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Short-term temperature impacts on soil respiration.

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Short

Short--term

term temperature

temperature impacts on

impacts on soil

soil respiration

respiration

Buysse P.1, Goffin S.1, Carnol M.2, Malchair S.2, Debacq A.1, Aubinet M.1 1

Unit of Biosystem Physics, Gembloux Agricultural University (FUSAGx), Gembloux, Belgium

2University of Liège (ULg), Plant and Microbial Ecology laboratory, Liège, Belgium

1. Introduction:

• There is still a lack of a good mechanistic understanding of soil heterotrophic respiration.

• Temperature is the most important driving factor and its impacts may be different according to the time scale.

• Despite their considerable importance, crop soils have been less investigated so far.

2. Objectives:

• To bring new elements to get to a better understanding of short-term temperature impacts on respiration of crop soils.

3. Material and Methods:

 Experimental site:

 Soil samples were taken at the Carbo-Europe site of Lonzée, Belgium.

 In this 12ha-field, 4 areas of 9m² each were weeded in March 2009 to provide bare areas for soil sampling.

 Soil characteristics:

Parameter Value

Soil type (FAO) Luvisol

Soil texture: Silt Sand Clay 70% 5% 25%

Soil organic carbon content [kg/m²] 6.2

EXPERIMENTAL SET-UP:

 3 incubators keeping the temperature constant between 5 and 35°C.  A water-bath to warm up or cool down the jars inside the incubators.  Sample ventilation with water-saturated air in each incubator.

 Checking of the temperature evolution in the samples with thermocouples.

Fig.3: Inner part of an incubator : detail of the ventilation system.

C:N ratio 9.40

Bulk density (0-30cm) [kg/m³] 1500

 Experimental protocol and measurements:  Pre-incubation period: 4 days ½.

 Cycle 1: Temperature modified sequentially by 10°C-steps between 5 and 35°C, starting from the incubation temperature (see the example in Fig. 4). This temperature cycle lasted about 22h.

 Soil sampling and subsample preparation:

Ø 5mm

Ø 2mm

HOMOGENIZATION

5°C 15°C 25°C

2 auger samples (6cm Ø , 14cm height) were taken from each of the 4 bare areas delimited in the field.

The samples were sieved at 5 and 2mm, and homogenized.

9 new samples (100 g fresh soil) were prepared from the whole quantity of soil, put into 210 mL jars and slightly compacted. 3 jars were placed into each incubator.

Incubator temperatures were set at 5, 15 and 25°C.

Fig.1: View of the 3 incubators. Fig.2: Zoom on 1 incubator.

ventilation system.

4. Results:

Fig. 5: Soil respiration flux vs. Temperature relationships in each incubator for cycle 1 (left) and cycle 2 (right). Error bars take account of the slope uncertainty and of the jar to jar variability in each incubator.

Fig.6: Measured soil respiration fluxes at 35°C (left) and at the beginning of both cycles (right) in each incubator. Cycle 1 is in blue and cycle 2 is in

 Cycle 2: same as cycle 1, repeated two days later.  Respiration flux measurements:

oAt each temperature step with a dynamic closed chamber system (infrared gas analyzer Gascard II, Edinburgh Instruments Ltd, UK). Three measurements sequentially on each jar.

oBetween each measurement, ventilation of jars with outside air to prevent CO2 from

accumulating inside the jars.

Fig. 4: The temperature cycle of incubator B.

5. Main observations

6. Conclusions

Fig.6: Measured soil respiration fluxes at 35°C (left) and at the beginning of both cycles (right) in each incubator. Cycle 1 is in blue and cycle 2 is in red. Error bars take account of the slope uncertainty and of the jar to jar variability in each incubator.

Short term impact of temperature was very clear (Fig.5 and Fig. 6 (left)): in the three incubators and during both cycles, soil respiration increased with temperature.

• Unexpectedly, the pre-incubation temperature had only a small impact on initial respiration fluxes to (Fig. 6 (right)).

• On the opposite the pre-incubation temperature impacted on the respiration temperature sensitivity. The sensitivity was larger in the coolest incubator (Fig.5).

• Large hysteresis effects were observed during both cycles in each incubator, higher fluxes being systematically measured during the heating phase (Fig.5).

In all incubators, the fluxes decreased with time. (Fig.5 and Fig.6).

Negative fluxes were measured during the cooling phase in all incubators (Fig.5).

• These results suggest that:

• The impact of temperature is not the same at a daily and a hourly scale.

• Soil respiration temperature sensitivity increases with pre-incubation temperature. • Soil respiration temperature sensitivity is larger during cooling phases compared to

heating phases.

• Microbial biomass and soil labile carbon content analyses are ongoing. They will allow a deeper interpretation of the preceding results.

Acknowledgements: This research is funded by the FRS-FNRS, Belgium

CONTACT PERSON: Pauline Buysse – FRS-FNRS Research fellow Unit of Biosystem Physics – Gembloux Agricultural University – Belgium

buysse.p@fsagx.ac.be R e sp ir a ti o n f lu x Temperature [°C]

Figure

Fig. 5: Soil respiration flux vs. Temperature relationships in each incubator for cycle 1 (left) and cycle 2 (right)

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