Articles | Volume 18, issue 22
https://doi.org/10.5194/amt-18-6545-2025
© Author(s) 2025. This work is distributed under the Creative Commons Attribution 4.0 License.
Special issue:
The TropoPause Composition TOwed Sensor Shuttle (TPC-TOSS): a new airborne dual platform approach for atmospheric composition measurements at the tropopause
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- Final revised paper (published on 17 Nov 2025)
- Preprint (discussion started on 08 Jul 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-2025-3175', Charles Brock, 10 Jul 2025
- AC1: 'Reply on RC1', Heiko Bozem, 26 Sep 2025
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RC2: 'Comment on egusphere-2025-3175', Anonymous Referee #2, 27 Jul 2025
- AC2: 'Reply on RC2', Heiko Bozem, 26 Sep 2025
Peer review completion
AR – Author's response | RR – Referee report | ED – Editor decision | EF – Editorial file upload
AR by Heiko Bozem on behalf of the Authors (26 Sep 2025)
Author's response
Author's tracked changes
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ED: Publish subject to technical corrections (29 Sep 2025) by André Ehrlich
AR by Heiko Bozem on behalf of the Authors (14 Oct 2025)
Author's response
Manuscript
This is a nice manuscript describing the use of a novel sensor package that is towed behind an aircraft on a cable. Case studies that demonstrate the use of this technique in the tropopause region where there can be very significant but transient structures that produce strong vertical gradients are presented. The manuscript is well written and generally clear, and the subject matter is appropriate for publication in AMT. Minor revisions are needed to address a few questions, correct technical issues, and provide additional information.
1) Table 2: Please provide a column for instrument uncertainties at the stated sampling frequency. I believe the SkyPOC particle size range is misstated; Bundke et al report a lower detection limit of 0.25 µm.
2) Section 3. At some point here I would like a brief discussion of how the cable system works and how far the TPC-TOSS module can be lowered. What is the total cable length and the typical vertical separation? This is evident only in graphs. What is the range of deltaZ (or cable length) that could be used safely? Alternatively this could go in Section 5.1.
3) Line 214. Change to, "the addition of insulation to protect the instrument by maintaining temperatures above 0 degrees C." Is this an arbitrary temperature limit or would the ozone instrument still function at colder temperatures? I ask because tropical missions near the tropopause might see much colder temperatures than this (if ~13-14 km altitude could be reached).
4) Figure 6b. What is the standard deviation of the Gaussian fit? This would inform as to total instrument variance.
5) Line 343. Surprising use of imperial length units. I thought this was strictly a problem in the U.S.!
6) Line 354 "peeks" -> "peaks" and line 302 "week" -> "weak".
7) Line 382 "Atomizer" -> "atomizer"
8) Line 395. Reference to Fig. 17 before Fig. 12. Generally figures need to be cited in order. You could place the bin diameters as vertical lines in Fig. 11b instead, if you prefer. This might help see how they span the range of compositions. Except, see the next comment below.
9) Fig. 11. There is a substantial (~20%) shift in diameter from the manufacturer's calibration, consistently for both instruments. It's not clear if this correction has been applied when the new wider bins were created. I'm not sure of the reason for creating the wider bins, other than some way to represent the range of possible sizes. It may be better to calculate a low-refractive index calibration and a high-refractive index calibration (by calibration, I mean relationship between channel number and calibration diameter for each calibrant), then a medium-refractive index calibration as the default value. Uncertainty bars would then span across the low- and high- refractive index cases and you could still use the full 99-channel resolution of the UHSAS. I'm not sure what the wider bins gains you since using that method a central bin diameter is assumed and only one size distribution, with no uncertainty range, comes out. Uncertainty ranges might be more useful than grouped wider bins.
10) Fig. 13. There are some surprising size-dependent counting efficiency differences between units here, which pass without much comment. ~30% is a big counting difference (i.e., 350 nm). What is going on? Any ideas?
11) With PSL, when you are comparing numbers do you just integrate the PSL peak, or are you counting additional surfactant/contamination particles in the smallest bins (assuming no DMA is used for the PSL calibrations to remove the smaller contaminant particles)?
12) Line 417. The yaw angle (alignment with respect to the local wind vector) of -147 degrees must be an error. I might believe -1.47 degrees.
13) Fig. 16. What is the shading on this plot?
14) Line 483. Two periods after "cabin".
15) Figure 17. I don't find log-log size distributions very useful. Of more interest (at least to me) would be how well the integrated number, surface, volume, and effective radius agree. These are the parameters governing CCN activity, heterogeneous chemistry, extinction and mass transport, and remote sensing retrieval, respectively.
16) If data need to be plotted on a log axis, it implies that the parameter is not normally (Gaussianly) distributed. Thus standard deviation, which assumes Gaussian statistics, is not valid and is meaningless in describing the statistics. A geometric standard deviation might be better here. (But I would prefer linear plots of N, S, and V vs log diameter instead.)
17) The lateral and fore-aft spacing of the TPC-TOSS is mentioned in Section 6, but of more importance is the vertical spacing, which is not mentioned.
18) Please make sure that all figures are plotted using colors and/or symbols that would allow a person with a color vision impairment to distinguish the different parameters. There are two such scientists in my close acquaintance and it can be a struggle for them.