Changes
On February 8, 2023 at 3:18:58 PM UTC, prod:
-
Changed value of field
datastore_active
toTrue
in resource export_data_1675869511.csv in Radiological analysis of 40K, 226Ra and 232Th in fish, crustacean and sediment samples from fresh and marine water in oil exploration area of Ondo State, Nigeria -
Changed value of field
validation_status
tofailure
in resource export_data_1675869511.csv in Radiological analysis of 40K, 226Ra and 232Th in fish, crustacean and sediment samples from fresh and marine water in oil exploration area of Ondo State, Nigeria -
Changed value of field
validation_timestamp
to2023-02-08T15:18:57.314543
in resource export_data_1675869511.csv in Radiological analysis of 40K, 226Ra and 232Th in fish, crustacean and sediment samples from fresh and marine water in oil exploration area of Ondo State, Nigeria
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8 | "author": "Ademola, J. A.; Ehiedu, S. I.;", | 8 | "author": "Ademola, J. A.; Ehiedu, S. I.;", | ||
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20 | "metadata_modified": "2023-02-08T15:18:52.234078", | 20 | "metadata_modified": "2023-02-08T15:18:52.234078", | ||
21 | "name": "radiological-analysis-of-40k-226ra-and-232th-in-fish", | 21 | "name": "radiological-analysis-of-40k-226ra-and-232th-in-fish", | ||
22 | "notes": "Radiological analysis was carried out on fish, crustacean | 22 | "notes": "Radiological analysis was carried out on fish, crustacean | ||
23 | and sediment samples collected from both fresh and marine water of | 23 | and sediment samples collected from both fresh and marine water of | ||
24 | river Igbokoda in the coastal area of Ondo State, Nigeria. The | 24 | river Igbokoda in the coastal area of Ondo State, Nigeria. The | ||
25 | activity concentrations of radionuclides were determined using gamma | 25 | activity concentrations of radionuclides were determined using gamma | ||
26 | spectrometry method. The means of the annual effective ingestion dose | 26 | spectrometry method. The means of the annual effective ingestion dose | ||
27 | varied between 23.3 \u00b1 10.2 \u03bcSv.y-1 | 27 | varied between 23.3 \u00b1 10.2 \u03bcSv.y-1 | ||
28 | (OreochromisniloticusandGymnarchusniloticus) and 34.8 \u00b1 1.7 | 28 | (OreochromisniloticusandGymnarchusniloticus) and 34.8 \u00b1 1.7 | ||
29 | \u03bcSv.y-1 (Parachnnaobscura) for fresh water fish samples and 6.4 | 29 | \u03bcSv.y-1 (Parachnnaobscura) for fresh water fish samples and 6.4 | ||
30 | \u00b1 0.7 \u03bcSv.y-1 (Chrysithctysnigrodigitatus) and 14.2 \u00b1 | 30 | \u00b1 0.7 \u03bcSv.y-1 (Chrysithctysnigrodigitatus) and 14.2 \u00b1 | ||
31 | 1.6 \u03bcSv.y-1 (Cynoglossussenegalensis) for marine water fish | 31 | 1.6 \u03bcSv.y-1 (Cynoglossussenegalensis) for marine water fish | ||
32 | samples. That of the crustacean samples (Peanusmonodon) was 2.4 \u00b1 | 32 | samples. That of the crustacean samples (Peanusmonodon) was 2.4 \u00b1 | ||
33 | 0.2 \u03bcSv.y-1. The equivalent dose to the skin of humans from | 33 | 0.2 \u03bcSv.y-1. The equivalent dose to the skin of humans from | ||
34 | contact with sediment was 2.0 \u03bcSv.y-1 and 1.2 \u03bcSv.y-1 for | 34 | contact with sediment was 2.0 \u03bcSv.y-1 and 1.2 \u03bcSv.y-1 for | ||
35 | the fresh and marine water sediments, respectively. The effective dose | 35 | the fresh and marine water sediments, respectively. The effective dose | ||
36 | was calculated as 0.010 \u03bcSv.y-1 and 0.006 \u03bcSv.y-1 for the | 36 | was calculated as 0.010 \u03bcSv.y-1 and 0.006 \u03bcSv.y-1 for the | ||
37 | fresh and marine water sediments, respectively. The equivalent doses | 37 | fresh and marine water sediments, respectively. The equivalent doses | ||
38 | obtained are less than the ICRP recommended 50mSv per annum for the | 38 | obtained are less than the ICRP recommended 50mSv per annum for the | ||
39 | public.", | 39 | public.", | ||
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43 | "approval_status": "approved", | 43 | "approval_status": "approved", | ||
44 | "created": "2023-02-06T08:37:57.637524", | 44 | "created": "2023-02-06T08:37:57.637524", | ||
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54 | "title": "The International Atomic Energy Agency", | 54 | "title": "The International Atomic Energy Agency", | ||
55 | "type": "organization" | 55 | "type": "organization" | ||
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58 | "preferred_form_of_citation": "IAEA MARIS, 2023. IAEA Marine | 58 | "preferred_form_of_citation": "IAEA MARIS, 2023. IAEA Marine | ||
59 | Radioactivity Information System. In: Division of IAEA Environment | 59 | Radioactivity Information System. In: Division of IAEA Environment | ||
60 | Laboratories [online]. Monaco. [Cited DATE] https://maris.iaea.org", | 60 | Laboratories [online]. Monaco. [Cited DATE] https://maris.iaea.org", | ||
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129 | "state": "active", | 129 | "state": "active", | ||
130 | "tags": [], | 130 | "tags": [], | ||
131 | "title": "Radiological analysis of 40K, 226Ra and 232Th in fish, | 131 | "title": "Radiological analysis of 40K, 226Ra and 232Th in fish, | ||
132 | crustacean and sediment samples from fresh and marine water in oil | 132 | crustacean and sediment samples from fresh and marine water in oil | ||
133 | exploration area of Ondo State, Nigeria", | 133 | exploration area of Ondo State, Nigeria", | ||
134 | "type": "dataset", | 134 | "type": "dataset", | ||
135 | "update_frequency": "ad-hoc", | 135 | "update_frequency": "ad-hoc", | ||
136 | "url": "https://maris.iaea.org/datasets", | 136 | "url": "https://maris.iaea.org/datasets", | ||
137 | "version": "1.0" | 137 | "version": "1.0" | ||
138 | } | 138 | } |