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COMMUNICATIONS EARTH & ENVIRONMENT | https://doi.org/10.1038/s43247-023-01050-7
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Fig. 7 Spatiotemporal analysis—impact global sulfur cap. Annual proportional difference of SO» VCD levels between 2019 and 2021.
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Fig. 8 Impact NECA on NO,. Box plot of annual NO, VCD levels between different areas before (BFNC) and after (AFNC) the European NECA entered into
force in 2021, with minimum, 25% percentile, median, 75% percentile and maximum.
satellite data clearly reveals visible shipping patterns (Supple-
mentary Fig. 11). Consequently, it can be stated that emissions
from OGVs provide the dominant factor in the observed NO,
VCD data.
When looking at the average NO, levels before and after the
implementation of the NECA for the different areas, it was
demonstrated that NO, levels after the introduction of the NECA
were impacted in different ways. The BAQPZJR area remained
ihe most polluted area, with the English Channel following
closely behind. However, since the implementation of the NECA,
che Bay of Biscay became the third most polluted area, before the
Northern NECA.
Temporal analysis of atmospheric NO; data. For the temporal
analysis of NO,, an annual and a monthly approach was used. For
the annual approach, the proportional difference between 2019
OMMUNICATIONS EARTH & ENVIRONMENT | (2023)4:391 | https: //doi.0rg/10.1038/s43247-023-01050-7 | www.nature.com/commsenv