• 한국식품위생안전성학회지
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• 제29권4호
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• pp.347-355
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• 2014

본 연구에서는 식품 중 동물성 사용원료의 진위 판별을 위하여 분자생물학적 기법을 이용한 시험법을 개발하였다. 동물성 식품원료의 종 판별을 위한 유전자로는 미토콘드리아 DNA에 존재하는 COI, Cytb, 및 16S rRNA 유전자를 대상으로 하였으며, 가공식품에 적용하기 위하여 PCR 산물의 크기는 200 bp 내외가 되도록 종 특이 프라이머를 설계하였다. 대상종으로는 가축류 2종, 가금류 6종, 민물어류 2종, 해양어류 13종 및 갑각류 1종, 총 24종을 선정하였으며 종 특이 프라이머를 이용하여 예상되는 PCR 산물의 생성 유무를 확인하였다. PCR을 수행한 결과 토끼, 여우, 꿩, 집비둘기, 멧비둘기, 메추리, 참새, 제비, 메기, 쏘가리, 날치, 열빙어, 청어, 까나리, 멸치, 참조기, 넙치, 조피볼락, 홍어, 가오리, 말쥐치, 농어, 성게 및 바닷가재에 대하여 각각 156, 204, 152, 160, 113, 163, 167, 152, 165, 121, 136, 151, 178, 178, 146, 188, 177, 166, 179, 218, 188, 185, 127 및 172 bp에서 PCR 증폭 산물을 확인하였다. 그리고 프라이머 별로 비교종에서는 비특이적 PCR 산물(non-specific PCR product)은 생성되지 않았다. 본 연구에서 개발된 유전자 분석법을 이용하여 동물성 식품원료가 사용된 식품 원료 및 가공식품의 진위 판별에 활용이 가능할 것이며, 불량식품 근절에 크게 기여할 것으로 기대된다.

• 헤리티지:역사와 과학
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• 제56권4호
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• pp.40-52
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• 2023

기와라는 건축 재료는 기본적으로 방수와 방습을 목적으로 하며, 중요 건축물에만 사용이 제한되어 권위까지 보여준다. 특히 출토 사례가 드문 삼국시대에는 더욱이 그럴 것이다. 그마저도 신라, 백제 지역의 유적에서 확인된 기와가 대부분이다. 현재까지 가야 지역에서 확인된 기와 중에서 가장 오래된 제작기법을 보이는 부원동 유적 출토 기와 이래로 금관가야 왕궁지로 추정되는 김해 봉황동 유적에서 최근 삼국시대 초기 기와가 출토되었다. 이들은 금관가야의 고도인 김해 지역 초기 기와의 양상을 살펴볼 수 있는 중요한 자료이다. 봉황동 유적 일대에서 출토된 기와는 연질 소성의 세석립이 일부 포함된 적· 황갈색 계통의 색조를 띠며, 두께가 얇다. 내면에는 포목흔이 확인되지 않으며, 점토띠 흔적이 보인다. 내· 외면에 타날흔 및 목리흔이 뚜렷하게 관찰되며, 깎기조정 및 물손질흔과 내면에 내박자흔도 확인된다. 이를 통해 무와통작법의 토기 제작방식과 동일하게 만들어졌음을 알 수 있다. 가야 토기를 제작하던 도공집단의 계통과 연결시켜 본다면, 고령 송림리, 인천 불로동, 경주 손곡동·천리 유적 등과 같이 와도겸업(瓦陶兼業)이 이루어졌을 것으로 추정된다. 현재까지 김해 지역 출토 기와는 김해 분지 일원의 금관가야 도성(왕성)으로 추정되는 범위 내에서만 확인되었으며, 이는 의미하는 바가 크다. 문헌기록과 지금까지의 발굴조사 성과 및 입지적 경관 등을 통해 보았을 때, 봉황동 유적 일대는 금관가야 도성 후보지로 유일하며, 출토된 기와의 존재를 통해서도 이러한 면모를 보여주기 충분하다. 이 시기 기와는 소량 출토되는 점 등으로 미루어 보아, 지붕자재로써의 기능보다는 상징적 의미를 지닌 위세품으로서의 역할이 더욱 컸을 것이며, 사용 범위의 제한 및 통제가 엄격히 이루어졌던 것으로 추정된다.

• 환경위생공학
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• 제24권4호
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• pp.1-26
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• 2009

We conclude the following with air pollution data measured from city measurement net administered and managed in Gwangju for the last 7 years from January in 2001 to December in 2007. In addition, some major statistics governed by Gwangju city and data administered by Gwangju as national official statistics obtained by estimating the amount of national air pollutant emission from National Institute of Environmental Research were used. The results are as follows ; 1. The distribution by main managements of air emission factory is the following ; Gwangju City Hall(67.8%) > Gwangsan District Office(13.6%) > Buk District Office(9.8%) > Seo District Office(5.5%) > Nam District Office(3.0%) > Dong District Office(0.3%) and the distribution by districts of air emission factory ; Buk District(32.8%) > Gwangsan District(22.4%) > Seo District(21.8%) > Nam District(14.9%) > Dong District(8.1%). That by types(Year 2004~2007 average) is also following ; Type 5(45.2%) > Type 4(40.7%) > Type 3(8.6%) > Type 2(3.2%) > Type 1(2.2%) and the most of them are small size of factory, Type 4 and 5. 2. The distribution by districts of the number of car registrations is the following ; Buk District(32.8%) > Gwangsan District(22.4%) > Seo District(21.8%) > Nam District(14.9%) > Dong District(8.1%) and the distribution by use of car fuel in 2001 ; Gasoline(56.3%) > Diesel(30.3%) > LPG(13.4%) > etc.(0.2%). In 2007, there was no ranking change ; Gasoline(47.8%) > Diesel(35.6%) > LPG(16.2%) >etc.(0.4%). The number of gasoline cars increased slightly, but that of diesel and LPG cars increased remarkably. 3. The distribution by items of the amount of air pollutant emission in Gwangju is the following; CO(36.7%) > NOx(32.7%) > VOC(26.7%) > SOx(2.3%) > PM-10(1.5%). The amount of CO and NOx, which are generally generated from cars, is very large percentage among them. 4. The distribution by mean of air pollutant emission(SOx, NOx, CO, VOC, PM-10) of each county for 5 years(2001~2005) is the following ; Buk District(31.0%) > Gwangsan District(28.2%) > Seo District(20.4%) > Nam District(12.5%) > Dong District(7.9%). The amount of air pollutant emission in Buk District, which has the most population, car registrations, and air pollutant emission businesses, was the highest. On the other hand, that of air pollutant emission in Dong District, which has the least population, car registrations, and air pollutant emission businesses, was the least. 5. The average rates of SOx for 5 years(2001~2005) in Gwangju is the following ; Non industrial combustion(59.5%) > Combustion in manufacturing industry(20.4%) > Road transportation(11.4%) > Non-road transportation(3.8%) > Waste disposal(3.7%) > Production process(1.1%). And the distribution of average amount of SOx emission of each county is shown as Gwangsan District(33.3%) > Buk District(28.0%) > Seo District(19.3%) > Nam District(10.2%) > Dong District(9.1%). 6. The distribution of the amount of NOx emission in Gwangju is shown as Road transportation(59.1%) > Non-road transportation(18.9%) > Non industrial combustion(13.3%) > Combustion in manufacturing industry(6.9%) > Waste disposal(1.6%) > Production process(0.1%). And the distribution of the amount of NOx emission from each county is the following ; Buk District(30.7%) > Gwangsan District(28.8%) > Seo District(20.5%) > Nam District(12.2%) > Dong District(7.8%). 7. The distribution of the amount of carbon monoxide emission in Gwangju is shown as Road transportation(82.0%) > Non industrial combustion(10.6%) > Non-road transportation(5.4%) > Combustion in manufacturing industry(1.7%) > Waste disposal(0.3%). And the distribution of the amount of carbon monoxide emission from each county is the following ; Buk District(33.0%) > Seo District(22.3%) > Gwangsan District(21.3%) > Nam District(14.3%) > Dong District(9.1%). 8. The distribution of the amount of Volatile Organic Compound emission in Gwangju is shown as Solvent utilization(69.5%) > Road transportation(19.8%) > Energy storage & transport(4.4%) > Non-road transportation(2.8%) > Waste disposal(2.4%) > Non industrial combustion(0.5%) > Production process(0.4%) > Combustion in manufacturing industry(0.3%). And the distribution of the amount of Volatile Organic Compound emission from each county is the following ; Gwangsan District(36.8%) > Buk District(28.7%) > Seo District(17.8%) > Nam District(10.4%) > Dong District(6.3%). 9. The distribution of the amount of minute dust emission in Gwangju is shown as Road transportation(76.7%) > Non-road transportation(16.3%) > Non industrial combustion(6.1%) > Combustion in manufacturing industry(0.7%) > Waste disposal(0.2%) > Production process(0.1%). And the distribution of the amount of minute dust emission from each county is the following ; Buk District(32.8%) > Gwangsan District(26.0%) > Seo District(19.5%) > Nam District(13.2%) > Dong District(8.5%). 10. According to the major source of emission of each items, that of oxides of sulfur is Non industrial combustion, heating of residence, business and agriculture and stockbreeding. And that of NOx, carbon monoxide, minute dust is Road transportation, emission of cars and two-wheeled vehicles. Also, that of VOC is Solvent utilization emission facilities due to Solvent utilization. 11. The concentration of sulfurous acid gas has been 0.004ppm since 2001 and there has not been no concentration change year by year. It is considered that the use of sulfurous acid gas is now reaching to the stabilization stage. This is found by the facts that the use of fuel is steadily changing from solid or liquid fuel to low sulfur liquid fuel containing very little amount of sulfur element or gas, so that nearly no change in concentration has been shown regularly. 12. Concerning changes of the concentration of throughout time, the concentration of NO has been shown relatively higher than that of $NO_2$ between 6AM~1PM and the concentration of $NO_2$ higher during the other time. The concentration of NOx(NO, $NO_2$) has been relatively high during weekday evenings. This result shows that there is correlation between the concentration of NOx and car traffics as we can see the Road transportation which accounts for 59.1% among the amount of NOx emission. 13. 49.1~61.2% of PM-10 shows PM-2.5 concerning the relationship between PM-10 and PM-2.5 and PM-2.5 among dust accounts for 45.4%~44.5% of PM-10 during March and April which is the lowest rates. This proves that particles of yellow sand that are bigger than the size $2.5\;{\mu}m$ are sent more than those that are smaller from China. This result shows that particles smaller than $2.5\;{\mu}m$ among dust exist much during July~August and December~January and 76.7% of minute dust is proved to be road transportation in Gwangju.