The national standard--Safety Specifications for Power Driven VehiclesOperating on Roads--is the most basic technical regulation for safety and technical management ofmotor vehicles in China. It is the safety and tech...The national standard--Safety Specifications for Power Driven VehiclesOperating on Roads--is the most basic technical regulation for safety and technical management ofmotor vehicles in China. It is the safety and technical basis for the Public Security TrafficControl Dept. to register new vehicles, periodic inspection of vehicles under operation andinspection of vehicles involved in traffic accidents. It is also one of the important technicalbases of our country for compulsory inspection of new vehicles on fi-nalization of its model,ex-works inspection of new vehicles and the inspection of imported motor vehicles. Since the formalcountrywide implementation of GB7258-1997 Safety Specifications for Power Driven Vehicles Operatingon Roads on Jan. 1, 1998, the standard has played a very active role in strengthening the operatingsafety management of motor vehicles, improving the operating safety level of motor vehicles, and insafeguarding road traffic safety, etc. However, along with the rapid and sustainable growth of ournational economy, the number of motor vehicles has increased rapidly, especially privately-ownedautomobiles, so that the incidence of road traffic accidents rises yearly and the road trafficsafety situation is becoming increasingly serious. Therefore, the General Administration of QualitySupervision, Inspection and Quarantine of the People's Republic of China (AQSIQ) and theStandardization Administration of China (SAC) have issued the revised standard GB725 8-2004 SafetySpecifications for Power Driven Vehicles Operating on Roads, which will be put into effect onOctober 1, 2004. The timely revision of this standard is very necessary for upgrading the safety andtechnical requirements for motor vehicles in China.展开更多
为评估不同交通状态下公交车运行特征和排放水平的差异,现场采集广州市B9、226线路公交车的逐秒GPS数据,以ES-VSP(发动机负荷-机动车比功率)分布表征畅通、轻度拥堵和中度拥堵下的公交车运行特征,结合IVE(international vehicle emissi...为评估不同交通状态下公交车运行特征和排放水平的差异,现场采集广州市B9、226线路公交车的逐秒GPS数据,以ES-VSP(发动机负荷-机动车比功率)分布表征畅通、轻度拥堵和中度拥堵下的公交车运行特征,结合IVE(international vehicle emission)模型求得公交车平均排放因子并分析其差异.结果表明:(1)所测公交车的发动机低负荷区中bin11(-1.6<ES≤3.1,-2.9 k W/t≤VSP<1.2 k W/t)频率范围为50.55%~83.39%,中度拥堵时bin 11频率是畅通时的1.1~1.3倍;(2)3种交通状态下公交车的CO、VOC(运行产生的挥发性有机物)、VOCevap(蒸发产生的挥发性有机物)、NOx(氮氧化物)和PM(颗粒物)平均排放因子范围分别为7.63~11.40、0.26~0.46、0.68~1.56、0.32~0.51和0.72×10-2~1.28×10-2g/km;(3)同种交通状态下,主干路公交车专用道和BRT车道的公交车的大部分污染物平均排放因子低于次干路混行车道、主干路混行车道,中度拥堵时主干路BRT车道的CO、VOC、VOCevap、NOx和PM平均排放因子相对其他道路最低,分别为7.66、0.27、0.87、0.32和0.75×10-2g/km;(4)次干路混行车道、主干路混行车道的公交车污染物平均排放因子随交通状态愈加拥堵而增大,但畅通时主干路BRT车道的公交车行驶速度、加速度较高,导致CO平均排放因子较高,对应3种交通状态其比例为1.0∶0.9∶0.8.研究显示,交通状态对公交车运行和排放具有显著影响.展开更多
Rather than parking at nearby hourly parking lots, many passenger-picking-up vehicles prefer to idle at terminals and/or drive cycling around terminal facilities. As a result, extra vehicle emissions may be produced i...Rather than parking at nearby hourly parking lots, many passenger-picking-up vehicles prefer to idle at terminals and/or drive cycling around terminal facilities. As a result, extra vehicle emissions may be produced in an airport area. Even though there are limited studies on such emissions at airports, these estimations were normally based on the date emission models, which might cause bias in emission estimations. This paper proposes an approach to employ the floating car method and Global Positioning System （GPS） to record speeds and acceleration rates of idling and cycling vehicles at airport terminals. The tests were conducted under different time periods and traffic demands with different waiting time. The speeds and acceleration rates are synthesized to yield Vehicle Specific Power＇s （VSP） and Operational Mode （OM） distributions. Utilizing the Environmental Protection Agency （EPA） emission estimation model Motor Vehicle Emission Simulator （MOVES）, pollutants and green house gas emission indexes （e.g. NOx, CO, CO2 and HC） and fuel consumptions can be easily estimated. As an illustration of the proposed approach, the research team collected GPS data at a terminal in Houston William Hobby Airport （HOU）, and calculated the VSP distributions and OM distributions. Emissions of passenger-picking-up vehicles around these congested airport terminals.展开更多
为研究高原环境下道路坡度对车辆比功率(vehicle specific power, VSP)、NOx和CO_(2)的影响,利用车载排放测试系统对轻型柴油车进行实际道路试验。试验结果表明:忽略坡度对VSP的数值大小造成差异,引起VSP分布趋势变化。在坡度10%范围内...为研究高原环境下道路坡度对车辆比功率(vehicle specific power, VSP)、NOx和CO_(2)的影响,利用车载排放测试系统对轻型柴油车进行实际道路试验。试验结果表明:忽略坡度对VSP的数值大小造成差异,引起VSP分布趋势变化。在坡度10%范围内,考虑坡度与忽略坡度的VSP差值和坡度具有较强相关性。当道路坡度绝对值小于1时,可以忽略坡度计算VSP值。忽略坡度的VSP对划Bin区间造成聚集,扰乱了Bin区间与排放相关性;忽略坡度Bin区间排放值更接近于平均排放值。考虑坡度计算的VSP值与NOx、CO_(2)排放速率有较好的相关性。展开更多
On-road tailpipe ammonia (NH3) emissions contribute to urban secondary organic aerosol formation and have direct or indirect adverse impacts on the environment and human health. To understand the tailpipe NH3 emission...On-road tailpipe ammonia (NH3) emissions contribute to urban secondary organic aerosol formation and have direct or indirect adverse impacts on the environment and human health. To understand the tailpipe NH3 emission characteristics, we performed comprehensive chassis dynamometer measurements of NH3 emission from two China 5 and two China 6 light-duty gasoline vehicles (LDGVs) equipped with three-way catalytic converters (TWCs). The results showed that the distance-based emission factors (EFs) were 12.72 ± 2.68 and 3.18 ± 1.37 mg/km for China 5 and China 6 LDGVs, respectively. Upgrades in emission standards were associated with a reduction in tailpipe NH3 emission. In addition, high NH3 EFs were observed during the engine warm-up period in cold-start cases owing to the intensive emissions of incomplete combustion products and suitable catalytic temperature in the TWCs. Notably, based on the instantaneous NH3 emission rate, distinct NH3–emitting events were detected under high/extra high velocity or rapid acceleration. Furthermore, NH3 emission rates correlated well with engine speed, vehicle specific power, and modified combustion efficiency, which were more easily accessible. These strong correlations were applied to reproduce NH3 emissions from China 5/6 LDGVs. The predicted NH3 EFs under different dynamometer and real-world cycles agreed well with existing measurement and prediction results, revealing that the NH3 EFs of LDGVs in urban routes were within 8.55–11.62 mg/km. The results presented here substantially contribute to improving the NH3 emission inventory for LDGVs and predicting on-road NH3 emissions in China.展开更多
利用OBS-2200车载测试系统,分别在高峰期、平峰期和低峰期的天津市典型路段进行了车载测试,并获得了碳氢化合物（HC）、一氧化碳（CO）和氮氧化物（NOx）等车辆排放的污染物的逐秒数据.结果显示在这3个时段内,车辆的加速度大都集中在-1....利用OBS-2200车载测试系统,分别在高峰期、平峰期和低峰期的天津市典型路段进行了车载测试,并获得了碳氢化合物（HC）、一氧化碳（CO）和氮氧化物（NOx）等车辆排放的污染物的逐秒数据.结果显示在这3个时段内,车辆的加速度大都集中在-1.5~1.5m/s2,速度大都集中在0~70km/h,并且HC、CO和NOx的最高排放率为0.0673、0.706和0.0178g/s,都集中在高速（速度（v）〉30km/h,加速度（a）〉0.5m/s2）工况范围内.通过拟合发现,HC、CO和NOx的排放率与比功率（Vehicle Specific Power,简称VSP）之间的拟合决定系数分别为0.71、0.86和0.85,相关性较高,说明VSP可以作为评价车辆排放率的一个重要参考性指标.展开更多
文摘The national standard--Safety Specifications for Power Driven VehiclesOperating on Roads--is the most basic technical regulation for safety and technical management ofmotor vehicles in China. It is the safety and technical basis for the Public Security TrafficControl Dept. to register new vehicles, periodic inspection of vehicles under operation andinspection of vehicles involved in traffic accidents. It is also one of the important technicalbases of our country for compulsory inspection of new vehicles on fi-nalization of its model,ex-works inspection of new vehicles and the inspection of imported motor vehicles. Since the formalcountrywide implementation of GB7258-1997 Safety Specifications for Power Driven Vehicles Operatingon Roads on Jan. 1, 1998, the standard has played a very active role in strengthening the operatingsafety management of motor vehicles, improving the operating safety level of motor vehicles, and insafeguarding road traffic safety, etc. However, along with the rapid and sustainable growth of ournational economy, the number of motor vehicles has increased rapidly, especially privately-ownedautomobiles, so that the incidence of road traffic accidents rises yearly and the road trafficsafety situation is becoming increasingly serious. Therefore, the General Administration of QualitySupervision, Inspection and Quarantine of the People's Republic of China (AQSIQ) and theStandardization Administration of China (SAC) have issued the revised standard GB725 8-2004 SafetySpecifications for Power Driven Vehicles Operating on Roads, which will be put into effect onOctober 1, 2004. The timely revision of this standard is very necessary for upgrading the safety andtechnical requirements for motor vehicles in China.
文摘为评估不同交通状态下公交车运行特征和排放水平的差异,现场采集广州市B9、226线路公交车的逐秒GPS数据,以ES-VSP(发动机负荷-机动车比功率)分布表征畅通、轻度拥堵和中度拥堵下的公交车运行特征,结合IVE(international vehicle emission)模型求得公交车平均排放因子并分析其差异.结果表明:(1)所测公交车的发动机低负荷区中bin11(-1.6<ES≤3.1,-2.9 k W/t≤VSP<1.2 k W/t)频率范围为50.55%~83.39%,中度拥堵时bin 11频率是畅通时的1.1~1.3倍;(2)3种交通状态下公交车的CO、VOC(运行产生的挥发性有机物)、VOCevap(蒸发产生的挥发性有机物)、NOx(氮氧化物)和PM(颗粒物)平均排放因子范围分别为7.63~11.40、0.26~0.46、0.68~1.56、0.32~0.51和0.72×10-2~1.28×10-2g/km;(3)同种交通状态下,主干路公交车专用道和BRT车道的公交车的大部分污染物平均排放因子低于次干路混行车道、主干路混行车道,中度拥堵时主干路BRT车道的CO、VOC、VOCevap、NOx和PM平均排放因子相对其他道路最低,分别为7.66、0.27、0.87、0.32和0.75×10-2g/km;(4)次干路混行车道、主干路混行车道的公交车污染物平均排放因子随交通状态愈加拥堵而增大,但畅通时主干路BRT车道的公交车行驶速度、加速度较高,导致CO平均排放因子较高,对应3种交通状态其比例为1.0∶0.9∶0.8.研究显示,交通状态对公交车运行和排放具有显著影响.
文摘Rather than parking at nearby hourly parking lots, many passenger-picking-up vehicles prefer to idle at terminals and/or drive cycling around terminal facilities. As a result, extra vehicle emissions may be produced in an airport area. Even though there are limited studies on such emissions at airports, these estimations were normally based on the date emission models, which might cause bias in emission estimations. This paper proposes an approach to employ the floating car method and Global Positioning System （GPS） to record speeds and acceleration rates of idling and cycling vehicles at airport terminals. The tests were conducted under different time periods and traffic demands with different waiting time. The speeds and acceleration rates are synthesized to yield Vehicle Specific Power＇s （VSP） and Operational Mode （OM） distributions. Utilizing the Environmental Protection Agency （EPA） emission estimation model Motor Vehicle Emission Simulator （MOVES）, pollutants and green house gas emission indexes （e.g. NOx, CO, CO2 and HC） and fuel consumptions can be easily estimated. As an illustration of the proposed approach, the research team collected GPS data at a terminal in Houston William Hobby Airport （HOU）, and calculated the VSP distributions and OM distributions. Emissions of passenger-picking-up vehicles around these congested airport terminals.
文摘为研究高原环境下道路坡度对车辆比功率(vehicle specific power, VSP)、NOx和CO_(2)的影响,利用车载排放测试系统对轻型柴油车进行实际道路试验。试验结果表明:忽略坡度对VSP的数值大小造成差异,引起VSP分布趋势变化。在坡度10%范围内,考虑坡度与忽略坡度的VSP差值和坡度具有较强相关性。当道路坡度绝对值小于1时,可以忽略坡度计算VSP值。忽略坡度的VSP对划Bin区间造成聚集,扰乱了Bin区间与排放相关性;忽略坡度Bin区间排放值更接近于平均排放值。考虑坡度计算的VSP值与NOx、CO_(2)排放速率有较好的相关性。
基金support of the National Natural Science Foundation of China(Nos.51978404,42105100,and 41977180)the Guangdong Basic and Applied Basic Research Foundation(China)(Nos.2021A1515110297 and 2022A1515010866)the Basic Research of Shenzhen Science and Technology Innovation Commission(China)(No.JCYJ20190808145218827).
文摘On-road tailpipe ammonia (NH3) emissions contribute to urban secondary organic aerosol formation and have direct or indirect adverse impacts on the environment and human health. To understand the tailpipe NH3 emission characteristics, we performed comprehensive chassis dynamometer measurements of NH3 emission from two China 5 and two China 6 light-duty gasoline vehicles (LDGVs) equipped with three-way catalytic converters (TWCs). The results showed that the distance-based emission factors (EFs) were 12.72 ± 2.68 and 3.18 ± 1.37 mg/km for China 5 and China 6 LDGVs, respectively. Upgrades in emission standards were associated with a reduction in tailpipe NH3 emission. In addition, high NH3 EFs were observed during the engine warm-up period in cold-start cases owing to the intensive emissions of incomplete combustion products and suitable catalytic temperature in the TWCs. Notably, based on the instantaneous NH3 emission rate, distinct NH3–emitting events were detected under high/extra high velocity or rapid acceleration. Furthermore, NH3 emission rates correlated well with engine speed, vehicle specific power, and modified combustion efficiency, which were more easily accessible. These strong correlations were applied to reproduce NH3 emissions from China 5/6 LDGVs. The predicted NH3 EFs under different dynamometer and real-world cycles agreed well with existing measurement and prediction results, revealing that the NH3 EFs of LDGVs in urban routes were within 8.55–11.62 mg/km. The results presented here substantially contribute to improving the NH3 emission inventory for LDGVs and predicting on-road NH3 emissions in China.
文摘利用OBS-2200车载测试系统,分别在高峰期、平峰期和低峰期的天津市典型路段进行了车载测试,并获得了碳氢化合物（HC）、一氧化碳（CO）和氮氧化物（NOx）等车辆排放的污染物的逐秒数据.结果显示在这3个时段内,车辆的加速度大都集中在-1.5~1.5m/s2,速度大都集中在0~70km/h,并且HC、CO和NOx的最高排放率为0.0673、0.706和0.0178g/s,都集中在高速（速度（v）〉30km/h,加速度（a）〉0.5m/s2）工况范围内.通过拟合发现,HC、CO和NOx的排放率与比功率（Vehicle Specific Power,简称VSP）之间的拟合决定系数分别为0.71、0.86和0.85,相关性较高,说明VSP可以作为评价车辆排放率的一个重要参考性指标.
