• 제목/요약/키워드: Uranium enrichment

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구룡산(九龍山)(옥천(決川)) 함(含)우라늄 흑색(黑色) 점판암(粘板岩)의 지화학(地化學) 및 성인(成因) (Geochemistry and Genesis of the Guryonsan(Ogcheon) Uraniferous Back Slate)

  • 김종환
    • 자원환경지질
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    • 제22권1호
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    • pp.35-63
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    • 1989
  • 구룡산(九龍山)(또는 옥천(沃川)) 함(含)우라늄 흑연질점판암(黑鉛質粘板岩)은 옥천대(沃川帶) 서북부(西北部)에 따라 증상(層狀) 또는 부딘상(狀)으로 90km이상(以上) 연장(延長) 분포(分布)한다. 함(含)우라늄점판암(粘板岩)의 오토레디오그라프에 나타나는 퇴적(堆積), 속성(續成), 변성구조(變成構造)는 우라늄과 동시퇴적물(同時堆積物)로서 속성작용과정(續成作用過程)에서 전혀 이동(移動)하지 않고 황성변성(廣域變成) 초기(初期)에 제자리에서 미립(微粒)우라니나이트로 재결정(再結晶)하였음을 보여준다. 동시(同時)에 유기물(有機物)은 미세환장흑연(微細環狀黑鉛)으로 되었다. 라미나구조(構造)의 발달(發達)과 평균(平均) 19.64% C, 2.32% S의 함유(含有)는 함(含)우라늄흑니(黑泥) 퇴적(堆積)의 일반조건(一般條件)으로서의 극(極)히 낮은 퇴적화(堆積比), 고유기물함유(高有機物含有), 염기성황경등을 충족(充足)하였으며 Th/U가 0.07로서 해수원(海水源)임을 뜻한다. 지역별(地域別) CaO, $P_2O_5$의 평균치(平均値)가 매우좁은 범위(範圍)의 일정치(一定値)이며 높은 CaO 평균치(平均値)를 나타내어 전퇴적(全堆積)분지를 통(通)하여 동일(同一) pH(7.8-8.0)조건(條件)의 환경(環境)에서 퇴적(堆積)하였음을 나타낸다. 함(含)우라늄점판암(粘板岩)은 같은 성인(成因)의 타산장(他産狀)에 비(比)하여 미량원소(微量元素) 부화도(富化度)가 매우 높다. 고부화(高富化)의 중요(重要)한 원인(原因)으로서 미량원소(微量元素)의 소스(source)인 해수(海水)의 주기적(週期的) 교체(交替)가 요구(要求)되는데 사이크릭퇴적구조(堆積構造)는 그러한 현상(現象)을 뒷받침하여 준다. 흑니(黑泥)의 성인별(成因別) 구성광물(構成鑛物)과 원소(元素)의 수반관계(隨伴關係)에서 쇄설성광물(鑛物)에는 Si, Al, K, Na, Ti, Zr, Th, Be, B, Li, 유기물(有機物)후락숀에, U, Ni, Cu, Co, Zn, Ag, Mo, Pb, Sn, Cd, S, Fe, V, Cr, Y, 탄산염광물(炭酸鹽鑛物)에 Ca, Mg, Mn, P, Ba가 높은 상관(相關)을 나타낸다. 유기물(有機物)의 우라늄고정심전능력(固定沈澱能力)에 있어 사프로페릭(Sapropelic)형(型)보다 휴믹(Humic)형(型)에서 더 높다. 육성식물(陸性植物)의 분해물(分解物)인 휴무스(Humus)는 고대성(古生代) 중기(中期)에 출현(出現)한다. 우라늄 함유(含有) 흑니(黑泥)는 이 시대(時代)의 형성물(形成物)로서 이런 형(型)의 광상(鑛床)은 생물상(生物相)의 진화(進化)에 규제(規制)된 광화작용(鑛化作用)의 산물(産物)이다.

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부산광역시 일대의 토양 내 라돈 농도 변화 특성 (Characteristics of Radon Variability in Soils at Busan Area)

  • 김진섭;김선웅;이효민;최정윤;문기훈
    • 자원환경지질
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    • 제45권3호
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    • pp.277-294
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    • 2012
  • 부산의 지역의 암석 종류에 따른 토양 내 라돈 농도의 시 공간적 변화 특성과 변화 요인에 대하여 연구하였다. 토양 내 라돈($^{222}Rn$)농도와 암석 및 토양의 모원소($^{226}Ra$,$^{228}Ra$ U, Th)의 농도를 부산지역 24개 지점에서 측정하였다. 모암과 토양 내 이들 모원소들의 분포와 거동 특징을 분석하고 라돈과의 상관성을 상세히 규명하였으며, 지형에 대한 영향도 평가하였다. 토양 내 라돈 농도 측정에는 두 가지 in-situ 방법(soil probe 방법과 지중매설튜브 방법)을 적용하여 측정의 정확성에 대하여 비교하였다. 토양 내 라돈의 공간적 분포는 모암의 암석 종류에 따른 U의 농도를 전반적으로 반영하여, 화산암에 비해 심성암에 높고, 산성암>중성암>염기성암 순으로 높은 변화양상을 보였다. 그러나 동일한 모암에서 유래된 토양내의 라돈 농도에서 큰 폭의 변화가 나타나며, 이는 라돈의 모원소인 U와 $^{226}Ra$의 암석과 토양에서의 현저한 방사능 비평형 결과이다. 따라서 토양 내 라돈 농도는 이들 모원소의 암석과 토양 내 농도와의 상관성은 매우 낮게 나타나며, 암석 내 농도에 비해 토양 내 농도와 더 높은 상관성을 보였다. Th과 $^{228}Ra$은 풍화작용과 토양 발달 특성에 따라 U와 지구화학적 거동 및 부하 특징을 달리하기 때문에, 동일한 모암에서 유래된 토양에서도 토양 특징에 따라 U와 현저히 다른 복잡한 농도 변화 양상을 나타내었다. 지형구배를 이루는 경사지의 동일 심도의 토양 내 라돈농도는 위치에 따라 차이를 나타내며, 모암을 같이하는 잔류토양(부산대 내 19개 지점)내에서는 소규모 지형 변화에 의해 토양 내 라돈 농도가 6.8~29.8Bq/L 범위로 변화하였다. 토양 내 라돈 농도는 토양 특성에 따라, 정반대의 계절적 변화 양상을 보인다. 지중매설튜브 방법이 soil probe 방법에 비해 더욱 정확히 토양 내 라돈농도를 측정할 수 있어, 토양 내 라돈의 시 공간적 변화 특성에 대한 분석에 매우 유용한 것으로 나타났다.

APPLICATION OF FUZZY SET THEORY IN SAFEGUARDS

  • Fattah, A.;Nishiwaki, Y.
    • 한국지능시스템학회:학술대회논문집
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    • 한국퍼지및지능시스템학회 1993년도 Fifth International Fuzzy Systems Association World Congress 93
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    • pp.1051-1054
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    • 1993
  • The International Atomic Energy Agency's Statute in Article III.A.5 allows it“to establish and administer safeguards designed to ensure that special fissionable and other materials, services, equipment, facilities and information made available by the Agency or at its request or under its supervision or control are not used in such a way as to further any military purpose; and to apply safeguards, at the request of the parties, to any bilateral or multilateral arrangement, or at the request of a State, to any of that State's activities in the field of atomic energy”. Safeguards are essentially a technical means of verifying the fulfilment of political obligations undertaken by States and given a legal force in international agreements relating to the peaceful uses of nuclear energy. The main political objectives are: to assure the international community that States are complying with their non-proliferation and other peaceful undertakings; and to deter (a) the diversion of afeguarded nuclear materials to the production of nuclear explosives or for military purposes and (b) the misuse of safeguarded facilities with the aim of producing unsafeguarded nuclear material. It is clear that no international safeguards system can physically prevent diversion. The IAEA safeguards system is basically a verification measure designed to provide assurance in those cases in which diversion has not occurred. Verification is accomplished by two basic means: material accountancy and containment and surveillance measures. Nuclear material accountancy is the fundamental IAEA safeguards mechanism, while containment and surveillance serve as important complementary measures. Material accountancy refers to a collection of measurements and other determinations which enable the State and the Agency to maintain a current picture of the location and movement of nuclear material into and out of material balance areas, i. e. areas where all material entering or leaving is measurab e. A containment measure is one that is designed by taking advantage of structural characteristics, such as containers, tanks or pipes, etc. To establish the physical integrity of an area or item by preventing the undetected movement of nuclear material or equipment. Such measures involve the application of tamper-indicating or surveillance devices. Surveillance refers to both human and instrumental observation aimed at indicating the movement of nuclear material. The verification process consists of three over-lapping elements: (a) Provision by the State of information such as - design information describing nuclear installations; - accounting reports listing nuclear material inventories, receipts and shipments; - documents amplifying and clarifying reports, as applicable; - notification of international transfers of nuclear material. (b) Collection by the IAEA of information through inspection activities such as - verification of design information - examination of records and repo ts - measurement of nuclear material - examination of containment and surveillance measures - follow-up activities in case of unusual findings. (c) Evaluation of the information provided by the State and of that collected by inspectors to determine the completeness, accuracy and validity of the information provided by the State and to resolve any anomalies and discrepancies. To design an effective verification system, one must identify possible ways and means by which nuclear material could be diverted from peaceful uses, including means to conceal such diversions. These theoretical ways and means, which have become known as diversion strategies, are used as one of the basic inputs for the development of safeguards procedures, equipment and instrumentation. For analysis of implementation strategy purposes, it is assumed that non-compliance cannot be excluded a priori and that consequently there is a low but non-zero probability that a diversion could be attempted in all safeguards ituations. An important element of diversion strategies is the identification of various possible diversion paths; the amount, type and location of nuclear material involved, the physical route and conversion of the material that may take place, rate of removal and concealment methods, as appropriate. With regard to the physical route and conversion of nuclear material the following main categories may be considered: - unreported removal of nuclear material from an installation or during transit - unreported introduction of nuclear material into an installation - unreported transfer of nuclear material from one material balance area to another - unreported production of nuclear material, e. g. enrichment of uranium or production of plutonium - undeclared uses of the material within the installation. With respect to the amount of nuclear material that might be diverted in a given time (the diversion rate), the continuum between the following two limiting cases is cons dered: - one significant quantity or more in a short time, often known as abrupt diversion; and - one significant quantity or more per year, for example, by accumulation of smaller amounts each time to add up to a significant quantity over a period of one year, often called protracted diversion. Concealment methods may include: - restriction of access of inspectors - falsification of records, reports and other material balance areas - replacement of nuclear material, e. g. use of dummy objects - falsification of measurements or of their evaluation - interference with IAEA installed equipment.As a result of diversion and its concealment or other actions, anomalies will occur. All reasonable diversion routes, scenarios/strategies and concealment methods have to be taken into account in designing safeguards implementation strategies so as to provide sufficient opportunities for the IAEA to observe such anomalies. The safeguards approach for each facility will make a different use of these procedures, equipment and instrumentation according to the various diversion strategies which could be applicable to that facility and according to the detection and inspection goals which are applied. Postulated pathways sets of scenarios comprise those elements of diversion strategies which might be carried out at a facility or across a State's fuel cycle with declared or undeclared activities. All such factors, however, contain a degree of fuzziness that need a human judgment to make the ultimate conclusion that all material is being used for peaceful purposes. Safeguards has been traditionally based on verification of declared material and facilities using material accountancy as a fundamental measure. The strength of material accountancy is based on the fact that it allows to detect any diversion independent of the diversion route taken. Material accountancy detects a diversion after it actually happened and thus is powerless to physically prevent it and can only deter by the risk of early detection any contemplation by State authorities to carry out a diversion. Recently the IAEA has been faced with new challenges. To deal with these, various measures are being reconsidered to strengthen the safeguards system such as enhanced assessment of the completeness of the State's initial declaration of nuclear material and installations under its jurisdiction enhanced monitoring and analysis of open information and analysis of open information that may indicate inconsistencies with the State's safeguards obligations. Precise information vital for such enhanced assessments and analyses is normally not available or, if available, difficult and expensive collection of information would be necessary. Above all, realistic appraisal of truth needs sound human judgment.

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