• 제목/요약/키워드: Deep Soil

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지하수내 갈색 부유/침전 물질의 생성 반응에 관한 평형 및 반응속도론적 연구: 적정 양수 기법 및 탁도 제거 방안에 대한 제안 (Geochemical Equilibria and Kinetics of the Formation of Brown-Colored Suspended/Precipitated Matter in Groundwater: Suggestion to Proper Pumping and Turbidity Treatment Methods)

  • 채기탁;윤성택;염승준;김남진;민중혁
    • 대한지하수환경학회지
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    • 제7권3호
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    • pp.103-115
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    • 2000
  • 갈색 침전물의 생성은 우리나라 지하수의 개발 및 공급에 있어 흔히 발생하는 문제 중의 하나인데, 이에 따라 색도, 맛, 탁도 및 용존 철 함량 등의 항목에 있어 먹는 물 수질 기준을 초과하게 되고, 물 공급 시스템에 스케일링의 문제를 야기하게 된다. 경기도 파주 지역 지하수의 경우에도 양수 후 몇 시간 내에 갈색 침전물이 형성되어 수질을 악화시키고 있다. 본 연구에서는 지하수의 탁도를 유발하는 원인과 지화학적 반응 경로를 이해하고자, 평형열역학 및 반응속도론적 접근을 통하여 갈색 침전물의 형성과정을 파악하였다. 본 연구결과는 침전물의 형성을 최소화하기 위한 적정 양수 기법은 물론 수질 향상을 위한 최적 수처리 기법을 설계하는데 있어 중요한 자료로 활용될 것이다. 파주 지역의 암반 지하수는 물/암석(편마암)반응에 의해 Ca-$HCO_3$형의 수질 특성을 보인다. SEM-EDS 및 XRD 분석 결과, 갈색 침전물은 비정질의 함철 산화물 또는 수산화물로 해석된다. 다양한 공극 크기(6, 4, 1, 0.45, 0.2 $\mu\textrm{m}$)를 갖는 여과지를 이용한 다단계 여과 결과, 이들 침전물은 크기에 있어 대부분 1 내지 0.45$\mu\textrm{m}$의 입도를 갖는 콜로이드 형태이지만, 질량 분포로 볼 때는 1 내지 6$\mu\textrm{m}$범위가 우세함(총 질량의 약 81%)을 알 수 있다. 다량의 용존 철(II)은 지하수 유동 중에 철 함량이 높은(최대 3wt.%) 단층 파쇄암 내의 녹니석(clinochore)의 용해로부터 기원하는 것으로 판단된다. PHREEQC 프로그램을 이용한 포화지수 계산 및 pH-Eh 관계도에 대한 검토 결과, 침전물은 함철 수산화물임이 확인되며, 환원 조건에 있던 심부 지하수가 양수에 의해 산소에 노출되면서 화학성 변화(특히, 산화)에 의하여 침전함을 알 수 있다. 양수 이후의 시간 경과와 더불어 양수된 지하수의 pH, DO, 알칼리도는 점차 감소하며. 탁도는 증가하다가 일정 시간 경과 후 감소하는 경향을 보인다. 양수 이후의 경과 시간에 따른 용존 철(II)의 농도 감소율(즉, 반응 속도)은 Fe(II)=10.l exp(-0.0009t)로 표현된다. 따라서 갈색 침전물의 생성 반응은 양수 및 양수 후 저장 과정 중에 산소의 유입에 따른 산화 반응에 기인하며, 그 반응은 시간, 산소분압 및 pH에 의존함을 알 수 있다. 탁도를 제거하여 음용 가능한 수질을 확보하기 위해서는, 충분한 시간 동안 충분한 크기를 갖는 탱크 내에서의 다단계 저장 및 폭기를 거친 이후에 응집된 침전물에 대한 여과가 제안된다. 이때, 비용 절감 차원에서 상이한 입도 조건에서의 다단계 여과가 효과적일 것으로 생각된다. 한편, 개발 관정 내에서의 스케일링을 최소화하기 위해서는 심부 지하수로 산소가 풍부한 천층 지하수가 유입되는 과정을 최소화할 필요가 있다. 이를 위해서는 적정 채수량 범위 내에서의 지속적인 양수가 효과적일 것이다. 아울러, 산소가 풍부한 천층 지하수의 채수를 위한 별도의 관정 설치도 고려할 수 있을 것이다.

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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
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    • 제16권1호
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    • pp.3225-3262
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    • 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)

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