• 생태와환경
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• 제49권2호
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• pp.67-79
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• 2016

Cyanotoxins in aquatic ecosystems have been investigated by many researchers worldwide. Cyanotoxins can be classified according to toxicity as neurotoxins (anatoxin-a, anatoxin-a(s), saxitoxins) or hepatotoxins (microcystins, nodularin, cylindrospermopsin). Microcystins are generally present within cyanobacterial cells and are released by damage to the cell membrane. Cyanotoxins have been reported to cause adverse effects and to accumulate in aquatic organisms in lakes, rivers and oceans. Possible pathways of microcystins in Lake Suwa, Japan, have been investigated from five perspectives: production, adsorption, physiochemical decomposition, bioaccumulation and biodegradation. In this study, temporal variability in microcystins in Lake Suwa were investigated over 25 years (1991~2015). In nature, microcystins are removed by biodegradation of microorganisms and/or feeding of predators. However, during water treatment, the use of copper sulfate to remove algal cells causes extraction of a mess of microcystins. Cyanotoxins are removed by physical, chemical and biological methods, and the reduction of nutrients inflow is a basic method to prevent cyanobacterial bloom formation. However, this method is not effective for eutrophic lakes because nutrients are already present. The presence of a cyanotoxins can be a potential threat and therefore must be considered during water treatment. A complete understanding of the mechanism of cyanotoxins degradation in the ecosystem requires more intensive study, including a quantitative enumeration of cyanotoxin degrading microbes. This should be done in conjunction with an investigation of the microbial ecological mechanism of cyanobacteria degradation.

• 한국환경과학회지
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• 제32권5호
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• pp.315-328
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• 2023

Cyanobacteria have been used as pollution indicator species in freshwater ecosystems, and identifying their fluctuations can be an important part about management of surface waters globally. Cyanotoxins produced by cyanobacteria are directly or indirectly a threat to human and environmental health. In order to confirm the potential risk of these cyanotoxins, the fluctuations of phytoplankton and phylogenetic analysis of cyanotoxin synthetase genes were conducted at each point in the Yeongsan River water system in Gwangju from November 2021 to October 2022. Diatoms which grow well in winter were dominant at 99.4 ~ 99.5%, and diatoms and green algae were dominant from the spring to autumn when the water temperature rises. Stephanodiscus spp. were dominant at 92.7 to 97.5 % at all sites in the winter, and Aulacoseira spp., which grow in warm water temperatures, were dominant in summer and autumn. Microcystis aeruginosa was dominant at 25.2% in summer only at site 5. mcyB and anaC have been detected as cyanotoxin synthetase genes. The phylogenetic tree of anaC could be divided into two groups (Group 1 & Group 2). Group 1 contained Aphanizomenon sp. and Cuspidothrix issatschenkoi. It is combined with Aphanizomenon sp. and Cuspidothrix issatschenkoi, which are known to produce cyanotoxins.

• 한국물환경학회지
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• 제25권4호
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• pp.597-605
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• 2009

Algae bloom occurred in reservoir in summer can cause taste and odor in water and disturb the flocculation and sedimentation processes in water treatment plant and cause sand filter plugging. It was also reported that microcystins, anatoxin and saxitoxin released from cyanobacteria had acute toxic effects on liver and nervous system. For these reasons, many advanced countries inclusive of WHO set the guideline for these toxins and cyanotoxins have been managed with regular monitoring in Korea as well. However, complex sample preparation steps such as a solid phase extraction (SPE) and derivatization are required with an existing analysis method with HPLC. We needed to improve an analysis method for low extraction efficiency and long sample preparation time. In this study, we have established a new LC/MS/MS method which can simultaneously determine 6 cyanotoxins (Microcystins-LR, Microcystins-RR, Microcystins-YR, Anatoxin-a, Saxitoxin, Neosaxitoxin) with only simple filtration step. When $75{\mu}L$ filterated sample was injected onto the LC-MS/MS, the recovery ranged from 86% to 112% and the MDL was $0.025{\sim}0.581{\mu}g/L$. We can make the MDL be lower than the guideline ($1{\sim}3{\mu}g/L$) of advanced countries with simple preparation.

• 대한환경공학회지
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• 제35권12호
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• pp.943-952
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• 2013

최근 국내의 호소들에 부영양화가 진행됨에 따라 남조류가 대량 번식하는 현상이 나타나고 있다. 남조류에 의한 녹조현상은 미관상 불쾌감을 유발하고 이취미 유발과 함께 정수장애도 일으킨다. 그리고 일부 남조류가 생산하는 남조류 독소에 의한 야생동물 및 가축에 대한 피해가 계속적으로 보고됨에 따라 우리나라에서도 조류주의보 발생 시 조류독성에 대한 모니터링을 강화하게 되었다. 이번 연구에서는 울산시가 상수원으로 사용하고 있는 회야호에서의 남조류 발생 특성을 조사하고, 물리, 화학적 환경요인과의 관계를 알아보았다. 그리고 남조류 발생 시 생성되는 남조류 독소(Cyanotoxins) 중 Microcystin 4종과 Anatoxin-a 등 5종을 LC-MS/MS를 이용해 분석하여 그 거동을 알아보았다. 조사 기간 동안 회야호에서는 남조류 중에서 Microcystis가 우점하였고, 남조류 개체수는 수온, pH와 양의 상관관계를 나타내었다. 이 시기 동안 Microcystin-LR의 최대 농도는 $0.424{\mu}g/L$, Microcystin-RR의 최대 농도는 $0.117{\mu}g/L$ 이었다. Cyanotoxins의 농도는 수온, pH와 강한 양의 상관관계를, 총인 농도와 양의 상관관계를 나타내었다. 그리고 정수장으로 유입되는 원수에서의 총 Cyanotoxins의 농도는 $0.182{\mu}g/L$이었고, 정수에서는 검출되지 않았다.

• 생태와환경
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• 제44권1호
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• pp.22-30
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• 2011

This study was purposed to develop an effective LC/MS/MS method for simultaneously determining five pre-treated cyanotoxins (anatoxin-a, microcystins-RR, -YR, -LR and -LA) of cyanobacteria blooms. Cyanobacterial bloom samples were collected from 11 major lakes and three downstream areas of river around Korea during 2005~2009. Cyanotoxins were identified in 38 samples from the lakes. The validity of the method was evaluated and the recovery rates were found ranging from 83~87%. The MDL turned out to be $0.046\;{\mu}g\;L^{-1}$ for anatoxin-a and $0.066\;{\mu}g\;L^{-1}$ for microcystins (RR, YR, LR and LA), which indicates that the method has high sensitivity and accuracy. The most dominant genus of the cyanobacterial blooms was Microcystis, which accounted for 71% of the analysed samples. Microcystis also contained the largest amount of microcystins ($398.5\;{\mu}g\;gDW^{-1}$) among the analyzed cyanobacteria. The analysis of the five cyanotoxins showed that anatoxin-a ranged between $0{\sim}41.833\;{\mu}g\;gDW^{-1}$ and microcystins ranged between $6.311{\sim}2,148.786\;{\mu}g\;gDW^{-1}$. Among the microcystins, micocystin-RR took up 58.3%, the largest portion. Anatoxin-a was found to account for 77.8% of the samples. This study has its significance in that it allowed the establishment of toxin criteria appropriate for the Korean water systems. Further studies may be necessary to conduct for improving water treatment methods.

• 대한환경공학회지
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• 제37권12호
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• pp.657-667
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• 2015

녹조현상을 형성하는 유독남조류는 세계 각지의 부영양화 호수에서 장기간 관찰되고 있다. 남조에 의해 생산되는 독소는 크게 신경독(anatoxin-a, anatoxin-a(s), saxitoxin)과 간독(microcystin, nodularin, cylindrospermopsin)으로 나뉜다. Microcystin은 남조세포내에 존재하며, 세포막이 손상되면 외부로 방출된다고 사료되며, 용출된 microcystin은 생물에 악영향을 끼치며, 호수, 하천 및 해양의 수생생물에 microcystin이 축적된다고 알려져 있다. 자연계에서는 포식자에 의한 남조세포의 섭식 또는 남조세포로부터 용출된 microcystin의 미생물에 의한 분해에 의해 microcystin의 제거가 가능하지만, 정수처리 과정에서는 microcystin을 분해하는 미생물이 존재하지 않으므로, 세포제거를 위해 황산구리를 사용할 경우 대량의 microcystin이 용출되므로 주의가 필요하다. 지금까지의 보고에 의하면 세포 밖으로 용출된 micorcystin을 제거하는 기술은 물리, 화학 및 생물학적 방법이 있다. 녹조현상의 방지는 그 발생의 원인인 호수 외로부터 유입되는 영양염류인 질소와 인의 감소가 기본이지만, 부영양호의 경우 이미 유입된 영양염류를 축적하고 있으므로 투자에 비해 효과는 높지 않다. 호수가 본래의 상태일 때 부영양화 된다면, 호수의 연안부에 수생식물의 침입이 일어나고, 식물플랑크톤에 의한 조류 번무 현상은 보이지 않는 것이 보통이다. 이러한 관점으로 녹조현상 발생방지를 위해서는 일단 호수 연안을 정상적인 상태로 복원할 필요가 있다.

• 환경생물
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• 제41권4호
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• pp.370-385
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• 2023

수자원의 부영양화와 인위적인 수변환경 조성 및 기후 변화의 영향으로 인한 유해 남세균의 대발생의 빈도와 강도가 증가하고 있다. 유해 남세균은 시아노톡신 (Cyanotoxins)을 배출하여 수자원의 안전뿐 아니라 생태계에 악영향을 주기 때문에 국제적인 환경문제로 관심을 받고 있다. 특히, 독성이 강한 마이크로시스틴(microcystins, MCs)의 제거를 위한 연구가 가장 활발히 연구되어 왔으며 이를 위한 다양한 수처리 방법이 제안되고 있다. 본 논문에서는 기존에 보고된 마이크로시스틴 제거를 위한 기술 중 경제적, 효율적인 방안으로 평가받고 있는 흡착기술(adsorption)에 대하여 주안점을 두고 조사하였다. 활성탄(activated carbons)은 마이크로시스틴 제거를 위한 흡착소재로 가장 광범위하게 활용되고 있으며 우수한 마이크로시스틴 흡착성능이 보고되고 있다. 바이오차(biochar), 생체흡착소재(biosorbents)와 같은 활성탄을 대체하는 흡착소재의 활용 연구도 진행되고 있으나 활성탄에 비하여 그 효과가 미흡한 실정이다. 이러한 마이크로시스틴 흡착에는 흡착소재의 특성(기공 특성과 표면화학적 특성)과 환경인자(용액의 pH, 온도, 자연 유기물 및 이온성 물질)가 영향을 미치는 것으로 보고되고 있으며 이에 대한 고찰을 진행하였다. 또한, 보다 효과적인 제어를 위하여 용존 마이크로시스틴의 제거뿐 아니라 유해 남세균의 직접적인 제거를 위한 흡착기술의 활용 가능성도 확인하였다. 하지만, 마이크로시스틴의 제거를 위한 실질적인 흡착소재의 활용을 위해서는 실제 환경조건에서 적용과 환경적, 경제적인 관점에서의 최적화 연구가 필요하다고 판단된다. 본 논문은 체계적인 자료 조사 및 분석을 통하여 향후 마이크로시스틴의 제거를 위한 효과적인 흡착소재 및 적용방법의 개발 및 선별에 관한 통찰을 제시할 수 있을 것이다.

• Journal of Microbiology and Biotechnology
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• 제13권1호
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• pp.50-56
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• 2003

A freshwater bloom-forming cyanobacterium, Microcystis aeruginosa, and local soil isolate Scytonema sp. strain BT 23 were demonstrated to contain biotoxic secondary metabolites with pesticidal and mosquito larvicidal activities. A purified toxic constituent from M aeruginosa showed an absorption maximum at 230 nm and its toxicity symptoms, Rf value on TLC, and retention time observed ill an HPLC analysis were similar to those of the hepatotoxic heptapeptide microcystin-LR. The bioactive constituent of the Scytonema sp. was less polar in nature and exhibited two peaks at 240 and 285 m. When applied to two cruciffrous pests, Pieris brassicae and Plutella flostella, the crude extracts and toxic principles from the two cyanobacteria showed significant antifeedant activity in a no-choice bioassay, and at higher concenuations exhibited contact toxicity to the insect larvae. The purified toxin from M. aeruginosa was found to be more effective and produced 97.5 and $92.8\%$ larval mortality in the two pests, fo11owing 2 h of toxin treatment at a concentration of $25{\mu}g$ Per leaf disc (2.5 cm dia.). Meanwhile, similar treatment with the purified toxin from Sytonema sp. stain BT 23 only produced 73 and $78\%$ mortality in the two pests. The cyanobacterial constituents also showed significant activity against Culex and Anopheles larvae. The M. aeruginosa toxin ($20{\mu}g\;ml^-1$) caused 98.2 and $88.1\%$ mortality in the Culex and Anopheles larvae, respectively, while the purified toxin from the Sytonema sp. was less toxic and only produced a 96.3 and $91.2\%$ mortality, respectively, at a much higher concentration ($40{\mu}g\;ml^-1$). Accordingly, the current results point to certain hitherto unknown biological properties of cyanobacterial biotoxins.

• Membrane and Water Treatment
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• 제6권3호
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• pp.225-235
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• 2015

During low-pressure membrane treatments of cyanobacterial cells, including microfiltration (MF) and ultrafiltration (UF), there have reportedly been releases of intracellular compounds including cyanotoxins and compounds with an earthy-musty odor into the water, probably owing to cyanobacterial cell breakage retained on the membrane. However, to our knowledge, no information was reported regarding the effect of growth phase of cyanobacterial cells on the release of the intracellular compounds. In the present study, we used a geosmin-producing cyanobacterium, Anabaena smithii, to investigate the effect of the growth phase of the cyanobacterium on the release of intracellular geosmin during laboratory-scale MF experiments with the cells in either the logarithmic growth or stationary phase. Separate detection of damaged and intact cells revealed that the extent of cell breakage on the MF membrane was almost the same for logarithmic growth and stationary phase cells. However, whereas the geosmin concentration in the MF permeate increased after 3 h of filtration with cells in the logarithmic growth phase, it did not increase during filtration with cells in the stationary phase: the trend in the geosmin concentration in the MF permeate with time was much different between the logarithmic growth and stationary phases. Adsorption of geosmin to algogenic organic matter (AOM) retained on the MF membrane and/or pore blocking with the AOM were greater when the cells were in the stationary phase versus the logarithmic growth phase, the result being a decrease in the apparent release of intracellular geosmin from the stationary phase cells. In actual drinking water treatment plants employing membrane processes, more attention should be paid to the cyanobacterial cells in logarithmic growth phase than in stationary phase from a viewpoint of preventing the leakage of intracellular earthy-musty odor compounds to finished water.

• BMB Reports
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• 제39권4호
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• pp.346-354
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• 2006

The full-length cDNA of grass carp (Ctenopharyngodon idellus) and silver carp (Hypophthalmichthys molitrix) uncoupling protein 2 (UCP2) was obtained from liver. The grass carp UCP2 cDNA was determined to be 1152 bp in length with an open reading frame that encodes 310 amino acids. Five introns (Intron 3, 4, 5, 6 and 7) in the translated region, and partial sequence of Intron 2 in the untranslated region of grass carp UCP2 gene were also obtained. Gene structure comparison between grass carp and mammalian (human and mouse) UCP2 gene shows that, the UCP2 gene structure of grass carp is much similar to that of human and mouse. Partial UCP2 cDNA sequences of bighead carp (Aristichthys nobilis) and mud carp (Cirrhinus molitorella), were further determined. Together with the common carp (Cyprinus carpio) UCP2 sequence from GenBank (AJ243486), multiple alignment result shows that the nucleotide and amino acid sequences of the UCP2 gene, were highly conserved among the five major Chinese carps that belong to four subfamilies. Using beta-actin as control, the ratio UCP2/beta-actin mRNA (%) was determined to be $149.4{\pm}15.6$ (common carp), $127.4{\pm}22.1$ (mud carp), $96.7{\pm}12.7$ (silver carp), $94.1{\pm}26.8$ (bighead carp) and $63.7{\pm}16.2$ (grass carp). The relative liver UCP2 expression of the five major Chinese carps, shows a close relationship with their food habit: benthos and detrituseating fish (common carp and mud carp) > planktivorious fish (silver carp and bighead carp) > herbivorious fish (grass carp). We suggest that liver UCP2 might be important for Chinese carps to detoxify cyanotoxins and bacteria in debris and plankton food.