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GB/T 47538.1-2026Technical requirements for the assessment of emission reduction effects - Part 1: Travel (English PDF)

减排效果评估技术要求 第1部分:出行

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Issued by

SAMR; SAC

Level / Type

National · Recommended

Issue date

April 30, 2026

Implementation date

August 1, 2026

Scope

GB/T 47538.1-2026 is the English-translated version of 减排效果评估技术要求 第1部分:出行.

GB/T 47538.1-2026 is the Chinese national standard covering how the emission reduction from a change in how people travel is assessed - the baseline journey that would otherwise have been made, the mode shifted to, the data collected from the platform or the app, and the conservative assumptions that keep the claim honest. This is the machinery behind the personal carbon accounts several Chinese cities have launched. Part 1, first edition, in force since 1 August 2026. It was issued on 30 April 2026 and has been in force since 1 August 2026, as a first edition. The document is under the responsibility of the Standardization Administration of China. This page is published from the official record of the 2026 edition; the clause text of a standard this recent is not yet in circulation, and the figures, limits and tables it contains are those of the document itself, delivered in full with the English translation.

Document preview — GB/T 47538.1-2026

National Standard of the People's Republic of China

ICS
13.020
Classification
Z 04

Issued by: State Administration for Market Regulation; Standardization Administration of the PRC

Contents

  • 1 Scope
  • 4 Basic Principles
  • 9 Assess emission reductions
  • 9.4 Calculation of Emissions from Low-Carbon Travel Projects
  • 9.4.2 Carbon Emission Factors of Low-Carbon Travel
  • 10 Project Monitoring
  • 10.1 General Requirements

Foreword

This document complies with the provisions of GB/T 1.1-2020 "Standardization Work Guidelines Part

1.Structure and Drafting Rules of Standardization Documents". Drafting. This document is Part 1 of GB/T 47538 "Technical Requirements for Emission Reduction Effect Evaluation". GB/T 47538 has the following parts published.

1.Travel. Please note that some content in this document may involve patents. The issuing organization of this document assumes no responsibility for identifying patents. This document was proposed by the National Technical Committee on Standardization of Environmental Management (SAC/TC207). It is jointly managed by the Technical Committee (SAC/TC207) and the National Technical Committee on Standardization of Carbon Emission Management (SAC/TC548). This document was drafted by: China National Institute of Standardization, Beijing Municipal Center for Climate Change Management, and Jiangxi Provincial Government Affairs Administration Bureau. Beijing Jiaotong University, Beijing Didi Infinite Technology Development Co., Ltd., Beijing AutoNavi Cloud Technology Co., Ltd., Xinjiang Uygur Autonomous Region Quality... Basic Development Research Institute, Beijing Energy Group Co., Ltd. The main drafters of this document are. Zhang Lan, Hu Yongfeng, Bai Yan, Yu Fengju, Wang Chengyu, Sun Fen, Wang Li, Shen Xinyi, Feng Hua, Ding Junqiang, and Li Zhanyu. Halidan Abibula, Yang Ming, Zhao Yi, Wei Jiewen, Bu Qunjie, He Furong, Huo Shaowei, Li Xuebing.

To implement the national "dual-carbon" strategy and standardize the quantitative assessment of greenhouse gas emission reductions from voluntary social emission reduction projects, this document clarifies the reduction... The procedures and boundaries for emission quantification were established, and a scientific and feasible method for setting baselines and calculating emission reductions was developed. The techniques for quantitative assessment were also refined. Based on the technical procedures and data monitoring requirements, a unified and standardized quantitative assessment system for greenhouse gas emission reduction in social voluntary emission reduction projects was established. Standardized quantitative assessment techniques are used to verify the emission reduction effectiveness of voluntary emission reduction projects, optimize project planning, and facilitate carbon credit transactions. This provides quantitative evidence for easy mechanism alignment and policy incentive implementation, promotes standardized management of voluntary social emission reduction projects, and contributes to greenhouse gas reduction. Effective implementation of emission reduction targets will promote the formation of a green and low-carbon lifestyle throughout society. To facilitate domestic and international communication, the units of measurement in this document are "International Units of Measurement for Substances (Elements)" or "International Units of Measurement for Substances (Elements)". The values are expressed in the form of "units", such as tC for tons of carbon, tCO2 for tons of carbon dioxide, and Nm3 for cubic meters under standard conditions. GB/T 47538, "Technical Requirements for Emission Reduction Effectiveness Evaluation," will clarify the quantitative evaluation basis for emission reduction based on the characteristics of different voluntary emission reduction projects. This framework includes principles, procedures, quantitative scope, greenhouse gas identification, baseline scenarios, emission reduction assessment, project monitoring, data quality management, and emission reduction. The quantitative assessment report, according to GB/T 47538, is proposed to consist of the following parts.

3.Procurement. Technical Requirements for Emission Reduction Effectiveness Evaluation Part

1 Scope

GB/T 47538.1-2026 is the Chinese national standard covering how the emission reduction from a change in how people travel is assessed - the baseline journey that would otherwise have been made, the mode shifted to, the data collected from the platform or the app, and the conservative assumptions that keep the claim honest. This is the machinery behind the personal carbon accounts several Chinese cities have launched. Part 1, first edition, in force since 1 August 2026. It was issued on 30 April 2026 and has been in force since 1 August 2026, as a first edition. The document is under the responsibility of the Standardization Administration of China. This page is published from the official record of the 2026 edition; the clause text of a standard this recent is not yet in circulation, and the figures, limits and tables it contains are those of the document itself, delivered in full with the English translation.

1.Scope This document specifies the basic principles, procedures, scope of quantification, greenhouse gas identification, and baseline conditions for the quantitative assessment of emission reductions in low-carbon travel projects. The process includes. assessment of emission reductions, project monitoring, data quality management, and preparation of emission reduction quantification assessment reports. This document applies to personal use of public buses (electric buses), urban rail transit, new energy passenger cars, and carpooling new energy passenger cars within urban areas. A quantitative assessment of emission reductions for low-carbon travel behaviors such as using fuel-powered passenger cars, cycling, and walking to move from the origin to the destination. This document does not cover the quantitative assessment of lifecycle emission reductions of the products used for low-carbon travel.

4 Basic Principles

4.1 Correlation Select appropriate greenhouse gas sources, data, and methods.

4.2 Integrity This includes all relevant greenhouse gas emissions that meet the needs of individuals within the target town.

4.3 Consistency It enables meaningful comparisons of information related to greenhouse gases.

Note. When the same criteria and procedures are used, and emissions reductions are assessed twice periodically (e.g., at one-year intervals), and the results of the two assessments are comparable, it is called [a specific assessment]. Meaningful comparison.

4.4 Accuracy Minimize bias and uncertainty as much as possible.

4.5 Transparency Subject to compliance with national policies and trade secret requirements, publish fully applicable greenhouse gas information so that individuals in the target towns can access it. Make reasonable decisions.

Note. To meet the principle of transparency, the following are generally required, but not limited to.

a) Explain and clarify the principles and related content on which the baseline scenario and low-carbon travel scenario are selected, and document them;

b) Explain and document the selection of assessment procedures, assessment methods, emission factors, activity data, etc.

4.6 Conservatism Ensure that the assumptions, figures, and assessment methods used do not overestimate greenhouse gas emission reductions.

5.Procedure The procedure for assessing emission reductions from low-carbon travel is shown in Figure 1.

6.Quantification range Figure 2 shows a schematic diagram of the boundary and scope of the quantitative assessment of emission reduction for low-carbon travel.

7.Identification of Greenhouse Gas Types Table 1 shows the identification of greenhouse gas types for low-carbon travel projects within the target towns.

8.Baseline Scenario The baseline scenario in this document is the most recent year for which data was available before project implementation, and the average annual overall travel status of all residents in the target town. See section

9 Assess emission reductions

9.1 General Rules Project owners or their clients collect data on low-carbon travel-related activities of individuals within the target town over a specific period. Emission reductions will be assessed in accordance with the procedures outlined in this document. The formulas for calculating the project's emission reductions are shown in

9.2 Emission Reduction The formula for calculating emission reduction is shown in equation (1).

9.3 Calculation of baseline scenario emissions The formulas for calculating baseline scenario emissions over a certain period are shown in equations (2) and (3).

9.4 Calculation of Emissions from Low-Carbon Travel Projects

9.4.1 General Provisions The formula for calculating individual low-carbon travel emissions within a certain period is shown in equation (4).

9.4.2 Carbon Emission Factors of Low-Carbon Travel

9.4.2.1 Carbon emission factors from taking public buses (trolleybuses) and urban rail transit Based on the availability and detail of travel data in each region, carbon emission factors are calculated, and regions can be categorized into those with detailed travel data. Districts and areas with basic transportation data. For areas with detailed traffic data, the carbon emission factor calculation formula for taking public buses (trolleybuses) is shown in equation (5).

9.4.2.3 Carbon emission factors of carpooling new energy passenger vehicles The formula for calculating the carbon emission factor of carpooling new energy passenger vehicles is shown in equation (8).

9.4.2.4 Carbon emission factors of carpooling gasoline-powered passenger vehicles The formula for calculating the carbon emission factor of a shared fuel-powered passenger car is shown in equation (9). In areas with basic traffic data, the carbon emission factor for driving gasoline-powered passenger cars can be calculated using the default value method, see Appendix B.

9.4.2.5 Carbon Emission Factors of Cycling The default carbon emission factor EF6 for non-electric riding is 0. Based on the principle of conservatism, sampling surveys can be conducted to investigate the proportion of electric and non-electric riding, electricity consumption, and corresponding riding distances. Data is used to calculate the carbon emission factor of cycling.

9.4.2.6 Carbon Emission Factors of Walking The default carbon emission factor EF7 for walking is 0.

9.4.3 Low-carbon travel activity level The activity level (ADn) for low-carbon travel should be based on the travel trajectory obtained from relevant monitoring platforms and systems, i.e., the starting position (Ls,n) and ending position of the trip. The trajectory coordinates (Lc,n) during the journey, the end position of the journey (Le,n), etc. The activity level ADn for low-carbon travel involves AD1, AD2, AD3, AD4, AD5, AD6, and AD

7.When n is 1, it represents taking public transportation. (Electric) vehicle; when n is 2, it means taking urban rail transit; when n is 3, it means driving a new energy passenger car; when n is 4, it means sharing a new energy passenger car. Vehicle; when n is 5, it is a shared fuel-powered passenger car; when n is 6, it is cycling; when n is 7, it is walking. Accurate data should be obtained from the ticketing system to identify and use public buses (trolleybuses) and urban rail transit as modes of transportation. Travel mileage. When relevant ticketing system data is unavailable, travel mileage should be based on the travel trajectory monitored on the relevant platform. The mileage should be identified based on the monitored driving trajectory of the new energy passenger vehicle. The corresponding mode of transportation and travel distance should be identified based on the usage information collected by the platform that can record ride-sharing order information. The corresponding mode of transportation and mileage should be identified based on usage information collected by platforms that can record cycling order information. Where it is not possible to obtain... When obtaining relevant information, identification should be based on the driving trajectory monitored on the relevant platform. Mileage should be identified based on planned routes and actual monitored walking trajectories on relevant platforms.

Note. The monitoring method for the travel mileage corresponding to double and single card swipes on public buses (trolleybuses) is detailed in Appendix C.

10.1 General Requirements

10.1.1 The project owner or its client shall establish a monitoring plan to guide the acquisition, recording, and analysis of greenhouse gas emissions from low-carbon travel. Data and information on the volume of data. The monitoring plan should include, but is not limited to.

a) Monitoring objectives;

b) Types and units of measurement of data and information;

d) Monitoring methods, including estimation, measurement, or calculation methods, should all employ calibrated measurements that conform to relevant industry standards. The instrument is used;

e) Monitoring frequency, real-time monitoring;

f) Quality assurance and quality control of data and information;

g) Monitoring responsibilities;

h) Greenhouse gas information system, including the storage and location of data.

10.1.2 The project owner or the party commissioning the project owner shall take necessary measures to ensure the effective implementation of the monitoring plan.

10.1.3 For default values in case data is unavailable, see Appendix B.

10.2 Baseline Scenario-Related Monitoring Data and Parameters Table 2 shows the units, descriptions, and acquisition methods of baseline scenario-related monitoring data and parameters.

11 Data Quality Management The project owner or its authorized representative should collect relevant data and information on individual low-carbon travel within the town and the baseline scenario obtained. Management, including but not limited to.

a) Establish and maintain a complete data monitoring and baseline scenario information collection and analysis management system for low-carbon travel;

b) Conduct routine checks on accuracy, regularly maintain and manage low-carbon travel monitoring data, and record and archive the data. The archived data should be kept at least [number missing]. Deposit until two years after the end of the last crediting period;

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This preview omits tables, figures, formulas and parts of the technical clauses. The complete document — 30 pages — is available in the English PDF.

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