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Journal ArticleDOI

Nitrogen Mineralization Potentials of Soils

George Stanford, +1 more
- 01 May 1972 - 
- Vol. 36, Iss: 3, pp 465-472
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TLDR
In this paper, a 30-week period at 35C, using incubation intervals of 2, 2, 4, 6, 8, and 8 weeks, was used to determine the net mineralization of 39 widely differing soils.
Abstract
Net mineralization of N in 39 widely differing soils was determined over a 30-week period at 35C, using incubation intervals of 2, 2, 4, 4, 4, 6, and 8 weeks. Mineral N was leached from the soils before the first incubation and following each of seven incubations by means of 0.01M CaCl₂ and a minus-N nutrient solution. Soil water contents were adjusted by applying suction (60 cm Hg), and losses of water during incubation under aerobic conditions were negligible. With most soils, cumulative net N mineralized was linearly related to the square root of time, t½. The pH of soils changed very little in the course of 30 weeks' incubation. Because of the generally consistent results, the data were employed in calculating the N mineralization potential, Nₒ, of each soil, based on the hypothesis that rate of N mineralization was proportional to the quantity of N comprising the mineralizable substrate. Values of Nₒ ranged from about 20 to over 300 ppm of air-dry soil. The fraction of total N comprising Nₒ varied widely (5 to 40%) among soils. Mineralization rate constants did not differ significantly among most of the soils. The most reliable estimate of the rate constant, k was .054 ± .009 week⁻¹. The time required to mineralize one-half of Nₒ, t½, was estimated to be 12.8 ± 2.2 weeks. Results suggest that the forms of organic N contributing to Nₒ were similar for most of the soils.

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Effects of Biological Nitrogen Reactions on Soil Lime Requirement Determined by Incubation

TL;DR: In this paper, the pH change following CaCO 3 incubations for 60 d with those following 3-d incubations with Ca(OH) 2 and to determine the possible role of soil N reactions causing any differences in pH change.
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Municipal biosolids as an alternative nutrient source for bioenergy crops: II. Decomposition and organic nitrogen mineralization.

TL;DR: In this paper, the authors compared the season of season of application on organic N mineralization rate and dry matter (DM) decomposition of Class A municipal biosolids measured in the field with litter bags and compared with that predicted from the DECOMPOSITION model.
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TL;DR: In this paper, the kinetics of Pb sorption were investigated on clay (silty clay, Torrifluvents), CaCO3-rich (sandy clay, Calciorthids), and sandy soils at two different temperatures.
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Factors Affecting Microbial Formation of Nitrate-Nitrogen in Soil and Their Effects on Fertilizer Nitrogen Use Efficiency

TL;DR: Predictions of the soil nitrate-N concentrations with a relative precision of 1 to 4 μg N g of soil were obtained with a computerized N fertilizer decision aid and grain yields obtained were not measurably different from those using adjacent farmer practices, but N fertilizer use was reduced by >10%.
Journal ArticleDOI

Kinetic Parameters of Gross N Mineralization of Peat Soils as Related to the Composition of Soil Organic Matter

TL;DR: In this article, the N-supplying capacity, one of the most important soil properties in terms of crop production, of peat soils was examined, and 10 peat soil samples were collected from Indonesia, Malaysia, and Japan.