Abstract:Decomposition of O horizon organic matter made up 20% or less of soil respiration in the younger (o40 years since fire) stands, increasing to $ 50% in mature stands. This is a minimum for total heterotrophic contribution, since mineral soil CO 2 had D 14 C close to or less than those we have assigned to autotrophic respiration. Decomposition of old organic matter in mineral soils clearly contributed to soil respiration in younger stands in 2003, a very dry year, when D
14C of soil respiration in younger succes… Show more
“…Capturing the heterotrophic respiration end member can be challenging, due to lateral spatial heterogeneity associated with new C inputs, but also due to vertical changes in the location of microbial decomposition with soil temperature and moisture variations. The autotrophic respiration end member can also vary (albeit less so) within ecosystems, across vegetation types, and seasonally depending on stored carbohydrate (older C) contributions to root respiration (Czimczik et al 2006;Schuur and Trumbore 2006). Finally, 14 C measurements are expensive so studies are limited in Biogeochemistry (2011) 102:1-13 5 the number of replicates in time and space, and interpretation of the results must take into account sample size and uncertainty within the measurements.…”
Section: Isotope Approachesmentioning
confidence: 99%
“…To date, this approach has been used to look at autotrophic and heterotrophic contributions over seasonal to interannual timescales in temperate (Cisneros-Dozal et al 2006;Gaudinski et al 2000), boreal (Czimczik et al 2006;Hahn et al 2006;Schuur and Trumbore 2006), and semi-arid ecosystems; and with manipulations of rain (Borken et al 2006) and snow ). In addition, 14 C partitioning may also be an effective approach to test more specific process-level hypotheses on shorter timescales, particularly when combined with automated soil respiration measurements .…”
Soil respiration, the flux of CO 2 from the soil to the atmosphere represents a major flux in the global carbon cycle. Our ability to predict this flux remains limited because of multiple controlling mechanisms that interact over different temporal and spatial scales. However, new advances in measurement and analyses present an opportunity for the scientific community to improve the understanding of the mechanisms that regulate soil respiration. In this paper, we address several recent advancements in soil respiration research from experimental measurements and data analysis to new considerations for modeldata integration. We focus on the links between the soil-plant-atmosphere continuum at short (i.e., diel) and medium (i.e., seasonal-years) temporal scales. First, we bring attention to the importance of identifying sources of soil CO 2 production and highlight the application of automated soil respiration measurements and isotope approaches. Second, we discuss the need of quality assurance and quality control for applications in time series analysis. Third, we review perspectives about emergent ideas for modeling development and model-data integration for soil respiration research. Finally, we call for stronger interactions between modelers and experimentalists as a way to improve our understanding of soil respiration and overall terrestrial carbon cycling.
“…Capturing the heterotrophic respiration end member can be challenging, due to lateral spatial heterogeneity associated with new C inputs, but also due to vertical changes in the location of microbial decomposition with soil temperature and moisture variations. The autotrophic respiration end member can also vary (albeit less so) within ecosystems, across vegetation types, and seasonally depending on stored carbohydrate (older C) contributions to root respiration (Czimczik et al 2006;Schuur and Trumbore 2006). Finally, 14 C measurements are expensive so studies are limited in Biogeochemistry (2011) 102:1-13 5 the number of replicates in time and space, and interpretation of the results must take into account sample size and uncertainty within the measurements.…”
Section: Isotope Approachesmentioning
confidence: 99%
“…To date, this approach has been used to look at autotrophic and heterotrophic contributions over seasonal to interannual timescales in temperate (Cisneros-Dozal et al 2006;Gaudinski et al 2000), boreal (Czimczik et al 2006;Hahn et al 2006;Schuur and Trumbore 2006), and semi-arid ecosystems; and with manipulations of rain (Borken et al 2006) and snow ). In addition, 14 C partitioning may also be an effective approach to test more specific process-level hypotheses on shorter timescales, particularly when combined with automated soil respiration measurements .…”
Soil respiration, the flux of CO 2 from the soil to the atmosphere represents a major flux in the global carbon cycle. Our ability to predict this flux remains limited because of multiple controlling mechanisms that interact over different temporal and spatial scales. However, new advances in measurement and analyses present an opportunity for the scientific community to improve the understanding of the mechanisms that regulate soil respiration. In this paper, we address several recent advancements in soil respiration research from experimental measurements and data analysis to new considerations for modeldata integration. We focus on the links between the soil-plant-atmosphere continuum at short (i.e., diel) and medium (i.e., seasonal-years) temporal scales. First, we bring attention to the importance of identifying sources of soil CO 2 production and highlight the application of automated soil respiration measurements and isotope approaches. Second, we discuss the need of quality assurance and quality control for applications in time series analysis. Third, we review perspectives about emergent ideas for modeling development and model-data integration for soil respiration research. Finally, we call for stronger interactions between modelers and experimentalists as a way to improve our understanding of soil respiration and overall terrestrial carbon cycling.
“…Autotrophic respiration is driven by photosynthesis and vascular plant activity and not SOC mineralization. CO 2 derived from the mineralization of SOM, however, is independent of photosynthesis and represents a net loss of SOC [31]. Most soil CO 2 estimates do not differentiate between these sources and it is rarely possible to infer anything about changing SOC stores from CO 2 efflux data.…”
Section: Introductionmentioning
confidence: 99%
“…Vegetation fires affect SOC directly by volatilizing C during combustion [43] and indirectly through modification of the soil temperature, moisture, C and microbial environment [31,44]. If fire results in widespread vegetation death, then organic C input to the soil as ash and part-burned vegetation will increase over the short term.…”
Biological soil crusts (BSCs) are an important source of organic carbon, and affect a range of ecosystem functions in arid and semiarid environments. Yet the impact of grazing disturbance on crust properties and soil CO 2 efflux remain poorly studied, particularly in African ecosystems. The effects of burial under wind-blown sand, disaggregation and removal of BSCs on seasonal variations in soil CO 2 efflux, soil organic carbon, chlorophyll a and scytonemin were investigated at two sites in the Kalahari of southern Botswana. Field experiments were employed to isolate CO 2 efflux originating from BSCs in order to estimate the C exchange within the crust. Organic carbon was not evenly distributed through the soil profile but concentrated in the BSC. Soil CO 2 efflux was higher in Kalahari Sand than in calcrete soils, but rates varied significantly with seasonal changes in moisture and temperature. BSCs at both sites were a small net sink of C to the soil. Soil CO 2 efflux was significantly higher in sand soils where the BSC was removed, and on calcrete where the BSC was buried under sand. The BSC removal and burial under sand also significantly reduced chlorophyll a, organic carbon and scytonemin. Disaggregation of the soil crust, however, led to increases in chlorophyll a and organic carbon. The data confirm the importance of BSCs for C cycling in drylands and indicate intensive grazing, which destroys BSCs through trampling and burial, will adversely affect C sequestration and storage. Managed grazing, where soil surfaces are only lightly disturbed, would help maintain a positive carbon balance in African drylands.
“…Fire can affect the physical, chemical and biological properties of soil, e.g., aggregate stability, poresize distribution, water repellency, bulk density, decomposer/mineralization food webs, modification of mineralization rates, carbon sequestration, microbial species composition, and nutrient availability [2]. Most studies that consider the effects of fire on soil properties and soil biotic communities have been conducted in forest ecosystems [1,[3][4][5][6].…”
Prescribed fire produced a landscape with two types of severely burned patches: charred shrub patches and charred patches with tree trunks at the center. Soil nematodes were more abundant in burned and unburned juniper (Juniperus monosperma) tree patches than in yucca-shrub patches. There were no differences in nematode abundance between burned and unburned patches during the late spring and summer samples. Nematode abundance was significantly (p < 0.05) higher in unburned patches than in burned patches in the early spring samples, reflecting large differences in soil moisture between unburned and burned patches. There were no differences in soil nematode abundance between burned and unburned patches at oneyear post-burn and three-year post-burn sites. When all samples were pooled, taxonomic diversity, ecological indices, and abundance of trophic groups (bacteria-feeders, fungi-feeders, and omnivore-predators) were higher in unburned than burned patches. These results suggest that the long-term (up to three years post-burn) effects of fire on soil nematodes are indirect, i.e., by loss of tree canopies, litter accumulation, and shrub foliage, which affects soil temperatures and water redistribution.
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