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博碩士論文 etd-0905111-214512 詳細資訊
Title page for etd-0905111-214512
論文名稱
Title
多環麝香與雙酚A對浴用海綿(Spongia ceylonensis)幼生著苗及變態之影響
Effects of polycyclic musks and bisphenol A on the settlement and metamorphosis on sponge, Spongia ceylonensis
系所名稱
Department
畢業學年期
Year, semester
語文別
Language
學位類別
Degree
頁數
Number of pages
63
研究生
Author
指導教授
Advisor
召集委員
Convenor
口試委員
Advisory Committee
口試日期
Date of Exam
2011-08-22
繳交日期
Date of Submission
2011-09-05
關鍵字
Keywords
雙酚A、浴用海綿、幼生、著苗、變態、多環麝香
larvae, Spongia ceylonensis, settlement, metamorphosis, acetone, bisphenol A, polycyclic musk
統計
Statistics
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The thesis/dissertation has been browsed 5694 times, has been downloaded 676 times.
中文摘要
海綿族群大小部分依賴幼生的入添來維持,但海綿幼生著苗不只會受
到環境物理因素的影響,化學因子或是汙染也都會有影響。本研究以澎湖
潮間帶常見的浴用海綿(Spongia ceylonensis)為研究物種,探討多環麝香
(HHCB 與AHTN)與bisphenol A(BPA)對海綿幼生著苗與變態之影響。
研究內容包含,(1)半致死濃度測試,(2)有機溶劑(acetone)與多環麝
香或BPA 對海綿幼生著苗與變態影響,(3)HHCB、AHTN 與BPA 對海
綿幼生著苗與變態影響。半致死濃度實驗之HHCB 與AHTN 對海綿幼生
96 h - LC50 皆大於1.00 mg/L,而BPA 的96 h - LC50 為0.58 mg/L。有機溶
劑實驗結果顯示,1.00 mg/L acetone 對海綿幼生的著苗與變態並沒有影
響。海綿幼生在HHCB 或AHTN 濃度0.12、0.25、0.50 與1.00 mg/L 下,
著苗率與變態率沒有顯著差異(p > 0.05),但在BPA 濃度1.00 mg/L 下,
著苗率顯著下降20 %(p < 0.05),在濃度0.50 與1.00 mg/L 下,變態率也
分別下降20 %與80 %(p < 0.05)。在兩個多環麝香對海綿幼生毒性比較
的結果顯示,AHTN 對海綿幼生著苗的影響較HHCB 大。
Abstract
Sponge population partly depends on larval recruitment. Environmental
factors, e.g. light, salinity, pH and temperature, chemical factors and pollution
may influence larval settlement and metamorphosis. In this study, the effects
of galaxolide(HHCB)、tonalide(AHTN)and bisphenol A(BPA)on the
settlement and metamorphosis of an intertidal sponge (Spongia ceylonensis)
were examined. The experiments included LC50 test, effects of solvent,
HHCB, AHTN and BPA on sponge settlement and metamorphosis. In the
LC50 tests, the 96 hr–LC50 value of HHCB and AHTN all greater than 1.00
mg/L, and the 96 hr–LC50 of BPA was 0.58 mg/L. Acetone concentration
(1.00 mg/L ) in this study didn’t affect sponge settlement and metamorphosis.
Effect of HHCB and AHTN on sponge settlement and metamorphosis
concentrations of 0.13, 0.25, 0.50 and 1.00 mg/L was insignificant. In
contrast, the settlement rate was decrease by 20 % at treatment of 1.00 mg/L
BPA. The metamorphosis rates were also decrease by 20 % and 80 % at
concentrations of 0.50 mg/L and 1.00 mg/L BPA. In conclusion, the toxicity
of AHTN was greater than that of HHCB to sponge settlement and
metamorphosis.
目次 Table of Contents
謝辭 .............................................................................................................................. i
中文摘要 ...................................................................................................................... ii
Abstract ....................................................................................................................... iii
目錄 ............................................................................................................................. iv
表目錄 ......................................................................................................................... v
圖目錄 ......................................................................................................................... vi
前言 ............................................................................................................................. 1
材料與方法 .................................................................................................................. 6
結果 ............................................................................................................................. 9
討論 ............................................................................................................................ 21
參考文獻 ..................................................................................................................... 26
表 ................................................................................................................................ 33
圖 ................................................................................................................................ 38

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