Immediate and long-term effect of tannins on the stabilization of soil aggregates
Introduction
Aggregate stability is a key indicator of several soil properties, such as erodibility (Barthès and Roose, 2002, Ding and Zhang, 2016), carbon storage (Jastrow and Miller, 1997) or penetration by roots (Angers and Caron, 1998). Soil organic matter has been widely recognized as a major determinant of aggregate stability (Abiven et al., 2009, Le Bissonnais et al., 2007, Six et al., 2004). The influence of organic inputs depends on their nature (Abiven et al., 2009, Monnier, 1965). Certain specific organic compounds have been studied in detail, such as root and microbial polysaccharides (Chenu, 1989, Chenu et al., 1994, Schlecht-Pietsch et al., 1994, Traoré et al., 2000, Czarnes et al., 2000, Zibilske et al., 2000) or fungal-related proteins (Rillig, 2004, Wright and Upadhyaya, 1998), which are shown to have an important, positive, short to mid-term stabilizing role. In contrast, other specific compounds such as plant tannins, which are polyphenols of high molecular weight, have been poorly explored. To our knowledge, the only study on tannins showed that tannic acids prolonged the effect of polysaccharides (Griffiths and Burns, 1972). Nevertheless, tannins can be considered as good candidates for stabilizing soil aggregates for different reasons: (i) large amounts of these compounds can enter the soil from leaf and root litter (Gallet and Lebreton, 1995, Hättenschwiler and Vitousek, 2000; Kraus et al., 2003, Meier et al., 2008); (ii) tannins possess a rapid sorption ability and remain for a longer time in soils than other substances (Schmidt et al., 2012), especially condensed tannins (Nierop and Verstraten, 2006), and most importantly (iii) tannins are known to react with different classes of macromolecules, which influence aggregate stability. In particular, the reaction of tannins with proteins is known to occur through multiple hydrogen bonds and hydrophobic interactions, resulting in the formation of macromolecular cross-linked complexes (Hagermann, 1989, Hättenschwiler and Vitousek, 2000, Kraus et al., 2003). This ability of tannins to form complexes suggests a potentially important role in the stabilization of soil aggregates, through enhanced chemical bonding between organic soil compounds, and in particular proteins already present in the soil. When in contact with polysaccharides, tannins are known to perturb the gelling process of these macromolecules because of their function as proton scavengers (Wüstenberg, 2014). Therefore, tannins could also inhibit the gelling process of certain polysaccharides found in root mucilage. Polysaccharides in root mucilage react with calcium (Ca2+) to form gel-like structures (de Kerchove and Elimelech, 2007), with a strong positive effect on soil stability (Czarnes et al., 2000). If tannins alter mucilage properties, they will have a potentially negative effect on soil aggregate stability.
Mediterranean road embankments provide a useful terrain for exploring the links between tannins and soil aggregate stability. Sparsely covered by plants after road construction, vegetation cover of embankments then follows a successional trend with significant changes in plant community composition (Odum, 1969), resulting in the replacement of grass and herb species (generally with low tannin concentrations in leaves and roots), by small shrubs and tree species (with higher quantities of tannins). In the Mediterranean region, concentrations of tannins in plant roots were found to range from 0.2 ± 0.2 to 9.42 ± 4.4% of tannins per gram of dried roots between early (>10 years-old) and late successional plant communities (40–69 years-old) (Balmot, unpublished data). These differences in tannin concentrations should therefore result in an increase of tannins in litter and soils along a successional gradient (Nierop and Verstraten, 2006), but whether they play a role in the stabilization of soil aggregates, which also augments along successional gradients (Andres and Jorba, 2000, Erktan et al., 2016), is not known.
We explored the role of tannins in the stabilization of Mediterranean soil aggregates from road embankments and tested whether this effect varied over time. We hypothesize that tannins influence soil aggregate stability through: (i) their ability to complex proteins and (ii) their ability to perturb the stabilizing gelling property of the root mucilage analogue polygalacturonic acid (PGA). If, according to our first hypothesis, tannins enhance aggregate stability by binding proteins and other macromolecules already present in soil, then soil enrichment with proteins prior to tannin addition should result in an increased positive impact of tannins. Similarly, if, as in our second hypothesis, tannins decrease aggregate stability by perturbing the gelling of the PGA, then soil enrichment with PGA prior to tannin addition should enhance such negative modulation.
To test these hypotheses, we observed the impact of tannins on the aggregate stability of two soils from road embankments, representing early and late plant successional stages. Experiments were conducted under controlled conditions, and tannins were added either alone or in combination with protein or polysaccharide compounds.
Section snippets
Site selection, soil sampling and isolation of soil aggregates
Soil samples were collected from road embankments near Montpellier in Southern France. The area is characterized by a Mediterranean sub-humid climate, with frequent freeze and thaw cycles in winter and a warm, dry summer. Over a 20 year period (1996–2015), mean annual temperature was 14.6 ± 6.8 °C with major daily variations (12.4 ± 4.7 °C) (INRA, Agroclim, France). Over the same period of time, mean annual precipitation was 774 ± 210 mm with most rainfall occurring in the autumn (3.9 ± 8.7 mm
Initial soil aggregate stability
Initial values of soil aggregate stability were all above 1.9 mm and weakly contrasted between the two sites. More precisely, only the slow wetting test resulted in significantly higher values for late successional soils (2.9 ± 0.1 mm) as compared to early successional soils (2.2 ± 0.1 mm; P < 0.01; Table 1). The fast wetting test did not discriminate between the two sites in term of initial soil aggregate stability, with 1.9 ± 0.1 mm in early successional soils and 2.0 ± 0.2 mm in late
Effect of tannins
We showed that when tannins were added alone to aggregates, effects were limited, both immediately and also after a 6 month incubation period. The main effects of tannins occurred through the modulation of the effects of the BSA model protein and the polysaccharide PGA. The failure to detect any significant effects of only tannins can be explained by different mechanisms: (i) soil proteins and polysaccharides with gelling properties were not concentrated enough in the soil to highlight the role
Conclusion
Tannins alone had very limited effects on aggregate stability from a Mediterranean soil. However, tannins increased the stabilizing role of BSA but decreased that of PGA, suggesting that the complexation of tannins with BSA enhanced chemical cohesion, but the reaction of tannins with PGA lowered the soil binding ability. Over time, tannins maintained longer the effect of BSA on stability, suggesting that their ability to slow down N degradation confers on them an indirect stabilizing role by
Acknowledgments
We thank Jean-Luc Belotti (INRA) for his technical assistance with soil aggregate stability measurements, performed at the LisaH laboratory. David Delguedre (CNRS) provided valuable assistance with incubation chambers. We are thankful to Virginie Moine and Grégoire Duthoit, from the Laffort compagny, who generously provided the tannin extracts. We thank Diane Bouchet and Mathieu Millan (INRA) for performing botanical surveys at the field sites. We thank the two anonymous reviewers and Claire
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