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Changes in soil microbial biomass and microbial activities in response to 7 years simulated pollutant nitrogen deposition on a heathland and two grasslands

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Changes in soil microbial biomass and microbial activities in response to 7 years simulated pollutant nitrogen deposition on a heathland and two grasslands. / Johnson, D; Leake, JR; Lee, John A. et al.
In: Environ. Pollut., Vol. 103, No. 2-3, 30.11.1998, p. 239-250.

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Johnson D, Leake JR, Lee JA, Campbell CD. Changes in soil microbial biomass and microbial activities in response to 7 years simulated pollutant nitrogen deposition on a heathland and two grasslands. Environ. Pollut. 1998 Nov 30;103(2-3):239-250. doi: 10.1016/S0269-7491(98)00115-8

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@article{0be39d77d297443b8f51f4cf0684658e,
title = "Changes in soil microbial biomass and microbial activities in response to 7 years simulated pollutant nitrogen deposition on a heathland and two grasslands",
abstract = "The effects of 7 years simulated pollutant nitrogen (N) deposition on soil microbial biomass C (Cmic), soil phosphomonoesterase (PME) activity and utilisation of carbon (C) and organic N and phosphorus (P) sources by soil bacteria are reported for a heathland, an acidic grassland and a calcareous grassland. N additions increased Cmic in the heathland, decreased it in the acid grassland, and had no effect in the calcareous grassland. These effects mirrored the changes in plant cover, indicating close-coupling of plant and microbial responses to chronic N additions. In the heathland, PME activity generally rose with each increment of N addition while in the acid grassland, PME activity significantly increased only in the 14 g N m−2 y−1 (ammonium nitrate) treatment. In the calcareous grassland, PME activity was highly correlated with KCl extractable N (R2 = 0.71), indicating increased PME activity in response to increasing N saturation. At all three sites, PME activity per mg Cmic was greater in plots receiving N inputs, reflecting greater P limitation. In the heathland, N treatments caused a 3-fold increase in the utilisation rate of C and organic N substrates in BIOLOG plates, whereas utilisation of organic P substrates rose 10-fold in response to 8 g N m−2 y−1 and 18-fold in response to 12 g N m−2 y−1. In the acid grassland, utilisation of the C sources decreased in response to the N treatments. The results demonstrate that long-term chronic inputs of pollutant N can significantly increase microbial biomass and activity in N-limited heathland ecosystems, but may reduce microbial biomass and microbial activity in P-limited grasslands.",
keywords = "nitrogen, nitrogen saturation, phosphase activity, soil microbial biomass, BIOLOG plates",
author = "D Johnson and JR Leake and Lee, {John A.} and Campbell, {Colin D.}",
year = "1998",
month = nov,
day = "30",
doi = "10.1016/S0269-7491(98)00115-8",
language = "English",
volume = "103",
pages = "239--250",
journal = "Environ. Pollut.",
issn = "0269-7491",
publisher = "Elsevier Ltd",
number = "2-3",

}

RIS

TY - JOUR

T1 - Changes in soil microbial biomass and microbial activities in response to 7 years simulated pollutant nitrogen deposition on a heathland and two grasslands

AU - Johnson, D

AU - Leake, JR

AU - Lee, John A.

AU - Campbell, Colin D.

PY - 1998/11/30

Y1 - 1998/11/30

N2 - The effects of 7 years simulated pollutant nitrogen (N) deposition on soil microbial biomass C (Cmic), soil phosphomonoesterase (PME) activity and utilisation of carbon (C) and organic N and phosphorus (P) sources by soil bacteria are reported for a heathland, an acidic grassland and a calcareous grassland. N additions increased Cmic in the heathland, decreased it in the acid grassland, and had no effect in the calcareous grassland. These effects mirrored the changes in plant cover, indicating close-coupling of plant and microbial responses to chronic N additions. In the heathland, PME activity generally rose with each increment of N addition while in the acid grassland, PME activity significantly increased only in the 14 g N m−2 y−1 (ammonium nitrate) treatment. In the calcareous grassland, PME activity was highly correlated with KCl extractable N (R2 = 0.71), indicating increased PME activity in response to increasing N saturation. At all three sites, PME activity per mg Cmic was greater in plots receiving N inputs, reflecting greater P limitation. In the heathland, N treatments caused a 3-fold increase in the utilisation rate of C and organic N substrates in BIOLOG plates, whereas utilisation of organic P substrates rose 10-fold in response to 8 g N m−2 y−1 and 18-fold in response to 12 g N m−2 y−1. In the acid grassland, utilisation of the C sources decreased in response to the N treatments. The results demonstrate that long-term chronic inputs of pollutant N can significantly increase microbial biomass and activity in N-limited heathland ecosystems, but may reduce microbial biomass and microbial activity in P-limited grasslands.

AB - The effects of 7 years simulated pollutant nitrogen (N) deposition on soil microbial biomass C (Cmic), soil phosphomonoesterase (PME) activity and utilisation of carbon (C) and organic N and phosphorus (P) sources by soil bacteria are reported for a heathland, an acidic grassland and a calcareous grassland. N additions increased Cmic in the heathland, decreased it in the acid grassland, and had no effect in the calcareous grassland. These effects mirrored the changes in plant cover, indicating close-coupling of plant and microbial responses to chronic N additions. In the heathland, PME activity generally rose with each increment of N addition while in the acid grassland, PME activity significantly increased only in the 14 g N m−2 y−1 (ammonium nitrate) treatment. In the calcareous grassland, PME activity was highly correlated with KCl extractable N (R2 = 0.71), indicating increased PME activity in response to increasing N saturation. At all three sites, PME activity per mg Cmic was greater in plots receiving N inputs, reflecting greater P limitation. In the heathland, N treatments caused a 3-fold increase in the utilisation rate of C and organic N substrates in BIOLOG plates, whereas utilisation of organic P substrates rose 10-fold in response to 8 g N m−2 y−1 and 18-fold in response to 12 g N m−2 y−1. In the acid grassland, utilisation of the C sources decreased in response to the N treatments. The results demonstrate that long-term chronic inputs of pollutant N can significantly increase microbial biomass and activity in N-limited heathland ecosystems, but may reduce microbial biomass and microbial activity in P-limited grasslands.

KW - nitrogen

KW - nitrogen saturation

KW - phosphase activity

KW - soil microbial biomass

KW - BIOLOG plates

U2 - 10.1016/S0269-7491(98)00115-8

DO - 10.1016/S0269-7491(98)00115-8

M3 - Journal article

VL - 103

SP - 239

EP - 250

JO - Environ. Pollut.

JF - Environ. Pollut.

SN - 0269-7491

IS - 2-3

ER -