Abstract

Abstract. Future trends in air pollution and greenhouse gas (GHG) emissions for China are of great concern to the community. A set of global scenarios regarding future socio-economic and climate developments, combining shared socio-economic pathways (SSPs) with climate forcing outcomes as described by the Representative Concentration Pathways (RCPs), was created by the Intergovernmental Panel on Climate Change (IPCC). Chinese researchers have also developed various emission scenarios by considering detailed local environmental and climate policies. However, a comprehensive scenario set connecting SSP–RCP scenarios with local policies and representing dynamic emission changes under local policies is still missing. In this work, to fill this gap, we developed a dynamic projection model, the Dynamic Projection model for Emissions in China (DPEC), to explore China's future anthropogenic emission pathways. The DPEC is designed to integrate the energy system model, emission inventory model, dynamic projection model, and parameterized scheme of Chinese policies. The model contains two main modules, an energy-model-driven activity rate projection module and a sector-based emission projection module. The activity rate projection module provides the standardized and unified future energy scenarios after reorganizing and refining the outputs from the energy system model. Here we use a new China-focused version of the Global Change Assessment Model (GCAM-China) to project future energy demand and supply in China under different SSP–RCP scenarios at the provincial level. The emission projection module links a bottom-up emission inventory model, the Multi-resolution Emission Inventory for China (MEIC), to GCAM-China and accurately tracks the evolution of future combustion and production technologies and control measures under different environmental policies. We developed technology-based turnover models for several key emitting sectors (e.g. coal-fired power plants, key industries, and on-road transportation sectors), which can simulate the dynamic changes in the unit/vehicle fleet turnover process by tracking the lifespan of each unit/vehicle on an annual basis. With the integrated modelling framework, we connected five SSP scenarios (SSP1–5), five RCP scenarios (RCP8.5, 7.0, 6.0, 4.5, and 2.6), and three pollution control scenarios (business as usual, BAU; enhanced control policy, ECP; and best health effect, BHE) to produce six combined emission scenarios. With those scenarios, we presented a wide range of China's future emissions to 2050 under different development and policy pathways. We found that, with a combination of strong low-carbon policy and air pollution control policy (i.e. SSP1-26-BHE scenario), emissions of major air pollutants (i.e. SO2, NOx, PM2.5, and non-methane volatile organic compounds – NMVOCs) in China will be reduced by 34 %–66 % in 2030 and 58 %–87 % in 2050 compared to 2015. End-of-pipe control measures are more effective for reducing air pollutant emissions before 2030, while low-carbon policy will play a more important role in continuous emission reduction until 2050. In contrast, China's emissions will remain at a high level until 2050 under a reference scenario without active actions (i.e. SSP3-70-BAU). Compared to similar scenarios set from the CMIP6 (Coupled Model Intercomparison Project Phase 6), our estimates of emission ranges are much lower than the estimates from the harmonized CMIP6 emissions dataset in 2020–2030, but their emission ranges become similar in the year 2050.

Highlights

  • The rapid development of China has led to severe air pollution due to the ever-increasing energy demand and lax environmental legislation over the past decades, and this exerts negative influences on human health, climate, agriculture, and ecosystems (Liu et al, 2019; Xue et al, 2019a; Zheng et al, 2019)

  • We created our scenarios based on the Coupled Model Intercomparison Project Phase 6 (CMIP6) global development modes and societal conditions, more realistic short- and long-term emission control policies are integrated into our emission scenarios in China

  • There are obvious gaps for major air pollutant emissions in the base year except for NMVOCs, and the SO2, NOx, and black carbon (BC) emissions in 2015 from the CMIP6 database are higher than those from our Multi-resolution Emission Inventory for China (MEIC) emission inventory by 43 %, 39 %, and 79 %, respectively. These gaps are mainly caused by the underestimation of emission reductions obtained from China’s Action Plan in the CMIP6 database, and the emission bias in the base year would pass to the future and lead to different emission mitigation pathways

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Summary

Introduction

The rapid development of China has led to severe air pollution due to the ever-increasing energy demand and lax environmental legislation over the past decades, and this exerts negative influences on human health, climate, agriculture, and ecosystems (Liu et al, 2019; Xue et al, 2019a; Zheng et al, 2019). The purposes of developing the DPEC and creating a new set of Chinese scenarios are as follows: (1) connect with the IPCC scenario assembly, (2) synthetically consider region-specific and sectorbased local policies, (3) develop technology-based turnover models for key emitting sectors to simulate the dynamic changes in future technologies, and (4) provide a set of emission projection datasets to the community. The development of this dynamic model and associated scenarios aims to identify win-win measures and pathways to support the future’s short- and long-term synergizing actions on the environment and climate for policymakers

Model framework
The GCAM-China model
Linkage between GCAM-China and MEIC emission model
Harmonization of energy consumption for the year 2015
Sector-based emission projection module
Energy supply
Industrial combustion
Industrial non-combustion
Residential sector
Transportation sector
Agriculture
Definition of scenarios
Power sector
Industrial sector
Evolution of China’s future energy system during 2015–2050
Emission trends during 2010–2050
Discussion
Limitations and uncertainties
Policy implications
Full Text
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