• 대한환경공학회지
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• 제22권4호
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• pp.651-659
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• 2000

천연중화제의 스크러버 타입의 탈취장치에 의한 암모니아 제거반응 특성 및 중화반응에의 산화반응의 관여여부에 대하여 연구하였다. 중화제 희석비 및 유입유량, 공기유량, 암모니아 초기 농도를 운전인자로 선정하여 이들이 암모니아 제거효율에 미치는 영향을 살펴본 결과, 중화제 희석비는 1.0%, 중화제 유입유량은 $60m{\ell}/min$이 적절하고, 암모니아 초기농도 및 공기유량에 대해서는 loading rate를 함께 고려하면 제거효율에 큰 영향성은 나타내지 않았다. 암모니아의 중화반응에 산화반응의 관여여부를 살펴본 결과, 암모니아의 아질산염 및 질산염으로의 산화반응이 확인되었으며, 중화제량이 증가할수록 그 산화반응의 진행정도도 증가함을 확인하였다. 즉, 중화제에 의한 흡수현상과 함께 부분적으로 산화반응이 관여함을 확인하였다.

• 한국양식학회지
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• 제6권4호
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• pp.311-321
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• 1993

Ammonia accumulation is regarded as the limiting factor of the first priority in water qualities of aquatic culture systems. Nitrification efficiency and characteristics in seawater were evaluated using Rotating Biological Contactor (RBC) process as a part of the recycling water treatment facilities for marine fish culture system. Ammonia removal efficiency regarded 99.7 to $83.7\%$ at the ammonia surface loading rates of 48 to $393 mg/m^2$ -day. RBC process was able to withstand to the fluctuation of influent ammonia concentrations and loading and produced the stable effluent. The mathematical model on the fixed-film biological reactor developed by Kornegay seemed to be suitable to RBC process kinetic evaluation for the recycling water treatment of the marine fish culture system. Area capacity constant (P) and half-velocity constant (Ks) in the model were 0.188g/m^2$-day and 1.25mg/l, respectively.

• 한국생물공학회:학술대회논문집
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• 한국생물공학회 2000년도 춘계학술발표대회
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• pp.339-342
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• 2000

황화수소와 암모니아 함유악취의 동시처리를 위해 Thiobacillus sp.IW가 함유된 3상 생물막유동층반응기를 사용하였다. 본 연구에서 황화수소는 미생물에 의해 산으로 전환되었으며 이어서 유입된 암모니아와 반응하여 황산암모늄이 생성됨으로서 양성분은 제거되었다. 황화수소의 경우 45 mg/l h의 유입량에서도 거의 완전한 처리 효율을 보여주었으나, 암모니아의 경우 유입량이 10 mg/l h에서 증가함에 따라 처리효율은 점차 감소하였다.

• 한국수산과학회지
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• 제52권3호
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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 ${\geq}3$.

• Korean Chemical Engineering Research
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• 제48권3호
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• pp.391-396
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• 2010

본 연구에서는 퇴비공장 또는 공공시설에서 발생되는 악취폐가스의 대표적인 제거대상 오염원인 암모니아의 효율적 처리를 위하여, 여러 운전 조건 하에서 동 부피의 폐타이어담체와 compost를 충전하고 반송슬러지를 고정한 바이오필터의 암모니아 제거 특성을 조사하고 바이오필터공정의 적정운전조건을 구축하였다. 암모니아를 함유한 폐가스의 처리를 위하여 바이오필터를 30일(2회/1일의 회수로 총 60회 실험) 동안 약 $30^{\circ}C$의 온도조건 하에서 암모니아부하를 $2.18g-N/m^3/h$부터 $70g-N/m^3/h$ 까지 증가시키면서 운전하였다. 바이오필터를 가동하여 I부터 IV 단계까지는 암모니아 제거율이 거의 100%로서, 암모니아부하가 $17g-N/m^3/h$에 이르기까지 거의 모든 암모니아가 제거되었으나, 바이오필터 운전 V 단계에서 암모니아부하를 약 $35g-N/m^3/h$로 증가시켰을 때에 암모니아제거율은 약 80% 정도로 급락하여 암모니아 제거용량이 약 $28g-N/m^3/h$이었다. 그러나 바이오필터 운전 VI 단계에서 암모니아부하를 약 $70g-N/m^3/h$로 두 배로 증가시켰을 때에도 암모니아제거율은 80%를 유지하여 최대암모니아 제거용량이 약 $55g-N/m^3/h$에 달하였다. 이와 같이 본 연구의 최대 암모니아 제거용량은, 분뇨슬러지를 유기담체인 rock wool에 접종하고 Kim 등에 의하여 수행된 바이오필터실험의 최대 암모니아 제거용량인 $1,200g-N/m^3/day$(i.e., $50g-N/m^3/h$)보다 다소 우월하였다. 그러나 본 연구의 암모니아 질소 임계부하는 Kim 등에 의하여 수행된 바이오필터실험의 암모니아 질소의 임계부하인 $810g-N/m^3/day$(i.e., $33.75g-N/m^3/h$)에 미치지 못하였다. 본 연구의 최대 암모니아 제거용량이 Kim 등보다 우월한 이유는 Kim 등에 의하여 사용된 미생물담체보다 본 연구에서 사용한 미생물담체인 폐타이어담체의 코코넛 활성탄분말로 도포된 표면 및 발달된 내부공극이 각각 질산화 및 탈질 미생물이 고정화되기 더욱 쉬운 환경을 제공하기 때문이라고 사료된다.

• 한국신재생에너지학회:학술대회논문집
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• 한국신재생에너지학회 2010년도 춘계학술대회 초록집
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• pp.253-253
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• 2010

Rice straw was pretreated with aqueous ammonia in order to enhance enzyme digestibility. Soaking in ammonia aqueous (SAA) was conducted with 15% ammonia, at $60^{\circ}C$. for 24 h. Optimization of both saccharification conditions and enzyme loading of SAA rice straw was carried out. Especially enzyme loading test was performed using statistical method. Moreover proton beam irradiation (PBI) was also performed to overcome the problem which inhibit the enzyme digestibility at 1-25 kGy doses with 45 MeV of beam energy. Optimal condition for enzymatic saccharification was follows; pH 4.8, $50^{\circ}C$, 60 FPU of enzyme activity, 1:4 ratio of celluase and ${\beta}$-glucosidase. Also, optimal doses of PBI on rice straw and SAA-treated rice straw for efficient sugar recovery were found to be 3 kGy, respectively. When saccharification was performed with optimal condition, glucose conversion yield was 89% of theocratical maximum in 48 h, and 3 kGy of PBI was applied to SAA-treated rice straw, approximately 90% of the theoretical glucose yield was obtained in 12 h. The results of X-ray diffractometry (XRD) support the effect of both SAA and PBI on sugar recovery, and scanning electron microscopy (SEM) images unveiled the physical change of the rice straw surface since rugged rice straw surface was observed.

• 한국물환경학회지
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• 제20권1호
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• pp.24-31
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• 2004

This study was initiated to evaluate the efficiencies of DEPHANOX and Modified-DEPHANOX, which were devoloped to enhance nitrogen removal efficiency in municipal wastewater treatment. In the results, removal efficiency of organic matters was not affected much by increased loading rate of organic matters which is contained in influent. The nitrogen removal efficiencies according to the loading rate of influent TN was decreased drastically in conditions of over $0.2kg/m^3{\cdot}day$, which is T-N loading rate, and the DEPHANOX process was affected more sensitively than the M-DEPHANOX was. When the temperature was altered from $25^{\circ}C$ to $16^{\circ}C$ at HRT 6hrs, the removal efficiency of ammonia nitrogen was still over 90% and it was concluded that both DEPHANOX and M-DEPHANOX were strong enough to endure temperature variation. Moreover, both processes showed over 90% in ammonia removal efficiencies in over HRT 5hrs, so it was concluded that they were strong in HRT variation. M-DEPHANOX process showed a higher value than DEPHANOX did in T-N removal efficiency to the extent of 4~21 %, which resulted from differency of denitrification rates and the biosorption efficiency of organic matter in both processes. In the condition of HRT less than 4hrs, concentrations of ammonia nitrogen contained in effluents and nitrification reactors, might be sensitively affected by biosorption efficiency of organic matters in first separation tank. In the effect of effluent nitrate concentration in phosphorus removal, the more effluent nitrate concentration was decreased, the more phosphorus removal efficiency was increased. This result is related to the decrease of concentration of effluent nitrate which resulted from nitrification inhibition by decreased HRT.

• Korean Chemical Engineering Research
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• 제45권3호
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• pp.258-263
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• 2007

배가스 이산화탄소 처리를 위한 화학적 흡수공정의 새로운 흡수제로서 암모니아수의 적용 가능성을 고찰하였다. 이산화탄소 흡수용량과 침전 발생의 관점에서 적합한 암모니아수 흡수제 농도와 $CO_2$ 부하(loading, $molCO_2/molNH_3$)를 결정하였다. 이를 위하여 전해액에 대한 Pitzer 모델을 이용하여 암모니아 흡수제 농도에 따른 흡수용량과 침전 발생여부를 계산하였다. $5\;molNH_3/kgH_2O$ 이상의 암모니아수 흡수제를 사용하여 기존 아민류 흡수제 이상의 흡수용량은 얻을 수 있었다. 각 암모니아 흡수제 농도에서 $NH_4HCO_3$ 침전의 발생으로 인하여 조업이 제약되는 $CO_2$ 부하를 구하였다. $5{\sim}14\;molNH_3/kgH_2O$의 암모니아 흡수제는 293, 313 K에서 $CO_2$ 부하 0.5 이상에서 침전이 발행하였다. 침전 생성 $CO_2$ 부하값 이하로 흡수탑을 조업함으로써 고농도 암모니아 흡수제가 배가스 $CO_2$ 처리 공정에 사용될 수 있음을 알 수 있었다. 흡수용량과 침전발생을 고려하여 배가스 이산화탄소 처리를 위한 흡수제 최적온도는 암모니아수 농도에 따라 297~312 K이었다.

• 한국물환경학회지
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• 제21권6호
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• pp.687-694
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• 2005

Lab-scale experiments have been carried out to investigate the effect of F/R ratio of ASBR (Anaerobic Sequencing Batch Reactor) process on the removal of the organic matters in ammonia stripped swine wastewater. Three ASBR inoculated with sludge mixed with granular sludge of UASB (Upflow Anaerobic Sludge Blanket) and anaerobic digested sludge of municipal wastewater treatment plant were operated. Ammonia stripped swine wastewater was used as influent. Prior to conducting the experiments with varied conditions, the effect of increasing organic loading rate from 2.34 to $5.79gTCOD_{Cr}/L$-day at a fixed F/R ratio of 0.1 on the organic removal efficiency has been studied during start-up period. As the result of the experiment, under the condition of varied organic loadings, less than $4.14gTCOD_{Cr}/L$-day, the removed efficiency $TCOD_{Cr}$ of the ASBR process is 83% resulted from the mean value of effluent $TCOD_{Cr}$, 9,125 mg/L during the start-up period. Then ASBRs were operated with F/R ratio of 0.024, 0.303 and 0.91 respectively. Organic loading rate was increased from 4.56 to $15.43gTCOD_{Cr}/L$-day to investigate the effects of F/R ratio and organic loading rate on the organic removal efficiency. As the result of the experiment, less than $6.23gTCOD_{Cr}/L$/L-day, F/R ratio haven't an effect on the organic removal efficiency and the mean removal efficiency of TSS, $TCOD_{Cr}$ and $SCOD_{Cr}$ was about 80%, 86% and 78% at the all of F/R ratio. But as organic loading rate was increased from 8.54 to $12.04gTCOD_{Cr}/L$-day at the F/R ratio of 0.024, the removal efficiency of $SCOD_{Cr}$ decreased from 71% to 63%. The range of decreased removal efficiency of $SCOD_{Cr}$ at the F/R ratio of 0.024 was much more higher than at the F/R ratio of 0.303, 0.91. Thus, as organic loading rate was increased, ASBRs were operated with high F/R ratio to obtain high removal efficiency.

• 상하수도학회지
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• 제23권5호
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• pp.547-555
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• 2009

The objectives of this research were focused on the effects of various operating parameters on nitrous oxide emission such as C/N ratio, ammonia concentration and HRT in the hybrid and suspension reactors. With the decreasing of C/N ratios, $N_2O$ emission rates in the both processes were increased because organic carbon source for denitrification was depleted. In case of biofilm reactor operated using medium, $N_2O$ release from the nitrification was not affected by the variation of ammonia concentration. But in the suspension reactor, $N_2O$ production from the nitrification was rapidly increased with the increase of ammonia. Nitrite accumulation caused by undesirable nitrification conditions could be a important reason for the increase in the $N_2O$ production from the aerobic reactor. And rapid increase in $N_2O$ production was reflected by the decrease of HRT, similar to the results observed in the results of ammonia loading changes. So it could be said that it is very important to put in consideration both its optimum conditions for wastewater treatment efficiency and suitable conditions for $N_2O$ diminish, simultaneously, in order to development an eco-friendly and advanced wastewater treatment, especially in BNR process.