• 한국환경보건학회지
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• 제27권2호
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• pp.37-42
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• 2001

Zebrafish(Brachdanio rerio)를 실험어류로 하여 methidathion 과 phosalone의 생물농축계수(bioconcentration factor : BCF)와 배설속도상수 (depuration rate constant) 및 LC$_{50}$를 측정하였다. Methidathion의 24, 48, 72, 96시간 LC$_{50}$는 각각 28.34, 35.98, 24.43, 22.03 mg/$\ell$로 측정되었다. Methidathion 0.22 mg/$\ell$(고농도)와 0.022 mg/$\ell$(저농도)에서 어류 체내에서의 농축정도는 두 농도군에서 각각 12시간 이후에 정류상태에 도달하여 72시간동안 거의 일정하였고, BCF값도 12시간에서 72시간 사이에 고농도와 저농도에서 8.72(n=4)와 11.25(n=4)로 조사되었다. 배설속도상수는 고농도와 저농도에서 6시간 이내에 모두 배설되어 배설속도상수를 구할 수 없었다. Phosalone의 24, 48, 72, 96시간 LC$_{50}$는 각각 3.76, 2.43, 1.86, 1.05 mg/$\ell$로 측정되었다. Zebrafish 체내에서의 농축정도와 BCF값은 고농도(0.01 mg/$\ell$)에서 12시간 이후에 정류상태에 도달하여 72시간동안 거의 일정하였고, BCF값은 12시간에서 72시간 사이에 48.88(n=4)로 측정되었다. 저농도(0.001 mg/$\ell$)에서는 실험 전기간동안 zebrafish 체내에서 phosalone이 검출되지 않아 BCF값을 산출할 수 없었다. Zebrafish 체내에서 phosalone(고농도)의 배설속도상수와 반감기를 구하기 위하여 6,12시간의 배설실험 결과 각각 0.17$hr^{-1}$과 4.01 시간이었다. Methidathion과 phosalone의 BCF값은 phosalone이 methidathion 보다 약 5배 정도 높게 나타났으며, 농약의 배설속도는 phosalone이 methidathion보다 빨랐다.

• Environmental Analysis Health and Toxicology
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• 제25권3호
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• pp.229-240
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• 2010

During the last decade, perfluorinated compounds (PFCs) have gained more attention due to their toxicity and global distribution. The aim of this study was to examine the distribution and bioaccumulation of perfluorinated compounds (PFCs) in aquatic wildlife effected from a sewage treatment plant. The concentrations of 12 PFCs were determined in water, sediment and fish samples. PFOS were predominantly detected in both ambient environment and fish. In fish, the concentration of PFCs in blood was the highest (i.e., 112.47 ng/mL wet-wt. PFOS) in comparison to other tissues. However, PFOA and PFHpS were highly detected in gonad as 3.87 and 4.58 ng/g wet-wt., respectively. The bioconcentration factor (BCF) of PFCs was greatest in the blood > liver${\cong}$gonad > kidney > gill, and lowest in the muscle tissue. The BCFs of PFUnDA (39,000), PFDA (2,700) and PFOS (1,100) were rated as high values based on wet weight concentration. BCFs increased with increasing the length of the perfluoralkyl chain.

• 한국환경보건학회지
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• 제21권3호
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• pp.38-47
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• 1995

The Bioconcentration factor (BCF) is used as an important criterion in the risk assessment of environmental contaminants. Also it can be used as indicator of biomagnification of environmentally hazardous chemicals through food-chain as well as a tool for ranking the bioconcentration potential of the chemicals in the environment. This paper reports the measured BCF value on Chlorothalonil in Carassius auratus(goldfish), under steady state, and examined correlation between the BCF value and the partition coefficient or acute toxicity or physicochemical properties. Carassius auratus(goldfish) was chosen as test organism and test period were 3-day, 5-day. Experimental concentrations were 0.005, 0.01 and 0.05 ppm. Chlorothalonil in fish tissue and in test water were extracted with n-hexane and acetonitrile. GC-ECD was used to detecting and quantitating of Chlorothalonil. Partition coefficient was determined by stir-flask method. $LC_{50}$ was determined on Chlorothalonil. Carbaryl and BPMC. The obtained results were as follows. 1. It was possible to determine short term BCFs of Chlorothalonil through relatively simple procedure in environmental concentrations. 2. $BF_3$ of Chlorothalonil in concentration of 0.005, 0.01 and 0.05 ppm were 2.1866$\pm$0.23446, 3.5269$\pm$0.23517, 10.2045$\pm$0.18053 and BCFs were 6.6543$\pm$0.55257, 6.9774$\pm$0.02500, 23.4576$\pm$2.06884, respectively. 3. Chlorothalonil concentration in fish extract and BCFs of Chlorothalonil were increased as increasing test concentration and prolonging test period. 4. Fate of test-water concentration on Chlorothalonil was greater than that of control-water con-centration. It is considered that greater fate of test-water concentration on Chlorothalonil is due to hydrolyzing nitrile group under the mild condition and substituting chloro group by some aromatic compounds in test water. 5. Determined logP of Chlorothalonil was 2.80. And determined $LC_{50}$ of Chlorothalonil in time of 24, 48, 72 and 96 hr were 0.1684, 0.1402, 0.1400, 0.1352(mg/l) respectively. And $LC_{50}$ of Carbaryl in above times were 19.918, 18.635, 18.466, 18.12(mg/l) respectively. $LC_{50}$ of BPMC were 10.248, 9.166, 9.087, 8.921(mg/l) respectively. 6. It is suggested that the BCF of Carbamates depend on partition coefficients. But BCF of Chlorothalonil, organochlorine pesticide, would be strongly influenced by steric, electronic effect of substituents than partition coefficient.

• 한국환경보건학회지
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• 제23권2호
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• pp.72-82
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• 1997

This study was performed to investigate the effect of co-existence of BPMC, carbaryl and chlorothalonil on the short-term bioconcentration factor in Carassius auratus(goldfish). The fishes were exposed to the combined treatment of BPMC, carbaryl and chlorothalonil (0.05 ppm+0.05 ppm+0.005 ppm, 0.05 ppm+0.05 ppm+0.010 ppm, 0.05 ppm+0.10 ppm+0.005 ppm, 0.10 ppm+0.05 ppm+0.005 ppm, 0.10 ppm+0.10 ppm+0.005 ppm) for 3 and 5 days, respectively. BPMC, carbaryl and chlorothalonil in fish and in test water were extracted with n-hexane and acetonitrile. GC-ECD was used to detect and quantitate BPMC, carbaryl and chlorothalonil. 3-day and 5-day bioconcentration factors(BCF$_3$ and BCF$_5$) of each pesticide were calculated from the quantitation results. The depuration rate of each pesticide-from the whole body of fish was determined over the 72-h period after combined treatment.The results were as follows: BCF$_3$ values of BPMC were 4.163, 4.011, 4.122, 4.750 and 4.842 when the concentration of BPMC+ carbaryl+chlorothalonil in combined treatment were 0.05 ppm+0.05 ppm+0.005 ppm, 0.05 ppm+0.05 ppm+0.010 ppm, 0.05 ppm+0.10 ppm+0.005 ppm, 0.10 ppm+0.05 ppm+0.005 ppm and 0.10 ppm+ 0.10 ppm+0.005 ppm. BCF$_5$ values of BPMC were 3.465, 3.270, 3.472, 3.162, 4.227 and 4.157, respectively, under the above conditions. While BCF$_3$ values of carbaryl were 4.583, 4.642, 4.571, 3. 637 and 3.529, respectively, and BCF$_5$ values of carbaryl were 3.932, 3.797, 3.843, 4.293 and 4.132, respectively, under the conditions. While BCF$_3$ values of chlorothalonil were 2.024, 3.532, 2.213, 2.157 and 2.271, respectively, and BCF$_5$ of chlorothalonil were 6.712, 7.013, 6.457, 6.694 and 6.597, respectively, under the conditions. Depuration rate constants of BPMC were 0.019, 0.018, 0.020, 0.022 and 0.021 when the concentration of BPMC+carbaryl+chlorothalonil in combined treatment were the same as above. And depuration rate constants of carbaryl were 0.030, 0.029, 0.030, 0.029 and 0.031, respectively, under the same condition of pesticide mixtures. While depuration rate constants of chlorothalonil were 0.004, 0.004, 0.003, 0.004 and 0.003, respectively, under the same condition. It was observed that no significant differences of BCFs and concentrations of the compounds in fish extracts, test water between combined treatment and single treatment. It was considered that no appreciable interaction at experimental concentrations was due to low concentrations, near environmental level, 0.005-0.1 ppm. Coexistence of BPMC, carbaryl and chlorothalonil had no effect on depuration rate of each pesticide and depuration rate of chlorothalonil was investigated 1/8 and 1/6 slower than those of carbaryl and BPMC in combined treatment. It is similar result in comparison with single treatment. Therefore, it is considered that the persistence of chlorothalonil in fish body would be higher than those of carbaryl and BPMC.

• 한국환경보건학회지
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• 제23권2호
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• pp.64-71
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• 1997

This study was performed to investigate the effect of co-existence of carbofuran and chlorothalonil on the short-term bioconcentration factor in Brachydanio rerio(zebrafish). The fishes were exposed to the single and combined treatment of carbofuran and chlorothalonil for 1, 3 and 5 days. Experimental concentrations of carbofuran were 0.05 and 0.10 ppm under the single treatment. And those of chlorothalonil were 0.005 and 0.010 ppm. Experimental concentrations of the combined treatment of carbofuran and chlorothalonil were 0.05 ppm+0.005 ppm, 0.05 ppm+0.010 ppm, 0.10 ppm+0.005 ppm for 1, 3 and 5 days, respectively. Carbofuran and chlorothalonil in fish and in test water were extracted with n-hexane and acetonitrile. GC-ECD was used to detect and quantitate carbofuran and chlorothalonil. 1-day, 3-day and 5-day bioconcentration factors(BCF$_1$, BCF$_3$ and BCF$_5$) of each pesticide were obtained from the quantitation results. The depuration rate of each pesticide was determined over the 24-h period after combined treatment. The results were as follows: Carbofuran did not bioaccumulate in zebrafish under the single and combined treatment for testing periods. BCF$_1$ values of chlorothalonil in concentration of 0.005 and 0.010 ppm under the single treatment were 0.508, 0.621, BCF$_3$ were 1.327, 1.511 and BCF$_5$ were 1.331, 1.597, respectively. BCF$_1$ values of chlorothalonil were 0.512, 0.520 and 0.619, respectively, when the concentration of carbofuran and chlorothalonil in combined treatment were 0.05+0.005, 0.05+0.010 and 0.10+0.005 ppm. BCF$_3$ values of chlorothalonil 1.341, 1.338 and 1.513, respectively, and BCF$_5$ values of chlorothalonil were 1.332, 1.327 and 1.521, respectively, under the above combined treatment. Depuration rate constants of chlorothalonil in concentration of 0.005 and 0.010 ppm under the single treatment were 0.011 and 0.012. Depuration rate constants of chlorothalonil were 0.011, 0.010 and 0.011, when the concentration of carbofuran and chlorothalonil in combined treatment were 0.05+0.005, 0.05+0.010 and 0.10+0.005 ppm. It was observed that no significant difference of carbofuran and chlorothalonil concentration in fish extracts, test water, BCFs and depuration rate constants of carbofuran and chlorothalonil between combined treatment and single treatment. It was considered that no appreciable interaction at experimental concentrations due to lower concentrations than LC$_{50}$. It is suggested that the difference of BCFs between carbofuran and chlorothalonil due to those of fat composition of fish and solubility of carbofuran and chlorothaionil.

• 한국식품위생안전성학회지
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• 제18권4호
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• pp.251-256
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• 2003

본 연구는 zebrafish를 실험어류로 하여 국내에서 혼합제로 사용되고 있는 dichlovos와 phosalone을 선정하여 단독 및 혼합폭로시 생물농출계수와 배설속도상수를 측정함으로써, 두 농약의 공존이 개별농약의 생물농축성에 미치는 영향을 알아보고자 하였다. Dichlorvos와 phoslone의 혼합폭로시(dichlorvos : 0.55${\mu}g$/ml, phosalone : 0.01 ${\mu}g$/ml) zebrafish 체내에서 dichlorvos의 농축정도는 6시간에 정류상태에 도달하여 72시간까지 거의 일정하였으며 단독폭로시 (12시간)보다 더 빠르게 정류상태에 도달하였다. 6시간에서 72시간 사이의 BCF평균값은 0.80(n=5)으로 단독 폭로시의 12시간에서 72시간 사이의 BCF평균값 0.74(n=4)보다 더 높게 측정되었다. 배설속도상수는 $0.12h^{-1}$으로 단독 폭로시와 차이가 거의 없었다. Dichlorvos와 phosalone의 혼합폭로시(dichlorvos: 0.55${\mu}g$/ml, phosalone : 0.01${\mu}g$/ml) zebrafish 체내에서 phosalone의 농축정도는 단독폭로시와 같이 12시간에 정류상태에 도달하여 72시간까지 거의 일정하였고, 12시간에서 72시간 사이의 BCF평균값은 53.89(n=4) 로 단독폭로시의 BCF평균갑 48.88(n=4)보다 더 높게 측정되었다. 배설속도상수는 단독폭로시와 같이 6시간 안에 어류체내에서 phosalone이 모두 배출되어 구하지 못했다. 두 농약(dichlorvos, phosalone)의 혼합폴로시의 BCF평균값이 단독폭로시의 BCF평균값이 단독폴로시의 BCF평균값보다 더 높게 나왔으나, 각 실험시간대(6, 12, 24, 48, 72시간)의 BCF실험값을 t-test로 분석한 결과 phosalone의 48시간을 제외하고는 두 농약의 단독폭로와 혼합폴로시의 BCF값에는 유의한 차이가 없었다(p<0.05), 이상의 결과를 종합해 볼때, dichlorvos와 phosalone을 zebrafish에 혼합폭로시 개개 농약의 생무농축성과 배설속도상수에는 유의한 영향을 미치지 않는 것으로 나타났다.

• Applied Biological Chemistry
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• 제45권1호
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• pp.30-36
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• 2002

제초제 butachlor의 어류농축 계수를 결정하기 위하여 동위원소 표지화합물과 비표지 화합물을 사용하여 송사리 체내에서의 농축시험을 수행하였다. 비표지 화합물을 사용하였을 때 송사리 체내에서의 butachlor농축은 0.036ppm농도에서 40시간 경과 후 가장 높은 어류생체 중 296의 생체 농도/수중 농도$(C_f/C_w)$ 비율을 보였고, 64시간 이후부터는 평형상태에 이르렀으며, 이 때의 bioconcentration factor(BCF)는 87이었다. 또한, 0.0036 ppm도에서는 18시간 경과 후 가장 높게 축적되어 $C_f/C_w$의 비율이 169였고, 60시간 이후에는 평형상태에 도달하여 BCF 값은 51이었으며, 이 두 농도로부터 결정된 BCF 값은 $69{\pm}28$이었다. $^{14}C-butachlor$의 송사리 체내에서의 농축 및 배설은 총 $^{14}C$를 기준으로 하였을 때 17시간 경과 후 가장 높은 539 $C_f/C_w$의 비율을 나타내었고, 74시간 이후부터는 평형상태에 이르러 BCF는 394로 계산되었다. 그러나 14C-butachlor의 양만을 고려했을 때 $C_f/C_w$의 비율은 총 흡수량의 1/3이었고, 2/3은 $^{14}C-butachlor$의 대사물 이었으며, 평형상태에서의 $^{14}C-butachlor$의 BCF는 334로 계산되었다. 또한, 송사리 체내로부터의 $^{14}C-butachlor$의 배설은 12시간 이내에 50% 이상이, 30시간이 되면서 90% 이상이 배설되었다. 생체 내에서의 대사물은 아주 극성이 강한 대사물들로서 TLC상에서 $R_f$이 0.43인 대사물 M-II와 $R_f$값이 0.7인 대사물 M-III로 확인되었고, 신선한 사육수로 어체내 대사산물을 배설시켰을 때 $R_f$ 값이 0.25인 대사물 M-I을 확인하였다. M-I은 어체내에서 배출되는 과정중의 주요한 중간 대사물 임을 예상할 수 있었다.

• 한국환경보건학회지
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• 제22권4호
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• pp.16-24
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• 1996

This study was performed to investigate the effect of co-existence of carbaryl and chlorothalonil on the short-term bioconcentration factor in Carassius auratus(goldfish). The fishes were exposed to the combined treatment of carbaryl and chlorothalonil(0.05 ppm+0.005 ppm, 0.05 ppm+0.010 ppm, 0.10 ppm+0.005 ppm) for 1, 3 and 5 days, respectively. Carbaryl and chlorothalonil in fish and in test water were extracted with n-hexane and acetonitrile. GC-ECD was used to detect and quantitate carbaryl and chlorothalonil. 1-day, 3-day and 5-day bioconcentration factors($BCF_1, BCF_3$ and $BCF_5$) of each pesticide were calculated from the quantitation results. The depuration rate of each pesticide from the whole body of fish was determined over the 72-h period after combined treatment. The results were as follows: $BCF_1$ values of carbaryl were 3.521, 3.802 and 3.587, respectively, when the concentration of carbaryl and chlorothalonil in combined treatment were 0.05+0.005, 0.05+0.010 and 0.10+0.005 ppm. BCF3 values of carbaryl were 4.825, 4.556 and 3.828, respectively, and $BCF_5$ values of carbaryl were 3.974, 3.921 and 4.186, respectively, under the conditions. While $BCF_1$ of chlorothalonil were 0.829, 0.829 and 1.540, respectively, under the same condition of pesticide concentrations $BCF_3$ of chlorothalonil were 2.040, 2.208 and 3.633, respectively, and $BCF_5$ of chlorothalonil were 6.222, 6.667 and 7.095, respectively, under the conditions. Depuration rate constants of carbaryl were 0.022, 0.022 and 0.152, respectively, when the concentration of carbaryl and chlorothalonil in combined treatment were 0.05+0.005, 0.05+0.010 and 0.10+0.005 ppm. While depuration rate constants of chlorothalonil were 0.004, 0.004 and 0.006, respectively, under the same condition of pesticide concentrations. It was observed that no significant differences of carbaryl and chlorothalonil concentration in fish extracts, test water and $BCF_s$ of carbaryl and chlorothalonil between combined treatment and single treatment. It was considered that no appreciable interaction at experimental concentrations was due to low concentrations, 0.005~0.1 ppm. Co-existence of carbaryl and chlorothalonil had no effect on excretion of each pesticide and depuration rate of chlorothalonil was investigated 1/8 slower than that of carbaryl in combined treatment. Therefore, it is considered that the persistence of chlorothalonil in fish body would be higher than that of carbaryl.

• 한국환경보건학회지
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• 제24권1호
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• pp.24-31
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• 1998

This study was performed to investigate the difference in species of test fish on the determination of short-term bioconcentration factor in zebrafish(Brachydanio rerio), red sword tail(Xiphophorus hellieri) and goldfish(Carassius auratus). Experimental concentrations of carbamates were 0.05 and 0.10 ppm and chlorothalonil were 0.005 and 0.01 ppm for 3 and 5 days, respectively. This paper reports the measured BCF value on pesticides in various species of test fish, under steady state, and examined correlation between the BCF value and depuration rate constant or LC$_{50}$ or lipid content. Carbamates and chlorothalonil concentration in fish extract and BCF of carbamate and chlorothalonil were increased as incresing test concentration. Carbamates concentration in fish extract and BCF of carbamate were decreased as incresing test period, but chlorothalonil concentration in fish extract and BCF of chlorothalonil were increased as prolonging test period. Determined pesticide concentration in fish extract and BCF were highest in red sword tail, and followed by goldfish, and zebrafish. Determined depuration rate constant were highest in zebrafish, and followed by goldfish, and red sword tail. 96hr-LC$_{50}$ were highest in red sword tail, and followed by zebrafish, and goldfish. Lipid compositions were highest in red sword tail, and followed by goldfish, and zebrafish. Therefore, it is suggested that the difference of BCF between each pesticide due to those of lipid composition of fish and deputation rate constant, while LC$_{50}$ have no effect on BCF.

• Environmental Analysis Health and Toxicology
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• 제23권2호
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• pp.67-77
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• 2008

It has been observed that the linear relationship between the logarithm of bioconcentration factor (log BCF) of highly hydrophobic chemicals and their log $K_{ow}$ breaks when log $K_{ow}$ becomes greater than 6.0. Consequently, super hydrophobic chemicals were not thought to cause baseline toxicity as a single compound. Researchers often call this phenomenon as "hydrophobicity cutoff" meaning that bioconcentration or corresponding baseline toxicity has a certain cutoff at high log $K_{ow}$ value of hydrophobic organic pollutants. The underlying assumption is that the increased molecular size with increasing hydrophobicity prohibits highly hydrophobic compounds from crossing biological membranes. However, there are debates among scientists about mechanisms and at which log $K_{ow}$ this phenomenon occurs. This paper reviews three hypotheses to explain observed "cutoff": steric effects, kinetic or physiological limitations, and chemical activity cutoff. Although the critical molecular size that makes biological membranes not permeable to hydrophobic organic chemicals is uncertain, size effects in combination with kinetic limitation would explain observed non-linearity between log BCF and log $K_{ow}$. Chemical activity of hydrophobic chemicals generally decreases with increasing melting point at their aqueous solubility. Thus, there may be a chemical activity cutoff of baseline toxicity if there is a critical chemical activity over which baseline effects can be observed.