten in different habitats on the 3 study reefs. Vertical lines represent + 2 standard errors. Numbers in parenthe- ses = N. At each reef, all differences are significant (p < .05, ANOVA and Newman-Keuls Test). Fig. 2. Percentage of individuals eaten when placed on the shallow reef slope. For Carrie Bow, numbers in parentheses = N. Significant differences (p < .05) were evaluated using Contingency Table Analysis or Fishers Exact Test (if cell sizes were small). Susceptibility to herbivory of seaweeds from
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