• 한국미생물·생명공학회지
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• 제20권5호
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• pp.498-504
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• 1992

고구마효소 갈변반응생성물(SPEBRP)의 항돌연변이 효과를 검토하기 위하여 DNA breaking test, spore rec assay, Ames test를 행하였다. DNA breaking test에서 catechol- 및 hydroxyhydroquinone-SPEB-RPs는 $Fe^{2+}$ 존재하에서 DNA breaking effect를 저해하였다. Bacillus subtilis H17(rec+) 및 M45(rec-)를 이용한 spore rec assay엣 3,4-dihydroxytoluene-SPEBRP는 MNNG에 대하여 강한 돌연변이 효과를 나타내었다. Salmonella typhimurium TA98 및 TA 100를 이용한 Ames test에서 pyrogallol-, 3,4-dihyd-roxytoluene-, hydroxyhydroquinone-SPEBRPs 들은 발암물질인 Benzo($\alpha$)Pyrene에 대하여 67.71, 63%의 강한 활성억제를 나타내었다.

• Environmental Sciences Bulletin of The Korean Environmental Sciences Society
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• 제2권1호
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• pp.57-68
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• 1998

Polycyclic aromatic hydrocarbons (PAMs) are ubiquitous contaminants in marine environments. PAMs enter estuarine and nearshore marine environment via several routes such as combustion of fossil fuels, domestic and industrial effluents and oil spills. PAHs have been the focus of numerous studies in the world because they are potentially carcinogenic, mutagenic, and teratogenic to aquatic organisms and humans from consuming contaminated food. However, one can hardly find any available data on PAM content in marine organisms in Korea. The present study was carried out in order to determine PAM content in oysters from the intertidal and subtidal zones of Chinhae Bay, which is located in near urban communities and an industrial complex, and the bay is considered to be a major repositories of PAHs. 16 PAHs were analyzed by High Performance Liquid Chromatography (HPLC) with uv/vis and fluorescence detectors in oysters: they are naphthalene (NPTHL), acenaphthylene (ANCPL), acenaphthylene (ACNPN), fluorene (FLURN), phenanthrene (PHEN), anthracene (ANTHR), fluoranthene (FLRTH), pyrene (PYR), benzo(a)anthracene (BaA), chrysene (CHRY), benzo(b)fluoranthene (BbF), benzo(k)fluoranthene (BkF), benzo(a)pyrene (BaP), dibenz(a,h)anthracene(DahA), benzo(g,h,i)peryne (BghiP) and indeno(1,2,3,-cd)pyrene (I123cdP). The PAM contents in oysters from the intertidal and subtidal zones of Chinhae Bay ranged from < 0.1 to 992.0 ug/kg (mean $69.8\pm9.8$ ug/kg).

• 한국식품조리과학회지
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• 제10권3호
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• pp.301-307
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• 1994

Benzo(a)pyrene [B(a)P], one of the polycyclic aromatic hydrocarbons(PAHs) is know as a potent careinogen. As consumption of lipid food and fried food increases recently, the toxic effect of overheated lipid foods has report increasingly. This study was undertaken to measure the contents of B(a)P and other PAHs of fried chicken and frying oil. At the same time, the rancidities of frying oil and descarded oil were determined. B(a)P and other PAHs contents of all samples were measured by HPLC/UV method. The results obtained were as follows; B(a)P contents of fresh chicken and soybean oil were 0.073 and 0.146 ${\mu}$g/kg, respectively. During fried chicken at 180${\pm}$5$^{\circ}C$ and 200${\pm}$5$^{\circ}C$, B(a)P and PAHs contens decreased or increased In 20 times fried chicken, PAHs contents except Pyr and DMBA increased at 180${\pm}$5$^{\circ}C$ and PAHs contents except DMBA, DBA, and 3-MC increased at 200${\pm}$5$^{\circ}C$. In frying oils fried chicken, PAHs contents increased in 10 and 15 times frying oil at 180${\pm}$5$^{\circ}C$ and grew more increase and more increase during frying at 200${\pm}$5$^{\circ}C$. The changing pattern of PAHs contents of frying oils was remotely related that of rancidities of frying oils. In fried chicken, frying oils, and discarded oils obtained from fried chicken house at market, PAHs contents of fried chickens were lower than those of fried chicken cooked at laboratory but those of frying oils and discarded oils were higher than those of frying oils cooked at laboratory.

• 한국미생물학회:학술대회논문집
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• 한국미생물학회 2001년도 추계학술대회
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• pp.157-163
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• 2001

Mycolic acid-containing gram-positive bacteria, so called nocardioform actinomycetes, have become a great interest to environmental microbiologists due to their metabolic versatility, multidegradative capacity and potential for bioremediation of priority pollutants. For example, Rhodococcus rhodochrous N75 was able to metabolize 4-methy1catechol via a modified $\beta$-ketoadipate pathway whereby 4-methylmuconolactone methyl isomerase catalyzes the conversion of 4-methylmuconolactone to 3-methylmuconolactone in order to circumvent the accumulation of the 'dead-end' metabolite, 4-methylmuconolactone. R. rhodochrous N75 has also shown the ability to transform a range of alkyl-substituted catechols to the corresponding muconolactones. A novel 3-methylmuconolactone-CoAsynthetase was found to be involved in the degradation of 3-methylmuconolactone, which is not mediated in a manner analogous to the classical $\beta$-ketoadipate pathway but activated by the addition of CoA prior to hydrolysis of lactone ring, suggesting that the degradative pathway for methylaromatic compounds by gram-positive bacteria diverges from that of proteobacteria. Mycobacterium sp. Strain PYR-l isolated from oil-contaminated soil was capable of mineralizing various polyaromatic hydrocarbons (PAHs), such as naphthalene, phenanthrene, pyrene, fluoranthrene, 1-nitropyrene, and 6-nitrochrysene. The pathways for degradation of PAHs by this organism have been elucidated through the isolation and characterization of chemical intermediates. 2-D gel electrophoresis of PAH-induced proteins enabled the cloning of the dioxygenase system containing a dehydrogenase, the dioxygenase small ($\beta$)-subunit, and the dioxygenase large ($\alpha$)-subunit. Phylogenetic analysis showed that the large a subunit did not cluster with most of the known sequences except for three newly described a subunits of dioxygenases from Rhodococcus spp. and Nocardioides spp. 2-D gel analysis also showed that catalase-peroxidase, which was induced with pyrene, plays a role in the PAH metabolism. The survival and performance of these bacteria raised the possibility that they can be excellent candidates for bioremediation purposes.

• 한국지하수토양환경학회지:지하수토양환경
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• 제19권6호
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• pp.59-71
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• 2014

We investigated soil contamination depending on the land use by examining the contamination levels and distribution characteristics of 16 polycyclic aromatic hydrocarbons (PAHs) in the national soil. Total PAHs (the sum of 16 PAH concentrations) and carcinogenic PAHs (the sum of seven carcinogenic PAH concentrations) were $8.50{\sim}3,437.16{\mu}g/kg$ and $2.94{\sim}2,136.96{\mu}g/kg$, respectively. The concentration of benzo(a)pyrene, one of the contaminants regulated by the soil quality standard in the nation, was $ND{\sim}924.73{\mu}g/kg$. Its maximum value of $924.73{\mu}g/kg$ was detected in railroad (Region 3) and is approximately 13% of the standard value for Region 3 (i.e., 7 mg/kg). We also investigated the characteristics of contamination sources of PAHs in soil of the upland, forests, roads, and railroads, examining the fraction distribution of PAHs concentration by the number of benzene rings against the total PAHs concentration. The results demonstrate that the mean fraction of 4~6-ring PAHs against total PAHs concentration in soil was in the range of 51.8~80.7% with relative abundance of high-molecular PAHs, showing that the origin of contamination is under the category of combustion sources. When the molecular indices (Flu/(Flu/Pyr), Ant/(Ant+Phe), InP/(InP+BP), and BaA/(BaA+Chr)) were applied, they were also categorized as petroleum-based combustion sources. The individual PAH concentrations in soil by the land use were grouped into Regions 1, 2, and 3, which are statistically treated and are the parts of the national category system of soil quality standard. As a result, the concentration level of 16 PAHs was $0.02{\sim}2.63{\mu}g/kg$ in Region 1, $0.05{\sim}4.26{\mu}g/kg$ in Region 2, and $2.36{\sim}178.27{\mu}g/kg$ in Region 3. The concentration level of 6 carcinogenic PAHs was 14.2~320.4% against that of benzo(a)pyrene in Region 3 and sites of recycling waste sleepers. Considering that there were similarities among PAHs in terms of structures and toxicities, it would be recommended to review other types of carcinogenic PAHs together with benzo(a)pyrene when developing the soil quality standards in the nation.

• 한국식품조리과학회지
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• 제9권4호
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• pp.323-328
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• 1993

유지를 가열할때 생성되는 B(a)P 및 기타 PAHs함량과 각 유지의 이화학적 성질변화와의 관계를 비교해 봄으로써 각 유지의 적절한 가열 온도와 시간을 알아보기 위하여 시판 대두유를 $180\pm$5^{\circ}C$$,$200\pm$5^{\circ}C$$, $300\pm$5^{\circ}C$$,에서 50시간 가열한 것을 시료로 취하였다. 이들 각 시료의 B(a)P 및 기타 PAHs함량은 HPLC/UV를 사용하여 측정하였고, 산패와 관련된 이화학적 성질변화를 알아보기 위하여 가열유지의 산값(Acid Value, AV)과, 공액이중 산값(Conjugated Diene Value, CDNV)을 측정하였다. 그 결과는 다음과 같았다. 1. 시료로 사용한 대두유의 B(a)P 및 PAHs함량은 Pyr 1.093, B(a)P 0.986, Ch 1.147, DMBA 1.082, B(e)P 0.664, Per 1.135, B(a)P 0.146, DBA 1.053, 3-MC 0.055 $\mu\textrm{g}$/kg 이었다. 대두유를 $180\pm$5^{\circ}C$$, 에서 10,20,30,50시간 가열했을 때 B(a)P함량은 각각 0.391, 0.692, 0.451, 0.372$\mu\textrm{g}$/kg이었으며 $200\pm$5^{\circ}C$$, 와 $300\pm$5^{\circ}C$$,에서 가열했을 때 B(a)P함량은 각각 10시간일때 0.844와 0.466, 20시간일때 0.512와 0.706, 30시간일때 0.479와 0.607, 50시간일때 0.367과 0.247 $\mu\textrm{g}$/kg이었다. 2. 대두유를 10,20,30,50시 간 가열했을 때 산값은 180$\pm$5$^{\circ}C200\pm$5^{\circ}C$$,에서는 0.26, 0.26, 0.27, 0.33이었고, 200$\pm$5$^{\circ}C$에서는 0.23, 0.21, 0.21, 0.52였으며 $300\pm$5^{\circ}C$$,에서는 0.47, 1.57, 3.90, 6.42였다. CDNV는 $180\pm$5^{\circ}C$$,에서는 0.67,0.76,0.99,1.04였으며, $200\pm$5^{\circ}C$$,$^{\circ}C$에서는 0.39, 0.49, 3.27, 3.89였고 $300\pm$5^{\circ}C$$,에서는 0.65, 2.I5, 3.00, 3.88이었다. 3. 대두유를 가열했을 때 B(a)P의 생성과 산패도의 변화와의 관계를 볼때 B(a)P함량은 $180^{\circ}C$에서는 20시간가열시 0.692$\mu\textrm{g}$/kg, $200\pm$5^{\circ}C$$,에서는 10시 간 가열시 0.844$\mu\textrm{g}$/kg, $300\pm$5^{\circ}C$$,에서는 20시간 가열시 0.706$\mu\textrm{g}$/kg으로 가장 높게 생성된 후 서서히 감소하였다. 그러나 산값과 공액이중산값은 계속 증가하는 양상을 나타냈다. 즉 B(a)P생성과 산패도 변화사이에는 일정한 관계를 나타내지는 않았다.

• 한국지하수토양환경학회지:지하수토양환경
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• 제27권2호
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• pp.50-60
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• 2022

The concentration levels and distribution characteristics of 16 polycyclic aromatic hydrocarbons (PAHs) were investigated and evaluated for total 100 soil samples as a part of the survey on soil contamination in Gwangju. The results (median and range) of T-PAHs (sum of 16 PAH concentrations), C-PAHs (sum of carcinogenic PAH concentrations) and T-TEQs (sum of 16 TEQ concentrations) were 20.8 (7.6~1158.1), 2.2 (N.D~509.6), and 0.3 (N.D~424.6) ㎍/kg, respectively. There was a positive correlation between C-PAHs/T-PAHs and T-TEQs/T-PAHs except one point where the concentration of benzo(a)pyrene was high. The ratios of the C-PAHs/T-PAHs were 31.7% for low molecular weight-PAHs and 68.3% for high molecular weight-PAHs, suggesting that PAHs generation mainly arose from combustion sources. The ratio of isomers of individual PAHs, Phe/Ant, Flu/Pyr, Ant/(Ant+Phe), Flu/(Flu+Pyr), and BaA/(BaA+Chr), also confirmed the predominance of PAHs from combustion activities. Statistical tracing of the source of PAHs through principal component analysis indicated that the main sources of combustion were automobile fuel and coal. The overall results of this study suggested HMW-PAHs, T-PAHs, C-PAHs and T-TEQs should be separately evaluated to better assess the toxicity and environmental behavior of individual PAHs.

• 한국대기환경학회지
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• 제24권2호
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• pp.133-142
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• 2008

이 연구에서는 2005년 5월부터 2006년 6월까지 5차례에 걸쳐 서울시 신촌동에 위치한 도로변에서 입자상 PAHs의 농도 분포 특성을 살펴보았다. 도로변에서 입자상 PAHs 농도 분포는 측정시기별로 다른 양상을 보였지만, 2005년 11월을 제외하고는 벤젠고리가 $5{\sim}6$개로 구성된 고분자량 성분들의 농도가 높았다. 입자상 PAHs의 도로변 고유한 특성을 살펴보기 위해 기존 대기와 터널에서 측정한 입자상 PAHs 농도들과 비교하였다. 터널 결과에 비해 상대적으로 도로변에서는 BbF, Ind, BghiP 등의 고분자량 성분들의 비율이 높았는데, 이것은 동력계 시험을 바탕으로 알려진 자동차의 PAHs 배출 특성과 유사하였다. 대기에서는 도로변에 비해 Phen, Pyr, Flt이 높았지만, 도로변에서는 이들 성분들이 고분자량 성분들과 비슷한 비율로 분포하였다. 서울과 고산 대기 중 입자상 PAHs에는 석탄 연소를 포함한 여러 배출원에서 배출된 PAH 성분들이 혼합되어 있는 반면, 도로변에서 측정한 이 연구결과는 자동차 배출에 의한 영향이 지배적이었기 때문인 것으로 여겨졌다. 도로변에서 입자상 PAHs의 주요 배출원을 추정하기 위하여 특정 성분들의 농도비를 분석한 바에 의하면, 일반적으로 도로변에서는 자동차 배출에 의한 영향이 지배적이었고, 자동차 중에서도 경유 자동차 배출의 영향이 컸던 것으로 판단되었다. 2005년 9월과 11월에는 석탄과 바이오매스 연소의 영향이 보였는데, 이는 도로변이 대기와 혼재되어 나타난 결과로 추정된다.