Home > Research > Publications & Outputs > Nitrogen losses from two grassland soils with d...
View graph of relations

Nitrogen losses from two grassland soils with different fungal biomass.

Research output: Contribution to Journal/MagazineJournal articlepeer-review

Published

Standard

Nitrogen losses from two grassland soils with different fungal biomass. / de Vries, Franciska T.; van Groenigen, Jan Willem; Hoffland, Ellis et al.
In: Soil Biology and Biochemistry, Vol. 43, No. 5, 05.2011, p. 997-1005.

Research output: Contribution to Journal/MagazineJournal articlepeer-review

Harvard

de Vries, FT, van Groenigen, JW, Hoffland, E & Bloem, J 2011, 'Nitrogen losses from two grassland soils with different fungal biomass.', Soil Biology and Biochemistry, vol. 43, no. 5, pp. 997-1005. https://doi.org/10.1016/j.soilbio.2011.01.016

APA

de Vries, F. T., van Groenigen, J. W., Hoffland, E., & Bloem, J. (2011). Nitrogen losses from two grassland soils with different fungal biomass. Soil Biology and Biochemistry, 43(5), 997-1005. https://doi.org/10.1016/j.soilbio.2011.01.016

Vancouver

de Vries FT, van Groenigen JW, Hoffland E, Bloem J. Nitrogen losses from two grassland soils with different fungal biomass. Soil Biology and Biochemistry. 2011 May;43(5):997-1005. doi: 10.1016/j.soilbio.2011.01.016

Author

de Vries, Franciska T. ; van Groenigen, Jan Willem ; Hoffland, Ellis et al. / Nitrogen losses from two grassland soils with different fungal biomass. In: Soil Biology and Biochemistry. 2011 ; Vol. 43, No. 5. pp. 997-1005.

Bibtex

@article{6f9819856e8e48dbbcd3bbcee55762e7,
title = "Nitrogen losses from two grassland soils with different fungal biomass.",
abstract = "Nitrogen losses from agricultural grasslands cause eutrophication of ground- and surface water and contribute to global warming and atmospheric pollution. It is widely assumed that soils with a higher fungal biomass have lower N losses, but this relationship has never been experimentally confirmed. With the increased attention for soil-based ecosystem services and sustainable management of soils, such a relationship would be relevant for agricultural management. Here we present a first attempt to test this relationship experimentally . We used intact soil columns from two plots from a field experiment that had consistent differences in fungal biomass (68 ± 8 vs. 111 ± 9 μg C g-1) as a result of different fertilizer history (80 vs. 40 kg N ha-1 y-1 as farm yard manure), while other soil properties were very similar. In the greenhouse, the columns received either mineral fertilizer N or no N (control). We measured N leaching, N2O emissions and denitrification from the columns during 4 weeks, after which we analyzed fungal and bacterial biomass and soil N pools. We found that N2O emission and denitrification were lower in the high fungal biomass soil, irrespective of the addition of fertilizer N. After fertilizer addition, N leaching in low fungal biomass soil showed a 3-fold increase compared to the control (11.9 ± 1.0 and 3.9 ± 1.0 kg N ha-1, respectively), but did not increase in high fungal biomass soil (6.4 ± 0.9 after N addition vs. 4.5 ± 0.8 kg N ha-1 in the control). Thus, in the high fungal biomass soil more N was immobilized. An additional experiment with 15N–labelled mineral fertilizer, showed a 2-fold higher immobilization of 15N into microbial biomass in the high fungal biomass soil. However, only 3% of total 15N was found in the microbial biomass 2 weeks after the mineral fertilization. Most of the recovered 15N was in the plants (approximately 25%) or in the soil organic matter (approximately 15%). Our main experiment confirmed the assumption of lower N losses in a soil with higher fungal biomass. The additional 15N experiment showed that higher fungal biomass is probably not the direct cause of higher N immobilization, but rather the result of low nitrogen availability. Both experiments confirmed that higher fungal biomass can be considered as an indicator of higher nutrient retention in soils.",
author = "{de Vries}, {Franciska T.} and {van Groenigen}, {Jan Willem} and Ellis Hoffland and Jaap Bloem",
year = "2011",
month = may,
doi = "10.1016/j.soilbio.2011.01.016",
language = "English",
volume = "43",
pages = "997--1005",
journal = "Soil Biology and Biochemistry",
issn = "0038-0717",
publisher = "Elsevier Ltd",
number = "5",

}

RIS

TY - JOUR

T1 - Nitrogen losses from two grassland soils with different fungal biomass.

AU - de Vries, Franciska T.

AU - van Groenigen, Jan Willem

AU - Hoffland, Ellis

AU - Bloem, Jaap

PY - 2011/5

Y1 - 2011/5

N2 - Nitrogen losses from agricultural grasslands cause eutrophication of ground- and surface water and contribute to global warming and atmospheric pollution. It is widely assumed that soils with a higher fungal biomass have lower N losses, but this relationship has never been experimentally confirmed. With the increased attention for soil-based ecosystem services and sustainable management of soils, such a relationship would be relevant for agricultural management. Here we present a first attempt to test this relationship experimentally . We used intact soil columns from two plots from a field experiment that had consistent differences in fungal biomass (68 ± 8 vs. 111 ± 9 μg C g-1) as a result of different fertilizer history (80 vs. 40 kg N ha-1 y-1 as farm yard manure), while other soil properties were very similar. In the greenhouse, the columns received either mineral fertilizer N or no N (control). We measured N leaching, N2O emissions and denitrification from the columns during 4 weeks, after which we analyzed fungal and bacterial biomass and soil N pools. We found that N2O emission and denitrification were lower in the high fungal biomass soil, irrespective of the addition of fertilizer N. After fertilizer addition, N leaching in low fungal biomass soil showed a 3-fold increase compared to the control (11.9 ± 1.0 and 3.9 ± 1.0 kg N ha-1, respectively), but did not increase in high fungal biomass soil (6.4 ± 0.9 after N addition vs. 4.5 ± 0.8 kg N ha-1 in the control). Thus, in the high fungal biomass soil more N was immobilized. An additional experiment with 15N–labelled mineral fertilizer, showed a 2-fold higher immobilization of 15N into microbial biomass in the high fungal biomass soil. However, only 3% of total 15N was found in the microbial biomass 2 weeks after the mineral fertilization. Most of the recovered 15N was in the plants (approximately 25%) or in the soil organic matter (approximately 15%). Our main experiment confirmed the assumption of lower N losses in a soil with higher fungal biomass. The additional 15N experiment showed that higher fungal biomass is probably not the direct cause of higher N immobilization, but rather the result of low nitrogen availability. Both experiments confirmed that higher fungal biomass can be considered as an indicator of higher nutrient retention in soils.

AB - Nitrogen losses from agricultural grasslands cause eutrophication of ground- and surface water and contribute to global warming and atmospheric pollution. It is widely assumed that soils with a higher fungal biomass have lower N losses, but this relationship has never been experimentally confirmed. With the increased attention for soil-based ecosystem services and sustainable management of soils, such a relationship would be relevant for agricultural management. Here we present a first attempt to test this relationship experimentally . We used intact soil columns from two plots from a field experiment that had consistent differences in fungal biomass (68 ± 8 vs. 111 ± 9 μg C g-1) as a result of different fertilizer history (80 vs. 40 kg N ha-1 y-1 as farm yard manure), while other soil properties were very similar. In the greenhouse, the columns received either mineral fertilizer N or no N (control). We measured N leaching, N2O emissions and denitrification from the columns during 4 weeks, after which we analyzed fungal and bacterial biomass and soil N pools. We found that N2O emission and denitrification were lower in the high fungal biomass soil, irrespective of the addition of fertilizer N. After fertilizer addition, N leaching in low fungal biomass soil showed a 3-fold increase compared to the control (11.9 ± 1.0 and 3.9 ± 1.0 kg N ha-1, respectively), but did not increase in high fungal biomass soil (6.4 ± 0.9 after N addition vs. 4.5 ± 0.8 kg N ha-1 in the control). Thus, in the high fungal biomass soil more N was immobilized. An additional experiment with 15N–labelled mineral fertilizer, showed a 2-fold higher immobilization of 15N into microbial biomass in the high fungal biomass soil. However, only 3% of total 15N was found in the microbial biomass 2 weeks after the mineral fertilization. Most of the recovered 15N was in the plants (approximately 25%) or in the soil organic matter (approximately 15%). Our main experiment confirmed the assumption of lower N losses in a soil with higher fungal biomass. The additional 15N experiment showed that higher fungal biomass is probably not the direct cause of higher N immobilization, but rather the result of low nitrogen availability. Both experiments confirmed that higher fungal biomass can be considered as an indicator of higher nutrient retention in soils.

U2 - 10.1016/j.soilbio.2011.01.016

DO - 10.1016/j.soilbio.2011.01.016

M3 - Journal article

VL - 43

SP - 997

EP - 1005

JO - Soil Biology and Biochemistry

JF - Soil Biology and Biochemistry

SN - 0038-0717

IS - 5

ER -