以大豆(Glycine max (L.) Merrill)黄化苗为材料,通过优化提取线粒体DNA(mtDNA)时差速离心过程中的离心力和离心时间,以及纯化过程中设置不同的蔗糖密度梯度和裂解液浓度,结合高盐法去除蛋白质,改良大豆mtDNA的提取方法。结果表明,该方...以大豆(Glycine max (L.) Merrill)黄化苗为材料,通过优化提取线粒体DNA(mtDNA)时差速离心过程中的离心力和离心时间,以及纯化过程中设置不同的蔗糖密度梯度和裂解液浓度,结合高盐法去除蛋白质,改良大豆mtDNA的提取方法。结果表明,该方法提取的mtDNA浓度和纯度较高,无叶绿体和核基因组DNA的污染,可用于后续大豆线粒体基因组的相关研究。展开更多
An intensive investigation was conducted to study the distribution of polycyclic aromatic hydrocarbons （PAHs）, to show firstly the level of pollution in the agricultural areas and analyses specifically the status of...An intensive investigation was conducted to study the distribution of polycyclic aromatic hydrocarbons （PAHs）, to show firstly the level of pollution in the agricultural areas and analyses specifically the status of soil polluted by these persistent pollutants in some locations of Xiamen region. Soil samples collected from Jiulong agricultural catchment have been analysed for 16 PAH compounds, using gas chromatography flame ionization detection in order to determine the level of selected PAH components and to identify the factors that may control their distribution and persistence in the area. The main PAHs found in soil samples were the low molecular weight. The total PAHs detected in soil samples ranged from 0.50 to 0.95 μg/g soil. The highest values of PAHs were significantly detected in the orange tree leaves, which range from 236.1 to 249.3 μg/g soil showing recent atmospheric inputs of these volatile pollutants. The distribution of PAHs in vegetable were monitored and indicating that the concentration were high and ranged from 8.24 to 58.87 μg/g. Other sediment samples were also collected and analysed from urban sewage （5.26 μg/g dw）, aquacultural （0.52 μg/g dw） and industrial areas （from 0.62 to 2.09 μg/g dw）, during this investigation. The contamination of Jiulong river estuary and Xiamen Western Sea by PAHs has been then widely justified by wastcwatcr discharges and soil runoffs from these areas. The results, therefore, provide important information on the current contamination status caused by the atmospheric transport and point to the need for urgent actions to stop the release of these hydrocarbons to the environment. The necessity of implementing systematic monitoring of PAHs is also emphasized.展开更多
文摘以大豆(Glycine max (L.) Merrill)黄化苗为材料,通过优化提取线粒体DNA(mtDNA)时差速离心过程中的离心力和离心时间,以及纯化过程中设置不同的蔗糖密度梯度和裂解液浓度,结合高盐法去除蛋白质,改良大豆mtDNA的提取方法。结果表明,该方法提取的mtDNA浓度和纯度较高,无叶绿体和核基因组DNA的污染,可用于后续大豆线粒体基因组的相关研究。
文摘An intensive investigation was conducted to study the distribution of polycyclic aromatic hydrocarbons （PAHs）, to show firstly the level of pollution in the agricultural areas and analyses specifically the status of soil polluted by these persistent pollutants in some locations of Xiamen region. Soil samples collected from Jiulong agricultural catchment have been analysed for 16 PAH compounds, using gas chromatography flame ionization detection in order to determine the level of selected PAH components and to identify the factors that may control their distribution and persistence in the area. The main PAHs found in soil samples were the low molecular weight. The total PAHs detected in soil samples ranged from 0.50 to 0.95 μg/g soil. The highest values of PAHs were significantly detected in the orange tree leaves, which range from 236.1 to 249.3 μg/g soil showing recent atmospheric inputs of these volatile pollutants. The distribution of PAHs in vegetable were monitored and indicating that the concentration were high and ranged from 8.24 to 58.87 μg/g. Other sediment samples were also collected and analysed from urban sewage （5.26 μg/g dw）, aquacultural （0.52 μg/g dw） and industrial areas （from 0.62 to 2.09 μg/g dw）, during this investigation. The contamination of Jiulong river estuary and Xiamen Western Sea by PAHs has been then widely justified by wastcwatcr discharges and soil runoffs from these areas. The results, therefore, provide important information on the current contamination status caused by the atmospheric transport and point to the need for urgent actions to stop the release of these hydrocarbons to the environment. The necessity of implementing systematic monitoring of PAHs is also emphasized.
