Abstract

The availability of P is often insufficient and limited by accumulation in soils. This led to the necessity of solutions for the recovery as well as recycling of secondary P resources. Batch experiments were conducted with CaCl2 and citric acid to characterize P release kinetics from vivianite, hydroxyapatite, and bone char. While the P release during the CaCl2 treatment was so low that only vivianite and hydroxyapatite showed a slightly higher release with increasing CaCl2 concentration, the increase of dissolved P was more pronounced for citric acid. The application of citric acid resulted in a 32,190-fold higher P release for bone char. Fourier-transform infrared spectroscopic data suggested higher instability of hydroxyapatite than for bone char. The kinetic data showed that bone char, especially at a lower particle size, had a higher long-term P release than hydroxyapatite or vivianite. The suitability of hydroxyapatite and bone char as a poorly soluble, but sustainable P source is better than that of vivianite. However, the efficiency as a P fertilizer is also dependent on present soil P mobilization processes. The results underline the importance of the accessibility of fertilized or naturally bound P for plant roots to benefit from the excretion of organic acids.

Highlights

  • Phosphorus (P) is an essential nutrient for physiological processes during plant growth and fertilization in agriculture is necessary to maintain crop productivity

  • The kinetic data indicated that Bone char (BC) samples, especially BC200, had a lower short-term P release [53], but a higher long-term P release than HA or VI

  • While the P release during the CaCl2 treatment was so low that only VI and HA showed a slightly higher release with increasing CaCl2 concentration, the increase of dissolved P was more pronounced for the citric acid (CA) treatment

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Summary

Introduction

Phosphorus (P) is an essential nutrient for physiological processes during plant growth and fertilization in agriculture is necessary to maintain crop productivity. Many soils worldwide have accumulated substantial amounts of fertilized P because of excessive applications over a longer period of time [4,5,6]. These soil P reserves, if they cannot be used efficiently, can cause eutrophication to marine and aquatic environments if lost [7]. It has become necessary to find sustainable solutions for an efficient use of the existing soil P reserves as well as secondary P sources (e.g., bone char or sewage sludge to substitute conventional fertilizers)

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