Abstract:The residual 239+240Pu concentration in the Nagasaki soil was observed 36 years after the plutonium atomic bombing of Nagasaki in 1945. The highest level of 239+240Pu contamination was discovered in the soil at the edge of the Nishiyama reservoir, a level about 10–30 times higher than in other areas of Nagasaki. In the Nishiyama district, 97% of the total plutonium in the soil was retained to a depth of 0.3 m, but the remaining 3% was dispersed over a 0.3‐ to 2.25‐m depth at approximately 0.037 Bq/kg of dry so… Show more
“…Core sample A was a 2.25-m-long core taken in 1981 from point A, core sample B was a 4.5-m-long core collected in 1984 from point B, and core sample C was a 0.3-m-long taken in 1981 from point C. These points were observed to have heavy fallout deposits produced by the atomic bomb in 1945. 15 To prevent cross contamination, the soil cores were carefully excavated by hand from the center of a 0.5-m-diameter soil pedestal. The soil core samples (cores A, B, and C) were carefully quarried with a sharp knife from the 0.5-m-diameter pedestal.…”
Section: Soil Samplesmentioning
confidence: 99%
“…11 On the other hand, on August 9, 1945, a plutonium A-bomb exploded 500 m above Urakami in Nagasaki city at 11:02 LT. Half an hour after the detonation, large quantities of fission products and unfissioned plutonium in the form of fallout reached the ground (the so-called black rain). The greatest Pu and 137 Cs depositions were found at Nishiyama in an eastern suburb of Nagasaki city, 2.8 km east of the hypocenter, [12][13][14][15][16][17][18] strongly suggesting that the local fallout was not deposited as dust or aerosol particles, but as precipitate. 16 The Tokyo metropolitan area belongs to the Kanto loam region, which mainly consists of clays derived from weathered volcanic ash.…”
Section: Introductionmentioning
confidence: 99%
“…We obtained the content of deposited 137 Cs and the 10-cm-depth profile of 137 Cs in Kanto loam of the ETMA seven months after the Fukushima accident, and compared it to the vertical profiles of 137 Cs in the loam 36 -38 years later after the detonation of the Pu A-bomb reported by Mahara and Miyahara 15 and Mahara.…”
Section: Introductionmentioning
confidence: 99%
“…The Nishiyama and Tokyo metropolitan areas are located in the Nishiyama and Kanto loam areas, respectively, and the soil of both areas is derived from volcano activity. Mahara and Miyahara 15 and Mahara 14 determined the relative contributions of the local fallout from the Nagasaki A-bomb and the global fallout from nuclear-weapon tests to the total concentration of 137 Cs, 90 Sr, and 239 Pu in the Nishiyama soil 36 and 38 years after the Nagasaki A-bomb. On the other hand, Igarashi et al 19,20 studied the migration of stable Sr, Co, and Cs through the unsaturated Kanto loamy soil by using various field tracer experiments under the direct influence of natural rainfall and evapotranspiration.…”
2000 to 10000, respectively. This difference in the retardation factors is attributed to an aging effect that corresponds to seven months and 36 to 38 years after the deposition of 137 Cs occurred on the soil minerals.
“…Core sample A was a 2.25-m-long core taken in 1981 from point A, core sample B was a 4.5-m-long core collected in 1984 from point B, and core sample C was a 0.3-m-long taken in 1981 from point C. These points were observed to have heavy fallout deposits produced by the atomic bomb in 1945. 15 To prevent cross contamination, the soil cores were carefully excavated by hand from the center of a 0.5-m-diameter soil pedestal. The soil core samples (cores A, B, and C) were carefully quarried with a sharp knife from the 0.5-m-diameter pedestal.…”
Section: Soil Samplesmentioning
confidence: 99%
“…11 On the other hand, on August 9, 1945, a plutonium A-bomb exploded 500 m above Urakami in Nagasaki city at 11:02 LT. Half an hour after the detonation, large quantities of fission products and unfissioned plutonium in the form of fallout reached the ground (the so-called black rain). The greatest Pu and 137 Cs depositions were found at Nishiyama in an eastern suburb of Nagasaki city, 2.8 km east of the hypocenter, [12][13][14][15][16][17][18] strongly suggesting that the local fallout was not deposited as dust or aerosol particles, but as precipitate. 16 The Tokyo metropolitan area belongs to the Kanto loam region, which mainly consists of clays derived from weathered volcanic ash.…”
Section: Introductionmentioning
confidence: 99%
“…We obtained the content of deposited 137 Cs and the 10-cm-depth profile of 137 Cs in Kanto loam of the ETMA seven months after the Fukushima accident, and compared it to the vertical profiles of 137 Cs in the loam 36 -38 years later after the detonation of the Pu A-bomb reported by Mahara and Miyahara 15 and Mahara.…”
Section: Introductionmentioning
confidence: 99%
“…The Nishiyama and Tokyo metropolitan areas are located in the Nishiyama and Kanto loam areas, respectively, and the soil of both areas is derived from volcano activity. Mahara and Miyahara 15 and Mahara 14 determined the relative contributions of the local fallout from the Nagasaki A-bomb and the global fallout from nuclear-weapon tests to the total concentration of 137 Cs, 90 Sr, and 239 Pu in the Nishiyama soil 36 and 38 years after the Nagasaki A-bomb. On the other hand, Igarashi et al 19,20 studied the migration of stable Sr, Co, and Cs through the unsaturated Kanto loamy soil by using various field tracer experiments under the direct influence of natural rainfall and evapotranspiration.…”
2000 to 10000, respectively. This difference in the retardation factors is attributed to an aging effect that corresponds to seven months and 36 to 38 years after the deposition of 137 Cs occurred on the soil minerals.
“…This is considerably less than the rainwater infiltration rate of 2.5 m y 1 . Furthermore, 137 Cs was not detected in the groundwater of the Nishiyama area, suggesting that 137 Cs has not yet migrated to the groundwater table [14]. We collected 4 L of shallow groundwater in the Kashiwa city in the ETMA on August 17, 2012.…”
We evaluated the migration of radionuclides ( 131 I, 129 I, 134 Cs, 136 Cs, 137 Cs, and 132 Te) in the surface soil after the Fukushima nuclear accident. The radionuclides in the soil collected late March in 2011 were barely leached with ultrapure water, indicating that these are insoluble. We observed the chemical behavior of 137 Cs and 129 I in soil: (1) 137 Cs was predominantly adsorbed within a depth of 2.5 cm from the ground surface; (2) 137 Cs was hardly released from soil by the water leaching experiments that lasted for 270 days; (3) approximately, more than 90 % of 137 Cs was adsorbed on organic matters and the residual fractions, while 129 I was mainly fixed on the Fe-Mn oxide and organically bounded fraction. Therefore, we conclude that 137 Cs and 129 I in soil seldom leach into the soil water and migrate downward because of the irreversible adsorption. The shallow groundwater which residence time is short.
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