Earthworms build a complex network of stable biopores with diameters of up to 0.5 cm existing over years and decades in soil. Besides the direct habitat and pathway functions for the earthworms, the biopores strongly accelerate the diffusion and migration of gases,...
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Carbon (C) balance, rhizodeposition and root respiration during development of Lolium perenne were studied on a loamy Gleyic Cambisol by 14CO2 pulse labeling of shoots in a two-compartment chamber under controlled laboratory conditions. The losses from shoot respiration were about 36% of the total assimilated C. The highest respiration intensity was measured in the first night after the labeling, and diminishes exponentially over time. Total 14CO2 efflux from the soil (root respiration, microbial respiration of exudates and dead roots) in the first eight days after the 14C pulse labeling increased with plant development from 2.7 to 11% of the total 14C assimilated by plants. A model approach used for the partitioning of rhizosphere respiration showed that measured root respiration was between 1.4 and 3.5% of assimilated 14C, while microbial respiration of easily available rhizodeposits and dead root residues was between 0.9 and 6.8% of assimilated C. Both respiration processes increased during plant development. However, only the increase in root respiration was significant. The average contribution of root respiration to total 14CO2 efflux from the soil was approximately 46%. Total CO2 efflux from the soil was separated into plant-derived and soil-derived CO2 using 14C labeling. Additional decomposition of soil organic matter (positive priming effects) in rhizosphere was calculated by subtracting the CO2 efflux from bare soil from soil-derived CO2 efflux from soil with plants. Priming effects due to plant rhizodeposition reach 60kg of Cha−1 d−1. 14C incorporated in soil micro-organisms (extraction–fumigation) amounts to 0.8–3.2% of assimilated C. The total below-ground transfer of organic C by Lolium perenne was about 2800kg of Cha−1. The C input into the soil consists of about 50% of easily available organic substances.
Aims, and Scope. Reducing heavy metal solubility and bioavailability in contaminated area without removing them from the soil is one of the common practice
In a laboratory experiment, the following methods of separating the soil CO2 flux into the root respiration and the respiration of the rhizosphere and nonr
We developed a new concept of soil organic matter (SOM) formation and microbial utilization of organic carbon (C) and energy: microorganisms use most of the organics entering the soil as energy rather than as a C source, while SOM accumulates as a residual by-product because the microbial energy investment in its decomposition exceeds the energy gain. So, the energy use efficiency (EUE) is at least as important as the carbon use efficiency (CUE). The microbial EUE depends on the nominal oxidation state of carbon (NOSC) of organic compounds, which is the exact proxy of energy content: The energy content per C atom (enthalpy of combustion) increases by 108 kJ mol−1 C per one NOSC unit. The NOSC in litter remaining by decomposition decreases, and the energy content increases. Consequently, the NOSC of the remaining compounds drops to −0.3 units, and the oxidation decreases due to the residual accumulation of aromatic and aliphatic compounds, and entombment of the necromass. Preferential recycling of energy-rich reduced (lipids, aromatics, certain amino acids, amino sugars) and the microbial degradation of oxidized compounds (carboxylic acids) enrich energy content in remaining SOM. This explains why SOM is not fully mineralized (thermodynamically unfavorable). Energy from litter activates decomposers to mine nutrients stored in SOM (the main function of priming effects) because the nutrient content in SOM is 2–5 times higher than that of litter. Thus, the energy captured by photosynthesis is the main reason why microorganisms utilize organic matter, whereby SOM is merely a residual by-product of nutrient storage and a mediator of energy fluxes. For the first time we assessed the NOSC of microbial biomass in soil (−0.52) and calculated the corresponding energy content of −510 kJ mol−1 C, whereas bacteria contain less energy per unit of C than fungi. We linked CUE and EUE considering the NOSC of microbial biomass and element compositions of substrates utilized by microorganisms. The microbial EUE is always lower than CUE. This is one of the reasons why microbial growth is more limited by energy than by C. Based on the comparison of processes of C and energy utilization for cell growth and maintenance, we concluded that the two main mechanisms behind lower EUE versus CUE are: (i) microbial recycling: C can be microbially recycled, whereas energy is always utilized only once, and (ii) chemical reduction of organic and inorganic compounds: Energy is used for reduction, which is ongoing without C utilization. Gunina A, Kuzyakov Y 2022. From energy to (soil organic) matter. Global Change Biology 28 (7), 2169-2182Wang C, Kuzyakov Y 2023. Energy use efficiency of soil microorganisms: Driven by carbon recycling and reduction. Global Change Biology 29, 6170-6187