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. 2013 Jun 28;8(6):e67212. doi: 10.1371/journal.pone.0067212

Table 2. Concentration of polycyclic aromatic hydrocarbons, PAHs (µg L−1), in the water at the different crude oil exposure levels (5–100 µl L−1) used in the experiments.

[crude oil]µl L−1 [crude oil]mg L−1 Nap Ace Acy Flu Phe An Flua Pyr BaA Chr BbF
5 4.2 4.22 0.43 0.07 1.41 3.04 0.04 0.08 0.15 0.07 0.97 0.10
10 8.5 8.45 0.85 0.14 2.82 6.08 0.08 0.15 0.31 0.14 1.94 0.20
20 16.9 16.89 1.71 0.28 5.65 12.17 0.16 0.31 0.62 0.28 3.88 0.39
25 21.1 21.12 2.14 0.35 7.06 15.21 0.20 0.38 0.77 0.35 4.85 0.49
30 25.4 25.34 2.56 0.42 8.47 18.25 0.24 0.46 0.93 0.42 5.82 0.59
50 42.3 42.23 4.27 0.70 14.11 30.42 0.40 0.76 1.54 0.70 9.70 0.98
100 84.5 84.46 8.54 1.40 28.23 60.83 0.80 1.53 3.08 1.40 19.39 1.96

Concentration of PAHs was estimated from the oil added to the containers using the concentration of PAHs determined in the crude oil (Fig. 2) Crude oil exposure levels are also expressed in mg L−1 using a crude oil density of 0.845g/ml. Naphthalene (Nap), acenaphthene (Ace), acenaphthylene (Acy), fluorene (Flu), phenanthrene (Phe), anthracene (An), fluoranthene (Flua), pyrene (Pyr), benzo[a]anthracene (BaA), chrysene (Chr), benzo[b]fluoranthene (BbF).