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Please be aware that this old REACH registration data factsheet is no longer maintained; it remains frozen as of 19th May 2023.

The new ECHA CHEM database has been released by ECHA, and it now contains all REACH registration data. There are more details on the transition of ECHA's published data to ECHA CHEM here.

Diss Factsheets

Administrative data

Endpoint:
distribution modelling
Type of information:
calculation (if not (Q)SAR)
Remarks:
Migrated phrase: estimated by calculation
Adequacy of study:
key study
Study period:
2003
Reliability:
2 (reliable with restrictions)
Rationale for reliability incl. deficiencies:
other: Not GLP, accepted calculation method
Cross-referenceopen allclose all
Reason / purpose for cross-reference:
reference to same study
Reason / purpose for cross-reference:
reference to other study

Data source

Reference
Reference Type:
other company data
Title:
Unnamed
Year:
2003

Materials and methods

Model:
other: EPIWIN fugacity Level III Model Program
Calculation programme:
Prediction of Equilibrium Environmental Distribution
Release year:
1 999
Media:
other: air-water-soil-sediment

Test material

Constituent 1
Chemical structure
Reference substance name:
2-nitropropane
EC Number:
201-209-1
EC Name:
2-nitropropane
Cas Number:
79-46-9
Molecular formula:
C3H7NO2
IUPAC Name:
2-nitropropane
Details on test material:
No data

Study design

Test substance input data:
See below
Environmental properties:
See below

Results and discussion

Percent distribution in media

Air (%):
70.5
Water (%):
29
Soil (%):
0.6
Other distribution results:
Level I: Predicted equilibrium distribution among air, water, soil, and sediments

Emission Scenario: 100,000 kg total emissions
Percentage and amount distributed to
Air Water Soil Sediment

70.5% 29.0% 0.6% <0.1%
7.0 x 10^4 kg 2.9 x 10^4 kg 5.7 x 10^2 kg 13 kg

This substance has high water solubility, moderate vapor pressure, and low log Kow. In the absence of advective and reactive processes, these physical properties dictate that the substance will be distributed primarily among the air and water compartments at equilibrium. The substance has a low potential for adsorption to soil or sediments, and moderate potential to volatilize from water.

Level III: Predicted distribution among air, water, soil, and sediments

Emission Scenario
Percentage and amount distributed

1,000 kg/hr to Air (most likely scenario)
Air 91.8%
2.0 x 10^3 kg
Water 5.0%
1.1 x 10^2 kg
Soil 3.2%
70 kg
Sediment <0.1%
<1 kg
Residence Time (days) 0.1 (without advection=98)

1,000 kg/hr to Water
Air 0.2%
8.1 x 10^2 kg
Water 99.8%
5.0 x 10^5 kg
Soil <0.1%
29 kg
Sediment <0.1%
2.4 x 10^2 kg
Residence Time (days) 21 (without advection=216)


1,000 kg/hr to Soil
Air 0.3%
1.6 x 103 kg
Water 32.2%
1.5 x 105 kg
Soil 67.5%
3.2 x 105 kg
Sediment <0.1%
76 kg
Residence Time (days) 20 (without advection=325)


1,000 kg/hr simultaneously to Air, Water, and Soil Air 0.4%
4.4 x 103 kg
Water 66.6%
6.5 x 105 kg
Soil 32.9%
3.2 x 105 kg
Sediment <0.1%
3.2 x 102 kg
Residence Time (days) 14 (without advection=257)

Any other information on results incl. tables

None

Applicant's summary and conclusion

Conclusions:
This substance has high water solubility, moderate vapor pressure, and low log Kow. The substance therefore has a low potential for adsorption to soil or sediments, and moderate potential to volatilize from water or soil to the atmosphere. If released to air (the most probable emission route), 2-nitropropane will remain primarily in the atmospheric compartment, with some deposition to surface water and soil. 2-Nitropropane is slowly reacted in the atmosphere, and therefore advection is the dominant process affecting atmospheric fate. If released directly to water, the substance will remain dissolved in water; 2-nitropropane may undergo limited biodegradation under some conditions. If released to soil, 2-nitropropane will be primarily dissolved in soil pore water (groundwater); 2-nitropropane may undergo limited biodegradation under some conditions
Executive summary:

None