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基于LCA的道路基础设施碳排放核算与低碳减排技术综述

冉茂平 邓须红 关佳希 肖神清 蒋睿锲 周兴林

冉茂平, 邓须红, 关佳希, 肖神清, 蒋睿锲, 周兴林. 基于LCA的道路基础设施碳排放核算与低碳减排技术综述[J]. 交通运输工程学报, 2025, 25(5): 23-37. doi: 10.19818/j.cnki.1671-1637.2025.05.002
引用本文: 冉茂平, 邓须红, 关佳希, 肖神清, 蒋睿锲, 周兴林. 基于LCA的道路基础设施碳排放核算与低碳减排技术综述[J]. 交通运输工程学报, 2025, 25(5): 23-37. doi: 10.19818/j.cnki.1671-1637.2025.05.002
RAN Mao-ping, DENG Xu-hong, GUAN Jia-xi, XIAO Shen-qing, JIANG Rui-qie, ZHOU Xing-lin. Review on road infrastructure carbon emission accounting and low-carbon reduction technologies based on LCA[J]. Journal of Traffic and Transportation Engineering, 2025, 25(5): 23-37. doi: 10.19818/j.cnki.1671-1637.2025.05.002
Citation: RAN Mao-ping, DENG Xu-hong, GUAN Jia-xi, XIAO Shen-qing, JIANG Rui-qie, ZHOU Xing-lin. Review on road infrastructure carbon emission accounting and low-carbon reduction technologies based on LCA[J]. Journal of Traffic and Transportation Engineering, 2025, 25(5): 23-37. doi: 10.19818/j.cnki.1671-1637.2025.05.002

基于LCA的道路基础设施碳排放核算与低碳减排技术综述

doi: 10.19818/j.cnki.1671-1637.2025.05.002
基金项目: 

国家自然科学基金项目 52172392

湖北省重点研发计划 2023BAB091

详细信息
    作者简介:

    冉茂平(1981-),女,重庆人,武汉科技大学教授,工学博士,从事路面材料与性能研究

    通讯作者:

    周兴林(1965-),男,湖北监利人,武汉科技大学教授,工学博士

  • 中图分类号: U416

Review on road infrastructure carbon emission accounting and low-carbon reduction technologies based on LCA

Funds: 

National Natural Science Foundation of China 52172392

Key R&D Program of Hubei Province 2023BAB091

More Information
    Corresponding author: ZHOU Xing-lin (1965-), male, professor, PhD, zxl65@163.com
Article Text (Baidu Translation)
  • 摘要: 为了厘清生命周期评价(LCA)方法在道路基础设施碳排放核算方法以及现有减排技术的发展状况,通过定量挖掘现有文献方法,明确了当前道路交通系统碳排放的研究热点;总结了道路基础设施LCA碳排放核算分析框架,对比分析了不同类型LCA的碳排放核算方法和评估工具的特点;按照原材料获取、施工建造、运营使用、养护维修、报废回收5个生命阶段,分别总结了道路基础设施各阶段的碳排放贡献水平、影响因素与主要的减排措施。研究结果表明:在道路基础设施全生命周期中,材料生产和使用阶段对碳排放量的贡献最大;材料生产、建设、使用、维护等阶段碳排放主要影响因素分别源于材料及其生产加工方案、路面类型与结构、施工机械、车辆排放、养护技术及其导致的交通延误等;相应地,优化材料生产过程、使用清洁生产技术和回收材料,缩短材料运输距离、选用环保修复技术等方法则是道路基础设施全生命周期中主要的减排措施;未来道路基础设施LCA可开展建立现场核算数据库、构建标准化的碳核算体系框架、制定标准化的评估方法等工作,为实现道路基础设施的低碳可持续发展提供技术支持。

     

  • 图  1  英文文献出现频次最高的关键词

    Figure  1.  Top keywords derived from English literature

    图  2  英文文献关键词共现聚类图谱

    Figure  2.  Keywords co-occurrence cluster map of English literature

    图  3  中文文献关键词共现聚类图谱

    Figure  3.  Keywords co-occurrence cluster map of Chinese literature

    图  4  道路基础设施LCA碳排放系统边界

    Figure  4.  LCA carbon emission system boundary of road infrastructure

    图  5  不同沥青材料的碳排放(单位:kg·t-1)[5]

    Figure  5.  Carbon emissions of different asphalt materials (unit: kg·t-1)[5]

    图  6  道路生命周期四阶段排放比例[36]

    Figure  6.  Emission proportion in four stage of road life cycle[36]

    图  7  道路主要结构建造阶段的碳排放比例

    Figure  7.  Proportion of carbon emissions during construction stage of main road structure

    图  8  子项目二氧化碳的排放结果

    Figure  8.  CO2 emission results for sub-project

    图  9  不同竖曲线半径的单位距离碳排放[8]

    Figure  9.  Carbon emissions of different vertical curve segments[8]

    图  10  面层和基层在回收阶段的能耗[37]

    Figure  10.  Energy consumption of surface layer and base layer in recovery stage[37]

    图  11  不同车辆类型燃油消耗随路面平整度的增加情况[12]

    Figure  11.  Vehicle fuel consumption increase with road roughness levels[12]

    图  12  主要修复技术全生命周期碳排放量比值

    Figure  12.  Carbon emissions ratio of main repair techniques in life cycle

    表  1  不同类型生命周期评价方法对比

    Table  1.   Comparison of different types of LCA methods

    方法类型 优点 缺点 适用范围
    P-LCA 数据较有针对性,结果较准确 生命周期清单不完整,过程数据存在缺失;分析过程较为耗时 单个产品、项目
    EIO-LCA 生命周期清单较详尽, 可涵盖上游/间接环境影响且截断误差、时间成本以及复杂度较低 生命周期边界不完整且缺少详细过程信息,数据更新慢、数据精度低;不同部门对经济汇总的做法很难评估;经济的输入-输出只涉及不同部门,而消费者被排除在外 行业、区域、国家
    H-LCA 生命周期清单最完整、最准确 存在重复计算,遗漏PCA与IOA边界分析,特定研究中对该方法的描述不清晰,使用困难;缺少实时更新,缺乏可直接使用的自动化软件 单个产品、项目行业、区域、国家
    下载: 导出CSV

    表  2  生命周期评价工具

    Table  2.   LCA tools

    工具名称 研发者(年份) 主要应用领域 主要特点 相关性
    PaLATE[24] 加州大学伯克利分校(2003) 道路交通碳排放评估 具有生命周期思维,可分析不同阶段的碳排放贡献 与CHANGER和asPECT相关,但更侧重于整个道路交通系统的碳排放评估
    ECORCE[25] 法国交通科学技术研究所(2008) 生态系统评估 能够识别潜在的生态问题和短期/长期影响,评估多种生态因素,进行多样性分析 与Roadprint在生态方面有相似之处
    CHANGER[26] 国际道路联盟(2009) 道路交通系统温室气体排放评估 综合评估道路交通系统的温室气体排放,考虑不同因素对碳排放的影响 与Roadprint和ECORCE相关,但更专注于交通系统的温室气体排放
    Roadprint[27] 华盛顿大学(2012) 公路路面评价 能够评估新建和修复路面,可以作为一个升级版本的PaLATE,操作灵活 路面建设和维护方面的生态评估工具
    asPECT[28] 运输研究实验室(2012) 沥青路面碳排放评估 能够进行细化的碳排放分析,以嵌入式方式集成在路面设计软件中 与Roadprint不同,专注于沥青路面的碳排放评估
    PE-2[29] 密歇根技术大学(2012) 项目排放评估 综合定量评估项目各个阶段的碳排放 与以上工具相比,更专注于项目整体的排放评估
    下载: 导出CSV

    表  3  材料生产阶段主要材料消耗量和碳排放量

    Table  3.   Main material consumptions and carbon emissions in material production stage

    材料类型 消耗量 碳排放量/t
    炸药 1.02×103 t 2.71×103
    5.47×103 t 2.86×103
    矿粉 4.78×104 t 4.01×103
    沥青 4.69×104 t 1.14×104
    砂石 5.05 m3 1.51×104
    生石灰 3.47×105 t 2.78×105
    水泥 4.78×105 t 3.36×105
    钢材 2.29×105 t 3.78×105
    下载: 导出CSV

    表  4  维修1 km标准高速公路材料消耗量和机械投入量[55]

    Table  4.   Material consumption and mechanical input for repairing 1-kilometer standard expressway[55]

    材料类型 消耗量 机器类型 能源消耗量
    柴油/kg 汽油/kg 电力/(kW·h)
    石油沥青 485.6 t 沥青拌合设备 50 637.4 20 864.8
    改性沥青 160.7 t 轮胎式装载机 3 630.0
    乳化沥青 43.8 t 自卸车 16 538.5 230.58
    碎石 5 676.6 m3 沥青混合料摊铺机 789.3
    463.6 t 光轮压路机 5 354.5
    水泥 275.2 t 平地机 479.7
    下载: 导出CSV

    表  5  温拌技术与热拌技术排放对比

    Table  5.   Comparison of emissions between warm-mix technology and hot-mix technology

    测试项目 热拌沥青 温拌沥青 降幅比例/%
    二氧化碳排放量/% 2.6 1.0 61.5
    碳氧化合物排放量/(mg·m-3) 151 40 73.5
    一氧化碳排放量/(mg·m-3) 104.0 91.3 12.2
    二氧化硫排放量/(104 mg·m-3) 13.0 3.3 74.6
    烟尘排放量/(mg·m-3) 5.60 2.59 53.8
    下载: 导出CSV
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  • 收稿日期:  2024-06-21
  • 录用日期:  2024-12-23
  • 修回日期:  2024-09-23
  • 刊出日期:  2025-10-28

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