石油炼制与化工 ›› 2026, Vol. 58 ›› Issue (7): 137-144.

• 节能减排 • 上一篇    下一篇

不同行驶里程轻型车的颗粒物排放特性研究

李艳光1,陈子兵1,李叶清1,周冰洁2,张欣2,3,刘乐2,李铭3,4,毛佳伟3,4,朱浙辉5,6   

  1. 1. 奇瑞汽车股份有限公司

    2. 中汽研汽车检验中心(天津)有限公司

    3. 国家市场监督管理总局重点实验室(车用燃料质量安全与风险评估)
    4. 四川省产品质量监督检验检测院

    5. 西藏自治区产品质量监督检验所

    6. 国家市场监督管理总局重点实验室(高原成品油质量安全)

  • 收稿日期:2025-11-28 修回日期:2026-02-10 出版日期:2026-07-12 发布日期:2026-06-29
  • 通讯作者: 刘乐 E-mail:liule@catarc.ac.cn

STUDY ON PN EMISSION CHARACTERISTIC OF LIGHT-DUTY VEHICLES AT DIFFERENT MILEAGE LEVELS

  • Received:2025-11-28 Revised:2026-02-10 Online:2026-07-12 Published:2026-06-29

摘要: 为探究汽油车在不同使用阶段的颗粒物排放数量(PN)特征及其演变规律,选取2辆代表性汽油车,分别在WLTC工况和RDE工况下开展了不同行驶里程时PN测试,结果表明:随着行驶里程的增加,车辆PN呈先上升后下降最终趋于稳定趋势;当行驶里程小于10000 km时,PN水平较高,推测与车辆未充分磨合且后处理器GPF转化效率不稳定有关;当行驶里程为10000~40000 km时,PN显著降低;当行驶里程大于40000 km时,PN趋于稳定,推测发动机性能和GPF转化效率均趋于稳定。进一步,深入分析影响车辆PN的因素,结果发现:在WLTC工况下,冷启动阶段和减速阶段的PN高;在RDE工况下,车辆频繁启停和加速阶段高负荷是PN高的主要原因;WLTC工况下,城市阶段PN占其总排放量的70%以上,超高速阶段占比为2%~20%,城郊阶段和高速阶段PN的水平较低;WLTC工况和RDE工况下车辆PN测试结果存在显著差异,仅凭WLTC工况的测试结果难以准确反映车辆的颗粒物排放情况,应加强RDE工况下车辆PN的研究和监管。

关键词: 汽油车, 行驶里程, 颗粒物排放数量, 影响因素, WLTC工况, RDE工况

Abstract: To investigate the characteristics and evolution of particle number (PN) emissions from gasoline vehicles at different stages of use, two representative gasoline vehicles were selected for PN emission tests under both the WLTC and RDE driving cycles at various mileage intervals. The results show that as mileage increases, vehicle PN emissions exhibit a trend of first rising and then stabilizing. When the mileage is less than 10,000 km, PN emissions are relatively high, which is likely attributed to incomplete engine break-in and unstable conversion efficiency of the aftertreatment system, particularly the gasoline particulate filter (GPF). When the mileage ranges from 10,000 to 40,000 km, PN emissions increase significantly. When the mileage exceeds 40,000 km, PN emissions tend to stabilize, suggesting that both engine performance and GPF conversion efficiency have reached a steady state.Furthermore,depth analysis factorsof influencing PN emissions reveals that under the WLTC cycle, high PN emissions occur during cold-start and deceleration phases. Under the RDE cycle, frequent vehicle starts/stops and high-load acceleration are the primary causes of elevated PN emissions. During the WLTC test, urban driving phase accounts for more than 70% of total PN emissions, while the extra-high-speed phase contributes 2%–20%. In contrast, PN emissions during suburban and highway phases are relatively low. Moreover, significant differences exist between PN emission results obtained under WLTC and RDE conditions. Relying solely on WLTC test results cannot accurately reflect real-world particle emissions. Therefore, greater emphasis should be placed on research and regulation of vehicle PN emissions under RDE conditions.

Key words: gasoline vehicle, mileage, PN emissions, influencingfactors, WLTC, RDE