• Title/Summary/Keyword: $Mg_3N_2$

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Herbicide Resistant Cabbage (Brassica oleracea ssp. capitata) Plants by Agrobacterium-mediated Transformation

  • Lee, Yeon-Hee;Lee, Seung-Bum;Suh, Suk-Chul;Byun, Myung-Ok;Kim, Ho-Il
    • Journal of Plant Biotechnology
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    • v.2 no.1
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    • pp.35-41
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    • 2000
  • Transgenic cabbage (Brassica oleracea ssp. capitata) plants resistant to the commercial herbicide Bast $a^{R}$ were obtained by Agrobacterium tumefaciens - mediated transformation. Hypocotyl segments of in vitro grown plants were infected with Agrobacterium tumefaciens LBA 4404 harboring plasmid pMOG6-Bar which contains hpt and bar genes. Explants were cultured on callus induction medium (MS basal medium + 1 mg/L NAA + 2 mg/L BA + 2 mg/L AgN $O_3$+ 100 mg/L carbenicillin + 250 mg/L cefotaxime) supplemented with 15 mg/L hygromycin. Hygromycin resistant calluses were transferred to shoot regeneration medium (MS basal medium + 0.1 mg/L NAA + 2 mg/L BA + 3% sucrose + 2 mg/L AgN $O_3$+ 15 mg/L hygromycin + 250 mg/L cefotaxime + 100 mg/L carbenicillin). In order to induce roots, elongated shoots were placed on the MS medium without plant growth regulators and hygromycin. Southern blot analysis of several putative transgenic plants indicated that one to five intact copies of Apt and bar genes were incorporated into the genome. Expression of bar gene was confirmed by Northern blot analysis and by herbicide resistant phenotype. Seed progeny from self-pollinated transformants expressed the herbicide resistance and showed Mendelian segregation of the introduced gene.e.

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Impacts of the Hydraulic Loading Rate and C/N Ratio on Nitrification in a Trickling Filter with Styrofoam Bead Media in Seawater (살수식 여과조의 질산화작용에 대한 수리학적 부하량과 C/N 비의 영향)

  • Choi, TaeGun;Kim, Pyong-kih;Park, JeongHwan
    • Korean Journal of Fisheries and Aquatic Sciences
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    • v.52 no.3
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    • pp.256-267
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    • 2019
  • Styrofoam beads, which are relatively inexpensive and can provide a large specific surface area, were tested as filter media. Styrofoam beads with a diameter of $3{\pm}0.5mm$ were used; the specific surface area of the beads was $1,034m^2{\cdot}m^{-3}$. Five independent recirculating culture systems were used in the experiment. Each system consisted of one culture tank and three trickling bio-filters. Using the systems, nitrification efficiency was evaluated with respect to hydraulic loading rate (HLR) and carbon/nitrogen (C/N) ratio. The lowest ammonia and nitrogen concentrations were $0.84mg{\cdot}L^{-1}$ and $1.30mg{\cdot}L^{-1}$, respectively, observed at an HLR of $50.9m^3{\cdot}m^{-2}{\cdot}h^{-1}$. Nitrification efficiency in the culture tank was highest at a C/N ratio of 0, with ammonia and nitrite nitrogen concentrations of $0.32mg{\cdot}L^{-1}$ and $0.90mg{\cdot}L^{-1}$, respectively. Ammonia and nitrite nitrogen concentrations in the culture tank abruptly changed at C/N ratios ${\geq}3$.

Pollutants Unit Loadings of the Stormwater Runoff in Industrial Complex (강우시 산업단지에서의 유출오염부하량 원단위 산정)

  • Lee, Jun-Ho;Bang, Ki-Woong;Choi, Jong-Soo
    • Journal of Korean Society of Environmental Engineers
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    • v.22 no.2
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    • pp.355-362
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    • 2000
  • The objective of this paper is to estimate the pollutant load based on event mear concentrations(EMC) in industrial complex. Eight sub-basins in the Chongju industrial complex were selected for sampling and study with different characteristics during the period from June 1997 to August 1998. During the storm events, measured EMC ranges of $BOD_5$, COD, SS, TKN, TP, HEM, $NO_3-N$, $PO_4-P$, Cr, Pb, Cu and Fe in the industrial complex watersheds were 11~176mg/L, 40~502mg/L, 23~633mg/L, 104~20.9mg/L, 0.22~7.51mg/L, 12.7~548.7mg/L, 0.06~2.66mg/L, 0.12~3.39mg/L, 0.01~0.50mg/L. 0.02~0.42mg/L, 0.01~0.15mg/L and 1.29~11.51mg/L respectively. And the calculated annual average pollutant unit loadings of $BOD_5$ COD, SS, TKN, $NO_3-N$, $PO_4-P$, TP, HEM, Cr, Pb, Cu and Fe were 374.4kg/ha/yr 924.1kg/ha/yr, 983.6kg/ha/yr, 48.8kg/ha/yr, 8.1kg/ha/yr, 9.7kg/ha/yr, 17.8kg/ha/yr 943.0kg/ha/yr, 0.7kg/ha/yr, 0.9kg/ha/yr, 0.3kg/ha/yr and 28.9kg/ha/yr, respectively.

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Isolation and Quantitative Analysis of BACE1 Inhibitory Compounds from Cirsium maackii Flower

  • Bhatarrai, Grishma;Seong, Su Hui;Jung, Hyun Ah;Choi, Jae Sue
    • Natural Product Sciences
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    • v.25 no.4
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    • pp.326-333
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    • 2019
  • The purpose of our study was to evaluate anti-AD potential of Cirsium maackii flowers. MeOH extract, CH2Cl2, EtOAc, and n-BuOH fraction of this flower notably inhibited BACE1 (IC50 = 76.47 ± 1.66, 22.98 ± 1.45, 8.65 ± 0.63, and 72.47 ± 3.04 ㎍/mL, respectively). β-amyrenone (49.70 mg) (1), lupeol acetate (1.43 g) (2), lupeol (1.22 g) (3), lupenone (23.70 mg) (4), β-sitosterol (1.01 g) (6), and β-sitosterol glucoside (13.00 mg) (7) from CH2Cl2, apigenin (100.20 mg) (8), luteolin (19.00 mg) (9), apigenin 7-O-glucuronide methyl ester (21.30 mg) (14), and tracheloside (53.70 mg) (5) from EtOAc, apigenin 5-O-glucoside (11.00 mg) (10), luteolin 5-O-glucoside (11.00 mg) (11) and apigenin 7-O-glucuronide (91.00 mg) (12) from n-BuOH, and luteolin 7-O-glucuronide (22.00 mg) (13) from H2O fraction were isolated. HPLC showed high levels of 8, 9 and 12 in MeOH extract (33.07 ± 0.07, 31. 44 ± 0.17 and 16.89 ± 0.33 mg/g, respectively), EtOAc (161.01 ± 1.78, 96.93 ± 0.34 and 73.38 ± 0.06 mg/g, respectively), and n-BuOH fraction (32.18 ± 0.33, 44.31 ± 0.32 and 105.94 ± 0.36 mg/g, respectively). Since, 3 and 9 are well-known BACE1 inhibitors, the anti-AD activity of C. maackii flower might be attributable to their presence.

Evaluation for Impacts of Nitrogen Source to Groundwater Quality in Livestock Farming Area

  • Lee, Gyeong-Mi;Park, Sunhwa;Kim, Ki-In;Jeon, Sang-Ho;Song, Dahee;Kim, Deok-hyun;Kim, Tae-Seung;Yun, Seong-Taek;Chung, Hyen Mi;Kim, Hyun-Koo
    • Korean Journal of Soil Science and Fertilizer
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    • v.50 no.5
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    • pp.345-356
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    • 2017
  • We investigated 52 livestock farming complexes in Gyeong-Gi and Incheon provinces based on low, medium, and high livestock density and groundwater quality. The objective of this study was to evaluate a relationship between nitrate N concentration in groundwater and animal factors, such as livestock density and animal species. 2,200 groundwater samples for 3 years from 2012 to 2014 at Gyeong-Gi and Incheon provinces were collected and analyzed for pH, EC, DO, ORP, temperature, major anions and cations, such as $NO_3-N$, ${HCO_3}^-$, ${PO_4}^-$, ${SO_4}^{2-}$, $Cl^-$, $NH_4-N$, $K^+$, $Na^+$, $Ca^{2+}$, $Mg^{2+}$, T-N, and TOC. Average concentration of total N for generated load density was $23,973g\;day^{-1}\;km^{-2}$ for cattle, $51,551g\;day^{-1}\;km^{-2}$ for pig, and $52,100g\;day^{-1}\;km^{-2}$ for poultry. For animal feeding species, average ratio for generated load over discharge load was 16.1% for cattle, 7.8% for pig, and 7.1% for poultry. Therefore, cattle feeding region is highly vulnerable for water pollution compared to pig and poultry feeding areas. The concentrations of chloride, nitrate, and total N in the groundwater samples were higher at high animal farming regions than other regions. The average concentration of nitrate, and chloride in groundwater samples was $5.0mg\;L^{-1}$, $16.6mg\;L^{-1}$ for low livestock density, $6.9mg\;L^{-1}$, $17.7mg\;L^{-1}$ for medium livestock density and $7.6mg\;L^{-1}$, $22.7mg\;L^{-1}$ for high livestock density and total nitrogen (T-N) was $7.7mg\;L^{-1}$ for low livestock density, $9.4mg\;L^{-1}$ for medium livestock density, $10.7mg\;L^{-1}$ for high livestock density. In conclusion, based on this research, for managing groundwater quality near livestock farming regions, $Ca-(Cl+NO_3)$ group from the Piper diagram is more efficient than using 19 factors for water quality standard.

Evaluation of the Effect of Agricultural Activity on Stream Water Quality by Watershed Modeling (유역모형을 이용한 농업활동이 수질에 미치는 영향평가)

  • Jung, KwangWook;Jung, Inkyun;Kang, SooMan;Kwon, Jinwook
    • Proceedings of the Korea Water Resources Association Conference
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    • 2016.05a
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    • pp.510-510
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    • 2016
  • 농업 비점오염원의 영향을 분석하고 여러 가지 대안(관리정책)이 수계의 수질에 미치는 영향을 평가하기 위해서 유역모형의 적용이 필요하다. 이러한 유역모형에는 모형의 복합성, 계산시간 등에 따라 simple method, mid-range model, detail model로 나눌 수 있다. Simple methods는 요구되는 자료가 작으나 그 결과의 정확성은 떨어진다. 반면에 detail model는 정확한 결과를 획득할 수 있으나 그만큼 방대한 자료와 모니터링을 요구하며, 보정 및 검증에 많은 시간과 노력을 필요로 한다. 특히, 복잡한 유역특성 및 축산오염원을 포함한 복잡한 특성들을 고려해서 모델링하기 위해서는 detail model이 필요하며 본 연구에서는 HSPF모델을 이용해서 그 영향을 분석하고자 하였다. 따라서 본 연구에서는 농업에 미치는 영향을 평가하기 위해서 청미천 유역 및 덕천천 유역을 대상유역으로 선정하여 그 영향을 분석하였다. 농업에 미치는 영향을 평가하기 위해서 유역내 투입된 비료사용량을 통계청 자료를 활용하여 산정후 적용하였으며, 축산 부산물중 자원화되는 축산 액비 및 퇴비량을 산정하여 그 영향에 대해 분석하였다. 또한 기존에 광범위하게 활용되고 있는 수질오염총량관리제도에서 산정되는 배출부하량에 유달율을 고려하여 점오염으로 입력하였으며, 직접방류되는 하수처리장도 함게 고려하여 구축하였다. 청미천 유역의 청미천1 지점의 BOD, T-N, T-P에 대한 보정기간의 평균 관측값은 4.205mg/L, 3.844mg/L, 0.137mg/L이며 검정기간의 관측값은 2.741mg/L, 4.638mg/L, 0.144mg/L로 나타났다. BOD, T-N, T-P에 대한 보정기간의 NSE는 -0.58, -0.20, -0.33이며, 검정기간의 NSE는 -0.26, -1.35, -3.54로 분석되었다. BOD, T-N, T-P에 대한 보정기간의 RMSE는 2.65, 1.63, 0.12이며, 검정기간의 RMSE는 1.36, 1.64, 0.07로 나타났다. 덕천천 유역의 경우 국가관측망이 없어 동진강의 제일 말단 지점인 동진강3 지점의 BOD, T-N, T-P에 대한 보정기간 평균관측값은 2.891mg/L, 3.455mg/L, 0.096mg/L이며, 검정기간의 관측값은 2.293mg/L, 3.223mg/L, 0.104mg/L로 나타났다. BOD, T-N, T-P에 대한 보정기간의 NSE는 -0.20, -0.56, -0.49이며, 검정기간의 NSE는 0.24, -0.06, -0.19으로 분석되었다. BOD, T-N, T-P에 대한 보정기간의 RMSE는 1.53, 2.12, 0.05이며, 검정기간의 RMSE는 1.05, 0.98, 0.06으로 나타났다. 본 연구의 분석결과는 점오염원, 축산계비점오염, 토지계비점오염, 시비량, 배경부하로 구분하여 분석을 실시하였으며 분석결과 청미천 유역의 비점오염 기여율이 약 65%를 차지하고 있는 것으로 평가되었으며, 덕천천 말단에서는 약 37.7%의 비점오염물질이 하천수질에 영향을 미치는 것으로 나타났다. 또한, 기존 수질오염 총량관리제도에서 점오염의 감소에 의한 비점오염비중이 커지는 것으로 평가되었으며, 그 중 축산이 차지하는 비중이 상대적으로 높은 것으로 평가되고 있지만, 본 연구의 결과에서는 그보다 적은 수준이 수계에 영향을 미치는 것으로 분석되었다.

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The Nitrogen Behavior and Budget in Lake Paldang (팔당호의 질소거동과 수지)

  • Lee, Jangho;Park, Hae-Kyung;Lee, Kyoo;Kim, Eunmi
    • Journal of Korean Society on Water Environment
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    • v.26 no.1
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    • pp.71-80
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    • 2010
  • We studied the nitrogen behavior and budget of Lake Paldang from March to December 2008. The particulate nitrogen (PN) concentrations ranged from 7 to 13% of the total nitrogen concentration (TN) in the stream inflows, the downstream outflow, and the lake water. The nitrate nitrogen ($NO_3-N$) concentration ranged from 67 to 78% of the TN. In the three rivers of Lake Paldang, Gyeongan River (In3 site) had the highest average of the TN, 5.037 mgN/L, but North Han River (In2 site) had the lowest average TN, 1.683 mgN/L. South Han River (In1 site) had the average TN of 2.399 mgN/L. In the dam discharge, TN showed the average 2.063 mgN/L. In the lake water, L4 site (Gyeongan River area) had the highest average TN, 3.781 mgN/L, but L3 site (North Han River) had the lowest average TN, 1.587 mgN/L. Total input of nitrogen loads to Lake Paldang was about 30,875 ton/year in 2008. Inflow rivers contributed 30,643 ton/year (South Han River: 18,111 ton/year (59%), North Han River: 11,333 ton/year (37%), and Gyeongan River: 1,199 ton/year (4%)). The atmospheric deposition had 135 ton/year, the nitrogen release from the bottom sediments had 88 ton/year, and macrophytes had 9 ton/year. Total output of nitrogen loads from Lake Paldang was about 31,256 ton/year. The downstream from dam contributed 29,877 ton/year, and the sediment deposition was 1,379 ton/year.

Geochemical Characteristics and Assesment of Nitrate Nitrogen in Groundwater in Yanggu-Gun, Gangwon-Do in Korea

  • Choi, Won Gyu
    • Journal of Soil and Groundwater Environment
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    • v.24 no.6
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    • pp.26-32
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    • 2019
  • An analysis of groundwater quality is significant for monitoring and managing water contamination and groundwater system. For the purpose of those, the geochemical characteristics of groundwater were studied over the concern for water quality, water type and origin of nitrate nitrogen. Total colony counts were detected in 11 out of 20 samples, and the average value was 31.73 CFU/ml. Range and average of NO3-N concentrations were 0.9~24.0 mg/L and 8.3 mg/L. All groundwater types were found to be Ca2+-HCO3-. The range and average of NO3-N were 0.2~17.4 mg/L and 8.7 mg/L, and those of δ15N were 1.7~8.9‰, and 5.0‰. Careful consideration is required for evaluating the origin of nitrogen when NO3-N concentration is low. In general, noticeable difference between rockbed and alluvial water was not found. The ranges of nitrate origins by chemical fertilizer, livestock manure and domestic sewage, and natural soil were 29.6~76.4%, 14.2~58.9% and 2.6~7.0%, and the average values of those were 57.4%, 37.4%, and 5.3%, respectively. Origin of nitrate was affected by more chemical fertilizer than the other parameters. Rockbed water was more affected by chemical fertilizer than alluvial water.

Assessment of Water Quality and Pollutant Loads on Agricultural Watershed in Jeonbuk Province (전북지역 농업용 하천유역의 수질과 부하량 특성)

  • Uhm, Mi-Jeong;Moon, Young-Hun;Ahn, Byung-Koo;Shin, Yong-Kyu
    • Korean Journal of Environmental Agriculture
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    • v.27 no.2
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    • pp.111-119
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    • 2008
  • This study was conducted to evaluate water quality and pollutant loads on small agricultural watershed in Jeonbuk province. The EC level of investigated watershed ranged from 0.07 to 0.52 dS/m, BOD level ranged from 0.1 to 5.0 mg/L, and $COD_{Cr}$ level ranged from 0.6 to 17.7 mg/L. As above, contents of water quality indicators covered wide range, but each indicator was alike in mean content every other year. The contents of EC, $Ca^{2+},\;Mg^{2+},\;K^+\;and\;Na^+$ were decreased in rainy season, but the contents of BOD, $COD_{Cr},\;COD_{Mn}$, T-N and T-P were not greatly different as compared to dry season. And high content of SS showed substantial sediments near the surface flow out and influence on water system in rainy season. The pollutant loads measured in terminal of watershed were $9.6{\sim}757.9$ kg/day for BOD, $51.2{\sim}1418.5$ kg/day for T-N and $0.3{\sim}44.7$ kg/day for T-P. The pollutant loads of BOD, T-N and T-P in rainy season increased several times as compared to dry season. In rainy season, watershed with more than 30% in the proportion of paddy field to land showed relatively low discharge and pollutant loads in comparison to watershed with less than 30%. The discharge of watershed in rainy season increased 5.7times compared with the dry season in watershed with less than 30% in the proportion of paddy field to land, whereas was only 2.3times in watershed with more than 30%. The correlation coefficient($R^2$) of regression between discharge and pollutant loads of T-N were higher than those of BOD and T-P.

Application of the Hybrid Constructed Wetland for a Reuse of the Effluent from Bio-industrial Wastewater Treatment Plant (바이오산업폐수처리수의 재이용을 위한 hybrid 인공습지 시스템의 적용가능성 연구)

  • Shin, Jae-Suk;Kim, Sung-Chul;Cho, Kwang-Ju;Choi, Choong-Ho;Choi, In-Wook;Park, Jeong-Ja;Park, Goo-Hyeon
    • Journal of Wetlands Research
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    • v.11 no.1
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    • pp.115-121
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    • 2009
  • The hybrid constructed wetland(HCW) as tertiary treatment process of a bio industrial wastewater treatment plant was employed to estimate applications for the reuse of final effluent. Raw wastewater was sequently treated through chemical and biological treatment processes and the biologically treated water was flowed into the HCW. The HCW system was composed of two constructed wetlands connected in series; The one is the aerobic constructed wetland with natural air draft system whose driving force for air supply was the difference between the temperature of the air inside the wetland and the ambient air, and the other is the anaerobic/anoxic constructed wetland. Average influent concentrations of BOD, SS, T-N and T-P in the HCW were 53mg/L, 48mg/L, 34mg/L and 3mg/L, respectively. After being treated at HCW, final effluent concentrations of BOD, SS, T-N and T-P were 2.3mg/L, 1.2mg/L, 7.95mg/L and 0.83mg/L, respectively. Referring to a reuse standard for a sewage wastewater, final effluent could sufficiently be reuse as landscaping, washing or agriculture water. HCW system with the aerobic/anaerobic combined constructed wetland could be achieved a high removal efficiency because each constructed wetland was functionalized to be removed efficiently organics, nitrogen and phosphorus. HCW system could be estimated to be successful application as tertiary treatment process of a various industrial and municipal wastewater.

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