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1 Lecture 9: Case Studies in Marine Pollution Distribution of Anthropogenic radionuclides in the Moroccan coastal waters and sediments Moncef Benmansour CNESTEN, Rabat, Morocco IAEA Regional Training Course Sediment Core Dating Techniques - RAF/7/008 Project CNESTEN, Rabat, 05-09 July 2010 IAEA CNESTEN
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2 Contents Introduction Introduction Material and Methods Material and Methods Results and Discussion Results and Discussion Conclusion Conclusion
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3 Introduction Long coast (~ 3500 km), Long coast (~ 3500 km), Development of National and Mediterranean industrial activities Development of National and Mediterranean industrial activities Marine traffics Marine traffics Characteristics of the Mediterranean sea Characteristics of the Mediterranean sea
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4 Introduction IAEA regional project ( North of Africa): RAF7/004 IAEA regional project ( North of Africa): RAF7/004 –«Contamination assessment of the south Mediterranean sea» Specific objectives Specific objectives –Obtaining data on R.N contaminants 137 Cs, 239,240 Pu, 238 Pu, 241 Am, 90 Sr, natural ( 210 Pb, 210 Po, 226 Ra…), but also heavy metals and organics –Understanding the behaviour and the fate of contaminants –Modelling the dispersion of contaminants –Development of national databases
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5 Explored Stations
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6 Material and Methods R.V: Charif El Idrissi -INRH- Technical Staff: CNESTEN (2), IAEA (2) INRH (3)
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7 Material and Methods N°Name & Position Maximal depth (m)Samples collected St.1Mohammedia 33°46'N; 7°28'W 300Surface water St.2M'Diq 35°47'N; 04°48'W 800Water column, Sediment core Biota St.3M'Diq 35°47'N; 05°15'W 270Surface water St.4Tangier 35°52'N; 05°51'W 200Surface water
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10 Material and Methods Pre-treatment Pre-treatment –Sea water ( 239,240 Pu, 241 Am, 137 Cs, 90 Sr) filtered (0.45 filtered (0.45 m) addition of tracers and carriers ( 242 Pu, 243 Am, 85 Sr, Cs, Sr…) addition of tracers and carriers ( 242 Pu, 243 Am, 85 Sr, Cs, Sr…) sequential concentrations sequential concentrations – 239,240 Pu and 241 Am with MnO 2, 137 Cs with AMP, 90 Sr with oxalic acid –Sediment cores ( depth profiles: 239,240 Pu, 137 Cs 210 Pb, 226 Ra) sectioned ( 0.5 – 2 cm) sectioned ( 0.5 – 2 cm)
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11 Material and Methods Physical preparation Physical preparation –Freeze-drying –Homogenisation Radiochemical separation ( Pu- Am) Radiochemical separation ( Pu- Am) –Digestion ( HNO 3 ) –Separation of transuranics : Pu and Am –Electrodeposition on stainless steel discs
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13 Material and Methods Other R.N Other R.N – 137 Cs in sea water Dilution of AMP precipitate in NaOH 10M Dilution of AMP precipitate in NaOH 10M – 210 Pb and 210 Po in sediment Total digestion ( HNO 3, HCl, HF, HClO 4 ) Total digestion ( HNO 3, HCl, HF, HClO 4 ) Spontaneous deposition in silver discs Spontaneous deposition in silver discs R.N Mesurements R.N Mesurements – spectrometry HPGe detector (Canberra) – n-type, 45% - HPGe detector (Canberra) – n-type, 45% - – spectrometry: Semi-conductor detectors (Si) EG&G Ortec Semi-conductor detectors (Si) EG&G Ortec
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14 Preparation and Radiochemical Laboratories
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15 Analysis Laboratories
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16 242 Pu 239,240 Pu 238 Pu 243 Am 241 Am Alpha Spectrometry: 239,249 Pu & 241 Am
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17 Alpha spectrometry: 210 Po
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18 Gamma spectrum
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19 Quality Control
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20 Heavy Metal Analyses in Sediment Preparation of sediment: - -dry-freezing - - ground - - sieving (63mm) - - digestion: teflon reactors, HNO3 H2SO4, Aqua- Regal, HF Measurements: – – Atomic Absorption System – –hydrure system for Hg, graphite oven
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21 Petroleum HC Analyses Sediment – –extraction by soxhlet extractors and hexane/dichloromethane – –Purification – –dosage CPG « HP plus-Agilent 6890 », Spectrofluometer (P.E ) Water – – extraction by carbon tetrachloride – – separation from O.M – – Measurements by IR
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22 RESULTS
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23 Waters
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24 Waters 2170 Bq.m -2 23 Bq.m -2
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25 Data in Bibliography
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26 Data in Bibliography
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27 Data in bibilography
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28 Data in bibilography
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29 Data in bibilography
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30 Data in bibilography
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31 Sediment: 137 Cs and 239,240 Pu Peaks 1963: Global Fallout ? 284 Bq/m 2 32 Bq/m 2
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32 Sediment: 210 Pb
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33 Dating of Sediment Core: 210 Pb Dashed line is the best fit corresponding to the CIC- CSR model while the continuous line corresponds to the CM-CSR model
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34 Dating of Sediment Core: 210 Pb CIC-CSR Model: CIC-CSR Model: –Initial Concentration and sedimentation rate constant w = 0.10 ± 0.02 g cm -2 y -1 F = A(0) w, 720 ± 150 Bq m -2 y -1.
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35 Dating of Sediment Core: 210 Pb CRS Model: Constant Rate of supply is Constant but Sedimentation rate vary CRS Model: Constant Rate of supply is Constant but Sedimentation rate vary Mean value: w = 0.10 g.cm- 2 y- 1 F = I, 712 ± 25 Bq m -2 y -1.
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36 Dating of Sediment Core: 210 Pb CM-CSR Model: Constant Mixing and constant Sedimentation Rate CM-CSR Model: Constant Mixing and constant Sedimentation Rate k m is an effective mixing coefficient given in terms of the diffusion coefficient D and the bulk density (Abril 2003b) w= 0.092 ± 0.003 g cm- 2 y -1 F = 670 ± 25 Bq m -2 y -1.
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37 Reconstruction of 137 Cs, 239,240 Pu Profiles Reconstruction of 137 Cs, 239,240 Pu Profiles with boundary conditions C w : radionuclide concentration in overlying water
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38 Historical records of 137 Cs, 239,240 Pu in water
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39 Reconstruction of 137 Cs, 239,240 Pu profiles in sediment
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40 Laissaoui, M. Benmansour N. Ziad, M. Ibn Majah J. M. Abril and S. Mulsow. Anthropogenic radionuclides in the water column and a sediment core from the Alboran Sea: application to radiometric dating and reconstruction of historical water column radionuclide concentrations. Journal of Paleolimnology 40 (2008) 823-833 Laissaoui, M. Benmansour N. Ziad, M. Ibn Majah J. M. Abril and S. Mulsow. Anthropogenic radionuclides in the water column and a sediment core from the Alboran Sea: application to radiometric dating and reconstruction of historical water column radionuclide concentrations. Journal of Paleolimnology 40 (2008) 823-833 M. Benmansour, A. Laissaoui, S. Benbrahim, M. Ibn Majah, A.Chafik and P.Povinec. Distribution of anthropogenic radionuclides in Moroccan coastal waters and sediments. Radioactivity in the Environment. Book Series. 8 ( 2006) 145-150 M. Benmansour, A. Laissaoui, S. Benbrahim, M. Ibn Majah, A.Chafik and P.Povinec. Distribution of anthropogenic radionuclides in Moroccan coastal waters and sediments. Radioactivity in the Environment. Book Series. 8 ( 2006) 145-150
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41 Heavy metals
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43 Total hydrocarbons
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45 Summary Levels of Anthropogenic R.N ( 137 Cs, 239,240 Pu, 241 Am) in surface sea water and sediment - Morocco coast – Levels of Anthropogenic R.N ( 137 Cs, 239,240 Pu, 241 Am) in surface sea water and sediment - Morocco coast – Vertical distributions of R.N in water column and sediment core Vertical distributions of R.N in water column and sediment core Use of 210 Pb ex, 137 Cs, 239,240 Pu: sedimentation rate, chronology of contaminants Use of 210 Pb ex, 137 Cs, 239,240 Pu: sedimentation rate, chronology of contaminants Main source of R.N : Global fallout Main source of R.N : Global fallout Heavy metals (Mn, Hg) important in the sediment surface Cr high / Cd, Hg, and / previous studies No significant contamination by HC
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