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AIRUSE LIFE+: Biomass burning emission factors and chemical profiles in Southern Europe Fulvio Amato C.A. Alves, E. Vicente, C. Gonçalves, M. Duarte, L. Tarelho, T. Nunes, C. Pio, C. Colombi, V. Gianelle, X. Querol TFEIP/EIO NET M eeting (11 th – 12 th M ay)

AIRUSE LIFE+: Biomass burning emission factors and chemical profiles in Southern Europe Fulvio Amato C.A. Alves, E. Vicente, C. Gonçalves, M. Duarte, L

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Page 1: AIRUSE LIFE+: Biomass burning emission factors and chemical profiles in Southern Europe Fulvio Amato C.A. Alves, E. Vicente, C. Gonçalves, M. Duarte, L

AIRUSE LIFE+: Biomass burning emission factors and chemical profiles

in Southern Europe

Fulvio Amato

C.A. Alves, E. Vicente, C. Gonçalves, M. Duarte, L. Tarelho, T. Nunes, C. Pio, C. Colombi, V.

Gianelle, X. Querol

TFEIP/EIONET Meeting (11th – 12th May)

Page 2: AIRUSE LIFE+: Biomass burning emission factors and chemical profiles in Southern Europe Fulvio Amato C.A. Alves, E. Vicente, C. Gonçalves, M. Duarte, L

2

Source apportionment: Biomass burning contribution (2013)

PM10Porto-

TRBarcelona-

UBFlorence-

UBMilan-

UBAthens-

SUB

Contributions to the annual mean 14%(5) <2%(<0.5) 16%(3) 24%(9) 7%(1.4)

Contributions during PM10 exceedances days

25%(16) <2%(<0.5) 30%(22) 35%(28) 1%(0.6)

PM2.5Porto-

TRBarcelona-

UBFlorence-

UBMilan-

UBAthens-

SUB

Contributions to the annual mean 18%(5) <3%(<0.5) 21%(3) 21%(6) 10%(1.2)

Contributions during PM10 exceedances days

33%(22) <3%(<0.5) 33%(23) 26%(14) 2%(0.5)

Contribution of biomass burning to PM10 and PM2.5 levels, mass fractions (%) and µg m-3, in AIRUSE cities

Page 3: AIRUSE LIFE+: Biomass burning emission factors and chemical profiles in Southern Europe Fulvio Amato C.A. Alves, E. Vicente, C. Gonçalves, M. Duarte, L

3

Based on forest inventories and information provided by the AIRUSE partners, wood species widely used as biofuels in residential combustion in Southern European countries were burned in traditional appliances (manually fed)

(Fagus sylvatica)European beech

(Quercus pyrenaica)Pyrenean oak

(Populus nigra)Black poplar

Pine(Pinus pinaster)

Eucalypt(Eucalyptus globulus)

Cork oak(Quercus suber )

Golden wattle(Acacia longifolia)

Portuguese oak(Quercus faginea)

Olive(Olea europea)

Holm oak(Quercus ilex rotundifolia)

Briquettes

Biomass burning profiles – biofuels and appliances

Page 4: AIRUSE LIFE+: Biomass burning emission factors and chemical profiles in Southern Europe Fulvio Amato C.A. Alves, E. Vicente, C. Gonçalves, M. Duarte, L

4

Traditional brick

fireplace

Traditional cast iron

wood stove

Eco-labelledchimney-typewood stove

Manually fed combustion appliances

Page 5: AIRUSE LIFE+: Biomass burning emission factors and chemical profiles in Southern Europe Fulvio Amato C.A. Alves, E. Vicente, C. Gonçalves, M. Duarte, L

5

Emissions from a pellet stove were also measured. In addition to different types of pellets, other alternative biofuels (agro-fuels) that are becoming common in Southern Europe were also burned in this combustion appliance.

4 types of pelletsOlive pit

Shell of pine nutsAlmond shell

Automatically fed combustion appliance

Pellets type I – made of wood (ENPlus certification)Pellets type II to IV – manufactured with residues from the furniture industry and from civil construction, in different proportions

Page 6: AIRUSE LIFE+: Biomass burning emission factors and chemical profiles in Southern Europe Fulvio Amato C.A. Alves, E. Vicente, C. Gonçalves, M. Duarte, L

Termocouple T6

Sample Gas (SG) / Pressure

Warm water (out)

Combustion flue gases Cold water (in)

Temperature

S

N2Zero Gas (ZG)

L

UCD0J

I

Pressure

045

000

UCD1

SG

Sam

ple G

as (SG

) / Pressure

UCE1

CO

R

UCD2

K

CO2

O2

HC

Q

O

P

N

Heated sampling line (190ºC)

G

Ice

Bat

h

ZG

Condensed material

Ice

Bat

h

SGSG

MTermocouple T5

Termocouple T4

Termocouple T3

Termocouple T2

D

A

C Air

B

F

E

H

Termocouple T1

A - Stove

B – Grate of the stove

C – Load cell (weight sensor)

D – Air flow meter

E – Thermal insulation of the exhaust duct

F – Exhaust duct (Chimney)

G – Water-cooled gas sampling probe

H – Heated sampling line

I, J, K – Command and gas distribution units (UCD0, UCD1, UCD2)

L – Gas sampling pump

M – Gas condensation unit for moisture removal

N, O, P, Q – Automatic on-line gas analysers (THC, CO2, O2, CO)

R – Electronic command unit (UCE1)

S – Computer data acquisition and control system

Dashed line – Electric circuit,

Continuous line – Pneumatic circuit.

Termocouple T6

Sample Gas (SG) / Pressure

Warm water (out)

Combustion flue gases Cold water (in)

Temperature

S

N2Zero Gas (ZG)

L

UCD0J

I

Pressure

045

000

UCD1

SG

Sa m

pl e Ga s (S

G) / P

re ssur e

UCE1

CO

R

UCD2

K

CO2

O2

HC

Q

O

P

N

Heated sampling line (190ºC)

G

Ice

Ba t

h

ZG

Condensed material

Ice

Ba t

h

SGSG

MTermocouple T5

Termocouple T4

Termocouple T3

Termocouple T2

D

A

C Air

B

F

E

H

Termocouple T1

Termocouple T6

Sample Gas (SG) / Pressure

Warm water (out)

Combustion flue gases Cold water (in)

Temperature

S

N2Zero Gas (ZG)

L

UCD0J

I

Pressure

045

000

UCD1

SG

Sam

ple G

as (SG

) / Pre ssu

re

UCE1

CO

R

UCD2

K

CO2

O2

HC

Q

O

P

N

Heated sampling line (190ºC)

G

Ice

Ba

t h

ZG

Condensed material

Ice

Ba

t h

SGSG

MTermocouple T5

Termocouple T4

Termocouple T3

Termocouple T2

D

A

C Air

B

F

E

H

Termocouple T1

Termocouple T6

Sample Gas (SG) / Pressure

Warm water (out)

Combustion flue gases Cold water (in)

Temperature

S

N2Zero Gas (ZG)

L

UCD0J

I

Pressure

045

000

UCD1

SGS

amp le

Ga s (S

G) / P

re ss u re

UCE1

CO

R

UCD2

K

CO2

O2

HC

Q

O

P

N

Heated sampling line (190ºC)

G

Ice

Bat

h

ZG

Condensed material

Ice

Bat

h

SGSG

MTermocouple T5

Termocouple T4

Termocouple T3

Termocouple T2

D

A

C Air

B

F

E

H

Termocouple T1

Termocouple T6

Sample Gas (SG) / Pressure

Warm water (out)

Combustion flue gases Cold water (in)

Temperature

S

N2Zero Gas (ZG)

L

UCD0J

I

Pressure

045

000

UCD1

SG

Sam

pl e G

as ( SG

) / Pressur e

UCE1

CO

R

UCD2

K

CO2

O2

HC

Q

O

P

N

Heated sampling line (190ºC)

G

I ce

Bat

h

ZG

Condensed material

I ce

Bat

h

SGSG

MTermocouple T5

Termocouple T4

Termocouple T3

Termocouple T2

D

A

C Air

B

F

E

H

Termocouple T1

Termocouple T6

Sample Gas (SG) / Pressure

Warm water (out)

Combustion flue gases Cold water (in)

Temperature

S

N2Zero Gas (ZG)

L

UCD0J

I

Pressure

045

000

UCD1

SG

Sam

p le Gas ( S

G) / P

re s su r e

UCE1

CO

R

UCD2

K

CO2

O2

HC

Q

O

P

N

Heated sampling line (190ºC)

G

Ice

Ba t

h

ZG

Condensed material

Ice

Ba t

h

SGSG

MTermocouple T5

Termocouple T4

Termocouple T3

Termocouple T2

D

A

C Air

B

F

E

H

Termocouple T1

E – Thermal insulation of the exhaust duct F – Exhaust duct (Chimney)G – Water-cooled gas sampling probeH – Heated sampling lineA - Stove

B – Grate of the stoveC – Load cell (weight sensor)D – Air flow meter

R – Electronic command unit (UCE1)S – Computer data acquisition and control system

I, J, K – Command and gas distribution units (UCD0, UCD1, UCD2)L – Gas sampling pumpM – Gas condensation unit for moisture removalN, O, P, Q – Automatic on-line gas analysers (THC, CO2, O2, CO)

• 0.2 m int. diameter

• 3.3 m height

Combustion facility

Page 7: AIRUSE LIFE+: Biomass burning emission factors and chemical profiles in Southern Europe Fulvio Amato C.A. Alves, E. Vicente, C. Gonçalves, M. Duarte, L

Termocouple T6

Sample Gas (SG) / Pressure

Warm water (out)Cold water (in)

Temperature

S

N2Zero Gas (ZG)

L

UCD0J

I

Pressure

045

000

UCD1

SG

Sam

ple

Gas (S

G) / P

r essure

UCE1

CO

R

UCD2

K

CO2

O2

HC

Q

O

P

N

Heated sampling line (190ºC)

G

Ice

Bat

h

ZG

Condensed material

Ice

Bat

h

SGSG

MTermocouple T5

Termocouple T4

Termocouple T3

Termocouple T2

D

A

C Air

B

F

E

H

Termocouple T1

Atm

osph

eric

air

Co

mbu

stio

n f lu

e ga

ses

Z

Electron ic flow sampler

Y

TECORA

Thermocouple T8

XTCR PM Air Inlet

T

Thermocouple T7

Pres sure (P

1 )

W

UPASSIVE CAVITY AEROSOL SPECTROMETER PROBE

Dilution air

Dilution air

V

Termocouple T6

Sample Gas (SG) / Pressure

Warm water (out)Cold water (in)

Temperature

S

N2Zero Gas (ZG)

L

UCD0J

I

Pressure

045

000

UCD1

SG

Sam

ple

Ga s (S

G) / P

res sure

UCE1

CO

R

UCD2

K

CO2

O2

HC

Q

O

P

N

Heated sampling line (190ºC)

G

Ice

Bat

h

ZG

Condensed material

Ice

Bat

h

SGSG

MTermocouple T5

Termocouple T4

Termocouple T3

Termocouple T2

D

A

C Air

B

F

E

H

Termocouple T1

Atm

osph

eric

air

Co

mbu

stio

n flu

e ga

ses

Z

Electronic flow sampler

Y

TECORA

Thermocouple T8

XTCR PM Air Inlet

T

Thermocouple T7

Pressu re (P

1)

W

UPASSIVE CAVITY AEROSOL SPECTROMETER PROBE

Dilution air

Dilution air

V

T - Dilution tunnel

U - Aerosol size distribution probe (PCASP-X)

V - Venturi system

W - Pitot tube

X - Sampling head for PM10 or PM2.5 (TECORA)

Y - TECORA control and data acquisition system

Z - Blower

Combustion facility

Page 8: AIRUSE LIFE+: Biomass burning emission factors and chemical profiles in Southern Europe Fulvio Amato C.A. Alves, E. Vicente, C. Gonçalves, M. Duarte, L

Analytical techniques

Thermal-optical method

Ion chromatography

ICP-MSICP-AES

GC-MS

Water solubleions

Organic carbonElemental carbon

Elements

Organic speciation

HPLC-electrochemistry,HPAEC/ESI-MS,

HPAEC-PADor GC-MS

Anhydrosugars

Page 9: AIRUSE LIFE+: Biomass burning emission factors and chemical profiles in Southern Europe Fulvio Amato C.A. Alves, E. Vicente, C. Gonçalves, M. Duarte, L

9

PM emission factors

0

200

400

600

800

1000

1200

Fireplace Traditionalwoodstove

Eco-labelledwoodstove

Pellet stove

mg

MJ-1

(dry

bas

is)

0

200

400

600

800

1000

1200

Fireplace Traditionalwoodstove

Eco-labelledwoodstove

Pellet stove

mg

MJ-1

(dry

bas

is)

Particle emissions from the fireplace were about 3, 9 and 12-fold higher than those from the traditional woodstove, eco-labelled appliance and pellet stove, respectively.

Emissions from the traditional woodstove exceeded 5 to 6 times those of the two more modern combustion devices

Page 10: AIRUSE LIFE+: Biomass burning emission factors and chemical profiles in Southern Europe Fulvio Amato C.A. Alves, E. Vicente, C. Gonçalves, M. Duarte, L

10

PM emission factors

0

20

40

60

80

100

120

140

160

180

200

Pellet - typeI

Pellet - typeII

Pellet - typeIII

Pellet - typeIV

Olive Pit Shell of PineNuts

AlmondShell

mg

MJ-1

(dry

bas

is)

0

20

40

60

80

100

120

140

160

180

200

Pellet - typeI

Pellet - typeII

Pellet - typeIII

Pellet - typeIV

Olive Pit Shell of PineNuts

AlmondShell

mg

MJ-1

(dry

bas

is)

PELLET STOVE: only one type of pellets, with ENplus quality seal, complies with the limits stipulated in countries where certification of combustion appliances is required

(e.g. 50 mg MJ-1 in Denmark and Switzerland, 35 mg MJ-1 for wood fuels and 25 mg MJ-1 for pellets in Austria, and 27 mg MJ-1 in Germany).

Page 11: AIRUSE LIFE+: Biomass burning emission factors and chemical profiles in Southern Europe Fulvio Amato C.A. Alves, E. Vicente, C. Gonçalves, M. Duarte, L

11In the fireplace and the old type stove, OC dominated the emissions, while more efficient combustion in the eco-labelled and pellet stoves contributed to 1.3 to 4.7-fold higher EC relative fractions in PM. An increase of EC emissions with increasing combustion temperature is generally observed.

Chemical composition of PM

0

10

20

30

40

50

60

70

Maritime pine Golden wattle Eucalypt Cork oak

(OC+

EC)/

PM10

(%w

t.)

Eco-labelled woodstove

0102030405060708090

(OC+

EC)/

PM2.

5(%

wt.

)

Fireplace

EC OC

0102030405060708090

(OC+

EC)/

PM2.

5(%

wt.

)

Woodstove

0

10

20

30

40

50

60

70

Pellet I Pellet II Pellet III Pellet IV Olive Pit Shell ofPine Nuts

AlmondShell

(OC+

EC)/

PM10

(%w

t.)

Pellet stove

Page 12: AIRUSE LIFE+: Biomass burning emission factors and chemical profiles in Southern Europe Fulvio Amato C.A. Alves, E. Vicente, C. Gonçalves, M. Duarte, L

12

Water-soluble ions

2%

Elements 0.4%

EC9%

OM89%

Pine, Fireplace

Water-soluble ions

11%Elements

2%

EC15%

OM72%

Pine, Eco-labelled stoveAlkanes0.24%

Alkenes0.010%

PAHs1.5%

Phenolic compounds

2.6%Alcohols0.022%

Acids44%

Sugars48%

Other compounds

4.3%

Alkanes2% Alkenes

1%

PAHs13%

Phenolic compounds

1%

Alcohols2%

Acids60%

Sugars18%

Other Compounds

3%

Chemical composition of PM (manually fed appliances)

Higher mass fractions of inorganic constituents, EC and polyaromatics in PM from more efficient combustion devices

Organic compounds, such as sugars and acids, completely dominate emissions from old-type appliances that operate at lower temperatures

Page 13: AIRUSE LIFE+: Biomass burning emission factors and chemical profiles in Southern Europe Fulvio Amato C.A. Alves, E. Vicente, C. Gonçalves, M. Duarte, L

13

Chemical composition of PM (pellet stove)EC7%

OM 52%

Elements and their oxides

39%

Undetermined2%

Pellets type I

EC3.2%

OM 57%

Elements and their oxides

32%

Undetermined7.8%

Olive pit

EC41%

OM 37%

Elements and their oxides

22%

Shell of pine nuts

Much higher inorganic PM10 mass fractions (up to 42%)

Under typical conditions, organic particles are most relevant in poorly operated

manual wood combustion devices, while inorganic particles are most dominant in automatic biomass combustion devices

operated at high temperatures

Page 14: AIRUSE LIFE+: Biomass burning emission factors and chemical profiles in Southern Europe Fulvio Amato C.A. Alves, E. Vicente, C. Gonçalves, M. Duarte, L

23 parent-PAHs, 11 NPAHs and 15 OPAHs in PM10 were quantified

0

5000

10000

15000

20000

25000

30000

35000

40000

Eucalypt,devolatilisation

Eucalypt, flaming+ smouldering

Pine,devolatilisation

Pine, flaming +smouldering

µg

kg-1

of f

uel

bu

rned

, dry

bas

is

Woodstove

parent-PAHs

OPAHs

NPAHs

0

100

200

300

400

500

600

700

800

900

Pellets typeI

Pellets typeII

Pellets typeIII

Pellets typeIV

Olive pit Shell ofpine nuts

Almondshell

µg

kg-1

of f

uel

bu

rned

, dry

bas

is

Pellet stove

parent-PAHs

OPAHs

NPAHs

Polycyclic aromatic compounds

Page 15: AIRUSE LIFE+: Biomass burning emission factors and chemical profiles in Southern Europe Fulvio Amato C.A. Alves, E. Vicente, C. Gonçalves, M. Duarte, L

15

BaP (and PM) emission factors

nd – not detected; --- not determined

FIREPLACE  Softwood Hardwood Briquettesg PM2.5 kg-1 biofuel 7.02 16.9 13.8µg BaP kg-1 biofuel 260 475 31.4

TRADITIONAL WOODSTOVE  Softwood Hardwood Briquettesg PM2.5 kg-1 biofuel 3.64 13.5 9.02µg BaP kg-1 biofuel 46.7 322 85.3

ECO-LABELLED STOVE  Softwood Hardwood Briquettesg PM10 kg-1 biofuel 1.12 2.06 ---µg BaP kg-1 biofuel 1543 146 ---

PELLET STOVE  Pellets I Pellets II Pellets III Pellets IV Olive pit Shell of pine nuts Almond shellg PM10 kg-1 biofuel 0.49 1.51 1.77 1.35 3.12 2.19 2.07

µg BaP kg-1 biofuel 4.43 nd nd 4.61 nd 17.2 9.19

Combustion of resinous wood (softwood) at higher temperatures in the eco-labelled stove produces very intense flames, contributing to oxygen-starved conditions and, consequently, to higher PAH emissions

Page 16: AIRUSE LIFE+: Biomass burning emission factors and chemical profiles in Southern Europe Fulvio Amato C.A. Alves, E. Vicente, C. Gonçalves, M. Duarte, L

16

0

50

100

150

200

250

mg/

g PM

2.5

Woodstove

0.0

0.5

1.0

1.5

2.0

2.5

Pelletstype I

Pelletstype II

Pelletstype III

Pelletstype IV

Olive Pit Shell ofPineNuts

AlmondShell

mg/

g PM

10

Pellet stove

0

50

100

150

200

250

Maritime pine Golden wattle Eucalypt Cork oak

mg/

g PM

10

Eco-labelled stove

Levoglucosan

Levoglucosan is not a suitable tracer for automatically fired combustion appliances in which high temperatures are reached.

Page 17: AIRUSE LIFE+: Biomass burning emission factors and chemical profiles in Southern Europe Fulvio Amato C.A. Alves, E. Vicente, C. Gonçalves, M. Duarte, L

Levoglucosan-to-mannosan ratios

Authors Levo/Man

Schmidl et al., 2007

Fagus sylvatica Quercus robur

Picea abies Larix decidua

14.8 ± 2.2 14.4 ± 2.7 3.6 ± 0.35 3.9 ± 0.1

Fine et al., 2004Hardwood Softwood

19 - 26 5.4 ± 3.7

This study

(eco-labelled stove)

Eucalyptus globulus

Pinus pinaster

Quercus suber Acacia longifolia

34.9 3.0 24.8 10.4

Much lower levoglucosan/mannosan ratios in softwood (in blue) than in hardwood smoke particles

Page 18: AIRUSE LIFE+: Biomass burning emission factors and chemical profiles in Southern Europe Fulvio Amato C.A. Alves, E. Vicente, C. Gonçalves, M. Duarte, L

Potassium

0.0

0.5

1.0

1.5

2.0

2.5

K (w

t% P

M2.

5)

Fireplace Woodstove

0

2

4

6

8

10

12

Maritime pine Golden wattle Eucalypt Cork oak

K+(w

t% P

M10

)

Eco-labelled woodstove

0

5

10

15

20

25

30

Pelletstype I

Pelletstype II

Pelletstype III

Pelletstype IV

Olive Pit Shell ofPineNuts

AlmondShell

K (w

t% P

M10

)

Pellet stoveProportion of K in PM10 inorganic fraction from the pellet stove: 66 (pellets I) – 88% (almond shell)

K may be a good tracer for smoke particles from more efficient combustion systems, but not for all biofuels

Page 19: AIRUSE LIFE+: Biomass burning emission factors and chemical profiles in Southern Europe Fulvio Amato C.A. Alves, E. Vicente, C. Gonçalves, M. Duarte, L

19

0.169

5.29

2.91

1.70

0.027 0.005 0.0110

1

2

3

4

5

6

Pelletstype I

Pelletstype II

Pelletstype III

Pelletstype IV

Olive pit Shell ofpine nuts

Almondshell

Pb

0.81

5.98

3.56 3.26

0.05 0.134 0.0640

1

2

3

4

5

6

7

Pelletstype I

Pelletstype II

Pelletstype III

Pelletstype IV

Olive pit Shell ofpine nuts

Almondshell

Zn

0.128 0.054

1.70

5.10

0.0120.248

bdl0

1

2

3

4

5

6

Pelletstype I

Pelletstype II

Pelletstype III

Pelletstype IV

Olive pit Shell ofpine nuts

Almondshell

Fe

0.001

0.079

0.0300.022

0.001 bdl bdl0

0.01

0.02

0.03

0.04

0.05

0.06

0.07

0.08

0.09

Pelletstype I

Pelletstype II

Pelletstype III

Pelletstype IV

Olive pit Shell ofpine nuts

Almondshell

As

PM10 mass fractions of trace elements (wt.%)

Standards need to be established in the EU for elemental composition of commercial wood pellets and chips to avoid the inclusion of extraneous materials. Only Germany has standards containing extensive trace element limits.

Page 20: AIRUSE LIFE+: Biomass burning emission factors and chemical profiles in Southern Europe Fulvio Amato C.A. Alves, E. Vicente, C. Gonçalves, M. Duarte, L

Average OC-normalised concentrations of some tracers (mg/g OC)

Other organic tracers

Tracers Equipment Softwood Hardwood

Vanillic acid Fireplace 2.01 1.58

Traditional woodstove 8.26 2.73

Eco-labelled stove 15.0 7.79

Syringic acid Fireplace 0.07 7.77

Traditional woodstove 0.18 6.59

Eco-labelled stove 1.75 29.9

Stigmasterol Fireplace --- 0.61

Traditional woodstove --- 0.28

Eco-labelled stove --- 0.43

Retene Fireplace 3.99 0.11

Traditional woodstove 9.75 0.19

Eco-labelled stove 14.3 0.15

Page 21: AIRUSE LIFE+: Biomass burning emission factors and chemical profiles in Southern Europe Fulvio Amato C.A. Alves, E. Vicente, C. Gonçalves, M. Duarte, L

21

Conclusions (1)

Chemically treated material should not be allowed in any quality class of pellets; all pellets sold at the market must have quality certification.

Emission requirements for the eco-labelling or certification of small-scale combustion appliances must be mandatory in all countries. Traditional residential appliances should be replaced by certified equipment.

www.airuse.eu provides updated and speciated EFs (including condensables), for several domestic heating appliances and fuel types (softwood, hardwood, pellets, alternative agrofuels)

Page 22: AIRUSE LIFE+: Biomass burning emission factors and chemical profiles in Southern Europe Fulvio Amato C.A. Alves, E. Vicente, C. Gonçalves, M. Duarte, L

22

Conclusions (2)

Some of the identified organic compounds can be used as tracers of biomass burning and to distinguish between soft- or hardwood ( syringyl and vanillyn compounds, retene, stigmasterol).

Levoglucosan and their stereoisomers are not formed at the higher temperatures achieved in efficient, automatically fired, combustion aplliances. Good tracer only for traditional, batch operated, devices.

Differences in source profiles of organic compounds between wood types and combustion appliances deserves consideration in receptor modelling techniques, such as CMB, to apportion the contribution of biomass burning to ambient aerosol concentrations.

Page 23: AIRUSE LIFE+: Biomass burning emission factors and chemical profiles in Southern Europe Fulvio Amato C.A. Alves, E. Vicente, C. Gonçalves, M. Duarte, L

Thank you very much for your attention

[email protected]@ua.pt

Page 24: AIRUSE LIFE+: Biomass burning emission factors and chemical profiles in Southern Europe Fulvio Amato C.A. Alves, E. Vicente, C. Gonçalves, M. Duarte, L

Other organic tracers

Average OC-normalised concentrations of RESIN ACIDS (mg/g OC)

RESIN ACIDS Equipment Softwood Hardwood

Pimaric acid Fireplace 218 6.90

Traditional woodstove 146 10.2

Eco-labelled stove 4.70 ---

Isopimaric acid Fireplace 24.0 0.87

Traditional woodstove 17.8 2.01

Eco-labelled stove 31.2 0.32

Abietic acid Fireplace 19.2 0.40

Traditional woodstove 12.0 3.34

Eco-labelled stove 1.50 0.30

Dehydroabietic acid Fireplace 187 8.84

Traditional woodstove 119 7.17

Eco-labelled stove 5.44 0.12

Page 25: AIRUSE LIFE+: Biomass burning emission factors and chemical profiles in Southern Europe Fulvio Amato C.A. Alves, E. Vicente, C. Gonçalves, M. Duarte, L

25

0

5

10

15

20

25

Vanillin Vanillic acid Syringic acid Coniferylalcohol

Isopimaric acid Dehydroabieticacid

Abietic acid

µg

com

pou

nd

mg-1

OC

Pellets type I

Pellets type II

Pellets type III

Pellets type IV

Olive pit

Shell of pine nuts

Almond shell

Other organic tracers – automatically fed appliance