Shell carbonate diagenesis occurs in interaction with soil solution, where the concentration of Ca2+ is in equilibrium with exchangeable Ca2+ and weathering of Ca-bearing minerals. While the exchange process takes place within seconds, the dissolution equilibrium with Ca-bearing minerals achieves after months. We hypothesized that shell carbonate diagenesis proceeds slower in soils with high cation exchange capacity (CEC) than those with low CEC. The goal of this study was to determine the effects of soil CEC and exchangeable cations on shell carbonate diagenesis. Shells of Protothaca staminea were mixed in glass bottles with 1) carbonate-free sand (CEC = 0.37 cmol+kg-1) (S), 2) a native loamy soil (CEC = 16 cmol+kg-1) (LS) and 3) the same loamy soil saturated with KCl (replacing exchangeable cations with K+) (LSK). Samples were incubated at room temperature for 5, 20, 60 and 120 days. Bottles air was labeled with 14CO2 at the beginning and day 55. 14C was measured at sampling dates in bottles air, soil solutions, bulk soils and shells. Dissolved and exchangeable cations were measured. Shell carbonate diagenesis in LS and LSK (0.016 and 0.024 mg CaCO3, respectively) was one order of magnitude lower than in S (0.13 mg CaCO3). Shell carbonate dissolution and consequently recrystallization decreased at high amounts of exchangeable Ca2+ because exchange is faster than dissolution. Therefore, soil CEC and composition of exchangeable cations is a determinant factor of shell carbonate diagenesis and it should be considered by radiocarbon dating. Because shells in soils with lower CEC undergo more intensive diagenesis, they need further pretreatments before dating. Soil CEC should be also included in shell carbonate diagenesis models. Furthermore, 14C labeling can be used to investigate the rates of minerals weathering - at least for Ca-bearing minerals - and soil acidification.
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This contribution provides an elaboration of the theoretical background of an easy procedure allow- ing quantitative separate estimation of root respiration and rhizomicrobial respiration in nonsterile soils. The method is based on 13 C natural abundance by growing C 4 plants on C 3 soil or vice versa. Four δ 13 C values are necessary: of the soil organic matter, of the roots, of the soil microbial biomass, and of CO 2 efflux from the soil. The advantages and assumptions of the new approach, as well as possible applications including FACE systems and continuous labeling ( 13 C or 14 C) experiments are discussed. It is expected that the new method will become the standard procedure for separate estimation of root respiration (=respiration of autotroph organisms) and rhi- zomicrobial respiration (=respiration of heterotroph organisms) in nonsterile soils.
Various anionic polyacrylamide polymers (PAMs) are frequently used to improve soil properties and reduce erosion. However, the effects of their application on plant growth remain unclear. Aggregate-free loess with high water holding capacity was used as growing substrate to test the effects of two rates (10 and 40 kg ha−1) of a linear PAM on the growth of maize (Zea maize L.) for a period up to one month. The PAM effects were evaluated at three levels of soil water content (SWC) and three plant ages, based on water consumption, shoot and root biomass, as well as allocation of recently assimilated C in plants and soil using 14C labeling. Both SWC and maize age significantly affected water consumption, biomass accumulation, and 14C allocation in plant parts and soil. Even though consistent increases in plant biomass and total assimilated 14C were observed, the effects of PAM application were insignificant on either of these variables. The effects of PAM application were directly connected to soil rather than to maize, and could be masked by the non-structural loess. The effects tended to be age and soil-moisture specific, and were modulated by the rhizodeposition processes. The possible mechanisms of PAM application on plant growth were also discussed.
Earthworms produce biopores with strongly increased microbial and enzyme activities and consequently they form microbial hotspots in soil. In extremely dynamic microhabitats and hotspots such as earthworm biopores, the in situ enzyme activities are a footprint of...