the Creative Commons Attribution 4.0 License.
the Creative Commons Attribution 4.0 License.
Quantifying the soil sink of atmospheric Hydrogen: a full year of field measurements from grassland and forest soils in the UK
Abstract. Emissions of hydrogen (H2) gas from human activities are associated with indirect climate warming effects. As the hydrogen economy expands globally (e.g. the use of H2 gas as an energy source), the anthropogenic release of H2 into the atmosphere is expected to rise rapidly as a result of increased leakage. The dominant H2 removal process is uptake into soils; however, removal mechanisms are poorly understood and the fate and impact of increased H2 emissions remains highly uncertain. Fluxes of H2 with soils are rarely measured, and data to inform global models is based on few studies. This study presents soil H2 fluxes from two field sites in central Scotland, a managed grassland and a planted deciduous woodland, with flux measurements of H2 covering full seasonal cycles. A bespoke flux chamber measurement protocol was developed to deal with the fast decline in headspace concentrations associated with rapid H2 fluxes, in which non-linear regression models could be fitted to concentration data over a 7-minute enclosure time. We estimate annual H2 uptake of -3.1 ± 0.1 and -12.0 ± 0.4 kg H2 ha-1 yr-1 and mean deposition velocities of 0.012 ± 0.002 and 0.088 ± 0.005 cm s-1 for the grassland and woodland sites, respectively. Soil moisture was found to be the primary driver of H2 uptake at the grassland site, where the high clay content of the soil resulted in anaerobic conditions (near zero H2 flux) during wet periods of the year. Uptake of H2 at the forest site was highly variable and did not correlate well with any localised soil properties (soil moisture, temperature, total carbon and nitrogen content). It is likely that the high clay content of the grassland site (55 % clay) decreased aeration when soils were wet, resulting in poor aeration and low H2 uptake. The well-drained forest site (25 % clay) was not as restricted by exchange of H2 between the atmosphere and the soil, showing instead a large variability in H2 flux that is more likely to be related to heterogeneous factors in the soil that control microbial activity (e.g. labile carbon and microbial densities). The results of this study highlight that there is still much that we do not understand regarding the drivers of H2 uptake in soils and that further field measurements are required to improve global models.
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RC1: 'Comment on egusphere-2024-3654', Anonymous Referee #1, 09 Jan 2025
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The paper presents a time-resolved dataset of H2 flux measurements in two different ecosystems in central Scotland—a managed grassland and a deciduous woodland. It addresses a critical data gap in H2 biogeochemistry that constrains accurate projection of atmospheric H2 levels in a changing world. Deposition velocities reported for both sites indicate net uptake, although with greater spatial variability in the woodland site. While uptake was primarily controlled by soil moisture at the grassland site, no significant driver was identified at the woodland site, underscoring critical knowledge gaps in H2 cycling across soil and ecosystem types. The paper also presents a customized flux chamber protocol and regression analyses for measuring rapid H2 fluxes. The flux data as well as the measurement/analyses protocols are valuable contributions to the field of H2 biogeochemistry.
Specific comments:
Lines 55-56: “The soil H2 sink is caused by microbial activity, both under aerobic and anaerobic condition” clarify that the soil sink for atmospheric H2 (which is typically what term “soil sink” refers to) occurs under aerobic conditions.
Lines 60-61: The referenced paper does not discuss “the high H2 demand of microbes”, rather I believe the implication of their findings is that the large capacity of soils for H2 uptake is primarily constrained by diffusive limitation.
Lines 61-62: Clarify that such measurements exist, but are sparse/few in number (e.g., Conrad and Seiler, 1985; Yonemura et al., 1999, 2000a, 2000b; Smith-Downey et al., 2006, Smith-Downey 2008, Lallo et al., 2009, Khdhiri et al., 2015, etc.)
Lines 68-71: The second part of this sentence does not seem tied in with the idea of temperature controlling enzyme activity.
Lines 70-72: This appears to be an inaccurate/incomplete discussion of the interaction between the soil sinks of CH4 and H2. The authors seem to be referencing H2 dynamics in methanogenic environments, as suggested by the cited reference. If such environments, H2 is not competing with CH4 as the energy source for microbes but is instead being consumed by methanogens to produce CH4 (i.e., CH4 is the product of metabolism, not a direct competitor for H2). This is likely not directly relevant to the atmospheric H2 sink, except insofar as H2 emissions from such environments could contribute to atmospheric H2 levels. In terms of H2 vs. CH2 specifically as energy sources with implications for the soil sinks, a more relevant discussion would be the interaction between high-affinity H2 oxidizers and methanotrophs in aerated soils.
Line 73: Specifically, spatial variation in microbial diversity.
Line 255-260: Looks like total carbon varies between 2.2-4% at the woodland site (Fig. S4)—does this really indicate high spatial variability? Which figure or table compares the variability in C and N at the chamber-scale vs at the plot scale?
Line 295-296: Suggestion to clarify that the “increase” is referring to the difference between measured and predicted uptake rates. Also reference Table 4 (this should be called Table 3?).
Line 303: Table 3 or 4?
Lines 347-350: Perhaps, it is worth emphasizing that while both soils have similar porosity values (based on Table 1), the difference in texture implies variations in pore size distribution and connectivity, leading to different sensitivities to moisture changes.
Lines 350-351: Minor suggestion, but it may be helpful to rephrase this sentence to clarify that it’s the “well-drained” property of the soil that’s providing “ideal conditions” for H2 uptake, and not the litter lying on top. (The litter layer being thin is possibly contributing to this effect).
Figure S1: This figure is supposed to show the deposition velocity, but it looks identical to Fig. 2. The y-axis label also says “H2 flux” not “deposition velocity”
Citation: https://doi.org/10.5194/egusphere-2024-3654-RC1
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