Articles | Volume 18, issue 18
https://doi.org/10.5194/gmd-18-6479-2025
© Author(s) 2025. This work is distributed under
the Creative Commons Attribution 4.0 License.Implementation of the MOSAIC aerosol module (v1.0) in the Canadian air quality model GEM-MACH (v3.1)
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- Final revised paper (published on 26 Sep 2025)
- Supplement to the final revised paper
- Preprint (discussion started on 17 Oct 2024)
- Supplement to the preprint
Interactive discussion
Status: closed
Comment types: AC – author | RC – referee | CC – community | EC – editor | CEC – chief editor
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RC1: 'Comment on egusphere-2024-2958', Peter Colarco, 17 Jan 2025
- AC1: 'Reply to RC1', Kirill Semeniuk, 18 Feb 2025
- AC2: 'Additional information on RC1', Kirill Semeniuk, 15 Mar 2025
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RC2: 'Comment on egusphere-2024-2958', Anonymous Referee #2, 24 Jan 2025
- AC3: 'Reply to RC2', Kirill Semeniuk, 15 Mar 2025
Peer review completion
AR: Author's response | RR: Referee report | ED: Editor decision | EF: Editorial file upload
AR by Kirill Semeniuk on behalf of the Authors (25 Mar 2025)
Author's response
Author's tracked changes
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ED: Referee Nomination & Report Request started (11 Apr 2025) by Samuel Remy
RR by Anonymous Referee #3 (24 Apr 2025)

ED: Publish as is (30 Jun 2025) by Samuel Remy
AR by Kirill Semeniuk on behalf of the Authors (09 Jul 2025)
Author's response
Manuscript
Two sectional aerosol schemes are tested in the GEM-MACH modeling framework. A relatively simpler scheme based on the Canadian Aerosol Module (CAM) is compared to a more complex scheme based on Model for Simulating Aerosol Interactions and Chemistry (MOSAIC). The CAM and MOSAIC configurations are both run for a year using the same size bin structure, emissions, and meteorology. Two simulations are performed for each configuration, a baseline using the default dry deposition scheme (called REF) and a sensitivity experiment that implements a newer dry deposition scheme (called EMR). Model results are compared to surface observations of component PM2.5 concentrations from networks over Canada and the USA, as well as retrieved columnar volume size distributions from AERONET sub photometers. Performance is evaluated in terms of sulfate, nitrate, ammonium, total particular mass, and aerosol water content.
My observation is that performance is more alike than dissimilar across the suite of simulations performed. Particularly for sulfate the results of the different configurations are very similar in terms of the seasonal cycles and spatial distributions. There is more diversity between the MOSAIC and CAM nitrate comparisons (although still highly correlated). Ammonium is somewhat intermediate. There is a notable improvement in the simulated nitrate surface concentration for the MOSAIC scheme with the updated (EMR) dry deposition scheme, which seems to give overall the best performance for total PM of nitrate (Figure 9). THE MOSAIC scheme additionally better agrees with the AERONET retrieved particle size distribution in terms of the placement of the fine mode and simulation of the observed gap between the fine and coarse modes. CAM by contrast has a larger fine mode that “smears” into the coarse mode with no gap. (Neither configuration represents the coarse mode especially well.) In part the differences are attributed to numerical diffusion (CAM does not conserve particle number explicitly and so numerical diffusion is more prevalent) and the CAM result is slightly improved by calling thermodynamics routines for each bin rather than in a bulk approach (at added computational expense).
It seems that the MOSAIC scheme with the EMR dry deposition produces overall the best set of results, albeit with a computational cost 3x the CAM run. Some improvements to the CAM configuration seem to be possible. A difference in the thermodynamics (no treatment of cations in CAM while they are treated in MOSAIC) are important to the nitrate simulation. There does not seem to be sufficient information given to judge the “best” approach. For example, if the goal is 5 day forecast of PM and it takes 1 hour to produce with CAM and 3 hours to produce with MOSAIC that seems insignificant. If it is 1 day versus 3 days then it matters. I can’t judge this given what was in the paper.
I suggest accepting the paper subject to minor revisions. The paper is thorough and well written with only a few errors noted. I do suggest some slight alteration of the presentation in terms of providing some quantitative information in tables.
Specific points:
Line 70 - what is the implication here of chemical and aerosol tracers not being transported by convection? This seems like it would be important to determining the vertical profile. Can you add anything about why this is not a first order issue to be addressed?
Line 213 - I am confused about what is being discussed here, noting particularly the claim to be using GEOS-5 driving data. Later on line 264 you say you are getting dynamical information from GDPS. Is something in error here?
Captions to figures 2b and 2c need to be corrected to refer to figure 2a (not 3a)
The numerical values in the labeling on Figure 5 are impossible to read even blown up on my screen. I suggest that you tabulate these either in the main text of the supplement. This would also give a more clear presentation of “best” values. Same comment applies to figures 6-9.
Line 625 - I find the appeal to non-sphericity to be unconvincing (although it could even be right). Why not consider that you just don’t have a great simulation of coarse aerosol amounts? You don’t seem to be evaluating it particularly here and so maybe things like dust and sea salt that gets into your domain from remote sources isn't done well (or local dust size distribution).
Line 711 - type - “presented in Sections 4.1 and 4.2”
Figure 14 - State explicitly here that the difference is EMR-REF