• 한국농공학회지
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• 제15권4호
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• pp.3170-3180
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• 1973

This study of the subject will review past and present irrigation development in Korea. Particular attention will be given to water pricing structure and a case study on the purpose of rational operation and management of irrigation water and organizations, and the optimum irrigation water and organizations, and the optimum irrigation water fee inorder to reduce farmers burden and to rationalize the farmland associations management so as to achieve development of the rural environment. In 1971, the reservoir of the Farmland Improvement A sociation (FIA) produced only 775 millison $m^3$ of irrigation water or 77% of planned capacity of 1,015 million $m^3$. It was caused by inefficient maintenance of irrigation facilities; for instance, about 21% of reservoirs, pumping stations and weirs in Korea have been silted by soil erosion which hinder to water production according to an ADC survey. The first Irritation Association was established in 1906, whcih was renamed the Farmland Assoeiation by the Rural Development Enouragement Law in 1970. By the end of 1971, 411,000 ha of rice paddies were under the control of 267 associations nationwide. The average water price assessed by Associations nationwide rose from 790 won per 0.1 ha. in 1966 to 1,886 won in 1971. The annual growth rate was 20%. The highest water price in 1971 was 4,773 won her 0.1 ha. and the lowest was 437 won. This range was caused by differences in debt burden, geographic conditions and management efficiency among the Associations. In 1971, the number of Associations which exceeded the average water price of 1,886 won per 0.1 ha. was 144, or 55.1% of all Association. In determination of water price, there are two principles; one is determined by production cost such as installation cost of irrigation facilities, maintenance cost, management cost and depreciation ect. For instance, the Yong San River Development project was required 33.7 billion won for total construction and maintenance cost is 3.1 billion won for repayment, maintenance and management cost per year. The project produces 590 million $m^3$ of irrigation water annually. Accordingly, the water price per $m^3$ is 5.25 won. The other principle is determined by water value in the crop products and in compared with production of irrigated paddy and non-irrigated paddy. By using this method, water value in compared with paddy rice vs. upland rice(Average of 1967-1971) was 14.15 won per $m^3$ and irrigated paddy vs. non-irrigated paddy was 2.98 won per $m^3$. In contrast the irrigation fee in average association of 1967-1971 was 1.54 won per $m^3$. Accordingly, the current national average irrigation fee(water price) is resonable compared with its water value. In this study, it is found that the ceiling of water price in terms of water value is 2.98 won per $m^3$ or 2,530 won per 0.1 ha. However, in 1971 55% of the associations were above the average of nationwide irrigation fees. which shows the need for rationalization of the Association's management. In connection with rationalization of the Association's management, this study recommends the following matters. (1) Irrigation fee must be assessed according to the amount of water consumption taking intoaccount the farmer's ability. (2) Irrigation fee should be graded according to behefits and crop patterns. (3) Training personnel in the operation and procedures of water management to save O&M costs. (4) Insolvent farmland association should be integrated into larger, sound associations in the same GUN in order to reduce farmers' water cost. (5) The maintenance and repair of existing irrigation facilities is as important as expansion of facilities. (6) Establishment of a new Union of Farmland Association is required to promoted proper maintenance and to protect the huge investment in irrigation facilities by means of technical supervision and guidance.

• 한국수자원학회:학술대회논문집
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• 한국수자원학회 2015년도 학술발표회
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• pp.237-237
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• 2015

The district of Marlborough has had more than its share of river management projects over the past 150 years, each one uniquely affecting the geomorphology and flood hazard of the Wairau Plains. A major early project was to block the Opawa distributary channel at Conders Bend. The Opawa distributary channel took a third and more of Wairau River floodwaters and was a major increasing threat to Blenheim. The blocking of the Opawa required the Wairau and Lower Wairau rivers to carry greater flood flows more often. Consequently the Lower Wairau River was breaking out of its stopbanks approximately every seven years. The idea of diverting flood waters at Tuamarina by providing a direct diversion to the sea through the beach ridges was conceptualised back around the 1920s however, limits on resources and machinery meant the mission of excavating this diversion didn't become feasible until the 1960s. In 1964 a 10 m wide pilot channel was cut from the sea to Tuamarina with an initial capacity of $700m^3/s$. It was expected that floods would eventually scour this 'Wairau Diversion' to its design channel width of 150 m. This did take many more years than initially thought but after approximately 50 years with a little mechanical assistance the Wairau Diversion reached an adequate capacity. Using the power of the river to erode the channel out to its design width and depth was a brilliant idea that saved many thousands of dollars in construction costs and it is somewhat ironic that it is that very same concept that is now being used to deal with the aggradation problem that the Wairau Diversion has caused. The introduction of the Wairau Diversion did provide some flood relief to the lower reaches of the river but unfortunately as the Diversion channel was eroding and enlarging the Lower Wairau River was aggrading and reducing in capacity due to its inability to pass its sediment load with reduced flood flows. It is estimated that approximately $2,000,000m^3$ of sediment was deposited on the bed of the Lower Wairau River in the time between the Diversion's introduction in 1964 and 2010, raising the Lower Wairau's bed upwards of 1.5m in some locations. A numerical morphological model (MIKE-11 ST) was used to assess a number of options which led to the decision and resource consent to construct an erodible (fuse plug) bank at the head of the Wairau Diversion to divert more frequent scouring-flows ($+400m^3/s$)down the Lower Wairau River. Full control gates were ruled out on the grounds of expense. The initial construction of the erodible bank followed in late 2009 with the bank's level at the fuse location set to overtop and begin washing out at a combined Wairau flow of $1,400m^3/s$ which avoids berm flooding in the Lower Wairau. In the three years since the erodible bank was first constructed the Wairau River has sustained 14 events with recorded flows at Tuamarina above $1,000m^3/s$ and three of events in excess of $2,500m^3/s$. These freshes and floods have resulted in washout and rebuild of the erodible bank eight times with a combined rebuild expenditure of $80,000. Marlborough District Council's Rivers & Drainage Department maintains a regular monitoring program for the bed of the Lower Wairau River, which consists of recurrently surveying a series of standard cross sections and estimating the mean bed level (MBL) at each section as well as an overall MBL change over time. A survey was carried out just prior to the installation of the erodible bank and another survey was carried out earlier this year. The results from this latest survey show for the first time since construction of the Wairau Diversion the Lower Wairau River is enlarging. It is estimated that the entire bed of the Lower Wairau has eroded down by an overall average of 60 mm since the introduction of the erodible bank which equates to a total volume of $260,000m^3$. At a cost of $$0.30/m^3$ this represents excellent value compared to mechanical dredging which would likely be in excess of $$10/m^3$. This confirms that the idea of using the river to enlarge the channel is again working for the Wairau River system and that in time nature's "excavator" will provide a channel capacity that will continue to meet design requirements.

• 환경영향평가
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• 제28권5호
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• pp.492-506
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• 2019

공용화기사격장 내 중금속 오염물은 대부분 탄두원형으로 존재하거나 입자로 존재하는 금속조각편이며 이들 미세한 금속입자들은 오랜 기간 풍화되어 표면이 산화물 또는 탄산화물로 존재할 가능성이 매우 높다. 특히 사격장 토양에서 대표적 오염물질인 납은 연성이 높아 무르고 잘 늘어나므로 더 미세입자로 존재한다. 따라서 물리적 세척 실험으로 입도분석, 입경별 중금속농도, 금속물질 성분분석, 비중, 자력, 부상선별의 적용성 평가를 실시하였다. 금속파편의 경우 FESEM분석과 무게측정결과 납은 무른 특성에 따라 얇게 조각나고 편모양의 구조로 비슷한 면적의 구형 토양보다 무게가 더 적게 나가는 것을 확인하였으며 비중선별 적용성이 높은 것을 확인할 수 있었다. 이 결과를 적용하여 하이드로사이클론을 이용한 정화효율평가 결과 1회 71%, 2회 80%, 3회 91%의 누적 정화효율을 보였다. 이에 비해 자력선별은 17%의 낮은 효율을 보였고 부상선별은 입경 0.5 mm 미만으로 선별한 대상토는(-35 mesh) 39%로 비교적 높은 효율을 보였으나 입경 2 mm 미만으로 선별한 대상토의(-10 mesh) 효율은 16%에 불과하였다. 토양세척의 대상 처리입경은 2 mm ~ 0.075 mm로 입도구분을 추가로 하여 실규모 장치에 적용하여야 하며 이는 설치비용과 공정이 추가로 구성됨에 따른 관리가 필요할 것으로 분석되었다. 결과적으로 공용화기사 격장 오염의 토양정화는 탄두 원형을 유지한 탄두는 5.56 mm 이상으로 자갈입경보다 크므로 고비중을 이용한 비중선별을 실시하고, 금속파편으로 존재하는 오염물질은 얇게 조각나고 편모양의 구조로 같은 입경의 토양보다 무게가 더 적음에 따라 토양세척의 하이드로사이클론을 이용하여 분리하여 처리할 수 있음을 확인할 수 있었다.

• 지능정보연구
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• 제26권4호
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• pp.87-109
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• 2020

현재 육상에서는 유무선 통신의 발전으로 다양한 IT 서비스를 제공받고 있다. 이러한 변화는 육상을 넘어서서 해상에서 항해 중인 선박에서도 다양한 IT 서비스가 제공되어야 하며 육상에서 이용하는 것과 마찬가지로 양방향 디지털 데이터 전송, Web, App 등과 같은 다양한 IT 서비스들의 제공에 대한 요구가 증가될 것으로 예상하고 있다. 하지만 이러한 초고속 정보통신망은 AP(Access Point)와 기지국과 같은 고정된 기반 구조를 바탕으로 네트워크를 구성하는 지상에서는 쉽게 사용할 수 있는 반면 해상에서는 고정된 기반 구조를 이용하여 네트워크를 구성할 수 없다. 그래서 전송 거리가 긴 라디오 통신망 기반의 음성 위주의 통신 서비스를 사용하고 있다. 이러한 라디오 통신망은 낮은 전송 속도로 인해 매우 기본적인 정보만을 제공할 수 있었으며, 효율적인 서비스 제공에 어려움이 있다. 이를 해결하기 위해서 디지털 데이터 상호교환을 위한 추가적인 주파수가 할당되었으며 이 주파수를 사용하여 활용할 수 있는 선박 애드 혹 네트워크인 SANET(ship ad-hoc network)이 제안되었다. SANET은 높은 설치비용과 사용료의 위성 통신을 대신하여 해상에서 IP 기반으로 선박에 다양한 IT 서비스를 제공할 수 있도록 개발되었다. SANET에서는 육상 기지국과 선박의 연결성이 중요하다. 이러한 연결성을 갖기 위해서는 선박은 자신의 IP 주소를 할당 받아 네트워크의 구성원이 되어야 한다. 본 논문에서는 선박 스스로 자신의 IP 주소를 할당 받을 수 있는 SANET-CC(Ship Ad-hoc Network-Cell Connection) 프로토콜을 제안한다. SANET-CC는 중복되지 않는 다수의 IP 주소들을 육상기지국에서 선박들에 이어지는 트리 형태로 네트워크 전반에 전파한다. 선박은 IP 주소를 할당할 수 있는 육상 기지국 또는 나누어진 구역의 M-Ship(Mother Ship)들과 간단한 요청(Request) 및 응답(Response) 메시지 교환을 통해 자신의 IP 주소를 할당한다. 따라서 SANET-CC는 IP 충돌 방지(Duplicate Address Detection) 과정과 선박의 이동에 의해 발생하는 네트워크의 분리나 통합에 따른 처리 과정을 완전히 배제할 수 있다. 본 논문에서는 SANET-CC의 SANET 적용가능성을 검증하기 위해서 다양한 조건의 시뮬레이션을 수행하였으며 기존 연구와 비교 분석을 진행하였다.