Aurora Gaxiola’s research while affiliated with Pontifical Catholic University of Chile and other places

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Publications (57)


Metabolic scaling from cells to catchments
  • Article

December 2024

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50 Reads

Proceedings of the National Academy of Sciences

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Aurora Gaxiola



Relationship between initial litter carbon (C) to nitrogen (N) ratio (proxy of litter quality) and decomposition rates (k) of the three species of litter, Aristotelia, Nothofagus, and Lomatia across three soil types. High initial litter C:N promotes lower decomposition rates than low initial C:N, but this effect is lower in the soil of Nothofagus, where the same differences in initial litter C:N resulted in less differences in decomposition rates. Error bars represent 1 standard error of the mean (n = 24 and 20).
Nitrogen (N) release patterns throughout litter decomposition. Values are litter N contents, expressed as percentage of the initial N, from each four plates collected at each removal date. Panels show values for each litter species × soil type combination. We used a non‐linear regression from the model proposed by Manzoni et al. (2008) to build each N release curve (solid lines). Dotted horizontal lines represent initial litter N content (100%), thus, values over this line indicate N accumulation. Dashed lines indicate those curves where the threshold element ratio (TER) is identical to initial litter C:N and represents the trajectory of neither C nor N limitation during litter decomposition.
Values of threshold element ratios (TER; shown in solid lines) throughout the decomposition experiment, calculated as the ratio of BG over NAG activities times litter carbon (C) to nitrogen (N) ratio (Equation 4). Mean values were calculated for every combination of litter species and soil type (vertical panels) for each removal date (n = 3). Dashed lines are trajectories of litter C:N during decomposition. Error bars represent 1 standard error of the mean. TER values higher than litter C:N imply higher allocation towards C acquisition (e.g. higher activity of BG vs. NAG; see Equation 4), the opposite results from higher allocation towards N acquisition.
Figure 1. Relationship between initial litter carbon (C) to nitrogen (N) ratio (proxy of litter quality) and decomposition rates (k) of the three species of litter, Aristotelia, Nothofagus, and Lomatia across three soil types. High initial litter C:N promotes lower decomposition rates than low initial C:N, but this effect is lower in the soil of Nothofagus, where the same differences in initial litter C:N resulted in less differences in decomposition rates. Error bars represent 1 standard error of the mean (n = 24 and 20).
Figure 2. Nitrogen (N) release patterns throughout litter decomposition. Values are litter N contents, expressed as percentage of the initial N, from each four plates collected at each removal date. Panels show values for each litter species × soil type combination. We used a non-linear regression from the model proposed by Manzoni et al. (2008) to build each N release curve (solid lines). Dotted horizontal lines represent initial litter N content (100%), thus, values over this line indicate N accumulation. Dashed lines indicate those curves where the threshold element ratio (TER) is identical to initial litter C:N and represents the trajectory of neither C nor N limitation during litter decomposition.

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Variability in terrestrial litter decomposition can be explained by nutrient allocation strategies among soil decomposer communities
  • Article
  • Publisher preview available

March 2023

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101 Reads

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7 Citations

Leaf litter decomposition is a key process for nutrient cycling with broad ecosystem‐level consequences. However, we still cannot explain an important amount of the observed variability in decomposition rates. Therefore, a mechanistic model of how litter quality impacts the metabolic capacity of microbial decomposers to degrade litter at a given rate could improve our understanding of litter decomposition. Elemental imbalances between leaf litter and microbial decomposers can lead to nutrient‐limited decomposition. Microbial decomposers can deal with elemental imbalances via three main physiological mechanisms; by adjusting their carbon use efficiency (i.e. the proportion of assimilated carbon that is not respired), accumulating nitrogen or adjusting extracellular enzyme allocation between carbon (C) and nitrogen (N). Therefore, decomposer communities that adjust to elemental imbalances using these strategies should decompose litter faster than those unable to adjust. In this study, in a reciprocal transplant microcosm, we experimentally evaluated whether differences in the capacity of decomposers to reduce elemental imbalances help explain variability in decomposition rates. We used litter and soils from three coexisting woody species with contrasting litter C:N. Throughout the decomposition experiment, we quantified litter biomass loss, the allocation to β‐1,4‐glucosidase and β‐N‐acetylglucosaminidase (i.e. C and N degrading enzymes), and N accumulation. These data allowed us to identify the main strategies through which decomposers deal with elemental imbalances and their concomitant effects on litter decomposition rates. Our results confirm that litter decomposition rates are strongly controlled by litter quality, but differences in decay rates are a function of C and N demands of decomposers. Here, decomposers dealt with elemental imbalances mainly through N accumulation and, to a lesser extent, through extracellular enzyme allocation and lower carbon use efficiency. However, when enzymatic allocation and N accumulation were insufficient to reduce elemental imbalances, decomposition rates were slower irrespective of litter quality. Finally, we show that the effectiveness of physiological strategies used by decomposers to reduce elemental imbalances will affect decomposition rates, a key ecosystem process. Read the free Plain Language Summary for this article on the Journal blog.

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Fig. 1 LTSER-Chile Network timeline and projection. The color bands indicate the various social actors involved. The grey dots indicate the relevant milestones of these actors, and the segmented black lines indicate the time frame of each milestone. The projections concern how best to configure a long-term monitoring program in Chile for the current decade to address the principal impacts of global change (adapted from [29])
Chilean long-term Socio-Ecological Research Network: progresses and challenges towards improving stewardship of unique ecosystems: Red Chilena de Investigación Socio-Ecológica de Largo Plazo: Avances y desafíos para el manejo responsable de ecosistemas únicos

March 2023

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104 Reads

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4 Citations

Revista Chilena de Historia Natural

Ecosystems provide a variety of benefits to human society and humanity’s utilization of ecosystems affects their composition, structure, and functions. Global change drivers demand us to study the interactions between ecological and social systems, and advise strategies to protect the large fraction of Chilean unique ecosystems. Long-term research and monitoring are vital for meaningful understanding of human impacts and socio-ecological feedback, which occur over multiple spatial and time-scales and can be invisible to traditional grant-sponsored short-term studies. Despite the large fraction of unique ecosystems, Chilean government agencies have not established long-term monitoring programs to inform and guide management decisions for use, conservation, and adaptation to climate change. Responding to this void, the Chilean Long-Term Socio-Ecological Research Network (LTSER-Chile) was created, comprising nine study sites funded by a variety of private and public institutions, that broadly seeks to understand how global change is altering biodiversity and ecosystem functions. The LTSER-Chile is currently in a phase of institutional consolidation to achieve its objectives of alignment with international efforts, fill the need for high-quality, long-term data on social, biological and physical components of Chilean ecosystems, and develop itself as an open research platform for the world. Despite the wide diversity of ecosystems ecncompased by LTSER-Chile sites, several common variables are monitored, especially climatic and hydrographic variables and many ecological indicator variables that consider temporal fluctuations, population and community dynamics. The main challenges currently facing the LTSER-Chile are to secure funding to maintain existing long-term monitoring programs, to persuade public and private decision-makers about its central role in informing and anticipating socio-ecological problems, and to achieve greater ecosystem representation by integrating new long-term study sites. This will require a more decisive political commitment of the State, to improve the stewardship of our unique terrestrial and marine ecosystems, and the realization that sound ecologically-sustainable policies will never be possible without a national monitoring network. We argue that the State should build on LTSER and several other private and university initiatives to provide the country with a monitoring network. In the absence of this commitment, the LTSER system is subject to discontinuity and frequent interruptions, which jeopardizes the long-term effort to understand the functioning of nature and its biodiversity.


Figure A2. Stone gardens: from the ancestors of Rapa-Nui to the world. Source: Young people, High school Aldea, Rapa Nui, GYPC. Figure A2. Stone gardens: from the ancestors of Rapa-Nui to the world. Source: Young people, High school Aldea, Rapa Nui, GYPC.
Figure A3. Hydroponics for all. Source: Young people, High school Cordillera, GYCP. Figure A3. Hydroponics for all. Source: Young people, High school Cordillera, GYCP.
Multi-criteria assessment of the success of projects.
Results of the Multi-criteria assessment of projects.
Cont.
sustainability-14-15116- Paper 2022

November 2022

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137 Reads

Sustainability

This paper contributes to a critical re-reading of the notion of climate services. It does so by problematizing the discontinuity between young people’s commitment to climate change, and the lack of a common vision regarding climate policy among governments. In this essay, youth commitment is characterized in terms of participation in the Global Youth Climate Pact (GYCP, 2015–2022). Here, young people share projects from their own high schools and communities and participate in a citizen consultation. Most projects have achieved a good success score, increasing over the years, especially for those carried out in emerging and developing countries. Some of them were presented at the COPs. In contrast, a textual analysis of intended nationally determined contributions (INDC) illustrates divergent understandings of the Paris Agreement and exemplifies the poor results of governmental climate diplomacy. This study establishes the need to closely monitor early warning signs of climate change in conjunction with high schools and school communities. The initiatives of young people are building a civic and planetary awareness for climate change in contrast with governmental division and inertia. In this sense, climate services, directed to young people, could contribute to design a sustainable future. We approach the practices, attitudes, and commitments of young people from the angle of cooperation rather than a moral vision of responsibility. Particularly, we propose a dialogical link between the treatment of climate issues and its effects on the constitution of networks, notably as they relate to practices of action, that is, the way in which distinct groups of young people develop relationships with their environments, organize themselves, and act and transform reality.


Fuente: Elaboración propia. Nota: Las líneas punteadas representan los límites nacionales superiores calculados con las distintas metodologías que han aplicado un enfoque top-down (ver cuadro 3).
Fuente: Elaboración propia.
Fuente: Elaboración propia a partir de los datos de Turbelin et al. 2017.
Las tres brechas del desarrollo sostenible y el cierre de la brecha ambiental en Chile: Oportunidades para una recuperación pospandemia más sostenible y con bajas emisiones de carbono en América Latina y el Caribe

El presente estudio implementa la hoja de ruta denominada “gran impulso para la sostenibilidad” propuesta por la CEPAL utilizando a Chile como caso de estudio. La ruta se genera adoptando una perspectiva de límites planetarios para calcular las brechas ambientales de Chile y con miras a la identificación de políticas públicas que fomenten el desarrollo de estrategias de crecimiento económico que sean ambientalmente sostenibles.



Overall relative abundances of the main bacterial and fungal phyla in each studied site.
PLS regression for the dominant OTUs of bacteria and fungi in all samples. For both groups, sites were significantly separated along axis 1, while a significant interaction between site (Lauca, Atacama, Farellones and Paine) and microhabitat (beneath Azorella and bare soil) was found along axis 2. This significant site:microhabitat interaction is further explored in Table 2. Colors represent sites: orange—Lauca; yellow—Atacama; green—Farellones; blue—Paine. Symbols represent microhabitat: circles—under Azorella; inverted triangles—bare soil.
A Importance of the main predictors on the relative abundance of the ten modules identified in the co-occurrence network of soil microbial communities after random forest analysis. B Co-occurrence network of soil microbial communities with colors representing the seven ecological clusters defined by random forest analysis. Dark green: Presence of Azorella. Light green: Absence of Azorella. Orange: Aridity. Yellow: Mesic ecosystems. Purple: High UV-B. Blue: Low UV-B. Gray: Tmean. Nodes are sized relative to the number of interactions. The table shows the main predictors, ecological clusters, the original modules contained in each ecological cluster (in brackets) and the number of bacterial and fungal OTUs in each ecological cluster.
Relative effect (RII values; mean ± CI (95%)) of Azorella cushion plants on soil parameters, total soil DNA, abundance (qPCR) of microbial groups and diversity of the main bacterial and fungal phyla. The effect of Azorella is significant when bars do not cross the 0 line. Data are organized along the X-axis from more arid (Lau (Lauca), Ata (Atacama)) to more mesic sites (Far (Farellones), Pai (Paine)).
Azorella Cushion Plants and Aridity are Important Drivers of Soil Microbial Communities in Andean Ecosystems

November 2021

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392 Reads

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14 Citations

Ecosystems

Cushion plants are specialized keystone species of alpine environments that can have a positive effect on ecosystem structure and function. However, we know relatively little about how cushion plants regulate the diversity and composition of soil microbial communities, major drivers of soil processes and ecosystem functioning. Identifying what factors drive the diversity and composition of soil microbial communities in high-elevation ecosystems is also fundamental to predict how global changes will affect their conservation and the services and functions they provide. Thus, we sampled four sites along the southern Andes following the vegetation belt of Azorella cushion species. The field sites spread along a latitudinal gradient and had contrasting levels of aridity, UV-B radiation, mean temperature and soil properties. Overall, Azorella, as well as aridity and UV-B radiation, were the major drivers of the distribution, composition and diversity of soil microbial communities in the studied ecosystems of the Chilean Andes. UV-B radiation affected particularly soil fungi, while soil properties such as pH, total C and N content, essential predictors of microbial diversity globally, had a much lower effect on the composition of soil microbial communities. Understanding the factors driving the structure and composition of microbial communities, particularly the role of cushion plants and the feedbacks between plant, climate and soil is of uttermost importance for the preservation of the functionality of high-elevation ecosystems threatened by climate change.


FIGURE 1 | Map showing the mean annual nitrogen deposition during 2006-2017 period and the location of the study sites within TeaComposition initiative. Data from the 524 colored sites have been used in the present study. Colors of each site depict biomes classified according to Walter and Breckle (1999). See Table 1 and Supplementary Table 1 for more detailed information of sites.
FIGURE 3 | Relationships between mass loss of Green tea and Rooibos tea and precipitation (A,D), air temperature (B,E) and N deposition values (C,F) after 3-month (A-C) and 12-month (D-F) incubation periods in all biomes. Blue and orange circles show the means and the bars are the standard errors based on the total number of observations. Climatic variables and N deposition were obtained from CHELSA ver. 1.2 and ACCMIP dataset, respectively. Band shows 95% confidence interval. Relationships without regression lines show non-significant relationships.
FIGURE 4 | Temperate-biome relationships between mass loss of Green tea and Rooibos tea and precipitation (A,D), air temperature (B,E), and N deposition (C,F) after 3-month (A-C) and 12-month (D-F) incubation periods. Blue and orange circles show the means and the bars are the standard errors based on the total number of observations. Band shows 95% confidence interval. Relationships without regression lines show non-significant relationships.
Summarized characteristics of the study sites used for the analyses within the TeaComposition initiative.
The effects of climatic factors and N deposition on the mass loss of Green tea and Rooibos tea after 3 and 12 months of incubation in all biomes.
Effects of Climate and Atmospheric Nitrogen Deposition on Early to Mid-Term Stage Litter Decomposition Across Biomes

July 2021

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1,094 Reads

Litter decomposition is a key process for carbon and nutrient cycling in terrestrial ecosystems and is mainly controlled by environmental conditions, substrate quantity, and quality as well as microbial community abundance and composition. In particular, the effects of climate and atmospheric nitrogen (N) deposition on litter decomposition and its temporal dynamics are of significant importance, since their effects might change over the course of the decomposition process. Within the TeaComposition initiative, we incubated Green tea and Rooibos tea at 530 sites across nine biomes. We assessed how macroclimate and atmospheric inorganic N deposition under current and predicted scenarios (RCP 2.6, RCP 8.5) might affect the litter decomposition rates measured after 3 and 12 months. Our study shows that the early to mid-term litter decomposition rates at the global scale were affected predominantly by litter quality (explaining 73% and 62% of the total variance in decomposition after 3 and 12 months, respectively) followed by climate and N deposition. The effects of climate was not litter-specific, and became increasingly significant as decomposition progressed, with MAP explaining 2% and MAT 4% of the variation after 12 months incubation. The effect of N deposition was litter-specific, and significant only for 12-month decomposition of Roibos tea at the global scale. However, in the temperate biome where atmospheric N deposition rates are relatively high, the 12-month loss of Green and Rooibos teas decreased significantly with increasing N deposition, explaining 9.6% and 1.1% of the variance, respectively. The expected changes in macroclimate at the global scale by the end of this century are estimated to increase the 12-month easily decomposable litter by 1.1 –3.5% and of the more stable substrates by 3.8 – 10.6%, relative to current mass loss. In contrast, expected changes in atmospheric N deposition will decrease the mid-term decomposition rate of high quality litter by 1.4 -2.2% and that of low-quality litter by 0.9 - 1.5% in the temperate biome. Our results suggest that projected increases in N deposition may have the capacity to dampen the climate-driven increases in litter decomposition depending on the biome and decomposition stage of substrate. Keywords: Tea bag, Green tea, Rooibos tea, Litter decomposition, Carbon turnover, Nitrogen deposition, TeaComposition initiative


Citations (41)


... Cover cropping provides above-and below-ground plant biomass and root exudates that boost soil microbial growth and prevent rich topsoil from eroding [51]. These findings align with previous research, including meta-analyses, which have documented increases in soil carbon, microbial biomass, and organic matter dynamics following cover cropping [52,53]. Enhanced soil microbial activity under higher SOM triggered by cover cropping was reported in the literature [54]. ...

Reference:

A Comparative Study of Agroecological Intensification Across Diverse European Agricultural Systems to Assess Soil Structure and Carbon Dynamics
Effects of sustainable agricultural practices on soil microbial diversity, composition, and functions
  • Citing Article
  • May 2024

Agriculture Ecosystems & Environment

... Chile, located in the southwestern part of South America, will be particularly affected due to the dependence on snow and ice melt (Barria et al 2019, Dussaillant et al 2019), reduction in precipitation (Ortega et al 2021, Salazar et al 2023 and increase droughts frequency and intensity (Ukkola et al 2020). Moreover, continental Chile contains unique environments and a myriad of climatic regimes that are highly vulnerable to global warming (Heusser 1974, Eshel et al 2021, Muñoz-Sáez et al 2021, Frêne et al 2023, Marquet et al 2023. ...

Chilean long-term Socio-Ecological Research Network: progresses and challenges towards improving stewardship of unique ecosystems: Red Chilena de Investigación Socio-Ecológica de Largo Plazo: Avances y desafíos para el manejo responsable de ecosistemas únicos

Revista Chilena de Historia Natural

... This led to similar remaining C levels for these amendments in both soils. This finding is in agreement with previous studies, such as Nett et al. [42] and Murúa and Gaxiola [43], which indicated that substrate-specific amendment history had minimal or no effect on the decomposition of recently added amendments. In contrast, a notable exception was observed with OP. ...

Variability in terrestrial litter decomposition can be explained by nutrient allocation strategies among soil decomposer communities

... La participación activa de la juventud en movimientos sociales refleja su compromiso con la equidad y la justicia y buscan revertir la exclusión histórica que han sufrido. De esta manera, a través de la implicación en iniciativas comunitarias y ambientales, la población joven no solo defiende sus derechos, sino que también promueven prácticas sostenibles que benefician a toda la comunidad (Pena-Vega et al., 2022). ...

Young People Are Changing Their Socio-Ecological Reality to Face Climate Change: Contrasting Transformative Youth Commitment with Division and Inertia of Governments
  • Citing Article
  • January 2022

... The station is located 15 km east of the city of Ancud, in the northern part of Chiloé Island, Chile (Fig. 1a-c), in a rural landscape mosaic of pastures, shrublands and forest patches, at 25 m above sea level and about 6 km from the coast. The climate is temperate with a strong oceanic influence (Beck et al., 2018), with a mean annual temperature of 9.7°C and a mean annual precipitation of 2087 mm, with the driest period from December to March (Perez-Quezada et al., 2021a). Soils are classified as Placic Andosols, which are waterlogged volcanic ash soils located on flat fluvial-glacial terraces (Centro de Información de Recursos Naturales, 2003). ...

Biotic and abiotic drivers of carbon, nitrogen and phosphorus stocks in a temperate rainforest
  • Citing Article
  • May 2021

Forest Ecology and Management

... As islands of more favorable micro-environments, cushion plants also serve as a refuge for organisms beyond the plant kingdom. They favor fungi and microbes (Rodríguez-Echeverría et al., 2021;Roy et al., 2013), which in turn serve as resources for higher trophic levels such as mites (Minor et al., 2016) or arthropods (Molina-Montenegro et al., 2006), whose diversity and abundance are also enhanced by cushion plants (Hugo et al., 2004;Molenda et al., 2012). Cushion plants are thus foundation species since they contribute to the formation of unique ecological communities within otherwise harsh high-alpine environments (Kikvidze et al., 2015;Wang et al., 2021). ...

Azorella Cushion Plants and Aridity are Important Drivers of Soil Microbial Communities in Andean Ecosystems

Ecosystems

... Likewise, it constitutes an area of ancestral connection between the indigenous peoples and nature. To preserve the tradition and customary coastal uses, local communities are claiming the management of the Guafo Island [33]. These island dwellers between the waters surrounding the island and the Gulf of Corcovado have also been considered for the delimitation of the coastal zones. ...

Indigenous rights to Patagonia’s Guafo Island
  • Citing Article
  • November 2020

Science

... This response might be due to grasses responding quickly to light rainfall (Lightfoot et al. 2012). Other rodent communities did not respond to precipitation but did respond to primary productivity (Ernest et al. 2000, Hernández et al. 2011, Lightfoot et al. 2012, Farías et al. 2021. ...

Species interactions across trophic levels mediate rainfall effects on dryland vegetation dynamics

... The bioaccumulation of soil organic carbon relies on the activities of soil microorganisms and plants, whose growth and activity are often nitrogen-limited in the newly exposed glacier forefields [5]. Nitrogen-fixation microorganisms (diazotrophs) play an important role in providing bioavailable nitrogen in glacier forefields, with their abundance increasing with soil age [1,50]. Due to their activities, nitrogen limitation is mitigated in the later stages of ecosystem succession [53]. ...

Soil microbial abundance and activity across forefield glacier chronosequence in the Northern Patagonian Ice Field, Chile

... Such values are even higher than those measured in typical wellaerated soils as in forests or grasslands, with average rates of 0.4-1.26 mg C m −2 d −1 (Murguia-Flores et al., 2021;Perez-Quezada et al., 2021). Twice the value of uptake during dry conditions compared to wet ones appears to be consistent with some proposed mechanisms promoting CH 4 reduction according to the existing literature, since the increase of temperature together with gas diffusivity due to loss of water may increase methane oxidation in a similar way to terrestrial ecosystems (Chen et al., 2011;Rafalska et al., 2023). ...

Long term effects of fire on the soil greenhouse gas balance of an old-growth temperate rainforest
  • Citing Article
  • February 2021

The Science of The Total Environment