街道峡谷内汽车排放污染物浓度分布的观测与数值模拟

在上海某典型街道峡谷内按一定的空间布点,在一定时段内同时对各布点进行采样并做一氧化碳浓度分析,同时记录车辆种类、车流量、气象条件等,分析街道峡谷内污染物浓度的分布.运用风向频率加权(WDFW)方法,结合大气流动和污染物扩散的CFD模型进行数值模拟计算.结果表明,数值模拟结果和现场观测结果较吻合,建筑物低的一侧污染物浓度远高于建筑物高的一侧污染物浓度,两侧的污染物浓度随着高度的增加而降低.     

汽车燃料和排放物的快速气相色谱分析

1　IntroductionGaschromatographyisthemostfrequentlyusedmethodsforthespeciationandquantificationoforganiccompoundsingasphaseandliquidphase .Thechemicalanalysisoforganiccompoundsintheautomotivefuelsandexhaustspeciesisanextremelyimportantandcomplexprocedure …     

燃用甲醇燃料的发动机尾气排放

本文主要报导了在二冲程、四冲程汽油机及柴油机上燃用甲醇-汽油混合燃料、M_(100)甲醇燃料的发动机尾气排放方面所做的研究,并与燃用汽油、柴油的尾气排放进行了对照。结果表明,无论是甲醇-汽油混合燃料,还是M_(100)甲醇燃料尾气排放,都较汽油、柴油尾气排放的常规污染物,均有不同程度的减少。因此,应用甲醇燃料对改善环境是有益的。     

Rh-Al-MCM-41上NO选择性催化还原的原位红外研究

利用气-固相固定床反应装置考察了Rh交换的Al-MCM-41在高气体空速条件下对贫燃NOx的选择性催化还原活性,考察了氧含量对其的影响。结果表明,在200000h~(-1)的气体空速、O_2/C_3H_6=20、603K时,NO转化率为74.3％。利用原位FTIR技术研究了该催化剂的表面吸附物种及表面程序升温反应行为,并结合实验观察探讨了贫燃条件下Rh-Al-MCM-41催化剂上NO的选择性催化还原机理。     

我国汽车尾气污染,污染控制与对策

本文综述了我国汽车尾气污染的现状与发展趋势，着重阐述了我国汽车尾气的催化剂研制和催化净化器技术水平和现状，提出了我国汽车尾气污染控制技术的发展方向，并探讨了减少汽车尾气污染的对策和建议。     

汽车尾气催化转化器模型研究进展

本文主要介绍汽车尾气催化转化器模型的研究进展 ,包括反应器内气体流动特性、单通道反应器内的传递现象和反应动力学、通道间的热传递和反应行为的模拟 ;并指出认识反应器内的各种特性和规律对设计汽车尾气催化转化器的必要性和意义     

Isomer distribution of nitrotriphenylenes in airborne particles, diesel exhaust particles, and the products of gas-phase radical-initiated nitration of triphenylene

The formation of mutagenic nitro-polycyclic aromatic hydrocarbons (NPAHs) 1- and 2-nitrotriphenylene (1- and 2-NTP) via gas-phase OH or NO₃ radical-initiated reactions of triphenylene was demonstrated for the first time using a flow reaction system. In contrast with the results of conventional electrophilic nitration, 2-NTP was formed in larger yield than 1-NTP, but this is consistent with the mechanism proposed for gas-phase radical-initiated nitration of PAH. In diesel exhaust particle (DEP) samples, both 1- and 2-NTP were identified and their concentrations determined, as well as 1-nitropyrene (1-NP), which is a representative combustion-derived NPAH: the mean concentrations of 1-NTP, 2-NTP, and 1-NP were 4.7, 1.9, and 32 pmol mg_DEP^–1, respectively. The mean 2-NTP/1-NTP, 1-NTP/1-NP, and 2-NTP/1-NP ratios in samples of airborne particles collected in a residential area in Osaka, Japan, were>1.55,<0.25, and 0.37, respectively; these values are much higher than those of the DEP samples. This finding indicates that there is another source for airborne NTPs, especially 2-NTP, apart from diesel exhaust. These results strongly suggest that airborne NTPs originate from atmospheric processes such as radical-initiated reactions of triphenylene, and this has a significant influence on the atmospheric occurrence of NTPs.     

废气治理的低温等离子体-催化协同净化技术

低温等离子体 催化协同净化技术具有能耗低、投资少、处理效率高、不产生二次污染等显著优点备受人们的关注。从挥发性有机化合物 (VOC)的转化、氮氧化合物的脱除、汽车尾气净化等不同废气治理的角度 ,概括了目前国内外在这方面的研究进展 ,最后提出了该项技术在环境保护领域的应用前景及研究方向     

汽车尾气净化催化剂涂层改性研究

汽车尾气净化催化剂的净化转化效果及其耐久性，与催化剂涂层的涂覆量以及涂层和载体的结合强度密切相关。本文研究了几种不同类型表面活性剂对浆料固体含量、涂层涂覆量以及涂层结合强度的影响。研究结果表明，不使用表面活性剂时，30％为最佳的固体含量；在使用表面活性剂的情况下，浆料的固体含量可以提高至35％。非离子型表面活性剂有助于提高催化剂涂层涂覆量，而使用离子型表面活性剂的浆料球磨过程中产生大量泡沫，无法涂覆。使用非离子型表面活性剂的催化剂涂层的结合强度最好。     

Influence of driving cycles on exhaust emissions and fuel consumption of gasoline passenger car in Bangkok

The influence of different driving cycles on their exhaust emissions and fuel consumption rate of gasoline passenger car was investigated in Bangkok based on the actual measurements obtained from a test vehicle driving on a standard chassis dynamometer. A newly established Bangkok driving cycle (BDC) and the European driving cycle (EDC) which is presently adopted as the legislative cycle for testing automobiles registered in Thailand were used. The newly developed BDC is constructed using the driving characteristic data obtained from the real on-road driving tests along selected traffic routes. A method for selecting appropriate road routes for real driving tests is also introduced. Variations of keyed driving parameters of BDC with different driving cycles were discussed. The results showed that the HC and CO emission factors of BDC are almost two and four times greater than those of EDC, respectively. Although the difference in the NOx emission factor is small, the value from BDC is still greater than that of EDC by 10%. Under BDC, the test vehicle consumes fuel about 25% more than it does under EDC. All these differences are mainly attributed to the greater proportion of idle periods and higher fluctuations of vehicle speed in the BDC cycle. This result indicated that the exhausted emissions and fuel consumption of vehicles obtained from tests under the legislative modal-type driving cycle (EDC) are significantly different from those actually produced under real traffic conditions especially during peak periods.