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上海市污水治理二期工程扩散器的改进设计 总被引:1,自引:0,他引:1
首先对污水海洋处置工程进行了简单介绍 ,根据国内外污水海洋处置工程的设计经验 ,论述了污水海洋处置工程扩散器设计的一般准则 ;结合上海市污水治理二期工程白龙港排放口水较浅的特点 ,为了提高污水近区稀释度 ,根据物理模型试验 ,对扩散器的设计进行了改进 ,可为国内较浅水域污水海洋处置工程扩散器的设计提供参考 相似文献
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分析了传统空管裂解生产四氟乙烯工艺存在的污染问题 ,介绍了水蒸汽稀释裂解生产四氟乙烯工艺的污染控制情况。 相似文献
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嘉兴市污水海洋处置工程扩散器长度的确定 总被引:1,自引:1,他引:1
为了能满足设计初始稀释度并降低工程费用,结合嘉兴市污水海洋处置工程,利用Jetlag3模型确定了其扩散器长度。计算结果表明,八团(0-1500)扩散器长度取200-250m,场前(0+000)和场前(0+1400)扩散器长度取250-300m,能满足近区初始稀释度的要求。 相似文献
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氮、氧稳定同位素指标在N2 O源汇识别、全球源汇质量估算中具有独特的定量作用。本文主要讨论N2 O的氮、氧稳定同位素真空制样系统的基本原理、总体设计和技术难点 ,为建立N2 O氮、氧稳定同位素真空制样系统提供理论基础。 相似文献
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通过对燃烧设备在燃料燃烧时,理论空气量、理论烟气量及烟气组成、实际空气量、实际烟气量及烟气组成的分析,指出过量空气系数的大小,直接影响燃料的完全燃烧,同时也直接影响烟气中污染物的排放浓度,提出了监测污染物的排放浓度时应控制过量空气系数. 相似文献
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Explosive gas mixtures and explosive dust clouds, once existing, exhibit similar ignition and combustion features. However, there are two basic differences between dusts and gases which are of substantially greater significance in design of safety standards than these similarities. Firstly, the physics of generation and up-keeping of dust clouds and premixed gas/vapour clouds are substantially different. This means that in most situations where accidental explosive gas clouds may be produced quite readily, generation of explosive dust clouds would be highly unlikely. Secondly, contrary to premixed gas flame propagation, the propagation of flames in dust/air mixtures is not limited only to the flammable dust concentration range of dynamic clouds. The state of stagnant layers/deposits offers an additional discrete possibility of flame propagation.
The two European Directives 94/9/EC (1994) and 1999/92/EC (1999) primarily address gases/vapours, whereas the particular properties of dusts are not addressed adequately. Some recent IEC and European dust standards resulting from this deficiency are discussed, and the need for revising the two directives accordingly is emphasized. 相似文献
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By using a dynamic dilution system, the atmospheric measurement of 11 selected toxics VOCs (ethylene, acetylene, propene, 1-butene, 1,3-butadiene, 1-pentene, 1-hexene, benzene, toluene, ethylbenzene, m+p-xylene) from the list WHO of 1996 and TO-14 method of US EPA by preconcentration by thermal desorption (TD), analysis by gas chromatography (GC), identification and quantification with a flame ionisation detector (FID) was developed and validated in term of metrology, especially the techniques of sampling of these VOCs with adsorbents cartridges "Air Toxics" when used with an "UMEG sampler" equipped in the inlet with a nafion membrane. In particular the influence of climatic conditions (temperature and relative humidity) and the influence of chemical factors like ozone, on the representativity of sampling were studied. Experiments made with various humidities showed that the addition of a nafion membrane in the inlet of the sampling system was required. Without this membrane, losses of compounds were observed for RH >50%. With this membrane, storage for 2 weeks in a refrigerator, as for canisters, did not induce a loss of compounds. No significative decrease of concentrations of the studied VOCs after 14 days storage, which are known to react with ozone, were observed with an ozone concentrations of 55 ppb. One explanation is that nafion membrane, placed in the inlet of the sampler, will neutralize ozone before entering the sampling tubes. This observation is in accordance with literature which states that the sampling of VOCs on Carbotrap cartridges without ozone scrubber induce a loss of compounds. 相似文献