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1.
Mar Pollut Bull ; 164: 112033, 2021 Mar.
Article in English | MEDLINE | ID: mdl-33515826

ABSTRACT

Baseline study of natural (7Be, 210Pb, 226Ra, 234Th, 228Ra, 40K) and anthropogenic (137Cs) radionuclides was carried out in two cores collected from Sabaki River estuary (Kenya, Indian Ocean). There was no exponential decrease of excess 210Pb down the cores, which did not allow dating and determination of heavy metal pollution history. The use of 137Cs as a time marker was not possible due to its low fallout rates in East Africa. The short-lived radioisotope 7Be, a tracer of river floods, confirmed 2018 flood in Sabaki River estuary. Heavy metal concentration in the two cores showed nonsystematic trends with depth. Only Pb concentration in Sabaki River estuary was higher than the background levels. Application of the "Environmental Risk from Ionising Contaminants Assessment and management" (ERICA) tool confirmed that the potential dose rates to biota from the sediment radioactivity concentrations are unlikely to pose appreciable ecological risks.


Subject(s)
Metals, Heavy , Water Pollutants, Chemical , Africa, Eastern , China , Environmental Monitoring , Estuaries , Geologic Sediments , Indian Ocean , Kenya , Metals, Heavy/analysis , Rivers , Water Pollutants, Chemical/analysis
2.
Mar Pollut Bull ; 159: 111490, 2020 Oct.
Article in English | MEDLINE | ID: mdl-32738641

ABSTRACT

Laboratories from 14 countries (with different levels of expertise in radionuclide measurements and 210Pb dating) participated in an interlaboratory comparison exercise (ILC) related to the application of 210Pb sediment dating technique within the framework of the IAEA Coordinated Research Project. The laboratories were provided with samples from a composite sediment core and were required to provide massic activities of several radionuclides and an age versus depth model from the obtained results, using the most suitable 210Pb dating model. Massic concentrations of Zn and Cu were also determined to be used for chronology validation. The ILC results indicated good analytical performances while the dating results didn't demonstrate the same degree of competence in part due to the different experience in dating of the participant laboratories. The ILC exercise enabled evaluation of the difficulties faced by laboratories implementing 210Pb dating methods and identified some limitations in providing reliable chronologies.


Subject(s)
Lead Radioisotopes/analysis , Lead , Environmental Monitoring , Geologic Sediments , Humans , Radiometry
3.
J Environ Radioact ; 114: 126-30, 2012 Dec.
Article in English | MEDLINE | ID: mdl-22265846

ABSTRACT

Following the Fukushima power plants accident on the 11th March 2011, the radioactivity monitoring programme at the Italian ENEA research centres was activated in order to detect the possible new input of radionuclides through atmospheric transport and precipitation. Measurements of (131)I and (134,137)Cs were carried out on atmospheric particulate, atmospheric deposition, seawater and mussels and sheep milk. In the daily samples of air particulate, (131)I was detectable between March 28 and April 12, with extremely low concentrations (<1 mBq m(-3); the detection limit for (131)I was ~0.2 mBq m(-3)) while Cs isotopes were always below the detection limit (<0.2 mBq m(-3)). The two main episodes of (131)I atmospheric deposition were registered in La Spezia research centre, around March 28 and April 15, reaching values of 17.8 ± 1.1 and 8.0 ± 2.5 Bq m(-2) respectively; maximum values of (134)Cs and (137)Cs were 0.11 ± 0.03 and 0.17 ± 0.02 Bq m(-2), respectively, detected in Brasimone research centre in April (reference date April 15). Mussels and seawater were collected in the Gulf of La Spezia: only mussels after the main (131)I deposition, on March 28, contained a measurable, although very small, amount of (131)I (0.18 ± 0.05 Bq kg(-1), detection limit (131)I = 0.03 Bq kg(-1) wet weight - soft parts). The (131)I was also detected in sheep milk in Rome (Casaccia research centre) until May 5, showing a maximum concentration of 4.9 ± 0.4 Bq L(-1). As for other European Countries for which data are available, activity levels remain of no concern for public health.


Subject(s)
Cesium Radioisotopes/analysis , Food Contamination, Radioactive/analysis , Fukushima Nuclear Accident , Iodine Radioisotopes/analysis , Radioactive Pollutants/analysis , Animals , Italy , Japan , Milk/chemistry , Mytilus/chemistry , Radiation Monitoring , Radioactivity , Seafood/analysis , Seawater/analysis , Sheep
4.
Sci Total Environ ; 409(15): 2959-70, 2011 Jul 01.
Article in English | MEDLINE | ID: mdl-21561644

ABSTRACT

Different pelagic areas of the Mediterranean Sea have been investigated in order to quantify physical and biological mixing processes in deep sea sediments. Herein, results of eleven sediment cores sampled at different deep areas (> 2000 m) of the Western and Eastern Mediterranean Sea are presented. ²¹°Pb(xs) and ¹³7Cs vertical profiles, together with ¹4C dating, are used to identify the main processes characterising the different areas and, finally, controlling mixing depths (SML) and bioturbation coefficients (D(b)). Radionuclide vertical profiles and inventories indicate that bioturbation processes are the dominant processes responsible for sediment reworking in deep sea environments. Results show significant differences in sediment mixing depths and bioturbation coefficients among areas of the Mediterranean Sea characterised by different trophic regimes. In particular, in the Oran Rise area, where the Almeria-Oran Front induces frequent phytoplankton blooms, we calculate the highest values of sediment mixing layers (13 cm) and bioturbation coefficients (0.187 cm² yr⁻¹), and the highest values of ²¹°Pb(xs) and ¹³7Cs inventories. Intermediate values of SML and D(b) (~6 cm and ~0.040 cm² yr⁻¹, respectively) characterise the mesothrophic Algero-Balearic basin, while in the Southern Tyrrhenian Sea mixing parameters (SML of 3 cm and D(b) of 0.011 cm² yr⁻¹ are similar to those calculated for the oligotrophic Eastern Mediterranean (SML of 2 cm and D(b) of ~0.005 cm² yr⁻¹).


Subject(s)
Geologic Sediments/chemistry , Geological Phenomena , Water Pollutants, Chemical/analysis , Environmental Monitoring , Geologic Sediments/analysis , Mediterranean Sea
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