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931.
UPLC-线性离子阱串联质谱法测定水中新烟碱类杀虫剂 总被引:1,自引:0,他引:1
水样经离心后,采用直接进样超高效液相色谱线性离子阱串联质谱法快速测定水中9种新烟碱类杀虫剂.试验表明,该方法在20.0 ng/L~200 ng/L范围内线性良好,方法检出限为2.9 ng/L~8.4 ng/L,实际水样的加标回收率为81.2% ~109%,测定6次结果的RSD为4.1% ~13.9%,基质效应不明显.将... 相似文献
932.
采用溶剂热法合成了金属有机骨架材料UiO-66。通过XRD、SEM、FTIR对其进行了表征。考察了UiO-66对溶液中NO_3~-的吸附性能。实验结果表明,加入冰乙酸作调节剂后,得到的UiO-66晶体形貌均匀,直径在100nm左右,结晶度更好。在初始溶液pH为5、反应温度为30℃的条件下,UiO-66吸附NO_3~-反应90 min后,吸附达到平衡,平衡吸附量为39.67 mg/g。UiO-66吸附NO_3~-的吸附行为符合Freundlich等温线和准二级动力学吸附模型。吸附作用主要是材料中金属位点Zr对NO_3~-的静电吸附。UiO-66材料具有良好的再生性能,可重复使用。 相似文献
933.
酸性矿井水成分复杂、产量大,是严重的矿山环境问题,也是处理难度大的污废水体。采用超高石灰铝法,通过分别投加Ca O和Na Al O2对实验室配置的模拟酸性矿井水进行处理。实验分析溶液p H值、药剂投药比、初始浓度以及反应温度等因素对氯离子和硫酸根去除率的影响。结果表明,当Cl-的质量浓度为2 500 mg/L,SO2-4质量浓度为1 500 mg/L时,搅拌温度40℃,投加Ca O和Na Al O2的量分别为4.0 g和1.0 g,滴加Na OH调节p H值为10,搅拌15 min,Cl-,SO2-4去除率分别为87.9%,96.0%。 相似文献
934.
With data from in vitro and in situ investigations, we developed a mathematical model to describe cellular uptake of uranium and arsenic in solution by living Lemna gibba under homeostatic regulation. The model considers the ability of healthy cells to resist accumulation of toxic metal species by regulating physicochemical properties of the cell membrane. In the bulk solution, the ratio of the total amounts of bioavailable metal ions to the metal ions uptake by the cells is very high. Consequently, the main rate-limiting processes of uptake are the biosorption kinetics on both external and internal surfaces at the biological interface, and the transport of the metal ions across the cell membrane. The model prediction correlates well with uptake results from field and microcosm experiments for uranium and arsenic by L. gibba, a model ecotoxicological test organism. 相似文献
935.
碳羟磷灰石的制备及其对水中Cu2+的吸附 总被引:1,自引:0,他引:1
以废弃蛋壳为原料、尿素为添加剂,采用掺杂技术制备碳羟磷灰石(CHAP),并用其作吸附剂去除水中的Cu^2+。考察了Cu^2+的初始质量浓度、pH、吸附时间、CHAP加入量及温度等因素对CHAP吸附Cu^2+效果的影响。实验结果表明,在温度40℃、溶液pH6、搅拌1h后静置1h的条件下,用5g/L的CHAP处理Cu^2+初始质量浓度为60mg/L的水溶液,Cu^2+去除率为99.30%。吸附等温线基本符合Freundlich和Langmuir方程。 相似文献
936.
937.
Arsenite oxidation by three types of manganese oxides 总被引:5,自引:0,他引:5
Oxidation of As(Ⅲ) by three types of manganese oxides and the effects ofpH, ion strength and tartaric acid on the oxidation were investigated by means of chemical analysis, equilibrium redox, X-ray diffraction (XRD) and transmission electron microscopy (TEM). Three synthesized Mn oxide minerals, bimessite, cryptomelane, and hausmannite, which widely occur in soil and sediments, could actively oxidize As(Ⅲ) to As(Ⅴ). However, their ability in As(Ⅲ)-oxidation varied greatly depending on their structure, composition and surface properties. Tunnel structured cryptomelane exhibited the highest ability of As (Ⅲ) oxidation, followed by the layer structured birnessite and the lower oxide hausmannite. The maximum amount of As (Ⅴ) produced by the oxidation was in the order (mmol/kg) of cryptomelane (824.2) 〉 bimessite (480.4) 〉 hausmannite (117.9), As pH increased from the very low value(pH 2.5), the amount of As(Ⅲ) oxidized by the tested Mn oxides was firstly decreased, then negatively peaked in pH 3.0 6.5, and eventually increased remarkably. Oxidation of As(Ⅲ) by the Mn oxides had a buffering effects on the pH variation in the solution. It is proposed that the oxidative reaction processes between As (Ⅲ) and biruessite(or cryptomelane) are as follows: (1) at lower pH condition: (MnO2)x+ H3AsO3 + 0.5H^+=0.5H2AsO4^- + 0.5HAsO4^2- +Mn〉^2+ (MnO2)x-1 + H2O; (2) at higher pH condition: (MnO2)x + H3AsO3 = 0.5H2AsO4^- + 0.5HAsO4^2- + 1.5H^+ + (MnO2)x-1. MnO. With increase of ion strength, the As(Ⅲ) oxidized by bimessite and cryptomelane decreased and was negatively correlated with ion strength. However, ion strength had little influence on As (Ⅲ) oxidation by the hausmarmite. The presence of tartaric acid promoted oxidation of As(Ⅲ) by birnessite. As for cryptomelane and hansmannite, the same effect was observed when the concentration of tartaric acid was below 4 mmol/L, otherwise the oxidized As(Ⅲ) decreased. These findings are of great significance in improving our understanding of As geochemical cycling and controlling As contamination. 相似文献
938.
Evrendilek F Berberoglu S Taskinsu-Meydan S Yilmaz E 《Environmental monitoring and assessment》2006,119(1-3):527-543
Abstact Aboveground biomass, aboveground litterfall, and leaf litter decomposition of five indigenous tree stands (pure stands ofPinus brutia,Pinus nigra,Cedrus libani,Juniperus excelsa, and a mixed stand ofAbies cilicica,P. nigra, andC. libani) were measured in an eastern Mediterranean evergreen needleleaf forest of Turkey. Measurements were converted to regional scale estimates of carbon (C) stocks and fluxes of forest ecosystems, based on general non-site-specific allometric relationships. Mean C stock of the conifer forests was estimated as 97.8± 79 Mg C ha−1consisting of 83.0 ± 67 Mg C ha−1in the aboveground and 14.8 ± 12 Mg C ha−1in the belowground biomass. The forest stands had mean soil organic carbon (SOC) and nitrogen (SON) stocks of 172.0 ± 25.7 Mg C ha−1and 9.2 ± 1.2 Mg N ha−1, respectively. Mean total monthly litterfall was 376.2± 191.3 kg C ha−1, ranging from 641 ± 385 kg C ha−1forPinus brutiato 286 ± 82 kg C ha−1forCedrus libani. Decomposition rate constants (k) for pine needles were 0.0016 forCedrus libani, 0.0009 forPinus nigra, 0.0006 for the mixed stand, and 0.0005 day−1forPinus brutiaand
Juniperus excelsa. Estimation of components of the C budgets revealed that the forest ecosystems were net C sinks, with a mean sequestration rate of 2.0 ± 1.1 Mg C ha−1 yr−1ranging from 3.2 ± 2 Mg C ha−1forPinus brutiato 1.6 ± 0.6 Mg C ha−1forCedrus libani. Mean net ecosystem productivity (NEP) resulted in sequestration of 98.4 ± 54.1 Gg CO2 yr−1from the atmosphere when extrapolated for the entire study area of 134.2 km2(Gg = 109 g). The quantitative C data from the study revealed the significance of the conifer Mediterranean forests as C sinks 相似文献
939.
The Characteristics of Tropospheric Ozone Seasonality Observed from Ozone Soundings at Pohang, Korea
This paper presents the first analysis of vertical ozone sounding measurements over Pohang, Korea. The main focus is to analyze
the seasonal variation of vertical ozone profiles and determine the mechanisms controlling ozone seasonality. The maxima ozone
at the surface and in the free troposphere are observed in May and June, respectively. In comparison with the ozone seasonality
at Oki (near sea level) and Happo (altitude of 1840 m) in Japan, which are located at the same latitude as of Pohang, we have
found that the time of the ozone maximum at the Japanese sites is always a month earlier than at Pohang. Analysis of the wind
flow at the surface shows that the wind shifts from westerly to southerly in May over Japan, but in June over Pohang. However,
this wind shift above boundary layer occurs a month later. This wind shift results in significantly smaller amounts of ozone
because the southerly wind brings clean wet tropical air. It has been suggested that the spring ozone maximum in the lower
troposphere is due to polluted air transported from China. However, an enhanced ozone amount over the free troposphere in
June appears to have a different origin. A tongue-like structure in the time-height cross-section of ozone concentrations,
which starts from the stratosphere and extends to the middle troposphere, suggests that the ozone enhancement occurs due to
a gradual migration of ozone from the stratosphere. The high frequency of dry air with elevated ozone concentrations in the
upper troposphere in June suggests that the air is transported from the stratosphere. HYSPLIT trajectory analysis supports
the hypothesis that enhanced ozone in the free troposphere is not likely due to transport from sources of anthropogenic activity. 相似文献
940.
Recent measurements at different locations suggest that the emission of mercury from soils may play a more pronounced role in the global mercury cycle as suggested by global emission inventories and global mercury cycling models. For up scaling and modelling of mercury emissions from soils a comprehensive assessment of the processes controlling the emission of mercury from soils is imperative. We have developed a laboratory flux measurement system (LFMS) to study the effect of major environmental variables on the emission of mercury under controlled conditions. We have investigated the effects of turbulent mixing, soil temperature and solar radiation on the emission of mercury from soils. The emission of mercury from soils is constant over time under constant experimental conditions. The response of the mercury emission flux to variations of the atmospheric transfer parameters such as turbulence requires a rapid adjustment of the equilibrium that controls the Hg(o) concentration in the soil air. It has been shown that the light-induced flux is independent of the soil temperature and shows a strong spectral response to UV-B. 相似文献