• Title/Summary/Keyword: Mg-Si-O

Search Result 1,154, Processing Time 0.021 seconds

청산 일대에 분포하는 화강암류의 광물조성과 주성분원소 지구화학 (Mineral chemistry and major element geochemistry of the granitic rocks in the Cheongsan area)

  • 사공희;좌용주
    • 암석학회지
    • /
    • 제6권3호
    • /
    • pp.185-209
    • /
    • 1997
  • 청산지역의 화강암류는 기재적인 특징으로부터 백록 화강섬록암, 청산 반상 화강암 및 청산복운모 화강암으로 분류할 수 있다. 백록 화강섬록암의 각섬석은 외각섬석군에 속하고, 중심부의 Mg- 보통각섬석에서 주변부의 양기석질 보통각섬석으로 조성적 변화를 보인다. 청산 지역 화강암류의 흑운모는 금운모와 애나이트의 중간 조성을 나타낸다. 복운모 화강암에서 산출되는 백운모는 그 산출상태와 조성으로부터 마그마 정출의 1차적인 백운모로 판단된다. 주성분 산화물의 변화 경향에서 각각의 화강암류는 체계적인 변화를 나타낸다. 백록 화강섬록암은 청산 반상 화강암 및 복운모 화강암과는 주성분의 변화 경향에서 매우 뚜렷한 차이를 보인다. 반상 화강암과 복운모 화강암의 경우 일부 성분에서는 연속성이 관찰되지만, 몇몇 원소에서는 뚜렷한 차이를 보인다. 따라서 청산 지역의 세 화강암류는 각각 이질적 성인의 다른 조성의 마그마로부터 형성된 것으로 판단된다. 화강암류의 전암 화학조성으로부터 청산 지역 화강암류는 칼크-알칼리질임을 알 수 있다. 한편, 백록 화강섬록암과 청산 반상 화강암은 그 전암 조성이 I-타입과 메타알루미나질임에 비해, 청산 복운모 화강암은 I-/S-타입 양쪽과 과알루미나질을 나타낸다. 불투명광물의 함량과 전암 대자율값으로부터 청산지역 화강암륜느 모도 티탄철석계열에 속해 비교적 환원적인 환경에서 관입·고결되었음을 알 수 있다. 또한 세 화강암류는 활동성 대륙연변부에서 일어난 화성활동의 결과로 형성되었음이 추정된다. 청산 반상 화강암에 나타나는 알칼리장석의 거정은 그 결정의 크기, 형태, 배열 및 포유물의 분포 양상 등으로부터 마그마 기원임을 추정할 수 있다. 반상 화강암의 조직적 특징은 2단계 정출작용으로 설명된다. 즉, 알칼리장석 거정의 크기와 형태는 과냉각 정도가 적은 상태에서 결정의 느린 핵형성과 빠른 성장속도로 말미암아 형성된 반면, 석기는 과냉각 정도가 큰 상태에서 핵형성 밀도와 속도가 증가하여 형성된 것으로 판단된다.

  • PDF

토양중(土壤中) 비소(砒素)의 행동(行動)과 수도(水稻)의 비소흡수(砒素吸收)에 의(依)한 피해생리(被害生理) 생태(生態)에 관(關)한 연구(硏究);Ⅲ.물관리(管理)가 수도의 비소흡수(砒素吸收) 및 생육(生育)에 미치는 영향(影響) (Behaviors of Arsenic in Paddy Soils and Effects of Absorbed Arsenic on Physiological and Ecological Characteristics of Rice Plant lll. Effect of Water Management on As Uptake and the Growth of Rice Plant at As Added Soil)

  • 이민효;임수길
    • 한국환경농학회지
    • /
    • 제6권1호
    • /
    • pp.1-6
    • /
    • 1987
  • 물관리 방법(方法)에 따른 수도(水稻)의 비소흡수(砒素吸收) 및 생육(生育)에 미치는 영향(影響)을 구명(究明)하기 위해 토양(土壤)에 비소(砒素)의 농도(濃度)를 달리하고 물관리(管理)를 상시담수(常時湛水)와 이앙후(移秧後) 10일(日)부터 간단관수(間斷灌水)하여 시험(試驗)한 결과(結果)는 다음과 같다. 1) 수도체(水稻體)의 비소흡수(砒素吸收)는 토양중(土壤中) 비소처리구(砒素處理區) 모두 상시담수구(常時湛水區)에 비(比)해 간단관수구(間斷灌水區)에서 뿌리 및 경엽중(莖葉中) 비소함량(砒素含量)이 크게 억제(抑制)되었고 수도(水稻)의 생육(生育)도 상시담수구(常時湛水區)에 비(比)해 간단관수구(間斷灌水區)에서 그 피해(被害)가 크게 경감(輕減)되었다. 2) 토양중(土壤中) 비소농도(砒素濃度)가 증가(增加)할수록 경엽(莖葉) 및 뿌리 중(中) 무기성분함량(無機成分含量)은 크게 감소(減少)하는 경향(傾向)이나 질소함량(窒素含量)은 증가(增加)되었으며, 간단관수구(間斷灌水區)에 비(比)해 상시담수구(常時湛水區)에서 이들 무기양분함량(無機養分含量)은 더 높았다. 3) 토양중(土壤中) 비소농도(砒素濃度)가 증가(增加)함에 따라 토양(土壤) pH는 증가(增加)하는 경향(傾向)이나 토양(土壤) Eh는 별(別)차이가 없었으며, 상시담수구(常時湛水區)에서는 간단담수구(間斷灌水區)에 비(比)해 토양(土壤) pH는 높아지나, 토양 Eh는 낮아졌다. 4) 물관리(管理)에 의(依)한 토양중(土壤中) 비소형태별(砒素形態別) 분포(分布)는 토양중(土壤中) 비소농도(砒素濃度)가 높아짐에 따라 상시담수구(常時湛水區)에서는 수용성비소(水溶性砒素)(Ws-As)와 Ca-As가 증가(增加)하는 경향(傾向)이나 간단관수구(間斷灌水區)에서는 별다른 경향(傾向)이 없었다.

  • PDF

비정질 파이로프의 저온 압축에 따른 구조 변화를 이용한 멀티 앤빌 프레스의 상온 압력-부하 보정 (Pressure-load Calibration of Multi-anvil Press at Ambient Temperature through Structural Change in Cold Compressed Amorphous Pyrope)

  • 이주호;김용현;이아침;김은정;이서영;이성근
    • 광물과 암석
    • /
    • 제35권1호
    • /
    • pp.65-73
    • /
    • 2022
  • 지구/행성 내부의 다양한 지질학적 과정을 이해하기 위해서는 고온-고압 환경에서 지구 내부 구성물질의 특성을 이해하는 것이 필수적이다. 이러한 고압환경을 생성하기 위하여 사용되는 멀티 앤빌 프레스(multi-anvil press)는 주로 상부맨틀조건의 극한 상황을 재현하는데 사용된다. 멀티 엔빌프레스의 지질학적 사용을 위한 필수 보정 과정 중 하나는 압력을 생성하기 위한 프레스의 유압과 실제로 시료에 가해지는 압력 사이의 관계인 압력-부하 보정(pressure-load calibration)이다. 압력-부하 보정은 일반적으로 고온-고압 조건에서는 결정질 물질의 상전이를 이용해서 이루어지는데, 고온에서의 경우와 달리 저온(상온)의 경우 상전이 과정이 상대적으로 비효율적이므로 압력-부하 보정의 다른 방법론이 요구된다. 본 연구에서는 파이로프 조성(Mg3Al2Si3O12)의 비정질(비정질 파이로프)의 상온에서의 압축(cold compression)에 따라 발생하는 영구적인 고밀도화 현상(permanent densification)과 그 기원이 되는 알루미늄 배위 환경의 변화를 고해상도의 27Al MAS 및 3QMAS NMR 분광분석을 통해 정량화하고, 이로부터 압력에 따른 알루미늄의 배위수 변화를 이용해 14/8 HT 조립세트(assembly set)와 1,100톤 멀티 앤빌 프레스에 대한 상온에서의 압력-부하 보정을 수행하였다. 본 연구는 NMR분광분석을 이용하여 압력보정을 수행한 최초의 연구결과이며, 비정질 파이로프의 압축-감압에 따른 원자 단위에서의 비가역적 구조 변화는 섭입대 환경과 같은 저온 고압 환경에서 비정질 물질이 겪는 변화와 그에 따른 지질학적 현상의 이해고양에 실마리를 제공한다.

지하수 관개에 의한 수도의 멸준양상과 그 방지책에 관한 연구 (Studies on the Rice Yield Decreased by Ground Water Irrigation and Its Preventive Methods)

  • 한욱동
    • 한국농공학회지
    • /
    • 제16권1호
    • /
    • pp.3225-3262
    • /
    • 1974
  • The purposes of this thesis are to clarify experimentally the variation of ground water temperature in tube wells during the irrigation period of paddy rice, and the effect of ground water irrigation on the growth, grain yield and yield components of the rice plant, and, furthermore, when and why the plant is most liable to be damaged by ground water, and also to find out the effective ground water irrigation methods. The results obtained in this experiment are as follows; 1. The temperature of ground water in tube wells varies according to the location, year, and the depth of the well. The average temperatures of ground water in a tubewells, 6.3m, 8.0m deep are $14.5^{\circ}C$ and $13.1^{\circ}C$, respercively, during the irrigation period of paddy rice (From the middle of June to the end of September). In the former the temperature rises continuously from $12.3^{\circ}C$ to 16.4$^{\circ}C$ and in the latter from $12.4^{\circ}C$ to $13.8^{\circ}C$ during the same period. These temperatures are approximately the same value as the estimated temperatures. The temperature difference between the ground water and the surface water is approximately $11^{\circ}C$. 2. The results obtained from the analysis of the water quality of the "Seoho" reservoir and that of water from the tube well show that the pH values of the ground water and the surface water are 6.35 and 6.00, respectively, and inorganic components such as N, PO4, Na, Cl, SiO2 and Ca are contained more in the ground water than in the surface water while K, SO4, Fe and Mg are contained less in the ground water. 3. The response of growth, yield and yield components of paddy rice to ground water irrigation are as follows; (l) Using ground water irrigation during the watered rice nursery period(seeding date: 30 April, 1970), the chracteristics of a young rice plant, such as plant height, number of leaves, and number of tillers are inferior to those of young rice plants irrigated with surface water during the same period. (2) In cases where ground water and surface water are supplied separately by the gravity flow method, it is found that ground water irrigation to the rice plant delays the stage at which there is a maximum increase in the number of tillers by 6 days. (3) At the tillering stage of rice plant just after transplanting, the effect of ground water irrigation on the increase in the number of tillers is better, compared with the method of supplying surface water throughout the whole irrigation period. Conversely, the number of tillers is decreased by ground water irrigation at the reproductive stage. Plant height is extremely restrained by ground water irrigation. (4) Heading date is clearly delayed by the ground water irrigation when it is practised during the growth stages or at the reproductive stage only. (5) The heading date of rice plants is slightly delayed by irrigation with the gravity flow method as compared with the standing water method. (6) The response of yield and of yield components of rice to ground water irrigation are as follows: \circled1 When ground water irrigation is practised during the growth stages and the reproductive stage, the culm length of the rice plant is reduced by 11 percent and 8 percent, respectively, when compared with the surface water irrigation used throughout all the growth stages. \circled2 Panicle length is found to be the longest on the test plot in which ground water irrigation is practised at the tillering stage. A similar tendency as that seen in the culm length is observed on other test plots. \circled3 The number of panicles is found to be the least on the plot in which ground water irrigation is practised by the gravity flow method throughout all the growth stages of the rice plant. No significant difference is found between the other plots. \circled4 The number of spikelets per panicle at the various stages of rice growth at which_ surface or ground water is supplied by gravity flow method are as follows; surface water at all growth stages‥‥‥‥‥ 98.5. Ground water at all growth stages‥‥‥‥‥‥62.2 Ground water at the tillering stage‥‥‥‥‥ 82.6. Ground water at the reproductive stage ‥‥‥‥‥ 74.1. \circled5 Ripening percentage is about 70 percent on the test plot in which ground water irrigation is practised during all the growth stages and at the tillering stage only. However, when ground water irrigation is practised, at the reproductive stage, the ripening percentage is reduced to 50 percent. This means that 20 percent reduction in the ripening percentage by using ground water irrigation at the reproductive stage. \circled6 The weight of 1,000 kernels is found to show a similar tendency as in the case of ripening percentage i. e. the ground water irrigation during all the growth stages and at the reproductive stage results in a decreased weight of the 1,000 kernels. \circled7 The yield of brown rice from the various treatments are as follows; Gravity flow; Surface water at all growth stages‥‥‥‥‥‥514kg/10a. Ground water at all growth stages‥‥‥‥‥‥428kg/10a. Ground water at the reproductive stage‥‥‥‥‥‥430kg/10a. Standing water; Surface water at all growh stages‥‥‥‥‥‥556kg/10a. Ground water at all growth stages‥‥‥‥‥‥441kg/10a. Ground water at the reproductive stage‥‥‥‥‥‥450kg/10a. The above figures show that ground water irrigation by the gravity flow and by the standing water method during all the growth stages resulted in an 18 percent and a 21 percent decrease in the yield of brown rice, respectively, when compared with surface water irrigation. Also ground water irrigation by gravity flow and by standing water resulted in respective decreases in yield of 16 percent and 19 percent, compared with the surface irrigation method. 4. Results obtained from the experiments on the improvement of ground water irrigation efficiency to paddy rice are as follows; (1) When the standing water irrigation with surface water is practised, the daily average water temperature in a paddy field is 25.2$^{\circ}C$, but, when the gravity flow method is practised with the same irrigation water, the daily average water temperature is 24.5$^{\circ}C$. This means that the former is 0.7$^{\circ}C$ higher than the latter. On the other hand, when ground water is used, the daily water temperatures in a paddy field are respectively 21.$0^{\circ}C$ and 19.3$^{\circ}C$ by practising standing water and the gravity flow method. It can be seen that the former is approximately 1.$0^{\circ}C$ higher than the latter. (2) When the non-water-logged cultivation is practised, the yield of brown rice is 516.3kg/10a, while the yield of brown rice from ground water irrigation plot throughout the whole irrigation period and surface water irrigation plot are 446.3kg/10a and 556.4kg/10a, respectivelely. This means that there is no significant difference in yields between surface water irrigation practice and non-water-logged cultivation, and also means that non-water-logged cultivation results in a 12.6 percent increase in yield compared with the yield from the ground water irrigation plot. (3) The black and white coloring on the inside surface of the water warming ponds has no substantial effect on the temperature of the water. The average daily water temperatures of the various water warming ponds, having different depths, are expressed as Y=aX+b, while the daily average water temperatures at various depths in a water warming pond are expressed as Y=a(b)x (where Y: the daily average water temperature, a,b: constants depending on the type of water warming pond, X; water depth). As the depth of water warning pond is increased, the diurnal difference of the highest and the lowest water temperature is decreased, and also, the time at which the highest water temperature occurs, is delayed. (4) The degree of warming by using a polyethylene tube, 100m in length and 10cm in diameter, is 4~9$^{\circ}C$. Heat exchange rate of a polyethylene tube is 1.5 times higher than that or a water warming channel. The following equation expresses the water warming mechanism of a polyethylene tube where distance from the tube inlet, time in day and several climatic factors are given: {{{{ theta omega (dwt)= { a}_{0 } (1-e- { x} over { PHI v })+ { 2} atop { SUM from { { n}=1} { { a}_{n } } over { SQRT { 1+ {( n omega PHI) }^{2 } } } } LEFT { sin(n omega t+ { b}_{n }+ { tan}^{-1 }n omega PHI )-e- { x} over { PHI v }sin(n omega LEFT ( t- { x} over {v } RIGHT ) + { b}_{n }+ { tan}^{-1 }n omega PHI ) RIGHT } +e- { x} over { PHI v } theta i}}}}{{{{ { theta }_{$\infty$ }(t)= { { alpha theta }_{a }+ { theta }_{ w'} +(S- { B}_{s } ) { U}_{w } } over { beta } , PHI = { { cpDU}_{ omega } } over {4 beta } }}}} where $\theta$$\omega$; discharged water temperature($^{\circ}C$) $\theta$a; air temperature ($^{\circ}C$) $\theta$$\omega$';ponded water temperature($^{\circ}C$) s ; net solar radiation(ly/min) t ; time(tadian) x; tube length(cm) D; diameter(cm) ao,an,bn;constants determined from $\theta$$\omega$(t) varitation. cp; heat capacity of water(cal/$^{\circ}C$ ㎥) U,Ua; overall heat transfer coefficient(cal/$^{\circ}C$ $\textrm{cm}^2$ min-1) $\omega$;1 velocity of water in a polyethylene tube(cm/min) Bs ; heat exchange rate between water and soil(ly/min)

  • PDF