assement of radionuclide concentration in various samples by gamma spectrometry and lsc

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Assement of radionuclide concentration in various samples by gamma spectrometry and LSC J. Berzins, D.Riekstina, O. Veveris Institute of Solid State Physics University of Latvia Dresden 2010

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Assement of radionuclide concentration in various samples by gamma spectrometry and LSC. J. Berzins, D.Riekstina, O. Veveris Institute of Solid State Physics University of Latvia Dresden 2010. The Laboratory was organized as the group of the Laboratory of nuclear reactions in 1986 after the - PowerPoint PPT Presentation

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  • Assement of radionuclide concentration in various samples by gamma spectrometry and LSCJ. Berzins, D.Riekstina, O. Veveris

    Institute of Solid State Physics University of Latvia

    Dresden 2010

  • The Laboratory was organized as the group of the Laboratory of nuclear reactions in 1986 after the accident in Chernobil NPS with the aim to control via gamma spectrometry the environment and measure the radioactivity in foodstof and other samples. Since 1998 the group was reorganized to the Material radioactivity testing laboratory. The quality assurance system was implemented in our laboratory since the year 2000.

  • Different contaminate samples: soils, waters, metal scrap and various types of samples, irradiated in the research nuclear reactor, were measured by gamma spectrometer. The concentrations of radionuclide were determined using the high resolution HPGe gamma- spectrometer type Ortec within the energy range of 50- 2000 keV. For measuring of large radioactive waste volums in the metal barrel, gamma-spectrometer with NaJ detector were used. The uncertainty of measurements was within the range of 3-10%, but the minimal detectable activity 0.3 Bq/kg.

  • The measurements of high tritium activities in reactor basin and for monitoring contaminate groundwater were carried out with the liquid scintillation spectrometer Packard TRI-CARB using the scintillation liquid OptiPhase HiSafe3. The measurement time for H-3 didnt exceed some hours and uncertainty was less than 2%. The credibility of obtained results is ensured by the quality assurance and control. The main requisitions involved in the quality assurance of the laboratory according to the requirements of ISO/IEC 17025:2005 are: 1) the use of calibrated equipment only; 2) the regular long-time use of reference materials for the control of equipment; 3) the regular participation in the interlaboratory intercomparison exercises, organized by the RISO National Laboratory (Denmark) and IAEA (Vienna).

  • Measurements

    Free release of reactor materialsMonitoring for potentially contaminated territoriesWater quality controlCustomer service J-131 from hospitals - metal scrap from foreign countries - samples from illegal radioactive material transport

  • HPGe gamma spectrometer

  • Efficiency of HPGe detectors

  • NaJ gamma spectrometer

  • Liquid scintilator spectrometer

  • iSOLO equipment for alfa and beta measurements

  • Methods

    For the measurements we use 15 methods.The most importent are:Determination of the radionuclides concentration by high resolution gamma-ray spectrometry. T190-1-24-237-2004Water quality Determination of the activity concentration of radionuclides by high resolution gamma-ray spectrometry. LVS ISO 10703:2008.Water quality. Determination of the specific activity of tritium. Liquid scintilation counting method. LVA ISO 9698:2003. Building materials quality Determination of the radionuclides and specific activity of radionuclides in building materials by gamma-ray spectrometry. LVS ISO 257:2000.

  • Our internal quality audit program covers all requirements of ISO/IEC 17025:2005 standard, but the main attention is paid to the analysis of results of laboratorys participation in intercomparison measurements, their evaluation, interpretation and determination of uncertainty sources. Since 1999 laboratory is a regular participant in the interlaboratory intercomparison exercises organized by the RISO National Laboratory (Denmark) and IAEA (Vienna). Such nuclides as K-40, Mn-54, Co-57, Co-60, Zn-65, Cs-134, Cs-137, Eu-152, Ra-226, U-238 and Th-232 were analyzed in following intercomparison samples: soils, sediment, seaweed, aerosol, grass, hay, meat, dray milk, waters.

  • Quality assurance Quality System Quality control

    Experienced staff Use of standard samples Premises, surroundings Measurement of background Validated methods Analysis in duplicates Calibrated equipment Control charts: background, standard peak stability Calibrated standards Reference materials Internal audit Staff training Participation in intercalibration

  • Participation of laboratory in the intercomparison exercises

    YearOrganizerObjectRadionuclides1999Risoe National laboratory, DenmarkSediment, milk, meat, seaweed, hayK-40, Mn-54, Co-60, Cs-137, Ra-226, Th-2322000Risoe National laboratory, DenmarkMilk, aerosols, soil, seaweedK-40, Cs-137, Co-60, Mn-54, Ra-226, Th-2322002IAEA, ViennaMineral matrixMn-54, Co-57, Co-60, Cs-134, Cs-137, Eu-1522003Risoe National laboratory, Denmarkmilk, mineral matrix, seaweedCs-137, K-402004-2005Risoe National laboratory, DenmarkSediment, soil, seaweedK-40, , Cs-137, U-238, Th-2322006IAEA, ViennaSoil, grass, waterK-40, Mn-54, Co-60, Zn-65, Cs-134, Cs-137

  • Figure compares our results with the weighted mean in seaweed. There is a good agreement between them.

  • Column diagram of sum of z-scores for results from all radionuclides combined showing contributions from individual samples (No. 17-Laboratory of Radiation Physics).

  • 137Cs content in mushrooms in Latvia (1987)

  • *

  • * Shut-down medical facility DubultiBoring of samples

  • Pollution with Ra-226 depending on the depth in Dubulti

  • Ra_226 concentration in the waste from Dubulti (in barrels)

    Chart1

    215

    608

    1410

    124

    93

    75

    113

    908

    5450

    130

    182

    251

    191

    173

    170

    129

    104

    95

    394

    845

    264

    426

    672

    146

    633

    1116

    152

    526

    124

    184

    393

    242

    215

    340

    258

    186

    1032

    1192

    714

    1027

    453

    621

    201

    709

    845

    836

    112

    134

    164

    370

    458

    903

    D(nSv/h)

    A(Bq/kg)

    Sheet1

    338215

    7.6608

    22801410

    12124

    38.293

    28.475

    51.6113

    1010908

    65005450

    28.6130

    75.4182

    224251

    31.2191

    70173

    33.8170

    50129

    20.4104

    10095

    290394

    1366845

    51264

    694426

    212672

    66.8146

    764633

    9001116

    238152

    362526

    1124

    47.6184

    34393

    430242

    40215

    232340

    298258

    155186

    5481032

    3221192

    1220714

    17.41027

    452453

    202621

    392201

    174709

    920845

    646836

    426112

    3134

    29.8164

    378370

    428458

    468903

    Sheet1

    D(nSv/h)

    A(Bq/kg)

    Sheet2

    Sheet3

  • Chart1

    509151632

    486131015

    52514120

    693421618

    60121167

    62118132

    56615111

    55213113

    58415123

    530161211

    46114112

    57619158

    513211613

    49313111

    51716121

    49614111

    Concentration of radionuclides in soils (Salaspils)

    K-40

    Th-232

    U-238

    Cs-137

    Sampling points

    Bk/kg

    Sheet1

    K-40Th-232U-238Cs-137

    509151632

    486131015

    52514120

    693421618

    60121167

    62118132

    56615111

    55213113

    58415123

    530161211

    46114112

    57619158

    513211613

    49313111

    51716121

    49614111

    54517137

    Sheet1

    0000

    0000

    0000

    0000

    0000

    0000

    0000

    0000

    0000

    0000

    0000

    0000

    0000

    0000

    0000

    0000

    Koncentration of radionuclides in soils (Salaspils)

    K-40

    Th-232

    U-238

    Cs-137

    Sampling points

    Bk/kg

    Sheet2

    Sheet3

  • Chart2

    82654251

    75858269

    43458265

    99362314

    474442111

    357442410

    30938206

    36678365

    382331816

    411352014

    38736189

    54359322

    52049.916666666724.757.6666666667

    K-40

    Th-232

    U-238

    Cs-137

    Sampling points

    Bk/kg

    Concentration of radionuclides in soils (Baldone)

    Sheet1

    82654251

    75858269

    43458265

    99362314

    474442111

    357442410

    30938206

    36678365

    382331816

    411352014

    38736189

    54359322

    52050258

    Sheet1

    0000

    0000

    0000

    0000

    0000

    0000

    0000

    0000

    0000

    0000

    0000

    0000

    0000

    K-40

    Th-232

    U-238

    Cs-137

    Paraugu noemanas punkti

    Bk/kg

    Radionukldu koncentrcija augsn (Baldone)

    Sheet2

    Sheet3

  • Results of tritium detection in Latvia:

    Communal water sources 155 objects 5 Bq/L < T < 10 Bq/L0,01 Bq/l < < 0,2 Bq/l 0,1 Bq/l < < 0,6 Bq/l

    Water for food industry 54 objects 5 Bq/L < T < 10 Bq/L 0,01 Bq/l < < 0,05 Bq/l 0,1 Bq/l < < 0,4 Bq/l

  • Chart1

    1290210150

    3.57427

    4602119

    1453.59.8

    55911.8

    3209351

    Activity in building materials

    Bq/kg

    Chart2

    1290210150

    3.57427

    4602119

    1453.59.8

    55911.8

    3209351

    K-40

    Th-232

    U-238

    Bq/kg

    Acivity concentration in building materials

    Sheet1

    Granite1290210150

    Marble3.57427

    Sand4602119

    Dolomite1453.59.8

    Line55911.8

    Cement3209351

    Sheet2

    Sheet3

  • Conclusions

    The use of gamma and beta spectrometry methods allow:establish the pollution level in the territories included in the monitoring decrease during the last years however unexpected changes was detected;identify and evaluate the wastes of various origin;control the quality of drinking water according to the Latvian Cabinet of Ministers regulations No.235, adopted in 2003, provision the entry in force of the EU Council Directive 98/83/EC.

    Only credible and justified results can be the basis for further use in any field, thus making it possible to make legitimate decisions.

  • Thank you for your attentionThank you for your attention

    **