• 한국토양환경학회지
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• 제4권2호
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• pp.63-75
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• 1999

본 연구에서는 폐탄광폐수를 처리하기 위한 SRB의 탄소원으로 하수슬러지와 제지슬러지를 활용가능성과 아울러 석회석에 의한 영향을 검토하였다. 유입 폐탄광폐수의 pH가 평균 3.3정도로 낮음에도 불구하고 전 실험기간동안에 유출수중 평균 pH는 약알칼리성으로 SRB의 생육에 적합한 pH를 유지하였다. 실험초기에 Washout현상으로 높은 TCODcr농도를 나타내었지만 시간이 경과함에 따라 낮아져 유기물의 상승으로 인한 이차적인 오염문제는 없을 것으로 여겨진다. Mn을 제외한 대부분의 중금속은 ${SO_4}^2$ 환원량이 많아짐에 따라 고정경향이 강하여 유출수 중 낮은 농도를 나타내었으나, Mn의 경우에는 유출수중 높은 농도를 나타내었다. 하수슬러지의 혼합비율이 제지슬러지와 같거나 많은 경우에 비교적 중금속 제거효율과 ${SO_4}^2$ 환원율이 높으나 제지슬러지 보다 단기간 분해가능한 하수슬러지가 2배 정도 많은 경우에 유기물의 지속성 측면에서 적절하지 못하며 오히려 혼합비율이 같은 경우가 더 적절하다고 여겨진다. 석회석과 생물학적 처리에 의한 효율을 비교.검토해본 결과, 생물학적 처리에서 pH 중화와 중금속 제거효율이 높았다.

• 한국지하수토양환경학회:학술대회논문집
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• 한국지하수토양환경학회 1999년도 정기총회 및 춘계 공동 학술발표회
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• pp.149-156
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• 1999

In the United States (U.S.), the monitored natural attenuation (MNA) approach has been used as an alternative remedial option for organic and inorganic compounds retained in soil and dissolved in groundwater. The U.S. Environmental Protection Agency (EPA) defines the MNA as“in-situ naturally-occurring processes include biodegradation, diffusion, dilution, sorption, volatilization, and/or chemical and biochemical stabilization of contaminants and reduce contaminant toxicity, mobility or volume to the levels that are protective of human health and the environment”. The Department of Soil Environment. National Institute Environmental Research (NIER) is in the process for demonstrating the MNA approach as a potential remedial option for the BTEX contaminated site in Uiwang City. The project is charactering the research site in terms of the nature and extend of contamination, biological degradation rate, and geochemical and hydrological properties. The microbial-degradation rate and effectiveness of nutrient and redox supplements will be determined through laboratory batch and column tests. The geochemical process will be monitored for determining the concentration changes of chemical species involved in the electron transfer processes that include methanogenesis, sulfate and iron reduction, denitrification, and aerobic respiration. Through field works, critical soil and hydrogeologic parameters will be acquired to simulate the effects of dispersion, advection, sorption, and biodegradation on the fate and transport of the dissolved-phase BTEX plume using Bioplume III model. The objectives of this multi-years research project are (1) to evaluate the MNA approach using the BTEX contaminated site in Uiwang City, (2) to establish a standard protocol for future application of the approach, (3) to investigate applicability of the passive approach as a secondary treatment remedy after active treatments. In this presentation, the overall picture and philosophy behind the MNA approach will be reviewed. Detailed discussions of the site characterization/monitoring plans and risk-based decision-making processes for the demonstration site will be included.

• 한국식품저장유통학회지
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• 제9권2호
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• pp.154-160
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• 2002

박피 토란의 저장성을 향상시키기 위한 방안으로 전해산화수, 유자과즙을 첨가한 전해산화수 및 명반수를 사용하여 제조한 침지저장액에 따른 저장 효과를 살펴본 결과, 토란 수분함량은 80.05%에서 저장 25일째 수분의 흡수로 인해 82.12~84.24%로 다소 증가하였으나 처리구간의 차이는 거의 없었다. 색도는 전반적으로 L값은 감소하였으며 a, b값이 증가되는 현상을 보여주었으며, 조직감은 모든 처리구에서 초기 4,520$\pm$75 g에서 점차로 감소하는 경향을 보였으나 그 감소 폭이 유자과즙첨가구가 가장 적은 것으로 나타나 저장 25일째 4,160$\pm$80 g의 수준을 보였다. 총 vitamin C함량은 0.5%유자과즙 첨가 구에서 25일째 6.99 mg%로 약 57%의 보존율을 보여 가장 손실이 적었다. 총당은 대부분의 처리구에서 저장 15일째까지 급격히 하강하다가 저장 15일 이후에는 감소속도가 완만한 것을 볼 수 있었으며, 저장 중의 유리당의 함량은 저장기간에 따른 증감의 큰 변화 폭은 관찰할 수 없었다. 단지 sucrose 함량은 저장 중반기인 10일 전후에 일부 감소하다가 다시 증가하여 저장 25일째에는 처리구에 관계없이 저장 초기 값의 1.5~2배 수준에 도달하였으며, fructose, glucose, maltose는 저장기간별 처리구간에 따른 유의적인 차이가 나타나지 않았다. 박피 토란의 주 아미노산은 aspartic acid와glutamic acid로 각각 1,084.8 mg/100g. 691.8 mg/100g으로 나타났으며, 전해산화수에 침지하여 저장한 경우 aspartic acid 함량이 초기보다 13.9% 수준 증가하였다. 한편, 필수아미노산총량은 유자과즙 첨가구에 저장한 경우가 총당 감소율 측면에서 가장 유리한 것으로 나타났다.

• Korean Chemical Engineering Research
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• 제53권1호
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• pp.46-52
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• 2015

A leaching kinetics was conducted for the purpose of recovery of praseodymium in sulfuric acid ($H_2SO_4$) from REE slag concentrated by the smelting reduction process in an arc furnace as a reactant. The concentration of $H_2SO_4$ was fixed at an excess ratio under the condition of slurry density of 1.500 g slag/L, 0.3 mol $H_2SO_4$, and the effect of temperatures was investigated under the condition of 30 to $80^{\circ}C$. As a result, praseodymium oxide ($Pr_6O_{11}$) existing in the slag was completely converted into praseodymium sulfate ($Pr_2(SO_4)_3{\cdot}8H_2O$) after the leaching of 5 h. On the basis of the shrinking core model with a shape of sphere, the first leaching reaction was determined by chemical reaction mechanism. Generally, the solubility of pure REEs decreases with the increase of leaching temperatures in sulfuric acid, but REE slag was oppositely increased with increasing temperatures. It occurs because the ash layer included in the slag is affected as a resistance against the leaching. By using the Arrhenius expression, the apparent activation energy of the first chemical reaction was determined to be $9.195kJmol^{-1}$. In the second stage, the leaching rate is determined by the ash layer diffusion mechanism. The apparent activation energy of the second ash layer diffusion was determined to be $19.106kJmol^{-1}$. These relative low activation energy values were obtained by the existence of unreacted ash layer in the REE slag.

• 한국환경농학회지
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• 제39권4호
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• pp.297-304
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• 2020

BACKGROUND: Emission of nitrous oxide (N2O) from the soil is expected to depend on the types of nitrogen fertilizer used. Biochar has recently been proposed as a potential mitigation of climate change by reducing the N2O emission. Although laboratory studies reported that biochar applications could reduce N2O emission, the number of field-based studies is still limited. Therefore, a field experiment was conducted to investigate the effect of biochar on N2O emission when different nitrogen fertilizers were applied in corn cultivated field. METHODS AND RESULTS: The field experiment consisted of six treatments: urea fertilizer without biochar (U), ammonium sulfate fertilizer without biochar (A), oil cake fertilizer without biochar (O), urea fertilizer with biochar (U+B), ammonium sulfate fertilizer with biochar (A+B), and oil cake fertilizer with biochar (O+B). Biochar was applied at a rate of 10 t/ha. Greenhouse gas fluxes were measured during growing seasons using static vented chambers. The cumulative N2O emissions were 0.99 kg/ha in the U, 1.23 kg/ha in the A, 3.25 kg/ha in the O, 1.19 kg/ha in the U+B, 0.86 kg/ha in the A+B, and 1.55 kg/ha in the O+B. CONCLUSION: It was found that N2O emission was related to application of both nitrogen fertilizer type and biochar. In particular, the N2O reduction effect was the highest in the corn field incorporated with biochar when oil cake was applied to the soil.

• 상하수도학회지
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• 제25권2호
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• pp.223-230
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• 2011

An electrolytic oxidation process was applied to remove odorous compounds from non-point odor sources including wastewater pipelines and manholes. In this study, a distance between the anode and the cathode of the electrolytic process was varied as a system operating parameters, and its effects on odor removal efficiencies and reaction characteristics were investigated. Odor precursors such as sediment organic matters and reduced sulfur/nitrogen compounds were effectively oxidized in the electrolytic process, and a change in oxidation-reduction potential (ORP) indicated that an stringent anaerobic condition shifted to a mild anoxic condition rapidly. At an electrode distance of 1 cm and an applied voltage of 30 V, a system current was maintained at 1 A, and the current density was 23.1 $mA/cm^{2}$. Under the condition, the removal efficiency of hydrogen sulfide in gas phase was found to be 100%, and 93% of ammonium ion was removed from the liquid phase during the 120 minute operating period. Moreover, the sulfate ion (${SO_4}^{2-}$) concentration increased about three times from its initial value due to the active oxidation. As the specific power consumption (i.e., the energy input normalized by the effective volume) increased, the oxidation progressed rapidly, however, the oxidation rate was varied depending on target compounds. Consequently, a threshold power consumption for each odorous compound needs to be experimentally determined for an effective application of the electrolytic oxidation.

• 환경생물
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• 제17권2호
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• pp.183-190
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• 1999

The bioleaching of heavy metals from fly ash was performed by Thiobacillus thiooxidans MET isolated from the enrichment culture of an anaerobically digested sludge. The effect of solid concentrations on the efficiency of metal leaching was studied in shaken flasks. In the range of solid concentrations 20 g.L­$^1$to 100 g.L­$^1$T. thiooxidans MET oxidized S$^{0}$ to sulfate without any lag period. The final pH of slurry solution was decreased to below pH 1, and the final oxide-redox potential (ORP) was increased to over 420 mV in the solid concentrations below 100 g.L­$^1$. However, the initial lag period of 4 to 8 days was required to obtain the pH reduction and ORP increase of the slurry solutions in the range of solid concentrations 150 g.L­$^1$to 300 g.L­$^1$. The sulfur oxidation rate of T. thiooxidans MET in 20~100 g.L­$^1$solid concentrations was 0.70~0.75 g-S.L­$^1$ㆍ d­$^1$, but its sulfur oxidation activity was remarkably inhibited with increasing solid concentration over 150 g.L­$^1$. Increasing fly ash solids concentration in the range of solids concentration 20 g.L­$^1$ to 200 g.L­$^1$decreased the removal efficiency of Zn, Cu, Mn, Cr and Pb. The solubilization of heavy metals from fly ash was strongly correlated with the pH value of slurry solution. When the pH of slurry solution was reduced to 3, the solubilization process of Zn, Cu and Mn started, and their solubilization efficiency of Zn, Cu and Mn was progressively increased below pH 2. However, the solubilization process of Cr and Pb started at pH 2.5 and 2.0, respectively.

• Mycobiology
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• 제44권4호
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• pp.260-268
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• 2016

Regulation of alkaline-resistant laccase from Perenniporia tephropora KU-Alk4 was proved to be controlled by several factors. One important factor was the initial pH, which drove the fungus to produce different kinds of ligninolytic enzymes. P. tephropora KU-Alk4 could grow at pH 4.5, 7.0, and 8.0. The fungus produced laccase and MnP at pH 7.0, but only laccase at pH 8.0. The specific activity of laccase in the pH 8.0 culture was higher than that in the pH 7.0 culture. At pH 8.0, glucose was the best carbon source for laccase production but growth was better with lactose. Low concentrations of glucose at 0.1% to 1.0% enhanced laccase production, while concentrations over 1% gave contradictory results. Veratryl alcohol induced the production of laccase. A trace concentration of copper ions was required for laccase production. Biomass increased with an increasing rate of aeration of shaking flasks from 100 to 140 rpm; however, shaking at over 120 rpm decreased laccase quantity. Highest amount of laccase produced by KU-Alk4, 360 U/mL, was at pH 8.0 with 1% glucose and 0.2 mM copper sulfate, unshaken for the first 3 days, followed by addition of 0.85 mM veratryl alcohol and shaking at 120 rpm. The crude enzyme was significantly stable in alkaline pH 8.0~10.0 for 24 hr. After treating the pulp mill effluent with the KU-Alk4 system for 3 days, pH decreased from 9.6 to 6.8, with reduction of color and chemical oxygen demand at 83.2% and 81%, respectively. Laccase was detectable during the biotreatment process.

• Molecules and Cells
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• 제23권3호
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• pp.370-378
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• 2007

A superoxide dismutase was purified 62-fold in seven steps to homogeneity from Methylobacillus sp. strain SK1, an obligate methanol-oxidizing bacterium, with a yield of 9.6%. The final specific activity was 4,831 units per milligram protein as determined by an assay based on a 50% decrease in the rate of cytochrome c reduction. The molecular weight of the native enzyme was estimated to be 44,000. Sodium dodecyl sulfate gel electrophoresis revealed two identical subunits of molecular weight 23,100. The isoelectric point of the purified enzyme was found to be 4.4. Maximum activity of the enzyme was measured at pH 8. The enzyme was stable at pH range from 6 to 8 and at high temperature. The enzyme showed an absorption peak at 280 nm with a shoulder at 292 nm. Hydrogen peroxide and sodium azide, but not sodium cyanide, was found to inhibit the purified enzyme. The enzyme activity in cell-free extracts prepared from cells grown in manganese-rich medium, however, was not inhibited by hydrogen peroxide but inhibited by sodium azide. The activity in cell extracts from cells grown in iron-rich medium was found to be highly sensitive to hydrogen peroxide and sodium azide. One mol of native enzyme was found to contain 1.1 g-atom of iron and 0.7 g-atom of manganese. The N-terminal amino acid sequence of the purified enzyme was Ala-Tyr-Thr-Leu-Pro-Pro-Leu-Asn-Tyr-Ala-Tyr. The superoxide dismutase of Methylobacillus sp. strain SK1 was found to have antigenic sites identical to those of Methylobacillus glycogenes enzyme. The enzyme, however, shared no antigenic sites with Mycobacterium sp. strain JC1, Methylovorus sp. strain SS1, Methylobacterium sp. strain SY1, and Methylosinus trichosproium enzymes.

• 대한환경공학회지
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• 제28권5호
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• pp.563-572
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• 2006

정체수역 호소 퇴적물로부터 인 용출 저감을 위한 최적의 In-situ 처리 방법을 제시하고자 실험실 규모의 batch test를 수행하였다. 실험에 사용된 퇴적물의 성상은 평균입도 $7.7{\phi}$(mud)로 매우 세립하고, 유기탄소 함량은 2.4%로 매우 높다. 인 용출 실험은 수층 미생물의 영향을 고려한 경우와 미생물의 영향을 배제한 호소수와 증류수로 구분하여 총 12개 컬럼을 비교 평가하였다. In-situ capping 소재로는 모래와 황토를 사용하였으며, in-situ chemical treatment로는 Fe-Gypsum, $SiO_2$-Gypsum의 산화제를 적용하였다. 또한 산화제와 모래층을 결합시킨 복합층에 대해서도 비교 평가하였다. 미생물의 영향을 고려한 호소수의 경우, 실험 초기에는 인의 농도가 급격히 감소하다 10일 이후부터 서서히 증가되는 것을 확인할 수 있었다. 이는 수층의 미생물에 의해 인이 섭취(uptake)되었다가 다시 용출되는데 시간이 소요되는 것으로 나타났다. 30일간 퇴적물로부터 용출된 인의 flux는 control의 경우 $3.0mg/m^2{\cdot}d$로 매우 높고, 모래층(5 cm), 황토층(5 cm)으로 rapping을 한 경우 역시 충분한 압밀이 이루어지지 않아 $2.5mg/m^2{\cdot}d,\;1.8mg/m^2{\cdot}d$로 인 저감 효율이 낮았다. 화학적 소재를 적용한 Fe-gypsum와 $SiO_2$-gypsum은 $1.4mg/m^2{\cdot}d$로 control과 비교시 인 용출 저감 효율이 약 40% 이상으로 나타났다. 복합층으로 rapping을 한 경우는 $1.0mg/m^2{\cdot}d$로 60% 이상의 높은 인 저감 효율을 보였다. 즉, 오염퇴적물에 산화제로서 gypsum($CaSO_4{\cdot}2H_2O$) 적용은 인의 용출을 감소시키며, 퇴적물내 황산염이 서서히 용해되어 SRB(sulfate reducing bacteria)의 활성과 유기물의 광물화를 촉진시킬 수 있다.