The Stockholm Convention, which was adopted in Sweden in 2001 to protect human health and the environment, includes regulations for Persistent Organic Pollutant Rotors such as toxic and bioaccumulatives. Currently, there are 28 types of materials. This prohibits and limits the production, use, and manufacture of products. Korea is a member of the Convention, and it is necessary to prepare management and treatment plans to address the POP trends. Thus, we experimentally investigate whether the environmentally stable incineration is achieved when the sample is thermally treated using the Lab-scale (1 kg/hr). The target samples is pesticides in liquid phase and solid phase. In this study, organic chlorinated pesticides and their thermal characteristics were analyzed. We calculated the theoretical air volume based on the element analysis results. Because the interior of the reactor is small, more than 10 times of the air ratio was injected. The retention time was set to at least 4 seconds using a margin. The incineration temperature was 850℃ and 1100℃. Thus, we experimentally investigated whether the environmentally stable incineration was achieved when the sample was thermally treated using the Lab-scale (1 kg/hr). We analyzed five types of exhaust gas; the 02 concentration was high, but the CO amount decreased. Complete combustion is difficult because of the small size of the furnace due to the nature of Lab-scale. The organic chlorine-containing pesticide had an average decomposition rate of 99.9935%. Considering the decomposition rates of organic chlorine-containing pesticide in this study, the incineration treatment at over 2 ton/hour, which is typical for a conventional incinerator, is possible. Considering the occurrence of dioxins and unintentional persistent organic pollutants, it can operate at more than 1,100℃.

Sorption of chlorinated pesticides such as 2,4-dichlorophenoxyacetic acid (2,4-D) and atrazine onto natural clays (montmorillonite and zeolite) modified with cationic surfactant, hexadecyltrimethyl-ammonium (HDTMA) and a natural soil was investigated using batch adsorbers. The clays were transformed from hydrophilic to hydrophobic by the cation exchange between clay surface and HDTMA up to 100% of the cation exchange capacity (CEC). Physicochemical characteristics of the sorbents such as pH, PZC (point of zero charge), organic carbon content (foc), fourier transform infrared spectroscopy (FT-IR), differential thermogravimetric analysis (DTGA) and X-ray diffraction (XRD) were analyzed. Sorption isotherm models such as Freundlich and Langmuir were fitted to the experimental data, resulting Langmuir model (R2 > 0.986) was fitted better than Freundlich model (R2 > 0.973). Sorption capacity (Q0) for 2,4-D and atrazine was in the order of HDTMA-montmorillonite > HDTMA-zeolite > natural soil corresponding to the increase in organic carbon content (foc). The sorption of the pesticides was also affected by pH. The sorption of 2,4-D decreased with the increase in pH, whereas that of atrazine was not changed. This indicated that the sorption capacity (Q0) of 2,4-D and atrazine was not affected by the solution pH because they exist as anionic (deprotonated) forms at pH above pKa. The results indicate that organoclay has a promising potential to reduce chlorinated pesticides in the effluent from golf courses.

To obtain the risk assessment of hazardous materials in ginseng, the residues of heavy metals and organochlorine pesticides in samples on the Yeungju and Sangju are surveyed. Cd and Hg in ginseng on Yeungju and Sangju is not detected. 0.21 mg/kg of As, 0.39 mg/kg of Cr, 0.14 mg/kg of Pb, 1.83 mg/kg of Cu, 3.93 mg/kg of Zn and 0.43 mg/kg of Ni in ginseng on Sangju are shown. 0.25 mg/kg of Cr, 0.08 mg/kg of Pb, 1.11 mg/kg of Cu, 8.99 mg/kg of Zn and 1.15 mg/kg of Ni in ginseng on Yeungju are detected. As and Pb in ginseng on Sangju are 7.0% and 2.8% for Korea Food & Drug Administration(KFDA) advisory level, respectively. Pb in ginseng on Yeongju are 1.6% for Korea Food & Drug Administration(KFDA) advisory level. The heavy metals such as AS, Cr, Cd, Pb, Cu, Zn, Hg, Ni in soil on Yeongju and Sangju are range of 0-20% for with Korea Food & Drug Administration (KFDA) level. BHC isomer, DDT isomer and endosulfan isomer are not detected in ginseng and soil on Yeongju and Sangju, respectively. Finally, the assessment of hazardous materials of the heavy metals and organochlorine pesticides in ginseng on the Youngju and Sangju are verified the safety the level compare with tolerances level for Korea

본 연구에서는 식품의약품안전청고시에서 규제한 유기염소계 농약을 포함하여 다성분 동시분석법을 확립하였으며, 경상북도 상주지역 인삼자원의 재배토양 및 인삼 시료 중에서 유기염소계 농약의 잔류성을 검토하였다. α-BHC의 유지시간은 21.455분이었는데 이를 1.00으로 하였을때 β-BHC, δ-BHC, Quintozene, γ- BHC, Aldrin, Captan, o,p-DDE 및 α-Endosulfan의 상대적인 유지시간은 각각 1.025, 1.034, 1.038, 1.056, 1.143, 1.183, 1.199 및 1.218이었다. 또한 p,p-DDE, o,o-DDD, Dieldrin, Fenhexamid, Endrin, β- Endosulfan, o,p-DDT, o,p-DDD, p,p-DDT 및 Endosulfan-sulfate의 상대적인 유지시간은 각각 1.230, 1.242, 1.246, 1.261, 1.279, 1.283, 1.286, 1.329, 1.333, 1.338이었다. 피이크 분리가 정량분석하기에 지장이 없었으며, 따라서 19가지 유기염소계열 농약을 동시 다성분 분석 할 수 있었다. 최소검출농도는 α-BHC, Quintozene, Aldrin, Captan, α-Endosulfan, Dieldrin이 각각 0.95ng/g, 0.27ng/g, 1.04ng/g, 0.63ng/g, 0.55ng/g 및 0.62ng/g이었다. 또한 Fenhexamid, Endrin, β-Endosulfan, o,p-DDT, Endosulfan-sulfate도 각각 5.71ng/g, 0.61ng/g, 0.48 ng/g, 0.44ng/g 및 0.51ng/g이었다 상주지역의 인삼자원은 식품의약품안전청고시에서 생약의 잔류농약 허용기준으로 제시된 BHC, Aldrin, Dieldrin, Endrin 및 DDT가 불검출되었다. 또한 재배토양에서도 불검출 되었다. 따라서 경상북도 상주 인삼 재배환경은 유기염소계 농약으로 오염되지 않았다.

To obtain the residual organochlorine pesticides in the coastal environment, the methods of analysis for BHC's isomer, Kelthane, Orthocide and Endrin by GC-ECD are surveyed. The relative retention time for α-BHC, β-BHC, γ-BHC and δ-BHC is 1.00, 1.18, 1.24, 1.31 and it's of Kelthane, Orthocide, Endrin is 1.56, 1.70, and 2.02, respectively. The BHC isomers, Kelthane, Orthocide and Endrin are separated on the base line. The plate height(H) for α-BHC, β-BHC, γ-BHC and δ-BHC is 50mm, 35mm, 32mm and 29mm, and it's of Kelthane, Orthocide, Endrin is 81mm, 68mm and 48mm, respectively. The qualified defection concentration for α-BHC, β-BHC, γ-BHC and δ-BHC is 0.26, 0.36, 0.37 and 0.39ng/g and it's of Kelthane, Orthocide, Endrin is 0.55, 1.39 and 0.56ng/g, respectively. BHC's isomer, Kelthane, Orthocide and Endrin are not detected in soil environment on South Cheju Island. Also residual organochlorine pesticides are not detected in the sea water and sediment in the ocean environment.

Pesticides were extracted from samples with 70% acetone and methylene chloride in order, and then cleaned up via open-column chromatography apparatus packed with florisil, and finally analyzed simultaneously the organochlorine and pyrethroid pesticides using GC(ECD). An ultra-2 fused silica capillary column was used to separate and identify the products. The resolution between the last isomeric peak of cypermethrin(59.987min) and the first isomeric peak of flucythrinate(60.043min) was not satisfactory. The last isomeric peak of fenvalerate(62.344min) and the first isomeric peak of fluvalinate(62.397min) were overlapped. Recoveries of soybean sample for the most pesticides were 73.3% to 102.4%. Detection limits were between 0.004 and 0.063㎍/㎎ when this method was used.

본 실험은 1998년 1월부터 2001년 12월가지 4년간 경기도와 인천지역에 납품된 군납 농산물 17종(배추, 무, 오이, 감자, 사과, 양파, 파, 양배추, 고추, 당근, 상추, 호박, 마늘, 미나리, 시금치, 쑥갓, 부추)을 대상으로 유기염소계 농약 10종 (BHC, captafol, captan, chlorobenzilate, chlorothalonil, DDT, dicofol, endosulfan, folpet, tetradifon)을

A method for the simultaneous analysis of 31 residual organic chloride pesticides was studied using gas chromatography. Prepared analytical samples were injected to gas chromatography (HP 5890 Series II plus) on the Ultra-2 column with ECD. The packing materials for column were changed as the following reagents ; florisil and alumina N. The residual solution was loaded to column and was eluted with elution solvents ; ether : benzene (2 : 8) solution, hexane : benzene (1:1) solution, dichloromethane, acetone, and methanol. The analytical results showed that 6 kinds of organic chlorides were not detected when florisil (first condition) was used as the column packing material. The nondetected 6 kinds of organic chlorides in the first analytical condition were detected and the recoveries of thrin-pesticides were increased, in particular, captan and captafol, but the recoveries of benzene hexachloride compounds were decreased when dichloromethane and methanol were added as elution solvents (packing material was florisil as in the first condition). The recoveries of dichlorfluanid, chlorofenvinfos, folpet, and dicofol were increased and that of aldrin was increased, but those of captan and captafol were not good when alumina N was used as the packing material. To detect simultaneously thrin-pesticides, captan, and captafol, florisil and alumina N were used as the packing materials. The elution result showed that captan and captafol were not detected. This was because the column was activated insufficiently. The analytical method was the best (31 kinds of organic chlorides in the residual pesticides were detected sharply and showed high sensitivity) when the column (packing materials were florisil and alumina N, together) was fully activated and the impurities were removed using various elution solvents.