changes in the lignic portion of the organic layer

1
4. Results 2. Goal Gain knowledge on the short- (1 yr) and mid-term (17 yrs) effect of the harvest of lignic material on carbon (C) pools in boreal forest sites of eastern Canada. Changes in the Lignic Portion of the Organic Layer Following Harvesting in the Boreal Forest Jérôme Laganière* 1 , David Paré 1 , Évelyne Thiffault 2 *[email protected] 1 Canadian Forest Service, Laurentian Forestry Centre, Québec, QC, Canada; 2 Département des sciences du bois et de la forêt, Université Laval, QC, Canada. 1. Context Forest harvesting periodically removes lignic materials that would eventually, if not harvested, contribute to the soil organic matter (SOM) pool. The long term effects of modifying the quality and quantity of lignic material inputs to the soil, specifically on SOM storage and soil fertility, are poorly known. Recent studies suggest that this material has a modest contribution to stable soil pools. Nevertheless, as this material decays slowly it may contribute to the SOM pool for a certain period and provide water retention capacity as well as to anion and cationic exchange sites as well as habitat. Conclusion These results suggest that the recent history of woody inputs (SOH vs. WTH after 17 yrs) in these forests has little impact on C accumulation in woody debris, organic layer and mineral soil pools. 3. Method Chronosequence approach Pairs of plots under similar ecological conditions for which historical management and disturbance have created different inputs of lignic material were studied. CAWCOT sites 1 yr after harvesting (3 paired-plots) GOUIN sites 17 yrs after harvesting (7 paired-plots) Two treatments Treatment A: Stem-only harvesting (SOH) Treatment B: Whole-tree harvesting (WTH) Analysis Paired-plots were sampled and analysed for dead carbon pools (woody debris and soil) and significant differences between treatments were assessed using ANOVAs. Acknowledgements We are grateful to J. Morissette, S. Dagnault, F. Michaud and S. Rousseau for field/lab assistance. We also thank F. Laliberté and S. Bédard from Chantiers Chibougamau for help with field inventory. No significant reduction in C stored in organic layer and mineral soil 1 yr and 17 yrs following WTH Orthic humo-ferric podzol (Haplorthod in US soil taxonomy) is the typical soil profile found in the study area. 0 1 2 3 4 5 6 7 CAW (1 yr) GOU (17 yrs) Woody debris C (Mg C ha -1 ) Coarse: >3 cm diam. a a a a CAW (1 yr) GOU (17 yrs) Small: 1-3 cm diam. a b bc c CAW (1 yr) GOU (17 yrs) SOH WTH Fine: <1 cm diam. a b cd d 0 20 40 60 80 100 CAW (1 yr) GOU (17 yrs) Soil C (Mg C ha -1 ) Organic layer b b a a The difference in woody material between treatments lasted only for a short period of time (<17 yrs) CAW (1 yr) GOU (17 yrs) SOH WTH Mineral soil 0-55 cm a a a a The amount of C stored in small and fine woody debris was higher in treatments that received more inputs (i.e. treatment ASOH) but C stored in larger debris was not significantly different between treatments.

Upload: others

Post on 09-Jan-2022

0 views

Category:

Documents


0 download

TRANSCRIPT

Page 1: Changes in the Lignic Portion of the Organic Layer

4. Results

2. Goal • Gain knowledge on the short- (1 yr) and mid-term (17 yrs) effect

of the harvest of lignic material on carbon (C) pools in boreal forest sites of eastern Canada.

Changes in the Lignic Portion of the Organic Layer Following Harvesting in the Boreal Forest

Jérôme Laganière*1, David Paré1, Évelyne Thiffault2

*[email protected] 1Canadian Forest Service, Laurentian Forestry Centre, Québec, QC, Canada; 2Département des sciences du bois et de la forêt, Université Laval, QC, Canada.

1. Context • Forest harvesting periodically removes lignic materials that

would eventually, if not harvested, contribute to the soil organic matter (SOM) pool.

• The long term effects of modifying the quality and quantity of lignic material inputs to the soil, specifically on SOM storage and soil fertility, are poorly known.

• Recent studies suggest that this material has a modest contribution to stable soil pools. Nevertheless, as this material decays slowly it may contribute to the SOM pool for a certain period and provide water retention capacity as well as to anion and cationic exchange sites as well as habitat.

Conclusion • These results suggest that the recent history of woody inputs (SOH

vs. WTH after 17 yrs) in these forests has little impact on C accumulation in woody debris, organic layer and mineral soil pools.

3. Method Chronosequence approach • Pairs of plots under similar ecological conditions for which

historical management and disturbance have created different inputs of lignic material were studied.

CAWCOT sites 1 yr after harvesting (3 paired-plots) GOUIN sites 17 yrs after harvesting (7 paired-plots) Two treatments Treatment A: Stem-only harvesting (SOH) Treatment B: Whole-tree harvesting (WTH)

Analysis • Paired-plots were sampled and analysed for dead carbon pools

(woody debris and soil) and significant differences between treatments were assessed using ANOVAs.

Acknowledgements We are grateful to J. Morissette, S. Dagnault, F. Michaud and S. Rousseau for field/lab assistance. We also thank F. Laliberté and S. Bédard from Chantiers Chibougamau for help with field inventory.

No significant reduction in C stored in organic layer and mineral soil 1 yr and 17 yrs following WTH

Orthic humo-ferric podzol (Haplorthod in US soil taxonomy) is the typical soil profile found in the study area.

0

1

2

3

4

5

6

7

CAW (1 yr) GOU (17 yrs)

Woo

dy d

ebris

C (M

g C

ha-1

)

Coarse: >3 cm diam. a

a a

a

CAW (1 yr) GOU (17 yrs)

Small: 1-3 cm diam.

a

b bc c

CAW (1 yr) GOU (17 yrs)

SOH

WTH

Fine: <1 cm diam.

a

b

cd d

0

20

40

60

80

100

CAW (1 yr) GOU (17 yrs)

Soil

C (M

g C

ha-1

)

Organic layer

b b

a

a

The difference in woody material between treatments lasted only for a short period of time (<17 yrs)

CAW (1 yr) GOU (17 yrs)

SOH

WTH

Mineral soil 0-55 cm

a a a

a

The amount of C stored in small and fine woody debris was higher in treatments that received more inputs (i.e. treatment ASOH) but C stored in larger debris was not significantly different between treatments.