152 publications from this institution
Highlights• Soil organic matter (SOM) includes pools of various thermal stability• Thermal stability of soil organic matter reflects to its microbial decomposition• Fire rises thermal stability of SOM reducing labile and increasing persistent pools• Increase in SOM thermal stability after fire reduced its microbial decomposition
No abstract is provided for this article.
There are scientific benefits for using an automated closed steady-state flow 13C (carbon; C) plant–soil labeling system (PSLS) for online recording and adjustment of 13CO2 (carbon dioxide) concentration equivalents to those used by photosynthesis, as compared to widely used uncontrolled open pulse labeling systems. Wheat plants were labeled at four growth stages (four leaves, tillering, late boot, and early dough) with 13CO2 for 2 and 6 h continuously. Analyses of the 13C/12C isotope using isotope ratio mass spectrometry of plant, soil solution, and rhizosphere soil samples showed that the injected 13CO2 was closely correlated with the 13C pools. The labeled 13C root exudates at tillering stage to rhizosphere soil increased from 0.4 ± 0.1 mg 13C pot−1 (four plants) after 2 h to 2.5 ± 1.0 mg 13C pot−1 after 6 h of labeling. The steady-state PSLS permits rapid control and maintenance of 13C by 13CO2 injection, enabling detailed examination of the C budget over short labeling periods.
No abstract is provided for this article.
ISHS Small Fruits, XXIII IHC PROSPECTIVE BLUEBERRY (VACCINIUM ASHEI READE AND V. CORYMBOSUM L.) GROWING AREAS IN SOUTH-CENTRAL CHILE
<p>Electron acceptors (NO<sub>3</sub><sup>–</sup>, SO<sub>4</sub><sup>2–</sup>, Fe<sup>3+</sup>, Mn<sup>4+</sup>) play a crucial function in the oxidation of soil recalcitrant organic compounds. Soils that present large amount of total Fe (8-57 g kg<sup>-1</sup>soil) and organic (C) (10-110 g kg<sup>-1</sup>soil), iron-reducing bacteria (IRB)  may play a importan role. In the present study we hypothesized that IRB which reduce Fe(III)(oxyhydr)oxide of low solubility to soluble Fe(II), can contribute substantially to the degradation of lignin from soil organic matter (SOM). The aim of this study was to isolate IRB and evaluate their importance in lignin degradation. IRB were obtained from topsoils of different climates (humid temperate, cold temperate, subpolar), vegetation type (steppe, rainforest) and parent materials (granitic, volcanic, fluvio-glacial, basaltic-Antartic and metamorphic). The potential of IRB to reduce Fe(III) was assessed with lactate substrate as source of carbon (C) and anthraquinone-2,6-disulfonate (AQDS) as electron acceptor. The contribution of IRB to lignin degradation was assessed in an anaerobic microcosms experiment for 36 h. The CO<sub>2</sub> efflux from sterilized and reinoculated soil with IRB was compared with sterilized (abiotic), non-sterilized (biotic) and induced Fenton reaction. Lignin degradation by IRB was examined by: 1) bacterial growth containing alkali lignin and alkali lignin disappearance during incubation, 2) Lignin peroxidase and manganese peroxidase activities originated from IRB, 3) cells abundance estimated from ATP synthase from bacteria growing in alkali lignin and 4) lignin degradation monitored by fluorescence disappearance intensity. The major microbial group for Fe(III) reduction, as essayed by PLFA and nested-PCR and sequencing different species were Geobactericeae-strains (G. metallireducens and G. lovleyi) in all studied. The CO<sub>2</sub> respiration in reinoculated soils was 140% higher than the CO<sub>2 </sub>release by abiotic and Fenton reaction and, 40% lower than biotic treated soil. The Fe(II) extractable in HCl in soil derived from basaltic-Antarctic parent material showed 362 % more Fe(II) solubilisation than that of biotic treatment. Fluorescence intensity decreased during lignin degradation and it was closely correlated with CO<sub>2</sub> release in the same sample. We conclude that IRB community such as Geobacter spp. Uses intensively Fe(III) as an electron acceptor to oxidize lignin compounds, and this process is especially active in Fe rich soils.</p>
Andic soils contain a large amount of stabilised soil organic matter (SOM). The present study aims to review and integrate the determining factors and mechanisms of SOM stabilisation in andic compared with other (non-andic) soil types. We have reviewed recent literature regarding the nature of SOM and its stabilisation processes in the top- and sub-soil to address and discuss the interaction between the SOM and the mineral phase. The carbon (C) storage capacity by the metal-humus-complex formation of volcanic soils is also evaluated. The most important stabilisation processes are related to the incorporation and decomposition of microbial-derived C along with the changing C storage capacity with increasing soil development. The priming and destabilisation of adsorbed SOM are crucial mechanisms influencing the soil C sequestration in subsoils. The C storage capacity of andic soils was closely related to the Na-pyrophosphate extractable Al and Fe. The upper boundary for SOM saturation with Al and Fe was a molar metal:C ratio of 0.18. The influence of climate, mineralogy and soil disturbances on the SOM storage capacity of andic soils also require further attention.
No abstract is provided for this article.
Rhizosphere, a thin area of soil surrounding roots receiving carbon (C) exudation from plants, represents a site of intense competition for available C and nutrient between surface-reactive particles and soil microorganisms.This competition can reduce the amount of available C to a critical level, it becomes limiting for microbial growth and soil organic matter decomposition.On the other hand, acceleration or retardation of decomposition of soil organic C caused by root activity is termed rhizosphere priming effect (RPE).This effect has been increasingly recognized to play a crucial role on native C destabilization as is influenced by fresh C availability, microbial activity and soil mineralogy such as crystallinity of clay minerals and Al-, Fe-oxides.Combining microbial ecology and soil mineral interactions, we can understand how soil characteristics and climate change can influence below ground competition and finally RPE.In this review, we focus on the competition for available C in soil, limiting our analyses to the interaction at rhizospheric space, where most processes between microorganisms and mineral phase occurs.
No abstract is provided for this article.
Although dry combustion (DC) carbon dioxide (CO2) is an accurate method to measure total soil carbon (C), it is a rather expensive one. Therefore, wet oxidation by the Walkley–Black (WB) method is widely used in acidic Chilean volcanic soils, although there are no studies comparing both WB and DC. The aim of this article was to compare DC and WB in a range of volcanic soils containing between 2% and 9% of soil C on a regional scale. Results indicated that the recovery (R) of soil C by WB with respect to DC varied between 70% and 82%. Consequently, the correction factor (100 / R) ranged between 1.26 and 1.47. The standardized major axis regression analysis indicated that the slope and the intercept of the fitted line on volcanic soils were similar to 1:1 line. In conclusion, WB was an economically suitable method to determine the soil C content of Chilean volcanic soils.
CCCada suelo posee una limitada capacidad de proteger fisico - quimicamente la materia organica contra la biodegradacion en sus particulas de arcilla y limo. Las tasas de mineralizacion de carbono (C) y nitrogeno (N) de los suelos estarian relacionadas al grado de saturacion de C en estas particulas. En el presente estudio se investigo la hipotesis de que la disminucion del C en la arcilla y limo a medida que el contenido de estas fracciones aumenta en los suelos se debe a una disminucion en la superficie especifica en las particulas de arcilla y limo. Tambien se investigo la relacion entre las tasas de mineralizacion de C y N con el grado de saturacion con C en las particulas de arcilla y limo. Seis suelos cultivados (cereales) y tres suelos de praderas (Medicago sativa L.) fueron muestreados a 0-20 cm de profundidad. Todos los suelos fueron dispersados con ultrasonido y gravimetricamente separados en fracciones > 50 µm (arena) y < 50 µm (arcilla y limo). A todas las muestras y al suelo entero se les determino el C - organico y la superficie especifica con etilenglicol. Por otra parte, se probo que existe una estrecha relacion entre el grado de saturacion con C en las particulas de arcilla y limo con las tasas de mineralizacion. Sin embargo, tambien se encontro una buena relacion entre el C-organico total del suelo y las tasas de mineralizacion. Esto ultimo coincidio con el hecho de haber encontrado una buena correlacion entre el C-organico del suelo y el grado de saturacion. Nuestros resultados explican parcialmente la hipotesis de que las tasas de mineralizacion estan mas relacionadas al grado de saturacion que a la textura (limo + arcilla) y al contenido de materia organica del suelo.