Carbon storage in engineered wood products in landfills · Carbon storage in engineered wood products in landfills ... wood products and paper from landfills; 2) ... * Results confirmed

Carbon storage in engineered wood products in landfills

Presented by Fabiano Ximenes, NSW DPI, 2013

Talk Outline

- Background to project

- Landfills in Australia - Excavations

- Experimental work - Implications to industry

Project background

- Previous projects: long-term C storage in solid wood

-Funding: FWPA / Laminex / DAFF

1) Long-term C storage in engineered wood products and paper from landfills; 2) Long-term C storage in engineered wood products and paper in anaerobic reactors in the laboratory

Why is it important?

- Greenhouse credentials of wood products (Carbon trading)

- Life Cycle Assessments - More accurate estimates of national greenhouse emissions

Landfill types

Municipal solid waste landfills

C&D landfills

C&I landfills

Bioereactor landfills

Landfills

Past: shallow, no compaction, aerobic

Sanitary landfills: 20 -

30’s

Engineered landfills: 60-70’s

Modern landfills: large, deep, compaction, anaerobic

Landfills

Wood waste disposal Current options: Recycle/reuse; landfill

Wood waste to landfills in Australia: 1.5 -

2 Mt / year; paper : 1.3 Mt / year Eventually – most recycled products

either decay or placed in landfills

Alternative: Incineration for energy recovery (Europe model)

*Fossil-fuel displacement benefits

Decomposition in landfills

• Decay of organics: 50:50 CO2 and CH4 • Oxidation factor: 0.1 (default) – probably

higher

• Best-practice landfills: 75 - 90% CH4 recovery

• Methane generation: 0-30 years

Decay of wood in landfills

Wood is made up primarily of cellulose, hemicellulose and lignin

Wood type

Cellulose (%)

Hemicellulose (%)

Lignin (%)

Softwood 45-50 15-20 25-35

Hardwood 50-55 15-25 18-25



Lignin is degraded under aerobic conditions

Undegraded wood

Bacterial attack Severe fungal attack

Wood degradation (Aerobic)

From: MSc thesis: Preservation of wood using oxy -aluminium compounds. Ximenes 2000



Lignin is degraded under aerobic conditions

If landfill is under anaerobic conditions, then

lignin (and some of the cellulose and hemicellulose) will not degrade

Methodology - Excavations

Identification of sites (worst case scenario) Site characterization Target products

Chemical composition: Cellulose /

Hemicellulose / Lignin / Ash Comparison with matching controls

Excavation at Lucas Heights

“To understand garbage you have to touch it, to fee l it, to sort it, to smell it” Rathje and Murphy , 2001

Excavation at Meadowbank

20 years in landfill




Ximenes et al 2008

Analysed range of solid wood samples from two landfills in Sydney

No significant loss of carbon in one landfill (samples buried for 19-29 years)

Approx. 18% loss of carbon from samples buried in another landfill (46 years)

Cairns - Portsmith

Sampling (0.5 m intervals), until the bottom of the cells (2.5-3.5 m in depth)

The pH ranged from 5.6 to 7.4 . The

temperature of the waste was slightly higher than the ambient temperature

Samples buried for 16-18 years

Brisbane - Fitzgibbon Sampling (0.5 m intervals), until the

bottom of the cells (3.5-6.5 m in depth).

The pH ranged from 6.4 to 6.8. The

temperature of the waste was slightly higher than the ambient temperature.

Samples buried for 18 years

Table 1. Mean pH and temperature of waste buried at Roghan Rd. landfill

Cell Depth of cell (m)

pH (Mean, SD)

Temperature (°C; Mean, SD)

1 3.5 6.4 (0.3) 25.8 (0.4)

2 5.0 6.5 (1.0) 26.4 (0.6)

3 6.5 6.8 (0.3) 27.0 (2.0)

4 5.0 6.8 (0.2) 25.4 (0.8)

Combined 6.7 (0.6) 26.2 (1.3)

Brisbane - Fitzgibbon

Brandown (Kemps Creek) Sampling (0.5 m intervals), until the

bottom of the cells (7.0 m in depth). The pH ranged from 6.8 to 7.0. The

temperature of the waste increased slightly with depth.

Samples buried for 19-20 years

Brandown (Kemps Creek)

Table 2. Mean pH and temperature of waste buried at Brandown landfill

Cell Depth of cell (m)

pH (Mean, SD)

Temperature (°C; Mean, SD)

1 7.0 7.2 (0.5) 23.6 (3.8)

2 2.8 7.7 (0.2) 20.5 (0.5)

3 6.4 6.6 (0.7) 22.3 (3.1)

Combined 7.0 (0.7) 22.7 (3.3)

Excavation in Brisbane

“To understand garbage you have to touch it, to fee l it, to sort it, to smell it” Rathje and Murphy , 2001

Excavation in Brisbane

Excavation in Kemps Creek

Excavation in Kemps Creek





Plywood - Cairns

Brisbane

Kemps Creek

Brisbane

Cairns

Kemps Creek

Brisbane

Cairns

Kemps Creek

Excavations – Moisture content

Table. Moisture content of engineered wood products recovered from Sydney, Brisbane and Cairns according to product type

Site Moisture content (%) Mean (SD, N)

Particleboard MDF Plywood / Veneer

Kemps Creek

37 (8.8, 29) 44.7 (10.0, 19) 38.9 (10.1, 12)

Brisbane 45 (10.0, 21) 47.9 (9.7,20)

41.4 (10.0,10)

Cairns 39-8-58.3

70.6 (4.2, 6) 56.9 (3.0, 4)

Excavation – Fibre analysis

Composite wood product type N Sample type

Normalised Ash

(%, SD)

Holocel. Lignin MDF 9 Landfill 62.2 (1.7) 37.8 (1.7) 4.8 (1.5)

1 Control 67.9 32.1 0.3

Plywood 8 Landfill 59.4 (6.9) 40.6 (6.9) 5.3 (3.3)

1 Control 63.1 36.9 2.9

Particleboard 2 Landfill 63.8 36.2 17.7

1 Control 66.4 33.6 0.4

Table . Chemical composition analysis of engineered wood product samples recovered from Portsmith landfill, Cairns.

* Standard deviation provided for landfill engineered wood product types with at least 3 samples. Range provided for landfill engineered wood product types with 2 samples only


Composite wood

product type N Sample

type

Normalised Ash

(%,SD) Holocel. Lignin MDF 21 Landfill 65 (1.7) 35 (1.7) 6.8 (5.4)

1 Control 67.9 32.1 0.3

Particleboard 25 Landfill 64.1 (4.7) 35.9 (4.7) 9.4 (9.2)

4 Control 66.9 (0.3) 33.1 (0.3) 0.5 (0.01)

Plywood 5 Landfill 62.9 (5.0) 37.1 (5.0) 4.1 (2.3)

1 Control 63.1 36.9 2.9

Veneer 6 Landfill 63.4 (5.4) 36.6 (5.4) 4.6 (1.8)

1 Control 63.1 36.9 2.9

Table . Chemical composition analysis of engineered wood product samples recovered from Roghan Rd. landfill, Brisbane.

* Standard deviation provided for landfill engineered wood product types with at least 3 samples.


Composite wood product type N

Sample type

Normalised

Ash (%,SD)

Holocel. Lignin MDF 19 Landfill 63.4 (4.8) 36.6 (4.8) 4.1 (3.2)

1 Control 67.9 32.1 0.3

Particleboard 28 Landfill 64.6 (2.4) 35.4 (2.4) 5.1 (6.7)

4 Control 66.9 (0.3) 33.1 (0.3) 0.5 (0.01)

Veneer 6 Landfill 64.9 (1.5) 35.1 (1.5) 5.0 (2.3)

1 Control 63.1 36.9 2.9

Table . Chemical composition analysis of engineered wood product samples recovered from Brandown landfill, Sydney.

* Standard deviation provided for landfill engineered wood product types with at least 3 samples.

Results - Excavation

Product type

Carbon storage (%)

Cairns Sydney Brisbane

MDF 86.4 89.0 92.6

Particleboard 93.8 94.2 93.0

Plywood 90.6 NA 99.5

Veneer NA 100 100

Table . Carbon storage in engineered wood products recovered from MSW landfills in Cairns and Brisbane, and engineered wood products recovered from a C&D landfill in Sydney

Excavation - issues Possibility of decay while the products where in service (before disposal); Possibility of decay taking place in the aerobic

stages of the landfill life; Possibility of loss of carbon due to decay of a

chemical nature in landfills; Difficulties in finding suitable controls for

comparisons with landfill samples Difficulties in finding enough controls to enable

meaningful statistical comparisons

Lab-Scale Reactors

To determine carbon storage / loss for products under controlled, optimised anaerobic decay conditions

Products included (Laminex): – Particleboard (Trade Essentials): 1.8 kg – MDF (Trade Essentials Craftwood): 1.8 kg – HPL (Laminex Redback): 2.2 kg

Methodology - Laboratory Reactors filled with composite wood

products and seed material (anaerobic conditions)

Moisture, temperature, pH, nutrients

optimum Monitoring release of CH4 and CO2 (gas

chromatography) Mass balance after gas release is finished Carbon storage / loss determined

Lab-Scale Reactors

Conditions to maximize decomposition

– Temperature: 39°C – Leachate neutralization and

recirculation (Veolia bioreactor landfill, Goulburn)

– Regular monitoring of nutrients: target concentrations • NH3-N: 100 mg of N/L • PO4-P: 5-10 mg of P/L

Lab-Scale Reactors

Particleboard / MDF samples: before and after

Particleboard

MDF

Results - Laboratory pH

Results - Laboratory

Gas Composition – Particleboard

Reactor 1

Reactor 2


Gas Composition – MDFReactor 3

Reactor 4


Product type

Carbon storage (%) Carbon loss (%)

Particleboard 98.25 1.75

MDF 100 0

High-pressure laminate 100 0

Table . Carbon storage and carbon loss (range) from engineered wood products in bioreactors

Research Outputs: Summary

Field - High levels of C storage in engineered wood products after up to 20 years Lab

- 0% carbon loss from MDF and particleboard * * Results confirmed in an independent study in the US (Wang et al 2011)

Carbon Storage in Australia's Forest Plantations, Wood Products in Service and in Landfill

88 Mt C

94.6 Mt C

137.5 Mt C

Plantations

Wood in service

Wood in landfills

Implications for Industry – cont. - Demonstration of long-term carbon storage: carbon credits * Additional carbon revenue (additional carbon to trade) * Increasing value of thinnings / incentive for plantation expansion

MORE $ FOR C

Implications for Industry

- Use of engineered wood products has a significant beneficial GHG impact

- Any of the current end-of-life options: Recycling Energy Landfill

POSITIVE GHG OUTCOME

Implications for Industry

- Improved outcomes in LCAs of engineered wood products

- Improved outcomes in building rating schemes

WOOD PRODUCTS MORE COMPETITIVE IN BUILDING RATING SCHEMES

Summary - Excavations of engineered wood products in a range of climatic zones: high C storage after up to 18 years - Laboratory reactors: no C loss under controlled, optimised, anaerobic decay conditions

- Engineered wood products in Australia: long-term storage of C

Wang et al 2011

Aim: characterize the anaerobic biodegradability of major wood products in municipal waste in the USA

Experimental set-up: 8 L bioreactors

Carbon loss from solid wood: 0 – 7.8%

Carbon loss from Particleboard, MDF and plywood: 1.1-1.4%

Current work - Consolidation of data from more recent excavations - Consolidation of data from experimental work in the US (paper products) and in Australia (paper products and composite wood products)

- Bioreactor experiments with range of Australian solid wood types ongoing

Key references Ximenes, F.A.; Gardner, W.D.; Cowie, A. The decomposition of wood products in landfills in Sydney, Australia. Waste Manag. 2008, 28, 2344–2354. Wang, X.; Padgett, J.M.; De la Cruz, F.B.; Barlaz, M.A. Wood biodegradation in laboratory scale landfills. Environ. Sci. Technol. 2011, 45, 6864–6871.

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Carbon storage in engineered wood products in landfills · Carbon storage in engineered wood products in landfills ... wood products and paper from landfills; 2) ... * Results confirmed

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