the Creative Commons Attribution 4.0 License.
the Creative Commons Attribution 4.0 License.
Resolving seasonal and diel dynamics of non-rainfall water inputs in a Mediterranean ecosystem using lysimeters
Sinikka Jasmin Paulus
Tarek Sebastian El-Madany
René Orth
Anke Hildebrandt
Thomas Wutzler
Arnaud Carrara
Gerardo Moreno
Oscar Perez-Priego
Olaf Kolle
Markus Reichstein
Mirco Migliavacca
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- Final revised paper (published on 13 Dec 2022)
- Preprint (discussion started on 02 Nov 2021)
Interactive discussion
Status: closed
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RC1: 'Comment on hess-2021-519', Anonymous Referee #1, 19 Nov 2021
This paper perfectly interprets the composition of non-rainfall water input using data from lysimeters and meteorological data. However, author pointed out that condensation processes are dew when water originates from the atmosphere or soil distillation when the water originates from the soil beneath. Therefore, difference between soil surface temperature and dewpoint temperature of nearby air is an important factor for dew. So, Dew was therefore assigned when Ts < (Tdew− Tdew;t) where Tdew;t is set to 1:4 â¦C in Flux partitioning (Lines 162-175).Then, how to quantify the part of dew from soil. This part of water is only the process of water migration in soil and not the input of external water.
Citation: https://doi.org/10.5194/hess-2021-519-RC1 -
AC3: 'Reply on RC1', Sinikka Paulus, 04 Mar 2022
We thank referee #1 for acknowledging the interpretation of our data and we are grateful for the comments posted that helped us to clarify some assumptions that the analysis is based on.
The detailed answers to the comments were uploaded in the form of a supplement.
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AC3: 'Reply on RC1', Sinikka Paulus, 04 Mar 2022
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RC2: 'Comment on hess-2021-519', Giora J. Kidron, 15 Dec 2021
The authors presented a thorough and clearly written research paper, which I enjoyed reading. There are some points, however, that should be pointed out, whether in order to clarify some issues or to point to possible directions for future research.
- Unfortunately, the reader is not provided with a full description of the lysimeter. I assume that the lysimeter is covered with vegetation which reflects the vegetation at the site. Data regarding the cover and height of the vegetation at the site, along with photographs would have been helpful.
- Scholars tend to refer to the amount of NRW that they obtained as representative of their site. Consequently, a comparison with other sites is often made, and similar values are taken as a supportive evidence for the reliability of the newly published data. Differences may be explained to stem from "site-specific timing" (l 302), but this may however not necessarily be the case. The authors were indeed aware of the complexity stemming from the sharp temperature gradient above ground, and the Td was corrected to that of 10 cm above ground. One however should note that this height above ground yielded the highest NRW in the Negev (Kidron, 1998, 2010). At higher height a decrease in NRW took place due to higher wind turbulence while at lower height a decrease in NRW stemmed from the heat emitted from the soil. While the 10 cm height taken by the authors is relevant for plants (as correctly indicated by the authors, and was in line with eddy covariance measurements), it is not necessarily relevant for biocrusts.
- Large lysimeters may better reflect the NRW. The extent to which heat loss through the walls of a large lysimeter will affect the NRW in comparison to the large effect recorded for microlysimeters (MLs) has yet to be evaluated. Once MLs are used, as was the case for the Tabernas (Uclés et al., 2013, 2014, 2015, 2016), one may have assumed, based on the published NRW that the Tabernas may be considered as a 'dew desert' and that NRW has an important contribution to the biocrusts there. However, based on data from the Negev (Kidron and Kronenfeld, 2020a, 2020b; Kidron et al., 2021) and analysis of the microclimatological variables in the Tabernas (Kidron and Lázaro, 2020; Kidron and Kronenfeld, 2020c), the published data for the Tabernas should be taken with caution. It is not merely the distance from the Mediterranean (l 294), but rather the method used that may largely explain the differences in the reported NRW between the current site and the Tabernas.
- Certainly, while the method employed by the authors may yield relatively reliable values in comparison to other methods which use lysimeters, verification against manual measurements is necessary. I assume that in this case, vapor condensation on the plant leaves should be measured. For a comparison to other sites (including the Tabernas) where great efforts were made to evaluate the amount of NRW obtained by biocrusts, direct NRW measurements also at the surface would be helpful.
With pleasure,
Giora J Kidron
Kidron, G.J., 1998. A simple weighing method for dew and fog measurements. Weather 53, 428-433.
Kidron, G.J., 2010. The effect of substrate properties, size, position, sheltering and shading on dew: an experimental approach in the Negev Desert. Atmospheric Research 98, 378-386
Kidron, G.J., Lázaro, R., 2020. Are coastal deserts necessarily dew deserts? An example from the Tabernas Desert. Journal of Hydrology and Hydromechanics 68, 19-27.
Kidron, G.J., Kronenfeld, R., 2020a. Assessing the likelihood of the soil surface to condense vapor: The Negev experience. Ecohydrology 13;e2200.
Kidron, G.J., Kronenfeld, R., 2020b. Microlysimeters overestimate the amount of non-rainfall water – an experimental approach. Catena 194, 104691.
Kidron, G.J., Kronenfeld, R., 2020c. Atmospheric humidity is unlikely to serve as an important water source for crustose soil lichens in the Tabernas Desert. Journal of Hydrology and Hydromechanics 68, 359-367.
Kidron, G.J., Kronenfeld, R., Xiao, B., 2021. Why dew and fog measurements carried out by microlysimeters do not adequately reflect the intact soil? The role of temperature. Agricultural and Forest Meteorology 310, 108648.
Uclés, O., Villagarcía, L., Cantón, Y., Domingo, F., 2013. Microlysimeter station for long term non-rainfall water input and evaporation studies. Agricultural and Forest Meteorology 182-183, 13-20.
Uclés, O., Villagarcía, L., Moro, M.J., Cantón, Y., Domingo, F., 2014. Role of dewfall in the water balance of a semiarid coastal steppe ecosystem. Hydrological Processes 28, 2271-2280.
Uclés, O., Villagarcía, L., Cantón, Y., Lázaro, R., Domingo, F., 2015. Non-rainfall water inputs are controlled by aspect in a semiarid ecosystem. Journal of Arid Environments 113, 43-50.
Uclés, O., Villagarcía, L., Cantón, Y., Domingo, F., 2016. Partitioning of non rainfall water input regulated by soil cover type. Catena 139, 265-270.
Citation: https://doi.org/10.5194/hess-2021-519-RC2 -
AC1: 'Reply on RC2', Sinikka Paulus, 04 Mar 2022
The authors presented a thorough and clearly written research paper, which I enjoyed reading. There are some points, however, that should be pointed out, whether in order to clarify some issues or to point to possible directions for future research.
Response: Thank you very much for the comments and suggestions and for helping us to improve the manuscript. We considered them very helpful and changed the manuscript accordingly. Below, we provide answers to your comments (in italic). Additional Figures with captions are included in the .pdf supplement to this comment.
1. Unfortunately, the reader is not provided with a full description of the lysimeter. I assume that the lysimeter is covered with vegetation which reflects the vegetation at the site. Data regarding the cover and height of the vegetation at the site, along with photographs would have been helpful.
Response: Thank you very much for this comment, it is now clear to us that we should refer more clearly to the work of Perez-Priego et al. 2017, where a more detailed description of the setup is published. We added the following sentence to section 2.2 accordingly: “A full description of the technical details of the lysimeters is given in Perez-Priego et al. 2017.”
We further followed your recommendation and added information on the vegetation in section 2.2 and added photographs of the setup and lysimeter cover in the Appendix (Figure A1):
“The lysimeters were installed in 2015 by excavating undisturbed soil monoliths from open grassland areas. The natural herbaceous vegetation cover was preserved. Pictures of the lysimeter columns and an aerial photograph of the site are shown in Fig. A1.”
2. Scholars tend to refer to the amount of NRW that they obtained as representative of their site. Consequently, a comparison with other sites is often made, and similar values are taken as a supportive evidence for the reliability of the newly published data. Differences may be explained to stem from "site-specific timing" (l 302), but this may however not necessarily be the case. The authors were indeed aware of the complexity stemming from the sharp temperature gradient above ground, and the Td was corrected to that of 10 cm above ground. One however should note that this height above ground yielded the highest NRW in the Negev (Kidron, 1998, 2010). At higher height a decrease in NRW took place due to higher wind turbulence while at lower height a decrease in NRW stemmed from the heat emitted from the soil. While the 10 cm height taken by the authors is relevant for plants (as correctly indicated by the authors, and was in line with eddy covariance measurements), it is not necessarily relevant for biocrusts.
Response: If we understand correctly, the comment refers to the effect of the height of the vegetation on the amount of NRW (or dew in particular) and the effect of the sensor height to estimate if conditions are suitable for dew formation.
Concerning the amount of NRW it should not differ since in this setup the quantification is independent of height in contrast to the cloth plate or Plexiglas methods used in Kidron et al. (1998, 2010).Concerning the reference height, we received a similar comment from referee # 3, Werner Eugster, on the approximated height. He suggested we should use an approximation for 1 cm height above the surface because this height was used in the work from Monteith 1957. As the reviewer points out here, the 10 cm height is relevant for vegetation at our site which has a mean canopy height of 0.1 m (Migliavacca et al. 2017). Biocrusts in contrast are rather rare which might be a consequence of regular grazing (Concostrina‐Zubiri et al. 2017). Since we nevertheless understood that the manuscript is lacking more explicit reasoning for the readers we added some sentences on the effect of surface height on dew amounts and the relevance to take into account measurement height and the height of the condensation surfaces (vegetation or biocrust).
“Since the installation height of the sensor is 1 m we needed to approximate a value that better reflects Tdew at the height of the condensation surfaces. Despite a reference height of 1 cm is generally used (Monteith, 1957), we approximated 10 cm which reflects the average canopy height of the herbaceous layer.”
3. Large lysimeters may better reflect the NRW. The extent to which heat loss through the walls of a large lysimeter will affect the NRW in comparison to the large effect recorded for microlysimeters (MLs) has yet to be evaluated.
Response: Yes, we agree. We are also not aware of a study that analyzes this effect. We added a sentence in the discussion to point out that in face of the identified overestimation of Micro-Lysimeters a similar analysis for large weighing lysimeters would be recommended before excluding the possibility of the same underlying effect (despite the lower boundary heat exchange system).
“Despite the lysimeters being built in a way that heat losses are prevented, the extent to which heat loss through walls of a large lysimeter will affect NRW despite the lower boundary control has yet to be evaluated.“4. Once MLs are used, as was the case for the Tabernas (Uclés et al., 2013, 2014, 2015, 2016), one may have assumed, based on the published NRW that the Tabernas may be considered as a 'dew desert' and that NRW has an important contribution to the biocrusts there. However, based on data from the Negev (Kidron and Kronenfeld, 2020a, 2020b; Kidron et al., 2021) and analysis of the microclimatological variables in the Tabernas (Kidron and Lázaro, 2020; Kidron and Kronenfeld, 2020c), the published data for the Tabernas should be taken with caution. It is not merely the distance from the Mediterranean (l 294), but rather the method used that may largely explain the differences in the reported NRW between the current site and the Tabernas.
Response: Thank you for this informative assessment. We changed the sentence in the following way:
“In a similar semi-arid steppe ecosystem in Spain, the mean number of days per year with suitable conditions for dew formation was 285 days (Uclés, 2014), however, this finding is based on measurements with micro-lysimeters and might therefore overestimate the real dew formation frequency (Kidron and Kronenfeld, 2020a, b).”5. Certainly, while the method employed by the authors may yield relatively reliable values in comparison to other methods which use lysimeters, verification against manual measurements is necessary. I assume that in this case, vapor condensation on the plant leaves should be measured. For a comparison to other sites (including the Tabernas) where great efforts were made to evaluate the amount of NRW obtained by biocrusts, direct NRW measurements also at the surface would be helpful.
Response: We fully agree with the reviewer that this would be most desirable and would also help identify whether the large weighing lysimeters potentially overestimate NRWI similar to Micro-lysimeters, as pointed out in comment 3. However, since the start of this analysis, the traveling regulations were forcing us to cancel several field campaigns in which such data could have been collected. Therefore, the manual sampling was unfortunately not possible to perform and included in this analysis. To point out this shortcoming of our study and that the NRW amounts should be handled carefully we extended the Discussion and the Outlook by the following sentences:
Discussion: “However, NRW sums often deviated between different measurement instruments and manual sampling (Kidron and Starinsky, 2019; Kidron et al., 2000). Unfortunately, quantitative validation of NRW sums was not possible in our current study.”
Outlook: “Until a quantitative validation has been carried out for NRW from large weighing lysimeters, the measured sums should be interpreted with caution. Ideally, such validation would take the form of several campaigns with a manual sampling of soil and plants throughout the year to cover the seasonally varying NRW fluxes.”
References:
Concostrina‐Zubiri, L., Molla, I., Velizarova, E., & Branquinho, C. (2017). Grazing or not grazing: implications for ecosystem services provided by biocrusts in Mediterranean cork oak woodlands. Land Degradation & Development, 28(4), 1345-1353.
Kidron, G. J., Yair, A., & Danin, A. (2000). Dew variability within a small arid drainage basin in the Negev Highlands, Israel. Quarterly Journal of the Royal Meteorological Society, 126(562), 63-80.
Kidron, G. J., & Starinsky, A. (2019). Measurements and ecological implications of non‐rainfall water in desert ecosystems—A review. Ecohydrology, 12(6), e2121.
Kidron, G. J., & Lázaro, R. (2020). Are coastal deserts necessarily dew deserts? An example from the Tabernas Desert. Journal of Hydrology and Hydromechanics, 68(1), 19-27.
Kidron, G. J., & Kronenfeld, R. (2020a). Atmospheric humidity is unlikely to serve as an important water source for crustose soil lichens in the Tabernas Desert. Journal of Hydrology and Hydromechanics, 68(4), 359-367.
Kidron, G. J., & Kronenfeld, R. (2020b). Microlysimeters overestimate the amount of non-rainfall water–an experimental approach. Catena, 194, 104691.
Monteith, J. L. (1957). Dew. Quarterly Journal of the Royal Meteorological Society, 83(357), 322-341.
Perez-Priego, O., El-Madany, T. S., Migliavacca, M., Kowalski, A. S., Jung, M., Carrara, A., ... & Reichstein, M. (2017). Evaluation of eddy covariance latent heat fluxes with independent lysimeter and sapflow estimates in a Mediterranean savannah ecosystem. Agricultural and Forest Meteorology, 236, 87-99.
Uclés, O., Villagarcía, L., Moro, M. J., Canton, Y., & Domingo, F. (2014). Role of dewfall in the water balance of a semiarid coastal steppe ecosystem. Hydrological Processes, 28(4), 2271-2280.
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RC3: 'Interesting and relevant manuscript, but requires some moderate revisions before acceptance', Werner Eugster, 28 Dec 2021
Non-rainfall water inputs (NRWI) can be an important hydrological water source to plants in arid and semi-arid ecosystems, but also elsewhere during dry spells and drought periods. The authors argue that so far most measurements were done with microlysimeters that may overestimate NRWI if their construction is of a simple type that does not attempt to bring microlysimeter soil temperatures in good agreement with the surrounding soil. Contrastingly, a normal size lysimeter---of which the authors have 6 on site, where one was excluded from the analysis---have the advantage that a temperature control of the soil slab is possible and hence less of the problems reported for microlysimeters should result from using standard lysimeters with highly resolving weight measurement.
The authors present a full year of data from a Mediterranean site in Spain, but the focus of the manuscript is more on the method, the real measurements are more used in a proof-of-concept mode without independent and reliable (and established) validation data as obtained from blotting paper water collection and analysis. Thus, the manuscript could actually be classified as a "technical note". My suggestion is to suggest moderate revisions before accepting the paper. There are a few scientific errors that can be easily rectified in a thorough revision round (wrong physical units, mostly) and with some information the context and wording can be quite misleading and should be corrected. Moreover, the main shortcoming of the manuscript is the (1) the absence of a (at least simple) visibility sensor to be able to scientifically correctly separate fog from dew conditions, and (2) lack of robust and independent validation data for supporting the claim that the presented method---which seems to be a further development of Zhang et al.'s (2019) method---is more accurate than other approaches. Nevertheless I recommend proceeding with the manuscript, there is indeed a need for better and more accurate quantification of NRWI in all ecosystems where rainfall can be absent for prolonged periods.
MAJOR POINTS
Title: the paper is clearly focused on NRWI, and evaporation in my view is rather treated a side aspect (and not very clearly associated with NRWI except for the short discussion about downward latent heat flux being in good agreement with water vapor absorption estimates from the lysimeter). In my view a title of the kind of ``Lysimeter based quantification of non-rainfall water inputs to a Mediterranean ecosystem'' (maybe clearly classified as a technical note) would represent the contents much better.
62: ``Recently Kidron and Kronenfeld (2020b) found that temperature inside the micro-lysimeters deviated from that in the surrounding soil, \ldots''---here some rewriting is required. Firstly, the original paper makes unacceptable generalisations that require some caution when using that reference; secondly, the statement as presented here does not correctly reflect the contents. Kidron and Kronenfeld (2020b) used microlysimeters (ML) with a huge gap between ML and original soil, a cold-air trap that leads to excessive cooling of the pit at night and consequently to lower than normal soil temperatures. And that's the key effect, \textbf{not} that the soil temperature is different from the surrounding soil: if the soil inside the ML is colder than it should be, then you expect additional condensation to occur in the ML, thereby artificially suggesting and NRWI that is in fact an artifact. As you can see in Riedl et al. in Fig. 5 the soil inside our MLs is actually somewhat warmer or equal in temperature compared to the control. In this way the artifact of the ML critisised by Kidron and Kronenfeld (2020b) is avoided. Thus, the problem with Kidron and Kronenfeld (2020b) is that they generalize from their overly simplistic ML to all ML (which is not correct, a simple lid actually solves the problem, or at least reduces this artifact). A normal-size lysimeter with such a large gap around the lysimeter would also act as a cold air pit, the only advantage you have with a large lysimeter is that you could more easily add heating wires to heat the soil to more closely match the control temperature. Thus, I agree with your argumentation in lines 64--66.
169: The 10\,cm $T_a$ is not a real reference, see Monteith (1957). Why not extrapolate to the 1\,cm height? At least you must reference and consider Monteith (1957), this is an omission which is not understandable. In my view all papers with Monteith as author or co-author are of a quality that makes them relevant even after decades, and omitting Monteith knowledge normally goes in the wrong direction (scientifically), away from what we call ``progress''.
313--315: see my remarks further up (line 62). This statement needs a rewording to take care of the flaw of Kidron \& Kronfeld's questionable generalisation to all ML, and the fact that this overestimation could be overcome easily by using a smarter ML design with a lid to avoid the nocturnal cold-air pit.
Appendix A1: this is never referenced in the text and is a mess---either remove or rectify all the errors. If the latter is desired: $C_p$ has wrong units; $s$ see my comments; $LW$ and $SW$ have wrong units; $\Delta W$ has wrong units; use $\Delta q$ instead of $\delta q$; $\varepsilon$ has wrong units (should be dimensionless or simply (---)); $e_a$ has wrong units; $u_*$ should have the asterisk in subscript
Appendix A2: Eq. (A1) would be simpler to read as \begin{displaymath}T_s = \sqrt[4]{\frac{1}{\sigma \cdot \varepsilon} \cdot \left[ LW_\uparrow - (1-\varepsilon) LW_\downarrow \right]} \end{displaymath}
Appendix A2: the mathematical convention is to use either $\cdot$ (\verb+\cdot+) or space for multiplications of scalars, and only use $\times$ for vector products; please update equations accordingly. Use ``upwelling'' and ``downwelling'' for radiation fluxes; there is always the potential confusion that a down-looking sensor actually measures upwelling radiation, etc. Replace the erroneous NA with (---) or (dimensionless)
Figure 6 and the text is actually a result of the study, not a discussion point. Maybe this is the reason why I think the title and text do not agree---if evaporation as mentioned in the title were the focus of the paper this aspect would have come first in the Results section, not last as an add-on in the Discussion section.
OTHER IMPORTANT POINTS
12: ``eddy covariance-derived latent heat flux estimates'': since the paper focuses on NRWI I found this statement somewhat misleading because it only addresses the ET losses but not the gains that would be associated with NRWI. Moreover, the authors do not even define ET, which indicates that this was not the real focus of the manuscript.
23: horizontal precipitation does not belong to NRWI. It is rainfall (precipitation) which is not measured by standard rain gauges (but e.g. by special rain gauges on vessels).
26: it is not Feigenwinter et al. who defined the classification of fog. Rather use a primary source here, AMS, WMO, or (what I use) the AMS Glossary of Meteorology by Glickman (2000):
@Book{Glickman2000,
editor = {Todd S. Glickman},
publisher = {American Meteorological Society},
title = {Glossary of Meteorology},
year = {2000},
address = {Boston, MA},
edition = {2},
comment = {formerly: http://amsglossary.allenpress.com/glossary/},
url = {https://glossary.ametsoc.org/wiki/Welcome},
}30: ``However, differentiating between these two origins is commonly not possible (Li et al., 2021b)''---this is wrong, please read the text: Li just shows the opposite that because the sources of the vapor used in dew formation and the vapor from soil water are of such different origins, using stable isotopes allows to differentiate. You may argue about the word "common", but stable isotopes are common by now (at least the simple-to-measure ones such as $^{18}$O and $^2$H in water and water vapor). MPI Jena is doing this since its establishment. Please reword to convey the correct content and context with this statement.
88: ``However, the structure of the cage allowed for grazing to maintain the lysimeters comparable with the rest of the plot.''---this is a challenge and it would be interesting to read some more details how this is successfully done. As is, it is not possible to reproduce this as a reader.
128--129: Note to Editor: I cannot check the data and code which will be made available once the manuscript is the same. I normally also only publish code and data once a manuscript is accepted, but here the authors do not provide the details in the paper and expect readers to go into the code.
134: question: an animal stepping onto the column, is this not bringing $\Delta W$ outside of the accepted range and is thus treated there?
148: ``water input''---reword, NRWI is also a water input and this is \textbf{not} to be included here!
166: That's why Monteith (1957) uses 1\,cm $T_a$ would be good if you could relate your text more to Monteith's outstanding work which is still our reference.
251: you show ET with negative sign convention, although you use a positive sign convention for $\lamda E$ in Eq. (2.1). Moreover, you never defined ET nor its sign convention. My recommendation is to use positive values as ET losses from the soil to the atmosphere. I have not seen papers using the reverse sign convention, yours is the first, and this confuses me and maybe also the reader. Recall that the standard hydrological budget equation is still: precipitation = runoff + ET +/- change in soil storage. Moreover, you use a positive ET in Fig. 3b. At least you need to be consistent and declare your symbols and sign conventions (if they should deviate from commonsense notation)
280: ``evaluation statistics improve by one hour''---I am unable to see this one-hour improvement in Table A2. Is there an error here, either in Table A2 or in the wording?
306: the absolute value of adsorption may be low (as total NRWI may be low), but the relative share in NRWI is quite high in my view. Maybe rather compare the relative numbers to focus on the processes leading to the different components of NRWI
377: ``At our site, this pattern is obvious and indicates that night-time EC measurements could serve to detect adsorption (Fig. 6).''---I partially disagree, but you may convince me with your arguments. In my view adsorption is not directional as dew formation (from vapor above the canopy) or distillation (from vapor below the canopy), and hence should in my view not leave the best trace in EC-based flux measurements. I though (so far) that dew formation should lead to negative $\lamda E$, whereas distillation is not seen by an EC system; and adsorption should only be seen in EC fluxes if its vapor source is above the canopy, but not below. Your Figure 6 of course empirically shows better performance (qualitatively) for vapor adsorption than dew formation, but for me the explanation is not that obvious as your text implies.
397: ``LE fluxes at dry conditions''---you never defined or used LE, but this appears to be an important statement that should have appeared in Discussion already. Conclusions should not bring up new aspects that were neither addressed in Results nor in Discussion.
Figure 1: in the text it sounds as if you want to use this as a general workflow also for other sites. But then my recommendation is to avoid site-specific magic numbers in the scheme and provide the site-specific values in the caption to be clear. E.g.: $T_s < (T_\textrm{dew} - T_\textrm{dew, t})$ with the information that $T_\textrm{dew, t}$ = 1.4\,$^\circ$C for your lysimeters and site.
Figure 1: just of curiosity because we were challenged on this aspect with our ML: why do you not use the high-quality measurements of the drainage outflow of your lysimeter to make sure that drainage loss at the bottom of the soil slab is not erroneously treated as ET? You classify $\Delta W \le 0$ as ET, although it could be drainage loss after intensive rain. This may be an important aspect if you think the method should also be applicable elsewhere.
Figure 1: the percentile approach to separate fog from dew is in my view weak and questionable. Namely dew can only form under conditions that you classify as ``fog'' but fog droplets---if advected---can be present at relative humidities that are not showing saturated air (high $\mathrm{rH}).
Figure 4: move the text in the dial at upper right so that there are no overlaps
Figure 4: reduce the size of the end marks of the whiskers
Figure A1: there is an error on the x-axis, this is $\mathrm{rH}$ as a fraction, not in \%. Moreover Oswin (1946) and Lewicki (200?) are missing in references. And please don't chomp off the right part of the display. I also cannot see the 95$^\textrm{th}$ percentile in my printout, and the 85$^\textrm{th}$ would profit from a thicker line width. Why do you use x and y in the equation when your variables are actually $\mathrm{rH}$ and $\mathrm{SWC}$? You never defined that x = $\mathrm{rH}$ and y = $\mathrm{SWC}$.
Table A2: The caption claims that the units of all values are hours day$^{-1}$, but the table heading claims that this is only hours; and then there might be an error: if cor means correlation, a unitless and dimensionless information, both are not correct. To be standalone you must define cor, mae and rmse (you don't use mse defined on the previous page). Moreover I cannot see what you want me to see according to the text (see comment elsewhere)
DETAILS
32: Meissner et al. is not a complete reference, year etc. are missing
42: what do you mean with ``modeling frequency''---not intelligible to me
51: please add Riedl et al., accepted on 16 November 2021 at HESS. Last manuscript version available here (note that one more co-author appears in the finally accepted version): http://homepage.usys.ethz.ch/eugsterw/publications/pdf/Riedl.2021.FINAL.pdf, discussion paper version available via https://doi.org/10.5194/hess-2021-317
77 and elsewhere: data are plural in formal English, please correct
81: \textit{ilex} should be lower case; and remove the excessive white space before 20 trees
95--96: ``They rest \ldots'': this sentence is not intelligible to me, please rephrase in an understandable way
112: add ``and'' (Pt-100 and capacitive \ldots)
115: add ``The'' in The Netherlands
120 and elsewhere: $u_*$ always has the asterisk in subscript, never in superscript
120: add reduced space between $m$ and $s$
121: add comma in R3-50, Gill \ldots
127 and elsewhere: note that Figure should be upper case if a specific figure of your manuscript is referenced; it is however lower case if you use figure for ``Zahl'' or ``Wert'' in German
131: delete ``together''
139: not a number is \textbf{NaN}, whereas \textbf{NA} means not available (it is the code for missing values). That's wrong here. I assume you mean not available \textbf{NA}.
184: add s to describe\textbf{s}
190: remove s from model precitions (not model\textbf{s} \ldots)
207: $\delta$ is conventionally only used for isotopic ratios, $\partial$ is used for partial differentials, and $\Delta$ is used for finite differences. Here I think using $\Delta q$ instead of $\delta q$ would reduce confusion if readers are familiar with isotopes, and personally I even think that using capital delta is the correct notation anyway.
209: the Clausius-Clapeyron relationship is not a straight line and thus ``slope'' is the wrong word here. $s$ is actually $de/dT$; thus rewording is required
209: there is an error here, $\lamda E$ is not the latent heat (of whatever), but the latent heat \textbf{flux}. Please correct.
221: you defined $\gamma$ to be in units of Pa K$^{-1}$, but here the implicit assumption is that is is in kPa K$^{-1}$. Stick to your definitions; if readers use the equation as is with saturation pressures in kPa, then the first term is 1000 times too large.
223: $C_p$ is not specific heat of air. It is the specific heat \textbf{capacity} of the air at constant pressure. Please correct.
227: replace moments with periods
229: in the text you correctly use ``diel'', probably being aware that diurnal can also express the opposite of nocturnal. My suggestion is to modify the subsection title to match the text (diel)
247: should be ``its'' without apostrophe
254: a sum has no $\pm$ unless you specify in M\&M how you obtained the uncertainty (the reason: random errors of the mean have an average of zero, and thus for a sum there are no degrees of freedom to specify a random uncertainty). Please correct.
258: you arbitrarily change from ET to $ET$ -- please homogenise (and define the version you keep)
263: your total of the components is 41.9 mm, but you specify 42.0 mm. The convention is to either specify the component that contains the missing 0.1 mm or to round accordingly if no additional component is part of the game. Note that modern round rules round 0.05 to 0.00 but 0.15 to 0.20 (this is essential to avoid drift). Another conventional rule is to round up the component that was closest to rounding down, to correctly represent the reported total.
264: I am surprised to see 50.6\% vapor adsorption. This seems to be quite a large value, but maybe is correct in this ecosystem. Here some independent (e.g. blotting paper) validation of the components would really have strengthened the paper.
294: ``Our observation that especially nights 295 are prone to the formation of NRWI is also documented in the literature. '' This is an utterly trivial statement, do you really want to keep this in a scientific manuscript? For me it is on the same level as ``the grass was green and photosynthesis was important during daylight hours, as reported in the literature'' \ldots
336: should be ``its'' without apostrophe
379: use ``scale up'' instead of ``up scaling''
Figure 3: suggestion to move the legend to the panels and only show the curves that relate to the respective panel. In the legend some colors are hard to distinguish as is. Moreover, having a legend outside the plot area is Excel standard, not with scientific presentations.
Figure 3: use \verb+par(lend=1)+ to avoid the rounded (and thus unclear) endings of the bars
Figure 5: panel (e) is not described. I assume that the second mentioning of (d) should actually be (e)
General: \LaTeX typesets equation by assuming that characters are variables (if they are known), hence $\mathrm{rH}$ and $\mathrm{SWC}$ look odd in your text. Consider using \verb+\mathrm{rH}+ and \verb+\mathrm{SWC}+ instead
References: add doi or URL to Thom et al. (with scanned papers the doi is normally only shown on the publisher's website)
References: add doi to Sonntag et al.
References: add space before parenthesis in Zhang et al. (2019a)
References: check Dirks et al.
References: check Kosmas et al., seems to be an incomplete / corrupted entry
References: check Nair et al.
References: check Peters et al. (2014)
References: check Rodrigues-Iturbe et al.
References: generally only the doi is necessary, not doi resolved by the standard doi resolver plus the doi with the publisher's doi resolver and/or an alternative URL. See https://www.hydrology-and-earth-system-sciences.net/submission.html#references
References: generally rectify the entries according to the guidelines. Paper titles are normally in sentence case whereas journal names and book titles are using capitalised words
References: is there no doi/URL for IUSS \ldots
References: Meissner et al. is incomplete
References: Monteith is incomplete
References: Orchiston is incomplete
The editor is informed about my (friendly) long-term relationship with some of the co-authors.
PS: sorry for the LaTeX markups, I was not aware that HESS removed that option this year …
Citation: https://doi.org/10.5194/hess-2021-519-RC3 -
AC2: 'Reply on RC3', Sinikka Paulus, 04 Mar 2022
We would like to thank the Referee for the valuable comments and suggestions. We provide additional analysis to address the comments, and make necessary changes in the revised manuscript, as described in the supplement file with the detailed author's response to all comments.
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AC2: 'Reply on RC3', Sinikka Paulus, 04 Mar 2022