Differences in labile soil organic matter explain potential denitrification and denitrifying communities in a long-term fertilization experiment

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  • Martin Luther University Halle-Wittenberg
  • Technical University of Munich (TUM)
  • Helmholtz Zentrum München - German Research Center for Environmental Health
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Original languageEnglish
Article number103630
JournalApplied soil ecology
Volume153
Early online date11 May 2020
Publication statusPublished - Sept 2020

Abstract

Content and quality of organic matter (OM) may strongly affect the denitrification potential of soils. In particular, the impact of soil OM fractions of differing bioavailability (soluble, particulate, and mineral-associated OM) on denitrification remains unresolved. We determined the potential N2O and N2 as well as CO2 production for samples of a Haplic Chernozem from six treatment plots (control, mineral N and NP, farmyard manure - FYM, and FYM + mineral N or NP) of the Static Fertilization Experiment Bad Lauchstädt (Germany) as related to OM properties and denitrifier gene abundances. Soil OM was analyzed for bulk chemical composition (13C-CPMAS NMR spectroscopy) as well as water-extractable, particulate, and mineral-associated fractions. Soils receiving FYM had more total OM and larger portions of labile fractions such as particulate and water-extractable OM. Incubations were run under anoxic conditions without nitrate limitation for seven days at 25 °C in the dark to determine the denitrification potential (N2O and N2) using the acetylene inhibition technique. Abundances of nirS, nirK, and nosZ (I + II) genes were analyzed before and after incubation. The denitrification potential, defined as the combined amount of N released as N2O + N2 over the experimental period, was larger for plots receiving FYM (25.9–27.2 mg N kg 1) than pure mineral fertilization (17.1–19.2 mg N kg 1) or no fertilization (12.6 mg N kg 1). The CO2 and N2O production were well related and up to three-fold larger for FYM-receiving soils than under pure mineral fertilization. The N2 production differed significantly only between all manured and non-manured soils. Nitrogenous gas emissions related most closely to water-extractable organic carbon (WEOC), which again related well to free particulate OM. The larger contribution of N2 production in soils without FYM application, and thus, with less readily decomposable OM, coincided with decreasing abundances of nirS genes (NO2 reductase) and increasing abundances of genes indicating complete denitrifying organisms (nosZ I) during anoxic conditions. Limited OM sources, thus, favored a microbial community more efficient in resource use. This study suggests that WEOC, representing readily bioavailable OM, is a straightforward indicator of the denitrification potential of soils.

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Differences in labile soil organic matter explain potential denitrification and denitrifying communities in a long-term fertilization experiment. / Surey, Ronny; Lippold, Eva; Heilek, Stefan et al.
In: Applied soil ecology, Vol. 153, 103630, 09.2020.

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title = "Differences in labile soil organic matter explain potential denitrification and denitrifying communities in a long-term fertilization experiment",
abstract = "Content and quality of organic matter (OM) may strongly affect the denitrification potential of soils. In particular, the impact of soil OM fractions of differing bioavailability (soluble, particulate, and mineral-associated OM) on denitrification remains unresolved. We determined the potential N2O and N2 as well as CO2 production for samples of a Haplic Chernozem from six treatment plots (control, mineral N and NP, farmyard manure - FYM, and FYM + mineral N or NP) of the Static Fertilization Experiment Bad Lauchst{\"a}dt (Germany) as related to OM properties and denitrifier gene abundances. Soil OM was analyzed for bulk chemical composition (13C-CPMAS NMR spectroscopy) as well as water-extractable, particulate, and mineral-associated fractions. Soils receiving FYM had more total OM and larger portions of labile fractions such as particulate and water-extractable OM. Incubations were run under anoxic conditions without nitrate limitation for seven days at 25 °C in the dark to determine the denitrification potential (N2O and N2) using the acetylene inhibition technique. Abundances of nirS, nirK, and nosZ (I + II) genes were analyzed before and after incubation. The denitrification potential, defined as the combined amount of N released as N2O + N2 over the experimental period, was larger for plots receiving FYM (25.9–27.2 mg N kg− 1) than pure mineral fertilization (17.1–19.2 mg N kg− 1) or no fertilization (12.6 mg N kg− 1). The CO2 and N2O production were well related and up to three-fold larger for FYM-receiving soils than under pure mineral fertilization. The N2 production differed significantly only between all manured and non-manured soils. Nitrogenous gas emissions related most closely to water-extractable organic carbon (WEOC), which again related well to free particulate OM. The larger contribution of N2 production in soils without FYM application, and thus, with less readily decomposable OM, coincided with decreasing abundances of nirS genes (NO2 − reductase) and increasing abundances of genes indicating complete denitrifying organisms (nosZ I) during anoxic conditions. Limited OM sources, thus, favored a microbial community more efficient in resource use. This study suggests that WEOC, representing readily bioavailable OM, is a straightforward indicator of the denitrification potential of soils.",
author = "Ronny Surey and Eva Lippold and Stefan Heilek and Leopold Sauheitl and Sina Henjes and Horn, {Marcus A.} and Mueller, {Carsten W.} and Ines Merbach and Klaus Kaiser and J{\"u}rgen B{\"o}ttcher and Robert Mikutta",
note = "Funding Information: This study was funded by the Deutsche Forschungsgemeinschaft within the research unit RU 2337: “Denitrification in Agricultural Soils: Integrated Control and Modeling at Various Scales (DASIM)” (Grants MI1377/8-1 , BO 1299/11-1 ). We are grateful to Christine Krenkewitz, Gudrun Nemson-von Koch, and Alexandra Boritzki for laboratory assistance, Heidrun Beschow for the C/N analysis of the POM material, Isabel Prater for NMR spectroscopy of bulk soils, and Anne Herwig for gas measurements. ",
year = "2020",
month = sep,
doi = "10.1016/j.apsoil.2020.103630",
language = "English",
volume = "153",
journal = "Applied soil ecology",
issn = "0929-1393",
publisher = "Elsevier",

}

Download

TY - JOUR

T1 - Differences in labile soil organic matter explain potential denitrification and denitrifying communities in a long-term fertilization experiment

AU - Surey, Ronny

AU - Lippold, Eva

AU - Heilek, Stefan

AU - Sauheitl, Leopold

AU - Henjes, Sina

AU - Horn, Marcus A.

AU - Mueller, Carsten W.

AU - Merbach, Ines

AU - Kaiser, Klaus

AU - Böttcher, Jürgen

AU - Mikutta, Robert

N1 - Funding Information: This study was funded by the Deutsche Forschungsgemeinschaft within the research unit RU 2337: “Denitrification in Agricultural Soils: Integrated Control and Modeling at Various Scales (DASIM)” (Grants MI1377/8-1 , BO 1299/11-1 ). We are grateful to Christine Krenkewitz, Gudrun Nemson-von Koch, and Alexandra Boritzki for laboratory assistance, Heidrun Beschow for the C/N analysis of the POM material, Isabel Prater for NMR spectroscopy of bulk soils, and Anne Herwig for gas measurements.

PY - 2020/9

Y1 - 2020/9

N2 - Content and quality of organic matter (OM) may strongly affect the denitrification potential of soils. In particular, the impact of soil OM fractions of differing bioavailability (soluble, particulate, and mineral-associated OM) on denitrification remains unresolved. We determined the potential N2O and N2 as well as CO2 production for samples of a Haplic Chernozem from six treatment plots (control, mineral N and NP, farmyard manure - FYM, and FYM + mineral N or NP) of the Static Fertilization Experiment Bad Lauchstädt (Germany) as related to OM properties and denitrifier gene abundances. Soil OM was analyzed for bulk chemical composition (13C-CPMAS NMR spectroscopy) as well as water-extractable, particulate, and mineral-associated fractions. Soils receiving FYM had more total OM and larger portions of labile fractions such as particulate and water-extractable OM. Incubations were run under anoxic conditions without nitrate limitation for seven days at 25 °C in the dark to determine the denitrification potential (N2O and N2) using the acetylene inhibition technique. Abundances of nirS, nirK, and nosZ (I + II) genes were analyzed before and after incubation. The denitrification potential, defined as the combined amount of N released as N2O + N2 over the experimental period, was larger for plots receiving FYM (25.9–27.2 mg N kg− 1) than pure mineral fertilization (17.1–19.2 mg N kg− 1) or no fertilization (12.6 mg N kg− 1). The CO2 and N2O production were well related and up to three-fold larger for FYM-receiving soils than under pure mineral fertilization. The N2 production differed significantly only between all manured and non-manured soils. Nitrogenous gas emissions related most closely to water-extractable organic carbon (WEOC), which again related well to free particulate OM. The larger contribution of N2 production in soils without FYM application, and thus, with less readily decomposable OM, coincided with decreasing abundances of nirS genes (NO2 − reductase) and increasing abundances of genes indicating complete denitrifying organisms (nosZ I) during anoxic conditions. Limited OM sources, thus, favored a microbial community more efficient in resource use. This study suggests that WEOC, representing readily bioavailable OM, is a straightforward indicator of the denitrification potential of soils.

AB - Content and quality of organic matter (OM) may strongly affect the denitrification potential of soils. In particular, the impact of soil OM fractions of differing bioavailability (soluble, particulate, and mineral-associated OM) on denitrification remains unresolved. We determined the potential N2O and N2 as well as CO2 production for samples of a Haplic Chernozem from six treatment plots (control, mineral N and NP, farmyard manure - FYM, and FYM + mineral N or NP) of the Static Fertilization Experiment Bad Lauchstädt (Germany) as related to OM properties and denitrifier gene abundances. Soil OM was analyzed for bulk chemical composition (13C-CPMAS NMR spectroscopy) as well as water-extractable, particulate, and mineral-associated fractions. Soils receiving FYM had more total OM and larger portions of labile fractions such as particulate and water-extractable OM. Incubations were run under anoxic conditions without nitrate limitation for seven days at 25 °C in the dark to determine the denitrification potential (N2O and N2) using the acetylene inhibition technique. Abundances of nirS, nirK, and nosZ (I + II) genes were analyzed before and after incubation. The denitrification potential, defined as the combined amount of N released as N2O + N2 over the experimental period, was larger for plots receiving FYM (25.9–27.2 mg N kg− 1) than pure mineral fertilization (17.1–19.2 mg N kg− 1) or no fertilization (12.6 mg N kg− 1). The CO2 and N2O production were well related and up to three-fold larger for FYM-receiving soils than under pure mineral fertilization. The N2 production differed significantly only between all manured and non-manured soils. Nitrogenous gas emissions related most closely to water-extractable organic carbon (WEOC), which again related well to free particulate OM. The larger contribution of N2 production in soils without FYM application, and thus, with less readily decomposable OM, coincided with decreasing abundances of nirS genes (NO2 − reductase) and increasing abundances of genes indicating complete denitrifying organisms (nosZ I) during anoxic conditions. Limited OM sources, thus, favored a microbial community more efficient in resource use. This study suggests that WEOC, representing readily bioavailable OM, is a straightforward indicator of the denitrification potential of soils.

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U2 - 10.1016/j.apsoil.2020.103630

DO - 10.1016/j.apsoil.2020.103630

M3 - Article

AN - SCOPUS:85084373803

VL - 153

JO - Applied soil ecology

JF - Applied soil ecology

SN - 0929-1393

M1 - 103630

ER -

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