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Partitioning of N in growing plants, microbial biomass and soil organic matter after amendment of N-ammonoxidized lignins

Nitrogen (N) availability is a crucial factor for maintaining soil productivity, but application of mineral N-fertilizer raises environmental concerns. Based on earlier humification models, ammonoxidized technical lignins were suggested as potential slow N-release fertilizers. In order to obtain fir...

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Published in:Soil biology & biochemistry 2013-05, Vol.60, p.125-133
Main Authors: De la Rosa, José M., Liebner, Falk, Pour, Georg, Knicker, Heike
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description Nitrogen (N) availability is a crucial factor for maintaining soil productivity, but application of mineral N-fertilizer raises environmental concerns. Based on earlier humification models, ammonoxidized technical lignins were suggested as potential slow N-release fertilizers. In order to obtain first insights on their efficiency as plant fertilizer, their impact on soil organic matter composition and stability, and its role within the N cycle in soils, pot experiments were performed in which perennial ryegrass (Lolium perenne L.) was grown on a typical Andalusian soil (Luvisol, chromic) after amendment of N-lignins highly enriched in 15N (Sarkanda and Indulin ammonoxidized lignins) for 75 days. For comparison, the incubation study was also carried out with soils with and without 15NO3 fertilization. Among these experiments, the addition of K15NO3 resulted in the greatest aboveground plant production. However, most of the growth occurred during the first 28 days. Thereafter, a fast decrease of the bioavailable N pool occurred. The application of ammonoxidized lignins altered the pH and electrical conductivity of the soil. At higher concentrations a retardation of seed germination was evidenced. After 75 days, the plant shoots from the pots amended with 15N-Indulin and 15N-Sarkanda accumulated 8% and 20% of the initial 15N present in the amended soils at the beginning of the experiment (15N0). In the 15N-Indulin pots the N was efficiently sequestered from fast release or leaching and most of 15N0 remained in the soil (64%). In contrast, the 15N-Sarkanda pots showed a lower efficiency in N retention. After 28 days of incubation only 42% of 15N0 was retained in the 15N-Sarkanda amended soil, but more than 17% was recovered within the soil microbial biomass. Until the end of the incubation time, the 15N0 detected in the soil microbial biomass decreased to less than 3%, whereas the amount associated with the soil matrix maintained around 37%. The notable increase of 15N in the above-ground plant production (20%) evidences an efficient use of 15N released from the 15N-Sarkanda for plant production. Solid-state nuclear magnetic resonance (NMR) spectroscopy revealed that the 15N of the added 15N-lignins was quickly transformed into peptide-type N, most tentatively of microbial origin, without major alteration of the lignin backbone. This indicates that in soils the competition for nutrients favors N immobilization into biomass with its subsequent sequestration wit
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At higher concentrations a retardation of seed germination was evidenced. After 75 days, the plant shoots from the pots amended with 15N-Indulin and 15N-Sarkanda accumulated 8% and 20% of the initial 15N present in the amended soils at the beginning of the experiment (15N0). In the 15N-Indulin pots the N was efficiently sequestered from fast release or leaching and most of 15N0 remained in the soil (64%). In contrast, the 15N-Sarkanda pots showed a lower efficiency in N retention. After 28 days of incubation only 42% of 15N0 was retained in the 15N-Sarkanda amended soil, but more than 17% was recovered within the soil microbial biomass. Until the end of the incubation time, the 15N0 detected in the soil microbial biomass decreased to less than 3%, whereas the amount associated with the soil matrix maintained around 37%. The notable increase of 15N in the above-ground plant production (20%) evidences an efficient use of 15N released from the 15N-Sarkanda for plant production. Solid-state nuclear magnetic resonance (NMR) spectroscopy revealed that the 15N of the added 15N-lignins was quickly transformed into peptide-type N, most tentatively of microbial origin, without major alteration of the lignin backbone. 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Based on earlier humification models, ammonoxidized technical lignins were suggested as potential slow N-release fertilizers. In order to obtain first insights on their efficiency as plant fertilizer, their impact on soil organic matter composition and stability, and its role within the N cycle in soils, pot experiments were performed in which perennial ryegrass (Lolium perenne L.) was grown on a typical Andalusian soil (Luvisol, chromic) after amendment of N-lignins highly enriched in 15N (Sarkanda and Indulin ammonoxidized lignins) for 75 days. For comparison, the incubation study was also carried out with soils with and without 15NO3 fertilization. Among these experiments, the addition of K15NO3 resulted in the greatest aboveground plant production. However, most of the growth occurred during the first 28 days. Thereafter, a fast decrease of the bioavailable N pool occurred. The application of ammonoxidized lignins altered the pH and electrical conductivity of the soil. At higher concentrations a retardation of seed germination was evidenced. After 75 days, the plant shoots from the pots amended with 15N-Indulin and 15N-Sarkanda accumulated 8% and 20% of the initial 15N present in the amended soils at the beginning of the experiment (15N0). In the 15N-Indulin pots the N was efficiently sequestered from fast release or leaching and most of 15N0 remained in the soil (64%). In contrast, the 15N-Sarkanda pots showed a lower efficiency in N retention. After 28 days of incubation only 42% of 15N0 was retained in the 15N-Sarkanda amended soil, but more than 17% was recovered within the soil microbial biomass. Until the end of the incubation time, the 15N0 detected in the soil microbial biomass decreased to less than 3%, whereas the amount associated with the soil matrix maintained around 37%. The notable increase of 15N in the above-ground plant production (20%) evidences an efficient use of 15N released from the 15N-Sarkanda for plant production. Solid-state nuclear magnetic resonance (NMR) spectroscopy revealed that the 15N of the added 15N-lignins was quickly transformed into peptide-type N, most tentatively of microbial origin, without major alteration of the lignin backbone. This indicates that in soils the competition for nutrients favors N immobilization into biomass with its subsequent sequestration within recalcitrant biopolymers rather than its stabilization via covalent binding to lignins. ► Plants can use N from-ammonoxidized lignins for plant growth. ► Backbone of N-lignins amended to soil was not subject of major alteration during plant growth. ► NMR spectra showed quick transformation of N fixated in ammonoxidized-lignins into peptide-type N. ► Peptide N formed after release of N from N-lignins increase N-sequestration.</description><subject>Agronomy. Soil science and plant productions</subject><subject>Biochemistry and biology</subject><subject>Biological and medical sciences</subject><subject>biopolymers</subject><subject>Chemical, physicochemical, biochemical and biological properties</subject><subject>electrical conductivity</subject><subject>fertilizers</subject><subject>Fundamental and applied biological sciences. Psychology</subject><subject>General agronomy. Plant production</subject><subject>humification</subject><subject>leaching</subject><subject>lignin</subject><subject>Lolium perenne</subject><subject>Luvisols</subject><subject>microbial biomass</subject><subject>Microbiology</subject><subject>N fertilization</subject><subject>nitrogen</subject><subject>Nitrogen, phosphorus, potassium fertilizations</subject><subject>nuclear magnetic resonance spectroscopy</subject><subject>nutrients</subject><subject>Organic matter</subject><subject>Other nutrients. Amendments. Solid and liquid wastes. Sludges and slurries</subject><subject>Physics, chemistry, biochemistry and biology of agricultural and forest soils</subject><subject>Plant-available N</subject><subject>Recalcitrance of technical lignins</subject><subject>seed germination</subject><subject>shoots</subject><subject>Soil amendment</subject><subject>soil organic matter</subject><subject>Soil organic N stabilization</subject><subject>soil productivity</subject><subject>Soil science</subject><subject>Soil-plant relationships. Soil fertility. Fertilization. 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Soil science and plant productions</topic><topic>Biochemistry and biology</topic><topic>Biological and medical sciences</topic><topic>biopolymers</topic><topic>Chemical, physicochemical, biochemical and biological properties</topic><topic>electrical conductivity</topic><topic>fertilizers</topic><topic>Fundamental and applied biological sciences. Psychology</topic><topic>General agronomy. Plant production</topic><topic>humification</topic><topic>leaching</topic><topic>lignin</topic><topic>Lolium perenne</topic><topic>Luvisols</topic><topic>microbial biomass</topic><topic>Microbiology</topic><topic>N fertilization</topic><topic>nitrogen</topic><topic>Nitrogen, phosphorus, potassium fertilizations</topic><topic>nuclear magnetic resonance spectroscopy</topic><topic>nutrients</topic><topic>Organic matter</topic><topic>Other nutrients. Amendments. Solid and liquid wastes. Sludges and slurries</topic><topic>Physics, chemistry, biochemistry and biology of agricultural and forest soils</topic><topic>Plant-available N</topic><topic>Recalcitrance of technical lignins</topic><topic>seed germination</topic><topic>shoots</topic><topic>Soil amendment</topic><topic>soil organic matter</topic><topic>Soil organic N stabilization</topic><topic>soil productivity</topic><topic>Soil science</topic><topic>Soil-plant relationships. Soil fertility. Fertilization. Amendments</topic><toplevel>peer_reviewed</toplevel><toplevel>online_resources</toplevel><creatorcontrib>De la Rosa, José M.</creatorcontrib><creatorcontrib>Liebner, Falk</creatorcontrib><creatorcontrib>Pour, Georg</creatorcontrib><creatorcontrib>Knicker, Heike</creatorcontrib><collection>AGRIS</collection><collection>Pascal-Francis</collection><collection>CrossRef</collection><collection>Ecology Abstracts</collection><collection>Industrial and Applied Microbiology Abstracts (Microbiology A)</collection><collection>Water Resources Abstracts</collection><collection>Technology Research Database</collection><collection>Environmental Sciences and Pollution Management</collection><collection>ASFA: Aquatic Sciences and Fisheries Abstracts</collection><collection>Engineering Research Database</collection><collection>Aquatic Science &amp; Fisheries Abstracts (ASFA) 1: Biological Sciences &amp; Living Resources</collection><collection>Aquatic Science &amp; Fisheries Abstracts (ASFA) Professional</collection><collection>Biotechnology and BioEngineering Abstracts</collection><jtitle>Soil biology &amp; biochemistry</jtitle></facets><delivery><delcategory>Remote Search Resource</delcategory><fulltext>fulltext</fulltext></delivery><addata><au>De la Rosa, José M.</au><au>Liebner, Falk</au><au>Pour, Georg</au><au>Knicker, Heike</au><format>journal</format><genre>article</genre><ristype>JOUR</ristype><atitle>Partitioning of N in growing plants, microbial biomass and soil organic matter after amendment of N-ammonoxidized lignins</atitle><jtitle>Soil biology &amp; biochemistry</jtitle><date>2013-05-01</date><risdate>2013</risdate><volume>60</volume><spage>125</spage><epage>133</epage><pages>125-133</pages><issn>0038-0717</issn><eissn>1879-3428</eissn><coden>SBIOAH</coden><abstract>Nitrogen (N) availability is a crucial factor for maintaining soil productivity, but application of mineral N-fertilizer raises environmental concerns. Based on earlier humification models, ammonoxidized technical lignins were suggested as potential slow N-release fertilizers. In order to obtain first insights on their efficiency as plant fertilizer, their impact on soil organic matter composition and stability, and its role within the N cycle in soils, pot experiments were performed in which perennial ryegrass (Lolium perenne L.) was grown on a typical Andalusian soil (Luvisol, chromic) after amendment of N-lignins highly enriched in 15N (Sarkanda and Indulin ammonoxidized lignins) for 75 days. For comparison, the incubation study was also carried out with soils with and without 15NO3 fertilization. Among these experiments, the addition of K15NO3 resulted in the greatest aboveground plant production. However, most of the growth occurred during the first 28 days. Thereafter, a fast decrease of the bioavailable N pool occurred. The application of ammonoxidized lignins altered the pH and electrical conductivity of the soil. At higher concentrations a retardation of seed germination was evidenced. After 75 days, the plant shoots from the pots amended with 15N-Indulin and 15N-Sarkanda accumulated 8% and 20% of the initial 15N present in the amended soils at the beginning of the experiment (15N0). In the 15N-Indulin pots the N was efficiently sequestered from fast release or leaching and most of 15N0 remained in the soil (64%). In contrast, the 15N-Sarkanda pots showed a lower efficiency in N retention. After 28 days of incubation only 42% of 15N0 was retained in the 15N-Sarkanda amended soil, but more than 17% was recovered within the soil microbial biomass. Until the end of the incubation time, the 15N0 detected in the soil microbial biomass decreased to less than 3%, whereas the amount associated with the soil matrix maintained around 37%. The notable increase of 15N in the above-ground plant production (20%) evidences an efficient use of 15N released from the 15N-Sarkanda for plant production. Solid-state nuclear magnetic resonance (NMR) spectroscopy revealed that the 15N of the added 15N-lignins was quickly transformed into peptide-type N, most tentatively of microbial origin, without major alteration of the lignin backbone. This indicates that in soils the competition for nutrients favors N immobilization into biomass with its subsequent sequestration within recalcitrant biopolymers rather than its stabilization via covalent binding to lignins. ► Plants can use N from-ammonoxidized lignins for plant growth. ► Backbone of N-lignins amended to soil was not subject of major alteration during plant growth. ► NMR spectra showed quick transformation of N fixated in ammonoxidized-lignins into peptide-type N. ► Peptide N formed after release of N from N-lignins increase N-sequestration.</abstract><cop>Amsterdam</cop><pub>Elsevier Ltd</pub><doi>10.1016/j.soilbio.2013.01.024</doi><tpages>9</tpages><oa>free_for_read</oa></addata></record>
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ispartof Soil biology & biochemistry, 2013-05, Vol.60, p.125-133
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subjects Agronomy. Soil science and plant productions
Biochemistry and biology
Biological and medical sciences
biopolymers
Chemical, physicochemical, biochemical and biological properties
electrical conductivity
fertilizers
Fundamental and applied biological sciences. Psychology
General agronomy. Plant production
humification
leaching
lignin
Lolium perenne
Luvisols
microbial biomass
Microbiology
N fertilization
nitrogen
Nitrogen, phosphorus, potassium fertilizations
nuclear magnetic resonance spectroscopy
nutrients
Organic matter
Other nutrients. Amendments. Solid and liquid wastes. Sludges and slurries
Physics, chemistry, biochemistry and biology of agricultural and forest soils
Plant-available N
Recalcitrance of technical lignins
seed germination
shoots
Soil amendment
soil organic matter
Soil organic N stabilization
soil productivity
Soil science
Soil-plant relationships. Soil fertility. Fertilization. Amendments
title Partitioning of N in growing plants, microbial biomass and soil organic matter after amendment of N-ammonoxidized lignins
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