城市轨道交通多层地下车站公共区排烟方案设计

随着城市轨道交通线网建设的发展,后建线路深埋将会加大,地下车站也将由原来常规的两层变为多层。车站深埋后对人员疏散和排烟系统提出了新的课题。在分析了地铁排烟系统设计与民用建筑的区别的基础上,研究提出了多层车站排烟系统设计及运行模式,包括站台、站厅及中间层的排烟系统方案及运行模式设计,可为同行提供参考。     

诱导排烟系统应用于地下车库的实验研究

运用实验研究的方法分析了诱导排烟系统在地下车库中应用的可行性,研究了布置方式、诱导风速等敏感参数对排烟效果的影响,主要分析了火源上游不同位置处温度的变化。结果表明,诱导排烟系统能有效地抑制烟气向上游的逆流并能加强烟气的热对流,降低上游烟气的温度;另外,开启少于均匀布置诱导风机数目下,菱形布置诱导风机下的排烟效果优于均匀排列布置;在实验风速范围内,诱导排烟系统对上游烟气的控制和降温能力随着诱导风速的增加而提高,同时,在火源功率一定的条件下,增大诱导风速对控烟效果的改善存在临界值。     

重庆市道路交通空气监测现状及控制对策

分析重庆市道路交通空气质量自动监测站的各项参数监测数据的变化趋势,并对机动车尾气对大气环境的影响进行了分析与评估。同时结合一些先进的预防、控制和处理汽车尾气污染的方法,提出了一些意见和建议来防止机动车尾气污染进一步蔓延。     

作业机废气减排技术研究

柴油发动机尾气排放中含有比汽油发动机更多的颗粒污染物。文章叙述了尾气净化装置反应原理,触媒及化学稳定性,柴油氧化催化剂和颗粒催化过滤器优点。通过外部加装尾气净化装置,解决了尾气污染问题,具有较好的发展前景、较强的实用性和可操作性。     

混合动力汽车尾气余热回收系统的研究

针对尾气余热能量浪费问题,建立了某直列四缸汽油机尾气余热回收发电的系统模型。通过B.T米特罗欣的数学分析法和涡轮特征曲线快速匹配到适合的涡轮机,然后根据涡轮特征曲线对高速发电机进行了匹配。以满足国Ⅴ标准的NEDC工况为参考,对整个系统进行了仿真分析。结果表明,该系统能够实现尾气余热能量的回收,在市区和市郊平均分别可以回收能量1 k W和1.5 k W,市郊最高可达1.8 k W。     

通风口高度对太阳能烟囱建筑自然通风和自然排烟性能的影响研究

安装太阳能烟囱后的建筑具有效果优良、节能环保的自然通风系统。室内通风口高度是太阳能烟囱建筑性能的关键参数之一。提出通过改变太阳能烟囱建筑室内通风口高度位置,使太阳能烟囱既可用于建筑的日常自然通风,也能实现室内火灾场景下的自然排烟。利用缩比例实验台研究了不同室内通风口高度对太阳能烟囱建筑自然通风与自然排烟效果的影响,发现自然通风和自然排烟效果随通风口高度增加呈现先增大后减小的趋势,且最佳室内通风口高度位于窗户上檐位置附近。研究结果对太阳能烟囱建筑的建筑结构关键参数设计具有指导意义。     

Multipoint source method in air pollution modelling of cold start emission

The paper presents a new method of air pollution modelling on a micro scale. For estimation of concentration of car exhaust pollutants, each car is treated as an instantaneous moving emission source. This approach enables us to model time and spatial changes of emission, especially during cold and cool start of an engine. These stages of engine work are a source of significant pollution concentration in urban areas. In this work, two models are proposed: one for the estimation of emission after cold start of the engine and another for the prediction of pollutant concentration. The first model (defined for individual exhaust gas pollutants) enables us to calculate the emission as a function of time after the cold or cool start, ambient temperature and average speed of motion. This model uses the HBEFA database. The second mathematical model is developed in order to calculate the pollutant dispersion and concentrations. The finite volume method is applied to discretise the set of partial differential equations describing wind flow and pollutant dispersion in the domain considered. Models presented in this paper can be called short-term models on a small spatial scale. The results of numerical simulation of pollutant emission and dispersion are also presented.     

Spatial & temporal variations of PM10 and particle number concentrations in urban air

The size of particles in urban air varies over four orders of magnitude (from 0.001 μm to 10 μm in diameter). In many cities only particle mass concentrations (PM10, i.e. particles <10 μm diameter) is measured. In this paper we analyze how differences in emissions, background concentrations and meteorology affect the temporal and spatial distribution of PM10 and total particle number concentrations (PNC) based on measurements and dispersion modeling in Stockholm, Sweden. PNC at densely trafficked kerbside locations are dominated by ultrafine particles (<0.1 μm diameter) due to vehicle exhaust emissions as verified by high correlation with NOx. But PNC contribute only marginally to PM10, due to the small size of exhaust particles. Instead wear of the road surface is an important factor for the highest PM10 concentrations observed. In Stockholm, road wear increases drastically due to the use of studded tires and traction sand on streets during winter; up to 90% of the locally emitted PM10 may be due to road abrasion. PM10 emissions and concentrations, but not PNC, at kerbside are controlled by road moisture. Annual mean urban background PM10 levels are relatively uniformly distributed over the city, due to the importance of long range transport. For PNC local sources often dominate the concentrations resulting in large temporal and spatial gradients in the concentrations. Despite these differences in the origin of PM10 and PNC, the spatial gradients of annual mean concentrations due to local sources are of equal magnitude due to the common source, namely traffic. Thus, people in different areas experiencing a factor of 2 different annual PM10 exposure due to local sources will also experience a factor of 2 different exposure in terms of PNC. This implies that health impact studies based solely on spatial differences in annual exposure to PM10 may not separate differences in health effects due to ultrafine and coarse particles. On the other hand, health effect assessments based on time series exposure analysis of PM10 and PNC, should be able to observe differences in health effects of ultrafine particles versus coarse particles.     

机动车尾气污染物NO_X在主干道水平、垂直方向上的浓度分布规律初探

对南海市主干道汽车尾气污染物ＮＯｘ 在水平、垂直方向上的扩散分布进行初步探究。结果表明,ＮＯｘ 在水平、垂直方向上的扩散呈现一定的规律。并且交通、风、气温、光照是影响ＮＯｘ 浓度分布的重要因素。     

Physical Modeling of Emissions from Naturally Ventilated Underground Parking Garages

The dispersion of pollutants from naturally ventilated underground parking garages has been studied in a boundary layer wind tunnel. Two idealized model setups have been analysed, one was simulating pollutant dispersion around an isolated rectangular building and one was representing dispersion in a finite array of idealized building blocks. Flow and dispersion close to modelled ground level emission sources was measured. The results illustrate the complexity of the flow around buildings and provide insight in pollutant transport from ground level sources located directly on building surfaces. As a result, areas critical with respect to high pollutant concentrations could be visualized. Particularly, the results show high concentration gradients on the surface of the buildings equipped with modelled emission sources. Inside the boundary layers on the building walls, a significant amount of pollutants is transported to upwind locations on the surface of the building. The paper documents the potential of physical modelling to be used for the simulation and measurement of dispersion close to emission sources and within complex building arrangements.