Water-Extractable Organic Matter of Soils with Different Degrees of Erosion and Avulsion in a Small Catchment in the Central Forest-Steppe of the Central Russian Uplands: Soil Sediments at the Dry Valley Bottom

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Abstract

We studied the composition of water-extractable organic matter (WEOM) of reclaimed soils (Novic Protocalcic Chernozems) in the unplowed bottom of the dry valley and to compared it with the composition of WEOM of the plowed soils (Protocalcic Chernozems) on cropland in the small catchment. A layer-by-layer study of the composition of the WEOM of reclaimed soils was carried out from the surface to a depth of 120 cm with a step of 20 cm. Aqueous extracts were characterized by the content of organic carbon, nitrogen and pH value. The optical properties of WEOM were assessed by spectrophotometry and fluorescence spectroscopy. The optical properties of WEOM of Protocalcic Chernozems were compared with those of sediments. The features of changes in these properties with depth in sediments were also analyzed. It was revealed that erosion-accumulation processes have a significant impact on the composition of soil WEOM. The content of dissolved carbon in WEOM does not differ significantly either between arable chernozems and sediments, or along the depth of the vertical profiles of sediments. At the same time, content of nitrogen WEOM in the arable chernozems is generally higher than in the sediments, and in the sediments it naturally decreases with the depth. Probably the decrease of nitrogen content of WEOM with the depth of sediments is associated with its absorption by plant roots and with an increase with the depth in the proportion of anaerobic zones where denitrification processes are activated. The top 0–60 cm of soil sediments actively retain nutrients leached from arable soils, primarily dissolved nitrogen. This process promotes the accumulation of carbon in the underlying layers. The increase in the content of total organic carbon in Novic Protocalcic Chernozems layers deeper than 60 cm can be explained by the accumulation of DOM penetrating from above. DOM in the lower layers of Novic Protocalcic Chernozems, on the one hand, is sorbed by the soil, and on the other hand, it is preserved due to a decrease in microbial activity due to a lack of nutrients.

About the authors

V. A. Kholodov

Dokuchaev Soil Science Institute

Author for correspondence.
Email: vkholod@mail.ru
ORCID iD: 0000-0002-6896-7897
Russian Federation, Moscow

N. V. Yaroslavtseva

Dokuchaev Soil Science Institute

Email: vkholod@mail.ru
Russian Federation, Moscow

A. R. Ziganshina

Dokuchaev Soil Science Institute

Email: vkholod@mail.ru
Russian Federation, Moscow

N. N. Danchenko

Dokuchaev Soil Science Institute

Email: vkholod@mail.ru
Russian Federation, Moscow

I. V. Danilin

Dokuchaev Soil Science Institute

Email: vkholod@mail.ru
Russian Federation, Moscow

Yu. R. Farkhodov

Dokuchaev Soil Science Institute

Email: vkholod@mail.ru
Russian Federation, Moscow

A. P. Zhidkin

Dokuchaev Soil Science Institute

Email: vkholod@mail.ru
Russian Federation, Moscow

References

Supplementary files

Supplementary Files
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1. JATS XML
2. Fig. 1. The layout of a small watershed (left) and a satellite image of a small watershed with superimposed contour lines and soil survey points (right).

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3. Fig. 2. Content of organic carbon (OC), nitrogen (N) in soil layers, pH value of aqueous extract (pH), amount of dissolved organic carbon in WEO (WEO): 1 – average values ​​of the layer 1–2 cm of arable chernozems; 2 – average values ​​of layers from different depths of stratozems in the bottom of the ravine.

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4. Fig. 3. Averaged absorption spectra of soil EEOC: filled symbols – layers of stratosols at the bottom of the ravine every 20 cm from 120 cm to 120 cm; unfilled symbols – for the layer 120–20 cm above the arable chernozems.

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5. Fig. 4. Indicators of the absorption spectra of SUVA254, E2/E3, E4/E6, S275–295, S350–400 and SR of the VEOV in soil layers: 1 – average indicators of the layer ٠– 2٠ cm above the arable chernozems; 2 – stratozems of the ravine bottom.

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6. Fig. 5. Typical three-dimensional fluorescence spectra of VEOV in soil layers (1–12 cm): 1 – arable chernozems; 2 – stratozems of the ravine.

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7. Fig. 6. Components C1–C5 see Table 1, obtained by decomposition of fluorescent 3D spectra of HEOV using PARAFAC. Each component in RU is normalized to its maximum intensity.

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8. Fig. 7. Values ​​of fluorescent components C 1–C 5 see Table 1 (RU) of VEOV in soil layers: 1 – average values ​​of the layer ٠– 2٠ cm above the arable chernozems; 2 – stratozems of the ravine bottom.

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