• 한국신재생에너지학회:학술대회논문집
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• 한국신재생에너지학회 2005년도 제17회 워크샵 및 추계학술대회
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• pp.299-306
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• 2005

Anaerobic fermentation of food waste (FW) and waste activated sludge (WAS) for hydrogen production was performed in CSTR (Continuous Stirred tank reactor) under various HRTs and volumetric mixing ratio (V/V) of two substrates, FW and WAS. The specific hydrogen production potential of FW was higher than that of WAS. However, pH drop in the CSTR for hydrogen production from FW was higher than that from WAS. The maintenance of desired pH during fermentative hydrogen production is regarded as the most important operation parameter for the stable hydrogen production. Therefore, when the potential of hydrogen production from FW and better buffer capacity of WAS, the proper mixture of FW and WAS for fermentative hydrogen production were considered as a useful complementary substrate. The maximum yield of specific hydrogen production, 140 mL/g VSS, was found at HRT of 2 day and the volumetric mixing ratio of 20:80 (WAS : FW). The spatial distribution of hydrogen producing bacteria was observed in anaerobic fermentative reactor using fluorescent in situ hybridization (FISH) method.

• KSBB Journal
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• 제20권6호
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• pp.393-400
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• 2005

수소를 생산하는 미생물은 크게 광합성 세균(photosynthetic bacteria), 혐기성세균(non-photosynthetic anaerobic bacteria), 조류(algae) 등으로 구분되고, 이들의 수소 생성 기작, 사용가능기질 및 수소 발생량은 상당한 차이가 있다. 광합성세균은 Rhodospirillaceae, Chromatiaceae 및 Chlorobiaceae로 구분되며, 이는 각각 홍색비유황세균(purple non-sulfur bacteria), 홍색유황세균(purple sulfur bacteria), 녹색유황세균(green sulfur bacteria)으로 통칭된다. 혐기성 세균은 절대 또는 통성혐기세균중 일부가 수소생산에 관여하며, 조류는 녹조류(green algae)와 남조류(blue-green algae, cyanobacteria)가 알려져 있다. 생물학적 수소생산 기술은 (1) 녹조류(green algae)가 광합성 메카니즘에 의해 수소를 생산하는 직접 물 분해 수소생산(direct bio-photolysis) (2) 광합성 작용에 의해 물을 분해하여 산소를 발생하고, 동시에 공기 중 이산화탄소를 고정하여 고분자 저장물질로 균체 내에 저장한 후 혐기 발효 또는 광합성 발효에 의해 수소를 발생하는 간접 물 분해 수소생산(indirect bio-photolysis or two stage photolysis) (3) 빛이 존재하는 혐기상태 배양 조건에서 홍색 세균에 의한 광합성 발효(photo-fermentation) 또는 (4) 광이 존재하지 않는 조건에서 혐기 미생물에 의해 수소와 유기산을 내는 혐기 발효(dark anaerobic fermentation) (5) 균체 외(in virro) 수소 발생 (6) 일산화탄소 가스 전환 반응(microbial gas shift reaction)에 의한 수소 생산 기술로 구분할 수 있다. 물로부터 생물학적 기술에 의한 수소생산은 공기 중의 이산화탄소를 고정하고, 수소와 산소를 발생하는 원천기술로써 오래 전부터 미국, 유럽에서 태양에너지를 이용하는 광합성 미생물의 분리, 개선 및 반응기에 관한 연구가 축적되어 왔으며, 유기물 즉 바이오매스로부터 혐기 및 광합성 발효를 연속적으로 적용하는 기술은 비교적 최근에 일본을 비롯한 유기성 폐기물이 많은 국가에서 수소에너지 생산과 유기성 폐기물 처리라는 두 가지 목적에 부합하는 연구로써 활발히 진행되고 있다. 유기성 폐기물이나 폐수와 같은 수분함량이 높은 바이오매스는 대부분이 매립처리 되는 실정이지만 높은 수분 함량 때문에 매립 시 발생하는 침출수는 환경오염의 주범으로 가까운 장래에는 매립도 금지될 전망이다. 이와 같은 수소에너지 생산기술과 이용시스템 개발은 화석연료 사용을 최소화 할 수 있으며, 국내에서 다량 발생하는 유기성 폐기물을 이용한 에너지 생산으로 자원 강대국 입지에 설 수 있다. 미생물에 의한 수소생산 기술은 청정에너지 생산과 아울러, 동시에 산소 발생, 공기 중 이산화탄소 고정, 식품공장 폐수 및 음식쓰레기와 같은 유기성 폐기물 처리 등 환경에 이로운 방향으로 진행될 뿐만 아니라, 미생물 자체가 갖는 생물 산업성도 높아서 비타민류, 천연색소, 피부암 치료제등의 고부가가치 의약품 생산도 활성화할 수 있다.

• 한국미생물·생명공학회지
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• 제49권1호
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• pp.57-64
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• 2021

Lactic acid bacteria (LAB), belonging to the Firmicutes phylum, lack heme biosynthesis and, thus, are characterized as fermentative and catalase-negative organisms. To verify the hypothesis that heme-rich-nutrients might compensate the heme-biosynthesis incapability of non-respiratory LAB in animal gut, a heme-rich-nutrient was fed to a dog and its fecal microbiome was analyzed. Firmicutes abundance in the feces from the heme-rich-nutrient-fed dog was 99%, compared to 92% in the control dog. To clarify the reason of increased Firmicutes abundance in the feces from the heme-rich-nutrient-fed dog, Lacobacillus gasseri were used as model anerobic LAB to study a purified heme (hemin). The anaerobic growth of L. gasseri in the medium with 25 µM hemin supplementation was faster than that in the medium without hemin, while the growth in the 50 µM hemin-supplemented medium did not vary. Cellular activities of the cytochrome bd complex were 1.55 ± 0.19, 2.11 ± 0.14, and 2.20 ± 0.08 U/gcell in the cells from 0, 25, and 50 µM hemin-supplemented medium, while intracellular ATP concentrations were 7.90 ± 1.12, 11.95 ± 0.68, and 12.56 ± 0.58 µmol_ATP/g_cell, respectively. The ROS-scavenging activities of the L. gasseri cytosol from 25 µM and 50 µM hemin-supplemented medium were 68% and 82% greater than those of the cytosol from no hemin supplemented-medium, respectively. These findings indicate that external hemin could compensate the heme-biosynthesis incapability of L. gasseri by increasing the cytosolic ROS-scavenging and extra ATP generation, possibly through increasing the electron transfer. Increase in the number of anaerobic bacteria in heme-rich-nutrient-fed animal gut is discussed based on the results.

• 한국축산시설환경학회지
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• 제11권2호
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• pp.97-102
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• 2005

Anaerobic decomposition is one of the most common processes in nature and has been extensively used in waste and wastewater treatment for several centuries. New applications and system modifications continue to be adapted making the process either more effective, less expensive, or suited to the particular waste in question and the operation to which it is to be applied. Animal manure is a highly biodegradable organic material and will naturally undergo anaerobic fermentation, resulting in release of noxious odors, such as in manure storage pits. Depending on the presence or absence of oxygen in the manure, biological treatment process may be either aerobic or anaerobic. Under anaerobic conditions, bacteria carry on fermentative metabolisms to break down the complex organic substances into simpler organic acids and then convert them to ultimately formed methane and carbon dioxide. Anaerobic biological systems for animal manure treatment include anaerobic lagoons and anaerobic digesters. Methane and carbon dioxide are the principal end products of controlled anaerobic digestion. These two gases are collectively called biogas. The biogas contains $60\~70\%$ methane and can be used directly as a fuel for heating or electrical power generation. Trace amounts of ammonia and hydrogen sulfide ($100\~300\;ppm$) are always present in the biogas stream. Anaerobic lagoons have found widespread application in the treatment of animal manure because of their low initial costs, ease of operation and convenience of loading by gravity flow from the animal buildings. The main disadvantage is the release of odors from the open surfaces of the lagoons, especially during the spring warm-up or if the lagoons are overloaded. However, if the lagoons are covered and gases are collected, the odor problems can be solved and the methane collected can be used as a fuel. Anaerobic digesters are air-tight, enclosed vessels and are used to digest manure in a well-controlled environment, thus resulting in higher digestion rates and smaller space requirements than anaerobic lagoons. Anaerobic digesters are usually heated and mixed to maximize treatment efficiency and biogas production. The objective of this work was to review a current anaerobic biological treatment of animal manure for effective new technologies in the future.

• 한국미생물·생명공학회지
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• 제22권4호
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• pp.407-414
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• 1994

Anaerobic fermentative bacteria were isolated from the acidogenic reactor of a labora- tory scale 2-stage anaerobic digestor. The isolate 1-6 was selected for its ablity to produce more fatty acids from distillery wastewater than others, and was identified as a strain of Clostridium. The isolate Clostridium sp. 1-6 is a thermophilic bacterium growing at 55$\circ$c , and grew best at pH 5.5. An acidogenic reactor using immobilized cells of the isolate Clostridium sp. 1-6 removed about 15% of COD from distillery wastwater as hydrogen, producing about 50 mM butyrate and about 10 mM acetate, when the reactor was operated at the hydraulic retention time(HRT) of 0.8 hr. It is proposed that this system can be used to convert the distillery wastewater to hydrogen and butyrate. More than 90% of COD was removed from the wastewater by anaerobic digestion using a 2-stage digestor consisting of a UASB methanogenic reactor and an acidogenic reactor of the immobilized cells of isolate Clostridium sp. 1-6.

• 한국수소및신에너지학회논문집
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• 제19권1호
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• pp.41-48
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• 2008

Fermentative $H_2$ production was studied using microbial consortia isolated from heat-treated ($90{\circ}C$, 20 min) sewage sludge. Important parameters investigated were carbon(C) and nitrogen(N)-sources, C/N ratio, phosphate concentration, pH and temperature during anaerobic cultivation in serum bottles. Starch, ribose, sucrose and glucose were good C-sources for the culture growth and $H_2$ production. Yeast extract was better N-source than $(NH_4)_2SO_4$ or peptone when individually added to the synthetic media, however the combination of above three N-sources exhibited the additional effect for cell growth and $H_2$ evolution. Addition of 100 mM phosphate as a buffering agent prevented the rapid pH drop during the cultivation. The optimum initial pH for the cell growth was at 7.0, whereas $H_2$ production was observed at pH 5.5. Optimum temperature for the cell growth and $H_2$ production was $37{\circ}C$. Initial C/N ratio of 1.22 in the media using glucose and yeast extract as the C- and N-sources, respectively, showed the $H_2$ yield 1.0 mol $H_2$/mol glucose.

• 대한환경공학회지
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• 제27권9호
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• pp.958-964
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• 2005

혐기성균에 의해 각종 탄수화물로부터 생성되는 수소가스의 량을 측정하였으며, 이 때 생성되는 유기산의 생성 특성을 파악하고자 하였다. 또한 이를 기초로 카드뮴과 구리와 같은 중금속이 배양액에 존재할 경우 혐기성균에 의한 수소생산량과 발효산물의 변화양상을 파악하고자 하였다. sucrose가 탄소원으로 사용되었을 때 3.43 mol H2/mol hexose의 최적 수소 생산량을 보였으며, 발효산물인 유기산은 acetic acid와 butyric acid가 주로 생성되었다. 카드뮴과 구리가 배양액에 존재함에 따라 수소생산량이 낮아지는 경향을 보인 반면, 유기산 중에서 acetic acid의 생성이 높아지는 경향을 나타내었으며 수소생산에 미치는 영향은 구리가 더 큰 것으로 나타났다.

• Korean Chemical Engineering Research
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• 제44권1호
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• pp.16-22
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• 2006

생물학적 수소생산 공정은 다른 열화학적 공정이나 전기화학적 공정에 비하여 환경친화적이며 에너지를 덜 소모하는 공정이다. 생물학적 수소생산 공정은 크게 두 가지로 구별할 수 있는데, 광합성에 의한 수소생산과 혐기발효에 의한 수소생산이 그것이다. 광합성에 의한 수소생산 공정은 주로 물로부터 수소를 생산하고 동시에 공기 중의 이산화탄소도 저감하는 특징을 가지고 있으며, 혐기발효에 의한 수소생산 공정은 유기 탄소원을 섭취하는 박테리아에 의한 발효를 통해 이루어지는 공정이다. 본 논문에서는 생물학적 수소생산 공정에 대한 그간의 연구들에 대하여 살펴 보았다.

• 대한환경공학회지
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• 제31권6호
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• pp.434-441
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• 2009

황산염의 농도변화에 따른 연속 혐기성 수소 발효에 미치는 영향을 고찰하기 위해서 혼합균주를 사용한 완전 혼합형 반응조를 운전하였다. 기질은 글루코오스를 사용하였고, 수리학적 체류시간은 1, 0.5, 0.25 일로 각각 고정하였다. 황산염 농도는 0${\sim}$20,000 mg/L로 단계별 증가시켰고 pH 5.5로 운전하였다. 실험 결과 높은 황산염 농도에 관계없이 수소가 발생하였고, HRT 0.25일로 짧아짐에 따라 수소 발생이 높게 나타났다. HRT 1, 0.5, 0.25일 각 조건별 수소 생성량과 수소 수율은 2.9, 4.6, 9.4 L/day, 2.0, 1.8, 1.6 mol $H_2$/mol glucose로 나타났으며, 잔존 황산염 96${\sim}$98, 95${\sim}$97 94${\sim}$97%로 나타나 황산염 환원이 발생하지 않았다. FISH 결과 모든 조건에서 수소생성균의 분포는 나타났지만 황산염환원균의 분포는 나타나지 않았다.

• 농업과학연구
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• 제43권3호
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• pp.387-393
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• 2016

This study was conducted to determine the fermentative characteristics of wheat bran inoculated with a starter culture of direct-fed microbes as a microbial wheat bran (DMWB) feed additive. Wheat bran was prepared with 1% (w/w, 0.5% Lactobacillus plantarum and 0.5% of Saccharomyces cerevisiae) starter culture treatment (TW) or without starter culture as a control (CW). Those were fermented under anaerobic conditions at $30^{\circ}C$ incubation for 3 days. Samples were taken at 0, 1, 2, and 3 days to analyze chemical composition, microbial growth, pH, and organic acid content. Chemical composition was not significantly different between CW and TW (p > 0.05). In TW, the number of lactic acid bacteria and yeast increased during the 3 days of fermentation (p < 0.05) and the population of lactic acid bacteria was significantly higher than in CW (p < 0.05). After 3 days, the number of yeast in TW was $7.50{\pm}0.07log\;CFU/g$, however, no yeast was detected in CW (p < 0.05). The pH values of both wheat bran samples decreased during the 3 days of fermentation (p < 0.05), and TW showed significantly lower pH than CW after 3 days of fermentation (p < 0.05). Contents of lactic acid and acetic acid increased significantly at 3rd day of fermentation in TW. However, no organic acids were generated in CW during testing period. These results suggest that 3 days of fermentation at $37^{\circ}C$ incubation after the inoculation wheat bran with starter culture makes it possible to produce a direct-feed with a high population of lactic acid bacteria at more than $10^{11}CFU/g$.