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Verrecchia, Eric
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Verrecchia, Eric
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- PublicationAccès libreComposition and superposition of alluvial deposits drive macro-biological soil engineering and organic matter dynamics in floodplains(2019-8)
; ;Sebag, D. ;Turberg, P.; ;Guenat, C.; ;Adatte, T. ;Schlaepfer, R.Soil structure formation in alluvial soils is a fundamental process in near-natural floodplains. A stable soil structure is essential for many ecosystem services and helps to prevent river bank erosion. Plants and earthworms are successful soil engineering organisms that improve the soil structural stability through the incorporation of mineral and organic matter into soil aggregates. However, the heterogeneous succession of different textured mineral and buried organic matter layers could impede the development of a stable soil structure. Our study aims at improving the current understanding of soil structure formation and organic matter dynamics in near natural alluvial soils. We investigate the effects of soil engineering organisms, the composition, and the superimposition of different alluvial deposits on the structuration patterns, the aggregate stability, and organic matter dynamics in in vitro soil columns, representing sediment deposition processes in alluvial soils. Two successions of three different deposits, silt–buried litter–sand, and the inverse, were set up in mesocosms and allocated to four different treatments, i.e. plants, earthworms, plants+earthworms, and a control. X-ray computed tomography was used to identify structuration patterns generated by ecosystem engineers, i.e. plant root galleries and earthworm tunnels. Organic matter dynamics in macro-aggregates were investigated by Rock- Eval pyrolysis. Plant roots only extended in the top layers, whereas earthworms preferentially selected the buried litter and the silt layers. Soil structural stability measured via water stable aggregates (%WSA) increased in the presence of plants and in aggregates recovered from the buried litter layer. Organic matter dynamics were controlled by a complex interplay between the type of engineer, the composition (silt, sand, buried litter) and the succession of the deposits in the mesocosm. Our results indicate that the progress and efficiency of soil structure formation in alluvial soils strongly depends on the textural sequences of alluvial deposits. - PublicationAccès libreRock-Eval pyrolysis discriminates soil macro-aggregates formed by plants and earthworms(2018)
; ; ;Guenat, C.; ;Sebag, D.Plants and earthworms, as soil ecosystem engineers, play a crucial role during stabilisation of organic matter in soil through its incorporation into soil aggregates. It is therefore essential to better understand the mechanisms and interactions of soil engineering organisms regarding soil organic matter stabilisation. Several methods have already been successfully applied to differentiate soil aggregates by their origin, but they cannot specify the degree of organic matter stability within soil aggregates. Rock-Eval pyrolysis has already been proved to be pertinent for analyses of soil organic matter bulk chemistry and thermal stability, but it has not yet been directly applied to identify biogenic organic matter signatures within soil aggregates. In this study, Rock-Eval pyrolysis was used for the identification of the soil aggregate origin as well as for the determination of the soil organic matter bulk chemistry and thermal stability in a controlled experiment. Mesocosms were set up, containing treatments with a plant, an earthworm species, or both. Water stable soil macro-aggregates > 250 μm were sampled and tested with Rock-Eval pyrolysis after a two-month incubation period. Rock-Eval pyrolysis was able to differentiate soil macro-aggregates by their origin, and to identify a specific signature for each treatment. Macro-aggregates from the plant and earthworm treatment were characterized by a mixed signature incoming from the two soil engineers, indicating that both engineers contribute concomitantly to soil aggregate formation. Organic matter thermal stability was not positively affected by earthworms and even tends to decrease for the plant treatment, emphasising that organic matter was mainly physically protected during the incubation period, but not stabilised. However, future research is required to test if signatures for the tested organisms are species-specific or generally assignable to other plant and earthworm species. - PublicationAccès libreRock-Eval pyrolysis discriminates soil macro-aggregates formed by plants and earthworms(2018)
;Schomburg, Andreas; ;Guenat, Claire; ;Sebag, DavidLe Bayon, Renée ClairePlants and earthworms, as soil ecosystem engineers, play a crucial role during stabilisation of organic matter in soil through its incorporation into soil aggregates. It is therefore essential to better understand the mechanisms and interactions of soil engineering organisms regarding soil organic matter stabilisation. Several methods have already been successfully applied to differentiate soil aggregates by their origin, but they cannot specify the degree of organic matter stability within soil aggregates. Rock-Eval pyrolysis has already been proved to be pertinent for analyses of soil organic matter bulk chemistry and thermal stability, but it has not yet been directly applied to identify biogenic organic matter signatures within soil aggregates. In this study, Rock-Eval pyrolysis was used for the identification of the soil aggregate origin as well as for the determination of the soil organic matter bulk chemistry and thermal stability in a controlled experiment. Mesocosms were set up, containing treatments with a plant, an earthworm species, or both. Water stable soil macro-aggregates > 250 μm were sampled and tested with Rock-Eval pyrolysis after a two-month incubation period. Rock-Eval pyrolysis was able to differentiate soil macro-aggregates by their origin, and to identify a specific signature for each treatment. Macro-aggregates from the plant and earthworm treatment were characterized by a mixed signature incoming from the two soil engineers, indicating that both engineers contribute concomitantly to soil aggregate formation. Organic matter thermal stability was not positively affected by earthworms and even tends to decrease for the plant treatment, emphasising that organic matter was mainly physically protected during the incubation period, but not stabilised. However, future research is required to test if signatures for the tested organisms are species-specific or generally assignable to other plant and earthworm species. - PublicationAccès libreExploiting the fungal highway: development of a novel tool for the in situ isolation of bacteria migrating along fungal mycelium(2015)
; ; ; ;Wick, Lukas Y.; ;Kooli, Wafa M.; Fungi and bacteria form various associations that are central to numerous environmental processes. In the so-called fungal highway, bacteria disperse along fungal mycelium. We developed a novel tool for the in situ isolation of bacteria moving along fungal hyphae as well as for the recovery of fungi potentially involved in dispersal, both of which are attracted towards a target culture medium. We present the validation and the results of the first in situ test. Couples of fungi and bacteria were isolated from soil. Amongst the enriched organisms, we identified several species of fast-growing fungi (Fusarium sp. and Chaetomium sp.), as well as various potentially associated bacterial groups, including Variovorax soli, Olivibacter soli, Acinetobacter calcoaceticus, and several species of the genera Stenotrophomonas, Achromobacter and Ochrobactrum. Migration of bacteria along fungal hyphae across a discontinuous medium was confirmed in most of the cases. Although the majority of the bacteria for which migration was confirmed were also positive for flagellar motility, not all motile bacteria dispersed using their potential fungal partner. In addition, the importance of hydrophobicity of the fungal mycelial surface was confirmed. Future applications of the columns include targeting different types of microorganisms and their interactions, either by enrichment or by state of the art molecular biological methods. - PublicationAccès libreIsolation and characterization of oxalotrophic bacteria from tropical soils(2015)
; ;Braissant, Olivier; ; The oxalate–carbonate pathway (OCP) is a biogeochemical set of reactions that involves the conversion of atmospheric CO2 fixed by plants into biomass and, after the biological recycling of calcium oxalate by fungi and bacteria, into calcium carbonate in terrestrial environments. Oxalotrophic bacteria are a key element of this process because of their ability to oxidize calcium oxalate. However, the diversity and alternative carbon sources of oxalotrophs participating to this pathway are unknown. Therefore, the aim of this study was to characterize oxalotrophic bacteria in tropical OCP systems from Bolivia, India, and Cameroon. Ninety-five oxalotrophic strains were isolated and identified by sequencing of the 16S rRNA gene. Four genera corresponded to newly reported oxalotrophs (Afipia, Polaromonas, Humihabitans, and Psychrobacillus). Ten strains were selected to perform a more detailed characterization. Kinetic curves and microcalorimetry analyses showed that Variovorax soli C18 has the highest oxalate consumption rate with 0.240 μM h-1. Moreover, Streptomyces achromogenes A9 displays the highest metabolic plasticity. This study highlights the phylogenetic and physiological diversity of oxalotrophic bacteria in tropical soils under the influence of the oxalate–carbonate pathway. - PublicationAccès libre
- PublicationAccès libre
- PublicationAccès libreIdentification of active oxalotrophic bacteria by Bromodeoxyuridine DNA labeling in a microcosm soil experiments(2013)
; ;Martin, Gaëtan ;David, Maude M; ; - PublicationAccès libreThe impact of oxalogenic plants on soil carbon dynamics: formation of a millennium carbon storage as calcium carbonate(2012)
;Ferro, Katia ImeriaAu sud du Burkina Faso, des milliers d’années de pédogénèse ont produit des «Plinthic Ferralsols Arenic» (suivant la WRB). Il a toutefois été observé que sous l’influence d’arbres oxalogènes tels que Milicia excelsa, Afzelia africana et Bombax costatum, les sols évoluent vers des «Ferralic Calcisols Arenic» (selon la WRB) en quelques décennies. Il est admis que le moteur de cette accumulation carbonatée est l’oxalotrophie bactérienne, qui crée une pompe à carbone entre l’atmosphère et les sols.
Les buts de ce travail sont (1) de dresser un bilan de carbone, (2) de modéliser son accumulation et (3) de calculer un temps de résidence du carbone minéral dans le sol sous les arbres. Les échantillons ont été prélevés dans cinq profils à proximité d’arbres oxalogènes et un dans un sol de référence, hors de leur influence. Les teneurs en carbone organique total, en oxalates et en carbonates ont été ensuite mesurées. Les principaux outils utilisés pour quantifier ces trois formes de carbone ont été respectivement la pyrolyse Rock-Eval, la digestion enzymatique (Trinity-Biotech) et la titration en retour après dissolution acide des carbonates.
L’analyse de la matière organique indique que le carbone organique total évolue de manière quantitative et qualitative depuis les feuilles jusqu’aux horizons minéraux. Le stock de carbone organique est intégré dans les bio-molécules dans les horizons de surface (A) et dans les géo-molécules plus stables dans les horizons minéraux (B et C).
Cette étude montre que la quantité en oxalates dans les feuilles (considérées comme un premier réservoir d’oxalate) est de 20 x 10-2 mg/g de matière sèche. A cette source peut être ajoutée celle des champignons excréteurs d’acide oxalique. En effet, par la mise en culture d’échantillons de sol, les espèces oxalogènes suivantes ont été identifiées: Aspergillus sp., Fusarium sp. et Mucor sp..
Malgré ces deux apports d’oxalate (feuilles et champignons), la concentration mesurée dans les sols reste faible, ne dépassant pas 6.5 x 10-3 mg d’oxalate/g de sol à un instant t. Ceci-ci peut être expliqué par l’efficacité de l’oxydation bactérienne des oxalates menant à la précipitation de calcite faiblement magnésienne. En effet cette dernière, non présente dans les feuilles fraîches, a été observée dans la litière et les sols où les concentrations peuvent atteindre 15% de la masse totale.
Ces résultats ont permis de construire un premier modèle proposant que (1) la teneur en carbonates doublerait chaque 30 ans, (2) entre 70 et 170 ans l’accumulation en carbonates serait telle que le sol pourrait être cimenté, et (3) le temps de résidence du carbone pourrait aisément dépasser 4000 ans., South of Burkina Faso, thousands of years of pedogenesis have resulted in “Plinthic Ferralsols (Arenic)” (according to the WRB). However, it is observed that under the influence of oxalogenic trees, such as Milicia excelsa, Afzelia africana, and Bombax costatum, the soil evolves into a “Ferralic Calcisol (Arenic)” in less a millenium. It has been proposed that the driving force of this carbonate accumulation is the bacterial oxalotrophy, which generates a carbon pump between the atmosphere and the soil.
The principal goals of this work are (1) to provide a carbon balance, (2) to propose a model of the carbonate accumulation, and (3) to estimate the residence time of the inorganic carbon in the soil under the trees. Samples were taken from five profiles near the considered oxalogenic trees and a reference soil beyond their respective influence. Contents of total organic carbon, oxalate, and carbonate were measured. The main tools used to quantify these three different forms of carbon were the Rock-Eval pyrolysis, enzymatic digestion (Trinity Biotech), and back titration after acid dissolution of carbonate.
Analysis of organic matter indicates that the total organic carbon evolves both quantitatively and qualitatively from leaves to mineral horizons. The stock of organic carbon is incorporated in the bio-molecules at the surface horizons (A) and in stable geo-molecules in mineral horizons (B and C).
This study shows that the amount of oxalates in leaves (considered as a first oxalate reservoir) is of 20 x 10-2 mg / g of dry matter. Oxalogenic fungi may also have to be added to this source. Indeed, by culturing soil samples, the following oxalogenic strains were identified: Aspergillus sp., Fusarium sp. and Mucor sp..
Despite these contributions (leaves and fungi) of oxalate, the concentration measured in the soil is low, never exceeding 6.5 x 10-3 mg oxalate / g of soil at any time t. This unexpected outcome may be explained by the efficiency of the bacterial oxidation of oxalate, leading to low magnesium calcite precipitation. Indeed, the latter, while not present in fresh leaves, was found in litter and soils, where its concentration can reach values as high as 15% of the soil total mass.
All these results were finally used to propose a preliminary model suggesting that (1) the carbonate content is doubling every 30 years, (2) between 70 and 170 years the accumulation of carbonate is so significant that the soil may even become cemented, and (3) the residence time of carbon may easily exceed 4000 years. - PublicationAccès libreFungi, bacteria and soil pH: the oxalate–carbonate pathway as a model for metabolic interaction(2012)
;Martin, Gaëtan ;Guggiari, Matteo; ; ; ; ; ; The oxalate–carbonate pathway involves the oxidation of calcium oxalate to low-magnesium calcite and represents a potential long-term terrestrial sink for atmospheric CO2. In this pathway, bacterial oxalate degradation is associated with a strong local alkalinization and subsequent carbonate precipitation. In order to test whether this process occurs in soil, the role of bacteria, fungi and calcium oxalate amendments was studied using microcosms. In a model system with sterile soil amended with laboratory cultures of oxalotrophic bacteria and fungi, the addition of calcium oxalate induced a distinct pH shift and led to the final precipitation of calcite. However, the simultaneous presence of bacteria and fungi was essential to drive this pH shift. Growth of both oxalotrophic bacteria and fungi was confirmed by qPCR on the frc (oxalotrophic bacteria) and 16S rRNA genes, and the quantification of ergosterol (active fungal biomass) respectively. The experiment was replicated in microcosms with non-sterilized soil. In this case, the bacterial and fungal contribution to oxalate degradation was evaluated by treatments with specific biocides (cycloheximide and bronopol). Results showed that the autochthonous microflora oxidized calcium oxalate and induced a significant soil alkalinization. Moreover, data confirmed the results from the model soil showing that bacteria are essentially responsible for the pH shift, but require the presence of fungi for their oxalotrophic activity. The combined results highlight that the interaction between bacteria and fungi is essential to drive metabolic processes in complex environments such as soil.