Development of an improved product based approach … of an improved product based approach for the...

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Development of an improved product based approach for the calculation of NMVOC emissions from solvent use in Germany and uncertainty analysis Jochen Theloke University of Stuttgart San Diego/JT/30/04/03

Transcript of Development of an improved product based approach … of an improved product based approach for the...

Development of an improved product based approach for the calculation of

NMVOC emissions from solvent use in Germany and uncertainty analysis

Jochen ThelokeUniversity of Stuttgart

San Diego/JT/30/04/03

Contents

1. Introduction

2. Definitions

3. Method

4. Results

5. Uncertainties

6. Conclusion

San Diego/JT/30/04/03

Solvent use was the largest NMVOC emissionsource group in Germany in 1998

Sum: 2 436 kt

combustion sources from industry and

power plants 1%

small combustion plants/households

3%

traffic27%

solvent use36%

production processes8%

biogenic 27%

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VOC - Volatile Organic Compound

“Volatile organic compound shall mean any organic compound having at 293,15 K a vapour pressure of 0,01 kPa or more, or having a corresponding volatility under the particular condition of use.”

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Solvent Use• Application of solvents

• Application of solvent containing products

• Production of solvent containing products

• Propellants (Propane/Butane)

• Extraction of fat, edible and non edible oil (n-hexane)

• Cooling agents (HFHC`s, HFCHC`s, alcohols)

• Softening agents (Phtalates)

• Concrete additives

• Application of thinners

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Method for the calculation of emissions from solvent use

importsolvent x

exportsolvent x

productionsolvent x

inlandconsumption

solvent x

manufacturechem.

product y

importchem.

product y

exportchem.

product y

inland consumptionchem.

product y

emissionreduction techniques

other pathways

Solvent Balance Manufacture Consumption

emissions

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870 Gg NMVOC emitted from solvent use in Germany 2000

thinner without specific

application26%

Degreasing, dry cleaning and electronics

4%

Products manufacturing or

processing5%

Preservation of wood

4%

Paint application25%

Domestic solvent use (other than

paint application)13%

other14%

printing industry9%

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Paint application (sum 223 Gg)

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Manufacture of automobiles

6%

Synthetics4%

Plate emballages

3%

other paint applications

16%

Wood16%

constructions and buildings-professional

14%Car repairing

10%

Corrosion-inhibiting

primer8%

Mechanical engineering

8%

Do It Yourself 6%

white goods3%

Boat building2%

Prefabricated units

2% road marking varnishes

2%

The domestic consumption of thinners increasedcontinously in the last years

100

150

200

250

300

1992 1994 1996 1998 2000 2002Year

Th

inn

er C

on

sum

pti

on

[G

g/y

]

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NMVOC emissions from domestic solvent use (sum 105 Gg)

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coolant and fire extinguisher

2%aftershave, hygienic water and perfume

19%

hairspray19%

personal hygiene products

22%

antifreeze for cars24%

detergents14%

*) pure Ethanol

NMVOC emissions from domestic solvent use

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Solvent consumption

Emission factor

NMVOC emissions

Mg/y % Mg/y

Antifreeze for cars 51 100 50 25 550

Detergent for dishwasher 9 900 3 300

Detergent for car washing 10 900 3 330

Detergent for washing-machine 12 660 3 380

Alcohol consumption 750 000* 1 7 500

Hairsprays 19 350 95 18 400

Personal hygiene products 24 400 95 23 150

Toilet water 6 100 95 5 800

Aftershave 5 600 95 5 300

Perfume 2 500 95 2 400

Deodorants 1 180 95 1 120

NMVOC emissions from printing processes (sum 80 Gg)

Rotogravure printing14,8%

Offset printing39,4%Offset-Heatset-

printing21,9%

Letterpress printing

0,6%

Package printing20,1%

Screen printing3,1%

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Speciation of the NMVOC emissions from solvent use to substance classes

glycol derivates8,5%

alcohols26,3%

aromatics21,7%aliphatics

20,8%

ketones6,2%

halogenated hydrocarbons

1,5%other2,5%

terpenes1,2%

aldehydes0,02%

organic acids0,1%

ethers1,5%

esters9,8%

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Verification - Plausibility check

Substance classes

Domestic consumption [t]

(solvent industry)

Domestic consumption

[t](own

estimation)

Deviation[%]

Aliphatics 300 000 280 000 - 6,7Aromatics 250 000 286 000 +14,4Terpenes 10 000Halogenic hydrocarbons 35 000 35 000Alcohols 360 000 316 000 -12,2-Ethanol 50 000 85 000-Isopropanol 250 000 144 000-n-Propanol 40 000 200-n/i-Butanol 10 000 56 000Glycolderivates 75 000 78 000 +4,0Esters 75 000 76 000 +1,3Ketones 60 000 61 000 +1,7Ethers 30 000 29 000 -3,3Aldehydes 200Organic Acids 800Softening agents 225 000Other VOC`s 65 000Sum (Sum of bold faced substance classes)

1 185 000 1 161 000 -2,0

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Assessment and calculation of uncertainties of NMVOC emissions from solvent use - Methods

Uncertainty analysis

ØQualitative assessmentØ Semiquantitative methods

Quantitative methods

Ø Error propagationØMonte-Carlo simulation

Verification

Ø Plausibility checksØ Evaluation experiments

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Semi-quantitative methods

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Uncertainty bandwith

Source groups

Yearly

emissions

Spatial

resolution

Tem

poral resolution

VO

C

speciation

Paint application 2-3 3 3-4 3 Domestic solvent use 3 2 5 2 Printing processes 2 2 3 2 Synthetics processing 4 4 4 3 Metal degreasing 4 4 4 4 Other source groups 3 3 3-4 4 Solvent use Complete assessment

3 3 4 3

Monte-Carlo simulations for emissions from paintapplication - Preliminary results

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0

1

2

3

4

180 200 220 240 260 280 300Emissions in Gg per year

Val

ues

in

10^

-5

Mean value: 231 Gg

Calculated : 222 Gg (without uncertainty

analysis)209 255

90 % of the calculated values between 209 Gg

and 255 Gg

Germany 2000

Verification - Results of city experiments

0,1 1 10

2,3-Dimethylpentane

Ethane

Ethine

n-Heptane

3-Methylhexane

2-Methylhexane

Ethene

3-Methylpentane

Benzene

2-Methylpentane

Propane

Propene

Ethylbenzene

n-Octane

i-Pentane

EVA

ESQUIF

(HCi/CO)modelled / (HCi/CO)measured

0,5 2

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0,1 1 10 100

m/p-Xylene

i-Butane

n-Pentane

Toluene

1,2,4-TMB

o-Xylene

n-Butane

n-Hexane

1,3,5-TMB

Propylbenzene

n-Nonane

n-Decane

(HCi/CO)modelled / (HCi/CO)measured

EVA

ESQUIF

0,5 2

Verification - Results of city experiments

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Conclusion• Emissions from solvent use was the largest NMVOC emission source

group in Germany in 1998

• The developed improved product based approach for the calculation of NMVOC emissions from solvent use in Germany was further developed and applied for 2000

• The method can in principle also be used for other OECD countries

• Nearly 75% of emissions from solvent use are caused by paint application, application of thinners, domestic solvent use and printing processes

• Nearly 50% of emitted solvents are oxygen containing NMVOC`s

• A plausibility check between a solvent based approach and a product based approach yielded a good agreement

• The results of city experiments in Augsburg and Paris indicates thatfurther experiments especially with measurements of OVOC are required

• Monte-Carlo simulation appears to be a promising approach for thequantification of uncertainties from solvent use emissions

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