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논문 기본 정보

자료유형
학술저널
저자정보
Dahee Song (National Institute of Environmental Research) Sunhwa Park (National Institute of Environmental Research) Sang-Ho Jeon (National Institute of Environmental Research) Ki-In Kim (Mokpo National University) Jong Yeon Hwang (National Institute of Environmental Research) Moonsu Kim (National Institute of Environmental Research) Hun-Je Jo (National Institute of Environmental Research) Deok-hyun Kim (National Institute of Environmental Research) Gyeong-Mi Lee (National Institute of Environmental Research) Hye-Jin Kim (National Institute of Environmental Research) Tae-Seung Kim (National Institute of Environmental Research) Hyen Mi Chung (National Institute of Environmental Research) Hyun-Koo Kim (National Institute of Environmental Research)
저널정보
한국토양비료학회 한국토양비료학회지 한국토양비료학회지 제50권 제5호
발행연도
2017.10
수록면
434 - 451 (18page)

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초록· 키워드

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For this study, groundwater samples for 3 years from 2011 through 2013 were collected at 106 groundwater monitoring site in Korea. These groundwater samples were analyzed for 13 pesticides such as cabofuran, pentachlorobenzene, hexachlorobenzene, simazine, atrazine, lindane (gamma-HCH), alachlor, heptachlor, chlordane (total), endosulfan (1, 2), dieldrin, endrin, 4,4-DDT. The objectives of this study were to determine the detection frequency and their concentrations of 13 pesticides and evaluate the health risk level considering ingestion, inhalation, and skin contact using concentrations of 13 pesticides in groundwater samples. An analysis was used for the simultaneous determination for 13 pesticides using GC-MS. GC-MS was performed on HP-5ms, using helium (1 ml min<SUP>-1</SUP>) as carrier gas. The average recoveries of the pesticides were from 92.8% to 120.8%. The limits of detection (LODs) were between 0.004 μg L<SUP>-1</SUP> and 0.118 μg L<SUP>-1</SUP> and the limits of quantification (LOQs) were between 0.012 μg L<SUP>-1</SUP> and 0.354 μg L<SUP>-1</SUP>. 106 groundwater wells were selected. 54 wells were from well to monitor background groundwater quality and 52 wells were from well to monitor groundwater quality in industrial or contamination source area. Eight pesticides including pentachlorobenzene, lindane (Gamma-HCH), heptachlor, chlordane (total), Endosulfan (1, 2), dieldrin, endrin, and 4,4-DDT were not detected in groundwater samples. The detection frequency for hexachlorobenzene, alachlor, carbofuran and simazine was 23.4%, 11.4%, 7.3%, and 1.0%, respectively. Atrazine was detected once in 2011. The average concentrations were 0.00423 μg L<SUP>-1</SUP> for carbofuran, 0.000243 μg L<SUP>-1</SUP> for alachlor, 0.00015 μg L<SUP>-1</SUP> for simazine, and 0.00001 μg L<SUP>-1</SUP> for hexachlorobenzene. The detection frequency of hexachlorobenzene was high, but the average concentration was low. In the contaminated groundwater, the detection frequency for hexachlorobenzene, alachlor, carbofuran, simazine and atrazine was 26.1%, 21.3%, 7.1%, 1.9% and 0.3%, respectively. In the uncontaminated groundwater, detection frequency for hexachlorobenzene, carbofuran and alachlor were 20.2%, 7.5%, and 1.9% respectively. Simazine and atrazine were not detected at uncontaminated groundwater wells. According to the purpose of groundwater use, atrazine was detected for agricultural groundwater use. Hexachlorobenzene showed high detection frequency at agricultural groundwater use area where the animal feeding area and golf course area were located. Alachlor showed more than 50% detection frequency at cropping area, pollution concern river area, and golf course area. Atrazine was detected in agricultural water use area. By land use, the maximum detection frequency of alachlor was found near an orchard. For human risk assessment, the cancer risk for the 5 pesticides was between 10<SUP>-7</SUP> and 10<SUP>-10</SUP>, while the non-cancer risk (HQ value) was between 10<SUP>-4</SUP> and 10<SUP>-6</SUP>. For conclusion, these monitoring study needs to continue because of the possibility of groundwater contamination based on various purpose of groundwater use.

목차

ABSTRACT
Introduction
Materials and Methods
Conclusions
References

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UCI(KEPA) : I410-ECN-0101-2018-523-001420112