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中尺度模式中各种湿物理过程的数值模拟 总被引:14,自引:1,他引:14
利用PSU/NCAR的MM5对1999年6月下旬发生在江淮流域的梅雨锋暴雨进行数值模拟试验,研究MM5中不同湿物理过程中对MM5模拟梅雨锋暴雨的影响。试验结果显示:中尺度模式MM5能一定程度再现一些观测的中尺度特征,对流参数化方案对网格格距的大小比较敏感;显式云物理方案考虑冰相后可明显改善模式对暴雨的模拟能力,尤其是采用Reisner包含霰的混合相双变参数谱方案的双重嵌套网格对降水量的模拟取得较好的效果。 相似文献
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本文介绍了一种在奔腾4处理器微机上Linux操作系统下的优化编译方法。作者通过查询、试验发现:使用Intel编译器优化中尺度模式MM5,能够使得MM5在奔腾4上的运行速度提高1.4~1.5倍。利用Intel编译器优化后的MM5模式,进行了三个月资料的计算,模式运行稳定。给出了一个使用Intel编译器和通常使用的PGI编译器分别编译的计算实例,对比表明:使用Intel编译器明显提高了运算速度,两种编译方法预报的降水场和形势场没有太大差异。 相似文献
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本软件采用Foxpro2.5新一代数据库管理系统编写,主要用于遥测地震台网的设备管理及常规系统标定参数的计算,并已在1995年系统标定中得到了实践检验。 相似文献
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P. K. Mukhopadhyay F. Goodarzi M. A. Kruge M. H. Alimi 《International Journal of Coal Geology》1997,34(3-4)
Organic-rich from the Schei Point group (middle to late Triassic in age) and the Ringnes formation (late Jurassic) from the Sverdrup basin of the Canadian arctic archipelago have been geochemically evaluated for source rock characterization. Most samples from the Schei Point group are organic-rich (> 2% TOC and are considered as immature to mature oil-prone source rocks [kerogen types I, I–II (IIA) and II (IIA)]. These kerogen types contain abundant AOM1, AOM2 and alginite (Tasmanales, Nostocopsis, Leiosphaeridia, acritarch and dinoflagellate) with variable amounts of vitrinite, inertinite and exinite. Samples from the Ringnes formation contain dominant vitrinite and inertinite with partially oxidized AOM2, alginite and exinite forming mostly immature to mature condensate- and gas-prone source rocks [kerogen type II–III (IIB), III and a few II (IIA)]. Schei Point samples contain higher bitumen extract, saturate hydrocarbons and saturate/ aromatic ratio than the Ringnes samples. Triterpane and sterane (dominant C30) distribution patterns and stable carbon isotope of bitumen and kerogen suggest that the analyzed samples from the Schei Point group are at the onset of oil generation and contain a mixture of sapropelic (algal) and minor terrestrial humic organic matter. Sterane carbon number distributions in the Ringnes formation also suggest a mixed algal and terrestrial organic matter type. There are some variations in hopane carbon number distributions, but these are apparently a function of thermal maturity rather than significant genetic differences among samples. Pyrolysis-gas chromatography/mass spectrometry of the two samples with similar maturity shows that the Schei Point sample generates three times more pyrolyzate than the Ringnes sample. Both samples have a dominant aliphatic character, although the Ringnes sample contains phenol and an aromaticity that is higher than that of the Schei Point sample. 相似文献
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铅—试铁灵络合物吸附波及溴化十六烷基三甲基铵增敏效应的研究 总被引:1,自引:0,他引:1
在030mol/LHAc介质中,Pb(Ⅱ)与7_碘_8_羟基喹啉_5_磺酸(试铁灵,Feron)的络合物于-054V(vs.SCE)产生一尖锐的极谱波,加入溴化十六烷基三甲基铵(CTMAB)显著增敏,可使极谱波增高约4倍。峰电流与Pb(Ⅱ)浓度在96×10-9~48×10-6mol/L呈良好的线性关系,检出限为48×10-9mol/L。用多种电化学方法研究了该极谱波的性质及电极反应机理表明,络合物组成比为nPb(Ⅱ)∶nFeron=1∶1,极谱波为吸附波,峰电流由中心离子Pb(Ⅱ)还原产生,电子转移数为2。试验了多种离子对峰电流的影响,拟定的方法用于矿样分析,结果与原结果相符。 相似文献
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Most anti-tumour agents are known to be carcinogenic, mutagenic, teratogenic, embryotoxic or fetotoxic. Only little is known about the environmental impact of pharmaceuticals. Unmetabolized active substances are excreted and will show up in municipal wastewater. Therefore, we examined the biodegradability of the widely used anti-tumour agent 5-fluorouracil (5-FU), also as an example for assessing the impact of hospital effluent on the biodegradation of a test compound. The biodegradability of the structurally similar anti-tumour agents cytarabine and gemcitabine was also examined. Test systems used were the closed bottle test (OECD 301 D) and the modified Zahn-Wellens test (OECD 302 B). 5-FU was not biodegradable in the closed bottle test (CBT) nor in the Zahn-Wellens test (ZWT). At the highest concentration of 5-FU, with hospital effluent an inhibition of the degradation of substances present in hospital effluent was observed, probably as a result of a synergistic effect by 5-FU with antibiotics present in hospital sewage. Gemcitabine was biodegraded 42% in the CBT. The prolongation of the test period to 40 days only improved the result to 45%. In the ZWT, the biodegradation of gemcitabine was 50%. Cytarabine was partially biodegraded in the CBT (50%), but only after an adaptation period of 20 days. After a test prolongation to 40 days, the degree of biodegradation was 80%. In the ZWT, the biodegradability was > 95% after only a few days. 相似文献
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Rate constants for the gas-phase reactions of OH radicals, NO3 radicals and O3 with the C7-carbonyl compounds 4-methylenehex-5-enal [CH2=CHC(=CH2)CH2CH2CHO], (3Z)- and (3E)-4-methylhexa-3,5-dienal [CH2=CHC(CH3)=CHCH2CHO] and 4-methylcyclohex-3-en-1-one, which are products of the atmospheric degradations of myrcene, Z- and E-ocimene and terpinolene, respectively, have been measured at 296 ± 2 K and atmospheric pressure of air using relative rate methods. The rate constants obtained (in cm3 molecule–1 s–1 units) were: for 4-methylenehex-5-enal, (1.55 ± 0.15) × 10–10, (4.75 ± 0.35) × 10–13 and (1.46 ± 0.12) × 10–17 for the OH radical, NO3 radical and O3 reactions, respectively; for (3Z)-4-methylhexa-3,5-dienal: (1.61 ± 0.35) × 10–10, (2.17 ± 0.30) × 10–12, and (4.13 ± 0.81) × 10–17 for the OH radical, NO3 radical and O3 reactions, respectively; for (3E)-4-methylhexa-3,5-dienal: (2.52 ± 0.65) × 10–10, (1.75 ± 0.27) × 10–12, and (5.36 ± 0.28) × 10–17 for the OH radical, NO3 radical and O3 reactions, respectively; and for 4-methylcyclohex-3-en-1-one: (1.10 ± 0.19) × 10–10, (1.81 ± 0.35) × 10–12, and (6.98 ± 0.40) × 10–17 for the OH radical, NO3 radical and O3 reactions, respectively. These carbonyl compounds are all reactive in the troposphere, with daytime reaction with the OH radical and nighttime reaction with the NO3 radical being predicted to dominate as loss processes and with estimated lifetimes of about an hour or less. 相似文献