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. 2019 Mar 16;76(4):657–669. doi: 10.1007/s00244-019-00617-w

Table 3.

Molecular diagnostic ratios and possible sources of PAHs in the water and sediment samples from Buffalo River Estuary

PAHs Petrogenic Pyrolytic Surface water Sediment
Anth/178 < 0.1 ≥ 0.1 0.01 ± 0.001 1.22 ± 0.33
Anth/Anth + Phen < 0.1 > 0.1 0.5 ± 0.07 0.44 ± 0.06
BaA/228 < 0.2 0.2–0.35 0.01 ± 0.002 0.98 ± 0.32
BaA/BaA + Chry < 0.2 0.2–0.35 0.52 ± 0.05 0.41 ± 0.06
Chry/BaA < 0.4 > 0.9 2.19 ± 0.62 3.09 ± 0.69
Flt/Pyr < 1.0 > 1.0 0.05 ± 0.03 1.67 ± 0.56
Flt/Flt + Pyr < 0.4 > 0.4 0.04 ± 0.02 0.4 ± 0.09
InPy/InPy + BghiP < 0.2 > 0.2 0.47 ± 0.06
LMW/HMW > 1.0 < 1.0 0.54 ± 0.91 0.42 ± 0.34
Phen/Anth > 15 < 10 0.61 ± 0.12 2.38 ± 0.91

Phen phenanthrene, Anth anthracene, Chry chrysene, BaA benzo[a]anthracene, Flt fluoranthene, Pyr pyrene, InPy indeno(123,cd)pyrene, BghiP benzo[g,h,i]perylene, LMW low molecular weight, HMW high molecular weight (Moyo et al. 2013; Adeniji et al. 2018a, b)