야외에서 채집한 C. plumosus를 대상으로 잠재적 내분비계 교란물질인 DEHP, BPA 및 Tebufenozide를 처리 물질로 하여 형태적인 교란 효과를 살펴보았다. 약제에 노출된 개체의 하순기절은 부드러워...
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https://www.riss.kr/link?id=A45041361
2005
Korean
472.5
KCI등재
학술저널
11-17(7쪽)
3
0
상세조회0
다운로드국문 초록 (Abstract)
야외에서 채집한 C. plumosus를 대상으로 잠재적 내분비계 교란물질인 DEHP, BPA 및 Tebufenozide를 처리 물질로 하여 형태적인 교란 효과를 살펴보았다. 약제에 노출된 개체의 하순기절은 부드러워...
야외에서 채집한 C. plumosus를 대상으로 잠재적 내분비계 교란물질인 DEHP, BPA 및 Tebufenozide를 처리 물질로 하여 형태적인 교란 효과를 살펴보았다. 약제에 노출된 개체의 하순기절은 부드러워지거나(smooth) 손실(loss)이 가장 많았으며 엷은 갈색을 보였다. 처리 물질에 따른 기형의 정도를 살펴보면, DEHP는 46.2~85.7%, BPA는 73.7 ~90.9% 그리고 tebufenozide는 57.6~78.9%가 기형을 입어 BPA>tebufenozide>DEHP순으로 기형이 크게 나타났다. 처리 물질별 기형 부위를 살펴보면, MIX(32~46%)>MLT(25~34%)>LT(3~7%)로 두 부분이 함께 기형을 입는 형태가 가장 많았으며 LT단독의 기형이 가장 적었다 MIX형태로 기형이 가장 높은 물질은 BPA (46%) > DEHP(33%) > tebufenozide (32%)이고, MLT에 가장 높은 기형을 보인 것은 DEHP(34%) > tebufenozide (31%)>BPA(25%)로 나타났다.
Tebufenozide처리에 따른 하순기절의 색은 처리 농도가 높아지면 엷은 갈색 하순기절의 발생 빈도가 증가되었다(27.8~84.2%). 반면, BPA(8.7%)와 DEHP (18.2%)는 1 ㎍L^(-1)에서 가장 낮은 엷은 갈색의 하순기절의 발생 빈도를 보였으나 0.3㎍L^(-1)처리에서는 매우 높은 엷은 갈색의 하순기절이 다수 발생하였다(BPA 52.6%; DEHP 30.8%).
다국어 초록 (Multilingual Abstract)
Egg masses of C. plumosus were collected from Jungnang Stream in Seoul and reared in an incubator chamber. The larvae of C. plumosus were treated with potential endocrine disruption chemicals (EDCs) such as Diethylhexyl phthalate (DEHP), Bisphenol A (...
Egg masses of C. plumosus were collected from Jungnang Stream in Seoul and reared in an incubator chamber. The larvae of C. plumosus were treated with potential endocrine disruption chemicals (EDCs) such as Diethylhexyl phthalate (DEHP), Bisphenol A (BPA) and Tebufenozide, and the effects of morphological abnormalities were observed. The deformities of the mentum following exposure to EDCs showed the smooth/round tooth, the loss of 1 tooth, reduced median lateral teeth (MLT) and light brown color. The incidence rates of the mentum deformity were associated with chemicals: BPA (73.7~90.9%)>tebufenozide (57.6~78.9%) > DEHP (46.2~85.7%). The deformity type of the mentum showed MIX (MLT+LT, 32 46%) > MLT (25~34%) > LT (lateral teeth, 3~7%). Also, the incidence of MIX type was in the order of BPA (46%) > DEHP (33%) > tebufenozide (32%), and that of MLT type showed DEHP (34%) > tebufenozide (31%) > BPA (25%).
As the concentration of Tebufenozide increased, the incidence of light brown mentum was dose dependent. While the incidences of light brown mentum following exposure to BPA and DEHP were not associated with their concentrations.
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1 "국립환경연구원 내분비계장애물질 측정분석방법" 2002
2 "Trace nutrient deficiencyin Daphnia magna cultured in standard medium fortoxicity testing; effects of the optimization of cultureconditions on life history parameters of Daphnia magna" 1157-1167, 1990
3 "Toxicity of 4-nonylphenol in a life-cycle test with the midge Chironomus tentans." 38 : 155-160, 1997
4 "Toxicity and bioaccumulation of 2 8-tetrachlorodibenzo-p-dioxin in long-term testswith the freshwater benthic invertebrates Chironomustentans and Lumbriculus variegatus" 16 : 1287-1294, 1997
5 "Thein situ relationship between sediment concentrations ofmicropollutants and morphological deformities inChironomus thummi larvae from genes to ecosystems Commonwealth ScientificThe Mentum Deformity of C" 1995
6 "The occurrence ofcharacteristic deformities in the chrononmid larvae ofseveral Canadian lakes" 363-368, 1971
7 "The effect of phthalate esterplasticisers on the emergence of the midge" 32 : 2177-2187, 1996
8 "The concentration of cadmium copper and zinc in Chironomus gr" dipteachiro (dipteachiro): 141-239 149, 1992
9 "Teratogensin the Niagara River watershed as reflected by chironomid" 24 : 47-79, 1990
10 "Persistence of tebufenozide inaquatic ecosystems under laboratory and field conditions" 7-20, 1997
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19 "Gamete viability as anindicator of reproductive endocrine disruption in fish" 233 : 123-129, 1999
20 "Field and experimentalmorphological response of Chironomus larvae" Nematocera 47 : 227-239, 1997
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학술지 이력
연월일 | 이력구분 | 이력상세 | 등재구분 |
---|---|---|---|
2022 | 평가예정 | 계속평가 신청대상 (계속평가) | |
2021-12-01 | 평가 | 등재후보로 하락 (재인증) | ![]() |
2018-01-01 | 평가 | 등재학술지 유지 (등재유지) | ![]() |
2015-01-01 | 평가 | 등재학술지 유지 (등재유지) | ![]() |
2013-03-20 | 학술지명변경 | 한글명 : 한국하천호수학회지 -> 생태와 환경외국어명 : Korean Journal of Limnology -> Korean Journal of Ecology and Environment | ![]() |
2011-01-01 | 평가 | 등재학술지 유지 (등재유지) | ![]() |
2009-01-01 | 평가 | 등재학술지 유지 (등재유지) | ![]() |
2008-02-21 | 학회명변경 | 한글명 : 한국육수학회 -> 한국하천호수학회 | ![]() |
2008-02-21 | 학술지명변경 | 한글명 : 한국육수학회지 -> 한국하천호수학회지 | ![]() |
2008-01-24 | 학술지명변경 | 한글명 : 한국육수학회지 -> 한국하천호수학회지 | ![]() |
2007-01-01 | 평가 | 등재학술지 유지 (등재유지) | ![]() |
2005-01-01 | 평가 | 등재학술지 유지 (등재유지) | ![]() |
2002-01-01 | 평가 | 등재학술지 선정 (등재후보2차) | ![]() |
1999-07-01 | 평가 | 등재후보학술지 선정 (신규평가) | ![]() |
학술지 인용정보
기준연도 | WOS-KCI 통합IF(2년) | KCIF(2년) | KCIF(3년) |
---|---|---|---|
2016 | 0.54 | 0.54 | 0.54 |
KCIF(4년) | KCIF(5년) | 중심성지수(3년) | 즉시성지수 |
0.52 | 0.47 | 0.719 | 0.42 |