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Diss Factsheets

Environmental fate & pathways

Distribution modelling

Currently viewing:

Administrative data

Endpoint:
distribution modelling
Type of information:
experimental study
Adequacy of study:
supporting study
Study period:
1996
Reliability:
2 (reliable with restrictions)
Rationale for reliability incl. deficiencies:
other: Model considered reliable and the main basis for fugacity modelling.

Data source

Referenceopen allclose all

Reference Type:
publication
Title:
Evaluating the environmental fate of a variety of types of chemicals using the EQC model.
Author:
Mackay, D. DiGuardo, A., Paterson, S. and Cowan, C.
Year:
1996
Bibliographic source:
Env. Toxicol. Chem. 15(9):1627-1637.
Reference Type:
secondary source
Title:
No information
Author:
Trent University
Year:
2009
Bibliographic source:
http://www.trentu.ca/academic/aminss/envmodel/EQCD.html
Reference Type:
publication
Title:
Multimedia Environmental models, the fugacity approach-second edition
Author:
Mackay D
Year:
2001
Bibliographic source:
Lewis, Boca Raton

Materials and methods

Model:
calculation according to Mackay, Level III
Calculation programme:
Mackay fugacity model III version 2.80.1
Release year:
2 004
Media:
air - biota - sediment(s) - soil - water

Test material

Constituent 1
Chemical structure
Reference substance name:
Isopropyl acetate
EC Number:
203-561-1
EC Name:
Isopropyl acetate
Cas Number:
108-21-4
Molecular formula:
C5H10O2
IUPAC Name:
isopropyl acetate
Details on test material:
not applicable.

Study design

Test substance input data:
All physichemical data as per section 4.
- Reaction half-life estimates (all from EPIWEB 4)
- Air: 75hr
- Water: 360 hr
- Soil: 720hr
- Sediment: 3240hr
Environmental properties:
EU TGD defaults for compartment sizes.

Results and discussion

Percent distribution in media

Air (%):
23.2
Water (%):
35.9
Soil (%):
40.7
Sediment (%):
0.31
Susp. sediment (%):
0
Biota (%):
0
Aerosol (%):
0

Any other information on results incl. tables

Results above are for first scenario shown below.

Results shown below are for emissions of ~10,000tpa with different potential emission patterns for comparison.

Emission to air (kg/hr)

333

1000

0

0

Emission to water (kg/hr)

333

0

1000

0

Emission to soil (kg/hr

333

0

0

1000

Air concentration (ug/m3)

.62

.73

0.53

0.60

Water concentration (ug/l)

10.6

0.09

26.6

5.3

Sediment concentration (ug/kg)

2.2

0.02

5.4

1.1

Soil concentration (ug/kg)

2.9

0.03

0.03

8.7

From this it can be concluded that air concentrations are effectively independent of emission compartment, emissions to the water compartment remain in the same compartment (with some partitioning to sediment) whilst emissions to soil partition to all three compartments.

Applicant's summary and conclusion

Conclusions:
Environmental background levels of ethyl acetate at regional and continental levels from emissions of ethanol during use are not likely to be of concern.
Executive summary:

Level III fugacity calculations based on realistic emissions quantities predict that environmental levels of ethyl acetate will be very low (<25ug/l in water, <1.5ug/kg in soil, <2.5ug/kg in sediment and <3.5ug/m3 in air.)