The Disposition of Americium-241 Oxide Following Inhalation by Beagles

The disposition of americium-241 in beagles was followed for up to 810 days after a single inhalation exposure to ^{241}{\rm AmO}{}_{2}$ aerosols having an activity median aerodynamic diameter (AMAD) of 1.3 μm and a geometric standard deviation (GSD) of 1.8 for medium (∼40 nCi/liter) and high (∼340...

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Veröffentlicht in:Radiat. Res.; (United States) 1979-06, Vol.78 (3), p.455-473
Hauptverfasser: Craig, Douglas K., Park, James F., Powers, Gerald J., Catt, Dennis L.
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container_title Radiat. Res.; (United States)
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creator Craig, Douglas K.
Park, James F.
Powers, Gerald J.
Catt, Dennis L.
description The disposition of americium-241 in beagles was followed for up to 810 days after a single inhalation exposure to ^{241}{\rm AmO}{}_{2}$ aerosols having an activity median aerodynamic diameter (AMAD) of 1.3 μm and a geometric standard deviation (GSD) of 1.8 for medium (∼40 nCi/liter) and high (∼340 nCi/liter) concentrations. At low concentrations (< 1 nCi/liter), the aerosols were smaller (AMAD ∼0.6 μm) and the distribution broader (GSD ∼2.6). Excreta were analyzed for up to 30 days postexposure and where appropriate, during the last week before sacrifice. Tissue analyses for 241 Am were conducted on groups of three dogs sacrificed 10, 30, 90, 270, and 810 days postexposure. Forty percent of the final body burden of 241 Am was located in tissues other than the lung parenchyma by 10 days postexposure and only 6% remained in the lung by 810 days postexposure. Translocation was primarily to the liver and skeleton, with roughly equal fractions of the final body burden in each at all postexposure sacrifice times. There was very little retention in the thoracic lymph nodes (< 1%) and 241 Am activity found in the gonads was negligible (< 0.05%) for these dogs. Both the rate of translocation and the organ distribution as a function of time are different from those found in dogs that inhaled ^{238}{\rm PuO}{}_{2}$ or 239 PuO2. Therefore it is not appropriate to use data derived from 239 PuO2 experiments or observations to predict the behavior of other transuranic isotopes and elements.
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At low concentrations (&lt; 1 nCi/liter), the aerosols were smaller (AMAD ∼0.6 μm) and the distribution broader (GSD ∼2.6). Excreta were analyzed for up to 30 days postexposure and where appropriate, during the last week before sacrifice. Tissue analyses for 241 Am were conducted on groups of three dogs sacrificed 10, 30, 90, 270, and 810 days postexposure. Forty percent of the final body burden of 241 Am was located in tissues other than the lung parenchyma by 10 days postexposure and only 6% remained in the lung by 810 days postexposure. Translocation was primarily to the liver and skeleton, with roughly equal fractions of the final body burden in each at all postexposure sacrifice times. There was very little retention in the thoracic lymph nodes (&lt; 1%) and 241 Am activity found in the gonads was negligible (&lt; 0.05%) for these dogs. Both the rate of translocation and the organ distribution as a function of time are different from those found in dogs that inhaled ^{238}{\rm PuO}{}_{2}$ or 239 PuO2. Therefore it is not appropriate to use data derived from 239 PuO2 experiments or observations to predict the behavior of other transuranic isotopes and elements.</description><identifier>ISSN: 0033-7587</identifier><identifier>EISSN: 1938-5404</identifier><identifier>DOI: 10.2307/3574972</identifier><identifier>PMID: 451167</identifier><language>eng</language><publisher>United States: Academic Press, Inc</publisher><subject>560172 - Radiation Effects- Nuclide Kinetics &amp; Toxicology- Animals- (-1987) ; ACTINIDE COMPOUNDS ; ACTINIDE ISOTOPES ; ACTINIDE NUCLEI ; AEROSOLS ; ALPHA DECAY RADIOISOTOPES ; Americium ; Americium - metabolism ; Americium - urine ; AMERICIUM 241 ; AMERICIUM COMPOUNDS ; AMERICIUM ISOTOPES ; AMERICIUM OXIDES ; ANIMALS ; BEAGLES ; BIOLOGICAL MATERIALS ; BIOLOGICAL WASTES ; BLOOD ; BODY ; Body Burden ; BODY FLUIDS ; CHALCOGENIDES ; CLEARANCE ; COLLOIDS ; DATA ; DATA FORMS ; DIGESTIVE SYSTEM ; DISPERSIONS ; DISTRIBUTION ; DOGS ; DOSES ; Environmental Exposure ; Excreta ; EXCRETION ; EXPERIMENTAL DATA ; EXPOSURE CHAMBERS ; FECES ; Feces - analysis ; GASTROINTESTINAL TRACT ; GLANDS ; GONADS ; HEAVY NUCLEI ; Humans ; INFORMATION ; INHALATION ; INTAKE ; ISOTOPES ; LIVER ; Lung - metabolism ; LUNG CLEARANCE ; LUNGS ; LYMPH NODES ; LYMPHATIC SYSTEM ; MAMMALS ; MUSCLES ; NUCLEI ; NUMERICAL DATA ; ODD-EVEN NUCLEI ; ORGANS ; OXIDES ; Oxides - metabolism ; OXYGEN COMPOUNDS ; Percentages ; RADIATION DOSES ; RADIATION, THERMAL, AND OTHER ENVIRON. POLLUTANT EFFECTS ON LIVING ORGS. AND BIOL. MAT ; RADIOACTIVE AEROSOLS ; RADIOISOTOPES ; RADIONUCLIDE KINETICS ; Respiration ; RESPIRATORY SYSTEM ; SKELETON ; SKIN ; SOLS ; TABLES ; TIME DEPENDENCE ; Time Factors ; TISSUE DISTRIBUTION ; TRANSURANIUM COMPOUNDS ; URINE ; VERTEBRATES ; WASTES ; YEARS LIVING RADIOISOTOPES</subject><ispartof>Radiat. 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Res.; (United States)</title><addtitle>Radiat Res</addtitle><description>The disposition of americium-241 in beagles was followed for up to 810 days after a single inhalation exposure to ^{241}{\rm AmO}{}_{2}$ aerosols having an activity median aerodynamic diameter (AMAD) of 1.3 μm and a geometric standard deviation (GSD) of 1.8 for medium (∼40 nCi/liter) and high (∼340 nCi/liter) concentrations. At low concentrations (&lt; 1 nCi/liter), the aerosols were smaller (AMAD ∼0.6 μm) and the distribution broader (GSD ∼2.6). Excreta were analyzed for up to 30 days postexposure and where appropriate, during the last week before sacrifice. Tissue analyses for 241 Am were conducted on groups of three dogs sacrificed 10, 30, 90, 270, and 810 days postexposure. Forty percent of the final body burden of 241 Am was located in tissues other than the lung parenchyma by 10 days postexposure and only 6% remained in the lung by 810 days postexposure. Translocation was primarily to the liver and skeleton, with roughly equal fractions of the final body burden in each at all postexposure sacrifice times. There was very little retention in the thoracic lymph nodes (&lt; 1%) and 241 Am activity found in the gonads was negligible (&lt; 0.05%) for these dogs. Both the rate of translocation and the organ distribution as a function of time are different from those found in dogs that inhaled ^{238}{\rm PuO}{}_{2}$ or 239 PuO2. Therefore it is not appropriate to use data derived from 239 PuO2 experiments or observations to predict the behavior of other transuranic isotopes and elements.</description><subject>560172 - Radiation Effects- Nuclide Kinetics &amp; Toxicology- Animals- (-1987)</subject><subject>ACTINIDE COMPOUNDS</subject><subject>ACTINIDE ISOTOPES</subject><subject>ACTINIDE NUCLEI</subject><subject>AEROSOLS</subject><subject>ALPHA DECAY RADIOISOTOPES</subject><subject>Americium</subject><subject>Americium - metabolism</subject><subject>Americium - urine</subject><subject>AMERICIUM 241</subject><subject>AMERICIUM COMPOUNDS</subject><subject>AMERICIUM ISOTOPES</subject><subject>AMERICIUM OXIDES</subject><subject>ANIMALS</subject><subject>BEAGLES</subject><subject>BIOLOGICAL MATERIALS</subject><subject>BIOLOGICAL WASTES</subject><subject>BLOOD</subject><subject>BODY</subject><subject>Body Burden</subject><subject>BODY FLUIDS</subject><subject>CHALCOGENIDES</subject><subject>CLEARANCE</subject><subject>COLLOIDS</subject><subject>DATA</subject><subject>DATA FORMS</subject><subject>DIGESTIVE SYSTEM</subject><subject>DISPERSIONS</subject><subject>DISTRIBUTION</subject><subject>DOGS</subject><subject>DOSES</subject><subject>Environmental Exposure</subject><subject>Excreta</subject><subject>EXCRETION</subject><subject>EXPERIMENTAL DATA</subject><subject>EXPOSURE CHAMBERS</subject><subject>FECES</subject><subject>Feces - analysis</subject><subject>GASTROINTESTINAL TRACT</subject><subject>GLANDS</subject><subject>GONADS</subject><subject>HEAVY NUCLEI</subject><subject>Humans</subject><subject>INFORMATION</subject><subject>INHALATION</subject><subject>INTAKE</subject><subject>ISOTOPES</subject><subject>LIVER</subject><subject>Lung - metabolism</subject><subject>LUNG CLEARANCE</subject><subject>LUNGS</subject><subject>LYMPH NODES</subject><subject>LYMPHATIC SYSTEM</subject><subject>MAMMALS</subject><subject>MUSCLES</subject><subject>NUCLEI</subject><subject>NUMERICAL DATA</subject><subject>ODD-EVEN NUCLEI</subject><subject>ORGANS</subject><subject>OXIDES</subject><subject>Oxides - metabolism</subject><subject>OXYGEN COMPOUNDS</subject><subject>Percentages</subject><subject>RADIATION DOSES</subject><subject>RADIATION, THERMAL, AND OTHER ENVIRON. POLLUTANT EFFECTS ON LIVING ORGS. AND BIOL. MAT</subject><subject>RADIOACTIVE AEROSOLS</subject><subject>RADIOISOTOPES</subject><subject>RADIONUCLIDE KINETICS</subject><subject>Respiration</subject><subject>RESPIRATORY SYSTEM</subject><subject>SKELETON</subject><subject>SKIN</subject><subject>SOLS</subject><subject>TABLES</subject><subject>TIME DEPENDENCE</subject><subject>Time Factors</subject><subject>TISSUE DISTRIBUTION</subject><subject>TRANSURANIUM COMPOUNDS</subject><subject>URINE</subject><subject>VERTEBRATES</subject><subject>WASTES</subject><subject>YEARS LIVING RADIOISOTOPES</subject><issn>0033-7587</issn><issn>1938-5404</issn><fulltext>true</fulltext><rsrctype>article</rsrctype><creationdate>1979</creationdate><recordtype>article</recordtype><sourceid>EIF</sourceid><recordid>eNp1kEtLw0AURgfxVav4B1wEEVxF5z2TZa1WC4Vu6jpMZm7aKUmmZFK0_95oxJ2ry-U7nMVB6JrgB8qwemRC8UzRIzQiGdOp4JgfoxHGjKVKaHWOLmLc4v4nMjtDp1wQItUIzVYbSJ593IXoOx-aJJTJpIbWW7-vU8pJsvz0DpJZqKrw4Zt1Mm82pjI_bHFInsCsK4iX6KQ0VYSr3ztG77OX1fQtXSxf59PJIrWUyy4VrlRcYQfaUicElFRlnCupHHclxhyUMdpYwwgDq3GhiNSZJlg4WkhbWDZGt4M3xM7n0foO7MaGpgHb5ZLS3pH10P0A2TbE2EKZ71pfm_aQE5x_x8p_Y_XkzUDu9kUN7o8b6vTz3TBvYxfafy1fA7ttDw</recordid><startdate>197906</startdate><enddate>197906</enddate><creator>Craig, Douglas K.</creator><creator>Park, James F.</creator><creator>Powers, Gerald J.</creator><creator>Catt, Dennis L.</creator><general>Academic Press, Inc</general><scope>CGR</scope><scope>CUY</scope><scope>CVF</scope><scope>ECM</scope><scope>EIF</scope><scope>NPM</scope><scope>AAYXX</scope><scope>CITATION</scope><scope>OTOTI</scope></search><sort><creationdate>197906</creationdate><title>The Disposition of Americium-241 Oxide Following Inhalation by Beagles</title><author>Craig, Douglas K. ; Park, James F. ; Powers, Gerald J. ; Catt, Dennis L.</author></sort><facets><frbrtype>5</frbrtype><frbrgroupid>cdi_FETCH-LOGICAL-c246t-5df7470de8c2d55ef27944767d4df004e7aa8aca313ec80b716898105d2b6cbc3</frbrgroupid><rsrctype>articles</rsrctype><prefilter>articles</prefilter><language>eng</language><creationdate>1979</creationdate><topic>560172 - Radiation Effects- Nuclide Kinetics &amp; Toxicology- Animals- (-1987)</topic><topic>ACTINIDE COMPOUNDS</topic><topic>ACTINIDE ISOTOPES</topic><topic>ACTINIDE NUCLEI</topic><topic>AEROSOLS</topic><topic>ALPHA DECAY RADIOISOTOPES</topic><topic>Americium</topic><topic>Americium - metabolism</topic><topic>Americium - urine</topic><topic>AMERICIUM 241</topic><topic>AMERICIUM COMPOUNDS</topic><topic>AMERICIUM ISOTOPES</topic><topic>AMERICIUM OXIDES</topic><topic>ANIMALS</topic><topic>BEAGLES</topic><topic>BIOLOGICAL MATERIALS</topic><topic>BIOLOGICAL WASTES</topic><topic>BLOOD</topic><topic>BODY</topic><topic>Body Burden</topic><topic>BODY FLUIDS</topic><topic>CHALCOGENIDES</topic><topic>CLEARANCE</topic><topic>COLLOIDS</topic><topic>DATA</topic><topic>DATA FORMS</topic><topic>DIGESTIVE SYSTEM</topic><topic>DISPERSIONS</topic><topic>DISTRIBUTION</topic><topic>DOGS</topic><topic>DOSES</topic><topic>Environmental Exposure</topic><topic>Excreta</topic><topic>EXCRETION</topic><topic>EXPERIMENTAL DATA</topic><topic>EXPOSURE CHAMBERS</topic><topic>FECES</topic><topic>Feces - analysis</topic><topic>GASTROINTESTINAL TRACT</topic><topic>GLANDS</topic><topic>GONADS</topic><topic>HEAVY NUCLEI</topic><topic>Humans</topic><topic>INFORMATION</topic><topic>INHALATION</topic><topic>INTAKE</topic><topic>ISOTOPES</topic><topic>LIVER</topic><topic>Lung - metabolism</topic><topic>LUNG CLEARANCE</topic><topic>LUNGS</topic><topic>LYMPH NODES</topic><topic>LYMPHATIC SYSTEM</topic><topic>MAMMALS</topic><topic>MUSCLES</topic><topic>NUCLEI</topic><topic>NUMERICAL DATA</topic><topic>ODD-EVEN NUCLEI</topic><topic>ORGANS</topic><topic>OXIDES</topic><topic>Oxides - metabolism</topic><topic>OXYGEN COMPOUNDS</topic><topic>Percentages</topic><topic>RADIATION DOSES</topic><topic>RADIATION, THERMAL, AND OTHER ENVIRON. POLLUTANT EFFECTS ON LIVING ORGS. AND BIOL. MAT</topic><topic>RADIOACTIVE AEROSOLS</topic><topic>RADIOISOTOPES</topic><topic>RADIONUCLIDE KINETICS</topic><topic>Respiration</topic><topic>RESPIRATORY SYSTEM</topic><topic>SKELETON</topic><topic>SKIN</topic><topic>SOLS</topic><topic>TABLES</topic><topic>TIME DEPENDENCE</topic><topic>Time Factors</topic><topic>TISSUE DISTRIBUTION</topic><topic>TRANSURANIUM COMPOUNDS</topic><topic>URINE</topic><topic>VERTEBRATES</topic><topic>WASTES</topic><topic>YEARS LIVING RADIOISOTOPES</topic><toplevel>peer_reviewed</toplevel><toplevel>online_resources</toplevel><creatorcontrib>Craig, Douglas K.</creatorcontrib><creatorcontrib>Park, James F.</creatorcontrib><creatorcontrib>Powers, Gerald J.</creatorcontrib><creatorcontrib>Catt, Dennis L.</creatorcontrib><creatorcontrib>Battelle, Pacific Northwest Lab., Richland, WA</creatorcontrib><collection>Medline</collection><collection>MEDLINE</collection><collection>MEDLINE (Ovid)</collection><collection>MEDLINE</collection><collection>MEDLINE</collection><collection>PubMed</collection><collection>CrossRef</collection><collection>OSTI.GOV</collection><jtitle>Radiat. Res.; (United States)</jtitle></facets><delivery><delcategory>Remote Search Resource</delcategory><fulltext>fulltext</fulltext></delivery><addata><au>Craig, Douglas K.</au><au>Park, James F.</au><au>Powers, Gerald J.</au><au>Catt, Dennis L.</au><aucorp>Battelle, Pacific Northwest Lab., Richland, WA</aucorp><format>journal</format><genre>article</genre><ristype>JOUR</ristype><atitle>The Disposition of Americium-241 Oxide Following Inhalation by Beagles</atitle><jtitle>Radiat. Res.; (United States)</jtitle><addtitle>Radiat Res</addtitle><date>1979-06</date><risdate>1979</risdate><volume>78</volume><issue>3</issue><spage>455</spage><epage>473</epage><pages>455-473</pages><issn>0033-7587</issn><eissn>1938-5404</eissn><abstract>The disposition of americium-241 in beagles was followed for up to 810 days after a single inhalation exposure to ^{241}{\rm AmO}{}_{2}$ aerosols having an activity median aerodynamic diameter (AMAD) of 1.3 μm and a geometric standard deviation (GSD) of 1.8 for medium (∼40 nCi/liter) and high (∼340 nCi/liter) concentrations. At low concentrations (&lt; 1 nCi/liter), the aerosols were smaller (AMAD ∼0.6 μm) and the distribution broader (GSD ∼2.6). Excreta were analyzed for up to 30 days postexposure and where appropriate, during the last week before sacrifice. Tissue analyses for 241 Am were conducted on groups of three dogs sacrificed 10, 30, 90, 270, and 810 days postexposure. Forty percent of the final body burden of 241 Am was located in tissues other than the lung parenchyma by 10 days postexposure and only 6% remained in the lung by 810 days postexposure. Translocation was primarily to the liver and skeleton, with roughly equal fractions of the final body burden in each at all postexposure sacrifice times. There was very little retention in the thoracic lymph nodes (&lt; 1%) and 241 Am activity found in the gonads was negligible (&lt; 0.05%) for these dogs. Both the rate of translocation and the organ distribution as a function of time are different from those found in dogs that inhaled ^{238}{\rm PuO}{}_{2}$ or 239 PuO2. Therefore it is not appropriate to use data derived from 239 PuO2 experiments or observations to predict the behavior of other transuranic isotopes and elements.</abstract><cop>United States</cop><pub>Academic Press, Inc</pub><pmid>451167</pmid><doi>10.2307/3574972</doi><tpages>19</tpages></addata></record>
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subjects 560172 - Radiation Effects- Nuclide Kinetics & Toxicology- Animals- (-1987)
ACTINIDE COMPOUNDS
ACTINIDE ISOTOPES
ACTINIDE NUCLEI
AEROSOLS
ALPHA DECAY RADIOISOTOPES
Americium
Americium - metabolism
Americium - urine
AMERICIUM 241
AMERICIUM COMPOUNDS
AMERICIUM ISOTOPES
AMERICIUM OXIDES
ANIMALS
BEAGLES
BIOLOGICAL MATERIALS
BIOLOGICAL WASTES
BLOOD
BODY
Body Burden
BODY FLUIDS
CHALCOGENIDES
CLEARANCE
COLLOIDS
DATA
DATA FORMS
DIGESTIVE SYSTEM
DISPERSIONS
DISTRIBUTION
DOGS
DOSES
Environmental Exposure
Excreta
EXCRETION
EXPERIMENTAL DATA
EXPOSURE CHAMBERS
FECES
Feces - analysis
GASTROINTESTINAL TRACT
GLANDS
GONADS
HEAVY NUCLEI
Humans
INFORMATION
INHALATION
INTAKE
ISOTOPES
LIVER
Lung - metabolism
LUNG CLEARANCE
LUNGS
LYMPH NODES
LYMPHATIC SYSTEM
MAMMALS
MUSCLES
NUCLEI
NUMERICAL DATA
ODD-EVEN NUCLEI
ORGANS
OXIDES
Oxides - metabolism
OXYGEN COMPOUNDS
Percentages
RADIATION DOSES
RADIATION, THERMAL, AND OTHER ENVIRON. POLLUTANT EFFECTS ON LIVING ORGS. AND BIOL. MAT
RADIOACTIVE AEROSOLS
RADIOISOTOPES
RADIONUCLIDE KINETICS
Respiration
RESPIRATORY SYSTEM
SKELETON
SKIN
SOLS
TABLES
TIME DEPENDENCE
Time Factors
TISSUE DISTRIBUTION
TRANSURANIUM COMPOUNDS
URINE
VERTEBRATES
WASTES
YEARS LIVING RADIOISOTOPES
title The Disposition of Americium-241 Oxide Following Inhalation by Beagles
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