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71.
A simple method for the quantitative gradient analysis of a xerotermic forest-margin ecotone is described. In this method, the mean value of the coefficient of similarity between all plots of the transect is used for estimating the rate of changes in species composition. Changes in the phytosociological spectrum are analyzed. The method adequately reflects trends in the displacement of forest species by forest-margin, steppe, and meadow species. 相似文献
72.
AFS-830型双道原子荧光光度计同时测定饮用水中砷、汞 总被引:1,自引:0,他引:1
主要探讨应用AFS-830型双道原子荧光光度计,在饮用水监测中同时测定水中砷、汞的方法和技术。此法是在硝酸介质,以硼氢化钠作还原剂,进行原子化,被测元素原子激发出荧光强度值在一定范围内与被测元素的浓度成正比。砷与汞的检出限分别为0.0618和0.0158ug/L。 相似文献
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Küster A Pohl K Altenburger R 《Environmental science and pollution research international》2007,14(6):377-383
Background, Goals and Scope During the last years the miniaturization of toxicity test systems for rapid and parallel measurements of large quantities
of samples has often been discussed. For unicellular algae as well as for aquatic macrophytes, fluorescence-based miniaturized
test systems have been introduced to analyze photosystem II (PSII) inhibitors. Nevertheless, high-throughput screening should
also guarantee the effect detection of a broad range of toxicants in order to ensure routinely applicable, high-throughput
measuring device experiments which can cover a broad range of toxicants and modes of action others than PSII inhibition. Thus,
the aim of this study was to establish a fast and reproducible measuring system for non-PSII inhibitors for aquatic macrophyte
species to overcome major limitations for use.
Methods A newly developed imaging pulse-amplitude-modulated chlorophyll fluorometer (I-PAM) was applied as an effect detector in short-term
bioassays with the aquatic macrophyte species Lemna minor. This multiwell-plate based measuring device enabled the incubation and measurement of up to 24 samples in parallel. The
chemicals paraquat-dichloride, alizarine and triclosan were chosen as representatives for the toxicant groups of non-PSII
herbicides, polycyclic aromatic hydrocarbons (PAHs) and pharmaceuticals and personal care products (PPCPs), which are often
detected in the aquatic environment. The I-PAM was used (i) to establish and validate the sensitivity of the test system to
the three non-PSII inhibitors, (ii) to compare the test systems with standardized and established biotests for aquatic macrophytes,
and (iii) to define necessary time scales in aquatic macrophyte testing. For validation of the fluorescence-based assay, the
standard growth test with L. minor (ISO/DIS 20079) was performed in parallel for each chemical.
Results The results revealed that fluorescence-based measurements with the I-PAM allow rapid and parallel analysis of large amounts
of aquatic macrophyte samples. The I-PAM enabled the recording of concentration-effect-curves with L. minor samples on a 24-well plate with single measurements. Fluorescence-based concentration-effect-curves could be detected for
all three chemicals after only 1 h of incubation. After 4–5 h incubation time, the maximum inhibition of fluorescence showed
an 80–100% effect for the chemicals tested. The EC50 after 24 h incubation were estimated to be 0.06 mg/L, 0.84 mg/L and 1.69
mg/L for paraquatdichloride, alizarine and triclosan, respectively.
Discussion The results obtained with the I-PAM after 24 h for the herbicide paraquat-dichloride and the polycyclic aromatic hydrocarbon
alizarine were in good accordance with median effective concentrations (EC50s) obtained by the standardized growth test for
L. minor after 7 d incubation (0.09 mg/L and 0.79 mg/L for paraquat-dichloride and alizarine, respectively). Those results were in
accordance with literature findings for the two chemicals. In contrast, fluorescence-based EC50 of the antimicrobial agent
triclosan proved to be two orders of magnitude greater when compared to the standard growth test with 7 d incubation time
(0.026 mg/L) as well as with literature findings.
Conclusion Typically, aquatic macrophyte testing is very time consuming and relies on laborious experimental set-ups. The I-PAM measuring
device enabled fast effect screening for the three chemicals tested. While established test systems for aquatic macrophytes
need incubation times of ≥ 7 d, the I-PAM can detect inhibitory effects much earlier (24 h), even if inhibition of chemicals
is not specifically associated with PSII. Thus, the fluorescence-based bioassay with the I-PAM offers a promising approach
for the miniaturization and high-throughput testing of chemicals with aquatic macrophytes. For the chemical triclosan, however,
the short-term effect prediction with the I-PAM has been shown to be less sensitive than with long-term bioassays, which might
be due to physicochemical substance properties such as lipophilicity.
Recommendations and Perspectives The results of this study show that the I-PAM represents a promising tool for decreasing the incubation times of aquatic macrophyte
toxicity testing to about 24 h as a supplement to existing test batteries. The applicability of this I-PAM bioassay on emergent
and submerged aquatic macrophyte species should be investigated in further studies. Regarding considerations that physicochemical
properties of the tested substances might play an important role in microplate bioassays, the I-PAM bioassay should either
be accompanied by evaluating physicochemical properties modeled from structural information prior to an experimental investigation,
or by intensified chemical analyses to identify and determine nominal concentrations of the toxicants tested. The chemicals
paraquat-dichloride, alizarine and triclosan were chosen as representatives for the toxicant groups of non-PSII herbicides,
PAHs and PPCPs which are often detected in the aquatic environment. Nevertheless, in order to ensure a routinely applicable
measuring device, experiments with a broader range of toxicants and samples of surface and/or waste waters are necessary.
ESS-Submission Editor: Dr. Markus Hecker (MHecker@Entrix.com) 相似文献
76.
The submerged macrophyte Potamogeton crispus L. was subjected to varying doses of cadmium (0, 20, 40, 60 and 80 μM) for 7 d, and the plants were analyzed for subcellular distribution of Cd, accumulation of mineral nutrients, photosynthesis, oxidative stress, protein content, and ultrastructural distribution of calcium (Ca). Leaf fractionation by differential centrifugation indicated that 48-69% of Cd was accumulated in the cell wall. At all doses of Cd, the levels of Ca and B rose and the level of Mn fell; the levels of Fe, Mg, Zn, Cu, Mo, and P rose initially only to decline later. Exposure to Cd caused oxidative stress as evident by increased content of malondialdehyde and decreased contents of chlorophyll and protein. Photosynthetic efficiency, as indicated by the quenching of chlorophyll a fluorescence (Fv/Fm, Fo and Fm), decreased significantly, the extent of decrease being directly proportional to the concentration of Cd. Increased amounts of precipitates of calcium were noticed in the treated plants, located either outside the cell membrane or in chloroplasts, mitochondria, the nucleus, and the cytoplasm whereas control plants showed small deposits of the precipitates around surface of the vacuole membrane and in the intercellular space but rarely in the cytoplasm. Photosynthetic efficiency and oxidative stress could be used as indicators of physiological end-points in determining the extent of Cd phytotoxicity. 相似文献
77.
煤的低温氧化实验研究及红外光谱分析 总被引:7,自引:0,他引:7
对不同温度下的氧化煤样通过红外光谱分析其微观结构及特征,得到煤样在不同低温氧化阶段的基团变化,从微观角度掌握煤样氧化过程的变化规律.通过对唐口煤矿1302工作面煤样的低温氧化和红外光谱分析,得到唐口煤矿煤样在低温氧化阶段的自燃倾向性和氧化过程中微观结构的变化规律,该成果为制定矿井内火灾的防治技术提供了科学依据. 相似文献
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79.
苏通大桥结构健康状态评估技术研究与应用(2):主梁损伤预警 总被引:1,自引:0,他引:1
为了建立"环境因素归一化"的苏通大桥主梁损伤预警方法,本文对苏通大桥主梁240天的小波包能量谱与温度实测数据进行了季节相关性研究。分析结果表明,苏通大桥主梁的小波包能量谱与温度具有明显的季节相关性,其特征频带能量比的日平均值,随着温度的季节变化在一年中可以发生平均约200%的变化。在此基础上,采用6次多项式模型对小波包能量谱—温度进行了统计建模,并采用均值控制图法对特征频带能量比的异常变化进行了统计模式识别。结果表明,运用本文方法可以有效地消除温度的季节变化对斜拉桥实测小波包能量谱的影响,较好地识别出结构损伤引起的特征频带能量比10%的异常变化,适合于苏通大桥主梁的实时在线监测。 相似文献
80.