Aquafluor藻细胞活体分析法在三峡库区次级河流回水区Chla测定中的校准及应用

从三峡库区次级河流大宁河、小江、汤溪河及梅溪河139m回水区中段采集水样,经实验室培养后,用丙酮萃取分光光度法和Aquafluor藻细胞活体分析法测定Chla浓度.通过对Chla萃取值(y)和活体值(x)进行回归分析,得到其回归方程为y=4.15x 2.48,t检验显示回归方程具有线性.在库区次级河流139m回水区富营养化监测中,Chla模拟值与萃取值基本吻合,相对误差＜±7%,故可以采用Chla模拟值对水体富营养化程度进行评价.     

罗丹明染料荧光猝灭法分别测定痕量二氧化氯和亚氯酸根

在碱性条件下,ClO2氧化罗丹明染料发生荧光猝灭可选择性地测定ClO2的含量,而ClO2-不干扰测定;在酸性条件下可测量ClO2与ClO2-共同产生的荧光猝灭强度,利用差减法可求出ClO2-的含量.对于罗丹明S,罗丹明G,罗丹明B及丁基罗丹明B四体系,ClO2浓度分别在0.00840-0.53μg·ml-1,0.0930-3.15μg·ml-1,0.215-2.610μg·ml-1及0.0825-1.096μg·ml-1范围内,与四体系的荧光猝灭强度呈线性关系;亚氯酸根浓度分别在0.00950-0.711μg·ml-1,0.0940-2.36μg·ml-1,0.473-4.73μg·ml-1及0.473-2.36μg·ml-1范围内,与四体系的荧光猝灭强度呈线性关系.另外,选择罗丹明S荧光猝灭法分别测定了饮用水中ClO2及ClO2-,获得了满意的结果.     

4-硝基苯胺与人血清白蛋白相互作用的研究

通过荧光和紫外光谱法研究了4-硝基苯胺与人血清白蛋白（HSA）的作用.结果表明,4-硝基苯胺对HSA的内源荧光具有强烈的猝灭作用.猝灭机理为静态猝灭,同时伴随有非辐射能量转移的发生.根据双对数方程计算其结合常数和结合位点数.确定4-硝基苯胺与HSA有一类结合部位.根据热力学参数得出4-硝基苯胺与HSA之间的主要作用力为氢键和疏水作用力.同步荧光的结果表明,作用点位靠近色氨酸,并且使色氨酸的疏水环境增强.     

荧光分光光度法测定土壤中石油类

建立了荧光分光光度法测定土壤中石油类.方法检出限为3 mg/kg,实际土壤加标回收率为95.5％ ～108％,精密度(RSD,n=6)为2.4％ ～8.7％.实验结果表明,该方法准确可靠、灵敏度高、选择性好、操作简便,与红外分光光度法有较好的可比性,满足土壤中石油类分析要求.     

流动注射催化光度法测定环境水样中的痕量亚硝酸根

基于在pH为2.7的一氯乙酸缓冲溶液中亚硝酸根对溴酸钾氧化亮绿具有催化作用,建立了测定环境水样中痕量亚硝酸根的流动注射催化光度法。在室温下,当溴酸钾浓度为0.15mol/L、亮绿溶液浓度为1.12×10-3mol/L时,该方法的线性范围为0.04～0.36mg/L,检出限为7.44×10-4mg/L,测定频率为60次/h,相对标准偏差为1.1%(n=11)。     

重金属离子存在下腐植酸和芘之间的相互作用

建立并验证了腐植酸(HA)和芘结合常数(Koc)测定的荧光猝灭法,进而研究了重金属离子对HA和芘相互作用的影响,测定了重金属离子存在下HA和芘之间的Koc.结果表明:纯化后的HA是分子质量较小的部分,水溶性较高,具有羟基、羧基和碳氧键等极性基团;HA利用其分子中的羟基、羧基、碳氧键等基团和重金属离子产生络合作用,这种络合作用影响了HA的结构;随着重金属离子浓度的增大,Koc遵循先增大,再减小,最后趋于不变的趋势.     

流动注射-氢化物发生-原子荧光光谱法测定土壤中铅

采用流动注射-氢化物发生-原子荧光光谱法测定土壤中的铅,工作曲线线性关系良好,检出限为0.25 mg/kg,相对标准偏差＜3.5%,加标回收率为93.0%～105%.该方法简便快速,测定结果准确可靠.     

原子吸收法测定土壤中铅的方法

通过湿法消解土壤样品,利用石墨炉原子吸收分光光度法(GAAS)和火焰原子吸收分光光度法(FAAS)测定不同土壤样品中铅的含量,以验证2种方法的有效性并加以对比。实验结果表明:2种方法均满足土壤中铅含量的测定要求,测定的标准土样含量均在标准值的不确定度范围内,GAAS方法测定结果更接近保证值。二者的相对标准偏差(RSD)值均低于1.5%,FAAS方法的精密度更高,且具有快速简单等优势。     

Spring leaf flush in aspen (Populus tremuloides) clones is altered by long-term growth at elevated carbon dioxide and elevated ozone concentration

Early spring leaf out is important to the success of deciduous trees competing for light and space in dense forest plantation canopies. In this study, we investigated spring leaf flush and how long-term growth at elevated carbon dioxide concentration ([CO₂]) and elevated ozone concentration ([O₃]) altered leaf area index development in a closed Populus tremuloides (aspen) canopy. This work was done at the Aspen FACE experiment where aspen clones have been grown since 1997 in conditions simulating the [CO₂] and [O₃] predicted for ∼2050. The responses of two clones were compared during the first month of spring leaf out when CO₂ fumigation had begun, but O₃ fumigation had not. Trees in elevated [CO₂] plots showed a stimulation of leaf area index (36%), while trees in elevated [O₃] plots had lower leaf area index (−20%). While individual leaf area was not significantly affected by elevated [CO₂], the photosynthetic operating efficiency of aspen leaves was significantly improved (51%). There were no significant differences in the way that the two aspen clones responded to elevated [CO₂]; however, the two clones responded differently to long-term growth at elevated [O₃]. The O₃-sensitive clone, 42E, had reduced individual leaf area when grown at elevated [O₃] (−32%), while the tolerant clone, 216, had larger mature leaf area at elevated [O₃] (46%). These results indicate a clear difference between the two clones in their long-term response to elevated [O₃], which could affect competition between the clones, and result in altered genotypic composition in future atmospheric conditions.     

Phytotoxicity of atrazine, isoproturon, and diuron to submersed macrophytes in outdoor mesocosms

The submersed macrophytes Elodea canadensis, Myriophyllum spicatum and Potamogeton lucens were constantly exposed over a five-week period to environmentally relevant concentrations of atrazine, isoproturon, diuron, and their mixture in outdoor mesocosms. Effects were evaluated investigating photosynthetic efficiency (PE) of the three macrophytes and growth of M. spicatum and E. canadensis. Adverse effects on PE were observed on days 2 and 5 after application. M. spicatum was found to be the more sensitive macrophyte. E. canadensis and P. lucens were less sensitive to atrazine, diuron and the mixture and insensitive to isoproturon. PE of M. spicatum was similarly affected by the single herbicides and the mixture demonstrating concentration addition. Growth of E. canadensis and M. spicatum was not reduced indicating that herbicide exposure did not impair plant development. Although PE measurements turned out to be a sensitive method to monitor PSII herbicides, plant growth remains the more relevant ecological endpoint in risk assessment.