• Korean Journal of Environmental Agriculture
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• v.4 no.1
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• pp.6-10
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• 1985

Residue levels of 10 kinds of organochlorine insectides in/on garlic produced in Chungnam area during $1982{\sim}1983$ were investigated. Residue levels ranged in $trace{\sim}0.004 ppm$ (aver. 0.002 ppm) for ${\alpha}-BHC$, $0.015{\sim}0.176 ppm$ (aver. 0.083 ppm) for ${\gamma}-BHC$, $0.001{\sim}0.008 ppm$ (aver. 0.005 ppm) for heptachlor, ND(not detected) ${\sim}0.006 ppm$ (aver. 0.003 ppm) for aldrin, $trace{\sim}0.011 ppm$(aver. 0.003 ppm) for ${\alpha}-endosulfan$, $ND{\sim}0.004 ppm$ (aver. 0.001 ppm) for heptachlor epoxide, $trace{\sim}0.002 ppm$(aver. 0.001 ppm) for dieldrin, $trace{\sim}0.008 ppm$(aver. 0.001 ppm) for ${\beta}-endosulfan$, and trace for p,p'-DDD and p,p'-DDT.

• Korean Journal of Food Science and Technology
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• v.12 no.3
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• pp.141-149
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• 1980

In order to determine the residue levels of organochlorine insecticides in cow's milk, 66 commercial milk samples were collected from markets in major cities of Korea and analyzed for their fat contents and pesticide residue levels. The fat contents were in the range of $2.65{\sim}3.87%$, the average being 3.35%. The average residue levels of organochlorine insecticides on fat basis (whole milk basis in parentheses) were 0.196 ppm (0. 0066 ppm) of ${\alpha}-BHC$, 0.159ppm (0.0055 ppm) of ${\beta}-BHC$, 0.066 ppm (0.0022 ppm) of heptachlor epoxide and 0.042ppm (0.0015 ppm) of DDE. Heptachlor, DDT and drin insecticides were not detected. These residue levels corresponding to $1/10{\sim}1/50$ of tolerance levels adopted in Japan appear to exhibit no adverse effect as yet from the standpoint of food safety.

• YAKHAK HOEJI
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• v.18 no.1
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• pp.29-38
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• 1974

In order to study the residual amounts of absorbed organochlorine pasticides in vegetables, heptachlor and endrin were sprayed 2,4 and 6kg per 10a., respectively, before sowing the seeds in the station. The experiemental study is primarily concerned with the absorption in lettuce nad garland chrysanthemum. The absorption of each pesticide into lettuce and garland chrysanthemum, and residual pesticides in soil by timne have been analyzed by the gas chromtographic method, and the ratio of residual pesticides in vegetablesand soil were estimated. Heptachlor, heptachlor epoxide and endrin in lettuce nad garland chrysanthemum at the market in Seoul area hvae also analyzed and found extremely low level of pesticides in comparison with the level in above experimental vegetables as well as same vegetables in Japan.

• Proceedings of the Korean Environmental Sciences Society Conference
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• 2004.05a
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• pp.101-102
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• 2004

유기염소계 농약류 14종을 분석한 결과 황소개구리의 경우 모든 시료에서 검출되지 않았다. 붕어의 경우 11종의 분석대상물질이 검출되지 않았고, heptachlor epoxide B, trans-nonachlor, p,p´-DDE가 각각 3개 지점, 7개 지점, 5개 지점에서 검출되었다.

• Environmental Analysis Health and Toxicology
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• v.22 no.2 s.57
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• pp.177-184
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• 2007

Gaseous organochlorine pesticides (OCPs : heptachlor epoxide, p, p'-DDE, ${\gamma}-HCH,\;{\alpha}-chlordane,\;{\gamma}-chlordane$ and trans-nonachlor) concentration was measured using PUF high volume sampler from June, 2000 to June, 2002 in the semi-rural atmosphere. The OCPs concentration in atmosphere, which is estimated by the slope (m) of Clausius-Clapeyron equation and phase-transition energy $({\Delta}H)$, was influenced by revolatilization from environmental matrix (soil, water and tree leaves) and a long range transportation of air mass. But the former affected OCPs concentration more than the latter. The degradation rate constants (k) of OCPs calculated using multiple regression analysis and revised standard temperature method were in good agreement each other. The value of k of ${\gamma}-HCH$ was very low as -0.0007, but the range of k of other components were $-0.00l8{\sim}-0.0038$. The half-life $({\tau})$ which was calculated by k of ${\gamma}-HCH$ was 2.6 years-the longest one, but that of heptachlor epoxide was in 0.5 year-the shortest one. $({\tau})\;of\;{\alpha}-chlordane,\;{\gamma}-chlordane$ and trans-nonachlor in technical chlordane was 1.0, 1.1 and 0.7 year respectively.

• Journal of Food Hygiene and Safety
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• v.1 no.2
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• pp.163-169
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• 1986

소, 돼지, 닭 및 염소의 근육, 지방조직 및 내장부위에서 11가지 유기염소계 잔류농약을 분석하여 다음과 같은 결과를 얻었다. 1. 육류시료 모두에서 검출된 유기염소계의 잔류량은 $\alpha$-BHC, $eta$-BHC, pp'-DDE, Heptachlor epoxide, ${\gamma}$-BHC순으로 검출되었고, Heptachlor, pp'-DDE 및 pp'-DDD는 극미량 내지는 흔적 정도 검출되었고 Drins류는 검출되지 않았다. 2. Total BHC 잔류량의 범위는 소의 경우 0.389ppb~1.111ppb로 평균 0.713ppb였고, 돼지는 0.139ppb~0.150ppb로 평균 0.631ppb였으며 닭은 0.312ppb~0.80ppb로서 평균 0.517ppb였다. 그리고 염소의 경우에는 0.238ppb~1.134ppb로써 평균 0.586ppb의 수준이었다. 3. 육류별 잔류량은 소, 돼지, 염소, 닭의 순서이고 부위별 잔류량은 지방조직이 가장 많았고 그 다음이 근육, 그외 부위별 잔류량의 차이는 거의 없었다.

• The Korean Journal of Pesticide Science
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• v.15 no.4
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• pp.502-506
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• 2011

Most countries have the legislation and regulation for POPs control in food. In here, we studied the quantitative analysis of 24 organochlorine POPs (${\alpha}$-HCH 1, ${\beta}$-HCH 2, ${\gamma}$-HCH 3, ${\delta}$-HCH 4, trans-chlrodane 5, 2,4'-DDE 6, ${\alpha}$-endosulfan 7, cis-chlordane 8, 2,4'-DDD 9, endrin 10, ${\beta}$-endosulfan 11, 2,4'-DDT 12, endosulfan sulfate 13, HCB 14, aldrin 15, trans-nonachlor 16, 4,4'-DDE 17, dieldrin 18, 4,4'-DDD 19, cis-nonachlor 20, 4,4'-DDT 21, heptachlor 22, heptachlor epoxide 23 and mirex 24) with GC-ECD. The retention time of analytes were ranged between 19.18 min and 34.69 min, and their peak intervals were over 0.05 min at least. LOQs were ranged 0.003 ~ 0.033 ng/g, and their recovery rates were showed 60.9 ~ 120.8% on the 0.1 ng/g concentration of 24 organochlorine POPs. All tested 30 sundried salts were collected on Korean retailed market, and any analyte was not found in all the samples on LOQ levels.

• Journal of Plant Biology
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• v.20 no.1
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• pp.53-57
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• 1977

The appearence of organochlorine pesticide residues in some marinealgae, e.g. Sargassum thunbergii, Ulva pertusa, Codium fragile, and Enteromorpha linza, collected from various sites of Kwang Yang Bay, southern coast of Korea, was surveyed through the year from May 1974 to March 1975. The residues were found to appear in the order to July>September>May>November≒March≒January; $\alpha$-BHC>heptachlor epoxide>dieldrin>aldrin>endrin; and in the range of 0-93 $\mu\textrm{g}$/kg dry matter.

• Journal of Preventive Medicine and Public Health
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• v.32 no.2
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• pp.155-161
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• 1999

Objectio ostinato the carcinogenic risks from the ingestion of some carcinogenic pesticides (CPs) in vegetables sampled at a local agricultural product market in Seoul. Methods: After applying a hazard identification step, we selected four pesticides, such as DDT, dieldrin, folpet, and heptachlor epoxide, for this risk assessment. Concentrations of each pesticide were measured from randomly sampled vegetables. In order to estimate the human exposure levels, we combined the concentration of pesticides in the vegetables with consumption rate of those vegetables. Three scenarios were hypothesized for human exposure assessment. Scenario I was the most conservative which supposed the undetected CPs would be the detection limit values. Scenario II was assumed that the undetected CPs would be a half of the detection limit values, and finally scenario III merely considered only values greater than the detection limit values. We finally presented the estimated carcinogenic risks on the basis of the traditional risk assessment procedure suggested by U.S. EPA. Results: Pesticides including DDT, dieldrin, folpet and heptachlor epoxide were detected in 9 samples (6%) in the range of $0.0006\sim0.09ppm$. The daily intake levels of carcinogenic pesticides were estimated in the range of $0.0009\sim0.0079{\mu}g/day$. As we expected, excess cancer risks based on scenario I was also the highest $(1.1\times10^{-8}\sim5.5\times10^{-5})$. Conclusions: We found that the estimated risks from the pesticides we investigated were not serious. We, however, propose that a continuos monitoring is needed to make sure for the protection of public health.

• Environmental Analysis Health and Toxicology
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• v.22 no.4
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• pp.299-304
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• 2007

This paper was studied to investigate the equilibrium state between organochlorine pesticides (OCPs) concentration of air and soil, and to know whether soil is a secondary pollution source of OCPs in air or not. The OCPs concentration of air ($C_{air}$) and soil ($C_{soil}$) is not related to molecular weight, vapor pressure ($P_L$) and octanol-air partition coefficient ($K_{oa}$). The slope of the regression line between soil-air partition coefficient ($K_{sa}$) and scavenging coefficient ($C_{soil}/C_{air}$) was 0.2952, which the OCPs concentration between air and soil did not reached to the equilibrium state. The soil/air fugacity quotients ($f_{soil}/f_{air}$) of p, p'-DDT/DDD/DDE and ${\beta}-HCH\;(0.30{\sim}0.67$), which is smaller than 1, means the deposit of OCPs from air to soil. However, $f_{soil}/f_{air}$ of heptachlor, heptachlor epoxide, ${\alpha}/{\gamma}-chlordane$, trans-nonachlor, endosulfan sulfate and ${\alpha}/{\gamma}-HCH\;(1.90{\sim}73.25)$, which is greater than 1, means that soil is secondary pollution source of OCPs in air.