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| 02114nam 2200325za 4500 |
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001 | 9.813868 |
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003 | CaOODSP |
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005 | 20221107141638 |
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007 | cr ||||||||||| |
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008 | 161005s2016 quc ob f000 0 eng d |
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020 | |a978-0-660-04984-7 |
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040 | |aCaOODSP|beng |
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043 | |an-cn--- |
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086 | 1 |aEn84-134/2016E-PDF |
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245 | 00|aFCSAP advisory bulletin (FAB) |h[electronic resource] : |bradionuclides in groundwater. |
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246 | 1 |iAt head of title: |aFederal Contaminated Sites Action Plan (FCSAP) |
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246 | 30|aRadionuclides in groundwater |
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246 | 13|aFederal Contaminated Sites Action Plan advisory bulletin : |bradionuclides in groundwater |
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260 | |aGatineau, QC : |bEnvironment and Climate Change Canada, |cc2016. |
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300 | |a2 p. |
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500 | |aIssued also in French under title: Bulletin d’avis du PASCF (BAP) : radionucléides dans les eaux souterraines. |
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504 | |aIncludes bibliographical references. |
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520 | |a“At contaminated sites where radionuclides are a concern, it is important that groundwater sampling protocols be in place to investigate the potential for colloid-facilitated transport, in addition to standard sampling protocols for radionuclides (Canadian Council of Ministers of the Environment (CCME), 2011a). Radionuclides in groundwater can be initially investigated using inductively coupled plasma-mass spectrometry (ICPMS) to screen samples for radionuclide contamination. Those contaminants of potential concern analyzed with an ICPMS are uranium, thorium, and radium (International Atomic Energy Agency (IAEA), 2010). The main advantages to using this method are high sensitivity and short analytical times, requiring only a few minutes (IAEA, 2010)“--p. 1-2. |
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692 | 07|2gccst|aContaminated sites |
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692 | 07|2gccst|aGroundwater |
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692 | 07|2gccst|aRadioactive materials |
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692 | 07|2gccst|aRisk management |
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710 | 1 |aCanada. |bEnvironment and Climate Change Canada. |
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775 | 08|tBulletin d'avis du PASCF (BAP) |w(CaOODSP)9.813869 |
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856 | 40|qPDF|s1.81 MB|uhttps://publications.gc.ca/collections/collection_2016/eccc/En84-134-2016-eng.pdf |
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