Registration Dossier

Data platform availability banner - registered substances factsheets

Please be aware that this old REACH registration data factsheet is no longer maintained; it remains frozen as of 19th May 2023.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

Environmental fate & pathways

Adsorption / desorption

Currently viewing:

Administrative data

Link to relevant study record(s)

Reference
Endpoint:
adsorption / desorption: screening
Remarks:
adsorption
Type of information:
calculation (if not (Q)SAR)
Adequacy of study:
key study
Study period:
2019
Reliability:
2 (reliable with restrictions)
Rationale for reliability incl. deficiencies:
other: Scientifically accepted estimation method
Reason / purpose for cross-reference:
other: log Pn input parameter for the calculation
Reason / purpose for cross-reference:
other: pKa input parameter for the calculation
Qualifier:
no guideline followed
Principles of method if other than guideline:
Calculation method determining the Koc for charged molecules according to Franco & Trapp (2008), Franco, Fu and Trapp (2009) and additional information via personal communication from A. Franco (2010).
GLP compliance:
no
Type of method:
other: calculation of log Koc for ionized molecule
Media:
soil
Radiolabelling:
no
Test temperature:
not applicable, calculation
Details on study design: HPLC method:
not applicable, calculation
Analytical monitoring:
not required
Details on sampling:
not applicable, calculation
Details on matrix:
not applicable, calculation
Details on test conditions:
not applicable, calculation
Computational methods:
The following input parameters were used for the calculation:
1. Test substance is an acid.

2. Octanol-water partition coefficient for the neutral molecule, Pn= Kow (neutral). This value was determined in a reliable study (OECD 117) at acidic pH (pH 3.0), such that nearly 100% of molecules were in the neutral, non-dissociated state.
log Kow (neutral) = logPn = 3.2

3. Dissociation constant
pKa was determined in a reliable study (OECD 112, titration method) to be 4.8.
pKa = 4.8

For further details, see IUCLID section "Any other information on materials and methods incl. tables".
Sample No.:
#1
Type:
Koc
Value:
79.5 L/kg
pH:
8
Temp.:
20 °C
Matrix:
Soil
Sample No.:
#2
Type:
Koc
Value:
92.9 L/kg
pH:
7
Temp.:
20 °C
Matrix:
Soil
Key result
Sample No.:
#5
Type:
Koc
Value:
122.9 L/kg
pH:
6.5
Temp.:
20 °C
Matrix:
Soil
Sample No.:
#3
Type:
Koc
Value:
200.6 L/kg
pH:
6
Temp.:
20 °C
Matrix:
Soil
Sample No.:
#4
Type:
Koc
Value:
620.4 L/kg
pH:
4.5
Temp.:
20 °C
Matrix:
Soil
Details on results (HPLC method):
not applicable, calculation
Statistics:
not applicable, calculation
Validity criteria fulfilled:
not applicable
Remarks:
estimation method
Conclusions:
The Koc for 3,5,5-trimethylhexanoic acid was estimated by calculation as a function of soil pH using the method of Franco, Fu and Trapp (2009), with the following results (OXEA, 2019):
pH 8.0: 79.5 L/kg
pH 7.0: 92.9 L/kg
pH 6.5: 122.9 L/kg
pH 6.0: 200.6 L/kg
pH 4.5: 620.4 L/kg
Executive summary:

The Koc for 3,5,5-trimethylhexanoic acid was estimated by calculation as a function of soil pH using the method of Franco, Fu and Trapp (2009).

The model considers as the main parameters governing adsorption the log Kow of the neutral compound (logPn = 3.2, determined experimentally) as well as the dissociation degree, characterized by pKa (4.8, determined experimentally) and the prevailing soil pH. As such, adsorption of a compound to soil is broken down into the sum of adsorption of the neutral species multiplied by the non-dissociated fraction and the adsorption of the ionized species multiplied by the dissociated (ionized) fraction at a given soil pH. The model allows calculation of Koc as a function of soil pH, with the following results obtained for 3,5,5-trimethylhexanoic acid (OXEA, 2019):

pH 8.0:               79.5 L/kg

pH 7.0:               92.9 L/kg

pH 6.5:               122.9 L/kg

pH 6.0:               200.6 L/kg

pH 4.5:               620.4 L/kg

For environmental exposure and risk assessment, the value of (rounded) 123 L/kg obtained for Koc at soil pH 6.5 is regarded to be most relevant, because European soils are predominantly of neutral to slightly acidic pH.

Description of key information

The Koc for 3,5,5-trimethylhexanoic acid was estimated by calculation as a function of soil pH using the method of Franco, Fu and Trapp (2009), with the following results (OXEA, 2019):

pH 8.0:       79.5 L/kg

pH 7.0:       92.9 L/kg

pH 6.5:       122.9 L/kg - key value for agricultural soils in Europe

pH 6.0:       200.6 L/kg

pH 4.5:       620.4 L/kg

Key value for chemical safety assessment

Koc at 20 °C:
123

Additional information

The Koc for 3,5,5-trimethylhexanoic acid was estimated by calculation as a function of soil pH using the method of Franco, Fu and Trapp (2009).

The model considers as the main parameters governing adsorption the log Kow of the neutral compound (logPn = 3.2, determined experimentally) as well as the dissociation degree, characterized by pKa (4.8, determined experimentally) and the prevailing soil pH. As such, adsorption of a compound to soil is broken down into the sum of adsorption of the neutral species multiplied by the non-dissociated fraction and the adsorption of the ionized species multiplied by the dissociated (ionized) fraction at a given soil pH. The model allows calculation of Koc as a function of soil pH, with the following results obtained for 3,5,5-trimethylhexanoic acid (OXEA, 2019):

 

pH 8.0:               79.5 L/kg

pH 7.0:               92.9 L/kg

pH 6.5:               122.9 L/kg

pH 6.0:               200.6 L/kg

pH 4.5:               620.4 L/kg

 

For environmental exposure and risk assessment, the value of (rounded) 123 L/kg obtained for Koc at soil pH 6.5 is regarded to be most relevant, because European soils are predominantly of neutral to slightly acidic pH.