the Creative Commons Attribution 4.0 License.
the Creative Commons Attribution 4.0 License.
The importance of spatial resolution in the modelling of methane emissions from natural wetlands
Abstract. An important uncertainty in the modelling of methane (CH4) emissions from natural wetlands is the wetland area. It is difficult to model wetlands CH4 emissions because of several factors, including its spatial heterogeneity on a large range of scales. In this study, we investigate the impact of model resolution on the simulated wetland methane emission for the Fenno-Scandinavian Peninsula. This is done using a high-resolution wetland map (100 × 100m2) and soil carbon map (250 × 250m2) in combination with a highly simplified CH4 emission model that is coarsened in six steps from 0.005° to 1°. We find a strong relation between wetland emissions and resolution, which is sensitive, however, to the sub-grid treatment of the wetland fraction. In our setup, soil carbon and soil moisture are positively correlated at high-resolution with wetland location leading to increasing CH4 emissions with increasing resolution. Keeping track of wetland fraction reduces the impact of resolution. However, uncertainties in CH4 emissions remain high because of the large uncertainty in the representation of wetland area, as demonstrated using the output of the WetChimp intercomparison over our study domain. Because of wetlands mapping uncertainties, the existing models are unlikely to realistically represent the correlation between soil moisture and soil carbon availability. The correlation is positive in our simplified model, but maybe different in more complex models depending on their method of representing substrate availability. Therefore, depending on the correlation, CH4 emissions may be over or underestimated. As increasing the model resolution is an effective approach to mitigate the problem of accounting for the correlation between soil moisture and soil carbon and improve the accuracy of models, the main message of this study is that increasing the resolution of global wetland models, and especially the input datasets that are used, should receive high priority.
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RC1: 'Comment on bg-2022-55', Anonymous Referee #1, 17 Apr 2022
Title: The importance of spatial resolution in the modelling of methane emissions from natural wetlands
Author(s): Yousef Albuhaisi, Ype van der Velde and Sander Houweling
MS No.: bg-2022-55
MS type: Research article
https://doi.org/10.5194/bg-2022-55
This paper aims to evaluate the impact of spatial resolution in methane emissions estimate from wetlands. The authors hypothese that methane emissions uncertainties can possibly be reduced by employing high-resolution (HR) wetland maps. In order to challenge this hypothesis series of simulations of the Fennoscandinavian area at resolution ranging from 0.001° to 1° using a simple methane emissions model are employed.
General comments:
The goal of the paper is of interest for the scientific community and the approach seems interesting but because the paper is not easy to understand doubt remain on the approach. For instant, some details are missing in sections 2 and 3 that are explained later in the results or discussion sections and reduce the clarity of these sections. For example, in section 3 maps resolutions are provided but not explanation is given on how maps are rescaled or not to be employed for the simulations at various resolution. Then the results description in section 4 is fine but is structured with too many sub-sections. The content of the result section can stand with no subsections, I believe. While results are consistent with the previous section 1 to 3, the discussion section 5 is disappointing. There is a discussion on the wetland map resolutions and a reanalysis of wetland extend of models employed in the WetChimp model intercomparison paper of Melton et al. (2013) and a very small discuss on methane emissions and on the actual simulation results of the paper. It is also disappointing not to have some discussion on the complexity of methane emissions models for example for models employed in the WetChimp model intercomparison versus the simple model employed here. The main conclusions of the paper is that wetland distribution is the main uncertainty for methane emissions and it has been demonstrated using a simplified model and conceptual framework. However, this uncertainty has already be addressed and demonstrated in a different manner in the paper of the global methane budget by Saunois et al. (2020) by comparing methane emissions estimated by 13 land surface models using the same wetland map.
For all the above reason, I recommend some major revisions of the paper before to be reconsidered for publication. Below are some comments to help the authors revising the manuscript.
Specific comments:
- Abstract: Line 13 the rang of resolution, from 0.005° to 1° resolution, indicates in the abstract is different than the one in table 3 that range from 0.001° to 1° resolution. Could you explain why? You show results at 0.001°, even though it is employed as a reference, it is still compared to the other runs.
- Units: Sometimes the resolutions are given in different units than degree such as in line 147, 191 and 256; please make sure that all the units are the same for each variable. Also, some numbers in the text are formatted using scientific notation, others are not, such as in lines 298-303. It will ease the reading of the paper to have the same format of numbers.
- Although, the author sometimes qualifies the methane model by “highly simplified model” I think the model is a “simple model”.
-Figures and Tables:
- I believe that Figure 1 and 2 can be merged into one single figure and by adding case 1 next to the content of Figure 1, case 2 next to the content of figure 2 and adjusting the figure caption.
- Figure 3 can be removed, it is not useful to understand the paper. Possibly it can be placed in the appendix or supplementary document.
-Figure 4: My understanding is that you also run Sn 1 at 0.001° resolution which is also you “reference resolution” why does it not appear in Figure 4?
-Figure 5: the axis labels are not clear what is the right y axis, methane concentration? methane emissions? and the left y axis which ratio is it? Figure captions should describe more the figures. Also, I would advise to modify Sn.1-Sn.3 to Sn.1 to Sn.3 to avoid any misunderstanding such as the difference between Sn.1 and Sn.3
-Figure 6: please add the resolution for each box diagram in larger characters. Also, axis need labels that describe each axis in addition of the units. In each box diagrams all text should be enlarged except for the boxes with KCH4.
-Figure 7-8-9 and A2: the text is very small as well but map sizes are fine.
- Figure 10: It is the correlation matrix of wetland extent? Please add this detail in the caption
-Table 1: The table caption needs to provide all details for the reader to understand the table. All acronyms need to be defined in the caption.
- The title can possibly be modified to :” Spatial resolution significance in methane emissions modelling of natural wetlands”
-I think a better suited subtitle for section 2.1 could be “conceptual framework”
In this section the author explains the conceptual framework that they employed to evaluate wetland, soil organic carbon and soil moisture maps resolution on methane emissions. They use two cases: (1) an area entirely covered with wetlands and (2) the same area with one half cover with wetland and the other half with uplands. Both cases are well described however the aim of this section is not obvious.
- It is unclear to me the transition between the calculation of methane emissions over the all-domain area (up to line 105) and the calculation of methane emissions only for wetland areas (after line 105). Indeed, for case (2) the authors make the hypothesis that for uplands soil organic carbon and soil moisture are null then resume equation 2 and 3. Because of this hypothesis both equations serve to estimate methane emitted only by wetlands. This suggests that uplands are not emitting methane whereas simulation protocols defined for scenario 2 and 3 suggest otherwise which is confusing.
- In addition, I do not understand how the average of the SC or SM of the wetlands and the uplands over AHR (which for me is (nwl SCwl + nuplands SCuplands)/( nwl + nuplands)) is equivalent to the average of SC or SM of only wetlands over AHR (which is for me nwl SCwl/ nwl)? Because it is SC or SM that is equal to zero and not nuplands (which gives after simplification (nwl SCwl) /( nwl + nuplands)). Then, if I am not mistaking, in equation 3 : EHR = [nwl SCwl /( nwl + nuplands)] x [nwl SMwl /( nwl + nuplands)] x AHR = [nwl /( nwl + nuplands)]2 x SCwl x SMwl x AHR and equation 4: EHR/ELR = [1/( nwl + nuplands)2] x ALR/AHR
If I am mistaking, I need some explanations to understand the equations in the manuscript.
- It is also unclear to me, at this stage of the paper, what the wetland fraction Fwl represent? In equation 4 Fwl is defined as the proportional ratio of methane emissions estimated using LR map over the HR map. Therefore, to me Fwl is a ratio of methane emissions and not a fraction of wetland area. It is only because of the hypothesis that uplands are emitting no methane that the emission ratio is directly proportional to the wetlands fraction but it not clearly explained in the text.
- In section 2.2, the authors define the wetlands methane model and scenarios that are simulated. It is not clear which model/method there are using to simulate these scenarios, equation 2-3 or equation 1?
-Line 132-133: It is explained that it is considered that upland does not emit methane but in the next sentence methane emissions are still simulated for uplands? Then lines 135 – 137 seem to be some results or results discussion rather than method description.
-Line 176: Scenario 5 is not in table 1? Could you define it somewhere?
-Line 178-179: “The underlying assumption is that soil carbon in the ISRIC map is limited by the peat fraction at 250x250m resolution, and that the highest values represent grid boxes that are fully covered by peat.” Finally, how much peatland area is estimated for the total area domain considered?
- Line 200-201: “This gives rise to variations in soil surface temperature that we are unable to account for but are assumed to be second order in importance compared to variations in soil carbon and soil moisture." In the present study, authors may considered soil temperature as secondary however in sensitivity analysis of more complex methane models that represent methane production, oxidation and transport in global land surface models show that soil temperature is the first variable controlling methane emissions before soil carbon content and soil moisture (van Huissteden et al., 2009, https://doi.org/10.5194/bg-6-3035-2009; Riley et al., 2011, https://doi.org/10.5194/bg-8-1925-2011; Salmon et al., 2022, https://doi.org/10.5194/gmd-15-2813-2022)
- At the end of section 3, it is unclear which map resolution is employed for the SC, SM average soil temperature and wetland maps for each scenario?
- In section 4, I believe that subsection’s titles 4.1 to 4.4 can be removed.
- Line 222: “Significant differences are seen across the wide range of scales from the reference resolution to the coarsest resolution of 1ºx1º” why does the reference resolution is not displayed in Figure 4?
- Line 224 “the reference resolution integrated CH4 emissions is ~1.68 Tg CH4 yr-1” please add Table 3 in the text such as “the reference resolution integrated CH4 emissions (Table 3) is ~1.68 Tg CH4 yr-1”
-Line 237 “Figure A.1 compares total CH4 emission for the study area obtained using prescribed values for SC and SM in Table 2.” How do you obtain uplands emissions since in lines 132-134 you explain that equation (5) does not apply?
- Line258 : “This is done in two ways;” what is the second way?
- Line 292 : “Secondly, the representation of wetland area in models is associated with large uncertainties.” Please explain further the large uncertainties?
-From line 294 to 311, I believe that the figure numbers do not correspond to the right figures. Please check the figure numbers in the text.
Technical corrections:
Line 13: replace “that is coarsened in six steps from 0.005° to 1°.” To “at resolution from 0.005° to 1°.
Line 24: replace “improve the accuracy of models, the main message of this study” to “improve the accuracy of models. The main message of this study”
Line 90: “the availability of soil carbon” do you mean soil organic carbon or soil carbon that include organic and inorganic carbon?
Line 91: “that we will use in the remainder of this study” this could be modified to “that we will use in this study”
Equation 2 is right only if SC and SM of each High-resolution grid box are equal and if SC and SM for uplands are nul.
I do not understand what the wetland fraction corresponds to? For me it is the proportional ratio of CH4 emissions at Low resolution over high resolution.
Line 110: Are “the grid boxes that covered by wetland” entirely covered by wetlands?
Line 121:”the number of model parameters is only small” please modify to “the number of model parameters is small”
Line 122: “the basic CH4 controls of soil temperature” please modify to “soil temperature”
Line128-130 “KCH4 is a calibration constant relating the driving variables to a CH4 flux in units of [g CH4 m-2 yr-1]. We want to note here that The input data used in Eq.5 are for year 2015 as will be and are described in section 3.2.” please modifies to “KCH4 is a calibration constant relating the driving variables to a CH4 flux in [g CH4 m-2 yr-1]. The input data used in Eq.5 are for year 2015 and are described in section 3.2.”
Line 145: “For the remained scenario” please modify to “For the last scenario (Sn.4)”
Line 146: “(5arcmin)” please confer to resolution degree.
Line 156:”that are reporting” please modify to “that are reported”
Citation: https://doi.org/10.5194/bg-2022-55-RC1 - AC1: 'Reply on RC1', Yousef Albuhaisi, 11 Jul 2022
- AC2: 'Reply on RC2', Yousef Albuhaisi, 11 Jul 2022
-
RC2: 'Comment on bg-2022-55', Anonymous Referee #2, 24 Jun 2022
This manuscript investigated the importance of spatial resolution in quantifyiing CH4 fluxes from natural wetland. My main issue with this manuscript is that the authors made a lot of simplifications (chose certain values/threhold, and ‘randomly’ took different datatsets, for instance using reanalysis soil temperature data and then modelled soil mositure at 5 cm) without sound reasons. By taking a lot of unrealistic values, the authors want to demostrate the impacts of resolution on the modelled total methane emissions. There are so many steps/simplifcations which could lead to different results: such as data resampling approach (how did the authors get different resolutions of wetland maps?), soil moisture and soil temperature dataset used (why only top soil layer, and why took two very different datasets?) and also why use the same dataset to calibrate model parameter and evaluate the results.
The authors should really work through their approaches, and thoroughly investigate how different steps/assumption might influence their final results. It is really difficult to understand the simplifcation/approach and the article is lacking in depth and impartiality. Thus, I would not recommend it for publication in its current form.
Detailed comments:
L42-43: Another important process which could contribute to the differences between top-down and bottom-up methods are the details in CH4 transport pathways.
L128, the unit for the KCH4 is not correct. The authors should define the meaning of K values, especially if using T0 equals to 273.15.
L134, Is it true to assume all upland soils take up methane?
L157-158, what do you mean by “network density”? Then in the earlier part of the sentence, it says the reason to choose this study area is due to data availability at a few sites, but then it turns out only 2 sites were monitored. It reads contradictory.
L176: why here comes with scenario 5 now? I did not follow here.
L176-182, I am not sure I follow the authors’ argument to make this type of assumption. 1, why do you need to stick to the highest density values from a dataset that is limited by the peat fractions? 2. It is fine to just assume zero emissions from upland soil, but on L180-192, why this assuption is linked to different soil carbon contents?
L192-193, not sure why you only need to use the top 5 cm soil layer, and which approach did you use it for resampling? It is not clear for me why you introduce another hydrological model for getting soil moisture? Have you evaluated the modelled soil moisture? Why not use the soil moisture data from ERA5?
L 208-210: not clear how the authors obtain the K_CH4 value? What values did you get for KCH4?
Figure 3, where are the color legend?
Figure 4, why are there emissions for Sn2 if you only have upland?
Figure 6, not clear for me how you can use the same observation data to calibrate K_CH4 and then evaluate the calculated model, please clarify this.
Citation: https://doi.org/10.5194/bg-2022-55-RC2 - AC2: 'Reply on RC2', Yousef Albuhaisi, 11 Jul 2022
Status: closed
-
RC1: 'Comment on bg-2022-55', Anonymous Referee #1, 17 Apr 2022
Title: The importance of spatial resolution in the modelling of methane emissions from natural wetlands
Author(s): Yousef Albuhaisi, Ype van der Velde and Sander Houweling
MS No.: bg-2022-55
MS type: Research article
https://doi.org/10.5194/bg-2022-55
This paper aims to evaluate the impact of spatial resolution in methane emissions estimate from wetlands. The authors hypothese that methane emissions uncertainties can possibly be reduced by employing high-resolution (HR) wetland maps. In order to challenge this hypothesis series of simulations of the Fennoscandinavian area at resolution ranging from 0.001° to 1° using a simple methane emissions model are employed.
General comments:
The goal of the paper is of interest for the scientific community and the approach seems interesting but because the paper is not easy to understand doubt remain on the approach. For instant, some details are missing in sections 2 and 3 that are explained later in the results or discussion sections and reduce the clarity of these sections. For example, in section 3 maps resolutions are provided but not explanation is given on how maps are rescaled or not to be employed for the simulations at various resolution. Then the results description in section 4 is fine but is structured with too many sub-sections. The content of the result section can stand with no subsections, I believe. While results are consistent with the previous section 1 to 3, the discussion section 5 is disappointing. There is a discussion on the wetland map resolutions and a reanalysis of wetland extend of models employed in the WetChimp model intercomparison paper of Melton et al. (2013) and a very small discuss on methane emissions and on the actual simulation results of the paper. It is also disappointing not to have some discussion on the complexity of methane emissions models for example for models employed in the WetChimp model intercomparison versus the simple model employed here. The main conclusions of the paper is that wetland distribution is the main uncertainty for methane emissions and it has been demonstrated using a simplified model and conceptual framework. However, this uncertainty has already be addressed and demonstrated in a different manner in the paper of the global methane budget by Saunois et al. (2020) by comparing methane emissions estimated by 13 land surface models using the same wetland map.
For all the above reason, I recommend some major revisions of the paper before to be reconsidered for publication. Below are some comments to help the authors revising the manuscript.
Specific comments:
- Abstract: Line 13 the rang of resolution, from 0.005° to 1° resolution, indicates in the abstract is different than the one in table 3 that range from 0.001° to 1° resolution. Could you explain why? You show results at 0.001°, even though it is employed as a reference, it is still compared to the other runs.
- Units: Sometimes the resolutions are given in different units than degree such as in line 147, 191 and 256; please make sure that all the units are the same for each variable. Also, some numbers in the text are formatted using scientific notation, others are not, such as in lines 298-303. It will ease the reading of the paper to have the same format of numbers.
- Although, the author sometimes qualifies the methane model by “highly simplified model” I think the model is a “simple model”.
-Figures and Tables:
- I believe that Figure 1 and 2 can be merged into one single figure and by adding case 1 next to the content of Figure 1, case 2 next to the content of figure 2 and adjusting the figure caption.
- Figure 3 can be removed, it is not useful to understand the paper. Possibly it can be placed in the appendix or supplementary document.
-Figure 4: My understanding is that you also run Sn 1 at 0.001° resolution which is also you “reference resolution” why does it not appear in Figure 4?
-Figure 5: the axis labels are not clear what is the right y axis, methane concentration? methane emissions? and the left y axis which ratio is it? Figure captions should describe more the figures. Also, I would advise to modify Sn.1-Sn.3 to Sn.1 to Sn.3 to avoid any misunderstanding such as the difference between Sn.1 and Sn.3
-Figure 6: please add the resolution for each box diagram in larger characters. Also, axis need labels that describe each axis in addition of the units. In each box diagrams all text should be enlarged except for the boxes with KCH4.
-Figure 7-8-9 and A2: the text is very small as well but map sizes are fine.
- Figure 10: It is the correlation matrix of wetland extent? Please add this detail in the caption
-Table 1: The table caption needs to provide all details for the reader to understand the table. All acronyms need to be defined in the caption.
- The title can possibly be modified to :” Spatial resolution significance in methane emissions modelling of natural wetlands”
-I think a better suited subtitle for section 2.1 could be “conceptual framework”
In this section the author explains the conceptual framework that they employed to evaluate wetland, soil organic carbon and soil moisture maps resolution on methane emissions. They use two cases: (1) an area entirely covered with wetlands and (2) the same area with one half cover with wetland and the other half with uplands. Both cases are well described however the aim of this section is not obvious.
- It is unclear to me the transition between the calculation of methane emissions over the all-domain area (up to line 105) and the calculation of methane emissions only for wetland areas (after line 105). Indeed, for case (2) the authors make the hypothesis that for uplands soil organic carbon and soil moisture are null then resume equation 2 and 3. Because of this hypothesis both equations serve to estimate methane emitted only by wetlands. This suggests that uplands are not emitting methane whereas simulation protocols defined for scenario 2 and 3 suggest otherwise which is confusing.
- In addition, I do not understand how the average of the SC or SM of the wetlands and the uplands over AHR (which for me is (nwl SCwl + nuplands SCuplands)/( nwl + nuplands)) is equivalent to the average of SC or SM of only wetlands over AHR (which is for me nwl SCwl/ nwl)? Because it is SC or SM that is equal to zero and not nuplands (which gives after simplification (nwl SCwl) /( nwl + nuplands)). Then, if I am not mistaking, in equation 3 : EHR = [nwl SCwl /( nwl + nuplands)] x [nwl SMwl /( nwl + nuplands)] x AHR = [nwl /( nwl + nuplands)]2 x SCwl x SMwl x AHR and equation 4: EHR/ELR = [1/( nwl + nuplands)2] x ALR/AHR
If I am mistaking, I need some explanations to understand the equations in the manuscript.
- It is also unclear to me, at this stage of the paper, what the wetland fraction Fwl represent? In equation 4 Fwl is defined as the proportional ratio of methane emissions estimated using LR map over the HR map. Therefore, to me Fwl is a ratio of methane emissions and not a fraction of wetland area. It is only because of the hypothesis that uplands are emitting no methane that the emission ratio is directly proportional to the wetlands fraction but it not clearly explained in the text.
- In section 2.2, the authors define the wetlands methane model and scenarios that are simulated. It is not clear which model/method there are using to simulate these scenarios, equation 2-3 or equation 1?
-Line 132-133: It is explained that it is considered that upland does not emit methane but in the next sentence methane emissions are still simulated for uplands? Then lines 135 – 137 seem to be some results or results discussion rather than method description.
-Line 176: Scenario 5 is not in table 1? Could you define it somewhere?
-Line 178-179: “The underlying assumption is that soil carbon in the ISRIC map is limited by the peat fraction at 250x250m resolution, and that the highest values represent grid boxes that are fully covered by peat.” Finally, how much peatland area is estimated for the total area domain considered?
- Line 200-201: “This gives rise to variations in soil surface temperature that we are unable to account for but are assumed to be second order in importance compared to variations in soil carbon and soil moisture." In the present study, authors may considered soil temperature as secondary however in sensitivity analysis of more complex methane models that represent methane production, oxidation and transport in global land surface models show that soil temperature is the first variable controlling methane emissions before soil carbon content and soil moisture (van Huissteden et al., 2009, https://doi.org/10.5194/bg-6-3035-2009; Riley et al., 2011, https://doi.org/10.5194/bg-8-1925-2011; Salmon et al., 2022, https://doi.org/10.5194/gmd-15-2813-2022)
- At the end of section 3, it is unclear which map resolution is employed for the SC, SM average soil temperature and wetland maps for each scenario?
- In section 4, I believe that subsection’s titles 4.1 to 4.4 can be removed.
- Line 222: “Significant differences are seen across the wide range of scales from the reference resolution to the coarsest resolution of 1ºx1º” why does the reference resolution is not displayed in Figure 4?
- Line 224 “the reference resolution integrated CH4 emissions is ~1.68 Tg CH4 yr-1” please add Table 3 in the text such as “the reference resolution integrated CH4 emissions (Table 3) is ~1.68 Tg CH4 yr-1”
-Line 237 “Figure A.1 compares total CH4 emission for the study area obtained using prescribed values for SC and SM in Table 2.” How do you obtain uplands emissions since in lines 132-134 you explain that equation (5) does not apply?
- Line258 : “This is done in two ways;” what is the second way?
- Line 292 : “Secondly, the representation of wetland area in models is associated with large uncertainties.” Please explain further the large uncertainties?
-From line 294 to 311, I believe that the figure numbers do not correspond to the right figures. Please check the figure numbers in the text.
Technical corrections:
Line 13: replace “that is coarsened in six steps from 0.005° to 1°.” To “at resolution from 0.005° to 1°.
Line 24: replace “improve the accuracy of models, the main message of this study” to “improve the accuracy of models. The main message of this study”
Line 90: “the availability of soil carbon” do you mean soil organic carbon or soil carbon that include organic and inorganic carbon?
Line 91: “that we will use in the remainder of this study” this could be modified to “that we will use in this study”
Equation 2 is right only if SC and SM of each High-resolution grid box are equal and if SC and SM for uplands are nul.
I do not understand what the wetland fraction corresponds to? For me it is the proportional ratio of CH4 emissions at Low resolution over high resolution.
Line 110: Are “the grid boxes that covered by wetland” entirely covered by wetlands?
Line 121:”the number of model parameters is only small” please modify to “the number of model parameters is small”
Line 122: “the basic CH4 controls of soil temperature” please modify to “soil temperature”
Line128-130 “KCH4 is a calibration constant relating the driving variables to a CH4 flux in units of [g CH4 m-2 yr-1]. We want to note here that The input data used in Eq.5 are for year 2015 as will be and are described in section 3.2.” please modifies to “KCH4 is a calibration constant relating the driving variables to a CH4 flux in [g CH4 m-2 yr-1]. The input data used in Eq.5 are for year 2015 and are described in section 3.2.”
Line 145: “For the remained scenario” please modify to “For the last scenario (Sn.4)”
Line 146: “(5arcmin)” please confer to resolution degree.
Line 156:”that are reporting” please modify to “that are reported”
Citation: https://doi.org/10.5194/bg-2022-55-RC1 - AC1: 'Reply on RC1', Yousef Albuhaisi, 11 Jul 2022
- AC2: 'Reply on RC2', Yousef Albuhaisi, 11 Jul 2022
-
RC2: 'Comment on bg-2022-55', Anonymous Referee #2, 24 Jun 2022
This manuscript investigated the importance of spatial resolution in quantifyiing CH4 fluxes from natural wetland. My main issue with this manuscript is that the authors made a lot of simplifications (chose certain values/threhold, and ‘randomly’ took different datatsets, for instance using reanalysis soil temperature data and then modelled soil mositure at 5 cm) without sound reasons. By taking a lot of unrealistic values, the authors want to demostrate the impacts of resolution on the modelled total methane emissions. There are so many steps/simplifcations which could lead to different results: such as data resampling approach (how did the authors get different resolutions of wetland maps?), soil moisture and soil temperature dataset used (why only top soil layer, and why took two very different datasets?) and also why use the same dataset to calibrate model parameter and evaluate the results.
The authors should really work through their approaches, and thoroughly investigate how different steps/assumption might influence their final results. It is really difficult to understand the simplifcation/approach and the article is lacking in depth and impartiality. Thus, I would not recommend it for publication in its current form.
Detailed comments:
L42-43: Another important process which could contribute to the differences between top-down and bottom-up methods are the details in CH4 transport pathways.
L128, the unit for the KCH4 is not correct. The authors should define the meaning of K values, especially if using T0 equals to 273.15.
L134, Is it true to assume all upland soils take up methane?
L157-158, what do you mean by “network density”? Then in the earlier part of the sentence, it says the reason to choose this study area is due to data availability at a few sites, but then it turns out only 2 sites were monitored. It reads contradictory.
L176: why here comes with scenario 5 now? I did not follow here.
L176-182, I am not sure I follow the authors’ argument to make this type of assumption. 1, why do you need to stick to the highest density values from a dataset that is limited by the peat fractions? 2. It is fine to just assume zero emissions from upland soil, but on L180-192, why this assuption is linked to different soil carbon contents?
L192-193, not sure why you only need to use the top 5 cm soil layer, and which approach did you use it for resampling? It is not clear for me why you introduce another hydrological model for getting soil moisture? Have you evaluated the modelled soil moisture? Why not use the soil moisture data from ERA5?
L 208-210: not clear how the authors obtain the K_CH4 value? What values did you get for KCH4?
Figure 3, where are the color legend?
Figure 4, why are there emissions for Sn2 if you only have upland?
Figure 6, not clear for me how you can use the same observation data to calibrate K_CH4 and then evaluate the calculated model, please clarify this.
Citation: https://doi.org/10.5194/bg-2022-55-RC2 - AC2: 'Reply on RC2', Yousef Albuhaisi, 11 Jul 2022
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