• 제목/요약/키워드: Maximum nitrogen removal

검색결과 133건 처리시간 0.021초

호흡률을 이용한 연속회분식반응조의 질산화 공정 해석 (Nitrification process analysis by respirometry in a sequencing batch reactor)

  • 김동한;김성홍
    • 상하수도학회지
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    • 제33권1호
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    • pp.55-62
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    • 2019
  • The respirometric technique has been used to analyze the nitrification process in a sequencing batch reactor(SBR) treating municipal wastewater. Especially the profile of the respiration rate very well expressed the reaction characteristics of nitrification. As the nitrification process required a significant amount of oxygen for nitrogen oxidation, the respiration rate due to nitrification was high. The maximum nitrification respiration rate, which was about $50mg\;O_2/L{\cdot}h$ under the period of sufficient nitrification, was related directly to the nitrification reaction rate and showed the nitrifiers activity. The growth rate of nitrifiers is the most critical parameter in the design of the biological nutrient removal systems. On the basis of nitrification kinetics, the maximum specific growth rate of nitrifiers in the SBR was estimated as $0.91d^{-1}$ at $20^{\circ}C$, and the active biomass of nitrifiers was calculated as 23 mg VSS/L and it was about 2% of total biomass.

전기투석과 이온교환수지를 이용한 스테인레스 산업의 산세폐수 내 질산성 질소의 제거 (Removal of Nitrate-Nitrogen in Pickling Acid Wastewater from Stainless Steel Industry Using Electrodialysis and Ion Exchange Resin)

  • 윤영기;박연진;오상화;신원식;최상준;류승기
    • 한국환경과학회지
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    • 제18권6호
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    • pp.645-654
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    • 2009
  • Lab-scale Electrodialysis(ED) system with different membranes combined with before or after pyroma process were carried out to remove nitrate from two pickling acid wastewater containing high concentrations of $NO_3\;^-$(${\approx}$150,000 mg/L) and F($({\approx}$ 160,000 mg/L) and some heavy metals(Fe, Ti, and Cr). The ED system before Pyroma process(Sample A) was not successful in $NO_3\;^-$ removal due to cation membrane fouling by the heavy metals, whereas, in the ED system after Pyroma process(Sample B), about 98% of nitrate was removed because of relatively low $NO_3\;^-$ concentration (about 30,000 mg/L) and no heavy metals. Mono-selective membranes(CIMS/ACS) in ED system have no selectivity for nitrate compared to divalent-selective membranes(CMX/AMX). The operation time for nitrate removal time decreased with increasing the applied voltage from 10V to 15V with no difference in the nitrate removal rate between both voltages. Nitrate adsorption of a strong-base anion exchange resin of $Cl\;^-$ type was also conducted. The Freundlich model($R^2$ > 0.996) was fitted better than Langmuir mode($R^2$ > 0.984) to the adsorption data. The maximum adsorption capacity ($Q^0$) was 492 mg/g for Sample A and 111 mg/g for Sample B due to the difference in initial nitrate concentrations between the two wastewater samples. In the regeneration of ion exchange resins, the nitrate removal rate in the pickling acid wastewater decreased as the adsorption step was repeated because certain amount of adsorbed $NO_3\;^-$ remained in the resins in spite of several desorption steps for regeneration. In conclusion, the optimum system configuration to treat pickling acid wastewater from stainless-steel industry is the multi-processes of the Pyroma-Electrodialysis-Ion exchange.

미생물 활성토탄을 이용한 암모니아 제거에 관한 연구 (A Study on the Removal of Ammonia by Using Peat Biofilter)

  • 정연규;안준성
    • 대한토목학회논문집
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    • 제14권3호
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    • pp.655-668
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    • 1994
  • 기존의 토양상 및 퇴비상을 이용한 악취제거가 주로 흡착에 의존한 나머지 탈취상이 쉽게 탈취능의 한계에 이른다. 따라서, 본 연구에서는 미생물 활성 탈취상의 조건인 높은 유기물함량, 보수성, 통기성 및 낮은 정압 등을 고르게 갖추고 있는 토탄에 활성슬러지를 식종하여 분뇨처리장, 하수처리장 등에서 발생빈도 및 취기강도가 큰 무기성악취 중 암모니아의 제거실험을 수행하였다. 실험결과, 자연 토탄상에서는 암모니아의 토탄수분에 의한 이온화에 따라서 pH가 상승하여 암모니아의 자연 유출 현상이 관찰되었다. 암모니아 제거 기작은 주로 음이론 콜로이드에 의한 흡착에 의존하였다. 미생물 활성 토탄상에서는 미생물 활동에 따른 pH의 완만한 상승으로 이론적 암모늄 이온의 비율이 자연토탄상보다 높았으나, 실제로 토탄상에 축적된 암모니아성 질소의 값은 질산균의 질산화에 의해 자연 토탄상보다 적었다. 암모니아의 제거기작은 반응조 운영 초기에는 흡착이 우세하였으며, 중반이후에는 질산화가 두드러졌다. 실험으로 얻은 암모니아 유입부하량, 암모니아 유출부하량, $NH_4{^+}$-N, $NO_x$-N, Org-N을 이용하여 질소에 대한 물질수지(Mass Balance)를 산정하고, 실험결과로 얻은 미생물 활성 탈취상의 최대 활성 시점인 비정상상태의 임계시간과 회귀분석에 의해 구한 암모니아의 흡착곡선을 이용하여 미생물 활성 토탄상에서 흡착능 포화의 연장시간을 산정하였다.

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Identification of bacteria isolated from rockworm viscera and application of isolated bacteria to shrimp aquaculture wastewater treatment

  • Ja Young Cho;Kyoung Sook Cho;Chang Hoon Kim;Joong Kyun Kim
    • 환경생물
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    • 제41권2호
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    • pp.167-178
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    • 2023
  • Large amounts of waste and wastewater from aquaculture have negatively impacted ecosystems. Among them, shrimp aquaculture wastewater contains large amounts of nitrogen contaminants derived from feed residues in an aerobic environment. This study isolated candidate strains from adult rockworms to treat shrimp aquaculture wastewater (SAW) in an aerobic environment. Among 87 strains isolated, 25 grew well at the same temperature as the shrimp aquaculture with excellent polymer degradation ability (>0.5 cm clear zone). Six isolates (strains AL1, AL4, AL5, AL6, LA10, and PR15) were finally selected after combining strains with excellent polymer degradation ability without antagonism. 16S rRNA sequencing analysis revealed that strains AL1, AL4, AL5, AL6, LA10, and PR15 were closely related to Bacillus paramycoides, Bacillus pumilus, Stenotrophomonas rhizophila, Bacillus paranthracis, Bacillus paranthracis, and Micrococcus luteus, respectively. When these six isolates were applied to SAW, they reached a maximum cell viability of 2.06×105 CFU mL-1. Their chemical oxygen demand (CODCr) and total nitrogen(TN) removal rates for 12h were 51.0% and 44.6%, respectively, when the CODCr/TN ratio was approximately 10.0. Considering these removal rates achieved in this study under batch conditions, these six isolates could be used for aerobic denitrification. Consequently, these six isolates from rockworms are good candidates that can be applied to the field of aquaculture wastewater treatment.

Electro-Fenton 반응을 이용한 유독성 유기화합물 처리 (Removal of Toxic Organic Compound using Electro-Fenton Reaction)

  • 박상원
    • 한국환경과학회지
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    • 제13권6호
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    • pp.551-560
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    • 2004
  • The feasibility and efficiency of the hydrogen peroxide produced by an electrolysis cell reactor was investigated, From regulating voltages for the given reaction time, the concentration of the hydrogen peroxide was gradually increased with increasing voltages. Optimal voltage range was found to be 10~15 V. The concentration of hydrogen peroxide was much higher with oxygen gas than without oxygen gas in the cathodic chamber. But there was a little difference in the generating rate of hydrogen peroxide regardless of the presence of nitrogen gas. Under given conditions, the maximum value of ICE(Instantaneous Current Efficiency) was about 38%, and then current density was 74 $mA/\textrm{cm}^2.$ The specific energy consumption was $0.694[kWh/kg-H_2O_2].$ Since Esp (Specific Energy Consumption)was very little value, It did not demand high energy in this system. Using the hydrogen peroxide gained in the experiment, Fenton's reaction was conducted and the removal of nitrobenzene, 3-chlorophenol and dye wastewater was studied. This results were very similar to the Fenton's reaction by using commercial hydrogen peroxide.

Sorption of Chromium Ions from Aqueous Solution onto Chemically Activated Carbons Developed from Maize Cobs

  • Youssef, A.M.;El-Nabarawy, Th.;Shouman, Mona A.;Khedr, S.A.
    • Carbon letters
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    • 제9권4호
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    • pp.275-282
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    • 2008
  • Chemically activated carbons were prepared from maize cobs, using phosphoric acid of variable concentration. The textural parameters of the activated carbons were determined from the nitrogen adsorption isotherms measured at 77 K. The chemistry of the carbon surface was determined by measuring the surface pH, the pHPZC and the concentration of the carbon - oxygen groups of the acid type on the carbon surface. Kinetics of Cr(VI) sorption/reduction was investigated at 303 K. Two processes were investigated in terms of kinetics and equilibrium namely; Cr(VI) removal and chromium sorption were studied at various initial pH (1-7). Removal of Cr(VI) shows a maximum at pH 2.5. At pH<2.5, sorption decreases because of the proton competition with evolved Cr(III) for ion exchange sites. The decrease of sorption at pH>2.5 is due to proton insufficiency and to the decrease of the extent of Cr(VI) reduction. The chemistry of the surface of activated carbon is an important factor in determining its adsorption capacity from aqueous solutions particularly when the sorption process involves ion exchange.

자성으로 표면개질된 제올라이트 흡착제를 이용한 수중 암모늄 이온 제거 특성 (Removal Properties of Aqueous Ammonium ion with Surface Modified Magnetic Zeolite Adsorbents)

  • 정용준
    • 한국습지학회지
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    • 제21권2호
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    • pp.152-156
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    • 2019
  • 본 연구는 수중 암모늄 이온을 처리하기 위하여 자성 제올라이트를 합성하여 흡착 특성을 평가하였다. 표면개질된 자성 제올라이트는 수열작용으로 합성되었다. 제올라이트와 $Fe_3O_4$ 복합체는 SEM과 XRD 분석 결과 혼합비 12.6% 범위이내에서 최적인 상태로 침투 혼합된 것으로 관찰되었다. 최적의 흡착 pH는 중성부근인 약 8근처에서 나타났고, 최대 흡착량은 $Fe_3O_4$ 함량의 증가에 따라 감소하였다. 수중 암모늄 이온은 Langmuir 식에 근사하는 흡착식으로 나타났다. 개발된 합성제올라이트 흡착제는 질소농도의 관리가 필요한 습지환경 보호에도 적용 가능할 것으로 판단된다.

배기가스중 질소산화물의 신속측정법과 그 제거에 관한 연구 (제 2 보). 암모니아에 의한 $NO_x$의제거 (Method for Rapid Determination and Removal of Nitrogen Oxides in Flue Gas (II). Removal of Nitrogen Oxides Using Ammonia)

  • 이용근;팽기정;황규자
    • 대한화학회지
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    • 제30권2호
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    • pp.207-215
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    • 1986
  • 본 연구는 대기중의 질소산화물($NO_x$)을 효율적으로 제거하기 위하여 기존의 방법을 개선한 것으로서, $NH_3$를 이용한 환원법을 개량하였다. 상대습도 60%에서 50 ppm의 $NO_x$는 1% hr-1의 분해율을 나타낸 반면 5배 이상의 $NH_3$를 첨가함으로써 50 ppm $NO_x$인 경우에는 6% $hr^{-1}$, 20ppm인 경우는 10% $hr^{-1}$의 제거율을 나타내었다. 그러나 실제 배기기체에서는 과량의 수분과 탄화수소나 일산화탄소같은 환원성 기체가 포함되고 미량의 금속이온들이 공존되므로 최고 15% $hr^{-1}$까지 $NO_x$의 제거가 촉진되었다. 또한 SO_2와 같은 산성기체의 공존은 분해율을 감소시켰다. 이 $NO_x$의 분해현상은 주로 계에 가해진 수증기의 응축으로 생긴 수막에 NO_x가 용해되는 동시에 염기성인 $NH_3$기체도 용해되어 이루어진 이들 이온들의 환원반응에 기인된다고 생각된다.

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ISOLATION, IDENTIFICATION AND CHARACTERIZATION OF AN IMMOBILIZED BACTERIUM PRODUCING N2 FROM NH4+ UNDER AN AEROBIC CONDITION

  • Park, Kyoung-Joo;Cho, Kyoung-Sook;Kim, Jeong-Bo;Lee, Min-Gyu;Lee, Byung-Hun;Hong, Young-Ki;Kim, Joong-Kyun
    • Environmental Engineering Research
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    • 제10권5호
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    • pp.213-226
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    • 2005
  • To treat wastewater efficiently by a one-step process of nitrogen removal, a new bacterial strain producing $N_2$ gas from ${NH_4}^+$ under an aerobic condition was isolated and identified. The cell was motile and a Gram-negative rod, and usually occurred in pairs. By 16S-rDNA analysis, the isolated strain was identified as Enterobacter asburiae with 96% similarity. The isolate showed that the capacity of $N_2$ production under an oxic condition was approximately three times higher than that under an anoxic condition. Thus, the consumption of ${NH_4}^+$ by the isolate was significantly different in the metabolism of $N_2$ production under the two different environmental conditions. The optimal conditions of the immobilized isolate for $N_2$ production were found to be pH 7.0, $30^{\circ}C$ and C/N ratio 5, respectively. Under all the optimum reaction conditions, $N_2$ production by the immobilized isolate resulted in reduction of ORP with both the consumption of DO and the drop of pH. The removal efficiencies of $COD_{Cr}$, and TN were 56.1 and 60.9%, respectively. The removal rates of $COD_{Cr}$, and TN were the highest for the first 2.5 hrs with the removal $COD_{Cr}/TN$ ratios of 32.1, and afterwards the rates decreased as reaction proceeded. For application of the immobilized isolate to a practical process of ammonium removal, a continuous operation was executed with a synthetic medium of a low C/N ratio. The continuous bioreactor system exhibited a satisfactory performance at 12.1 hrs of HRT, in which the effluent concentrations of ${NH_4}^+$-N was measured to be 15.4 mg/L with its removal efficiency of 56.0%. The maximum removal rate of ${NH_4}^+$-N reached 1.6 mg ${NH_4}^+$-N/L/hr at 12.1 hrs of HRT(with N loading rate of $0.08\;Kg-N/m^3$-carrier/d). As a result, the application of the immobilized isolate appears a viable alternative to the nitrification-denitrification processes.

Biofilm Processes for Volume Decrease in Recirculating Water Treatment Systems for Aquaculture

  • Kim Jeong-Sook;Yoon Gil-Ha;Ghim See-Jun;Kang Lim-Seok;Lee Byung-Hun
    • Fisheries and Aquatic Sciences
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    • 제1권2호
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    • pp.242-249
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    • 1998
  • The engineering aspect of water treatment processes in the recirculating aquaculture system was studied. To recycle the water in the aquaculture system, a wastewater treatment process was required to maintain high water quality for the growth and health of the cultured fish. In this study, three different biofilm processes were used to reduce the concentration of organic matters and ammonia from the recirculating water - two phase fluidized bed, three phase fluidized bed, and trickling filter. The objectives of this research were to evaluate the optimum treatment conditions of the biofilm processes for the recirculating aquaculture system, and thereby reduce the volume of biofilm processes, which are commonly used for the recycle water treatment processes for aquaculture. The result of this study showed that the removal efficiency of organic matters by trickling filter was found to be lower than that of the fluidized bed. In the trickling filter system, anthracite showed better organic removal efficiency than crushed stone as a media. In the two phase fluidized bed, the maximum removal efficiency of either organics or ammonia was obtained when both the packing rate of media was maintained to $40\%$ of total reactor depth excepting sediment zone and the bed expansion rate was maintained to $100\%$. When 100 tilapia (Oreochromis niloticus) of each average 200g was reared, the pollutant production rate was 0.07g $NH_4\;^+-N/kg$ fish/day and 0.06g P04-3-P/kg fish/day, and sludge production rate was 0.39 g SS/kg fish/day. In the two phase and three phase fluidized bed, the volume of water treatment tank could be calculated from an empirical equation by using the relationship between the influent COD to $NH_4\;^+-N$ ratio (C/N, -), media concentration (Cm, g/L), influent ammonia nitrogen concentration (Ni, mg/L), effluent ammonia nitrogen concentration (Ne, mg/L), bed expansion rate $(E,\;\%)$, and influent flowrate $(Q,\;m^3/hr)$. The empirical equation from this study is $$V_2\;=\;10^{3.1279}\;C/N^{3.5461}\;C_m\;^{-3.7473}\;N_i\;^{4.6477}\;E^{0.0326}\;N_e\;^{-0..8849}\;Q\;(Two\;Phase\;FB) V_3\;=\;10^{11.7507}\;C/N^{-1.2330}\;C_m\;^{-6.5715}\;N_i\;^{1.5091}\;N_e\;^{-1.8489}\;Q (Three\;Phase\;FB)$$

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