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231222s2003 xx ||||| 00| ||eng c |
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|a pubmed25n0420.xml
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|a (NLM)12830940
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|a DE-627
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|c DE-627
|e rakwb
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|a eng
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|a Tabata, A
|e verfasserin
|4 aut
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|a The effect of chlorination of estrogenic chemicals on the level of serum vitellogenin of Japanese medaka (Oryzias latipes)
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|c 2003
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|a Text
|b txt
|2 rdacontent
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|a ohne Hilfsmittel zu benutzen
|b n
|2 rdamedia
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|b nc
|2 rdacarrier
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|a Date Completed 07.10.2003
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|a Date Revised 21.11.2013
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|a published: Print
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|a Citation Status MEDLINE
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|a Mature male medaka were continually exposed to four chemicals, p-n-nonylphenol (p-n-NP), nonylphenol (p-NP), bisphenol-A (BPA) and 17beta-estradiol (E2) to evaluate their estrogenic activities in the laboratory. In order to understand the effect of the chlorination that is applied widely in water and wastewater treatment, the above chemicals were chlorinated and then exposed to mature male medaka. Furthermore, in the case of vitellogenin, a is a female specific protein induced by the exposure to test waters containing the above chemicals after 5 weeks, medaka was returned to uncontaminated tap water to determine whether male medaka have a self recovery function from the effect of estrogenic chemicals. Much greater vitellogenin compared to the background levels were induced in the male medaka by separate exposure to 100 microg/L of p-NP, 1,000 microg/L of BPA and 0.05 microg/L of E2. The levels of vitellogenin increased with increasing exposure periods. The relative potencies of these chemicals descended in the order of E2>>p-NP>BPA. Vitellogenin levels inducible by these chemicals were drastically reduced as a result of the chlorination for 24 hours. However, a moderate increase in hepatocyte somatic index (HSI) meant the hepatic fatness was observed as a result of chlorination. It is not clear at this stage whether or not the formation of chlorination byproducts is responsible for this moderate increase in HSI. The vitellogenin concentration of male medaka exposed to chemicals for 5 weeks decreased gradually after return to the uncontaminated water. However, the vitellogenin concentration did not return to the initial normal levels even after 5 weeks. A clear relationship between the serum vitellogenin concentration and the hepatic vitellogenin concentration was also found. Since quantitative analytical procedures for hepatic vitellogenin are easier than those of the serum vitellogenin, measuring the estrogenic effect using the measurement of vitellogenin in liver is recommended
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|a Journal Article
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|a Chlorine Compounds
|2 NLM
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|a Phenols
|2 NLM
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7 |
|a Vitellogenins
|2 NLM
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| 650 |
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7 |
|a Water Pollutants, Chemical
|2 NLM
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| 650 |
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|a Estradiol
|2 NLM
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|a 4TI98Z838E
|2 NLM
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|a Miyamoto, N
|e verfasserin
|4 aut
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|a Ohnishi, Y
|e verfasserin
|4 aut
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| 700 |
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|a Itoh, M
|e verfasserin
|4 aut
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| 700 |
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|a Yamada, T
|e verfasserin
|4 aut
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|a Kamei, T
|e verfasserin
|4 aut
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| 700 |
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|a Magara, Y
|e verfasserin
|4 aut
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| 773 |
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|i Enthalten in
|t Water science and technology : a journal of the International Association on Water Pollution Research
|d 1986
|g 47(2003), 9 vom: 09., Seite 51-7
|w (DE-627)NLM098149431
|x 0273-1223
|7 nnas
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| 773 |
1 |
8 |
|g volume:47
|g year:2003
|g number:9
|g day:09
|g pages:51-7
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|a GBV_USEFLAG_A
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|a AR
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| 952 |
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|d 47
|j 2003
|e 9
|b 09
|h 51-7
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