농약류 3종의 독성평가를 위해 FETAX(Frog Embryo Teratogenesis Assay-Xenopus) 기법에 따라 국내에 서식 중인 두꺼비(Bufo gargarizans)의 배아를 배양하면서 Benomyl(살균제), Carbofuran(살충제), Thiobencarb(제초제)의 영향을 probit 분석법으로 조사하였다. 그 결과, Benomyl, Carbofuran, Thiobencarb의 농도에 의존하여 유생의 체장 길이는 감소하고 치사율과 기형율은 증가하였다. Benomyl, Carbofuran, Thiobencarb의 teratogenic concentration(EC50)은 각각 1.03, 8.74, 4.98㎎/ℓ 을 나타내어 Benomyl이 기형 유발에 가장 민감하게 반응하였으며, embryo lethal concentrations(LC50)은 7.26, 560.72, 16.87㎎/ℓ 을 나타내어 Benomyl이 가장 낮은 농도에서 배아가 치사되는 것으로 나타났다. Teratogenic index (TI=LC50/EC50)는 Benomyl 7.05, Carbofuran 64.16, Thiobencarb 3.39를 나타내어 TI값이 모두 기형유발물질로 판단되는 기준인 1.5이상으로 시험에 사용된 농약류 3종은 최기형성 물질로 판단된다. Carbofuran이 가장 강력한 최기형성물질로 작용함을 알 수 있었으며, 농약류가 두꺼비 및 양서류의 배아 발달에 미치는 영향과 그 작용기작을 규명하기 위해서는 보다 구체적인 연구가 필요할 것으로 판단된다.

국내에 서식중인 청개구리의 배아를 활용하여 농약류 3종의 독성평가를 위해 FETAX(Frog Embryo Teratogenesis Assay-Xenopus) 기법에 따라 청개구리(Hyla japonica)의 배아를 배양하면서 Benomyl(살균제), Carbofuran(살충제), Thiobencarb(제초제)의 효과를 probit 분석법으로 조사하였다. 그 결과, Benomyl, Carbofuran, Thiobencarb의 농도에 의존하여 유생의 체장 길이는 감소하고 치사율과 기형율은 증가하였다. Benomyl, Carbofuran, Thiobencarb의 teratogenic concentration(EC50)은 각각 1.00, 0.58, 4.75mg/L을 나타내어 Carbofuran이 기형유발에 가장 민감하게 반응하였으며, embryo lethal concentrations(LC50)은 7.04, 28.71, 16.12mg/L을 나타내어 Benomyl이 가장 낮은 농도에 서 배아를 치사하는 것으로 나타났다. Teratogenic index(TI=LC50/EC50)는 Benomyl 7.04, Carbofuran 49.50, Thiobencarb 3.39를 나타내어 TI값이 모두 기형유발물질로 판단하는 기준인 1.5 이상을 나타내어 시험에 사용된 농약류 3종은 최기형성 물질로 판단되며 Carbofuran이 가장 강력한 최기형성물질로 작용함을 알 수 있었다.

Risk assessment traditionally are conducted on individual chemicals; however, humans are exposed to multiple chemicals in daily life. The organophosphotus (OP) pesticides are considered in a single risk assessment because they act by a common mechanism of toxicity, and there is likely to be expose to multiple OP pesticides simultaneously or sequentially. The OP pesticides act by inhibiting the enzyme acetylcholinesterase (AChE) and have available extensive database. AChE is widely distributed droughout the body, most importantly in the nervous system. Inhibition of AChE results in accumulation of acetylcholine in the nervous system that results in clinical signs of cholinergic toxicity, including increased salivation and lacrimation, nausea and vomiting, muscle fasciculation, lethargy and fatigue, among others. To conduct an exposure assessment for pesticides in the diet, we need to know the food consumption patterns of the population, and the pesticide residue levels in the foods that are consumed. This study was conducted to identify cumulative dietary risk due to multiple OP pesticides that can be exposed through various foods. Total 22 food samples including cereals, vegetables and fruits were collected randomly two times from food markets in several sites (4 cities). The subjected foods were selected by regarding of highly consumed foods to general Korean people. The 12 OP pesticides including Acephate, Azinphos-methyl, Chlorpyrifos, and Diazinon were monitored. For the exposure assessment, general adult group of 60 kg body weight was regarded as target population and food consumption data suggested by Lee et al. (2000) were used as consumed value of individual food Analyses of samples for OP pesticides have been carried out according to the multiclass multiresidue analysis method and acephate and methamidophos analysis method of Korea Food Code. In general the levels of OP pesticides found in the food samples were very low or not detected. The detected highest value was 0.282 ppm as methidathion in mandarin and acephate, chlorpyrifos, methamidophos and methidathion were detected in several foods. To quantify simultaneous exposure, toxic equivalency factor of proportionately corresponding potency giving decreased AChE activity on the basis of reference dose 0.3 ㎍/kg/day to the chlorpyrifos was applied. The estimated dietary daily intake of OP pesticide was 4.52 × 10^(-2) ㎍/kg/day as mean value. The hazard index (HI) is the sum for OP pesticides being considered together was 0.15. The HI less than 1 indicates the exposure may be lower than an acceptable level.

The analytical method for 16 organophosphorus pesticides was developed in this study. The 16 organophosphorus pesticides were analyzed by liquid chromatography-tandem mass spectrometry (LC/MS/MS) using on-line solid phase extraction (on-line SPE) with PLRP- S cartridge. Analysis of all analytes in the MS/MS was processed in the electrospray ioni-zation (ESI) positive mode. They are Azinphos ethyl, Chlorfenvinphos, Ethion, Famphur, Phosmet, Phosphamidon, Terbufos, Aspon, Chlorpyrifos-methyl, Crotoxyphos, Dichlofenthi-on, Dicrotophos, Fonofos, Thionazin, Dimethoate and Iprobenfos. Limits of detection (LODs) and Limits of quantification(LOQs) were obtained as 0.8~2.0 ng/L and 2.6~6.4 ng/L, respectively. All compounds were not detected at the 8 sampling points of the raw water and clean water.