• 한국농공학회지
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• 제32권E호
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• pp.1-19
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• 1990

Abstract Over the last several decades, crop production in the United States increased largely due to the extensive use of animal waste and fertilizers as plant nutrient supplements, and pesticides for crops pests and weed control. Without the application of animal waste best management, the use of animal waste can result in nonpoint source pollution from agricultural land area. In order to increase nutrient levels and decrease contamination from agricultural lands, nonpoint source pollution is responsible for water quality degradation. Nonpoint source pollutants such as animal waste, ferilizers, and pesticides are transported primarily through runoff from agricultural areas. Nutrients, primarily nitrogen and phosphorus, can be a major water quality problem because they cause eutrophic algae growth. In 1985, it was presented that Watershed/Water Quality Monitoring for Evaluation BMP Effectiveness was implemented for Nomini Creek Watershed, located in Westmoreland County, Virginia. The watershed is predominantly agricultural and has an aerial extent of 1505 ha of land, with 43% under cropland, 54% under woodland, and 3% as homestead and roads. Rainfall data was collected at the watershed from raingages located at sites PNI through PN 7. Streams at stations QN I and QN2 were being measured with V-notch weirs. Water levels at the stream was measured using an FW-l Belfort (Friez FWl). The water quality monitoring system was designed to provide comprehensive assessment of the quality of storm runoff and baseflow as influenced by changes in landuse, agronomic, and cultural practices ill the watershed. As this study was concerned with the Nomini Creek Watershed, the separation of storm runoff and baseflow measured at QNI and QN2 was given by the master depletion curve method, and the loadings of baseflow and storm runoff for TN (Total Nitrogen) and TP (Total Phosphorus) were analyzed from 1987 through 1989. The results were studied for the best management practices to reduce contamination and loss of nutrients, (e.g., total nitrogen and total phosphorus) by nonpoint source pollution from agricultural lands.

• 한국항행학회논문지
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• 제21권2호
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• pp.193-199
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• 2017

본 논문에서는 이중대역 저지 특성을 가지는 2.4 GHz WLAN (2.4 ~ 2.484 GHz) 및 UWB (3.1 ~ 10.6 GHz) 겸용 모노폴 안테나를 제안하였다. 3.5 GHz WiMAX 대역 저지 특성을 얻기 위하여 기존의 방사패치 중앙에 위치한 U-형태 슬롯을 대신하여 방사패치 가장자리에 위치하는 한쌍의 L-형 슬롯이 사용되고, 반면에 7.5 GHz 대역 저지를 위하여 급전선 인근에 배치되는 한 쌍의 C-형태의 스트립 공진기를 사용한다. 제안된 안테나의 제작 및 측정 결과, 임피던스 대역폭 (${\mid}S_{11}{\mid}{\leq}-10dB$) 이 8.62 GHz (2.38 ~ 11 GHz)로 2.4 GHz WLAN 대역을 포함한 UWB 대역을 충분히 만족하고, 반면에 3.5 GHz WiMAX 저지 대역 (${\mid}S_{11}{\mid}$ > -10 dB) 은 1.13GHz (3.15 ~ 4.28 GHz), 7.5 GHz 저지 대역은 800 MHz (7.2~8 GHz) 의 저지 대역폭을 가지는 것을 확인 할 수 있었다. 특히 사용하고자 하는 전 주파수 대역에서 안정되고 우수한 무지향성 방사패턴을 얻을 수 있었으며 2.51~6.81 dBi의 높은 이득 또한 얻을 수 있었다.

• 한국항해항만학회:학술대회논문집
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• 한국항해항만학회 2009년도 공동학술대회
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• pp.475-486
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• 2009

목도의 지질조사가 한국 역사상 이번에 처음으로 수행되었다. 목도가 중생대 말기 약$7,000{\sim}8,000$만년 전에 성층화산으로 분출하여 화산원형이 개석됨으로서 현재는 Planeze 단계를 지나 골격단계에 이른 것으로 밝혀졌다. 추후에 정밀조사를 한다면 분화구 자리도 찾아질 수 있을 것이다. 목도에는 50m고도에 해성단구면이 있다. 이는 제4단구면에 대비되고 홍적세 후기에 생성된 것으로 추정된다. 목도의 해안에 발달한 해안의 미지형으로는 해안단구, 해식애, 해식동, 파식대, 해안석주, 낭식장, 타포니(풍화혈) 등이 발견되었다. 목도는 산경도(山徑圖)에 표시되어 있는 낙동정맥의 남방 연장선 위 몰운대 앞바다에 위치하며 "물에 뜬 거북이"형국(부해금귀형(浮海金龜形)) 혹은 "물에서 나오고 있는 거북이"형국(출수금귀형(出水金龜形))이다. 목도의 도서명은 그 정체성을 위하여 "유구도"(游龜島) "남구도"(南龜島) "회구도"(廻龜島)중에서 선택하여 개칭할 필요가 있다. 목도는 부산의 관광수요를 위한 새로운 관광명소로 발전, 개발되는데 필요한 관광자연배경을 충분히 가지고 있으며, 앞으로 이 무인도서가 분산의 등대섬, 그리고 유,무인도서라 연계하여 해양관광을 개발한다면 새로운 관광지로서 행양수도발전에 지대한 영향력을 가질 수 있다고 평가되었다. 목도의 주변해역에 해양수족관과 해초정원을 조성하고 수목원을 조성하며 기타 해양문화공간조성의 종합기본계획이 이 연구에서 완성되었다.

• Restorative Dentistry and Endodontics
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• 제27권2호
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• pp.142-149
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• 2002

Low-viscosity composite resins may produce better sealed margins than stiffer compositions (KempScholte and Davidson, 1988: Crim, 1989). Plowable composites have been recommended for use in Class V cavities but it is also controversial because of its high rates of shrinkage. On the other hand, in the study comparing elastic moduli and leakage, the microfill had the least leakage (Rundle et at. 1997) Furthermore, in the 1996 survey of the Reality Editorial Team, microfills were the clear choice for abfraction lesions. The purpose of this study was to evaluate the microleakage of 6 compostite resins (2 hybrids, 2 microfills, and 2 flowable composites) with and without load cycling. Notch-shaped Class V cavities were prepared on buccal surface of 180 extracted human upper premolars on cementum margin. The teeth were randomly divided into non-load cycling group (group 1) and load cycling group (group 2) of 90 teeth each. The experimental teeth of each group were randomly divided into 6 subgroups of 15 samples. All preparations were etched, and Single bond was applied. Preparations were restored with the following materials (n=15) : hybrid composite resin [Z250(3M Dental Products Inc. St. Paul, USA), Denfil(Vericom, Ahnyang, Korea)], microfill [Heliomolar RO(Vivadent, Schaan, Liechtenstein), Micronew(Bisco Inc. Schaumburg, IL, USA)], and flowable composite［AeliteFlo(Bisco Inc. Schaumburg, IL, USA), Revolution(Kerr Corp. Orange, CA, USA)]. Teeth of group 2 were subjected to occlusal load (100N for 50,000 cycles) using chewing simulator(MTS 858 Mini Bionix II system, MTS Systems Corp. Minn. USA). All samples were coated with nail polish 1mm short of the restoration, placed in 2％ methylene blue for 24 hours, and sectioned with a diamond wheel. Enamel and dentin/cementum margins were analyzed for microleakage on a sclale of 0 (no leakage) to 3 (3/3 of wall). Results were statistically analyzed by Kruscal-Wallis One way analysis, Mann-Whitney U-test, and Student-Newmann-Keuls method. (p = 0.05) Results : 1. There was significantly less microleage in enamel margins than dentinal margins of all groups (p＜0.05) 2. There was no significant between six composite resin in enamel margin of group 1. 3. In dentin margin of group 1, flowable composite had more microleakage than others but not of significant differences. 4. there was no significant difference between six composite resin in enamel margin of group 2. 5. In dentin margin of group 2, the microleakage were R＞A =H=M＞D＞Z. But there was no significant differences. 6. In enamel margins, load cycling did not affect the marginal microleakage in significant degree. 7. In enamel margins, load cycling did affect the marginal microleakage only in Revolution. (p＜0.05).