Effects of urea amended with urease and nitrification inhibitors on soil nematode communities were studied in a Hapli- Udic Argosol (Cambisol, FAO) in Liaoning Province of Northeast China. A completely random design...Effects of urea amended with urease and nitrification inhibitors on soil nematode communities were studied in a Hapli- Udic Argosol (Cambisol, FAO) in Liaoning Province of Northeast China. A completely random design with four treatments, i.e., conventional urea (CU), slow-release urea amended with a liquid urease inhibitor (SRU1), SRU1 +nitrification inhibitor dicyandiamide (SRU2), and SRU1 + nitrification inhibitor 3,5-dimethylpyrazole (SRU3) and four replicates were applied. Thirty-nine genera of nematodes were identified, with Cephalobus and Aphelenchus being dominant; and in all treatments, the dominant trophic group was bacterivores. In addition, during the growth period of spring wheat (Triticum aestivum L.), soil urease activity was lower in SRUs than in CU. The numbers of total nematodes and bacterivores at wheat heading and ripening stages, and omnivores-predators at ripening stage were higher in SUR3 than in CU, SRU1 and SRU2 (P 〈 0.05).展开更多
Gibbs free binding energy and adsorption energy between cations and charged soil particles were used to evaluate the interactions between ions and soil particles. The distribution of Gibbs free adsorption energies cou...Gibbs free binding energy and adsorption energy between cations and charged soil particles were used to evaluate the interactions between ions and soil particles. The distribution of Gibbs free adsorption energies could not be determined experimentally before the development of Wien effect measurements in dilute soil suspensions. In the current study, energy relationships between heavy metal ions and particles of Hapli-Udic Argosol (Alfisol) and Ferri-Udic Argosol were inferred from Wien effect measurements in dilute suspensions of homoionic soil particles (〈 2 μm) of the two soils, which were saturated with ions of five heavy metals, in deionized water. The mean Gibbs free binding energies of the heavy metal ions with Hapli-Udic Argosol and Ferri-Udic Argosol particles diminished in the order of Pb^2+ 〉 Cd^2+ 〉 Cu^2+ 〉 Zn^2+ 〉 Cr^3+, where the range of binding energies for Hapli-Udic Argosol (7.25-9.32 kJ mol^-1) was similar to that for Ferri-Udic Argosol (7.43-9.35 kJ mol^-1). The electrical field-dependent mean Gibbs free adsorption energies of these heavy metal ions for Hapli-Udic Argosol and for Ferri-Udic Argosol descended in the order: Cu^2+ 〉 Cd2^+ 〉 Pb^2+ 〉 Zn^2+ 〉 Cr^3+, and Cd^2+ 〉 Cu^2+ 〉 Pb^2+ 〉 Zn^2+ 〉 Cr^3+, respectively. The mean Gibbs free adsorption energies of Cu^2+, Zn^2+, Cd^2+, Pb^2+, and Cr^3+ at a field strength of 200 kV cm^-1, for example, were in the range of 0.8-3.2 kJ mo1^-1 for the two soils.展开更多
基金Project supported by the National Key Basic Research Support Foundation of China (No. 2005CB121105) and the National High Technology Research and Development Program of China (No. 2005AA001480).
文摘Effects of urea amended with urease and nitrification inhibitors on soil nematode communities were studied in a Hapli- Udic Argosol (Cambisol, FAO) in Liaoning Province of Northeast China. A completely random design with four treatments, i.e., conventional urea (CU), slow-release urea amended with a liquid urease inhibitor (SRU1), SRU1 +nitrification inhibitor dicyandiamide (SRU2), and SRU1 + nitrification inhibitor 3,5-dimethylpyrazole (SRU3) and four replicates were applied. Thirty-nine genera of nematodes were identified, with Cephalobus and Aphelenchus being dominant; and in all treatments, the dominant trophic group was bacterivores. In addition, during the growth period of spring wheat (Triticum aestivum L.), soil urease activity was lower in SRUs than in CU. The numbers of total nematodes and bacterivores at wheat heading and ripening stages, and omnivores-predators at ripening stage were higher in SUR3 than in CU, SRU1 and SRU2 (P 〈 0.05).
基金Project supported by the National Natural Science Foundation of China(Nos.40401030 and 20577054).
文摘Gibbs free binding energy and adsorption energy between cations and charged soil particles were used to evaluate the interactions between ions and soil particles. The distribution of Gibbs free adsorption energies could not be determined experimentally before the development of Wien effect measurements in dilute soil suspensions. In the current study, energy relationships between heavy metal ions and particles of Hapli-Udic Argosol (Alfisol) and Ferri-Udic Argosol were inferred from Wien effect measurements in dilute suspensions of homoionic soil particles (〈 2 μm) of the two soils, which were saturated with ions of five heavy metals, in deionized water. The mean Gibbs free binding energies of the heavy metal ions with Hapli-Udic Argosol and Ferri-Udic Argosol particles diminished in the order of Pb^2+ 〉 Cd^2+ 〉 Cu^2+ 〉 Zn^2+ 〉 Cr^3+, where the range of binding energies for Hapli-Udic Argosol (7.25-9.32 kJ mol^-1) was similar to that for Ferri-Udic Argosol (7.43-9.35 kJ mol^-1). The electrical field-dependent mean Gibbs free adsorption energies of these heavy metal ions for Hapli-Udic Argosol and for Ferri-Udic Argosol descended in the order: Cu^2+ 〉 Cd2^+ 〉 Pb^2+ 〉 Zn^2+ 〉 Cr^3+, and Cd^2+ 〉 Cu^2+ 〉 Pb^2+ 〉 Zn^2+ 〉 Cr^3+, respectively. The mean Gibbs free adsorption energies of Cu^2+, Zn^2+, Cd^2+, Pb^2+, and Cr^3+ at a field strength of 200 kV cm^-1, for example, were in the range of 0.8-3.2 kJ mo1^-1 for the two soils.