43 resultados para 67-500


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The effect of thermal annealing on the Raman spectrum of Si0.33Ge0.67 alloy grown on Si (100) by molecular beam epitaxy is investigated in the temperature range of 550-800 degrees C. For annealing below 700 degrees C, interdiffusion at the interface is negligible and the residual strain plays the dominant role in the Raman shift. The strain-shift coefficients for Si-Ge and Ge-Ge phonon modes are determined to be 915 +/- 215 cm(-1) and 732 +/- 117 cm(-1), respectively. For higher temperature annealing, interdiffusion is significant and strongly affects the Raman shift and the spectral shape.

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近年来各种环境污染事故频发,据统计仅2001~2003年间,发生的各类环境污染事故就高达5606次,其中水污染事故3235次,占全部的57.7%。这些事故不仅给人民生命财产造成巨大损失,也给生态环境造成严重的破坏。因此开发安全高效的应急处理技术迫在眉睫。本研究以筛选高效苯胺降解菌为基础,通过对高效菌降解性能的研究指导将高效菌作为功能郡主投加到已有生物处理系统强化应急处理苯胺突发污染事故废液,取得了良好的效果。 苯胺高效降解菌AN-P1为红球菌(Rhodococcus sp.),其通过间位途径降解苯胺,AN-P1利用苯胺生长和降解的最佳pH为6,最适浓度为2000 mg/L,最适温度为30 ℃,最佳接种量为0.3‰。AN-P1降解含500 mg/L、1000 mg/L、2000 mg/L苯胺的培养物分别经过28 h、24 h、32 h降解,出水苯胺含量能达到《污水综合排放标准》(GB8978-1996)一级标准。但由于苯胺降解过程中释放了大量氨氮,出水氨氮仍较高未能达标排放。而常规SBR系统应急处理效果较差,苯胺和COD去除率均低于10%,出水未能达标排放。活性碳吸附后的回收和后续处理也会带来操作不变和二次污染问题,且处理后出水往往难于达标排放,尚需进行进一步处理。 生物处理系统应急处理后恢复运行处理效果监测和PCR-DGGE图谱分析显示,用AN-P1菌强化应急处理系统后不仅能快速高效的去除苯胺,而且可以有效保障处理系统对污染物的净化性能,有效的保护系统中的功能微生物免受苯胺毒害。 研究结果表明,从实际处理效果、对原有生物系统性能保护及实际应用操作等多方面考虑,用AN-P1菌强化应急处理苯胺突发污染事故在技术上都是可行的。本研究为应急处理苯胺突然污染事故废液提供了新的方法。 Recent years, environment pollution accidents happened frequently, the data showed that there are 5606 accidents between 2001 and 2003, including 3235 water environment accidents, which is 57.7% of all. These accedents not only caused money lost and life lost but also caused serious damage to the ecologicl environment. So exploring highly-effective and secure methods to solve these accidents is an urgent mission. We screened a highly-effective aniline-degrading bacterium and did some researches on its ability to degrade aniline, in order to guide the emergency treatment of aniline containing wastewater that caused by sudden accident pollution with bioaugmentation. A highly-effective aniline-degrading bacterium AN-P1 was isolate and characterized as Rhodococcus sp. It degrades aniline through meta-cleavage pathway. The optimal pH and temperature for cell growth and aniline degradation were 6 and 30 ℃, respectively, and the opitimal concentration of aniline was 2000 mg/L, the optimal inoculation amount was 0.3‰.It took bacterium AN-P1 only 18 h, 24 h and 32 h, respectively, for the treatment of MSB containing 500 mg/L, 1000 mg/L, 2000 mg/L aniline to meet the first grade of national some of the NH4+-N which caused by aniline degradation. It took bacterium AN-P1 only 10 h, 20 h and 32 h, respectively, for the treatment of wastewater containing 500 mg/L, 1000 mg/L, 2000 mg/L aniline to meet the first grade of national integrated wastewater discharge standard. The bacterium AN-P1 can also remove some of the NH4+-N which caused by aniline degradation. It took bacterium AN-P1 only 10 h, 20 h and 32 h, respectively, for the treatment of wastewater containing 500 mg/L, 1000 mg/L, 2000 mg/L aniline to meet the first grade of national integrated wastewater discharge standard. By combing AN-P1 with regular SBR system, it took only 36 h for the emergency treatment of wastewater containing 2000 mg/L aniline under simulating engineering conditions to meet the discharge standard. While the NH4+-N of effluent can not meet the standard because of the high amount NH4+-N caused by aniline degradation. The regular SBR system was not good at aniline and COD removal. The removal efficiency of which are less than 10%. It cost 67.8 g activated carbon to absorbed 1000 mg aniline. It is inconvenient to transport and use it for the emergency treatment of aniline when the sudden pollution accident happened. Meanwhile, it was complex ad hard to recycle the activated carbon and treat the aniline wastewater get from activated carbon recycling too. Hard to meet the effluent standard was also a problem of activated carbon absorption method. According to the PCR-DGGE profile and removal efficiency of pollutants and COD when the systerm recover from emergency treatment, AN-P1 can efficiently protect the microbial community of regular activated sludge system against the aniline. It proved that combing AN-P1 with regular biological system is a feasible strategy for emergency treatment of aniline sudden pollution accident. The research offered a new way for emergency treatment of aniline sudden pollution accident.

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This paper reports laboratory measurements of the spectrum of highly ionized sulfur. The spectrum of S Ⅸ–S ⅩⅢ has been observed in the wavelength range 170–500 Å. A total of 54 lines have been measured. Forty-two of them have been classified as 2s22pk–2s2pk+1and 2s2pk–2pk+1 transitions. Twelve other lines have been ascribed to 2s–2p,4p–5s,5p–6s,5d–6p, and 6p–8d transitions. These spectral lines have been identified, among which 22 are new and accurately measured. The analysis of the spectra was based on a comparison with other experimental results and calculated values.

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Target ionization and projectile charge changing were investigated for 20-500 keV/u Cq+, Oq++He (q=1-3) collisions. Double- to single-ionization ratios R-21 of helium associated with no projectile charge change (direct ionization), single-electron capture, and single-electron loss were measured. The cross-section ratio R-21 depends strongly on the collision velocity v, the projectile charge state q, and the outgoing reaction channel. Meanwhile, a model extended from our previous work [J. X. Shao, X. M. Chen, and B. W. Ding, Phys. Rev. A 75, 012701 (2007)] is presented to interpret the above-mentioned dependences. Good agreement is found between the model and the experimental data.

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Recent experimental data have revealed large mirror energy differences (MED) between high-spin states in the mirror nuclei Se-67 and As-67, the heaviest pair where MED have been determined so far. The MED are generally attributed to the isospin symmetry breaking caused by the Coulomb force and by the isospin-nonconserving part of the nucleon-nucleon residual interaction. The different contributions of the various terms have been extensively studied in the fp shell. By employing large-scale shell-model calculations, we show that the inclusion of the g(9/2) orbit causes interference between the electromagnetic spin-orbit and the Coulomb monopole radial terms at high spin. The large MED are attributed to the aligned proton pair excitations from the p(3/2) and f(5/2) orbits to the g(9/2) orbit. The relation of the MED to deformation is discussed.

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本论文以A~160区奇奇核的高自旋态核结构为研究对象,详细地总结分析了该区奇奇核[h11/2]p[i13/2]n带的性质,利用在束核谱学实验手段布居和测量了166Ta核高自旋态能级结构、借助模型理论对该核实验结果进行分析,还从理论方面系统地研究了A~160区奇奇核[h11/2]p[i13/2]n带的signature反转现象与形变的关系,取得了一些创新成果。 奇奇核高j组态带的signature反转现象系统地存在于A~160、A~130和A~80核区,目前理论上提出的各种可能机制还不能彻底解释清楚这一现象。本文中较详细地归纳了A~160区奇奇核signature反转带,即[h11/2]p[i13/2]n带,实验数据的一些系统学规律,具体贡献在于 1、总结了晕态[h11/2]p[i13/2]n带的跃迁能量系统学规律,指出存在这种规律的原因在于形变和价核子耦合性质随质子数和中子数增减的有规律变化。 2、展示了随质子数增大和中子数减小该带准粒子顺排角动量相加性逐渐变差的现象,指出这种变差的原因可能是形变减小导致剩余n-p相互作用的增强,以及奇奇核带和与之相比较的奇核带形变差异增大。文中强调了使用顺排角动量相加性规则时要考查相加前后两个signature分支顺排角动量的相对大小。跃迁能量系统学规律和顺排角动量相加性规则是目前指定该区奇奇核[h11/2]p[i13/2]n带核态自旋值的有效工具,上述工作有益于研究新核时正确运用这些工具。文中其它归纳和总结工作也为后续研究提供了较为系统的参考资料。 此前尚未有人对166Ta核做过在束研究,我们在中国原子能科学研究院利用HI-13串列加速器通过141Pr(28Si,3n)反应布居和测量了166Ta核高自旋态。实验中使用了5片厚500μg/cm2纯度98.0%的141Pr自衬靶,7台HpGe反康谱仪和1台平面型HpGe探测器。用改变束流能量测量在束单谱和剩余放射性的方法确认实验中生成了166Ta核并为符合实验选定了束流能量。γ-γ符合实验束流能量为127MeV,实验中共收集到约50×106个两重符合事件。实验后用152Eu放射源对探测系统进行了能量和效率刻度。符合实验数据被反演成γ-γ、X-γ和DCO二维谱。通过处理和分析实验数据,得到以下主要结果: 1、用TaKX射线开窗、比较不同束流能量下的在束单谱和排除已知核射线等方法确认了属于166Ta的射线,根据这些射线的级联关系首次建立起了166Ta核的在束能级纲图,其中包括4条转动带,60条射线。166Ta核的晕带是一条耦合性较强的带,建立起的该带能级纲图中包括16条能级和29条射线,每一signature分支有7条E2拉伸跃迁。另外三条带是两条耦合带和一条双退耦带。其中一条耦合带的耦合性较强、位置较高,可能是4准粒子带。 2、计算γ-γ符合矩阵和DCO矩阵开窗谱中峰下面积,得到了166Ta核55条射线在实验中的相对强度Iγ、29条射线的方向关联系数Iγ(35°)/Iγ(75°)和21个核态退激过程的跃迁强度分支比λ等数据。 3、借助模型计算,为实验中发现的4条转动带指定了组态。晕核组态定为9/2[514]p3/2[651]n, Kπ值为6-。另外两条耦合带的组态被定为9/2[514]p3/2[521]n和9/2[514]p3/2[521]n{3/2[651]n}2,退偶带的组态可能是1/2[514]p3/2[651]n。 4、通过分析跃迁能量系统学规律和运用顺排角动量相加性规则指定了166Ta核晕带核态的自旋值,还使用其它方法倾向性地指定了另外三条带的自旋值。 5、提取了一些核态退激过程B(M1)/B(E2)理论值比实验值偏大,指示该带可能存在负γ形变。另外两条耦合带的B(M1)/B(E2)计算值与实验值比较接近,这方面支持我们对其组态的指定。回弯之前的166Ta核晕带B(M1)/B(E2)值与已知的同位素和同中子素奇奇核晕带值相比大许多,我们认为这是组态和形变变化造成的。 6、166Ta和邻核晕带集体转动惯量随转动角频率平方的变化关系显示准质子占据h11/2子壳顶部轨道时顺排发生得较晚,准中子占据i13/2子壳低部轨道时顺排发生得较早。 7、实验结果显示166Ta核的晕带出现signature反转,signature反转点自旋值和反转点之下M1跃迁摆动幅度都与全区规律相符。 我们研究166Ta核的高自旋态能级结构旨在为研究奇奇核signature反转提供新的实验数据,实验研究达到了预期的目的,实验结果证实了在轻Ta奇奇核同位素中也系统地存在signature反转。 在讨论A~160区奇奇核[h11/2]p[i13/2]n带的signature反转机制方面,作者首次利用现有的TRS计算方法系统地考察了该区32个奇奇核该带形变极其随核子数增减的变化趋势,进而通过CSM计算考察了形变对该带signature劈裂的影响。这方面的研究成果主要包括: 1、计算结果显示,该区核芯较容易在γ形变方向受到价核子的形状极化作用,89≤Z≤95时i13/2准中子一般具有正γ形变驱动作用且随着中子数减小此正γ形变驱动作用逐渐增强,67≤Z≤75时h11/2准质子一般具有负γ形变驱动作用且随着质子数增大此负γ形变驱动作用逐渐增强,Z=63和65时h11/2准质子两个signature组态具有不同方向的γ形变驱动作用,总体看h11/2准质子的γ形变驱动作用没有i13/2准中子的强。 2、只考虑ε2和γ形变参量的TSR计算结果显示A~160区中N=89和91奇奇核的[h11/2]p[i13/2]n带有较大的正γ形变,N≥93奇奇核中该带γ形变则较小或为负γ形变。计算出的不同核该带的γ形变值随中子数增加逐渐减小、随质子数变化的规律较复杂且变化幅度没有随中子数变化时那么明显,Z≤67时一些核两signature的形变还有明显的差异。 3、CSM计算表明正γ形变可以导致费米面附近的h11/2准质子轨道signature反转,并且存在正γ形变时ε2形变、ε4形变、质子对力和质子数的不同都对signature反转幅度和反转点对应的角频率都有影响,[h11/2]p[i13/2]n带两个signature组态形变的不同对费米面附近i13/2准中子轨道的位置也有影响。 4、利用从TRS计算出的形变参量所做CSM计算显示,该区部分奇奇核[h11/2]p[i13/2]n带出现signature反转。计算出的signature反转随中子数或质子数变化趋势有些和实验结果相符,也有一些与实验结果不符,对有些实验上发现signature反转的核还计算不出反转。计算结果预言该区一些没有实验数据的奇奇核[h11/2]p[i13/2]n带中也会存在signature反转,这些核是154Eu、162Ta、164Ta和168Re等。 此前对解释A~160区奇奇核signature反转的系统规律时是否必须考虑γ形变还没有定论,本文工作证实了较明显的正γ形变对signature反转起着重要的作用。但是,单纯考虑γ形变并不能完全再现A~160区奇奇核signature反转规律,今后的研究工作还要系统而细致地考虑各方面因素。

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色泽是构成食品感官质量的一个重要因素,保持或赋予食品良好色泽是食品工业中亟待解决的重要问题。板栗壳棕色素是一种稳定性好,无毒副作用,甚至对人体具一定保健作用的天然色素,故可作优良的食品添加剂。然所含杂质则大大地降低其色价和品质,本文将板栗壳棕色素分别用101果汁澄清剂、ZTC1+1Ⅱ型澄清剂和壳聚糖进行絮凝处理,确定了各自的作用条件,并对其絮凝效果进行比较。101果汁澄清剂法:101果汁澄清剂1/125(v/v),温度室温(约15℃),色价7.27;ZTC1+1Ⅱ型澄清剂法:先B后A,B1/500(v/v),A1/1000(v/v),温度约40℃,色价9.39;壳聚糖法:1/125(v/v),温度约50℃,色价6.67。实验结果表明,三种方法对棕色素色价提高均有较好的效果,但总体上看,ZTC1+1Ⅱ型澄清剂法效果最好,色价高达9.39,故ZTC1+1Ⅱ型澄清剂法明显优于其它两种方法。

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在历史旱涝记载资料可靠性检验的基础上,重建了湖北省3个区域近500年来的干湿气候变化序列,并比较分析了各区域干湿气候变化的趋势特征、准周期性及跃变现象。结果表明:在3个区域中,鄂东区1570~1770、1890~1950年两个时段偏湿,1470~1520、1790~1830年则偏干;鄂北区偏湿时期主要在1470~1530、1710~1750、1850~1910年三个时段,1470~1530、1770~1830年则偏干;鄂西南区有1550~1610、1650~1710、1830~1890、1930~1990