资源科学 ›› 2019, Vol. 41 ›› Issue (7): 1201-1212.doi: 10.18402/resci.2019.07.02
收稿日期:
2018-08-04
修回日期:
2019-01-22
出版日期:
2019-07-25
发布日期:
2019-07-25
作者简介:
作者简介:王悦,女,安徽人,硕士生,研究方向为城市生态学。E-mail:
基金资助:
Yue WANG1,2(), Feng LI3(
), Xiao SUN1,2
Received:
2018-08-04
Revised:
2019-01-22
Online:
2019-07-25
Published:
2019-07-25
摘要:
家庭生活消费碳排放是全球碳排放的重要组成部分并已成为新的增长点,中国家庭直接和间接的能源消耗及碳排放量占有率逐渐扩大的趋势明显,为国家实现减排目标带来难题。本文运用文献计量及对比分析的方法在整理归纳家庭消费碳排放研究进展的基础上,明确碳排放系数法、投入产出法、生命周期评价法和消费者生活方式法的主要内容与适用对象,比较其优缺点与适用情景。指出了在实证分析中影响研究结果的4个主要因素:问卷数据有效性、家庭消费行为模式差异性、社区影响和回弹效应。发现2009年以来,家庭碳排放研究成果逐年递增,基于宏观统计数据的研究成果显著多于微观调查研究;碳排放系数法和投入产出法是最常用的2种碳排放核算方法,具体应用则取决于研究目的和数据的可获取性;充分考虑家庭碳排放的影响因素,适当优化核算方法有利于提高研究结果的准确度。本文可为今后城市家庭消费碳排放研究视角与方法提供参考,为城市家庭碳排放管理提供了科学依据。
王悦, 李锋, 孙晓. 城市家庭消费碳排放研究进展[J]. 资源科学, 2019, 41(7): 1201-1212.
Yue WANG, Feng LI, Xiao SUN. Progress of research on carbon emissions of urban household consumption[J]. Resources Science, 2019, 41(7): 1201-1212.
表1
家庭消费碳排放来源"
类别 | 消费种类 | 消费行为 |
---|---|---|
直接碳排放 | 家庭直接用能 | 消费各类化石燃料(煤炭、汽油、柴油、煤油、液化石油气、天然气、煤气) |
私人交通 | 私家车、摩托车等化石燃料用车 | |
间接碳排放 | 食品 | 消费粮食、豆类及豆制品、油和脂肪、肉类、家禽及相关产品、蛋、牛奶和奶制品等食物 |
衣着 | 消费服装及服装辅料、鞋、帽;服装裁剪费、清洗等相关加工服务 | |
居住 | 消费或自建房屋;房屋装修、日常维护与修理消费;用水、用电、集体供暖 | |
生活用品及服务 | 消耗家用电器设备、家具设备、家用纺织品、个人护理用品等 | |
交通通信 | 交通和通信工具及相关的各种服务费、维修费和车辆保险等消费 | |
教育、文化和娱乐 | 教育服务、文娱用品及服务消费 | |
医疗保健 | 医疗保健器具、药品保健品消费、医疗服务消费 | |
其他用品及服务 | 个人饰品、箱包、旅馆住宿、美容美发和洗浴、保险等社会保护消费 |
表2
家庭消费CO2排放系数"
类型 | 种类 | 单位 | 碳排放系数 | 类型 | 种类 | 单位 | 碳排放系数 |
---|---|---|---|---|---|---|---|
能源与资源 | 电力 | kgCO2/kW·h | 0.98a | 交通 | 电瓶车 | kgCO2/km | 0.08h |
液化石油气 | kgCO2/罐 | 43.21b | 摩托车 | kgCO2/L | 2.24e | ||
管道天然气 | kgCO2/m3 | 2.15b | 私家车(汽油) | kgCO2/L | 2.34d | ||
集中供暖 水 垃圾 | kgCO2/m2 kgCO2/t kgCO2/kg | 42.63c 0.30d 2.06e | 私家车(柴油) | kgCO2/L | 2.78e | ||
公交车 | kgCO2/km | 0.04h | |||||
出租车 | kgCO2/km | 0.50d | |||||
食品、服装 | 大米 | kgCO2/kg | 0.3268f | 地铁 | kgCO2/km | 0.06e | |
畜禽肉类 | kgCO2/kg | 0.2546f | 单位班车 | kgCO2/km | 0.04e | ||
水产品类 | kgCO2/kg | 0.1433f | |||||
蛋类 | kgCO2/kg | 0.1510f | 按照行业和消费支出划分计算 | 食品 | kgCO2/元 | 0.068i | |
蔬菜 | kgCO2/kg | 0.0274f | 衣着 | kgCO2/元 | 0.065i | ||
水果 | kgCO2/kg | 0.0498f | 居住 | kgCO2/元 | 1.001i | ||
牛奶 酒饮类 植物油 衣服 鞋 | kgCO2/kg kgCO2/kg kgCO2/kg kgCO2/件 kgCO2/双 | 0.0629f 0.0411f 0.7666f 6.4000d 5.7600g | 生活用品和服务 交通通信 教育文化和文娱 医疗保健 其他用品和服务 | kgCO2/元 kgCO2/元 kgCO2/元 kgCO2/元 kgCO2/元 | 0.032i 0.134i 0.166i 0.050i 0.058i |
表3
投入产出法的3种类型"
种类 | 适用对象 | 计算方法 |
---|---|---|
基本投入产出法 (IO-EA-basic) | 计算经济部门或一般家庭的平均商品需求,能比较不同国家的环境负荷以及经济结构变化产生的影响 | 部门累计能源强度乘以家庭最终需求的消费货币数据 |
投入产出消费支出法(IO-EA-expenditure) | 衡量不同家庭消费模式产生的碳排放量差异,可反映出每个消费项目和消费类别的能源需求 | 家庭消费支出调查数据乘以部门累计碳排放强度 |
投入产出过程分析法(IO-EA-process) | 能够分析输入输出的各个阶段,计算出各部门累计能源强度、家庭直接和间接的能源需求、每个消费项目的能源需求、累计能源强度和产品与服务的需求 | 将物理数据、能源数据和经济数据(消费者价格、剩余价值等)相结合,运用混合能流分析法计算 |
表4
家庭消费碳排放研究方法的优缺点比较"
方法 | 数据需求 | 优点 | 缺点 |
---|---|---|---|
碳排放系数法 | 各项消费的碳排放系数; 统计数据或家庭调查数据 | 计算过程简便容易普及 | 不同地区的碳排放系数难以准确估计计算结果,真实度一般 |
投入产出法 | 全国家庭支出调查; 投入产出表; 燃料和能源的价格指数 | 提供一种可以以统一的方式更新或应用于不同的人群的标准分析方法 | 预测长期影响时缺乏可靠性,假设的固定技术系数不能反映技术的进步和弹性 |
生命周期评价法 | 家庭调查数据; 文献调研数据; 公共数据库; 产品生产中各环节的详细数据; 企业年度财务报告等 | 能对家庭消费对象的整个生命周期各阶段能耗产生的碳排量进行分析,可计算微观产品的碳排放量 | 对数据要求较高、获取不易,获取的数据量大,不易处理;难以进行经济、技术、社会效益分析 |
消费者生活方式法 | 家庭调研数据; 投入产出表; 区域统计数据 | 考虑了影响消费的相互作用因素,重在分析个体特征对碳排放的影响;将投入产出法和碳排放系数法结合,能很好地反应宏观和微观层面的家庭碳排放量 | 调研工作量大且对调研数据准确性要求高;模型应用程序复杂;进出口产品消费产生的碳排放难以计算;居民消费支出数据与宏观投入产出数据难以高度契合 |
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