the Creative Commons Attribution 4.0 License.
the Creative Commons Attribution 4.0 License.
Soil-plant-water relationships and crop yield under conservation agricultural practices: A biophysical basis for tailored adoption
Abstract. Conservation agriculture is widely promoted to reduce soil degradation, restore and maintain soil health, enhance crop productivity, and mitigate greenhouse gas emissions. This generally entails three core practices: reduced soil disturbance, permanent organic soil cover, and crop rotation. However, the universal applicability of these practices across diverse biophysical and socioeconomic contexts is under debate due to inconsistent agronomic performance and practical challenges associated with implementing all three practices simultaneously. To better understand the associated biophysical dynamic, we evaluated changes in soil-plant-water relationships and crop yields under five practices: no-till without residue (NT), reduced tillage without residue (RT), no-till with residue (NT+RR), reduced tillage with residue (RT+RR) and conventional tillage with residue retention (CT+RR), each compared with conventional tillage without residue retention (CT), using a global meta-analysis of observations from 338 studies across 361 experimental sites. Overall, yield declined by 6.1% (p = 0.024) under NT. However, yield reductions diminished with increasing tillage intensity (from NT to CT) and residue retention (p = 0.041). Sensitivity analysis revealed that yield reductions under NT are likely driven by compaction-driven adverse changes in soil hydraulic and mechanical properties limiting water movement (infiltration, redistribution and drainage), retention, and availability to crops, and root growth. Specifically, NT, irrespective of residue management, reduced soil near-saturated hydraulic conductivity – a property governing soil water replenishment, redistribution and drainage – by 26.9% (p = 0.008), increased soil penetration resistance by 29.4% (p < 0.001), and changed the pore size distribution, resulting in smaller air-capacities and larger wilting points. When reduced tillage and residue retention treatments were combined (RT+RR), yield variability was more strongly associated with changes in soil organic carbon and saturated hydraulic conductivity than water retention, and penetration resistance. Yield responses varied with local climate and soil type. NT increased yields in semi-dry climates (aridity index: 0.3-0.65) by 16.3% (p = 0.004). In contrast, NT reduced yield in humid regions (-7.2%, p < 0.001) as well as in dry regions (-8.3%, p = 0.038) where irrigated agriculture is likely to dominate. These yield responses by climate context closely mirrored the observed differences in saturated hydraulic conductivity. Yield penalties were generally greatest in clayey soils (e.g., under RT -19.3%, p = 0.047) and consistently diminished toward sandy soils, both under NT and RT. These findings highlight the need for context-specific implementation of conservation agriculture to achieve balanced agronomic and environmental benefits.
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RC1: 'Comment on egusphere-2026-2816', Anonymous Referee #1, 24 Jun 2026
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AC1: 'Reply on RC1', Mosisa Tujuba Wakjira, 12 Jul 2026
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First, we would like to sincerely thank Referee 1 for the time and expertise devoted to reviewing our manuscript. We greatly appreciate the constructive feedback, insightful comments, and valuable suggestions provided. Here, we provide clarifications on these comments. Referee comments are in normal, and our responses are in italic font.
This manuscript analysis soil-plant-water relationships and crop yield under conservation agricultural practices using global meta-analysis based on observations from 338 studies across 361 experimental sites worldwide. A series soil structural and mechanical parameters of convention tillage (CT) and conservation agricultural practices (NT, NT+RR, RT, RT+RR, CT+RR) under different regions (i.e., dry, semi-dry, and humid regions) were compared. The dataset is very impressive and the analyzed hydrological and mechanic parameters have a good link with crop yield. The manuscript is well-written and the results are important for the selection of the conservation agricultural in different regions. There are some comments needs to be considered before final publication on SOIL.
We thank Referee 1 very much for the positive feedback.
As is shown in Table 2, the penetration resistance largely depends on soil moisture conditions as well as measurement procedure (field measurement v.s., lab measurement under controlled moisture), but in the manuscript how to eliminate this difference on different studies? Are all the PenR from the same water content across the 361 experiment sites? Does the author filter or standardize the soil moisture status at which the PenR was measured? If it not, the authors should explicitly discuss how this affects the sensitivity analysis (Figure 6) where PenR shows lower importance for yield.
We thank the referee for this comment. We did not standardize penetration resistance (PenR) by soil moisture because in the majority of the source literature, PenR measurements were not reported together with the corresponding moisture conditions at the time of measurement. Only a few studies provided such information (e.g., PenR measurements at field capacity), while other studies only reported the timing of the sampling (e.g., after planting, at flowering, or after harvest). For this reason, our analysis represents what we assume as an average condition. We fully agree with the referee that this is an important limitation, given the strong sensitivity of PenR to soil moisture content. In our analysis, we assume that the soil moisture states of the paired treatments (conventional tillage, CT and conservation agriculture practices, CA) at each site are comparable. Therefore, by using response ratio (CA/CT) as a relative effect size, differences in soil moisture conditions among studies are minimized because ideally, these differences cancel out within studies (at the site level). Nevertheless, there are situations where this assumption may not hold. For example, when crop performance or root systems differ strongly between treatments, the soil moisture status of the treatments may also differ because of differences in crop water uptake. As a result, if PenR measurement is carried out a relatively longer period after the last rainfall or irrigation event, the soil moisture profiles of the CA and CT treatments may differ substantially, potentially violating the assumption of comparable moisture conditions between treatments. We will clarify this in the revised manuscript, extending the discussion in Lines 485-493.
Besides, air-capacity (AC) is defined as the difference between moisture content at saturation and field capacity. However, across literature, water content at field capacity is defined differently at pF 2.0 (10 kPa) or pF 2.5 (33 kPa). The pore size boundary between 10 kPa and 33 kPa is significantly different, this boundary determines whether AC captures true aeration macropores or structural mesopores. It is recommended to clarify the proportion of studies using pF 2.0 versus pF 2.5 and whether this introduces a bias across soil textural classes (Figure 4).
We thank the referee for the valuable comment. In the majority (56%) of the studies from which moisture content at field capacity (FC) was extracted, FC was measured at pF2.5 whereas in about 19% of the studies it was measured at pF 2.0. In the remaining 25% of the studies, the suction head at which FC was measured was not reported. The dominant proportion of measurements pF 2.5 reflects the larger proportion of medium- and fine-textured soils than coarse-textured soils. This is expected as FC is determined at pF 2.0 for coarse-textured soils and closer to pF 2.5 for medium- and fine-textured soils (Hillel, 1998). While the choice of pF influences the absolute magnitude of FC and consequently AC across soil textures, it does not meaningfully affect the absolute difference in FC between NT and CT (Figure 4), as well as the response ratio of AC, as the same definition of FC was used for each individual pair of control (conventional tillage, CT) and treatment (no-till, NT). We will clarify this point in the revised manuscript where appropriate.
In the discussion, Figures 7 and Figure 8 show new information about global correlation matrix and comprehensive pedoclimatic grid cross-referencing 12 soil properties with crop yields. However, the discussion part should be ideally reserved for mechanic interpretation, literature comparison, etc, rather than introducing new complex statistical analysis. Therefore, it’s recommended to create a new subsection in results part and put figure 7and 8 into this part, and this would make discussion more logical and coherent for readers.
Thank you very much for this constructive comment; we will implement this in the revision.
Line 55: …plant CO2 uptake; Line 90: all reporting 90 overall yield reductions under no-till when it is adopted alone; Line 116: delete the repeated sentence “for identifying the conditions in which CA”; Figure 8: check the spelling error “Robust positive” in the legend.
Thank you. We will correct them in the revised manuscript.
Table Formatting: For Tables 1 and 2, please reform them into the standard three-line table format as required by the SOIL journal guidelines. Remove all vertical lines and keep only three primary horizontal lines (top, bottom, and header line).
Thank you. We will revise the table as per the guidelines of the journal.
References:
Hillel, D.: Environmental Soil Physics, Toronto, 801 pp., 1998.
Citation: https://doi.org/10.5194/egusphere-2026-2816-AC1
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AC1: 'Reply on RC1', Mosisa Tujuba Wakjira, 12 Jul 2026
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This manuscript analysis soil-plant-water relationships and crop yield under conservation agricultural practices using global meta-analysis based on observations from 338 studies across 361 experimental sites worldwide. A series soil structural and mechanical parameters of convention tillage (CT) and conservation agricultural practices (NT, NT+RR, RT, RT+RR, CT+RR) under different regions (i.e., dry, semi-dry, and humid regions) were compared. The dataset is very impressive and the analyzed hydrological and mechanic parameters have a good link with crop yield. The manuscript is well-written and the results are important for the selection of the conservation agricultural in different regions. There are some comments needs to be considered before final publication on SOIL.
As is shown in Table 2, the penetration resistance largely depends on soil moisture conditions as well as measurement procedure (field measurement v.s., lab measurement under controlled moisture), but in the manuscript how to eliminate this difference on different studies? Are all the PenR from the same water content across the 361 experiment sites? Does the author filter or standardize the soil moisture status at which the PenR was measured? If it not, the authors should explicitly discuss how this affects the sensitivity analysis (Figure 6) where PenR shows lower importance for yield.
Besides, air-capacity (AC) is defined as the difference between moisture content at saturation and field capacity. However, across literature, water content at field capacity is defined differently at pF 2.0 (10 kPa) or pF 2.5 (33 kPa). The pore size boundary between 10 kPa and 33 kPa is significantly different, this boundary determines whether AC captures true aeration macropores or structural mesopores. It is recommended to clarify the proportion of studies using pF 2.0 versus pF 2.5 and whether this introduces a bias across soil textural classes (Figure 4).
In the discussion, Figures 7 and Figure 8 show new information about global correlation matrix and comprehensive pedoclimatic grid cross-referencing 12 soil properties with crop yields. However, the discussion part should be ideally reserved for mechanic interpretation, literature comparison, etc, rather than introducing new complex statistical analysis. Therefore, it’s recommended to create a new subsection in results part and put figure 7and 8 into this part, and this would make discussion more logical and coherent for readers.
Line 55: …plant CO2 uptake
Line 90: all reporting 90 overall yield reductions under no-till when it is adopted alone
Line 116: delete the repeated sentence “for identifying the conditions in which CA”
Table Formatting: For Tables 1 and 2, please reform them into the standard three-line table format as required by the SOIL journal guidelines. Remove all vertical lines and keep only three primary horizontal lines (top, bottom, and header line).
Figure 8: check the spelling error “Robust positive” in the legend.