The impact of drought length and intensity on N cycling gene abundance, transcription and the size of an N2O hot moment from a temperate grassland soil

被引:12
|
作者
Barrat, H. A. [1 ]
Clark, I. M. [2 ]
Evans, J. [3 ]
Chadwick, D. R. [4 ]
Cardenas, L. [1 ]
机构
[1] Rothamsted Res, Sustainable Agr Sci Dept, Devon, North Wyke, England
[2] Rothamsted Res, Sustainable Agr Sci Dept, Harpenden, Herts, England
[3] Rothamsted Res, Computat & Analyt Sci, Harpenden, Herts, England
[4] Bangor Univ, Sch Nat Sci, Bangor LL57 2UW, Gwynedd, Wales
来源
关键词
Soil moisture; Nitrous oxide; Dry wet cycles; Legacy; Water filled pore space; NITROUS-OXIDE PRODUCTION; NITRIC-OXIDE; CARBON-DIOXIDE; ORGANIC N; DENITRIFICATION; NITRIFICATION; HYDROXYLAMINE; RESPONSES; EMISSION; CYCLES;
D O I
10.1016/j.soilbio.2022.108606
中图分类号
S15 [土壤学];
学科分类号
0903 ; 090301 ;
摘要
This study aimed to investigate the relationship between drought length, drought intensity and the size of the N2O hot moment. It selected two treatments to deduce the main nitrogen cycling process producing N2O (increasing WFPS from 40% to 90%, and from 70% to 90%), by destructively sampling soil cores to analyse gene abundance, transcription, and changes in soil chemistry (TON, NH4+, DOC). Five other drought and rewetting treatments on packed soil cores were selected to create the drought curves described in Barrat et al. (2020): these included increases of WFPS from 40% to 90%, 50%-90%, 60%-90%, 70%-90%, and 30%-60%. For each treatment, drought lengths were imposed from 0 to 30 days. A quadratic linear regression was fitted to the cumulative emissions data. This model explained a significant proportion of the total variation in the data (R-2 = 0.72, p & LE; 0.001). All treatments had an increase in daily N2O emissions post wetting typical of a hot moment apart from the 30%-60% WFPS treatment. In terms of drought intensity, the 40%-90% WFPS was significantly larger than rest, probably due to a relatively larger change in water potential compared to the other treatments. The response to drought length followed a quadratic curve with a downward linear trend, with the largest emissions observed between 10 and 15 days of drought, and the smallest at 0 and 30 days. We suggest a 2-stage dormancy strategy to explain this, where microbes under dry conditions store osmolytes which are catabolised upon rewetting, however at prolonged negative water potentials this strategy is no longer effective, and so they enter a deeper state of dormancy where they can no longer rapidly respond to the changing water potential. Given the delayed response after rewetting, and the inverted U shaped curve in terms of drought length, it seems likely that the majority of emissions are of biological origin. The soil's chemistry data suggested that NH4+ was a key factor controlling the emission flux, but the transcriptional and genomic data were inconclusive. This study therefore suggests that future experiments should focus changes in osmolyte accumulation and catabolism as the key explanation for N2O hot moments, rather than changes in genomic and transcriptomic data or soil substrates, which do not always correlate with emissions.
引用
收藏
页数:10
相关论文
共 50 条
  • [1] The impact of drought length and intensity on N cycling gene abundance, transcription and the size of an N2O hot moment from a temperate grassland soil
    Barrat, H.A.
    Clark, I.M.
    Evans, J.
    Chadwick, D.R.
    Cardenas, L.
    Soil Biology and Biochemistry, 2022, 168
  • [2] An experimental determination of the scale length of N2O in the soil of a grassland
    Neftel, A
    Blatter, A
    Schmid, M
    Lehmann, B
    Tarakanov, SV
    JOURNAL OF GEOPHYSICAL RESEARCH-ATMOSPHERES, 2000, 105 (D10) : 12095 - 12103
  • [3] Managed grassland alters soil N dynamics and N2O emissions in temperate steppe
    Lijun Xu
    Xingliang Xu
    Xuejuan Tang
    Xiaoping Xin
    Liming Ye
    Guixia Yang
    Huajun Tang
    Shijie Lv
    Dawei Xu
    Zhao Zhang
    Journal of Environmental Sciences, 2018, 66 (04) : 20 - 30
  • [4] Managed grassland alters soil N dynamics and N2O emissions in temperate steppe
    Xu, Lijun
    Xu, Xingliang
    Tang, Xuejuan
    Xin, Xiaoping
    Ye, Liming
    Yang, Guixia
    Tang, Huajun
    Lv, Shijie
    Xu, Dawei
    Zhang, Zhao
    JOURNAL OF ENVIRONMENTAL SCIENCES, 2018, 66 : 20 - 30
  • [5] Microbial processes and the site of N2O production in a temperate grassland soil
    Müller, C
    Stevens, RJ
    Laughlin, RJ
    Jäger, HJ
    SOIL BIOLOGY & BIOCHEMISTRY, 2004, 36 (03): : 453 - 461
  • [6] Influence of organic and mineral N fertiliser on N2O fluxes from a temperate grassland
    Jones, S. K.
    Rees, R. M.
    Skiba, U. M.
    Ball, B. C.
    AGRICULTURE ECOSYSTEMS & ENVIRONMENT, 2007, 121 (1-2) : 74 - 83
  • [7] Influence of urinary N concentration on N2O and CO2 emissions and N transformation in a temperate grassland soil
    Bol, R
    Petersen, SO
    Dittert, K
    Hansen, MN
    CONTROLLING NITROGEN FLOWS AND LOSSES, 2004, : 295 - 297
  • [8] Variability of soil N cycling and N2O emission in a mixed deciduous forest with different abundance of beech
    Guckland, Anja
    Corre, Marife D.
    Flessa, Heiner
    PLANT AND SOIL, 2010, 336 (1-2) : 25 - 38
  • [9] Variability of soil N cycling and N2O emission in a mixed deciduous forest with different abundance of beech
    Anja Guckland
    Marife D. Corre
    Heiner Flessa
    Plant and Soil, 2010, 336 : 25 - 38
  • [10] Fluxes of NO and N2O from temperate forest soils: impact of forest type, N deposition and of liming on the NO and N2O emissions
    K. Butterbach-Bahl
    R. Gasche
    L. Breuer
    H. Papen
    Nutrient Cycling in Agroecosystems, 1997, 48 : 79 - 90