• Journal of environmental and Sanitary engineering
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• v.14 no.1
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• pp.103-115
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• 1999

생물학적 처리공정내 미생물은 물리화학적, 생태학적으로 처리공정의 운전조건과 유입하·폐수 특성에 따라 존재량 및 반응조내 존재하는 우점종이 달라진다. 특히,폐수의 생물학적 처리시 유입수내 존재하는 독성 및 저해물질은 생물반응조내 존재하는 미생물의 양을 감소시키거나 미생물의 종류를 단순화시키거나 환경조건 및 폐수 특성변화에 능동적으로 대처할 수 있는 능력을 감소시킨다. 따라서 이러한 문제점을 극복하기 위한 방안으로 생물능력향상(bio-augmentation)이 필요하며, 여러 가지 방법으로 생물능력향상을 이룰 수 있다. 본 연구에서는 생물능력향상을 위하여 기존의 효소활성이 강한 미생물군을 투입함으로써 처리효율향상에 미치는 영향 및 제한성을 고찰하였다. 처리효율 향상을 위해서는 생존성, 폐수에 대한 순응기간 및 미생물의 체류가 매우 중요하였으며, 특히 누입된 미생물군이 처리효율을 향상시키기 위해서는 일정기간 이상의 순응기간이 필요하였다. 한편, 토착미생물군인 UB-1의 경우 기존 생물능력향상 미생물군과 거의 동일한 처리효율을 나타내고 있으며, 사전에 순양기간을 거친 UB-2의 경우도 기존 생물능력향상 미생물군과 비슷한 처리효율을 보였다. 따라서 본 결과로 볼 때 생물능력향상 미생물군 투입에 의한 처리효율의 향상은 크지 않으며, 하·폐수의 생물학적 처리공정에 적요하는데는 다소 제한성이 있은 것으로 판단되었다.

• Proceedings of the Korean Society of Applied Entomolohy Conference
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• 2006.09a
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• pp.17-26
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• 2006

• Korean Journal of Environmental Biology
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• v.39 no.1
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• pp.88-99
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• 2021

In this study, a land-based marine closed mesocosm (LMCM) experiment was performed to objectively assess the initial stability of an artificial ecosystem experiment against biological and non-biological factors when evaluating ecosystem risk assessment. Changes in the CV (coefficient of value) amplitude were used as data to analyze the stability of the experimental system. The CV of the experimental variables in the LMCM groups (200, 400, 600, and 1,000 L) was maintained within the range of 20-30% for the abiotic variables in this study. However, the difference in CV amplitude in biological factors such as chlorophyll-a, phytoplankton, and zooplankton was high in the 600 L and 1,000 L LMCM groups. This result was interpreted as occurring due to the lack of control over biological variables at the beginning of the experiment. In addition, according to the ANOVA results, significant differences were found in biological contents such as COD (chemical oxygen demand), chlorophyll-a, phosphate, and zooplankton in the CV values between the LMCM groups(p<0.05). In this study, the stabilization of biological variables was necessary to to control and maintain the rate of changes in initial biological variables except for controllable water quality and nutrients. However, given the complexity of the eco-physiological activities of large-scale LMCMs and organisms in the experimental group, it was difficult to do. In conclusion, artificial ecosystem experiments as a scientific tool can distinguish biological and non-biological factors and compare and analyze clear endpoints. Therefore, it is deemed necessary to establish research objectives, select content that can maintain stability, and introduce standardized analysis techniques that can objectively interpret the experimental results.

• Journal of Korea Soil Environment Society
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• v.2 no.3
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• pp.23-30
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• 1997

The purpose of this study was to evaluate effects of solids content and mixing speed in treatment of petroleum hydrocarbon contaminated soils using a slurry-phase bioreactor. Performance results on slurry-phase bioremediation of diesel fuel contaminated soil were generated at the bench-scale level. The fate of TPH(Total Petroleum Hydrocarbon) was evaluated in combination with biological treatment. Abiotic and biotic fate of the TPH were determined using soil not previously exposed to compounds in diesel fuel. The reactor volume for given throughput can be reduced by maximizing the solids content. Applications of 50% and 20% solids content(dry weight basis) were showed a little difference(57.5% : 61.6%) in biological TPH removal rate each other. Mixing and particle suspension are critical to desorption and biological degradation. In this standpoint, this study was performed using two mixing speed. When the reactor was operated at 70rpm, it had a better result in the particle suspension and TPH removal rate than the reactor with mixer rotated at 20rpm. In the reactor applied 20rpm, it was resulted in failure of particle suspension.

• Proceedings of the Korean Society of Soil and Groundwater Environment Conference
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• 2001.04a
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• pp.164-167
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• 2001

현장에서 채취한 토양을 이용하여 Microcosm test를 실시한 결과 온도 및 수분함량이 높을수록 BTEX 분해율이 증가하는 것으로 나타났으며 산소 농도는 21~32% 정도가 적당하였다. 그러나 BTEX 초기농도가 높은 경우에는 생분해율이 감소하는 것으로 나타났다. Bioventing 공법을 현장에 적용한 결과 OUR(Oxygen Utilization Rate)값은 6.3~16.3%O$_2$/day로 조사되었으며 Biodegradation rate 값은 3.4~8.8 mg hydrocarbon/kg soil/day로 조사되어 생물학적 처리 가능성이 있는 것으로 평가되었다.

• Proceedings of the Korean Environmental Sciences Society Conference
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• 2005.05a
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• pp.116-118
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• 2005

강화된 배출수 허용 농도를 만족시키기고 염색폐수의 적정 처리를 위하여 두 가지 생물학적 처리방법을 거친 처리수에 입상활성탄을 적용하여 흡착의 적용성과 흡착의 강도, 경제적인 실용가능성을 알아보기 위해 Batch 실험을 실시한 결과는 다음과 같다. 활성탄을 흡착공정에 적용하기 전에 수행되는 흡착능력을 평가하는 등온흡착실험을 수행한 결과 대상폐수 I ,II과 활성탄의 흡착능력은 Langmuir isotherm을 적용하여 표현하는 것이 가장 적합하다.

• Proceedings of the Korea Society of Environmental Toocicology Conference
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• 1996.12a
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• pp.44-44
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• 1996

• Proceedings of the Korea Society of Environmental Biology Conference
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• 2004.05a
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• pp.64-64
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• 2004

• Proceedings of the Korean Environmental Sciences Society Conference
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• 1999.04a
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• pp.182-184
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• 1999

• Journal of Environmental Impact Assessment
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• v.28 no.2
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• pp.169-182
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• 2019

This study assessed biological water quality using epilithic diatoms in the Yeong river, Naeseong stream and Wi stream in the upper region of the Nakdong river from May to October 2016. Epilithic diatoms were not mobile, so they could reflect long-term water quality. The sampled epilithic diatoms were identified a total 158 taxa which were composed to 2 orders, 3 suborders, 8 families, 34 genera, 143 species and 15 varieties. Dominant species were Achnanthes convergens and Achnanthes minutissima at Yeong river, Nitzschia inconspicua at Naeseong stream, and Achnanthes minutissima, Cocconeis placentula var. lineata and Navicula minima at Wi stream. As a result of the CCA, Electrical conductivity, total nitrogen and total phosphorus were important factors determining the diatom species composition in the upper region of the Nakdong river. The correlation between diatom indices (DAIpo & TDI) measured to be high in the correlation coefficient (0.87) from the result of correlation analysis. In the result of the assessment of biological water quality using DAIpo and TDI, Yeong river was rated as class A at most sites. Naeseong stream was rated as class C to D at all sites except for N1 which was rated as Class A. Wi stream was rated as class B to C for DAIpo of W1, and TDI was rated as class D. The assessment of biological water quality at this site showed inferior TDI result compared to that of DAIpo. DAIpo and TDI of W2 were rated as class A to D, and the water quality has changed a lot. W3 and W4 were mostly rated as class B and C respectively.