꽁치봉수망 조업시 어선의 집어등에 의한 수중환경의 변화를 밝혀 광 환경이 꽁치의 어획에 미치는 영향을 분석하기 위한 기초 단계로 수중 조도를 측정하여 꽁치가 분포하는 어획 수층의 광 환경을 분석한 결과를 요약하면 다음과 같다. 공기중에서 홍색 백열등과 할로겐등의 방사조도는 둘 다 1,052nm의 파장에서 최대치를 보인 후 감소하는 경향을 나타내었고, 600nm이하의 파장에서는 할로겐등이 홍색 백열등에 비해 방사조도가 약간 높게 나타났다. 공기중 조도는 좌현 선미에서 가장 높았고 선수에서 가장 낮게 나타났다. 조사해역에서의 집어등 불빛의 수중투과 특성은 50m 수층에서 각각 0.31x, 0.61x 이하로 나타났으며 일반적인 꽁치어장의 특성을 가진 어장에서 볼 때 , 꽁치가 집어되는 수층의 조도는 0.51x 이상인 것으로 보인다.

초망어업에 있어서 멸치군을 집어하기 위한 집어등의 광량을 구명하기 위한 기초연구로서 1 ㎾ 와 2 ㎾ 백열등의 방사조도 특성을 계측하였으며, 그 결과를 요약하면 다음과 같다. 1. 백열등의 수중방사조도는 파장 690 nm에서 최대치를 보였고, 2가지 백열등의 수중 방사조도 L(W/ cm2/nm)와 섬도 Z(m)와의 관계식은, 1 ㎾ : L = 3851.9 e-1.4587Z R2=0.9952 2 ㎾ : L= 8211.9 e-1.2852Z R2=0.9977이었다. 2. 2 ㎾ 백열등의 수중 방사조도는 섬도 4m 층보다 얕은 수층에서는 1 ㎾ 백열등보다 3~4배 높게 나타났지만 심도 6m보다 깊은 수층부터는 동일한 밝기를 나타내었다. 3. 1 ㎾ 백열등의 빛은 정횡방향보다 연직방향쪽으로 많이 투과되었으며, 집어등의 연직방향에 있어서 심도 20m층의 수중방사조도는 0.1 lχ이었다.

The purpose of this study was to compare the experimental pain threshold when used in luminous lamp radiation and nonluminous lamp radiation with healthy person. Thirty normal subjects were randomly assigned two groups: a luminous lamp radiation group, and a nonluminous lamp radiation group. The infrared lamps were applied on L3 for thirty minutes. Each group was measured for experimental pain threshold and local temperature before, 15 and 30 minute radiation. For statistical differences in change of the experimental pain threshold and local temperature due to differences in lamp ray was compared using the independent t-test. And, General linear model for profile plots test was used. The results were as: 1. Local temperature was significantly increased in the nonluminous lamp group (p<.01). 2. Experimental pain thershold was significantly increased in the luminous lamp group (p<.05),(p<.01). This study indicate that luminous lamp radiation was more effects of increase experimental pain thershold than nonluminous lamp radiation. Further study is needed to compare the effects of after period radiation.

멸치초망어업에서는 반사갓에 AC 100V, 1kW 백열등 1개를 끼워서 집어등으로 사용하고 있다. 집어등은 저층에 있는 어군을 표층까지 부상시키고, 또한 표층에 유집된 어군을 자루그물로 유도하는 역할을 수행하고 있다. 본 연구에서는 멸치군을 유효하게 집어, 유도할 수 있는 집어 등을 구명하기 위한 기초연구로서 현재 초망어업에서 사용되고 있는 반사갓의 방사효율과 1kW 백열등의 파장별 방사특성을 계측하였으며, 그 결과를 요약하면 다음과 같다. 1. 반사갓은 백열등의 방사효율을 1.8배 정도 증가시켰으며, 전구를 중심으로 원형에 가깝게 빛을 수중으로 방사시켰고, 이는 수중광도계로 측정한 방사조도와도 잘 일치하였다. 2. 공기중에서 백열등의 방사조도는 994nm의 파장에서 최대치를 보인 반면 심도 0.5m, 1.0m 층에서 최대치를 보인 반면 심도 0.5m, 1.0m층에서는 모두 690nm의 파장에서 최대치를 보였다. 3. 집어등의 연직 하방에 있어서 심도(x)과 수중조도(y)와의 관계식은 다음과 같다. y=146.03e 상(-0.37x) 4. 1kW 백열등의 빛은 정횡방향보다 연직방향쪽으로 많이 투과되었으며, 집어등 직하에서의 빛은 심도 20m이심에는 도달하지 않는다고 추정된다.

The author examined the response of Amberjacks, Seriola quinqueradiata [TEMMINCI et SCHLIBEL] to the surface attracting lamps (0.5W, 0.8W, 1W) line in the experimental water tank (550 L×58W×73Hcm).The attracting rate was investigated in accordance with the intervals of lighting and putting out hour (1,5 minute) when each of the attracting lamps was gradually switched off after they were switched on all at once. The results are as follows:1. Total distribution rate of fish in the illuminated section was 92.4% (mean 18.5%) in case of 1 minute interval, and 95.8% (mean 19.2%) in case of 5 minutes interva. 2. Mean distribution rate of fish at the illuminated section: Distribution rate at interval of 1 minute were 19.0% in 1W, 18.4% in 0.5W, and 18.0% in 0.8W respectively. distribution rate at interval of 5 minutes were 19.5% in 1W, 19.2% in 0.5 W, and 18.8% in 0.8W respectively.3. Attracting rates of the last section showed very much increasing as illuminating time elapsed, but there was a little difference of attracting rates according to interval and lighting source. 4. Attracting rate of fish in only last section switched on : Attracting rate at interval in case of 1 minute were 97.0% in 1W, 86.0% in 0.8W and 74.0% in 0.5W respectively. Attracting rate at interval in case of 5 minutes were 97.3% in 1W, 90.0% in 0.5W and 88.0% in 0.8W respectively.

We selected horse mackerel Trachurus japonicus, mackerel Scomber japonicus and arrow squid Todarodes pacificus, to use in the experiment. These fishes migrate to the Cheju coast and were caught by set-net. We studied the leading effect on the fish schools using the attracting lamps in an outdoor water tank at the Marine Research Institute in Cheju National University. The results obtained are summarized as follows; 1. The attracting rate of fish schools was increasing as the time between switching on and off each lamp was getting longer when each of the attracting lamps was switched on and off in order. However, the attracting rate of mackerel school showed a tendency to be higher than that of the other two species. 2. The attracting rate of fish schools was increasing as the time of switching off the lamps was getting longer when the attracting lamps which had been switched on were switched off in order. However, the attracting rate of mackerel school showed a tendency to be higher than that of the other two species. 3. The attracting rate of fish schools was decreasing as the speed of moving the attracting lamp was getting faster when the attracting lamp was moving. However, the attracting rate of mackerel school showed a tendency be higher than that of the other two species. 4. To determine the distance between the attracting lamps, there would be two methods. One is switching on and off the attracting lamps in order, and the other is switching off the attracting lamps in order which had been switched on. The methods showed that the attracting rate of fish schools were decreasing as the distance between the attracting lamps were getting longer. However, the attracting rate of mackerel school showed a tendency to be higher than that of the other two species.

The author examined the response of Yoroi-mebaru, Sebastes hubbsi [MATSUBARA] to the underwater attracting lamps (0.5 W, 0.8 W, 1 W) line in the experimental water tank (550 L x 58 W x 73 H cm). The attracting rate investigated in accordance with the intervals of lighting and putting out hour (1, 5 minutes) when each of the underwater attracting lamps was gradually switched off after they were switched on all at once. The results are a follows: 1. Distribution rates of fish in the illuminated area was 35.7 % in case of 1 minute interval, and 50.3 % in case of 5 minutes interval. 2. Mean distribution rate of fish at the illuminated section: \circled1 Distribution rates at interval of 1 minute were 9.8 % in 1 W, 6.5 % in 0.8 W and 5.1 % in 0.5 W, respectively. \circled2 Distribution rates at interval of 5 minutes were 15.6 % in 1 W, 8.5 % in 0.5 W and 6.1 % in 0.8 W, respectively. 3. Attracting rates of the last section showed a little increasing as illuminating time elapsed. A difference of attracting rates according to lighting source in 5 minutes interval were bigger than that in 1 minute interval. 4. Attracting rates of fish in only last section switched on: \circled1 Attracting rates at interval in case of 1 minute were 30.0 % in 0.8 W, 16.0 % in 1 W and 8.0 % in 0.5 W, respectively. \circled2 Attracting rates at interval in case of 5 minutes were 56.0 % in 1 W, 30.7 % in 0.5 W and 10.7 % in 0.8 W. respectively.

The author examined the response of Armorclad rockfish, Sebastes hubbsi [MATSUBARA]to the surface attracting lamps (0.5W, 0.8W, 1W) line in the experimental water tank (550L×58W×73Hcm). The attraction rate was investigated in accordance with the intervals of lighting and putting out hour (1,5 minute) when each of the attraction lamps was gradually switched off after they were switched on all at once. The results are as follows : 1. Total distribution rate of fish in the illuminated section was 61.6%(mean 12.3%) in case of 1 minute interval, and 41.0%(mean 8.2%) in case of 5 minutes interval. 2. Mean distribution rate of fish at the illuminated section : ①Distribution rate at interval of 1 minute were 12.7% in 0.8W, 12.4% in 0.5W and 11.9% in 1 W respectively. ②Distribution rate at interval of 5 minutes were 9.0% in 1W, 8.6% in 0.8W and 7.0% in 0.5W respectively. 3. Attraction rates of the last section showed a little increasing as illuminating time elapsed. A difference of attraction rates according to lighting source in 1 minute interval was bigger than that in 5 minute interval. 4. Attraction rate of fish in only last section switched on : ①Attraction rate at interval in case of 1 minute were 52.0% in 0.8W, 46.7% in 0.5%W and 45.3% in 1W respectively. ②Attraction rate at interval in case of 5 minutes were 32.0% in 1W, 24.0% in 0.8W and 14.7% in 0.5W respectively.

The author examined the response of File fish, Stephanolepis Cirrhifer (TEMMINCK et SCHLEGEL) to the surface attracting lamps(0.5W, 0.8W, 1W) line in the experimental water tank (550L×58W×73H cm). the attracting rate was investigated in accordance with the interval of lighting and putting out hour (1, 5 minute)when each of the attracting lamps was gradually switched off after they were switched on all at once. The results are as follows: 1. Total distribution rate of fish in the illuminated section was 96.9%(mean 19.4%) in case of 1 minute interval, and 98.4%(mean 19.7%) in case of 5 minutes interval. 2. Mean distribution rate of fish at the illuminated section: ① Distribution rate at interval of 1 minute were 19.9% in 0.8W, 19.3% in 1W and 18.9% in 0.5W respectively. ② Distribution rate at interval of 5 minutes were 19.8% in 1W, 19.8% in 0.8W, and 19.5% in 0.5W respectively. 3. Attracting rate of the last section showed increasing as illuminating time elapse without interval and lighting source. 4. Attracting rate of fish in only last section switched on: ① Attracting rate at interval in case of 1 minute were 98.0% in 1W, 97.0% in 0.5W and 83.0% in 0.8W respectively. ② Attracting rate at interval in case of 5 minutes were 99.3% in 1W, 97.3% in 0.5W and 93.3% in 0.8W respectively.

ZMR공정에서 발생하기 쉬운 폴리실리콘의 엉김현상(agglomeration), 슬림, 그리고 실리콘기판이 국부적으로 녹는 현상 등을 방지하기 위한 방법과 재결정화된 박막의 질을 향상시키기 위하여 폴리실리콘과 보호 산화막(capping oxide)두계를 변화시킨 실험 결과를 서술한다. 폴리실리콘의 엉김현상은 폴리실리콘과 보호 산화막 그리고 폴리실리콘과 매몰 산화막(buried oxide)의 계면에서의 wetting각과 관계되는데, 엉김현상을 방지하기 위해서는 암모니아 가스 분위기에서 1100˚C, 3시간 동안 열처리하여 폴리실리콘과 보호 산화막 그리고 폴리실리콘과 매몰 산화막의 계면에 질소를 주입시키면 된다. 실리콘 기판의 뒷면이 국부적으로 녹아 SOI구조가 파괴되는 현상과 슬립은 실리콘 기판의 뒷면을 모래타격(sandblast)하여 약 20μm의 거칠기를 가지도록 했을때 방지할 수 있었다. 재결정화된 폴리실리콘의 두께가 두꺼워짐에 따라 재결정화된 박막에서 subboundary의 간격은 넓어지고, 재결정화된 실리콘 두께의 균일성은 보호 산화막이 두꺼울수록 향상된다. 폴리실리콘의 두께를 1μm로 하였을때 subboundary의 간격은 약 70-120μm정도였고 폴리실리콘의 두께가 1μm이고 보호산화막의 두께가 2.5μm일때, 재결정화 후 실리콘의 두게 균일도는 약 ±200Å정도였다.

The author has examined the response of sting fish, Sebastes inermis and black porgy, Acanthopagrus schlegelii to the attraction lamps(1 W) line in an experimental water tank(550 L× 58 W × 73H cm). Attraction lamp was set up at intervals of 55 cm for each section. The frequency rate was investigated at the illuminated section in accordance with the intervals of lighting on and putting out that was 1, 3 and 5 minutes under two conditions of light stimulus. The results are as follows: 1. Frequency rate at the last section when each of the attraction lamps was gradually switched on and off: (1) Sting fish was 27.2 % in case of 3 minutes interval, and 17.4 % in 1 minutes interval, and 15.8 % in 5 minutes interval. (2) Black porgy was 28.5 % in case of 5 minutes interval, and 25.8 % in 3 minutes interval, and 12.0 % in 1 minutes interval. 2. Distribution of fish at the illuminated section when each of the attraction lamps was gradually switched off after they were switched on all at once: (1) Sting fish was much gathered in the section adjacent to the extinguished section under the condition of 1 and 3 minutes interval, and not regular trend under 5 minutes interval. (2) Black porgy was much gathered last section under the condition of 1 and 3 minutes interval, and almost evenly distributed under 5 minutes interval. 3. Each of the attraction lamps was gradually switched off after they were switched on all at once, and only the last one was on: (1) The frequency rate of Sting fish was 27.2 % in case of 5 minutes interval, and 16.0 % in 1 minute interval, and 8.0 % in 3 minutes interval. (2) The frequency rate of Black porgy was 10.7 % in case of 1 minute interval, and 8.9 % in 3 minutes interval, and 0.8 % in 5 minutes interval.

유도등예로써 집어된 어류를 목적 장소까지 유도하기 위하여 9개의 유도등을 동시에 점등한 후 1등씩 순차적으로 소등하는 방법으로 능성어 Epinephelus Septemfasciatus에 광자극을 주었을 때의 반응을 수상유도등과 수중유도등으로 구분 조사한 결과는 다음과 같다. 1. 유도등의 점등구간에서의 어류분포는 1) 소등한 구간에 인접한 소등구간에 다소 많이 분포하였다. 2) 수상유도등에 의한 어류분포가 수중유도등에 비해 인접구간에 따른 분포차가 더 컸다. 3) 유도등의 소등간격이 1분일때는 수상유도등이, 소등간격이 5분일때는 수중유도등에 의한 분포가 각각 더 많았다. 2. 최종구간에서의 유도율의 변화는 1) 시간이 경과함에 따라 유도율이 증가하는 경향을 보였다. 2)유도등의 소등간격이 1분일때는 수중유도등에 의한 유도율이, 소등간격이 5분일때는 수중유도등에 의한 유도율이 각각 더 높았다.

유도등렬로서 집어된 어류를 목적장소까지 유도하기 위하여 2가지의 유도등 점멸방법 (Normal, Nega 방법), 3가지의 점멸간격 (1,5,10분) 및 3 가지의 적응등용전구 (1, 10, 20 W)를 사용해서 말쥐치 Navodon modestus(GUNTHER)에 광자극을 주었을 때 그에 대한 반응을 조사한 결과는 다음과 같다. 1. Normal 방법에 의한 점멸간격과 적응등의 밝기에 따른 유도율의 변화를 나타내는 변동계수는 각각 16.78% (1 분), 9.71% (5 분), 8.96% (10 분), 9.71% (1 W), 15.00% (10W), 21.08% (20 W)였고, 최종구간에서의 유도율은 각각 80.0% (1 분), 86.0% (5 분), 85.0% (10 분), 86.0% (1 W), 78.7% (10W), 72.7% (20 W)였다. 2. Nega 방법에 의한 각 점멸구간에서의 어류분포는 점멸간격과 적응등의 밝기에 관계없이 거의 모든 점등구간에 분포했으며 그 중 소등구간에 인접한 점등구간에 많이 분포하였다. 3. Nega 방법에 의한 최종구간에 대한 유도율의 변화는 L자형이 되었으며, 최종유도등만 점등되었을 때의 유도율은 각각 96.7% (1 분), 100% (5 분), 96.0% (10 분), 100% (1 W), 100% (10W) and 88.0% (20 W)였다.

수은은 인체독성과 생물농축성 그리고 대기를 통한 장거리 이동성이 크기 때문에 국제적으로 관리가 필요한 화학물질로 인식되어 왔다. 이에 따라 유엔환경계획(UNEP) 집행이사회에서는 2013년 “수은에 관한 미나마타협약”을 채택하였다. 미나마타협약은 국제적으로 수은사용 및 배출을 저감하는 것이며, 이를 위해 모니터링, 배출원 관리, 원자재 및 제품관리, 폐기물 처리, 노출저감, 기술개발 등 6개 주요 분야별 관리방안을 마련하도록 요구하고 있다. 본 연구에서는 국내 폐형광등 재활용처리시설에 처리방식에 따라 처리공정별 수은 농도변화를 측정하여 공정단계별 수은 물질수지를 분석하였다. 처리방식으로 건식과 습식시설을 각각 선정하여 현장에서 공정단계별 입자상과 기체상 수은 농도, 유량을 측정하거나 시료를 일정시간 동안 3회 채취하여 분석하였다. 또한 직관형 형광등 무게 당 투입 갯수를 확인하였다. 형광등 투입구, 파쇄장치, 건식 및 습식 수은 처리공정, 대기방지시설 등에서 분진, 유리, 비철, 활성탄 등 26개 시료를 채취하고, 수은농도를 측정하여 물질수지를 계산하였다. 연구 결과, 폐형광등 재활용시설로 입고되는 직관형 폐형광등은 박스 당 무게는 약 40-45 kg이고, 형광등 개수는 약 240개 정도이었다. 일부 환형, 일체형 형광등이 처리시설 투입구로 투입되지 않도록 미리 제거하였고, 처리과정에서 발생한 폐기물 중 수은 함량농도를 측정한 결과, 분진, 슬러지, 폐활성탄 및 폐수에서 높게 검출되었다.

국내 자원의 절약과 재활용 촉진에 관한 법률에 근거한 생산자책임재활용제도(EPR System)의 대상 품목인 폐형광등은 2017년 기준 재활용 의무율은 35.6%로 책정되었으며 한국환경공단에 따르면 2015년 기준 형광등의 출고량은 약 18 천톤 정도로 나타났으나 공제조합과 재활용업 간의 재활용 위･탁 계약의 미체결로 인해 폐형광등의 실제 재활용율은 약 5.0%로 재활용 의무율을 달성하지 못하고 있는 실정이다(｢생산자책임재활용제도 시행 13년｣ 운영성평가, 한국환경공단, 2017). 폐기물로 발생되는 폐형광등에 관한 선행연구에 따르면 폐형광등에 포함된 수은은 대부분 형광분말에 포함되어 있어 이를 적절하게 처리할 필요가 있다. 또한, 형광분말에는 희유금속(이트륨, 유로퓸 등)이 포함되어 있어 형광분말에 포함된 수은을 제거하여 희유금속을 회수하여 희유금속을 필요로 하는 산업체 등에서 활용할 수 있다. 이를 위하여 폐형광등 형광분말에 포함된 수은을 제거하기 위하여 Pilot plant 규모의 폐형광등 형광분말 증류 실험을 실시하였다. 실험의 원료는 경기도 K대학에 설치된 Pilot plant 규모의 폐형광등 재활용 공정에서 회수되는 폐형광등 형광분말을 사용하였다. Pilot plant 규모의 폐형광등 형광분말의 수은증류 실험의 조건으로 증류온도는 400~600℃로 변화시켰고 각 온도에서 증류장치 내 체류시간을 1~8시간으로 변화시켰다. 본 연구에서는 각 실험조건에서 회수되는 형광분말의 수은함량을 분석하였고 증류온도와 체류시간에 따른 수은함량을 비교하여 반응속도를 고찰하였다. 또한, 각 실험조건에서 소모되는 에너지양을 비교하여 Pilot plant 규모의 폐형광등 형광분말 증류장치의 최적 에너지 사용량을 평가하고자 하였다.

This study investigates leaching and thermal treatment characteristics of mercury in waste phosphor powder from UV lamp for industrial use. Waste phosphor powder contaminated with mercury compounds requires proper treatment for final disposal. A sequential extraction procedure was conducted in order to estimate the stability of mercury compounds in waste phosphor powder. The fraction of mercury compounds leached in initial steps by ion-exchangeable and low acidic solutions was 62%, which would be unstable. Finally 36% of mercury compounds was left as a strongly stable form before last step of acid digestion by aqua regia. Mercury was decomposed rapidly during initial period in thermal treatment. However, the decomposition rate reached in steady later. Correlation of mercury content in residues with concentration of leaching extract was attempted in order to set a thermal treatment condition. When mercury content in residue of phosphor powder could be lowed up to about 13 mg-Hg/kg by thermally with satisfying the Korean leaching standard limit of 0.005 mg-Hg/L.

Material flow analysis (MFA) of recycling material and of mercury from linear-type spent fluorescent lamps (SFLs was performed to estimate the material composition of the chain recycling process by an input-output approach. The recycling process system for linear-type SFLs was established using an end-cutting system, a hammer crusher, a screen separation system, a mercury distillation system, and an activated carbon adsorption component. From the results of the MFA of lineartype SFLs, 92% of materials used in linear-type SFLs such as glass, aluminum, and phosphor powder can be recycled. For MFA of mercury, the mercury content in the phosphor powder was the highest among material compositions tested and the total mercury amount in the recycling materials from 1 ton of SFLs was estimated to be 75.43 g. In the recycling process system for linear-type SFLs, the mercury amount in the vapor phase was analyzed and found to be 2228 mg in the endcutting system, 172 mg in the hammer crusher, and 2585 mg in the screen separation system. The total mercury amount in the vapor phase was estimated to be 4985 mg, which was only 6.22% of the total mercury amount emitted from the recycling process system. Hence, it was estimated that the MFA of the total mercury amount obtained from the vapor phase and the recycling materials of 1 ton of SFLs using the recycling process system was 80.175 g.