DETERMINATION OF URANIUM AND THORIUM CONCENTRATIONS IN UNPROCESSED SOIL SAMPLES

被引:2
作者
LAZO, EN
ROESSLER, GS
BERVEN, BA
机构
[1] UNIV FLORIDA, CTR NUCL SCI 202, GAINESVILLE, FL 32611 USA
[2] OAK RIDGE NATL LAB, OAK RIDGE, TN 37831 USA
来源
HEALTH PHYSICS | 1991年 / 61卷 / 02期
关键词
D O I
10.1097/00004032-199108000-00007
中图分类号
X [环境科学、安全科学];
学科分类号
08 ; 0830 ;
摘要
An assay technique that directly determines the amount of U-238 and Th-232 in unprocessed, bulk soil samples has been developed. In this technique, a sample consisting of a 125-mL plastic bottle full of contaminated, moist, unprocessed soil is irradiated with gamma-rays from Co-57. Induced U and Th K-alpha fluorescent x rays are detected using a high-purity intrinsic germanium planar detector. Because of sample irradiation geometry, the fluorescent x-ray peaks lie on top of a large Compton backscatter peak. Spectral data are first fit to a combination polynomial and ERFc-step-function background that is subtracted from the peak data. The remaining peak data are fit to a Voigt Profile to properly determine peak area. The Voigt Profile, which is the convolution of the Gaussian response of the detector system and the Lorentzian energy distribution of x rays, describes the spectral peak better than a simple Gaussian distribution. A mathematical point-node model of the source-target-detector system, which includes fluorescent x-ray production by singly scattered Compton gamma-s, calculates the predicted x-ray peak area per Bq cm-3 of target contamination. Soil attenuation coefficients, which are measured for each sample, are used by the model to properly transport gamma-s and x rays through the soil sample. The sample U-238 and Th-232 concentrations are then calculated by dividing the measured peak areas by the model-predicted peak areas per Bq cm-3. No "soil standards," no assumptions about progeny equilibrium, and no sample preparation are required for this technique.
引用
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页码:231 / 243
页数:13
相关论文
共 13 条
[1]  
[Anonymous], 1983, ANN ICRP, V11-13
[2]  
EVANS RD, 1972, ATOMIC NUCLEUS
[3]   ALGORITHM FOR FITTING LORENTZIAN-BROADENED, K-SERIES X-RAY PEAKS OF HEAVY ELEMENTS [J].
GUNNINK, R .
NUCLEAR INSTRUMENTS & METHODS, 1977, 143 (01) :145-149
[4]  
GUNNINK R, 1974, UCRL51577 LAW LIV LA
[5]  
KERR GD, 1979, ORNLTM8727
[6]  
Knoll GF, 1979, RAD DETECTION MEASUR
[7]   AUTOMATIC-ANALYSIS OF GAMMA-RAY SPECTRA FROM GERMANIUM DETECTORS [J].
PHILLIPS, GW ;
MARLOW, KW .
NUCLEAR INSTRUMENTS & METHODS, 1976, 137 (03) :525-536
[8]   PROSPECTS FOR NEAR STATE-OF-THE ART ANALYSIS OF COMPLEX SEMICONDUCTOR SPECTRA IN THE SMALL LABORATORY [J].
PRUSSIN, SG .
NUCLEAR INSTRUMENTS & METHODS IN PHYSICS RESEARCH, 1982, 193 (1-2) :121-128
[9]   AIR-GROUND INTERFACE EFFECT ON GAMMA-RAY SUBMERSION DOSE [J].
RYMAN, JC ;
FAW, RE ;
SHULTIS, K .
HEALTH PHYSICS, 1981, 41 (05) :759-768
[10]  
Salem S. I., 1976, Atomic Data and Nuclear Data Tables, V18, P233, DOI 10.1016/0092-640X(76)90026-7