原子能科学技术
原子能科學技術
원자능과학기술
ATOMIC ENERGY SCIENCE AND TECHNOLOGY
2015年
9期
1722-1728
,共7页
申慧芳%闫江雨%杨海兰%黄莎%辛存田%姚仁太
申慧芳%閆江雨%楊海蘭%黃莎%辛存田%姚仁太
신혜방%염강우%양해란%황사%신존전%요인태
氚化水蒸汽%花生%短期释放%氚含量
氚化水蒸汽%花生%短期釋放%氚含量
천화수증기%화생%단기석방%천함량
atmospheric HTO%peanut%short-term exposure%tritium concentration
为研究氚化水(HTO)蒸汽晚上和白天短期释放情况下花生对 HTO 的吸收和有机氚(OBT )形成的差异,利用盆栽试验在花生开花下针期和结荚期分白天和晚上模拟 HTO 的短期释放,并在试验结束和收获时分别测量叶子和果实中组织自由水氚(TFWT )和 OBT 的含量。研究结果表明,花生叶子晚上对 HTO 的吸收小于白天。开花下针期晚上暴露试验结束时,叶子中 TFWT 和 OBT 的相对浓度分别是白天相应值的1/6和1/3;收获时叶子中的 TFWT 和 OBT 均小于暴露试验结束时的值。结荚期晚上暴露试验结束时,花生叶子和果实中 TFWT 和 OBT 的相对浓度分别是白天相应值的1/3、2/3和2/3、1.13倍,收获时果实中的 TFWT 大于暴露试验结束时的值,叶子中 OBT 的相对浓度为暴露试验结束时的1.7倍,果实中 OBT 相对浓度却减少为原来的1/4;而白天试验收获时叶子中 OBT 的相对浓度小于试验结束时的值,但果实中 OBT 的相对浓度大于暴露试验结束时的值。表明 HTO 在不同生育期白天和晚上释放情况下,花生叶子和果实中 TFWT 和 OBT 的变化趋势不同,所以在气态氚短期释放情况下预测植物中的 OBT 浓度时,应根据不同的释放时间选择相应的参数。
為研究氚化水(HTO)蒸汽晚上和白天短期釋放情況下花生對 HTO 的吸收和有機氚(OBT )形成的差異,利用盆栽試驗在花生開花下針期和結莢期分白天和晚上模擬 HTO 的短期釋放,併在試驗結束和收穫時分彆測量葉子和果實中組織自由水氚(TFWT )和 OBT 的含量。研究結果錶明,花生葉子晚上對 HTO 的吸收小于白天。開花下針期晚上暴露試驗結束時,葉子中 TFWT 和 OBT 的相對濃度分彆是白天相應值的1/6和1/3;收穫時葉子中的 TFWT 和 OBT 均小于暴露試驗結束時的值。結莢期晚上暴露試驗結束時,花生葉子和果實中 TFWT 和 OBT 的相對濃度分彆是白天相應值的1/3、2/3和2/3、1.13倍,收穫時果實中的 TFWT 大于暴露試驗結束時的值,葉子中 OBT 的相對濃度為暴露試驗結束時的1.7倍,果實中 OBT 相對濃度卻減少為原來的1/4;而白天試驗收穫時葉子中 OBT 的相對濃度小于試驗結束時的值,但果實中 OBT 的相對濃度大于暴露試驗結束時的值。錶明 HTO 在不同生育期白天和晚上釋放情況下,花生葉子和果實中 TFWT 和 OBT 的變化趨勢不同,所以在氣態氚短期釋放情況下預測植物中的 OBT 濃度時,應根據不同的釋放時間選擇相應的參數。
위연구천화수(HTO)증기만상화백천단기석방정황하화생대 HTO 적흡수화유궤천(OBT )형성적차이,이용분재시험재화생개화하침기화결협기분백천화만상모의 HTO 적단기석방,병재시험결속화수획시분별측량협자화과실중조직자유수천(TFWT )화 OBT 적함량。연구결과표명,화생협자만상대 HTO 적흡수소우백천。개화하침기만상폭로시험결속시,협자중 TFWT 화 OBT 적상대농도분별시백천상응치적1/6화1/3;수획시협자중적 TFWT 화 OBT 균소우폭로시험결속시적치。결협기만상폭로시험결속시,화생협자화과실중 TFWT 화 OBT 적상대농도분별시백천상응치적1/3、2/3화2/3、1.13배,수획시과실중적 TFWT 대우폭로시험결속시적치,협자중 OBT 적상대농도위폭로시험결속시적1.7배,과실중 OBT 상대농도각감소위원래적1/4;이백천시험수획시협자중 OBT 적상대농도소우시험결속시적치,단과실중 OBT 적상대농도대우폭로시험결속시적치。표명 HTO 재불동생육기백천화만상석방정황하,화생협자화과실중 TFWT 화 OBT 적변화추세불동,소이재기태천단기석방정황하예측식물중적 OBT 농도시,응근거불동적석방시간선택상응적삼수。
In order to study the differences of HTO uptake and OBT formation in peanut following a short atmospheric HTO release in nighttime and daytime condition ,the pot‐ted peanut plants were exposed to evaporated HTO for 1 h in an exposure box at the flowering and podding stages under nighttime and daytime ,respectively .The concentra‐tions of tissue free water tritium (TFWT ) and organically bound tritium (OBT ) in leav‐es and peanut kernels were measured at the end of the exposure and at the harvest , respectively .The results show that HTO uptake in peanut leaves during the nighttime is several times lower than that during the daytime .At the flowering stage ,the relative TFWT and OBT concentrations in leaves under night conditions at the end of the expo‐sure are about one sixth and one third from the concentration for day conditions .And at the harvest ,the TFWT and OBT concentrations of leaves are lower than that at the end of exposure .At the podding stage ,the relative TFWT and OBT concentrations in leav‐es and peanut kernels under night conditions are one third ,two third and two third , 1.13 times from the concentration under day conditions at the end of exposure .At the harvest ,the TFWT concentration in peanut kernels is higher than that at end of the ex‐posure ,and the relative OBT concentration in leaves increases by factor of 1.7 ,but the OBT concentration in peanut kernels is only one fourth of that at the end of exposure under night condition .At the harvest ,the OBT concentration in leaves is lower than that at the end of exposure ,however the OBT concentration in kernels increases under day condition . Following a short atmospheric HTO release in nighttime and daytime conditions at the different grow th and development stages , the variation tendency of TFWT and OBT in leaves and kernels are different .Therefore ,the parameters of triti‐um concentration prediction model in plant should base the grow th stages for accidental release of atmospheric HTO ,which could make the ingestion doses for tritium be esti‐mated accurately and objectively .