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Phosphorus activators contribute to legacy phosphorus availability in agricultural soils: A review

TLDR
There is growing evidence that P activators can promote the release of phosphate from soil and, hence, have potential for mitigating the impending global P crisis.
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This article is published in Science of The Total Environment.The article was published on 2018-01-15 and is currently open access. It has received 336 citations till now. The article focuses on the topics: Crop residue.

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Exploring phosphorus fertilizers and fertilization strategies for improved human and environmental health

TL;DR: It is argued that the improvement of the nutritional value of crops, especially cereals, through reduced phytic acid and increased zinc and iron contents should be among the most important drivers toward the development of innovative fertilizer products and fertilization technologies.
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Phosphate-Solubilizing Microorganisms: Mechanism and Their Role in Phosphate Solubilization and Uptake

TL;DR: In this article, a review of different mechanisms and modes of action of phosphate-solubilizing microorganisms, their contribution to phosphorus solubilization, growth-promoting attributes in plants, and the molecular aspects of phosphatization are discussed.
Journal ArticleDOI

Characterization of phosphate solubilizing bacteria isolated from heavy metal contaminated soils and their potential for lead immobilization.

TL;DR: High concentration of lead can inhibit the growth of PSBs, and L1-5 isolate can transform lead ions into lead hydroxyapatite and pyromorphite, which could be exploited for bioremediation of Pb polluted soils in future.
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Phosphorus and phosphate solubilizing bacteria: Keys for sustainable agriculture

TL;DR: In this article, the most important minerals required for plant growth occupying a strong position among soil macro nutrients, such as P, are often fulfilled by phosphate fertilizers, which is one of the most essential minerals required by plant growth.
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Journal ArticleDOI

The story of phosphorus: Global food security and food for thought

TL;DR: In this article, the authors put forward the case for including long-term phosphorus scarcity on the priority agenda for global food security, and presented opportunities for recovering phosphorus and reducing demand together with institutional challenges.
Journal ArticleDOI

Forecasting agriculturally driven global environmental change

TL;DR: Should past dependences of the global environmental impacts of agriculture on human population and consumption continue, 109 hectares of natural ecosystems would be converted to agriculture by 2050, accompanied by 2.4- to 2.7-fold increases in nitrogen- and phosphorus-driven eutrophication of terrestrial, freshwater, and near-shore marine ecosystems.
Journal ArticleDOI

Changes in Inorganic and Organic Soil Phosphorus Fractions Induced by Cultivation Practices and by Laboratory Incubations

TL;DR: In this paper, changes in inorganic and organic phosphorus fractions resulting from 65 years of cropping in a wheat-wheat-fallow rotation were studied using a sequential extraction technique.
Journal ArticleDOI

Organic acids in the rhizosphere: a critical review

TL;DR: In this article, a review of the role of organic acids in rhizosphere processes is presented, which includes information on organic acid levels in plants (concentrations, compartmentalisation, spatial aspects, synthesis), plant efflux (passive versus active transport, theoretical versus experimental considerations), soil reactions (soil solution concentrations, sorption) and microbial considerations (mineralization).
Journal ArticleDOI

Bioavailability of soil inorganic P in the rhizosphere as affected by root-induced chemical changes: A review

TL;DR: In this paper, the authors give an overview of those chemical processes that are directly induced by plant roots and which can affect the concentration of P in the soil solution and, ultimately, the bioavailability of soil inorganic P to plants.
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Frequently Asked Questions (19)
Q1. What have the authors contributed in "Phosphorus activators contribute to legacy phosphorus availability in agricultural soils: a review" ?

In this paper, the authors try to clear up the potential for making 6 use of legacy P in soils for crop growth potentially alleviating the global P resource shortage. Specifically, 7 the authors try to clear up the potential of soil “ P activators ” for releasing fixed P. P activators accelerate and 8 strengthen process which transform P into bio-available forms via a range of chemical reactions and 9 biological interactions. Although reported performance is variable, there is growing evidence that P activators can 12 promote the release of phosphate from soil and, hence, have potential for mitigating the impending global P 13 crisis. Further basic and applied research is required to better understand the mechanisms of interaction of P 14 activators with natural soils and to maximize activator efficacy. 

247 Phosphodiesterase and phosphomonoesterase may act sequentially in the mineralization of Po: 248 phosphomonoesterase can dissociate the phosphate group from phosphate monoester compounds and 249 phosphodiesterase can hydrolyze the phosphate diester bond in nucleic acids. 

These include PSMs, phosphatase enzymes, enzyme activators, low molecular weight organic 519 acids, humic acids, lignin, crop residues, manure, biochar, zeolites, fly and wood ash, water-dissolved 520organic polymers, bentonite, mugineic acid and ABT rooting powder. 

Wanner (1996) found that 232many enzymes can function as organic phosphoester scavengers, releasing inorganic phosphates from 233 nucleotides and sugar phosphates. 

Biochar may also alter P availability through sorption of chelating organic 455 molecules like phenolic acids, amino acids and complex proteins or carbohydrates (Joseph et al., 2010). 

Bacteria which are known to enhance P 178availability include species of Pseudomonas, Azotobacter, Burkholderia, Bacillus and Rhizobium (Jones 179 and Oburger, 2011). 

Polyvinyl alcohol, polyacrylamide and polyethylene glycol have been shown to 501 increase P sorption and pH in red ferralitic soils (rich in ferric oxide hydrate). 

Crop residues, manure and biochar 406Like chemical phosphate fertilizer, crop residues, manure and biochar (charcoal produced from crop 407 residues) can also act as P sources. 

Xu et al. (2016) reported that biochar application can decrease P 462availability in saline sodic soil due to enhanced P sorption and precipitation. 

it is likely that remaining reserves will have increasingly lower quality and will be increasingly 43 more costly to extract, which means that the supply of high quality phosphate fertilizer will also become 44progressively more restricted (Cordell et al., 2009). 

In addition, a kind of 259 inorganic phosphatase (pyrophosphate phosphohydrolase) has been identified which can hydrolyze 260pyrophosphate (used as a fertilizer) to Pi (Dick and Tabatabai, 1978). 

Phosphatase enzyme and enzyme activators 244Phosphatase enzymes are widely distributed in natural environments and play a major role in Po 245 regulation (Fig. 3) by hydrolyzing ester-phosphate bonds in Po, leading to the release of phosphate (Burns 246 and Dick, 2002). 

Land application is the predominant method for disposing of 408agricultural residues, thereby recycling their nutrients Fig. 5) (Dai et al., 2016). 

Phosphate solubilizing bacteria (PSB: 170Achromobacter, Aereobacter, Agrobacterium, Alcaligenes, Arthrobacter, Aspergillus, Azotobacter, Bacillus, 171 Bradyrhizobium, Burkholderia, Chromobacterium, Enterbacter, Erwinia, Escherichia, Flavobacterium, 172Klebsiella, Micrococcus, Pantoea agglomerans, Pseudomonas, Rhizobium, Salmonella, Serratia, 173Thiobacillus) and phosphate solubilizing fungi (PSF: Alternaria, Arbuscular mycorrhiza, Aspergillus, 174Fusarium, Helminthosparium, Penicillium, Rhizopus, Sclerotium) make up 1-50% and 0.1-0.5% 175 respectively of the total PSMs in soil with an additional minor role played by phosphate solubilizing 176actinomycetes (PSA: Streptomyces, Nocardia) (Khan et al., 2007). 

These include desorption and 106solubilization of rapidly exchangeable Pi; uptake of P by soil microorganisms and plants (either through 107 their roots or through mycorrhizal hyphae); the release of Pi from the soil solid phase or from fertilizers, 108 induced by the exudation of phosphatases and organic acids from roots or microorganisms; the release of Pi 109 from plant residues or organic fertilizers to the soil solution; and the release of Pi from organic matter 110 mineralization by microorganisms (Frossard et al., 2011). 

It is possible that low molecular weight organic 351 acids could influence the activity of PSMs and, hence, affect the activity of phosphatases secreted by these 352organisms (Turner, 2008).353 3543.2.2. 

Results from a 415 dual-labelling experiment suggest that, on average, 16% of the P contained in surface-applied residues 416could be classed as labile P (Noack et al., 2014). 

Fig. 6 gives a summary of several methods for the modification of natural zeolites (Dai et al., 2011) 471 to enhance cation exchange capacity (due to the favorable ion-exchange selectivity of natural zeolites for 472certain cations, such as Cs+, Sr2+, and NH4+) and to the pH change induced by zeolites. 

153 Although activation processes are complex, several key factors have consistently been demonstrated to 154govern the availability of fixed P.