Carbon Pools in a Eucalyptus pilularis (Blackbutt) Regrowth Forest Managed for Production or...

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Transcript of Carbon Pools in a Eucalyptus pilularis (Blackbutt) Regrowth Forest Managed for Production or...

Carbon Pools in a Eucalyptus pilularis (Blackbutt) Regrowth Forest Managed for Production

or Conservation

Daniel St Merryn Payne

Australian National University

Canberra, Australia

Rationale• Kyoto Protocol Article 3.4

– Native forest management (harvesting, fire)

Objectives

• Assess and measure the carbon pools in a forest ecosystem

• Predict the effect of different management regimes on the carbon pools

Study Area

• Ourimbah State Forest (SFNSW)• Blackbutt dominant overstorey• 2 Ha Plot, 1 Ha harvested

Data collection• Overstorey: Forest inventory

– DBH, height, stem quality

Basal Area

Blackbutt Dead Forest Oak Turpentine Other

Data Collection cont.• Overstorey: destructive sampling

– 10 Blackbutts

• Allometric equation development

Data collection cont.• Understorey: stratified by understorey type

– 12 2m * 2m plots

Data Collection cont.• Litter and dead material

– Same 2m*2m plot

Data Collection cont.• Timber Products measured at harvest

Data Collection cont.

• Post harvest assessment– Forest inventory– Visual assessment of understorey

Results:Actual carbon pools Pre and Post Harvest Carbon Storage

0

20

40

60

80

100

120

140

160

Understorey Litter Deadwood Products Slash Overstorey

Carbon Pool

Carb

on (

T/h

a)

Pre-Harvest Post-Harvest

Modelling management options CAMFor

• 2 hypothetical management regimes– Production management

• Harvesting, fire

– Conservation management• Fire

• Inputs from actual carbon pool assessment and literature search

CAMFor

 Carbon stored in trees, debris and products pool

Species parametersGrowth, carbon content,Decomposition rates

Harvest regimeIntensity and frequency

Fire regimeIntensity and frequency

Initial ConditionsOverstorey biomass, litter

 CAMForVersion 2.1

 

Optimal Regimes

• Production option (50 years):– harvest 2000 and every 10 years– Low intensity fire in 2002 and every 2 years

after harvest

• Conservation option (50 years):– Low intensity fire in 2002 and every 10 years

after

ResultsComparison of Production and Conservation Options

0

50

100

150

200

250

300

350

400

450

2000 2005 2010 2015 2020 2025 2030 2035 2040 2045 2050

Year

Carb

on (

T/h

a)

Production Conservation

Results cont.Carbon Stored in Overstorey

0

50

100

150

200

250

300

350

400

450

2000 2005 2010 2015 2020 2025 2030 2035 2040 2045 2050

Year

Carb

on (

T/h

a)

Production Products Conservation

First Kyoto Period

0

50

100

150

200

250

300

350

2008 2009 2010 2011 2012

Year

Carb

on (

T/h

a)

Production (tree + products) Carbon in Trees

Results cont.

Carbon stored in trees after a wildfire

0

50

100

150

200

250

300

350

400

2000 2005 2010 2015 2020 2025 2030 2035 2040 2045 2050

Year

Carb

on (

T/h

a)

Production Conservation Products

Results cont.

Modelling conclusions

• Overstorey important carbon storage pool– Production versus Conservation

• Type of timber products– Decay rate

• Effect of wildfire

Summary

• Cost and time constraints for data collection– Refine data collection methods– Allometric equations

• Soil pool not measured

• Debris post-harvest: product?