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  • Baseline PAHs, N-PAHs and 210Pb in Segment Samples from Bodo Creek

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Baseline PAHs, N-PAHs and 210Pb in Segment Samples from Bodo Creek: Comparison with Bonny Estuary, Niger Delta

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Baseline PAHs, N-PAHs and 210Pb in Segment Samples from Bodo Creek: Comparison with Bonny Estuary, Niger Delta. / Anyanwu, I.N.; Sikoki, F.D.; Semple, K.T.
In: Water, Air, and Soil Pollution, Vol. 232, No. 9, 366, 28.08.2021.

Research output: Contribution to Journal/MagazineJournal articlepeer-review

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Anyanwu IN, Sikoki FD, Semple KT. Baseline PAHs, N-PAHs and 210Pb in Segment Samples from Bodo Creek: Comparison with Bonny Estuary, Niger Delta. Water, Air, and Soil Pollution. 2021 Aug 28;232(9):366. doi: 10.1007/s11270-021-05316-8

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Anyanwu, I.N. ; Sikoki, F.D. ; Semple, K.T. / Baseline PAHs, N-PAHs and 210Pb in Segment Samples from Bodo Creek : Comparison with Bonny Estuary, Niger Delta. In: Water, Air, and Soil Pollution. 2021 ; Vol. 232, No. 9.

Bibtex

@article{dde61ab02e6e4854b17b6aa2cc339079,
title = "Baseline PAHs, N-PAHs and 210Pb in Segment Samples from Bodo Creek: Comparison with Bonny Estuary, Niger Delta",
abstract = "Polycyclic aromatic hydrocarbons (PAHs), the nitrogen-containing analogues (N-PAHs) and lead 210 (210Pb) were measured in 2-cm interval core segments from Bodo Creek to evaluate impact of oil pollution in the waterbody. PAHs and N-PAHs were measured by gas chromatography analysis with mass spectrometry detection, and 210Pb activity concentration was determined by alpha spectrometry measurement. Data shows that ƩPAHs and ƩN-PAHs ranged from 12,774.3–18,470.2 µg/kg and 524.0–672.2 µg/kg, respectively. Concentrations were found to increase with increase in depth (cm). Petrogenic PAHs predominated the surface sediment (with elevated levels of 2,3,6-trimethyl-naphthalene, phenanthrene and 1-methyl-phenanthrene), while pyrogenic-PAHs dominated the deeper segments (with high levels of pyrene, benzo[a]anthracene, chrysene and benzo[k]fluoranthene). For N-PAHs, benzo[h]quinoline, 4,7-phenanthroline and benzo[a]acridine recorded high values. Chemicals comparison with values measured from Bonny Estuary revealed greater PAHs contamination in the estuary, while N-PAHs recorded elevated values in the creek. 210Pb activity concentration in the creek showed relatively low activity compared to the estuary, and similar distribution with the aromatic hydrocarbons. The measured hydrocarbons were high and exceeded the Canadian sediment quality guidelines. However, there are concerns over toxic ratios > 70% and radioactivity (EPR-D-values) > 3 – 4.E ± 01 Bq measured in the polluted creek. This gives insight on the level of radioactivity, PAHs, N-PAHs and PAHs toxic ratios in Bodo creek which would be useful in future remediation studies and/or monitoring the ability of sediments to recover under natural conditions.  ",
keywords = "210Pb, Bodo Creek, Bonny Estuary, N-PAHs, Niger Delta, PAHs, Toxic ratios, Anthracene, Gas chromatography, Mass spectrometry, Mineral oils, Radiation, Radioactivity, Sediments, Water pollution, Activity concentration, Alpha spectrometry, Benzo[a]anthracene, Benzo[h]quinoline, Gas chromatography analysis, Natural conditions, Polycyclic aromatic hydrocarbons (PAHS), Sediment quality guidelines, Estuaries",
author = "I.N. Anyanwu and F.D. Sikoki and K.T. Semple",
note = "The final publication is available at Springer via http://dx.doi.org/10.1007/s11270-021-05316-8",
year = "2021",
month = aug,
day = "28",
doi = "10.1007/s11270-021-05316-8",
language = "English",
volume = "232",
journal = "Water, Air, and Soil Pollution",
issn = "0049-6979",
publisher = "Springer Netherlands",
number = "9",

}

RIS

TY - JOUR

T1 - Baseline PAHs, N-PAHs and 210Pb in Segment Samples from Bodo Creek

T2 - Comparison with Bonny Estuary, Niger Delta

AU - Anyanwu, I.N.

AU - Sikoki, F.D.

AU - Semple, K.T.

N1 - The final publication is available at Springer via http://dx.doi.org/10.1007/s11270-021-05316-8

PY - 2021/8/28

Y1 - 2021/8/28

N2 - Polycyclic aromatic hydrocarbons (PAHs), the nitrogen-containing analogues (N-PAHs) and lead 210 (210Pb) were measured in 2-cm interval core segments from Bodo Creek to evaluate impact of oil pollution in the waterbody. PAHs and N-PAHs were measured by gas chromatography analysis with mass spectrometry detection, and 210Pb activity concentration was determined by alpha spectrometry measurement. Data shows that ƩPAHs and ƩN-PAHs ranged from 12,774.3–18,470.2 µg/kg and 524.0–672.2 µg/kg, respectively. Concentrations were found to increase with increase in depth (cm). Petrogenic PAHs predominated the surface sediment (with elevated levels of 2,3,6-trimethyl-naphthalene, phenanthrene and 1-methyl-phenanthrene), while pyrogenic-PAHs dominated the deeper segments (with high levels of pyrene, benzo[a]anthracene, chrysene and benzo[k]fluoranthene). For N-PAHs, benzo[h]quinoline, 4,7-phenanthroline and benzo[a]acridine recorded high values. Chemicals comparison with values measured from Bonny Estuary revealed greater PAHs contamination in the estuary, while N-PAHs recorded elevated values in the creek. 210Pb activity concentration in the creek showed relatively low activity compared to the estuary, and similar distribution with the aromatic hydrocarbons. The measured hydrocarbons were high and exceeded the Canadian sediment quality guidelines. However, there are concerns over toxic ratios > 70% and radioactivity (EPR-D-values) > 3 – 4.E ± 01 Bq measured in the polluted creek. This gives insight on the level of radioactivity, PAHs, N-PAHs and PAHs toxic ratios in Bodo creek which would be useful in future remediation studies and/or monitoring the ability of sediments to recover under natural conditions.  

AB - Polycyclic aromatic hydrocarbons (PAHs), the nitrogen-containing analogues (N-PAHs) and lead 210 (210Pb) were measured in 2-cm interval core segments from Bodo Creek to evaluate impact of oil pollution in the waterbody. PAHs and N-PAHs were measured by gas chromatography analysis with mass spectrometry detection, and 210Pb activity concentration was determined by alpha spectrometry measurement. Data shows that ƩPAHs and ƩN-PAHs ranged from 12,774.3–18,470.2 µg/kg and 524.0–672.2 µg/kg, respectively. Concentrations were found to increase with increase in depth (cm). Petrogenic PAHs predominated the surface sediment (with elevated levels of 2,3,6-trimethyl-naphthalene, phenanthrene and 1-methyl-phenanthrene), while pyrogenic-PAHs dominated the deeper segments (with high levels of pyrene, benzo[a]anthracene, chrysene and benzo[k]fluoranthene). For N-PAHs, benzo[h]quinoline, 4,7-phenanthroline and benzo[a]acridine recorded high values. Chemicals comparison with values measured from Bonny Estuary revealed greater PAHs contamination in the estuary, while N-PAHs recorded elevated values in the creek. 210Pb activity concentration in the creek showed relatively low activity compared to the estuary, and similar distribution with the aromatic hydrocarbons. The measured hydrocarbons were high and exceeded the Canadian sediment quality guidelines. However, there are concerns over toxic ratios > 70% and radioactivity (EPR-D-values) > 3 – 4.E ± 01 Bq measured in the polluted creek. This gives insight on the level of radioactivity, PAHs, N-PAHs and PAHs toxic ratios in Bodo creek which would be useful in future remediation studies and/or monitoring the ability of sediments to recover under natural conditions.  

KW - 210Pb

KW - Bodo Creek

KW - Bonny Estuary

KW - N-PAHs

KW - Niger Delta

KW - PAHs

KW - Toxic ratios

KW - Anthracene

KW - Gas chromatography

KW - Mass spectrometry

KW - Mineral oils

KW - Radiation

KW - Radioactivity

KW - Sediments

KW - Water pollution

KW - Activity concentration

KW - Alpha spectrometry

KW - Benzo[a]anthracene

KW - Benzo[h]quinoline

KW - Gas chromatography analysis

KW - Natural conditions

KW - Polycyclic aromatic hydrocarbons (PAHS)

KW - Sediment quality guidelines

KW - Estuaries

U2 - 10.1007/s11270-021-05316-8

DO - 10.1007/s11270-021-05316-8

M3 - Journal article

VL - 232

JO - Water, Air, and Soil Pollution

JF - Water, Air, and Soil Pollution

SN - 0049-6979

IS - 9

M1 - 366

ER -