• 한국산림과학회지
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• 제56권1호
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• pp.26-50
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• 1982

본(本) 연구(硏究)에서는 효소(酵素) 알칼리 증해(蒸解)의 리그닌 용출거동(溶出挙動) 파악하기 위(爲)해 잣나무(Pinus koraiensis S. et Z.) 목분(木粉)을 공시(供試)하여 $110^{\circ}C$, $120^{\circ}C$, $130^{\circ}C$, $140^{\circ}C$, 및 $150^{\circ}C$의 5 수준(水準) 온도(溫度)로 60분간(分間) 1단(段) 등온(等溫) 효소(酵素) 알칼리 탈(脱)리그닌 처리(処理)를 행(行)한 후(後), 그 탈(脱)리그닌 반응속도(反応速度), 활성화(活性化)에너지 및 반응시간별(反応時間別) 알칼리와 효소(酵素)의 소비동향(消費動向)을 동역학적(動力學的) 방법(方法)으로 구명(究明)하였다. 그 결과(結果)를 보면 탈(脱)리그닌은 반응초기(反応初期)에 전(全)리그닌 함량(含量)의 2/5가량이 급속(急速)히 용출(溶出)되는 초기(初期) 산화반응(酸化反応)을 나타냈다. 탈(脱)리그닌 반응(反応)의 속도상교(速度常敎)(K)는 반응온도(反応溫度) $150^{\circ}C$의 경우, 소오다법(法)에 비(比)해 3배정도(倍程度) 더 컸다. 본 법(法)의 활성화(活性化)에너지 값은 크라프트나 소오다 펄프법화(法化)보다 1/3정도(程度) 낮은 수준(水準)이었다. 알칼리소비량은 효소(酵素)의 경우와 마찬가지로 반응초기(反応初期)에 총투입량(總投入量)의 1/2가량이 급속히 소모된 후, 완만한 소비협추세(消費趨勢)를 보였다. 탈(脱)리그닌 반응속도(反応速度)는 증해과정중 생성되는 유기산(有機酸) 때문에 pH가 감소됨에 따라 크게 영향을 받았다. 또한 증해용출(蒸解溶出)된 리그닌은 잘 침전(沈澱)되지 않을 만큼 저분자화(低分子化) 됨을 알수 있었다. 리그닌의 메톡실기(基)는 급속히 감소(減少)되는데 반(反)해, 페놀성(性) 하이드록실기(基), 카보닐기(基) 및 카복실기(基)는 증가(增加)추세를 보였다.

• Asian Journal of Atmospheric Environment
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• 제7권4호
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• pp.177-190
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• 2013

Air pollution trends in Japan between 1970 and 2012 were analyzed, and the impact of air pollution countermeasures was evaluated. Concentrations of CO decreased from 1970 to 2012, and in 2012, the Japanese environmental quality standard (EQS) for CO was satisfied. Concentrations of $SO_2$ dropped markedly in the 1970s, owing to use of desulfurization technologies and low-sulfur heavy oil. Major reductions in the sulfur content of diesel fuel in the 1990s resulted in further decreases of $SO_2$ levels. In 2012, the EQS for $SO_2$ was satisfied at most air quality monitoring stations. Concentrations of $NO_2$ decreased from 1970 to 1985, but increased from 1985 to 1995. After 1995, $NO_2$ concentrations decreased, especially after 2006. In 2012, the EQS for $NO_2$ was satisfied at most air quality monitoring stations, except those alongside roads. The annual mean for the daily maximum concentrations of photochemical oxidants (OX) increased from 1980 to 2010, but after 2006, the $98^{th}$ percentile values of the OX concentrations decreased. In 2012, the EQS for OX was not satisfied at most air quality monitoring stations. Non-methane hydrocarbon (NMHC) concentrations generally decreased from 1976 to 2012. In 2011, NMHC concentrations near roads and in the general environment were nearly the same. The concentration of suspended particulate matter (SPM) generally decreased. In 2011, the EQS for SPM was satisfied at 69.2% of ambient air monitoring stations, and 72.9% of roadside air-monitoring stations. Impacts from mineral dust from continental Asia were especially pronounced in the western part of Japan in spring, and year-round variation was large. The concentration of $PM_{2.5}$ generally decreased, but the EQS for $PM_{2.5}$ is still not satisfied. The air pollution trends were closely synchronized with promulgation of regulations designed to limit pollutant emissions. Trans-boundary OX and $PM_{2.5}$ has become a big issue which contains global warming chemical species such as ozone and black carbon (so called SLCP: Short Lived Climate Pollutants). Cobeneficial reduction approach for these pollutants will be important to improve both in regional and global atmospheric environmental conditions.

• 한국토양비료학회지
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• 제19권2호
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• pp.115-121
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• 1986

원자력시설(原子力施設)에서 방출(放出)될 수 있는 장반감기핵종중(長半減期核種中)의 하나인 $Cs^{137}$을 5개 답토양(畓土壤)에 처리(處理)하여 토양중(土壤中)에서의 흡(吸) 탈착상태(脫着狀態)를 조사하여 다음과 같은 결과를 얻었다. 1. $Cs^{137}$은 토양(土壤)에 다량(多量) 흡착(吸着)되며 치환성형태(置換性形態)의 탈착량(脫着量)은 K첨가에 따라서는 감소(減少)하였고, $Cs^{137}$ 처리량(處理量)의 증가에 따라서는 비례적으로 증가하였으며 치환성형태의 탈착량(脫着量)은 수용성(水溶性)에 비하여 매우 높았다. 2. 토양(土壤)에 첨가된 $Cs^{137}$의 존재형태(存在形態)는 토양(土壤)에 따라서 차이(差異)가 있으나 평균적으로 수용성(水溶性)이 5.9%, 치환성(置換性)이 17.1%, 비치환성(非置換性)이 77.0%로 나타났다. 3. 토양(土壤)에 흡착(吸着)된 $Cs^{137}$의 수용성(水溶性) 및 치환성탈착량(置換性脫着量)은 토양(土壤)pH와 치환성 염기함량의 증가에 따라 감소(減少)하였고, 유기물과 점토함량(粘土含量)의 증가에 따라서는 증가하였다. 4. 토양(土壤)에 흡착(吸着)된 $Cs^{137}$은 Illite와 Vermiculite가 많은 토양(土壤)에서 비치환성형태(非置換性形態)로의 흡착(吸着)이 많았다.

• 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.

• 한국환경생태학회지
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• 제27권6호
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• pp.718-732
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• 2013

본 연구는 천연기념물 제469호로 지정된 예천 금당실 송림의 실질적인 보존관리방안 수립을 위한 기초자료를 확보하고 지속가능한 관리 및 보호방안을 제안하였다. 숲에 영향을 주는 문제점을 방지하고 저감하여 숲의 지속가능한 이용과 보전을 위해 본 연구에서는 지형 및 지세, 토지이용, 수목 생육현황, 토양환경, 이용 및 관리현황 등을 조사 분석하였다. 예천 금당실 송림은 해발 130~140m의 평탄지에 위치하며, 주변지역은 대부분 경작지로 이용되었다. 송림에 식재된 수목은 총 565주이며, 이중 소나무가 558주이고 25개의 밑둥이 확인되었다. 식재된 소나무는 흉고직경 30~50cm에 집중되어 있었으며, 평균 수령은 85.4년이었고, 최고 수령은 약 200년으로 추정되었다. 표본목의 가지 생장량은 연간 4.3~5.1cm이며 가장 생장이 왕성한 중앙의 가지는 3년간 평균 24.2cm의 생장을 보였다. 7개 조사구의 토양 이화학적 특성 분석 결과 유기물 함량, 전질소, 유효인산, 전기전도도 항목은 비교적 양호하였으나, 토양 pH, 치환성 양이온 등의 항목에서 개선이 필요하였다. 현재 내부의 시설물와 이용압력은 많지 않은 상태이나, 경작에 의한 잠식 등의 위협요인이 남아있으며, 생태계 관리에 치중한 관리로 시설물, 이용객, 운영 관리 등의 종합적인 관리가 필요한 상태이었다. 본 연구에서 제시한 지속가능한 관리방안은 생태계관리, 시설물관리, 이용객관리, 운영관리 4가지 부분을 고려하였다.