A multi-model approach to monitor emissions of CO<sub>2</sub> and CO from an urban–industrial complex
Monitoring urban–industrial emissions is often challenging because observations are scarce and regional atmospheric transport models are too coarse to represent the high spatiotemporal variability in the resulting concentrations. In this paper we apply a new combination of an Eulerian model (Wea...
Main Authors: | , , , , , |
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Format: | Article |
Language: | English |
Published: |
Copernicus Publications
2017-11-01
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Series: | Atmospheric Chemistry and Physics |
Online Access: | https://www.atmos-chem-phys.net/17/13297/2017/acp-17-13297-2017.pdf |
Summary: | Monitoring urban–industrial emissions is often challenging
because observations are scarce and regional atmospheric transport models are
too coarse to represent the high spatiotemporal variability in the resulting
concentrations. In this paper we apply a new combination of an Eulerian model
(Weather Research and Forecast, WRF, with chemistry) and a Gaussian plume model (Operational Priority
Substances – OPS). The modelled
mixing ratios are compared to observed CO<sub>2</sub> and CO mole fractions at
four sites along a transect from an urban–industrial complex (Rotterdam, the
Netherlands) towards rural conditions for October–December 2014. Urban
plumes are well-mixed at our semi-urban location, making this location suited
for an integrated emission estimate over the whole study area. The signals at
our urban measurement site (with average enhancements of 11 ppm CO<sub>2</sub>
and 40 ppb CO over the baseline) are highly variable due to the presence of
distinct source areas dominated by road traffic/residential heating emissions
or industrial activities. This causes different emission signatures that are
translated into a large variability in observed
ΔCO : ΔCO<sub>2</sub> ratios, which can be used to identify
dominant source types. We find that WRF-Chem is able to represent synoptic
variability in CO<sub>2</sub> and CO (e.g. the median CO<sub>2</sub> mixing ratio
is 9.7 ppm, observed, against 8.8 ppm, modelled), but it
fails to reproduce the hourly variability of daytime urban plumes at the
urban site (<i>R</i><sup>2</sup> up to 0.05). For the urban site, adding a plume model to
the model framework is beneficial to adequately represent plume transport
especially from stack emissions. The explained variance in hourly, daytime
CO<sub>2</sub> enhancements from point source emissions increases from 30 %
with WRF-Chem to 52 % with WRF-Chem in combination with the most detailed
OPS simulation. The simulated variability in
ΔCO :  ΔCO<sub>2</sub> ratios decreases drastically from 1.5 to
0.6 ppb ppm<sup>−1</sup>, which agrees better with the observed standard
deviation of 0.4 ppb ppm<sup>−1</sup>. This is partly due to improved wind
fields (increase in <i>R</i><sup>2</sup> of 0.10) but also due to improved point source
representation (increase in <i>R</i><sup>2</sup> of 0.05) and dilution (increase in <i>R</i><sup>2</sup> of
0.07). Based on our analysis we conclude that a plume model with detailed and
accurate dispersion parameters adds substantially to top–down monitoring of
greenhouse gas emissions in urban environments with large point source
contributions within a ∼ 10 km radius from the observation sites. |
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ISSN: | 1680-7316 1680-7324 |