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Effects of a simulated drying-rewetting cycle on microbial activity in soils degraded by post-fire erosion Elena Fernandez-Boy* 1 , Mª Belén Herrador 1 , Violeta Ordoñez 1 , Laura Morales 1 , Oscar González-Pelayo 2 , Jan Jacob Keizer 2 , María T. Domínguez 1 1 Departamento de Cristalografía, Mineralogía y Química Agrícola, Universidad de Sevilla, Profesor García González nº 1, 41012, Sevilla, Spain. 2 Centre for Environmental and Marine Studies (CESAM) and Department of Environment & Planning Universidade de Aveiro, Campus Universitário de Santiago 3810-193, Aveiro, Portugal. Departamento de Cristalografía, Mineralogía y Química Agrícola © Authors. All rights reserved Contact info: Elena Fernández ([email protected]) María T. Domínguez ([email protected])

PRESENTACIÃ N EGU 2020 Maite · 3krwr 5$)$(/ 0$5&+$17( 5(87(56 (o 3dtv ,qwhuqdflrqdo mxqh wk 3rvw iluh vrlo hurvlrq lv dq lpsruwdqw lvvxh lq 0hglwhuudqhdq frxqwulhv

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Page 1: PRESENTACIÃ N EGU 2020 Maite · 3krwr 5$)$(/ 0$5&+$17( 5(87(56 (o 3dtv ,qwhuqdflrqdo mxqh wk 3rvw iluh vrlo hurvlrq lv dq lpsruwdqw lvvxh lq 0hglwhuudqhdq frxqwulhv

Effects of a simulated drying-rewetting cycle on

microbial activity in soils degraded by post-fire erosion

• Elena Fernandez-Boy*1, Mª Belén Herrador1, Violeta Ordoñez1, Laura

Morales1, Oscar González-Pelayo2, Jan Jacob Keizer2, María T. Domínguez1

• 1Departamento de Cristalografía, Mineralogía y Química Agrícola, Universidad de Sevilla, Profesor

García González nº 1, 41012, Sevilla, Spain.

2Centre for Environmental and Marine Studies (CESAM) and Department of Environment & Planning

Universidade de Aveiro, Campus Universitário de Santiago 3810-193, Aveiro, Portugal.

Departamento de Cristalografía, Mineralogía y Química Agrícola

© Authors. All rights reservedContact info: Elena Fernández ([email protected])María T. Domínguez ([email protected])

Page 2: PRESENTACIÃ N EGU 2020 Maite · 3krwr 5$)$(/ 0$5&+$17( 5(87(56 (o 3dtv ,qwhuqdflrqdo mxqh wk 3rvw iluh vrlo hurvlrq lv dq lpsruwdqw lvvxh lq 0hglwhuudqhdq frxqwulhv

Photo: RAFAEL MARCHANTE (REUTERS). El País Internacional, june 18th, 2017.

• Post-fire soil erosion is an important issue in Mediterranean countries because of its potential large impact on soil carbon stocks and functioning.

• Addition of mulching to burnt soils has been proved as an effective measure to reduce post-fire erosion.

• Could this measure also increase the stability of microbial activity to drought events? These events are expected to be more frequent in the Mediterranean region with the current climate change projections.

• Sampling involved the organic surface horizon as well as the upper 15 cm of the

Ah horizon

• A drying-rewetting experiment was conducted under controlled conditions

OBJECTIVE: analysing the influence of some post-firemitigation measurements on the response of soil microbialactivity to drying-rewetting events.

Comparison with soils from an adjacentunburnt pine stand

© Authors. All rights reserved

METHODS: Two post-fire mitigation field experiments

conducted in Portugal

(burnt in large fires in 2017)

Pine Tree Plantation

Spontaneousmulching (SpM)

Addition of pinemulching (AM)

Control (no mulching)

Photo: Jan Jacob Keizer

Strawberry Tree Stand

Control (no mulching) Addition of strawmulching (StM)

Photo: Jan Jacob Keizer

Page 3: PRESENTACIÃ N EGU 2020 Maite · 3krwr 5$)$(/ 0$5&+$17( 5(87(56 (o 3dtv ,qwhuqdflrqdo mxqh wk 3rvw iluh vrlo hurvlrq lv dq lpsruwdqw lvvxh lq 0hglwhuudqhdq frxqwulhv

Samples were preincubated

28 days at 25°C and at 70% of field

capacity (FC)

Two sets

Half

30 days drought event

Soil moisture contents reduce to

5-10% FC

Afterwards, they were rehydrated

until initial moisture content (14 days)

Half Control Maintained to 70% FC

Soildehydrogenase

activity

Soil β-glucosidase

activity

SoilAminopeptidase

activity

SoilAminopeptidase

activity

Soil Phosphataseactivity

N-mineralizationrates

DNA present in soil samples

As a index of microbial biomass

Soil respiration rates (IRGA)

Soil analysis to evaluateinitial differences in microbial

activity among treatments, and to monitore the resistance of

this activity to the drying event

© Authors. All rights reserved

Photo: María T. Domínguez Photo: María T. Domínguez

Page 4: PRESENTACIÃ N EGU 2020 Maite · 3krwr 5$)$(/ 0$5&+$17( 5(87(56 (o 3dtv ,qwhuqdflrqdo mxqh wk 3rvw iluh vrlo hurvlrq lv dq lpsruwdqw lvvxh lq 0hglwhuudqhdq frxqwulhv

MAIN RESULTS

Most of microbial variables discriminated wellbetween burnt and unburnt soils (reducedactivity in the burnt soils)

Re

spir

atio

n ra

te r

educ

tion

(fro

m m

ois

ture

con

trol

tre

atm

ent

)

-1.0

-0.8

-0.6

-0.4

-0.2

0.0

Organic horizonAh horizon

AM SpM NoMulch

Unburnt

Re

spira

tion

rate

re

duc

tion

(fro

m m

ois

ture

co

ntro

l tre

atm

ent

)

-1.0

-0.8

-0.6

-0.4

-0.2

0.0

Organic horizonAh horizon

StM NoMulch

Pine tree plantation Strawberry tree stand

CONCLUSIONS

Forest fire still affected soil microbialactivity almost two years after the fireevent

Post-fire management (addition of mulching) did not confer more resistanceof soil to drying events (but haveadditional benefits, mainly control of soilerosion…)

When comparing across soils, the highestresistance to drought was found in thesoils with higher organic matter content

Similar response to the drying-rewetting eventbetween mulched and unmulched soils

Greater resistance to drought (lower reduction in respiration rates at the end of the drying period) in the organic soils from the Pine tree stand (greatest levels of organic matter)

© Authors. All rights reserved

DEGRAMED Project (CGL2017-85891-R)

Acknowledgments

AM: Added mulching; SpM: Spontaneous mulching; StM: straw mulching