Recent reduction in NO <i> _x </i> emissions over China: synthesis of satellite observations and emission inventories

TLDR

Tropospheric nitrogen dioxide (NO₂) column densities measured from space are widely used to infer trends in terrestrial nitrogen oxide (NOx) emissions. The study investigates changes in NO₂ column densities over China from 2005 to 2015 to examine NOx emission trends and their driving forces. The authors use OMI satellite observations and compare them with bottom‑up emission inventories to assess these trends. OMI data show a national NO₂ peak in 2011 followed by a 32 % decline to 2015, matching a 21 % drop in bottom‑up NOx estimates, with the decline driven mainly by power‑plant SCR deployment (56 % reduction) and earlier vehicle emission regulations in major cities.

Abstract

Tropospheric nitrogen dioxide (NO2) column densities detected from space are widely used to infer trends in terrestrial nitrogen oxide (NOx) emissions. We study changes in NO2 column densities using the Ozone Monitoring Instrument (OMI) over China from 2005 to 2015 and compare them with the bottom-up inventory to examine NOx emission trends and their driving forces. From OMI measurements we detect the peak of NO2 column densities at a national level in the year 2011, with average NO2 column densities deceasing by 32% from 2011 to 2015 and corresponding to a simultaneous decline of 21% in bottom-up emission estimates. A significant variation in the peak year of NO2 column densities over regions is observed. Because of the reasonable agreement between the peak year of NO2 columns and the start of deployment of denitration devices, we conclude that power plants are the primary contributor to the NO2 decline, which is further supported by the emission reduction of 56% from the power sector in the bottom-up emission inventory associated with the penetration of selective catalytic reduction (SCR) increasing from 18% to 86% during 2011–2015. Meanwhile, regulations for vehicles also make a significant contribution to NOx emission reductions, in particular for a few urbanized regions (e.g., Beijing and Shanghai), where they implemented strict regulations for vehicle emissions years before the national schedule for SCR installations and thus reached their NO2 peak 2–3 years ahead of the deployment of denitration devices for power plants.