中国环境科学
中國環境科學
중국배경과학
CHINA ENVIRONMENTAL SCIENCE
2001年
1期
4-7
,共4页
铜%斜生栅藻%蛋白核小球藻%月形藻%毒性
銅%斜生柵藻%蛋白覈小毬藻%月形藻%毒性
동%사생책조%단백핵소구조%월형조%독성
运用评价化学品对藻类毒性的标准实验方法,根据实验结果采用机率单位法进行数据处理,分别得出铜抑制蛋白核小球藻(Chlorella pyrenoidosa),斜生栅藻(Scenedesmus obliquus),月形藻(Closterium lunula)生长的96h半效应浓度(96h-EC50)分别为67,51,202mg/L,并对各剂量反应方程进行X2检验,结果表明均符合精度要求,计算出的96h-EC50真实可靠.研究结果表明, 斜生栅藻对铜最敏感,而月形藻对铜有很强的抵抗能力.这3种藻类对铜敏感度由大到小的顺序为斜生栅藻、蛋白核小球藻、月形藻.不同藻种细胞的大小不同和藻细胞壁表面的含硫基团不同是导致藻类对铜敏感性不同的主要原因.
運用評價化學品對藻類毒性的標準實驗方法,根據實驗結果採用機率單位法進行數據處理,分彆得齣銅抑製蛋白覈小毬藻(Chlorella pyrenoidosa),斜生柵藻(Scenedesmus obliquus),月形藻(Closterium lunula)生長的96h半效應濃度(96h-EC50)分彆為67,51,202mg/L,併對各劑量反應方程進行X2檢驗,結果錶明均符閤精度要求,計算齣的96h-EC50真實可靠.研究結果錶明, 斜生柵藻對銅最敏感,而月形藻對銅有很彊的牴抗能力.這3種藻類對銅敏感度由大到小的順序為斜生柵藻、蛋白覈小毬藻、月形藻.不同藻種細胞的大小不同和藻細胞壁錶麵的含硫基糰不同是導緻藻類對銅敏感性不同的主要原因.
운용평개화학품대조류독성적표준실험방법,근거실험결과채용궤솔단위법진행수거처리,분별득출동억제단백핵소구조(Chlorella pyrenoidosa),사생책조(Scenedesmus obliquus),월형조(Closterium lunula)생장적96h반효응농도(96h-EC50)분별위67,51,202mg/L,병대각제량반응방정진행X2검험,결과표명균부합정도요구,계산출적96h-EC50진실가고.연구결과표명, 사생책조대동최민감,이월형조대동유흔강적저항능력.저3충조류대동민감도유대도소적순서위사생책조、단백핵소구조、월형조.불동조충세포적대소불동화조세포벽표면적함류기단불동시도치조류대동민감성불동적주요원인.
A standard test method for evaluating the toxicity of chemicals to algae was applied; and 96h-EC50 of copper on inhibition of the growths of Chlorella pyrenoidosa, Scenedesmus obliquus, Closterium lunula were calculated as 67,51 and 202mg/L respectively using the method of probability unit for data treatment based on the test results. The results from the X2 test of each dose-response equations showed that 96h-EC50s calculated were all precise and credible. It was found that S. obliquus was most sensitive to copper but C. lunula had a strong resistibility to copper. The toxicities of copper on inhibition of the growths are different. The order of algae sensibility to copper was: S. obliquus>C. pyrenoi-dosa>C. lunula. The different volumes of cells of different species of algae and the different amounts of functional groups containing sulfur on algae surface were the main cause for the different sensitivity of algae to copper.