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Environmental fate & pathways

Henry's Law constant

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Endpoint:
Henry's law constant
Type of information:
calculation (if not (Q)SAR)
Remarks:
Estimated by calculation
Adequacy of study:
key study
Study period:
2013
Reliability:
2 (reliable with restrictions)
Rationale for reliability incl. deficiencies:
other: Episuite modelling, using vapour pressure - and water solubility data from OECD SIDS (2004)
Qualifier:
according to guideline
Guideline:
other: Episuite: Henrywin v3.10
H:
ca. 0 Pa m³/mol
Temp.:
25 °C
Remarks on result:
other: calculated value: 1.141 E-11 atm m3/mol
Conclusions:
From the water surface, the substance will not evaporate into the atmosphere.
Executive summary:

The EPISuiteTM calculated Henry's law constant of maleic anhydride of 1.141E-11 atm-m³/mole suggests that the substance will not evaporate from water surfaces to the air.

Endpoint:
Henry's law constant
Type of information:
calculation (if not (Q)SAR)
Remarks:
Estimated by calculation
Adequacy of study:
supporting study
Reliability:
2 (reliable with restrictions)
Rationale for reliability incl. deficiencies:
accepted calculation method
Remarks:
Calculated by using vapour pressure and water solubility.
Qualifier:
no guideline required
Principles of method if other than guideline:
calculated from water solubility and vapour pressure
GLP compliance:
no
H:
0 Pa m³/mol
Temp.:
25 °C
Conclusions:
Maleic acid will not evaporate from water surfaces.
Executive summary:

The Henry's law constant calculated (SRC HENRYWIN v3.20) for maleic acid of 0.000001 Pa*m³/mol indicates that maleic acid will not evaporate from water surfaces.

Endpoint:
Henry's law constant
Type of information:
read-across from supporting substance (structural analogue or surrogate)
Remarks:
Estimated by calculation
Justification for type of information:
Upon contact with water, maleic anhydride hydrolyses rapidly (DT50 = 0.3 min), forming maleic acid (Bunton et al., 1963). This constitutes almost instantaneous abiotic degradation, particularly in comparison to the residence/transport times in the wastewater stream. Therefore, both sewage treatment plants and subsequently surface waters will be exposed to maleic acid (if at all) instead of maleic anhydride. Accordingly, read-across of environmental effects from maleic acid to maleic anhydride is justified.
Reason / purpose for cross-reference:
read-across source
H:
0 Pa m³/mol
Temp.:
25 °C
Conclusions:
Maleic acid will not evaporate from water surfaces.
Executive summary:

The Henry's law constant calculated (SRC HENRYWIN v3.20) for maleic acid of 0.000001 Pa*m³/mol indicates that maleic acid will not evaporate from water surfaces.

 

This information for maleic acid is used in a read-across approach in the assessment of the target substance maleic anhydride. Upon contact with water, maleic anhydride hydrolyses rapidly (DT50 = 0.3 min), forming maleic acid. Therefore, read-across from maleic acid to maleic anhydride is justified.

 

Description of key information

From the water surface, the substance will not evaporate into the atmosphere.

The calculated Henry's law constant of maleic anhydride of 1.141E-11 atm-m³/mole suggests that the substance will not evaporate from water surfaces to the air.

Key value for chemical safety assessment

Henry's law constant (H) (in Pa m³/mol):
0
at the temperature of:
25 °C

Additional information

The calculated Henry's law constant of maleic anhydride of 1.141E-11 atm-m³/mole suggests that the substance will not evaporate from water surfaces to the air (SRC HENRYWIN v3.10, 2009). However, since the substance rapidly hydrolyses in contact with water forming maleic acid, the product of hydrolysis should be considered when evaluating the fugacity of the substance. The Henry's law constant calculated for maleic acid of 0.000001 Pa*m³/mol indicates that maleic acid will not evaporate from water surfaces (SRC HENRYWIN v3.20, BASF 2009).

 

Maleic anhydride and maleic acid are readily biodegraded under aerobic conditions in sewage sludge, and are expected to biodegrade in soil and water as well. Fugacity-based fate and transport modelling suggest that maleic anhydride, hydrolyzed to maleic acid in water and under humid conditions, will partition primarily to water. Level III fugacity modelling indicates water as the primary compartment for distribution (air 0.3%, water 59%, soil 40.6%, sediment 0.02%) (OECD, 2004).