Articles | Volume 18, issue 21
https://doi.org/10.5194/amt-18-6021-2025
© Author(s) 2025. This work is distributed under the Creative Commons Attribution 4.0 License.
Urban pollution monitoring with the AOTF-based NO2 camera: validation with other DOAS instruments
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- Final revised paper (published on 03 Nov 2025)
- Preprint (discussion started on 02 Jun 2025)
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-2025-2255', Anonymous Referee #1, 25 Jun 2025
- AC1: 'Response to referee comments', Pierre Gramme, 06 Aug 2025
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RC2: 'Comment on egusphere-2025-2255', Anonymous Referee #2, 07 Jul 2025
- AC1: 'Response to referee comments', Pierre Gramme, 06 Aug 2025
Peer review completion
AR: Author's response | RR: Referee report | ED: Editor decision | EF: Editorial file upload
AR by Pierre Gramme on behalf of the Authors (06 Aug 2025)
Author's response
Author's tracked changes
Manuscript
ED: Publish subject to minor revisions (review by editor) (10 Aug 2025) by Ulrich Platt
AR by Pierre Gramme on behalf of the Authors (20 Aug 2025)
Author's response
Author's tracked changes
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ED: Publish as is (30 Aug 2025) by Ulrich Platt
AR by Pierre Gramme on behalf of the Authors (08 Sep 2025)
Review of Gramme et al. (2025): "Urban pollution monitoring with the AOTF-based camera: NO2 validation with other DOAS instruments"
The manuscript presents a novel ground-based NO2 imaging instrument based on acousto-optic tunable filter (AOTF). The new instrument builds on a previous AOTF-based instrument and aims at capturing high spatial and temporal variability of the reactive NO2, a key trace gas for air pollution studies. The capabilities of the new instrument are described and tested during a field campaign in an urban environment in Italy. The imager was mounted next to two DOAS-type well-established instruments (MAX-DOAS and Pandora). NO2 differential slant column densities (dSCD) obtained after performing the DOAS analysis of the three instruments’ spectra are compared and their differences assessed. Overall, the imaging results show good agreement with the reference instruments (strong correlation for SCD observations), demonstrating the potential of the new instrument in the context of urban air quality monitoring. The authors assess the limitations of the new instrument and suggest future work to keep on improving the technique and its applications.
The manuscript is well presented and the methodology is well described. Figures are clear and support conclusions. Overall, publication is recommended after addressing the following comments in the manuscript to further strengthen its impact.
General Comments:
The manuscript could benefit from a more detailed comparison with other NO2 remote sensing instrument, particularly alternative imaging approaches such as grating-based imaging DOAS, gas correlation cameras (e.g. volcanoes studies) or Fabry-Perot systems. This would help to frame the novelty of the instrument presented.
The manuscript uses NO2 dSCD for instrument comparison and, towards the end of the draft, the authors state a future use of the O4 bands for light path assessment. However, it could help the reader if the authors could clearly state at the beginning of the manuscript that the relationship between NO2 dSCD and actual concentrations of NO2 depends on several factors (e.g., aerosol, clouds, surface albedo), which may not have the same effect on all the three instruments. Indeed, including O4 band and inversion of NO2 concentration would be crucial for a thorough assessment of the capabilities of the (three) instruments, their detection limits and their comparability.
Also, the authors compare the new instrument with the two reference instruments and later on, they compare the reference instruments between themselves (last paragraph of Sect. 5.2). However, the authors are comparing three instruments, with three different field of view and two different DOAS (reference type) analysis. Also, as shown in Table 3, three different DOAS settings are used for the analysis. All these differences will affect the comparability of the data. The manuscript and conclusions could benefit if the two reference instruments were firstly compared with each other so a baseline for the quality of the comparison could be set. This could e.g. state (and quantify) the limitation of comparing NO2 dSCD analyzed with a fixed zenith reference spectrum (new instrument and MAXDOAS) with those analyzed with a sequential reference spectrum (Pandora).
Specific Comments:
P3, L52: “…, many more wavelengths are now acquired in routine operations in order to achieve higher accuracy”. Please be more specific.
P3, L56: Instrument description. Is the instrument calibrated radiometrically? How does temperature changes affect the AOTF spectral tunning?
P3, L70: “more compact”. Please provide size.
P6, L118: “In that case, a 1-D NO2 field can be observed”. Do the authors mean “can be observed per azimuth?”. In that, case, would it be a 2-D field?
P6, L124: “…capture complete images of the scene, but one wavelength at a time”. How long does it take to gather one image at a given λ before moving to the next λ?
P7, L128: “lower signal-to-noise ratio”. Does the instrument have a SZA limit where the SNR is far too low to assure the quality of the observation? Given the case, please provide such SZA limit.
P7, L131: “… focusing on a limited number of wavelengths”. How do authors decide how many λ are a minimum? Please specify the rationale behind.
P8, L161: “PRNU” How is the PRNU characterized?
P9, L166: “cosmetic step”. What do the authors mean with that? Do you mean the PRNU correction could be omitted? Is PRNU 100% independent of light intensity?
P14, L266: “lowest elevation angle”. Which angle? Elevation angle of the Sun or of the telescope? Clarify
P14, L267-269: The way it is written how the MAX-DOAS is compared to the Pandora observations seems a bit confusing. Please, detail the procedure in more detail.
P16, L295-296: “not shown”. Including the comparison with Pandora could assist the reader and the conclusions (supplementary?).
P16, L296-297: “…short slant column of NO2 between them and the instruments.” What do the authors mean? A shorter light path?
P17, L325: The authors refer to the effect of “moving clouds”. How would aerosols affect?
P21, L346: “Given the unconventional concept of the NO2 camera...”. What do the authors mean by “unconventional”?
P21, L361: What is the result of those changes in illumination conditions?
P22, L373: “pollution events” are often linked not only to NO2 but also to particles. The draft could benefit if the authors could assess the possible effect of aerosol on observations.
Technical Corrections:
P1, L2-5: “Existing instruments….. hot spots and quick variations”. This is a rather long sentence. Consider splitting it.
P3, L53: “In the following section,…”. Please change to “In Sect. 2.4,…”
P3, L70: “RF”. Define acronym.
P5, L97: “Fig. 6”. In the text of the manuscript, “Fig. 6” appears before Fig. 3, 4 and 5. It would ease things for the reader if the number of the figures were re-numbered.
P8, Fig. 5: Please add the units of the vertical and horizontal axes
P11, L214: “PTC”. Define acronym.
P14, L262: “In order to dSCD comparable…”. Consider rephrasing it “In order to compare dSCD from…”
P14, L272: “The each different…”. Change to “Each different…”
P17, L327: “comparison made earlier”. In Table 4?
P20, L331: “Sections 3.4, 4.2.2 and 4.2.1”. Better change to “Previous sections”
P20, Table 5: Please, specify for which elevation angle are those values