Microbial growth efficiencies across a soil moisture gradient assessed using 13C-acetic acid vapor and 15N-ammonia gas

One integrative measurement of microbial activity in soils is the efficiency by which microbes convert assimilated carbon (C) into biomass C. This efficiency, called the microbial growth efficiency ( Y), is a key physiological characteristic that regulates soil carbon sequestration, nutrient immobil...

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Published inSoil biology & biochemistry Vol. 41; no. 6; pp. 1262 - 1269
Main Authors Herron, Patrick M., Stark, John M., Holt, Carson, Hooker, Toby, Cardon, Zoe G.
Format Journal Article
LanguageEnglish
Published Amsterdam Elsevier Ltd 2009
Elsevier
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Abstract One integrative measurement of microbial activity in soils is the efficiency by which microbes convert assimilated carbon (C) into biomass C. This efficiency, called the microbial growth efficiency ( Y), is a key physiological characteristic that regulates soil carbon sequestration, nutrient immobilization, and greenhouse gas emissions. Changes in rainfall patterns and soil water content as the result of global climate change have the potential to influence microbial activity and lead to changes in Y and thus, nutrient cycling at the ecosystem level. Unfortunately, little information is available on how environmental variables such as soil moisture influence Y. We have developed a new method for injecting 13C-labeled carbon as acetic acid vapor into soil that will allow measurement of microbial growth efficiency (as Y C) without increasing soil moisture content. We compare Y determined with this new approach with an alternate method where injected 15N-labeled ammonia gas is used to quantify microbial N immobilization, and microbial growth efficiency is calculated based on microbial C:N and respiration rate (as Y N). We also include injections of a solution containing labeled ammonium and acetate in our experiment to compare the results of our vapor methods with more commonly employed liquid-based methods. The 13C-acetic acid vapor, which was supplied to soils with soil moisture content ranging from 0.05 to 0.21 g H 2O g −1 soil, was readily assimilated and respired by microbes. Between 0.10 and 0.21 g H 2O g −1 soil (−0.60 to −0.04 MPa), values of Y C averaged 0.46, and were significantly lower than values of Y N, with average values of 0.58. Over this range, soil moisture content had no significant effect on either Y C or Y N. However, at the lowest soil moisture content (0.05 g H 2O g −1 soil; <−6.0 MPa), Y C and Y N diverged substantially, suggesting that in very dry soils, constraints on microbial growth cause differential uptake of C and N resources.
AbstractList One integrative measurement of microbial activity in soils is the efficiency by which microbes convert assimilated carbon (C) into biomass C. This efficiency, called the microbial growth efficiency (Y), is a key physiological characteristic that regulates soil carbon sequestration, nutrient immobilization, and greenhouse gas emissions. Changes in rainfall patterns and soil water content as the result of global climate change have the potential to influence microbial activity and lead to changes in Y and thus, nutrient cycling at the ecosystem level. Unfortunately, little information is available on how environmental variables such as soil moisture influence Y. We have developed a new method for injecting 13C-labeled carbon as acetic acid vapor into soil that will allow measurement of microbial growth efficiency (as YC) without increasing soil moisture content. We compare Y determined with this new approach with an alternate method where injected 15N-labeled ammonia gas is used to quantify microbial N immobilization, and microbial growth efficiency is calculated based on microbial C:N and respiration rate (as YN). We also include injections of a solution containing labeled ammonium and acetate in our experiment to compare the results of our vapor methods with more commonly employed liquid-based methods. The 13C-acetic acid vapor, which was supplied to soils with soil moisture content ranging from 0.05 to 0.21 g H2O g-1 soil, was readily assimilated and respired by microbes. Between 0.10 and 0.21 g H2O g-1 soil (-0.60 to -0.04 MPa), values of YC averaged 0.46, and were significantly lower than values of YN, with average values of 0.58. Over this range, soil moisture content had no significant effect on either YC or YN. However, at the lowest soil moisture content (0.05 g H2O g-1 soil; <-6.0 MPa), YC and YN diverged substantially, suggesting that in very dry soils, constraints on microbial growth cause differential uptake of C and N resources.
One integrative measurement of microbial activity in soils is the efficiency by which microbes convert assimilated carbon (C) into biomass C. This efficiency, called the microbial growth efficiency ( Y), is a key physiological characteristic that regulates soil carbon sequestration, nutrient immobilization, and greenhouse gas emissions. Changes in rainfall patterns and soil water content as the result of global climate change have the potential to influence microbial activity and lead to changes in Y and thus, nutrient cycling at the ecosystem level. Unfortunately, little information is available on how environmental variables such as soil moisture influence Y. We have developed a new method for injecting 13C-labeled carbon as acetic acid vapor into soil that will allow measurement of microbial growth efficiency (as Y C) without increasing soil moisture content. We compare Y determined with this new approach with an alternate method where injected 15N-labeled ammonia gas is used to quantify microbial N immobilization, and microbial growth efficiency is calculated based on microbial C:N and respiration rate (as Y N). We also include injections of a solution containing labeled ammonium and acetate in our experiment to compare the results of our vapor methods with more commonly employed liquid-based methods. The 13C-acetic acid vapor, which was supplied to soils with soil moisture content ranging from 0.05 to 0.21 g H 2O g −1 soil, was readily assimilated and respired by microbes. Between 0.10 and 0.21 g H 2O g −1 soil (−0.60 to −0.04 MPa), values of Y C averaged 0.46, and were significantly lower than values of Y N, with average values of 0.58. Over this range, soil moisture content had no significant effect on either Y C or Y N. However, at the lowest soil moisture content (0.05 g H 2O g −1 soil; <−6.0 MPa), Y C and Y N diverged substantially, suggesting that in very dry soils, constraints on microbial growth cause differential uptake of C and N resources.
Author Hooker, Toby
Herron, Patrick M.
Holt, Carson
Stark, John M.
Cardon, Zoe G.
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Issue 6
Keywords Substrate-use efficiency
Isotope dilution
N immobilization
Growth efficiency
N mineralization
Acetic acid
Vapor
Gradient
Microorganism growth
Isotope labelling
Soil moisture
Immobilization
Substrate
Ammonia
Nitrogen cycle
C-13
Mineralization
Nitrogen-15
Soil science
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Snippet One integrative measurement of microbial activity in soils is the efficiency by which microbes convert assimilated carbon (C) into biomass C. This efficiency,...
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SubjectTerms Acetic acid
Agronomy. Soil science and plant productions
ammonia
Biochemistry and biology
Biological and medical sciences
carbon
carbon sequestration
Chemical, physicochemical, biochemical and biological properties
Fundamental and applied biological sciences. Psychology
gas emissions
greenhouse gases
Growth efficiency
immobilization in soil
Isotope dilution
microbial growth
N immobilization
N mineralization
nitrogen
nutrients
Physics, chemistry, biochemistry and biology of agricultural and forest soils
soil analysis
soil ecology
soil microorganisms
Soil science
soil water content
stable isotopes
Substrate-use efficiency
vapors
Title Microbial growth efficiencies across a soil moisture gradient assessed using 13C-acetic acid vapor and 15N-ammonia gas
URI https://dx.doi.org/10.1016/j.soilbio.2009.03.010
Volume 41
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