Different temperature sensitivity and kinetics of soil enzymes indicate seasonal shifts in C, N and P nutrient stoichiometry in acid forest soil

2013 ◽  
Vol 117 (2-3) ◽  
pp. 525-537 ◽  
Author(s):  
Jiří Bárta ◽  
Petra Šlajsová ◽  
Karolina Tahovská ◽  
Tomáš Picek ◽  
Hana Šantrůčková
1985 ◽  
Vol 49 (3) ◽  
pp. 746-750 ◽  
Author(s):  
G. T. Weaver ◽  
P. K. Khanna ◽  
F. Beese
Keyword(s):  

1976 ◽  
Vol 64 (1) ◽  
pp. 119-130
Author(s):  
M. V. Thomas

About 90% of the butanol uptake by the cockroach abdominal nerve cord washed out with half-times of a few seconds, in good agreement with an electrophysiological estimate, and the temperature sensitivity suggested an activation energy of 3 Kcal mole-1. The remaining activity washed out far more slowly, with a similar time course to that observed in a previous investigation which had not detected the fast fraction. Its size was similar to the non-volatile uptake, and was considerably affected by the butanol concentration and incubation period. It apparently consisted of butanol metabolites, which could be detected by chromatography.


Author(s):  
Ángela Machuca ◽  
Carolin Córdova ◽  
Neal Brian Stolpe ◽  
Juan Alberto Barrera ◽  
Daniel Chávez ◽  
...  

BIOPHYSICS ◽  
2018 ◽  
Vol 63 (5) ◽  
pp. 769-778
Author(s):  
E. V. Menko ◽  
E. N. Tikhonova ◽  
R. V. Ulanova ◽  
M. V. Sukhacheva ◽  
T. V. Kuznetsova ◽  
...  

2020 ◽  
Author(s):  
Haoming Yu ◽  
Yunting Fang ◽  
Ronghua Kang

<p>N<sub>2</sub>O and N<sub>2</sub> Emissions from soil in terrestrial ecosystems is a crucial component of the global nitrogen (N) cycle. The response of these two gases emissions from forest soil to temperature change and its underlying mechanisms are essential for predicting N cycle to global warming. Despite the warming-induced effects on soil N cycle is considered to be positive in general, our understanding of temperature sensitivity (Q<sub>10</sub>) of N<sub>2</sub>O and N<sub>2</sub> emissions is rather limited. We quantified the Q<sub>10</sub> of N<sub>2</sub>O and N<sub>2</sub> emissions in forest soils and explored their major driving factors by conducting an incubation experiment using <sup>15</sup>N tracer (Na<sup>15</sup>NO<sub>3</sub>) with soil samples from nineteen forest sites from temperate to tropical zones. The environmental conditions largely varied: mean annual temperature (MAT) ranging from -5.4 to 21.5<sup>o</sup>C and mean annual precipitation (MAP) ranging from 300 to 2449 mm. The soil pH varied between 3.62 to 6.38. We incubated soil samples under an anaerobic condition with temperature from 5 to 35<sup>o</sup>C with an interval of 5<sup>o</sup>C for 12 or 24 hours, respectively. Soil temperature strongly affected the production of N<sub>2</sub>O and N<sub>2</sub>. N<sub>2</sub>O and N<sub>2</sub> production rates showed a positive exponential relation with incubate time and temperature for all forest soils. Our results showed that the Q<sub>10</sub> values ranged from 1.31 to 2.98 for N<sub>2</sub>O emission and 1.69 to 3.83 for N<sub>2</sub> emission, indicating a generally positive feedback of N<sub>2</sub>O and N<sub>2</sub> production to warming. Higher Q<sub>10</sub> values for N<sub>2</sub> than N<sub>2</sub>O implies that N<sub>2</sub> emission is more sensitive to temperature increase. The N<sub>2</sub>O/(N<sub>2</sub>O+N<sub>2</sub>) decreased with increasing temperature in fifteen of nineteen forest soils, suggesting that warming accelerates N<sub>2</sub> emission. Strong spatial variation in Q<sub>10</sub> were also observed, with tropical forest soils exhibiting high Q<sub>10</sub> values and relatively low Q<sub>10</sub> in temperate forest soils. This variation is attributed to the inherent differences in N biogeochemical cycling behavior between the microbial communities among sites. Despite soil temperature primarily controls the N<sub>2</sub>O and N<sub>2</sub> emissions, we  explored the effects of other factors such as pH, C/N, DOC and related functional genes. In addition, we partitioned N<sub>2</sub>O and N<sub>2</sub> emissions to different microbial processes (e.g., denitrification, co-denitrification and anammox). The results indicated that denitrification was the main pathway of N<sub>2</sub>O and N<sub>2</sub> production under anaerobic environment and the contribution increased as temperature rise.</p><p>Key words: Temperature sensitivity, N<sub>2</sub>O, N<sub>2</sub>, Forest soil, Nitrogen cycle, Global warming, Denitrification</p>


2020 ◽  
Author(s):  
Carolina Urbina Malo ◽  
Ye Tian ◽  
Chupei Shi ◽  
Shasha Zhang ◽  
Marilena Heitger ◽  
...  

<p>Despite the intensified efforts to understand the impacts of climate change on forest soil C dynamics, few studies have addressed the long term effects of warming on microbially mediated soil C and nutrient processes. In the few long-term soil warming experiments the initial stimulation of soil C cycling diminished with time, due to thermal acclimation of the microbial community or due to depletion of labile soil C as the major substrate for heterotrophic soil microbes. Thermal acclimation can arise as a consequence of prolonged warming and is defined as the direct organism response to elevated temperature across annual to decadal time-scales which manifest as a physiological change of the soil microbial community. This mechanism is clearly different from apparent thermal acclimation, where the attenuated response of soil microbial processes to warming is due to the exhaustion of the labile soil C pool.</p><p>The Achenkirch experiment, situated in the Northern Limestone Alps, Austria (47°34’ 50’’ N; 11°38’ 21’’ E; 910 m a.s.l.) is a long term (>15 yrs) soil warming experiment that has provided key insights into the effects of global warming on the forest soil C cycle. At the Achenkirch site, we have observed a sustained positive response of heterotrophic soil respiration and of soil CO<sub>2</sub> efflux to warming after nine years (2013), making it an appropriate setting for testing hypotheses about continued or decreasing warming effects at decadal scales. We collected soil from six warmed and six control plots in October 2019, from 0-10 cm and 10-20 cm depth, and incubated them at three different temperatures: ambient, +4, and +10 °C. We measured potential soil enzyme activities with fluorimetric assays, gross rates of protein depolymerization, N mineralization, and nitrification with <sup>15</sup>N isotope pool dilution approaches, and microbial growth, respiration, and C use efficiency (CUE) based on the <sup>18</sup>O incorporation in DNA and gas analysis.  Our preliminary results show that potential enzyme activities of aminopeptidase, N-acetylglucosaminidase, b-glucosidase, and acid phosphatase were stimulated by decadal soil warming by 1.7- to 3.5-fold, measured at the same i.e. ambient temperature. In contrast, the temperature sensitivity (Q10) remained unaltered between warmed and control soils for all enzyme activities (Q10=1.63-2.28), except for aminopeptidase where we observed a decrease in Q10 by 25% in warmed topsoils (0-10 cm). Aminopeptidase also had the highest temperature-sensitivity (Q10=2.39), causing a decrease of the enzymatic C: N acquisition ratio with warming. These results indicate an increasing investment in microbial N acquisition with warming. We will follow these trends based on results on gross rates of soil C and N processes, allowing to delineate decadal soil warming effects on soil microbial biogeochemistry and to understand their effect on the cross-talk between organic C and N cycling in calcareous forest soils.</p>


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