• 방사성폐기물학회지
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• 제13권4호
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• pp.315-319
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• 2015

전해환원공정의 금속전환체로부터 우라늄을 회수하는 전해정련공정의 수율을 높이기 위해 고수율 전해정련장치가 개발되었다. 전해정련장치의 수율을 증대시키기 위해서는 고체음극에 전착되는 우라늄 덴드라이트를 음극 표면으로부터 효율적으로 회수할 수 있어야 한다. 철강 재료의 음극을 고체음극으로 사용하면, 우라늄 덴드라이트가 전착되어 쉽게 떨어지고 않고 고착 되어 점착계수(sticking coefficient)가 높아진다. 본 연구에서는 효율적으로 고체음극의 점착계수를 낮출 수 있는 진동 탈리법을 개발하였고 이를 적용하였다. 고체음극에 진동을 가함으로써 고체 표면에서 우라늄 전착물이 흑연음극의 자발특성과 유사하게 효율적으로 탈리됨을 확인하였다. 이러한 진동모드에 의한 고체음극에서의 전착물의 탈리 특성을, 고수율 전해정련장치 개념으로 개발한 흑연음극의 자발탈리 특성과 비교 검토하였다. 그리고 우라늄 덴드라이트의 진동 탈리에 대한 인가전류밀도와 진동 스트로크에 의한 영향 등을 고찰하였다.

• 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.

• 방사성폐기물학회지
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• 제14권2호
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• pp.101-112
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• 2016

본 연구는 고방사성해수폐액 (HSW)으로부터 Barium (Ba)이 함침된 4A 제올라이트 (BaA)에 의한 고방사성핵종 중에 하나인 Sr의 흡착 제거를 수행하였다. BaA에 의한 Sr의 흡착 (BaA-Sr)은 Ba의 함침농도 20.2wt% 이상에서 Ba의 함침농도가 증가할수록 감소하며 Ba 함침농도는 20.2wt% 정도가 적당하였다. 그리고 BaA-Sr 흡착은 BaA 내 4A에 의한 Sr 흡착 (4A-Sr)에 $BaSO_4$ 침전에 따른 Sr 공침이 첨가되어, Sr의 농도가 0.2 mg/L 이하 (HSW 내 실제 Sr 농도 수준)에서 BaA는 m/V (흡착제량/용액 부피)=5 g/L, 4A는 m/V >20 g/L에서 99% 이상의 Sr 제거가 가능하였다. 이는 흡착제 단위 g 당 Sr의 처리용량 및 2차 고체폐기물 (폐흡착제 등) 발생량 저감화 차원에서 BaA-Sr 흡착이 4A-Sr 흡착보다 우수함을 나타낸다. 또한 BaA-Sr 흡착이 증류수보다 해수폐액에서 Sr의 제거능이 우수하여 HSW로부터 직접 Sr을 제거하는 데 효과적일 것으로 보인다. 반면에 BaA에 의한 Cs의 흡착 (BaA-Cs)은 주로 BaA 내 4A에 의해서 이루어지고 있어 함침 Ba의 영향은 거의 없는 것 같다. 한편 BaA-Sr 흡착속도는 유사 2차 속도식으로 표현할 수 있으며, Sr의 초기농도 및 V/m 비 증가에 따라서 속도상수 ($k_2$)는 감소하지만 평형흡착량 ($q_e$)은 증가하고 있다. 그러나 용액의 온도증가에 따라서는 반대로 $k_2$는 증가하지만 $q_e$는 감소하고 있다. BaA-Sr 흡착 활성화에너지는 약 38 kJ/mol 로 강력한 결합 형태를 이룬 화학흡착은 아니더라도 물리적 흡착보다 화학적 흡착이 지배적일 것으로 보인다.

• Carbon letters
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• 제18권
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• pp.49-55
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• 2016

Refuse-derived fuel (RDF) produced using municipal solid waste was pyrolyzed to produce RDF char. For the first time, the RDF char was used to remove aqueous copper, a representative heavy metal water pollutant. Activation of the RDF char using steam and KOH treatments was performed to change the specific surface area, pore volume, and the metal cation quantity of the char. N₂ sorption, Inductively Coupled Plasma-Atomic Emission Spectrometer (ICP-AES), and Fourier transform infrared spectroscopy were used to characterize the char. The optimum pH for copper removal was shown to be 5.5, and the steam-treated char displayed the best copper removal capability. Ion exchange between copper ions and alkali/alkaline metal cations was the most important mechanism of copper removal by RDF char, followed by adsorption on functional groups existing on the char surface. The copper adsorption behavior was represented well by a pseudo-second-order kinetics model and the Langmuir isotherm. The maximum copper removal capacity was determined to be 38.17 mg/g, which is larger than those of other low-cost char adsorbents reported previously.

• Advances in environmental research
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• 제3권3호
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• pp.231-251
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• 2014

The present study examines the phosphate adsorption potential and behavior of mixture of Ground Burnt Patties (GBP), a solid waste generated from cooking fuel used in earthen stoves and Red Soil (RS), a natural substance in fixed bed column mode operation. The characterization of adsorbent was done by Proton Induced X-ray Emission (PIXE), and Proton Induced ${\gamma}$-ray Emission (PIGE) methods. The FTIR spectroscopy of spent adsorbent reveals the presence of absorbance peak at $1127cm^{-1}$ which appears due to P = O stretching, thus confirming phosphate adsorption. The effects of bed height (10, 15 and 20 cm), flow rate (2.5, 5 and 7.5 mL/min) and initial phosphate concentration (5 and 15 mg/L) on breakthrough curves were explored. Both the breakthrough and exhaustion time increased with increase in bed depth, decrease in flow rate and influent concentration. Thomas model, Yoon-Nelson model and Modified Dose Response model were used to fit the column adsorption data using nonlinear regression analysis while Bed Depth Service Time model followed linear regression analysis under different experimental condition to evaluate model parameters that are useful in scale up of the process. The values of correlation coefficient ($R^2$) and the Sum of Square Error (SSE) revealed the Modified Dose Response model as the best fitted model to the experimental data. The adsorbent mixture responded effectively to the desorption and reusability experiment. The results of this finding advocated that mixture of GBP and RS can be used as a low cost, highly efficient adsorbent for phosphate removal from aqueous solution.

• Nuclear Engineering and Technology
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• 제26권4호
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• pp.453-460
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• 1994

암반(Porous Rock Matrix)과 균열(fracture)에서 일차원의 이동 방정식(Migration Equation)을 3-Member Decay Chain까지 화장하고, Laplace Transform을 이용하여 초기조건이 Delta Function과 Bateman Equation인 각각에 대해 해석해를 구한다. 그 해를 이용하여 Actinide Chain 중 4n＋1과 4n＋2 Chain에서 선택된 Np$^{241}$-U$^{233}$ -Th$^{229}$ 와 U$^{234}$ -Th$^{230}$ -Ra$^{226}$ Chain의 각 핵종들의 균열에서의 농도를 상대농도로 나타낸다. 이핵종들의 지연계수(Retardation Coefficient)는 화강암에 대한 것을 사용하여 균열에서의 농도 변화를 볼 수 있다. 본 연구에 의한 결과로는 U$^{233}$ , Th$^{229}$ , Th$^{230}$ Ra$^{226}$ 같은 핵종들은 비록 초기 inventory에는 작은 양일지라도 균열과 암반에서 모핵종의 붕괴(decay)에 의해 생기므로써 처분장으로부터 먼 거리에서는 중요한 핵종이 된다는 것을 알 수 있다.

• 한국신재생에너지학회:학술대회논문집
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• 한국신재생에너지학회 2010년도 추계학술대회 초록집
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• pp.101-101
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• 2010

Anaerobic digestion(AD) is the most promising method for treating and recycling of different organic wastes, such as organic fraction of municipal solid waste, household wastes, animal manure, agro-industrial wastes, industrial organic wastes and sewage sludge. During AD, i.e. organic materials are decomposed by anaerobic forming bacteria and fina1ly converted to excellent fertilizer and biogas which is a mixture of carbon dioxide and methane. AD has been one of the leading technologies that can make a large contribution to produce renewable energy and to reduce $CO_2$ and other green-house gas(GHG) emission, it is becoming a key method for both waste treatment and recovery of a renewable fuel and other valuable co-products. Currently some 80% of the world's overall energy supply of about 400 EJ per year in derived from fossil fuels. Nevertheless roughly 10~15% of this demand is covered by biomass resources, making biomass by far the most important renewable energy source used to date. The representative biofuels produced from the biomass are bioethanol, biodiesel and biogas, and currently biogas plays a smaller than other biofuels but steadily growing role. Traditionally anaerobic digestion applied for different biowaste e.g. sewage sludge, manure, other organic wastes treatment and stabilization, biogas has become a well established energy resource. However, the biowaste are fairly limited in respect to the production and utilization as renewable source, but the plant biomass, the so called "energy crops" are used for more biogas production in EU countries and the investigation on the biomethane potential of different crops and plant materials have been carried out. In Korea, with steadily increasing oil prices and improved environmental regulations, since 2005 anaerobic digestion was again stimulated, especially on the biogasification of different biowastes and agro-industrial biomass including "energy crops". This study have been carried out to investigate anaerobic biodegradability by the biochemical methane potential(BMP) test of animal manures, different forage crops i.e. "energy crops", plant and industrial organic wastes in the condition of thermophilic temperature, The biodegradability of animal manure were 63.2% and 58.2% with $315m^3CH_4/tonVS$ of cattle slurry and $370m^3CH_4/tonVS$ of pig slurry in ultimate methane yields. Those of winter forage crops were the range 75% to 87% with ultimate methane yield of $378m^3CH_4/tonVS$ to $450m^3CH_4/tonVS$ and those of summer forage crops were the range 81% to 85% with ultimate methane yield of $392m^3CH_4/tonVS$ to $415m^3CH_4/tonVS$. The forge crops as "energy crops" could be used as good renewable energy source to increase methane production and to improve biodegradability in co-digestion with animal manure or only energy crop digestion.

• 방사성폐기물학회지
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• 제5권1호
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• pp.19-27
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• 2007

추출크로마토그래피법과 액체섬광계수법을 이용하여 고체 시료중의 $^{55}Fe$와 $^{63}Ni$ 방사능을 측정할 수 있는 분석법을 확립하고 연구로 2호기의 해체시 발생되는 방사화된 콘크리트 폐기물을 분석하였다. 침전법과 추출크로마토그래피법으로 화학분리를 하면, 경우 Fe의 화학적 회수율은 대부분의 시료에서 90%이상이었으나 Ni의 회수율은 43.6과 46.5%를 나타낸 시료가 있으며 나머지는 62% 이상을 나타내었다. Spiked 시료를 이용하여 분리과정과 액체섬광계수법의 과정을 확인한 결과 $^{55}Fe$의 경우는 3.7% 오차내의, $^{63}Ni$의 경우는 0.7% 오차내의 결과가 얻어졌다. 연구로 2호기의 해체 콘크리트 시료중 $^{55}Fe$ 방사능은 MDA이하의 값도 있으나 TC3시료의 경우는 362Bq/g의 값이 얻어졌다. 그리고 $^{63}Ni$의 경우는 모든 시료에서 MDA이하 값이 얻어져 $^{63}Ni$이 존재하지 않음을 알 수 있었다. 그리고 콘크리트 벽의 해체시 표면의 시료는 $^{55}Fe$의 방사능이 높다가 표면으로부터 깊은 시료일수록 $^{55}Fe$의 방사능이 급격히 줄어들었다.

• 방사성폐기물학회지
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• 제2권2호
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• pp.97-104
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• 2004

NIPS 시스템은 중성자 핵반응 결과 방출되는 즉발 감마선을 정량적으로 측정하는 장치이며 고체 및 액체 폐기물 중 존재하는 다양한 원소를 비파괴적으로 분석할 수 있는 장점이 있다. 본 연구에서는 NIPS 시스템에 이용된 고순도반도체 검출기의 계측효율을 $^{l33}$Ba 및 $^{152}$Eu 방사성 동위원소 선원과 $^{35}$ Cl(n, ${\gamma}$)$^{36}$ Cl 핵반응 시 발생되는 즉발감마선을 이용하여 80 keV에서 8 MeV까지 넓은 영역에 대하여 구하였다. $^{35}$ Cl(n, ${\gamma}$)$^{36}$ Cl 핵반응을 이용한 고에너지 감마선의 계측효율은 즉발감마선의 방사능 값을 정확히 알 수 없기 때문에 저 에너지 영역에서 정확히 알고 있는 검출기 효율곡선에 규격화시켜 전 에너지 영역에서의 효율보정곡선을 구하였다. 또한 KCl 표준용액에 $^{252}$ Cf 중성자 선원을 조사시켜 표준용액으로부터 방출되는 즉발 감마선을 고순도반도체 검출기로 측정하고 광대역 계측효율 곡선을 이용하여 수용액 시료에서의 평균 열중성자 속을 예측하였다. NIPS 측정시스템은 주변 재료 물질의 핵반응으로 방출되는 감마선 background를 줄이기 위해 두 개의 고순도반도체 검출기를 이용한 동시계수 장치가 고안되었으며, 동시계수 모드에서의 계측효율도 함께 고려되었으며, 표준선원을 이용하여 전 계수 또는 동시계수모드에서의 background에 대한 측정감도를 비교하였다.다.

• 유기물자원화
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• 제26권3호
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• pp.55-61
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• 2018

본 연구에서는 D시 내의 바이오매스와 폐플라스틱을 적정 비율로 혼합하여 고형연료제품(SRF) 품질기준을 만족하는지 분석하기로 하였다. 수분함량의 경우 바이오매스 구성비가 약 40% 이하일 때부터 9.81% 이하로 분석되었다. 회분함량의 경우 최대 4.19%로 분석되었고, 원소분석 추정식(Steuer, Dulong) 및 발열량계에 근거한 저위발열량은 최소 4,851, 4,181 및 3,847kcal/kg로 나타났다. 원소분석 결과 황(S)과 염소(Cl)는 0.05% 이하로 측정되었고 중금속(Hg, Cd, Pb, As) 함량 또한 기준치 이하를 나타냄으로써 SRF 품질기준치를 만족하였다. 이러한 결과를 바탕으로, 현재 적절하게 활용되지 못하고 산림에 버려져 있는 임목부산물을 효율적으로 사용할 수 있을 뿐만 아니라 수분에 약한 목재의 물리적 특성을 플라스틱으로 보완할 수 있을 것으로 사료된다. 또한 플라스틱 소각 시 고온으로 인한 소각로의 수명문제도 비교적 완화시킬 수 있을 것으로 판단하였다.