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. 2016 Feb 19;6:21153. doi: 10.1038/srep21153

Table 3. Concentrations of TPAH (ΣBTEX + ΣPAHs) that inhibit 50% (IC50) and 10% (IC10) metamorphosis of coral and sponge larvae (95% CV intervals) calculated from dose-response curves presented in Figs 1 and 3.

  Coral condensate Sponge condensate Coral
−UV +UV −UV +UV Benzene Toluene Xylene Naphthalene
IC50 339a 132b ~16,000 ~13,000 80,351 15,559 3,939 2,077
  (271–424) (118–148) (NA) (NA) (70,661–91,369) (13,054–18,543) (3423–4532) (1694–2548)
IC10 103 64 NA NA 31,087 8,282 2,160 1,285
  (63–168) (49–84) (NA) (NA) (23,508–41,109) (5,416–12,666) (1,576–2,960) (797–2,070)
R2 0.871 0.943 0.833 0.867 0.920 0.831 0.891 0.733
NOEC 180 63 11,000 11,000 34,000 15,000 4,800 1,900
LOEC 350 130 23,000 23,000 69,000 30,000 9,600 3,800
ANOVA F9 34.6 52.3 26.9 26.9 61.4 33.3 46.4 27.3
Meta. (%) in controls 79 75 82 90 84 70 76 67
(±4) (±5) (±6) (±5) (±4) (±4) (±4) (±4)

Different superscripted letters indicate statistically different IC50 values for condensate toxicity to coral larvae (F1,120 = 29.2, p < 0.0001). Estimates of the IC50s for sponge larval metamorphosis were made from limited data points on the slopes of the curves and IC10s were not calculated for that reason (NA). No significant observed effect concentrations (NOEC) and lowest significant observed effect concentrations (LOEC) are reported (one-way ANOVA, p < 0.05). Meta. = mean metamorphosis of control larvae in uncontaminated conditions ( ± SE).